Soil Biology
Dilfuza Egamberdieva
Smriti Shrivastava
Ajit Varma Editors
Plant-GrowthPromoting
Rhizobacteria
(PGPR) and
Medicinal Plants
Soil Biology
Volume 42
Series Editor
Ajit Varma, Amity Institute of Microbial Technology,
Amity University Uttar Pradesh, Noida, UP, India
mkumar9@amity.edu
More information about this series at
http://www.springer.com/series/5138
mkumar9@amity.edu
Dilfuza Egamberdieva • Smriti Shrivastava •
Ajit Varma
Editors
Plant-Growth-Promoting
Rhizobacteria (PGPR) and
Medicinal Plants
mkumar9@amity.edu
Editors
Dilfuza Egamberdieva
Department of Biotechnology and
Microbiology, Faculty of Biology
and Soil Science
National University of Uzbekistan
Tashkent, Uzbekistan
Smriti Shrivastava
Ajit Varma
Amity Institute of Microbial Technology
(AIMT)
Amity University Uttar Pradesh
Noida, Uttar Pradesh, India
ISSN 1613-3382
ISSN 2196-4831 (electronic)
ISBN 978-3-319-13400-0
ISBN 978-3-319-13401-7 (eBook)
DOI 10.1007/978-3-319-13401-7
Springer Cham Heidelberg New York Dordrecht London
Library of Congress Control Number: 2015931076
© Springer International Publishing Switzerland 2015
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mkumar9@amity.edu
Foreword
The editors of the volume “PGPR and Medicinal Plants” asked me to write the
Foreword to this book. I have gone through the volume contents and some chapters,
which prompted me to write the Foreword. Microorganisms are abundantly distributed in the soil, ranging from bacteria, actinomycetes, fungi, algae, cyanobacteria,
and protozoa. These microbes contribute many beneficial elements, like carbon,
sulfur, phosphorus, and nitrogen, to the soil by taking part in the nutrient cycle. The
zone of contact between the root and soil is the rhizosphere. This region has intense
activity and concentration of microbes and is considered vital for plant vigor and
full development to maturity. Plant growth and development promoting
rhizobacteria (PGPR) are present in the vicinity of the root system and at times
adhering to the root. Such bacteria have been applied to a wide range of agriculturally important crops for the purpose of plant growth promotion, including
emergence seed germination and value addition.
The influence of root exudates on the proliferation of soil microorganisms
around and inside roots as well as interactions between soil microorganisms,
rhizosphere colonies, and plant hosts have been widely studied. Studies based on
molecular techniques have estimated about 4,000 microbial species per gram of soil
samples. Powerful methods of estimation provide only the crudest measure of its
magnitude. Nonetheless, many such estimates exist, suggesting that a single gram
of soil may contain over 10 billion microbial cells and more than 1,800 bacterial
species (Zhang et al. 2008).
PGPRs are well established to colonize plant roots and stimulate plant growth.
They serve the purpose of being used as biofertilizers, plant growth regulators, and
biotic elicitors and promote plant growth by several mechanisms such as phosphorus solubilization, production of volatile organic compounds, induction of systemic
disease resistance, nitrogen fixation, maintenance of soil fertility and nutrient
uptake, and resistance of water stress. How to classify the newly found diverse
microorganisms remains an open question. As molecular methods, such as whole
genome sequencing, are more widely applied to characterize bacterial diversity, our
ability to make taxonomic sense of what we learn is severely challenged.
v
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vi
Foreword
From a structural, functional, and taxonomical perspective, soil bacteria are an
impressively diverse group. It is well known that they vary from free-living bacteria
to single fungi capable of extending their growth over a large distance of multiple
square kilometers. Still, we know little about soil bacteria because of the difficulties
associated with their cultivation (Witzany 2011). Only a very limited number of
species have been classified because less than 1 % grow easily on nutrient agar
plates. Consequently, scientists depend on indirect analytical methodologies,
mainly biochemical markers, as well as on measures of the metabolic activity in
either entire soil microbial communities or selected segments of such communities.
Research has underscored the essential functions that microorganisms play in soil
quality. This is particularly evident in the important areas of the cycling of essential
nutrients, the decomposition of organic materials, the regulation of essential nutrients, the decomposition of organic materials, and the regulation of the productive
capacity of plant life, in the dynamics of soil microbial community considered
holistically.
Restoration-related research into the roles of microbes has branched off in two
principal directions: investigation that describes conditions and target locations in
the ecosystem and research that focuses on system manipulation. This second
direction stresses the creative manipulation of system components to facilitate
more rapid arrival at desired systematic states through overcoming challenges
posed by the paucity of mutualists and other positive components or by the presence
of invasive plants and other negative influences.
Plant–PGPR associations are mediated through an exchange of chemical metabolites. Root exudates provide energy-rich organic acids, sugars, and amino acids
that are metabolized within a short time by soil microorganisms, while specialized
microorganisms generate an array of biologically active compounds that elicit plant
growth promotion.
Fuqua et al. (1996, 2002) defined the term “quorum sensing” (QS) as the
bacterial regulatory process that couples gene expression to cell density. This
process is mediated by low-molecular-weight signal molecules that are synthesized
by bacterial population and accumulate in the environment. The presence of
molecules is sensed by bacteria and induces either the expression or repression of
QS-regulated gene(s). Earlier it was thought that bacteria are unable to communicate. Investigations on QS have drastically changed this view that biologists had on
bacteria. Indeed, bacteria not only communicate but they do so in multiple languages using QS signals.
Considering that several plant pathogenic bacteria also rely upon QS molecules
to regulate virulence or virulence-related functions, the same evolutionary reading
provides potential explanation for the plant capacity to detect the presence of the
bacterial signal molecules. The general occurrence of functions capable of inducing
QS signal degradation in fungi and bacteria, including noncultivable ones, strongly
suggests that these functions might play a significant biological role. The QS
strategies have been developed and present a multifaceted value. They may be
developed to prevent or limit biofilm functions on several structures, or the impact
of bacterial diseases in plants.
mkumar9@amity.edu
Foreword
vii
The moot questions remain: how do microbes perceive environmental and
metabolic signals and how do they integrate this information to modulate gene
expression? Genome-wide comparisons indicate that the ability to accurately sense
the environment and to change gene expression accordingly is critical to the
bacteria that spend at least a part of their life cycle in the complex and uncertain
environments of soil. Quorum sensing (QS) is one of the mechanisms by which
microbes change global patterns of gene expression in response to increases in their
population densities within a diffusion-limited environment.
The time is ripe to commercialize the products by establishing strong linkages
between academic and industries. The volume “PGPR and Medicinal Plants” edited
by eminent microbiologists Drs. Dilfuza Egamberdieva, Smriti Srivastava, and Ajit
Varma presents innovative ideas and thoughts . I congratulate them. This volume
should be useful for active researchers, teachers, and scientists. It is published as
part of the Soil Biology Series by Springer, Heidelberg, Germany.
Secunderabad, India
K.V.V. Sairam
References
Fuqua C, Greenberg EP (2002) Listening in on bacteria: acylhomoserinelactone signaling.
Nat Rev Mol Cell Biol 3:685–695
Fuqua C, Wanians SC, Greenberg EP (1996) Census and consensus in bacterial ecosystems:
the LuxR-LuxI family of quorum-sensing transcriptional regulators. Annu Rev Microbiol
50:727–751
Witzany G (2011) Biocommunication in soil microorganisms. In: Ajit Varma (ed) Soil biology
series, vol 23. Springer, Berlin
Zhang H, Xie X et al (2008) Soil bacteria augment Arabidopsis photosynthesis by decreasing
glucose and abscisic acid levels in plant. Planta J 56:264–273
mkumar9@amity.edu
ThiS is a FM Blank Page
mkumar9@amity.edu
Preface
This book was conceptualized during finalizing the Soil Biology volume “Root
engineering: Basic concepts and Applications” edited by Asuncion Morte and Ajit
Varma (2014). Soon it was realized that the basic functions of roots are heavily
regulated by the microorganisms around them and thus a new volume “PGPR and
Medicinal Plants” was depicted. The prime aim and objective of this volume is to
highlight various aspects of action, effect, and application of PGPRs in medicinal
plants to lend a hand to scientists throughout the world working in this field.
The rhizosphere concept was first introduced by Hiltner (1904) to describe the
narrow zone of soil surrounding the roots where microbial populations are stimulated by root activities. The term “plant growth-promoting rhizobacteria (PGPR)”
was first used by Joseph W. Kloepper in the late 1970s and has become commonly
used in scientific literature. A large number of microorganisms such as bacteria,
fungi, protozoa, and algae coexist in the rhizosphere; however, the most abundant
organism is bacteria. Plants select those bacteria contributing most to their fitness
by releasing organic compounds through exudates creating a very selective environment where diversity is low. Since bacteria are the most abundant microorganisms in the rhizosphere, it is highly probable that they influence the plants’
physiology to a greater extent, especially considering their competitiveness in
root colonization, hence, referred as plant growth-promoting rhizobacteria
(PGPR). PGPRs are the group of microorganisms which colonize and have symbiotic relationship with the plant roots and promote plant growth via various plant
growth-promoting substances and also act as biofertilizers.
The world today comes up with a new ailment after every short span of time and
thus our requirement of medicines and drugs continues to amplify. Natural compounds are most preferred over synthetic drugs for curing diseases and these natural
compounds are variedly obtained from medicinal plants. All we need is to enhance
quality and quantity of plant secondary metabolites, which can be skillfully used for
drug production. Numerous plant growth-promoting rhizobacteria are well known
to exhibit beneficial effects on plenty of medicinal plants.
ix
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Preface
PGPRs have different relationships with different species of host plants, mainly
rhizospheric and endophytic. Rhizospheric relationships consist of the PGPRs that
colonize the surface of the root, or superficial intercellular spaces of the host plant,
often forming root nodules. The dominant species found in the rhizosphere is a
microbe from the genus Azospirillum. Endophytic relationships involve the PGPRs
residing and growing within the host plant in the apoplastic space. It is well
established that only 1–2 % of bacteria promote plant growth in the rhizosphere
while acting as PGPR. PGPRs have been known to be present within many different
bacterial taxa, among which most commercially industrial PGPRs are species of
Bacillus which form endospores that confer population stability during formulation
and storage of products. The main groups of PGPR can be found along with the phyla
Cyanobacteria, Actinobacteria, Bacteroidetes, Firmicutes, and Proteobacteria.
Fluorescent pseudomonads are identified to suppress soilborne fungal pathogens
by producing antifungal metabolites and by sequestering iron in the rhizosphere
through the release of iron-chelating siderophores, rendering it unavailable to other
organisms.
PGPRs have several applications like increasing the availability of nutrients in
the rhizosphere, increased root volume which is related to more nutrient absorption,
to stimulate plant growth, e.g., through the production of plant hormones, to control
or inhibit the activity of plant pathogens, to improve soil structure, and mineralization of organic pollutants, i.e., bioremediation of polluted soils, and are also used
as biofertilizers and also known for phytohormone production, phosphate solubilization, siderophore production, biocontrol agents, and biological fungicides, etc.
PGPRs are a healthier choice to improve the crop efficiency as well as quality.
PGPRs improve the chemical and microbial property of soil and enhance the
amount of plant enzymes for better defense mechanism in plant.
During the past couple of decades, the use of PGPRs for sustainable agriculture
has increased tremendously in various parts of the world. Significant increases in
growth and yield of agronomically important crops in response to inoculation with
PGPR have been repeatedly reported. Recent reports have identified several volatile
organic compounds produced by a variety of bacteria that promote plant growth and
induce systemic resistance in Arabidopsis thaliana. Beneficial effects of PGPRs
have also been attributed to shifts in the microbial ecology of the rhizosphere.
Previous research has shown the practicality of introducing PGPR into commercial
peat-based substrates for vegetable production in order to increase plant vigor,
control root diseases, and increase yields. Results of tomato (Lycopersicon
esculentum) and pepper (Capsicum annuum) trials in Florida included significant
increases in tomato and pepper transplant growth during greenhouse production in
response to various formulations of PGPR tested. As a result of increased growth,
the time required to produce a standard sized transplant was reduced as were
greenhouse applications of fertilizer. Also, transplant vigor and survival in the
field were improved by PGPR treatments in both tomato and pepper. An overall
view on the salient functions of PGPRs is depicted in the diagram below.
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Preface
xi
Morphological and physiological changes in plants by application of PGPR leading to abiotic
stress tolerance [Adopted from Dutta and Khurana (2015)]
This volume is composed of 20 chapters, divided into 5 parts, encompassing
various aspects of effect of PGPRs on medicinal plants. The first chapter provides
an overview on PGPR and medicinal plants and their state of the art. The first
section of this book focuses on plant improvement and is composed of 5 chapters.
Chapter 2 provides a wide and comprehensive account on interaction of rhizosphere
microbes with medicinal plants. Chapter 3 covers the handsome story toward
enhancement of efficiency of medicinal and aromatic plants on interaction with
PGPRs, and Chap. 4 deliberates the usefulness of vermicompost and associated
microorganisms in enhancing soil health and agriculture productivity. Following
this Chap. 5 describes the effect of Arbuscular mycorrhizae fungus and plant
growth-promoting rhizobacteria of potential bioinoculants on growth, yield, and
forskolin content of Coleus forskohlii, and Chap. 6 beautifully describes emergence
and future facets of plant growth-promoting rhizobacteria upon interaction with
medicinal plants. The second part with Chaps. 7, 8, and 9 relates to alleviation of
plant stress tolerance with the help of PGPRs. The third section of this book focuses
on biological control activity of PGPRs. Chapters 10, 11, and 12 highlight the
ecological manifestation of rhizobacteria for curbing medicinal plant diseases,
mechanism and control of plant associated diseases, and role of PGPRs in increasing soil fertility and plant health, respectively. The fourth part of the book brilliantly
highlights some mechanisms of actions of PGPRs. It includes Chaps. 13–16 and
highlights systemic induction of secondary metabolites, new frontiers for
mkumar9@amity.edu
xii
Preface
phytochemicals, and rhizosphere microflora in advocacy of heavy metal tolerance
in plants. The last part, composed of Chaps. 17–20, evidently describes diversity
and characterization of PGPRs and also focuses locations like North West
Himalayas and Argentina.
It has been a pleasure to edit this book, primarily due to the stimulating
cooperation of the contributors. We wish to thank Hanna Hensler-Fritton and
Jutta Lindenborn at Springer, Heidelberg, for their generous assistance and patience
in finalizing the volume. Finally we give special thanks to our families––immediate
and extended––for their kind support and their incentive to put everything together.
Ajit Varma and Smriti Shrivastava are particularly very thankful to Dr. Ashok
K. Chauhan, Founder President of Ritanand Balved Education Foundation
(an umbrella organization of Amity Institution), New Delhi, for his kind support
and constant encouragement.
Tashkent, Uzbekistan
New Delhi, India
New Delhi, India
Dilfuza Egamberdieva
Smriti Shrivastava
Ajit Varma
References
Dutta S, Khurana SMP (2015) Plant growth promoting rhizobacteria (pgpr) for alleviating abiotic
stresses in medicinal plants. In: Egamberdieva D, Shrivastava S, Varma A (eds) Plant growthpromoting rhizobacteria (PGPR) and medicinal plants. Soil biology, vol 42. Springer,
Heidelberg
Hiltner L (1904) Über neuere Erfahrungen und Probleme auf dem Gebiete der Bodenbakteriologie
unter besonderer Berücksichtigung der Gründüngung und Brache. Arb DLG 98:59–78
Morte A, Varma A (eds) (2014) Root engineering: basic and applied concepts. Soil biology, vol
40. Springer, Heidelberg
mkumar9@amity.edu
Contents
1
Plant Growth-Promoting Rhizobacteria (PGPR) and Medicinal
Plants: The State of the Art . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Smriti Shrivastava, Dilfuza Egamberdieva, and Ajit Varma
Part I
Plant Improvement
2
Rhizosphere Microbes Interactions in Medicinal Plants . . . . . . . . .
Zakaria M. Solaiman and Hossain Md Anawar
3
Enhanced Efficiency of Medicinal and Aromatic Plants
by PGPRs . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Mansour Ghorbanpour, Mehrnaz Hatami, Khalil Kariman,
and Kazem Khavazi
4
5
6
1
Plant Growth-Promoting Microbes from Herbal
Vermicompost . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Rajendran Vijayabharathi, Arumugam Sathya, and Subramaniam
Gopalakrishnan
Effect of AM Fungi and Plant Growth-Promoting Rhizobacteria
(PGPR) Potential Bioinoculants on Growth and Yield
of Coleus forskohlii . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Uliyan Sakthivel and Balathandayutham Karthikeyan
19
43
71
89
Plant Growth-Promoting Rhizobacteria (PGPR): Emergence and
Future Facets in Medicinal Plants . . . . . . . . . . . . . . . . . . . . . . . . . . 109
Shivesh Sharma, Vasudha Singh, Vivek Kumar, Shikha Devi, Keshav
Prasad Shukla, Ashish Tiwari, Jyoti Singh, and Sandeep Bisht
xiii
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xiv
Contents
Part II
Alleviation Plant Stress
7
Alleviation of Abiotic Stress in Medicinal Plants by PGPR . . . . . . . 135
Sher Muhammad Shahzad, Muhammad Saleem Arif, Muhammad Ashraf,
Muhammad Abid, Muhammad Usman Ghazanfar, Muhammad Riaz,
Tahira Yasmeen, and Muhammad Awais Zahid
8
Plant Growth-Promoting Rhizobacteria for Alleviating Abiotic
Stresses in Medicinal Plants . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 167
Swarnalee Dutta and S.M. Paul Khurana
9
Efficiency of Phytohormone-Producing Pseudomonas to Improve
Salt Stress Tolerance in Jew’s Mallow (Corchorus olitorius L.) . . . . 201
Dilfuza Egamberdieva and Dilfuza Jabborova
Part III
Biological Control
10
Ecological Manipulations of Rhizobacteria for Curbing Medicinal
Plant Diseases . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 217
S.K. Singh and Rakesh Pathak
11
Mechanism of Prevention and Control of Medicinal
Plant-Associated Diseases . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 231
Ram Kumar Pundir and Pranay Jain
12
Role of PGPR in Soil Fertility and Plant Health . . . . . . . . . . . . . . . 247
Ram Prasad, Manoj Kumar, and Ajit Varma
Part IV
Mechanism of Action
13
Systemic Induction of Secondary Metabolite Biosynthesis
in Medicinal Aromatic Plants Mediated by Rhizobacteria . . . . . . . 263
Maricel Valeria Santoro, Lorena Cappellari, Walter Giordano,
and Erika Banchio
14
Medicinal Plants and PGPR: A New Frontier for
Phytochemicals . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 287
Dilfuza Egamberdieva and Jaime A. Teixeira da Silva
15
Plant Growth Promoting Rhizobacteria for Value Addition:
Mechanism of Action . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 305
H. Deka, S. Deka, and C.K. Baruah
16
Rhizosphere Microflora in Advocacy of Heavy Metal Tolerance
in Plants . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 323
Shivangi Upadhyay, Monika Koul, and Rupam Kapoor
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Contents
Part V
xv
PGPR: Diversity and Characterization
17
Diverse Endophytic Microflora of Medicinal Plants . . . . . . . . . . . . 341
Pranay Jain and Ram Kumar Pundir
18
Molecular Approach to Study Soil Bacterial Diversity . . . . . . . . . . 359
Satwant Kaur Gosal and Amita Mehta
19
Plant Growth-Promoting Rhizobacteria of Medicinal Plants
in NW Himalayas: Current Status and Future Prospects . . . . . . . . 381
Anjali Chauhan, C.K. Shirkot, Rajesh Kaushal, and D.L.N. Rao
20
Biocontrol Activity of Medicinal Plants from Argentina . . . . . . . . . 413
Ver
onica Vogt, Javier A. Andrés, Marisa Rovera, Liliana Sabini,
and Susana B. Rosas
Index . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 431
mkumar9@amity.edu
Chapter 1
Plant Growth-Promoting Rhizobacteria
(PGPR) and Medicinal Plants: The State
of the Art
Smriti Shrivastava, Dilfuza Egamberdieva, and Ajit Varma
1.1
Introduction
Plant growth-promoting rhizobacteria (PGPR) are bacteria colonizing rhizospheres
of plant that enhance plant growth through various mechanisms like nitrogen
fixation, solubilization of phosphate, quorum sensing, etc. (Bhattacharya and Jha
2012). PGPR offer various ways to replace chemical fertilizers, pesticides, etc., and
thus this quality has significantly led to their increased demand.
Before we start with the current applications and state of the art related to PGPR
and medicinal plants, it will really be interesting to know the basic and history
behind this wonderful science. Basis of application of plant growth-promoting
bacteria may be said to be led days back when Theophrastus (372–287 B.C.)
suggested mixing of different soil samples to remove defects of one and add life
to soil (Tisdale and Nelson 1975). Certainly the technical approach behind the same
only became clear after microscopy came into play. Establishment of legumes on
cultivable land was recorded for the first time by Virgil (Chew 2002). Investigation
of rhizosphere root colonization in grasses and confirmation of the fact that soil
bacteria could convert atmospheric nitrogen into plant-usable forms were reported
by Hellriegel and Wilfarth (1888). The term “rhizobacteria” was coined by
Kloepper and Schroth (1978), based on their experiments with radishes, and they
defined these bacteria as a community that competitively colonizes plant root and
enhances their growth and also reduces plant diseases. Few properties strictly
S. Shrivastava (*) • A. Varma
Amity Institute of Microbial Technology (AIMT), Amity University Uttar Pradesh, E-3 Block,
Fourth Floor, Sector 125, Noida, UP 201303, India
e-mail: sshrivastava1@amity.edu; ajitvarma@amity.edu
D. Egamberdieva
Department of Biotechnology and Microbiology, National University of Uzbekistan,
University str. 1, 100174 Tashkent, Uzbekistan
e-mail: egamberdieva@yahoo.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_1
mkumar9@amity.edu
1
2
S. Shrivastava et al.
associated with PGPR are their properties of aggressive colonization and plant
growth stimulation and their biocontrol ability (Weller et al. 2002; Vessey 2003).
Rhizobacteria show all positive, negative, and neutral interaction with plants
(Whipps 2001). PGPR are further classified as extracellular plant growth
rhizobacteria or intracellular plant growth rhizobacteria depending upon their
intimacy in interaction with plants (Martinez-Viveros et al. 2010). These are
designated as ePGPR and iPGPR. The ePGPR is mainly existing in rhizosphere,
rhizoplane, or between cells of root cortex include generally bacteria from genera
like Azotobacter, Chromobacterium, Agrobacterium, Caulobacter, etc. (Gray and
Smith 2005). Specialized nodular structures for root cells are home for iPGPR
which includes endophytes (Allorhizobium, Azorhizobium, Bradyrhizobium,
Mesorhizobium, etc.) and Frankia species (Verma et al. 2010; Wang and
Martinez-Romero 2000).
Studies have reported that application of PGPR increases nodulation and nitrogen fixation in many plants including soybean (Glycine max (L.) Merr.) (Zhang
et al. 1996). PGPR have both direct and indirect mechanisms to promote growth
and yield of crop plants. Rhizosphere colonization accounts for siderophore
(Schippers et al. 1988), antibiotic (Weller 1988), and hydrogen cyanide (Stutz
et al. 1986) production.
The objective of this chapter is to understand the mechanisms of plant growth
promotion by rhizobacteria and to know about the state of the art of this wide area
of study.
1.2
Plant–Microbe Interaction
The interaction of plants with microbes occurs at three different layers, namely,
endosphere, phyllosphere, and rhizosphere. The region of contact between root and
soil is rhizosphere. This region is a cloud of microbes which literally surrounds
plant roots and is vital for the plant’s survival and growth. The term “rhizosphere”
was coined by Lorenz Hiltner in 1904. Clark proposed the term “rhizoplane” for the
external root surface and closely adhering particles of soil and debris. The influence
of root exudates on the proliferation of soil microorganisms around and inside roots
(Hartmann et al. 2008) and interactions between soil microorganisms, rhizosphere
colonists, and plant hosts (Dennis et al. 2010; Friesen et al. 2011; Berendsen
et al. 2012) has been widely studied. In rhizosphere, the microbial population
differs both quantitatively and qualitatively from that in the soil. As per the
hypothesis, most of the plant roots are surrounded by mycorrhizae. Hence, it is
appropriate to use the word mycorrhizosphere instead of rhizosphere (Shrivastava
et al. 2014). Amino acids and sugars released as plant exudates are rich sources of
energy and nutrition. Plant root interaction in the rhizosphere is a combinatorial
effect of root–root interaction, root–microbe interaction, and root–insect
interaction.
mkumar9@amity.edu
1 Plant Growth-Promoting Rhizobacteria (PGPR) and Medicinal Plants: The. . .
3
Studies based on molecular techniques have estimated about 4,000 microbial
species per gram of soil sample (Montesinos 2003). One of the most important
communities in rhizosphere microbiota is filamentous actinomycetes (Benizri
et al. 2001). Rhizosphere microbial colonies have dynamic association with biogeochemical cycling of nutrients (C, P, N, and S) and production of phytohormones
or antibiotics (Cardoso and Freitas 1992). PGPR are well known to colonize plant
roots and stimulate plant growth (Andrews and Harris 2000). Azospirillum sp.,
Bacillus subtilis sp., and Pseudomonas sp. have been well studied as plant
rhizosphere-colonizing microorganisms (Steenhoudt and Vanderleyden 2000;
Trivedi et al. 2005). Soil microorganisms (free-living, associative, and symbiotic
rhizobacteria) belonging to the genera like Acinetobacter, Burkholderia,
Enterobacter, Alcaligenes, Arthrobacter, Azospirillum, Azotobacter, Bacillus,
Erwinia, Flavobacterium, Rhizobium, Serratia, Xanthomonas, Proteus, and Pseudomonas are the integral parts of rhizosphere biota (Glick 1995; Kaymak 2011) and
exhibit successful rhizosphere colonization. Rhizospheric colonization is a crucial
step in the application of microorganisms for beneficial purposes such as biofertilization, phytostimulation, biocontrol, and phytoremediation, although the colonization of rhizosphere by PGPR is not a uniform process.
1.3
1.3.1
PGPR in Agriculture
PGPR as Biofertilizer
Biofertilizers are the substances prepared from living microorganisms which, when
applied to the seeds or plant surfaces adjacent to soil, can colonize rhizosphere or
the interior parts of the plants and thereby promote root growth. Allorhizobium,
Azorhizobium, Bradyrhizobium, Mesorhizobium, Rhizobium, and Sinorhizobium
are reported as the potent PGPR strains for their ability to act as biofertilizers
(Vessey 2003). In rhizospheric relationship, the PGPR can colonize the rhizosphere, the surface of the root, or even the superficial intercellular spaces of plant
roots (McCully 2001). It is only due to the changes in different physicochemical
properties of rhizospheric soil such as soil pH, water potential and partial pressure
of O2, and plant exudation as compared to the bulk soil that in turn can affect the
ability of PGPR strains to colonize the rhizosphere (Griffiths et al. 1999). In
endophytic relationship, PGPR reside within the apoplastic spaces inside the host
plants. There is a direct evidence of existence of endophytes in the apoplastic
intercellular spaces of parenchyma tissue (Dong et al. 1997) and xylem vessel
(James et al. 2001). The best examples can be cited from legume–rhizobia symbioses in leguminous plants (Vessey 2003).
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1.3.2
S. Shrivastava et al.
Plant Growth Regulator by PGPR
PGPR can alter root architecture and promote plant development with the production of different phytohormones like IAA, gibberellic acid, and cytokinins
(Kloepper et al. 2007). Several PGPR as well as some pathogenic, symbiotic, and
free-living rhizobacterial species are reported to produce IAA and gibberellic acid
in the rhizospheric soil and thereby play a significant role in increasing the root
surface area and number of root tips in many plants (Han et al. 2005). Recent
investigations on auxin synthesizing rhizobacteria (Spaepen et al. 2007) as phytohormone producer demonstrated that the rhizobacteria can synthesize IAA from
tryptophan by different pathways, although the general mechanism of auxin synthesis was basically concentrated on the tryptophan-independent pathways.
1.3.3
PGPR as Phosphorous Solubilizers
Phosphorus is one of the most essential nutrient requirements in plants. Ironically,
soils may have large reservoir of total phosphorus (P) but the amounts available to
plants are usually a tiny proportion of this total. This low availability of phosphorus
to plants is because of the vast majority of soil P found in insoluble forms, while the
plants can only absorb it in two soluble forms, the monobasic (H2PO4 ) and the
diabasic (HPO42 ) ions (Glass 1989). Several phosphate-solubilizing microorganisms (PSMs) are now recorded to convert the insoluble form of phosphorus to
soluble form through acidification, secretion of organic acids or protons (Richardson et al. 2009), and chelation and exchange reactions (Hameeda et al. 2008).
Saprophytic bacteria and fungi are reported for the chelation-mediated mechanisms
(Whitelaw 2000) to solubilize phosphate in soil. Release of plant root exudates such
as organic ligands can also alter the concentration of P in soil solution (Hinsinger
2001).
1.3.4
PGPR as Producers of Volatile Organic Compounds
The discovery of rhizobacterial-produced volatile organic compounds (VOCs)
constitutes an important mechanism for the elicitation of plant growth by
rhizobacteria. Ryu et al. (2003) recorded some PGPR strains, namely, Bacillus
subtilis GB03, B. amyloliquefaciens IN937a, and Enterobacter cloacae JM22 that
released a blend of volatile components, particularly, 2,3-butanediol and acetoin,
which promoted growth of Arabidopsis thaliana, suggesting that synthesis of
bioactive VOCs is a strain-specific phenomenon. Acetoin-forming enzymes have
been identified earlier (Forlani et al. 1999) in certain crops like tobacco, carrot,
maize, and rice although their possible functions in plants were not properly
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established in that period. It has now been established that the VOCs produced by
the rhizobacterial strains can act as signaling molecule to mediate plant–microbe
interactions as volatiles produced by PGPR colonizing roots are generated at
sufficient concentrations to trigger the plant responses (Ryu et al. 2003). Farmer
(2001) identified low molecular weight plant volatiles such as terpenes, jasmonates,
and green leaf components as potent signal molecules for living organisms in
different trophic levels. However, to acquire a clear appreciation on the mechanisms of VOCs in signaling plants to register plant defense, more investigations into
the volatile components in plant–rhizobacteria system should follow.
1.3.5
PGPR as Biotic Elicitors
Elicitors are chemicals or biofactors of various sources that can trigger physiological and morphological responses and phytoalexin accumulation in plants. It may be
abiotic elicitors such as metal ions or inorganic compounds and biotic elicitors,
basically derived from fungi, bacteria, viruses, plant cell wall components, and
chemicals that are released due to antagonistic reaction of plants against phytopathogens or herbivore attack. It has now been observed that the treatment of plants
with biotic elicitors can cause an array of defense reactions including the accumulation of a range of plant defensive bioactive molecules such as phytoalexins in the
intact plants. Thus, elicitation is being used to induce the expression of genes
responsible for the synthesis of antimicrobial metabolites. Rhizosphere microbes
are best known to act as biotic elicitors, which can induce the synthesis of secondary products in plants (Sekar and Kandavel 2010). Signal perception is the first
committed step toward the biotic elicitor signal transduction pathway in plants.
Jasmonic acid and its methyl ester are the signal transducers in a wide range of plant
cell cultures that could accumulate rapidly when the suspension cultures of
Rauvolfia canescens L. and Eschscholzia californica Cham. are treated with a
yeast elicitor (Roberts and Shuler 1997). Ajmalicine, serpentine, picrocrocin,
crocetin, hyoscyamine and scopolamine, safranal compounds, and tanshinone are
recorded as the important metabolites produced by PGPR species in eliciting the
physiological and morphological responses in crop plants.
1.3.6
Induction of Systemic Disease Resistance by PGPR
Application of mixtures of different PGPR strains to the seeds or seedlings of
certain plants has resulted in increased efficiency of induced systemic resistance
(ISR) against several pathogens (Ramamoorthy et al. 2001). Various nonpathogenic
PGPR strains have the ability to induce systemic disease resistance in plants against
broad-spectrum phytopathogens (Kloepper et al. 2004; Elbadry et al. 2006). Induction of systemic disease resistance in faba bean (Vicia faba L.) against bean yellow
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S. Shrivastava et al.
mosaic virus (BYMV) via seed bacterization with Pseudomonas fluorescens and
Rhizobium leguminosarum has been investigated by Elbadry et al. (2006). They
isolated PGPR strains from the roots of faba bean and examined singly or in
combination for the induction of resistance in faba bean against BYMV. The results
established a pronounced and significant reduction in percent disease incidence
(PDI) as well as in virus concentration (ELISA) in plants treated with Pseudomonas
fluorescens and Rhizobium leguminosarum as compared to the non-bacterized
plants. Similarly, induction of systemic resistance by Pseudomonas putida strain
89B-27 and Serratia marcescens strain 90–166 against Fusarium wilt of cucumber
incited by Fusarium oxysporum f. sp. cucumerinum has been investigated by Liu
et al. (1995). Alstroem (1991) observed induced systemic protection of PGPR
against the bacterial diseases. He reported that the bean seeds when treated with
Pseudomonas fluorescens protected the plant against the halo blight disease caused
by Pseudomonas syringae pv. phaseolicola. Kloepper et al. (1993) treated cucumber seeds with rhizobacterial strains like Pseudomonas putida 89 B-27 and Serratia
marcescens 90–166 and recorded a significant decrease in incidence of bacterial
wilt. Similar investigations on the treatment of cucumber seeds against angular leaf
spot disease caused by Pseudomonas syringae pv. lachrymans, with a large number
of PGPR strains such as Pseudomonas putida 89B-27, Flavimonas oryzihabitans
INR-5, Serratia marcescens 90–166, and Bacillus pumilus INR-7, have been made
by Wei et al. (1996). They observed more systemic protection in the plants
(indicated by the reduction of total lesion diameter) whose seeds are inoculated
with the strains of PGPR as compared to the uninoculated plants. Pieterse
et al. (2001) studied rhizobacterial strain Pseudomonas fluorescens to enhance the
defensive capacity in plants against broad-spectrum foliar pathogens (Fig. 1.1).
Based on their experiments they concluded that Pseudomonas fluorescens strain
WCS417r could elicit systemic disease resistance in plants through a variety of
signal translocation pathways like SA-independent JA-ethylene-dependent signaling, ISR-related gene expression, NPR 1-dependent signaling, etc. Recently, interactions between Bacillus spp. and plants with special reference to induced systemic
disease resistance have been elicited by Choudhary and Johri (2009). Several
strains of Bacillus like B. amyloliquefaciens, B. subtilis, B. pasteurii, B. cereus,
B. pumilus, B. mycoides, and B. sphaericus (Ryu et al. 2004) are presently recorded
to elicit significant reduction in disease incidence on diversity of hosts. Elicitation
of resistance by the strains has been demonstrated both in greenhouse and field
trials on tomato, bell pepper, muskmelon, watermelon, sugar beet, tobacco, and
cucumber. Through the activation of various defense-related enzymes like
chitinases, β-1, 3-glucanase, peroxidise (PO), phenylalanine ammonia-lyase
(PAL), and polyphenol oxidase (PPO), PGPR strains can induce this type of
systemic resistance in plants (Bharathi 2004).
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Fig. 1.1 Possible involvement of jasmonic acid and ethylene in Pseudomonas fluorescens
WCS417r-mediated induced systemic resistance in Arabidopsis (Adapted from Pieterse
et al. 2001)
1.3.7
Nitrogen Fixation
Nitrogen is a principal plant nutrient. Apart from being the most important, it is also
a limiting factor in the agricultural ecosystem due to its loss by rainfall and mineral
leaching. PGPR strains such as Klebsiella pneumoniae, Pantoea agglomerans, and
Rhizobium sp. are reported to fix atmospheric N2 in soil and avail it to plants
(Antoun et al. 1998; Riggs et al. 2001). Fluorescent Pseudomonades and Pseudomonas fluorescens have been reported to promote nodulation in chickpea (Parmar
and Dadarwal 1999) and tomatoes (Minorsky 2008). They promote enhanced plant
height and increased fruiting and flowering capability. Ability of microorganisms to
fix nitrogen symbiotically or nonsymbiotically in soil and enhance crop yield could
replace the use of nitrogen fertilizers (Vessey 2003). Symbiotic N2 fixation to
legume crops with the inoculation of effective PGPR is well known (Dobereiner
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S. Shrivastava et al.
1997; Barea et al. 2005; Esitken et al. 2006). Symbiotic N2 fixation is mostly done
by Azotobacter spp., Bacillus spp., Beijerinckia spp., etc. and is limited to leguminous plants, trees, and shrubs that form actinorhizal roots with Frankia, whereas
nonsymbiotic nitrogen fixation is carried out by free-living diazotrophs like
Azospirillum (Bashan and de-Bashan 2010), Burkholderia (Estrada de los Santos
et al. 2001), Azoarcus (Reinhold-Hurek et al. 1993), Gluconacetobacter (FuentesRamirez et al. 2001), and Pseudomonas (Mirza et al. 2006). Researchers have also
studied the effect of combined inoculation of symbiotic and nonsymbiotic microorganisms on plant growth enhancement. Combined inoculations of
Bradyrhizobium sp. with Pseudomonas striata have established enhanced nodule
occupancy in soybean resulting in more biological N2 fixation (Dubey 1996).
1.3.8
PGPR as Plant Growth Enhancement
Enormous PGPR are known to promote plant growth, crop yield, seed emergence,
etc., thus promoting agriculture (Minorsky 2008). Plant properties like leaf area,
chlorophyll content, total biomass, etc. are enhanced by inoculation of PGPR (Baset
Mia et al. 2010). They also studied the effect of PGPR on external layers of root
cortex of maize and wheat seedlings. Increasing demand for food and improving
environmental quality have focused on the importance of PGPR in agriculture.
Dobbelaere et al. (2001) assessed the inoculation effect of Azospirillum sp. on the
development of agriculturally important plants and observed a noteworthy boost in
the dry weight of both the root system and aerial parts of the PGPR-inoculated
plants, resulting in better progress and flowering. Foliar applications of
rhizobacterial microbes in mulberry and apricot and their better development in
leaf area and chlorophyll production were investigated by Esitken et al. (2003).
Bacillus subtilis, B. licheniformis, Achromobacter xylosoxidans, B. pumilus,
Brevibacterium halotolerans, and Pseudomonas putida are identified as having
critical roles in cell elongation, escalating ACC deaminase activity, and plant
growth promotion (Sgroy et al. 2009). The effect of Pseudomonas fluorescens on
tomato and cucumber roots was studied by Saravanakumar and Samiyappan (2007).
Seeds of various crops and ornamental plants bacterized with a mixture of PGPR
and rhizobia before planting resulted in enhanced growth and disease resistance
(Zehnder et al. 2001). Growth responses in wheat after the inoculation with
rhizobacteria basically depends on various factors like plant genotype, nature of
PGPR inoculants, as well as environmental conditions as observed by Khalid
et al. (2004). The root inoculation of apple tree with Bacillus M3 and
Microbacterium FS01 (Karlidag et al. 2007) and the effect of arbuscular mycorrhizal (AM) fungi and PGPR in soils differing in nitrogen concentration (Ahanthem
and Jha 2007) are few other important studies in this field. It was found that
enhancing apple tree growth in the study might be due to enhanced production of
plant growth regulators and mobilization of available nutrients by PGPR.
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Ahanthem and Jha (2008) also studied the interactions between Acaulospora and
Azospirillum and their synergistic effect on rice growth at different sources.
1.3.9
Maintenance of Soil Fertility and Nutrient Uptake
by PGPR
Plant physiology and nutritional and physical properties of rhizospheric soil are all
altered by PGPR. Rhizobacteria are reported to increase uptake of nutrient elements
like Ca, K, Fe, Cu, Mn, and Zn through proton pump ATPase (Mantelin and
Touraine 2004). Bacillus and Microbacterium inoculants improve uptake of mineral elements by crop plants (Karlidag et al. 2007). The importance of
rhizobacterial activities on maintaining soil fertility is well studied by many
scientists (Phillips 1980; Forde 2000; Glass et al. 2002). Rhizobacteria also help
in solubilizing unavailable forms of nutrients and facilitating its transport in plants
(Glick 1995).
1.3.10 Enhancement of Resistance to Water Stress
PGPR are beneficial to the wide variety of plants growing in water-stressed
conditions (Aroca and Ruiz-Lozano 2009). Drought stress causes limitation to the
plant growth and productivity of agricultural crops particularly in arid and semiarid
areas. Figueiredo et al. (2008) suggested that inoculation of plants with PGPR can
enhance the drought tolerance that might be due to the production of IAA, cytokinins, antioxidants, and ACC deaminase and inoculation of seeds of Phragmites
australis with Pseudomonas asplenii improved germination and protects the plants
from growth inhibition (Bashan et al. 2008).
1.4
Commercialization of PGPR
Commercialization of PGPR is important for its beneficial usage and this very
aspect requires a proper tuning between scientific organization and industries.
Different stages in the process of commercialization include isolation of antagonist
strains, screening, pot tests and field efficacy, mass production and formulation
development, fermentation methods, formulation viability, toxicology, industrial
linkages, and quality control (Nandakumar et al. 2001). Isolation of effective strain
is the prime criteria for better agricultural development (Nakkeeran et al. 2005), and
then selection of the best antagonistic strain can be carried out by screening for
antimicrobial action against soilborne pathogens. The next stage of study is when
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S. Shrivastava et al.
the plant, pathogen, and antagonists are tested for their efficacy in field trials along
with recommended fungicides (Pengnoo et al. 2000). Mass production is achieved
through liquid (Manjula and Podile 2001), semisolid, and solid fermentation
requirement for entrepreneurship requires a patent application of the identified
strain.
The next crucial step to retain the confidence of farmers on efficacy of antagonistic strain is quality control. The first commercial product of Bacillus subtilis was
developed in 1985 in the USA. 60–75% of cotton, peanut, soybean, corn, vegetables, and small grain crops raised in the USA are now treated with commercial
product of B. subtilis, which become effective against soilborne pathogens such as
Fusarium and Rhizoctonia (Nakkeeran et al. 2005). The potential of Bacillus spp.
has also been widely studied by Backman et al. (1997). Besides Bacillus spp.,
certain other PGPR strains belonging to the genera such as Agrobacterium,
Azospirillum, Burkholderia, Pseudomonas, and Streptomyces are also used for the
production of several commercial products, which are generally being applied
against several target pathogens like Botrytis cinerea, Penicillium spp., Pythium
sp., Geotrichum candidum, Mucor piriformis, Erwinia amylovora, russet-inducing
bacteria, Fusarium sp., Rhizoctonia sp., Fusarium sp., Phytophthora sp., and
P. tolaasii (Nakkeeran et al. 2005).
Chet and Chernin (2002) studied a wide variety of PGPR and have also been
successful in developing formulations for commercialization of products.
1.5
Future Prospects and Challenges
PGPR inoculants can fulfill diverse beneficial interactions in plants. Applications of
rhizosphere soil with desirable bacterial populations have established considerable
promises in both the laboratory and greenhouse experiments. Combined applications of transgenic plants with PGPR have proved another promising future (Ali and
Hj 2010) in advancing rhizoremediation technologies. Rationalizing the understanding of PGPR may promote plant growth, leading to its use as biofertilizer at
a wide level. Denton (2007) worked on the use of PGPR to remediate complex
contaminated soil which could result in increased crop yield. The rhizobacterial
community can be specifically engineered to target various pollutants at
co-contaminated sites to provide customized rhizoremediation system
(Wu et al. 2006). Production of transgenic plants and then inoculating it with
PGPR has also increased efficiency (Zhuang et al. 2007; Farwell et al. 2007).
Modern technology based on the transformations of 1-aminocyclopropane-1-carboxylic acid deaminase gene, which directly stimulates plant growth by cleaving
the immediate precursor of plant ethylene into Pseudomonas fluorescens CHAO,
not only increased the plant growth but also accelerated biocontrol properties of
PGPR species (Holguin and Glick 2001). Genomic tinkering of naturally occurring
PGPR strains with effective genes (Nakkeeran et al. 2005) could lead to accentuated expression of genomic products, thereby alleviating the attack of both pests
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and diseases on field crops that would further facilitate for better introduction of a
single bacterium with multiple modes of action to benefit the growers.
1.6
Conclusions
PGPR enhance plant growth by direct and indirect means, but the specific mechanisms involved have not all been well characterized. The present review indicates
the advances and formulations of PGPR in biological promotion of different
characteristics of plant growth. Most PGPR isolates significantly increase plant
height, root length, and dry matter production in various agricultural crops like
potato, tomato, maize, wheat, etc. One of the promising approaches of replacing the
use of chemical fertilizers is developing stable formulation of antagonistic PGPR in
sustainable agricultural systems. Another approach is through activation of
octadecanoid, shikimate, and terpenoid pathways which in turn assists the plant
growth promotion. Plenty of research in this field is going on and various are fruitful
too. It can be concluded that vigilantly controlled field trials of crop plants inoculated along with rhizobacteria are necessary for utmost commercial exploitation of
PGPR strains.
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mkumar9@amity.edu
Part I
Plant Improvement
mkumar9@amity.edu
Chapter 2
Rhizosphere Microbes Interactions
in Medicinal Plants
Zakaria M. Solaiman and Hossain Md Anawar
2.1
Introduction
The diversity and functions of microbes in the rhizosphere, a narrow region around
the root, are related to the root exudates (proteins and sugars), biogeochemical
reactions and respiration (Narula et al. 2009). The rhizosphere contains abundant
bacteria, fungi, protozoa and nematodes. Some nematodes are feeding on bacteria
and fungi. The root exudates in the rhizosphere may control disease suppression and
help in nutrient cycling. The different compounds secreted by plant roots into the
rhizosphere perform multiple functions. For example, strigolactones stimulate the
colonisation of the mycorrhiza fungi and germination of the parasitic plant such as
Striga. The flavonoids secreted by the roots of leguminous plants increase the
growth of symbiotic and non-symbiotic nitrogen-fixing bacteria, root nodules and
nitrogen uptake by plants. Allelochemicals can inhibit the growth of other microorganisms in the rhizosphere, and therefore interactions are complex.
In the mycorrhizosphere around the mycorrhiza-colonised roots, most of the
actively absorbing rootlets are extended to the surrounding soil for nutrient uptake
(Johansson et al. 2004). Since mycorrhizal fungi stimulated by some root exudates
may modify root morphology and metabolic functions, the volume of the mycorrhizosphere soil is larger than the rhizosphere soil (Linderman 1988), and root
exudates in the mycorrhizosphere is quantitatively and qualitatively different
from that in the rhizosphere (Leyval and Berthelin 1993; Rygiewicz and Andersen
1994) producing the ‘mycorrhizosphere effect’ (Linderman 1988). In addition,
mycorrhizal fungi can produce antibiotics that may reduce bacterial activity in
sandy soil (Olsson et al. 1996).
Z.M. Solaiman (*) • H.M. Anawar
School of Earth and Environment, and UWA Institute of Agriculture, The University
of Western Australia (M087), 35 Stirling Highway, Crawley, WA 6009, Australia
e-mail: zakaria.solaiman@uwa.edu.au
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_2
mkumar9@amity.edu
19
20
Z.M. Solaiman and H.M. Anawar
A wide range of organic compounds secreted by plant roots in the rhizosphere
provide a food source for microorganisms increasing microbial density and activity
in the rhizosphere than in the bulk soil (the soil away from the rhizosphere is known
as bulk soil). Most of the microorganisms in the rhizosphere are related to plant
species that can efficiently solubilise poorly soluble inorganic P and mineralise
organic P sources (unaccessible to plants) and markedly increase plant growth in
soils with low P availability. However, the contribution of the plant-specific
microorganisms to plant P uptake in soils with low P availability is poorly understood. The arbuscular mycorrhizal (AM) fungi form symbioses with more than
80 % of all land plant species and can help for plant P acquisition via the fungal
hyphae (Jasper et al. 1989; Smith and Read 2008).
Medicinal plants are a rich source of bioactive compounds (Toussaint
et al. 2007), and these are thought to be safe to human beings and the environment
compared to the synthetic medicines for the treatment of cancer and many other
diseases (Nema et al. 2013). The use of medicines of plant origin has a long
tradition in Europe and Asia such as traditional Chinese medicine, Indian Ayurvedic medicine and herbal medicine. More than 600 medicinal plants, comprising
more than 30 % of known plant species, are recorded in the Chinese Materia
Medica, citing the first use of medicinal herbals in China as early as 1100 BC
(Cragg et al. 1997; Joy et al. 1998). With the increased population pressure, costs
and side effects and the development of resistance to allopathic drugs for infectious
diseases, the uses of medicines of plant sources for a wide variety of human
ailments are increasing. So, large-scale productions of medicinal plants using
modern cultivation technologies are being practised across Asian countries, to
meet the demand of medicinal plants. The pests and diseases of plant are hampering
the growth and quality of medicinal plants. In addition, excessive use of pesticides
may degrade the quality of medicinal plant products. Therefore, the development of
innovative technologies for cultivation of medicinal plants is required.
Many recent research works have indicated that mycorrhizal colonisation is
common in most of the medicinal plants in Fiji Island and Hawaii, America
(Taber and Trappe 1982), Pakistan (Waheed 1982; Gorsi 2002; Haq and Hussain
1995; Iqbal and Nasim 1986), China (Wei and Wang 1989), Japan (Udea
et al. 1992) and many other areas that play many significant roles in increasing
soil structure, nutrient uptake by plants, plant growth, productivity and biodiversity
in the diverse agroecosystems (Smith and Read 2008). The AM fungi are the most
widely distributed symbioses out of all types of mycorrhizas such as arbuscular
mycorrhiza, ectomycorrhiza, ectoendomycorrhiza, ericoid, orchid, arbutoid and
monotropoid mycorrhiza (Smith and Read 2008). Many researches have focused
on the AM fungal community and diversity in the rhizosphere of medicinal plants
(e.g. Kumar et al. 2010; Wubet et al. 2003; Zeng et al. 2013) and improved plant
growth (Karthikeyan et al. 2009; Chandra et al. 2010) and medicinal values by AM
fungal colonisation (e.g. Copetta et al. 2006, Yuan et al. 2007; Morone-Fortunato
and Avato 2008; Toussaint et al. 2008; Sasanelli et al. 2009; Koeberl et al. 2013).
However, the microbes in the rhizosphere of medicinal plants are largely
unexplored. Therefore, further research is recommended to provide the novel
mkumar9@amity.edu
2 Rhizosphere Microbes Interactions in Medicinal Plants
21
insights on (1) the microbiome of medicinal plants, (2) plant- and microbe-derived
ingredients of medicinal plants and (3) plant growth promotion and plant protection
for pests and diseases.
2.2
2.2.1
Microbial Diversity in the Rhizosphere of Medicinal
Plants
Bacterial Diversity
The study of rhizosphere bacteria from the important medicinal plants is very
crucial, as they are well known to have impact on plant growth and also produce
industrially important metabolites and improve quality of medicinal product
(Bafana and Lohiya 2013). A significant number of bacteria produce the
phytotherapeutic compounds (Koeberl et al. 2013) and increase the growth of the
medicinal plants when they are associated with rhizosphere of plants that are listed
in Table 2.1. This information will be useful in developing a biofertiliser consortium for commercially grown medicinal plants.
Gram-negative, nonmotile, catalase-positive and oxidase-negative short rods
and exopolysaccharide-producing bacterium, designated as strain DRP 35
(T) (Whang et al. 2014) and DR-9(T) (Lee et al. 2013), were isolated from the
rhizosphere soil of a medicinal herb, Angelica sinensis. The phylogenetic analyses
based on 16S rRNA gene sequences indicated that strain DRP 35(T) belongs to the
genus Terriglobus in the phylum Acidobacteria with a similarity to Terriglobus
saanensis SP1PR4(T) and Terriglobus roseus KBS63(T), while strain DR-9(T)
formed a lineage within the genus Mucilaginibacter and was closely related to
Mucilaginibacter polysacchareus DRP28(T), Mucilaginibacter myungsuensis
HMD1056(T), Mucilaginibacter ximonensis XM-003(T) and Mucilaginibacter
boryungensis BDR-9(T).
The soil microbes in the rhizosphere of three medicinal plants (Matricaria
chamomilla L., Calendula officinalis L. and Solanum distichum Schumach. &
Thonn.) grown on the desert ecosystem had a high abundance of Gram-positive
bacteria of prime importance for pathogen suppression (Koeberl et al. 2013). For all
three plants, a plant-specific selection of the microbes as well as highly specific
diazotrophic communities was found. The results identified that the plant species
were important drivers in structural and functional diversity. Furthermore, the
native Bacillus strains promoted the plant growth and elevated the plants’ flavonoid
production. Among 28 endophytic bacterial isolates from different organs of
Plectranthus tenuiflorus medicinal plant, 8 isolates were Bacillus sp., Bacillus
megaterium, Bacillus pumilus, Bacillus licheniformis, Micrococcus luteus,
Paenibacillus sp., Pseudomonas sp. and Acinetobacter calcoaceticus (El-Deeb
et al. 2013). Li et al. (2013) found the great differences in the endophytic bacterial
diversity in the three medicinal plant species of Codonopsis pilosula, Ephedra
mkumar9@amity.edu
22
Z.M. Solaiman and H.M. Anawar
Table 2.1 Medicinal plants and rhizosphere-associated bacteria
Plant species
Microorganisms
References
Angelica sinensis
Terriglobus saanensis
Mucilaginibacter polysacchareus
Mucilaginibacter myungsuensis,
Mucilaginibacter ximonensis
Bacillus sp.
Whang
et al. (2014)
Lee
et al. (2013)
Koeberl
et al. (2013)
Qi et al. (2013)
Matricaria chamomilla Calendula officinal, Solanum distichum
Rumex patientia
Atractylodes lancea
Plectranthus tenuiflorus
Origanum vulgare
Typhonium giganteum
Ginseng plants
Hypericum silenoides
Proteobacterium
Bacteroidetes
Acidobacteria
Gemmatimonadetes
Verrucomicrobia
Planctomycetes
Actinobacteria
Firmicutes
Chloroflexi
Gram-negative bacteria
Bacillus sp.
Bacillus megaterium
Bacillus pumilus
Bacillus licheniformis
Micrococcus luteus
Paenibacillus sp.
Pseudomonas sp.
Acinetobacter calcoaceticus
Pseudomonas, Stenotrophomonas
Kribbella flavida
K. karoonensis
K. alba
Actinomycetes
Ajuga bracteosa
Acinetobacter
Enterobacter
Pseudomonas
Sphingobium
Stenotrophomonas
Agrobacterium
Pantoea
Serratia
Pseudomonas
Nerium indicum
Pontibacter
Fritillaria thunbergii
Proteobacteria
Acidobacteria
Actinobacteria
Bacteroidetes
Dai
et al. (2013)
El-Deeb
et al. (2013)
Bafana and
Lohiya (2013)
Xu et al. (2012)
Zhang
et al. (2013)
Lopez-Fuentes
et al. (2012)
Kumar
et al. (2012)
Raichand
et al. (2011)
Shi
et al. (2011)
(continued)
mkumar9@amity.edu
2 Rhizosphere Microbes Interactions in Medicinal Plants
23
Table 2.1 (continued)
Plant species
Astragalus membranaceus
Microorganisms
Geodermatophilus obscurus
Phytolacca acinosa
Aspergillus fumigatus
Agathosma betulina
Cryptococcus laurentii
Ocimum sanctum, Coleus forskohlii,
Catharanthus roseus, Aloe vera
Azospirillum
Azotobacter
Pseudomonas
Bacillus
Pseudomonas
Enterobacter, Corynebacterium,
Micrococcus
Serratia
Annona squamosa
Eclipta alba
Cassia auriculata
References
Zhang
et al. (2011a)
Guo
et al. (2010)
Cloete
et al. (2010)
Karthikeyan
et al. (2008)
Tamilarasi
et al. (2008)
sinica and Lamiophlomis rotata. Zhao et al. (2013) explored the microbial diversity
from the rhizosphere soils of some medicinal plants and found a total of 50 strains
identified into 7 genera, Myxococcus (18), Corallococcus (11), Cystobacter (7),
Archangium (8), Stigmatella (1), Chondromyces (4) and Pyxidicoccus (1) with the
dominant genera of Myxococcus and Corallococcus.
The continuous cropping of Rehmannia glutinosa, an important medicinal plant,
on the same land decreases its productivity (Qi et al. 2009). An alteration of soil
microbial community following R. glutinosa cropping might be an important
reason for the constraints associated with continuous cropping. There were several
characteristic differences in the microbial community composition and activities in
the rhizosphere following Rehmannia glutinosa monoculture (Qi et al. 2009; Wu
et al. 2013). However, the interactions among plant, soil and microflora are crucial
for the productivity and quality of Rehmannia glutinosa in consecutive monoculture system (Wu et al. 2011). The relative proportion of bacterial communities in
rhizosphere soils of the wild medicinal plant Rumex patientia was similar to
non-rhizosphere soils in five phylogenetic groups (Acidobacteria, Actinobacteria,
Chloroflexi, Planctomycetes and Proteobacteria), but there were differences in five
other phylogenetic groups (Bacteroidetes, Firmicutes, Gemmatimonadetes,
Verrucomicrobia and unclassified bacteria) (Qi et al. 2012). Qi et al. (2013) identified a total of 83 unique phylotypes classified as Proteobacterium (43.37 %),
Bacteroidetes (13.25 %), Acidobacteria (10.84 %), unclassified bacteria (9.64 %),
Gemmatimonadetes (7.23 %), Verrucomicrobia (4.82 %), Planctomycetes
(4.82 %), Actinobacteria (3.61 %), Firmicutes (1.20 %) and Chloroflexi (1.20 %)
in the rhizosphere soil of Rumex patientia.
The peanut production in continuous monocrop farming system is affected by
various environmental factors that deteriorate soil microbial communities, especially decrease in fungal diversity and increase in fungal pathogens. Whereas, the
peanut production was increased by the improved soil microcosm environment and
mkumar9@amity.edu
24
Z.M. Solaiman and H.M. Anawar
the fungal diversity and decreased fungal pathogens such as Fusarium sp. and
Verticillium sp. when peanut was intercropped with Atractylodes lancea and
Euphorbia pekinensis, traditional Chinese medicinal plants (Dai et al. 2009,
2013). The increase in the Gram-negative bacterial population and the decrease
of phenolic allelochemicals resulted in the promotion of peanut growth and
increased peanut yield in the intercropping treatments.
The Origanum vulgare is a perennial medicinal aromatic plant rich in phenolic
antioxidants. Bafana and Lohiya (2013) isolated both root endophytes and
rhizospheric soil bacteria with a total of 120 morphologically different isolates
grouped into 21 phylotypes. Majority of the isolates belonged to Firmicutes and
gamma-Proteobacteria. Pseudomonas and Stenotrophomonas were the most dominant species and together constituted 27.5 % of the total isolates. Lopez-Fuentes
et al. (2012) isolated and identified the 103 bacterial communities in the rhizosphere
and roots of Hypericum silenoides Juss, mostly belonging to the genera
Acinetobacter, Agrobacterium, Enterobacter, Pseudomonas, Sphingobium,
Stenotrophomonas, Pantoea and Serratia. In order to determine their plant
growth-promoting and biotechnological potential, Kumar et al. (2012) isolated a
total of 123 morphologically different bacteria from the rhizospheric soil and roots
of the medicinal plant Ajuga bracteosa that belonged to alpha- and gammaProteobacteria, with Pseudomonas constituting the most dominant species. The
endophytic bacterial community consisted almost exclusively of Firmicutes.
Raichand et al. (2011) isolated a Gram-negative, pink pigmented bacterium
strain from the rhizosphere of an Indian medicinal plant, Nerium indicum
(Chuvanna arali), that matched with most of the phenotypic and chemotaxonomic
properties of the genus Pontibacter and represents a novel species. The main
bacterial population found in the rhizosphere of medicinal plant Fritillaria
thunbergii was Proteobacteria (55 %), Acidobacteria (12 %), Actinobacteria
(12 %) and Bacteroidetes (18 %) (Shi et al. 2011). The bacterial diversity of
Indigofera tinctoria and Pueraria mirifica rhizospheres was significantly different
from that of Derris elliptica Benth rhizosphere (Nimnoi et al. 2011). The microbial
population is more in the rhizosphere soil compared to non-rhizosphere soil of the
medicinal plants Ocimum sanctum L., Coleus forskohlii Briq., Catharanthus roseus
(L.) G. Don and Aloe vera. The diazotrophic bacterial population studied includes
Azospirillum, Azotobacter and Pseudomonas (Karthikeyan et al. 2008).
The actinobacterial biocontrol strains in medicinal plants are important as they
can be a source of potent antibiotics. Zhao et al. (2012) analysed the actinobacterial
diversity in the rhizosphere of seven traditional medicinal plant species and found
18 actinobacterial genera. In particular, Diels hosted a diverse selection of
Actinobacteria. Xu et al. (2012) isolated an actinomycete, designated XMU 198
(T), from the rhizosphere soil of a pharmaceutical plant, Typhonium giganteum
Engl., exhibiting highest sequence similarities with Kribbella flavida,
K. karoonensis and K. alba. Zhang et al. (2011a) isolated a novel actinobacterial
strain, CPCC 201356(T), from a rhizosphere soil sample of the medicinal plant
Astragalus membranaceus that belonged to the family Geodermatophilaceae.
mkumar9@amity.edu
2 Rhizosphere Microbes Interactions in Medicinal Plants
25
Table 2.2 Medicinal plants and rhizosphere-associated fungi
Plant species
Microorganisms
References
Atractylodes lancea
Dioscorea
zingiberensis, Euphorbia pekinensis
Ophiopogon
platyphyllum, Pinellia
ternata
Andrographis
paniculata
Fusarium sp.
Verticillium sp.
Dai
et al. (2009)
Acaulospora scrobiculata, Glomus aggregatum
Radhika and
Rodrigues
(2010)
Radhika and
Rodrigues
(2010)
Hemidesmus indicus
Aloe vera
Azadirachta indica
Naregamia alata
Physalis minima
Centella asiatica
Panax ginseng
Panax notoginseng
Arnica montana
Echinacea purpurea
Ambispora leptoticha
G. maculosum
G. geosporum
G. multicaule
G. fasciculatum
G. maculosum
G. multicaule
G. geosporum
A. scrobiculata
G. fasciculatum
Gi. albida
S. calospora
A. scrobiculata
Am. Leptoticha
A. nicolsonii
G. rubiforme
G. maculosum
G. fasciculatum
S. verrucosa
A. rehmi
G. fasciculatum
G. multicaule
G. maculosum
G. geosporum
G. rubiforme
G. multicaule, G. clarum, G. fasciculatum,
A. delicate, S. scutata
A. cavernata, A. spinosa, G. fasciculatum,
G. geosporum, G. macrocarpum,
G. microaggregatum, G. mosseae
G. versiforme, G. monosporum, G. mosseae,
G. constrictum, G. claroideum
G. geosporum, G. constrictum, G. intraradices,
G. mosseae, G. macrocarpum, G. fasciculatum,
G. versiforme
G. intraradices
mkumar9@amity.edu
Radhika and
Rodrigues
(2010)
Radhika and
Rodrigues
(2010)
Radhika and
Rodrigues
(2010)
Radhika and
Rodrigues
(2010)
Radhika and
Rodrigues
(2010)
Cho
et al. (2009)
Zhang
et al. (2011b)
Jurkiewicz
et al. (2010)
Araim
et al. (2009)
(continued)
26
Z.M. Solaiman and H.M. Anawar
Table 2.2 (continued)
Plant species
Cercidiphyllum
japonicum
Hippophae rhamnoides
Ziziphus jujuba Mill.
var. inermis
Lycium barbarum
Taxus chinensis
Euptelea pleiosperma
Cassia alata
C. occidentalis
C. sophera
Curcuma mangga
Centella asiatica and
Ocimum sanctum
Paeonia suffruticosa
Artemisia annua
Magnolia cylindrica
Bacopa monnieri
Leptadenia reticulata
Mitragyna parvifolia
Withania coagulans
Microorganisms
G. aggregatum, G. constrictum, G. dimorphicum,
G. fasciculatum, G. flavisporum, G. intraradices,
G. mosseae, S. aurigloba, Archaeospora leptoticha
G. albidum, G. claroideum, G. constrictum,
G. coronatum, G. intraradices
G. coronatum, G. intraradices, G. monosporum,
G. reticulatum
Gi. margarita, G. albidum
G. aggregatum, G. ambisporum, G. clarum,
G. constrictum, G. fasciculatum, G. geosporum,
G. magnicaule, G. reticulatum, G. verruculosum,
G. viscosum, A. denticulate
G. ambisporum, G. constrictum, G. fasciculatum,
G. geosporum, G. hyderabadensis,
G. intraradices, S. verrucosa
Glomus spp.
Alternaria brassicicola, Colletotrichum
gloeosporioides
Fusarium oxysporum, Penicillium digitatum,
Sclerotium rolfsii
AM and endophytic fungi
Glomus
Acaulospora
Scutellospora
Glomus mosseae
G. aggregatum
G. fasciculatum
G. intraradices
Acaulospora
Glomus
Gigaspora
Scutellospora
Glomus mosseae
Glomus intraradices
G. constrictum
G. fasciculatum
G. geosporum
G. intraradices
G. mosseae
G. rubiforme
References
Wang
et al. (2008)
Tang
et al. (2004)
Tang
et al. (2004)
Tang
et al. (2004)
Wang
et al. (2008)
Wang
et al. (2008)
Chatterjee
et al. (2010)
Khamna
et al. (2009)
Sagar and
Kumari (2009)
Shi
et al. (2013)
Awasthi
et al. (2011)
Yang
et al. (2011)
Khaliel
et al. (2011)
Panwar and
Tarafdar
(2006)
(continued)
mkumar9@amity.edu
2 Rhizosphere Microbes Interactions in Medicinal Plants
27
Table 2.2 (continued)
Plant species
Sorghum bicolor
Curculigo orchioides
Ginseng plants
Microorganisms
G. mosseae
G. intraradices
G. geosporum
G. microcarpum
Soil fungi
References
Sun and Tang
(2013)
Sharma
et al. (2008)
Zhang
et al. (2013)
Zhang et al. (2010) determined that allelochemicals released by the medicinal
plant Scutellaria baicalensis Georgi negatively affected S. baicalensis directly by
inducing autotoxicity and indirectly by increasing pathogen activity in the soil.
2.2.2
Fungal Diversity
AM fungal colonisations in the medicinal plants have been reported widely.
However, the diversity of AM fungal species and the extent of colonisation in the
rhizosphere of medicinal plants may vary depending on host plant species, growing
season, soil properties, local climate and environmental factors. Various informations of medicinal plants and rhizosphere-associated fungi are stated in Table 2.2.
The Egyptian henbane (Hyoscyamus muticus L.), a medicinal plant of family
Solanaceae native to the desert producing pharmaceutically important compounds
(tropane alkaloids) as secondary metabolites, is colonised by a higher number of
fungal species and endophytic fungi (El-Zayat et al. 2008). Rhizosphere soil of the
medicinal plants (Centella asiatica and Ocimum sanctum) revealed the presence of
16–17 species of fungi (Sagar and Kumari 2009). The endophytic fungi were also
isolated from the roots and leaves of Centella asiatica and Ocimum sanctum. There
was a massive variation in the AM fungi spore population and root colonisation in
the rhizosphere of ten medicinal plant species(Aloe barbadensis, Centella asiatica,
Emblica officinalis, Euphoria longan, Mimosa pudica, Rauvolfia tetraphylla, Rauwolfia serpentina, Sapindus trifoliatus, Smilax sp. and Trachyspermum copticum) in
spite of their growth in similar climatic conditions (Hussain and Srinivas 2013).
Chatterjee et al. (2010) surveyed the mycorrhizal status in three different species of
Cassia plants such as C. alata, C. occidentalis and C. sophera. Cassia alata
possesses maximum root colonisation by the AM fungus that belongs mostly to
the Glomus species followed by C. occidentalis and C. sophera. It seems that
C. alata is the most potent species for having significant antimicrobial activity.
Mycorrhizal plants (colonised by Glomus mosseae or Glomus intraradices) of
Sorghum (Sorghum bicolor) compared with non-mycorrhizal plants contained more
alcohols, alkenes, ethers and acids (Sun and Tang 2013). The AM fungi can alter
the profile of volatile organic carbon released by roots as well as the root morphology of sorghum plants to adapt to the soil environments. The rhizosphere of
mkumar9@amity.edu
28
Z.M. Solaiman and H.M. Anawar
14 common cultivars of tree peony (Paeonia suffruticosa) was colonised by AM
fungi (Shi et al. 2013). A total of 31 AM fungi species belonging to 3 genera were
identified in the rhizospheric soil. Glomus (21) was the dominant genus, followed
by Acaulospora (7) and Scutellospora (3). The Paris-type, 17 species of AM fungi
and fungal colonisation structures (hyphae, hyphal coils and vesicles) were present
in roots of medicinal plant Huangshan magnolia (Magnolia cylindrica) (Yang
et al. 2011). The species were from the genera Acaulospora (6 species), Glomus
(8 species), Gigaspora (1 species) and Scutellospora (2 species).
AM fungi (colonised by Glomus mosseae and Glomus intraradices) have
increased plant growth and salinity tolerance by various mechanisms in
B. monnieri, an important medicinal plant (Khaliel et al. 2011). Sundar
et al. (2011) identified 21 AM fungal species in roots of the medicinal plants such
as Eclipta prostrata, Indigofera aspalathoides and I. tinctoria. The mean AM fungi
colonisation and diversity pattern was dependant on edaphic factors and type of
vegetation. Panwar and Tarafdar (2006) identified 5 genera of AM fungi in the
rhizosphere of 3 medicinal plant species (Leptadenia reticulata, Mitragyna
parvifolia, Withania coagulans). The association with AM fungi of these plant
species native to the extreme environmental conditions of the Indian Thar Desert
may play a significant role in the re-establishment and conservation of these
medicinal plants.
The Artemisia annua L. (Asteraceae) is an important medicinal plant whose
secondary metabolite artemisinin is used for the treatment of cerebral malaria.
Awasthi et al. (2011) found the compatibility and synergy between AM fungus
Glomus mosseae and Bacillus subtilis bacteria and suggested the use of this
microbial consortium in Artemisia annua L. (Asteraceae) for enhancing growth
and the content and yield of artemisinin. Zubek and Blaszkowski (2009) and Zubek
et al. (2011) studied AM fungi and dark septate endophyte (DSE) associations in
36 medicinal plant species from 33 genera and 17 families. AM was found in 34 of
36 plant species, and the abundance of AM fungi hyphae in roots varied with
particular species, ranging from 2.5 % (Helianthus tuberosus) to 77.9 %
(Convallaria majalis). The mycelium of DSE was observed in 13 plant species;
however, the percentage of root colonisation by these fungi was low.
Khamna et al. (2009) obtained a total of 445 actinomycete isolates from
16 medicinal plant rhizosphere soils. Among them, 23 Streptomyces isolates
showed activity against phytopathogenic fungi. The consecutive monoculture of
Rehmannia glutinosa L. could be a causative agent to decrease the diversity of
fungal community in the rhizosphere soil (Zhang et al. 2011b). Sharma et al. (2008)
suggest the use of mixed consortium of AM fungi (Glomus geosporum,
G. microcarpum and one crude consortium of AM fungal spores) over monospecific
cultures for the sustainable cultivation and conservation of endangered medicinal
plant such as Curculigo orchioides.
The 76 medicinal plants were reported to have AM fungi in Pakistan (Gorsi
2002). Radhika and Rodrigues (2010) found that 30 out of 36 medicinal plant
species were mycorrhizal in Goa region, India. The molecular diversity of AM
fungi associated with Prunus africana revealed that 109 sequences obtained belong
mkumar9@amity.edu
2 Rhizosphere Microbes Interactions in Medicinal Plants
29
to the members of the Glomeromycota (Wubet et al. 2003), and subsequent 5.8S/
ITS2 rDNA sequence analysis indicated high AM fungal diversity and dominance
of Glomus species. Appoloni et al. (2008) analysed AM fungi community in roots
of Dichanthelium lanuginosum and found that 18S rDNA phylotypes belong to the
genera Acaulospora, Archaeospora, Glomus, Paraglomus and Scutellospora. The
most diverse and abundant AM fungi were from the genera Glomus, with the most
frequent phylotype corresponding to Glomus intraradices. The AM fungal community in the rhizosphere of Phellodendron amurense showed three general groups
of Glomus, Scutellospora and Hyponectria, respectively (Cai et al. 2009).
2.3
Effect of Microbial Inoculation on the Growth
of Medicinal Plants
More than 24 genera of nonpathogenic rhizobacteria have been identified till today.
Plant growth-promoting rhizobacteria, first defined by Kloepper and Schroth
(1978), after being inoculated on seeds, could successfully colonise plant roots
and positively enhance plant growth. Besides this, the plant root-secreted growthpromoting compounds (e.g. auxins or cytokinins) and improvement in mineral
nutrient uptake (e.g. siderophore) can increase the plant growth. The synthesis of
antibiotics or secondary metabolite-mediated induced systemic resistance can control the pathogens (biocontrol) and promote the plant growth (van Loon 2007).
AM could promote nutrient uptake, improve the functional diversity and activity
of microbes in the rhizosphere of Atractylodes lancea medicinal plant and influence
the composition of the organic matter leading to the growth of A. lancea, but not to
the quality (Guo et al. 2006). The root-nodulating bacterium, Rhizobium meliloti,
isolated from the medicinal plant, Mucuna pruriens, produced siderophores and
thus promotes the plant growth (Arora et al. 2001). The medicinal sclerophyll,
Agathosma betulina (Berg.) Pillans, grown under nutrient-poor conditions was
colonised by Cryptococcus laurentii soil yeast as a plant nutrient-scavenging
microsymbiont (Cloete et al. 2010). Guo et al. (2010) screened and exploited
molluscicidal microorganisms against Oncomelania hupensis from the rhizosphere
of medicinal plant Phytolacca acinosa Roxb. that had a higher similarity to
Aspergillus fumigatus. The symbiotic interaction between the common soil yeast,
Cryptococcus laurentii, and medicinal plant Agathosma betulina (Berg) Pillans
helped the plant growth on nutrient-poor soils (Cloete et al. 2009). The addition
of Streptomyces pactum (Act12) could improve the soil microbial activity which,
eventually, enhances the resistance and root activity of ginseng plant and could
increase yield and its quality (Zhang et al. 2013). The medicinal plants forming
association with various microorganisms can be formulated as biofertiliser and
biocontrol tools. Therefore, it is very important to identify, characterise and use
rhizospheric microorganisms associated with medicinal plants (Vasudha
et al. 2013).
mkumar9@amity.edu
30
Z.M. Solaiman and H.M. Anawar
The rhizobacterial strain Jdm2 (Bacillus subtilis) isolated from the rhizosphere
of the traditional Chinese medicinal herb Trichosanthes kirilowii enhances plant
growth and inhibits the activity of nematode and has the potential to be a safe and
effective microbial pesticide (Wei et al. 2014). The bacterial endophytes isolated
from medicinal plant Annona squamosa L. showed antimicrobial activity (Baker
and Satish 2013), and the bacterium belonged to the genus Pseudomonas sp.,
identified by using 16s rRNA and biochemical tests. Yang et al. (2012) discussed
the mechanisms involved in controlling the soilborne disease of medicinal plants by
different species of microorganisms as biocontrol agents from the following
aspects: improving host plant nutrient uptake, the nutrient and space competition
with the pathogenic bacteria, changing anatomical structure and the morphology of
roots, balancing the host plants’ endogenous hormones, activating the host plants’
defence system and restoring the balance of host rhizosphere soil conditions. Plant
growth-promoting rhizobacteria (PGPR) isolated from the medicinal weed, Cassia
occidentalis, are an attractive ecofriendly alternative to chemicals in agriculture
and open up possibilities for the utilisation of these in plant growth increase and
subsequent boost of yield for agricultural crops (Arun et al. 2012).
The mycorrhizal medicinal plants have higher nutrient uptake capacity and
growth than non-mycorrhizal plants (e.g. Karagiannidisa et al. 2011; Nisha and
Rajeshkumar 2010). The mycorrhizal inoculation increased the dry matter of five
medicinal plants (Abelmoschus moschatus, Clitoria ternatea, Plumbago zeylanica,
Psoralea corylifolia and Withania somnifera) grown in five different types of soil
(Chandra et al. 2010). The shoot height and root biomass of Poncirus trifoliata,
Piper longum, Salvia officinalis and Plectranthus amboinicus medicinal plants
were promoted by mycorrhizal colonisation (Wang et al. 2006; Rajeshkumar
et al. 2008; Geneva et al. 2010; Gogoi and Singh 2011).
2.4
Effect of Rhizosphere Microbes on P Solubility
and Availability to Medicinal Plants
The Aspergillus niger, A. fumigatus and Penicillium pinophilum fungal isolates,
identified in the rhizosphere of different plants, can effectively solubilise rock
phosphate or tricalcium phosphate (Wahid and Mehana 2000) and increase the
uptake of phosphorus (P) by the growth of plants. Pseudomonas aeruginosa is a
plant growth-promoting rhizobacterium. The application of P. aeruginosa with a
medicinal plant Launaea nudicaulis as soil amendment resulted in maximum
reduction in Macrophomina phaseolina infection on mung bean roots (Mansoor
et al. 2007). The endophytic strain of Bacillus pumilus isolated from tissues of the
medicinal plant Ocimum sanctum can be used as a bioinoculant to enhance plant
growth and also as a probiotic (Murugappan et al. 2013). Gupta et al. (2011)
evaluated the potential of phosphate-solubilising bacteria, Burkholderia gladioli,
Enterobacter aerogenes and Serratia marcescens, for utilising Mussoorie rock
mkumar9@amity.edu
2 Rhizosphere Microbes Interactions in Medicinal Plants
31
phosphate to enhance the medicinal plant growth as biofertiliser because some
medicinal plants are less dependent on chemical fertilisers. The strains differed in
the extent of rhizosphere colonisation, carbon source utilisation pattern and whole
cell fatty acid methyl esters composition.
Despite the high concentrations of total P in soil, its P concentration in the soil
solution and uptake by plants is very low (Marschner et al. 2006) due to the low
availability of inorganic and organic P compounds and poorly available inorganic P
forms (Ca phosphates, Fe/Al phosphates and P adsorbed onto Fe/Al oxides and
organic matter) (Schachtman et al. 1998; Richardson and Hadobas 1997). The
microbial biomass is another important P pool in soil ranging from 1 to more
than 10 % of total soil P (Richardson 2001), because plants and microorganisms
compete for P uptake. The microbial biomass may also represent a slow sustained
source of available P through decomposition of dead microbial cells (Oberson
et al. 2001). Plant P uptake causes depletion of available P in the rhizosphere due
to the low solubility and slow diffusion of P in soils (Jungk and Claassen 1986). The
plants with the assistance of rhizosphere microorganisms can develop various
strategies to increase P uptake and overcome the low P availability in soils.
Bacterial and mycorrhizal fungi symbiosis can increase the plant P uptake and P
acquisition efficiency (Smith and Read 2008; Rengel 1999) by increasing root
growth, mineralisation of organic P by phosphatase enzymes released by roots
and microorganisms (Tarafdar and Jungk 1987) and by excretion of organic acids
into the rhizosphere and/or changing the rhizosphere pH (Gerke and Meyer 1995;
Imas et al. 1997). The microbe in the rhizosphere has different capacity to solubilise
or mineralise poorly available P (Banik and Dey 1983) and therefore could affect P
availability to medicinal plants.
2.5
Effect of Rhizosphere Microbes on Nutrient Uptake
and Stress Tolerance
The AM fungal inoculation has played a significant positive role on plant growth
via improved acquisition of nutrients of low mobility, especially P in low-nutrient
and constrained soils. AM fungi increase plant uptake of nutrients such as P, Zn,
Cu, Mn and Fe in poor soils (Chen and Zhao 2009; Hosamani et al. 2011) and
increase the shoot dry weight of plants (Gupta and Janardhanan 1991; Hosamani
et al. 2011). The external hyphae of AM fungi can also increase NH4+ and NO3
uptake by plants and assimilate these molecules into free amino acids (Johansen
et al. 1996). However, the effectiveness of AM fungi differs with the plant species,
soil fertility and plant growth environments (Smith and Smith 2011). For example,
Zhao and Yan (2006) reported that leaf nitrogen contents were lower in the
mycorrhizal Camptotheca acuminata than its non-mycorrhizal counterpart.
AM fungi-colonised plants have greater tolerance capacity over
non-mycorrhizal plants to several biotic and abiotic stresses, such as toxic metals,
mkumar9@amity.edu
32
Z.M. Solaiman and H.M. Anawar
root pathogens, drought, high soil temperature, saline soils (Khaliel et al. 2011),
adverse soil pH and transplanting shock (Evelin et al. 2009; Lu et al. 2003; Tang
et al. 1999). Inoculation with AM fungi enhanced tolerance of Rosa multiflora to
HCO3 as indicated by greater nutrient uptake and leaf chlorophyll and lower root
iron reductase activity and alkaline phosphatase activity (Cartmill 2004). The
possible drought-induced genes may enhance the tolerance of AM plants to water
deficit (Fan and Liu 2011; Ruiz-Lozano et al. 2008). The AM colonisations may
alleviate metal stress of plants showing capability in binding heavy metals (Joner
et al. 2000; Salvaraj and Kim 2004; Prasad et al. 2011), even though the mechanisms involved in metal tolerance of AM plants are still poorly understood
(Hildebrandt et al. 2007) and need to be explored.
2.6
Effect of Rhizosphere Microbes on Quantity
and Quality Medicinal Compounds
Bacteria and AM fungi can improve secondary metabolite contents in medicinal
plants via improving plant phosphorus status or an altered hormonal balance of the
plants (Koeberl et al. 2013; Toussaint 2007). Root diseases (rot and wilt) caused by
a complex involving Fusarium chlamydosporum (Frag. & Cif.) and Ralstonia
solanacearum (Smith) are serious diseases affecting the cultivation of Coleus
forskohlii, a medicinal plant producing forskolin compound (Singh et al. 2013).
Coinoculation of Pseudomonas monteilii with Glomus fasciculatum significantly
improved the AM root colonisation and spore numbers, and Pseudomonas monteilii
can be a mycorrhiza helper bacterium. The forskolin content of tubers was significantly increased by the inoculation treatments of G. fasciculatum, P. monteilii and
P. monteilii + G. fasciculatum.
Terpenoids, phenolics and alkaloids are the three major groups of secondary
plant metabolites and natural medicinal products used for pharmacological and
therapeutical purposes. Essential oils mostly consisting of monoterpenes, sesquiterpenes and phenylpropanoids are often used as flavours and fragrances, antimicrobials and antioxidants and medicines (Deans and Waterman 1993). AM fungi
increased the content of essential oil and alterations of its composition, such as in
the medicinal plant basil (O. basilicum) (Copetta et al. 2006). Andrographis
paniculata that has been used to treat gastrointestinal tract, upper respiratory
infections, fever, herpes, sore throat and other chronic and infectious diseases in
Asian countries from ancient time contains the primary medicinal compound of
andrographolide, a colourless diterpene lactone with a bitter taste. The AM symbiosis after inoculation with Gigaspora albida produced the high concentration of
andrographolide in the leaf extracts of A. paniculata (Radhika and Rodrigues
2011), mostly at flowering growth stage.
The inoculation of Glomus intraradices, either alone or in a mixture with
G. mosseae, significantly increased total phenolic content in leaves and flower
heads of Cynara cardunculus (Ceccarelli et al. 2010). The AM fungi colonisation
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2 Rhizosphere Microbes Interactions in Medicinal Plants
33
increased the concentrations of isoflavone in roots of legume plants (Catford et al.
2006); flavonoid in white clover (Trifolium repens) (Ponce et al. 2004), Bupleurum
chinense, Ginkgo biloba and Astragalus membranaceus (Meng and He 2011);
rosmarinic acid, a highly antioxidant phenolic compound, in basil (Toussaint
et al. 2008); and total coumarin and imperatorin in Angelica dahurica (Zhao and
He 2011). The AM fungal colonisation could induce two different signalling
pathways in the accumulation of phenylpropanoid metabolism: one is through the
induction of phenylalanine ammonia-lyase and chalcone synthase, and the other is
through the suppression of isoflavone reductase (Zhao and Yan 2006).
The camptothecin in Camptotheca acuminata and vinca alkaloids in vinca
(Catharanthus roseus) are two important anticancer compounds (Rosa-Mera et al.
2011). The castanospermine is effectively used in the treatments against AIDS and
cancers (Spearman et al. 1991). Sweet basil has been traditionally used for the
treatment of headaches, coughs and diarrhoea (Jayasinghe et al. 2003). AM fungal
inoculation significantly enhanced plant growth and the total content of vinblastine
in Vinca leaves (Rosa-Mera et al. 2011), castanospermine content in seeds and
leaves of Castanospermum australe (Abu-zeyad et al. 1999), rosmarinic acid
(antioxidant activity) in sweet basil shoots (Toussaint et al. 2007), camptothecin
in Camptotheca acuminata, vinca alkaloids in vinca (Rosa-Mera et al. 2011) and
total phenols, ortho-dihydroxyphenols, flavonoids, alkaloids and tannins in the root
and leaf of O. basilicum and Coleus amboinicus (Hemalatha 2002).
However, a few other studies reported some controversial results for mycorrhizal effects on phenolic contents in medicinal plants. Zeng et al. (2013) showed
neutral effects of AM colonisation on the composition of phenolic ingredients. AM
symbiosis did not alter the total concentrations of phenolic and rosmarinic acid in
roots of Salvia officinalis (Nell et al. 2009) and the polyphenolic profile in leaves
and stems of basil (Lee and Scagel 2009) after AM fungal inoculation.
2.7
Conclusions
The quality of medicinal plants (active compound content) is largely influenced by
abiotic and biotic factors of the rhizosphere. The rhizosphere microbes play an
important role in improving medicinal values of medicinal plants. The role of
microbes in plant growth, nutrient availability, disease resistance, yield and quality
of medicinal compounds is demonstrated in medicinal plants. There are increasing
interests in the research of the interaction between medicinal plant and their
rhizosphere microbes for the improvement of medicinal plants. A wide variety of
bacteria and fungi diversity including AM fungi is recognised in the rhizosphere of
medicinal plants that have high significance in plant nutrient acquisition and
secondary metabolite alteration. The inoculation of PGPR and/or AM fungi is a
sustainable technology to enhance the quantity and quality of the medicinal plant
compounds. However, selecting and inoculating specific and efficient bacteria
and/or fungi for a particular plant are essential for the cultivation of medicinal
mkumar9@amity.edu
34
Z.M. Solaiman and H.M. Anawar
plants in order to obtain the high-quality secondary plant metabolites. Therefore,
further research is recommended to better understand the diversity and function of
rhizosphere bacteria and/or fungi and their uses in the increased production of
medicinal plants by identifying relationship between genetic and functional diversity of bacteria and/or fungal species.
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Chapter 3
Enhanced Efficiency of Medicinal
and Aromatic Plants by PGPRs
Mansour Ghorbanpour, Mehrnaz Hatami, Khalil Kariman,
and Kazem Khavazi
3.1
Introduction
Other than nutritional value for human and livestock, plants have gained significant
attention in recent years due to their secondary metabolites, which are widely used
in aromatic, therapeutic, or chemical industries. Higher plants use primary metabolites such as carbohydrates, lipids, and amino acids to synthesize various secondary metabolites that serve a variety of functions including plant defense against
herbivores and microbes, protection against environmental stresses, and contribution to specific odors, tastes, and colors in plants (Seigler 1998). Plant secondary
metabolites are unique sources for food additives, flavors, fragrances, and pharmaceuticals (Bennett and Wallsgrove 1994; Ravishankar and Rao 2000). Plants
accumulate secondary metabolites mostly under stress conditions in response to
various biotic and abiotic elicitors or signal molecules. Physiological traits and
genetic diversity, environmental conditions, geographic variation, and evolution
are among the main factors affecting the accumulation and composition of secondary metabolites (Figueiredo et al. 2008). Moreover, infection by microorganisms
and abiotic factors such as osmotic stresses can induce particular secondary metabolite pathways in plants (Sanchez et al. 2004).
M. Ghorbanpour (*) • M. Hatami
Department of Medicinal Plants, Faculty of Agriculture and Natural Resources,
Arak University, Arak, 38156-8-8349, Iran
e-mail: m-ghorbanpour@araku.ac.ir
K. Kariman
School of Earth and Environment, The University of Western Australia (M087), Crawley, WA,
6009, Australia
K. Khavazi
Department of Microbiology, Soil and Water Research Institute, Karaj, Iran
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_3
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M. Ghorbanpour et al.
Plant growth-promoting rhizobacteria (PGPRs) are a specific group of soil
bacteria that aggressively colonize the rhizosphere and rhizoplane, and substantially improve plant growth and productivity. PGPRs function as plant growth
promoters and biological control agents via direct or indirect mechanisms. Direct
mechanisms by PGPRs include the provision of bioavailable phosphorus and
nitrogen for plant uptake, sequestration of iron by siderophores, production of
plant hormones like auxins, cytokinins, and gibberellins, and lowering ethylene
levels inside plants using ACC deaminase that accumulate in plants subjected to
biotic and abiotic stresses (Glick 1995; Glick et al. 1999; Mayak et al. 2004). The
indirect mechanisms include the production of antibiotics, reducing iron availability for phytopathogens in the rhizosphere, enzymatic lysis of fungal cell wall and
insect-gut membrane secreting chitinase enzyme for the hydrolysis of chitin layer
of the eggshell of nematodes, competition with detrimental microorganisms for
sites on plant roots, and induction of systemic resistance in plants against various
pathogens and pests (Ramamoorthy et al. 2001). Bacterial strains showing PGPR
activity have been reported for diverse bacterial taxa including Agrobacterium,
Arthrobacter, Azotobacter, Azospirillum, Bacillus, Burkholderia, Caulobacter,
Chromobacterium, Erwinia, Flavobacterium, Micrococcus, Pseudomonas, and
Serratia (Gray and Smith 2005).
To date, PGPRs have been shown to promote the growth of cereals, ornamentals,
vegetables, and food crops (Vessey 2003; Lugtenberg and Kamilova 2009; Mishra
et al. 2010). However, a limited number of studies have been undertaken regarding
the interactions between PGPRs and medicinal or aromatic plants. This chapter,
therefore, aims to introduce proven or putative mechanisms by which PGPRs
promote seed germination, growth, nutrient acquisition, and production of primary
and secondary metabolites in aromatic and medicinal plants.
3.2
Seed Germination and Vigor Index in Medicinal Plants
Under PGPRs Inoculation
Medicinal plants, native to the arid lands, often readily germinate within their
native environment, while low germination rates have been observed under laboratory or field conditions (Gupta 2003). Recent advances in ex situ propagation
methods, however, encourage the cultivation of these plants and reduce the pressure
on their natural environment. Seeds and clones (produced by micro-propagation)
are the most common means of propagation in medicinal plants. For the majority of
species, seed is considered as the most effective and convenient propagation
method.
Use of PGPRs as stimulants of seed germination in medicinal and aromatic
species can provide more uniformity in germination, seedling emergence, and other
growth stages in particular flowering, which is a critical time to achieve more
bioactive secondary metabolites. PGPRs are able to increase the rate of seed
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
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germination and seedling emergence and improve plant growth (Shaukat
et al. 2006). The development stage of the plant organ (leaf, flower, and fruit
ontogeny) can be a determinant factor for the composition of volatiles (Figueiredo
et al. 1997; Badalamenti 2004). Several studies have reported increases in the yield
of the volatiles from the flower bud to the mature flower. Concomitantly, the
composition of secondary metabolites can undergo major changes, some components varying from traces to 10 % in the initial stages, and 50–70 % in the full
flowering stage (Figueiredo et al. 2008). However, there are also reports indicating
that the volatiles are largely accumulated before the organ is fully expanded
(Figueiredo et al. 2008). Therefore, uneven or poor germination and subsequently
inhomogeneous seedling growth can lead to the production of plants with variable
content and composition of secondary metabolites.
Although PGPRs have been broadly used to improve seed germination and
overall yield of many crops in different agro-ecosystems, there is a lack of literature
on seed germination and vigor index in medicinal and aromatic species. Recently,
the role of PGPRs on growth and phytochemical parameters, from seed germination
to the mature flower stage, was evaluated in two types of medicinal plants
containing different classes of secondary metabolites including alkaloids and
essential oils (Ghorbanpour et al. 2013a, b, 2014). Inoculation of Hyoscyamus
niger seedling radicles with 20 PGPR strains belonging to Pseudomonas putida
(PP) and P. fluorescens (PF) on vigor index [seedling length (root length + shoot
length) germination %] under two conditions, in vitro (with agar media) or sand
culture tubes, indicated that PGPRs can have contrasting effects on vigor index. The
most efficient strains were shown to be those producing the optimum auxin level
(PP-168 and PF-187). The PF-187 strain increased root and shoot elongation by
73 and 51 % compared with uninoculated controls, respectively. Moreover, two PP
strains (PP-4 and PP-11) had negative effects on vigor index when compared with
the uninoculated controls. Under both assay conditions, PF-187 and PP-168 strains
were the most effective strains for early seedling development (Ghorbanpour and
Hatami 2013). The fluorescent pseudomonads used had substantial effects on plant
growth under various conditions particularly via auxin secretion. However, the
production of this phytohormone at the amount beyond that is needed for plant
produces additional levels of ACC, the immediate precursor of ethylene production,
which significantly inhibits root elongation and decreases vigor index and plant
growth (Fig. 3.1) (Glick et al. 1998).
Similar to H. niger, treatment of Salvia officinalis seeds by PGPRs including
P. fluorescens (PF-23) and P. putida (PP-41, PP-108 and PP-159) differently
affected the germination and vigor parameters (Ghorbanpour and Hatami 2014).
The maximum (78.5 %) and minimum (16.75 %) germination percentages were
recorded for PP-41 and PF-23 treatments, respectively. Also, the highest germination rate, root and shoot length, seedling vigor index, and the lowest mean germination time were recorded in seeds inoculated with PP-41, a strain with the ability to
produce moderate auxin, when compared to other treatments (Fig. 3.2 and
Table 3.1). According to the studies mentioned above, the net effect of plant–
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Fig. 3.1 Schematic model
of PGPRs’ effects on
ethylene synthesis and
inhibition of root
elongation. IAA Indole
acetic acid, ACC
1-aminocyclopropane
1-carboxylic acid, and SAM
S-adenosylmethionine
(Ghorbanpour and Hatami
2014)
PGPRs interactions on seed germination, root elongation, and subsequently vigor
index could be positive, neutral, or negative.
Jahanian et al. (2012) studied the effects of seed inoculation of artichoke
(Cynara scolymus) with different PGPR strains (Azotobacter, Azospirillum,
P. putida PP-41, and PP-168) on seed germination and plant early growth characteristics. The combination of PP-168, Azotobacter, and Azospirillum strains was the
most effective treatment in increasing the germination percentage, number of
normal plants, radicle and shoot weight, shoot length, and vigority and in decreasing the mean time of germination. Moreover, either sole or the integrated application of phosphate-solubilizing bacteria along with nitrogen-fixing ones led to
significant increases in radicle and shoot length, shoot weight, coefficient of
velocity of germination, seedling vigor index, and significant decrease in mean
germination time compared to uninoculated controls.
The PGPR strain P-35 with multiple PGPR activities (like IAA, ammonia, HCN,
and catalase) was subjected to seed germination test for Withania somnifera plants.
The results established a significant enhancement in seed germination rate as well
as root and shoot growth of this valuable medicinal plant (Rathaur et al. 2012).
A commercial soil amendment containing a mixture of four PGPR strains
(Azospirillum lipoferum, Azotobacter chroococcum, P. fluorescens, and Bacillus
megaterium) was evaluated for impact on germination and initial growth of
Catharanthus roseus (Lenin and Jayanthi 2012). The results indicated that
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Fig. 3.2 Effects of Pseudomonas putida (PP-41, PP-108 and PP-159 strains) and P. fluorescens
(PF-23 strain) on root morphology, root hair formation, and seedling vigor index in Salvia
officinalis L. (Ghorbanpour and Hatami 2014)
Table 3.1 Seed germination behaviors and seedling vigor index in Salvia officinalis plants
inoculated with Pseudomonas putida (PP-41 and PP-159) and P. fluorescens (PF-23) strains
(Ghorbanpour and Hatami 2014)
PGPR
strain
treatment
Germination characteristics
Mean
Germination
germination
percentage
time (day)
(%)
Germination
rate (seed/
day)
Root
length
(cm)
Shoot
length
(cm)
Vigor
index
Control
PP-41
PP-159
PP-23
41.25c
78.50a
57.75b
16.75d
0.66c
1.05a
0.83b
0.17d
3.92c
8.45a
6.47b
2.25d
2.32c
4.20a
3.37b
1.87c
257.03c
992.13a
570.40b
69.63d
7.75a, b
4.25c
7.5b
9.75a
In each column, values followed by different letters differ significantly (P < 0.01) according to
Duncan’s multiple range test
inoculation by PGPR strains significantly increased germination rate and vigor
index. Harish Kumar and Maheshwari (2011) studied five bacterial strains (TR1–
TR5) isolated from the root nodules of fenugreek (Trigonella foenum-graecum) for
their plant growth promontory traits. The TR2 isolate was identified as Rhizobium
leguminosarum, and the other four strains were Ensifer meliloti. The maximum
increments in vigor index, nodule number, and root and shoot biomass were
recorded for seeds inoculated with consortium (TR1 + TR2) followed by single
inoculation as compared to uninoculated fenugreek plants. In addition, seed treatment of two Acacia senegal genotypes with B. licheniformis or Sinorhizobium
saheli, either individually or in combination, had positive effects on the phenotypic
traits of germination (Singh et al. 2011). However, inhibition of seed germination
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M. Ghorbanpour et al.
has also been recorded when Ambrosia artemisiifolia seeds were inoculated with
P. fluorescens (Vrbnicanin et al. 2011). Moreover, P. fluorescens has been classified
as either deleterious rhizobacteria (DRB) (Zdor et al. 2005) or PGPR (Jaleel
et al. 2007), depending on the experimental conditions in which bacterial cultures
develop.
Growth promotion and beneficial effects conferred by PGPRs may involve
various mechanisms of action. Direct growth promotion by PGPRs is regarded as
one of the most important mechanisms of action, which include the production of
plant growth regulators such as indole acetic acid (IAA) (Mishra et al. 2010),
gibberellic acid (Narula et al. 2006), cytokinins (Castro et al. 2008), and ethylene
(Saleem et al. 2007). The improved germination rate in plants inoculated by PGPRs
(Nelson 2004) may be due to the increased synthesis of hormones like gibberellins,
which would have triggered the activity of specific enzymes such as a-amylase that
promote early germination by facilitating starch assimilation (Bharathi 2004).
Moreover, significant increases in seedling vigor have been attributed to better
synthesis of auxins (Bharathi 2004).
3.3
PGPRs Stimulate Plant Growth and Modify Enzyme
Activities in Medicinal and Aromatic Plants Under
Normal or Stress Conditions
Plant growth in the field is a reflection of diverse interactions with physiochemical
and biological components that exist in the soil and modulated by environmental
conditions. Microorganisms are a driving force for fundamental metabolic processes in soil. The genetic and functional diversities of the extensive microbial
populations have a critical impact on soil function and plant growth (Nannipieri
et al. 2003). Plant production and health are negatively affected by a large number
of both biotic and abiotic stresses through the formation of reactive oxygen species
(ROS). The induction of ROS-scavenging enzymes including superoxide dismutase
(SOD), peroxidase (POX), and catalase (CAT) is the most common mechanism for
detoxifying ROS synthesized under stress conditions (Munns and Termaat 1986).
To deal with these biotic and abiotic stresses, chemical inputs have been extensively used during the past few decades to achieve high yields, causing harmful
effects on the environment. Sustainable agriculture needs to be further promoted as
a key strategy to counteract the rapid decline in environmental quality via the
gradual reduction in the use of chemical fertilizers and pesticides accompanied
by greater use of the biological and genetic potential of plant species and microbial
communities in order to gain sustainable high yields. The plant’s ability to modify
its physiology and metabolism to either avoid or partially overcome the environmental stresses can be improved by the aid of certain microorganisms existing in
the rhizosphere (Govindasamy et al. 2008). Here, we introduce several detailed
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
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mechanistic studies exploring the positive effects of PGPRs on medicinal plants
under normal or stress conditions.
The effects of inoculation with PGPR strains P. putida (PP-168) and
P. fluorescens (PF-187) on growth parameters, proline and chlorophyll content,
leaf relative water content (RWC), as well as antioxidant enzymes activity (SOD,
POX, and CAT) were investigated in Hyoscyamus niger under three water-deficit
stress (WDS) levels of 30 % (W1), 60 % (W2), and 90 % (W3) water depletion of
field capacity (Ghorbanpour et al. 2013a). Inoculation with PP and PF strains
minimized the deleterious effects of WDS on growth parameters, whereas
uninoculated plants had a grave reduction in plant growth. The number of leaves,
leaf area, and leaf greenness decreased with the increase in water stress levels, but
PP- and PF-inoculated plants had lower reduction percentages compared to
uninoculated control plants. The greatest accumulation of proline was found in
PF-inoculated plants against severe WDS. In contrast, proline accumulation in
PP-inoculated plants and in uninoculated control plants was observed only up to
the W2 treatment level, and it later started to decline, particularly in the
uninoculated control plants. Furthermore, inoculation with PP and PF strains
significantly improved the chlorophyll content of plants. The results also unearthed
that the RWC was significantly higher in plants subjected to PP and PF strains under
all WDS conditions than their respective controls. This effect may be associated
with the hydraulic nature of branch root junctions, which facilitate the radial flow of
water (Kothari et al. 1990). The advantageous effects of PGPRs and common
adaptation mechanisms of plants exposed to WDS are always mutually related to
exceptional changes in root morphological and anatomical traits such as root
branching networks and biomass (Fig. 3.3). The PF strain had higher efficiency
than the PP strain in plants growing under moderate (W2) and severe (W3) WDS
conditions. This outstanding capacity might be linked with the geographical origin
of the PF strain as it was isolated from the wheat rhizosphere in rainfed wheat fields
(dry land farming), where water is restricted and dry periods often take place.
In contrast, the PP strain was isolated from wheat rhizosphere in irrigated wheat fields
showing no phosphate-solubilizing activity and inferior performance under limited
water supply compared to the PF strain (Ghorbanpour et al. 2013a).
Thus, it can be concluded that selection of PGPR strains should be based on
multiple plant growth-promoting characteristics and their ecological adaptation
with respect to the potential abiotic stresses of the host plant.
Inoculation with PGPRs can stimulate the activities of antioxidant enzymes and
increase proline accumulation under drought stress conditions (Kohler et al. 2008)
and induce systemic resistance against fungal plant diseases through the activation
of various defense-related enzymes (Bharathi 2004). The activities of SOD and
POX in root and leaf tissues of Hyoscyamus niger plant increased to a significant
extent after inoculation with PP and PF strains (and with WDS treatment as well),
while CAT activity decreased with increasing WDS, except in PF-inoculated plants
(Ghorbanpour et al. 2013a). This is in keeping with a report by Kohler et al. (2008),
suggesting that the overexpression of SOD, if accompanied by enhanced
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M. Ghorbanpour et al.
Fig. 3.3 Effects of seed inoculation with Pseudomonas putida (PP-168) and P. fluorescens
(PF-187) on root and shoot growth in Hyoscyamus niger (Ghorbanpour et al. 2013a)
H2O2-scavenging mechanisms like CAT and POX activities, is an important
antidrought mechanism to cope with oxidative stress during WDS conditions.
The effects of water stress and PGPR strains Pseudomonades sp., B. lentus, and
Azospirillum brasilense were assessed on proline, soluble carbohydrates, chlorophyll, and mineral content in basil (Ocimum basilicum L.) plants (Heidari
et al. 2011). The proline and soluble carbohydrate content increased significantly
with increasing water stress in plants inoculated with Pseudomonas sp. and
B. lentus, respectively. The chlorophyll content was also increased in all plants
inoculated with the PGPR strains.
PGPR-mediated resistance has been documented against certain biotic stresses.
Bacterization of seeds of cucumber plants with different PGPR strains resulted in
enhanced growth and efficiency, and also induced resistance against bacterial wilt,
which is caused by Erwinia tracheiphila and transmitted by a beetle vector
(Zehnder et al. 2001). In this case, the induced systemic resistance was attributed
to a reduction in cucurbitacin (a secondary metabolite stimulating the beetle
feeding) and induction of other plant defense mechanisms.
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The general mechanisms by which PGPRs enhance plant growth and productivity are given in Fig. 3.4 which are as follows: (1) producing plant growth
regulators including IAA (Mishra et al. 2010), gibberellic acid (Narula
et al. 2006), cytokinins and analogs (Castro et al. 2008), jasmonate, salicylate,
and volatile growth stimulants such as ethylene and 2,3-butanediol (Saleem
et al. 2007; Vessey 2003); (2) producing ACC deaminase (1-amino-cyclopropylcarboxylic acid) to reduce the ethylene levels in the roots of developing plants
(Dey et al. 2004); (3) asymbiotic nitrogen fixation (Ardakani et al. 2010); (4) exhibition of antagonistic activity against plant pathogens by producing iron-chelating
Fig. 3.4 A diagram of signaling cascades involved in plant growth promotion by PGPRs. Thick
pink arrows indicate secretions or bioactive components from the PGPRs. Dark green ovals are
phytohormones; pink boxes show the exudate elicitors in the signaling cascades; solid black
arrows represent active signaling pathways; broken lines indicate inhibitory effects [modified
from Ping and Boland (2004)]. Abbreviations: ISR induced systemic resistance, SAR systemic
acquired resistance, NO nitric oxide, NPR1 nonexpressor of PR genes, PR pathogenesis-related
proteins, ROS reactive oxygen species, LRR-RLK leucine-rich repeat receptor-like kinases, ACC
1-Aminocyclopropane-1-carboxylate deaminase
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siderophores, ß-1,3-glucanase and chitinase enzymes, antibiotics, fluorescent pigments, and cyanide (Pathma et al. 2011); and (5) solubilization of phosphate and
other nutrients (Hayat et al. 2010). PGPRs may simultaneously apply a combination
of these mechanisms to improve the plant’s performance (van Loon 2007;
Martinez-Viveros et al. 2010). However, regardless of the type of mechanism
involved, PGPRs must colonize the rhizosphere or root itself (Glick 1995).
Lenin and Jayanthi (2012) observed that root inoculation of Catharanthus roseus
with different PGPR strains (Azospirillum lipoferum, Azotobacter chroococcum,
P. fluorescens, and B. megaterium) increased chlorophyll and nutrient (N, P, and K)
content. They concluded that PGPRs in combination have a greater potential to
increase plant growth, nutrient uptake, and yield. Similarly, vegetative growth and
chemical composition in Catharanthus roseus were promoted by the combined
treatment of Azotobacter and phosphate-solubilizing bacteria (Attia and Saad
2001). Together, inoculation with diverse PGPR strains can contribute to
maintaining good soil health and fertility in order to achieve sustainable high yields
and high-quality products.
Arbuscular mycorrhizal (AM) fungi interact synergistically with other soil
microorganisms such as nitrogen-fixing bacteria (Barea and Azcon-Aguilar
1983), phosphate-solubilizing bacteria (Villegas and Fortin 2002), and biocontrol
agents (Abdel-Fattah and Mohamedin 2000) to favor plant growth. This interaction
could be direct by providing niche and/or habitat or indirect by modifying physiology of the host plant (Bianciotto et al. 2000; Walley and Germida 1997). PGPRs
in combination with other beneficial microorganisms such as AM fungi can induce
plants to produce certain metabolites making the rhizosphere a more suitable
environment for their stay (Dutta and Podile 2010). Certain PGPRs have been
reported to enhance the activity of AM fungi and plant growth, consequently
(Jayanthi et al. 2003). It appears that PGPRs and AM fungi establish mutually
beneficial relationships in rhizosphere to support their co-existence and promote the
plant’s performance.
Investigations into the interaction between the AM fungus G. aggregatum and
the PGPR strain B. coagulans and T. harzianum in soil and their consequent effects
on growth, nutrition, and enzyme activity of Solanum viarum seedlings demonstrated that plant biomass and nutrient (P, Fe, Zn, Cu, K, and Mn) content were
maximum in the plants co-inoculated with all three microorganisms
(Hemashenpagam and Selvaraj 2011). The positive effects were probably due to
the enhanced mycorrhizal colonization resulting in efficient nutrient uptake. The
results also showed that acid phosphatase, alkaline phosphatase, and dehydrogenase
activities in the root zone soil of all the inoculated seedlings were significantly
higher compared to those in uninoculated control plants. Moreover, root zone soil
of plants co-inoculated with all three microbes had higher B. coagulans population
suggesting the stimulatory effect and synergistic activity between the organisms
involved. Here, the mycorrhiza helper bacteria enhanced the activity of
G. aggregatum presumably by producing organic acids which serve as a carbon
source to the fungus or by producing hydrolytic enzymes enabling the AM fungus
to penetrate and ramify in the root system of the host plant (Lakshmipathy
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
53
et al. 2002; Selvaraj et al. 2008). In another study, inoculation of pot marigold
(Calendula officinalis L.) seeds with PGPR strains (Azotobacter, Pseudomonas, and
Azospirillum) and the AM inocula substantially increased growth parameters, root
and shoot dry weight, photosynthetic pigments (chlorophyll a and b, carotene, and
xanthophylls), and the content of N, P, and K in leaves and roots (Hosseinzadah
et al. 2011).
Kohler et al. (2008) investigated the effects of inoculation with the PGPR strain
P. mendocina Palleroni, alone or in combination with an AM fungus
(G. intraradices or G. mosseae), on activities of antioxidant enzymes (SOD,
CAT, and POX), phosphatase and nitrate reductase, and solute accumulation in
leaves of Lactuca sativa L. cv. Tafalla under different levels of water stress. At
moderate drought, PGPR and AM inoculation with G. intraradices, alone or in
combination, significantly stimulated the nitrate reductase activity. At severe
drought, inorganic fertilization and P. mendocina inoculation, alone or in combination with either of the selected AM fungi, significantly increased phosphatase
activity in lettuce roots and proline accumulation in leaves. Inorganic fertilization
and combined treatment of PGPR with either AM fungus showed the highest values
of leaf POX activity under severe drought conditions. The highest CAT activity was
recorded in the fertilized plants inoculated by P. mendocina grown under severe
stress conditions. These results highlight the potential capacity of PGPRs to alleviate the oxidative damage produced under WDS (Kohler et al. 2008). Similarly,
Liddycoat et al. (2009) demonstrated the remarkable effects of PGPRs on plant
vigor and productivity under stress conditions. The effects of PGPRs (Pseudomonas
sp.) treatment on 3-week-old seedlings and seeds of two asparagus (Asparagus
officinalis L.) cultivars (Guelph Millennium and Jersey Giant) were studied.
According to the results, single inoculation of seedlings resulted in positive growth
response under optimal and drought stress for both cultivars tested. Seed inoculation led to enhanced growth for Guelph Millennium under optimal conditions,
while no positive response was observed for the Jersey Giant cultivar under either
normal or stress treatments.
The literature noted above highlights the key role of PGPRs to improve nutrition
and productivity in various plants with therapeutic and industrial significance. The
potential biofertilizer activities of PGPRs could be divided into five distinct areas
including biological N2 fixation, increasing the nutrient availability in rhizosphere,
increasing the root surface area, enhancing beneficial symbioses of the host plant,
and finally the combinations of all these mechanisms (Bhattacharyya and Jha 2012).
However, the effectiveness of PGPRs–plant interactions depends on soil biological
components, the genetic and physiological properties of the organisms involved,
and their adaptation to the existing ecosystem-related constraints.
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3.4
M. Ghorbanpour et al.
PGPRs Function as Biotic Elicitors in the Biosynthesis
of Plant Secondary Metabolites
Plant secondary metabolites are unique sources for pharmaceuticals, fragrances,
flavors, food additives, and other industrially important compounds. The major
roles of plant secondary metabolites are to protect plants from attack by insect
pests, herbivores, and phytopathogens or to help plants survive other biotic and
abiotic stresses. The environmental stresses (microbial, physical, or chemical
factors) can function as biotic/abiotic elicitors leading to an increase in the production of secondary metabolites (Radman et al. 2003; Ghorbanpour et al. 2013a, b,
2014). The biotic elicitors have biological origin and are derived from microorganisms such as fungi, bacteria, viruses, or plant cell wall components and
chemicals that are released by plants against phytopathogens or herbivore attack.
Thus, elicitors could be employed for improving the production of plant valuable
secondary metabolites (Namdeo 2007).
Rhizosphere microbes such as PGPRs are best known as biotic elicitors, which
have the potential to induce the synthesis of secondary metabolites in plants. Below,
we summarize some of the recent studies dealing with the major role of PGPRs to
improve the production of secondary metabolites in plants. The effects of PGPR
strains P. putida (PP-168) and P. fluorescens (PF-187) were studied on the root and
shoot content and yield of two tropane alkaloids hyoscyamine (HYO) and scopolamine (SCO) in black henbane (Hyoscyamus niger) under different WDS levels
(30, 60, and 90 % water depletion of field capacity; W1, W2, and W3, respectively)
at vegetative, full flowering, and seed-ripening stages (Ghorbanpour et al. 2013a,
b). The SCO content of roots in PGPR-inoculated and uninoculated control plants
increased significantly with increasing WDS up to W2 treatment, and later it started
to decline, except for PF-inoculated plants, which kept an upward trend continuously. The highest root SCO content was observed in the PF-inoculated plants
under W3 conditions. Also, the maximum root HYO content was observed in W3
treatment, where both PP and PF strains had identical effects in this regard. In
shoots, however, HYO content significantly increased with increasing WDS in both
PGPR treatments. The SCO content of shoots in all employed treatments had same
changes as root, and was mildly increased with increasing WDS only under PF
treatment. Inoculation of H. niger plants with the PF strain promoted HYO and
SCO accumulation in both root and shoot organs. Almost the same trend was
observed for alkaloid yield in both tissues under all employed treatments. Although
shoot HYO yield decreased with increasing WDS in both PGPR-inoculated and
uninoculated control plants, the reduction percentage in PGPR treatments was
lower than uninoculated controls. Shoot SCO yield also decreased with increasing
WDS in PP-inoculated and uninoculated control plants, but in plants inoculated
with the PF strain showed unchanged. The largest total alkaloids (HYO + SCO)
yield belonged to the PP treatment under W1 conditions. Accordingly, it can be
concluded that an integrative use of effective PGPRs (biotic elicitor) and WDS
(abiotic elicitor) could be an encouraging and eco-friendly strategy for increasing
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
55
Fig. 3.5 Diagram of a generic tropane alkaloid-producing plant like Hyoscyamus niger. The
diagram highlights the key role of plant roots in determining the spatial and temporal patterns of
bioactive secondary metabolites such as hyoscyamine and scopolamine synthesis in response to
biotic and abiotic (nutrient deficiency) stresses
the yield and content of these two alkaloids in H. niger organs (Ghorbanpour
et al. 2013a). Furthermore, PP-inoculated plants under W1 conditions had higher
proportion of fine roots compared to other treatments. Plant fine roots without
secondary growth have been found to be the principal site for production of tropane
alkaloids and the location for main enzymes involved in their biosynthesis pathway
(Suzuki et al. 1999). Although root is known to be the location for the biosynthesis
of tropane alkaloids in Solanaceae, these alkaloids may be transported through the
xylem to the aboveground parts of the plant (Figs. 3.5 and 3.6).
Higher plants activate various defense mechanisms when attacked by microbial
pathogens such as fungi, bacteria, or viruses. These defense responses include
suicide of the attacked host cell (hypersensitive response); the production of
antimicrobial secondary metabolites (phytoalexins); the production of pathogenesis-related (PR) proteins with potential antimicrobial properties; and the production and oxidative cross-linking of cell wall polymers (Penninckx et al. 1998).
The effective defense system is a result of a synchronized expression of a series of
these defense responses (Ayers et al. 1976). Ghorbanpour et al. (2013a, b) observed
that Hyoscyamus niger plants inoculated with PGPRs had higher values of HYO
than SCO, which could be due to the high antimicrobial activity of HYO. AbdelMotal et al. (2009) investigated the antifungal activity of HYO and SCO against
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M. Ghorbanpour et al.
Fig. 3.6 Biosynthetic steps
for tropane alkaloids. PMT
putrescine
N-methyltransferase; TR I
tropine-forming tropinone
reductase; TR II
pseudotropine-forming
tropinone reductase; H6H
hyoscyamine-6Hydroxylase
40 fungal strains associated with Hyoscyamus muticus and found that all fungal
strains were tolerant to SCO but sensitive to HYO.
The essential oils (EOs) production can also be positively affected by PGPRs.
Treatment of cuttings and foliage of Salvia officinalis plants with PGPR strains
P. fluorescens (PF-23) and P. putida (PP-41 and PP-159) significantly affected the
EOs content, yield, and composition (Ghorbanpour et al. 2014). The highest
(3.95 g/plant) and lowest (1.22 g/plant) EOs yields were observed for PP-159 and
uninoculated plants, respectively. Plants inoculated with PP-159 or PP-41 showed
significant increases in total EOs yield of 69.1 and 68.5 % compared to
uninoculated controls, respectively. The increases in total essential oil yield in
response to PGPRs inoculation were due to both increased plant dry weight and
the biosynthesis of terpenes. The increased EOs yield was associated with a
significantly larger density of trichomes, the main structure for EOs secretion
(Fig. 3.7). Totally, 27 different compounds were identified in the EOs of Saliva
officinalis plants under all employed treatments. Inoculation with PGPRs (PP-159
in particular) stimulated the production of certain monoterpenes such as cisthujone, camphor, and 1,8-cineol.
Essential oils serve important ecological roles. The reported increases in the
synthesis of EOs can be considered as a defensive response to colonization by
harmful microorganisms, since several EOs exhibit antimicrobial properties
(Sangwan et al. 2001). The EOs compounds rich in cis-thujone, camphor, and
1,8-cineole (eucalyptol) are well-known chemicals with strong antimicrobial activity against different pathogenic bacteria (Tzakou et al. 2001; Cha et al. 2005).
Ghorbanpour et al. (2014) proved that the EOs of Saliva officinalis plants under
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
57
Fig. 3.7 Effect of foliar application of Pseudomonas putida (PP-41 and PP-159 strains) and
P. fluorescens (PF-23 strain) on density of trichomes in Salvia officinalis plants grown in pot
cultures under greenhouse conditions (Ghorbanpour et al. 2014)
PGPRs treatment (PP-159) have strong antibacterial activity (disc diffusion) against
the test pathogenic microorganisms including gram-positive (Staphylococcus
aureus, S. epidermidis, Enterococcus faecalis, and Streptococcus agalactiae) and
gram-negative (Escherichia coli) bacteria (Tables 3.2 and 3.3). The EOs obtained
from PP-inoculated plants showed the maximum antibacterial activity with 23.44mm inhibition zone against Staphylococcus aureus. The minimal inhibitory concentration (MIC) and minimal bactericidal concentration (MBC) values for
Escherichia coli were 5 and 10 μl for EOs obtained from control plants, while
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M. Ghorbanpour et al.
Table 3.2 Antibacterial activity of Salvia officinalis essential oils against test microorganisms in
plants inoculated with a PGPR strain (PP-159) and uninoculated control plants (Ghorbanpour
et al. 2014)
Pathogenic
bacteria
Inhibition zone (mm)
EOs of
EOs of PP-159
control
treated plants
plants
EOs (μL) in 5 ml of pathogen
suspension
EOs of
EOs of control
PP-159-inoculated
plants
plants
10
20
30
5
10
20
30
Staphylococcus
aureus
19.54 1.61
23.44 1.74
5
+
+
+
+
+
+
++
+
++
++
Staphylococcus
epidermidis
14.32 1.42
18.36 1.14
+
+
+
+
++
++
+
Escherichia coli
Enterococcus
faecalis
8.65 0.76
12.62 0.98
11.78 0.65
13.54 1.12
+
+
+
+
+
++
++
++
+
Streptococcus
agalactiae
11.23 1.01
10.42 0.93
+
+
+
+
+
+
+
+
+
+
+
+
+
+
+
+
+
++
++
+
Antimicrobial activities were expressed as inhibition diameter zones in millimeters (mm),
(negative) ¼ 0 mm; + (weak) ¼ 1–4 mm; ++ (moderate) ¼ 5–10 mm; +++ (strong) ¼ 10–15 mm
and ++++ (very strong) 16 mm
Table 3.3 Antibacterial activity of Salvia officinalis essential oils (MIC and MBC, μg/ml) against
test microorganisms in plants inoculated with a PGPR strain (PP-159) and uninoculated plants
using the disc diffusion method (Ghorbanpour et al. 2014)
Pathogenic bacteria
EOs of control plants
MIC
MBC
EOs of PP-159-inoculated plants
MIC
MBC
Staphylococcus aureus
Staphylococcus epidermidis
Escherichia coli
Enterococcus faecalis
Streptococcus agalactiae
2
3
5
3
3
1
3
3
2
4
4
5
10<
4
6
2
4
6
4
6
MIC minimal inhibitory concentration; MBC minimal bactericidal concentration
these values were 3 and 6 μl for plants inoculated with PP-159, respectively
(Table 3.3).
Banchio et al. (2008) studied the effects of PGPR strains P. fluorescens,
B. subtilis, Sinorhizobium meliloti, and Bradyrhizobium sp. on qualitative and
quantitative composition of EOs in Origanum majorana. The results demonstrated
that inoculation with PGPRs can increase the production of certain terpenes. Plants
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
59
inoculated with Bradyrhizobium sp. or P. fluorescens showed significant increases
in total EOs yield by 10- and 24-fold, respectively. Based on the results, they
suggested that increases in total EOs yield in response to inoculation were not
merely due to increased biomass, and might have resulted from increased biosynthesis of terpenes. The main compounds affected by inoculation with
P. fluorescens were terpinene-4-ol, cis-sabinene hydrate, trans-sabinene hydrate,
and a-terpineol as the concentrations of these compounds in inoculated plants were
>1,000-fold higher than uninoculated controls. Furthermore, the lack of effect of
B. subtilis and S. meliloti strains tested was attributed to their poor adaptation to
root exudates and/or insufficient root colonization.
The synergistic effects of combined inoculation of PGPRs with AM fungi have
been reported on the production of EOs in plants. According to Prasad et al. (2012),
the chemical composition of geranium oil was significantly affected by inoculation
with phosphate-solubilizing bacteria (PSB) and/or AM fungi and phosphate fertilization. The content of linalool, geranial, 10-epi-γ-eudesmol, and citronellol in
geranium oil increased and that of cis- and trans-rose oxide decreased by inoculation with PSB alone or in combination with AM fungi as compared to uninoculated controls. The changes in various constituents in the EOs of all inoculated and
fertilized geranium plants could be related to the enhanced uptake of P and divalent
metallic cations in plant tissues (Prasad et al. 2012).
In a study by Vafadar et al. (2013), tissue culture-regenerated plantlets of Stevia
rebaudiana Bertoni were transferred to pots and subsequently inoculated with
PGPR strains (B. polymyxa, P. putida, and Azotobacter chroococcum) and an AM
fungus (G. intraradices). Although inoculation with a single microorganism significantly increased the stevioside content, the highest stevioside value was obtained in
plants dually inoculated with G. intraradices + Azotobacter chroococcum, followed
by G. intraradices + B. polymyxa and Azotobacter chroococcum + P. putida. Triple
inoculations had less positive effects compared to dual inoculations, probably due
to higher competition between microorganisms (Vafadar et al. 2013).
The root system of Italian oregano (Origanum majoricum) was subjected to
inoculation with three PGPR strains (P. fluorescens, B. subtilis, and Azospirillum
brasilense), and the EOs content was measured (Banchio et al. 2010). The total
EOs yield for plants inoculated with P. fluorescens or Azospirillum brasilense was
approximately 2.5-fold higher than controls, without change of quantitative oil
composition. The major EOs compounds cis- and trans-sabinene hydrate,
γ-terpinene, carvacrol, and thymol showed increased biosynthesis.
Nonpathogenic PGPRs have been shown to stimulate the biosynthesis of secondary metabolites in plants through a mechanism termed ISR (induced systemic
resistance) (Van Loon and Glick 2004). It is well established that biological agents
can act as effective elicitors of key enzymes involved in biosynthetic pathways of
secondary metabolites (Chen et al. 2000), which are clearly related to plants’
defense responses against pathogenic agents despite being induced by nonpathogenic bacteria (Kloepper 1993).
Biosynthesis of terpenoids depends on primary metabolism, e.g., photosynthesis,
and oxidative pathways for carbon and energy supply (Singh et al. 1990).
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60
M. Ghorbanpour et al.
Giri et al. (2003) found that net photosynthesis of PGPRs hosting plants increases as a
result of improved nutritional status. Factors linked with increased dry matter production may influence the interrelationship between primary and secondary metabolism,
leading to increased biosynthesis of secondary metabolites (Shulka et al. 1992). The
increased plant biomass appears to be correlated with a greater availability of substrate
for monoterpene biosynthesis (Harrewijn et al. 2001). The increased concentration of
monoterpenes in PGPR-inoculated plants may be due to growth-promoting substances
produced by the microorganisms, which affect metabolic pathways in plants.
The effect of combined inoculation of Begonia malabarica Lam. (Begoniaceae)
plants by an AM fungus (G. mosseae), a PGPR strain (B. coagulans), and T. viride
was studied on the production of secondary metabolites (Selvaraj et al. 2008).
Plants inoculated with microbial consortium consisting of G. mosseae
+ B. coagulans + T. viride showed the highest increase in leaf secondary metabolites
(total phenols, ortho dihydroxy phenols, flavonoids, alkaloids, and tannins)
followed by the plants dually inoculated with G. mosseae + B. coagulans.
In a similar study, the effects of the AM fungus G. aggregatum, the PGPR strain
B. coagulans, and T. harzianum were evaluated on secondary metabolites content
of Solanum viarum seedlings (Hemashenpagam and Selvaraj 2011). Triple inoculation of G. aggregatum + B. coagulans + T. harzainum resulted in maximum
secondary metabolites including total phenols, orthodihydroxy phenols, flavonoids,
alkaloids, saponins, and tannins. Here, the higher secondary metabolites values in
inoculated plants were attributed to the enhanced mycorrhizal colonization and
improved nutrient status of the host plants.
Cappellari et al. (2013) investigated the effects of single inoculation and
co-inoculation with two PGPR strains (P. fluorescens and Azospirillum brasilense)
on EOs composition and phenolic content in Mexican marigold (Tagetes minuta)
and observed that EOs yield increased by 70 % in P. fluorescens-inoculated and
co-inoculated plants in comparison with uninoculated controls, without altering the
EOs composition. The biosynthesis of major EOs components increased in inoculated plants. The total phenolic content was two-fold higher in singly inoculated or
co-inoculated treatments than in uninoculated control plants. Accordingly, they
suggested that considering the economic importance of monoterpenes and phenolic
compounds for a variety of applications in food and cosmetic industries,
P. fluorescens and other suitable PGPRs have clear potential for improving EOs
yield and productivity of cultivated medicinal plants.
Employing microorganisms as coculture in biotization has been another important area of research in recent decades. Biotization is a metabolic response of
in vitro-grown plant materials to microbial inoculants leading to developmental
and physiological changes of the derived propagules, which enhances resistance
against biotic and abiotic stresses in plants. Here, plantlets are usually cocultured
with PGPRs to achieve higher biomass and secondary metabolites. For instance,
Origanum vulgare L. plantlets cocultured with Pseudomonas spp. produced more
phenolics and chlorophyll than nonbacterized control plants (Nowak 1998).
The use of biotic elicitors is one of the effective strategies to increase the
production of important secondary metabolites in plants. Secretions or bioactive
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
61
components from PGPRs (Fig. 3.4), besides being involved in plant growth promotion, are the components that were found to work in an elicitor signal transduction network. On the other hand, indole acetic acids (IAAs), cytokinins (CTKs),
gibberellins (GAs), brassinosteroids (BRs), salicylic acid (SA), jasmonic acid
(JA or analogs), ethylene, abscisic acid (ABA), nitric oxide (NO), and ROS
which increase plant immunity by activating defense pathways, have long been
observed to be transducers of elicitor signals in the production of plant secondary
metabolites. Multiple signaling pathways and important mechanisms of action of
elicitors in the biosynthesis of plant secondary metabolites are shown in Fig. 3.8.
Signal perception is regarded as the first committed step of the elicitor signal
transduction pathways in plants. Following perception, plant receptors are activated
initially, and then in turn they activate their effectors such as ion channels,
GTP-binding proteins (G-proteins), and protein kinases. The activated effectors
transfer the elicitor signals to secondary messengers, which further amplify the
elicitor signal to other downstream reactions (Ebel and Mithoefer 1998; Blume
et al. 2000). The sequentially occurring events and reactions in elicitor-induced
defense pathways can be organized as follows: perception of elicitor by a receptor,
reversible phosphorylation and dephosphorylation of plasma membrane proteins
and cytosolic proteins, cytosolic [Ca2+] cyt spiking, plasma membrane depolarization, Cl and K+ efflux/H+ influx, extracellular alkalinization and cytoplasmic
acidification, mitogen-activated protein kinase (MAPK) activation, NADPH oxidase activation and ROS production, early defense gene expression, ethylene and
jasmonate production, late defense response gene expression, and accumulation of
secondary metabolites (Zhao et al. 2005).
Different molecules produced by PGPRs play a crucial role in pathways linked to
the biosynthesis of secondary metabolites. Salicylic acid (SA) is a well-known
inducer of plant’s systematic acquired resistance (SAR) in plant–microbe interactions
through inducing expression of genes related to the biosynthesis of certain classes of
secondary metabolites in plants (Taguchi et al. 2001). For example, indole alkaloids
can be induced in C. roseus cell cultures by acetylsalicylic acid, an analog of SA
(Zhao et al. 2000). Nitric oxide (NO), besides its effects on root branching and
architecture, serves as a signal molecule for plant growth, development, and defense
(Neill et al. 2002). Transcriptional profiling studies showed that NO treatment
induces some stress- and disease-related signal transduction component genes along
with defense genes, implying that the NO signal pathway(s) could be involved in
secondary metabolism (Aziz et al. 2003). In addition, fungal elicitors were shown to
stimulate saponin production in ginseng cell cultures, and this is partially mediated by
NO, with NO biosynthesis also being induced by the fungal elicitor (Hu et al. 2003).
Exposure of plant cell culture or intact plant to jasmonic acid (JA), methyl
jasmonate, as well as their conjugated compounds can stimulate the biosynthesis
of secondary metabolites (Tamogami et al. 1997). The JA signaling pathway is
generally regarded as an integral signal for the biosynthesis of many plant secondary products including terpenoids, flavonoids, alkaloids, and phenylpropanoids.
Many elicitors (like pathogens and PGPRs) stimulate endogenous JA biosynthesis
in plants, so the JA signaling pathway functions as a transducer or mediator for
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62
M. Ghorbanpour et al.
Fig. 3.8 A schematic model of signal transduction events by elicitors, leading to the expression of
genes encoding enzymes involved in the biosynthesis of secondary metabolites in plants. Different
elicitors are perceived by distinct membrane receptors, though they may activate the same
signaling pathways. The activated receptors may then activate ion channels and G-proteins and
subsequently activate phospholipases (such as PLA2), through Ca2+ signaling or by G-protein
coupling. Phospholipases hydrolyze phospholipids such as PC, into fatty acid and lysoPC; the
former can function as a precursor for biosynthesis of JA and related oxylipins via the
octadecanoid pathway, or peroxidized by reactive oxygen species (ROS) to produce another
class of pentacyclic oxylipin phytoprostanes. Elicitors also activate mitogen-activated PK
(MAPK) cascades that phosphorylate transcription factors regulating the expression of early and
late response genes. All these pentacyclic oxylipins can activate biosynthesis of secondary
metabolites in plants (modified from Zhao et al. 2005)
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
63
elicitor signaling pathways, leading to the accumulation of secondary metabolites
in plants (Mueller et al. 1993). Application of methyl-jasmonate (0.5 mM) significantly increased the quantity of monoterpenes in basil (Ocimum basilicum) via
increasing the number of transcripts of the enzymes linked to metabolic pathways
of monoterpenes (Kim et al. 2003).
Ethylene is another phytohormone that regulates a wide range of plant processes
including growth, development, and defense responses, and its production can be
induced by various stresses and microbial infections like PGPRs. However, the
concentration of ethylene in the culture is critical for acquiring desirable effects, i.e.,
low concentrations can promote the elicitor-induced production of secondary metabolites, whereas high concentrations may have inhibitory effects (Zhao et al. 2004).
Different elicitors are perceived by distinct membrane receptors, though they
may activate the same signaling pathways. The activated receptors may then
activate ion channels and G-proteins and subsequently activate phospholipases
(such as PLA2), through Ca2+ signaling or by G-protein coupling. Phospholipases
hydrolyze phospholipids such as PC, into fatty acid and lysoPC; the former can
function as a precursor for the biosynthesis of JA and related oxylipins via the
octadecanoid pathway, or peroxidized by ROS to produce another class of
pentacyclic oxylipin phytoprostanes. Elicitors also activate mitogen-activated PK
(MAPK) cascades that phosphorylate transcription factors regulating the expression
of early and late response genes. All these pentacyclic oxylipins can activate the
biosynthesis of secondary metabolites in plants (modified from Zhao et al. 2005).
Growth regulators and plant hormones stimulate plant growth and terpene
biosynthesis in a broad number of aromatic plant species, which result in beneficial
changes in terpene quality and quantity (Farooqi and Sharma 1988).
Secretion of volatile organic compounds (VOCs) by PGPRs can be another
possible mechanism for enhancing the production of plant secondary metabolites.
All organisms produce VOCs, which are characterized by low molecular weight
and high vapor pressure, and play important roles in communication within and
between organisms. Bacterial VOCs have been reported as a rich source for new
natural compounds that may increase crop productivity and EOs yield in medicinal
and aromatic plants. Santoro et al. (2011) studied the effects of VOCs released by
three PGPR strains (P. fluorescens, B. subtilis, and Azospirillum brasilense) on
EOs composition of Mentha piperita (peppermint). The results showed that the
production of monoterpenes increased two-fold in plants inoculated with
P. fluorescens, which also increased biosynthesis of the two major EOs, (+)
pulegone and ( ) menthone. Menthol in Azospirillum brasilense-inoculated plants
was the only major EOs constituent that showed a significant decrease. It has also
been reported that the PGPR strain B. subtilis GB03 releases VOCs that elevate EOs
accumulation in Ocimum basilicum (Banchio et al. 2009). Two major EOs components, R-terpineol and eugenol, increased by two- and ten-fold, respectively. This
was seen in plants exposed to GB03 VOCs or with root inoculation, as compared to
uninoculated controls. Some of the PGPRs proven to be biotic elicitors for the
production of secondary metabolites in medicinal and aromatic plants are presented
in Table 3.4.
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64
M. Ghorbanpour et al.
Table 3.4 Efficient biotic elicitors used for the production of secondary metabolites in different
plant species
Elicitation of
secondary
metabolites
Reference
PGPRs as elicitors
Plant species
Pseudomonas putida
and fluorescens
Pseudomonas putida
and fluorescens
Glomus aggregatum,
Bacillus coagulans, and
Trichoderma harzianum
Hyoscyamus niger L.
Pseudomonas
fluorescens
Pseudomonas
fluorescens
Pseudomonas
fluorescens, Bacillus
subtilis, and
Azospirillum brasilense
Bacillus cereus
Catharanthus roseus
Hyoscyamine and
scopolamine
Cis-thujone, camphor, 1,8-cineole
Total phenols, orthodihydroxy phenols,
tannins, flavonoids,
saponins, and
alkaloids
Ajmalicine
Catharanthus roseus
Serpentine
Mentha piperita
(+) pulegone and ( )
menthone
Jaleel
et al. (2007)
Jaleel
et al. (2009)
Santoro
et al. (2011)
Salvia miltiorrhiza
Bunge
Catharanthus roseus
Tanshinone
Zhao et al. (2010)
Ajmalicine
Namdeo
et al. (2002)
Selvaraj
et al. (2008)
Trichoderma viride
Salvia officinalis L.
Solanum viarum
Glomus mosseae, Bacillus coagulans, and
Trichoderma viride
Begonia malabarica
Lam
Pseudomonas
fluorescens and
Bradyrhizobium sp.
Origanum majorana L.
Pseudomonas
fluorescens, Bacillus
subtilis, and
Azospirillum brasilense
Hormonema ssp.
homogenates
Bacillus polymyxa,
Pseudomonas putida,
Azotobacter
chroococcum, and Glomus intraradices
Arbuscular mycorrhizal
and phosphatesolubilizing bacteria
Origanum majoricum
Brugmansia candida
Stevia rebaudiana
Rose-scented geranium
(Pelargonium sp.)
Total phenols, orthodihydroxy phenols,
tannins, flavonoids,
and alkaloids
Terpinene- 4-o1, cissabinene hydrate,
trans-sabinene
hydrate, and
α-terpineol
Cis- and transsabinene hydrate,
gamma-terpinene,
carvacrol, and thymol
Hyoscyamine and
scopolamine
Stevioside
Citronellol, geraniol,
geraniol, and
10-epi-γ eudesmol
Ghorbanpour
et al. (2013a, b)
Ghorbanpour
et al. (2014)
Hemashenpagam
and Selvaraj
(2011)
Banchio
et al. (2008)
Banchio
et al. (2010)
Pitta-Alvarez
et al. (2000)
Vafadar
et al. (2013)
Prasad
et al. (2012)
(continued)
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3 Enhanced Efficiency of Medicinal and Aromatic Plants by PGPRs
65
Table 3.4 (continued)
PGPRs as elicitors
Pseudomonas
aeruginosa and Pseudomonas fluorescens
Bacillus subtilis and
Pseudomonas
fluorescens
Bacillus subtilis GB03
Plant species
Pisum sativum
Pseudomonas
fluorescens and
Azospirillum brasilense
Tagetes minuta
3.5
Pelargonium
graveolens
Ocimum basilicum
Elicitation of
secondary
metabolites
Phenolic compounds
(gallic, cinnamic, and
ferulic acid)
Essential oil yield
Reference
Bahadur
et al. (2007)
α-terpineol and
eugenol
Monoterpenes and
phenolic compounds
Banchio
et al. (2009)
Cappellari
et al. (2013)
Mishra
et al. (2010)
Conclusions
Infection by microorganisms as well as physiological and genetic factors and
environmental conditions are the main agents affecting the accumulation and
composition of secondary metabolites in plants. Among these, PGPRs seem to be
a promising candidate considering their well-established role in plant nutrition,
tolerance against biotic and abiotic stresses and enhancing the yield of different
classes of secondary metabolites. As an environmentally friendly strategy, PGPRs
should be considered to achieve sustainable high yields of industrially important
secondary metabolites in plants using minimum chemical inputs.
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mkumar9@amity.edu
Chapter 4
Plant Growth-Promoting Microbes from
Herbal Vermicompost
Rajendran Vijayabharathi, Arumugam Sathya,
and Subramaniam Gopalakrishnan
4.1
Introduction
Overreliance on chemical pesticides and fertilizers has resulted in problems including safety risks, outbreaks of secondary pests normally held in check by natural
enemies, insecticide resistance, environmental contamination, and decrease in biodiversity (Lacey and Shapiro-Ilan 2008). The increasing costs and negative effects
of pesticides and fertilizers necessitate the idea of biological options of crop
protection and production. This includes the use of animal manure, crop residues,
microbial inoculum (Rhizobium, Azotobacter, Azospirillum, and blue green algae),
and composts. They provide natural nutrition, reduce the use of inorganic fertilizers, develop biodiversity, increase soil biological activity, maintain soil physical
properties, and improve environmental health (Hue and Silva 2000; Vessey 2003).
On the other hand, a progressive increase in world’s population, intensive
industrialization of food and beverage processing, and animal husbandry production leads to the generation of large volumes of organic wastes. As per the estimation of World Bank, municipal solid waste alone from the urban areas of Asia is
projected to be 1.8 million tonnes/day in 2025 (Chandrappa and Das 2012). These
can be disposed by landfilling, pelletization, incineration, biomethanization, and
composting. Organic wastes act as a major source of environmental pollution and
create serious disposal problem, release odor and ammonia into air, contaminate
groundwater, and thereby pose health risks (Inbar et al. 1993). This problem can be
solved by vermicomposting, a process of decomposing organic wastes into a
valuable product of organic fertilizer and soil conditioner by the use of earthworms.
R. Vijayabharathi • A. Sathya • S. Gopalakrishnan (*)
International Crops Research Institute for the Semi-Arid Tropics (ICRISAT) Andhra Pradesh,
India, Patancheru 502 324, Andhra Pradesh, India
e-mail: s.gopalakrishnan@cgiar.org
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_4
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Vermicomposting is an enhanced bio-oxidative and nonthermophilic organic
decomposition process by the joint action of earthworms and microorganisms
which involves a wide range of organic wastes such as horticultural and agricultural
residues, weeds, dry leaves, cow dung, animal droppings, brewery wastes, sericulture wastes, municipal sewage sludge, industrial wastes, paper mills and dairy
plants sludge, and domestic and kitchen wastes (Kumar 2005; Chitrapriya
et al. 2013). The resultant product of vermicomposting is a stabilized, uniformly
sized substance with a characteristic earthy appearance known as “vermicast/
vermicompost.” Vermicompost exhibits better performance on various plants during field application due to its enrichment with various macro- and microelements,
enzymes, hormones, plant growth regulators, and antibiotics (Makulec 2002;
Tilak et al. 2010). Detailed methods of vermicomposting have been documented
by many authors (Domı́nguez 2004; Nagavallemma et al. 2004).
Vermicomposting accelerates decomposition rates which further leads to higher
nutrient turnover (Mikola and Setälä 1998; Sampedro and Domı́nguez 2008) than
the traditionally prepared compost which involves the action of microorganisms
alone. Though microorganisms act as primary partner for the biochemical decomposition of organic matter, the earthworms, as secondary partner, are crucial drivers
for the process and they are broadly grouped into three ecological categories:
(1) anecics such as Lumbricus terrestris, L. polyphemus, and Aporrectodea longa
are geophagous in nature and live in deep soils; (2) endogeics such as A. caliginosa,
Octolasion cyaneum, Pontoscolex corethrurus, and Aminthas sp. reside just below
the soil surface and feed the organic materials in soils, which were further
subdivided into polyhumic, mesohumic, and oligohumic endogeic earthworms;
and (3) epigeics such as Eisenia foetida, L. rubellus, and Eiseniella tetraedra live
in the upper surface of soils and feed mainly on plant litter and other organic debris
available on the soil surface. The details about different earthworm species, their
ecological niches, characteristic features, and beneficial actions on decomposition
have been reviewed by Pathma and Sakthivel (2012). Since the epigeic earthworms
are consumers of a variety of organic matters, they are most suitable for
vermicomposting process; however, the use of anecic and endogeic earthworms
has also been reported (Lavelle and Martin 1992).
Each earthworm has its own characteristic features on decomposition of organic
matter, and they are sensitive to fluctuating climatic and environmental conditions.
For instance, Eudrillus eugeniae known as the “African night crawler” can decompose large quantities of organic wastes rapidly as it has higher growth and reproduction rates. Hence it is applied widely for vermicomposting and also in
combination with other earthworms such as E. foetida and Perionyx excavates
(Pattnaik and Reddy 2010); P. excavates, a commercially produced tropical earthworm known as “blues/Indian blues,” is useful for vermicomposting in tropical and
subtropical regions (Chaudhuri and Bhattacharjee 2002); L. terrestris, an introduced species of North America, is a long-living, cold-tolerant species which
makes deep burrows beneath the frost line (Joschko et al. 1989). Domı́nguez
(2004) reported different earthworm species, the factors affecting earthworm
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4 Plant Growth-Promoting Microbes from Herbal Vermicompost
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survival (moisture content, temperature, pH, aeration, and ammonia), and also the
process of vermicomposting.
Earthworms harbor a variety of decomposer microbes in their gut and excrete
them along with nutrients in their excreta, and both are found to be mutual partners.
Various enzymes and intestinal mucus in the earthworm’s intestinal tract play a key
role in the breakdown of organic macromolecules, which in turn results in a greater
increment of the available surface area for microbial colonization, their biological
activity, and higher nutrient retention. So, vermicompost is a hotspot for the
isolation of beneficial microorganisms, including saprophytic bacteria and fungi,
protozoa, nematodes, and microarthropods. Maintenance of mesophilic conditions
throughout the entire process is another contributing factor (Domı́nguez
et al. 2010). These microorganisms directly or indirectly offer many agriculturally
favorable traits to the vermicompost, but exploration of those microbes has not been
studied in detail, though enough reports are available for the microbial diversity of
vermicompost (Huang et al. 2013; Pathma and Sakthivel 2012). An overview on the
effect of vermicompost and associated microbes on agriculturally useful traits is
depicted in Fig. 4.1.
Microbes with agriculturally favorable traits were categorized as plant growthpromoting (PGP) microbes—a heterogeneous group of beneficial bacteria/fungi/
actinomycetes which promotes plant growth either directly (nitrogen fixation,
phosphate solubilization, iron chelation, and phytohormone production) or
Fig. 4.1 Overview of vermicompost and its associated microbes on plant growth
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R. Vijayabharathi et al.
indirectly (suppression of plant pathogenic organisms, induction of resistance in
host plants against plant pathogens, and abiotic stresses).
PGP microbes include Bacillus, Pseudomonas, Erwinia, Caulobacter, Serratia,
Arthrobacter, Micrococcus, Flavobacterium, Chromobacterium, Agrobacterium,
Hyphomycrobium, and free-living nitrogen-fixing bacteria and also the members
of the family Rhizobiaceae such as Rhizobium, Bradyrhizobium, Sinorhizobium,
Azorhizobium, Mesorhizobium, and Allorhizobium. The practice of using such PGP
microorganisms to agriculturally important crops as inoculants is getting attraction
as it has a wide range of applications including the substantial reduction of the use
of chemical fertilizers/pesticides, increased soil health, inhibitory activity against
phytopathogens/insects, and enhanced crop yield (Bhattacharyya and Jha 2012;
Mehboob et al. 2012). Hence, in this chapter, we intend to deliberate the usefulness
of vermicompost and the associated microorganisms in enhancing soil health and
agricultural productivity.
4.2
Microbial Diversity of Earthworms
and Vermicomposts
Microbial communities including bacteria, actinomycetes, filamentous fungi, and
yeast have been reported in earthworms such as L. terrestris, Allolobophora
caliginosa, and A. terrestris (Parle 1963a, b), and most of them are mesophilic
bacteria, fungi, and actinomycetes (Benitez et al. 1999; Sen and Chandra 2009;
Vivas et al. 2009), which have been illustrated in Table 4.1. It is noticed that,
earthworm’s age hasn’t showed any influence on microbial community (FernándezG
omez et al. 2012), but the microbial counts between the earthworm species may
vary due to their different ability to digest and assimilate microbial biomass, their
ecological group, food, and environmental conditions in which earthworms live
(Brown and Doube 2004). These factors make the vermicompost a hotspot of
microbes. Unique indigenous gut-associated microflora has been documented in
E. foetida (Toyota and Kimura 2000). In contrary, microbes living in traditional
compost undergo a selection process during the heating phase, where the organic
material is decomposed by specially adapted thermophilic bacteria (Dees and
Ghiorse 2001). The microbial community which resides in the finished traditional
compost are the facultative thermophiles, which form spores during the hot phase
and recolonize during the mesophilic stage.
Microbial count in the ingested material of earthworms can be increased up to
1,000-fold while passing through their gut (Edwards and Fletcher 1988). Devi
et al. (2009) have given a distinction on the microbial count of vermicomposts
and of normal composts of fruit and vegetable waste, cow dung, and groundnut
husk for bacteria, fungi, and actinomycetes. A similar trend of supporting evidence
has been given by many research groups (Pedersen and Hendriksen 1993;
Devliegher and Verstraete 1995). Microbial biomass and activity were also
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4 Plant Growth-Promoting Microbes from Herbal Vermicompost
75
Table 4.1 Microbial diversity of earthworms
S. no
Microorganisms
Earthworm
References
1
An oxalate-degrading Pseudomonas oxalaticus
Pheretima
2
E. foetida
3
4
Anaerobic N2-fixing bacteria—Clostridium
butyricum, C. beijerinckii, and C. paraputrificum
Streptomyces lipmanii and Streptomyces spp.
Actinobacteria
5
Fluorescent pseudomonads
L. terrestris
6
Aeromonas hydrophila
E. foetida
7
Gammaproteobacteria, firmicutes, and
actinobacteria
Pseudomonas, Paenibacillus, Azoarcus,
Burkholderia, Spiroplasma, Acaligenes, and
Acidobacterium
Novel nephridial symbiont, Verminephrobacter
eiseniae
Gammaproteobacteria
L. rubellus
Khambata and
Bhat (1953)
Citernesi
et al. (1977)
Contreras (1980)
Krištüfek
et al. (1993)
Devliegher and
Verstraete (1997)
Toyota and
Kimura (2000)
Furlong
et al. (2002)
Singleton
et al. (2003)
8
9
10
11
12
Acidobacteria, actinobacteria, bacteroidetes,
chloroflexi, cyanobacteria, firmicutes,
Gemmatimonadetes, nitrospirae, planctomycetes,
proteobacteria, tenericutes, and verrucomicrobia
Aeromonadaceae, comamonadaceae, enterobacteriaceae, flavobacteriaceae, moraxellaceae,
“paenibacillaceae,” pseudomonadaceae,
rhodocyclaceae, sphingobacteriaceae, and
actinobacteria
E. lucens
L. rubellus
L. rubellus
E. foetida
Pinel et al. (2008)
L. rubellus
Knapp
et al. (2009)
Wüst et al. (2011)
L. terrestris
A. caliginosa
Ihssen
et al. (2003),
Horn et al. (2003)
significantly increased in vermicasts over composts (Brown and Doube 2004;
Aira et al. 2006; Monroy et al. 2009). Earthworms’ interaction with physical,
chemical, and biological components affects the structural features of the microflora and microfauna in vermicompost (Domı́nguez et al. 2003; Lores et al. 2006;
Monroy et al. 2009).
A recent study by Huang et al. (2013) on the bacterial communities of the
earthworm E. foetida showed different phyla including Bacteroidetes, Firmicutes,
Actinomycetes, Chlorobi, Planctomycetes, and Proteobacteria in vegetable waste
compost, in which Bacteroidetes were predominant. Enrichment of Bacteroidetes
(anaerobic group of microorganisms) in the vermicompost is probably due to the
anaerobic conditions in the earthworm’s gut (Karsten and Drake 1995). In contrast,
Pathma and Sakthivel (2013) noticed Bacillus as the dominating genus followed by
Pseudomonas and Microbacterium in goat manure compost. Bacterial diversity
analysis of commercial composts (poultry litter, sewage sludge, and municipal solid
waste) and homemade composts (vermicompost from food wastes) has been
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R. Vijayabharathi et al.
registered with the groups such as Firmicutes: Bacillus benzoevorans, B. cereus,
B. licheniformis, B. megaterium, B. pumilus, B. subtilis, and B. macroides; Actinobacteria: Cellulosimicrobium cellulans, Microbacterium spp., and M. oxydans;
Proteobacteria: Pseudomonas spp. and P. libaniensis; ungrouped genotypes:
Sphingomonas spp. and Kocuria palustris; and yeasts: Geotrichum spp. and
Williopsis californica (Vaz-Moreira et al. 2008). Fischer et al. (1995) observed
variations in the bacterial community of vermicasts and guts (including foregut,
midgut, and hindgut) of earthworms in which the bacterial count of α, β, and γ
subgroups of proteobacteria increased significantly toward the end of the gut and
remained high in the cast. Among the subgroups, α-proteobacteria was higher in
the hindgut and casts, and β- and γ- proteobacteria were predominant in the foreand hindgut. Similar studies conducted by Nechitaylo et al. (2010) revealed the
presence of Bacteroidetes, Alphaproteobacteria, Betaproteobacteria, and representatives of classes Flavobacteria, Sphingobacteria (Bacteroidetes), Pseudomonas
spp., and unclassified Sphingomonadaceae (Alphaproteobacteria) and Alcaligenes
spp. (Betaproteobacteria) in earthworm (L. terrestris and A. caliginosa), casts,
and soil.
In addition to bacteria, several studies have also been reported for fungal
diversity in vermicompost and earthworms. The phyla of Saccharomycetes,
Lecanoromycetes, and Tremellomycetes dominated in the initial substrate of
vermicompost (Bonito et al. 2010). The compost without earthworm was reported
to have less fungal diversity, whereas during earthworm treatment, the fungal
diversity has increased with Sordariomycetes, followed by Agaricomycetes,
Pezizomycetes, Eurotiomycetes, Saccharomycetes, and Orbiliomycetes (Bonito
et al. 2010; Huang et al. 2013). Besides this, other beneficial fungi in the
vermicompost have also been noticed and some of the identified populations
include Paecilomyces spp. and Dactylaria biseptata (Siddiqui and Mahmood
1996), Cephaliophora tropica (Morikawa et al. 1993), and Trichoderma spp.
(Harman 2006). A study by Anastasi et al. (2005) also revealed the differentiation
of fungal diversity in compost and vermicompost. Among the 194 fungal species
isolated, 66 were common to both the compost and vermicompost, whereas
118 were obtained from compost and 142 from vermicompost. This concludes
that fungal diversity is found more in vermicompost than in compost.
Next to bacteria, actinomycetes are the major gut flora of earthworm and have
been reported widely in the literature (Parle 1963a, b; Ravasz et al. 1987; Ravasz
and T
oth 1990; Jayasinghe and Parkinson 2009). It is noticed that vermicompost
has higher actinomycetes than fungus in the final product, which might be due to the
antagonistic activity of the former group against the latter group (Jayasinghe and
Parkinson 2009). For instance, Yasir et al. (2009) and Huang et al. (2013) detected
Streptomyces and Rhodococcus, the genera which have the ability to kill plant
pathogens from vermicompost and fresh sludge. The actinomycetes present in the
form of cell aggregates or individual cells and most of them belong to Streptomyces
spp., the well-known antibiotic producers (Krištüfek et al. 1993, 1994, 1995). Other
actinomycetes such as Micromonospora spp. were also recorded (Krištüfek
et al. 1990; Polyanskaya et al. 1996).
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4 Plant Growth-Promoting Microbes from Herbal Vermicompost
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Earthworms have food preference for substances colonized by certain fungal
(Tiwari and Mishra 1993; Moody et al. 1995; Marfenina and Ishchenko 1997) and
bacterial species (Wright 1972). Their food preference for actinomycetes has been
demonstrated by Polyanskaya et al. (1996) on E. foetida, which actively consumed
the spores of S. caeruleus than other actinomycete spores. Even though a substantial
quantity of actinomycetes is digested in the foregut of the earthworms, the
undigested remaining actinomycetes are able to develop rapidly in the earthworm’s
mid- and hindgut. Hence, the chances of survival for actinomycetes were found to
be higher in earthworm’s hindgut (Krištüfek et al. 1992; Polyanskaya et al. 1996;
Zenova et al. 1996). These ingested actinomycetes inhibit the growth of other
microorganisms particularly litter-decomposing and pathogenic fungi and Grampositive bacteria in the earthworm’s gut. This leads to the predominance of other
actinomycetes and other antibiotic-resistant microorganisms and hence the biocontrol properties against various phytopathogens (Doube et al. 1994a, b; Stephens
et al. 1994). Though the microbial community of bacteria/fungi/actinomycetes
varies with the earthworm species/vermicompost, it also depends on the initial
substrate of vermicompost.
4.3
Nutritional Values of Vermicompost
The nutritional quality of the vermicompost depends on the type of the initial
substrate, earthworm species (epigeic, endogeic, and anecic), microbial population
(cellulolytic, lignolytic, and N2-fixers), and environmental conditions like aeration,
humidity, pH, and temperature. The nutrient composition of vermicomposts has
been documented with organic carbon 9.2–17.9 %, total nitrogen 0.5–1.5 %, available phosphorus 0.1–0.3 %, available potassium 0.1–0.2 %, calcium and magnesium 22–70 mg/100 g, copper 2–9.3 ppm, zinc 5.7–11.5 ppm, and available sulfur
128–548 ppm (Kale 1995). Vermicompost has higher concentrations of exchangeable Ca2+, Mg2+, and K+ than the initial substrate, which indicates the conversion of
nutrients to plant-available forms during the passage in the earthworm’s gut and
associated microorganisms. Apart from the nutritional indices, the earthworm’s
activity also enhances the soil’s physical qualities like bulk density, pore size, water
infiltration rate, soil water content, and water-holding capacity (Edwards 1998).
A detailed study on the effect of substrate (cow dung, grass, aquatic weeds, and
municipal solid waste), liming (enhances earthworm activity and microbial population), and microbial community (Trichoderma viride, Phenerocrete crysosporium—lignolytic fungus and Bacillus polymyxa—free-living nitrogen-fixing
bacteria) on the nutritional status of vermicompost has been reported by Pramanik
et al. (2007). They found that the usage of cow dung, B. polymyxa, and lime
concentration of 5 g/kg was found to be the best combination in increasing NPK
values, humic acid content, and enzyme activities like urease and phosphatase;
however, T. viridae has shown equal nutrient effects irrespective of the lime
content. Ghosh et al. (1999) demonstrated the difference in composting of organic
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R. Vijayabharathi et al.
wastes such as cow dung, poultry droppings, kitchen wastes, municipal wastes, and
dry leaves with and without E. foetida and observed higher availability of macroand micronutrients in vermicast than compost without earthworms. Similarly,
three- to fourfold increased NPK and micronutrient content on cow dung
vermicompost than the noncomposted parental material was also noticed. Recent
studies also concluded the nutritional enrichment of vermicompost over normal
compost (Atiyeh et al. 2000; Hashemimajda et al. 2004; Lazcano et al. 2008).
Hence, it can be concluded that the extensive usage of vermicompost can reduce the
application of chemical fertilizers without affecting crop yield.
Vermicast has been documented with various enzyme activities including cellulase, amylase, invertase, protease, peroxidase, urease, phosphatase, and dehydrogenase in which the maximum enzyme activity is contributed by gut microbes
(Sharpley and Syers 1976; Edwards and Bohlen 1996; Devi et al. 2009). Though
vermicomposts have a wide range of enzyme activities, fluctuations are there during
the composting period that the maximum enzyme activities were observed during
21–35 days in vermicomposting, whereas in conventional composting it was
noticed on 42–49 days (Devi et al. 2009). This might be due to higher microbial
count and activity in vermicomposts than the conventional composts. Since earthworms influence soil physical, chemical, and biological properties, they have been
considered as soil engineers and as indicators of soil quality (Muys and Granval
1997; Jouquet et al. 2006).
4.4
Plant Growth Promoters of Vermicompost
Vermicompost was found to increase the growth of various vegetable, fruit, flower,
and food crops not only by their macro- and microelement composition of the
vermicast but also by their plant growth-promoting substances like growth hormones and enzymes. Microbes residing in the earthworm are the major contributors
of such known and other unknown growth-promoting elements. Rhizobium, one of
the PGP bacterium in soil that fixes nitrogen, was reported to disperse in soil by the
earthworm A. trapezoids (Bernard et al. 1994). The first report on the identification
of plant growth-promoting substances in earthworms was done by Nielson (1965).
He identified indole-like substances in the tissue extracts of A. caliginosa,
L. rubellus, and E. foetida and observed enhanced growth rate of garden pea.
Various researchers reported substantial quantities of plant growth promoters
such as auxins, gibberellins, cytokinins of microbial origin (Grappelli et al. 1985,
1987; Krishnamoorthy and Vajranabhaiah 1986; Tomati et al. 1988; Muscolo
et al. 1999), and humic acids (Masciandaro et al. 1997; Atiyeh et al. 2002) in
vermicomposts.
Vermiwash, the aqueous extracts of vermicompost, is a collection of excretory
compounds of earthworms and also the associated microbes. It serves as a fertilizer
and also a biocide due to the presence of macro- and micronutrients and antibiosis
compounds. Hence, the use of vermiwash also registered increased plant growth on
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4 Plant Growth-Promoting Microbes from Herbal Vermicompost
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a par with the use of hormones such as auxins, gibberellins, and cytokinins on plants
such as Petunia, Begonia, and Coleus (Grappelli et al. 1987; Tomati et al. 1987,
1988). Nagavallemma et al. (2004) showed a marked difference in the plumule
length of maize seedlings dipped in vermiwash than normal water. Comparative
studies on the impact of vermiwash and urea solution on seed germination and on
root and shoot length in cluster bean, Cyamopsis tertagonoloba, demonstrated the
enhanced growth in vermiwash solution which might be due to hormone-like
substances (Suthar 2010). HPLC and GC–MS analyses of the vermiwash of cattle
waste-derived vermicompost showed the presence of significant amounts of indole
acetic acid (IAA), gibberellins, and cytokinins (Edwards et al. 2004). Thus, it was
demonstrated that both vermicompost and vermiwash are rich source of plant
growth-promoting substances.
4.5
Biocontrol Properties of Vermicompost
Microbial population in vermicompost acts as powerful biocontrol agents due to the
production of antibiotics and secretion of extracellular enzymes such as chitinase
and lipase which cause the lysis of fungal and bacterial phytopathogens.
Vermicompost is a valuable source of antagonistic bacteria and/or actinomycetes;
several research reports are available to augment the biocontrol properties of
vermicompost against phytopathogens such as Botrytis cineria (Singh
et al. 2008), Fusarium spp. (Yeates 1981; Moody et al. 1996), Gaeumannomyces
spp. (Clapperton et al. 2001), Rhizoctonia spp. (Doube et al. 1994a; Hoitink
et al. 1997; Stephens et al. 1994; Stephens and Davoren 1997), Phytophthora
(Ersahin et al. 2009), Plasmodiophora brassicae (Nakamura 1996), and
P. infestans (Kostecka et al. 1996). Control of powdery mildew in barley (Weltzien
1989), balsam, and pea by vermicompost application has been demonstrated under
field conditions (Singh et al. 2003). Pathogen control has been demonstrated in
other crops like clover, cabbage, cucumber, grapes, tomatoes, radish, and strawberry (Jack 2011). Besides the biocontrol properties of vermicompost, vermiwash
was also found to have biocontrol traits against B. cineria, Sclerotinia sclerotiorum,
Corticium rolfsii, R. solani, F. oxysporum (Nakasone et al. 1999), Erysiphe
cichoracearum, and E. pisi (Singh et al. 2003). Systemic plant resistance, microbial
competition, antibiosis, enzyme activity, and hyperparasitism are the suspected
reasons for pathogenic control (Hoitink and Grebus 1997). Yasir et al. (2009)
documented the presence of chitinolytic bacteria Nocardioides oleivorans, Streptomyces spp., and Staphylococcus epidermidis from vermicompost with inhibitory
activity against phytopathogens such as R. solani, Colletotrichum coccodes,
Pythium ultimum, P. capsici, and F. moniliforme. Similarly, antibiotic heliomycin-producing S. olivocinereus has been isolated from E. foetida’s gut
(Polyanskaya et al. 1996). The dispersed actinomycetes from earthworms act as
potential biocontrol agents against plant pathogenic fungi (Doube et al. 1994a, b;
Stephens et al. 1994) due to their production capacity for a wide range of secondary
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R. Vijayabharathi et al.
metabolites and antibiosis compounds. Besides pathogen control, insects or pests
such as jassids, aphids, spider mites, mealy bugs, sucking pests, caterpillars, and
beetles have also been controlled by vermicompost application (Edwards
et al. 2007; Biradar et al. 1998; Rao et al. 2001; Rao 2002, 2003) under greenhouse
and field conditions.
4.6
PGP Research at ICRISAT
ICRISAT has identified over 1,500 microbes including bacteria and actinomycetes,
isolated from various composts and rhizospheric soil, in which at least one out of
six has documented either single or multiple agriculturally favorable traits. Our
research group has a collection of 137 actinomycetes isolated from 25 herbal
vermicomposts prepared from Jatropha curcas, Annona squamosa, Parthenium
hysterophorus, Oryza sativa, Gliricidia sepium, Adhatoda vasica, Azadirachta
indica, Capsicum annuum, Calotropis gigantea, Calotropis procera, Datura
metal, Allium sativum, Zingiber officinale, Ipomoea batatas, Momordica charantia,
Moringa oleifera, Argyranthemum frutescens, Nerium indicum, Allium cepa,
Curcuma aromatica, Pongamia pinnata, Abacopteris multilineata, Nicotiana
tabacum, Tridax procumbens, and Vitex negundo using the epigeic earthworm
E. foetida (Gopalakrishnan et al. 2013a) and demonstrated plant growth-promoting
and biocontrol properties under laboratory, greenhouse, and field conditions.
Among them, actinomycetes, Streptomyces spp., S. caviscabies, S. globisporus
sub sp. caucasicus, and S. griseorubens isolated from herbal vermicomposts, have
registered in vitro PGP traits such as IAA and siderophore production and also
documented their positive effect on the upregulation of PGP genes such as IAA and
siderophore-producing genes. They proved these in vitro potentials by enhanced
growth performance on rice under field conditions via increased tiller numbers,
panicle numbers, filled grain numbers and weight, stover yield, grain yield, total dry
matter, root length, root volume (Fig. 4.2), and root dry weight. In addition, they
significantly enhanced rhizospheric total nitrogen, available phosphorous, %
organic carbon, microbial biomass carbon, microbial biomass nitrogen, and dehydrogenase activity over the uninoculated control. Apart from the PGP traits, they also
have the capacity to act as biocontrol agents due to the production of hydrogen
cyanide and enzymes such as lipase, chitinase, and β–1,3 glucanase (Gopalakrishnan
et al. 2012, 2013b, 2014). PGP actinomycetes such as Streptomyces spp.,
S. tsusimaensis, S. caviscabies, S. setonii, and S. africanus isolated from herbal
vermicomposts have proved this by their inhibitory activity against Fusarium
oxysporum f. sp. ciceri (FOC) (Gopalakrishnan et al. 2011a) and Macrophomina
phaseolina, a causative agent for the charcoal rot of sorghum (Gopalakrishnan
et al. 2011b) under greenhouse conditions. Antagonistic activity of these actinomycetes on Fusarium wilt-sick fields has also been demonstrated.
Besides the biocontrol activity of microbes isolated from herbal vermicomposts,
washings of vermicompost, “vermiwash or biowash,” were also demonstrated to
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4 Plant Growth-Promoting Microbes from Herbal Vermicompost
81
Fig. 4.2 Effect of PGP actinomycetes (a) S. caviscabies and (b) S. globisporus sub sp. caucasicus
on root development of rice over (c) uninoculated control (Gopalakrishnan et al. 2014)
have inhibitory activity against phytopathogens. Crude biowash and partially purified extracts of vermicompost prepared from Jatropha curcas, Annona squamosa,
and Parthenium hysterophorus marked their fungicidal activity on FOC, S. rolfsii,
and M. phaseolina (Gopalakrishnan et al. 2010). Additionally, insecticidal activity
has been registered by biowash and microbes isolated from herbal vermicomposts.
Our investigation proved this via the biowash of Annona, Datura, Jatropha, Neem,
Parthenium, Pongamia, and isolated PGP bacteria B. subtilis, B. megaterium,
Serratia mercescens, and Pseudomonas spp.; fungus Metarhizium anisopliae and
actinomycetes S. cavourensis sub sp. cavourensis, S. albolongus, S. hydrogenans,
S. antibioticus, S. cyaneofuscatus, S. carpaticus, S. bacillaris, and Streptomyces
spp. which were found to have broad-spectrum insecticidal properties against
lepidopteran pests such as Helicoverpa armigera, Spodoptera litura, and Chilo
partellus (Gopalakrishnan et al. 2011c; Vijayabharathi et al. 2014).
Besides the contribution of actinomycetes, bacteria have also been registered
with PGP activity. Phosphate-solubilizing bacteria and Azotobacter have been
isolated from the vermicompost of cow dung and saw dust with earthworms
E. eugeniae and P. excavatus (Chitrapriya et al. 2013). Similarly, Bacillus, Pseudomonas, Rhizobium, and Azotobacter with in vitro PGP traits such as IAA, ammonia,
and siderophore production were isolated from the vermicompost of paper mill
sludge, leaf litter, and press mud with E. foetida (Prakash and Hemalatha 2013). A
detailed study by Pathma and Sakthivel (2013), on vermicompost produced from
straw and goat manure with E. foetida, identified 193 bacteria with antagonistic
and/or biofertilizing potential. The dominance of identified bacteria was found to be
in the order of Bacillus (57 %) > Pseudomonas (15 %) > Microbacterium (12 %) >
Acinetobacter (5 %) > Chryseobacterium (3 %) with the other members such as
Arthrobacter, Pseudoxanthomonas, Stenotrophomonas, Paenibacillus, Rhodococcus, Enterobacter, Rheinheimera, and Cellulomonas. Functional analyses of
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R. Vijayabharathi et al.
these microbes have registered in vitro PGP traits such as phosphate solubilization,
nitrate reduction, assimilation of different carbon sources, and production of IAA,
siderophore, 1-aminocyclopropane-1-carboxylate (ACC) deaminase, chitinase,
lipase, and HCN. Besides this, they have also been reported with the production
of commercially important enzymes protease, cellulase, amylase, xylanase, and
Dnase. These studies thus conclude that vermicomposting organisms and biowash
have the potency to promote plant growth, control the infectious diseases, and
restrict pest attack. Hence, these PGP microorganisms are expected to replace
inorganic fertilizer, pesticides, and artificial plant growth regulators which have
numerous side effects to sustainable agriculture.
4.7
Conclusions
This chapter was intended to summarize the current knowledge on plant growthpromoting microbes associated with vermicompost. Vermicompost, vermiwash,
and earthworm, in specific earthworm gut, nephridia and alimentary canal, have
complex group of beneficial microorganisms. These microorganisms directly or
indirectly contribute to the beneficial properties of vermicompost and vermiwash in
enhancing soil health, plant growth, and hence agricultural productivity. Plenty of
literatures are available for the presence/diversity of bacteria, fungi, and actinomycetes in vermicompost and earthworm and also for the enhanced plant growth
by vermicompost application. However, studies related to the exploration of such
potential microbes with plant growth-promoting properties are scarce. So, investigation on the isolation, identification, and characterization of plant growth-promoting
microbes and their active metabolites from vermicompost will be useful for sustainable agriculture.
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mkumar9@amity.edu
Chapter 5
Effect of AM Fungi and Plant
Growth-Promoting Rhizobacteria (PGPR)
Potential Bioinoculants on Growth and Yield
of Coleus forskohlii
Uliyan Sakthivel and Balathandayutham Karthikeyan
5.1
Introduction
Coleus forskohlii (family Lamiaceae) grows perennially in the tropical and subtropical regions of India, Pakistan, Sri Lanka, East Africa, and Brazil. Its roots are
the source of a labdane diterpene compound called forskolin having a unique
property to stimulate adenylate cyclase. Forskolin is also a potent vasodilatory,
antihypertensive, and inotropic agent (Seamon 1984). The crop has a great potential
due to the expected increase in demand for forskolin, which is widely used for the
treatment of glaucoma, cardiac problems, and also certain types of cancers (Shah
et al. 1980; Kavitha et al. 2010). Its ethnomedicinal uses for the relief of cough,
eczema, skin infections, tumors, and boils have also been recorded (De Souza
et al. 1986). Because of the continuous collection of roots from wild sources, this
plant has been included in the list of endangered species (Boby and Bagyaraj 2003;
Singh et al. 2009a). Recently, its cultivation has picked up as a crop with an annual
production of about 100 t from 700 ha in India (Shivkumar et al. 2006).
Arbuscular mycorrhizal (AM) fungi of the phylum Glomeromycota are ubiquitous component of most agroecosystems, where they provide several benefits to
their host plant, including better phosphorus nutrition (Toro et al. 1998; Parniske
2008), increased drought tolerance (Ruiz-Lozano and Azcon 1995), increased
uptake of water (Graham and Sylvertsen 1984), and increased disease resistance
(Pozo et al. 1999; Whipps 2004). Evidences are being accumulated to show that the
inoculated AM fungi are an important component of organic farming (Powell and
Bagyaraj 1984; Gosling et al. 2006) and can benefit annual crops, temperate fruit
trees or shrubs, tropical plantation crops, ornamentals, spices, and medicinal and
aromatic plants (Azcon-Aguilar and Barea 1997; Barea et al. 2004; Vestberg
U. Sakthivel • B. Karthikeyan (*)
Department of Microbiology, Annamalai University, Annamalai Nagar, Chidambaram,
Tamil Nadu 608 002, India
e-mail: balakar02@yahoo.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_5
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U. Sakthivel and B. Karthikeyan
et al. 2002; Arpana et al. 2008; Singh et al. 2009a, b). Karthikeyan et al. (2007) also
reported the occurrence of vesicle AM fungi in certain medicinal plants of the
coastal plains of Tamil Nadu.
An intensive practice that warrants high yield and quality requires the extensive
use of chemical fertilizers, which are costly and may create environmental problems. Therefore, more recently, there has been a resurgence of interest in environmental friendly, sustainable, and organic agricultural practice (Esitken et al. 2005).
In this context, the use of biofertilizers containing plant growth-promoting
rhizobacteria (PGPR) strains instead of synthetic chemicals may serve as an
effective alternative and environmental friendly practice to improve plant growth
through the supply of plant nutrients and soil productivity. Moreover, it has been
found that exploiting these PGPR strains for growth promotion could reduce the
need for chemical fertilizers as well as the cost of cultivation.
PGPRs have gained considerable interest in recent years. Many rhizospherecolonizing bacteria especially PGPRs, including Azotobacter, Azospirillum, Bacillus, and Pseudomonas, typically produce substances that stimulate plant growth or
inhibit root pathogens (Kloepper et al. 1992; Glick 1995; Mantelin and Touraine
2004; Compant et al. 2005; Weyens et al. 2009; Karthikeyan et al. 2008, 2009;
Sakthivel and Karthikeyan 2012). Although numerous reports suggest the growthpromoting activities of bioinoculants, their use in the fields has not become popular
or effective. The main limitation being the effective delivery system of bioinoculants particularly in case of vegetative propagated crops (multiplied by vegetative
cuttings) for maintaining sufficient populations in the rhizosphere, though inoculation of seeds has been found effective in case of Rhizobium (Ben Rebah
et al. 2002). A few reports exist on the symbiotic growth and yield response of
patchouli to bioinoculants (Manjunatha et al. 2002; Arpana et al. 2008). Because of
current public concerns about the harmful effects of agrochemicals, there is an
increasing interest in improving the understanding of cooperative activities among
rhizospheric plant-beneficial microbial populations and how these might be applied
to agriculture (Kennedy 1998; Bowen and Rovira 1999; Barea et al. 2004;
Lucy et al. 2004; Malik et al. 2009).
Among the different groups of plant growth-promoting rhizobacteria, nitrogenfixing and phosphorus-solubilizing/phosphate-mobilizing organisms may be considered to be important since they improve plant nutrition by increasing N and P
uptake by plants, and they play a significant role as PGPR in the biofertilizers of
crops (Karthikeyan et al. 2008, 2013).
Certain cooperative microbial activities can be exploited as low-input biotechnology, and form a basis for a strategy to help sustainable, environmentally
friendly practices fundamental to the stability and productivity of both agricultural
systems and natural ecosystems (Kennedy and Smith 1995). A plant-beneficial
symbiosis may be obtained by the preinoculation of plants with the desired
bioinoculants. Preinoculation with AM fungi/bioinoculants is an obvious management practice in crops established as transplants and may lead to increased yield
(Sorensen et al. 2008), provided sufficient numbers are transferred and get established in the rhizosphere. Nurseries can realize two main benefits from introducing
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5 Effect of AM Fungi and Plant Growth-Promoting Rhizobacteria (PGPR). . .
91
bioinoculants to their plants: effective and stronger establishment resulting in
superior growth of the plants in the nursery and improved performance after their
transplanting in field (Gianinazzi et al. 2001).
5.2
Distribution and Population Dynamics of AM Fungi
and PGPR in Coleus forskohlii
The occurrence of Arbuscular Mycorrhizal fungi (AMF) in the roots of several
medicinal plants was noticed by Govinda Rao et al. (1989). The occurrence of
spore and colonization in the roots of Coleus forskohlii is also reported. The
percentage of mycorrhizal root colonization was significantly greater in plants
inoculated with AM fungi compared to uninoculated plants. Maximum colonization
was observed in plants inoculated with G. bagyarajii, which was significantly
different from all other treatments, the next best being with S. calospora. Spore
numbers in the root zone soil followed a similar trend. There was a positive
correlation between the intensity of mycorrhizal colonization and growth response
(Earanna et al. 2002).
Karthikeyan et al. (2007) also reported that certain species of medicinal plants
were screened for their VAM association by collecting rhizosphere soil samples of
individual species along with fine root from coastal plains. Fifteen species of
medicinal plants screened were found to colonize with VAM fungi. Among 15 species, Thulasi (Ocimum sanctum) recorded the maximum (58 %) VAM fungal
colonization followed by Nithya Kalyani (Catharanthus roseus). All the species
of VAM fungi such as Glomus sp., Gigaspora sp., and Acaulospora were found.
5.3
Growth Promotion by AM Fungi and PGPR
The association between mycorrhizae and medicinal herbs could result in better
plant growth as well as an increase in phytochemical concentrations. AM fungi are
known to play a pivotal role in the nutrition and growth of plants in many
production-oriented agricultural systems, but little is known about their potential
effect on secondary metabolites in medicinal and aromatic plants (Kapoor
et al. 2002a, b, 2004; Copetta et al. 2006; Khaosaad et al. 2006).
Mycorrhizal inoculation had a significant effect on the quality and quantity of
essential oils of Coriandrum sativum (Kapoor et al. 2002b). Variations in plant
growth and active principles in mycorrhizae-inoculated plants have been reported
for many other medicinal plants (Sailo and Bagyaraj 2005; Copetta et al. 2006).
The inoculation of AM fungi and other beneficial soil microorganisms significantly
increased the biomass of different medicinal plants (Sena and Das 1998;
Kothari et al. 1999).
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The role of mycorrhizae on plant growth has often been related to the increase in
the uptake of immobile nutrients, such as phosphorus. Inoculation with AM fungi
improved phosphorus uptake in Coleus aromaticus (Earanna et al. 2001). Coleus
forskohlii showed an increase in plant height, number of branches, biomass, P
content, and forskolin content when it was inoculated with Glomus bagyarajii
(Sailo and Bagyaraj 2005).
The mode of interaction between AM fungi and PGPR is a universally recognized interaction, marketing each symbiont as an individual entity capable of
inducing growth. PGPRs interact with host plants and indigenous Rhizobia through
endosymbiosis and release stimulatory control compounds, while AM fungi interact by forming infection sites (spores) on host plant’s roots, increasing the susceptibility for Rhizobia and PGPR induction, all the while increasing the surface area
through hyphal extensions (Bianciotto and Bonfante 2002). On coinoculation, AM
fungi and PGPR initiate morphological, physiological, and biological changes in
the rhizosphere and mycorrhizosphere with aims of attaining prolonged growth and
fertility in various types of soil conditions. Such parameters are generated through
interactions which promote nutrient acquisition, nitrogen fixation, phosphorus
capture, exudates’ secretion, and release of antipathogenic compounds (Barea
et al. 2005). It was observed that AM fungi, in association with nitrogen-fixing
bacteria, Azospirillum brasilense, increase plant productivity by stimulating AM
fungi root colonization, thereby increasing the number of internal vesicles relaying
nutrient capture and flow (Linderman and Paulitz 1990). Furthermore, inoculation
of Rhizobium sp. with phosphate-solubilizing microorganism (PSM) Pseudomonas
striata and AM fungi species Glomus fasciculatum enhanced plant yield and
nutrient and phosphorus uptake for chickpea plants in phosphorus-deficient sandy
clay loam soils (Zaidi et al. 2001).
In fact, the postinoculation period between 45 and 90 days was marked by
significant levels of growth through collective combinations of PSM on root
infection and spore density (Zaidi et al. 2001). This persistent symbiotic behavior
between AM fungi, PGPR, and rhizobia suggested that similar results can be
obtained in environmentally stressed soils where viable growth is hindered due to
source availability. AM fungi species Glomus fasciculatum as a coinoculant with
P. fluorescens exhibited varying deficit intensities. Individually, in water-deprived
soil, P. fluorescens (Pf) had limited grain and biomass production, while coinoculation with AM fungi increased the assimilation of phosphorus treatment. However,
when inoculated in water-deficient soil, dual inoculation with phosphorus fertilizer
and AM + P. fluorescens inoculation significantly increased grain phosphorus and
nitrogen concentrations as compared to uninoculated well-watered treatments (control). Root colonization was significantly higher in applications with dual inoculants, against control (uninoculated) and phosphorus fertilizer treatment in wellwatered soils (Ehteshami et al. 2007). Such increased levels of colonization coincide with increased ACC-deaminase and chitinase activity (Shaharoona
et al. 2006). Further, Ehteshami et al. (2007) suggest these gains market proliferation through the aid of plant hormones (phytohormones) and release of regulatory
metabolites to counteract and maintain vitality during erratic intensities of water
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5 Effect of AM Fungi and Plant Growth-Promoting Rhizobacteria (PGPR). . .
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deficit (Ehteshami et al. 2007). Earlier, Subramanian et al. (2006) suggested that the
increased adsorptive surface area and densely proliferated root growth in the
mycorrhizosphere complement increased root colonization and infection. These
characteristics support the use of bioinoculants as potential remediation tools to
combat water-deficit stresses. However, water uptake through a plant vascular
system can be hindered if severe stresses disrupt root architecture and distribution,
thereby affecting the rate of water absorption per unit root (Auge 2001).
Arpana and Bagyaraj (2007) reported the influence of inoculation with the
arbuscular mycorrhizal (AM) fungus Glomus mosseae and the plant growthpromoting rhizobacteria microorganisms (PGPR) Trichoderma harzianum singly
and in combination on the growth and yield of Kalmegh (Andrographis paniculata)
at two levels of P fertilizer application, i.e., at the recommended level and 75 % of
the recommended level. The plant height, plant spread, number of branches per
plant, number of leaves per plant, leaf area, plant dry matter, plant P content, and
andrographolide concentration were significantly higher in plants inoculated with
both the organisms, at both the levels of P as compared to uninoculated plants.
The effect of mycorrhization on growth and development has been observed in
other plant species, including members of Asteraceae. Mycorrhization of Annona
Squamosa has been reported to have a marked effect on the height of the plant and
fresh and dry weight of the roots and shoots compared to their respective controls
(Ojha et al. 2008).
Karthikeyan et al. (2008) evaluated the effectiveness of AMF and phosphorus
levels (100, 150, and 200 kg) for increasing biomass yield and ajmalicine content in
a medicinal plant (Catharanthus roseus). The plants treated 200 kg P2O5/ha along
with AMF had the maximum plant height, number of leaves, root biomass, phosphorus content, root colonization, spore count, and ajmalicine content on 120 days
after planting when compared with the control plants.
5.4
Influence of AM Fungi and PGPR for the Growth
and Yield of Coleus forskohlii
Sakthivel and Karthikeyan (2012) reported that the plant height of Coleus forskohlii
significantly increased due to the inoculated G. fasciculatum and PGPR strains. The
G. fasciculatum with PGPR consortium treatment (T4) at 180 DAP recorded the
maximum plant height of 68.5 cm/plant followed by the treatments T1, T3, and T2.
The uninoculated control treatment T5 recorded the minimum plant height for all
the sampling periods (Table 5.1 and Fig. 5.1).
The number of tubers per plant of Coleus forskohlii significantly increased due
to the inoculated G. fasciculatum and PGPR strains. G. fasciculatum with PGPR
consortium treatment (T4) at 180 DAP recorded the maximum number of tubers per
plant of 21.6 per plant followed by the treatments T1, T3, and T2. The uninoculated
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U. Sakthivel and B. Karthikeyan
Table 5.1 Effect of AM fungi and plant growth-promoting rhizobacteria (PGPR) inoculation on
plant height of Coleus forskohlii
Treatments
T1—Glomus fasciculatum
T2—Achromobacter xylosoxidans
T3—Azospirillum lipoferum
T4—Consortium (G. fasciculatum + A. xylosoxidans
+ A. lipoferum)
T5—Control (uninoculated)
Plant height (cm/plant)
135
90
45
DAP
DAP
DAP
180
DAP
23.8b
21.6c
22.5c
27.3a
42.5b
38.3d
40.2c
49.7a
55.2b
49.6d
52.9c
59.7a
64.5b
58.3d
60.2c
68.5a
15.7d
31.4e
44.5e
51.3e
Means of trials; the mean values in vertical columns followed by the same letter do not differ
statistically between themselves at P 0.05
Fig. 5.1 Overall view of Coleus forskohlii in pot culture experiment
control treatment T5 recorded the minimum number of tubers for all the sampling
periods (Table 5.2).
The number of tuber length per plant of Coleus forskohlii significantly increased
due to the inoculated G. fasciculatum and PGPR strains. The G. fasciculatum with
PGPR consortium treatment (T4) at 180 DAP recorded the maximum number of
tuber length per plant of 19.5 per plant followed by the treatments T1, T3, and T2.
The uninoculated control treatment T5 recorded the minimum tuber length for all
the sampling periods (Table 5.3).
Plants inoculated with G. fasciculatum and PGPR strains performed equally well,
showing that significant increases in treatment T4 recorded the tuber wet weight and
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5 Effect of AM Fungi and Plant Growth-Promoting Rhizobacteria (PGPR). . .
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Table 5.2 Effect of AM fungi and plant growth-promoting rhizobacteria (PGPR) inoculation on
number of tubers per plant of Coleus forskohlii
Treatments
T1—Glomus fasciculatum
T2—Achromobacter xylosoxidans
T3—Azospirillum lipoferum
T4—Consortium (G. fasciculatum + A. xylosoxidans
+ A. lipoferum)
T5—Control (uninoculated)
Number of tubers/plant
135
90
45
DAP
DAP
DAP
180
DAP
7.5b
6.2c
6.5c
9.8a
13.5b
12.0c
12.3c
16.4a
16.6b
14.0d
15.5c
18.9a
19.2b
16.6d
17.4c
21.6a
4.3d
9.8d
12.5e
14.3e
Means of trials; the mean values in vertical columns followed by the same letter do not differ
statistically between themselves at P 0.05
Table 5.3 Effect of AM fungi and plant growth-promoting rhizobacteria (PGPR) inoculation on
tuber length per plant of Coleus forskohlii
Treatments
T1—Glomus fasciculatum
T2—Achromobacter xylosoxidans
T3—Azospirillum lipoferum
T4—Consortium (G. fasciculatum + A. xylosoxidans
+ A. lipoferum)
T5—Control (uninoculated)
Tuber length (cm/plant)
135
90
45
DAP
DAP
DAP
180
DAP
5.4b
4.5c
4.8c
6.5a
9.2b
7.4d
8.6c
11.2a
13.4b
10.7d
12.3c
16.9a
16.9b
13.5d
14.8c
19.5a
2.0d
5.5e
9.0e
12.6e
Means of trials; the mean values in vertical columns followed by the same letter do not differ
statistically between themselves at P 0.05
dry weight of, respectively, 137.42 and 67.60 g/plant at 180 DAP followed by the
treatments T1, T3, and T2, compared with controls.
Forskolin concentration was not affected by any of the bioinoculant treatments,
but as a result of higher tuber yields, the total forskolin yield (calculated) was
significantly higher in plants treated with treatment T4—G. fasciculatum + PGPR
strains (97.0 %), T1—G. fasciculatum (88.0 %), T3—Azospirillum lipoferum
(82.0 %), and T2—Achromobacter xylosoxidans (78.0 %) than in T5— controls
(Table 5.4 and Figs. 5.2 and 5.3).
The results clearly indicate that efficient bioinoculants (G. fasciculatum and
Achromobacter xylosoxidans + Azospirillum lipoferum) significantly improved
plant growth parameters of C. forskohlii, in pot conditions, a finding also supported
by Earanna et al. (2001).
Tuberous roots are the main economic part of C. forskohlii. Glomus fasciculatum, Achromobacter xylosoxidans, and Azospirillum lipoferum produced significantly higher dry root yields. Earlier reports indicating the usefulness of
bioinoculants in improving growth and yield support these results (Earanna
et al. 1999; Singh et al. 2009a). Higher root yields might also be caused by the
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Table 5.4 Effect of AM fungi and plant growth-promoting rhizobacteria (PGPR) inoculation on tuber yield and forskolin content of Coleus forskohlii
mkumar9@amity.edu
Treatments
T1—Glomus fasciculatum
T2—Achromobacter xylosoxidans
T3—Azospirillum lipoferum
T4—Consortium (G. fasciculatum + A. xylosoxidans
+ A. lipoferum)
T5—Control (uninoculated)
Tuber wet weight (g/plant)
180
135
90
45
DAP
DAP
DAP
DAP
Tuber dry weight (g/plant)
135
90
45
DAP
DAP
DAP
180
DAP
Forskolin content
(%)
23.35b
19.88c
20.56b
36.44a
42.45a
36.61b
39.10b
48.33a
69.20b
52.84c
55.72c
86.25a
95.55b
76.10d
83.65c
137.42a
15.30b
11.00c
13.15c
18.85a
23.45a
18.30b
20.12b
27.25a
35.20b
27.44c
32.38b
46.65a
48.38b
38.65c
42.05b
67.60a
88.0b
78.0d
82.0c
97.0a
16.80c
28.15c
49.30d
64.88e
8.66d
14.20c
23.22c
29.40d
65.0e
U. Sakthivel and B. Karthikeyan
Values in each column followed by different letters are significantly different at P 0.05
5 Effect of AM Fungi and Plant Growth-Promoting Rhizobacteria (PGPR). . .
97
Fig. 5.2 Effect of AM fungi and plant growth-promoting rhizobacteria (PGPR) inoculation on
tuber yield of Coleus forskohlii (Pot culture experiment)
effectiveness of these bioinoculants and neem cake in controlling plant pathogens
(Singh et al. 1980, 2011) and in providing nutrition to the plants. Bioinoculants also
increased forskolin yield, which is supported by the results of Boby and Bagyaraj
(2003). Sakthivel and Karthikeyan (2012) reported that PGPR inoculation of
Coleus forskohlii significantly increased plant height, number of tubers, tuber
length, tuber yield, and forskolin yield on 180th day after planting.
Singh et al. (2013) reported that higher tuber yields in Coleus forskohlii plants
inoculated with Glomus fasciculatum and/or Pseudomonas monteilii under field
conditions may result from the effectiveness of the bioinoculants, improving the
availability of nutrients to the plants.
Santosh Dharana et al. (2006) reported the application of bioinoculants (Glomus
intraradices, G. fasciculatum, G. monosporum, G. mosseae, Sclerocystis dussii,
Gigaspora margarita, and a consortium of A. chroococcum, A. lipoferum,
P. striata, and trichoderma harzianum) to significantly increased the plant height,
plant spread, tuber yield, and forskolin yield in Coleus forskohlii.
Singh et al. (2009a) reported that treatments with AM fungus Glomus fasciculatum and P. fluorescens were the most effective that reduced the severity of
root rot and wilt of Coleus forskohlii under lower and higher levels of pathogen
F. chlamydosporum. Glomus fasciculatum increased the dry shoot and root weight,
while in plants treated with P. fluorescens, an increase of dry shoot and root weight
of Coleus forskohlii. A positive effect of Glomus mosseae and phosphorus levels
was observed on growth, biomass yield, and ajmalicine content of Catharanthus
roseus (Karthikeyan et al. 2008).
An investigation made by Karthikeyan et al. (2009) about the response of
vesicular mycorrhizal fungi of Glomus fasciculatum on Ocimum sanctum,
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U. Sakthivel and B. Karthikeyan
Fig. 3 (continued)
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5 Effect of AM Fungi and Plant Growth-Promoting Rhizobacteria (PGPR). . .
99
Fig. 5.3 Effect of AM fungi and plant growth-promoting rhizobacteria (PGPR) inoculation on
forskolin content of Coleus forskohlii tubers by HPLC. T1—Glomus fasciculatum, T2—
Achromobacter xylosoxidans, T3—Azospirillum lipoferum, T4—Consortium (G. fasciculatum
+ A. xylosoxidans + A. lipoferum), T5—Control (uninoculated)
Catharanthus roseus, Coleus forskohlii, and Cymbopogon flexuosus revealed an
increase in total dry matter production (shoot and root dry weight), protein content,
and total chlorophyll contents in mycorrhizae-inoculated plants.
Sailo and Bagyaraj (2005) reported the AM fungi (Glomus bagyarajii) to
significantly increase plant height, number of branches, length of fresh root, tuber
dry weight, P uptake, and forskolin content of Coleus forskohlii. A study carried out
by Senthilkumar et al. (2009) on Artemisia palleus has shown that the combined
application of nitrogen, phosphorus, and Azospirillum resulted in the highest number of laterals per plants, increase in fresh and dry weight, and increase in photosynthetic efficiency of the crop.
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5.5
U. Sakthivel and B. Karthikeyan
The Role of AM Fungi in Soil and as a Potential
Bioinoculant
When considering fungi as a source of soil inoculums, often negative connotations
propelled by the intensive degradation by fungal species (e.g., Fusarium oxysporum) are contributing factors to agricultural condemnation. However, recent
advances toward biotechnology have identified fungal species capable of promoting
successive growth and increasing soil fertility (Sharif and Moawad 2006). The
major groups of fungi that establish mutualistic symbiosis are categorized for their
ability to interact with the roots of various plant species, referred to as mycorrhizal
symbiosis (Ahmad et al. 2008a). AMF have been identified as existing entities in
most agroecosystems, colonizing the root cortex biotrophically and establishing a
mycelium bridge (hyphal network), connecting root to surrounding microhabitats
(Egamberdieva et al. 2004). AM fungi are considered as obligate microbial symbionts, dependent on the colonization of host plants to maintain viability in the
system. This mutually exclusive relationship benefits the host through correspondence with the mycorrhizal hyphal network, providing a large surface area for
the absorption of essential immobile ions such as phosphate, copper, and zinc
needed by the plant for sustaining growth (Paraskevopoulou Paroussi et al. 1997;
Masoumeh et al. 2009). Mycorrhizal symbiosis also provides the plant with versatility against various biotic and abiotic stresses through the formation of stable soil
aggregates, selective proliferation of synergistic microbial colonies, and formation
of macropore structures in soil to facilitate aeration and water penetration to deep
surface layers (Piotrowski et al. 2004). These compositional structure modifications
and branching complexes allow nutrients to be sequestered from various deep soil
reserves, mandating a push toward plant fitness and tolerance, increasing the
probability of survival when subsurface nutrient concentrations are limited or
faced with harsh environmental conditions (Ahmad et al. 2008b).
Macrophomina phaseolina (tassi) is a common root rot fungus, infecting about
500 plant species, one of which being Cicer arietinum (Srivastava et al. 2001).
Rhizobia provide an initial barrier to fungal pathogens; however, through the use of
AM fungus species, the potential for remediating pathogenesis while promoting
growth is possible (Siddiqui and Akhtar 2009; Ozgonen and Erkilic 2007; Akkopru
and Demir 2005). Akhtar and Siddiqui (2010) studied the influence of four AM
fungi species, Glomus intraradices, G. aggregatum, G. claroideum, and Glomus
sp., for the biocontrol of M. phaseolina on Cicer arietinum pod growth, nodulation,
chlorophyll, nitrogen, phosphorus, potassium concentrations, and effectiveness of
controlling root rot. The experimental design consisted of five randomized blocks,
each with different treatments of G. intraradices, G. aggregatum, G. claroideum,
Glomus sp., and Control in the presence and absence of M. phaseolina. The plants
were harvested 90 days after inoculation and grown in sandy loam soil mixed with
washed river sand and farm yard manure at the ratio 3:2:1. The inoculation of all
four AM fungi species without treatment of M. phaseolina exercised all growth
parameters as compared to the uninoculated control. Increases in shoot dry weight,
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5 Effect of AM Fungi and Plant Growth-Promoting Rhizobacteria (PGPR). . .
101
number of pods per plant, the number of nodules per root system, nitrogen,
potassium, phosphorus, chlorophyll, and degree of root colonization by AM fungi
were all exhibited after the 90-day harvest period, with G. intraradices optimizing
greatest yields. The influence of M. phaseolina, interestingly enough shoot dry
weight also increased, recording higher percentages, and then control and
nonpathogen treatment. This gain corresponded to the increased shoot dry weight
of pathogenic fungus manifested through AM fungi colonization; however, this also
resulted in considerable decreases in the number of pods per plant as compared to
non-M. phaseolina treatment (Akhtar and Siddiqui 2010). The number of nodules
per root system stayed relatively the same, while root colonization of AM fungus
was found to be considerably lower, suggesting the formulation of spores and/or the
activation of plant defense mechanisms, inhibiting growth and colonization (Demir
and Akkopru 2005). Through the influence of AM fungi on M. phaseolina-treated
plants, a reduction in root rot index was seen, suggesting that the uninoculated
control (index of 4) was less effective in secreting enzymes and biocontrol compounds necessary to maintain viability after infection (Pozo et al. 1999).
Arpana and Bagyaraj (2007) reported that the highest mycorrhizal root colonization in Kalmegh plant was observed when G. mosseae was coinoculated with
T. harzianum at both levels of P (75 and 100 %). Among the single inoculated
treatments, highest mycorrhizal colonization was observed in plants inoculated
with the AM fungus G. mosseae, thus supporting the well-documented fact that
inoculation with effective AM fungi enhances mycorrhizal root colonization (Rajan
et al. 2000).
5.6
AM Fungi Interactions with PGPR as a Potential
Bioinoculant
Diversity in the rhizosphere and surrounding microhabitats is marked by various
interactive microfloras, stimulating mechanisms to promote or suppress microbial
activity. AM fungi establish host specificity by infecting the host cortical cells,
forming arbuscules along the plant root architecture. In this, the soil-dwelling
Rhizobium and PGPR bacteria interact through endosymbiosis, forming an AM
fungal endophytic bacteria capable of promoting rhizobial interactions with mycorrhizae and plant (Bianciotto and Bonfante 2002). The typical rhizobacteria–AM
fungi interaction describes PGPR as the “mycorrhizae-helper microorganism/bacteria,” active in stimulating mycelial growth and/or enhancing mycorrhizal formation (Garbaye 1994). PGPR or soil-dwelling Rhizobia interact with the mycorrhizal
fungi by adhering to fungal spores and hyphal structures, initiating exposure and
spread to other microorganisms capable of symbiosis within the rhizosphere
(Bianciotto and Bonfante 2002). As PGPRs or rhizobia interact with the host
plant, the rate of exudate expulsion increases. When aided by the presence of AM
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U. Sakthivel and B. Karthikeyan
fungi, the secretion of root exudates stimulates mycelial growth in the rhizosphere
and initiates root penetration by the fungus (Azcon-Aguilar and Barea 1992).
Furthermore, as Azcon-Aguilar and Barea (1992, 1995) observed, the rhizobial
interaction influences presymbiotic stages of AM fungal development such as spore
germination and mycelia growth when coupled by the release of plant hormones,
instigating AM establishment within the rhizosphere and root cortex. Such morphological transformations induce physiological changes within the plant and the
surrounding environment to complement the interaction. Symbiosis alters the
chemical composition of root exudates through changes in host’s physiology,
establishing shifts in mineral nutrient deposition of plant tissues, carbon allocation
and utilization, and hormonal balances. However, physical development of AM
mycelium in the rhizosphere/rhizoplane induces the synthesis and metabolism of
essential plant and microbial parameters by acting as an abundant source of carbon
(Barea et al. 2005). Secretion, uptake, and availability of root exudates, phytoalexins, and phenolic compounds become more abundant, prompting soil composition to become systemically modified to accommodate elevated interactions
(Duponnois et al. 2005), thereby inducing physiological changes in the rhizobial
community, marketing both quantitative and qualitative production of viable active
symbionts, such as PGPR (Barea et al. 2005). This well-nourished and rich region
of interaction and growth of mycorrhizae and mycelia is referred to as the mycorrhizosphere (Linderman 1988; Gryndler 2000). In the mycorrhizosphere, the principle of
interaction is oriented toward promoting phosphorus uptake. Through the extensive
branching between AM fungal mycelium and host root structures, access to phosphate
ions in soil can be elevated, extending beyond the phosphate-depleting zone and into
deeper regions in soil (Smith and Read 1997). Besides providing the vessel for
transport and available carbon, AM fungi contributed to phosphorus capture by
linking the biotic and geochemical portions of the soil ecosystem, thereby affecting
both phosphorus cycling rates and patterns (Jeffries and Barea 2001).
Supplementing artificial phosphate feeds with aims of enriching soil content and
interactions has shown mediocre gains. It has been suggested that through ecological soil exploration, the naturally occurring uptake of phosphate from bulk soils
produces greater levels of activation and response between indigenous microflora
and host plant parameters (Gupta et al. 2007). Because the availability of appropriate enzymes and secretion of stimulated growth factors promote rhizobial and
soil competency, physiological and adaptive traits catered toward synchronizing
symbiosis are induced (Barea et al. 2005). However, large doses of phosphorus
fertilizer may potentially inhibit or hinder mycorrhizal growth and efficiency. As
the surface area is more prevalent, host and PGPR may absorb more phosphorus at
higher rates; however, biological response to meet the surplus may be overwhelmed
and may hinder escalation to appropriate metabolite requirements without taxing
the plant of other essential compounds (Gupta et al. 2007).
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5 Effect of AM Fungi and Plant Growth-Promoting Rhizobacteria (PGPR). . .
5.7
103
Conclusions
This study clearly indicated that the growth and yield of C. forskohlii could be
reduced by soil amendments such as bioinoculants such as G. fasciculatum,
Achromobacter xylosoxidans, and Azospirillum lipoferum. This management
approach will be particularly useful under organic farming conditions, especially
for medicinal plants, where the use of chemicals is restricted because of health and
residue considerations.
Acknowledgement The author thanks sincerely the authorities of Annamalai University for
enabling him to do the above pioneering work on PGPR inoculation for commercially grown
medicinal plants and for all facilities provided.
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mkumar9@amity.edu
Chapter 6
Plant Growth-Promoting Rhizobacteria
(PGPR): Emergence and Future Facets
in Medicinal Plants
Shivesh Sharma, Vasudha Singh, Vivek Kumar, Shikha Devi,
Keshav Prasad Shukla, Ashish Tiwari, Jyoti Singh, and Sandeep Bisht
6.1
Introduction
Medicinal plants are source of many potent and effective drugs which are used in
different countries for their different therapeutic purposes (Mahesh and Satish
2008). Medicinal plants are easily accessible healthcare alternative, and approximately 60–80 % of the world’s population still relies on these medicinal plants for
the treatment of common illnesses (Menghani et al. 2011). According to the World
Health Organization, more than 80 % of the world’s population relies on traditional
medicine for their primary healthcare needs (Shetty and Singh 1993; Goto
et al. 1998). Humans depend on more than 9,000 plant species for food, clothing,
shelter, medicines, forages, and industry, and about 1,200 herbal plants are mentioned in ancient Indian texts (Bairoch 2000; Yuan et al. 2010). About 900 species
have been domesticated for agriculture, and from these about 168 species are
specifically cultivated for food and agriculture (Bansal and Woolverton 2003).
India is a varietal emporium of medicinal plants, and it is one of the richest
countries in the world as regards genetic resources of medicinal plants (Alluri
et al. 2005). It is rich in its biological resources and has century’s old heritage of
medicinal plants and herbal medicines for curing human illness and promotion of
S. Sharma (*) • V. Singh • S. Devi • A. Tiwari • J. Singh
Department of Biotechnology, Motilal Nehru National Institute of Technology, Allahabad,
India
e-mail: shiveshs@mnnit.ac.in; ssnvsharma@gmail.com
V. Kumar
Amity Institute of Microbial Technology, Amity University, Noida, India
K.P. Shukla
Hindustan College of Science and Technology, Farah, Mathura, India
S. Bisht
Department of Microbiology, UUHF College of Horticulture, Bharsar, Pauri, India
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_6
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S. Sharma et al.
health in tribal and rural areas. Its ethnic people and tribals living in the remote
forest areas still depend to a great extent on the indigenous systems of medicine
(Dutta and Dutta 2005). A wide range in topography and climate is exhibited in
India which results in different types of vegetation and floristic composition.
Moreover the agroclimatical conditions are conducive for introducing and domesticating new exotic plant varieties (Alluri et al. 2005). In India, out of 18,864 species
of higher plants, 1,100 species are used in different systems (Das et al. 2009). The
number of higher plant species (angiosperms and gymnosperms) is estimated
between 215,000 and 500,000 species. Of these, only about 6 % have been screened
for biological activity, and a reported 15 % have been evaluated phytochemically
(Fabricant and Farnsworth 2001; Verpoorte 2000). Natural medicines are in great
demand in the developed world for primary health care because of their efficacy,
safety, and lesser side effects (News 2010). Medicinal plants represent a rich source
of antimicrobial agents (Das et al. 2009).
Many researchers have reported the activity of various medicinal plants from
various regions which are now being used as an alternative source for drugs
(Rajakumar and Shivanna 2009). In studies carried out by Sharma et al. (2009a,
b), it is observed that plants produce a wide variety of secondary metabolites which
are used either directly as precursors or as lead compounds in the pharmaceutical
industry, and it is expected that plant extracts showing target sites other than those
used by antibiotics will be active against drug-resistant microbial pathogens. These
active compounds inhibit the growth of disease causing microbes either singly or in
combination (Cowan 1999). Inhibition of the growth of microbes by these active
compounds is brought about by lysing the cell wall, breaking the peptide bonds,
acting as chelating agents, binding their surface proteins, altering their biochemical
systematics, or preventing utilization of available nutrients to the microorganisms
(Cowan 1999; Maji et al. 2010; Zafar et al. 1999).
Though the screening of Indian medicinal plants has revealed varying degrees of
activity against pathogenic microorganisms, due to lack of experimental scientific
studies, confirmation of the antimicrobial properties of a great number of these
remedies is not possible (Sharma et al. 2009a, b; Ahmed and Beg 2001). The most
important bioactive constituents of plants are alkaloids, tannin, flavonoid, and
phenolic compounds (Shihabudeen et al. 2010). Alternative sources for more
natural and environmentally friendly antibiotics, antimicrobials, crop protection
agents, and antioxidants are being searched by various industries; hence medicinal
plants are being investigated thoroughly for their bioactivity for different pharmacological purposes. They are mainly interested in the discovery of active chemical
structures from which they can develop and prepare synthetic analogues which are
more controllable from the point of reproducibility, patentability, and safety and are
more economically viable (Svoboda and Hampson 1999). Some researchers have
observed that volatile oils of many plants are known to have antimicrobial activity
(Henikoff et al. 1995). Plant essential oils also act as antioxidant which has been
researched in detail with the view to investigate their protective role for highly
unsaturated lipids in animal tissues (Henikoff et al. 1995; Deans et al. 1993;
Ushimaru et al. 2007). The multidrug-resistant strain of many microorganisms
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6 Plant Growth-Promoting Rhizobacteria (PGPR): Emergence and Future Facets. . .
111
has revealed exploration of alternative antimicrobial agent. As reported by
Bhaskarwar et al. (2008), Jatropha podagrica of family Euphorbiaceae is known
for many biological activities such as antitumor, antimicrobial, molluscicidal, and
anti-insect. Jatropha podagrica is also used as an antipyretic, diuretic, choleretic,
and purgative (Kupchan et al. 1970; Sigrist et al. 2002). Medicinal plants have
become the focus of intense study in terms of validation of their traditional uses
through the determination of their actual pharmacological effects (Sen et al. 2008;
Muniappan and Ignacimuthu 2011; Bhaskarwar et al. 2008; Nair and Chanda 2007;
Pullaiah 2002). This can be brought about by using different computational
approaches for identifying promising lead candidates for the development and
study of the bioactive substances of medicinal plants.
The plant kingdom is a very rich resource for discovering new antimicrobial
compounds for human medicine as well as many other applications such as food
preservation, disease management in agriculture, veterinary disease control, and the
coatings of household products (Fikret et al. 2000; Jagtap et al. 2009). Although
molds, actinomycetes, and bacteria are the chief sources of antibiotics, antibacterial
agents are also present in higher plants (Nimet 2002). Plants that possess therapeutic properties on the animal or plant body are generally designated as medicinal
plants. With the development of microorganisms resistant to chemicals applied
indiscriminately to crops, research has been done with the goal to search for
alternative and safe forms of agrochemical pest control without causing any
damage to environment and to humans, maintaining the crop qualitatively and
quantitatively (Babalola 2010). The use of phytochemicals as natural antimicrobial
agents commonly called biocides is gaining popularity (Menghani et al. 2011; Smid
and Gorris 1999). The undocumented medicinal plants and practices of a specific
community are known as ethnobotanical knowledge which is under the threat of
habitat destruction and biopiracy. Unsustainable harvesting of these medicinal
plants has led to exploitation and decrease of the species. Systematic efforts to
exploit the valuable potential are still lacking (Rai 2004). The large-scale deforestation of green forest wealth, a renewable resource, is leading to an accelerated loss
of valuable or potentially valuable biodiversity, extinction of species, and genetic
erosion. It has been reported by Botanical Survey of India that around 93 % of
medicinal plants of India now belong to endangered species. The soil factors also
have very important effects on the quality and quantity of genuine regional drug
(Ren et al. 2005).
The maintenance of a high diversity of plant species requires a correspondingly
high level of diversity in the soil microbial community (Wardle 1992, 2002; Wardle
and Nicholson 1996; Lugtenberg and Dekkers 1999). Plant growth-promoting
bacteria are associated with many, if not all, plant species and are commonly
present in many environments (Schroeder and Schwitzguebel 2004). Despite
inhabiting different niches, rhizosphere-associated bacteria share some mechanisms that improve plant growth and/or protect them from soilborne deleterious
organisms (Jain and Mudgal 1999).
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6.2
S. Sharma et al.
Rhizospheric Bacterial Diversity
Medicinal plants harbor a distinctive microbiome due to their unique and structurally divergent bioactive secondary metabolites that are most likely responsible for
the high specificity of the associated microorganisms (Shrivastava 2003; FAO
Investment Centre Socio-economic and Production Systems Studies). In general,
natural products play a highly considerable role in the drug discovery and development process, as about 26 % of the new chemical entities introduced into the
market worldwide from 1981 to 2010 were either natural products or those derived
directly therefrom, reaching a high of 50 % in 2010 (Newman and Cragg 2012;
Koberl et al. 2013). Plant rhizosphere is a versatile and dynamic ecological environment of intense microbe plant interactions for harnessing essential micro- and
macronutrients from a limited nutrient pool (Jeffries et al. 2003). Rhizosphere
microorganisms thus provide a critical link between plant and soil environments
(Kozhevin 1989). The “rhizosphere effect” is defined as the overall positive influence of interactions between plant roots and rhizoflora on the development of the
plant (Manoharachary and Mukerji 2006; Kandeler et al. 2002; Micallef et al. 2009;
Soderberg et al. 2002). The magnitude of the rhizosphere effect depends mainly on
the nature and amount of root exudates which appear to be related to plant age as
well as species on one hand and edaphic and climatic factors on the other hand
(Pandey and Palni 2007). The original concept includes the soil surrounding a root
in which physical, chemical, and biological properties have been changed by root
growth and activity (Tizzard et al. 2006). Plants release organic compounds through
root exudates and provide a rich environment for microbial activity (Pandey and
Palni 1998).
The root exudates of different plants support the development of different
bacterial communities. Root exudates provide a lot of nutrients for the soil microbes
and energy materials (Tilak et al. 2005). Microorganisms affect the permeability of
root cells, metabolism of roots, and absorption and excretion of certain compounds
in root exudates. Norman (1961) found that certain polypeptide antibiotics, for
example, polymyxin which is formed by Bacillus polymyxa from soil, altered cell
permeability and increased leakage. There are two main difficulties in interpreting
the significance of their results which show that culture filtrates or products increase
the leakiness of plant roots. First, the conditions under which the organisms are
grown are quite different both physically and nutritionally from those under which a
rhizosphere population grows. Second, as it is not possible to calculate the concentration of biologically active substances in the rhizosphere, the concentrations used
for “in vitro” experiments must of necessity be selected rather arbitrarily (Shukla
et al. 2011). Interactions between plants and soil microbes are highly dynamic in
nature and based on coevolutionary pressures (Dobbelaere et al. 2003; Duffy
et al. 2004; Klironomos 2002; Morgan et al. 2005; Morrissey et al. 2004; Reinhart
and Callaway 2006). Bacteria are the most abundant microorganisms in the rhizosphere, and they influence the plant physiology to a greater extent because of their
ability to compete for root colonization (Glick 1995). The negative rhizosphere
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6 Plant Growth-Promoting Rhizobacteria (PGPR): Emergence and Future Facets. . .
113
effect shows growth inhibitory relationships or the antagonistic behavior of microbial groups growing around roots of some plants that also result in a reduced or
smaller microbial population. This includes various categories of antagonism, such
as competition, antibiosis, parasitism, and predation (Chaiharn et al. 2008). These
antagonistic activities in a suppressive rhizosphere may maintain a low microbial
population in the rhizosphere (Pandey and Palni 2007). The influence of individual
plants is reflected in the rhizosphere as the R:S (rhizosphere to non-rhizosphere
ratio). R:S ratio determines the relative stimulation of the microorganisms in the
rhizosphere of different medicinal plant species (Pandey and Palni 1997). For
bacteria and fungi, values commonly range from 5 to 20. Actinomycetes, a somewhat less affected group of microorganisms by the rhizosphere, may reveal R:S
ratios between 2 and 12 (Pandey and Palni 1997).
6.3
Plant–Microbe Interaction
One of the most important indexes of soil quality is considered to be the diversity of
microbial communities present. Alteration in the activity of microbes is proposed to
be a sensitive indicator of anthropogenic effects on soil ecology (Shi et al. 2002;
Brookes 1995). Plant growth-promoting rhizobacteria (PGPR) are beneficial soil
bacteria, which may facilitate plant growth and development both directly and
indirectly (Chernin and Chet 2002). The root surface and surrounding rhizosphere
are significant carbon sinks (Kandeler et al. 2002). Photosynthate allocation to this
zone can be as high as 40 % (Degenhardt et al. 2003). Thus, along root surfaces,
there are various suitable nutrient-rich niches attracting a great diversity of microorganisms, including phytopathogens. Root exudates provide a lot of nutrients for
the soil microbes and energy materials. Competition for the nutrients and niches is a
fundamental mechanism by which PGPR protects plants from phytopathogens
(Asghar et al. 2002; Duffy 2001). Rhizodeposition of various exudates provides
an important substrate for the soil microbial community, and there is a complex
interplay between this community and the quantity and type of compounds released
(Kandeler et al. 2002; Marschner and Baumann 2003). Plant species is considered
to be one of the most important factors in shaping rhizobacterial communities, but
specific plant microbe interactions in the rhizosphere are still required to be studied
to fully understand it (Micallef et al. 2009). Based on their effects on the plant,
microbes interacting with plants can be classified as pathogenic, saprophytic, and
beneficial (Ben et al. 2002). Various species of bacteria like Pseudomonas,
Azospirillum, Azotobacter, Klebsiella, Enterobacter, Alcaligenes, Arthrobacter,
Burkholderia, Bacillus, and Serratia have been reported to enhance the plant
growth (Joseph et al. 2007).
Soil plant microbe interaction has got much importance in recent decades. Many
types of microorganisms are known to inhabit soil, especially rhizosphere, and play
important role in plant growth and development (Safdar et al. 2011). Direct
stimulations by microbes on plants include fixed nitrogen, phytohormones, iron
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that has been sequestered by bacterial siderophores, and soluble phosphate, whereas
indirect stimulation includes preventing phytopathogens (biocontrol) and this interaction promotes plant growth and development (Juanda 2005). PGPR performs
some of these functions through specific enzymes, which provoke physiological
changes in plants at molecular level. Microbes interacting with plants can be
classified as pathogenic, saprophytic, and beneficial, and beneficial microbes are
often used as inoculants (Bloemberg and Lugtenberg 2001). According to scientific
reports, 86 % of the bacterial isolates from the rhizosphere of various plants
produced phytohormones and also different vitamins (Nelson 2004). Rhizosphere
bacteria produce growth-promoting substances in culture media, in the rhizosphere,
and in the rhizoplane of forage grasses and many economically important cereals
like wheat and barley and vegetables, tomato, and bean plants under cultural
conditions (Whipps 2001). They can be classified according to the goal of their
application: biofertilizers (such as rhizobia, which have been applied commercially
for over a century), phytostimulators (such as auxin-producing, root-elongating
Azospirillum), rhizoremediators (pollutant degraders which use root exudate as
their carbon source), and biopesticides (Glick and Bashan 1997). Plant growth by
bacterial synthesis of plant hormones including indole-3-acetic acid, cytokinin, and
gibberellins as well as by increased mineral and nitrogen availability in the soil is
triggered by PGPR colonization (Saharan and Nehra 2011). Some of these plant
hormones are also known to protect their host plant from pathogenic microorganisms. Bacteria that can produce indole-3-acetic acid (IAA) and siderophores
and solubilize inorganic phosphate and HCN are capable of stimulating plant
growth and help plants to acquire sufficient iron, phosphate, and other essential
nutrients for optimal growth (Glick 1995, Idris et al. 2007; Chabot et al. 1996;
Rajkumar et al. 2006). However, little work has been done on PGPR activities of
forest plants (Chanway et al. 1991).
The role played by PGPR in relation to medicinal plants and their effect on the
production of botanicals is an area remaining naı̈ve (Sekar and Kandavel 2010).
Plant microbial interactions can be classified into three basic groups: (1) negative
(pathogenic) interactions; (2) positive interactions, in which either both partners
derive benefits from close association (symbiosis), both partners derive benefits
from loose association, or only one partner derives benefits without harming the
other (associative); and (3) neutral interactions, where none of the partners derive a
direct benefit from interaction and in which neither is harmed (Singh et al. 2004).
The indigenous phosphate-solubilizing microorganisms of the selected medicinal
plants and their inoculation in the plant rhizosphere can be used practically in
increasing the growth of plants (Safdar et al. 2011). Alternate ways of plant growth
by PGPR have also been observed like by associative N2 fixation, solubilizing
nutrients, promoting mycorrhizal function, regulating ethylene production in roots,
releasing phytohormones, and decreasing heavy metal toxicity (Saharan and Nehra
2011). Scientific studies of PGP activities and biocontrol in medicinal plants are
limited. There are two possibilities to influence the antagonistic/plant growthpromoting potential: (1) by managing the indigenous microbial potential, e.g., by
the introduction of organic or inorganic amendments (Wardle 2002; Emmert and
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Handelsman 1999; Conn and Lazarovits 2000), and (2) by applying autochthonous
microorganisms as biocontrol or plant growth-promoting agents (Compant
et al. 2005; Weller 2007; Weller et al. 2002; Whipps 2001). Direct plant growth
promotion by microbes is based on improved nutrient acquisition and hormonal
stimulation. Diverse mechanisms are involved in the suppression of plant pathogens, which is often indirectly connected with plant growth (Barazani and Friedman
1999; Khalid et al. 2004; Ashrafuzzaman et al. 2009; Bertland et al. 2001; De
Freitas and Germida 1990; Husen 2003). Beneficial plant microbe interaction leads
to the development of microbial inoculants for use in agricultural biotechnology
(Berg 2009). Traditional knowledge is one of the most important sources for
sustainable development of developing countries in various fields like agriculture,
food, and medicine where biological resources are the main components. A wide
array of natural products from botanicals are traditionally in use over several years
(Janovska et al. 2003). An enhanced production is necessary for the increasing
human population as well as basic compounds in industrial processes like in
pharmaceutical industry (Berg 2009). It has been observed that physical and
chemical properties of soil selected from different medicinal plant varied to some
extent from soil to soil (Safdar et al. 2011). The potential PGPR strains have been
recognized that can be used to inoculate tree roots in forests that require immediate
attention. As suggested by Tizzard et al. (2006), studies are required on investigating the application of PGPR and fungi for commercial forestry operation,
especially in the areas of enhancing tree growth and survival of tree seedlings
through microbially mediated phytohormone production.
6.4
Plant Growth-Promoting Attributes
PGPRs are usually in contact with the root surface and improve growth of plants by
several mechanisms, e.g., enhanced mineral nutrition, phytohormone production,
and disease suppression (Kremer et al. 2004; Mauch et al. 1988; Shakilabanu
et al. 2012; Schrey and Tarkka 2008; Tarkka et al. 2008; Hrynkiewicz and Baum
2011). Indian researchers have studied the diversity of rhizobacteria in a variety of
plants, cereals, legumes, and others along with the assessment of their functionality
based on the release of enzymes (soil dehydrogenase, phosphatase, nitrogenase,
etc.), metabolites (siderophores, antifungals, HCN, etc.), and growth promoters
(IAA, ethylene) and as inducers of systemic disease resistance (ISR) (Teixeira
et al. 2007; Singh et al. 2013). Two groups of PGPR were described: one group is
involved in the nutrient cycling and plant growth stimulation (biofertilizers)
(Vessey 2003), and the second group is involved in the biological control of plant
pathogens (biopesticides) (Whipps 2001). Medicinal plant constitutes a segment of
the flora which provides raw materials for the use of industries producing pharmaceuticals, cosmetics, fragrance, and biochemicals (Karthikeyan et al. 2008). Medicinal plants like any other plants take nutrients from the soil during growth, and
among macroelements, nitrogen results in the largest growth and yields response in
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medicinal plants (Ordookhani et al. 2013; Ayub et al. 2011; Cox 1992). The
contents of secondary metabolites are mostly increased through the positive effects
on the metabolic pathways of active compound synthesis in medicinal plants
(Papavizas and Ayers 1974; Ghorbanpour and Hatami 2013).
Biofertilizers are based on living microorganisms which colonize the rhizosphere or the interior of the plant (when applied to seed, plant surface, or soil)
and promote growth by increasing the availability of primary nutrients to the host
plant (Vessey 2003). There are a number of PGPR inoculants currently commercialized which promote plant growth with at least one mechanism, i.e., suppression of
plant disease (bioprotectants), improved nutrient acquisition (biofertilizers), or
phytohormones (biostimulants) (Kidoglu et al. 2007).
In summary, bacteria may support the plant growth by several mechanisms, e.g.,
increasing the ability of nutrients in the rhizosphere (1), inducing root growth and
thereby increasing the root surface area (2), and enhancing other beneficial symbioses of the host (3), and by combination of modes of action (Vessey 2003). The
occurrence of PGPR (Azotobacter, Azospirillum, Bacillus, and Pseudomonas) in the
rhizosphere of medicinal plants Catharanthus roseus, Coleus forskohlii, Aloe vera,
and Ocimum sanctum has been documented. Tamilarasi et al. (2008) isolated
various bacteria from rhizosphere of 50 medicinal plants, which among the isolated
bacteria, the dominant species was Bacillus followed by Pseudomonas, Enterobacter, Corynebacterium, Micrococcus, and Serratia. The main reason of microbial
specificity toward the various medicinal plants could be due to the exchange of
plant metabolites (Garagulia et al. 1974; Ramesh et al. 2012; Ghodsalavi
et al. 2013). Although in the recent years several researches were conducted to
study the effect of the PGPR on many plants, there is a lack of available reports on
medicinal plants.
6.4.1
Phosphate Solubilization
Plant root-associated phosphate-solubilizing bacteria (PSB) have been considered
as one of the possible alternatives for inorganic fertilizers for promoting plant
growth and yield (Islama et al. 2007). The ability to solubilize various insoluble
phosphates is always desirable to be a competent PGPR. Phosphorus is an essential
nutrient for plant growth and is one of the most important elements after nitrogen
(Nautiyal and Mehta 2001). It exists in organic and inorganic forms in soil and is
commonly deficient in most natural soils, especially acidic soils with low pH. It is
mostly fixed as insoluble iron and aluminum phosphates in acidic soil and fixed as
calcium phosphates in alkaline soils. It is required for several key plant structure
compounds like root development, stalk and stem strength, flower and seed formation, and crop maturity and production (Ordookhani et al. 2006). Phosphorus
nutrition is important for crop quality and resistance to plant diseases. Different
soils have varying phosphorus contents ranging between 0.02 and 0.5 %. Inadequate supply of phosphorus in soil can lead to diminished plant growth and plant
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6 Plant Growth-Promoting Rhizobacteria (PGPR): Emergence and Future Facets. . .
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yield (Halford 1997). The quality of crops, vegetables, and fruits can be enhanced
by providing sufficient phosphorus that will not only increase its yield but also
improve its resistance to diseases. Plant can acquire phosphorus from soil which is
available in the form of apatite (rock phosphate). Around 50–70 % phosphorus
found in soil is in inorganic form and its uptake by plant is low (Altomare
et al. 1999). The establishment and performance of phosphate-solubilizing microorganism is however affected severely under stressed conditions such as high salt,
pH, and temperature prevalent in degraded ecosystems represented by alkaline soils
with a tendency to fix phosphorus (Moran et al. 2001). The most efficient
phosphate-solubilizing microorganism (PSM) belongs to the genera Bacillus,
Rhizobium, and Pseudomonas among bacteria and Aspergillus and Penicillium
among fungi. Among the whole microbial population in soil, phosphatesolubilizing bacteria (PSB) constitute 1–50 %, while phosphate-solubilizing fungi
(PSF) are only 0.1–0.5 % (Chen et al. 2006). Bacterial isolates Pseudomonas
sp. and Azospirillum sp. from the rhizosphere soil and root cuttings of Piper nigrum
L. exhibit high phosphate-solubilizing ability in vitro (Ramachandran et al. 2007).
The phosphate-solubilizing microorganisms found in the rhizosphere of the
selected medicinal plant can be inoculated in the plant rhizosphere which can be
used for increasing the growth of plants (Kidoglu et al. 2007). Bacteria were found
to be more active than fungi in conversion of insoluble phosphorus to soluble
phosphorus (Alam et al. 2002; Safdar et al. 2011). Several publications have
demonstrated that phosphate-solubilizing strains of Bacillus sp. and Pseudomonas
sp. increase growth and phosphorus content of non-leguminous as well as leguminous plants (Antoun et al. 2004; Chabot et al. 1998; Halder et al. 1990). In the
study of Malviya and Singh (2012), phosphate-solubilizing bacteria were isolated
from soil, and their effect on germination of Glycine max seeds as well as seedling
growth was studied with an objective to develop a biofertilizer. Safdar et al. (2011)
conducted an experiment to characterize the phosphate-solubilizing microorganisms (PSM) isolated from the rhizosphere of selected medicinal plants and
their inoculation effect on plant growth and found that phosphate-solubilizing bacteria and fungi constituted 4.14 and 38.2 % of total microbial population, respectively.
6.4.2
Production of Indole-3-Acetic Acid (IAA)
IAA is phytohormone which is known to be involved in root initiation, cell division,
and cell enlargement (Salisbury 1994). The physiologically most active auxin in
plants is indole-3-acetic acid (IAA), which is known to stimulate both rapid (e.g.,
increases in cell elongation) and long-term (e.g., cell division and differentiation)
responses in plants (Gray and Smith 2005). IAA is the most common and best
characterized phytohormone. It has been estimated that 80 % of bacteria isolated
from the rhizosphere can produce plant growth regulator IAA (Patten and Glick
1996; Patten and Glick 2002). In addition to IAA, bacteria such as Paenibacillus
polymyxa and Azospirillum also release other compounds in the rhizosphere, like
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indole-3-butyric acid (IBA), Trp and tryptophol, or indole-3-ethanol (TOL) that can
indirectly contribute to plant growth promotion (Hayat et al. 2010; Lebuhn
et al. 1997; El Khawas and Adachi 1999). Patten and Glick (2002) demonstrated
that bacterial IAA from P. putida played a major role in the development of host
plant root system. Similarly, IAA production in P. fluorescens HP 72 correlated
with suppressing of creeping bent grass brown patch. Patten and Glick (2002) also
showed that bacterial IAA stimulates the development of the host plant root system.
The advantage for root-associated bacteria is a rich supply of nutrients, as much of
the metabolic products of the carbon fixed by plants are lost from roots and move
into the rhizosphere as exudates, lysates, and mucilage (Hayat et al. 2010). Independent of the origin (rhizosphere vs. phyllosphere), bacterial strains produced
IAA, which accounts for the overall synergistic effect on growth of peas and
wheat (Saharan and Nehra 2011). The highest concentration of IAA is produced
by bacterial strain P. fluorescens and Kocuria varians (Egamberdieva 2008). Joseph
et al. (2007) found while working on chickpea that all the isolates of Bacillus,
Pseudomonas, and Azotobacter produced IAA, whereas only 85.7 % of Rhizobium
was able to produce IAA (Joseph et al. 2007). Chaiharn and Lumyong (2011)
successfully screened rhizobacteria for in vitro solubilization of inorganic phosphate, IAA production, and their effects on root elongation of bean and maize
seedlings and found that Klebsiella isolated from rhizosphere was the best IAA
producer and produced the highest amount of IAA (291.97 0.19 ppm) in culture
media supplemented with L-tryptophan. Khamna et al. (2010) isolated Streptomyces sp. from the rhizosphere soils of 14 Thai medicinal plants, which were found
to produce the plant growth hormone indole-3-acetic acid (IAA) in a yeast malt
extract medium supplemented with 2 mg/ml L-tryptophan. However, the effect of
IAA on plants depends on the plant sensitivity to IAA and the amount of IAA
produced from plant-associated bacteria and induction of other phytohormones
(Peck and Kende 1995).
6.4.3
HCN Production
Rhizobacteria can inhibit phytopathogens by the production of hydrogen cyanide
(HCN) and/or fungal cell wall-degrading enzymes, e.g., chitinase and β-1,
3-glucanase (Bloemberg and Lugtenberg 2001; Persello Cartieaux et al. 2003;
Friedlander et al. 1993). HCN is produced by many rhizobacteria and is postulated
to play a role in biological control of pathogens (Defago and Haas 1990). The
cyanide ion is exhaled as HCN and metabolized to a lesser degree into other
compounds (Alizadeh et al. 2013). HCN first inhibits the electron transport, and
the energy supply to the cell is disrupted leading to the death of the organisms. It
inhibits proper functioning of enzymes and natural receptors’ reversible mechanism
of inhibition (Corbett 1974), and it is also known to inhibit the action of cytochrome
oxidase (Gehring et al. 1993). Fluorescent Pseudomonas strain RRS1 isolated from
Rajnigandha (tuberose) produced HCN, and the strain improved seed germination
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and root length (Saxena et al. 1996). HCN from P. fluorescens strain played a
significant role in disease suppression of F. oxysporum f. sp. radicis-lycopersici in
tomato (Duffy et al. 2003). Ramatte et al. (2003) reported that hydrogen cyanide is a
broad-spectrum antimicrobial compound involved in biological control of root
disease by many plant-associated fluorescent pseudomonads. The production of
HCN by certain strains of fluorescent pseudomonads has been involved in the
suppression of soilborne pathogens (Voisard et al. 1989). Suppression of black
root rots of tobacco (Stutz et al. 1986) and consumption of wheat by P. fluorescens
strain CHAO were attributed to the production of HCN (Defago and Haas 1990).
Pseudomonas fluorescens HCN inhibited the mycelial growth of Pythium in vitro
(Weststeijn 1990). Ahmad et al. (2008) explored for efficient PGPR strains with
multiple activities; a total of 72 bacterial isolates belonging to Azotobacter, fluorescent Pseudomonas, Mesorhizobium, and Bacillus were isolated from different
rhizospheric soils where it was found that HCN production was a more common
trait of Pseudomonas (88.89 %) and Bacillus (50 %). However, the role of cyanide
production is contradictory as it may be associated with deleterious as well as
beneficial rhizobacteria (Bakker and Schippers 1987; Alstrom and Burns 1989;
Ahmad et al. 2008).
6.4.4
Siderophore Production
Indirect plant growth promotion includes the prevention of deleterious effects of
phytopathogenic organisms (Schippers et al. 1987; Glick and Pasternak 2003;
Dobbelaere et al. 2003). This can be achieved by the production of siderophores,
i.e., small iron-binding molecules. In soils, iron is found predominately as ferric
ions, a form that cannot be directly assimilated by microorganisms. Siderophore
production enables bacteria to compete with pathogens by removing iron from the
environment (O’Sullivan and O’Gara 1992; Persello Cartieaux et al. 2003).
Siderophore production is very common among Pseudomonas (Kozhevin 1989;
O’Sullivan and O’Gara 1992; Boyer et al. 1999), and Streptomyces sp. has also been
shown to produce iron-chelating compounds (Loper and Buyer 1991). Fluorescent
Pseudomonas are characterized by the production of yellow-green pigments,
termed pyoverdines which fluoresce under UV light and function as siderophores
(Demange et al. 1987; Kloepper et al. 2004). The role of siderophores produced by
fluorescent pseudomonads in plant growth promotion was first reported by
Kloepper et al. (1981). Pseudomonas culture and purified siderophores showed
good antifungal activity against the plant deleterious fungi, viz., Aspergillus niger,
A. flavus, A. oryzae, F. oxysporum, and Sclerotium rolfsii (Manwar et al. 2004).
Though siderophores are part of primary metabolism (iron is an essential element),
on occasions they also behave as antibiotics which are commonly considered to be
secondary metabolites (Haas and Defago 2005). Suryakala et al. (2004) have
reported that siderophores exerted higher impact on Fusarium oxysporum than on
Alternaria sp. and Colletotrichum capsici. Arora et al. (2001) isolated Rhizobium
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meliloti from medicinal plant, Mucuna pruriens, which were able to produce
siderophores that not only act as biocontrol agents against M. phaseolina but also
proved to be plant growth promoter in nature as evidenced in the increase of
seedling biomass and fresh nodule weight over uninoculated controls.
6.4.5
Biocontrol Activity
Most sustainable and environmentally acceptable control may be achieved using
biocontrol agents due to the effort to reduce the use of agrochemicals and their
residues in the environment and in food (Haggag and Abdel-latif 2007). Identifying,
understanding, and utilizing microorganisms or microbial products to control plant
diseases and to enhance crop production are integral parts of sustainable agriculture.
Biological control is a potent means of reducing the damage caused by plant pathogens (Haggag 2002; Jeyarajan and Nakkeeran 2000). Biological control of plant
disease can occur through different mechanisms, which are generally classified as
antibiosis, competition, suppression, direct parasitism, induced resistance,
hypovirulence, and predation (Johnson and Curl 1972; Chaurasia et al. 2005). The
antagonistic activity has often been associated with the production of secondary
metabolites (Haggag and Abdel-latif 2007; Silva et al. 2001). Plant-associated
microorganisms fulfill important functions for plant growth and health. These
rhizospheric microorganisms could be exploited for its innumerable properties and
active metabolites (Tamilarasi et al. 2008). Biological control of plant disease is
defined as “The involvement of the use of beneficial microorganisms, such as
specialized fungi or yeast or bacteria, to attack and control the plant pathogens
(i.e., fungi, bacteria, nematodes, or weeds) and the diseases they are causing” (Fravel
2005). Biocontrol is a potent means of reducing the damage caused by plant
pathogens (Jeyarajan and Nakkeeran 2000). The relationship of PGPR and biocontrol is not only important but also worthwhile. A biocontrol strain should be
able to protect the host plant from pathogens and fulfill the requirement for strong
colonization. Numerous compounds that are toxic to pathogens, such as HCN,
phenazines, pyrrolnitrin, and pyoluteorin, as well as other enzymes, antibiotics,
metabolites, and phytohormones are the means by which PGPR acts, just as quorum
sensing and chemotaxis which are vital for rhizosphere competence and colonization
(Babalola 2010). Mostly Pseudomonas sp. and Bacillus sp. are known for their
antifungal properties; hence, they have great importance in the biological control
of a number of plant diseases (Safdar et al. 2011; Milner et al. 1996; Ryder
et al. 1999). Anith et al. 2004 reported that when PGPR (Pseudomonas putida,
Bacillus pumilus) and Actigard (acibenzolar-S-methyl) applications were combined,
the bacterial wilt incidence caused by R. solanacearum was reduced when compared
to the untreated control. Ahmadzadeh et al. (2004) reported that antagonistic
rhizobacteria more specifically fluorescent pseudomonads and certain Bacillus species possessed the ability to inhibit fungal and bacterial root diseases of agricultural
crops. In vitro evaluation of the P. fluorescens isolates also confirmed their
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antagonistic ability against both Pyricularia grisea and Rhizoctonia solani in dual
culture tests. Numerous rhizosphere organisms are capable of producing compounds
that are toxic to pathogens (plant diseases) (Ahmadzadeh et al. 2004). Bacillus
subtilis is one such commercialized PGPR organism, and it acts against a wide
variety of pathogenic fungi. Boby and Bagyaraj (2003) carried out a field study to
investigate the possibility of controlling the root rot or wilt of medicinal plant,
Coleus forskohlii using three biocontrol agents, viz., Glomus mosseae, Pseudomonas
fluorescens, and Trichoderma viride, singly and in combination, and observed that
Glomus mosseae and Trichoderma viride in combination not only controlled the
disease but also increased the tuber yield and the forskolin content. Some of the
ubiquitous microorganisms can be a significant component of management practices
to achieve sustainable yields. Literature pertaining to the plant growth promotion,
biocontrol activity, and mechanisms of actions of PGPR of medicinal plants is
limited.
The selection and use of PGPR should be done taking into account the adaptation
of the inoculant to a particular plant and soil in the rhizosphere ecosystem, though
the development of effective microbial inoculants remains a major scientific challenge (Richardson 2001). Many researchers suggest that microbial inoculants can
be used as an economic input to increase crop productivity and maintain the
sustainability of soil (Solanki et al. 2011). Though PGPR has a very good potential
in the management of pests and diseases, it cannot be used as cell suspension under
field conditions, and so it should be immobilized in certain carriers and should be
prepared as formulations for easy application, storage, commercialization, and field
use (Nakkeeran et al. 2005). A multipurpose formulation of the screened isolates is
prepared with suitable and available agricultural and industrial waste carriers that
support the survival of bacteria for a considerable length of time. The carrier must
display two fundamental properties; it must support the growth of the target
organism and maintain desired population of inoculant strains over the acceptable
time period. Carriers may be either organic or nonorganic. It should be economical
and easily available and have long shelf life. The carrier should be nearly sterile and
chemically and physically uniform, display high water holding capacity and high
water retention, be suitable for as many bacterial species and strains as possible, and
should support growth and survival. It should be easily manufactured, amendable to
nutrient supplement, nearly neutral pH or easily adjustable, and manageable in the
mixing, curing, and packaging operations. It should be nontoxic, biodegradable,
and nonpolluting and minimize environmental risks such as the dispersal of cells to
the atmosphere or to the groundwater.
Different types of carriers used by various researchers are peat and peat plus
additives, coal and coal with additives (Crawford and Berryhill 1983), clays and
inorganic soil (Kotb and Angle 1986; Chao and Alexander 1984; Smith 1995),
compost made from bagasse (Phipotts 1976), soybean meal (Iswaran et al. 1972),
wheat bran (Jackson et al. 1991), agricultural waste material, plant debris, vermiculite ground rock phosphate, calcium sulfate, polyacrylamide gels, alginate beads,
and synthetic carrier which have been formed by plain lyophilized microbial culture
and oil-dried bacteria (Johnston 1962).
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The rhizobacteria that is isolated from various agroecological zones of the
country based on their bioactivity reflected as control of root and soilborne diseases,
improved soil health, and increased crop yields. Effective rhizobacteria have been
further field tested with success which was chosen based on primary screening
protocols. These effective rhizobacteria are used for making several commercial
formulations, mostly based on dry powder (charcoal, lignite, farmyard manure, etc.)
which are field tested; however, problems of appropriate shelf life and cell viability
are still to be solved (Johri et al. 2003). Bacillus-based products are mostly used
commercially among several PGPR strains. It is mostly used based on bioformulation with plant growth-promoting activity because they produce endospores
which are tolerant to extremes of abiotic environments such as temperature, pH,
pesticides, and fertilizers. Several microbial inoculants have already been successfully commercialized (Sharma et al. 2009a, b; Abbasi et al. 2010), but a specific
biological control strategy for medicinal plants, which are increasingly affected by
different soilborne phytopathogens, has not been available until now (Shrivastava
2003).
The soil factors also have very important effects on the quality and quantity of
genuine regional drug (Ren et al. 2005). Only a small subset of potential microbial
strains could be definitively attributed to phytotherapeutic properties (Janovska
et al. 2003; Pestana-Calsa et al. 2010; Hegde 2007), and their relative contribution
to the recognized valuable bioactivity of medicinal plants is not clear as of yet
(Shrivastava 2003).
6.5
Conclusions
The indigenous plant growth-promoting microorganisms of the medicinal plants
and their inoculation in the plant rhizosphere are very useful in increasing the
growth of plants. The large-scale deforestation of green forest wealth, a renewable
resource, is leading to an accelerated loss of valuable or potentially valuable
biodiversity, extinction of species, and genetic erosion. Hence, alternative and
safe forms of preservation and cultivation of naturally occurring medicinal and
aromatic plants are required which can be carried out by utilizing the indigenous
rhizosphere bacteria of medicinal plants. Indigenous microorganisms of these
medicinal plants also influence the quality and quantity of bioactive constituents
and its potential in agriculture, pharmaceutical, and medicine. It can also influence
the metabolic activity and bioactivity of these medicinal plants. Hence studies are
required for the evaluation of the differences of rhizobacterial diversity and the
bioactive component of medicinal plants among different habitats which will lead
to undermine the relationship between microorganism diversity and the quality of
genuine authentic crude drug.
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6 Plant Growth-Promoting Rhizobacteria (PGPR): Emergence and Future Facets. . .
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mkumar9@amity.edu
Part II
Alleviation Plant Stress
mkumar9@amity.edu
Chapter 7
Alleviation of Abiotic Stress in Medicinal
Plants by PGPR
Sher Muhammad Shahzad, Muhammad Saleem Arif, Muhammad Ashraf,
Muhammad Abid, Muhammad Usman Ghazanfar, Muhammad Riaz,
Tahira Yasmeen, and Muhammad Awais Zahid
7.1
Introduction
Plants have been a fundamental component of human lives in terms of food, fibre
and health since the beginning of human civilisation. The use of medicinal plants
and their derived compounds/metabolites to cure various health ailments has been
in practice across cultures for thousands of years (Crispin and Wurtele 2013).
According to WHO, >80 % of the world’s population in developing countries is
primarily dependent on medicinal plant-derived herbal medicines for basic
healthcare needs (Kamboj 2000). Medicinal plants are known to be rich in secondary metabolites and are potentially useful to produce natural drugs (Briskin 2000;
Goldman 2001). The use of herbal medicines in developed countries has also
gained popularity in last few years (Sahoo et al. 2010). Identifiable characteristic
attributes involving antimicrobial (Taye et al. 2011), antioxidant (Thambiraj
et al. 2012) and nutraceutical (Royer et al. 2013) properties of these plants make
them a suitable alternative medicine. These plant bioagents control or prevent a
S.M. Shahzad (*) • M. Ashraf
Department of Soil and Environmental Sciences, University College of Agriculture, University
of Sargodha, Sargodha, Pakistan
e-mail: smshahzad_uaf@yahoo.com
M.S. Arif • M. Riaz • T. Yasmeen
Department of Environmental Sciences and Engineering, GC University Faisalabad,
Faisalabad, Pakistan
e-mail: msarif@outlook.com
M. Abid
Department of Soil and Environmental Sciences, Bahauddin Zakariya University, Multan,
Pakistan
M.U. Ghazanfar • M.A. Zahid
Department of Plant Pathology, University College of Agriculture, University of Sargodha,
Sargodha, Pakistan
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_7
mkumar9@amity.edu
135
136
S.M. Shahzad et al.
number of diseases in both human being and livestock (Table 7.1). The growth and
productivity of medicinal plants are adversely affected by several biotic and abiotic
constraints. These plants are frequently exposed to various stress factors such as
salt, drought, low temperature, flooding, heat, oxidative and heavy metal stress
(Kirakosyan et al. 2003; Ben Taarit et al. 2012; Ahmad et al. 2013; Flora
et al. 2013). Plants subjected to various abiotic stress conditions undergo different
physiological and biochemical changes leading to numerous modifications in the
structure and functions of cell membranes (Ben Taarit et al. 2010). Prevailing stress
factor is capable to induce changes in plant metabolism by affecting plant growth,
metabolite synthesis and their qualitative and quantitative composition to a great
extent (Ksouri et al. 2007). Several studies have confirmed the negative/positive
effect on medicinal plants exposed to various abiotic stress factors (Table 7.2).
In the present chapter, we aim to give an overview about the role of PGPR in a
biotic stress alleviation of medicinal plants against different types of stress factors.
7.2
Plant Growth-Promoting Rhizobacteria
The plant rhizosphere is a zone of intense microbial activity and ecological significance where numerous microorganisms colonise in, on and around the roots of
growing plants. The diverse groups of bacteria are associated with the root systems
of all higher plants (Khalid et al. 2006). These bacteria are considered as efficient
microbial competitors in the root zone, and the net effect of plant–microbe associations on plant growth could be positive, neutral or negative (Kennedy 2005;
Nadeem et al. 2006; Patel et al. 2008; Khalid et al. 2009; Shahzad et al. 2014).
Bacteria having close proximity with plant roots through aggressive colonisation
and capable of stimulating plant growth by any mechanism(s) of action are referred
to as plant growth-promoting rhizobacteria (PGPR) (Kloepper et al. 1986; Arshad
and Frankenberger 1998; Kremer 2006; Böhm et al. 2007; Shahzad et al. 2013).
The plant growth-promoting rhizobacteria are characterised by the following
inherent distinctivenesses: (a) they must be proficient to colonise the root surface;
(b) they must survive, multiply and compete with other microorganisms, at least for
the time needed to express their protection activities; and (c) they must promote
plant growth (Kloepper 1994; Ahemada and Kibret 2014). Nearly about 2–5 % of
rhizobacteria, when reintroduced by plant inoculation in a soil containing competitive microorganisms, exert a beneficial effect on plant growth and are known as
plant growth-promoting rhizobacteria (Kloepper and Schroth 1978; Antoun and
Kloepper 2001). As shown by Vessey (2003), soil bacterial species burgeoning in
plant rhizosphere which grow in, on or around plant tissues stimulate plant growth
by a plethora of mechanisms collectively known as PGPR. Alternatively, Somers
et al. (2004) classified PGPR based on their functional activities as (1) biofertilisers
(increasing the availability of nutrients to plant), (2) phytostimulators (plant growth
promotion, generally through phytohormones), (3) rhizoremediators (degrading
organic pollutants) and (4) biopesticides (controlling diseases, mainly by the
mkumar9@amity.edu
mkumar9@amity.edu
Common name
Botanical name
Family
Part used
Medicinal use
References
Amla (T)
Emblica
officinalis
Euphorbiaceae
Fruit
Vitamin C, cough, diabetes, cold, hyperacidity, laxative, prevention of cancer
Anantamool
(S)/Indian Sarap
sarilla
Ashok (T)
Hemidesmus
indicus
Asclepiadaceae
Root/leaf
Appetiser, carminative, aphrodisiac,
astringent, wound healing
Jacob et al. (1988), Saeed and Tariq
(2007), Yokozawa et al. (2007),
Baliga and Dsouza (2011)
Deeb et al. (2010), Ganesan
et al. (2012)
Saraca asoca
Caesalpiniaceae
Bark, flower
Ashwagandha
(H)
Withania
somnifera
Solanaceae
Roots,
leaves
Bach (H)
Sweet flag
Bael/bilva (T)
Acorus
calamus
Aegle
marmelos
Araceae
Rhizome
Rutaceae
Fruit, bark
Diabetes disorder, menstrual pain, uterine
problems
Restorative tonic, stress, nerves disorder,
aphrodisiac, regulation of reproductive
hormone
Antifungal, sedative, analgesic, epilepsy,
hypertensive, antimutagenic
Diarrhoea, dysentery, constipation
Bahada (T)
Terminalia
bellirica
Vetiveria
zizanioides
Phyllanthus
amarus
Stachytarpheta
cayennensis
Bacopa
monnieri
Combretaceae
Seed, bark
Poaceae/
Gramineae
Euphorbiaceae
Root
Whole plant
Verbenaceae
Whole plant
Scrophulariaceae
Whole plant
Benachar
(S) Khus/khus
Bhumi amla (H)
Blue snakeweed
(P)
Brahmi (H)
Cough, insomnia, dropsy, vomiting, ulcer,
triphala
Hyperdipsia, burning, ulcer, skin,
vomiting
Anaemic, jaundice, dropsy
Remedy for dysentery, syphilis,
gonorrhoea and catarrhal conditions
Nervous disorder, memory enhancer,
mental disorder
Cowen (1984), Varghese
et al. (1992), Pradhan et al. (2009)
Bucci (2000), Scartezzini and
Speroni (2000), Ahmad et al. (2010),
Pandit et al. (2013)
Ghosh (2006), Jabbar and Hassan
(2010)
Sharma et al. (1981), Pattnaik
et al. (1996), Brijesh et al. (2009),
Pallaty et al. (2011)
Sabu and Ramadasan (2002), Kumar
et al. (2010)
Singh et al. (1978), Thakur
et al. (1989)
Calixto et al. (1984), Nishiura
et al. (2004), Patel et al. (2011)
Gills (1992)
137
Singh and Dhawan (1997), Khare
(2003), Allan et al. (2007), Rastogi
et al. (2012), Aguiar and Borowski
(2013)
(continued)
7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
Table 7.1 Medicinal plant and their uses against different diseases of human being and animals
Common name
Kalahari/glory
lily (H)
Chirata (high
altitude) (H)
Botanical name
Gloriosa
superba
Swertia chirata
Coat buttons/
tridax daisy (P)
Dalchini (S)
mkumar9@amity.edu
Fireplant (Mexico) (T)
Fringed spider
flower (H)
Goatweed (T)
138
Table 7.1 (continued)
Family
Liliaceae
Part used
Seed, tuber
Gentianaceae
Whole plant
Tridax
procumbens
Asteraceae
Whole plant
Cinnamomum
zeylanicum
Euphorbia
heterophylla
Cleome
rutidosperma
S. dulcis
Lauraceae
Bark, oil
Euphorbiaceae
Root, leaves
Capparaceae
Leaves
Scrophulariaceae
Whole plant
Tribulus
terrestris
Zygophyllaceae
Whole plant
Aloe vera
Liliaceae
Leaves
Gudmar/
madhunasini (C)
Gymnema
sylvestre
Asclepiadaceae
Leaves
Guggul (T)
Commiphora
wightii
Burseraceae
Gum resin
Treatment of diarrhoea; stops bleeding,
malaria and stomachache; antidiabetic;
antiarthritic
Bronchitis, asthma, cardiac disorder,
fever
For erysipelas, cough, bronchial, paroxysmal asthma, hay fever, catarrh
Ear cure for inflammation, anthelmintic
and carminative
Antiviral, inhibitory and antitumour
activity; cough, chest pains and sore
throat; gonorrhoea
Sweet, cooling, aphrodisiac, appetiser,
digestive, urinary
Laxative, wound healing, skin burns,
ulcer
Diabetes, hydrocele, asthma
Rheumatism, arthritis, paralysis, laxative,
hyperlipidaemia
References
Duke (1985), Pawar and Nabar
(2010)
Natarajan et al. (1974), Ray
et al. (1996), Saha et al. (2005),
Tabassum et al. (2012)
Holm et al. (1997), Bhagwat
et al. (2008), Petchi et al. (2013)
Baratta et al. (1998), Gruenwald
et al. (2010)
Edeoga and Gomina (2001), Holm
et al. (1997), Gills (1992)
Burkill (1984), Gills (1992)
Hayashi et al. (1993), Gills (1992)
Tomova et al. (1979), Brown
et al. (2000), Gauthaman and
Ganesan (2008)
Maenthaisong et al. (2007), Eshun
and He (2004)
Sinsheimer et al. (1970), Baskaran
et al. (1990), Persaud et al. (1999),
Luo et al. (2001), Ramachandran
et al. (2003)
Szapary et al. (2003), Sahni
et al. (2005), Siddiqui and Mazumder
(2012)
S.M. Shahzad et al.
Gokhur
(H) crawling
puncture vine
Ghritkumari (H)
Medicinal use
Skin diseases, labour pain, abortion, general debility
Skin disease, burning sensation, antimalarial, antiamoebic, fever
Tinospora
cordifolia
Erica coccinea
Harida (T)
Terminalia
chebula
Lawsonia
inermis
S. anthelmia
mkumar9@amity.edu
Henna/mehandi
(S)
Indian pink/
water weed (H)
Kaincha/creeper
baidanka
Kalmegh/Bhui
neem (H)
Kantakari/
akranti perennial (H)
Kochila (T)
Kurai (S)
Long pepper/
pippali (C)
Makoi
(H) Kakamachi
Mandukaparni
(H)
Indian
pennywort
Mucuna
pruriens
Andrographis
paniculata
Solanum
xanthocarpum
Menispermaceae
Stem
Asteraceae
Whole plant
Combretaceae
Seed
Lythraceae
Leaf,
flower, seed
Root, bark,
leaves
Root, hair,
seed, leaf
Whole plant
Loganiaceae
Fabaceae
Acanthaceae
Solanaceae
Strychnos
nux-vomica
Holarrhena
antidysenterica
Piper longum
Loganiaceae
Whole
plant, fruit,
seed
Seed
Apocynaceae
Bark, seed
Piperaceae
Fruit, root
Solanum
nigrum
Centella
asiatica
Solanaceae
Fruit/whole
plant
Whole plant
Umbelliferae
Gout, pile, general debility, fever, jaundice, anti-tuberculosis
Treatment of fever and convulsions in
children, ulcer, craw-craw, ringworm
Anti-mutagenic, triphala, wound, ulcer,
leprosy, inflammation, cough
Burning, steam, anti-inflammatory,
reduce the secretion of sweat
Worm expeller
Singh et al. (2003), Badar
et al. (2005)
Burkill (1984)
Grover and Bala (1992), Carounanidi
et al. (2007)
Stulberg et al. (2002), Stante
et al. (2006)
Gills (1992)
Nervous disorder, constipation, nephropathy, strangury and dropsy
Fever, weakness, release of gas, antiinflammatory
Diuretic, anti-inflammatory, appetiser,
stomachic
Iauk et al. (1993), Amin et al. (1996),
Salau and Odeleye (2007)
Coon and Ernst (2004), Sheeja
et al. (2006), Mishra et al. (2007)
Patel et al. (2012)
Nervous disorder, paralysis, healing
wound
Scabies, antipyretic, amoebic dysentery
McIntosh (1940), Neetu et al. (2013)
Appetiser, enlarged spleen, bronchitis,
cold, antidote
Dropsy, general debility, diuretic,
antidysenteric, antitumour
Anti-inflammatory, jaundice, diuretic,
diarrhoea, anticancer, antiulcer
Gilani et al. (2010), Mehmood
et al. (2011)
Pathak et al. (2010), Kumar
et al. (2011)
Aslanov (1971), Jian et al. (2008)
7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
Guluchi/giloe
(C)
Hangertjie (S)
Nanasombat and Teckchuen (2009),
Abdulla et al. (2010)
139
(continued)
Common name
Nageswar
(T) Nag
Champa
Neem (T)
Pashan bheda
mkumar9@amity.edu
Pashan bheda/
Patharchur (H)
Peppermint
(H) perennial
Rakta chitrak
(H)
Sada Bahar
(H) periwinkle/
nayantara
Sandalwood (T)
Sarpagandha
(H)
Shatavari (C)
Sweet chitrak
Perennial (H)
Botanical name
Mesua ferrea
Family
Guttiferae
Part used
Bark, leaf,
flower
Medicinal use
Asthma, antimicrobial, skin, burning,
vomiting, dysentery, piles
References
Banerjee et al. (1993), Hemalatha
et al. (2013)
1x(111)
Azadirachta
indica
Coleus
barbatus
Coleus
barbatus
Mentha
piperita
Plumbago
indica
Vinca rosea/
Catharanthus
roseus
Santalum
album
Rauvolfia
serpentina
Asparagus
racemosus
Cassia
angustifolia
Plumbago
zeylanica
Meliaceae
Rhizome
Sedative, analgesic, epilepsy,
hypertensive
Rahim et al. (2010), Kumar and
Navaratnam (2013)
Lamiaceae
Root
Kidney stone, diabetes
Lamiaceae
Root
Kidney stone, calculus
Lamiaceae
Digestive, painkiller
Plumbaginaceae
Leaves,
flower, oil
Rootbar
Apocynaceae
Whole plant
Leukaemia, hypotensive, antispasmodic,
antidote
Day (1998), Bnouham et al. (2002),
Porfı́rio et al. (2010)
Valdes et al. (1987), Porfı́rio
et al. (2010)
McKay and Blumberg (2006),
Cappello et al. (2007)
Figueriedo et al. (2003), Vijayakumar
et al. (2006), Eldhose et al. (2013)
Singh et al. (2001), Prajakta and
Ghosh (2010)
Santalaceae
Apocynaceae
Heartwood,
oil
Root
Skin disorder, burning sensation, jaundice, cough
Hypertension, insomnia
Liliaceae
Tuber, root
Liliaceae
Dry tubers
Plumbaginaceae
Root,
rootbar
Enhance lactation, general weakness,
fatigue, cough, insulin enhancer
Rheumatism, general debility tonic,
aphrodisiac
Appetiser, antibacterial, anticancer,
antifertility
Dyspepsia, colic, inflammation, cough
Edeoga et al. (2005), Misra and Dey
(2012)
Obdoni and Ochuko (2001), Edeoga
et al. (2005)
Mathews et al. (2006), Hannan
et al. (2007)
Duncan (1957), Spiller et al. (2003)
Vijayakumar et al. (2006), Annan
et al. (2009), Vishnukanta and Rana
(2010)
S.M. Shahzad et al.
Senna (S)
140
Table 7.1 (continued)
Ocimum
sanctum
Embelia ribes
Vasa (S)
Adhatoda
vasica
Vringraj (H)
White
eye/Brazil
pusley (P)
Wireweed (S)
Lamiaceae
Leaves/seed
Myrsinaceae
Acanthaceae
Root, fruit,
leaves
Whole plant
Eclipta alba
Richardia
brasiliensis
Compositae
Rubiaceae
Seed/whole
Whole plant
Anti-inflammatory, digestive, hair tonic
Cure for eczema, treatment of boils,
active cure against avian malaria
S. acuta
Malvaceae
Whole plant
Stops bleeding, sores and wounds,
antipyretic
T Tree, H Herb, C Climber, S Shrub, P Flowering plant
Cough, cold, bronchitis, expectorant,
anticancer
Skin disease, helminthiasis,
cardioprotective, snake bite
Antispasmodic, antiulcer respiratory,
stimulant
Gupta et al. (2003), Baliga
et al. (2013)
Warrier et al. (1995), Suanarunsawat
et al. (2010)
Vinothapooshan and Sundar (2011),
Sheeba and Mohan (2012), Kumar
et al. (2013)
Franca et al. (1995), Roy et al. (2008)
Burkill (1994), Edeoga et al. (2005)
Egunjiobi (1969)
7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
mkumar9@amity.edu
Tulsi
(perennial)
Vai Vidanka (C)
141
142
Table 7.2 Effect of different abiotic stress factors on therapeutic properties of medicinal plants
Medicinal
plant
mkumar9@amity.edu
Plant part
Medicinal use
Stress factor
Impact on plant
Reference
Bunium
persicumi
Fruit,
leaves,
bark and
roots
Gastroesophageal reflux disease and
heartburn, promote to weight loss, kill
cancer cell and treat bronchitis,
antibacterial and antifungal activity
Drought stress
Saeidnejad et al. (2013)
Datura
stramonium
Leaves,
powder of
seeds
Effective for asthma, analgesic during
surgery, stimulation of the urinary
tract, respiratory tract
Drought stress
Emblica
officinalis
Fruit,
leaves,
roots
Vitamin C, cough, diabetes, cold,
hyperacidity, antibacterial, prevention of cancer, norovirus infection,
laxative
Salt stress
Aloe vera (L.)
Burm.f
Leaf parts
Heavy frost or
snow, salt
stress
Azadirachta
indica
Leaves,
fruits,
bark, roots
Analgesic, wound healing, immune
modulating, antitumour activities as
well as antibacterial, antifungal and
antiviral properties. Its juice lowers
cholesterol and diabetic effects
Diabetes mellitus, antihyperglycaemic action, antiviral,
antibacterial, antifungal, antiinflammatory, antipyretic, antiseptic
and antiparalitic uses
Due to water stress, essential oil yield
(terpinen-4-ol, β-sesquiphellandrene,
bornyl acetate) was significantly
decreased, while contents of limonene
and proline increased
Scopolamine N-oxide 17–20,
hydroxy hyoscyamine was significantly reduced, and activation of
phenylalanine ammonia-lyase in
plants is increased by abiotic stresses
Salt stress increased the phenolics and
ascorbic acid while decreased the
1-diphenyl-2-picryl hydrazyl. Similarly some amino acids decreased and
increased as a result of salt stress to
plant
Amino acids, anthraquinones,
enzymes, minerals, vitamins, lignins,
monosaccharide, polysaccharides,
salicylic acid, saponins and sterols
Nimbanene, 6-desacetylnimbinene,
nimbandiol, ascorbic acid,
n-hexacosanol, amino acid,
7-desacetyl-7-benzoylazadiradione,
7-desacetyl-7-benzoyl-gedunin,
17-hydroxy-azadiradione and nimbiol
Sheteawi et al. (2001),
Nema et al. (2013)
Biswas et al. (2002),
Ghosh et al. (2009),
Lucantoni et al. (2010)
S.M. Shahzad et al.
Salt stress,
heavy metal
stress
Das et al. (2012), Gaire
and Subedi (2013), Da
Silva et al. (2012)
Roots,
leaves
Restorative tonic, nerves disorder,
aphrodisiac, regulation of reproductive hormone
Salt stress
(NaCl and
CaCl2)
Catharanthus
roseus
Shoot,
leaves,
flowers
Diabetes, malaria, leukaemia and
Hodgkin’s lymphoma
Water-deficit
environments
with or without CaCl2
Arachis
hypogaea
Fruit, oil,
peanut
powder
Reducing the risk of heart disease,
without adding to body weight. Regular peanut use increases serum Mg
concentrations
Salt stress,
water stress
Moringa
oleifera Lam
Leaves,
stem bark,
roots
Salt and
drought stress
Santalum
album
Leaves,
bark, oil
Fevers, bronchitis, eye and ear infections, headaches, gastric ulcers, diarrhoea, cardiac and circulatory
stimulants, antitumour, antipyretic,
cholesterol lowering, antidiabetic,
antibacterial and antifungal activities
Bronchitis, antiulcer, skin disorders,
fever, infection of the urinary tract,
mouth, pharynx, liver and gallbladder
complaints
Salt stress
The NaCl with CaCl2-treated plants
increased total chlorophyll content
and proline oxidase activity and
decreased the γ-glutamyl kinase
activity in all plant parts compared to
NaCl-treated plant
Drought with CaCl2-treated plants
showed an increase in total indole
alkaloid content in shoots and roots
than drought-stressed and wellwatered plants
Results showed that shoot dry matter,
relative water content, chlorophyll
and K+ decreased significantly with
salinity, while Na+, H2O2 and proline
increased with salinity level
Due to salinity and drought, stress
severely limits plant growth, yield
and oil content mainly in semiarid
regions around the world
Significant decrease in growth attributes was observed while interestingly increase in some amino acids
and proline content under stress
conditions
Jaleel and Azooz (2009)
Jaleel et al. (2007)
Hossain et al. (2011)
Silveira et al. (2003),
Hussein and Abou-Baker
(2014)
7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
mkumar9@amity.edu
Withania
somnifera
Sindhu et al. (2010),
Swamy and Prasad
(2012)
143
144
S.M. Shahzad et al.
production of antibiotics and antifungal metabolites) (Antoun and Prévost 2005).
Furthermore, in most studied cases, a single PGPR will often reveal multiple modes
of action including biological control (Kloepper 2003; Vessey 2003; Nadeem
et al. 2013). Furthermore, Gray and Smith (2005) have recently shown that the
PGPR associations range in the degree of bacterial proximity to the root and
intimacy of association. In general, these can be separated into extracellular plant
growth-promoting rhizobacteria (ePGPR), existing in the rhizosphere, on the rhizoplane or in the spaces between cells of the root cortex, and intracellular plant
growth-promoting rhizobacteria (iPGPR), which exist inside root cells, generally in
specialised nodular structures (Figueiredo et al. 2011; Sundaramoorthy and
Balabaskar 2012). Some examples of ePGPR are like Agrobacterium, Arthrobacter,
Azotobacter, Azospirillum, Bacillus, Burkholderia, Pseudomonas, Serratia, etc.
Similarly, some examples of the iPGPR are Azorhizobium, Bradyrhizobium,
Mesorhizobium and Rhizobium of the family Rhizobiaceae (Bhattacharyya and
Jha 2012).
7.2.1
Growth-Promoting Mechanisms of PGPR
Investigations into the nature and types of association exhibited by different plant
beneficial microorganisms have so far indicated that these interactions may be
beneficial, harmful or neutral for the host plant. Bacteria that facilitate plant growth
may do so either by binding to exterior plant surface such as roots (rhizosphere) or
leaves (phyllosphere), or they may inhabit the interior surfaces of the plant forming
endophytic relationship (Dey et al. 2004; Yadav et al. 2005; Duan et al. 2013). In
general, the mechanisms involved in plant growth promotion by PGPR include
associative nitrogen fixation, lowering of ethylene levels, production of
siderophores and phytohormones, induction of pathogen resistance, solubilisation
of nutrients, promotion of mycorrhizal functioning and decreasing pollutant toxicity (Fig. 7.1) (Glick et al. 1999). Moreover, interaction of specific bacterium to
facilitate plant growth might be either direct or indirect depending upon growthpromoting traits exhibited by the bacterium (Castro et al. 2009).
Direct stimulation includes biological nitrogen fixation, producing phytohormones like auxins, cytokinins and gibberellins, solubilising minerals like phosphorus and iron, production of siderophores and enzymes and induction of systemic
resistance, while indirect stimulation is basically related to biocontrol (Table 7.3),
including antibiotic production, chelation of available Fe in the rhizosphere, synthesis of extracellular enzymes to hydrolyze the fungal cell wall and competition
for niches within the rhizosphere (Zahir et al. 2004).
PGPR strains, especially, Pseudomonas fluorescens and Bacillus subtilis are the
best noted for PGPR-mediated indirect plant growth stimulations (Damayanti
et al. 2007). Besides nitrogen transformation, increasing bioavailability of phosphate, iron acquisition, exhibition of specific enzymatic activity and plant protection from harmful pathogens with the production of antibiotics can also
mkumar9@amity.edu
7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
145
Fig. 7.1 Mechanisms used by PGPR to promote plant growth under abiotic stresses
successfully improve the quality of crops in agriculture (Spaepen et al. 2007). Thus,
based on their mechanism of action, PGPR can be categorised into three general
forms such as biofertiliser, phytostimulator and biopesticide (Fig. 7.2).
The phenomenon of quorum regulation can affect the expression of each of these
traits as PGPR are reported for their regular interactions with the resident microbial
community in rhizosphere (Lugtenberg and Kamilova 2009). Recent investigations
on PGPR revealed that it can promote plant growth mainly by following means:
(1) producing ACC deaminase to reduce the level of ethylene in the roots of
developing plants (Dey et al. 2004); (2) producing plant growth regulators like
indole-acetic acid (Mishra et al. 2010), gibberellic acid (Narula et al. 2006), cytokinins (Castro et al. 2008) and ethylene (Saleem et al. 2007); (3) a symbiotic
nitrogen fixation (Ardakani et al. 2010); (4) exhibition of antagonistic activity
against phytopathogenic microorganisms by producing siderophores,
b-1,3-glucanase, chitinases, antibiotics, fluorescent pigment and cyanide (Pathma
et al. 2011); and (5) solubilisation of mineral phosphates and other nutrients (Hayat
et al. 2010). PGPR may use more than one of these mechanisms to enhance plant
growth as experimental evidence suggests that the plant growth stimulation is the
net result of multiple mechanisms that may be activated simultaneously (Martı́nezViveros et al. 2010). Recently, biochemical and molecular approaches are providing new insight into the genetic basis of these biosynthetic pathways, their regulation and significance as biological tool (Joshi and Bhatt 2011). However, to be more
effective in the rhizosphere, PGPR must maintain a critical population density for a
longer period, although inoculation of plants with PGPR can temporarily enhance
the population size. Although researchers have reported both direct and indirect
ways of growth promotion by PGPR, there is no clear separation between these two
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146
Table 7.3 Biocontrol of fungal plant pathogen on medicinal plants through application of PGPR
Medicinal plant
Plant pathogen
Biocontrol agent
Mode of action
Reference
Launaea nudicaulis
(Bold-leaf Launaea)
Macrophomina phaseolina, Fusarium solani and Fusarium
oxysporum
Pythium ultimum
Thielaviopsis basicola
Rhizoctonia solani, Pythium
ultimum
Pythium debaryanum
Pseudomonas aeruginosa
Siderophores, HCN, diacetyl
phloroglucinol, chitinase activity,
lytic enzyme production
Diacetyl phloroglucinol, pyrrolnitrin
production
Viscosinamide, pyoluteorin, HCN
Mansoor
et al. (2007)
Beta vulgaris (sugar
beet)
Beta vulgaris (sugar
beet)
Capsicum annuum
(chilli)
mkumar9@amity.edu
Corynespora cassiicola (Berk and
Curt) Wei
Persea americana
Mill (avocado)
Rosellinia necatrix
Piper nigrum (black
pepper)
Phytophthora capsici and
Colletotrichum acutatum
Jerusalem artichoke
(sunchoke)
Aspergillus tamari (M10), Fusarium solani (M9) and Aspergillus
fumigatus (M2)
Alternaria tenuissima
Pseudomonas fluorescens
Bacillus subtilis (BSCBE4), Pseudomonas chlororaphis (PA23),
P. fluorescens (ENPF1)
Pseudomonas fluorescens isolates
(Q16, B25 and PS2)
Pseudomonas chlororaphis
PCL1606 and Bacillus subtilis
CB115
P. otitidis (YJR27), P. putida
(YJR92),Tsukamurella
tyrosinosolvens (YJR102) and
Novosphingobium capsulatum
(YJR107)
Pseudomonas spp. strain JK2
Production of siderophore, IAA,
HCN, phosphate solubilisation, NH3
and catalase
Produced both hydroxamate and
carboxylate types of siderophores
Producing phenazines is the secondary metabolites, siderophore, IAA,
HCN
Diacetyl phloroglucinol, pyrrolnitrin,
siderophores, kanosamine
ACC-deaminase, pyrrolnitrin,
siderophores, HCN, ACC-deaminase
activity
Pyoluteorin, pyrrolnitrin,
2,4-diacetylphloroglucinol and HCN
Shanahan
et al. (1992)
Nielsen
et al. (1998)
Ramyasmruthi
et al. (2012)
Mathiyazhagan
et al. (2004)
Jošić
et al. (2012)
GonzálezSáncheza
et al. (2013)
Sang
et al. (2013)
Jina
et al. (2013)
S.M. Shahzad et al.
Phyllanthus amarus
(Bahupatra,
Sanskrit)
Cynara cardunculus
L. (cardoon)
Pseudomonas sp.
Pseudomonas fluorescens (CHAO)
Pseudomonas fluorescens
Seiridium cardinale
Pseudomonas chlororaphis subsp.
aureofaciens strain M71
Production of phenazine-1-carboxylic acid, HCN, chitinase activity
Raioa
et al. (2011)
Fusarium oxysporum,
Macrophomina phaseolina, Aspergillus versicolor and Aspergillus
nidulans
Fusarium chlamydosporum (Frag.
and Cif.) and Ralstonia
solanacearum (Smith)
Pseudomonas putida MSC1 and
Pseudomonas pseudoalcaligenes
MSC4
Saraf
et al. (2013)
Solanum melongena
(brinjal)
Ralstonia solanacearum
Pseudomonas fluorescens
Antibiotic production—pyoluteorin,
pyrrolnitrin,
2,4-diacetylphloroglucinol and
HCN, siderophores
HCN, siderophores,
2-hydroxyphenazine, protease activity, chitinase activity, L-phenylalanine arylamidase, L-lysine
arylamidase
2,4-Diacetylphloroglucinol, HCN,
siderophores, antifungal activity
Panax
quinquefolius
(panax ginseng)
Coffea arabica
L. and Coffea
robusta L. (coffee)
Fusarium cf. incarnatum
Bacillus species
Hemileia vastatrix Berk
Bacillus lentimorbus Dutky and
Bacillus cereus Frank
Coleus forskohlii
(Makandi, Sanskrit)
Pseudomonas monteilii
mkumar9@amity.edu
Pyrrolnitrin, HCN, siderophores,
chitinase activity,
exopolysaccharides
Pyrrolnitrin, HCN, bacillomycin,
siderophores, antifungal activity
Singh
et al. (2012)
Chakravarty
and Kalita
(2012)
Song
et al. (2014)
Shiomi
et al. (2006)
7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
Cupressus
sempervirens (Italian cypress)
Jatropha curcas
L. (Barbados nut,
black vomit nut)
147
148
S.M. Shahzad et al.
Fig. 7.2 PGPR are categorised into three groups on the basis of their mechanism of action
mechanisms. Some bacteria possess multiple traits to promote plant growth where
one trait may dominate the other one (Hafeez et al. 2004; Shaharoona et al. 2008). A
bacterium influencing the plant growth by regulating synthesis of plant hormones
can also play a role in controlling plant pathogens and diseases (Fig. 7.3) and, vice
versa, barriers to the introduction of crop plants into areas that are not suitable for
crop cultivation. Drought, salinity, flooding, low temperature, air pollution and
heavy metals are key sources of abiotic stress. Depending upon the crop plant
exposed to an array of abiotic stress factors, losses in yield and its associated
attributes can range from 50 to 82 % (Kang et al. 2014). In semiarid and arid
regions of the world, crop yield is limited by increase salinisation of irrigation water
as well as soil. Under high salinity, plants exhibit a reduced leaf growth rate due to
decreased water uptake, which restricts photosynthetic capacity. Plant undergoes a
number of metabolic and physiological changes in response to salt stress and water
deficiency (drought) (Han and Lee 2005; Krasensky and Jonak 2012).
Numerous soil beneficial bacteria exhibited strong growth adaptation potential
under stressful condition. The long-term goal of improving plant–microbe interactions for salinity-affected fields and crop productivity can be met with an understanding of the mechanism of osmoadaptation in Azospirillum sp. The synthesis and
activity of nitrogenases in A. brasilense is inhibited by salinity stress (Tripathi
et al. 2002; Boojar 2009). Tripathi et al. (2002) documented that in Azospirillum
sp. there is an accumulation of compatible solutes such as glutamate, proline,
glycine betaine and trehalose in response to salinity/osmolarity; proline plays a
mkumar9@amity.edu
7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
149
Fig. 7.3 An overview of plant-protection mechanisms in biocontrol agents against soil-borne
phytopathogens
major role in osmoadaptation through increase in osmotic stress that shifts the
dominant osmolyte from glutamate to proline in A. brasilense. Azospirillum-inoculated sorghum plants had more water content, higher water potential and lower
canopy temperature in their foliage. Hence, they were less drought-stressed over
uninoculated plants (Table 7.4).
The PGPR containing ACC deaminase can lower the impact of various environmental stresses such as flooding, heavy metals, soil-borne phytopathogens
(Fig. 7.3), drought and high salt on host plant.
The phytohormone ethylene, which is found in all higher plants, is an important
regulator of plant growth and development both under normal and stress conditions.
However, overproduction of ethylene under stressful conditions can result in the
inhibition of plant growth or death, especially in young plant seedlings. PGPR that
express ACC deaminase can hydrolyze ACC, the immediate precursor of ethylene,
to ά-ketobutyrate and ammonia and in this way promote plant growth by regulating
ethylene production in plant. Inoculation of ACC deaminase-containing PGPR in
association with plants subjected to a wide range of abiotic stresses results in
enhanced plant tolerance against exposed stressors (Stepien and Klobus 2005;
Greenberg et al. 2006; Khalid et al. 2006; Shahzad et al. 2014).
PGPR can exert positive effects on seedling vigour and plant productivity under
stress conditions. Seed inoculations with PGPR in asparagus (Asparagus officinalis L.)
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150
Table 7.4 Effectiveness of PGPR for growth promotion of medicinal plants under stress conditions
mkumar9@amity.edu
Medicinal
plant
Type of
stress
Bacterial inoculate
PGPR attributes
Response
Reference
Silybum
marianum
(milk thistle)
Ociumum
basilicm
L. (basil)
Salt
Pseudomonas extremorientalis
TSAU20
Azospirillum brasilense
Significantly increased the root
length, shoot length and total
biomass of plant
Significant increase in dry biomass and chlorophyll content
was observed over control
Egamberdieva
et al. (2013)
Drought
Ociumum
basilicm
L. (basil)
Water stress
Pseudomonades sp., Bacillus
lentus, Azospirillum brasilense, a
combination of three bacterial
species
Auxin production,
exopolysaccharide, biofilm
formation
Siderophores of production,
P-solubilisation and other
nutrients, regulation of ethylene biosynthesis
ACC-deaminase activity, production of HCN, siderophore,
chitinase, IAA production and
P-solubilisation
Trigonella
foenumgraecum
L. (fenugreek)
Arachis
hypogaea
(groundnut)
Drought
Azotobacter chroococcum
Phosphate solubilisation,
exopolysaccharide production,
indole-acetic acid
Salt
Pseudomonas fluorescens TDK1,
Pseudomonas fluorescens PF2
and Pseudomonas fluorescens
RMD1
By lowering ethylene production, auxin production,
exopolysaccharide
Arachis
hypogaea
(groundnut)
Salt
Bacillus licheniformis A2
Production of NH3,
siderophore, chitinase and
HCN and assessment of their
antifungal activity, IAA production and P-solubilisation
Inoculation of rhizobacteria
showed significant increase in
antioxidant and photosynthetic
pigments, catalase activity in
basil plants under water stress
Improving significantly root
and shoot biomass and uptake
of nutrients
Heidaria and
Golpayegani
(2012)
Tank and Saraf
(2003)
Saravanakumar
and
Samiyappan
(2007)
Nautiyal
et al. (2013)
S.M. Shahzad et al.
Increasing salt tolerance of
Arachis hypogaea. The impact
of strains was variable and
P. fluorescens TDK1 proved to
be most effective than other
ones
Showed increase in fresh biomass, total length and root
length over respective control
Heidari
et al. (2011)
Drying soil
Bacillus spp.
Lactuca sativa
L. (lettuce)
Salts
Azospirillum
Brassica napus
(rapsi)
Heavy
metals
Brassica
oxyrrhina
(smooth-stem
turnip)
Ocimum
basilicum
(sweet basil)
Heavy
metals
Pseudomonas tolaasii
ACC23, P. fluorescens ACC9,
Alcaligenes sp. ZN4, Mycobacterium sp. ACC14
Bacillus cereus SRA10
Indole-acetic acid, phosphate
solubilisation, lowering ethylene biosynthesis
HCN, siderophore, indoleacetic acid, P-solubilisation
Significantly increased the root
and leaves biomass over
untreated control
Increased the fresh biomass of
the plants and enhanced N and P
uptake in plant tissues
PGPR strains protect canola
plant against the inhibitory
effects of cadmium
Arkhipova
et al. (2007)
Exopolysaccharides,
siderophores, heavy metal
mobilisation
Enhanced the metal accumulation in plant tissues by facilitating the release of Ni from soil
Ma et al. (2009)
Bacteria inoculation alleviated
the salinity effects on the antioxidant enzymes ascorbate peroxidase and glutathione
reductase, along with mineral
content and growth
Inoculation resulted in a significantly reduced upregulation or
even downregulation of the
stress-inducible genes over
control plants
Bacterial inoculation showed
effective increase in antioxidant
and colour pigments, catalase
activity in plants under heat
stress
Golpayegani
and Tilebeni
(2011)
Siderophores, indole-3-acetic
acid, exopolysaccharides
Salt
Pseudomonas ssp. and Bacillus
lentus
Indole-acetic acid,
P-solubilisation,
ACC-deaminase activity,
siderophores production,
chitinase activity
Capsicum
annuum
(pepper)
Osmotic
stress (45 %
PEG)
Arthrobacter sp., Bacillus sp.
ACC-deaminase activity, IAA,
P-solubilisation, siderophores
Vitis vinifera
(grapevine)
Temperature
Burkholderia phytofirmans
ACC-deaminase activity, phenylalanine ammonia,
siderophores, P-solubilisation
Barassi
et al. (2006)
Dell’Amico
et al. (2008)
Sziderics
et al. (2007)
7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
mkumar9@amity.edu
Lactuca sativa
L. (lettuce)
Barka
et al. (2006)
151
152
S.M. Shahzad et al.
result in a positive response and enhance plant growth under drought (Liddycoat
et al. 2009). On the basis of mutational studies of Azospirillum, Kadouri
et al. (2003) proved the role of PHB synthesis and accumulation in enduring various
stresses, viz. UV irradiation, heat, osmotic pressure, osmotic shock and desiccation.
A multi-process phytoremediation system (MPPS) utilises plant/PGPR interactions
to mitigate stress ethylene effects, thereby greatly increasing plant biomass, particularly in the rhizosphere, and it also causes the decontamination of persistent
petroleum and organic contaminants in soil (Glick and Stearns 2011; Gamalero
and Glick 2012a, b).
Drought affects the plant–water relation at cellular and whole plant level causing
specific and unspecific reactions and damages. PGPR adapted to endemic sites of
low rainfall area or limited water supply are more likely to protect plant from
drought stress than similar bacteria from sites where water is more abundant
(Mayak et al. 2004). Exopolysaccharides secreted by PGPR formed an organomineral sheath around microbial cell, enabling specific bacterium to survive under
prevailing stress such as drought and improve drought tolerance in plant through
osmotic and intracellular adjustment (Sandhya et al. 2009). Inoculation with
exopolysaccharide-producing PGPR revealed drought-exposed barley plant tolerance extended for 2 weeks than uninoculated control plants (Timmusk 2003). It is
now widely recognised that most bacteria in natural environments persist as
‘biofilm’ communities where cells are encased in an extracellular polymeric matrix.
The development of biofilm communities is a vital approach employed by bacteria
for survival under stress conditions (Fujishige et al. 2006).
Phosphorus is essential for all living cells and organisms. Low soil P availability
has profound impact on global agriculture and food production (Song et al. 2014).
Low solubility and precipitation of added P source is the major issue of semiarid
and arid regions of the world. Some PGPR are characterised for the production of
microbial metabolites which results in a decrease in soil pH, which probably plays
an important role in the solubilisation of P (Abd-Alla 1994; Rajkumar and Freitas
2008). The phosphate-solubilising microorganisms can interact positively in promoting plant growth as well as P uptake of maize plants, leading to plant tolerance
improving under water-deficit stress conditions (Ehteshami et al. 2007). The inoculation of some microorganisms that solubilise the insoluble phosphates into a
microcosm containing soil from a barren lakeside area enhances the plant growth
significantly and signified the potential capability of these bacteria to be used for the
rapid revegetation of barren or disturbed land (Jeon et al. 2003; Paul and Sarma
2006).
The metal-resistant plant growth-promoting bacteria (PGPB) can serve as an
effective metal sequestering and growth-promoting bio-inoculant for plants in
metal stressed soil (Rajkumar and Freitas 2008). The deleterious effects of heavy
metals taken up from the environment on plants can be lessened with the use of PGP
bacteria (Belimov et al. 2005; Glick 2010; Ahemada and Kibret 2014). Soil
microbes, plant growth-promoting rhizobacteria (PGPR), P-solubilising bacteria,
mycorrhizal-helping bacteria (MHB) and arbuscular mycorrhizal fungi (AMF) in
the rhizosphere of plants growing on trace metal-contaminated soils play an
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7 Alleviation of Abiotic Stress in Medicinal Plants by PGPR
153
important role in phytoremediation (Khan 2005; Gerhardt et al. 2009).
Phytoremediation provides a cheap, energy-efficient detoxification method that
manipulates intrinsic plant characteristics to concentrate the metal contamination
in shoot biomass and reduce the bioavailability of the heavy metals. Soil microbes
mitigate toxic effects of heavy metals on the plants through secretion of acids,
proteins, phytoantibiotics and other chemicals (Denton 2007). Jing et al. (2007)
reviewed recent advances in effect and significance of rhizobacteria in
phytoremediation of heavy metal-contaminated soils. Cd in soil induces plantstress ethylene biosynthesis (Pennasio and Roggero 1992; Gamalero and Glick
2011) and probably contributes to the accumulation of ACC in roots; PGPR protect
the plants against the inhibitory effects of cadmium (Amico et al. 2008). ACC
deaminase lowers ethylene production under cadmium stress condition when measured in vitro ethylene evolution by wheat seedlings treated with ACC deaminase
positive isolates (Govindasamy et al. 2009). Wu et al. (2006) carried out a greenhouse study with Brassica juncea to critically evaluate effects of bacterial inoculation on the uptake of heavy metals from Pb–Zn mine tailings by plants. The
presence of these beneficial bacteria stimulated plant growth and protected the plant
from metal toxicity; it had little influence on the metal concentrations in plant
tissues, but produced much larger aboveground biomass and altered metal bioavailability in the soil. As a consequence, higher efficiency of phytoextraction was
obtained compared with control treatments. The organism Pseudomonas putida is
also tolerant to a number of heavy metals at higher levels. These characteristics
make P. putida an excellent candidate for field application in contaminated soil
(Chacko et al. 2009). Pseudomonas fluorescens can survive under dry conditions
and hyper osmolarity (Schnider-Keel et al. 2001). The hydroxamate siderophores
contained in culture filtrates of S. acidiscabies E13 promote cowpea growth under
nickel contamination by binding iron and nickel, thus playing a dual role of
sourcing iron for plant use and protecting against nickel toxicity (Dimkpa
et al. 2008; Badri et al. 2009).
The application of microbial biocontrol agents has been shown to be
eco-friendly and effective approach against many plant pathogens responsible for
various diseases (Gray and Smith 2005). PGPR mediate biological control indirectly by the production of antimicrobial molecules (Ongena et al. 2007; Nithya and
Halami 2012), siderophores, and eliciting induced systemic resistance against a
number of plant diseases. Plant exposed to various abiotic stress factors are more
susceptible to pathogenic infestation due to weaker host defence mechanism as a
result of exposed stressor. PGPR mediated biocontrol potential against various
pathogenic agents (Beneduzi et al. 2012).
mkumar9@amity.edu
154
7.3
S.M. Shahzad et al.
Recent Advances and Future Prospects of PGPR
in the Field of Medicinal Plants
The explicit conclusion from the above discussion is that stressful environments
can cause a negative impact on plant growth and development by causing nutritional and hormonal imbalances. However, the stress-induced negative impact on
plant growth can be alleviated and/or minimised by naturally occurring microorganisms such as PGPR.
Recently, proteomic-based techniques have provided a powerful tool to reveal
the molecular mechanisms of several abiotic stress responses. Several stressresponsive proteins have been proposed for plant using these techniques, and
using these proteins and their corresponding genes, it will be possible to change
stress-sensitive to stress-tolerant medicinal plants in the near future.
Identification of genes controlling stress tolerance traits of PGPR would enhance
our knowledge about the molecular basis of the stress tolerance mechanisms. Most
of the in vitro studies lack biochemical and physiological mechanisms involved in
stress tolerance. Thus, the work on this aspect will significantly improve the
understating of the mechanism.
Another important aspect is to generate transgenic medicinal plants encoding the
genes of particular traits of PGPR. The literature shows that these transgenic plants
have the ability to withstand stress environment. However, such studies were
conducted in controlled conditions. Most of these studies are preliminary investigations which require further verification by performing extensive experimentation.
Moreover, information about the molecular mechanisms governing the process of
stress tolerance is limited.
Overall, future research should be focused: (1) to mediate PGPR-based metabolite engineering under stressful environments, (2) to explore what strains of PGPR
are beneficial for promoting plant growth, (3) to identify target genes for promoting
growth under stress and (4) to transfer target genes into plants through
biotechnology.
7.4
Conclusions
Numerous agro-biotechnological approaches have been employed to tackle the
decline in plant growth and health exposed to various abiotic stresses. One potential
way to reduce their drastic effect on plant is the utilisation of microbial bioresource.
Plant beneficial microbes (including plant growth-promoting rhizobacteria,
i.e. PGPR) and their associative interaction with host plant are termed as plant
growth and development stimulus (Shahzad et al. 2013) and have probably been
shaped by co-evolutionary mechanisms. In this way, microbial partners could have
significant effects on the physiology of the host plant. In recent times, PGPRmediated stress amelioration has evolved as a vital cog of a biotic stress
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management in plant and their potential contribution towards improving growth
and productivity.
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mkumar9@amity.edu
Chapter 8
Plant Growth-Promoting Rhizobacteria
for Alleviating Abiotic Stresses in Medicinal
Plants
Swarnalee Dutta and S.M. Paul Khurana
8.1
Introduction
Plants are exposed to various biotic and abiotic stresses leading to hazardous effect
on growth and reduction in yield. Such consequences are serious as plants are the
source of food, fodder, feed, fibre and medicines. The ever-increasing population of
the world has put tremendous pressure on the agriculture to ensure sufficient and
quality food. The accommodation of such explosion in human race has reduced the
total arable land leading to apprehensions about availability of adequate food. To
top it are the woes of changing climatic and environmental conditions with time.
Climatic changes influence the biotic and abiotic factors which are crucial for
proper plant growth and potential yields. Environmental changes, with special
reference to abiotic stress, can alter the development and productivity of plants
and even threaten their survival. Severe changes in the growth, physiology and
metabolism of plants caused by abiotic stresses lead to increased accumulation of
secondary metabolites. These changes pose challenge or threaten all economically
important crops. Harsh climatic conditions such as drought, salinity, extreme
temperatures (high and low) and heavy metal contamination significantly affect
qualitative and quantitative crop production (Edmeades 2009; Zhu 2002; Lee
et al. 2001). Moreover, injudicious use of agrochemicals, pesticides and fertilizers
has rendered severe environmental threats including loss of soil fertility. Urbanization and development of industries have led to deforestation and release of toxic
S. Dutta
Division of Agricultural Microbiology, National Academy of Agricultural Science, RDA,
South Korea
e-mail: swarnalee.dutta@gmail.com
S.M.P. Khurana (*)
Amity Institute of Biotechnology, Amity University, Gurgaon, Manesar, Haryana 122413,
India
e-mail: smpaulkhurana@gmail.com; smpkhurana@ggn.amity.edu
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_8
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wastes into the environment posing harmful consequences. Such adversities leading
to poor growth of plants are a major concern for agriculturists. Natural adversities,
excessive exploitation by human and lack of environment-friendly lifestyles have
led to extinction of many plant species.
Of all the economically important plants affected by biotic and abiotic stresses,
the medicinal plants are of utmost importance because of the dependency of human
population on them for pharmaceutically important metabolites. Chemical synthesis of all the compounds required for various drugs is not possible and also naturally
not economical. The production of stable pharmaceutically important compounds is
a major challenge for the chemists. The increasing emphasis on herbal treatment of
diseases has led to increasing reliance on natural sources rather than chemical
compounds. Awareness that the medicinally important plants are more effective
and stable when processed minimally has turned the attention of people to include
them in their diet. The processing leads to contamination by metals from vessels
used and other stabilizing agents used for the medicine. All these result into
negative side effects of the processed medicines.
Another problem related to the present-day fast and urbanized lifestyle is the
injudicious use of synthetic drugs and antibiotics. Self-medication due to lack of
time for consultation and over-the-counter availability of drugs have led to serious
complications and development of drug-resistant pathogens. With the increasing
awareness about hazards and toxic effects of synthetic drugs, exploitation of
medicinal plants for health consideration has become extremely popular.
Plants have evolved to survive the adverse effects of different stresses by
initiating a number of molecular, cellular and physiological changes which address
the ensuing stress environment. But such alterations may affect the production due
to channelizing of the metabolic activities towards acclimatization and adaptation
instead of normal growth and yield (Krasensky and Jonak 2012). This could lead to
drastic loss especially in case of medicinally important plants where primary and
secondary metabolites during normal growth and development are the important
sources of drugs. Any alteration in the physiology, biochemistry, genomic, proteomic and metabolic levels caused by abiotic stresses may lead to loss or reduction of
the pharmaceutically important chemical production in the plant. Therefore, the
changing environmental and climatic conditions along with the increase in global
demand for life security emphasize the need for stress-tolerant crop varieties
(Newton et al. 2011; Takeda and Matsuoka 2008).
Conventional methods of crop breeding to improve the growth and yield of
plants under different environmental threats like biotic and abiotic stresses are
time-consuming and not successful in many cases. Use of expensive harmful agrochemicals and pesticides causes severe threat to environment and renders development of resistant pathogens. Nowadays attention has been turned to cost-effective,
viable and environment-friendly alternatives such as biological means to improve
and facilitate plant growth. Beneficial bacteria, especially in the rhizosphere of
plants, have been studied and confirmed to have growth-promoting activities. The
beneficial rhizobacteria include the symbiotic Rhizobium species, certain actinomycetes and mycorrhizal fungi and free-living bacteria. Plant growth promoting
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rhizobacteria (PGPR) are a group of beneficial bacteria which have the potential of
improving plant growth and yield besides controlling diseases and rendering tolerance against various abiotic stresses.
Research on the effect of PGPR on medicinal plants is available (Lenin and
Jayanthi 2012), but the mechanisms involved have not been completely elucidated
as of now. The beneficial effects of PGPR on plants under abiotic stress have also
been a topic of research in recent times. A few works have been reported specifically for interaction of PGPR with medicinal plants for alleviation of abiotic stress.
The mechanisms reported for interaction with plants in general may also apply for
medicinal plants. This chapter is based on reports of plant–PGPR interaction under
abiotic stress with special emphasis on plants which are also reported to have
medicinal properties. Exclusive reports on PGPR and medicinal plants interaction
under abiotic stress are limited.
8.2
Types of Abiotic Stresses
Environmental conditions, like bright light, extreme temperatures, drought, flood,
salinity, heavy metals and hypoxia, seriously affect the agricultural production. The
changing climatic conditions, whether natural or man-made, are likely to increase
the impact of the alterations on crop growth and yield.
8.2.1
Water Stress
Of the various abiotic stresses leading to evolution in plants, availability of water is
the most important (Kijne 2006; Zhu 2002). Water stress includes drought, flood as
well as salt stress. The impact of drought is a major problem all over the world
causing huge loss to farmers and their inputs towards successful cropping. The year
2012 was recorded as the worst drought of the century. While droughts in Europe
and the United States had huge impact on commodity markets, shortage of food was
the consequence of droughts in Asia. In developing countries like India with its
diverse geographical and climatic conditions, farmers are continuously under the
threat of abiotic stresses which is a major decisive factor of successful crop yield.
8.2.2
Salinity
Soil salinity is a threat in both developed and developing countries severely
affecting agricultural productivity (Jaleel et al. 2007). The agricultural intensification and unfavourable natural conditions have led to increase in soil salinity in the
world. The term salt affected refers to soil that are saline (accumulation of salts) or
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S. Dutta and S.M.P. Khurana
sodic (too much sodium associated with the negatively charged clay particles)
(Rengasamy 2006). It is estimated that more than 800 million hectares of land is
affected by salinity throughout the world (FAO 2008). Salinity is of two types—
primary and secondary. Naturally occurring salinity in soil and water is known as
primary salinity, and those resulting from human activities, such as land development and agriculture, are called secondary salinity.
8.2.3
Extreme Temperatures
Changing temperatures are also a cause of worry for agriculturists all over the
world. National Aeronautics and Space Administration (NASA) and National
Oceanic and Atmospheric Administration (NOAA) ranked 2012 among the
10 warmest years on record globally. While the truth or myth of global warming
is still a topic of debate for scientists, environmentalists, socialists, politicians and
economists, there is no doubt about the changing scenario in world temperature
affecting the seasonal variations with respective impact on the crops grown.
NASA’s Goddard Institute for Space Studies (GISS) in New York stated that this
decade is warmer than the last decade which was in turn warmer than the previous
one. Warmer winters are also a common phenomenon which has serious implications. This alarming issue categorizes temperature as one of the most threatening
abiotic stress posing drastic consequences in the forthcoming times.
8.2.4
Heavy Metals
Global industrialization, especially in the field of mining, smelting, manufacturing,
fuel production, sewage, municipal wastes and application of fertilizers and pesticides, has significantly contributed to the increase in heavy metal contamination
leading to environmental pollution. In contrast to organic pollutants, metals cannot
be degraded to harmless products, and they continue to remain in the environment
entering water beds and agricultural lands. Common heavy metal contaminants
include cadmium, nickel, zinc, chromium, mercury, silver, lead, cobalt and copper.
Plants uptake the metals as these are common ingredients of macro- and microelements, and this is the basis of phytoremediation of heavy metals. However,
assimilation of heavy metals into plants leads to invasion of these harmful elements
into the food cycle leading to health threats of human and animals.
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171
Plant Response to Abiotic Stress
Plants have inherent ability to adjust with seasonal variations, but when subjected to
stress like harsh and rapid environmental or climatic conditions, a series of morphological, physiological, biochemical and molecular changes occur leading to alteration in development and yield (Wang et al. 2001). Abiotic stress leads to
dehydration and osmotic imbalance of the cells. Almost all types of abiotic stress
lead to similar alterations in the plant’s biochemical and physiological status.
Some of the medicinal plants, their economically important secondary metabolites and the threatening abiotic stresses have been listed in Table 8.1.
The primary effect of abiotic stress in plants is imbalance of ions and hyperosmotic stress which enhances the accumulation of reactive oxygen species (ROS).
Impairment between production of ROS and antioxidant defence leads to disruption
of cellular structures and drastic physiological changes like denaturation of proteins, lipids, carbohydrates and DNA (Debnath et al. 2011a). These changes
subsequently cause inhibition of photosynthesis and metabolic dysfunction leading
to reduced growth and fertility, premature senescence and low yield.
Salt tolerance is a common phenomenon in plants. Salinity induces a number of
processes in plants to alleviate osmotic and ionic imbalance. Excessive exposure to
salt for a longer period leads to inhibitory effects on growth and yield (Manaa
et al. 2011). In vitro studies showed reduced growth under high salinity for
medicinal plants Chlorophytum borivilianum (Debnath et al. 2011b), Bacopa
monnieri, Catharanthus roseus (Wang et al. 2008) and Jatropha curcas
(De Oliveira Campos et al. 2012; Gao et al. 2008). Growth and herb yield are
comparatively higher in plants under primary salinity than in secondary salinity and
plants tend to adapt to gradual increase in salinity after the harm of initial exposure.
Salt stress can lead to stomatal closure reducing CO2 availability in the leaves and
inhibits carbon fixation which leads to excessive excitation energy exposure of
chloroplasts, thereby generating ROS and oxidative stress (Parvaiz and Satyawati
2008). Excessive generation of ROS induces toxicity causing damage to protein
structures, inhibition of many important enzymes of metabolic pathways and
oxidation of macromolecules like lipids and DNA which may eventually lead to
cell death (Kar 2011; Gill and Tuteja 2010). ROS-initiated formation of oxylipins
represents endogenous signals of abiotic stress (Mithofer et al. 2004). Growth
inhibition, stimulation of secondary metabolism and lignification leading to cell
death occur as a consequence of disturbed redox state of the cell (Schutzendubel
and Polle 2002). As a defence response to ROS, plants under salt stress show
reduced photosynthetic activity and transpiration rate (Koca et al. 2007). The
antioxidant system of cell is composed of radical scavenging metabolites like
glutathione and ascorbate along with the protective enzymes. Glutathione donates
an electron to unstable molecules of ROS to make them less reactive. It acts as a
redox buffer for ascorbic acid to recycle from its oxidized state to the reduced form
by the enzyme dehydroascorbate reductase (Jozefczak et al. 2012). The protective
antioxidant enzymes include superoxide dismutase (SOD), peroxidase (POD),
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S. Dutta and S.M.P. Khurana
Table 8.1 Medicinal plants under abiotic stress (Debnath et al. 2011a)
Medicinal
plant
Pluchea
lanceolata
Dioscorea
bulbifera
Catharanthus
roseus
Ocimum sp.
Jatropha
curcas
Orthosiphon
stamineus
Melissa
officinalis L.
Thymus
maroccanus
Ball.
Matricaria
chamomilla
Bacopa
monnieri
Olea
europaea L.
Populus
euphratica
Matricaria
chamomilla
Ziziphora
clinopodioides
Dioscorea
dregeana
Datura
innoxia Mill
Uses
Bronchitis, dyspepsia and
rheumatoid arthritis
Antispasmodic, analgesic,
aphrodisiac and diuretic
Cancer and diabetes
mellitus
Cancers, antifertility and
adaptogenic
Skin diseases and rheumatism, piles
Antiallergenic, antihypertensive
Anti-inflammatory and
nephritis
Insomnia and anxiety
Antitussive, antiseptic,
antispasmodic and
antihelminthic
Mucositis and irritable
bowel syndrome
Antioxidant, epilepsy, loss
of memory and asthma
Antipruritic, antiseptic,
astringent and cholagogue
Anodyne, antiinflammatory, febrifuge
and vermifuge
Sore stomach, irritable
bowel syndrome and oral
mucositis
Antibacterial, sedative,
stomachache, carminative,
antiseptic and wound
healing
Sedative and antiinflammation
Anodyne, antispasmodic,
hallucinogenic, hypnotic
and narcotic
Secondary
metabolites
Abiotic
stress
Quercetin
Diosgenin
Heavy
metals
Metal
Vinblastine
Salinity
Eugenol
Drought
Curcin
Salinity
Polyphenols
Salinity
Quercetin
Thymol
Salinity and
water
Salinity
Ozturk
et al. (2004)
Belaqziz
et al. (2009)
Umbelliferone
CuCl2
Bacoside
Oleosides
Salinity and
drought
Salinity
Gallic acid
Salinity
Eliasova
et al. (2004)
Debnath
(2008)
Rejskova
et al. (2007)
Zhang
et al. (2004)
Apigenin
Salinity
Razmjoo
et al. (2008)
Leucoanthocyanins
Salinity and
defoliation
Koocheki
et al. (2008)
Paclobutrazol
Smoke,
temperature
Light, dark
and HCHO
deprivation
Kulkarni
et al. (2007)
Laszlo
et al. (1998)
Scopolamine
mkumar9@amity.edu
References
Kumar
et al. (2004)
Narula
et al. (2005)
Jaleel
(2009)
Khalid
(2006)
Gao
et al. (2008)
Ting
et al. (2009)
8 Plant Growth-Promoting Rhizobacteria for Alleviating Abiotic Stresses in. . .
173
catalase (CAT), tryptophan decarboxylase (TDC), reductase, redoxin and phenylalanine ammonia-lyase (PAL). An increase in activity of SOD, POD, CAT, TDC
and PAL has been reported in plants under salt stress (Gao et al. 2008).
Salt stress also affects proteins related to cell wall biogenesis, nitrogen, carbohydrate and lipid metabolism (Veeranagamallaiah et al. 2008). However, metabolic
adjustments in plants depend on the severity of the stress and on the cultivar.
Different genotypes and plants at different stages of growth also vary in their
response to salinity. Salt stress stimulates different response from different layers of
cells, and different genes were expressed throughout the duration of stress (Hines
2008). Cellular dehydration occurs in plants under salt stress leading to osmotic
stress and removal of water from the cytoplasm which results in reduction of the
cytosolic and vacuolar volumes. Ionic and osmotic imbalances due to intercellular
accumulation of Na+ disturb the K+ nutrition leading to cell toxicity and inhibition
of many crucial enzymes (Jaleel et al. 2008).
Similar to salinity, drought or water stress can induce various morphological,
biochemical and physiological changes in plants. Some of the alterations caused by
drought which inhibit growth include structural changes of stomata, reduced transpiration and photosynthesis, decreased water potential in tissues and membrane
disruption. Different stress-responsive genes are activated in plants under water
stress. Deficit of water or salinity activates the defence mechanisms through
chemical signals. Accumulation of abscisic acid (ABA) is a major signal for
drought and salinity in plants and reduces transpiration through stomatal closure
thereby diminishing the negative effect of water loss. ABA also induces decrease in
photosynthesis and photo-inhibition. ABA regulates expression of stressresponsive genes like late embryogenesis abundant proteins which helps in inducing drought tolerance in plants (Aroca et al. 2008). Deficiency of water also induces
accumulation of shikimic acid and levels of amino acids such as proline, tryptophan, leucine, isoleucine and valine (Warren et al. 2012; Bowne et al. 2012). The
ROS metabolism of plants is also affected by drought as in Catharanthus roseus
(Jaleel et al. 2008). Since salinity and water stress are mutually inclusive events,
there is overlapping response of plants exposed to these stresses.
Very high temperature also leads to drought conditions thereby causing stress in
plants. The physiological alterations in plants due to heat are similar to that under
water stress. Low temperatures alter the metabolite profile of plants including that
of sugars, phenolics and nitrogenous compounds (Janska et al. 2010; Zhang
et al. 1997). Low temperatures also affect the secondary metabolite production.
The hazardous effect of heavy metals on human and animal health is already
established. Heavy metal contamination in soil and water bodies leads to exposure
of plants to metal pollution. Although plants require trace amounts of heavy metals
as micronutrients, exposure to high concentration renders physiological stress (Hall
2002). Heavy metal contamination also inhibits the germination and growth of
plants due to production of ROS, disturbing the function and composition of biomolecules (Peng et al. 2010). Plants combat the heavy metal contamination by
production of phytochelatins (Hall 2002).
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S. Dutta and S.M.P. Khurana
Most of the changes in plants on exposure to any kind of abiotic stress are
similar. The ionic imbalance due to salinity-, flood- or heat-induced drought is a
common phenomenon. All the abiotic stresses including extreme temperatures and
heavy metals activate the defence response of plants leading to excessive generation of ROS and ROS-mediated harmful effects on the physiology of plants.
8.4
Plant Growth-Promoting Rhizobacteria
The zone surrounding the roots of plants in which complex relations exist among
the plant, the soil microorganisms and the soil is known as the “rhizosphere”. The
number, diversity and activity of microorganisms in the rhizosphere microenvironment are more than other parts of soil because of the different physical, chemical
and biological properties of the root-associated soil (Kennedy 1998). Rhizosphere
microflora includes both deleterious and beneficial elements that have the potential
to influence plant growth and crop yield significantly (Compant et al. 2005). PGPR
are defined as root-colonizing bacteria that exert beneficial effects on plant growth
and development (Cakmakci et al. 2006; Persello-Cartieaux et al. 2003). Bacteria of
diverse genera were identified as PGPR of which Bacillus and Pseudomonas spp.
are predominant (Podile and Kishore 2006). The root-colonizing bacteria are the
most sought-after group for their multifaceted qualities which include plant growth
promotion, disease control and bioremediation.
The effect of PGPR and the mechanisms of interaction have been critically
studied through years of vigorous research. PGPR can influence the growth of
plants either directly or indirectly. Plant hormone production, enhanced iron availability, phosphorus solubilization and nutrient mobilization are some of the direct
methods of growth improvement by PGPR. Indirect growth promotion occurs when
PGPR promote plant growth by improving growth-restricting conditions. Production of antagonistic substances to eliminate specific harmful microbes from the
vicinity of roots and induction of systemic resistance (ISR) provides protection
against pathogens thereby enhancing growth-promoting conditions (Weller
et al. 2002; Pierson and Thomashow 1992).
8.4.1
Mechanisms for Growth Promotion
PGPR can affect the plants by the production of diverse metabolites including
siderophore and hydrocyanic acid (HCN) (Bhatia et al. 2005), plant hormones such
as indole acetic acid (IAA) and some other auxins, gibberellins, cytokinins
(Persello-Cartieaux et al. 2001, 2003; Patten and Glick 2002; De Salamone
et al. 2001) and ethylene (Glick et al. 1995). There are evidences that the yieldincreasing bacteria and other Bacillus strains produce plant growth regulators in
laboratory culture (Chen et al. 1996). PGPR-produced metabolites like gibberellic
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8 Plant Growth-Promoting Rhizobacteria for Alleviating Abiotic Stresses in. . .
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acid, IAA and cytokinin like substances are reported to enhance seed germination
and radicle length (Persello-Cartieaux et al. 2003). The production of biologically
active metabolites, particularly the plant growth regulators by rhizosphere
microbiota, affects plant growth directly after being taken up by the plant or
indirectly by modifying the rhizosphere environment (Penrose and Glick 2001).
Glick et al. (1998) proposed a model in which PGPR bind to the surface of seeds
and in response to tryptophan and/or other amino acids exuded from the germinating seeds, synthesize and secrete IAA. This IAA may be taken up by the seeds and,
together with the endogenous IAA, stimulate the cell proliferation and cell elongation or induce the synthesis of 1-aminocyclopropane-1-carboxylate (ACC)
synthase. De Leij et al. (2002) suggested that 2,4-diacetylphloroglucinol (DAPG)
produced by a P. fluorescens strain can act as a plant hormone-like substance,
inducing physiological and morphological changes in the plant that can lead to
enhanced infection and nodulation by Rhizobium. Grimes and Mount (1984)
observed an increase in nodulation of plants co-inoculated with P. putida and
R. phaseoli. They proposed that the possible mechanisms for this enhancement
include either phosphate supply to the bean plant or a plant growth regulator effect
of P. putida.
Another mechanism by which certain rhizobacteria improve plant growth is by
the breakdown of ethylene which is inhibitory to root growth (Glick et al. 1998).
Large number of PGPR strains produces the enzyme ACC deaminase, which
hydrolyses ACC, the immediate precursor of the plant hormone ethylene (Belimov
et al. 2001; Glick et al. 1995). They stimulate root growth of various crop plants
(Belimov et al. 2001; Burd et al. 2000; Glick et al. 1997). This mechanism is most
effective on plants that are more susceptible to the effects of ethylene especially
under such stress conditions as flooding (Grichko and Glick 2001), drought (Lucy
et al. 2004) and phytopathogens (Wang et al. 2000). It has been shown that the
bacterial ACC deaminase is not induced in cells grown in nutrient medium abundantly supplied with ammonia (Belimov et al. 2001) which suggests that if sufficient nitrogen is provided to the bacteria, production of ACC deaminase is
inhibited.
PGPR can promote plant growth indirectly by affecting symbiotic N2 fixation,
nodulation, or nodule occupancy (Okon et al. 1998) by rhizobia. Co-inoculation of
some PGPR strains increased the nodulation of legumes by nitrogen-fixing rhizobia
(Kloepper et al. 1991), which were designated as nodulation-promoting
rhizobacteria (NPR). Tilak et al. (2006) reported that dual inoculation of
P. putida, P. fluorescens or B. cereus with Rhizobium increased plant growth,
nodulation and enzyme activity over Rhizobium-inoculated and Rhizobiumuninoculated control plants. In a study where soybean was co-inoculated with
Bradyrhizobium japonicum and different isolates of rhizobacteria, the increase in
the number and weight of nodules formed by B. japonicum was observed
(Polonenko et al. 1987). Similarly, Fuhrmann and Wollum (1989) reported fluorescent pseudomonads that consistently increased nodule occupancy of B. japonicum
in soybean grown in a potting medium with low availability of Fe. Inoculation of
legumes with root-colonizing bacteria and Rhizobium has been demonstrated to
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S. Dutta and S.M.P. Khurana
affect symbiotic nitrogen fixation by enhancing root nodule number or mass
(Saxena and Tilak 1994). Lucas-Garcia et al. (2004) had proposed the possibility
that metabolites other than phytohormones, such as siderophores, phytoalexins and
flavonoids from PGPR, might have a role in enhanced nodule formation. Parmar
and Dadarwal (1999) reported that PGPR treatment or application of ethyl acetate
extract of the culture supernatant increased concentration of flavonoid-like compounds in roots which are known as chemoattractant for rhizobia. They also
reported that rhizobacteria themselves are capable of producing fluorescent flavonoids similar to those produced by the host plant. In addition, PGPR are also known
for asymbiotic nitrogen fixation (Figueiredo et al. 2008).
Solubilization of mineral phosphates and mobilization of other essential nutrients by PGPR also help in growth improvement of plants (Bertrand et al. 2001; De
Freitas et al. 1997). Yield increase of groundnut by Pseudomonas isolates from
rhizosphere positively correlated with the ability of these strains to increase available soil phosphorus (Dey et al. 2004). The number of nodules in treated plants was
also found to be higher than untreated control, and therefore, it was hypothesized
that the energy needed for this symbiotic process is facilitated due to availability of
high soil phosphorus content.
8.4.2
Mechanisms for Disease Control
In addition to direct mechanisms for growth promotion, enhanced plant growth is
also attributed to the suppression of deleterious microflora by the introduced
bacteria (Lugtenberg et al. 2001; Kloepper et al. 1991). Antagonism against plant
pathogens are due to production of siderophores (Burd et al. 2000), β-1,3-glucanase
(Fridlender et al. 1993), antibiotics (Shanahan et al. 1992), chitinase (Renwick
et al. 1991) and hydrogen cyanide (Bhatia et al. 2005). Bacterial antagonists have
been widely exploited towards the management of plant diseases (Haas and Defago
2005; Commare et al. 2002). These microorganisms can also function as competitors of pathogens for colonization sites and nutrients.
Triggering the defence mechanism in plants may be one of the important factors
of ISR in PGPR-treated plants grown in pathogen-infested soil. Increase in
l-phenylalanine ammonia-lyase (PAL), peroxidise (POX) and polyphenol oxidase
(PPO) activity has been observed in plants treated with PGPR (Dutta et al. 2008;
Ongena et al. 2000). The relation between PAL activity and resistance, in different
seedling parts, has also been reported (Saikia et al. 2006). According to some
reports, the rapid induction of PAL genes in resistant host and its pathogen might
be due to the involvement of a signal transduction mechanism, triggered specifically as a result of interaction between elicitor and receptor molecules, thereby
showing differential transcriptional rates of PAL in compatible and incompatible
interactions (Kale and Choudhary 2001). Biochemical analysis of rice plants raised
from seeds treated with P. fluorescens showed an early induction of POX, PAL and
chitinase (Nandakumar et al. 2001). Sivakumar and Sharma (2003) reported that
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PAL, POX and PPO activities are higher in plants raised from P. fluorescens-treated
seeds than the increase in pathogen inoculated ones. Bacillus enhanced the levels of
total phenols, PAL, POX and lipoxygenase in the bacterized seedlings, indicating
the involvement of ISR in PGPR-mediated disease control (Sailaja et al. 1997).
Siderophore production by the PGPR may also contribute to the disease suppression in bacterized plants (Yeole and Dube 2000). Siderophores produced by
Pseudomonas exert killing effect on the plant deleterious fungi F. oxysporum and
A. flavus infecting wheat (Manwar et al. 2000). Fluorescent pseudomonads produce
pseudobactin (PSB)-type siderophores which are not readily available as an iron
source to other rhizosphere bacteria, but they gain an ecological advantage as they
are able to utilize a wide variety of other siderophores (Jurkevitch et al. 1993).
Mercado-Banco et al. (2001) reported the production of the siderophore pseudomonine in addition to the fluorescent pseudobactin type in biocontrol strain
P. fluorescens WCS374.
Production of antibiotics has been reported as another important factor for
suppression of diseases by PGPR strains. Bakker et al. (2003) reported that antibiotics do have direct effects on plants and, therefore, might induce systemic
resistance. A variety of antibiotics have been identified to be produced by pseudomonads (De Souza et al. 2003; Nielson and Sorensen 2003).
A blend of airborne chemicals released from specific strains of PGPR also
promotes growth in plants. It has been reported that volatile organic compounds
(VOCs) may play a key role in ISR (Ping and Bolland 2004; Ryu et al. 2004). VOCs
secreted by B. subtilis and B. amyloliquefaciens were able to induce ISR in
Arabidopsis against Erwinia carotovora (Ryan et al. 2001). The discovery that
VOCs of bacteria trigger enhancement in plant growth constitutes an unreported
mechanism for the elicitation of plant growth by rhizobacteria. It is possible that
volatiles produced by PGPR colonizing roots are generated at sufficient concentrations to trigger plant responses (Ryu et al. 2003).
8.5
PGPR a Boon Alleviating Abiotic Stress
PGPR from medicinal plants like Withania somnifera, Catharanthus roseus, Coleus
forskohlii, Ocimum sanctum and Aloe vera have been reported to improve growth
and yield (Karthikeyan et al. 2008; Attia and Saad 2001). Various PGPR strains
belonging to the genera Azospirillum, Azotobacter, Pseudomonas and Bacillus have
been isolated and applied for growth improvement. A formulation of PGPR including Azospirillum lipoferum, Azotobacter chroococcum, Pseudomonas fluorescens
and Bacillus megaterium significantly enhanced germination rate, vigour index and
chlorophyll content of Catharanthus roseus (Lenin and Jayanthi 2012).
Microbes from extreme environments are known to be adaptive to the surrounding environmental conditions. Bacteria from saline conditions can tolerate high salt
concentrations, from water-deficit areas can survive in high temperature and low
moisture content. Bacteria undergo various morphological, biochemical and
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S. Dutta and S.M.P. Khurana
physiological adaptations to survive in the changing environmental conditions.
These bacteria can act as a potential source of PGPR as they can survive and
establish in the roots of plants growing in harsh environment thereby exerting the
beneficial effect on plant growth and disease control under abiotic stress. The
influence of PGPR in alleviation of harmful effects caused by abiotic stresses has
been reported (Christian et al. 2009) such as drought (Alvarez et al. 1996),
waterlogging (Saleem et al. 2007), oxidative stress (Stajner et al. 1995, 1997) and
salinity (Weyens et al. 2009; Yang et al. 2009; Venkateswarlu et al. 2008). Bharti
et al. (2013) indicated the role of a halotolerant PGPR strain Exiguobacterium
oxidotolerans against salinity, improving the growth and yield of Bacopa monnieri.
PGPR improved tomato and pepper growth under water stress (Aroca and RuizLozano 2009). Tolerance of plants against abiotic stress due to physical and
chemical changes induced by PGPR is termed as “induced systemic tolerance”
(IST) (Sandhya et al. 2010). Native rhizobacteria from plants under drought conditions like in arid regions are more competent in enhancing tolerance against water
stress (Ilyas and Bano 2010; Marulanda et al. 2008).
Application of PGPR has been effective in reducing the harmful effects of
drought (Sarig et al. 1992). Crops treated with PGPR such as Azospirillum, Klebsiella and Paenibacillus under varied agro-climatic conditions have shown
improved growth and yield with extensive root growth facilitating better uptake of
water and minerals (Dobbelaere et al. 2001; Timmusk and Wagner 1999). PGPRtreated seedlings when exposed to water stress showed better water status (Casanovas et al. 2002; Creus et al. 1998) thereby indicating the efficacy of PGPR in waterdeficient soils (Okon 1985). Similar effect of A. brasilense was recorded against
salinity in wheat seedlings with relatively higher water content (Creus et al. 1997)
which could be due to various physiological changes induced by the colonizing
bacteria. Creus et al. (2004) showed a higher water status and elastic adjustment in
Azospirillum-inoculated wheat leading to higher grain yield with better mineral
quality. Various mechanisms involved in mitigation of abiotic stress include
increase in proline levels (Dimkpa et al. 2009), decrease in excessive ethylene
through ACC deaminase (Barnawal et al. 2012; Arshad et al. 2008), reduction in
uptake of Na ions through exopolysaccharide (EPS) production (Kohler et al. 2010).
The activity of ACC deaminase and production of EPS were strategies of
Bacillus and Exiguobacterium for abiotic stress elimination and growth improvement (Sgroy et al. 2009; Yumoto et al. 2004; Dastager et al. 2010; Selvakumar
et al. 2010). EPS production could restrict Na+ influx into the roots, and accumulation of proline and glutamate could act as osmoprotectant to reduce the negative
effects of salinity and water stress in Azospirillum-treated plants (Ashraf et al. 2004;
Casanovas et al. 2003, 2002). More than one mechanism seems to be involved in
mitigating abiotic stress by PGPR.
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Fig. 8.1 Morphological and physiological changes in plants by application of PGPR leading to
abiotic stress tolerance. IAA indole acetic acid, EPS exopolysaccharide, RE root exudate, ACC
1-aminocyclopropane-1-carboxylate, PGPR plant growth-promoting rhizobacteria, RAS rootadhering-soil, ???- unknown mechanism. Production of phytohormones increases the overall
growth and also alters root characteristics to facilitate uptake of water and minerals. IAA increases
the size of aerial parts of the plants. ACC deaminase reduces the ethylene level to eliminate the
negative effect on roots. Production of osmoprotectants by PGPR also contributes towards abiotic
stress tolerance. Soil aggregation due to production of EPS or alteration of RE hydrates the
rhizosphere and helps in increased uptake of water and minerals
8.5.1
Morphological and Physiological Changes
Fluorescent pseudomonads increased leaf number, leaf area and greenness of black
henbane under water-deficit stress conditions which was attributed to release of
IAA by the PGPR strains (Ghorbanpour et al. 2013). Exhaustive root system of
PGPR-treated plants could help the plants in better assimilation of nutrients and
water. Changes in root growth such as increase in root length, dry weight and
excessive root branching in PGPR-treated plants (Creus et al. 2005; Marcelo
et al. 2000; Okon and Vanderleyden 1997) help the plant to withstand water stress
(Fig. 8.1). Thin and branched root system is more efficient in water and mineral
uptake. Enhanced root growth due to production of ACC deaminase by PGPR may
also render benefit to the plants under stress conditions (Glick et al. 2007; Patten
and Glick 2002). Inoculation of plants with ACC deaminase-producing PGPR
partially reduced the negative effect of drought on growth, yield and ripening
(Arshad et al. 2008).
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Changes in stomatal conductance, leaf transpiration and root hydraulic properties are some of the physiological mechanisms of plant to cope with drought
conditions to increase the water-use efficiency (Tambussi et al. 2007). This is
important for the plant to survive under limited water conditions. Decrease in
stomatal conductance is reported by application of PGPR thereby increasing
water-use efficiency (Yasmin et al. 2013; Benabdellah et al. 2011) (Fig. 8.1).
Highest leaf relative water content and lowest membrane leakage have been
recorded in wheat and barley treated with PGPR strains of Bacillus and Azospirillum (Turan et al. 2012). Several studies report an increased positive effect
on plants under drought conditions upon treatment with arbuscular mycorrhizal
fungi along with rhizobia or PGPR (Fig. 8.1) like Enterobacter and Bacillus
(Tarafdar and Rao 2007; Valdenegro et al. 2001).
Higher cell wall elasticity and the ability to modify plant hormones are some of
the mechanisms induced by Azospirillum to combat with salinity and osmotic stress
(Creus et al. 1998; Bashan et al. 2004). Similar results of growth improvement due
to secretion of phytohormones by PGPR have been reported for Catharanthus
roseus and Phaseolus vulgaris (Jaleel and Panneerselvam 2007; Marcelo
et al. 2000). Production of secondary bioactive metabolites by bacteria stimulates
plant growth under saline conditions (Dilfuza 2012). Rice plants treated with
IAA-producing osmotolerant rhizobacteria showed enhanced root growth and
water uptake in drought condition (Yuwono et al. 2005). PGPR-inoculated plants
showed altered root respiration rate, root proliferation and metabolism through the
production of phytohormones thereby improving mineral and water uptake (Okon
and Itzigsohn 1995) (Fig. 8.1). Upregulation of proline biosynthesis pathway and
accumulation of total free amino acids in PGPR-inoculated plants maintain the
water level in cell thus helping in bearing the salinity and osmotic stress (Yoshiba
et al. 1997).
Although the uptake of sodium by plants is not altered by rhizobacteria (Mayak
et al. 2004), tomato plants bacterized with Achromobacter and exposed to salt stress
showed an enhancement in photosynthesis than untreated plants. The exact mechanism is yet to be understood, but it was suggested that increase in phosphorous and
potassium uptake might be responsible for this positive effect (Mayak et al. 2004).
Increase in chlorophyll and other pigment content of PGPR-treated plants could be
a biological strategy to reduce the drought-induced deleterious effect (Ghorbanpour
et al. 2013). Salt-stressed maize when inoculated with ACC deaminase containing
Pseudomonas syringae, Enterobacter aerogenes and P. fluorescens resulted in
higher K+/Na+ ratios, high relative water, chlorophyll and low proline contents
(Nadeem et al. 2007) (Fig. 8.1). High K+/Na+ ratios were also found in salt-stressed
maize in which selectivity for Na+, K+ and Ca2+ was altered upon inoculation with
Azospirillum (Hamdia et al. 2004). Moreover, exopolysaccharide-producing bacteria when applied to wheat showed a decrease of Na+ uptake (Ashraf et al. 2004).
This possibly may be due to reduced apoplastic flow of sodium ions into the stele
due to formation of soil layer surrounding the root.
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8 Plant Growth-Promoting Rhizobacteria for Alleviating Abiotic Stresses in. . .
8.5.2
181
Soil Structure Alteration
Soil aggregation is a major factor contributing to retention and movement of water,
aeration and temperature which, in turn, affect germination and root growth
(Dickson et al. 1990) as unstable aggregates have lower organic matter (Haynes
and Swift 1990). EPS production by microbes increase soil aggregation (Lynch and
Bragg 1985) and help in maintaining a hydrated microenvironment around the
microorganism (Chenu and Roberson 1996). PGPR are also reported to increase
root-adhering soil (RAS) due to EPS (Bezzate et al. 2000; Gouzou et al. 1993).
Changing the structure and aggregation of RAS by the production of EPS by PGPR
can help plants grow and survive under water-limiting conditions (Fig. 8.1).
Increase in soil around roots under stress condition to form a mucilaginous layer
around cells affects the absorption of water and mineral uptake (Bezzate et al. 2000;
Amellal et al. 1998; Gouzou et al. 1993). PGPR may also stimulate exudation of
more polysaccharides from root caps as an indirect method of improving soil
adhesion and aggregation in the roots. Alteration of plant root exudates by colonizing PGPR strains has been reported earlier (Dardanelli et al. 2009; Kamilova
et al. 2006). An increased RAS to root tissue ratio was observed in wheat treated
with Bacillus polymyxa or Pantoea agglomerans irrespective of the water conditions (Amellal et al. 1998; Gouzou et al. 1993). Thus, an increase in RAS and soil
aggregation due to EPS helps the rhizosphere to remain hydrated and protect plants
against abiotic stresses (Fig. 8.1).
8.5.3
PGPR Against Oxidative Stress
PGPR has been reported to increase drought tolerance in plants by production of
IAA, cytokinins, antioxidants and ACC deaminase. Proline along with other
non-enzymatic antioxidants induces resistance against salinity by protecting macromolecules from effects of oxidative stress (Galli et al. 1996) (Fig. 8.2).
ROS-mediated activation of lipid peroxidation destabilizes membrane. PGPR is
also reported to protect the plants under saline condition (Fig. 8.2) by reducing
membrane destabilizing activity in the cell (Khan and Panda 2008). PGPR enhances
ROS-scavenging enzymes such as catalase and ascorbate peroxidase (Gururani
et al. 2012; Kohler et al. 2010) which may help the plants under salinity and
drought stress to balance the harmful effects of ROS (Fig. 8.2). Treatment of
pathogen-challenged tomato, hot pepper and pigeon pea with fluorescent pseudomonads increased activities of POX and PPO (Ramamoorthy et al. 2002; Dutta
et al. 2008). Thus, increase in ROS-scavenging enzymes as a means of ISR can also
help the plants tolerate abiotic stresses (Fig. 8.2).
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Fig. 8.2 PGPR in mitigating ROS-mediated harmful effects. ISR induced systemic resistance, IST
induced systemic tolerance, IAA indole acetic acid, POX peroxidase, PPO polyphenol oxidase,
PGPR plant growth-promoting rhizobacteria. Production of phytohormones by PGPR induces
osmotolerance. ROS-scavenging enzyme mediated alteration of redox state helps plant tolerate
abiotic stress. Increase in proline and non-enzymatic antioxidants protect macromolecules improving plant growth under oxidative stress. PGPR resists ROS-mediated lipid peroxidation reducing
membrane destabilization
8.5.4
PGPR for Bioremediation of Soil
PGPR can alleviate soil contamination (Zhuang et al. 2007; Huang et al. 2004,
2005) through mineralization of organic compounds in association with plants
(Saleh et al. 2004). PGPR like Bacillus, Pseudomonas and Methanobacteria are
used for bioremediation of soil because of their high tolerance to heavy metals
(Milton 2007). Bacteria have been reported to remove carbon, nitrogen, phosphorus
and toxic metals aromatic compounds, herbicides and pesticides through both
aerobic and anaerobic metabolisms (Milton 2007; Zhang et al. 2003). Interaction
with other beneficial microbes like mycorrhizal fungi may contribute towards
resisting abiotic stress effects on plants (Gamalero et al. 2009; Marulanda
et al. 2009) (Fig. 8.3). Natural bioremediation of soil-polluting organic compounds
through application of bacterial and fungal isolates has been reported (Juwarkar
et al. 2010). Endophytic bacteria, such as Achromobacter xylosoxidans, Bacillus
pumilus and Corynebacterium flavescens, prevent plants from the harmful effects of
heavy metals and xenobiotics (Glick 2010). Production of pollutant-degrading
enzymes, like POX and phosphatase, contributes towards transformation of pollutants (Dowling and Doty 2009; Gerhardt et al. 2009) (Fig. 8.3). PGPR enhances the
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8 Plant Growth-Promoting Rhizobacteria for Alleviating Abiotic Stresses in. . .
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Fig. 8.3 Effect of PGPR in bioremediation. PAL phenylalanine ammonia-lyase, POX peroxidase,
ACC 1 aminocyclopropane-1-carboxylate, PGPR plant growth-promoting rhizobacteria. Production of pollutant-degrading enzymes like PAL and POX transform pollutants in soil making them
unavailable for plants. Alteration of pH in the rhizosphere and exudation pattern increases
osmotolerance and removes toxic metals through acidification of soil. Chelating agents
siderophores provide sufficient iron (Fe) to the plants reducing metal-induced toxicity. Through
aerobic and anaerobic metabolism, PGPR removes toxic metals from rhizosphere. PGPR in
combination with mycorrhiza helps in degradation of heavy metal pollutants. Plant and PGPR
work towards phytoremediation. Physical movement of PGPR from rhizoplane to rhizosphere
facilitates their binding to free metals such as Ni thereby making them unavailable for plants.
Metals are mobilized in plants through autotrophic and heterotrophic leaching and volatilization
by methylation
PAL activity in plants. This may help the plants thrive under heavy metal contamination such as nickel.
Microorganisms can affect the availability of metals in the rhizosphere by
altering the pH and by altering the redox potential (Smith and Read 1997).
Azospirillum brasilense can alter pH of the rhizosphere (Carrillo et al. 2002), and
inoculation with Azospirillum may change root physiology and patterns of root
exudation (Heulin et al. 1987) (Fig. 8.3). Chelating agents such as organic acids and
amino acids by PGPR and associated plants also help in remediation of heavy metal
soil contamination (Marchner et al. 1996). Since PGPR can change the root
exudates profile such as that of organic acids, the acidification of rhizosphere
might affect the metal availability. Tomato treated with biocontrol strain Pseudomonas fluorescens showed alteration in the composition of organic acids and sugars
in root exudates (Kamilova et al. 2006). Siderophore and ACC deaminaseproducing bacterium Kluyvera ascorbata protected canola plants from growth
inhibitory effects of high concentration of nickel by providing sufficient iron to
the plants so as to reduce the toxic effects of nickel and by reducing the nickel-
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induced stress ethylene formation (Burd et al. 1998). Also, autotrophic and heterotrophic leaching, volatilization through methylation and release of chelators can
mobilize metals (Fig. 8.3). Heavy metal availability can also be reduced due to
sorption to cell components followed by intracellular sequestration or precipitation
as insoluble organic or inorganic compounds (White and Gadd 1996). Klebsiella
mobilis-treated barley plants showed increase in grain yield and decrease of Cd
contents in grains when grown in Cd-rich soil and simulation of these effects with a
mathematical model revealed that the underlying mechanisms might be the migration of bacteria from rhizoplane to rhizosphere (Fig. 8.3) where bacteria bind to free
Cd ions forming a complex that cannot be taken up by the plant (Pishchik
et al. 2002). This indicates that the PGPR may themselves bind to heavy metals
and make them unavailable for plants, produce organic acids, chelators, etc., for
removal of heavy metals from the soil and/or may induce the plants to exude these
substances in the rhizosphere thereby altering the microenvironment to facilitate
degradation of metal pollutants (Fig. 8.3).
8.5.5
Factors Affecting Against Both Abiotic and Biotic
Stresses
PGPR exerting beneficial effects under abiotic stresses also result in ISR in plants
(Barriuso et al. 2008). The priming action during ISR by PGPR could help plants
tolerate abiotic stresses. The phenomenon of priming has not been completely
elucidated at molecular level but is associated with signaling proteins which remain
inactive under normal conditions and start accumulating and transduced in activated form when plants are exposed to stresses (Conrath et al. 2006). Studies on
gene expression in Arabidopsis thaliana treated with Paenibacillus polymyxa when
exposed to either biotic or abiotic stress showed co-regulation of genes (Timmusk
and Wagner 1999). Similar studies in rice showed the role of cold acclimation
transcription factor Osmyb4, in enhancing tolerance against both biotic and abiotic
stresses in transgenic A. thaliana (Vannini et al. 2006). Promoters of osmotins that
accumulate under abiotic stress such as salt also activate during pathogen attack
(Liu et al. 1995).
However, the regulatory mechanisms involved are very complex and can occur
in translational and post-translational levels (La Rosa et al. 1992). Xiong and Yang
(2003) confirmed the induction of an ABA-inducible mitogen-activated protein
kinase (MAPK) by both abiotic and biotic stresses and, further, tolerance against
drought, salinity and cold stress due to over expression of this gene. However,
suppression of MAPK enhances against pathogens whereas tolerance to abiotic
stresses is drastically reduced.
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8.6
185
Effect of Abiotic Stress on Secondary Metabolites
of Plants
Secondary metabolites of medicinal plants are of importance because most of the
pharmaceutically important chemicals are produced in the form of secondary
metabolites in plants. Secondary metabolites are crucial as they are important for
plant growth and development and are needed in plant defence against herbivores
and pathogens and confer protection against environmental stresses (Seigler 1998).
Secondary plant metabolites such as calcium, abscisic acid (ABA), salicylic acid
(SA), polyamines and jasmonates (JA) and nitric oxide accumulate in plants
exposed to stress, thus altering the physiology (Tuteja and Sopory 2008; Seigler
1998). Most of these chemicals have medicinal, nutritional and cosmetic value.
Drugs like morphine, codeine, cocaine and quinine; alkaloids from Catharanthus
and belladonna; colchicines, phytostigminine, pilocarpine and reserpine; and steroids like diosgenin, digoxin and digitoxin, flavonoids, phenolics, etc., are some of
the economically and industrially important secondary metabolites of plants
(Ramakrishna and Ravishankar 2011).
Abiotic stresses increase or decrease the production of secondary metabolites in
plants. Elicitation has been used to increase secondary metabolite production in
plant cell cultures under in vitro conditions (Dicosmo and Misawa 1985). However,
increase or decrease in response to abiotic stress depends on the genotype. Anthocyanins and JA are reported to increase in response to salt stress, but salt-sensitive
plants showed a decrease in anthocyanin (Daneshmand et al. 2010; Pedranzani
et al. 2003). Anthocyanins are reported to accumulate under drought and cold
temperature stress. Similarly, salt-tolerant alfalfa showed an increase in the proline
content under salt stress, but the increase was slow in salt-sensitive varieties
(Petrusa and Winicov 1997). Alteration in polyphenols and phenolic content in
response to abiotic stress has also been reported (Navarro et al. 2006; Dixon and
Paiva 1995). Similar alterations in phenolics, carotenoids and flavonoids have also
been reported in response to drought (Anjum et al. 2003). Drought induced decrease
in chlorophyll content in Catharanthus roseus and saponins in Chenopodium
quinoa (Soliz-Guerrero et al. 2002).
Influence of metal ions on secondary metabolites has been reported. Although
trace amounts of nickel (Ni) is required for plant growth, excess of Ni leads to a
decrease or inhibition in anthocyanin content (Hawrylak et al. 2007; Krupa
et al. 1996). This alteration is caused by the inhibition of PAL activity (Krupa
et al. 1996). Similarly, metal ions like Cu2+, Co2+, Zn2+ and Cd2+ stimulate the
production of betalains in Beta vulgaris (Trejo-Tapia et al. 2001), betacyanins in
callus cultures of Amaranthus caudatus, lepidine in cultures of Lepidium sativum
(Obrenovic 1990) and putrescine in oat and bean plants. However, Cd2+ and Cu2+
treatment has also been reported to reduce putrescine and spermidine content in
sunflower leaf discs (Groppa et al. 2001). Scopolamine and hyoscyamine were
elicited by silver or cadmium in cultures of Brugmansia candida (Angelova
et al. 2006).
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Variations in temperature affect the metabolite profile of plants. Low temperatures increase the synthesis of cryoprotectants, soluble sugars, phenolics, anthocyanins and nitrogenous compounds (Janska et al. 2010; Chan et al. 2010; Zhang
et al. 1997). Increase in endogenous jasmonates in Pinus pinaster and polyamines
like putrescine and spermine in carrots and alfalfa in response to low temperatures
is also reported (Pedranzani et al. 2003; Lei et al. 2004). In contrast, high temperature reduces the production of anthocyanin in Perilla frutescens suspension
cultures (Zhong and Yoshida 1993). High temperature enhanced the production
of secondary metabolites and storage ginsenoside in root of ginseng Panax
quinquefolius (Jochum et al. 2007).
8.7
Preference of PGPR over Abiotic Stress as Inducer
of Secondary Metabolites
Effect of PGPR on the secondary metabolites of plants has been documented. In
medicinal plants Artemisia annua and Centella asiatica, rhizosphere bacteria
enhanced triterpenoids (Satheesan et al. 2012; Awasthi et al. 2011). The increase
in secondary metabolite production was suggested because of increase in leaf to
stem ratio in PGPR-treated Bacopa (Bharti et al. 2013) (Fig. 8.4). Strain-specific
effect of PGPR on secondary metabolites of plants has been suggested by Walker
et al. (2011). E. oxidotolerans was also reported to increase herb yields and content
of bacoside A in plants.
Methyl jasmonates (MeJ) and JA are signaling molecules of biotic and abiotic
stresses (van der Fits and Memelink 2000). JA and MeJ elicit production of
secondary metabolites like alkaloids, terpenoid, phytoalexins, coumarins and
taxanes in plants some of which act as defence response. MeJ and growth regulators
like 2, 4-D, IAA and NAA supported growth and increased anthocyanin in treated
plants (Zhang et al. 2002; Fang et al. 1999). Anthocyanin production was also
enhanced through the manipulation of phytohormones in cell suspensions of
Ipomoea batatas (Nozue et al. 1995) and Oxalis reclinata (Makunga et al. 1997).
Alteration of phytohormones by PGPR has been reported. PGPR is reported for ISR
in plants through JA and ethylene pathway (Spoel and Dong 2012; van Wees
et al. 1999). Pieterse et al. (1998) reported that systemic resistance induced by
P. fluorescens requires responsiveness to ethylene and JA.
As precursors for JA and MeJ, the lipoxygenase (LOX) products also could be
involved in ISR (Xu et al. 1994) and secondary metabolite production. The products
of LOX pathway contribute to defence reactions by inhibition of pathogen growth
and development (Namai et al. 1990), induction of phytoalexin accumulation
and/or in signal transduction (Choi and Bostock 1994) (Fig. 8.4). The peroxidation
of polyunsaturated fatty acids (PUFAs) by LOXs could be a major source of
peroxidases in stressed plant tissue. Peroxidized fatty acids are highly reactive
and could be further metabolized to signal molecules such as jasmonates, traumatin
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Fig. 8.4 Effect of PGPR on enhancing secondary metabolites in plants. LOX lipoxygenase, ISR
induced systemic resistance, IST induced systemic tolerance, JA jasmonic acid, MeJ methyl
jasmonates, PUFA polyunsaturated fatty acids, PGPR plant growth-promoting rhizobacteria.
PGPR is known to induce systemic resistance in plants through the JA pathway which are signals
abiotic stress. ISR indirectly prepares the plants to tolerate abiotic stress. Phytohormone such as
auxins increase JA and MeJ through the precursor LOX. Peroxidation of PUFAs also produces
jasmonates affecting ISR and IST
and hexenals (Croft et al. 1993) (Fig. 8.4). Liu et al. (1991) suggested that the
auxins affect the LOX activity. PGPR are known to increase auxin in host plants
(Patten and Glick 2002), and B. subtilis has been reported to increase the hormone
levels, which in turn induce LOX (Sailaja et al. 1997). Thus, auxins produced by
PGPR could influence the LOX pathway enhancing JA and MeJ which, in turn,
could act as elicitors for increase in secondary metabolite production by plants
(Fig. 8.4). Thus, activation of JA by PGPR and production of phytohormones could
indirectly result in the production of secondary metabolites in plants besides
triggering the defence response in plants and growth promotion.
Abiotic stress has also been applied as elicitor for increasing secondary metabolites like alkaloids in medicinal plants. But plants under abiotic stress such as
salinity and water stress have reduced biomass which reduces the overall alkaloid
production. Thus, PGPR-induced increase in plant biomass with extensive root
branching and increased leaf size and area would lead to increased production of
secondary metabolites. Although abiotic stress increases some secondary metabolites, the hazardous effects on plants such as reduced chlorophyll content lead to
growth-limiting conditions. PGPR has been reported to increase chlorophyll content in plants. Dutta et al. (2005) reported that a P. fluorescens strain increased
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germination percentage, dry weight, leaf area and chlorophyll content over the
control in mung bean.
Moreover, increase in secondary metabolites production due to abiotic stress is
prevalent only at the initial stage of exposure, but PGPR induces long-term tolerance (Egamberdiyeva and Hoflich 2004). Furthermore, most of the studies indicating increase in secondary metabolites due to abiotic stress as elicitors are done
under in vitro conditions in cell cultures. The scenario may not resemble exactly
in vivo or under field conditions.
8.8
Conclusions
The positive influence of PGPR on growth and yield of plants under biotic and
abiotic stresses is well established. Although the mechanisms of action of PGPR for
plant growth improvement and disease control has been a vigorous topic of
research, complete elucidation of the interaction is yet to be accomplished. Beneficial effect of PGPR on various medicinal plants’ growth has been reported.
Studies on medicinal plants and PGPR are limited and more so under abiotic stress
conditions. The positive effect on secondary metabolite production of medicinal
plants by PGPR is also known. The mechanisms such as alteration of phytohormone
production, root morphology, ROS-scavenging enzymes and soil aggregation
which have been studied in PGPR-treated plants under abiotic stresses like drought,
salinity and soils contaminated with heavy metal indicate that the same mechanisms
may also be applicable to medicinal plants. However, detailed experimental studies
have to be done to establish the exact mechanisms involved. The application of
PGPR for improvement of growth and disease control under abiotic stress holds
promise. It needs to be exploited for sustainable improvement in growth and
production of economically important medicinal plants.
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Chapter 9
Efficiency of Phytohormone-Producing
Pseudomonas to Improve Salt Stress
Tolerance in Jew’s Mallow
(Corchorus olitorius L.)
Dilfuza Egamberdieva and Dilfuza Jabborova
9.1
Introduction
Natural salinity is the result of a long-term natural accumulation of salts in the soil
or in surface water, and it is estimated that 33 % of the potentially arable land area
of the world is affected by salinity (Ondrasek et al. 2009). Climate change will even
increase soil salinity further, since it is accompanied by less rainfall and higher
temperatures (Othman et al. 2006). Many studies have demonstrated that salinity
inhibits seed germination and growth of various agriculturally important crops,
vegetables, and also medicinally important plants (Teixeira da Silva and
Egamberdieva 2013; Egamberdieva et al. 2011, 2013a; Jamil et al. 2006; Xu
et al. 2011; Khodarahmpour et al. 2012). In aromatic and medicinal plants, growth
and synthesis of biological active compounds are influenced by various environmental factors such as salinity, drought, and water stresses (Hasegawa et al. 2000;
Parida and Das 2005). Soil salinity inhibits plant growth and the development of
Satureja hortensis and Eragrostis curvula (Colom and Vazzana 2002; Baher
et al. 2002), Citronella (Kumar and Gill 1995), Ammolei majus, and Hyoscyamus
niger (Ashraf 2004). Several explanations for these effects have been proposed,
such as inhibition of the activity of enzymes involved in nucleic acid metabolism
(Arbona et al. 2005) and inhibition of biosynthesis of plant hormones within plant
tissues (Prakash and Parthapasenan 1990). Debez et al. (2001) observed that salt
stress caused by NaCl inhibited the endogenous levels of phytohormones such as
gibberellins, abscisic acid, jasmonic acid, and salicylic acid in plants, which
correlated with a reduction of root growth in salt bush (Atriplex halimus L.).
In other study, Figueiredo et al. (2008) reported decreased levels of auxins and
gibberellins in the roots of common beans.
D. Egamberdieva (*) • D. Jabborova
Department of Biotechnology and Microbiology, National University of Uzbekistan,
University str. 1, Tashkent 100174, Uzbekistan
e-mail: egamberdieva@yahoo.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_9
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202
D. Egamberdieva and D. Jabborova
Jew’s mallow is, in the tropics and sub-tropics, among the most common plants
that thrive nearly anywhere including Middle East, Asia and Africa. The plant is
used as food ingredient, herb, and vegetable, and contains acidic polysaccharides,
proteins, calcium, thiamin, riboflavin, and dietary fibers (Leung et al. 1968; Tsukui
et al. 2004). C. olitorius is mostly distributed in arid and stress environment (Fawusi
et al. 1984; Chaudhuri and Choudhuri 1997). However its production is reduced by
high salinity and poor soil conditions (Velempini et al. 2003). It has been reported
that the plant growth and yield of jew’s mallow could be improved by Arbuscular
mycorrhizal (AM) fungi (Nwangburuka et al. 2012). It has been proposed that the
external supply of plant growth regulators produced by root-associated microorganisms under stressed conditions may help plants to cope with abiotic stress
(Li et al. 2005).
Most of the root-associated bacteria produce phytohormones such as IAA, GA,
abscisic acids, and cytokinins (Egamberdieva et al. 2001, 2004; Egamberdieva and
Hoflich 2002; Lyan et al. 2013; Jabborova et al. 2013a; Matiru and Dakora 2004;
Hayat et al. 2008). The abilities of PGPR strains to produce plant growth regulators
could balance the decrease in the phytohormone levels of the plant roots and
alleviate salt stress in plants (Egamberdieva 2009, 2013). The ameliorative effects
of PGPR on plant growth under saline conditions have been shown on various plant
species, including medicinally important plants (Yildirim and Taylor 2005;
Egamberdieva and Lugtenberg 2014). For example, Pseudomonas strains alleviated
the salinity effects on the growth of basil (Ocimum basilicum) (Golpayegani and
Tilebeni 2011), goats rue (Galega officinalis L.), and milk thistle (Silybum
marianum) (Egamberdieva et al. 2013a).
This study was conducted to evaluate the effectiveness of phytohormoneproducing Pseudomonas strain and plant growth regulators such as auxins and
gibberellins in improving growth and salt tolerance of jew’s mallow (Corchorus
olitorius L.) under saline conditions.
9.2
9.2.1
Materials and Methods
Plant and Bacteria
The seeds of jew’s mallow (Corchorus olitorius L.) were obtained from the Department of Botany, Faculty of Biology and Soil Sciences of Uzbekistan. Seeds were
sorted to eliminate broken, small, and infected seeds. Seeds were surface-sterilized
by immersing them for 1 min in concentrated 10 % v/v NaOCl, followed by 3 min in
70 % ethanol, and rinsed five times with sterile, distilled water. The sterility of seeds
was tested on Nutrient agar by incubating plates for 3 days at 28 C.
The salt-tolerant bacterial strain Pseudomonas extremorientalis TSAU6, which
produces IAA under saline conditions (7.4 μg/ml) and GA (0.4 μg/ml) was obtained
from the culture collection of National University of Uzbekistan. The strain
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9 Efficiency of Phytohormone-Producing Pseudomonas to Improve Salt. . .
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Pseudomonas fluorescens WCS365, which doesn’t produce IAA, was obtained
from the culture collection of Leiden University of the Netherlands.
9.2.2
Germination and Seedling Growth
Seed germination was carried out in 85 mm 15 mm tight fitting plastic petri
dishes with 5 ml solution consisting of 0 and 100 mM NaCl. Ten healthy and
uniform seeds were sown in each petri plate with three replicates. A filter paper
(Whatman No. 2) was soaked in a solution of the respective salt concentrations. To
determine the effects of plant growth regulators on seed germination and seedling
growth, auxins (IAA) and gibberellic acid (GA) were used at 1 and 0.1 and 0.01 and
0.001 μM concentrations under nonsaline and saline (100 mM NaCl) conditions.
Bacterial strains Pseudomonas fluorescens WCS365 and Pseudomonas
extremorientalis TSAU6 were grown overnight in KB broth. 1 ml of each culture
was pelleted by centrifugation, and the supernatant was discarded. Cell pellets were
washed with 1 ml phosphate buffered saline (PBS, 20 mM sodium phosphate,
150 mM NaCl, pH 7.4) and suspended in PBS. Cell suspensions were diluted to
an optical density of 0.1 at 620 nm, corresponding to a cell density of 108 cells/ml.
Seeds were placed in the bacterial suspension using sterile forceps and shaken
gently for a few seconds. After 10 min, the inoculated seeds were then aseptically
placed into petri dishes moistened with water, with 100 mM NaCl solution. All
germinations were carried out in a plant growth chamber at 28 C. The lengths of
roots and shoots of the germinated seeds which were more than 0.2 mm in length
were measured and recorded after 5 days.
9.2.3
Plant Growth in Gnotobiotic Sand Tubes
The effect of seed inoculation with IAA- and GA-producing Pseudomonas
extremorientalis TSAU6 and Pseudomonas fluorescens WCS365 on the growth
of jew’s mallow seedlings exposed to salt stress (100 mM NaCl) was studied under
gnotobiotic conditions. Experiments were carried out in test tubes (25 mm in
diameter, 200 mm in length) as described by Simons et al. (1996). The tubes
contained 60 g of sterilized high-quality sand (quartz sand 0.1–0.3 mm), which
was treated with 10 % Plant Nutrient Solution (PNS) (Kuiper et al. 2001). Salinity
conditions were established by adding 100 mM NaCl into the nutrient solution.
Bacterial inoculants were grown and prepared, and the sterilized seeds were
inoculated as described above. Inoculated seeds were planted into sterile glass
tubes, one seed per tube with three replicates. The seedlings were grown in a
growth cabinet with a 16-h light period at 22 C and an 8-h dark period at 16 C.
At harvest after 18 days, the length of the shoots and roots and the fresh weight of
whole plants were measured.
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9.2.4
D. Egamberdieva and D. Jabborova
Plant Growth in Saline Soils
The effect of Pseudomonas strain on plant growth of jew’s mallow under saline soil
conditions was conducted in plastic pots (12-cm diameter, 15-cm deep). The soil
has an EC value of 685 mS m 1 and contains 43 9 g sand/kg, 708 12 g silt/kg,
and 249 13 g clay/kg. The organic matter content of the soil is 0.694 %; total N,
0.091 %; Ca, 63.5 g/kg; Mg, 20.7 g/kg; K, 6.2 g/kg; P, 1.2 g/kg; Cl, 0.1 g/kg; and
Na, 0.7 g/kg, and the pH is 8.0.
The plant seeds were sterilized, allowed to germinate, and coated with bacteria
as described above, and the inoculated seedlings were planted in the plastic pots.
The inoculation treatments were set up in a randomized design with ten replications. The pot experiment had two treatments: seeds noninoculated with bacteria,
and the seeds inoculated with bacteria. Plants were grown at 19–22 C during the
day and 10–11 C at night, and after 8 weeks the shoot and root length and dry
matter of jew’s mallow were measured.
9.2.5
Statistical Analysis
Data were tested for statistical significance using the analysis of variance package
included in Microsoft Excel 2007. Mean comparisons were conducted using a least
significant difference (LSD) test (P < 0.05). Standard error and an LSD result were
recorded.
9.3
9.3.1
Results and Discussions
Microbial Plant Growth Stimulation
Seed germination is usually the most critical stage in seedling establishment
(Almansouri et al. 2001). In this study, salinity (100 mM NaCl) inhibited the
germination of jew’s mallow seeds by 30 %. Salt-exposed plants exhibited a
reduction in shoot and root growth and biomass compared to control plants. NaCl
reduced root length by 25 %, shoot length by 20 %, and plant’s fresh weight by
25 %. The present result agrees with the work of Gandour (2002) and Vadez
et al. (2007) where they observed decreases in percentage germination and seedling
emergence of chickpea with increases in salinity. Atak et al. (2006) and
Neamatollahi et al. (2009) pointed out that higher saline condition may reduce
germination percentage due to higher osmotic pressures. Ashraf (2004) found that
increasing salt concentrations caused a significant reduction in the shoot and root
growth as well as seed yield of Ammolei majus and Hyoscyamus niger. Similar
results were observed by Razmjoo et al. (2008), where increased salinity and
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9 Efficiency of Phytohormone-Producing Pseudomonas to Improve Salt. . .
205
drought stress caused reduction in the fresh and dry flower weight and essential oil
content of Matricaria chamomila.
It has been reported that salinity reduces the recovery of diffusible auxins from
maize coleoptile tips (Itai et al. 1968). It has been suggested that plants might
benefit from external supply of plant growth regulators under stressed conditions
(Li et al. 2005).
The root-associated bacteria which produce various phytohormones such
as auxins, gibberellins, and cytokinins may help plants to cope with salt stress
(Egamberdieva and Tulyasheva 2007; Yue et al. 2007; Egamberdieva et al. 2012).
In this study, bacterial strains which produce IAA and GA were also able to
alleviate salt stress in plants and improve seed germination of jew’s mallow
(up to 90 %). They also did reverse the growth-inhibiting effect of salt stress to a
certain extent in both shoot and root. The IAA-producing strain P. extremorientalis
TSAU6 significantly improved root length (66 %), shoot length (43 %), and fresh
weight of plants (11 %) under nonsaline conditions, whereas strain P. fluorescens
WCS365, which doesn’t produce IAA, stimulated root and shoot length and fresh
weight by 8, 25, and 6 %, respectively (Fig. 9.1a, c).
The inoculated jew’s mallow seeds with P. extremorientalis TSAU6 significantly increased jew’s mallow seedling root growth up to 45 % and shoot growth up
to 84 % at 100 mM NaCl compared to control plants (Fig. 9.1b, c). The strain
P. fluorescens WCS365 was not able to stimulate plant growth under salt stress
conditions. There are many reports on the role of phytohormones in changes of root
morphology exposed to drought, salinity, temperature, and heavy metal toxicity
(Spaepen et al. 2008; Spaepen and Vanderleyden 2010).
In our previous works, we have observed that IAA-producing root-associated
bacteria increase root growth, development, and yield of various agricultural crops
such as soybean, cotton, wheat, maize, cucumber, and pea (Egamberdieva and
Hoflich 2003; Jabborova et al. 2013b; Berg et al. 2010; Egamberdieva and
Jabborova 2012, 2013a, b). These results agree with Heidari et al. (2011) who
reported that the plant growth and auxin and protein contents of Ocimum basilicum
inoculated by Pseudomonas sp. under drought stress conditions were increased
compared to the control. Those reports demonstrated that phytohormones play a
major role in improving plant growth and development under saline conditions.
9.3.2
The Effect of Phytohormones on Plant Growth
We also determined the effect of individual phytohormones such as auxins and
gibberellins on the plant growth of jew’s mallow and development under saline
conditions. We observed that seed dormancy enforced by salinity was substantially
alleviated and germination was promoted by gibberellins and auxins from 80 to 95 %
(data not shown). This finding agrees with other studies in which GA and IAA
improved the emergence of rice (Wahyuni et al. 2003), wheat seedlings (Egamberdieva
2009), radishes (Egamberdieva 2008), brinjal (Solanum melongena L.) (Gupta 1971),
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a
Root, shoot length, cm
3.0
Root
Shoot
*
2.0
1.0
0.0
Control
WCS365
0 mM NaCl
TSAU6
b 3.0
*
Root
Root, shoot length, cm
Fig. 9.1 Effect of
inoculation of jew’s mallow
(Corchorus olitorius L.)
seedlings with
Pseudomonas
extremorientalis TSAU6
(produce IAA and GA) and
Pseudomonas fluorescens
WCS365 (doesn’t produce
IAA and GA) on (a) length
of roots, (b) length of
shoots, and (c) fresh weight
of whole plants. The
seedlings were grown in
petri plates with 0 mM and
100 mM NaCl solution.
Columns represent means
for five seedlings (N ¼ 5)
with error bars showing
standard error. Columns
with different letters
indicate significant
differences between
treatments at P < 0.05
(Tukey’s t-test)
D. Egamberdieva and D. Jabborova
Shoot
2.0
1.0
0.0
Control
Fresh weight, g/plant
c
WCS365
100 mM NaCl
TSAU6
0.04
0.03
0 mMNaCl
100 mMNaCl
*
0.02
0.01
0.00
Control
WCS365
TSAU6
chayote (Sechium edule) (Gregorio et al. 1995), and red sanders (Pterocarpus
santalinus Linn. F) (Naidu 2001). In previous works, several plant growth regulators
such as gibberellins (Afzal et al. 2005), auxins (Khan et al. 2004), and cytokinins
(Gul et al. 2000) have been shown to alleviate salinity stress in plants. All concentrations of IAA and GA showed stimulatory effect on the root and shoot growth of
jew’s mallow seedling under nonsaline and salt stress conditions (Fig. 9.2a–c).
mkumar9@amity.edu
9 Efficiency of Phytohormone-Producing Pseudomonas to Improve Salt. . .
a
6.0
Root
Shoot
*
Root, shoot length, cm
5.0
*
*
4.0
*
*
*
3.0
*
2.0
1.0
0.0
Control
1 mM
0.1 mM
0.01 mM 0.001 mM
IAA concentrations, 0 mM NaCl
b
6.0
Root
Shoot
Root, shoot length, cm
5.0
*
*
*
*
*
4.0
*
*
3.0
2.0
1.0
0.0
Control
c 0.04
Fresh weight, g/plant
Fig. 9.2 The effect of
various concentrations of
IAA on the seedling growth
of jew’s mallow (Corchorus
olitorius L.): (a) length of
roots, (b) length of shoots,
and (c) fresh weight of
whole plants. The seedlings
were grown in petri plates
with 0 mM and 100 mM
NaCl solution. Columns
represent means for five
seedlings (N ¼ 5) with error
bars showing standard
error. Columns with
different letters indicate
significant differences
between treatments at
P < 0.05 (Tukey’s t-test)
207
1 mM
0,1 mM 0,01 mM 0,001 mM
IAA concentrations, 100 mM NaCl
0 mMNaCl
0.03
*
* *
*
0.02
0.01
0.00
Control
1 mM
0,1 mM 0,01 mM 0,001 mM
IAA concentrations
mkumar9@amity.edu
208
D. Egamberdieva and D. Jabborova
We have also observed that GA stimulated the root and/or shoot growth of jew’s
mallow seedling at concentrations 0.1, 0.01, and 0,001 mM under nonsaline and
saline conditions (Fig. 9.3a–c). Lin and Kao (1995) reported that the application of
growth regulators such as GA3 and cytokinin on rice seedlings improved seedling
growth. Similar results were observed by Gul et al. (2000), where gibberellic acid
and zeatin alleviate the effect of salinity on germination and growth of Ceratoides
lanata, Salicornia pacifica, and Allenrolfea occidentalis (Khan et al. 2004). Under
both nonsaline and saline conditions, lower concentrations of GA (0.1, 0.01, and
0.001 mM) showed higher stimulatory effect compared to control plants. Similar
findings were reported by Remans et al. (2007), where low concentration of pure
IAA or low titer of IAA-producing bacteria enhanced root growth.
Javid et al. (2011) reviewed the importance of IAA, cytokinins, and gibberellic
acid in ameliorating salt stress in various plants. It is also suggested that IAA
enhanced different cellular defense systems for protecting plants from external
abiotic stresses (Bianco and Defez 2010).
9.3.3
Plant Growth in Gnotobiotic Sand System
and Saline Soil
The growth-promoting effect of IAA- and GA-producing P. extremorientalis
TSAU6 strain was also studied by growing inoculated salt-stressed jew’s mallow
seedlings for 18 days in a gnotobiotic sand system and 8 weeks in pots with saline
soil. The presence of NaCl clearly impaired the plant growth of jew’s mallow
seedlings. At 100 mM, the length of root, length of shoot, and fresh weight of whole
plants were inhibited by 54, 59, and 45 % than those of nonstressed seedlings. The
coinoculation of salt-stressed jew’s mallow exposed to 100 mM NaCl with
P. extremorientalis TSAU6 significantly improved fresh weight of plants
(on average by 35 %), length of shoots (by 42 %), and length of roots (by 50 %).
Also under nonstressed conditions, the addition of Pseudomonas strain significantly
enhanced root and shoot growth compared to uninoculated control plants.
Plant growth-promoting properties of the strain in pot experiments with saline
soil showed that P. extremorientalis TSAU6 significantly increased shoot length by
21 % and dry matter by 18 % (data not shown). These results were somewhat
similar to those obtained by Golpayegani and Tilebeni (2011) in which salinity
decreased plant growth, photosynthesis, and chlorophyll content of basil, whereas
Pseudomonas sp. alleviated the effects of salinity on plant growth. In our previous
work, we have also observed that IAA-producing Pseudomonas strains promoted
the enlargement of root system, enhancing nutrient uptake, and growth of goat’s rue
(Galega officinalis) (Egamberdieva et al. 2013a) and milk thistle (Silybum
marianum) (Egamberdieva et al. 2013b) grown in a salt-affected soil. Similar
observations were reported by other authors in which Pseudomonas fluorescens
stimulated the growth and yield of Catharanthus roseus under drought stress (Attia
mkumar9@amity.edu
9 Efficiency of Phytohormone-Producing Pseudomonas to Improve Salt. . .
a 6.0
Root
Shoot
Root, shoot length, cm
5.0
4.0
*
*
*
*
*
*
3.0
*
2.0
1.0
0.0
Control
b 6.0
1 mM
0,1 mM 0,01 mM 0,001 mM
GA concentrations, 0 mM NaCl
Root
Shoot
Root, shoot length, cm
5.0
*
*
*
4.0
3.0
2.0
1.0
0.0
Control
c 0.04
Fresh weight, g/plant
Fig. 9.3 The effect of
various concentrations of
GA on the seedling growth
of jew’s mallow (Corchorus
olitorius L.): (a) length of
roots, (b) length of shoots,
and (c) fresh weight of
whole plants. The seedlings
were grown in petri plates
with 0 mM and 100 mM
NaCl solution. Columns
represent means for five
seedlings (N ¼ 5) with error
bars showing standard
error. Columns with
different letters indicate
significant differences
between treatments at
P < 0.05 (Tukey’s t-test)
209
1 mM
0,1 mM 0,01 mM 0,001 mM
GA concentrations, 100 mM NaCl
0 mMNaCl
100 mMNaCl
0.03
*
*
*
*
* *
0.02
0.01
0.00
Control
1 mM
0,1 mM 0,01 mM 0,001 mM
GA concentrations
mkumar9@amity.edu
210
D. Egamberdieva and D. Jabborova
and Saad 2001; Jaleel et al. 2007). Karthikeyan et al. (2010) reported that PGPR
strains Pseudomonas significantly increased plant height, root length, root girth,
and alkaloid content in Madagascar periwinkle (Catharanthus roseus) relative to
the control.
9.4
Conclusions
The results presented here make it possible to recommend root-colonizing, phytohormone-producing P. extremorientalis TSAU to improve the growth of jew’s
mallow under saline soil conditions. It is also indicated that plant growth regulators,
such as auxins and gibberellins, considerably alleviated salinity stress in plants and
stimulated their growth and development.
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mkumar9@amity.edu
Part III
Biological Control
mkumar9@amity.edu
Chapter 10
Ecological Manipulations of Rhizobacteria
for Curbing Medicinal Plant Diseases
S.K. Singh and Rakesh Pathak
10.1
Introduction
Plants that possess therapeutic properties on the animals or plant body are generally
designated as medicinal plants. It is estimated that about 80 % population of the
developing countries relies on traditional medicines derived from plants or plant
extracts (Farnsworth 1994; Jamil et al. 2007). Naturally occurring soil bacteria that
colonize plant roots and have beneficial effects on plant growth are known as plant
growth-promoting rhizobacteria (PGPRs) (Vessey 2003). Some of these PGPRs can
also enter the root interior and establish as endophytes (Gray and Smith 2005).
Many of them are able to enter through the endodermis and establish in the stem,
leaf, and other plant parts (Hallmann et al. 1997; Compant et al. 2005). Ultimately
an intimate relationship between bacteria and host plant is formed without harming
the plant, and they may originate from other sources like phyllosphere, ethnosphere,
or spermosphere (Hallmann et al. 1997). The mechanism by which PGPR interact
with plants includes production of siderophores, phytochrome-induced resistance,
associative nitrogen fixation, solubilization of nutrients, depleting heavy metals,
and removal of pollutants (Glick et al. 1999).
10.2
Rhizobacteria Curbing Medicinal Plant Diseases
Atropa belladonna commonly known as Belladonna belongs to the family
Solanaceae. Belladonna is a perennial herbaceous plant. The leaf and root are
used to make medicine. The active constituents in Atropa belladonna are atropine,
hyoscyamine, and scopolamine (Hartmann et al. 1986; Rita and Animesh 2011). It
is used as a sedative and for treatment of whooping cough, bronchial asthma, hay
fever, and Parkinson’s disease and as a painkiller (Adler 2008; Moulton and Fryer
2011). Major biotic constraints are Phytophthora rot (Middleton 1943) and leafy
S.K. Singh (*) • R. Pathak
Central Arid Zone Research Institute, Indian Council of Agricultural Research, Jodhpur,
Rajasthan, India
e-mail: sksingh1111@hotmail.com; pathakjodhpur@gmail.com; pathakjodhpur@hotmail.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_10
mkumar9@amity.edu
217
218
S.K. Singh and R. Pathak
gall formation by the bacterium Rhodococcus fascians (Goethals et al. 2001; Nouar
et al. 2003). Cinchona spp. (C. pubescens, C. officinalis, C. rubra) better known as
Cinchona belongs to the family Rubiaceae. Significant phytochemicals are alkaloids, cinchonain, cinchonidine, cinchonine, quinicine, quinine, and quinidine
on et al. 2009; Buchberger et al. 2010). It is an
(Staba and Chung 1981; Pach
important ingredient in medicines to treat malaria (Willcox 2011). Cinchona bark
stimulates saliva and gastric juice secretion and possesses health properties like
antiarrhythmic, antimalarial, antiparasitic, antiprotozoal, antispasmodic, and cardiotonic (Bareness et al. 2006; Rojas et al. 2006). Phytophthora cinnamomi and
Phytophthora quininea cause stem canker, root rot, and dieback in cinchona
(Crandall 1950; Hee et al. 2013).
Plectranthus barbatus commonly known as Coleus forskohlii, forskolin, Indian
coleus, and false boldo belongs to the family Lamiaceae or Labiatae mint family.
The roots contain forskolin which is the active component that activates cellular
enzymes and used as a cardiotonic, digestive, and stimulant. It is found in many
herbal diet pills and traditionally used to treat high blood pressure, lose weight,
lower cholesterol, and improve the immune system. Some of the biotic production
constraints of Coleus forskohlii are Fusarium wilt caused by Fusarium oxysporum
(Zheng et al. 2012) and root rot/wilt (a complex problem involving Fusarium
chlamydosporum and Ralstonia solanacearum) (Singh et al. 2012). Plants treated
with arbuscular mycorrhizal fungus (Glomus fasciculatum), neem cake, or PGPR
Pseudomonas fluorescens showed significantly reduction in the disease incidence
and increased forskolin yield (Das et al. 2012).
Withania somnifera, a useful herb of the family Solanaceae, is commonly known
as ashwagandha or Indian ginseng. The name ashwagandha is from the Sanskrit
language and is a combination of the word ashva, meaning horse, and gandha,
meaning smell. The root has a strong aroma that is described as “horselike.” The
root and berry are used to make medicine. Withanolides from the roots are the main
chemical constituent of medicinal significance (Manwar et al. 2012). It is used for
the treatment of ulcers, arthritis, anxiety, insomnia, tumors, tuberculosis, asthma,
and leukoderma and as a sex stimulant and important component of DPT vaccine
(Gautam et al. 2004; Bhatnagar et al. 2005; Rasool and Varalakshmi 2006; Singh
et al. 2013). Leaf blight disease caused by the fungus Alternaria dianthicola (Militi
et al. 2012); root knot/wilt complex caused by soilborne pathogens Fusarium
chlamydosporum, Ralstonia solanacearum, and Meloidogyne incognita (Mallesh
et al. 2009); and root rot caused by Fusarium solani (Bharti et al. 2013) are the
major yield constraints of W. somnifera.
Foliar application of a talc-based formulation of PGPR Pseudomonas
aeruginosa strain WS-1 to field-grown W. somnifera reduced disease severity by
80 % compared to non-treated control (Militi et al. 2012). PGPR-treated plants
provided extended protection against soilborne pathogens Fusarium
chlamydosporum, Ralstonia solanacearum, and Meloidogyne incognita, causing
root knot/wilt complex, in Coleus forskohlii and W. somnifera (Mallesh et al. 2009).
Soil application of a commercial formulation of PGPR Pseudomonas fluorescens
resulted in the lowest root-knot nematode M. incognita population accompanied
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with highest economic yield in W. somnifera and Cassia angustifolia
(Ramakrishnan and Senthilkumar 2009). Combined applications of PGPR
P. fluorescens and chemical resistance inducers reduced root rot severity by
85 and 88 % and enhanced root yields by 358 and 419 %, respectively, against
Fusarium solani-induced root rot disease in W. somnifera. Reduction in disease
severity was correlated with defense-related enzymes peroxidase, polyphenol oxidase, and phenyl ammonium lyase (Bharti et al. 2013).
Panax ginseng is also known by its common names: American ginseng, Asiatic
ginseng, Chinese ginseng, five fingers, Japanese ginseng, Korean ginseng, ninjin,
oriental ginseng, schinsent, seng and sang, tartar root, and Western ginseng. The
roots contain triterpenoid saponins referred to collectively as ginsenosides or
panaxosides. It is used by the patients suffering from anemia, diabetes, gastritis,
neurasthenia, erectile dysfunction, and asthma.
Dioscorea spp. (D. villosa, D. opposita, D. hypoglauca, D. macrostachya,
D. barbasco) belonging to the family Dioscoreaceae are commonly known as
wild yam, colic root, devil’s bones, China root, yam, yuma, shan yao, etc. Wild
yam is a long perennial vine. The primary active chemical agent in wild yam is the
steroidal saponin diosgenin which is a primary source for the important female sex
hormone progesterone. Diosgenin is present in the rhizomes and roots of the wild
yam as dioscin, which is a steroidal saponin whose aglycone is diosgenin. In
addition to their benefits as a healthy vegetable, some species of wild yam are
also cultivated for their medicinal and healing values for diseases such as rheumatic
arthritis, biliary colic, irritable bowel syndrome, menopausal symptoms, whooping
cough, spasms, urinary tract disorders, hypocholesterolemia, menstrual cramps, and
pregnancy-related nausea among many others (Hou et al. 2001; Son et al. 2007).
Helminthosporium or Cercospora leaf spots were reported to infect Dioscorea
sp. (Chandel 2012).
Glycyrrhiza glabra also known as mulethi, jeshthamadh, licorice, liquorice, and
sweet licorice belongs to the family Fabaceae. Rhizome contains saponin
glycyrrhizin used in treating cervical cancer, kidney and bladder disorders, HIV,
hepatitis B, asthma, ulcers, and arthritis (Roshan et al. 2012). Leaf spot diseases
caused by Nigrospora, Cylindrosporium, and Phyllosticta are important diseases
(Paul and Bhardwaj 1992; Bharat et al. 2002; Verma and Gupta 2008).
Hyoscyamus niger known as black henbane that belongs to the family
Solanaceae is a medicinal herb. The leaves and seeds are the parts medicinally
used. Chemically henbane is hyosciamia. It is considered better than opium, as it
does not produce constipation. Combined with other preparations, it is used for
gout, rheumatism, asthma, chronic cough, and neuralgia and has strong analgesic
effects (Ghosian et al. 2012). The plant contains the anticholinergic tropane alkaloids (atropine, scopolamine, and hyoscine) (Hashimoto et al. 1991; Eeva
et al. 1998). Root infections by Rhizoctonia solani alone and in combination with
Meloidogyne incognita are major threats to Hyoscyamus niger cultivation (Kumar
et al. 2004).
Papaver somniferum a member of the Papaver family is the species of plant from
which opium and poppy seeds are derived. Opium is the source of narcotics,
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namely, morphine, thebaine, codeine, papaverine, and noscapine. Morphine is
prescribed for relief of severe pain (Singh et al. 2000; Hindson et al. 2007; Baros
et al. 2012). Opium is also used for pain relief and sedation and as an antioxidant
(Gülcin et al. 2004; Gotti 2011; Njoku et al. 2011).
The crop is attacked by various fungal, bacterial, and viral pathogens. Among
fungal diseases downy mildew, damping-off, collar rot (Rhizoctonia solani), wilt
(Fusarium solani), and soft rot (Pectobacterium carotovorum) are the most important (Kishore et al. 1985; Sattar et al. 1995, 1999; Aranda and Montes-Borrego
2008).
Catharanthus roseus commonly known as periwinkle is an herb that belongs to
the family Dogbane. The aboveground parts are used to make medicine. Active
constituents include alkaloid, carbohydrate, flavonoid, tannin, and steroid (Edwin
et al. 2008; Siddiqui et al. 2010). The ajmalicine content and biomass in C. roseus
increased due to P. fluorescens treatment under water deficit stress (Jaleel
et al. 2007). It is used for improving brain health, tonsillitis, sore throat, and for
blood purification (Islam et al. 2009; Siddiqui et al. 2010). Within periwinkle
plants, phytoplasmas induce symptoms such as leaf yellowing, growth aberrations
(proliferations, internode shortening, stunting), flower malformations, and/or
decline (Perica et al. 2007; Chaturvedi et al. 2009).
Plantago major also known as greater plantain, common plantain, rattail plantain, and way-bread is a member of the Plantaginaceae family. It is an herbaceous
common garden perennial weed. It contains salicylic, citric, and caffeic acid,
mucilage, tannins, proteins, flavonoids, vitamin C, dietary fiber, and potassium
(Samuelsen 2000). The plant is diuretic and is used to treat gastroenteritis, asthma,
cancer, bladder dysfunctions, etc. (Gomez-Flores et al. 2000). Aqueous extracts of
P. major inhibited Mycobacterium tuberculosis (Gautam et al. 2007). Fungal
diseases caused by Cercospora plantaginis, Septoria plantaginis, and Phyllosticta
plantaginis and little leaf disease (Witches broom) caused by phytoplasma are
major biotic constraints (Farr et al. 1995; Samad et al. 2002; Josic et al. 2012).
Podophyllum peltatum commonly called Indian apple, mayflower, umbrella
plant, or mayapple is an herbaceous perennial plant in the family Berberidaceae.
The root and rhizome are used for medicinal purpose. It is used for the removal of
warts and oral hairy leukoplakia and in the treatment of gynecologic infections and
is an anticancer agent (Beutner and Vonkrough 1990; Dwivedi and Dwivedi 2008).
Rauwolfia serpentina also known as sarpagandha belongs to the family
Apocynaceae and is a climbing evergreen shrub. Roots possess active alkaloid
reserpine, rescinnam, ajmalicine, rescinnamine, yohimbine, and serpentine (Chopra
et al. 1980). It is used as a sedative and in the treatment of hypertension, insomnia.
Among major diseases are leaf spot caused by Cercospora rauwolfia, Alternaria
tenuis, and Rhizoctonia solani and mosaic and root knot; pyralid caterpillar and
cockchafer grubs are important insect pests (Mohanthy and Addy 1957; Ganguly
and Pandotra 1962; Parashurama and Shivanna 2013).
Cassia angustifolia known by its common names Indian senna, Tinnevelly
senna, Cassia senna, and Alexandrian senna is an herb of the family Fabaceae.
Leaves and fruits are of medicinal importance. It contains mannitol, sodium,
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potassium, tartrate, salicylic acid, volatile oils, resins and calcium oxalate, and
chrysophanic acid. Senna is considered to be a laxative and used for the treatment of
typhoid, cholera, jaundice, gout, rheumatism, tumors, and bronchitis (Sastry
et al. 2000; Pandikumar et al. 2011; Mehrafarin et al. 2012). The seeds are used
as an anthelmintic and digestive and to treat piles, skin diseases, and abdominal
troubles (Srivastava et al. 2010). Major diseases of Senna include Alternaria blight
(caused by Alternaria alternata) (Tetarwal et al. 2008; Rai and Tetarwal 2010).
Like other cultivated plants, these medicinal plants are also attacked by a few or
more fungal, bacterial, viral, and/or nematode diseases and insect pests. Biological
control of the insect pests and diseases such as root rots caused by the species of
Phytophthora and Rhizoctonia; wilts by Fusarium; leaf blights and spots by
Ralstonia, Alternaria, Helminthosporium, Cercospora, Septoria, Nigrospora, and
Phyllosticta; leafy gall by the bacterium Rhodococcus fascians; soft rot by
Pectobacterium carotovorum; and nematode root knot by the species of
Meloidogyne reported by the application of PGPRs in other cultivated plants can
also be allied to manage sustainable cultivation of medicinal plants.
10.3
Investigating Plant-Microbe Interaction
The alternative approaches like investigating plant-microbe interactions with
medicinal plants and to produce enhanced levels of phytochemicals have recently
been reviewed (Sekar and Kandavel 2010; Singh et al. 2013). A thin layer of soil
surrounding plant roots and active area of root activity and metabolism is known as
the rhizosphere. Plant-microbe interactions can be negative, positive, or neutral.
PGPR have positive interactions and affect plant growth directly or indirectly. In
indirect mode, it prevents the harmful effects of phytopathogenic microorganisms,
whereas direct effects are by facilitating the uptake of nutrients.
Certain species belonging to PGPR genera Pseudomonas, Azospirillum, Azotobacter, Bacillus, Burkholderia, Enterobacter, Rhizobium, Erwinia, Mycobacterium, Mesorhizobium, Flavobacterium, Klebsiella, Alcaligenes, Arthrobacter, and
Serratia have been reported to exhibit plant growth-promoting activities by a
variety of mechanisms (Saharan and Nehra 2011; Singh 2013).
PGPR enhance plant growth by suppression of phytopathogens by producing
siderophores that chelate iron that makes it unavailable to pathogens. Under scarcity
of bioavailable iron, PGPR produce low molecular weight compounds called
siderophores. They are small, high-affinity iron-chelating compounds secreted by
microorganisms (Neilands 1995). PGPR convert iron from mineral phase by
converting them to soluble ferric complexes that are absorbed by the plants.
The bacteria belonging to Pseudomonas, Enterobacter, Bacillus, and Rhodococcus
produce siderophores and suppress phytopathogens (Tian et al. 2009). Some PGPR
draw iron from heterologous siderophores produced by other microorganisms
(Loper and Henkels 1999; Whipps 2001). Siderophore-mediated antagonism against
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S.K. Singh and R. Pathak
species of Aspergillus, Colletotrichum, and Fusarium by Acinetobacter calcoaceticus
has been observed (Prashant et al. 2009).
PGPRs have the capacity to synthesize antifungal metabolites such as antibiotics, fungal cell wall-degrading enzymes, hydrogen cyanide, etc. which suppress
the growth of fungal pathogens. Nowak-Thompson et al. (1994) reported that
P. fluorescens suppress the growth of phytopathogenic fungi by production of
2,4-diacetylphloroglucinol. Certain PGPRs have specific mechanism to suppress
or even prevent phytopathogens, e.g., by degrading fusaric acid produced by
Fusarium spp. (Toyoda and Utsumi 1991), by lysis of fungal mycelium by
P. stutzeri (Mauch et al. 1988), by rapid colonization of rhizosphere and available
nutrition otherwise to be utilized by plant pathogens (Dowling and O’Gara 1994),
and by production of volatile compounds (Hassanein et al. 2009). They exhibit
antifungal activities against Rhizoctonia solani, R. bataticola, F. oxysporum, and
Macrophomina phaseolina and root-knot nematodes (Pal et al. 2000; Siddiqui
et al. 2005).
PGPR also increases plant growth by changing the structure and composition of
microbial community in rhizosphere (Piromyou et al. 2011). Detoxification and
degradation of virulence factor of the pathogens by PGPR is another mechanism of
biological control of phytopathogens (Zhang and Birch 1996). Of late it has been
discovered that certain PGPR quench pathogen quorum-sensing capacity by
degrading autoinducer signals, thereby blocking expression of virulence genes
(Molina et al. 2003; Dong et al. 2004).
Endophytic bacteria colonize the internal tissue of the plant showing no external
sign of infection or deleterious effect on host (Schulz and Boyle 2006). The
bacterial endophytes are potential PGPRs and can form symbiotic, mutualistic,
commensalistic, and/or trophobiotic relationships with their host plants. Most of the
endophytes colonize in rhizosphere or phyllosphere, or some may be transmitted
through the seeds. Their ability to control or suppress plant pathogens, insects, and
nematodes has been demonstrated (Krishnamurthy and Gnanamanickam 1997;
Hallmann et al. 1998; Azevedo et al. 2000; Ryan et al. 2008). It has been shown
that prior inoculation with endophytes can reduce diseases caused by fungi, bacteria, and virus (Sturz et al. 2000; Berg and Hallmann 2006).
10.4
Induced and Acquired Systemic Resistance
Induced systemic resistance (ISR) or systemic acquired resistance (SAR) is defined
as the activation of chemical or physical defense mechanism of the host plant by an
inducer leading to the control of several pathogens (Kloepper et al. 1992). Application of mixture of different PGPRs to the seeds or seedlings of certain plants has
regulated in increased efficiency of ISR against several pathogens (Ramamurthy
et al. 2001). ISR against yellow mosaic Potyvirus upon seed bacterization with
P. fluorescens and Rhizobium leguminosarum has been achieved with significant
reduction in percent disease incidence in faba beans (Elbadry et al. 2006). Several
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PGPR traits and metabolites have been shown to trigger ISR such as volatile
secreted by B. subtilis (Ryan et al. 2001), salicylic acid (SA) independent pathways
involving jasmonate and ethylene signals (Pieterse et al. 1998; Pettersson and Baath
2004), thickening of cortical cell wall (Duijff et al. 1997), accumulation of phenolic
compounds at the site of pathogen attack (M’Piga et al. 1997), and induced
accumulation of pathogenesis-related proteins (PR-proteins) (Park and Kloepper
2000).
Nevertheless, there are several constraints in using PGPRs indiscriminately:
(1) The interaction between associative PGPR and plant can be unstable. The
good result obtained in vitro can always not be dependably reproduced under
field conditions (Chanway and Holl 1993). (2) Some failures derived from the use
of bio-fertilizers containing PGPRs may be due to interspecific genetic interactions
by the rhizobacteria and the host plant, i.e., different cultures and plant species may
produce different types of root exudates which may or may not support PGPRs to
produce biologically active substances required to promote plant growth or suppress phytopathogens. (3) Major constraints of massive commercial use of PGPRs
are regarding registration and marketing of products of PGPRs (Mathre et al. 1999).
(4) Currently, bio-fertilizers with PGPR are still not a reality of extensive commercialization due to lack of consistent response in different host cultivars (Remans
et al. 2008). (5) Dry powder-based commercial formulations often lack appropriate
shelf life and cell viability (Johri et al. 2003).
Having learnt from the constraints and with the advent and excess to modern
biotechnological tools and techniques, there are opportunities to develop, explore,
and/or exploit: (1) Stable formulations of antagonistic PGPRs in sustainable agricultural system to replace the use of chemical fertilizers. (2) Eco-friendly
biopesticides derived from microorganisms. (3) Soil microbial diversity for
PGPRs having combination of plant growth-promoting activities and well adapted
to particular soil environment. (4) Multi-strain inocula of PGPR with multiple
modes of action, multiple pathogens, and temporal and spatial variability to
increase crop production and health (Jetiyanon and Kloepper 2002; Siddiqui and
Shaukat 2002; Adesemoye et al. 2008). (5) The application of molecular tools is
enhancing our ability to understand and manage the rhizosphere and will lead to
new products and improved effectiveness of PGPRs (Nelson 2004). (6) Improvement of efficient PGPRs strains by creating transgenic that combine multiple
mechanisms of action (Chin-A-Woeng et al. 2001). (7) Combination of PGPR
strains, bacteria with bacteria, or bacteria with fungi to suppress phytopathogens
with broader spectrum of microbial weapons (Duffy et al. 1996; Kilic-Ekici and
Yuen 2004; Lutz et al. 2004; Olivain et al. 2004). (8) Future studies on endophytes
and rhizobacteria to promote the sustainable production of biomass and bioenergy
crops in conjunction with phytoremediation of soil and contamination (Ryan
et al. 2008). (9) Endophyte-plant interaction by identifying gene governing colonization and establishment of endophyte bacteria in plants can promote sustainable
production of biomass by suppressing phytopathogens and by phytoremediation of
soil contamination. (10) Interdisciplinary studies on rhizosphere biology, microbiology, and ecology of medicinal plants should be strengthened to enhance biomass
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S.K. Singh and R. Pathak
production enriched with phytochemicals making use of PGPRs under organic
conditions.
Besides the phytochemical study to determine active principles and biochemicals present in medicinal plants, attempts ought to be made to protect and multiply
endangered species of medicinal plants that are about to be extinct.
10.5
Conclusions
The demand for medicinal plants is ever increasing due to growing population and
health awareness as plant products are nontoxic and have no side effects. Deforestation has caused irreparable loss to valuable biodiversity resulting in inclusion of
many medicinal plants in the list of endangered species of which some are at the
verge of extinction. The global plant-based drugs are projected between US$30 and
60 billion with 7 % annual growth rate (Prabhuji et al. 2009). Atropa belladonna,
Cinchona spp., Plectranthus barbatus, Withania somnifera, Panax ginseng,
Dioscorea spp., Glycyrrhiza glabra, Hyoscyamus niger, Papaver somniferum,
Catharanthus roseus, Cassia angustifolia, Podophyllum peltatum, Rauwolfia
serpentina, and Plantago major are major medicinal plants. Several constraints in
using PGPRs indiscriminately and opportunities to develop, explore, and/or exploit
multi-strain stable formulations of antagonistic PGPRs in sustainable mode to
replace the use of chemical fertilizers have been advocated.
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mkumar9@amity.edu
Chapter 11
Mechanism of Prevention and Control
of Medicinal Plant-Associated Diseases
Ram Kumar Pundir and Pranay Jain
11.1
Introduction
Worldwide, over three quarters of the world population relies mainly on plants and
plant extracts for health care. It is estimated that world market for plant-derived
drugs may account for about Rs. 2,00,000 crores. Presently, Indian contribution is
less than Rs. 2,000 crores. Indian export of raw drugs has steadily grown at 26 % to
Rs. 165 crores in 1994–1995 from Rs. 130 crores in 1991–1992. The annual
production of medicinal and aromatic plant’s raw material is worth about
Rs. 200 crores. This is likely to touch US$5 trillion by 2050. Of the 2,50,000 higher
plant species on earth, more than 80,000 are medicinal. India’s diversity is unmatched
due to the presence of 16 different agro-climatic zones, 10 vegetation zones, 25 biotic
provinces, and 426 biomes (habitats of specific species) (Joy et al. 1998).
Of these, about 15,000–20,000 plants have good medicinal potentials. However,
only 7,000–7,500 species are used for their medicinal potentials by traditional
communities. In India, drugs of herbal origin have been used in traditional systems
of medicines such as Unani and Ayurveda since ancient times. The Ayurveda
system of medicine uses about 700 species, Unani 700, Siddha 600, Amchi
600, and modern medicine around 30 species. The drugs are derived either from
the whole plant or from different organs, like leaves, stem, bark, root, flower, seed,
etc. Some drugs are prepared from excretory plant product such as gum, resins, and
latex. Some important chemical intermediates needed for manufacturing the
R.K. Pundir (*)
Department of Biotechnology Engineering, Ambala College of Engineering and Applied
Research, Devsthali, P.O. Sambhalkha, Ambala, Haryana, India
e-mail: drramkpundir@gmail.com
P. Jain
University Institute of Engineering and Technology, Kurukshetra University, Kurukshetra,
Haryana 136119, India
e-mail: drpranayjain@gmail.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_11
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R.K. Pundir and P. Jain
Table 11.1 List of most
priced medicinal plants of
some states in India
State
Species
Gujarat
Maharashtra
Karnataka
Tamil Nadu
Kerala
Orissa
Uttar Pradesh
Rauwolfia serpentina, karaya gum
Rauwolfia serpentina
Sandalwood oil, Phyllanthus emblica
Terminalia chebula, Terminalia belerica
Gum, fibers, roots of rosewood
Sandalwood, rosewood
Gum, chiraunji
modern drugs are also obtained from plants (e.g., diosgenin, solasodine, b-ionone).
Plant-derived drug offers a stable market worldwide, but also plants continue to be
an important source for new drugs (Joy et al. 1998).
The term “medicinal plants” include various types of plants used in herbalism, and
some of these plants have medicinal activities. These medicinal plants are considered
rich resources of ingredients which can be used in drug development and synthesis.
Worldwide, these plants play an important role in the development of human
cultures. Medicinal plants have a promising future because there are about half a
million plants around the world, and most of their medical activities have not been
investigated yet and could be decisive in the treatment of present or future studies.
Table 11.1 shows a list of most priced medicinal plants of some states in India.
11.2
Alternative Medicine
Nowadays, the term “alternative medicine” became very common in western culture;
it focuses on the idea of using the plants for medicinal purposes. Currently, medicines
which come in capsules or pills are the only medicines that we can trust and use. Even
so most of these pills and capsules we take and use during our daily life came from
plants. Medicinal plants are frequently used as raw materials for the extraction of
active ingredients which are used in the synthesis of different plant-based drugs such
as laxatives, blood thinners, antibiotics, and antimalaria medications. Moreover, the
active ingredients of Taxol, vincristine, and morphine were isolated from foxglove,
periwinkle, yew, and opium poppy, respectively (Hassan 2012).
11.3
Characteristics of Medicinal Plants
Medicinal plants have many characteristics when used as a treatment, as follows:
1. Synergic medicine—the ingredients of plants all interact simultaneously, so their
uses can complement or damage others or neutralize their possible negative
effects.
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Mechanism of Prevention and Control of Medicinal Plant-Associated Diseases
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2. Support of official medicine—these are used to treat the complex cases like
cancer diseases.
3. Preventive medicine—it has been proven that the component of the plants is also
characterized by their ability to prevent the appearance of some diseases. This
will help to reduce the use of the chemical remedies which will be used when the
disease is already present, i.e., reduce the side effect of synthetic treatment
(webpage).
According to Kumar et al. (1997), the major medicinal plants such as Acorus
calamus, Aconitum sp., Adhatoda vasica, Aloe vera, Ammi majus, Atropa
acuminata, Berberis aristata, Carica papaya, Catharanthus roseus, Cassia senna,
Cephaelis ipecacuanha, Cinchona spp., Dioscorea spp., Glycyrrhiza glabra
Hedychium spicatum, Heracleum candicans, Hyoscyamus sp. muticus, Inula
racemosa, Juglans regia, Juniperus spp., Papaver somniferum, Plantago ovata,
Podophyllum emodi, Rauvolfia serpentina, Rheum emodi, Saussurea lappa, Swertia
chirata, Urginea indica, Valeriana wallichii, Zingiber officinale, Bacopa monnieri,
Boerhaavia diffusa, Duboisia myoporoides, Eclipta alba, Gymnema sylvestre,
Phyllanthus amarus, Piper retrofractum, Panax quinquefolius, Silybum marianum,
and Matricaria chamomilla can be cultivated in India and have established demand
for their raw materials. Kumar et al. (1997) also stated that medicinal plants in which
significant research leads have been obtained with respect to their pharmaceutical
potential for which processing and agrotechnology need to be established, include
such as Andrographis paniculata, Artemisia annum, Boswellia serrata, Centella
asiatica, Coleus forskohlii, Commiphora wightii, Curcuma longa, Phyllanthus
amarus, Picrorhiza kurroa, Sida rhombifolia, Taxus baccata, and Withania
somnifera. Plants which delay aging process and form healthy food ingredients
in several Ayurvedic formulations belong to Allium sativum, Aloe barbadensis,
Asparagus racemosus, Cassia senna, Curculigo orchioides, Commiphora wightii,
Centella asiatica, Capsicum annuum, Chlorophytum arundinaceum, Eclipta
alba, Fagopyrum esculentum, Glycyrrhiza glabra, Oenothera biennis, Panax
pseudoginseng, Plantago ovata, and Withania somnifera.
There are many diseases that occur in plants caused by living organisms. Plant
diseases need to be controlled to maintain the quality and abundance of food, feed,
and fiber produced by growers around the world. Different approaches may be used
to prevent, mitigate, or control plant diseases. The use of pesticides has contributed
significantly to the spectacular improvements in crop productivity and quality over
the past 100 years. However, the environmental pollution caused by excessive use
and misuse of agrochemicals has led to considerable changes in people’s attitudes
towards the use of pesticides in agriculture.
Plant diseases are the result of interactions among the components of disease
triangle, i.e., host, pathogen, and environment (Fig. 11.1a). It also includes the time
(Fig. 11.1b).
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R.K. Pundir and P. Jain
Fig. 11.1 Interactions
among the components of
plant diseases triangle, (a)
Host plant, pathogen and
environment, (b) Host plant,
pathogen, environment and
time
India is one of the leading countries in Asia in terms of the wealth of traditional
knowledge systems related to the use of plant species. India is also known to harbor
a rich diversity of higher plant species (about 17,000 species) of which 7,500 are
known as medicinal plants (Kala 2005; Shiva 1996).
Medicinal plants are attacked regularly by insects, mites, nematodes, bacteria,
fungi, and viruses. A plant disease caused by a pathogen particularly by fungal
pathogen is often recognizable from the particular plant organ infected and the type
of symptom produced. On this basis, the following general types of fungal diseases
can be distinguished.
•
•
•
•
•
•
•
•
•
•
•
•
Damping-off diseases
Root and foot rots
Vascular wilts
Downy mildews
Powdery mildews
Leaf spots and blights
Rusts
Smuts
Anthracnoses
Galls
Dieback
Postharvest diseases
11.4
Bacterial Plant Diseases and Their Control
Most plant pathogenic bacteria belong to the following genera: Erwinia,
Pectobacterium, Pantoea, Agrobacterium, Pseudomonas, Ralstonia, Burkholderia,
Acidovorax, Xanthomonas, Clavibacter, Streptomyces, Xylella, Spiroplasma, and
Phytoplasma. Plant pathogenic bacteria cause many different kinds of symptoms
that include galls and overgrowths, wilts, leaf spots, specks and blights, soft rots,
scabs, and cankers. In contrast to viruses, which are inside the host cells, walled
bacteria grow in the spaces between cells and do not invade them. The means by
which plant pathogenic bacteria cause disease is as varied as the types of symptoms
they cause. Some plant pathogenic bacteria produce toxins or inject special proteins
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Mechanism of Prevention and Control of Medicinal Plant-Associated Diseases
235
that lead to host cell death, or they produce enzymes that break down key structural
components of plant cells and their walls.
11.5
Control
To control bacterial diseases in plants is very difficult. The emphasis is on
preventing the spread of the bacteria rather than on curing the plant. There are
various integrated management measures for bacterial plant pathogens, which
include the following.
11.5.1 Genetic Host Resistance
It includes resistant varieties, cultivars, or hybrids as the most important control
procedure.
11.5.2 Cultural Practices
It includes the bacteria-free seed or propagation materials; sanitation, particularly
disinfestation of pruning tools; and either eliminating or reducing sources of
bacterial contamination, such as crop rotation to reduce over-wintering, preventing
surface wounds that permit the entrance of bacteria into the inner tissues, propagating only bacteria-free nursery stock, and prolonged exposure to dry air, heat, and
sunlight, which will sometimes kill bacteria in plant material.
11.5.3 Chemical Applications
There are many chemicals used to control bacterial diseases which include applications of copper-containing compounds or Bordeaux mixture (copper sulfate and
lime). Antibiotics, streptomycin and/or oxytetracycline, may also help kill or
suppress plant pathogenic bacteria prior to infection and reduce the spread of the
disease, but they will not cure plants that are already diseased, and antibiotics are
also used to treat diseases caused by fastidious vascular bacteria. Phytoplasma and
Spiroplasma are susceptible to certain antibiotics, particularly tetracycline, which
has been used to treat pear trees with the pear decline disease. Tetracycline must be
injected into mature trees on a routine or therapeutic schedule to be effective and
even then only appears to suppress the development of symptoms rather than curing
the infected plant. Applications made during the early stages of infection tend to be
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R.K. Pundir and P. Jain
more effective than in the later stages of disease development, and insect control
will help to eliminate vectors or reduce feeding wounds that can provide points of
entry.
11.5.4 Biological Control
The use of antagonistic or biological control products such as BlightBan and
Agrosin K84 may also be effective for managing bacterial diseases of plants.
11.5.5 Government Regulatory Measures
It includes the implementation of strict quarantines that exclude or restrict the
introduction or movement of fungal and FLO pathogens or infected plant material.
11.6
Nutrients as Plant Disease-Controlling Agents
Nutrients play an important role on growth and development of plants and also
microorganisms, and they are important factors in disease control (Agrios 2005).
All the essential nutrients can affect disease severity (Huber and Graham 1999).
However, there is no general rule, as a particular nutrient can not only decrease the
severity of a disease but can also increase the severity and the disease incidence of
other diseases or have a completely opposite effect in a different environment
(Graham and Webb 1991; Huber 1980). Despite the fact that the importance of
nutrients in disease control has been recognized for some of the most severe
diseases, the correct management of nutrients in order to control disease in sustainable agriculture has received little attention (Huber and Graham 1999).
11.7
Fungal Plant Diseases and Their Control
There are many fungal species such as Aecidium withaniae, Mucor mucedo,
Fusarium solani, Alternaria alternata, Aspergillus niger, Rhizopus solani,
Alternaria alternata, A. tenuissima, Fusarium spp., Aspergillus verocosa, Fusarium
oxysporum, Curvularia cragrotidis, Aspergillus flavus, Penicillium citrinum,
F. culmorum, Verticillium dahliae, V. albo-atrum, Rhizoctonia solani, Erysiphe
cichoracearum, Sphaerotheca fuliginea, Leveillula guttiferatum, E. hypersici,
E. artemisiae, E. beceleate, E. communis, and L. malvacearum that cause diseases
in medicinal plants, namely, Withania somnifera, Aloe vera, Datura metel,
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Lavandula angustifolia, Rosmarinus officinalis, Borago officinalis, Salvia
officinalis, Arctium lappa, Melissa officinalis L., Cucurbita pepo var. sterica,
Hypericum perforatum, Artemisia dracunculus, Solanum dulcamara, Descurainia
sophia, Althaea officinalis, Malva sylvestris, Glycyrrhiza glabra, Anethum
graveolens, Coriandrum sativum, Spinacia oleracea, Satureja hortensis, Thymus
serpyllum, Mentha pulegium, and Mentha piperita (Chavan and Korekar 2011).
In a study, the medicinal plant Withania somnifera Dunal is widely used in
Ayurvedic medicine, the traditional medical system of India. It is an ingredient in
many formulations prescribed for a variety of musculoskeletal conditions (e.g.,
arthritis, rheumatism), and as a general tonic to increase energy, it improves overall
health and longevity and prevents disease in athletes, the elderly, and during
pregnancy. Many herbal drugs and drinks have been formulated from A. vera plants
for the maintenance of good health (Davis and Moro 1989). A. vera gel has been
reported to be very effective for the treatment of sore and wounds, skin cancer, skin
disease, cold and cough, constipation, pile, fungal infection, etc. (Gill 1992; Kafaru
1994; Daodu 2000; Djeraba and Quere 2000; Olusegun 2000). The use of Aloe
plants in the treatment of other diseases such as asthma, ulcer, and diabetes has also
been reported (Davis and Moro 1989). In cosmetic industries, Aloe is used in the
production of soap for bathing, shampoo, hair wash, tooth paste, and body creams
(Daodu 2000). Datura metel L. is another important and widely available medicinal
plant of this region. It has a parasympatholytic with anticholinergic property, it
reduces secretion, and it is also an antidote in opium and chloral hydrate overdose
(Jarald 2006). These medicinally important plants are facing serious problems of
the fungal attack. Here are leaf, root, and seed diseases, namely, leaf spot, lead rust,
root spot, and seed spot caused by fungal pathogens that adversely affect the
medicinal plant parts and decrease the medicinal value of the part.
Using these infected parts as a medicine may be harmful to the human body.
Among all the plant pathogens, the fungal group is the major one. The above three
important medicinal plants, diseases, and their causal fungal agents are listed as
follows:
1. Withania somnifera (ashwagandha/Indian ginseng/poison gooseberry/or winter
cherry)
Leaf rust: Aecidium withaniae and Mucor mucedo
Leaf spot: Fusarium solani, Alternaria alternata, and Aspergillus niger
Root: Rhizopus solani
2. Aloe vera (ghee kawar)
Leaf spot: Alternaria alternata, A. tenuissima, and Fusarium spp.
Root: Aspergillus verocosa and Fusarium oxysporum
3. Datura metel (dhatura)
Leaf spot: Alternaria alternata and Curvularia cragrotidis
Seed spot: Aspergillus flavus and Penicillium citrinum
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R.K. Pundir and P. Jain
11.8
Management of Plant-Associated Diseases
11.8.1 Recent Advances in Management of Fungal
Pathogens
There are various ways to manage the fungal pathogens as follows:
Cultural practices
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
Heat treatment
Fumigation
Ionization radiation and UV illumination
Chemically impregnated wrapper
Antagonism
Biocontrol: integrated approaches
Induced resistant
Host defense through gene silencing
Plantibodies
Induced resistance
Disease-resistant transgenic plant
11.8.2 Management Practices
11.8.2.1
Cultural Management
1. Sanitation—clean environment; remove or reduce sources of inoculum (weed
and alternative hosts, insect vectors, debris)
2. Pruning—remove infected tissue, promote more vigorous growth, and increase
air circulation
3. Watering—avoid overwatering or underwatering and flooding soils
4. Planting date—unfavorable conditions for pathogen and favorable for host
5. Fertility—avoid overfertilization or underfertilization
6. Rotation—nonhost plants and resistant varieties; reduce soilborne pathogen
populations
7. Trap plants and antagonistic plants—e.g., marigolds
8. Quarantines, restrictions on moving plant materials across county, state, or
national borders
11.8.2.2
Chemical Management
There is a chemical barrier to protect the host plant and/or eradicate an existing
infection. Pesticides typically cannot “cure” heavily diseased plants. The types of
pesticides are fungicides, bactericides, nematicides, insecticides, and biocides.
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Mechanism of Prevention and Control of Medicinal Plant-Associated Diseases
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Contact fungicide: It is effective only at the site of application (protectant) and
must be applied before pathogen infects the plant; new growth emerging after
application is not protected, for example, mancozeb, coppers, chlorothalonil, and
captan.
Systemic fungicide: It is absorbed and translocated (moved from application site)
by the plant locally and systemically by moving short distances (towards the leaf
margin) within the plant from the site of application (e.g., benomyl, triforine).
Systemic: It moves further within the plant from the site of application (e.g.,
metalaxyl moves from roots up to shoots and foliage).
11.8.2.3
Genetic Resistance
Most plants resist infection by the majority of microorganisms. The degree of
resistance/susceptibility varies among plant species and varieties. Resistance is
dynamic (changes)—races or strains of a pathogen vary in pathogenicity (how
severe a pathogen), and the environment affects host resistance.
11.8.2.4
Physical Management
There are three important physical factors which are responsible for many of the
plant diseases:
1. Heat treatment: It is due to steam sterilization of soil/materials, soil solarization,
and heat treatments
2. Cold treatment: It is possible due to refrigeration (postharvest).
3. Moisture management: To reduce humidity, dry out bulbs, tubers, etc., for
winter storage.
11.8.2.5
Biological Management
Biocontrol of plant diseases involves the use of an organism or organisms to inhibit
the pathogen and reduce disease (Cook and Baker 1983). There are many definitions for biological control; however, the basic idea involves a strategy for reducing
disease incidence or severity by direct or indirect manipulation of microorganisms
(Baker and Cook 1974; Maloy 1993). Consequently, understanding the mechanisms of biological control of plant diseases through the interactions between
biocontrol agent and pathogen may allow us to manipulate the soil environment
to create conditions conducive for successful biocontrol or to improve biocontrol
strategies (Handelsman and Parke 1989).
Recently several methodologies for genetic analysis, such as the approach of
mutant analysis, have provided promise for the study of mechanisms of biocontrol
agents and their targets. Handelsman and Parke (1989) have suggested the application of Koch’s postulates to demonstrate a cause-effect relationship in the
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R.K. Pundir and P. Jain
involvement of a particular mechanism in biocontrol because it may not be adequate to demonstrate that a mechanism exists in vitro (Wilhite et al. 1994). The
following steps suggested by Handelsman and Parke should be demonstrated in
either biocontrol agents or their targets to ascertain the role of a particular mechanism. These steps are as follows:
1. The activity must be associated with a strain that is effective as a bioprotectant,
or a metabolite must be identified in situ, such as in the disease situation.
2. The gene(s) coding for the particular product or process must be cloned.
3. The activity of the mutant should be less effective than the wild-type parent if the
particular gene(s) is deleted.
4. Replacing the gene(s) encoding for the activity should restore the biocontrol
activity.
5. Mutants of the pathogen that are not affected by the activity of the metabolite or
process should be able to incite disease in the presence of the biocontrol agent.
6. Restoring sensitivity of the pathogen to the activity should reduce its ability to
cause disease. In addition, other steps such as transformation of the gene and
expression in heterologous organisms or induced overexpression in the same
bioprotectant also may be adequate to demonstrate the particular mechanism
(Handelsman and Parke 1989).
Various mechanisms employed by the biocontrol agents in controlling the plant
diseases are broadly classified into direct and indirect antagonism. Direct antagonism results from the physical contact and/or high degree of selectivity for the
pathogens by biocontrol agent. In such a scheme, hyperparasitism by obligate
parasites of a plant pathogen would be considered the most direct type of antagonism because the activities of no other organism would be required to exert a
suppressive effect.
Indirect antagonisms result from activities that do not involve sensing or
targeting a pathogen by the BCA(s). The stimulation of plant host defense pathways
by nonpathogenic BCAs is the most indirect form of antagonism. However, in the
natural environment, most described mechanisms of pathogen suppression will be
modulated by the relative occurrence of other organisms in addition to the pathogen. While many investigations have attempted to establish the importance of
specific mechanisms of biocontrol to particular pathosystems, all of the mechanisms described below are likely to be operating to some extent in all natural and
managed ecosystems. And, the most effective BCAs studied to date appear to
antagonize pathogens using multiple mechanisms. For instance, pseudomonads
known to produce the antibiotic 2,4-diacetylphloroglucinol (DAPG) may also
induce host defenses (Iavicoli et al. 2003). Additionally, DAPG producers can
aggressively colonize roots, a trait that might further contribute to their ability to
suppress pathogen activity in the rhizosphere of wheat through competition for
organic nutrients Pal and Gardener (2006).
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Mechanism of Prevention and Control of Medicinal Plant-Associated Diseases
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Hyperparasitism
Hyperparasitism is the most considered and the most direct form of antagonism Pal
and Gardener (2006). Hyperparasitism involves tropic growth of biocontrol agent
towards the target organism, coiling, final attack, and dissolution of target pathogen’s cell wall or membrane by the activity of enzymes. It is one of the main
mechanisms involved in Trichoderma (Sharma 1996). Trichoderma harzianum
exhibits excellent mycoparasitic activity against Rhizoctonia solani hyphae
(Altomare et al. 1999).
Mycoparasitism is under the control of enzymes. Harman (2000) reported the
involvement of chitinase and β-1,3-glucanase in the Trichoderma-mediated biological control. Since enzymes are the products of genes, slight change in the structure
of gene can lead to the production of different enzymes. Gupta et al. (1995) reported
that a strain of Trichoderma deficient in the ability to produce endochitinase had
reduced the ability to control Botrytis cinerea but shows increased ability to control
Rhizoctonia solani.
A single fungal pathogen can be attacked by multiple hyperparasites, e.g.,
Acremonium alternatum, Acrodontium crateriforme, Ampelomyces quisqualis,
and Gliocladium virens are few of the fungi that have the capacity to parasitize
powdery mildew pathogens (Kiss 2003).
Competition
From the microbial perspective, soils and living plant surfaces are frequently
nutrient-limited environment. So to colonize the phytosphere, a microbe must
effectively compete for the available nutrients Pal and Gardener (2006). Both the
biocontrol agents and the pathogens compete with one another for the nutrients and
space to get established in the environment. This process of competition is considered to be an indirect interaction between the pathogen and the biocontrol agent,
whereby the pathogens are excluded by the depletion of food base and by physical
occupation of site (Lorito et al. 1994).
So far as the competition for nutrients is concerned, biocontrol agents compete
for the rare but essential micronutrients, such as iron and manganese, especially in
highly oxidized and aerated soils. In these soils iron is present in ferric form, which
is insoluble in water and where the concentration may be as low as 10–8 M, too low
to sport the microbial growth. Competition for micronutrients exists because
biocontrol agents have more efficient utilizing uptake system for the substances
than the pathogens (Nelson 1990). This property can be attributed to the production
of iron binding ligands called siderophores as in Erwinia carotovora (Kloepper
et al. 1980). Siderophores chelate the Fe (II) ions and the membrane bind protein
receptors specifically recognize and take up the siderophore-Fe complex
(Mukhopadhyay and Mukherjee 1998). This results in making iron unavailable to
the pathogen, which produces less siderophores with lower binding power. The
result is less pathogen infection and biological control.
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R.K. Pundir and P. Jain
Biocontrol agents also compete with the pathogen for physical occupation of site
and thereby reduce or delay the root colonization by the pathogen. For example,
spray the pine sumps with the spore suspension of infection by Heterobasidion
annosum. Because the pathogen cannot gain a foothold for establishment on host,
biocontrol can thus reduce the severity of root rot of pine (Maloy 1993).
Some plant pathogens depend on growth substances or stimulants to overcome
their dormancy before they can cause infection, and biocontrol agents are known to
exert competition for these stimulants, thereby reducing their disease-causing
ability. These substances include fatty acids or peroxidation products of fatty
acids (Harman and Nelson 1994) and volatile compounds such as ethanol and
acetaldehyde (Paulitz 1991).
11.9
Antibiosis
Antibiosis is the antagonism resulting from the production by one microorganism of
a secondary metabolite toxic to another microorganism. It is a very common
phenomenon responsible for the activities of many biological control agents such
as Pseudomonas, Bacillus, Streptomyces, and Trichoderma spp.
It also refers to the production of low-molecular-weight compounds or an
antibiotic by microorganisms that have a direct effect on the growth of plant
pathogen (Weller 1988). In situ production of antibiotics by several different
biocontrol agents has been measured (Thomashow et al. 2002). However, the
effective quantities are difficult to estimate because of the small quantities produced
relative to the other less toxic, organic compounds present in the phytosphere. An
efficient biocontrol agent is one that produces sufficient quantities of antibiotics in
the vicinity of the plant pathogen (Chaube et al. 2003).
Most of the bioagents perform well in the laboratory conditions but fail to
perform to their fullest once applied to the soil. This is probably attributed to the
physiological and ecological constraints that limit the efficacy of bioagents. To
overcome this problem, genetic engineering and other molecular tools offer a new
possibility for improving the selection and characterization of biocontrol agents.
Various methods that can contribute to increase the efficacy of bioagent include
mutation or protoplasm fusion utilizing polyethylene glycol. There is also an urgent
need to mass produce the bioagents, understand their mechanism of action, and
evaluate the environmental factors that favor the rapid growth of biocontrol agents.
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Mechanism of Prevention and Control of Medicinal Plant-Associated Diseases
11.10
243
Medicinal Plant Extracts Used to Control Plant
Diseases
The increasing incidence of pesticide resistance is further fueling the need for new
generation of pesticides which are eco-friendly. A green plant represents a reservoir
of effective novel chemotherapeutants with different modes of action and can
provide valuable sources of natural pesticides against resistance pathogens
(Newman et al. 2003). The popularity of botanical pesticides is once again increasing, and some plant products are being used globally as green pesticides. The body
of scientific literature documenting the bioactivity of plant derivatives to different
pests continues to expand, yet only a handful of botanicals are currently used in
agriculture (Dubey et al. 2008). There are a lot of reports on the use of several plant
by-products on several human pathogenic bacteria and fungi, but reports on the
management of phytopathogenic bacteria are less. Plant-based antimicrobials have
enormous therapeutic potential as they can serve the purpose with lesser side effects
that are often associated with synthetic antimicrobials. Considering the rich diversity of plants, it is expected that screening and scientific evaluation of plant extracts
for their antimicrobial activity may provide new antimicrobial substances. In search
of better alternatives, natural products are considered to be environmentally safe for
the management of plant diseases, and hence the present study was carried out.
Plant extracts used to control the phytopathogens have been obtained mainly
from tree species such as eucalyptus and neem (24 % of the studies with extracts)
and herbaceous species like garlic, citronella, mint, rue, yarrow, ginger, basil
(Ocimum), camphor, and turmeric (54 %). Besides these, there are other 237 plants
from the Brazilian flora whose antimicrobial potential was tested by Brazilian
researchers. With respect to groups of pathogens, the majority of the work is with
those that cause disease in the plant canopy (30 % of the works with extracts), like
the genera Alternaria, Bipolaris, Crinipellis, Corynespora, and Colletotrichum,
which respond alone for 15 % of the works. The soilborne pathogens represent
20 % of the researches, especially Rhizoctonia, Sclerotium, Sclerotinia, Fusarium,
and Phytophthora. Postharvest pathogens like Penicillium, Aspergillus, and Rhizopus are in 9 % of the works and Meloidogyne nematode in 9.5 %. For the host
plants, 30 % of the works are with crops like beans, soybeans, coffee, wheat, cotton,
and cassava; 20 % with vegetables like cucumber and tomato, which later represent
alone 15 % of all the researches with extracts; and 10 % with the fruits like papaya,
strawberry, and cocoa.
According to Gahukar (2012), leaf and seed extracts in water (5–10 %), seed
cakes (250 kg ha 1), crude oils (0.5–3 %), or essential oils (3,000 ppm) have been
effectively used to control inter alia the sap-sucking pests, foliar diseases, and rootknot nematodes. Traditional and commercial products, especially those derived
from neem (Azadirachta indica A. Juss.) leaf or kernel, are commonly produced
from medicinal crops since the use of plant products including allelochemicals
results in reasonably effective, eco-friendly, and cheaper pest and disease management and crude extracts are easy to prepare.
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11.11
R.K. Pundir and P. Jain
Conclusions
More research is needed in order to find the nutrients or nutrient combinations
which can help to reduce disease severity. It is also necessary to find the best
integrated pest management approaches with disease-resistant varieties which can
be combined with specific cultural management techniques and can efficiently
control plant disease. In addition, more research is required to find how the nutrients
increase or decrease disease tolerance or resistance, what the changes are in plant
metabolism, and how this can be used to control plant disease. Medicinal plants
have a promising future because there are about half a million plants around the
world, and most of their medical activities have not been investigated yet and could
be decisive in the treatment of present or future studies.
Acknowledgment The authors are grateful to the Management, Director, Principal, and other
dignitaries of Ambala College of Engineering and Applied Research (ACE), Devsthali, PO
Sambhalkha, Ambala, Haryana, India, for encouraging us to write this chapter. We are also
thankful to Prof. Ajit Varma, distinguished scientists, Amity Institute of Microbial Technology,
Amity University, NOIDA, UP, India, for giving us the opportunity to write a chapter in his
edited book.
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mkumar9@amity.edu
Chapter 12
Role of PGPR in Soil Fertility and Plant
Health
Ram Prasad, Manoj Kumar, and Ajit Varma
12.1
Introduction
Plant growth-promoting rhizobacteria (PGPR) are naturally occurring soil bacteria
that aggressively colonize plant roots and benefit plants health. Their use in crop
production can reduce the agro-chemical use and support eco-friendly sustainable
food production. Plant growth promotion by PGPR is due to root hair proliferation,
root hair deformation and branching, increases in seedling emergence, early nodulation and nodule functioning, enhanced leaf surface area, vigor, biomass, phytohormone, nutrient, water and air uptake, promoted accumulation of carbohydrates,
and yield in various plant species (Podile and Kishore 2006). PGPR bring nutrient
elements into the ecosystem from atmospheric or mineral reserves in soluble form;
the roots take up the nutrients, break down the detritus, and also protect the roots
from pathogens. Microorganisms are great potential goldmine for the biotechnology industry because it offers countless new genes and biochemical pathways to
probe for enzymes, antibiotics, and other useful molecules.
Soil is the natural habitat for microorganisms beneficial as well as harmful to
plant community. They play an important role in soil processes that determine plant
productivity. For successful functioning of introduced microbial bioinoculants and
their influence on soil health, exhaustive efforts have been made to explore soil
microbial diversity of indigenous community, their distribution and behavior in soil
habitats. PGPR involved in various beneficial activities within the soil like decomposition of crop residues, mineralization of soil organic matter, immobilization of
mineral nutrients, phosphate solubilizers, synthesis of soil organic matter, nitrification, nitrogen fixation, and plant growth promoters including nutrient acquisition
(biofertilizers), phytohormone production (biostimulants), and suppression of plant
R. Prasad (*) • M. Kumar • A. Varma
Amity Institute of Microbial Technology, Amity University, Sector-125, Noida, Uttar Pradesh
201303, India
e-mail: rprasad@amity.edu; mkumar9@amity.edu; ajitvarma@amity.edu
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_12
mkumar9@amity.edu
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R. Prasad et al.
Fig. 12.1 Plant growth-promoting rhizobacteria has potential role in developing sustainable
systems in crop production (Courtesy by: PakAgri farming)
disease (termed bioprotectants), which help in crop production and protection. Soil
moisture content affects the colonization of the plant rhizosphere by the PGPR after
inoculation (Shrivastava et al. 2014). In the recent era of sustainable crop production, the plant–microbe interactions in the rhizosphere play a pivotal role in
transformation, mobilization, solubilization, etc. of nutrients from a limited nutrient
pool and subsequently uptake of essential nutrients by plants to realize their full
genetic potential (Fig. 12.1).
At present, the use of biological approaches is becoming more popular as an
additive to chemical fertilizers for improving crop yield in an integrated plant
nutrient management system. In this regard, the use of PGPR has found a potential
role in developing sustainable systems in crop production. A variety of symbiotic
(Rhizobium, Bradyrhizobium, Azorhizobium, Allorhizobium, Sinorhizobium,
Mesorhizobium) and free-living nitrogen-fixing bacteria or associative nitrogen
fixers, viz. Azospirillum, Azotobacter, Enterobacter, Klebsiella, and Pseudomonas,
are now being used in enhancing plant productivity (Cocking 2003). In the rhizosphere, rhizobacteria not only benefit from the nutrients secreted by the plant root
but also beneficially influence the plant in a direct or indirect way, resulting in a
stimulation of its growth. These PGPR can be classified according to their beneficial effects. For instance, biofertilizers can fix nitrogen, which can subsequently be
used by the plant, thereby improving plant growth when the amount of nitrogen in
the soil is limiting. Phytostimulators can directly promote the growth of plants,
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249
usually by the production of hormones. Biocontrol agents are able to protect plants
from infection by phyto-pathogenic organisms. However, this may be a function of
the type of bacterium utilized since high moisture content may decrease the oxygen
content of the soil.
12.2
The Rhizosphere
Hiltner (1904) discovered that the rhizosphere, i.e., the layer of soil influenced by
the root, is much richer in bacteria than the surrounding bulk soil. These rhizosphere microbes benefit because plant roots secrete metabolites that can be utilized
as nutrients. This rhizosphere effect is caused by the fact that a substantial amount
of the carbon fixed by the plant, 5–21 %, is secreted mainly as root exudates
(Marschner 1995). The rhizosphere is the zone of soil surrounding a plant root
where the biology and chemistry of the soil are influenced by the root. As roots
grow through soil, they release water-soluble compounds such as amino acids,
sugars, and organic acids that supply food for the microorganisms. The food supply
means microbiological activity in the rhizosphere is much greater than in soil away
from plant roots. In return, the microorganisms provide nutrients for the plants.
Some microorganisms, including bacteria and mycorrhizal fungi, form associations
with roots that are mutually beneficial to both the plant and the microorganism. The
rhizosphere is a center of intense biological activity due to the food supply provided
by the root exudates. Most soil microorganisms do not interact with plant roots,
possibly due to the constant and diverse secretion of antimicrobial root exudates.
However, there are some microorganisms that do interact with specific plants.
These interactions can be pathogenic (invade and kill roots and plants), symbiotic
(benefit plant growth), harmful (reduce plant growth), saprophytic (live on plant
debris), or neutral (no effect on plants). Interactions that are beneficial to agriculture
include mycorrhizae, legume nodulation, and production of antimicrobial compounds that inhibit the growth of pathogens (Fig. 12.2). Rhizosphere microorganisms produce vitamins, antibiotics, plant hormones, and communication molecules
that all encourage plant growth (Shrivastava et al. 2014).
12.3
Plant Growth-Promoting Rhizobacteria
Rhizosphere represents a nutrient-rich habitat for microorganisms; on the other
hand, the microbial colonization of the rhizosphere also affects the whole plant
(Hartmann et al. 2008). Kloepper and Schroth (1978) suggest the term “PGPR” for
an important group of rhizosphere bacteria that have beneficial effects on plant
growth when colonizing roots. Such effects are earlier seedling emergence, and
increased vigor, biomass, yield, as well as proliferation of the root system in various
plants (Kloepper 1993). PGPR as biological control agents and the ineffectiveness
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Fig. 12.2 PGPR promoting
plant growth and health:
mode of action and potential
use in biotechnological
applications
of PGPR in the field have often been attributed to their inability to colonize plant
roots (Bloemberg and Lugtenberg 2001). A variety of bacterial traits and specific
genes contribute to this process, but only a few have been identified (Benizri
et al. 2001). These include motility, chemotaxis to seed and root exudates, production of pili or fimbriae, production of specific cell surface components, ability to use
specific components of root exudates, protein secretion, and quorum sensing
(Lugtenberg et al. 2001). Several rhizospheric bacteria are plant growth promoters
stimulating seedling growth and development; while mycorrhizal fungi provide
vegetation with increased efficiency of nutrient uptake, increased productivity and
abiotic stress may contribute to plant diversity. These facts, among others, are
leading to a possible paradigm shift to a more microbial dominated or at least highly
reciprocal view of the relationship between plant and associated microbiota. PGPR
enhance plant growth either by producing plant hormones or by enhancing nutrient
uptake or absence of pathogens (Van Loon 2007).
12.4
Applications of PGPR
PGPR enhance plant growth due to various factors, among which the release of
phytohormones, nitrogen fixation, and regulation of ethylene production in roots,
solubilizing nutrients such as phosphate, siderophore production, promoting mycorrhizal function, and decreasing heavy metal toxicity are the most important
(Whipps 2001). The plant properties that are improved by PGPR during
phytoremediation include biomass, contaminant uptake, and plant nutrition and
health. Grain yields also an indication of plant health and growth. Plant growth
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Role of PGPR in Soil Fertility and Plant Health
251
benefits due to the addition of PGPR include increases in germination rates, root
growth, yield including grain, leaf area, chlorophyll content, magnesium content,
nitrogen content, protein content, hydraulic activity, tolerance to drought, shoot and
root weights, and delayed leaf senescence. Another major benefit of PGPR use is
disease resistance conferred to the plant, sometimes known as “biocontrol” (Lucy
et al. 2004).
The following genera of endophytes isolated from agricultural crops harbor
PGPR-active strains: Pseudomonas, Bacillus, Enterobacter, and Agrobacterium.
Pseudomonas spp. are typical PGPR and their reaction with arbuscular mycorrhizal
fungi has been studied by Barea et al. (1998). Pseudomonas spp. had a positive
effect on the spore germination and mycelial development of AMF in the soil as
well as in root colonization. These bacteria (Pseudomonas spp.) have been called
mycorrhization helper bacteria (Garbaye 1994). PGPR have stimulatory effect on
the arbuscular mycorrhizae formation and plant nutrition (Barea et al. 2004). The
ability to enter the root interior might help these microorganisms to evade the
highly competitive rhizosphere habitat (Whipps 2001).
Siderophores, including salicylic acid, pyochelin, and pyoverdin, which chelate
iron and other metals, also contribute to disease suppression by conferring a
competitive advantage to biocontrol agents for the limited supply of essential
trace minerals in natural habitat (Loper and Hankels 1997). Siderophores produced
by PGPR inhibit the root pathogens by creating iron-limiting conditions in the
rhizosphere and reduce probability of plant disease (Podile and Kishore 2006).
Some siderophores such as pseudobacin and pyoverdin (yellow green fluorescent
pigment of Pseudomonas bacteria) present high antimicrobial activity and affinity
to ions of trivalent iron (Das et al. 2007; Maksimov et al. 2011). Pseudobacin is
involved in induced systemic resistance, induction of Н2О2 local storage, phenol
compounds, and strengthening cell wall of rice plants in infection zone.
Siderophores may indirectly stimulate the biosynthesis of other antimicrobial
compounds by increasing the availability of these minerals to the bacteria. Antibiotics and siderophores may additionally function as stress factors or signal inducing
local and systemic host resistance. Biosynthesis of antibiotics and other antifungal
compounds is regulated by a cascade of endogenous signals.
12.5
Possible Mechanism of Interaction or Physiology
of Interaction
Plant growth promotion can be achieved by the direct interaction between beneficial microbes and their host plant and also indirectly due to their antagonistic
activity against plant pathogens. The current status of research, commercial development, and application of PGPR inoculants is to promote plant health and environmental sustainability. In comparison with chemically synthesized pesticides and
fertilizers, microbial inoculants have several advantages: they are more safe, show
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reduced environmental damage and potentially smaller risk to human health, show
much more targeted activity, are effective in small quantities, multiply themselves
but are controlled by the plant as well as by the indigenous microbial populations,
decompose more quickly than conventional chemical pesticides, resistance development is reduced due to several mechanisms, and can be also used in integrated
pest management systems (Gabriele 2009; Chadha et al. 2014; Prasad et al. 2014).
The possible mechanisms by which PGPR aid plant growth include suppression
of root pathogens through production of siderophores (compounds secreted by
microorganisms that bind iron, making it less available to pathogens) or production
of antibiotics (Kloepper et al. 1991), fixation of nitrogen (Chanway and Holl 1991),
and production of plant hormones (Holl et al. 1988). PGPR are synergistic with
mycorrhizae in stimulating plant growth and root colonization. There has been
some success with PGPR in agriculture and commercial preparations are likely to
become available (Linderman and Paulitz 1990). Major among them are Rhizobium
symbiosis with legumes and free-living associative rhizosphere soil bacteria—
Azotobacter and Azospirillum. The other group of beneficial microorganisms
includes rhizobacteria, mainly Pseudomonas, Erwinia, Flavobacterium, and
Bacilli, which improve health and productivity of crop plants through a variety of
secondary metabolites and involved in promotion of root growth. Members of the
bacterial genera Azospirillum and Rhizobium are well-studied examples for plant
growth promotion; Bacillus, Pseudomonas, Serratia, Stenotrophomonas, and Streptomyces and the fungal genera Ampelomyces, Coniothyrium, Piriformospora
indica, and Trichoderma are model organisms to demonstrate influence on plant
health (Chadha et al. 2014). Another challenge is that plant-associated bacteria
especially those from the rhizosphere play an emerging role as opportunistic human
pathogens (Berg et al. 2005). Examples are antagonistic species of the genera
Burkholderia, Enterobacter, Herbaspirillum, Ochrobactrum, Pseudomonas,
Serratia, Staphylococcus, and Stenotrophomonas that are root-associated bacteria
that can enter interactions with plant and human hosts (Ribbeck-Busch et al. 2005;
Egamberdieva et al. 2008). Mechanisms involved in the interaction between antagonistic plant-associated bacteria and their host plants are similar to those responsible for the pathogenicity of bacteria to humans (Berg et al. 2005).
For all successful plant–microbe interactions, the competence to root colonize
plant habitats is important for beneficial effects on plant growth (Kamilova
et al. 2005). Steps of colonization include recognition, adherence, invasion (only
endophytes and pathogens), colonization and growth, and several strategies to
establish interactions. Plant roots initiate crosstalk with soil microbes by producing
signals that are recognized by the microbes, which in turn produce signals that
initiate colonization (Bais et al. 2006). To participate and react in this crosstalk,
motile organisms are preferred (Lugtenberg et al. 2002). Moreover, there is growing appreciation that the intensity, duration, and outcome of plant–microbe interactions are significantly influenced by the conformation of adherent microbial
populations (Danhorn and Fuqua 2004). Bacterial traits, such as pili, outer membrane proteins, and flagella, are involved in the PGPR adherence to plant root
surfaces. Not only is the surface of roots colonized but also inner tissues of the
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Table 12.1 Production of plant growth regulators (PGRs) by PGPR
PGPR
PGRs
Plant
References
Rhizobium
leguminosarum
Azotobacter sp.
Indole-3-acetic acid
Rice
Indole-3-acetic acid
Maize
Pseudomonas fluorescens
Siderophores, indole-3-acetic acid
Groundnut
Azospirillum brasilense
A3, A4, A7, A10, CDJA
Azospirillum lipoferum
strains 15
Pseudomonas
denitrificans
Azotobacter sp.
Indole-3-acetic acid
Rice
Indole-3-acetic acid
Wheat
Auxin
Indole-3-acetic acid
Wheat,
maize
Sesbania
Pseudomonas sp.
Indole-3-acetic acid
Wheat
Bacillus cereus RC 18
Indole-3-acetic acid
Mesorhizobium loti MP6
Chrom-azurol, siderophore,
hydrocyanic acid, indole-3-acetic
acid
Siderophores, indole-3-acetic acid
Wheat,
spinach
Brassica
Biswas
et al. (2000)
Zahir
et al. (2000)
Dey
et al. (2004)
Thakuria
et al. (2004)
Muratova
et al. (2005)
Egamberdieva
(2005)
Ahmad
et al. (2005)
Roesti
et al. (2006)
Çakmakçi
et al. (2007)
Chandra
et al. (2007)
Pseudomonas tolaasii
ACC23
Bacillus sp.
Paenibacillus sp.
Indole-3-acetic acid
Brassica
Rice
Dell’Amico
et al. (2008)
Beneduzi
et al. (2008)
plant. Colonization of the rhizosphere by some nonpathogenic microorganisms can
protect the plant from a variety of bacterial, fungal, and viral diseases. This is
known as induced systemic resistance. Interaction between the plant and rootcolonizing microorganisms triggers signaling pathways and the production of
specific gene products that enhance the ability of the plant to resist pathogens.
Secondary metabolites involved in these pathways include phenolics, flavonoids,
alkaloids, and terpenoids (Table 12.1).
In the processes of plant growth, phytohormones, e.g., production of auxin
(IAA), cytokinins, and gibberellins, PGPR can increase root surface and length
and promote in this way plant development (Kloepper et al. 2007). Several PGPR as
well as symbiotic and free-living rhizobacterial species are reported to produce IAA
and gibberellins in the rhizospheric soil and thereby play a significant role in
increasing the root surface area and number of root tips in many plants
(Bhattacharyya and Jha 2012). A greater root surface area enables the plant to
access more nutrients from soil and thus contribute to plant growth promotion
(Vessey 2003). These hormones can be synthesized by the plant themselves and
also by their associated microorganisms. Furthermore, plant-associated bacteria can
influence the hormonal balance of the plant. Ethylene is an important example to
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show that the balance is most important for the effect of hormones: at low levels, it
can promote plant growth in several plant species including Arabidopsis thaliana,
while it is normally considered as an inhibitor of plant growth and known as a
senescence hormone (Pierik et al. 2006). Interestingly, bacteria are able to reduce
the ethylene level by the following way. The compound 1-aminocyclopropane-1carboyclic acid (ACC) is a precursor of ethylene in plants. As ACC deaminaseproducing bacteria are able to degrade this substance, the uptake by and the level in
the root is reduced. Thus, these bacteria can increase root growth by lowering the
endogenous ACC levels (Glick 2005). Due to the fact that ethylene has also
established as a stress hormone, ACC deaminase-producing bacteria have an
additional potential to protect plants against biotic and abiotic stress (Saleem
et al. 2007). Another example to explain the intimate plant–microbe interaction
regarding phytohormones is the root-associated bacterium Serratia plymuthica
HRO-C48 in which IAA production is surprisingly negatively regulated by quorum
sensing (QS) (Müller et al. 2009). Also, low amounts of IAA induced resistance in
the plant while IAA is involved in many bacteria-plant signaling, an important role
of auxin signaling for plant growth promotion was also shown for Trichoderma spp.
(Hartmann et al. 2004; Contreras-Cornejo et al. 2009). Besides these mechanisms,
improved nutrient acquisition is involved in direct growth promotion. The most
well-known example is bacterial nitrogen fixation. The symbiosis between rhizobia
and its legume plants is an important example for PGPR. Bacteria of this group
metabolize root exudates (carbohydrates) and in turn provide nitrogen to the plant
for amino acid synthesis. The ability to fix nitrogen also occurs in free-living
bacteria like Azospirillum, Burkholderia, and Stenotrophomonas (Dobbelaere
et al. 2003). Another nutrient is sulfate, which can be provided to the plant via
oxidation by bacteria (Banerjee and Yesmin 2002). Bacteria may contribute to plant
nutrition by liberating phosphorous from organic compounds such as phytates and
thus indirectly promote plant growth (Unno et al. 2005). Azospirillum treatment
resulted in enhancement of root growth and activities (e.g., acidification of the root
surroundings) that increases phosphorous and other macroelements and microelements uptake (Dobbelaere and Okon 2007). Mineral supply is also involved in plant
growth promotion and includes synthesis of siderophores and siderophore uptake
systems (Katiyar and Goel 2004). Poorly soluble inorganic nutrients can be made
available through the solubilization of bacterial siderophores and the secretion of
organic acids. Recently, de Werra et al. (2009) showed that the ability of Pseudomonas fluorescens CHA0 to acidify its environment and to solubilize mineral
phosphate is strongly dependent on its ability to produce gluconic acid. Furthermore, the study provides new evidence for a close association of gluconic acid
metabolism with antagonistic activity against plant pathogens. Some bacteria,
especially Bacillus and Pseudomonas sp., depress growth and development of
filamentous fungi both in vitro and in vivo by secreting lytic enzymes such as
chitinases and glucanase. It has been assumed that applying bacteria producing
chitinases to biological protection of crops from pathogens, especially those that
contain chitin and glucans within their cell wall structure (Maksimov et al. 2011).
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Rhizosphere microorganisms, which are able to eliminate or reduce other pathogenic microorganisms, have been defined as biocontrol agents. Important mechanisms of microbial antagonism to plant pathogens are antibiosis, parasitism, and
competition for nutrients and/or induced host defense responses (Podile and
Kishore 2006). Microbial antagonism include (1) the inhibition of microbial growth
by diffusible antibiotics and volatile organic compounds (VOCs), toxins, and
biosurfactants (antibiosis); (2) competition for colonization sites and nutrients;
(3) competition for minerals, e.g., for iron through production of siderophores or
efficient siderophore uptake systems; (4) degradation of pathogenicity factors of the
pathogen such as toxins; and (5) parasitism that may involve production of extracellular cell wall-degrading enzymes such as chitinases and β-1,3-glucanase
(Whipps 2001; Wheatley 2002; Compant et al. 2005; Haas and Défago 2005;
Raaijmakers et al. 2006; Kamal et al. 2008). Plant-associated bacteria can reduce
the activity of pathogenic microorganisms not only through microbial antagonisms
but also by activating the plant to better defend itself, a phenomenon termed
“induced systemic resistance” (Conrath et al. 2002; Van Loon 2007). However,
sometimes, the mechanism of ISR elicited by PGPR overlaps partly with that of
pathogen-induced systemic acquired resistance (SAR). Both ISR and SAR represent a state of enhanced basal persistence of the plant that depends on the signaling
compounds jasmonic acid and salicylic acid (Van Loon 2007). Pathogens are
differently sensitive to the resistance activated by these signaling pathways.
These interactions are highly specific on each component: the host plant, the
pathogen, as well as the PGPR strain. They recognize each other by chemical
signaling: root exudates as well as microbial metabolites. The mechanisms of ISR
include (1) developmental escape: linked to growth promotion, (2) physiologicaltolerance: reduced symptom expression, (3) environmental: associated with microbial antagonisms in the rhizosphere, and (4) biochemical-resistance: induction of
cell wall reinforcement, induction of phytoalexins, induction of pathogenesisrelated proteins, and “priming” of defense responses (resistance). Substances
involved in ISR are partly the same with those involved in microbial antagonisms:
siderophores, antibiotics, N-acyl-homoserine lactones, VOCs (e.g., 3-hydroxy-2butanone (acetoin), and 2, 3-butandiol). Whereas some PGPR activate defenserelated gene expression, other examples appear to act solely through priming of
effective resistance mechanisms, as reflected by earlier and stronger defense reaction once infection occurs.
PGPR can be used to enhance the growth of plants with natural health products.
Pre-inoculation of hosts with PGPR can induce/enhance specific human health
promoting compounds in plants; enhance root health; Increase resistance to environmental stress; and increase yield and quality of active ingredient products.
Although PGPR have not been used specifically to increase the production of
medicinal compounds in plants before, their ability to enhance plant growth and
root health has been demonstrated with many crop species (Glick 1995; Van Loon
et al. 1998). The use of microbial associations for medicinal plants provides a
sustainable approach to improving crop quality and yield and is suitable for use in
organic agriculture (Prasad et al. 2008; 2013). It provides the potential to increase
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production, value, and export of human health-enhancing crops and products. This
will open new avenues products and markets for inoculant manufacturers.
12.6
Ecological Significance of Microbial Interactions
Microorganisms may contribute to the biocontrol of pathogens and improved
supply of nutrients, thus maintaining plant health and production. Therefore,
understanding of these interactions and the mechanisms could have implications
for the progress of sustainable agriculture. Phosphate solubilizing bacteria are
widespread in soils and secretion conversion of insoluble forms of phosphorus to
plant-available forms (Vessey 2003). The biofertilizer properties of PGPR are
frequently attributed to their ability to increase the bioavailability of inorganic
and organic phosphorus, and some bacteria have documented synergistically effects
on nitrogen fixation and formation of mycorrhizal associations.
PGPR present an alternative to the use of chemicals for plant growth enhancement in many different applications. Extensive research has demonstrated that
PGPR could have an important role in agriculture and horticulture in improving
crop productivity. In addition, these organisms are also useful in forestry and
environmental restoration purposes. Because PGPR, which can fulfill diverse
functions in plants, lead to promising solutions for a sustainable, environmentally
friendly alternative to chemical fertilizers and pesticides, the use of which is
regulated and sometimes forbidden; the market for bioinoculants is still expanding.
While inoculants for plant growth promotion and biocontrol already exist, in the
future, stress-protecting agents (stress conditions like those generated by salinity,
drought, water logging, heavy metals, and pathogenicity) will be of emerging
importance not only due to climate change. Furthermore, to improve food quality
by PGPR is an important task.
12.7
Conclusions
PGPR are the potential tools for environmentally sustainable approach to increase
soil fertility and plant health. PGPR benefit the growth and development of plants
directly and indirectly through several mechanisms. The production of secondary
metabolites, i.e., plant growth substances, changes root morphology resulting in
greater root surface area for the uptake of nutrients, siderophores production,
antagonism to soil-borne root pathogens, phosphate solubilization, and
di-nitrogen fixation. The root surface area for uptake of nutrients and production
of PGPR may help to optimize nutrient cycling in the event of stresses due to
unsuitable weather or soil conditions. The beneficial effects of PGPR on plant
growth are from changing the root architecture and enhancing nutrient uptake to
biocontrol. The application of molecular tools is enhancing our ability to
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understand and manage the rhizosphere and will lead to new products with
improved effectiveness. The discovery of many traits and genes that are involved
in the beneficial effects of PGPR has resulted in a better understanding of the
performance of bioinoculants in the field and provides the opportunity to enhance
the beneficial effects of PGPR strains by genetic modification.
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Part IV
Mechanism of Action
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Chapter 13
Systemic Induction of Secondary Metabolite
Biosynthesis in Medicinal Aromatic Plants
Mediated by Rhizobacteria
Maricel Valeria Santoro, Lorena Cappellari, Walter Giordano,
and Erika Banchio
Abbreviation
EOs
PGPR
VOCs
13.1
Essential oils
Plant growth-promoting rhizobacteria
Volatile organic compounds
Introduction
Bacteria are by far the most abundant organisms in soil, where they play essential
roles in nutrient cycling and soil fertility. Root-colonizing bacteria are commonly
referred to as “rhizobacteria.” Many rhizobacterial strains, collectively termed
“plant growth-promoting rhizobacteria” (PGPR), enhance plant growth when inoculated on seeds. PGPR species and strains in the genera Acetobacter, Acinetobacter,
Alcaligenes, Arthrobacter, Azoarcus, Azospirillum, Azotobacter, Bacillus,
Beijerinckia, Burkholderia, Derxia, Enterobacter, Gluconacetobacter,
Herbaspirillum, Klebsiella, Ochrobactrum, Pantoea, Pseudomonas, Rhodococcus,
Serratia, Stenotrophomonas, and Zoogloea have been the subjects of extensive
research for many decades (Babalola 2010). PGPR promote plant growth by both
direct and indirect mechanisms (Kloepper 1993; Niranjan et al. 2006; Van Loon
2007). Direct mechanisms include production of stimulatory bacterial volatile
organic compounds (VOCs) and phytohormones, reduction of ethylene level in
plants, improvement of plant nutrient status (release of phosphates and
micronutrients from insoluble sources; nonsymbiotic nitrogen fixation), and
M.V. Santoro • L. Cappellari • W. Giordano • E. Banchio (*)
Departamento de Biologı́a Molecular. Laboratorio 10, Universidad, Nacional de Rı́o Cuarto,
Ruta Nac. 36- Km. 601, Rı́o Cuarto, C
ordoba, Argentina
e-mail: ebanchio@exa.unrc.edu.ar
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_13
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enhancement of disease-resistance mechanisms (induced systemic resistance).
Indirect effects of PGPR include functioning as biocontrol agents to reduce diseases, promotion of other beneficial symbioses, and protection of plants by
degrading xenobiotics in contaminated soils (Figueiredo et al. 2010). Studies during
the past 5 years have shown that some PGPR are capable of releasing functional
VOCs that trigger growth promotion and induced resistance (Ryu et al. 2004).
Depending on the PGPR species, two or more of the above growth-promoting
mechanisms may be present (Vessey 2003).
During the past three decades, medicinal and aromatic plants have undergone a
transition from unknown or minor agricultural plantings to major crops that farmers
may consider as alternatives to traditional food or feed crops. The steadily increasing agricultural role is driven by consumer interest in these plants for culinary,
medicinal, and other anthropogenic applications.
Aromatic plant species are a highly diverse group whose common characteristic
is the production of essential oils (EOs) (Guenther 1948). EOs are active compounds that can modify behavioral or physiological responses in other organisms
(Langenheim 1994). The major EOs in Lamiaceae, a large plant family that
includes many aromatic and medicinal species, are terpenes, particularly monoterpenes (C10 members of the terpenoid class).
Terpenes are responsible for the characteristic fragrances of aromatic plants
(Chen et al. 2011) and are typically emitted when plant structures are damaged
(Wittstock and Gershenzon 2002). Lamiaceae accumulate EOs in specific structures, glandular trichomes (also termed secretory or peltate trichomes), which are
lipophilic glands consisting of secretory cells and a cuticle-enclosed cavity that
becomes filled with the secreted compound (Werker 2000). The plastids in glandular trichomes have less-defined membrane structures in comparison with chloroplasts and may be associated with synthesis and/or secretion of secondary
metabolites such as terpenoids (Werker 2000).
Monoterpenes are among the best studied plant secondary metabolites with
defensive functions. These colorless, lipophilic, volatile substances are the major
constituents of plant EOs and display defensive effects (toxic, repellent, antifeeding, anti-ovipositing) against a variety of harmful insects and pathogens
(Harrewijn et al. 2001; Chen et al. 2011). Some monoterpenes are involved in
plant intraspecific communication (Wittstock and Gershenzon 2002).
Inducible chemical changes are of particular interest in medicinal and aromatic
plants, not only in relation to defensive mechanisms as above but also because the
altered compounds may have aromatic or therapeutic properties that enhance the
economic value of the plant (Banchio et al. 2005). Increased knowledge of factors
that affect EO quantity and quality in aromatic plants will be useful for improving
production of these natural products and in pest management strategies (Kogan and
Fischer 1991).
Chemical fertilizers and pesticides have been used increasingly in recent
decades to maximize agricultural production. However, they are responsible for a
variety of ecologically and agriculturally deleterious effects, e.g., depletion of
nonrenewable energy resources, pollution of watersheds, elimination of beneficial
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Systemic Induction of Secondary Metabolite Biosynthesis in Medicinal. . .
265
microorganisms and insects, increasing the susceptibility of the crop to disease, and
reducing soil fertility (Babalola 2010).
Interest in environmentally safe, sustainable, and organic agricultural practices
that reduce negative environmental effects associated with food and feed production is steadily increasing (Lind et al. 2004). “Organic agriculture” is a production
system that avoids or minimizes the use of synthetic fertilizers, pesticides, and
growth regulators, relying instead on biofertilization, crop rotation, crop residues,
mechanical cultivation, and biological pest control to maintain soil productivity.
Reduced yield is a major problem and concern in organic production systems. For
many medicinal and aromatic plants that are consumed without further processing
following harvest, it is important that synthetic compounds not be present.
Unconventional techniques such as inoculation with PGPR must be considered
and investigated in the search for new strategies of plant production with high yield
but without undesirable compounds or effects. The effects of PGPR inoculation in
medicinal and aromatic plants have received very little research attention to date.
New, less aggressive biotechnological methods involving the application of beneficial microorganisms as biofertilizers are a viable alternative to the use of chemical
fertilizers. There are economic, environmental, and health-related justifications for
research on PGPR strains as inoculants for cultivation of medicinal and aromatic
plants. Application of these techniques may contribute to environmental conservation, increased crop productivity, and sustainable agricultural practices.
We present here an integrated summary of our experimental findings on induced
responses to PGPR in various aromatic plant species of the families Lamiaceae and
Asteraceae. Our focus is on the changes in plant EO/VOC composition (particularly
of monoterpenes, the major EOs) induced by inoculation with various PGPR
species.
13.2
Materials and Methods
13.2.1 Bacterial Strains, Culture Conditions, Media,
and Treatments
Three bacterial strains well known as PGPR were used. Pseudomonas fluorescens
WCS417r and Azospirillum brasilense Sp7 (Van Loon 2007) were grown on LB
medium. Bacillus subtilis was grown on TSA for routine use and maintained in
nutrient broth with 15 % glycerol at 80 C for long-term storage.
Bacterial cultures were grown overnight at 30 C with rotation (120 rpm) until
reaching exponential phase. Each culture was then washed twice in 0.9 % NaCl by
centrifugation (4,300g, 10 min, 4 C) in an Eppendorf centrifuge, resuspended in
sterile water, and adjusted to a final concentration of ~109 CFU/ml for use as
inoculum. Plants were grown in plastic pots (diameter 12 cm, depth 22 cm)
containing 250 g sterilized vermiculite. Seeds were surface sterilized in 70 %
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ethanol for 5 min, rinsed 5 with sterile water, dipped in 1 % NaCl for 1 min, rinsed
5 with sterile water, planted in vermiculite (one seed per pot), and inoculated with
1 ml bacterial suspension.
13.2.2 Greenhouse Experiments
Plants were grown in a growth chamber under controlled conditions of light (16/8 h
light/dark cycle), temperature (22 2 C), and relative humidity (~70 %). Bacterial
suspensions as described above were applied to experimental seedlings, and sterile
water was applied to control seedlings. All plants were watered with Hoagland’s
nutrient medium (20 ml/pot) once per week (Banchio et al. 2008). All experiments
were performed under non-sterile conditions.
Each experiment was replicated (ten pots per treatment; one plant per pot). Pots
were arranged randomly in the growth chamber. Ninety days after inoculation,
plants were removed from pots, roots were washed to remove vermiculite, and
standard growth parameters (leaf number, shoot fresh weight, root dry weight) were
measured.
13.2.3 Micropropagation of Plants
Young shoots from Mentha x piperita plants grown in Traslasierra Valley (Cordoba
province, Argentina) were surface disinfected by soaking for 1 min in 17 % sodium
hypochlorite solution and rinsed 3 in sterile distilled water. Disinfected shoots
were cultured in 100 ml MS culture medium containing 0.7 % (w/v) agar and 1.5 %
(w/v) sucrose (Murashige and Skoog 1962). All culture media contained 30 g/L
sucrose and 7.5 g/L agar.
Stage I Initial shoot-tip culture: After 30 days, apical meristems with foliar
primordia and no sign of contamination were removed aseptically from terminal
buds of shoots obtained as above. Explants were cultured in test tubes containing
40 ml MS medium with 0.66 mg/L indolebutyric acid.
Stage II Growth and in vitro multiplication: Plantlets obtained from shoot tips as
above were multiplied by single-node culture, and MS medium was adjusted to
pH 5.6–5.8 prior to autoclaving (20 min, 121 C). Explants were placed in a growth
chamber under controlled conditions as in Sect. 13.2.2.
13.2.4 Exposure to VOCs
One node from an aseptically cultured plantlet or one sterilized O. basilicum seed
was placed on one side of a specialized plastic Petri dish (90 15 mm) containing a
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center partition (I-plate; Fisher Scientific). Both sides of the dish contained 50 %
strength MS solid medium. 20 μL suspension cultures of various PGPR strains in
sterile distilled water were applied one drop at a time to the side of the dish opposite
the plant node. By this method, plants were exposed to bacterial VOCs without
physical contact. Dishes were sealed with Parafilm, arranged in a completely
randomized design, and placed in a growth chamber under controlled conditions
as in Sect. 13.2.2. Plants were harvested after 30 days. Ten plants were used for
each treatment, and experiments were replicated 4 (Santoro et al. 2011).
13.2.5 Extraction of EOs
The shoot samples were individually weighed and subjected to hydrodistillation in
a Clevenger-like apparatus for 40 min, and the volatile fraction was collected in
dichloromethane. Delta-dodecalactone (0.1 μL in 50 μL ethanol) was added as an
internal standard.
The major EOs (accounting for ~75 % of the total EO volume) were identified
and quantified relative to the delta-dodecalactone standard. Flame ionization detector (FID) response factors for each compound generated equivalent areas with
negligible differences (<5 %).
Chemical analyses were performed using a PerkinElmer Clarus 600 gas chromatograph (GC) equipped with a CBP-1 capillary column (30 m 0.25 mm, film
thickness 0.25 μm) and mass-selective detector. Analytical conditions: injector/
detector temperatures 250/270 C; oven temperature programmed from 60 C
(3 min) to 240 C at 4 C/min; carrier gas ¼ helium at constant 0.9 ml/min flow;
source 70 eV. EO components were identified based on mass spectra and retention
times, in comparison with standards (Banchio et al. 2005). GC analysis was
performed using a PerkinElmer Clarus 500 GC fitted with a 30 m 0.25 mm
fused silica capillary column coated with Supelcowax 10 (film thickness
0.25 μm). GC operating conditions: oven temperature programmed from 60 C
(3 min) to 240 C at 4 C/min; injector/detector temperature 250 C; detector FID;
carrier gas ¼ nitrogen at 0.9 ml/min constant flow.
13.2.6 Determination of Total Phenols
Total phenols were determined as described by Singleton and Rossi (1965). Plant
extracts (each 0.5 ml) or gallic acid (standard phenolic reference compound) were
mixed with Folin-Ciocalteu reagent (0.5 ml, diluted with 8 ml distilled water) and
aqueous Na2CO3 (1 ml, 1 M). After 1 h, the level of total phenols was determined
by colorimetry at wavelength 760 nm and expressed in terms of mg gallic acid
equivalent per g plant dry weight (Lan et al. 2007).
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13.2.7 Statistical Analyses
Data were pooled and subjected to analysis of variance (ANOVA) followed by
comparison of multiple treatment levels with controls using Fisher’s post hoc LSD
(least significant difference) test. Differences between means were considered to be
significant for p < 0.05. The Infostat software program, version 2008 (Group
Infostat, Universidad Nacional de C
ordoba, Argentina), was used for all statistical
analyses.
13.3
Results
13.3.1 Sweet Marjoram (Origanum majorana)
Sweet marjoram is an herb native to Asia Minor (Turkey) and now abundant
throughout the Mediterranean region and southern Europe. It is a small woodystemmed shrub that grows best in well-drained alkaline soil. It reaches a height of
~75 cm and has a hairy stem, soft oval-shaped dark-green leaves, and tiny pinkishwhite flowers. The leaves are typically harvested just after flower bud formation but
before flowering. For blanching, harvested stems are hung in a dark, dry room ~7–
10 days, and leaves are stripped from the stems and stored in an airtight container.
O. majorana is an economically important species (Werker et al. 1993). Its EOs are
used as flavoring in foods and beverages, as fragrances, and as fungicides or
insecticides in pharmaceutical and industrial products (Deans and Svoboda 1990).
O. majorana has strong antioxidant activity, primarily because of its high content of
phenolic acids and flavonoids; this activity makes it useful in health supplements
and food preservation (Vági et al. 2005). O. majorana contains up to 3 % volatile
oils, comprising more than 40 distinct compounds. The major EOs, accounting for
~85 % of the total oil volume, are terpinen-4-ol, cis-sabinene hydrate, α-terpineol,
and trans-sabinene hydrate (Banchio et al. 2008).
The effects of inoculation on plant development differed between P. fluorescens
and B. subtilis (Table 13.1, Fig. 13.1). Some differences among treatments were
observed even after 90 days of growth. Leaf number was 80 % higher in plants
inoculated directly with P. fluorescens than in controls ( p < 0.05) (Table 13.1).
Shoot fresh weight and root dry weight were, respectively, 3.2-fold and 6-fold
higher in P. fluorescens-inoculated plants than in controls ( p < 0.05) (Table 13.1).
In terms of EO composition, PGPR inoculation caused increased production of
certain terpenes (Fig. 13.2). The total EO yield in P. fluorescens-treated plants was
~24-fold higher than in controls ( p ¼ 0.001) (Fig. 13.1).
The EO components that were affected most notably by P. fluorescens inoculation (Fig. 13.2) were terpinen-4-ol, cis-sabinene hydrate, trans-sabinene hydrate,
and α-terpineol. PGPR inoculation caused increases of not only EO synthesis but
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Table 13.1 Effects of single inoculation with P. fluorescens and B. subtilis on growth of
O. majorana plants
Treatment
Leaf number
Shoot fresh weight (mg)
Root dry weight (mg)
Control
P. fluorescens
B. subtilis
14.77 0.60a
25.70 2.10b
13.00 0.59a
0.17 0.01a
0.53 0.03b
0.21 0.02a
0.018 0.01a
0.120 0.02b
0.016 0.02a
Values followed by the same letter within a column are not significantly different according to
Fisher’s LSD test ( p < 0.05)
Essential Oil Yield (ug/ug fresh
weight)
2
b
1,6
1,2
0,8
0,4
a
a
0
Control
B. subtilis
P. fluorescens
200
b
160
120
b
80
40
a
a
a
a
0
cis-sabinene hydrate
EO yield (ug/mg fresh weight)
EO yield (ug/mg fresh weight)
Fig. 13.1 Total EO concentrations in O. majorana inoculated with B. subtilis and P. fluorescens.
Letters above bars indicate significant differences according to Fisher’s LSD test
1000
b
800
400
200
a
a
a
a
0
terpinen-4-ol
α-terpineol
control
b
600
B. subtilis
trans-sabine
hydrate
P. fluorescens
Fig. 13.2 Concentrations of major EO components in shoots of O. majorana inoculated with
B. subtilis and P. fluorescens. Letters above bars indicate significant differences according to
Fisher’s LSD test
also relative percentages (R%) of the EO components. Terpinen-4-ol showed an
increase of 66.65 % in P. fluorescens-treated plants as compared with 53.9 % in
controls. Percent increases for trans-sabinene hydrate (17.33 %, 15.50 %) showed a
similar trend.
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13.3.2 Italian Oregano (Origanum x majoricum)
Oregano, a member of the family Lamiaceae, is used extensively in the food
industry because of its aromatic and antioxidant properties (Petersen and Simmonds
2003). One economically important species is Origanum x majoricum Cambess.
(Italian oregano), a hybrid of O. majorana L. x O. vulgare L. ssp. virens Ietswaart
(Werker et al. 1993). O. x majoricum is a bushy, semiwoody subshrub with upright
or spreading stems and branches. It grows in mats and spreads by rhizomes. The
aromatic leaves are oval-shaped, ~3.8 cm long, and usually pubescent. The plant
bears tiny purple tube-shaped flowers ~0.3 cm long throughout the summer. The
flowers peek out from whorls of purplish-green leafy 2.5 cm long bracts that
resemble tiny pinecones. The abundant EOs located in the leaf trichomes are
lipophilic VOCs (mostly monoterpenes, sesquiterpenes, and phenylpropanoid
metabolites) that are widely used as flavoring in foods and beverages, as fragrances,
and as fungicides or insecticides in pharmaceutical and industrial products
(Harrewijn et al. 2001). O. x majoricum contains up to 3 % volatile oils, comprising
more than 35 different compounds (Tabanca et al. 2004). The major EOs, accounting for ~55 % of the total oil volume, are cis- and trans-sabinene hydrate, terpinene,
carvacrol, and thymol (Banchio et al. 2010).
The effects of direct PGPR inoculation on O. x majoricum development differed
for the three PGPR species examined (B. subtilis, P. fluorescens, A. brasilense)
(Table 13.2, Fig. 13.3). Leaf numbers did not differ significantly ( p > 0.05), but
certain differences among the treatments were evident even after 90 days’ growth.
Shoot fresh weight in all inoculated plants was ~50 % higher than in controls
(Table 13.2). This increase was due to a combination of increased leaf size and
internode elongation. Root dry weight was promoted by all three treatments and
was ~2-fold higher ( p < 0.05) in P. fluorescens-treated and A. brasilense-treated
plants than in controls (Table 13.2).
The total EO yield for P. fluorescens- and A. brasilense-treated plants was 3.57
and 3.41 μg/mg fresh weight, respectively, 2.5-fold higher than for controls
( p ¼ 0.001) (Fig. 13.3). PGPR inoculation caused increased production of certain
terpenes. No change of monoterpene production was observed in B. subtilis-treated
plants.
Table 13.2 Effect of single inoculation with three PGPR on growth of O. x majoricum plants
Treatment
Leaf number
Shoot fresh weight (g)
Root dry weight (g)
Control
P. fluorescens
B. subtilis
A. brasilense
19.77 0.60a
19.61 0.59a
22.70 2.10a
18.33 1.52a
0.59 0.13a
0.89 0.04b
0.97 0.08b
0.83 0.09b
0.10 0.01a
0.31 0.04b
0.21 0.04b
0.32 0.05b
Values followed by the same letter within a column are not significantly different according to
Fisher’s LSD test ( p < 0.05)
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EO Yield (ug/mg fresh weight)
5
b
b
4
3
ab
2
a
1
0
Control
B. subtilis
P. fluorescens
A. brasilense
1,6
c
1,4
bc
1,2
b
1
ab
0,8
ab
0,6
0,4
b
ab
b
a
a
a
0,2
0
g - terpinene
trans -sabinene hydrate
Control
B. subtilis
b
EO yield( ug/mg fresh weight)
EO yield (ug/mg fresh weight)
Fig. 13.3 Total EO concentrations in O. x majoricum inoculated with three PGPR. Letters above
bars indicate significant differences according to Fisher’s LSD test
0,6
b
ab
0,5
b
0,4
0,3
a
a
0,2
0,1
a
a
a
0
thymol
cis -sabinene hydrate
P. fluorescens
carvacrol
A. brasilense
Fig. 13.4 Concentrations of major EO components in shoots of O. x majoricum inoculated with
three PGPR. Letters above bars indicate significant differences according to Fisher’s LSD test
Concentrations of γ-terpinene, trans-sabinene hydrate, cis-sabinene hydrate, and
thymol were higher in PGPR-inoculated plants than in controls in most cases
(Fig. 13.4). Concentrations of trans- and cis-sabinene hydrate, the major EO
components, were ~3-fold and 2-fold higher, respectively, in P. fluorescens- and
A. brasilense-treated plants than in controls. The thymol content was increased by
all treatments. γ-terpinene showed a significant increase only in P. fluorescenstreated plants. Carvacrol showed a significant increase (~9-fold; p < 0.05) only in
A. brasilense-treated plants (Banchio et al. 2010).
13.3.3 Sweet Basil (Ocimum basilicum)
Ocimum basilicum is an aromatic, annual herb, generally 0.3–0.5 m tall (as high as
1 m tall for certain cultivars). The leaves of some cultivars have leaves and stems
with a deep purple color. The leaves are ovate, often puckered, the flowers are white
or pink, and the fruits have four small nutlets that become mucilaginous when wet.
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Table 13.3 Plant growth parameters of O. basilicum exposed to B. subtilis GB03 medium root
media inoculation or GB03 VOCs
Treatment
Root inoculation
Control
B. subtilis
VOC exposure
Control
B. subtilis
Leaf number
Shoot fresh weight (g)
Root dry weight (g)
6.30 0.03a
8.01 0.01b
0.25 0.04a
0.65 0.11b
0.05 0.01a
0.09 0.01b
5.04 0.40a
6.40 0.40b
0.88 0.04a
1.72 0.09b
0.01 0.001a
0.02 0.002a
Values followed by the same letter within a column are not significantly different according to
Fisher’s LSD test ( p < 0.05)
O. basilicum is used in perfumery, soapmaking, and flavoring liqueurs. The seeds
are edible and become mucilaginous when soaked in water. The leaves are used to
make an insecticide that protects stored crops from beetle damage. O. basilicum is
rich in stored EOs and is commonly utilized in the spice industry (Werker
et al. 1993). The abundant EOs located in leaf trichomes are lipophilic VOCs that
consist mostly of monoterpenes, sesquiterpenes, and phenylpropanoid metabolites.
O. basilicum EOs contain ~40 different metabolites. Two components, R-terpineol
and eugenol, account for almost 60 % of the total VOC content (Simon et al. 1990;
Zheljazkov et al. 2008).
O. basilicum was exposed to direct root inoculation with B. subtilis GB03 culture
medium and to VOCs emitted by GB03 (Banchio et al. 2009). To investigate whether
GB03 VOCs affected O. basilicum growth, the plants and bacteria were grown on the
same dish with physical separation such that VOCs but not solutes from the bacteria
could reach the plant. Leaf number was increased by both root inoculation and VOC
exposure in comparison with controls ( p < 0.05) (Table 13.3). Leaf area was
increased 2-fold in plants exposed to GB03 VOCs. Fresh shoot weight was increased
3-fold and 2-fold by root inoculation and VOC exposure, respectively ( p < 0.05).
Root dry weight was increased only in root-inoculated plants (Table 13.3).
EO production was increased by both GB03 medium root inoculation and
exposure to GB03 VOCs (Fig. 13.5). The total EO yield measured on a fresh weight
basis was 2-fold less for root inoculation than for VOC exposure.
Increases in the major EO components were observed for both experimental
treatments. Terpineol yield was increased ~2-fold for both treatments. Eugenol yield
was increased ~8-fold for root inoculation and ~6-fold for VOC exposure (Fig. 13.6).
13.3.4 Wild Marigold (Tagetes minuta)
Wild marigold (Tagetes minuta) is an important member of the Asteraceae family.
It has tiny involucres, toxic flowers, and a unique odor. T. minuta is native to the
temperate grasslands and mountain regions of southern South America but is now
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a Root inoculation
b VOC exposure
EO yield (ng/mg fresh weight)
6
EO yield (ug/mg fresh weight)
273
b
4
a
2
1,8
b
1,5
1,2
0,9
0,6
a
0,3
0
0
control
control
B.subtilis
B.subtilis
1,2
Root inoculation
b
b
1
0,8
0,6
0,4
a
0,2
a
0
terpineol
eugenol
control
EO yield (ug/mg fresh weight)
EO yield (ug/mg fresh weight)
Fig. 13.5 EO concentration in O. basilicum exposed to B. subtilis GB03 medium root inoculation
vs. GB03 VOCs. Letters above bars indicate significant differences according to Fisher’s LSD test.
(a) Root inoculation, (b) VOC exposure
VOC exposure
0,8
b
b
0,6
0,4
a
0,2
a
0
terpineol
eugenol
B.subtilis
Fig. 13.6 EO concentrations in O. basilicum exposed to B. subtilis GB03 medium root inoculation or GB03 VOCs. Letters above bars indicate significant differences according to Fisher’s
LSD test
distributed worldwide; it is a “weed” with the ability to grow in environments
ranging from extreme temperate to tropical (Singh and Singh 2003). T. minuta is an
annual plant, 50–150 cm high, with a glabrous, erect, branched stem and opposite
branches. The leaves are opposite and pinnately parted; the upper leaves are
alternate. The leaves have a length of 4–8 cm, width of 3–4.5 cm, and margins
that are acute and serrate. There are corymbiform dense inflorescences at the ends
of branches. The phyllaries form a cylindrical tube that is naked at the base. There
are three florets that are ligulate, dark brown, or lemon colored. Tubular florets are
orange. The achene is dark brown and covered with appressed hairs. In tropical
regions, T. minuta is grown for EO production (Shahzadi et al. 2010). The EO,
known as “Tagetes oil” to retailers and end users, is a commercially valuable
product (Singh and Singh 2003) used primarily in the preparation of high-grade
perfumes (Kaul et al. 2000). Because of the high demand for Tagetes oil, there has
been increasing cultivation of T. minuta for commercial production (Ghera and
Leon 1999).
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Table 13.4 Effects of single inoculation and co-inoculation with P. fluorescens and A. brasilense
on T. minuta growth parameters and total phenol content
Treatment
Leaf number
Shoot fresh
weight (g)
Root dry
weight (g)
Total phenol content
(Ac Gal/mg fresh weight)
Control
P. fluorescens
A. brasilense
P. fluorescens
+ A. brasilense
12.44 0.40a
16.18 0.54c
14.94 0.45b
16.68 0.52c
0.70 0.01a
0.97 0.04b
0.77 0.04a
1.01 0.06b
0.14 0.02a
0.20 0.03ab
0.26 0.04b
0.24 0.02b
0.15 0.02a
0.27 0.03b
0.33 0.03b
0.30 0.03b
Values followed by the same letter within a column are not significantly different according to
Fisher’s LSD test ( p < 0.05)
EO yield (ug/mg fresh weight)
1
ab
0,8
b
a
0,6
a
0,4
0,2
0
control
A. brasilense
P. fluorescens
P. fluorescens + A.
brasilense
Fig. 13.7 Total EO concentrations in O. basilicum single inoculated or co-inoculated with
P. fluorescens and A. brasilense. Letters above bars indicate significant differences according to
Fisher’s LSD test
The effects of PGPR inoculation on T. minuta growth and development varied
depending on the inoculated strain (P. fluorescens WCS417r, A. brasilense, or their
combination) (Table 13.4, Fig. 13.7). Most of the growth parameters evaluated
were significantly ( p < 0.05) increased by each of the three treatments (Table 13.4).
Leaf number, shoot fresh weight, and root dry weight were all increased significantly by A. brasilense treatment (Table 13.4); root dry weight was 80 % higher
than in controls. The increase of root weight was due primarily to an increased
number of lateral roots (data not shown). Shoot fresh weight was increased significantly (~50 %) by single inoculation of P. fluorescens or co-inoculation of
P. fluorescens and A. brasilense. Leaf number showed a similar trend (Table 13.4).
Leaf number was 33 % higher in P. fluorescens-inoculated and co-inoculated plants
than in controls, as reflected by the increased shoot fresh weight. Root dry weight in
these treated plants was significantly (~35 %) increased, partly because of an
increase in root length.
The total phenol content was 2-fold higher ( p < 0.005) in single-inoculated or
co-inoculated plants than in controls (Table 13.4). The total EO yield was 50 %
higher ( p ¼ 0.02) in P. fluorescens single-inoculated or co-inoculated plants than in
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0,005
b
c
a
a
0,002
ab
b
a a
0,001
0,06
0,04
0
(Z) tagetone
0,3
a
b
a
a
a
a
0,1
0
0
limonene
(E) tagetone
control
a
0,2
a
0,02
b
b
0,4
b
b
0,003
b
b
0,08
a
0,004
0,5
0,1
b
275
A. brasilense
(Z) ocimenone
P. fluorescens
(Z)- β ocimene
(E) ocimenone
P. fluorescens + A. brasilense
Fig. 13.8 Concentrations of major EO components in shoots of T. minuta plants single inoculated
or co-inoculated with A. brasilense and P. fluorescens. Letters above bars indicate significant
differences according to Fisher’s LSD test
controls (Fig. 13.7). Single inoculation with A. brasilense did not significantly
affect the total monoterpene content.
Levels of the major EO components analyzed, i.e., (Z )-(E)-tagetone, (Z )-(E)ocimenone, (Z)-β-ocimene, and limonene (which together accounted for ~60 % of
the total EO content), were usually different in inoculated plants than in controls
(Fig. 13.8). (E)-ocimenone was by far the predominant component (accounting for
~50 % of the total EO content) and was increased affected by each of the experimental treatments. A. brasilense single inoculation increased the levels of (E)ocimenone and (E)-tagetone by 71 and 66 %, respectively ( p < 0.005) (Fig. 13.8).
P. fluorescens single inoculation caused increases of each of the EO components
except (Z )-β-ocimene. The effects of co-inoculation were similar to those of
P. fluorescens single inoculation.
Single inoculation with A. brasilense or (to a greater degree) P. fluorescens
affected plant growth and development. Co-inoculation caused greater increases in
plant growth/development parameters and secondary metabolites, indicating a
synergistic effect of the two PGPR. The population size of P. fluorescens increased
from 105 CFU/ml at day 0 to 108 CFU/ml at day 7 and remained roughly constant
thereafter ( p > 0.05 for comparison between days 7 and 14). The population size of
A. brasilense increased from 105 to 106 CFU/ml during the same period ( p < 0.05
for comparison between days 7 and 14). Copresence of the two strains was observed
throughout the co-inoculation experiments. P. fluorescens showed the same behavior in co-inoculation as in single inoculation (108 CFU/ml; p > 0.05). In contrast,
A. brasilense in co-inoculation increased its population during days 0–7 and
maintained its population thereafter (106 CFU/ml) (Cappellari et al. 2013).
13.3.5 Peppermint (Mentha x piperita)
The genus Mentha, which includes >25 species, is responsible for ~2,000 t of EO
production worldwide, making it the second most important genus (after Citrus) in
this regard (Mucciarelli et al. 2003). Peppermint, a naturally occurring hybrid of
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Table 13.5 Effect of VOCs from three PGPR on M. x piperita growth parameters
Treatment
Leaf number
Shoot fresh weight (g)
Root dry weight (g)
Control
P. fluorescens
B. subtilis
A. brasilense
23.48 2.20a
33.81 3.61a
34.91 5.63a
28.22 4.11a
0.162 0.08a
0.278 0.04ab
0.319 0.03b
0.21 0.04a
0.005 0.001a
0.014 0.004ab
0.019 0.004b
0.009 0.003a
Values followed by the same letter within a column are not significantly different according to
Fisher’s LSD test ( p < 0.05)
water mint (Mentha aquatica) and spearmint (Mentha spicata), was first cultivated
in England in the late seventeenth century. It is an herbaceous rhizomatous perennial plant 30–90 cm tall, with smooth stems that are square in cross section. The
rhizomes are wide-spreading, fleshy, and bare fibrous roots. The leaves are 4–9 cm
long and 1.5–4 cm wide, dark green with reddish veins, with an acute apex and
coarsely toothed margins. The leaves and stems are usually slightly fuzzy. The
flowers are purple, 6–8 mm long, with a four-lobed corolla ~5 mm in diameter; they
are produced in whorls around the stem, forming thick, blunt spikes. Flowering is
from middle to late summer. M. x piperita is a fast-growing plant and spreads very
quickly. Plants growing in vitro contain 3 % volatile oils, consisting of >50
different compounds. The EOs, which account for 60 % of the total oil volume,
are (+) pulegone, ( ) menthone, ( ) menthol, and (+) menthofuran (Santoro
et al. 2011).
To investigate the effect of VOCs from three PGPR on M. x piperita growth,
plants and bacteria were grown in I-plates. The effect of VOC emission on plant
development varied depending on the PGPR species (Table 13.5, Fig. 13.9). Clear
differences among the treatments were detectable after 30 days’ growth.
Exposure to B. subtilis VOCs caused a 2-fold increase ( p < 0.05) in shoot fresh
weight, and similar effects were observed for P. fluorescens treatment (Table 13.5).
Root dry weight in B. subtilis-treated plants was 3.5-fold higher than in controls and
significantly ( p < 0.05) higher than in plants exposed to VOCs of P. fluorescens or
A. brasilense. The increased shoot fresh weight of B. subtilis-treated plants was due
to a 2-fold increase in leaf area in combination with internode elongation (data not
shown). Leaf number was not changed significantly by any of the treatments
(Table 13.5).
EO yields for P. fluorescens- and A. brasilense-treated plants were, respectively,
4.46 and 3.22 mg/mg fresh weight, ~2-fold higher than for controls (Fig. 13.9).
Yields of the major EOs (+) pulegone, ( ) menthone, ( ) menthol, and (+)
menthofuran were generally higher in treated plants than in controls (Fig. 13.10).
Pulegone concentration was significantly increased (3.14-fold; p < 0.05) only by
P. fluorescens treatment. Menthone was increased 15.4- and 13.5-fold ( p < 0.05) in
P. fluorescens- and A. brasilense-treated plants, respectively. Menthofuran was
increased significantly in P. fluorescens-treated plants. The only decreases in EO
yield (~5-fold) were observed for menthol and menthofuran in A. brasilense-treated
plants. Exposure to PGPR VOCs led to changes in relative percentage (R%), as well
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EO yield (ug/mg fresh weight)
6
b
5
ab
4
a
3
a
2
1
0
Control
P. fluorescens
B. subtilis
A. brasilensis
Fig. 13.9 EO concentrations in M. x piperita VOCs from three PGPR. Letters above bars indicate
significant differences according to Fisher’s LSD test
0,4
4
3
a
2
a
a
1
EO yield (ug/mg fresh weight)
EO yield (ug/mg fresh weight)
a
b
a
0,3
a
0,2
bc
c
ab
0,1
c
b
a
ab
bc
a
0
0
(-)-menthone
(+)-pulegone
Control
P. fluorescens
B. subtilis
(-)-menthol
(+)-menthofuran
A. brasilensis
Fig. 13.10 Concentrations of major EO components in M. x piperita exposed to VOCs from three
PGPR. Letters above bars indicate significant differences according to Fisher’s LSD test
as yield, of EOs. R% for pulegone, the major EO component, increased to 59.9 % in
P. fluorescens-treated plants, compared with 45.3 % in controls. R% for menthone
increased in all cases. R% for menthol was lower in P. fluorescens- and
A. brasilense-treated plants (6.1 %; 5.9 %) than in controls (9.6 %) but was higher
in B. subtilis-treated plants (11.3 %). The only EO that showed a significant R%
decrease in A. brasilense-treated plants was menthofuran.
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M.V. Santoro et al.
Discussions
Enhanced growth and development following inoculation with PGPR has been
reported for a number of plant species (Vessey 2003; Gray and Smith 2005; Van
Loon 2007). The possible causes vary depending on the species and may include
both direct and indirect mechanisms (Glick 1995; Gupta et al. 2002). Some
examples of these mechanisms, which may be active simultaneously or sequentially
at different stages of plant growth, are (1) increased mineral nutrient solubilization
and nitrogen fixation, which make nutrients available for the plant; (2) suppression
of soilborne pathogens (through production of hydrogen cyanide, siderophores,
antibiotics, and/or competition for nutrients); (3) enhancement of plant tolerance
to stress factors such as drought, salinity, and metal toxicity; and (4) production of
phytohormones such as indole-3-acetic acid (IAA) (Gupta et al. 2002). Some PGPR
have the enzyme 1-aminocyclopropane-1-carboxylate (ACC) deaminase, which
hydrolyzes ACC, the immediate precursor of ethylene in plants. By lowering
ethylene concentration (and thereby the inhibitory effect of ethylene) in seedlings,
these PGPR increase seedling root length (Glick 1995).
The effects of PGPR inoculation or VOC emission on the plant species
(O. majorana, O. x majoricum, O. basilicum, T. minuta, M. x piperita) evaluated
in this study varied depending on the inoculated strain (P. fluorescens WCS417r,
A. brasilense Sp7, Bacillus subtilis GB03, or their combination). Previous studies
have demonstrated host response specificity in plant species treated with PGPR
(O’Neal et al. 2002) and diverse responses to PGPR inoculation.
In our study, the growth parameters evaluated were significantly modified in
most cases by P. fluorescens single inoculation and by P. fluorescens/A. brasilense
co-inoculation. A. brasilense single inoculation promoted all growth parameters in
O. x majoricum, but only enhanced root dry weight in T. minuta.
B. subtilis inoculation caused significant increases in shoot fresh weight and root
dry weight in O. x majoricum and O. basilicum, but had no significant effect on
O. majorana.
Exposure of O. basilicum and M. x piperita to B. subtilis VOCs caused increases
in shoot fresh weight whereas exposure of M. x piperita to A. brasilense VOCs had
no such effect.
All plants in the study received Hoagland’s nutrient solution and were grown on
a sterilized, inert substrate in which nitrogen and other nutrients were available. The
growth stimulatory effects observed were therefore not due to solubilization of
phosphates, oxidation of sulfates, increased nitrate availability, extracellular production of antibiotics, or induction of plant systemic resistance (Kloepper 1993).
Rather, the enhanced growth of the plant species observed following PGPR inoculation was presumably due to increased production of growth hormones and/or
VOCs emitted by the PGPR.
Consistent with our findings, fluorescent pseudomonads were reported to promote overall growth of various crop species (Vikram 2007). P. fluorescens
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enhanced plant growth through production of growth-promoting substances such as
IAA and cytokinins (Vikram 2007; De Salamone et al. 2001). The role of auxins
and cytokinins in enhancing plant cell division and root development is well
documented (Arshad and Frankenberger 1993). IAA is involved in root initiation,
cell division, and cell enlargement (Gray and Smith 2005) and increases root
surface area and consequent access to soil nutrients. Cytokinins promote cell
division, cell enlargement, and tissue expansion in certain plant parts (Gray and
Smith 2005). A. brasilense, in addition to its nitrogen-fixing ability, secretes
phytohormones such as auxins, cytokinins, and gibberellins. Auxins are quantitatively the most abundant phytohormones secreted by Azospirillum. Auxin production, rather than nitrogen fixation, is considered to be the major factor responsible
for stimulation of rooting and enhancement of plant growth (Bloemberg and
Lugtenberg 2001).
We found that the effects of PGPR inoculation and VOCs on the formation of
plant secondary compounds are species specific. The total phenol content in
T. minuta was increased by single inoculation or co-inoculation with
P. fluorescens and A. brasilense. Phenolic compounds are a major class of plant
secondary metabolites and one of the most common and widespread groups of plant
components in general. They are essential for plant growth and reproduction. Some
phenolic compounds are produced constitutively; others are induced as a plant
defensive response. In contrast to basic metabolism, which refers to the anabolic
and catabolic processes required for cell maintenance and proliferation, secondary
metabolism refers to compounds present in specialized cells that are not directly
essential for basic photosynthetic or respiratory metabolism, but are considered to
be necessary for plant survival in the external physical environment (Lattanzio
et al. 2006). There has been recent interest in phenolic acids because of their
potential protective role, via ingestion of fruits and vegetables, against oxidative
damage diseases (coronary heart disease, stroke, cancers). Recent studies have
clearly demonstrated the important antioxidant activities of phenolic compounds
and the advantages of their use as natural antioxidants in processed foods (Lattanzio
et al. 2006). Phenolic compounds also act as defensive compounds (against herbivores, microbes, viruses, or competing plants) and as signaling compounds
(to attract pollinating or seed-dispersing animals) and protect the plant from
ultraviolet (Kutchan 2001).
EO yield was increased to varying degrees by P. fluorescens inoculation in
O. majorana, O. x majoricum, and T. minuta. Monoterpene production was
increased 2-fold in some plants and 24-fold in O. majorana. VOCs emitted by
P. fluorescens had the same effect on M. x piperita as direct root inoculation,
whereas the effects of B. subtilis VOCs vs. inoculation were different.
O. majorana and O. x majoricum did not show changes in EO yield, whereas EO
yield in O. basilicum was increased 2-fold. Similar results were observed for VOC
exposure in O. basilicum. VOC exposure did not affect the total monoterpene
accumulation in M. x piperita. An increase in the total EO yield by root inoculation
with A. brasilense was observed in O. x majoricum, but not in T. minuta.
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The enhanced EO accumulation response was not due to increased biomass. It
may have resulted from increased terpene biosynthesis, although we did not
measure this process. In addition to increased EO synthesis, relative percentages
(R%) of EO components were changed significantly by inoculation in several cases.
Our findings indicate that effects of PGPR VOCs on plants are species specific;
i.e., VOCs from a particular bacterial strain do not cause the same effects, or to the
same degree, in all plant species. A particular plant–bacteria combination has its
own characteristic responses. Possible explanations for this phenomenon are as
follows: (1) different plants respond to different component(s) of VOC mixtures;
(2) reactive sites are different; (3) plants differ in their ability to metabolize VOCs.
The concentration and composition of oils in plants serve important ecological
roles. Increased EO synthesis provides a defensive response to colonization by
microorganisms; several EOs have antimicrobial properties (Sangwan et al. 2001).
Analogously, monoterpene synthesis is induced by herbivore feeding in
Minthostachys mollis (Banchio et al. 2005) and other plant species, apparently to
protect damaged leaves from further attack (Harrewijn et al. 2001).
There have been few attempts to elucidate the relative quantitative and qualitative contributions of rhizobacteria to formation of plant secondary compounds.
Induction of secondary metabolite responses has been reported in other beneficial
microbe–plant interactions involving arbuscular mycorrhizal (AM) fungi. Gupta
et al. (2002) inoculated the AM fungus Glomus fasciculatum in cultivars of wild
mint (Mentha arvensis) and observed increased plant height, shoot growth, and oil
content. Khaosaad et al. (2006) observed changes of EO concentration (but not
composition) following mycorrhizal inoculation of Origanum sp. Copetta
et al. (2006) reported increases of glandular hair abundance and EO yield in
inoculated O. basilicum. The increased EO yield was associated with a larger
number of peltate glandular trichomes, the primary site of EO synthesis. Belowground AM fungi cause changes in leaf isoprenoid content that favor EO production, particularly under drought stress condition or following jasmonic acid
(JA) application (Asensio et al. 2012). AM fungi increase plant growth and EO
production because mycorrhization allows the root system to exploit a greater
volume of soil by (1) extending the root zone, (2) reaching smaller soil pores not
accessible by root hairs, and (3) acquiring organic phosphates through production
of extracellular acid phosphatases (Bouwmeester et al. 2007).
Terpene compounds help the plant’s photosynthetic apparatus recover from brief
episodes of high temperature. Isoprene may physically stabilize thylakoid membranes at high temperature or quench reactive oxygen species (e.g., ozone) that
cause membrane damage (Pichersky and Gershenzon 2002). Enhanced biosynthesis
of secondary metabolites can be triggered by certain stress factors (Ramomoorthy
et al. 2001). Nonpathogenic rhizobacteria have been shown to stimulate secondary
metabolism in plants through a mechanism termed ISR (induced systemic resistance) (van Oosten et al. 2008; Pozo et al. 2008; Pieterse et al. 2009; Pineda
et al. 2012). The occurrence of ISR has been demonstrated in various plants
inoculated with various species of rhizobacteria (Pineda et al. 2013). ISR may be
local or systemic (when it is expressed at sites not directly exposed to the inducing
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agent). The inducing agent may be a chemical activator or an extract of cells of
living organisms or microorganisms. ISR has been described as “activation of the
host plant’s physical or chemical defenses by an inducing agent” (Kloepper 1993).
Interestingly, PGPR simultaneously induce an ISR response and promote plant
growth (Kloepper et al. 2004; Yi et al. 2013).
Both direct and indirect defenses are under the control of a complex network of
signal transduction pathways that are regulated by various phytohormones, of
which JA is a central regulator (Snoeren et al. 2009; Kusnierczyk et al. 2011). JA
exerts its protective effects by regulating a wide range of defense-related processes,
including the synthesis of toxic secondary metabolites (Pauwels et al. 2009). JA
also triggers the biosynthesis of mono- and sesquiterpenes (Arimura et al. 2000)
that are presumed to act as master switches for plant responses stimulated by rootcolonizing bacteria, leading to activation of distinct sets of defense genes responsible for terpenoid formation (Pineda et al. 2012).
Some of the roles of EO components are relatively straightforward; e.g., they
play numerous generalized protective roles (antioxidant, free radical scavenging,
UV light absorbing, antiproliferative, etc.) and defend the plant against microorganisms (bacteria, fungi, viruses). EO components also help modulate interplant
relationships, acting as allelopathic defenders of the plant’s growing space against
competing plants. More complex roles include defining or modifying the plant’s
relationship with herbivores (Tahara 2007; Wink 2000). The primary role of EO
components is often viewed as feeding deterrence; to this end, many phytochemicals are bitter and/or toxic to potential herbivores. The toxic effects often extend to
direct interactions with the herbivore’s central and/or peripheral nervous systems
(Rattan 2010). Secondary metabolites often act as agonists or antagonists of
neurotransmitter systems (Wink 2000; Rattan 2010) or form structural analogs of
endogenous hormones (Miller and Heyland 2010).
Biosynthesis of terpenoids depends on primary metabolism (e.g., photosynthesis)
and oxidative pathways for carbon and energy supply (Singh et al. 1990). Giri
et al. (2003) found that net photosynthesis of PGPR host plants increases as a result
of improved nutritional status. Factors that increase dry matter production may
influence the interrelationship between primary and secondary metabolism, leading
to increased biosynthesis of secondary products (Shukla et al. 1992). Increased plant
biomass may result in greater availability of substrate for monoterpene biosynthesis
(Harrewijn et al. 2001). The increased concentration of monoterpenes in inoculated
plants may be caused by growth-promoting substances produced by the inoculated
microorganism that affect plant metabolic processes. Because the plants in the
present study were grown in enriched medium containing nitrogen and other nutrients, bacterial metabolites are the most likely growth-promoting substance.
Knowledge of the adaptive mechanisms of plants is of interest from an ecophysiological point of view. These mechanisms also provide an important (probably
crucial) starting point for improvement of plant production, including optimization
of secondary metabolite production. The use of fungal and bacterial inoculants is an
efficient biotechnological alternative for stimulating secondary metabolism in
plants. Studies of such inoculants will also clarify certain adaptive processes that
are poorly understood at present.
mkumar9@amity.edu
282
13.5
M.V. Santoro et al.
Conclusions
The present findings show that inoculation of certain PGPR causes systemic
induction of monoterpene pathways in various aromatic plants species, suggesting
that PGPR inoculation can significantly increase productivity and reduce the
amount of fertilizer required for economically viable aromatic crop production.
The markets for medicinal plants, aromatic plants, and organic foods are steadily
expanding (Adam 2005; Hartman Group 2006). As consumers become more
concerned and knowledgeable about their own health and wellness, there is
increasing demand for quality plant material, produced by sustainable methods
and uncontaminated by synthetic pesticides or genetically modified organisms
(Craker 2007).
Acknowledgments This study was supported by a grant from Consejo Nacional de
Investigaciones Cientı́ficas y Tecnol
ogicas. MS and LC have fellowships from Consejo Nacional
de Investigaciones Cientı́ficas y Técnicas of the República Argentina (CONICET). EB and WG
are Career Member of CONICET. The authors are grateful to Dr. S. Anderson for English editing
of the manuscript.
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mkumar9@amity.edu
Chapter 14
Medicinal Plants and PGPR: A New Frontier
for Phytochemicals
Dilfuza Egamberdieva and Jaime A. Teixeira da Silva
14.1
Introduction
Plant-derived medicines have been used worldwide in the treatment of numerous
human diseases for centuries (Chiariandy et al. 1999). Herbal products have been an
integral part of ancient traditional medicine systems that have enriched our modern
knowledge of herbal medicine (Abu-Irmaileh and Afifi 2003; Sarker and Nahar
2007). Increasing awareness of hazards and toxicity associated with the indiscriminate use of synthetic drugs and antibiotics, as well as the use of medicinal plants for
the treatment of various diseases, has became popular (Saganuwan 2010).
The medicinal value of these plants lies in some chemical substances that
produce a definite physiological action on the human body (Edeoga et al. 2005).
Numerous studies have validated the traditional use of medicinal plants by investigating numerous phytochemicals (including alkaloids, tannins, flavonoids, phenolic compounds, and terpenes) present in active extracts (Palombo 2006; Van Wyk
and Wink 2004). Plant leaves, roots, rhizomes, stems, bark, flowers, fruits, grains,
or seeds contain chemical components that are biologically active (Doughari
et al. 2009). Plants synthesize a diverse array of secondary metabolites that are
important for them to survive and flourish in their natural environment
(Wu et al. 2007), where they also have protective actions in relation to abiotic
stresses such as those associated with temperature, water status, and mineral
nutrients (Kaufman et al. 1999).
D. Egamberdieva (*)
Department of Biotechnology and Microbiology, National University of Uzbekistan,
University str. 1, Tashkent 100174, Uzbekistan
e-mail: egamberdieva@yahoo.com
J.A. Teixeira da Silva
P. O. Box 7, Miki-cho post office, Ikenobe 3011-2, Kagawa-ken 761-0799, Japan
e-mail: jaimetex@yahoo.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_14
mkumar9@amity.edu
287
288
D. Egamberdieva and J.A. Teixeira da Silva
Plant-derived novel biological active compounds continue to be used worldwide
and developed further for the treatments of various ailments, including asthma,
gastrointestinal symptoms, skin disorders, respiratory and urinary problems, and
hepatic and cardiovascular disease (Cousins and Huffman 2002; Saganuwan 2010).
Plant secondary metabolites are a major source of bioactive natural products and
are valuable pharma- and nutraceuticals; therefore, medicinal plants are commercially cultivated in many countries worldwide (Phillipson 2001). Successful cultivation of medicinal plants depends on biotic and abiotic factors which can modulate
the secondary metabolites, essential oil composition, and yield (Juliani et al. 2006).
It is important to avoid the use of chemical fertilizers and pesticides in the
cultivation of plants since they are typically consumed without being further
processed after harvest (Banchio et al. 2008).
Therefore, current research in drug discovery from medicinal plants involves
innovative biotechnologies such as the introduction of biological fertilizers and
biopesticides which increase the level of biologically active compounds in medicinal plants (Rajasekar and Elango 2011; Bharti et al. 2013; Teixeira da Silva and
Egamberdieva 2013). Plant growth-promoting rhizobacteria (PGPR) and arbuscular
mycorrhizal (AM) fungi are able to promote plant growth, nutrient uptake, and
phytochemical constituents, protect plants against various soilborne pathogens, and
can help plants to adapt to a number of environmental stresses (Jeffries et al. 2003;
Egamberdieva et al. 2013a; Egamberdieva and Lugtenberg 2014; Hameed
et al. 2014).
In this review, we examine the plant-microbe interactions with medicinal plants
and their functional characteristics. We also discuss the use of plant-associated
beneficial microorganisms to enhance the levels of phytochemicals.
14.2
Phytochemical Constituents of Medicinal Plants
The primary focus of research to date on plants, which are reservoirs of biologically
active compounds with therapeutic properties and have been used for curing
various diseases, has been in the areas of phytochemistry and pharmacognosy
(Briskin 2000). Biologically active compounds are primarily secondary metabolites
and their derivatives such as alkaloids (Sarker and Nahar 2007), glycosides (Firn
2010), flavonoids (Kar 2007), phenolics (Puupponen-Pimiä et al. 2001), saponins
(Sarker and Nahar 2007), tannins (Kar 2007), terpenes (Martinez et al. 2008),
anthraquinones (Maurya et al. 2008), essential oils (Martinez et al. 2008), and
steroids (Madziga et al. 2010). More than 12,000 alkaloids are known to exist in
about 20 % of plant species, and only few have been exploited for medicinal
purposes (Firn 2010), and over 4,000 flavonoids are known to exist with quercetin,
kaempferol, and quercitrin being common flavonoids present in nearly 70 % of
plants (Kar 2007). Glycosides are classified on the basis of type of sugar component, chemical nature of the aglycone, or pharmacological action (Sarker and Nahar
2007), and phenolics essentially represent a host of natural antioxidants (Kar 2007),
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Medicinal Plants and PGPR: A New Frontier for Phytochemicals
289
whereas saponins are shown to have hypolipidemic and anticancer activity. Essential oils are referred to as volatile oils or ethereal oils because they have a tendency
to evaporate on exposure to air; chemically, a single volatile oil comprises more
than 200 different chemical components (Martinez et al. 2008).
Plant secondary metabolites play protective roles as antioxidant, free radicalscavenging, and antiproliferative agents and defend the plant against herbivory and
pathogen attack (Wink and Schimmer 1999; Briskin 2000), and it is likely that their
ecological function may have potential medicinal effects for humans. According to
Wink and Schimmer (1999), bioactive agents involved in plant defense through
cytotoxicity toward microbial pathogens and/or against herbivores could have
beneficial effects in humans.
Environmental factors such as soil type, nutrients, temperature, drought, salinity,
as well as competition for nutrients among microorganisms are important variables
affecting phytochemical production in medicinal plants (Perez-Balibrea et al. 2008;
Egamberdieva et al. 2013b).
14.3
Plant Beneficial Microorganisms
The rhizosphere is colonized more intensively by microorganisms than other
regions of the soil (Lugtenberg et al. 2001). Beneficial rhizosphere bacteria are of
two general types, those forming a symbiotic relationship with the plant and those
that are free living in the soil and root (Barriuso et al. 2005; Lugtenberg and
Kamilova 2009; Berg et al. 2013). Beneficial rhizobacteria can improve seed
germination, root and shoot growth, yield, nutrient uptake, and plant stress tolerance and are able to control various diseases (Çakmakcı et al. 2005; Egamberdieva
and Islam 2008; Jabborova et al. 2013). Several root-associated bacteria showing
plant growth-promoting activity belong to several genera, including Arthrobacter,
Azospirillum, Azotobacter, Bacillus, Bradyrhizobium, Burkholderia, Cellulomonas,
Clostridium, Enterobacter, Flavobacterium, Micrococcus, Paenibacillus, Pseudomonas, Rhizobium, Sinorhizobium, and Serratia (Somers et al. 2004; Rajasekar and
Elango 2011; Egamberdieva et al. 2011, 2013b). Several studies have reported that
AM fungi also improve plant growth and development and supply mineral nutrients
to plants, especially phosphorus, which is precipitated by ions such as Ca, Mg, and
Zn (Al-Karaki et al. 2001; Hameed et al. 2014). They play a key role in alleviating
toxicity induced by salt stress, thus normalizing the uptake mechanism in plants by
supplying essential nutrients.
Moreover, the production of secondary metabolites such as total phenols, alkaloids, tannins, and lycopene and antioxidant activity on various plants was also
stimulated after treatment with PGPR and AM fungi (Elango 2004). Mixed inoculation with PGPR and Rhizobium or AM fungi creates synergistic interactions that
may result in a significant increase in growth, in symbiotic performance, and an
enhancement in the uptake of mineral nutrients such as phosphorus, nitrogen,
potassium, and other minerals (Adesemoye and Kloepper 2009; Egamberdieva
mkumar9@amity.edu
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D. Egamberdieva and J.A. Teixeira da Silva
et al. 2010). Recent studies show that root-associated beneficial microorganisms
play an important role in the improvement of plant growth of medicinally important
plants and increase phytochemical constituents which are widely used for curing
various diseases (Bharti et al. 2013; Teixeira da Silva and Egamberdieva 2013).
14.4
PGPR Improve Bioactive Phytochemical Levels
in Plants
There are many reports on the beneficial effect of PGPR and AM fungi on plant
growth, nutrient uptake, and secondary metabolite production, such as phenols,
flavonoids, alkaloids, saponins, and tannins of medicinal plants, including
Catharanthus roseus (Karthikeyan et al. 2009), Origanum majorana L. (Banchio
et al. 2008), Matricaria chamomilla (Razmjoo et al. 2008), Ocimum basilicum
(Banchio et al. 2009), Salvia militiorrhiza (Wu et al. 2007), Mentha arvensis (Gupta
et al. 2002), and Withania somnifera (Rajasekar and Elango 2011). The improvement of secondary metabolites in medicinal plants by plant beneficial microorganisms is given in Table 14.1.
Ocimum basilicum L. (sweet basil) is rich in essential oils and contains approximately 40 different metabolites, and among them more than 60 % are terpineol and
eugenol (Banchio et al. 2009). The content of those two essential oil components
increased up to tenfold in plants exposed to Bacillus subtilis GB03 root inoculation
or volatiles. In other studies, plant growth and the essential oil content of Ocimum
spp. increased after plants were inoculated with Glomus fasciculatum and Azotobacter chroococcum (Vinutha 2005), Pseudomonas putida and A. chroococcum
(Ordookhani et al. 2011), and the AM fungus, Glomus mosseae (Copetta
et al. 2006).
Banchio et al. (2008) studied the effects of root colonization by PGPR on
biomass and qualitative and quantitative composition of essential oils in the aromatic crop Origanum majorana L. (sweet marjoram). They found that plants
inoculated with P. fluorescens or Bradyrhizobium increased total essential oil
yield in plants and may have resulted from increased biosynthesis of terpenes.
The main compounds affected by inoculation with P. fluorescens were terpinen-4ol, cis-sabinene hydrate, trans-sabinene hydrate, and α-terpineol, and their concentrations increased by 1,000-fold compared to control plants.
Increased essential oil contents in the shoots of Origanum sp. (Khaosaad
et al. 2006) and Pelargonium species (Venkateshwar Rao et al. 2002) by the AM
fungus Glomus mosseae were also reported. Similar results were observed by Gupta
et al. (2002) where inoculation of Mentha arvensis with the AM fungus Glomus
fasciculatum increased plant height, shoot growth, and essential oil content.
According to Cappellari et al. (2013), PGPR Pseudomonas fluorescens and
Azospirillum brasilense increased the biosynthesis of the major EO components
up to 70 % and total phenolic content in Mexican marigold (Tagetes minuta).
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Medicinal Plants and PGPR: A New Frontier for Phytochemicals
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Table 14.1 The effect of plant beneficial microorganisms on phytochemical constituents of
medicinal plants
PGPR
Plant
Phytochemicals
References
Glomus mosseae,
Trichoderma harzianum
Andrographis
paniculata Nees.
(kalmegh)
Anethum
graveolens
L. (dill)
Anethum
graveolens
L. (dill)
Artemisia annua
L. (wormwood)
Coleus forskohlii
(Indian coleus)
Andrographolide
Arpana and
Bagyaraj
(2007)
Kapoor
et al. (2002)
Glomus macrocarpum,
Glomus fasciculatum
Pseudomonas putida
Glomus macrocarpum,
Glomus fasciculatum
Glomus fasciculatum
Glomus fasciculatum, Pseudomonas monteilii
Azospirillum brasilense,
Pseudomonas fluorescens
Glomus lamellosum
Glomus aggregatum,
Trichoderma harzianum,
Bacillus coagulans
Glomus lamellosum
Glomus intraradices, Glomus
etunicatum
Glomus fasciculatum
Glomus fasciculatum, Azotobacter chroococcum
Pseudomonas putida, Azotobacter chroococcum
Bacillus subtilis
Glomus mosseae
Pseudomonas fluorescens
Bradyrhizobium sp.
Coleus forskohlii
(Indian coleus)
Catharanthus
roseus
L. (Madagascar
periwinkle)
Geranium
dissectum
L. (germanium)
Glycyrrhiza
glabra
L. (liquorice)
Lavandula
angustifolia
L. (lavender)
Lonicera confuse
(honeysuckle)
Mentha arvensis
(wild mint)
Ocimum spp.
(basil)
Ocimum basilicum
(common basil)
Ocimum basilicum
(common basil)
Ocimum basilicum
(common basil)
Origanum
majorana
L. (marjoram)
Limonene,
α-phellandrene
Carvone, limonene
Tajpoor
et al. (2013)
Artemisinin
Kapoor
et al. (2007)
Sailo and
Bagyaraj
(2005)
Singh
et al. (2012)
Karthikeyan
et al. (2009)
Forskolin
Forskolin
Terpenoid indole alkaloid (ajmalicine)
Essential oil
Karagiannidis
et al. (2012)
Phenols, orthodihydroxy phenols, tannins, flavonoids,
alkaloids
Essential oil
Selvaraj and
Sumithra
(2011)
Chlorogenic acid
Essential oil
Essential oil
Essential oil
Terpineol, eugenol
Essential oil
Terpinen-4-ol, cissabinene hydrate, transsabinene hydrate,
α-terpineol
Karagiannidis
et al. (2012)
Shi
et al. (2013)
Gupta
et al. (2002)
Vinutha
(2005)
Ordookhani
et al. (2011)
Banchio
et al. (2009)
Copetta
et al. (2006)
Banchio
et al. (2008)
(continued)
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D. Egamberdieva and J.A. Teixeira da Silva
Table 14.1 (continued)
PGPR
Glomus mosseae
Glomus mosseae
Bacillus cereus
Glomus intraradices
Glomus lamellosum
Glomus walkeri, Bacillus
subtilis, Trichoderma viride
Burkholderia gladioli,
Enterobacter aerogenes,
Serratia marcescens
Bacillus megaterium,
Azospirillum sp. AM fungi
Pseudomonas fluorescens,
Azospirillum brasilense
Glomus mosseae, Bacillus
subtilis
Azospirillum, Azotobacter
chroococcum, Pseudomonas
fluorescens, Bacillus
megaterium
Plant
Origanum
sp. (oregano)
Pelargonium
sp. (germanium)
Salvia miltiorrhiza
Bunge (red sage)
Salvia officinalis
(common sage)
Santolina
chamaecyparissus
(cotton lavender)
Sphaeranthus
amaranthoides
(L.) Burm
(sivakaranthai)
Stevia rebaudiana
Bert. (sweet leaf)
Stevia rebaudiana
Bert. (sweet leaf)
Tagetes minuta
(Mexican
marigold)
Thymus daenensis
(thyme)
Withania
somnifera (Indian
ginseng)
Phytochemicals
Essential oil
Essential oil
Diterpenoid pigment,
tanshinones
Essential oil, bornyl
acetate, 1,8-cineole, αand β-thujones
Essential oil
Phenols, orthodihydroxy phenols, flavonoids, alkaloids,
tannins
Stevioside,
rebaudioside-A
contents
Stevioside
Essential oil, phenolic
content
Essential oil
Withaferin A
References
Khaosaad
et al. (2006)
Venkateshwar
Rao
et al. (2002)
Wu
et al. (2007)
Geneva
et al. (2010)
Karagiannidis
et al. (2012)
Sumithra and
Selvaraj
(2011)
Gupta
et al. (2011)
Das and Dang
(2010)
Cappellari
et al. (2013)
Bahadori
et al. (2013)
Rajasekar and
Elango (2011)
In other study the highest carvone content (63.22 %) and the lowest contents of
limonene (25.16 %) in essential oil of Anethum graveolens L. were obtained after
the treatment of Pseudomonas putida combined with vermicompost (Tajpoor
et al. 2013).
Bahadori et al. (2013) reported that co-inoculation of Thymus daenensis with
G. mosseae and Bacillus subtilis resulted in a 75 % increase in shoot/root dry weight
and a 117 % increase in plant yield and stimulated essential oil yield by 93 %
compared to uninoculated controls. Karagiannidis et al. (2012) observed the
increase of essential oil content in plants such as Santolina chamaecyparissus,
Salvia officinalis, Lavandula angustifolia, Geranium dissectum, and Origanum
dictamnus by 28.75, 55.56, 56.95, 53.63, and 55.24 % when inoculated with AM
fungus Glomus lamellosum. Similar results were observed by Geneva et al. (2010)
where essential oil content, bornyl acetate, 1,8-cineole, and α- and β-thujones of
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Medicinal Plants and PGPR: A New Frontier for Phytochemicals
293
Salvia officinalis were increased by Glomus intraradices (Geneva et al. 2010).
Inoculation of Anethum graveolens L. with AMF Glomus macrocarpum and Glomus fasciculatum significantly increased limonene and α-phellandrene content
(Kapoor et al. 2002).
Salvia miltiorrhiza Bunge is a well-known herbal plant in Chinese medicine used
for the treatment of menstrual disorders and cardiovascular disease and to prevent
inflammation (Wang et al. 2007). Wu et al. (2007) studied the diterpenoid pigment
derived from S. miltiorrhiza roots, which are generally known as tanshinones, and
its content in root of S. miltiorrhiza was stimulated by more than 12-fold when
the hairy root culture was inoculated with Bacillus cereus. Withania somnifera
(Ashwagandha) is a plant used in the treatment of cancer and nervous disorders,
and it contains withaferin A, a therapeutically active withanolide. The bacterial
composition of Azospirillum, Azotobacter chroococcum, Pseudomonas fluorescens,
and Bacillus megaterium significantly increased plant height, root length, and the
alkaloid and withaferin-A content (Rajasekar and Elango 2011).
Coleus forskohlii Briq. (Lamiaceae) is widely used to relieve coughs, eczemas,
skin infections, tumors, glaucoma, cardiac problems, and certain types of cancers
(Kavitha et al. 2010) and contains a labdane diterpene compound forskolin
(Seamon 1984). Forskolin content was significantly improved by as much as
25 % by inoculation with the AM fungus Glomus fasciculatum (Sailo and Bagyaraj
2005) and combined inoculation of G. fasciculatum and Pseudomonas monteilii
(Singh et al. 2012). Stevia rebaudiana is a medicinal plant that serves as a source of
natural sweeteners, steviol glycosides, which has been reported for hypotensive and
heart tonic actions (Ferri et al. 2006). Gupta et al. (2011) observed that
S. rebaudiana inoculated with a consortium of phosphorus-solubilizing bacteria
(PSB) Burkholderia gladioli MTCC 10216, B. gladioli MTCC 10217, Enterobacter
aerogenes MTCC 10208, and Serratia marcescens MTCC 10238 showed increased
root and shoot biomass and stevioside and rebaudioside-A contents (291 and 575 %,
respectively) on a whole-plant basis compared to control plants. The increased
stevioside content of S. rebaudiana by the combined inoculation of Bacillus
megaterium, Azospirillum sp., and AM fungi was also reported by Das and
Dang (2010).
Artemisia annua L. (Asteraceae) or annual wormwood is an herbal plant in
Chinese traditional medicine and has been used for the treatment of cerebral fever
and malaria (Ram et al. 1997) and is a source of complex terpenoids, including
artemisinin. Kapoor et al. (2007) observed increased plant growth and artemisinin
production in A. annua by two AM fungi, Glomus macrocarpum and Glomus
fasciculatum, which successfully colonized the roots.
Leaf-derived secondary metabolites such as total phenols, ortho-dihydroxy
phenols, flavonoids, alkaloids, and tannins of Sphaeranthus amaranthoides (L.)
Burm increased when plants were treated with Glomus walkeri, Bacillus subtilis,
and Trichoderma viride (Sumithra and Selvaraj 2011). Karthikeyan et al. (2009)
reported an increase in the production of terpenoid indole alkaloids (ajmalicine) in
Catharanthus roseus inoculated with Azospirillum brasilense and Pseudomonas
fluorescens. Arpana and Bagyaraj (2007) reported that Glomus mosseae and
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D. Egamberdieva and J.A. Teixeira da Silva
Trichoderma harzianum increased plant root, shoot growth, dry weight, phosphorus
uptake, and andrographolide (alkaloid) concentration in kalmegh (Andrographis
paniculata) compared to uninoculated plants.
Glycyrrhizin is a very sweet ingredient of liquorice (Glycyrrhiza glabra) and has
an anti-inflammatory effect which controls coughing (Patil et al. 2009). Selvaraj
and Sumithra (2011) observed that the AM fungi Glomus aggregatum,
Trichoderma harzianum, and Bacillus coagulans enhanced plant biomass and
polyphenolic compound production, namely, total phenols, ortho-dihydroxy phenols, tannins, flavonoids, and alkaloids in liquorice. Shi et al. (2013) demonstrated
increased growth and chlorogenic acid content in flowers of Lonicera confusa, a
traditional Chinese medicine herb for treating cold, flu, and acute fever, by inoculation with Glomus intraradices rather than with Glomus etunicatum.
Those studies demonstrate the effectiveness of PGPR and AM fungi in improving the concentration of phytochemical constituents and essential oil concentrations
in medicinally important plants.
14.5
The Role of Microbial Interactions in Nutrient Uptake
of Medicinal Plants
The activity of soil organisms is very important for ensuring sufficient nutrient
supply to a plant and plays a significant role in regulating the dynamics of organic
matter decomposition and the availability of plant nutrients such as N, P, K, Mg,
and other microelements (Egamberdieva 2011; Maheshwari et al. 2012). In earlier
studies, several authors reported an increase in nutrient content such as P, K, Zn,
Cu, and Fe due to mycorrhizal and PGPR (Glomus mosseae, Bacillus coagulans,
and Trichoderma harzianum) inoculation for several medicinal plants including
Saraca asoca (Roxb.) (Lakshmipathy et al. 2001), Calamus thwaitesii
(Lakshmipathy et al. 2002), and Begonia malabarica Lam. (Selvaraj et al. 2008).
The inoculation of annual wormwood (Artemisia annua L.) with AM fungi Glomus
macrocarpum and Glomus fasciculatum, combined with P fertilizer, resulted in
higher concentrations of Zn and Fe in shoots (Kapoor et al. 2007). Similar results
were observed by Selvaraj and Sumithra (2011), in which the root phosphorus,
potassium, zinc, copper, and iron contents increased after inoculation with a
consortium of Glomus aggregatum, Bacillus coagulans, and Trichoderma
harzianum in Glycyrrhiza glabra.
Prasad et al. (2012b) observed increased plant growth, alkaline phosphatase and
acidic phosphatase activity, and phosphorus uptake in shoots and roots of Chrysanthemum indicum L. inoculated with Glomus mosseae, Acaulospora laevis, and
phosphate-solubilizing Pseudomonas fluorescens. Similar results were observed by
Singh et al. (2012) where N, P, and K uptake of Coleus forskohlii plant significantly
(26, 60, and 43 %, respectively) increased following inoculation with Pseudomonas
monteilii and Glomus fasciculatum under field experiments. PSB treatments with
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Medicinal Plants and PGPR: A New Frontier for Phytochemicals
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Burkholderia gladioli, Enterobacter aerogenes, and Serratia marcescens combined
with Mussoorie rock phosphate (MRP) showed an increase of 86–576 % in available P content of soil and 63.9–273 % P content in Stevia rebaudiana shoots than in
control treatments (Gupta et al. 2011). A significant increase in N content of roots
and shoots of Galega orientalis was also observed after co-inoculation of Pseudomonas trivialis with Rhizobium galegae which significantly increased the N content
of the roots by 20 % and of the shoots by 52 % compared to R. galegae alone
(Egamberdieva et al. 2010).
Marigold (Calendula officinalis) is known for its antioxidant, anti-inflammatory,
and anticancer activities (Muley et al. 2009). The shoot and root growth, nitrogen,
phosphorus, potassium, and photosynthetic pigment contents of C. officinalis were
stimulated by PGPR strains Azotobacter, Azospirillum, Pseudomonas, and AM
fungi (Hosseinzadah et al. 2011). Ordookhani et al. (2011) showed increased Fe,
Mn, and Cu contents of Ocimum basilicum L. (sweet basil) by Pseudomonas putida,
Azotobacter chroococcum, and Azospirillum lipoferum. According to Shi
et al. (2013), concentrations of N, P, and K in leaves of Lonicera confusa increased
significantly by AM fungi G. intraradices and G. etunicatum inoculation.
Sphaeranthes amaranthoides (L.) Burm is a common medicinal plant in India,
and the plant juice is used in epilepsy, hepatopathy, gastropathy, diabetes, leprosy,
fever, cough, hemorrhoids, and dyspepsia (Sumithra and Selvaraj 2011). The
growth and nutrient uptake of phosphorus, potassium, zinc, copper, and iron content
were increased in plants treated with Glomus walkeri, Bacillus subtilis, and
Trichoderma viride (Sumithra and Selvaraj 2011).
Most P and K fertilizers are not readily available to a plant, and their use often
causes an insignificant yield increase in plants (Chabot et al. 1996). Some
rhizobacteria may convert insoluble rock P into soluble forms available for plant
growth (Varsha and Patel 2000). Release of P by PSB from insoluble and fixed/
adsorbed forms is an import aspect of P availability in soils (Khan et al. 2009). PSB,
mainly Enterobacter, Bacillus, Pseudomonas, and Arthrobacter, are very effective
for increasing the plant-available P in soil as well as plant growth (Egamberdieva
and Hoflich 2004). Moreover, the higher N content in treatments may have resulted
from the N2-fixation ability of this bacterium, as reported in other studies
(Çakmakcı et al. 2007).
14.6
Microbial Mediated Alleviation of Abiotic Stress
in Medicinal Plants
Abiotic factors such as drought and salinity negatively affect plant growth of
aromatic and medicinal plants and the production of biologic active compounds
(Parida and Das 2005). Razmjoo et al. (2008) reported that increased salinity and
drought stress caused a reduction in the fresh and dry flower weight and essential oil
content of Matricaria chamomilla. Water stress caused a significant increase in the
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concentrations of proline and soluble carbohydrate in the leaves of Ocimum
basilicum L. (sweet basil) and decreased mineral uptake (Heidari et al. 2011).
The content of chlorophyll, proline, and K uptake was significantly stimulated
after inoculating basil with Pseudomonas sp., Bacillus lentus, and Azospirillum
brasilense (Heidari et al. 2011). Similar results were observed for black henbane
(Hyoscyamus niger), which is considered an important medicinal plant and a source
of tropane alkaloids such as hyoscyamine (HYO) and scopolamine (SCO) (Pitta
et al. 2000), in which water stress reduced plant growth and development. Pseudomonas putida and Pseudomonas fluorescens alleviated water stress and increased
plant growth and tropane alkaloids such as hyoscyamine and scopolamine concentration in H. niger (Ghorbanpour et al. 2013).
Salinity decreased plant growth, development, and essential content of Pelargonium sp. Prasad et al. (2012a) studied the ameliorative effect of AM fungus, PSB,
combined with P fertilizers on plant growth, nutrient uptake, and chemical composition of essential oil in Pelargonium sp. They observed that shoot growth, mineral
element (P, K, Ca, Mg, Na, Fe, Cu, and Zn) uptake in shoot tissues, and essential oil
content such as citronellol, geraniol, geranial, and a sesquiterpene
(10-epi-γ-eudesmol) in shoot tissues of geranium were significantly increased by
the co-inoculation with Glomus intraradices and PSB compared to the control.
Similar results were observed by Golpayegani and Tilebeni (2011) in which PGPR
strains Pseudomonas sp. and Bacillus lentus alleviated the effect of potentially toxic
ions on the growth, antioxidant enzymes ascorbate peroxidase (APX) and glutathione reductase (GR), and mineral content (K, P, Ca, Na) in basil plants. Galega
officinalis L. (goat’s rue, French lilac) has been used for medicinal purposes
(Atanasov and Spasov 2000; Pundarikakshudu et al. 2001). Plant growth and
nitrogen content of co-inoculated plant roots with P. extremorientalis TSAU20
and R. galegae HAMBI 1141 increased significantly by on average 50 % under
saline conditions (Egamberdieva et al. 2013b).
Bacopa monnieri (Indian pennywort), which is commonly used as a nootropic
digestive aid, memory enhancer, and for improving respiratory functions (Russo
and Borrelli 2005), has many active compounds including alkaloids, flavonoids,
and saponins (bacoside A, bacoside B), but its synthesis is severely affected by
abiotic factors such as drought and salinity (Tiwari et al. 2001). Bharti et al. (2013)
studied the interaction of B. monnieri and PGPR under saline soil conditions.
Salinity inhibited root and shoot growth of B. monnieri and bacoside-A content.
Inoculation of plants with PGPR strains E. oxidotolerans and Bacillus pumilus
alleviated salt stress, stimulated herb yield, and also recorded higher bacoside-A
content under saline conditions. E. oxidotolerans-inoculated plants had 36 and
76 % higher bacoside-A content under primary and secondary salinity, respectively.
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Medicinal Plants and PGPR: A New Frontier for Phytochemicals
14.7
297
Biomechanisms Regulating Growth and Development
Mechanisms by which bacteria are able to stimulate plant growth, phytochemical
constituents, and nutrient uptake and alleviate abiotic stresses include various
enzymes (Lugtenberg and Kamilova 2009), mobilization of nutrients
(Egamberdieva and Lugtenberg 2014), induction of systemic resistance (Van
Loon 2007; Hameed et al. 2014), competition for nutrients and niches (Raaijmakers
et al. 2009), production of phytohormones like indole-3-acetic acid (IAA),
gibberellic acid, cytokinins (Mishra et al. 2010), production of ACC deaminase to
reduce the level of ethylene in the roots of developing plants (Dey et al. 2004), and
asymbiotic nitrogen fixation (Ardakani et al. 2010). For example, AM fungi
increase plant growth and essential oil production by extending the root zone and
acquisition of organic phosphates by production of extracellular acid phosphatases
(Bouwmeester et al. 2007; Hameed et al. 2014). The increased level of artemisinin
by AM fungi may be due to improved growth and nutrient status of the plants
(Kapoor et al. 2007). PSB also play an important role in P nutrition of plants (Ekin
2010). Phosphorus is an important source for essential oil synthesis by plants,
whereas isoprenoid biosynthesis requires acetyl coenzyme A, adenosine triphosphate (ATP), and nicotinamide adenine dinucleotide phosphate (NADPH) and is
dependent on the concentration of inorganic P in the plant (Lichtenthaler 2009).
Thus, increased P uptake mediated by PSB may stimulate essential oil synthesis in
medicinal plants. However, there is another explanation for the increased oil
concentration in plants: Sangwan et al. (2001) indicated that essential oil concentration and composition in medicinal plants serve important ecological roles in
which the majority of oils have antimicrobial properties. Application of a microbial
consortium to the root system of medicinal plants increased the synthesis of oils and
can be considered as a defensive response of plants to colonization by
microorganisms.
The colonization of a host plant’s rhizosphere by plant beneficial microbes is an
important factor for plant growth (Lugtenberg et al. 2001) because they deliver
various plant growth-promoting metabolites (Berg et al. 2010; Egamberdieva
2009). Plant growth regulators such as auxins, gibberellins, and cytokinins produced by rhizobacteria can influence plant growth, including root development, all
of which improve the uptake of essential nutrients and thus increase plant growth
(Somers et al. 2004). Root-associated bacteria utilize root exudates that also contain
tryptophan, a precursor of IAA, through which plants and bacteria may regulate
IAA biosynthesis in the rhizosphere (Dakora and Phillips 2002). Plant cells take up
some of the IAA that is secreted by the bacteria and, together with the endogenous
plant IAA, can stimulate plant cell proliferation (Glick et al. 2007). This increase
nutrient-absorbing surface may lead to greater rates of nutrient absorption through
which plant growth will increase significantly (Egamberdieva 2012). Some rootassociated rhizobacteria contain the enzyme ACC deaminase, which may decrease
the level of ethylene in the root and enhance the stress tolerance of plants (Glick
et al. 2007).
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14.8
D. Egamberdieva and J.A. Teixeira da Silva
Conclusions and Future Prospects
This chapter highlights the role of plant-associated microbes in plant growth
promotion and nutrient uptake under various climatic conditions. Most of the
PGPR isolates and AM fungi showed a significant increase in root and shoot weight
and nutrient uptake and improved the concentration of phytochemical constituents
and essential soil concentrations in medicinally important plants. Knowledge of
such interactions can provide direction as to which microbes might be selected for
an increase in novel medicinal compounds that possess antimicrobial, antimalarial,
antioxidant, and other biological activities. This microbial strategy offers an attractive way to replace the use of chemical fertilizers, pesticides, and other supplements
for cultivation of herbal plants. Information from various studies available
describes the mechanisms involved in the improvement of plant growth and stress
tolerance in plants. However, our understanding of the ability of plant beneficial
microbes to increase plant secondary metabolites remains scarce. Thus, more
studies are needed to investigate the possible mechanisms by which bacteria
increase phytochemical constituents in medicinal important plants at the tissue,
cell, or molecular level.
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mkumar9@amity.edu
Chapter 15
Plant Growth Promoting Rhizobacteria
for Value Addition: Mechanism of Action
H. Deka, S. Deka, and C.K. Baruah
15.1
Introduction
Application of microbes for improvement of plants has been carried out since
ancient times even before the discovery of microscopic animals and microscope
as well (Bhattacharyya and Jha 2012). The use of microorganisms with the aim of
improving nutrients availability for plants is an important practice and necessary for
agriculture (Freitas et al. 2007). During the past couple of decades, the use of plant
growth promoting rhizobacteria (PGPR) for sustainable agriculture has increased
tremendously in various parts of the world.
The soil zone in the vicinity of plant roots in which the chemistry and microbiology is influenced by their growth, respiration, and nutrient exchange is known
as rhizosphere. In the rhizosphere, bacteria are the most abundant microbes besides
other microbes like fungi, protozoa, algae, etc. Kloepper and Schroth (1978)
introduced the term “rhizobacteria” to the soil bacterial community that competitively colonized plant roots and stimulated plant growth and reduces the incidence
of plant diseases. In the rhizosphere, very important and intensive interactions take
place between the soil, plant, microorganisms, and soil microfauna. In fact, biochemical interactions and exchanges of signal molecules between plants and soil
microorganisms have been described and reviewed by various workers (Pinton
et al. 2001; Werner 2001, 2004). These interactions can significantly influence
plant growth and crop yields. The medicinal plants constitute a large segment of the
H. Deka • C.K. Baruah
Life Sciences Division, Institute of Advanced Study in Science & Technology, Guwahati,
Assam 781035, India
e-mail: dekahemen8@gmail.com
S. Deka (*)
Environmental Biotechnology Lab, Life Sciences Division, IASST, Garchuk, Vigyan Path,
Guwahati, Assam 781035, India
e-mail: sureshdeka@yahoo.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_15
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flora, as the source of raw materials for pharmaceutical, cosmetic, and fragrance
industries. A clear understanding and management of microbe species associated
with the medicinal plants is utmost important to improve their yield and quality
medicinal products (Karthikeyan et al. 2008).
15.1.1 What Are Plant Growth Promoting Rhizobacteria?
The species of bacteria that are associated with the plant rhizosphere that have
beneficial effect on plant’s growth and crop yield are collectively called as PGPR.
Kloepper and Schroth (1978) defined PGPR for the first time and since then several
definitions have been proposed by various workers. The PGPR are soil bacteria that
colonize the roots of plants and on inoculation with seed enhance the growth of
plant. It has been reported that about 2–5 % of rhizobacteria after reintroducing
through plant inoculation in a soil containing competitive microflora shows a
beneficial effect on plant growth (Kloepper et al. 1989). The PGPR are also termed
as plant health promoting rhizobacteria (PHPR) or nodule promoting rhizobacteria
(NPR) and are associated with the rhizosphere which is an important soil ecological
environment for plant–microbe interactions (Hayat et al. 2010; Burr and Caesar
1984). The PGPR includes both free-living and plant tissue invading bacteria that
cause unapparent and asymptomatic infections in plant root systems (Sturz and
Nowak 2000). The latter groups are also known as endophytes as they inhabit
within the plant tissue system. According to the original definition, rhizobacteria
are free-living bacteria that colonize the root zone. They differ from the nitrogenfixing Rhizobia and Frankia that forms symbiotic associations with plants and
cannot be considered as PGPR (Antoun and Prevost 2005). However, some other
workers divided PGPR into two groups according to their relationship and residing
sites in the plants, i.e., iPGPR (i.e., symbiotic bacteria), which live inside the plant
cells, produce nodules, and are localized inside the specialized structures, and
ePGPR (i.e., free-living rhizobacteria), which live outside the plant cells and do
not produce nodules, but still prompt plant growth (Gray and Smith 2005). The
best-known iPGPR are the species of Rhizobia, which produce nodules in leguminous plants. A number of bacterial species have been used as soil inoculants
intended to improve the supply of nutrients to crop plants. The bacteria such as
Rhizobium, Mesorhizobium, Bradyrhizobium, Azorhizobium, Allorhizobium, and
Sinorhizobium have been successfully used worldwide to permit an effective
establishment of the nitrogen-fixing symbiosis with leguminous crop plants
(Bottomley and Maggard 1990; Bottomley and Dughri 1989). On the other hand,
non-symbiotic nitrogen-fixing bacteria such as species of Azotobacter,
Azospirillum, Bacillus, and Klebsiella are also used to inoculate a large area of
arable land in the world with the aim of enhancing plant productivity (Lynch 1983).
Besides these, phosphate solubilizing bacteria such as species of Bacillus and
Paenibacillus (formerly Bacillus) have been applied specifically to enhance the
phosphorus status of soil for plants (Brown 1974). Even more recently, the
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application of PGPR has also been extended to remediate contaminated soils in
association with plants (Zhuang et al. 2007).
15.1.2 Why Is PGPR for Value Addition?
Sustainable soil health and crop production are key global issues today. Both plant
health and soil fertility are to be incorporated for better production and mitigating
the growing demand of food products. It is the interaction between beneficial
microbes and plants in the rhizosphere zone that primarily determines the plant
health and soil fertility (Klyuchnikov and Kozherin 1990). Hence, at present,
greater emphasis has been laid on application of beneficial microbes or PGPR
instead of inorganic input in the crop field. Continuous uses of synthetic fertilizers
have been reported to be deleterious for both chemical and biological components
of the soil. The long-term use of inorganic fertilizer without organic supplements
damages the physical, chemical, and biological properties of soil and causes
environmental pollution (Albiach et al. 2000). Therefore, in order to develop a
strategy for the sustainable soil health, it is necessary to apply the organic products.
Organic fertilizers such as PGPR are microbial inoculants consisting of living cells
of bacteria which help in increasing crop productivity. Organic fertilizers as against
the chemical fertilizers have lower nutrient content but they are more effective for
longer periods of use and maintain soil fertility intake due to their slow release of
nutrients. The use of biofertilizer containing strains of plant growth promoting
rhizobacteria instead of synthetic chemicals serves as an effective alternative and
environmental friendly practice to improve plant growth through the supply of plant
nutrients and soil productivity. Moreover, exploiting PGPR strains for the growth
promotion could reduce the need of chemical fertilizers and cost of cultivation
(Rajasekar and Elango 2011). However, survivability of PGPR in field condition,
application dose, adaptability, etc. are the limiting factors which are yet to be
addressed properly.
15.2
Role of PGPR in Improvement of Medicinal Plants
and Its Products
The present world relies on natural products that have no adverse effect on whole
biota. Therefore, exploitation of medicinal plants and extraction of its products in
health sector is increasing day by day. Demand for medicinal plants has increased in
both developing and developed nations due to growing recognition of natural
products, which are non-toxic, having no side effects and can be obtained in
affordable prices (Sekar and Kandavel 2010). The World Health Organization
(WHO) estimated that 80 % of the population of developing countries relies on
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traditional medicines, mostly plant base, for their primary health care (Farnsworth
1990). Moreover, it has been reported that modern pharmacopoeia contains at least
25 % drugs that are derived directly from plants (Sekar and Kandavel 2010).
Herbal products are the first choice in self-treatment to prevent immediate
development of certain diseases in developing countries like India, China,
South Africa, etc. It has been reported that traditional healers often prescribe
mixtures of medicinal plants in raw form for the treatment of several diseases
like common cold, malaria, arthritis, ulcers, hepatitis, and diabetes (Obiajunwa
et al. 2002; Sarma and Sarma 2008; Sarma et al. 2008). Even, in the country like
Ethiopia, more than 85 % of the population depends on herbal plants for primary
health care (Meena et al. 2010). Medicinal plants are particularly important in
developing countries because such plants are also dietary components and are
essential for health (Maiga et al. 2005; Cantarelli et al. 2010). Moreover, since
1992, the average use of medicinal and aromatic plants in European countries has
increased by 21 % in traditional as well as processed forms (Bernath 2002).
Considering the Indian scenario, it is estimated that about 2,000 drugs of plant
origin are used which even leads to extinction/endangerment of 20–25 % plant
species from their natural habitat (Sarma 2011; Laloo et al. 2006). Even, the
occurrence and distribution of medicinal plants is now under great pressure in
India because excessive amounts of them are collected from wild habitats and are
exploited for use in medicine (Sarma 2011). Nevertheless, threats to the medicinal
plants are not only because of over exploitation but rather because of the indiscriminate use of pesticides, insecticides, fertilizers, etc. which ultimately lead to degradation of the quality of the environment.
Various research reports are available regarding use of PGPRs for quality
improvement of medicinal plant products. A brief reference of the use of PGPR
for improvement of medicinal plants products has been listed in Table 15.1.
15.3
Mechanism of Action of PGPR
15.3.1 An Overview
Rhizosphere manipulation involves a very complex mechanism. In order to achieve
maximum benefit from plant–microbe interaction, it is necessary to understand the
PGPR action mechanisms for manipulating the rhizosphere. Traditionally, PGPR
action mechanisms can be divided into two groups, viz., direct and indirect mechanisms. In case of indirect mechanisms, action occurs outside the plant, whereas
direct mechanisms are those that occur inside the plant and directly affect the
plant’s metabolism. Nevertheless, the differences between these two types of
mechanisms are not always obvious. A schematic illustration of some important
mechanism of PGPRs has been presented in Fig. 15.1.
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Table 15.1 Use of PGPR for production of compounds from medicinal plants
Name of the PGPR strains
Plants compound/plants name
References
Pseudomonas fluorescens
Ajmalicine; Catharanthus roseus L.
Pseudomonas monteilii
Forskolin; Coleus forskohlii
Azotobacter
Azospirillum
Pseudomonas
Azotobacter chroococcum
Azospirillum lipoferum
Pseudomonas flouresence
Pseudomonas fluorescens
Bacillus subtilis, Sinorhizobium
meliloti, Bradyrhizobium sp.
Pseudomonas fluorescens elicitors
(PF elicitors)
Essential oil content
Anethol, methyl chavicol
Pimpinella anisum L.
Essential oil content, chamazulene
Matricaria chamomilla L
Jaleel
et al. (2007)
Singh
et al. (2013)
Sefidkon
(2012)
Salehi
et al. (2012)
Essential oil
Origanum majorana L.
Banchio
et al. (2008)
Ajmalicine, catharanthine, tabersonine,
serpentine, Vindoline, Catharanthus
roseus (L.) G. Don
Overall plant growth and alkaloids
Catharanthus roseus (L.) G. Don
Bacoside-A
Bacopa monnieri (L.)
Jaleel
et al. (2009)
Azotobacter, Bacillus,
Pseudomonas
Bacillus pumilus (STR2)
Exiguobacterium oxidotolerans
(STR 36)
Bacillus cereus
Azospirillum lipoferum
Azotobacter chrocooccum
Species of Pseudomonas
Klebsiella, Xanthomonas, Bacillus, Erwinia, Agrobacterium, and
Arthrobacter
Azotobacter
Pseudomonas fluorescens,
Azospirillum brasilense
Bacillus coagulans
Begonia malabarica Lam.
Tanshinone
Salvia miltiorrhiza
Yield and essential oil
Matricaria chamomilla L.)
Valeriana officinalis
Production of IAA, HCN, Lipase, and
protease
Thymus vulgaris L. Thyme
Essential oil and phenolic content
Karthikeyan
et al. (2010)
Bharti
et al. (2013)
Zhao
et al. (2010)
Dastborhan
et al. (2010)
Ghodsalavi
et al. (2013)
Naseri and
Sharafzadeh
(2013)
Cappellari
et al. (2013)
Tagetes minuta
Luteolin, quercetin, and β-sitosterol
Good numbers of literatures are available to describe the plant growth promotion
by PGPR through direct or indirect modes of action (Kloepper 1993; Van Loon and
Glick 2004; Van Loon 2007). In broader sense, direct mechanisms include the
production of stimulatory bacterial volatiles and phytohormones, lowering of the
ethylene level in plant, improvement of the plant nutrient status (liberation of
phosphates and micronutrients from insoluble sources; non-symbiotic nitrogen
fixation), and stimulation of disease-resistance mechanisms (induced systemic
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Fig. 15.1 Schematic illustration of important mechanisms known for plant growth promotion by
PGPR. Different mechanisms can be broadly studied under (1) Biofertilization and (2) Biocontrol
of pathogens. Biofertilization encompasses: (a) N2 Fixation, (b) Siderophore production, (c)
Phosphate solubilization by rhizobacteria. Biocontrol involves: (a) Antibiosis, (b) Secretion of
enzymes, and (c) Induction of Systemic Resistance (ISR) of host plant by PGPR (Adopted from
Kumar et al. 2011)
resistance). Indirect mechanism of PGPR originates when it acts like biocontrol
agents reducing diseases, when they stimulate other beneficial symbioses, or when
they protect the plant by degrading xenobiotics in inhibitory contaminated soils
(Jacobsen 1997; Jacobsen et al. 2004). PGPR strains such as Pseudomonas fluoresces and Bacillus subtilis are well studied (Damayanti et al. 2007). Depending on
the activities of the PGPR, some workers like Somers et al. (2004) classified them
as biofertilizer (increasing the availability of nutrients to plant), phytostimulators
(plant growth promoting, usually by the production of phytohormones), rhizoremediators (degrading organic pollutants), and biopesticides (controlling diseases,
mainly by the production of antibiotics and antifungal metabolites). However,
Dey et al. (2004) reported that the exact mechanisms of PGPR-mediated enhancement of plant growth and yield for many crops are not known. According to them
the possible mechanism includes:
1. The ability to produce a vital enzyme, 1-aminocyclopropane-1-carboxylate
(ACC) deaminase, to reduce the level of ethylene in the root of developing
plants thereby increasing the root length and growth (Li et al. 2000, 2005)
2. The ability to produce hormones like auxin, i.e., indole acetic acid (IAA) (Patten
and Glick 2002), abscisic acid (ABA) (Dangar and Basu 1987; Dobbelaere
et al. 2003), gibberellic acid (GA), and cytokinins (Dey et al. 2004)
3. A symbiotic nitrogen fixation (Kennedy et al. 1997, 2004)
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4. Antagonism against phytophatogenic bacteria by producing siderophores,
β-1,3-glucanase, chitinases, antibiotic, fluorescent pigment, and cyanide
(Cattelan et al. 1999; Glick and Pasternak 2003)
5. Solubilization and mineralization of nutrients, particularly mineral phosphates
(De Freitas et al. 1997; Richardson 2001; Banerjee and Yasmin 2002);
6. Enhanced resistance to drought (Alvarez et al. 1996), salinity, waterlogging
(Saleem et al. 2007), and oxidative stress (Stajner et al. 1995, 1997)
7. Production of water-soluble B group vitamins niacin, pantothenic acid, thiamine, riboflavine, and biotin (Martinez-Toledo et al. 1996; Sierra et al. 1999;
Revillas et al. 2000).
15.3.2 Direct Mechanism
The direct mechanism of PGPR involves production of stimulatory bacterial volatiles and phytohormones, lowering of the ethylene level in plant, improvement of
the plant nutrient status (liberation of phosphates and micronutrients from insoluble
sources; non-symbiotic nitrogen fixation), and stimulation of the disease-resistance
mechanisms (induced systemic resistance). A list of direct mechanism has been
presented in Table 15.2. Among these more emphasis has been given in production
of phytohormones and their regulation (ethylene), volatile organic compounds
(VOCs), and their stimulatory effects. Hence, a brief mechanism of PGPR
pertaining to this has been addressed below.
Table 15.2 Direct PGPR action mechanisms (Adopted from Solano et al. 2008; Chanway 1997)
Mechanism
Effect
References
Plant growth regulator production
Biomass (aerial part
and root)
Gutierrez Manero
et al. (1996)
Gutierrez Manero
et al. (2001)
Glick et al. (1994)
Van Loon
et al. (1998)
Sumner (1990)
Flowering
Ethylene synthesis inhibition
Induction of systemic resistance
Root length
Health
Root permeability increase
Biomass and nutrient
absorption
Biomass and nutrient
content
Biomass and phosphorus content
Organic matter mineralization (nitrogen,
sulfur, phosphorus)
Mycorrhizal fungus association
Insect pest control
Health
mkumar9@amity.edu
Liu et al. (1995)
Germida and Walley
(1996)
Toro et al. (1998)
Zehnder et al. (1997)
312
15.3.2.1
H. Deka et al.
PGPR in Production of Plant Growth Regulators/Hormones
and Their Regulation
PGPRs are reported to be associated with the production of plant growth regulators.
Plant growth regulators are the substances that regulate the growth, development,
and physiology of the plants. The principal plant growth regulators are auxin (IAA),
gibberellins (GBs), ethylene, cytokinins, and absisic acid (ABA). Out of these, the
production of auxin and ethylene is very common trait among PGPR (Solano
et al. 2008). Production of auxin and ethylene has been also enumerated by other
workers (Mishra et al. 2010; Saleem et al. 2007). Similarly, production of gibberellins has been documented in several PGPR belonging to Achromobacter
xylosoxidans, Acinetobacter calcoaceticus, Azospirillum spp., Azotobacter spp.,
Bacillus spp., Herbaspirillum seropedicae, Gluconobacter diazotrophicus, and
rhizobia (Gutierrez Manero et al. 2001; Bottini et al. 2004; Dodd et al. 2010).
Again, although production of absisic acid (ABA) by bacteria is infrequent, several
workers documented about the involvement of PGPR during its production (Dodd
et al. 2010; De Smet et al. 2006). It has been reported that inoculation of
Azospirillum brasilense Sp245 has increased the ABA content in Arabidopsis,
especially when grown under osmotic stress (Cohen et al. 2008). According to an
estimate about 80 % of bacteria isolated from the rhizosphere can produce plant
growth regulator IAA (Hayat et al. 2010). Moreover, production of cytokinins by
PGPRs is also well documented and correlated with plant growth. Castro
et al. (2008) reported about the role of PGPR in production of cytokinins. A recent
report has provided important information on the role played by cytokinin receptors
in plant growth promotion by Bacillus megaterium rhizobacteria. B. megaterium
UMCV1 strain isolated from the rhizosphere of bean (Phaseolus vulgaris L.) plants
and on inoculation of this bacterium was found to promote biomass production of
Arabidopsis thaliana and bean plants both in laboratory as well as field condition
(Ortiz-Castro et al. 2009; Lopez-Bucio et al. 2007). According to them, the effect
was related to altered root system architecture in inoculated plants, with an inhibition in primary root growth followed by an increase in lateral root formation and
root hair length. Further, the effects of bacterial inoculation on plant growth and
development were found to be independent of auxin and ethylene signaling as
revealed by normal responses of auxin resistant mutants aux1-7, axr4-1, and eir-1
and ethylene-response mutants etr-1 and ein-2, and the failure to activate the
expression of auxin-reporter markers (Lopez-Bucio et al. 2007). Similarly, Narula
et al. (2006) reported about the gibberellins productions which are limited to a few
species of Bacillus (Solano et al. 2008).
PGPR plays an important role in reduction of ethylene level which is necessary
for growth and development of plant as at higher concentration it induces defoliation and other cellular processes that show negative effect on plant’s health
(Bhattacharyya and Jha 2012). PGPR have the capacity to divert the ethylene
biosynthesis pathway particularly in the root system by using the amino cyclopropane carboxylic acid (ACC) deaminase activity. The work has been well illustrated
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Fig. 15.2 Ethylene regulation by PGPR, a proposed model (Adopted from Glick et al. 1998)
by Desbrosses et al. (2009) in case of Arabidopsis thaliana plant. Glick et al. (1998)
reported in detail about the mechanism of ethylene regulation in plant by PGPR
which is primarily based on the ability of some bacteria to degrade ACC, the direct
precursor of ethylene. The degradation of this compound generates ACC concentration gradient between the interior and the exterior of the plant, favoring its
exudation, which causes a reduction of the internal ethylene level. This, in combination with auxin that may be produced by the same microorganism, causes a
considerable effect on important physiological processes such as root system development (Fig. 15.2). The bacterial ACC deaminase competes with the plant’s ACC
oxidase. This enzyme has been isolated and identified in several PGPR, all having the
ability to use ACC as the sole nitrogen source. Even, this model has been widely
confirmed using various mutants (Solano et al. 2008).
15.3.2.2
Production of Volatile Organic Compounds
The volatile organic compounds (VOCs) produced by some PGPR also plays
important role in plant growth. Volatile organic compounds (VOCs) are defined
as compounds that have high enough vapor pressures under normal conditions to
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H. Deka et al.
Fig 15.3 Mechanisms involved in volatile organic compound modulation of plant growth.
Microorganisms produce VOCs, which can be sensed by plants to alter morphogenesis or activate
defense and stress-related responses (Adopted from Ortiz-Castro et al. 2009)
significantly vaporize and enter the atmosphere. In most of the mechanisms that
PGPR use to interact with plants, VOC emission has a crucial participation
(Fig. 15.3). The mechanism that has received most attention in the last decade is
the role of VOCs on antibiosis and the biocontrol of plant pathogens. The discovery
of rhizobacteria that produce volatile organic compounds (VOCs) constitutes an
important mechanism for the elicitation of plant growth by rhizobacteria
(Bhattacharyya and Jha 2012). There are numerous reports showing volatiles
produced by bacteria such as ammonia, HCN, phenazine-1-carboxylic acid, alcohols, etc.
The production of bioactive VOCs by PGPR is a strain specific phenomenon. For
example, PGPR strains namely Bacillus subtilis GB03, B. amyloliquefaciens
IN937a, and Enterobacter cloacae JM22 release a blend of volatile components,
particularly, 2,3-butanediol and acetoin that has been found to stimulate the growth
of Arabidopsis thaliana plant (Ryu et al. 2003). Forlani et al. (1999) also reported
acetoin-forming enzymes in certain crops like tobacco, carrot, maize, and rice, but
their possible functions in plants were not properly established. Now, it has been
established that the VOCs production by the rhizobacterial strains can act as
signaling molecule to mediate plant–microbe interactions. This is possible because
volatiles produced by PGPR colonizing roots are generated at sufficient concentrations to trigger the plant responses (Ryu et al. 2003). Farmer (2001) identified
low-molecular weight plant volatiles such as terpenes, jasmonates, and green leaf
components as potent signal molecules for living organisms in different trophic
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Plant Growth Promoting Rhizobacteria for Value Addition: Mechanism of Action
315
levels. Nevertheless, to understand the details of molecular and physiological
mechanisms and how volatile organic compounds signal plants and serve in plant
defense systems, detailed investigations are still needed.
15.3.3 Indirect Mechanism
The list of indirect action of PGPR includes various activities and is not conclusive
as the indirect mechanisms mentioned in this chapter do not cover all the activities
of PGPRs. Besides, it is also to be mentioned that several mechanisms are not fully
understood; hence, it is very difficult to have a comprehensive view regarding
indirect mechanism of action of rhizobacteria or PGPRs. As mentioned above,
indirect mechanisms are related to biocontrol, including antibiotic production,
chelation of available Fe in the rhizosphere, synthesis of extracellular enzymes
that hydrolyze the fungal cellular wall, and competition for niches within the
rhizosphere (Zahir et al. 2004). Some important indirect actions along with the
associated PGPRs are mentioned below (Table 15.3).
Table 15.3 Some indirect mechanism of PGPR
Mechanism
Associated PGPRs
References
Nitrogen fixation
Azoarcus sp.
Beijerinckia sp.
Klebsiella pneumoniae
Pantoea agglomerans Rhizobium sp.
Bacillus polymyxa
Azotobacter sp.
Rhizobia spp.
Azospirillum sp., etc.
Rhizobium meliloti
Pseudomonas sp.
Pseudomonas fluorescens
Species of Azospirillum
Azotobacter
Bacillus
Beijerinckia
Burkholderia
Enterobacter
Erwinia
Flavobacterium
Microbacterium
Pseudomonas
Rhizobium
Serratia
Pseudomonas solanacearum
Pseudomonas cepacia
Pseudomonas sp.
Riggs et al. (2001)
Bhattacharyya and Jha
(2012)
Hayat et al. (2010)
Solano et al. (2008)
Production of siderophores
Phosphate solubilization
Hydrolysis of molecules released by
pathogens
Synthesis of cyanhydric acid
mkumar9@amity.edu
Arora et al. (2001)
Solano et al. (2008)
Sturz and Nowak
(2000)
Sudhakar et al. (2000)
Mehnaz and Lazarovits
(2006)
Toyoda and Utsumi
(1991)
Voisard et al. (1989)
316
15.4
H. Deka et al.
Conclusions
PGPRs are the microbial inoculants. They can enhance plant growth as well as
quality of plants by various ways. They are ecofriendly, cost-effective, and
nonhazardous. Also they keep the soil health for sustainable use. It is revealed
from the literatures that PGPRs have an important role in improvement of medicinal properties of the plants. No doubt, application of inorganic fertilizers can help
the growth and development of the plants, but not the quality of the plants. Intensive
use of inorganic fertilizers may cause noticeable damage to our environment as well
as soil health. It also leads to deposit heavy metals in the soil. These heavy metals
can transmit into different parts of the plant and accumulated there. The medicinal
properties of the plants may vary or deteriorate as a result of accumulation of such
hazardous metals. So, application of PGPRs is important to maintain the quality of
the medicinal values of the plants. Not only that, it will particularly help to protect
our precious soil resource and environment as a whole. Moreover, molecular and
physiological mechanisms of growth and development of the plants or value
addition in it after application of PGPRs have not studied adequately. Comprehensive research in this field is needed to understand the detailed mechanisms of
action.
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Chapter 16
Rhizosphere Microflora in Advocacy
of Heavy Metal Tolerance in Plants
Shivangi Upadhyay, Monika Koul, and Rupam Kapoor
16.1
Introduction
The term “heavy metal” is used for metallic elements with a specific mass higher
than 5 g cm 3 and form sulfides (Adriano 1986). Heavy metals (HMs) are present in
background concentrations in the Earth’s crust, but over the years their concentrations have increased owing to anthropogenic activities, posing as a major abiotic
stress. Superfluous levels of HMs can result in decadence of soil quality, subsequent
crop yield attrition, and substandard agricultural products, thus pose as a preeminent health hazard. Some HMs have a tendency to get bioaccumulated, they enter
the food chains through uptake by producers and get magnified at consumer level
(Nagajyoti et al. 2010). Plants have evolved various ubiquitous and specific metalresistant and metal-tolerant mechanisms to maintain ionic homeostasis at the
advent of HM stress (Milner and Kochian 2008).
Rhizosphere microflora and their metabolic processes profoundly influence plant
growth and yield as they have an enormous potential to improve soil quality and
degrade and immobilize the toxic compounds (Gadd 1990). The composition of soil
microbial population is complex. Arbuscular mycorrhizal fungi (AMF) and plant
growth-promoting rhizobacteria (PGPR) have been confirmed to enhance (Joner
and Leyval 1997; Sheng and Xia 2006) or reduce (Heggo et al. 1990; Rajkumar
et al. 2006) the uptake of HMs by plants.
S. Upadhyay
Department of Botany, University of Delhi, Delhi 110007, India
M. Koul
Department of Botany, Hans Raj College, University of Delhi, Delhi 110007, India
R. Kapoor (*)
Department of Botany, University of Delhi, Delhi 110007, India
e-mail: kapoor_rupam@yahoo.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_16
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AMF offer plant a number of benefits in lieu of carbon products from the plant
and are important in capturing nutrients that have low availability and mobility in
soils (Parniske 2008). The basis of symbiosis is a bidirectional exchange of
nutrients, where the fungus provides phosphorous to plant and in return the plant
provides carbon products to it. The hyphal network prevents nutrient leakage,
thereby providing enhanced nutrition and greater water uptake. It has been connoted that AMF provide tolerance against biotic as well as abiotic stress to a variety
of plant species (Kapoor et al. 2013).
Another group of symbiotic and free-living soil microbes known as PGPR
influence the plant growth by improving plant nutritional status and synthesizing
plant growth-promoting compounds and phytohormones (Glick et al. 1998).
A number of PGPR species have been noted to increase HM stress tolerance in
plants by aiding plant growth in HM-contaminated soils (Burd et al. 2000).
Drugs are bioactive constituents or secondary metabolites released by plants
often in response to stress. Several HMs directly affect biochemical and physiological processes such as altered production of bioactive compounds and reduced
resistance to abiotic stress (Verpoorte et al. 2002). For over two decades HMs in
medicinal plants have been reported from Asia, Europe, and the United States
(Olujohungbe et al. 1994; Kakosy et al. 1996). Though it is well studied that HM
accumulation in medicinal plants exposes humans to a number of health risks
(Dwivedi and Dey 2002), still the utilization of AMF and PGPR in the same
respect has not been hard lined much. The review provides an insight into the role
of AMF and PGPR in HM stress alleviation in plants. The various mechanisms
involved in the purpose have also been discussed briefly (Fig. 16.1).
Fig. 16.1 Events describing HM-induced oxidative stress in plants
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Bioavailability of HMs in Soil and Their Site
of Accumulation in Plants
Metals exist in two forms: bioavailable and non-bioavailable (Sposito 2000). Levels
of HMs in plants vary extensively as the bioavailability of elements is influenced by
a multitude of factors (Nagajyoti et al. 2010). Soil physicochemical properties,
metal and plant species; competition between metals in rhizosphere; plant growth
conditions; plant root density and volume; and characteristics of the association
between plant and soil microbes affect the accumulation of HMs in soil (Leyval
et al. 1997). Transfer of a metal from soil to plant can be delineated quantitatively
by the soil–plant transfer factor (TF) that can be described as the ratio of contaminant concentration in plant parts to concentration in dry soil (Rodriguez
et al. 2002).
Accumulation of HMs in plant parts depends on the site of contact with metal
and its subsequent translocation. Ultracellular studies have depicted the metals in
the intercellular spaces and in the cell wall of root tissues (Marques et al. 2007). It
has been observed that the accumulation of HMs in plant parts increases in a
concentration-time-dependent manner (Khan et al. 2007). On the basis of ability
to accumulate metals differently, plants can be distinguished into metal excluders,
metal indicators, and metal accumulators (Baker and Walker 1990).
16.3
Rhizosphere Microflora Mediating HM Acquisition
in Plants
Interaction of plant roots with rhizosphere microflora influences the bioavailability
and uptake of HM ions through secretion of protons, organic acids, phytochelatins
(PCs), amino acids, and enzymes (Yang et al. 2005). Soil bacteria and AMF have
been characterized to catalyze redox transformations leading to an altered soil
metal bioavailability (Lasat 2002).
In anaerobic respiration, many microorganisms that catalyze redox reactions use
metals as terminal electron acceptors and are known as dissimilatory metalreducing bacteria. These bacteria are not only phylogenetically (Lonergan
et al. 1996) but also physiologically (Lovley et al. 1997) disparate, though most
of these administer Fe3+ and S0 as terminal electron acceptors. Rhizobacteria
produce metal-chelating agents called siderophores that have a conspicuous role
in the acquisition and speciation of several HMs (Burd et al. 2000). Fungal
symbiotic associations enhance the root absorption area and stimulate the remuneration of certain HM ions such as Cu and Zn (Smith and Read 2008). Low
molecular weight organic acids (LMWOA) can influence metal release from
absorbed metal in the soil and increase its solubility through formation of
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complexes like release of Cd by formation of Cd-LMWOA complex (Krishnamurti
et al. 1997). The hyphal mass produced by AMF can bind HMs beyond the plant
rhizosphere by releasing an insoluble glycoprotein commonly known as glomalin
(Gohre and Paszkowski 2006).
16.4
Implications of HM Stress on Plants
Over the years many studies have connoted the effects of HMs on medicinal plants
and these can be abridged as follows:
16.4.1 Growth and Development
Reduced growth and development has been reported in medicinal plants upon
exposure to HMs (Jiang et al. 2001). However, certain positive effects such as
yield enhancement have been observed in Matricaria chamomilla, Mentha
arvensis, and Stevia rebaudiana upon exposure to Zn, Co, Pb, and Ni (Misra
1992; Kartosentono et al. 2002; Das et al. 2005; Grejtovsky et al. 2006).
16.4.2 Disturbed Mineral Nutrition
Most HM ions compete with other metal ions for uptake, transport, and utilization
by plants and consequently result in various element deficiencies, for example,
arsenic competes with phosphorous (Meharg and Macnair 1992).
16.4.3 Membrane Disruption
HMs affect transport of solutes across plasma membrane by resulting in cellular
alterations such as plasma membrane disruption and chloroplast thylakoid swelling
(Valcho et al. 2008).
16.4.4 Effects on Physiological and Metabolic Processes
Certain HMs like Cu and Zn either serve as cofactors/activators in enzyme reactions
or exert a catalytic property as prosthetic group in metalloproteins (Nagajyoti
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et al. 2010). These HMs interact with nonspecific protein sites and displace other
metals from their characteristic binding sites. Reduction in seed germination has
been observed in medicinal plants such as Catharanthus roseus L., Eucomis
autumnalis, and Bowiea volubilis (Pandey et al. 2007; Street et al. 2007).
16.4.5 Oxidative Stress
Metal ions are essential cofactors of enzymes involved in antioxidant network; for
example, all isoforms of superoxide dismutase (SOD) contain bound HM ions like
Cu/Zn-SOD associated with chloroplast and Mn-SOD with glyoxysomes. Metals
are involved in direct or indirect generation of free radicals (FR) and reactive
oxygen species (ROS) in the following ways: (1) direct transfer of electron in
single electron reduction, (2) disturb the metabolic pathways and ensue an increase
in the rate of FR and ROS formation, (3) inactivation and downregulation of the
enzymes of the antioxidative defense system, and (4) depletion of low molecular
weight antioxidants (Aust et al. 1985).
16.4.6 Effect on DNA
Metal binding to the cell nucleus causes promutagenic damage including DNA base
modifications, inter- and intramolecular cross-linkage of DNA and proteins, DNA
strand breaks, rearrangements, and de-purination (Kasprzak 1995). Metal-mediated
production of ROS in DNA vicinity generates a promutagenic adduct 8-oxoG
(7,8-dihydro-8-oxoguanine) that could miss pair with adenine in the absence of
DNA repair, resulting in C to T transversion mutations (Cunningham 1997). Cell
treatment with Ni can cause chromatin condensation, leading to silencing of
putative anti-oncogenic gene expression, thus driving treated cells to a carcinogenic
state (Lee et al. 1995). Concentration and time-dependant Cd, Cu, and Ni
clastogenic effects have been observed in Helianthus annuus (Chakravarty and
Srivastava 1992).
16.4.7 Effects on Secondary Metabolite Production
The chemical composition of plants under HM stress may be altered, and as a result
the quality and potency of the natural products from medicinal plants may be
seriously affected (Zhu and Cullen 1995). The reduction in biosynthesis of active
constituents may be a result of loss or inactivation of specific essential enzymes
involved in the production of secondary metabolites, for example, on exposure to
Ni, the capacity of Hypericum perforatum to produce and accumulate hyperforin is
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Fig. 16.2 Effect of HMs on
secondary metabolite
production
ceased completely (Murch et al. 2003). Probably, to mitigate the phytotoxic effects
of HMs, alteration in secondary metabolism may be one of the plant’s strategies
(Cobbett and Goldsbrough 2000) (Fig. 16.2).
On the other hand, HMs in small concentrations may also act as abiotic elicitors
and improve the biosynthesis of specific compounds in certain medicinal plants
such as Cd enhanced the production of ajmalicine in Catharanthus roseus (Zheng
and Wu 2004), phyllanthin and hypophyllanthin production in Phyllanthus amarus
(Rai et al. 2005), and tropane alkaloids in Atropa belladonna (Lee et al. 1998); and
Pb enhanced sitosterol in Costus speciosus (Kartosentono et al. 2002).
16.4.7.1
Mechanism Involved in the Alteration of Secondary
Metabolite Production
The defensive processes in plants get activated in response to induced stress,
ensuing a change in the transcription of genes coding for enzymes that are involved
in the biosynthesis of secondary metabolites (Kasparova and Siatka 2004). Under
HM-induced oxidative stress, the ROS may elicit secondary plant metabolism to
result in structurally similar or even identical compounds (Mithöfer et al. 2004).
Besides this, in HM-exposed plants, upon stimulation of ACC
(1-aminocyclopropane-1-carboxylic acid) synthase and oxidase, ethylene has
been known to regulate a pathway that accounts for the production of tropane
alkaloids, scopolamine, and hyoscyamine (Maksymiec 2007; Nasim and Dhir
2010). In Brugmansia candida there is an increase in scopolamine in response to
Ag, whereas hyoscyamine production is diminished (Pitta-Alvarez et al. 2000). Ag
probably acts as ethylene blocking agent which downregulates hyoscyamine-
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6-β-hydroxylase (H6H); this enzyme is responsible for converting hyoscyamine to
scopolamine.
16.5
Effect of HM Stress on Rhizosphere Microflora
Elevated concentrations of HMs have multifarious effects on the soil microbial
communities like altered community structure of microbes (Gray and Smith 2005),
decreased numbers of specific populations (Chaudri et al. 2000), and reduced total
microbial biomass (Giller et al. 1998). Certain HMs like Hg, Pb, Zn, Cd, Cu, Ni, and
As inhibit various microbial metabolic activities by DNA damage, transcription
inhibition, protein denaturation, and inhibition of enzyme activity (Khan
et al. 2009). A few rhizospheric microorganisms can develop resistance or tolerance
that may be inherited or induced (Giller et al. 1998), for example, Bradyrhizobium
sp. RM8 provides IAA and siderophores to plants even in the presence of Zn and Ni
stress (Wani et al. 2007). Similarly, HM-tolerant AMF species have also been
reported; for example, Glomus intraradices is tolerant to Pb (Malcova et al. 2003).
To tolerate HM stress, PGPR have evolved several mechanisms (Nies 1999) that
can be enlisted as: (1) exclusion, physiologically active sites are kept away from the
metal ions; (2) extrusion, the metals are made to exit the cells through chromosomal/plasmid mediated events; (3) accommodation, metals associate with the
metal-binding proteins forming complexes such as metal–phytochelatin (PC) and
metal–metallothionein (MT) complexes; (4) biotransformation, reduction of a toxic
metal to a lesser toxic form; and (5) methylation and demethylation of DNA. These
mechanisms could be inducible or constitutive under HM stress (Khan et al. 2009).
In generic terms, the resistance mechanisms in bacteria are encoded on plasmids
and transposons. Resistance against As, Cr, and Cd in some PGPR has been
reported through plasmid-encoded energy-dependent metal efflux systems involving ATPases and chemiosmotic ion/proton pumps (Roane and Pepper 2000).
At elevated concentration HMs in soil reduce or entirely inhibit AMF colonization and henceforth forbid the beneficial effects of the mycorrhizal association
(Chen et al. 2005). Studies cast light on the morphogenetic changes in extraradical
hyphae of G. intraradices in response to Cu, Cd, Pb, and Zn concentrations (Bago
et al. 2004; Ferrol et al. 2009). At raised concentration the growth of the
extraradical mycelium is localized and limited to changes like loss of apical
dominance, cytoplasmic protrusions, extrametrical coils, and abatement of sporulation (Gonzàlez-Guerrero et al. 2005). These morphological alterations in fungus
indicate adaptive changes as (1) growth revocation can be a strategy aimed to avert
toxic-metal-contaminated areas (Gadd 2007), (2) augmentation of extramatrical
coils allows the fungus to produce steep local concentrations of extracellular
products, like metal chelators (this would depreciate metal availability in vicinity
of hyphae creating a stress-free zone), and (3) exaggerated hyphal elongation at
lower HM concentration portrays a strategy to grasp relatively less-contaminated
pockets of the soil to escape local metal enriched microenvironments (Fomina
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et al. 2003). Studies propose a potential adaptation of the indigenous AMF
populations in metal-contaminated sites; therefore, these are seen to have potential
for reclamation of degraded soils (Gildon and Tinker 1981).
16.6
AMF and PGPR at Plant’s Rescue
Experimental evidences connote positive effects of co-inoculation with AMF and
PGPR on removal of HMs from soils (Barea et al. 2005). Some of the mechanisms
by which soil microbes can alleviate HM stress include:
16.6.1 Dilution Effect
AMF can enhance plant growth and establishment against the high levels of HMs in
soil, owing to better nutrition, water uptake and availability, and soil aggregation
properties (Hildebrandt et al. 2007). An extensive range of PGPR is able to mitigate
the HM stress by advocating plant growth like Rhizobium, Pseudomonas,
Agrobacterium, Burkholderia, Azospirillum, Bacillus, Azotobacter, Serratia,
Alcaligenes (Ralstonia), Arthrobacter, and Brevibacillus (Glick 2003; Vivas
et al. 2006). The coalesced effects of AMF and soil bacteria can augment HM
tolerance in plants by promoting plant growth and by production of growth regulators such as indoleacetic acid (IAA) (Vivas et al. 2006).
16.6.2 Chelation
Extraradical mycelium of AMF is important for metabolism-independent binding
of HMs to cell walls and metabolism-dependent intracellular uptake and transport
of HMs (Leyval et al. 1997). Phytostabilization of HMs in the rhizosphere can occur
by production of compounds that precipitate them in soil and by chelation of these
in the cell wall and cellular structures of AMF (Gaur and Adholeya 2004; Gohre
and Paszkowski 2006). Constituents of hyphal cell wall like chitin (Zhou 1999) and
production of insoluble glycoprotein, glomalin, by the fungal hyphae influence the
absorption of HMs (Gonzàlez-Chavez et al. 2004). Also, AMF stimulates plant
roots to produce elevated levels of compounds that are able to chelate HMs, such as
cysteine and glutathione (Galli et al. 1995). PGPR produce siderophores and acids
for mobilizing metals in soils such as Fe. Siderophores mitigate deficiency of Fe
caused due to Ni toxicity (Burd et al. 2000).
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16.6.3 Compartmentalization
Immobilization of metals in the fungal biomass or in mycorrhizosphere is an
important mechanism of AMF to alleviate HM stress. In the intracellular compartmentalization strategy operated by AMF, the excess of HM such as Cu is
translocated to subcellular compartments (vacuoles) where it is stored in specific
fungal structures (extraradical spores and intraradical vesicles) that have restricted
core metabolic functions (Ferrol et al. 2009).
16.6.4 Biotic Sequestration
Metal dissolution by AMF may occur by proton-promoted or ligand-promoted
mechanisms and by organic acids as they provide both protons for solubilization
and metal-chelating anions to complex with metal cations (Finlay 2008). Interestingly, AMF associated with metal-tolerant plants accumulate HMs in plant roots in
nontoxic forms, for example, AMF in Voila calaminaria, an important medicinal
plant, efficiently sequester metals in the roots (Tonin et al. 2001). Certain PGPR
have also been attributed to have similar effects, such as Ochrobactrum bacillus
that lowers the toxicity of chromium by reducing Cr (VI) to Cr (III) (Faisal and
Hasnain 2006).
16.6.5 Molecular Mechanisms
In the roots of mycorrhizal plants, HM content is significantly altered, evincing that
the expression of genes involved in HM tolerance is altered at transcriptional and
translation levels (Ouziad et al. 2005). It has been connoted that AMF colonization
in roots significantly affects the expression of multifarious plant genes involved in
HM tolerance and detoxification (Rivera-Becerril et al. 2005). The expression of an
MT gene of Gigaspora margarita (BEG 34) is upregulated in the presence of Cu
(Lanfranco et al. 2002). Another gene encoding MT involved in metal chelation and
ROS scavenging has been classified in AMF (Ferrol et al. 2009). Expression of
certain transporter genes also gets affected under HM stress, like on exposure to Zn
there is enhanced transcript level of a Zn transporter gene GintZnT1 in
G. intraradices mycelium indicating its plausible role in protection against Zn
stress (González-Guerrero et al. 2005). Another transporter gene GintABC1 in
G. intraradices is upregulated in response to Cd and Cu. It encodes for a polypeptide bearing homology to the N-terminal region of the multidrug-resistance-protein
(MRP) subfamily of ABC transporters. This connotes that GintABC1 may be
involved in the detoxification of Cd and Cu (Gonzàlez-Guerrero et al. 2006). The
products of such HM responsive genes may act in a rather localized manner,
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conceivably restricted to fungal structures like the arbuscules. The concomitant
upregulation of stress-related AMF genes evince that in mycorrhizal plants
increased HM tolerance could be attributed to effective fungal HM tolerance
mechanisms (Hildebrandt et al. 2007).
A few genes encoding proteins plausibly involved in ROS homeostasis have also
been identified and delineated in AMF, viz., three genes coding for SODs
(González-Guerrero et al. 2005) and ten genes allegedly encoding glutathione
S-transferases (GSTs) (Waschke et al. 2006); in the hyphae of G. intraradices,
expression of four genes that result in the production of GST is observed under Zn
stress (Hildebrandt et al. 2007). The enzyme GST acts as a catalyzer in combination
with glutathione and some electron receivers ensuing alleviation of oxidative stress
(Moons 2003).
16.6.6 Effect of AMF and PGPR on Secondary Metabolite
Production in Medicinal Plants
A number of studies have revealed the potential of AMF in enhancing plant growth
and altering secondary metabolite production (Kapoor et al. 2002a, b; Copetta
et al. 2006), for example, castanospermine (an alkaloid of the indolizidine type)
was found to increase with AMF colonization in Castanospermum australe, an
important medicinal plant (Abu-Zeyad et al. 1999). Gigaspora rosea increases
biomass as well as the total amount of essential oil in Ocimum basilicum. Similar
roles of PGPR have been reported in medicinal plants, for example, PGPR increase
ajmalicine in Catharanthus roseus (Karthikeyan et al. 2010) and withaferin A in
Withania somnifera (Khalid et al. 2004). Attempts have been made to study the
synergism of AMF and PGPR in context of plant growth and secondary metabolite
production in medicinal plants, as in Begonia malabarica, upon co-inoculation of
PGPR and G. mosseae increase in plant growth, and enhancement of secondary
metabolite production has been noted (Thangavel et al. 2008).
16.7
Conclusions
The fact that HMs enhance the production of bioactive compounds in certain
medicinal plants presents a pragmatic aspect of utilizing contaminated sites for
cultivation of such plants. However, the applicability of this strategy will primarily
depend on the part of the plant used for medicinal purposes and the ability of that
medicinal plant species to exclude or accumulate HMs. The knowledge of which
plant part has medicinal value and its usage, viz., direct use such as dried powdered
form or a processed extract from it, is important. Direct consumption of medicinal
plant parts from HM accumulators poses a huge risk of exposure to HMs and their
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accumulation in humans over a period, leading to chronic health disorders. Also,
the medicinal extracts from the plants growing in such soils should undergo strict
quality check. Leverages of this strategy include the utilization of an otherwise
wasteland for achieving enhanced production of bioactive compounds, and at the
same time cultivation of contaminated food crops can be avoided.
To such sites application of rhizosphere microflora that enhances HM uptake can
further benefit. As the response of AMF and PGPR to HM toxicity is variable, there
are gaps in the understanding of pathways involved in metal transport and regulatory mechanisms. There is a need to evaluate rhizosphere microflora-induced
changes in HM speciation and whether these changes can affect the extent of
accumulation and site of distribution of HMs in medicinal plants. For the success
of this artifice, knowledge of a superior suitable strain of AMF and PGPR for every
medicinal plant species being used here is imperative. Assimilation of pertinent
features of microbial–plant–HM interaction in rhizosphere and understanding the
regulation of metal homeostasis along with metal forbearance strategies form the
very base of this strategy.
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mkumar9@amity.edu
Part V
PGPR: Diversity and Characterization
mkumar9@amity.edu
Chapter 17
Diverse Endophytic Microflora of Medicinal
Plants
Pranay Jain and Ram Kumar Pundir
17.1
Introduction
The term endophyte (Gr. endon, within; phyton, plant) was first coined by De Bary
(1866), and an endophyte is a bacterial or fungal microorganism, which spends the
whole or part of its life cycle colonizing inter- and/or intracellularly inside the
healthy tissues of the host plant, typically causing no apparent symptoms of disease
(Sturz et al. 2000; Wilson 1995). All vascular plants harbor endophytic organisms
(Zhang et al. 2006). These endophytes protect their hosts from infectious agents and
adverse conditions by secreting bioactive secondary metabolites (Carroll and
Carroll 1978; Azevedo et al. 2000; Strobel 2003).
Endophytes are now considered as an important component of biodiversity. The
distribution of endophytic microflora differs with the host. Medicinal plants are
known to harbor endophytic microorganisms that are believed to be associated with
the production of pharmaceutical products (Zhang et al. 2006). Therefore, it is
important to explore endophytic microflora in the medicinal plants. Endophytes are
mostly an unexplored group of microorganisms, but a few studies show them as a
huge source of medicinal compounds. Approximately 300,000 plant species growing in an unexplored area on the Earth are host to one or more endophytes, and the
presence of biodiverse endophytes in huge number plays an important role on
ecosystems with the greatest biodiversity (Souza et al. 2004).
P. Jain (*)
University Institute of Engineering and Technology, Kurukshetra University,
Kurukshetra 136119, India
e-mail: drpranayjain@gmail.com
R.K. Pundir
Department of Biotechnology Engineering, Ambala College of Engineering and Applied
Research, Devsthali, P.O. Sambhalkha, Ambala, Haryana, India
e-mail: drramkpundir@gmail.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_17
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Considering that only a small amount of endophytes have been studied, recently,
several research groups have been motivated to evaluate and elucidate the potential
of these microorganisms applied on biotechnological processes focusing on the
production of bioactive compounds. Endophytes provide a broad variety of bioactive secondary metabolites with unique structure, including alkaloids,
benzopyranones, flavonoids, phenolic acids, quinones, steroids, terpenoids,
tetralones, xanthones, and others (Tan and Zou 2001). Such bioactive metabolites
find wide-ranging application as agrochemicals, antibiotics, immunosuppressants,
antiparasitics, antioxidants, and anticancer agents (Strobel 2003).
Endophytic microorganisms are a significant reservoir of genetic diversity and
an important source in the discovery of novel bioactive secondary metabolites.
These group of strains can produce high or multiple kinds of antibiotics including
terpenoids, alkaloids, aromatic compounds, and polypeptides (Gao et al. 2010)
which are similar to host plant chemicals, thus triggering the expectations that
endophytes can serve as an alternative source (Priti et al. 2009). So, plants with
beneficial ethnobotanical history are also likely a candidate for study, since the
medicinal uses to which the plant may have selected relate more to its population of
endophytes than to the plant biochemistry itself. Endophytic organisms are found in
all the types of plant tissues such as stems, roots, leaves, fruits, ovules, seeds, tubers,
rachis, and bark. Probably, hundreds of endophytic species from a single plant are
also possible, and among them, at least one generally shows host specificity (Tan
and Zou 2001).
Medicinal plants harbor a distinctive microbiome due to their unique and
structurally divergent bioactive secondary metabolites that are most likely responsible for the high specificity of the associated microorganisms (Qi et al. 2012).
Plants contain numerous different biologically active compounds, and plantderived medicines have been part of traditional healthcare in most parts of the
world for thousands of years. In general, natural products play a highly considerable
role in the drug discovery and development process, as about 26 % of the new
chemical entities introduced into the market worldwide from 1981 to 2010 were
either natural products or those derived directly there from, reaching a high of 50 %
in 2010 (Newman and Cragg 2012). In regard to the alarming incidence of antibiotic resistance in bacteria with medical relevance, medicinal plants with
antibacterial properties are of central importance as bioresources for novel active
metabolites (Palombo and Semple 2001).
Likewise, there is an increasing need for more and better antimycotics to treat
those with weakened immune systems who are more prone to developing fungal
infections, such as from the AIDS epidemic, cancer therapy, or organ transplants
(Strobel and Daisy 2003; Strobel et al. 2004). For centuries, several phytotherapeutics have also been known for their antiphlogistic features, yet despite the
progress within medical research, chronic inflammatory diseases such as asthma,
arthritis, and rheumatism remain one of the world’s leading health problems
(Li et al. 2003). Hypertension is another critical issue for human health and is a
primary risk factor for stroke, heart disease, and renal failure. Many herbal remedies as well as foods, however, are known and effective folk medicines in the
prevention and/or treatment of high blood pressure (Abdel-Aziz et al. 2011). Hence,
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nature must still harbor plenty of currently unknown active agents that may serve as
leads and scaffolds for the development of desperately needed efficacious drugs for
a multitude of diseases (Newman and Cragg 2012). Today, globalization has also
had an impact on the use of medicinal plants and has proven beneficial in allowing
greater access to these medicines for people all across the globe.
17.2
Biodiversity of Endophytes
Of the myriad of ecosystems on Earth, those having the greatest biodiversity also
have endophytes with the greatest number and the most biodiverse microorganisms.
Almost all vascular plant species examined to date were found to anchor
endophytic bacteria and/or fungi (Sturz et al. 2000; Arnold et al. 2000). Moreover,
the colonization of endophytes in marine algae [Smith et al. 1989; mosses and ferns
(Petrini et al. 1992; Raviraja et al. 1996)] had also been detected. Based on fact,
endophytes are important components of microbial biodiversity. Commonly,
numerous endophyte species can be isolated from a single plant, and among
them, at least one species shows host specificity. The environmental conditions
under which the host is growing also affect the endophyte population (Hata
et al. 1998), and the endophyte profile may be more diversified in tropical areas.
Tropical and temperate rain forests are the most biologically diverse terrestrial
ecosystems on Earth. The most threatened of these spots cover only 1.44 % of the
land’s surface, yet they harbor more than 60 % of the world’s terrestrial biodiversity
(Mittermeier et al. 1999). 418 endophyte morphospecies (estimated 347 genetically
distinct taxa) were isolated from 83 healthy leaves of Heisteria concinna and
Ouratea lucens in a lowland tropical forest of central Panama and proposed that
tropical endophytes themselves could be hyperdiverse with host preference and
spatial heterogeneity (Arnold et al. 2000). Various species of endophytic fungi as
Cladosporium cladosporoides, Phoma spp., Phomopsis spp., and Xylaria spp. had
been reported in four types of tropical forests: dry thornforest, dry deciduous forest,
moist deciduous forest, and semi-evergreen forest (Suryanarayanan et al. 2002).
As such, one expects that areas of high plant endemicity also possess specific
endophytes that may have evolved with the endemic plant species. Ultimately,
biological diversity implies chemical diversity because of the constant chemical
innovation that exists in ecosystems where the evolutionary race to survive is the
most active. Tropical rain forests are a remarkable example of such type of
environment. Competition is great, resources are limited, and selection pressure is
at its peak. This gives rise to a high probability that rain forests are a source of novel
molecular structures and biologically active compounds (Redell and Gordon 2000).
A metabolic distinction was described between tropical and temperate endophytes
through statistical data which compared the number of bioactive natural products
isolated from endophytes of tropical regions to the number of those isolated from
endophytes of temperate origin. Not only did they find that tropical endophytes
provide more active natural products than temperate endophytes, but they also
distinguished that a significantly higher number of tropical endophytes produced
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a larger number of active secondary metabolites than did fungi from other temperate substrata (Bills et al. 2002). This observation suggests the importance of the host
plant in influencing the general metabolism of endophytic microbes. Moreover,
genotypic diversity too has been observed in single endophyte species originating
from conifers, birch, and grasses (Reddy et al. 1998). Accordingly, fungal endophytes have the ability to produce novel metabolites with novel structures than soil
isolates (Schulz et al. 2002) and are presumably ubiquitous in the plant kingdom
with the population being dependent on host species and location.
17.3
Biodiversity of Fungal Endophytes
A variety of relationships exist between fungal endophytes and their host plants,
ranging from mutualistic or symbiotic to antagonistic or slightly pathogenic
(Arnold 2007; Schulz and Boyle 2005). Endophytes may produce overabundance
of substances of potential use to agriculture, industry, and modern medicine such as
novel antibiotics, antimycotics, immunosuppressant, and anticancer compounds
(Mitchell et al. 2008). In addition, the studies of endophytic fungi and their
relationships with host plants will shed light on the ecology and evolution of both
the endophytes and their hosts: the evolution of endophyte plant symbioses and the
ecological factors that influence the direction and strength of the endophyte host
plant interaction (Saikkonen et al. 1998). Since natural products are likely adapted
to a specific function in nature, so search for novel secondary metabolites should
concentrate on organisms that inhabit novel biotopes (Schulz et al. 2002).
A study was undertaken by Das et al. (2012) to investigate the influence of plant
probiotic fungus Piriformospora indica on the medicinal plant Coleus forskohlii.
Interaction of the C. forskohlii with the root endophyte P. indica under field
conditions results in an overall increase in aerial biomass, chlorophyll contents,
and phosphorus acquisition. The fungus also promoted inflorescence development,
consequently the amount of p-cymene in the inflorescence increased. Growth of the
root thickness was reduced in P. indica-treated plants as they became fibrous, but
developed more lateral roots. Because of the smaller root biomass, the content of
forskolin was decreased. The symbiotic interaction of C. forskohlii with P. indica
under field conditions promoted biomass production of the aerial parts of the plant
including flower development. The plant aerial parts are an important source of
metabolites for medicinal application. Therefore it was suggested that the use of the
root endophyte fungus P. indica in sustainable agriculture will enhance the medicinally important chemical production.
Azadirachta indica A. Juss. (neem), native to India, is well known worldwide for
its insecticidal and ethanopharmacological properties. A variety of procedures and
a number of different media were used to isolate the maximum number of endophytic fungi from unripe fruits and roots by Verma et al. (2011). A total of
272 isolates of 29 filamentous fungal taxa were isolated at a rate of 68.0 % from
400 samples of three different individual trees (at locations Az1, Az2, Az3).
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Mycological agar (MCA) medium yielded the highest number of isolates (95, with
a 14.50 % isolation rate) with the greatest species richness. Mycelia Sterilia
accounted for 11.06 % and coelomycetes 7.25 %, while hyphomycetes showed
the maximum number of representative isolates (81.69 %). Mycelia Sterilia, based
on their 5.8S ITS1, ITS2, and partial 18S and 28S rDNA sequences, were identified
as Fusarium solani (99 %), Chaetomium globosum (93 %). Humicola, Drechslera,
Colletotrichum, and Scytalidium sp. respectively were some of the peculiar fungal
endophytes recovered from this plant.
Schulz et al. (2002) isolated about 6500 endophytic fungi from herbaceous
plants and trees and screened them for biologically active compounds. They
found a correlation between biological activity and biotope. They also got a higher
proportion of the fungal endophytes, in contrast to the soil isolates, suppressed at
least one of the test organisms for anti-algal and herbicidal activities. Medicinal
plants have been recognized as a repository of fungal endophytes with novel
metabolites of pharmaceutical importance (Kumar et al. 2005; Strobel et al. 2004;
Wiyakrutta et al. 2004). The various natural products produced by endophytic fungi
possess unique structures and great bioactivities, representing a huge reservoir
which offers an enormous potential for exploitation for medicinal, agricultural,
and industrial uses (Tan and Zou 2001; Zhang et al. 2006).
Most fungal endophytes isolated to date have been ascomycetes and their
anamorphs; however, Rungjindamai et al. (2008) reported that several endophytes
may also belong to basidiomycetes. However, their colonization rate and the
isolation rate of endophytic fungi from plants varied greatly. Some medicinal plants
harbored more endophytic fungi than others. Some of the common endophytes not
only existed in more plant hosts but also had higher relative frequencies within each
of the hosts. In contrast, some other endophytic fungi were detected in only one
given plant host (Arnold et al. 2001; Bettucci et al. 2004). Most of the researches on
endophytes have been carried out using hosts from temperate countries, specifically
from the Northern Hemisphere and New Zealand. The update data available from
tropical regions are scarce. However, these data are showing that tropical plant
hosts contain a great diversity of endophytic microorganisms, and many of them are
not yet classified and possibly belonging to new genera and species. In fact
potentially, they are of biotechnological importance as new pharmaceutical active
compounds, secondary metabolites, biological control agents, and other useful
characteristics could be found by further exploration of tropical endophytes. A
better understanding of plant–endophyte relationships in tropical conditions can be
achieved from these studies.
Enumeration of the endophytic fungi from the red listed, critically endangered
medicinal plant, Coscinium fenestratum was investigated for the first time in India
by Goveas et al. (2011). The ubiquitous presence of 41 endophytic fungi belonging
to 16 different taxa was identified from 195 samples of healthy leaves and stem
using traditional morphological methods. The overall colonization rate of endophytes in both the leaf and the stem was found to be 21.02 %. The stem showed low
percentage frequency of colonization of the endophytic fungi when compared to
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leaf segments. Among the endophytic flora, Phomopsis jacquiniana was found to
be the core-group fungus with a colonization frequency of 4.6 %.
A study by Dhanalakshmi et al. (2013) at Salem, Tamil Nadu, India, was
undertaken to isolate and identify the potential endophytic fungi from Moringa
oleifera, a traditional medicinal plant. A total of 24 segments each 12 from the leaf
and stem were collected, surface sterilized, and inoculated on to Sabouraud dextrose agar (SDA) plates. Based on the macroscopic and microscopic features, the
fungal isolates were identified as Alternaria spp., Aspergillus spp., Bipolaris spp.,
Exophiala spp., Nigrospora spp., and Penicillium spp. Many unidentified sterile
mycelia forms were also found which were grouped under the class Mycelia
Sterilia. The colonization frequency (CF) and endophytic infection rate (EIR)
were observed as 91.66 % and 45.83 %, respectively. The results of this study
suggest that traditional medicinal plants are a rich and reliable source of novel
endophytic fungi.
Endophytic fungi residing in medicinal plants have not been systematically
characterized. In a study carried out by, they classified 1,160 fungal isolates from
29 medicinal plant species using traditional morphological methods. The colonization rate, isolation rate, and relative frequency of these endophytes were investigated. The relationship between the composition of endophytic fungi and chemical
constituents of host plants was also explored for the first time. The results showed
that endophytic fungi from these medicinal plants exhibited high biodiversity, host
recurrence, tissue specificity, and spatial heterogeneity. The taxa of Alternaria,
Colletotrichum, Phoma, Phomopsis, Xylariales, and Mycelia Sterilia were the
dominant fungal endophytes. Some phenolic compounds were found to more likely
coexist with certain endophytic fungi in the same plants. Their systematic investigation revealed that traditional medicinal plants are a rich and reliable source of
novel endophytic fungi.
Qadri et al. (2013) conducted a study to characterize and explore the endophytic
fungi of selected medicinal plants from the Western Himalayas for their bioactive
potential. A total of 72 strains of endophytic fungi were isolated and characterized
morphologically as well as on the basis of ITS1-5.8S-ITS2 ribosomal gene
sequence acquisition and analyses. The fungi represented 27 genera of which two
belonged to Basidiomycota, each representing a single isolate, while the rest of the
isolates comprised of ascomycetous fungi. Among the isolated strains, ten isolates
could not be assigned to a genus as they displayed a maximum sequence similarity
of 95 % or less with taxonomically characterized organisms. Among the host plants,
the conifers, Cedrus deodara, Pinus roxburgii, and Abies pindrow, harbored the
most diverse fungi, belonging to 13 different genera, which represented almost half
of the total genera isolated. Several extracts prepared from the fermented broth of
these fungi demonstrated strong bioactivity against E. coli and S. aureus with the
lowest IC50 of 18 μg/ml obtained with the extract of Trichophaea abundans
inhabiting Pinus sp. In comparison, extracts from only three endophytes were
significantly inhibitory to Candida albicans, an important fungal pathogen. Further,
24 endophytes inhibited three or more phytopathogens by at least 50 % in coculture,
among a panel of seven test organisms. Extracts from 17 fungi possessed
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immunomodulatory activities with five of them showing significant immune suppression as demonstrated by the in vitro lymphocyte proliferation assay. This study
was an important step towards tapping the endophytic fungal diversity from the
Western Himalayas and assessing their bioactive potential. Further studies on the
selected endophytes may lead to the isolation of novel natural products for use in
medicine, industry, and agriculture.
Calotropis gigantea (L.) R.Br., a widely used medicinal plant in India, was
exploited for endophytes as a possible source of bioactive secondary metabolites by
Selvanathan et al. (2011). About 700 segments from 10 plants of Calotropis
gigantea, collected from different locations of Guindy Campus, University of
Madras during the year 2009–2010, were processed for the presence of endophytic
fungi. A total of 13 fungal species, viz., Aspergillus niger, Aspergillus flavipes,
Alternaria porri, Curvularia lunata, Fusarium oxysporum, Nigrospora sphaerica,
Colletotrichum falcatum, Pestalotiopsis sydowiana, Phoma exigua, Phomopsis
archeri, Leptosphaerulina chartarum, and Mycelia Sterilia, were isolated and
identified based on the morphology of the fungal culture and characteristics of
the spores.
The genus Acacia comprises over 1,300 species of which nearly 1,000 are found
in Australia. Acacia species are used widely as food (e.g., seeds are ground into
flour and the gum is edible), and the wood has been traditionally made into clubs,
spears, boomerangs, and shields. Several species are used as narcotics and painkillers, to treat headaches, cold, and fevers, and as antiseptics and bactericides, to
treat skin disorders by the indigenous people of Australia. While there is some
information available about the medicinal properties of Acacia, there is no information about the endophytic microorganisms of these plants. With increased need
for new bioactive compounds with medical, industrial, or biotechnological applications, Tran et al. (2010) investigated the bioactive properties of fungal endophytes of Acacia species. Specifically, they isolated endophytic fungi from the
phyllodes of Acacia baileyana, Acacia podalyriifolia, and Acacia floribunda. These
were classified as Aureobasidium, Chaetomium, and Sordariomycetes through
genetic analysis of ribosomal RNA genes. The bioactivity of the fungal endophytes
was examined, and a number of isolates exhibited antibacterial and antifungal
properties. Other isolates also exhibited amylase activity and were thus able to
hydrolyze starch. This study showed that fungal endophytes are readily isolated
from the phyllodes of Acacia species and that these exhibit promising bioactive
properties. Thus, endophytes from Australian native plants may be a useful source
of novel bioactive compounds.
Glycine max (L.) Merr, a widely used agricultural and pharmaceutical plant in
India, was exploited for endophytes as a possible source of bioactive secondary
metabolites by Tenguria and Firodiya (2013). All isolates were identified based on
colony morphology and examination of spores and fruiting bodies using stereo and
light microscopes. Total 118 endophytic fungi of nine genera were isolated from
200 segments of fresh Glycine max (L.) leaves, collected from central region of
Madhya Pradesh, India. The endophytic fungi recovered belong to ascomycetes
(4.26 %), coelomycetes (18.64 %), hyphomycetes (65.23 %), and sterile mycelium
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P. Jain and R.K. Pundir
(11.86 %) each. The most dominant endophytes were Alternaria (25.42 %), Phoma
sp. (18.64 %), Fusarium sp. (15.24 %), and Penicillium sp. (12.71 %).
First complete information on occurrence, distribution, and diversity of endophytic fungi associated with organs of Butea monosperma was presented by Tuppad
and Shishupala (2013). Seventy-three endophytic fungal isolates belonging to
genera Aspergillus, Cladosporium, Curvularia, Fusarium, Pithomyces,
Scopulariopsis, Colletotrichum, Chaetomium, Papulaspora, and Sclerotium and
three different morphotypes were found in different tissues. Colletotrichum
sp. was dominant in most of the plant parts with relative frequency of 21.9 %.
Isolates belonging to Sclerotium sp. had relative frequency of 13.6 %. Endophytic
fungal diversity appeared maximum in stem and lamina samples. Frequency of
occurrence of endophytic fungi differed greatly in different plant parts. Extent of
similarity in endophytic fungal colonization was maximum between stem and
lamina as indicated by Jaccards coefficient. Differential distribution of fungi in
various tissues of B. monosperma was evident.
Tropical and subtropical plants are rich in endophytic community diversity.
Endophytes, mainly fungi and bacteria, inhabit the healthy plant tissues without
causing any damage to the hosts. These fungi can be useful for biological control of
pathogens and plant growth promotion. Some plants of the genus Piper are hosts of
endophytic microorganisms; however, there is little information about endophytes
on Piper hispidum, a medicinal shrub used as an insecticide, astringent, diuretic,
stimulant, liver treatment, and for stopping hemorrhages. Orlandelli et al. (2012)
isolated the fungal endophyte community associated with P. hispidum leaves from
plants in a Brazilian forest remnant. The endophytic diversity was examined based
on the sequencing of the ITS1-5.8S-ITS2 region of rDNA. A high colonization
frequency was obtained, as expected for tropical angiosperms. Isolated endophytes
were divided into 66 morphogroups, demonstrating considerable diversity. They
identified 21 isolates, belonging to 11 genera (Alternaria, Bipolaris,
Colletotrichum, Glomerella, Guignardia, Lasiodiplodia, Marasmius, Phlebia,
Phoma, Phomopsis, and Schizophyllum); one isolate was identified only to the
order level (Diaporthales). Bipolaris was the most frequent genus among the
identified endophytes. Phylogenetic analysis confirmed the molecular identification
of some isolates to genus level, while for others it was confirmed at the species
level.
Endophytic fungi from medicinal plants are important due to their ability to
produce a variety of novel bioactive compounds possibly those produced by their
host plant. In a study carried out by Agarkar (2013), the endophytic fungus isolated
from the medicinal plant Ocimum sanctum Linn. was identified as Colletotrichum
species based on its morphological characteristics. Further, antimicrobial activity of
the ethyl acetate extract of endophytic Colletotrichum sp. was tested against five
different human pathogenic bacteria and a fungus Candida guilliermondii. The
extract was effective against all test pathogens, and significant activity was
observed against Salmonella typhi and Candida guilliermondii. In case of
C. guilliermondii, the combined effect of extract and standard antibiotic was
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enhanced greatly showing synergistic activity. Thus, endophytic Colletotrichum
sp. is a promising fungus for obtaining novel antimicrobial agent.
Dendrobium spp. are traditional Chinese medicinal plants, and the main effective ingredients (polysaccharides and alkaloids) have pharmacological effects on
gastritis infection, cancer, and antiaging. Previously, we confirmed endophytic
xylariaceous fungi as the dominant fungi in several Dendrobium species of tropical
regions from China. In the study carried out by Chen et al. (2013), the diversity,
taxonomy, and distribution of culturable endophytic xylariaceous fungi associated
with seven medicinal species of Dendrobium (Orchidaceae) were investigated.
Among the 961 endophytes newly isolated, 217 xylariaceous fungi (morphotaxa)
were identified using morphological and molecular methods. The phylogenetic tree
constructed using nuclear ribosomal internal transcribed spacer (ITS), large subunit
of ribosomal DNA (LSU), and beta-tubulin sequences divided these anamorphic
xylariaceous isolates into at least 18 operational taxonomic units (OTUs). The
diversity of the endophytic xylariaceous fungi in these seven Dendrobium species
was estimated using Shannon and evenness indices, with the results indicating that
the dominant Xylariaceae taxa in each Dendrobium species were greatly different,
though common xylariaceous fungi were found in several Dendrobium species.
These findings implied that different host plants in the same habitats exhibit a
preference and selectivity for their fungal partners. Using culture-dependent
approaches, these xylariaceous isolates may be important sources for the future
screening of new natural products and drug discovery.
In a study carried out by Paul et al. (2006), endophytic fungi were isolated from
healthy leaf and root samples of Taraxacum coreanum. Of the 72 isolates recovered, 39 were from leaves and 33 from roots with an isolation frequency of 54 %
and 46 %, respectively. Based on ITS sequence analysis, 72 isolates were classified
into 19 genera of which 17 were under the phylum Ascomycota and 2 were under
Basidiomycota. Diverse genera were found and Alternaria, Cladosporium, Fusarium, and Phoma were dominant. Out of 19 genera, Apodus, Ceriporia, Dothideales,
Leptodontidium, Nemania, Neoplaconema, Phaeosphaeria, Plectosphaerella, and
Terfezia were new to Korea. Seventy-two isolates were screened for antifungal
activity, of which 10 isolates (14 %) were found active at least against one of the
tested fungi. Isolate 050603 had the widest antifungal spectra of activity, and
isolates 050592 and 050611 were active against three plant pathogenic fungi.
Jatropha curcas L., a perennial plant grown in the tropics and subtropics is
popularly known for its potential as biofuel. The plant is reported to survive under
varying environmental conditions having tolerance to stress and an ability to
manage pest and diseases. The plant was explored for its endophytic fungi for use
in crop protection by Kumar and Kaushik (2013). Endophytic fungi were isolated
from the leaf of Jatropha curcas, collected from New Delhi, India. Four isolates
were identified as Colletotrichum truncatum, and other isolates were identified as
Nigrospora oryzae, Fusarium proliferatum, Guignardia cammillae, Alternaria
destruens, and Chaetomium sp. Dual plate culture bioassays and bioactivity assays
of solvent extracts of fungal mycelia showed that isolates of Colletotrichum
truncatum were effective against plant pathogenic fungi Fusarium oxysporum and
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Sclerotinia sclerotiorum. Isolate EF13 had the highest activity against
S. sclerotiorum. Extracts of active endophytic fungi were prepared and tested
against S. sclerotiorum. Ethyl acetate and methanol extract of C. truncatum EF10
showed 71.7 % and 70 % growth inhibition, respectively. Hexane extracts of
C. truncatum isolates EF9, EF10, and EF13 yielded oil, and the oil from EF10
was similar to the oil of the host plant, i.e., J. curcas.
17.4
Biodiversity of Endophytic Bacteria
and Actinomycetes
A total of 18 endophytic bacteria and 32 phyllosphere bacteria were isolated from
the herbal plants of Citrus sp., Pluchea indica, Curcuma longa, Nothopanax
scutellarium, Piper crocatum, and Andrographis paniculata by Soka et al. (2012)
from Indonesia. About 72 % of endophytic bacteria isolates have proteolytic
activity, and about 11 % have lipolytic activity. On the other hand, about 59 % of
phyllosphere bacteria isolates have proteolytic activity, and about 19 % have
lipolytic activity. Phylogenetic diversity analysis was conducted by using the
amplified ribosomal DNA restriction analysis (ARDRA) method, and the sequence
of 16S rDNA was digested with endonuclease restriction enzymes: MspI, RsaI, and
Sau961. The diversity of endophytic and phyllosphere bacterium from the samples
of herbal plants was high. Bacteria isolated from the same herbal plant do not
always have a close genetic relationship except for the bacteria isolated from the
P. indica plant which showed a close genetic relationship with each other.
The study carried out by Baker et al. (2012) uncapped the bacterial endophytes
inhabiting the stems and roots of Mimosa pudica L. located in the southern parts of
India. The screening resulted in isolation of 141 myriad bacterial endophytes with
different morphological characteristics. The endophytes isolated in the study could
be exploited for pharmaceutical research.
In traditional medicine, Tridax procumbens Linn. is used in the treatment of
injuries and wounds. The bacterial endophytes of medicinal plants could produce
medicinally important metabolites found in their hosts, and hence, the involvement
of bacterial endophytes in conferring wound healing properties to T. procumbens
cannot be ruled out. But, we do not know which types of bacterial endophytes are
associated with T. procumbens. The aim of study carried out by Praveena and Bhore
(2013) was to investigate the fast growing and cultivable bacterial endophytes
associated with T. procumbens.
Leaves and stems of healthy T. procumbens plants were collected and cultivables. Bacterial endophytes were isolated from surface-sterilized leaf and stem tissue
samples using Luria–Bertani (LB) agar (medium) at standard conditions. A polymerase chain reaction was employed to amplify 16S rRNA-coding gene fragments
from the isolates. Cultivable endophytic bacterial isolates were identified using 16S
rRNA gene nucleotide sequence similarity-based method of bacterial identification.
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Altogether, 50 culturable endophytic bacterial isolates were isolated. 16S rRNA
gene nucleotide sequence analysis using the Basic Local Alignment Search Tool
(BLAST) revealed identities of the endophytic bacterial isolates. Analysis revealed
that cultivable Bacillus spp., Cronobacter sakazakii, Enterobacter spp.,
Lysinibacillus sphaericus, Pantoea spp., Pseudomonas spp., and Terribacillus
saccharophilus are associated with T. procumbens. Based on the results, we conclude that 24 different types of culturable BEs are associated with traditionally used
medicinal plant, T. procumbens, and require further study.
The diversity and beneficial characteristics of endophytic microorganisms have
been studied in several host plants. However, information regarding naturally
occurring seed-associated endophytes and vertical transmission among different
life-history stages of hosts is limited. Endophytic bacteria were isolated from seeds
and seedlings of 10 Eucalyptus species and two hybrids by Ferreira et al. (2008).
The results showed that endophytic bacteria, such as Bacillus, Enterococcus,
Paenibacillus, and Methylobacterium, are vertically transferred from seeds to
seedlings. In addition, the endophytic bacterium Pantoea agglomerans was tagged
with the gfp gene, inoculated into seeds, and further reisolated from seedlings.
These results suggested a novel approach to change the profile of the plants, where
the bacterium is a delivery vehicle for desired traits. This is the first report of an
endophytic bacterial community residing in Eucalyptus seeds and the transmission
of these bacteria from seeds to seedlings. The bacterial species reported in this work
have been described as providing benefits to host plants. Therefore, we suggest that
endophytic bacteria can be transmitted vertically from seeds to seedlings, assuring
the support of the bacterial community in the host plant.
The association of endophytic bacteria with their plant hosts has a beneficial
effect for many different plant species. Taghavi et al. (2009) identified endophytic
bacteria that improve the biomass production and the carbon sequestration potential
of poplar trees (Populus spp.) when grown in marginal soil and to gain an insight in
the mechanisms underlying plant growth promotion. Members of the Gammaproteobacteria dominated a collection of 78 bacterial endophytes isolated from poplar
and willow trees. As representatives for the dominant genera of endophytic
Gammaproteobacteria, we selected Enterobacter sp. strain 638, Stenotrophomonas
maltophilia R551-3, Pseudomonas putida W619, and Serratia proteamaculans
568 for genome sequencing and analysis of their plant growth-promoting effects,
including root development. Derivatives of these endophytes, labeled with gfp,
were also used to study the colonization of their poplar hosts. In greenhouse studies,
poplar cuttings (Populus deltoides Populus nigra DN-34) inoculated with
Enterobacter sp. strain 638 repeatedly showed the highest increase in biomass
production compared to cuttings of noninoculated control plants. Sequence data
combined with the analysis of their metabolic properties resulted in the identification of many putative mechanisms, including carbon source utilization, that help
these endophytes to thrive within a plant environment and to potentially affect the
growth and development of their plant hosts. Understanding the interactions
between endophytic bacteria and their host plants should ultimately result in the
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design of strategies for improved poplar biomass production on marginal soils as a
feedstock for biofuels.
Wang et al. (2010) isolated four new p-aminoacetophenonic acid antibiotic from
endophytic Streptomyces sp. HK10552 of the mangrove plant Aegiceras
corniculatum. Streptomyces albidoflavus isolated from mangrove plants were able
to produce antimycin A18 which showed broad spectrum of activity against pathogenic microorganisms (Yan et al. 2010). Vollmar et al. (2009) isolated a Streptomyces sp. GS DV232 from traditional Chinese medicinal plants which was reported
to produce an alkaloid, 4-methyl-2-quinazolinamine, and exhibited antiproliferative bioactivity. Streptomyces aureofaciens CMYAc130 isolated from Zingiber
officinale Rose by Taechowisan et al. (2005) reportedly produced antifungal and
antitumour compound 4-arylcoumarins (5,7-dimethoxy-4-p-methoxylphenylcoumarin (1), 5,7-dimethoxy-4-phenylcoumarin (2)). These compounds were
found to exhibit inhibitory effect on s.c. transplanted Lewis lung carcinoma
(LLC) BDF-1 mice by intraperitoneal administration. The T/C value of
5,7-dimethoxy-4-phenylcoumarin was found to be 80.8 and 50.0 % at the doses
of 1 and 10 mg kg 1. These two antitumor compounds exhibited low toxicity in
human cell lines and are potentially active in malignant cell lines, Streptomyces
sp. A35-1 (NRRL 30566) isolated from Grevillea pteridifolia by Castillo
et al. (2003) produced broad-spectrum antibiotic kakadumycins. This quinoxaline
compound-related antibiotic was found to be more effective against plant pathogenic fungi including Botrytis sp., Alternaria sp., Helminthosporium sp., and
Pythium ultimum. They were found to be potentially active against various drugresistant pathogenic bacteria and inhibitory against malaria parasite Plasmodium
falciparum with an IC50 of 4.5 ng ml 1.
Castillo et al. (2002) isolated Streptomyces NRRL 30562 from Kennedia
nigricans which reportedly produced broad-spectrum active munumbicins A,
B, C, and D. These all were highly active against Bacillus anthracis, multidrugresistant Mycobacterium tuberculosis, methicillin-resistant Staphylococcus aureus,
and plant pathogenic fungal pathogens.
A novel actinomycete strain, designated YIM 61105T, was isolated from a leaf
of Maytenus austroyunnanensis from the tropical rain forest in Xishuangbanna,
Yunnan Province, southwest China, by Qin et al. (2009b). A 16S rRNA gene
sequence analysis revealed that the organism belonged to the phylogenetic cluster
of the genus Nonomuraea and was most closely related to Nonomuraea candida
HMC10T (98.2 %), Nonomuraea aegyptia S136 (97.9 %), Nonomuraea kuesteri
GW 14-1925T (97.5 %), and Nonomuraea turkmeniaca DSM 43926T (97.4 %).
The 16S rRNA gene sequence similarities to other Nonomuraea species were less
than 97.4 %. The main chemotaxonomic properties of strain YIM 61105T, such as
the principal amino acid of the peptidoglycan, the predominant menaquinone, and
the polar lipid profile, supported its classification within the genus Nonomuraea.
Strain YIM 61105T was also readily differentiated from closely related species on
the basis of a broad range of phenotypic properties and DNA–DNA hybridization
values. Thus, this isolate was considered to represent a novel species of the genus
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Nonomuraea, for which the name Nonomuraea antimicrobica sp. nov. was
proposed.
Endophytic Actinobacteria are relatively unexplored as potential sources of
novel species and novel natural products for medical and commercial exploitation.
Xishuangbanna is recognized throughout the world for its diverse flora, especially
the rain forest plants, many of which have indigenous pharmaceutical histories.
However, little is known about the endophytic Actinobacteria of this tropical area.
In a study carried out by Qin et al. (2009a), they studied the diversity of
Actinobacteria isolated from medicinal plants collected from tropical rain forests
in Xishuangbanna. By the use of different selective isolation media and methods, a
total of 2,174 Actinobacteria were isolated. Forty-six isolates were selected on the
basis of their morphologies on different media and were further characterized by
16S rRNA gene sequencing. The results showed an unexpected level of diversity,
with 32 different genera. This was the first report describing the isolation of
Saccharopolyspora, Dietzia, Blastococcus, Dactylosporangium, Promicromonospora, Oerskovia, Actinocorallia, and Jiangella species from endophytic
environments. At least 19 isolates are considered novel taxa. In addition, all 46 isolates were tested for antimicrobial activity and were screened for the presence of
genes encoding polyketide synthetases and nonribosomal peptide synthetases. The
results confirmed that the medicinal plants of Xishuangbanna represent an
extremely rich reservoir for the isolation of a significant diversity of Actinobacteria,
including novel species, which are potential sources for the discovery of biologically active compounds.
17.5
Future Prospectives
Endophytes, found ubiquitous in all plant species in the world, contribute to their
host plants by producing plenty of substances that provide protection and ultimately
survival value to the plant. Many researches have proven that endophyte is a new
and potential source of novel natural products for exploitation in modern medicine,
agriculture, and industry. So far, a great number of novel natural products
possessing antimicrobial, antioxidant, immunosuppressant, and anticancer activities have been isolated from endophytes. It is believed that screening for bioactive
compounds from endophytes is a promising way to overcome the increasing threat
of drug-resistant strains of human and plant pathogen. The bioactive substances
isolated from endophytes belong to diverse structural classes, including alkaloids,
peptides, steroids, terpenoids, phenols, quinones, and flavonoids. These achievements would provide the opportunity to utilize endophytes as a new source for
production of new drugs from the medicinal plants globally.
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17.6
P. Jain and R.K. Pundir
Conclusions
Endophytes are ubiquitous with rich biodiversity, which have been found in every
plant species estimated to date. In this view of the special colonization in certain
hosts, it is estimated that there may be as many as one million different endophyte
species. However, only a handful of them have been described, which means that
the opportunity to find new and targeting natural products from interesting endophytic microorganisms among myriads of plants in different niches and ecosystem
is great. Some of the endophytes are the chemical synthesizers inside the plants. It is
noteworthy that, of the nearly 300,000 plant species that exist, each individual plant
is host to one or more endophytes. Only a few of these plants have been completely
studied for their endophytic biology. Accordingly, an opportunity to find new and
beneficial endophytic microorganisms among the diversity of plants in different
ecosystems is considerable. Currently, endophytes looked upon as a prominent
source of bioactive natural products. It appears that these biotypical factors can
be important in plant selection, since they may govern the novelty and biological
activity of the products associated with endophytic microbes. Research on endophytes is burgeoning immense importance since recent years with almost all plants
harboring untold number of microorganisms as endophytes. Endophytic plethoras
are reported to secrete unique novel metabolites bearing therapeutic properties
which are being constantly exploited. The emergence of antibiotic-resistant microorganisms calls for inventive research and development strategies. Inhibition of
these pathogenic microorganisms may be a promising therapeutic approach. The
screening of antimicrobial compounds from endophytes is a promising way to meet
the increasing threat of drug-resistant strains of human and plant pathogens.
Acknowledgement The authors are grateful to Prof. Ajit Verma, Pro-Vice-Chancellor, Amity
University, Noida for giving this opportunity to write the chapter on endophytes. The authors are
also grateful to Dr. Dinesh Kumar, Director, UIET, Kurukshetra University, Kurukshetra for
giving infrastructural facilities for carrying out research on endophytes. The authors are also
grateful to the Department of Science and Technology, Government of India, for providing
financial support for carrying out research activities on endophytes.
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mkumar9@amity.edu
Chapter 18
Molecular Approach to Study Soil Bacterial
Diversity
Satwant Kaur Gosal and Amita Mehta
18.1
Introduction
The biosphere is dominated by microorganisms which sustain 4–6 1030 prokaryotic cells (Whitman et al. 1998). The large number of microorganisms is an
essential component of the earth’s biota which represents unexplored reservoir of
genetic diversity. The microorganisms present in soil represent bacteria, fungi,
actinomycetes, protozoans, and viruses. These microorganisms play key role in
maintaining biogeochemical cycles, soil structure formation, decomposition of
organic matter, and the microbiological characteristics of soils and act as indicator
of soil health because of the relationship between microbial diversity, soil and plant
quality, and ecosystem sustainability. The information theory defines diversity as
the amount and distribution of information in an assemblage of community
(Torsvik et al. 1998). In other words, microbial diversity refers to biological
diversity within species, species number, and community diversity (Harpole
2010). Diversities at different levels of resolution have been distinguished as α, β,
and γ-diversity, where α-diversity represents diversity within a local habitat,
β-diversity represents the changes of species composition along a gradient, and
γ-diversity represents microbial diversity over a region comprising many different
habitats. Diversity index provides us a measure of overall diversity in the biological
systems. Primary indices give the numbers of taxa in a community, whereas
secondary or composite indices are based on two components, i.e., richness and
evenness. The richness component describes the number of taxa in a community
and the evenness component describes how evenly distributed the individuals are
among the taxa.
As soil bacteria are responsible for the majority of biogeochemical processes in
soil, the assessment of soil microbial community structure and function through the
S.K. Gosal (*) • A. Mehta
Department of Microbiology, Punjab Agriculture University, Ludhiana, Punjab 141004, India
e-mail: skgosal@rediffmail.com; amita_mehta27@yahoo.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_18
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S.K. Gosal and A. Mehta
analysis of DNA/RNA molecules extracted from soil is of fundamental importance
so as to understand the soil environment as an ecological system. The culturable
bacteria represent a minor fraction of the total bacterial population (Giovannoni
et al. 1990). So, the work on both the culturable as well as the non-culturable
bacteria from different environments needs to be continued. The lack of adequate
knowledge about the extant and extinct bacteria is another reason for the study of
microbial diversity. Our knowledge of diversity existing within natural microbial
communities is partially limited by the inability to study microorganisms as a very
low percentage of bacteria can be cultured by standard laboratory methods (Kirk
et al. 2004). Bacteria can exchange and acquire genes from distantly related
organisms by horizontal gene transfer (HGT), consequently increasing rates of
speciation. There is no consensus on how many species exist in the world, the
potential usefulness of most of them, or the rate at which they are disappearing or
emerging. The capability of an ecosystem to resist extreme perturbations or stress
conditions can be dependent on the diversity that exists within the system. Diversity
analyses are important in order to:
•
•
•
•
Comprehend the distribution of organisms and the diversity of genetic resources
Increase the knowledge of the functional role of diversity
Identify differences in diversity associated with management disturbing
Infer the regulation of biodiversity
As indicated, the cultivation-dependent methods will only reveal information
about the soil bacteria that are able to grow under the conditions used. Direct
microscopic studies circumvent the biases of culturing and provide a more accurate
measure of the microbial diversity in soil, in terms of the numbers of organisms
present. Due to the non-culturability of the major fraction of bacteria from natural
microbial communities, the overall structure of the community has been difficult to
interpret (Dokić et al. 2010). Moreover, the information contained in the nucleic
acids can be used to address diversity at different levels from the community to
within species level. The information contained in nucleic acids can be used to
address diversity at different levels. The molecular-phylogenetic perspective is a
reference framework within which microbial diversity is described; the sequences
of genes can be used to identify organisms (Amann et al. 1995). The collection of
all genomes of bacteria in a soil sample can be considered to represent one large soil
microbial community genome, a microbial “metagenome.” The genomes of the
organisms in a soil community contain all information about the diversity in that
community. Recent improvements in techniques that allow us to survey the diversity of microbial communities have revolutionized in our understanding of microbial diversity. For many decades, microbiologists had grossly underestimated
microbial diversity levels by relying on cultivation-based techniques, which capture
only a few microbial taxa, which could grow under artificial laboratory conditions
(Pace 1997; Rappé and Giovannoni 2003). With few obvious morphological differences delineating most microbial taxa, direct microscopic analyses of environmental samples are of little use for quantifying microbial diversity (Fierer and
Lennon 2011). The use of high-throughput nucleic-acid-based analyses of
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Molecular Approach to Study Soil Bacterial Diversity
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microbial communities enables researchers to study the dynamics of microbial
diversity in specific habitats, the spatial and temporal variability in the levels of
microbial diversity, and the factors driving this variability (Christen 2008; Hamady
and Knight 2009; Hirsch et al. 2010).
18.2
Factors Governing Microbial Diversity
Ecologists have been busy in describing and systemizing the biodiversity on Earth.
Despite best efforts, we still lack sturdy estimates of species richness for the
majority of taxa present in the ecosystems. It is often challenging to determine
the factors that affect the patterns of species diversity in time and space (Pennisi
2005). Many different organisms may perform the same processes and probably be
found in the same niches in a bacterial community (Zhao et al. 2012). The factors
affecting microbial diversity can be classified into two groups, i.e., abiotic factors
and biotic factors. Abiotic factors include both physical and chemical factors such
as soil texture, salinity, oxic/anoxic conditions, temperature, pH, pressure, available
NPK, heavy metals, pesticides, antibiotics, and water availability (Bååth
et al. 1998). Ammoniacal and nitrate nitrogen contents of soils are important factors
which influence the diazotrophic count (Gosal et al. 2011). In general, all environmental variations affect bacteria in different ways and to different extent, resulting
in a shift in the diversity profile. Biotic factors include plasmids, phages, and
transposons that are types of accessory DNA that influence the genetic properties
and, in most cases, the phenotypes of their host and, thus, have a great influence on
microbial diversity (Zhao et al. 2012).
Furthermore, many basic questions remain unanswered, including why some
habitats have more species than other habitats, and what are the abiotic, biotic,
ecological, and evolutionary forces that determine how many species can be found
in a given set of environmental conditions? This is particularly true for many
microbial taxa as we often lack even a rudimentary understanding of their diversity
patterns.
The vast majority of bacterial communities in nature have not been cultured in
the laboratory. Therefore, the primary source of information for these uncultured
but viable organisms is their biomolecules such as nucleic acids, lipids, and proteins. Culture-independent nucleic acid approaches include analyses of whole
genomes or selected genes such as 16S and 18S ribosomal RNA (rRNA) for
prokaryotes and eukaryotes, respectively. Based on the comparative analyses of
these rRNA signatures, cellular life has been classified into three primary domains:
one eukaryotic (Eukarya) and two prokaryotic (Bacteria and Archaea) (Hugenholtz
2002). Over the last few decades, microbial ecology has seen tremendous progress,
and a wide variety of molecular techniques have been developed for describing and
characterizing the phylogenetic and functional diversity of microorganisms.
Broadly, these techniques have been classified into two major categories depending
on their capability of revealing the microbial diversity structure and function:
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S.K. Gosal and A. Mehta
(1) partial community analysis methods and (2) whole community analysis
methods.
Partial community analysis methods generally include polymerase chain reaction (PCR)-based methods where total DNA/RNA extracted from an environmental
sample is used as a template for the characterization of microorganisms. The PCR
product thus generated reflects a mixture of bacterial gene signatures from all
organisms present in a sample, including the VBNC fraction. PCR amplification
of conserved genes such as 16S rRNA from an environmental sample has been used
extensively in bacterial ecology primarily because these genes (1) are ubiquitous,
i.e., present in all prokaryotes, (2) are structurally and functionally conserved, and
(3) contain variable and highly conserved regions (Hugenholtz 2002). Sequence
analysis of 16S rRNA genes is commonly used in most microbial ecological
surveys. However, being a highly conserved molecule, the 16S rRNA gene does
not provide sufficient resolution at species and strain level (Konstantinidis
et al. 2006). The libraries of PCR-amplified 16S rRNA genes do not always
represent complete picture of bacterial community (Dokić et al. 2010). The whole
community analysis offers a more comprehensive view of genetic, metabolic, and
phylogenetic diversity stored in soil metagenome as compared to PCR-based
molecular approaches that target only a single or few genes. These techniques
attempt to analyze all the genetic information present in total DNA extracted from a
soil sample.
18.3
Genetic Fingerprinting Techniques
Genetic fingerprinting generates a profile of microbial communities based on direct
analysis of PCR products amplified from environmental DNA (Muyzer 1999).
These techniques include DGGE/TTGE, SSCP, RAPD, ARDRA, T-RFLP,
LH-PCR, RISA, and RAPD and produce a community fingerprint based on either
sequence polymorphism or length polymorphism. In general, genetic fingerprinting
techniques are rapid and allow simultaneous analyses of multiple samples. Fingerprinting approaches have been devised to demonstrate an effect on bacterial
communities or differences between microbial communities and do not provide
direct taxonomic identities. The “fingerprints” from different samples are compared
using computer assisted cluster analysis by software packages such as GelCompar,
and community relationships are inferred. Community fingerprints are scored as
present or absent, and the similarities among samples are determined using
Jaccards’ coefficient.
The general principle of most molecular techniques relies on the electrophoretic
separation of a pool of PCR products amplified from DNA or RNA directly
extracted from soil. The difference in the sequences of amplified gene can be
used for separation based on:
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Molecular Approach to Study Soil Bacterial Diversity
363
• Different melting behavior of the double-stranded PCR products due to differences in the primary structures of the target gene fragments using denaturing
gradient gel electrophoresis or temperature gradient gel electrophoresis
• Different localization of restriction endonuclease digestion sites along the investigated gene using terminal restriction length polymorphism, restriction fragment length polymorphism, or amplified ribosomal DNA restriction analysis
• Different electrophoretic mobilities of single DNA strands in non-denaturing
gels using single strand conformational polymorphism analysis
• Length polymorphism of entire gene fragments using length heterogeneity PCR
or ribosomal intergenic spacer analysis
18.4
Assessment of Soil Microbial Diversity Using
Molecular Methods
The assessment of soil microbial diversity can be divided into three categories
(Fig. 18.1) such as:
Fig. 18.1 Different methods for assessing bacterial diversity
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S.K. Gosal and A. Mehta
1. Broad scale low resolution methods
2. Intermediate resolution methods
3. High resolution methods
18.4.1 Broad Scale, Low Resolution Methods
These include methods based on nucleic acids or some biochemical markers (fatty
acids) as DNA reassociation or PLFA and LPS, respectively.
DNA Reassociation: In this method, total DNA is extracted from environmental
samples, purified, denatured, and allowed to reanneal. DNA extracted from a microbial community is a mixture of DNA from different microbial taxa that are present in
different proportions. The rate of hybridization or reassociation will depend on the
similarity of sequences present. As the complexity or diversity of DNA sequences
increases, the rate at which DNA reassociates will decrease (Theron and Cloete
2000). In other words, the kinetics of DNA reassociation in a sample reflects the
variety of sequences present in the environment, thus reflecting the diversity of the
microbial community of that environment. DNA reassociation estimates diversity by
measuring the genetic complexity of the microbial community (Torsvik et al. 1996).
The DNA reassociation rate can be used to calculate the genome size or genome
complexity. The parameter controlling the reassociation reaction is concentration of
DNA product (Co) and time of incubation (t), usually described as the half association value, Cot1/2 (the time needed for half of the DNA to reassociate). Under
specific conditions, Cot1/2 can be used as a diversity index, as it takes into account
both the amount and distribution of DNA re-association (Torsvik et al. 1998). Alternatively, the similarity between communities of two different samples can be studied
by measuring the degree of similarity of DNA through hybridization kinetics
(Griffiths et al. 1999). The community diversity comprises of the total amount of
genetic information in the community (richness) and the distribution of this information among the different genetic types (evenness). Thus, the DNA reassociation
method provides an estimate of the extent of diversity in prokaryotic communities.
G + C content: The diversity in soil bacterial communities can be assessed by
studying the difference in guanine + cytosine content of DNA (Nüsslein and Tiedje
1999). Different groups of microorganisms differ in their G + C content and the
taxonomically related groups of microorganisms differ by 3–5 % in their G + C
content. The technique provides us with a fractionated profile of entire community
that indicates relative abundance of DNA as a function of G + C content. The total
DNA is separated into different fractions which can be analyzed by additional
molecular techniques as DGGE and ARDRA to assess total community diversity.
The technique is advantageous as it includes all the DNA extracted from soil but
requires large amount of DNA, i.e., 50 μg (Tiedje et al. 1999).
Phospholipid Fatty Acid (PLFA) Analysis: PLFA analysis has been used as a
culture-independent method for assessing the structure of soil microbial communities. PLFAs are important components of cell membranes and potentially useful
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signature molecules. They constitute a significant proportion of organism biomass
under natural conditions (Kozdroj and van Elsas 2001). Phospholipids are found
exclusively in microbial cell membranes and not in other parts of the cell as storage
products. Cell membranes, consisting of phospholipids, are rapidly degraded following cell death. Consequently, phospholipids can serve as important indicators of
active microbial biomass as opposed to nonliving microbial biomass (Drenovsky
et al. 2004). An essential consideration in the use of PLFA molecules to describe
microbial communities is that unique fatty acids are indicative of specific groups of
organisms. The changes in PLFA patterns under environmental stress conditions
are useful biomarker tool to describe the community and physiological state of
certain microbial taxa (Misko and Germida 2002). Our knowledge of such signature
molecules comes from the use of fatty acid analysis for bacterial taxonomy, in
which specific fatty acid methyl esters (FAMEs) have been used as an accepted
taxonomic discriminator for species identification. Furthermore, PLFAs are easily
extracted from microbial cells in soil (Tunlid and White 1992; Zelles and Bai
1993), allowing access to a greater proportion of the microbial community resident
in soil than would otherwise be accessed during culture-dependent methods of
analysis. Although direct extraction of PLFA from soil does not permit delineation
down to species level, it is an efficient means by which gross changes in microbial
community structure can be profiled (Nannipieri et al. 2003). The method allows
the direct analysis of soil samples suitable to monitor changes in microbial community composition and can be used to assess specific microbial groups by measuring signature fatty acids. Despite the usefulness of this method, there are some
important limitations (Haack et al. 1994).
Limitations
1. Appropriate signature molecules are not known for all organisms in a soil
sample and, in a number of cases, a specific fatty acid present in a soil sample
cannot be linked with a specific microorganisms or group of microorganisms. In
general, the method cannot be used to characterize microorganisms to species.
2. Since the method relies heavily on signature fatty acids to determine gross
community structure, any variation in these signatures would give rise to false
community estimates created by artifacts in the methods.
3. Bacteria produce widely different amounts of PLFA and the types of fatty acids
vary with growth conditions and environmental stresses. Although signature
PLFAs can be correlated with the presence of some groups of organisms, they
may not necessarily be unique to only those groups under all conditions.
Consequently, this could give rise to false community signatures.
18.4.2 Intermediate Resolution Methods
Clone library and community finger printing techniques based on differences in
conserved genes like rRNA gene are considered as intermediate resolution
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methods. The 16S rRNA gene can be amplified from community DNA extracted
from soil, cloned, and sequenced to determine genetic diversity within microbial
community. They can be separated based on length, restriction pattern, or denaturing conformational properties. Hybridization using phylogenetic probes offers the
possibility to perform specific in situ measurements. The probes are used to target
specific rDNA sequences in community DNA or to probe colonies or single cells.
Whole cell fluorescence hybridization or fluorescence in situ hybridization (FISH)
using phylogenetic probes in combination with fluorescence microscope allows the
simultaneous detection and quantification of single cells of different phylogenetic
groups in same sample.
Clone Library Method: The most widely used method to analyze PCR products
amplified from an environmental sample is to clone and then sequence the individual gene fragments (DeSantis et al. 2007). Sequencing of the clone library generated from environmental DNA has advantages over fingerprint-based methods,
such as denaturing gradient gel electrophoresis, as it provides precise identification
and quantification of the phylotypes present in samples (Hur and Chun 2004). The
sequences are compared to known sequences in a database such as GenBank,
Ribosomal Database Project (RDP), and Greengenes. Cloned sequences are
assigned to phylum, class, order, family, subfamily, or species at sequence similarity cutoff values of 80, 85, 90, 92, 94, or 97 %, respectively (Rastogi et al. 2010).
While clone libraries of 16S rRNA genes permit an initial survey of diversity and
identify novel taxa, studies have shown that environmental samples like soil may
require over 40,000 clones to document 50 % of the richness (Dunbar et al. 2002).
However, typical clone libraries of 16S rRNA genes contain fewer than 1,000
sequences and therefore reveal only a small portion of the microbial diversity
present in a sample. A cloning and sequencing method was used to decipher the
microbial community composition in mining-impacted deep subsurface soils of the
former Homestake gold mine of South Dakota, USA (Rastogi et al. 2009). Phylogenetic analysis of 230 clone sequences could reveal only a partial view of
phylogenetic breadth present in soil samples. Rarefaction analyses of clone libraries
generated non-asymptotic plots, which indicated that diversity was not exhaustively
sampled due to insufficient clone sequencing, a common problem when assessing
environmental microbial diversity using cloning approaches. Despite its limitations
(e.g., labor-intensive, time-consuming, and cost factor), clone libraries are still
considered the “gold standard” for preliminary microbial diversity surveys
(DeSantis et al. 2007). With the advent of newer and inexpensive sequencing
methods, great progress is expected in this method of microbial diversity analysis.
Denaturant Gradient Gel Electrophoresis (DGGE)/Temperature Gradient Gel
Electrophoresis (TGGE): In denaturing gradient gel electrophoresis, DNA is
extracted from environmental samples and amplified using primers for specific
molecular markers such as 16S rRNA sequences. The PCR products are
electrophoresed on a polyacrylamide gel containing a linear gradient of DNA
denaturant such as a mixture of urea and formamide (Muyzer et al. 1993). Temperature gradient gel electrophoresis uses the same principle as DGGE except that a
temperature gradient is provided rather than using chemical denaturants. DNA
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fragments of same length but with different base pair sequences can be separated
using DGGE or TGGE. The separation of different DNA molecules is based on the
difference in mobility of partially melted DNA molecules in polyacrylamide gels
which have a gradient of DNA denaturants. The DNA fragments will migrate
according to their melting behavior under different denaturing conditions as chemical denaturants or temperature. The variation in sequences within the DNA fragments causes a difference in melting behavior and therefore amplicons or DNA
fragments with different sequences stop migrating at different positions in the gel.
The melting of the products occurs in different melting domains, which are
stretches of nucleotides with identical melting temperatures (Mühling
et al. 2008). In a linearly increasing denaturing gradient, DNA fragments migrating
under the influence of an electric current remain double-stranded until they reach
the denaturing conditions that cause melting of their lower temperature melting
domains. As a result of this melting branching of the molecules occurs, which
results in decreased mobility of molecules in the gel. The electrophoresis of mixed
amplicons from a complex community results in fingerprinting consisting of bands
at different migration distances in the gel. Both DGGE and TTGE involve the use of
a GC clamped (30–50 nucleotides) forward primer during the PCR step. This is
essential to prevent the two DNA strands from complete dissociation into single
strands during electrophoresis. DNA sequences having a difference in only one
base pair can be separated by DGGE (Miller et al. 1999). The DGGE/TGGE
fingerprints are reliable, reproducible, rapid, and less expensive. They can be
used to determine the phylogenetic identities by reamplification of the bands
excised from the gel and blotting them onto nylon membranes and hybridizing
them to molecular probes specific for different taxonomic groups. DGGE profiles
have successfully been used to determine the genetic diversity of microbial communities inhabiting different temperature regions in a microbial community (Ferris
et al. 1996), and to study the distribution of sulfate reducing bacteria in a stratified
water column (Teske et al. 1996).
Despite certain advantages, the DGGE/TGGE holds some limitations as PCR
biases (Wintzingerode et al. 1997), laborious sample handling (Muyzer 1999), and
variable DNA extraction efficiency (Theron and Cloete 2000). DGGE can only
detect 1–2 % of the microbial population representing dominant species present in
an environmental sample (MacNaughton et al. 1996). DNA fragments of different
sequences may have similar mobility characteristics in the polyacrylamide gel.
Therefore, one band may not necessarily represent one species (Gelsomino
et al. 1999) and one bacterial species may also give rise to multiple bands because
of multiple 16S rRNA genes with slightly different sequences (Maarit-Niemi
et al. 2001). DGGE/TGGE analysis of microbial communities produces a complex
profile which can be quite sensitive to spatial and temporal sampling variation
(Murray et al. 1998).
Terminal Restriction Fragment Length Polymorphism (T-RFLP): T-RFLP is an
extension of RFLP/ARDRA analysis which provides an alternate method for rapid
analysis of bacterial community diversity in various environments. It is based on
the same principle as RFLP except that one PCR primer is labeled with a fluorescent
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dye, such as TET (4,7,20 ,70 -tetrachloro-6-carboxyfluorescein) or 6-FAM (phosphoramiditefluorochrome 5-carboxyfluorescein) during the PCR reaction. The PCR
products are digested with restriction enzyme(s), and the fluorescently labeled
terminal restriction fragments (T-RFs) are separated on an automated DNA
sequencer (Thies 2007). The size, number, and peak height of T-RFs are used to
estimate community diversity. Each unique fragment length can be counted as an
Operational Taxonomic Unit (OTU) or ribotype and the frequency of each OTU can
be calculated. The banding pattern can be used to measure species richness and
evenness as well as similarities between samples (Liu et al. 1997). The technique
helps in the analysis of complex bacterial communities as only fluorescently labeled
terminal fragments are detected, thus simplifying the banding pattern (Marsh 1999).
T-RFLP has also been thought to be an excellent tool to compare the relationship
between different samples (Dunbar et al. 2000). T-RFLP has been used to measure
spatial and temporal changes in bacterial communities (Lukow et al. 2000), to study
complex bacterial communities (Moeseneder et al. 1999), and to detect and monitor
populations (Tiedje et al. 1999). The recent developments in bioinformatics have
provided us with several web-based programs to analyze T-RFLP patterns, which
enable us to rapidly assign putative identities based on a database of fragments
produced by known 16S rDNA sequences.
Despite the usefulness of T-RFLP in bacterial diversity analysis, it has some
limitations. T-RFLP may underestimate true diversity as only numerically dominant species are detected due to large quantity of available DNA (Liu et al. 1997).
Another limitation of T-RFLP is the choice of the universal primers. None of the
presently available universal primers can amplify all sequences from eukaryote,
bacterial, and archaeal domains. These primers are based on existing 16S rRNA,
18S rRNA, or Internal Transcribed Spacer (ITS) databases, which until recently
contained mainly sequences from culturable microorganisms, and therefore may
not be representative of the true bacterial diversity in a sample (Rudi et al. 2007).
Different enzymes will produce different community fingerprints (Dunbar
et al. 2000). The method underestimates community diversity because only a
limited number of bands per gel (generally <100) can be resolved, and different
bacterial species can share the same T-RF length. However, the method does
provide a robust index of community diversity, and T-RFLP results are generally
very well correlated with the results from clone libraries (Fierer and Jackson 2006).
18.4.2.1
Procedure for RFLP Analysis
Reagents
1. Lambda DNA (Hind III digest)
2. 100 bp ladder
3. 5 TBE buffer: 54 g Tris base, 20 ml of 0.5 M EDTA, pH 8.0, and 27.5 g of
boric acid dissolved in 1 l of water
4. Ethidium bromide (5 mg ml 1)
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5. Loading dye (6) (0.25 % Bromophenol blue in 40 % sucrose w/v)
6. Restriction endonucleases (Alu 1, BsuR 1, Msp 1, and Rsa 1) along with the
buffer (10)
Procedure
1. The reaction mixture for restriction analysis should be prepared as follows:
PCR product
Restriction endonuclease (3U)
Recommended buffer (for restriction enzyme)
Total volume
12.3 μL
0.3 μL
1.4 μL
14.0 μL
2. Keep the tubes in water bath maintained at 37 C FOR 2 h.
3. Analyze the restricted DNA by horizontal electrophoresis in 3 % agarose gel.
Carry out the electrophoresis at 100 V for 2 h. 30 min with the standard gels
(11 14 cm).
4. Visualize the gels under UV and record the observations.
Single Strand Conformation Polymorphism (SSCP): SSCP also relies on electrophoretic separation based on differences in DNA sequences and allows differentiation of DNA molecules having the same length but different nucleotide
sequences. This technique was originally developed to detect known or novel
polymorphisms or point mutations in DNA (Peters et al. 2000). In SSCP, the
environmental PCR products are denatured followed by electrophoretic separation
of single-stranded DNA fragments on a nondenaturing polyacrylamide gel
(Schwieger and Tebbe 1998). As formation of folded secondary structure or
heteroduplex and hence mobility are dependent on the DNA sequences, this method
reproduces an insight of the genetic diversity in a bacterial community. All the
limitations of DGGE are also equally applicable for SSCP. Again, some singlestranded DNA can exist in more than one stable conformation. As a result, same
DNA sequence can produce multiple bands on the gel (Tiedje et al. 1999). However, it does not require a GC clamp or the construction of gradient gels and has
been used to study bacterial or fungal community diversity (Stach et al. 2001).
Similar to DGGE, the DNA bands can be excised from the gel, reamplified, and
sequenced. However, SSCP is well suited only for small fragments (between
150 and 400 bp) (Muyzer 1999). A major limitation of the SSCP method is the
high rate of reannealing of DNA strands after an initial denaturation during
electrophoresis, which can be overcome using a phosphorylated primer during
PCR, followed by specific digestion of the phosphorylated strand with lambda
exonuclease. SSCP has been used to measure succession of bacterial communities
(Peters et al. 2000), rhizosphere communities (Schmalenberger et al. 2001), bacterial population changes in an anaerobic bioreactor (Zumstein et al. 2000), and AMF
species in roots (Kjoller and Rosendahl 2000).
Random-Amplified Polymorphic DNA Fingerprinting: Random-amplified polymorphic DNA (RAPD) and DNA amplification fingerprinting (DAF) techniques
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utilize PCR amplification with a short (usually ten nucleotides) primer, which
anneals randomly at multiple sites on the genomic DNA under low annealing
temperature, typically £35 C (Franklin et al. 1999). These methods generate
PCR amplicons of various lengths in a single reaction that are separated on agarose
or polyacrylamide gel depending on the genetic complexity of the bacterial communities. Because of the high speed and ease of use, RAPD/DAF has been used
extensively in fingerprinting overall bacterial community structure and closely
related bacterial species and strains (Franklin et al. 1999). Both RAPD and DAF
are highly sensitive to experimental conditions (e.g., annealing temperature, MgCl2
concentration) and quality and quantity of template DNA and primers. Thus,
several primers and reaction conditions need to be evaluated to compare the
relatedness between bacterial communities and obtain the most discriminating
patterns between species or strains. A RAPD profiling study was used with 14 random primers to assess changes in bacterial diversity in soil samples that were
treated with pesticides (triazolone) and chemical fertilizers (ammonium bicarbonate) (Yang et al. 2000). RAPD fragment richness data demonstrated that pesticidetreated soil maintained an almost identical level of diversity at the DNA level as the
control soil (i.e., without contamination). In contrast, chemical fertilizer caused a
decrease in the DNA diversity compared to control soil.
Amplified Ribosomal DNA Restriction Analysis: Amplified ribosomal DNA
restriction analysis (ARDRA) is based on DNA sequence variations present in
PCR-amplified 16S rRNA genes (Smit et al. 1997). The PCR product amplified
from environmental DNA is generally digested with tetracutter restriction endonucleases (e.g., AluI, HaeIII), and restricted fragments are resolved on agarose or
polyacrylamide gels (Liu et al. 1997). Divergence of a community rRNA restriction
pattern on a gel is highly influenced by the type of restriction enzyme used (Gich
et al. 2000). Although ARDRA provides little or no information about the type of
bacteria present in the sample, the method is still useful for rapid monitoring of
bacterial communities over time, or to compare bacterial diversity in response to
changing environmental conditions. ARDRA is also used for identifying the unique
clones and estimating OTUs in environmental clone libraries based on restriction
profiles of clones (Smit et al. 1997). The major limitation of ARDRA is that
restriction profiles generated from complex bacterial communities are sometimes
too difficult to resolve by agarose/PAGE (Kirk et al. 2004). Optimization is
required to produce fingerprinting profiles characteristic of the bacterial community
(Spiegelman et al. 2005). The ARDRA technique was applied for assessing the
effect of copper contamination on the bacterial communities in soil. Whole community ARDRA profiles showed a lower diversity in copper-contaminated soil
compared with control soil with no contamination (Smit et al. 1997).
Ribosomal Intergenic Spacer Analysis: RISA requires the extraction of genomic
DNA of the total bacterial population from the soil sample. The method involves
the PCR amplification of the selected DNA fragments with universal primers and
subsequent electrophoresis on a polyacrylamide gel. RISA profiles can be generated
from most of the dominant bacteria present in a sample by using primers for
conserved regions in the 16S and 23S rRNA genes. It is useful for differentiating
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Molecular Approach to Study Soil Bacterial Diversity
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between bacterial strains and closely related species because of heterogeneity of the
IGS length and sequence (Fisher and Triplett 1999). RISA provides a communityspecific profile, with each band corresponding to at least one organism in the
original community.
The RISA technique has been enhanced by the addition of an automated
component to the technique by using an automated genetic analyzer. The automated
ribosomal intergenic spacer analysis (ARISA) method is an effective, rapid, and
fairly inexpensive process that can be used to estimate the diversity and composition of bacterial communities without demonstrating a bias towards fast-growing or
dominant species. This is especially useful in ecological studies, where a large
number of samples need to be processed and diversity needs to be determined at a
spatial and temporal level. It involves use of a fluorescence-labeled *****forward
primer, and ISR fragments are detected automatically by a laser detector. ARISA
allows simultaneous analysis of many samples; however, the technique has been
shown to overestimate bacterial richness and diversity (Fisher and Triplett 1999).
Ranjard et al. (2001) evaluated ARISA to characterize the bacterial communities
from four types of soil differing in geographic origins, vegetation cover, and
physicochemical properties. ARISA profiles generated from these soils were distinct and contained several diagnostic peaks with respect to size and intensity. Their
results demonstrated that ARISA is a very effective and sensitive method for
detecting differences between complex bacterial communities at various spatial
scales (between- and within-site variability). Limitations of RISA include requirement of large quantities of DNA, relatively longer time requirement, insensitivity of
silver staining in some cases, and low resolution (Fisher and Triplett 1999). ARISA
has increased sensitivity than RISA and is less time consuming, but traditional
limitations of PCR also applies for ARISA (Fisher and Triplett 1999). RISA has
been used to compare bacterial diversity in soil (Borneman and Triplett 1997), in
the rhizosphere of plants (Borneman and Triplett 1997), in contaminated soil
(Ranjard et al. 2000), and in response to inoculation (Yu and Mohn 2001).
Length Heterogeneity (LH) PCR: LH-PCR analysis is similar to the commonly
used T-RFLP method. The difference between these two methods is that the
T-RFLP method identifies PCR fragment length variations based on restriction
site variability, whereas LH-PCR analysis distinguishes different organisms based
on natural variations in the length of 16S ribosomal DNA sequences (Ritchie
et al. 2000). LH-PCR differentiates microorganisms on the basis of natural length
polymorphisms which occur due to mutation within genes (Mills et al. 2007).
Amplicon LH-PCR interrogates the hypervariable regions present in 16S rRNA
genes and produces a characteristic profile. LH-PCR utilizes a fluorescent
dye-labeled forward primer, and a fluorescent standard is run with each sample to
measure the amplicon lengths in base pairs. The height or area under the peak in the
electropherogram is proportional to the relative abundance of that particular
amplicon. The advantage of using LH-PCR over the T-RFLP is that the former
does not require any restriction digestion and therefore PCR products can be
directly analyzed by a fluorescent detector. The limitations of LH-PCR technique
include inability to resolve complex amplicon peaks and underestimation of
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diversity, as phylogenetically distinct taxa may produce same-length amplicons
(Mills et al. 2007). LH-PCR was used in combination with FAME analysis to
investigate the bacterial communities in soil samples that differed in terms of
type and/or crop management practices (Ritchie et al. 2000). LH-PCR results
strongly correlated with FAME analysis and were highly reproducible and successfully discriminated different soil samples.
Fluorescence in situ Hybridization (FISH): FISH has been used for identification
and quantification of microorganisms within their natural habitat (Amann
et al. 1995; Kenzaka et al. 1998). Bacterial cells are hybridized with fluorescently
labeled taxon-specific oligonucleotide probes and the cells are viewed by scanning
confocal laser microscopy (Sanz and Kochling 2007). Hybridization with rRNAtargeted probes enhances the characterization of uncultured bacteria and also
facilitates the description of complex bacterial communities (Edgeomb
et al. 1999). The intensity of fluorescence is correlated to rRNA content of the
cells and their growth rate, thus, provides information regarding metabolic state of
the cells. FISH has certain advantages over immunofluorescence techniques as it
can detect bacteria at all phylogenetic levels and it is more sensitive as nonspecific
binding to soil does not take place (Amann et al. 1995). The fluorescing bacteria can
be differentiated from autofluorescing soil particles and plant debris by using
distinct florescent dyes (Macnaughton et al. 1996). For the analysis of mixed
bacterial populations, FISH can be combined with flow cytometry. FISH use does
not provide any insight to metabolic function of microorganisms. However, it can
be coupled with other techniques such as microautoradiography to describe functional properties of microorganisms in their natural environment (Wagner
et al. 2006). Many improvements have been made in FISH analysis to solve the
problems associated with it: Bright fluorochromes, hybridization with the probes
carrying multiple fluorochromes, treatment with chloramphenicol to increase the
RNA content of the cells (Rogers et al. 2007), or addition of nutrients to stimulate
bacterial activity (Hahn et al. 1992). The low signal intensity, target inaccessibility,
and background fluorescence are the common problems associated with FISH
analysis. The soil microorganisms should be in a metabolically active stage and
their cell wall should be permeable to allow the penetration of probes (Christensen
and Poulson 1994).
18.4.3 High Resolution Methods
The method with the highest level of resolution is based on sequencing of the entire
soil metagenome followed by careful analysis of the functional genes. Soil
metagenomic clone libraries can be used in combination with fingerprinting,
hybridization, and sequencing techniques to assess the diversity of particular genes.
Metagenomics: Nowadays, one of the most widely used strategies for studying
bacterial diversity is the metagenomic research. A metagenome is the entire genetic
composition of bacterial communities of soil which is based on direct isolation of
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total DNA in soil samples, construction of libraries, the amplification of 16S rRNA
genes and functional genes to study the total diversity, physiology, ecology, and
phylogeny of bacteria that cannot be cultivated in the laboratory (Lorenz and
Schleper 2002; Rondon et al. 2000; Voget et al. 2003; Steele and Streit 2005; Streit
and Schmitz 2004). Such investigations aim to reveal and understand the relationship between community composition and functional diversity in natural bacterial
ecosystems.
Metagenomics is the investigation of collective bacterial genomes retrieved
directly from environmental samples and does not rely on cultivation or prior
knowledge of the bacterial communities (Riesenfeld et al. 2004). It is also known
as environmental genomics or community genomics, or bacterial ecogenomics.
Metagenomic research is useful to exploit the unknown bacterial diversity in
different environments; it can be used to discover novel genes and to increase our
knowledge on bacterial ecology and physiology (Cowan et al. 2005). The 16S
rRNA gene accounts for a minor fraction of the average prokaryotic genome
(Rodrı́guez-Valera 2002) and 16S rRNA gene sequences have been used as a
phylogenetic marker to characterize uncultivated prokaryotes and can help to
discover metabolic functions, enhancing our knowledge about bacterial ecology
and phylogeny (Oremland et al. 2005; Riesenfeld et al. 2004; Tringe et al. 2005).
We can use metagenomic sequences to help understand how complex bacterial
communities function and how bacteria interact within these niches. Metagenomics
aims at identifying novel genes and increasing our understanding of bacterial
ecology.
Essentially, metagenomics does not include methods that interrogate only
PCR-amplified selected genes (e.g., genetic fingerprinting techniques) as they do
not provide information on genetic diversity beyond the genes that are being
amplified. In principle, metagenomic techniques are based on the concept that the
entire genetic composition of environmental bacterial communities could be
sequenced and analyzed in the same way as sequencing a whole genome of a
pure bacterial culture. Metagenomic investigations have been conducted in several
environments such as soil, the phyllosphere, the ocean, and acid mine drainage and
have provided access to phylogenetic and functional diversity of uncultured microorganisms (Handelsman 2004). Metagenomics is crucial for understanding the
biochemical roles of uncultured microorganisms and their interaction with other
biotic and abiotic factors. Environmental metagenomic libraries have proved to be
great resources for new bacterial enzymes and antibiotics with potential applications in biotechnology, medicine, and industry (Riesenfeld et al. 2004; Rondon
et al. 2000).
The construction of metagenomic library involves the following steps:
1. Isolation of total DNA from an environmental sample
2. Shotgun cloning of random DNA fragments into a suitable vector
3. Transforming the clones into a host bacterium and screening for positive clones
Metagenomic libraries containing small DNA fragments in the range of 2–3 kb
provide better coverage of the metagenome of an environment than those with
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larger fragments. It has been estimated that to retrieve the genomes from rare
members of bacterial communities, at least 1,011 genomic clones would be
required (Riesenfeld et al. 2004). Small-insert DNA libraries are also useful to
screen for phenotypes that are encoded by single genes and for reconstructing the
metagenomes for genotypic analysis. Large-fragment metagenomic libraries (100–
200 kb) are desirable while investigating multigene biochemical pathways.
Metagenomic libraries could be screened either by sequence-driven metagenomic
analysis that involves massive high-throughput sequencing or by functional screening of expressed phenotypes. Sequence-driven massive whole-genome
metagenomic sequencing sheds light on many important genomic features such as
redundancy of functions in a community, genomic organizations, and traits that are
acquired from distinctly related taxa through HGTs (Handelsman 2004). In
function-driven metagenomic analysis (functional metagenomics), libraries are
screened based on the expression of a selected phenotype on a specific medium.
DNA microarrays: DNA microarrays have been used primarily to provide a
high-throughput and comprehensive view of bacterial communities in environmental samples. The PCR products amplified from total environmental DNA is directly
hybridized to known molecular probes, which are attached on the microarrays
(Gentry et al. 2006). After the fluorescently labeled PCR amplicons are hybridized
to the probes, positive signals are scored by the use of confocal laser scanning
microscopy. The microarray technique allows samples to be rapidly evaluated with
replication, which is a significant advantage in bacterial community analyses. In
general, the hybridization signal intensity on microarrays is directly proportional to
the abundance of the target organism. DNA microarrays used in bacterial ecology
could be classified into two major categories depending on the probes as 16S rRNA
gene microarrays and functional gene arrays (FGA). 16S rRNA gene Microarrays
(PhyloChip) contain 30,000 probes of 16S rRNA gene targeted to several cultured
bacterial species and “candidate divisions” (DeSantis et al. 2007). PhyloChip
technology has been used for rapid profiling of environmental bacterial communities during bioterrorism surveillance, bioremediation, climate change, and source
tracking of pathogen contamination (Brodie et al. 2007; DeSantis et al. 2007).
PhyloChips had been used to investigate the indigenous soil bacterial communities
in two abandoned uranium mine sites, the Edgemont and the North Cave Hills in
South Dakota (Rastogi et al. 2010). PhyloChip analysis revealed greater diversity
than corresponding clone libraries at each taxonomic level and indicated the
existence of 1,300–1,700 bacterial species in uranium mine soil samples. Most of
these species were members of the phylum Proteobacteria and contained lineages
that were capable of performing uranium immobilization and metal reduction. FGA
are used to detect specific metabolic groups of bacteria. FGA contains more than
24,000 probes from all known metabolic genes involved in ammonia oxidation and
nitrogen fixation (He et al. 2007).
DNA–DNA hybridization has been used together with DNA microarrays to
detect and identify bacterial species (Cho and Tiedje 2001) or to assess bacterial
diversity (Greene and Voordouw 2003). This tool could be valuable in bacterial
diversity studies since a single array can contain thousands of DNA sequences
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(DeSantis et al. 2007) with high specificity. Specific target genes coding for
enzymes such as nitrogenase, nitrate reductase, and naphthalene dioxygenase can
be used in microarray to elucidate functional diversity information of a community.
Sample of environmental “standards” (DNA fragments with less than 70 % hybridization) representing different species likely to be found in any environment can
also be used in microarray (Greene and Voordouw 2003).
Another DNA microarray-based technique for analyzing bacterial community is
Reverse Sample Genome Probing (RSGP). This method uses genome microarrays
to analyze bacterial community composition of the most dominant culturable
species in an environment (Greene and Voordouw 2003). RSGP has four steps:
(1) Isolation of genomic DNA from pure cultures
(2) Cross-hybridization testing to obtain DNA fragments with less than 70 % crosshybridization (DNA fragments with greater than 70 % cross-hybridization are
considered to be of the same species)
(3) Preparation of genome arrays onto a solid support
(4) Random labeling of a defined mixture of total community DNA and internal
standard
This method has been used to analyze bacterial communities in oil fields and in
contaminated soils (Greene et al. 2000). Like DNA–DNA hybridization, RSGP and
microarrays have the advantages that these are not confounded by PCR biases.
Microarrays can contain thousands of target gene sequences but it only detects the
most abundant species. Using genes or DNA fragments instead of genomes on the
microarray offers the advantages of eliminating the need to keep cultures of live
organisms, as genes can be cloned into plasmids or PCR can continuously be used
to amplify the DNA fragments (Gentry et al. 2006). In addition, fragments would
increase the specificity of hybridization over the use of genomes, and functional
genes in the community could be assessed (Greene and Voordouw 2003).
Cross-hybridization is a major limitation of microarray technology. In addition,
the microarray is not useful in identifying and detecting novel prokaryotic taxa. The
ecological importance of a genus could be completely ignored if the genus does not
have a corresponding probe on the microarray.
18.5
Conclusions
All of the approaches that are available today have advantages and limitations,
though none of them provide complete access to the extremely important and
complex bacterial world. These new techniques, which are in constant development, have provided powerful and important conformation of previous phenotypic
and genotypic studies of bacteria. The combination of different methods is still the
most suitable way of having a better understanding about diversity, phylogeny,
ecology, evolution, and taxonomy of the largest group of living organisms on Earth,
the Prokaryotes. Several questions remain to be resolved and the collaboration of
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taxonomists, microbiologists, and molecular biologists is essential and very important for the integration of the different research methods to allow for a proper
assessment of bacterial diversity and its real potential. Several important questions
such as “How many bacterial species are there on the Earth?”, “What is the extent
of metabolic diversity in natural bacterial communities?”, and “How bacterial
communities are governed by biological, chemical, and physical factors?” remain
to be understood. An interdisciplinary systems approach embracing several
“omics” technologies to reveal the interactions between genes, proteins, and environmental factors will be needed to provide new insights into environmental
microbiology. Development of multi-“omics” approaches will be a high-priority
area of research in the coming years.
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Chapter 19
Plant Growth-Promoting Rhizobacteria
of Medicinal Plants in NW Himalayas:
Current Status and Future Prospects
Anjali Chauhan, C.K. Shirkot, Rajesh Kaushal, and D.L.N. Rao
19.1
Introduction
India is a natural, invaluable storehouse of medicinal plant diversity of great
importance for mankind. The Himalayas are one of the largest and youngest
mountain ranges of the world and cover about 10 % of India’s land area. Extending
across much of the northern and north-eastern borders of the country, the Himalayan massif regulates climate for a broad portion of Asia and provides ecosystem
services especially perennial water streams to much of the heavily populated plains
of India. In addition, due to its unique location as the meeting place of three
biogeographic realms (the Palaearctic, Indo-Malayan and Mediterranean), the
species diversity and endemism in the region are unique. At the same time, the
region is extremely fragile as a complex result of tectonic activities and anthropogenic influences. On account of its unique and diverse ecosystems and high levels
of threat, the Himalayas have recently been designated as a global biodiversity
hotspot by Conservation International (Joshi et al. 2010). Some of the important
medicinal plants are known to grow only in their indigenous niches, and it is very
difficult to increase their population. Overexploitation of natural resources due to
the increase in population may lead to the extinction of important medicinal plants.
Therefore, medicinal plants need to be protected in their natural habitat through
careful management so as to achieve a sustainable balance through systematic agrotechnique.
A. Chauhan • C.K. Shirkot • R. Kaushal
Department of Basic Sciences (Microbiology Section), Dr Y.S. Parmar University
of Horticulture and Forestry, Nauni, Solan 173230, Himachal Pradesh, India
e-mail: shirkotuhf@gmail.com
D.L.N. Rao (*)
All India Network Project on Soil Biodiversity-Biofertilizers, Indian Institute of Soil Science,
Bhopal 462 038, Madhya Pradesh, India
e-mail: desiraju.rao@gmail.com
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_19
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Over the last decades, world agriculture has experienced high increase in crop
yields, which is being achieved through massive use of inorganic fertilizers and
pesticides and mechanization driven by fossil fuel. The global necessity to increase
agricultural production from a steadily decreasing and degrading land resource base
has placed a considerable strain on agroecosystem health (Tilak et al. 2005; Rao
2013). Especially in developing countries including India, the demand of chemical
fertilizers for crop production has increased tremendously due to the release of
several high-yielding and nutrient-demanding varieties of crop plants. The excessive and imbalanced use of chemical fertilizers has resulted not only in the
deterioration of soil health but also leads to some major environmental problems.
This has evinced a great interest in the implementation of environmental friendly
sustainable agricultural practices. A progressive reduction in the application of
agrochemicals in farming practices without compromising on the yield or quality
of the crops and advancement of new generation technologies can be the only
possible sustainable alternative. During the last couple of decades, the recent
biotechnological advancements in agriculture have unlocked new avenues for the
augmentation of productivity in a sustainable manner and have made possible
exploitation of soil microorganisms for improving the crop health (Hayat
et al. 2010; Lugtenberg and Kamilova 2009) and mitigating environmental stresses
(Rao and Sharma 1995; Tank and Saraf 2010).
19.2
Plant Growth-Promoting Rhizobacteria
The concept of rhizosphere was first given by Hiltner (1904) to describe the
microbial population in the rhizosphere that colonizes the roots of plants, is
beneficial and enhances crop productivity and protects the environment. Root
colonization comprises the ability of introduced bacteria to survive and establish
on or in the plant root, propagate and disperse along the growing root in the
presence of indigenous microflora (Kloepper and Schroth 1978). Numerous microorganisms such as algae, bacteria, protozoa and fungi coexist in the rhizospheric
region, but bacteria are the most predominant. Plants preferentially select those
bacteria contributing to the plants by releasing sugars, amino acids, organic acids,
vitamins, enzymes and organic or inorganic ions through root exudates which
contribute to creating a rich environment for microbial proliferation. Plant
growth-promoting rhizobacteria are soil bacteria inhabiting around/on the root
surface and are directly or indirectly involved in promoting plant growth and
development via production and secretion of various regulatory chemicals in the
vicinity of rhizosphere. They stimulate plant growth through mobilizing nutrients in
soils, producing numerous plant growth regulators, protecting plants from phytopathogens by controlling or inhibiting them, improving soil structure and
bioremediating the polluted soils by sequestering toxic heavy metal species and
degrading xenobiotic compounds (Ahemad and Malik 2011). Indeed, the bacteria
lodging around/in the plant roots (rhizobacteria) is more versatile in transforming,
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mobilizing and solubilizing the nutrients compared to those from bulk soils (Hayat
et al. 2010). Therefore, the rhizobacteria are the dominant driving forces in
recycling the soil nutrients, and, consequently, they are crucial for soil fertility
(Glick 2012). Strains with PGPR activity, belonging to genera Azoarcus,
Azospirillum, Azotobacter, Arthrobacter, Bacillus, Clostridium, Enterobacter,
Gluconacetobacter, Pseudomonas and Serratia, have been reported by many
workers. Among these, species of Pseudomonas and Bacillus are the most extensively studied. These bacteria competitively colonize the roots of plant and can act
as biofertilizers and/or antagonists (biopesticides) or simultaneously both. PGPRs
promote plant growth by direct and indirect mechanisms and act as biofertilizers as
well as biopesticides (Das et al. 2013). With recent upsurge in the interest in organic
farming, several biodynamic preparations based on cow dung fermentations are
used all of which contain plant growth-promoting bacteria. Bacillus safensis,
Bacillus cereus, Bacillus subtilis, Lysinibacillus xylanilyticus and Bacillus
licheniformis were reported recently from cow dung ferments (Radha and Rao
2014). Of these, L. xylanilyticus and B. licheniformis were reported for the first
time in biodynamic preparations.
19.2.1 Relationship Between PGPR and Plant Host
For PGPR to have impact on plant growth, there is an obvious need for an intimate
association with the host plant. However, the degree of intimacy can vary
depending on where and how the PGPR colonizes the host plant. Relationships
between PGPR and their hosts can be categorized into two levels of complexity:
(1) rhizospheric and (2) endophytic.
19.2.1.1
Rhizospheric
The rhizosphere can be defined as any volume of soil specifically influenced by
plant roots and/or in association with roots, hairs and plant-produced material. This
space includes soil bound by plant roots, often extending a few mm from the root
surface (Bringhurst et al. 2001) and can include the plant root epidermal layer
(Mahafee and Kloepper 1997). Plant exudates in the rhizosphere, such as amino
acids and sugars, provide a rich source of energy and nutrients for bacteria,
resulting in bacterial populations greater in this area than outside the rhizosphere.
Extracellular PGPR (ePGPR) existing in the rhizosphere increases plant growth
through a variety of mechanisms; they include genera such as Bacillus, Pseudomonas, Chromobacterium, Agrobacterium and free-living nitrogen-fixing bacteria
such as Azotobacter and Azospirillum. Most rhizosphere organisms occur within
50 mm of root surface, and their populations within 10 mm of root surface may
reach 1.2 108 cells kg 1 soil. Despite large numbers of bacteria in rhizosphere,
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only 7–15 % of the total root surface is generally occupied by microbial cells (Gray
and Smith 2005).
19.2.1.2
Endophytic
Rhizobacteria that establish inside plant roots, forming more intimate associations,
are called endophytes. To aid in this conceptualization, simple terms have been
adopted; intracellular PGPR (iPGPR) refers to bacteria residing inside plant cells,
producing nodules and being localized inside those specialized structures. These
include a wide range of soil bacteria forming less formal associations than the
rhizobia–legume symbiosis; endophytes may stimulate plant growth, directly or
indirectly, and include the rhizobia. Soil bacteria in the genera Rhizobium,
Bradyrhizobium, Sinorhizobium, Mesorhizobium and Azorhizobium, belonging to
the family Rhizobiaceae, invade plant root systems and form root nodules (Wang
and Martinez-Romero 2000). Collectively, they are often referred to as rhizobia.
These PGPRs are mostly Gram-negative and rod-shaped, with a lower proportion
being Gram-positive rods, cocci and pleomorphic forms.
19.3
Mechanism of Plant Growth Promotion
Plant growth-promoting rhizobacteria (PGPR) colonizes plant roots and stimulates
plant growth. PGPRs control the damage to plants from phytopathogens and
promote the plant growth by a number of different mechanisms. According to
Glick (1995), the general mechanisms of plant growth promotion by PGPR include
associative nitrogen fixation, lowering of ethylene levels, production of
siderophores and phytohormones, induction of pathogen resistance, solubilization
of nutrients, promotion of mycorrhizal functioning and decreasing pollutant toxicity. The PGPR strains can thus promote plant growth and development either
directly or indirectly or both.
19.3.1 Direct
There are several ways in which different PGPRs may directly facilitate the
proliferation of their plant hosts. They may (1) solubilize minerals such as phosphorus, (2) fix atmospheric nitrogen and supply it to the plants and (3) synthesize
various phytohormones, including auxins and cytokinins (Chen et al. 2006).
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19.3.2 Indirect
The indirect mechanism of plant growth occurs when PGPR lessens or prevents the
deleterious effects of plant pathogens on plants by the production of inhibitory
substances or by increasing the natural resistance of the host (Nehl et al. 1997).
PGPRs provide different mechanisms for suppressing plant pathogens. These
include competition for nutrients and space (Elad and Chet 1987); antibiosis by
producing antibiotics, viz., pyrrolnitrin, pyocyanin and 2,4-diacetylphloroglucinol
(Pierson and Thomashow 1992) and production of siderophores (fluorescent yellow
pigment), viz., pseudobactin, which limits the availability of iron necessary for the
growth of pathogens (Lemanceau 1992). Other important mechanisms include
production of lytic enzymes such as chitinases and β-1,3-glucanases which degrade
chitin and glucan present in the cell wall of fungi (Frindlender et al. 1993), HCN
production and degradation of toxin produced by pathogen (Duffy and Defago
1997). PGPRs have attracted much attention for their role in reducing plant
diseases. Although the full potential has not been reached yet, the work to date is
very promising and may offer organic growers effective control of serious plant
diseases.
19.4
PGPR Associated With Medicinal Plants
Ecosystems in the Indian Himalayas encompass one of the largest altitudinal
gradients in the world and range from the subtropical forests of the Siwaliks to
alpine meadows and scrub in the higher peaks of the Great Himalayas. Some of the
richer assemblages of wild and medicinal plants are found in this region. It has been
estimated that the region supports over 4,500 species of vascular plants (Western
Himalaya Ecoregional BSAP 2002). Ancient Indian literature incorporates a
remarkably broad definition of medicinal plants and considers all plants as potential
sources of medicinal substances. However, this plant wealth is eroding at a fast pace
due to habitat loss, land fragmentation, overexploitation, invasion of exotics,
pollution and climate change. The population explosion and economic development
and urbanization the world over have been basic and fundamental reasons for the
depletion of natural resources. The biosphere has lost some valuable species, and
many more are threatened. According to some estimates, tropical forests alone are
losing one species per day. The erosion of species richness is going to erode the
valuable genes, genomes, ecosystem balance, ecosystem stability and a host of
other characteristics which are hard to retrieve back. The anthropogenic interferences have deflected the natural directions, posing threat to these pristine ecosystems. To protect these herbal medicinal plants in their natural habitat, a systematic
agro-technique needs to be developed (Malleswari and Bagyanarayana 2013).
Plant growth-promoting microbes found in the rhizosphere of various medicinal
plants grown in different soils and climatic conditions can provide a wide spectrum
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of benefits to plants (Mayak et al. 2004). Arbuscular mycorrhizal fungi (AMF) are
also known to increase the growth of many plant species, including medicinal and
aromatic plants (Selvaraj et al. 2008). Various PGPR strains have also proven to be
able to increase nutrient availability in the rhizosphere (Cakmakci et al. 2007). The
occurrence of Azospirillum, Azotobacter, Pseudomonas and Bacillus in the rhizosphere of Withania somnifera has been reported by Thosar et al. (2005). Species
such as Azospirillum, Azotobacter and Pseudomonas have been found in the
rhizosphere of Catharanthus roseus, Coleus forskohlii, Ocimum sanctum and
Aloe vera (Karthikeyan et al. 2008). Turrini et al. (2010) reported the occurrence
of AMF species such as Glomus coronatum, G. mosseae, G. etunicatum,
G. geosporum, G. viscosum and G. rubiforme in the rhizosphere of Smilax aspera
and Helichrysum litoreum. Species belonging to the genus Bacillus has been
registered as the dominant rhizobacteria associated with medicinal plants,
Valeriana jatamansi, Podophyllum hexandrum and Picrorhiza kurroa grown in
their natural habitat of Northwestern Himalayas (AINP on Biofertilizer Solan
Centre, UHF, Nauni).
In the rhizosphere, a synergism between various bacterial genera such as Bacillus, Pseudomonas, Arthrobacter and Rhizobium has been shown to promote plant
growth of various plants such as peanut (Arachis hypogaea L.) (Dey et al. 2004),
maize (Zea mays L.), soybean (Glycine max L.) (Cassan et al. 2009), fodder galega
(Galega orientalis L.) (Egamberdieva et al. 2011) and sweet basil (Ocimum
basilicum L.) (Hemavathi et al. 2006). Compared to single inoculation,
co-inoculation has improved the absorption of nitrogen (N), phosphorus (P) and
mineral nutrients by plants (Bashan and Holguin 1997). Such PGPR activity has
been reported in species belonging to Azospirillum, Azotobacter, Pseudomonas,
Bacillus, Burkholderia, Bradyrhizobium, Sinorhizobium and Trichoderma
(Sudhakar et al. 2000; Hemavathi et al. 2006; Rajasekar and Elango 2011).
An intensive practice to obtain high yield from cultivated plants requires the
extensive use of chemical fertilizers, fungicides and pesticides, which may create
environmental problems. Nowadays, the use of biofertilizers in production plays an
important role as a supplement to improve the growth and yield of several agricultural, horticultural and medicinal plants (Rao 2008; Lugtenberg and Kamilova
2009). There are several reports that PGPRs have promoted the growth of cereals,
ornamentals, vegetables and MAPs (Vessey 2003; Lugtenberg and Kamilova 2009;
Egamberdieva 2011; Radha and Rao 2014). Since some medicinal plants are on the
verge of extinction, therefore their domestic cultivation is thought to be a viable
alternative (Sekar and Kandavel 2010). But, certain drawbacks exist including
variability in yield and difference in phytochemical profile over those growing in
the wild habitat (Kala et al. 2006). Limited studies have been undertaken on
rhizobacteria associated with medicinal plants. The present effort is an exercise to
review the efforts on isolation, screening and characterization of PGPR with
multiple traits associated with medicinal plants, with an emphasis on methods,
and more importantly dwell on the nature of future investigations needed in the
field.
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19.5
387
Isolation, Enumeration and Characterization
of Culturable Rhizobacteria and Endorhizobacteria
by Replica Plating Technique
19.5.1 Isolation
Root systems of medicinal plants are exposed carefully by manual excavation and
shaken vigorously to remove the rhizospheric soil adhering to the roots. Isolation of
bacteria is done by diluting the soil suspension in tenfold dilution series (Fig. 19.1).
For endorhizobacteria, the root samples are surface sterilized in 0.2 % mercuric
chloride (HgCl2) for 3 min followed by washing in sterilized distilled water.
Root/Rhizosphere soil
Soil free root (1g)
Rhizosphere soil
Wash thoroughly in the
tap water
Prepare the serial 10-fold dilution (each tube
containing 9ml sterilized distilled water
Surface sterilize with 0.2 per
cent HgCl2 for 3 minutes
Rinse 5-7 times with
sterilized distilled water
Add 1 ml suspension to respective labelled
petri plates
Pour molten cooled (450C) medium and
rotate the plates gently to ensure the
uniforms distribution of cells/spores
Homogenized by grinding in paste and
mortar under aseptic conditions
Allow the medium to solidify
Incubate at 35± 20C for 48 h in an
inverted position
Observe for the appearance of
isolated colonies
Fig. 19.1 Flow sheet for the isolation of rhizospheric and endophytic rhizobacteria
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Fig. 19.2 Master plate for isolation of PGPR of Picrorhiza kurroa (a); replica plating on different
media (b): NA, PVK, N-free medium
The surface sterility of roots needs to be cross-checked by incubating the surfacesterilized roots in sterilized nutrient broth overnight. For isolation, one gram of
surface-sterilized root sample is placed in 9 ml of sterilized distilled water and then
grounded to produce slurry using pestle and mortar under aseptic conditions, and
finally plating of soil/root sample is done by pour plate technique on nutrient agar
(master plate) under aseptic conditions as per procedure depicted in Fig. 19.2. Plant
growth-promoting bacterial isolates from Picrorhiza kurroa and other medicinal
plants were also isolated by modified replica plating technique developed by AINP
on Biofertilizer laboratory, Solan Centre, UHF, Nauni. Populations are expressed as
colony-forming unit (CFU) per gram of dry soil weight and per gram of the root
weight.
The representative bacterial isolates of the total plated population from the
rhizosphere soil and rhizome/roots of the Picrorhiza kurroa from two locations of
Chamba district isolated by modified replica plating are presented in Fig. 19.2.
Replica plating technique was originally developed to isolate auxotrophic mutants,
but it can also be used for the quick isolation and screening of PGPRs for plant
growth-promoting traits (AINP on Biofertilizers Laboratory Solan, Shirkot and
Vohra 2007; Mehta et al. 2013). Rhizospheric and endorhizospheric bacterial
populations obtained on nutrient agar (master plate) are replica plated in the same
position as the master plate with the help of a wooden block, covered with sterilized
velveteen cloth onto the selective media: CAS medium (Schwyn and Neilands
1987) for siderophore-producing ability, nitrogen-free medium for nitrogen-fixing
ability and Pikovskaya medium for phosphate-solubilizing ability. At the end of the
incubation period (72 h), the location of the colonies appearing on the replica plates
is compared to the master plate (Mehta et al. 2010).
All the bacterial isolates were able to grow on nutrient agar, Pikovskaya’s
medium, nitrogen-free media and CAS media and were selected for screening
PGP traits. Four efficient P-solubilizing bacterial isolates exhibited very good
chitinase activity on agar plates with a zone size ranging from 30 to 45 mm.
Maximum IAA production (30.0 μg/ml) was exhibited by two isolates, and seven
isolates were found antagonistic against common fungal pathogens: Alternaria
solani, Fusarium oxysporum, Pythium aphanidermatum, Sclerotium rolfsii and
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Dematophora necatrix, and maximum siderophore unit (27.2 %) was observed by
one isolate (unpublished).
19.5.2 Enumeration
Pearson correlation analysis for total culturable rhizosphere soil and root endophytic bacterial population among six Valeriana jatamansi growing sites, viz.,
Bharmour, Salooni, Padri, Naingra, Holi and Hadsar of Chamba district of
Himachal Pradesh, was done (unpublished data from research work underway at
AINP on Biofertilizer laboratory, Solan Centre, UHF, Nauni, Table 19.1). There
was a positive and significant correlation (r ¼ 0.67) between the bacterial population in the rhizosphere and that inside the plants. The sampling sites differed in
soil physicochemical properties and environmental conditions. Significant variation
in the population of both indigenous rhizosphere soil bacteria and V. jatamansi root
endophytes was attributed to plant source, time of sampling and environmental
conditions, thus suggesting a close association between bacterial population and
medicinal plants.
19.5.3 Characterization
The in vitro screening of bacterial isolates for important PGPR attributes is depicted
in Fig.19.3. PGPR may use more than one mechanism (direct and indirect) to
enhance plant growth, as experimental evidence suggests that plant growth stimulation is the net result of multiple mechanisms that may be activated simultaneously. Recent investigations on PGPR revealed that it can promote plant
growth mainly by the following means: (1) producing 1-aminocyclopropane-1Table 19.1 Enumeration of total culturable rhizosphere and endophytic bacterial populations of
Valeriana jatamansi seedlings
Location
Sites
Chamba
Bharmour
Salooni
Padri
Naingra
Holi
Hadsar
LSD
Correlation
coefficient
Rhizosphere soil bacterial
populationa (106 cfu g 1 soil)
Root endophytic bacterial
populationa (103 cfu g 1 root)
29.3
20.2
28.4
27.8
25.0
27.4
9.0
r ¼ 0.67
26.2
16.2
20.0
23.2
21.2
17.3
10.8
a
Average of five samples
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Fig. 19.3 Multifarious plant growth-promoting traits of P-solubilizing bacterial isolates:
P-solubilization (a), chitinase activity (b), HCN production (c), siderophore production (d),
antifungal activity against Dematophora necatrix (e), growth on nitrogen-free medium (f) and
proteolytic activity (g)
carboxylic acid (ACC) deaminase to reduce the level of ethylene in the roots of
developing plants (Dey et al. 2004); (2) producing plant growth regulators like
indole acetic acid (IAA) (Mishra et al. 2010), gibberellic acid, cytokinins (SánchezCastro et al. 2012) and ethylene (Saleem et al. 2007); (3) asymbiotic nitrogen
fixation (Ardakani et al. 2010); (4) exhibition of antagonistic activity against
phytopathogenic microorganisms by producing siderophores, β-1,3-glucanase,
chitinases, antibiotics, fluorescent pigment and cyanide; and (5) solubilization of
mineral phosphates and other nutrients (Hayat et al. 2010). Recently, biochemical
and molecular approaches are providing new insight into the genetic basis of these
biosynthetic pathways, their regulation and their importance in biological control.
In AINP on Biofertilizers laboratory, Solan Centre, UHF, Nauni, work has been
carried out on the plant growth-promoting potential of PGPRs isolated from
Podophyllum hexandrum (unpublished data). Forty-one bacterial isolates were
isolated by modified replica plating technique, and representatives of the total
plated population from the rhizosphere and rhizome/roots of the P. hexandrum
were selected. All the bacterial isolates were able to grow on nutrient agar,
Pikovskaya’s, nitrogen-free media and CAS media and selected for further screening for various plant growth-promoting traits. Proportion of PGPR exhibiting
phosphate solubilization and siderophore production is depicted in Fig. 19.4. Percentage of bacteria exhibiting phosphate solubilization activity is arranged in the
order of S3(76.3 %) > S2(72.1 %) > S4(71.4 %) > S1(50.0) > S5 (40.0 %). In
particular, 100.0 % of the bacteria isolated from the endo-rhizosphere (ER) of
site S4 could solubilize phosphorus, even though only 16.7 % of isolates from
rhizosphere soil (RS) of site S5 samples could display this activity. The bacterial
isolates showing siderophore production were in the order of S2 (66.7 %) > S4
(64.3 %) > S3(61.5 %) > S1(46.2 %) > S5(40.0 %). The highest siderophore
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Fig. 19.4 Graphical representation of percentages of rhizosphere and endophytic bacterial isolates of five sites for PGP traits: (a) phosphate solubilization and (b) siderophore production (AINP
on Biofertilizer laboratory, Solan Centre, UHF, Nauni)
producers were recorded in samples collected from ER of site S2 (91.7 %), and
lowest percentages were recorded in RS of site S1 (35.3 %).
19.6
Plant Growth-Promoting Attributes of PGPR
19.6.1 Biological Nitrogen Fixation
Nitrogen is an essential element for all forms of life and a basic requisite for
synthesizing nucleic acids, proteins and other organic nitrogenous compounds.
The ability to reduce and derive such appreciable amounts of nitrogen from the
atmospheric reservoir and enrich the soil is confined to bacteria and archaea (Young
1992). Biological nitrogen fixation includes symbiotic nitrogen fixation in the case
of Rhizobium, the obligate symbionts in leguminous plants, and Frankia in
nonleguminous trees, while non-symbiotic nitrogen-fixing forms (free-living, associative or endophytic) include Azotobacter, Azospirillum, Azoarcus, Acetobacter
diazotrophicus and cyanobacteria.
Diazotrophs represent a physiologically and phylogenetically highly diverse
functional group, and consequently the functional gene nifH (nitrogenase reductase) is the prevailing marker gene for the detection and identification of potential
diazotrophs in environmental samples. However, for simple initial screenings to
test the efficacy of the rhizobacteria as nitrogen fixer, a loopful of 24-h-old culture
of each isolate is streaked on nitrogen-free medium (Jansen et al. 2002) and
incubated for 72 h, and the colonies that are able to grow are selected as putative
nitrogen fixers.
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Nitrogenase Activity (Husen 2003)
The ability of the bacteria to fix dinitrogen can be measured by standard protocol of
acetylene reduction assay given by Hardy et al. (1968). 50 μl of bacterial culture is
inoculated in 1 ml of Burk’s nitrogen-free medium (Subba Rao 1999) in 6 ml
vacutainer sealed with cotton plugs and incubated for 48 h at room temperature.
The cotton plug is then replaced with a rubber stopper, and 0.5 cm3 of the
atmosphere (10 %) in the vacutainer is replaced with acetylene and then incubated
for 20–24 h. Gas sample (1 ml) was removed from the vacutainer using 1 ml
syringe, and the ethylene gas concentration is measured by gas chromatography.
19.6.2 P-Solubilization
Phosphorous is one of the major nutrients required for the growth and development
of plants and microorganisms. Microorganisms offer a biological means of solubilizing the insoluble inorganic P of soil and make it available to the plants as
orthophosphate. The phosphate-solubilizing bacteria are a promising source of
plant growth-promoting agents in agriculture that help sustain agriculture. Most
efficient phosphate-solubilizing microorganisms (PSMs) belong to genera Bacillus
and Pseudomonas (Illmer and Schinner 1995; Richardson 2001) and among fungi,
Aspergillus and Penicillium. Certain strains of Rhizobium can also solubilize both
organic and inorganic phosphate (Alikhani et al. 2006).
19.6.2.1
Mechanism of Phosphate Solubilization
There are two components of P in soil: organic and inorganic phosphates. Inorganic
P occurs in soil, mostly in the form of insoluble mineral complexes; some of these
appearing after the application of chemical fertilizers. Organic matter, on the other
hand, is an important reservoir of immobilized P that accounts for 20–80 % of soil P
(Richardson 1994). Organic phosphate solubilization is also called mineralization
of organic phosphorus, and it occurs in soil at the expense of plant and animal
remains, which contain a large amount of organic phosphorus compounds. The
degradability of organic phosphorous compounds depend mainly on the physicochemical and biochemical properties of their molecules, e.g. nucleic acids,
phospholipids and sugar phosphates are easily broken down, but phytic acid,
polyphosphates and phosphonates are decomposed more slowly (McGrath
et al. 1995).
Several reports have suggested the ability of different bacterial species to
solubilize insoluble inorganic phosphate compounds, such as tricalcium phosphate,
dicalcium phosphate, hydroxyapatite and rock phosphate (Goldstein 1986; Mehta
et al. 2010; Walia et al. 2013). In two thirds of all arable soils, the pH is above 7.0,
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so that most mineral P is in the form of poorly soluble calcium phosphates (CaPs).
Microorganisms must assimilate P via membrane transport, so dissolution of CaPs
to Pi (H2PO4) is considered essential to the global P cycle. Evaluation of samples
from soils throughout the world has shown that, in general, the direct oxidation
pathway provides the biochemical basis for highly efficacious phosphate solubilization in Gram-negative bacteria via diffusion of the strong organic acids produced
in the periplasm to the adjacent environment.
19.6.2.2
Qualitative Estimation on Agar Plates
For the qualitative estimation of phosphorus, positive bacterial isolates obtained
after isolation by replica plating are streaked on the PVK agar plates containing
known amount of tricalcium phosphate [Ca3(PO4)2] and incubated at 37 C for 48 h.
The bacterial solubilization of phosphorus exhibited with yellow-coloured zones
produced around the isolated bacterial colony can be calculated by subtracting
colony size from total size. Phosphate solubilization index (PSI) is measured using
the formula given by Edi-Premono et al. (1996) (Fig. 19.5).
19.6.2.3
Quantitative Estimation in Liquid Broth
Fifty millilitre of PVK broth is dispensed in 250 ml of Erlenmeyer flask containing
0.5 % tricalcium phosphate (TCP) and autoclaved at 15 psi for 20 min, inoculated
with 10 % of the bacterial suspension (OD 1.0 at 540 nm) and incubated at 352 C
under shake conditions for 72 h along with two controls of PVK broth, one with
TCP plus inoculum and the other one with inoculum, and no TCP. The culture
supernatant is used for determination of the soluble phosphate as described by Bray
and Kurtz (1945). An aliquot (0.1–1.0 ml) from the culture supernatant is made to
final volume of 5 ml with distilled water and 5 ml ammonium molybdate. The
mixture is then thoroughly shaken. The contents of the flasks are finally diluted to
20 ml. Then add 1.0 ml of chlorostannous acid, and make its volume to 25 ml in the
volumetric flask. The contents are mixed thoroughly, and the blue-coloured intensity is measured after 10 min at 660 nm. An appropriate blank is kept in which all
Fig. 19.5 Figure showing
formula for calculating
phosphate solubilization
index (PSI)
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reagents were added except the culture. The results were extrapolated by standard
curve drawn using potassium dihydrogen phosphate.
P solubilization ¼ T
C
where
T ¼ PVK with TCP, inoculated
C ¼ PVK with TCP, uninoculated
In a study conducted in AINP on Biofertilizer laboratory, Solan Centre, an
isolate Bacillus subtilis CB8A from apple rhizosphere was found to produce
phosphate metabolite even without the addition of insoluble phosphate source to
the Pikovskaya’s broth and also possess five plant growth-promoting attributes
(IAA production, siderophore synthesis, chitinase activity, ability to fix atmospheric nitrogen and antifungal activity against Dematophora necatrix) at wide
range of temperatures (30–45 C), pH 7 to 9 and salt concentration (0–5 %). The
presence of gdh gene in Bacillus subtilis CB8A isolate along with organic acid
production has been detected which is considered as a possible mechanism responsible for phosphate solubilization (Mehta et al. 2013).
Similarly, in the case of medicinal plants, efficient PGPRs were isolated and
screened for P-solubilization and other PGP traits. Almost all the isolates from all
the three medicinal plants, viz., Valeriana jatamansi, Picrorhiza kurroa and Podophyllum hexandrum, screened were P-solubilizers and showed high P-solubilization
under in vitro conditions. Thirty P-solubilizing strains were isolated from
V. jatamansi, and among them Aneurinibacillus aneurinilyticus strain CKMV1
showed maximum P-solubilization of 257.0 mg/l; 40 strains were from P. kurroa,
Bacillus subtilis strain PkR(7a) exhibited high TCP solubilization of 320.0 mg/l,
and 45 P-solubilizing isolates were from P. hexandrum, while the maximum
P-solubilization was observed with B. subtilis strain 4a1 (320.0 mg/l).
19.6.3 Phytohormone Production
Phytohormones are organic compounds which are effective at low concentration
but play important role as regulators of growth and development of plants. They are
the chemical messengers that effect plant’s ability to respond to its environment.
There are five groups of phytohormones: auxins, gibberellins, cytokinins, ethylene,
and abscisic acid. The root is one of the plant’s organs that is most sensitive to
fluctuations in IAA, and its response to increasing amounts of exogenous IAA
extends from elongation of the primary root, formation of lateral and adventitious
roots, to growth cessation; hence, IAA is considered as the most important native
auxin (Ashrafuzzaman et al. 2009).
IAA is secreted by 80 % of microorganisms and especially secreted by
rhizobacteria and interferes with the many plant developmental processes because
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the endogenous pool of plant IAA may be altered by the acquisition of IAA (Glick
2012; Spaepen et al. 2007a, b). IAA acts as a reciprocal signalling molecule and
affects the gene expression in several microorganisms, and therefore it is considered to play a very important role in rhizobacteria–plant interactions (Costacurta
and Vanderleyden 1995). Tryptophan (Trp) is generally considered as the IAA
precursor, because its addition to IAA-producing bacterial cultures promotes an
increase in IAA synthesis since it requires Trp-dependent pathways (Costacurta and
Vanderleyden 1995).
IAA affects plant cell division, extension and differentiation; stimulates seed and
tuber germination; increases the rate of xylem and root development; controls the
processes of vegetative growth; initiates lateral and adventitious root formation;
mediates responses to light, gravity and florescence; and affects photosynthesis,
pigment formation, biosynthesis of various metabolites and resistance to stressful
conditions. Moreover, bacterial IAA increases root surface area and length and
thereby provides the plant greater access to soil nutrients. Also, the rhizobacterial
IAA loosens plant cell walls and as a result facilitates an increasing amount of root
exudation that provides additional nutrients to support the growth of rhizosphere
bacteria (Glick 2012). The downregulation of IAA as signalling is associated with
the plant defence mechanisms against a number of phytopathogenic bacteria as
evidenced in enhanced susceptibility of plants to the bacterial pathogen by exogenous application of IAA or IAA produced by the pathogen.
19.6.3.1
Quantitative Estimation of Indole-3-Acetic Acid (Auxins)
Quantitative measurement of auxin is done by colorimetric method (Gorden and
Paleg 1957) with slight modification. 2–3 drops of orthophosphoric acid are added
to 2 ml supernatant along with 4 ml of Salkowski reagent (2 ml of 0.5 M FeCl3 in
98 ml of 35% HClO4). This mixture is then incubated at room temperature in dark
for 25 min. Absorbance is measured at 535 nm for the development of pink colour.
Concentration of indole-3-acetic acid is estimated by preparing calibration curve
using indole-3-acetic acid.
19.6.4 Siderophore Production
Iron is one of the bulk minerals present in plentiful amounts on earth, yet it is
unavailable in the soil for the plants. This is because Fe3+ (ferric ion) is a common
form of iron found in nature and is meagrely soluble. To overcome this problem,
PGPR secretes siderophores which are iron-binding protein of low molecular mass
and high binding affinity with ferric ion. Siderophores are small molecular weight
compounds that bind to iron in the soil and make it unavailable to some of the
disease-causing microflora and thus starving them of the iron they otherwise need to
survive. Lankford coined the term siderophore in 1973 to describe low molecular
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Fig. 19.6 Plate assay for detection of type of siderophore: (a) catecholate, (b) hydroxamate and
(c) carboxylate
weight molecules that bind ferric iron with an extremely high affinity (Lankford
1973). Siderophores are of three types, (a) catecholate, (b) hydroxamate and
(c) carboxylate (Fig. 19.6), and have molecular weight ranging from approximately
600 to 1,500 Da, and because passive diffusion does not occur for molecules greater
than 600 Da, siderophores must be actively transported. Once actively transported
into the periplasm, the iron siderophore complex is bound to a periplasmic binding
protein (Braun and Braun 2002).
Siderophores secreted by PGPRs improve plant growth and development by
increasing the accessibility of iron in the soil surrounding the roots. Plants such as
oats, sorghum, cotton, peanut, sunflower and cucumber demonstrate the ability to
use microbial siderophores as sole source of iron than their own siderophores
(phytosiderophores). Microbial siderophores are also reported to increase the chlorophyll content and plant biomass in cucumber plants (Das et al. 2013). Nakouti and
Hobbs (2012) isolated organisms on the basis of their survival in an iron-limited
environment. The survivors of this treatment were largely actinomycetes, and the
most prolific producers as assessed and characterized by the chrome azurol sulfonate
assay were found to belong to the genus Streptomyces.
19.6.4.1
Estimation of Siderophores by Chrome-Azurol-S (CAS) Assay
(Schwyn and Neilands 1987)
Siderophore production is detected by chrome-azurol-S (CAS) plate assay and
assayed by procedure of Schwyn and Neilands 1987. Sterilized CAS blue agar is
prepared by mixing CAS (60.5 mg/50 ml distilled water) with 5 ml iron solution
(1 mM FeCl3·6H2O) and 5 ml of 10 mM HCl. This solution is slowly added to
hexadecyltrimethylammonium bromide (HDTMA) (72.9 mg/40 ml distilled water).
Then the CAS dye is poured into nutrient agar, and plates are poured for spotting of
24-h-old test bacterial culture. Formation of a bright zone with a yellowish
(hydroxamate), pinkish (catecholate) and whitish (carboxylate) colour in the dark
blue medium indicated the production of siderophore after incubating for 72 h at
37 C. In the case of liquid assay, the absorbance is recorded at 630 nm, and the
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minimal medium is used as a blank with reference (r) cell free extract of culture
supernatant. The siderophore units can be calculated using the formula:
Percent siderophore unit ¼
Ar
As
Ar
100
where
Ar is defined as absorbance at 630 nm of reference
As is the absorbance at 630 nm of the test bacteria
19.6.5 HCN Production
A secondary metabolite produced commonly by rhizosphere microorganisms is
hydrogen cyanide (HCN), a gas known to negatively affect root metabolism and
growth (Schippers et al. 1990). Cyanide production is one of the possible ways by
which rhizobacteria may suppress plant growth in soil. Although cyanide acts as a
general metabolic inhibitor, it is synthesized, excreted and metabolized by hundreds
of organisms, including bacteria, algae, fungi, plants and insects, as a means to
avoid predation or competition. It affects sensitive organisms by inhibiting the
synthesis of ATP-mediated cytochrome oxidase and is a potential environmentally
compatible way for biological control of weeds.
19.6.5.1
HCN Production Method (Baker and Schippers 1987)
The bacterial cultures are streaked on King’s medium B amended with 1.4 g/l
glycine agar plates, and the Whatman No. 1 filter paper strips soaked in 0.5 % picric
acid in 2 % sodium carbonate are placed inside the top lid of petri plates. Then the
petri plates are sealed with parafilm, inverted and incubated at 28 2 C for 1–4
days. Uninoculated plates are kept as a control for comparison. The results are
observed for change of colour of filter paper from yellow to orange brown to dark
brown.
19.6.6 Biocontrol Ability
The term “biological control” and its abbreviated synonym “biocontrol” have been
used in different fields of biology, but in plant pathology, this term is applied for the
use of microbial antagonists (the biological control agent or BCA) to suppress
diseases. Most narrowly, biological control refers to the suppression of a single
pathogen (or pest) by a single antagonist in a single cropping system.
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Soil-borne fungal diseases pose serious constraints on agro-productivity. Biological control is a non-hazardous strategy to control plant pathogens and improve
crop productivity. The use of indigenous endophytic bacteria is considered as an
environmentally friendly and ecologically efficient strategy. Further, it appears
inevitable that fewer pesticides will be used in the future and that greater reliance
will be laid on biological and biotechnological applications including the use of
microorganisms as antagonists. Therefore, the interest in biological control has
been increased in the past few years partly due to the change in the public concern
over the use of chemicals and the need to find alternatives of chemicals used for
disease control. Both Bacillus and Paenibacillus species express antagonistic
activities by suppressing the pathogens, and numerous reports covering this aspect
both under in vitro and in vivo conditions are available (Chen et al. 2006).
A total of 31 endophytic bacteria belonging to different genera, viz., Pseudomonas, Bacillus, Enterobacter, Klebsiella, Acetobacter, Burkholderia, Rhizobium
and Xanthomonas, were isolated from soybean (Glycine max (L) Merril) and were
screened in vitro for the antagonistic activity against soil-borne fungal pathogens of
soybean, viz., Rhizoctonia solani, Fusarium oxysporum, Sclerotium rolfsii,
Colletotrichum truncatum, Macrophomina phaseolina and Alternaria alternata
(Dalal and Kulkarni 2013). Pseudomonas sp. and Bacillus sp. are the major
constituents of rhizobacteria, encourage the plant growth through their diverse
mechanisms and act as biocontrol agents for various agriculture plants and medicinal plants (Noori and Saud 2012; Shehata et al. 2012; Shanmugam et al. 2011;
Zhang et al. 2011; Chauhan et al. 2014).
19.6.6.1
Assay for Antagonists by Agar Streak Method (Vincent 1947)
The rhizobacterial antagonists are screened by streaking a loopful of 48-h-old
culture of test isolates a little below the centre of the pre-poured petri plates of
malt yeast extract agar and then kept for overnight incubation at 37 C to check for
contamination. Mycelial disc of 4-day-old culture of the test fungal pathogen is
placed simultaneously on one side of the streak. A check inoculated with the test
pathogen only is kept for comparison. The plates are incubated at 24 1 C and per
cent growth inhibition is calculated according to Vincent (1947).
I¼
C
T
C
100
where
I ¼ per cent growth inhibition
C ¼ growth of fungus in control
T ¼ growth of fungus in treatment
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19.6.6.2
399
Production of Antibiotic in Liquid Culture
The inhibitory effect of the culture filtrate of test organisms and their consortium is
studied using standard method of agar dilution technique. Seventy-two-hour-old
culture is first centrifuged at 15,000 rpm for 20 min at 4 C and then filter sterilized
using millipore filter (pore size ¼ 0.22 μm). Different concentrations like 10 and
20 % of the filtrate are poured in malt yeast extract agar (MEA), and plates are
incorporated with fungal bits of the test pathogens. The plates are incubated at
temperature 24 1 C for 7 days when the control plate is filled completely with
fungal growth, and then colony diameter is measured.
19.6.7 Lytic Enzymes Production
Various kinds of enzymes are produced by microorganisms. The antagonistic
activity against different type of microbes may also be attributed to the production
of lytic enzymes that are produced by microorganisms. An enzyme chitinase and
chitobiase produced by some bacteria and fungi like Mucor, Trichoderma and
Pseudomonas species possessed a lytic effect which was related to antagonistic
behaviour (Pedraza Reyes and Lopez Romero 1991; Ulhoa and Peberdy 1991).
Chitinases are particularly useful in agriculture as biocontrol agents against fungal
phytopathogens because of their ability to hydrolyse the chitinous fungal cell wall
(Suresh et al. 2010; Wahyudi et al. 2011). Different Paenibacillus strains are
inhibitory to bacteria and/or fungi (Kajimura and Kaneda 1997) due to the production of antimicrobial substances and cell wall-degrading enzymes (β-1,3-glucanases, cellulases, chitinases and proteases) (Budi et al. 2000). Increased induction
of the pathogenesis-related chitinase isoform in Pseudomonas-treated rice in
response to R. solani infection indicated that the induced chitinase has a definite
role in suppressing disease development (Radjacommare et al. 2004).
19.6.7.1
Chitinase Assay (Robert and Selitrennikoff 1988)
Preparation of colloidal chitin (Berger and Reynolds 1958)
1. Powdered chitin is digested overnight with concentrated hydrochloric acid at
4 C.
2. After digestion step, distilled water is added carefully and mixed thoroughly.
3. Centrifuge and remove the supernatant carefully (the first two–three washes are
highly acidic).
4. Continued washing with distilled water until the pH of solution reaches around
4.0.
5. The pH of the colloidal chitin solution is adjusted by using 2N NaOH (a pH
around 6–6.5).
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6. The liquid (10 ml of chitin in 100 ml media) is added directly or the chitin
suspension in water and is centrifuged, and the pellet is collected, dried and used
at 0.3 % in minimal salt media.
The bacterial culture is spotted on prepared minimal agar plates amended with
0.3 % colloidal chitin and incubated at 30 C for 7 days. Development of halo zone
around the colony after addition of iodine was considered as positive for chitinase
enzyme production. In a study conducted in AINP on Biofertilizers laboratory,
Solan Centre, the chitinase activity was found in 11 isolates of medicinal plant
Picrorhiza kurroa (91.7 %) out of selected 12 endophytes and only in 21 rhizosphere soil (75 %) isolates out of total 28 isolates selected. The highest chitinase
activity was observed in the case of four isolates with a zone size ranging between
30 and 45 mm.
19.6.7.2
Proteolytic Activity by Plate Assay (Fleming et al. 1975)
Screening for proteolytic activity in bacterial isolates is done by spot inoculation of
bacterial culture (72-h-old) on skim milk agar (nutrient agar 100 ml supplemented
separately with sterilized skim milk) and incubation at 28 C for 28–48 h. Clear
zone (diameter, mm) formation around the bacterial spot is taken as positive test for
proteolysis.
19.6.7.3
Amylolytic Activity by Plate Assay (Shaw et al. 1995)
Spot inoculation of 24-h-old bacterial culture is done on starch agar plate and
incubated at 37 C for 24–48 h. After incubation, the petri plates are flooded with
iodine solution. Agar plates are observed for starch hydrolysis which is indicated by
the formation of clear zone (diameter, mm) around the bacterial spot.
19.7
Induced Systemic Resistance
Several rhizobacterial strains have been shown to act as plant growth-promoting
bacteria through both stimulation of growth and induced systemic resistance (ISR),
but it is not clear how far both the mechanisms are connected. Induced resistance is
manifested as a reduction of the number of diseased plants or in disease severity
upon subsequent infection by a pathogen. Such reduced disease susceptibility can
be local or systemic, result from developmental or environmental factors and
depend on multiple mechanisms. The spectrum of diseases to which PGPR elicited
ISR confers enhanced resistance overlaps partly with that of pathogen-induced
systemic acquired resistance (SAR). Both ISR and SAR represent a state of
enhanced basal resistance of the plant that depends on the signalling compounds,
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Plant Growth-Promoting Rhizobacteria of Medicinal Plants in NW Himalayas:. . .
401
jasmonic acid and salicylic acid, respectively. Pathogens are differentially sensitive
to the resistance activated by each of these signalling pathways. ISR-eliciting
rhizobacteria can induce typical early defence-related responses in cell suspensions; in plants, they do not necessarily activate defence-related gene expression.
Instead, they appear to act through priming of effective resistance mechanisms, as
reflected by earlier and stronger defence reactions once infection occurs (Van Loon
2007).
19.8
Identification and Characterization of PGPR
Plant growth-promoting rhizobacteria (PGPRs) establish positive interactions with
plant roots and play a key role in agricultural environments and are being currently
exploited commercially for agricultural uses. Their identification involves a polyphasic approach based on cultural, physiological and biochemical tests followed by
sequencing the 16S rDNA gene. Amplified ribosomal DNA restriction analysis as
well as RAPD patterns revealed a high level of intraspecific genetic diversity.
In a study conducted by Chauhan et al. (2014), a bacterial collection of approximately thirty native strains from rhizosphere soil associated with the seedlings of
Valeriana jatamansi grown in moist temperate forest located in and around
Chamba district of Himachal Pradesh were characterized. Four strains were
selected and analyzed for plant growth-promoting traits under in vitro (Fig. 19.7).
Strain CKMV1 of the total four selected strains identified as Aneurinibacillus
aneurinilyticus on the basis of morphological, biochemical and 16S rDNA analysis
showed maximum phosphate solubilization (257.0 mg l 1), indole acetic acid
(6.5 μ g ml 1) and siderophore production (53.4 %) at 35 2 C (Table 19.2).
Besides, the strain also exhibited growth on nitrogen-free medium, hydrogen
cyanide production and antifungal activity against different fungal pathogens.
Significant growth inhibition of fungal pathogens occurred in the order Sclerotium
rolfsii > Rhizoctonia solani > Dematophora necatrix > Phytophthora spp. >
Alternaria spp. > Fusarium oxysporum. The results suggested that the rhizosphere
of native V. jatamansi growing in their natural habitat of Himachal Pradesh is a rich
source of PGPRs which have a potential to be used in the future as PGP inoculants
to improve crop productivity.
The identification and analysis of genetic polymorphisms of strains isolated from
medicinal plants can be carried out by a combination of molecular, PCR-based
techniques like analysis of the restriction patterns produced by amplified DNA
coding for 16S rDNA. An analysis of RAPD patterns by the analysis of molecular
variance method revealed a high level of intraspecific genetic diversity in this
Burkholderia cepacia population (Cello et al. 1997). Whole-cell fatty acid methyl
ester (FAME) profile and 16S rDNA sequence analysis were employed to isolate
and identify the bacterial groups that actively solubilized phosphates in vitro from
rhizosphere soil of Valeriana jatamansi and other important medicinal plants
(unpublished data from AINP on Biofertilizer laboratory, Solan Centre).
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Collection of rhizospheric soil
and root sample from natural
habitat
Isolation on Master Plate (Nutrient Agar)
a
c
b
Replica Plate (a) CAS medium (b) PVK medium (c) Nitrogen Free Glucose
Antifungal activity
Protease acyivity
HCN activity
Chitinase activity
Screening of culturable bacterial isolates for multifarious plant growth promoting
activities
Identification of efficient PGPR
Morphological and
Biochemical characterization
Molecular characterization (16S
rDNA)
Plant growth promotion by PGPR
Fig. 19.7 Stepwise schematic representation of steps for the isolation, identification and characterization of plant growth-promoting rhizobacteria
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mkumar9@amity.edu
Isolates
Plant growth promoting traits
Quantitative assay
P-solubilization
Siderophore
(mg/l)b
unit (%)c
CKMV1
CKMV2e
CKMV3e
CKMV4
LSD
250.00
120.00
89.0
119.00
7.02
a
53.43
40.21
37.08
38.75
3.0
IAA production
(μg/ml)d
% Growth inhibition against fungal pathogensa
Phytophthora
F. oxysporum R. Solani S. Rolfsii spp.
Alternaria
spp.
D. necatrix
6.5
3.21
2.1
3.98
0.23
64.30
67.89
66.67
68.89
2.50
71.08
62.24
55.55
68.89
2.52
75.73
60.00
45.0
53.0
3.02
91.58
51.11
55.56
68.89
3.02
93.58
57.78
68.89
66.67
2.50
71.37
64.45
55.56
60.00
3.02
I ¼ CC T 100
T C; Where, T = Inoculated PVK with TCP, C (uninoculated PVK with TCP)
c
% Siderophore unit ¼ ArAsAs 100, Ar = Absorbance at 630 nm of reference; As = Absorbance at 630 nm of test sample
d
Ar = Absorbance at 630 nm of reference; As = Absorbance at 630 nm of test sample
e
Endophyte
Where, I = Per cent growth inhibition, C = Growth of fungus in control, T = Growth of fungus in treatment
b
Plant Growth-Promoting Rhizobacteria of Medicinal Plants in NW Himalayas:. . .
Table 19.2 Characterization of selected P-solubilizing bacterial isolates for quantitative estimation of plant growth promoting traits (Unpublished data from
AINP on biofertlizer, Solan centre)
403
404
19.9
A. Chauhan et al.
Application of PGPR
The application of plant growth-promoting rhizobacteria (PGPR) as crop inoculants
for biofertilization, phytostimulation and biocontrol is an attractive alternative to
reduce the use of chemical fertilizers which are costly inputs and also affect the
environment. Potential indigenous isolates from medicinal plants can be used as
biofertilizer/biostimulant/bioprotectant for protection of the endangered herbal
medicinal plants in their natural habitat by a systematic agro-technique. Inoculation
with efficient PGPR isolates has produced significantly positive effects on germination and growth (shoot, root length and biomass) of the plants.
The techniques for isolation (rhizobacteria and endorhizobacteria), screening for
PGP traits (P-solubilization, siderophore production, nitrogen fixation, hydrolytic
enzyme activity) and characterization (morphological, biochemical, physiological
and molecular) of PGPR of endangered medicinal plants of NW Himalayas are
depicted in Fig. 19.6. There is a further need to explore the varied agro-ecological
niches/habitat for the presence of native and new beneficial microflora associated
with medicinal plants. It is important to screen an ecoregion-specific PGPR strain
which can be used as potential plant growth promoter and bioprotectant. In studies
conducted on medicinal plants of trans-Himalayas under AINP on Biofertilizers
laboratory, Solan Centre, it has been found that the rhizosphere of Picrorhiza
kurroa, Podophyllum hexandrum and Valeriana jatamansi is a rich source of
potential PGPR strains with multifarious plant growth-promoting attributes.
These potential strains can be further explored for increasing growth parameters/
biomass/nutrient uptake under field conditions not only for parent host plant but
also for other agricultural crops because microflora associated with medicinal
plants possessed maximum number of PGP traits. The presence of specific and
limited population of PGPRs associated with medicinal plants unequivocally suggests the hypothesis that natural medicinal plant genotypic variants of a single
species can select specific microbial consortia as a result of their unique root
exudates profile which exerts selective influence in microbial colonization.
Our results revealed that the native strains rhizosphere of Valeriana, Podophyllum and Picrorhiza possessed a maximum number of PGP traits (Fig. 19.3) like
IAA production, phosphorus solubilization, in vitro antagonism to plant pathogens,
siderophore production and HCN production. These strains when further screened
to show their effect on growth promotion of tomato in terms of increase in growth
and biomass registered an increase of 22.6 % root length and 13.8 % of increase in
shoot length over control. In another study conducted under net house conditions
for plant growth-promoting attributes of the bacterial isolates of seabuckthorn
growing in trans-Himalayas (depicted in Fig. 19.7, AINP, Solan Centre), a significant increase in germination was observed from 87.5 % to 100 % when the seeds
were treated with SH35 and T2R (out of six PGPR isolates evaluated) as compared
to control and seedlings treated with other isolates, thus clearly indicating the
possible direct effect on seed germination in soil. However, for growth parameters,
T76* showed maximum per cent increase in shoot length (13.8 %), shoot dry weight
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Plant Growth-Promoting Rhizobacteria of Medicinal Plants in NW Himalayas:. . .
405
(29.5 %), root length (25.1 %) and root dry weight (33.3 %). All the three SH35, T2R
and T76* belonged to genus Bacillus and were isolated from stress environments
and can therefore be further explored as biofertilizer/bioprotectant for sustainable
agricultural practice under conditions of stressful environments. The increased
growth and biomass in seedlings raised from seeds treated with P-solubilizing
isolates may be attributed to the cumulative effect of phosphate solubilization,
nitrogen fixation and production of plant growth regulators.
A similar study was done elsewhere by Mundra et al. (2011), where a phosphatesolubilizing yeast strain PS4 identified as Rhodotorula sp. was isolated from the
rhizosphere of seabuckthorn (Hippophae rhamnoides L.) growing in the Indian
trans-Himalayas. The strain solubilizes Ca3(PO4)2 to a greater extent than FePO4
and AlPO4. The solubilization of insoluble phosphate was associated with a drop in
pH of the culture media. Inoculation of tomato seedling with the strain increased the
root and shoots length and fruit yield. Therefore, Rhodotorula sp. PS4 with
phosphate-solubilizing ability under stress conditions appears to be attractive for
exploring the plant growth-promoting ability for deployment as a microbial inoculant in stressed regions.
In another study conducted by Ghodsalavi et al. (2013) on Valeriana officinalis,
40 bacterial isolates showed different plant growth-promoting traits like production
of siderophores, indole acetic acid (IAA), hydrogen cyanide (HCN), lipase and
protease under in vitro conditions and growth promotion study under greenhouse
conditions. Rajasekar and Elango (2011) conducted field trials with microbial
consortium of Azospirillum, Azotobacter, Pseudomonas and Bacillus in combination or single inoculant application on Withania somnifera for two consecutive
years and recorded a significant increase in plant height, root length and alkaloid
content when compared to uninoculated control.
Malleswari and Bagyanarayana (2013) isolated 219 bacterial strains from the
rhizosphere sample from different locations of Andhra Pradesh and screened for
PGP activity like ammonia production, IAA production, phosphate solubilization,
HCN production and antifungal activity. They reported a significant increase with
inoculation of Pantoea sp., Bacillus sp. and Pseudomonas sp. on growth promotion
(germination and root/shoot length) of sorghum, maize and green gram.
We characterized 510 bacterial isolates from the rhizosphere of soybean, chickpea and wheat and from fresh vermicompost and vermicasts in central India.
Twelve bacterial isolates P2 (Bacillus amyloliquefaciens), P3 (Bacillus
megaterium), P4 (Bacillus subtilis), P6 (Bacillus subtilis), P10 (Bacillus subtilis),
P17 (Staphylococcus succinus), P25 (Lysinibacillus fusiformis), P26 (Dyella
marensis), P53 (Bacillus subtilis), P33 (Bacillus amyloliquefaciens), P41 (Bacillus
megaterium) and P48 (Bacillus licheniformis) showed multiple PGPR activities
in vitro and enhanced plant growth in vivo. 60 isolates shortlisted from above were
characterized for in vitro plant growth-promoting attributes. 70 % of the isolates
grew in N-free medium and 45 % solubilized phosphate. 76 % of isolates produced
IAA production, and none of them showed ACC deaminase activity. 83 % of the
isolates produced siderophores and 76 % of the isolates produced ammonia. Only
7 % isolates were HCN positive, and all of them were from wheat rhizosphere
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(AINP on Soil Biodiversity-Biofertilizers, IISS, Bhopal). In field studies, P3, P10
and P25 consistently performed well on soybean, chickpea and wheat. It will be
interesting to see how these strains from tropical vertisols perform in a different
rhizosphere (medicinal plants) in temperate climates.
In another study conducted for plant growth-promoting effect of PGP bacterial
isolates of Podophyllum hexandrum on tomato seedlings under growth chamber
conditions (AINP on Biofertilizer laboratory, Solan Centre), inoculation registered
a significant increase in root/shoot parameters. The effect of seed treatment by
Bacillus subtilis 2a1 improved the root length (90 %), shoot length (86.7 %), shoot
dry weight (334.5 %) and plant biomass (240.3 %) which was statistically significant as compared to other isolates. Bacillus subtilis strain 2a1 possessed maximum
PGP traits (IAA productivity, siderophore synthesis, chitinase activity, protease
activity, amylase activity and antifungal activity against Alternaria solani,
Dematophora necatrix, Sclerotium rolfsii and Phytophthora sp.)
Plant–microbe ecology is a complex system with all members interrelated.
Plants are always subjected to biotic and abiotic factors in their environment
which influence their growth and development. This is important from economical
point of view in most medicinal plants as these factors greatly affect the root
development and production. It is well known that rhizosphere and soil microorganisms (PGPR) play an important role in maintaining crop and soil health
through versatile mechanisms: nutrient cycling and uptake, suppression of plant
pathogens, induction of resistance in plant host and direct stimulation of plant
growth (Kloepper et al. 2004). Maintaining biodiversity of PGPR in soil is thus
an important component of environment-friendly sustainable agriculture strategies.
Some studies have demonstrated that agricultural practices affected the diversity
and function of rhizosphere and soil microorganisms. Therefore, the continued use
of growth-promoting rhizobacteria (PGPR) as inoculants is a promising solution for
environmentally friendly agriculture including the cultivation of medicinal plants.
19.10
Conclusions
Soil–plant–microbe interactions have been much studied in recent decades. Plant
species are considered to be one of the most important factors in shaping rhizobacterial communities, but specific plant–microbe interactions in the rhizosphere
require further studies to fully understand them. Plant-associated beneficial microorganisms or plant growth-promoting rhizobacteria (PGPRs) fulfil important functions in promoting plant growth and sustaining plant health (Walia et al. 2013).
Direct plant growth promotion by microbes is based on improved nutrient acquisition and hormonal stimulation (Walia et al. 2014). Diverse mechanisms are
involved in the suppression of plant pathogens which are often indirectly connected
with plant growth. Beneficial plant–microbe interactions have led to development
of microbial inoculants for use in agricultural biotechnology (Berg 2009). These
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Plant Growth-Promoting Rhizobacteria of Medicinal Plants in NW Himalayas:. . .
407
rhizospheric microorganisms are being exploited for their innumerable properties
and active metabolites (Tamilarasi et al. 2008).
This chapter provides an insight for the exploitation of beneficial plant–microbe
interactions and use of beneficial microorganisms occurring in their natural habitat
as biofertilizer. This offers an environmentally friendly strategy and is considered
as a potential tool for sustainable agriculture for enhanced production of medicinally important plants without creating any side effects. Such strategies will be
useful in reducing the use of chemical loads on plant production and a step forward
in the development of chemical-free herbals. However, the interactions among
PGPR and plants are still not well understood, especially in field applications and
different environments (Niranjan et al. 2005). Therefore, there is a need for
attention on the following aspects:
1. Many types of microorganisms are known to inhabit soil, especially rhizobacteria which play an important role in plant growth and development due to
a number of plant growth-promoting traits. More studies are needed on plant–
microbe interactions and their activities in different regions and ecologies,
including stressed ones. This will throw light on the exact mechanisms involved
in stimulation of plant growth in vivo through biologically active compounds,
potential competition between PGPR strains and indigenous soil microflora in
the rhizosphere of plants including medicinal plants. Availability of more
information will enable the development and widespread acceptance of new
inoculants and inoculation strategies that can improve soil ecology, plant development and resistance against diseases and pests.
2. Screening and application of root-colonizing rhizobacteria with enhanced colonizing potential is essential for developing sound strategies to manage the
rhizosphere in such a way that it becomes more difficult for pathogens to
colonize the rhizosphere; thus, these beneficial bacteria can engineer positive
interactions in the rhizosphere, control plant diseases and stimulate plant growth.
3. The question of whether medicinal plants grown ex situ in a different soil and
climatic zone and with applied fertilizers and organic manures in an integrated
way would have the same activity profile of the medicinally active ingredients as
those plants growing in the wild needs to be studied. If not, whether inoculation
of PGPR isolated from their native environments and inoculated on these ex situ
grown plants would help restore the activity profile needs to be assessed.
4. In their native wild, pristine habitat in the Himalayas growing in the adapted
soils and climatic zone, how would these plants respond to inoculation with
PGPR isolated from their own rhizosphere in situ? In case they respond in terms
of better growth, would there still be an improvement in the profile of active
ingredients? This would help to achieve the full potential of medicinal plants
even in their own habitats.
5. Is there a species endemism in PGPR like in rhizobia? How would medicinal
plants in the Himalayas respond to inoculation with PGPR from tropical crop
rhizosphere? Would they influence the profile of active ingredients in a similar
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A. Chauhan et al.
way as PGPR isolated from temperate soils from the rhizosphere of medicinal/
cultivated plants?
Acknowledgement We are grateful to the Indian Council of Agricultural Research, New Delhi,
for funding the investigations under the aegis of the All India Network Project on Soil
Biodiversity-Biofertilizers, IISS, Bhopal.
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Chapter 20
Biocontrol Activity of Medicinal Plants from
Argentina
Ver
onica Vogt, Javier A. Andrés, Marisa Rovera, Liliana Sabini,
and Susana B. Rosas
20.1
Introduction
Crops are easily infected by phytopathogenic fungi around the world, and fungal
diseases are hard to control without the use of synthetic fungicides. However, the
application of large quantities of chemicals in agriculture has the potential to exert
toxic effects on humans and wildlife as well as to cause environmental pollution
(Nguyen et al. 2009).
The intensive use of fungicides has resulted in major problems such as the
induction of resistance, altering the dynamic equilibrium of terrestrial and aquatic
ecosystems, the accumulation of toxic waste, elimination of natural enemies, the
death of humans and animals, household poisoning caused by exposure to toxic
substances or by eating foods with waste, pollution of virtually all components of
the biosphere, the emergence of new diseases, and the increase in production costs
(Alcalá de Marcano et al. 2005; Bajpai et al. 2007).
V. Vogt • S.B. Rosas
Laboratorio de Interacci
on Microorganismo—Planta, Facultad de Ciencias Exactas,
Fı́sico-Quı́micas y Naturales, Universidad Nacional de Rı́o Cuarto, Campus Universitario
X5804BYA, Rı́o Cuarto, C
ordoba, Argentina
J.A. Andrés (*)
Laboratorio de Interacci
on Microorganismo—Planta, Facultad de Ciencias Exactas,
Fı́sico-Quı́micas y Naturales, Universidad Nacional de Rı́o Cuarto, Campus Universitario
X5804BYA, Rı́o Cuarto, C
ordoba, Argentina
Laboratorio de Microbiologı́a Agrı́cola, Facultad de Agronomı́a y Veterinaria, Universidad
Nacional de Rı́o Cuarto, Campus Universitario X5804BYA, Rı́o Cuarto, C
ordoba, Argentina
e-mail: jandresjov@yahoo.com.ar; jandres@ayv.unrc.edu.ar
M. Rovera • L. Sabini
Departamento de Microbiologı́a e Inmunologı́a, Facultad de Ciencias Exactas,
Fı́sico-Quı́micas y Naturales, Universidad Nacional de Rı́o Cuarto, Campus Universitario
X5804BYA, Rı́o Cuarto, C
ordoba, Argentina
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR)
and Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7_20
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V. Vogt et al.
For that reasons, the discovery of new antifungal agents against fungal plant
pathogen with less toxic effects is desirable. Natural products obtained from plants
are an attractive alternative for disease control in agricultural crops since they can
be degraded by one or other organism.
The use of plants with therapeutic properties is as ancient as human civilization,
and for a long time, they were the main sources of drugs. In recent years, there has
been a growing interest in alternative therapies especially those derived from plants
(Rates 2001).
Often plant products used for the treatment of endemic infections served as a
starting point for researchers to find treatments for these diseases (Aqil et al. 2006).
The plant kingdom is extremely rich in biologically active compounds, and only
10–15 % of higher plant species have been studied to clarify, compare, and classify their
properties or determine the chemical structures of their active ingredients. The latter are
products or substances exerting a pharmacological action on the living body and are
found in low concentration in medicinal plants (Bisht et al. 2006; Wilkinson 2006).
However, these substances have the potential to exert toxic effects on humans
and wildlife as well as to cause environmental pollution. Within this context,
natural products from plants seem to be a good alternative since numerous plants
have the potential to control phytopathogenic fungi and have much prospect to be
used as a fungicide. Additionally, natural products are generally easily biodegradable. In many countries there are now available in the market pesticides based on
plant for the biological control of plant diseases. One example of those commercial
products is developed with neem (Azadirachta indica) (Dubey et al. 2009).
20.2
Use of Plants as Pesticides
The use of plant extracts for the management of plant diseases has gained importance in recent decades. They are relatively easy to obtain, are safe for the
environment and populations, and are easily broken down into agricultural systems.
Currently it is possible to extract substances from plants grown under natural
conditions or cultured in the laboratory to evaluate their insect antifeedant or
antimicrobial properties against fungi, bacteria, and viruses (Zarins et al. 2009).
Natural fungicides from plants are presented as an alternative for the control of crop
diseases. The use of extracts of several plant species is investigated in order to explore
their biological activities. In some cases, these extracts are able to safely replace,
completely or partially to conventional chemical fungicides (Meepagala et al. 2005;
Park et al. 2005; Aliero et al. 2006; Gulluce et al. 2007; Tabanca et al. 2007).
The active principles of plants are usually secondary metabolites, which are
relatively complex chemical structures, restricted and characteristic distribution of
the different vegetables. The functions of these metabolites include biochemical
defense to repel the aggression of herbivorous animals, fungi, and other microorganisms, attract pollinators, and adapt to situations such as water stress or lack of
light (Lira-Saldı́var 2003).
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A large number of secondary metabolites in plants are phenolic compounds that
can come from two biosynthetic pathways: polyacetates route, which originates
quinones, xanthones, orcinoles, and the shikimic acid pathway, where from the
synthesis of aromatic amino acids cinnamic acid synthesized as simple phenols and
derivatives, phenolic acids, coumarins, flavonoids, tannins, quinones, and lignans
(Lira-Saldı́var 2003).
Over a hundred different lignans have been described in different parts of plants,
including heartwood, bark, stems, roots, rhizomes, flowers, leaves, fruits, and seeds.
Furthermore, lignans can be secreted by the plant in the form of resin. Lignans
play an important role in the defense of plants against pathogens and predators.
They were reported as chemicals with effects on bacteria, fungi and viruses
(Rı́os et al. 2002).
In species of the Asteraceae and Piperaceae families has been isolated the lignan
sesamolin, which has inhibitory activity of the monooxygenase enzyme. This
enzyme is present in insects, such as Ostrinia nubilalis, which attack crops of
economic importance in Europe (Bernard et al. 1989).
Other lignans, nordihydroguaiaretic acid (NDGA) and methyl NDGA isolated
from leaves of Larrea tridentata, inhibit the growth of Aspergillus flavus and Aspergillus parasiticus in a concentration of 500 mg ml–1 (Vargas-Arispuro et al. 2005). In
another study, these two compounds at concentrations of 10 and 25 μM completely
inhibited β-1,3-glucanase enzyme that plays an important physiological role in the
development process and fungal differentiation (Vargas-Arispuro et al. 2009).
The lignan 8,80 -bis-(methylenedioxy) cinnamic acid has been reported to be a
powerful competitive inhibitor of the enzyme lignin peroxidase of the fungus
Phanerochaete chrysosporium and Phlebia radiata. The accumulation of some
lignans in the trunks of the trees is a chemical defense strategy of the plant to
inhibit fungal enzymes involved in the degradation of wood (Frı́as et al. 1995).
NDGA also presents allelopathic activity and is responsible for inhibiting the
growth of other species around Larrea tridentata. A study conducted in vitro lignan
found that this dramatically reduces root growth of seedlings of barnyard grass,
green foxtail, perennial ryegrass, annual ryegrass, red millet, pigweed, lettuce, and
alfalfa (Elakovich and Stevens 1985).
20.3
Medicinal Plants of Argentina
The central region of Argentina has a rich and varied flora, little studied in the
search for antifungal compounds of plant application. Of the wide range of plants,
seven species were selected as features that stand out places to study their activity
against phytopathogenic fungi. Different extracts of Achyrocline satureioides,
Aspidosperma quebracho blanco, Larrea cuneifolia, Larrea divaricata, Maytenus
vitis-idaea, Minthostachys verticillata, and Verbascum thapsus were studied
in vitro and in vivo on phytopathogenic growth affecting crops of regional importance and were also evaluated for their safety in seedlings.
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20.3.1 Botanical Description and History of the Species
Under Study
20.3.1.1
Genus Achyrocline
This genus includes 32 species distributed in tropical regions of South America and
Africa. The main native species are A. satureioides, A. alata, A. flaccida, and
A. tormentosa. Members of this genus are herbs or shrubs, with a dense undercoat,
erect stems, often branched. The leaves are simple, alternate, and longer than the
wide (linear) sheet.
Achyrocline satureioides, popularly known as “marcela” or “marcela del
campo” is a sub-bush that belongs to the family Asteraceae and is widely used in
South America (Rivera et al. 2004). Experimental studies have shown
hepatoprotection (Kadarian et al. 2002), antioxidant (Desmarchelier et al. 1998),
antitumor and cytotoxic (Ruffa et al. 2002), antiviral (Zanon et al. 1999), and
immunomodulatory properties (Cosentino et al. 2008). In spite of the widespread
biological activities investigated for A. satureioides aerial part, there is no report of
the activity on fungal plant pathogens growth.
20.3.1.2
Genus Larrea
This genus is composed of species of woody evergreen shrubs with a wide geographical distribution in the large hot deserts of America, covering large arid and
semiarid regions of Argentina, Chile, Bolivia, Peru, Mexico, and the southwestern
United States. It contains five species (Larrea ameghinoi, L. cuneifolia,
L. divaricata, L. nitida and L. tridentata), of which the first four are found in
Argentina (Sakakibara et al. 1976).
A common feature of all members of the genus is that they have resin blades.
This resin has been of interest because it represents 10–15 % of the dry weight of
the leaves. The composite material is approximately 50 % by NDGA and the
remaining 50 % of flavonoids plus waxy substances (Horn and Gisvold 1945;
Waller and Gisvold 1945; Gonnet and Jay 1972; Sakakibara et al. 1976).
In L. cuneifolia, Valesi et al. (1972) identify the following structure flavonoids:
quercetin 3,7,30 ,40 -tetramethyl ether, quercetin 3,7,30 -trimethyl ether, quercetin
3,7,40 -trimethyl ether, quercetin 3,7-dimethyl ether, quercetin 3,30 -dimethyl ether,
quercetin 7,30 -dimethyl ether, quercetin 3-methyl ether, kaempferol 3,7-dimethyl
ether, kaempferol 3-methyl ether, apigenin 7-methyl ether, and apigenin.
Other studies in this specie report the presence of proteins (Trione and Ruiz Leal
1972), essential oil composed of monoterpenes, phenylpropanoids, sesquiterpenes
(Bohnstedt and Mabry 1979), and flavonoids in leaves (Timmermann 1979).
Larrea divaricata (jarilla) is a perennial woody shrub with a wide distribution in
Argentina and has long been used for its medicinal and aromatic properties. It is
frequently used in traditional medicine as anti-inflammatory, antirheumatic,
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febrifuge, and as a pest control agent and is a plant with reports of traditional
antifungal use (Goleniowski et al. 2006; Svetaz et al. 2010). Recently, the water
extract of L. divaricata was found to decrease proliferation and induced apoptosis
of lymphoma cell line (Davicino et al. 2010), and the alcoholic extract has been
reported to exert antibacterial activity (Zampini et al. 2007) and antifungal activity
against yeast and filamentous dermatophytes (Svetaz et al. 2010). Phytochemical
studies had reported the presence of lignans, essential oils, flavonoids, and glycosides (Mabry et al. 1977).
20.3.1.3
Genus Verbascum
This genus is native to Europe and Asia and is composed of about 250 species. They
are biennial or perennial, and rarely annuals or subshrubs plants will reach 0.5–3 m
high. The leaves are arranged spirally and they have a lot of hairs. The flowers have
five symmetrical petals: yellow or white, orange, brown, red, purple, and blue. The
fruit is a capsule containing numerous seeds.
Verbascum thapsus is a medicinal plant popularly known as “common mullein.”
It has been used for the treatment of inflammatory diseases, asthma, spasmodic
coughs, diarrhea, and other pulmonary problems. Although it is native from Europe
and Asia, it was introduced in America several times (Turker and Camper 2002).
This plant is reported to be active against influenza virus (Mehrotra et al, 1989),
bovine herpesvirus type 1 (Mc Cutcheon et al. 1995), bacteria (Turker and Camper
2002), fungi (Mc Cutcheon et al. 1994), and against mosquito larvae (Gross and
Werner 1978). In spite of the numerous studies made of mullein, antifungal activity
against plant pathogens has not been investigated.
20.3.1.4
Genus Aspidosperma
The genus Aspidosperma is from South America and comprises about 80 species,
distributed in tropical and subtropical regions. It consists of large or medium trees,
with simple leaves, alternate, opposite, or whorled. The most important species in
Argentina is A. quebracho blanco, dwelling from the north to the Midwest. It is
used in carpentry for being trees with very good quality wood as firewood, fencing
poles, and rods. It is traditionally used as febrifuge, antiasthmatic, in cardiac
dyspnea and an appetizer. Leaves and shoots were cited as abortion, contraception,
hepatoprotective, blood purifier, and against colics. The database shows that the
genus Aspidosperma is known to be a rich source of indole alkaloid compounds and
tannins (Deutsch et al. 1994; Landau et al. 2000).
In the case of A. quebracho blanco, studies to evaluate their bioactivities are
scarce, reporting only antimalarial activity (Bourdy et al. 2004).
mkumar9@amity.edu
418
20.3.1.5
V. Vogt et al.
Genus Maytenus
Maytenus is a genus of trees which has about 200 species of which 11 are in
Argentina. Species of the genus grow in a variety of climates from tropical to
subpolar. It is widely distributed in America, Africa, and South Asia (Alonso and
Desmarchelier 2007).
Las hojas y tallos preparados en infusi
on son empleados en caso de úlceras
sangrantes, hipertensi
on arterial, dolores articulares, como depurativo, contra el
asma y como antitumoral; la raı́z es utilizada como diurético (Bueno et al. 2009).
The specie M. vitis-idaea is known as “colquiyuyo,” “ibirá-Yuqui,” “salt of the
Indian,” “fat meat,” and “salty logging,” among others. In traditional medicine it is
used as an astringent, ophthalmic, and antiasthmatic contraceptive. This species is
very important in maintaining the ecological balance, primarily for the restoration
of degraded forest areas in the original because of its rapid turnover of organic
matter (Bueno et al. 2009).
One study reports that compounds isolated from the root bark of M. vitis-idaea
have insecticidal effects, antifeedant and growth regulator on larvae of the codling
moth. Aqueous extracts from fresh and dried leaves showed the presence of nonhydrolizable or condensed tannins. These are responsible for the astringency of the
leaves and they may be used as antiviral and antioxidant compounds (Vonka and
Chifa 2008).
20.3.1.6
Genus Minthostachys
Plants of the genus are aromatic shrubs and climbers up to 3 m high. Some species
are used in South American countries as a condiment to flavor foods and in the
treatment of respiratory diseases. Moreover, infusions or oils of this genus have
been used as digestive, sedative, and as a topical antifungal and antiparasitic.
Decoctions have also been used to protect stored potatoes against insects
(Schmidt-Lebuhn 2008).
This plant lives in the central and northern Argentina. The leaves, stems and
flowers are used in many preparations, from teas to spirits. The applications range
from peppermint tea to liquor. In addition, M. verticillata is a commercially
important source of essential oil. Stimulant, digestive, carminative, vulnerary,
antispasmodic, and antirheumatic are attributed to this plant (Schmidt-Lebuhn
2008).
Some studies report on antibacterial and antiviral properties (De Feo et al. 1998)
and that the oil is the most active fraction against bacteria (Primo et al. 2000). Other
authors reported antiviral activity against herpesvirus type I (Zanon et al. 1999) and
immunomodulatory and antiallergic properties in human cell lines (González
Pereyra et al. 2005).
mkumar9@amity.edu
20
Biocontrol Activity of Medicinal Plants from Argentina
20.4
419
Obtention of Plant Extracts and Antifungal Activity
Plants of different species under study were collected manually, following the
instructions of the World Health Organization for the collection of medicinal
plants.
The aerial part was left dried, powdered, and successively extracted for 48 h at
room temperature in n-hexane (HE), methanol (ME), and chloroform (CE). Warm
aqueous extract (WAE) was obtained when plant material was extracted with water
at 70 C for 48 h. Extracts were concentrated to dryness and dissolved in dimethyl
sulfoxide (DMSO) to give a concentration of 100 mg ml–1.
The microorganisms used for the antifungal evaluation were the following plant
pathogens of economic importance in agriculture: Fusarium graminearum, Fusarium solani, Fusarium verticillioides, Macrophomina phaseolina, and Sclerotium
rolfsii.
20.4.1 Agar Dilution Method
The extracts were added to molten potato dextrose agar (PDA) to obtain a final
concentration of 1,000 μg ml 1 and then pour in to the Petri dishes (9.0 cm in
diameter). A 4 mm diameter plug of actively growing fungi, taken from PDA plates,
was placed onto the center of Petri dishes; treatments were incubated at 30 C.
Each treatment was tested in triplicate and experiment was repeated three times.
Parallel negative controls were included by mixing DMSO with PDA medium.
Sensitivity of each fungal species to each tested extract was calculated as percentage of mycelia growth inhibition, according to Pandey et al. (1982).
The chloroform extracts of L. cuneifolia and L. divaricata inhibited the growth
of the microorganisms tested between 54.6 and 98.9 %. At the concentration of
1,000 mg ml 1, the L. divaricata extract showed a high inhibitory effect on the
radial growth of all pathogens. The effect of L. cuneifolia extract was also high,
inhibiting fungal growth: S. rolfsii (98.9 %), M. phaseolina (91.6 %),
F. verticillioides (81.8 %), F. graminearum (65.1 %), and F. solani (58.0 %).
Due to the high inhibitory activities shown by these extracts, they were again tested
at lower concentrations (500, 300, 100, and 50 μg ml–1). Macrophomina phaseolina
was the most sensitive fungus.
Other extracts showed high antifungal activity. Thus, the methanol extract of
L. cuneifolia significantly reduced the growth of F. graminearum, F. verticillioides,
S. rolfsii, and M. phaseolina; the hexane extract of L. cuneifolia inhibited
F. verticillioides, M. phaseolina, and S. rolfsii. The hexane extract of
A. satureioides significantly decreased the growth of S. rolfsii, M. phaseolina, and
F. verticillioides, while the chloroform extract of this species inhibited
F. graminearum, M. phaseolina, and S. rolfsii. The hexane extract of
M. verticillata exerted strong inhibition on the growth of M. phaseolina.
mkumar9@amity.edu
420
V. Vogt et al.
Among the extracts that showed moderate inhibitory activity against at least one
of the tested fungi is the chloroform extract of A. quebracho blanco, which only
inhibited M. phaseolina.
Several investigators have used the same methodology for the study of plant
fractions on the growth of phytopathogenic fungi. This is how Tegegne et al. (2008)
evaluated in assays in vitro activity of different extracts of the plant species
Agapanthus africanus. In their results, the growth of S. rolfsii was inhibited
100 % by the methanol extract of the roots, leaves, and flowers to the concentration
of 1,000 mg ml 1. Also evaluated is the antifungal effect of ethanol extracts of
L. divaricata and L. cuneifolia, and results were similar to those found by our group
(Table 20.1).
20.4.2 Broth Dilution Method
Potato dextrose broth (PDB) was prepared for estimation of M. phaseolina mycelial
yield at 1,000, 500, and 100 μg ml–1 of HE, ME, CE, and WAE. Flasks containing
20 ml of PDB (potato dextrose broth) with appropriate volume of extracts were
inoculated with three agar blocks (each of 2 mm diameter) taken from a PDA plate
of actively growing fungi and were incubated at 30 C for 3 days. Thereafter,
cultures were filtered through pre-weighed Whatman filter paper No. 1. Mycelial
yield was determined after drying the mycelial at 75 C for 5 days. Percent loss/gain
in mycelial dry weight was calculated according to Dubey et al. (2009).
In this test, the majority of the tested extracts inhibited the growth of
M. phaseolina and S. rolfsii in liquid medium. Among the extracts that exerted
inhibition greater than 20 % at the concentration of 100 mg ml 1, the methanol
extract of L. cuneifolia stands decreased the growth of M. phaseolina and S. rolfsii.
There are no previous reports of the use of this methodology with extracts of the
plant species we studied. Dubey et al. (2009) found a high inhibition in the
production of mycelium from the aqueous extract of the bark and leaves of
Azadirachta indica (neem) at 10 % concentration in Czapek Dox broth
(Table 20.2).
20.5
Phytotoxicity Assay
A bioassay based on germination, radicle, and epicotil growth of Lycopersicon
esculentum Mill. (tomato) and Triticum aestivum (wheat) was used to study the
allelopathic effects of extracts when applied at a concentration of 1,000 μg ml–1.
Seeds were surface disinfected and then placed on Petri dishes (20–40 seeds per
dish) containing a layer of Whatman filter paper on cotton, which had previously
been impregnated with 20 ml of extract solution dissolved in distilled water or 1 %
DMSO (control). Dishes were then incubated at 25 C for 3 days for T. aestivum and
mkumar9@amity.edu
Concentration
(μg ml–1)
mkumar9@amity.edu
Fusarium
solani
Fusarium
verticillioides
Macrophomina
phaseolina
Sclerotium
rolfsii
43.0 5.9a
46.8 7.9a
17.4 7.7b
20.6 1.1a
9.4 1.3c
13.2 2.9b
52.9 2.4a
39.0 4.0b
8.9 1.6c
57.2 6.8a
62.6 7.2a
39.3 9.3b
49.9 6.7a
47.1 6.9a
17.8 6.9b
8.0 2.2c
14.7 4.3ab
7.2 2.9c
19.0 2.7a
3.1 1.5b
6.3 0.6a
N.I.
1.4 3.8b
10.4 3.3b
21.7 4.3a
8.6 5.1b
9.3 2.7b
13.0 2.5c
43.9 5.5a
24.3 4.0b
N.I.
4.1 2.8a
12.1 5.3a
6.3 2.3a
11.7 0.9a
35.2 4.6b
65.1 6.5a
49.3 1.8b
44.1 1.4b
62.8 6.7a
13.3 3.6c
27.9 1.2b
58.0 4.2a
30.9 1.1b
19.5 0.3c
31.4 5.7b
9.4 1.0d
57.1 0.6c
81.8 0.7a
73.1 0.1b
69.4 0.8b
69.4 3.7b
33.7 4.9d
65.0 3.9c
91.6 3.5a
71.6 3.2c
59.6 1.8d
76.8 5.8b
14.2 4.2e
72.1 5.9b
98.9 3.2a
5.3 3.7d
71.0 5.4a
63.3 7.7a
56.2 2.5b
25.2 3.8c
5.1 3.5d
54.6 6.5a
41.2 2.2b
26.6 6.3c
3.0 2.1d
13.8 4.9d
80.6 1.3a
65.9 4.2b
48.2 2.8b
23.3 6.4c
13.3 4.2c
91.1 5.8a
87.2 8.0a
81.8 1.7a
25.2 6.1b
7.1 6.1c
96.8 4.7a
85.1 9.0a
48.3 6.2b
8.3 6.5b
NI
2.9 2.0
1.7 1.0
NI
NI
76.0 6.3b
36.7 6.5c
421
Achyrocline satureioides
HE
1,000
CE
1,000
WAE
1,000
Aspidosperma quebracho blanco
HE
1,000
CE
1,000
ME
1,000
WAE
1,000
Larrea cuneifolia
HE
1,000
CE
1,000
500
300
ME
1,000
WAE
1,000
Larrea divaricata
HE
1,000
CE
1,000
500
300
ME
1,000
Maytenus vitis-idaea
CE
1,000
Inhibition (%)
Fusarium
graminearum
Biocontrol Activity of Medicinal Plants from Argentina
Plant species and
extracts
20
Table 20.1 Effect of plant extracts against plant pathogenic fungi growth
(continued)
mkumar9@amity.edu
Concentration
Plant species and
(μg ml–1)
extracts
ME
1,000
Minthostachys verticillata
HE
1,000
CE
1,000
ME
1,000
WAE
1,000
Verbascum thapsus
HE
1,000
CE
1,000
ME
1,000
WAE
1,000
Control captan
643
422
Table 20.1 (continued)
Inhibition (%)
Fusarium
graminearum
NI
Fusarium
solani
NI
Fusarium
verticillioides
5.4 2.1
Macrophomina
phaseolina
NI
Sclerotium
rolfsii
NI
61.9 6.3a
63.2 6.6a
33.4 3.9b
25.2 4.0c
14.7 3.4a
15.1 3.1a
0.9 1.9b
0.5 4.7b
50.5 4.9b
69.2 6.5a
17.3 4.3c
10.5 1.8d
43.1 6.4a
39.5 4.9a
16.2 6.5b
13.0 7.6b
36.7 7.2b
57.6 6.1a
6.1 6.5d
15.1 6.4cd
34.5 2.1c
44.0 2.9b
56.3 4.1a
8.1 2.7d
88.3 0.7
NI
NI
29.6 6.9a
0.9 5.0b
91.1 4.8
17.7 1.6b
14.3 3.8bc
36.6 6.5a
2.2 5.7d
94.4 1.9
21.0 1.5b
26.3 2.8b
56.8 1.8a
NI
100.0 0.0
20.4 0.7b
14.9 3.3b
49.1 6.8a
NI
100.0 0.0
Agar dilution method
HE hexanic extract, CE chloroformic extract, ME methanolic extract, WAE warm aqueous extract, NI no inhibition
b
Values within the same column, and for each plant, followed by the same letter do not differ significantly ( p < 0.05) according to the Turkey test
a
V. Vogt et al.
20
Biocontrol Activity of Medicinal Plants from Argentina
423
Table 20.2 Effect of plant extracts against plant pathogenic fungi growth
Plant species and extracts
Achyrocline satureioides
HE
CE
WAE
Aspidosperma quebracho blanco
HE
CE
ME
WAE
Larrea cuneifolia
CE
ME
Larrea cuneifolia
WAE
Larrea divaricata
HE
CE
ME
Maytenus vitis-idaea
CE
ME
Minthostachys verticillata
Concentration
(μg ml 1)
Inhibition (%)
Macrophomina
phaseolina
Sclerotium
rolfsii
1,000
500
100
1,000
500
100
1,000
96.6 0.3ª
59.0 2.9b
53.2 7.0b
94.3 1.0a
49.6 6.3b
26.2 20.0c
8.5 12.0d
66.0 15.1ª
35.6 10.2b
NI
57.7 18.2ª
NI
NI
18.6 9.4b
1,000
1,000
1,000
1,000
NI
42.0 5.6ª
48.3 6.0a
NI
NI
30.1 4.2ª
35.8 7.1ª
1.9 4.6b
1,000
500
100
50
25
1,000
500
100
50
99.2 0.4ª
98.3 0.4ª
98.0 0.6ª
61.0 0.9b
43.8 5.0c
99.7 0.1ª
86.1 7.8ª
21.9 9.3c
NI
98.1 0.5ª
96.4 2.3ª
95.3 1.5ª
54.6 10.2b
30.0 10.8b
1,000
500
96.0 1.0a
25.6 8.0b
11.7 4.5
NI
1,000
1,000
500
100
50
25
1,000
500
100
8.5 1.8d
97.8 2.7ª
92.8 2.2ª
83.1 5.8ª
35.0 2.6b
26.8 3.7c
83.3 8.7ª
48.2 4.6b
19.3 8.0c
NI
97.6 0.2ª
96.1 1.1ª
79.6 1.2ab
69.0 3.8b
45.8 10.3b
88.4 2.5ª
19.9 10.8c
NI
1,000
1,000
NI
NI
NI
NI
(continued)
mkumar9@amity.edu
424
V. Vogt et al.
Table 20.2 (continued)
Plant species and extracts
HE
CE
ME
WAE
Verbascum thapsus
HE
CE
ME
WAE
Control captan
Concentration
(μg ml 1)
1,000
500
100
1,000
500
1,000
1,000
1,000
1,000
500
1,000
500
1,000
643
64.3
6.43
Inhibition (%)
Macrophomina
phaseolina
99.5 0.5ª
64.0 9.8b
7.2 9.0c
97.6 2.2ª
61.6 8.7b
0.2 7.2c
NI
40.1 6.8b
82.5 8.4ª
25.6 1.3c
66.2 8.2ª
NI
97.3 1.4ª
97.2 0.8ª
52.6 8.7b
Sclerotium
rolfsii
98.0 0.3ª
97.8 0.9ª
9.3 10.0b
96.1 2.9ª
93.2 4.3ª
NI
20.5 14.3b
NI
38.4 7.3b
N.I.
66.6 9.8ª
25.0 9.3b
25.4 4.5b
99.0 0.1ª
88.7 10.0a
39.2 10.7b
Broth dilution method
a
HE hexanic extract, CE chloroformic extract, ME methanolic extract, WAE warm aqueous
extract, NI no inhibition
b
Values within the same column, and for each plant, followed by the same letter do not differ
significantly ( p < 0.05) according to the Turkey test
7 days for L. esculentum. Three replicates were carried out for each assay. The
number of germinated seeds was determined according to the 2 mm radicle
extrusion criterion. Radical and epicotyl growth were measured in twenty germinated seeds.
The possible toxic effect of the extracts was evaluated on some plant species, as
suggested Macias et al. (1999). These authors recommend conducting such trials on
L. esculentum, T. aestivum, Lactuca sativa L., Daucus carota L., Lepidium sativum
L., Allium cepa L., Hordeum vulgare L., and Zea mays L. since they have low
coefficient of variation in growth medium and high values in the parameters of
epicotyl and root length. All these species are called together by the authors as
standard species or “standard target species” for the development of bioassays in
allelopathic phytotoxicity studies.
Plant extracts variously affect germination of L. esculentum and growth parameters evaluated. Some of the extracts increased epicotyl length only, as with the hot
aqueous extract of A. satureioides, others stimulated root growth, as the methanol
extract of M. verticillata and hot aqueous extract of V. thapsus, while in other cases
both parameters were positively affected, as with the hexane extract of V. thapsus
and aqueous extracts of L. cuneifolia and A. quebracho blanco.
mkumar9@amity.edu
20
Biocontrol Activity of Medicinal Plants from Argentina
425
Among the extracts that significantly reduced some of the evaluated parameters
are the hot aqueous extract of L. cuneifolia, the methanol extract of M. vitis-idaea,
the aqueous extract of A. satureioides, the hexane and methanol extracts of
A. quebracho blanco, the methanol extracts of V. thapsus and L. cuneifolia, the
hexane extract of L. divaricata, and the hot aqueous extract of M. verticillata.
Some extracts showed high toxicity. These include the hexane extract of
A. satureioides, the aqueous extract of A. quebracho blanco, the chloroform and
methanol extracts of L. cuneifolia, the methanol extract of L. divaricata, and the
hexane and chloroform extracts of M. vitis-idaea and M. verticillata.
The results obtained by germinating seeds of T. aestivum with plant extracts
showed, as in L. esculentum, various effects. So, the hot aqueous extracts of
A. satureioides, A. quebracho blanco, and L. cuneifolia and the hexane and chloroform extracts of M. vitis-idaea and the hexane extract of V. thapsus increased root
length and epicotyl.
At the other end, the chloroform and methanolic extracts of L. cuneifolia, the
chloroform extract of L. divaricata, and the hexane and methanolic extracts of
M. verticillata negatively affected all parameters, showing a considerable toxicity
at the concentrations tested.
As the chloroform extract of L. divaricata was one that showed higher antifungal
activity and at the same time proved toxic to L. esculentum and T. aestivum, it was
evaluated at lower concentrations in order to find a concentration that maintains the
antifungal capacity without toxic effect on the germination of the crop. The results
showed that a concentration of 100 mg ml–1 was the appropriate (Vogt 2011).
Dicot specie L. esculentum was more sensitive than T. aestivum in certain
parameters on germination and seedling growth. This result is similar to that
obtained by other authors (Gonçalves et al. 2009).
20.6
Isolation and Structural Identification of Secondary
Metabolites of Larrea divaricata
The chloroformic extract was subjected to flash chromatography on silica gel,
eluting with n-hexane, n-hexane-EtOAc with increasing polarity mixtures, and
EtOAc–MeOH (97:3) to afford 36 fractions. The n-hexane-EtOAc (7:3) fraction
was purified by column chromatography on Sephadex LH-20 eluting with MeOH to
give 23 fractions. Each fraction obtained from Sephadex column was monitored by
TLC (C6H6–dioxane-AcOH 30:5:1), and fractions 6–7 were separated and purified
by TLC (C6H6–AcOH 8.5:1.5) to furnish compound 1 (11 mg). Fractions 10–11
were separated and purified by TLC (C6H6–AcOH 8.5:1.5) to furnish compound
2 (10 mg). Fractions 12–20 were separated and purified by TLC (C6H6–AcOH
8.5:1.5) to furnish compound 3 (9 mg). Their structures were determinated by
spectroscopic methods and comparison with authentic samples (NMR spectra:
Bruker-Avance-200 instrument, 1H NMR: 200 MHz, 13C NMR: 50 MHz, CDCl3
mkumar9@amity.edu
426
V. Vogt et al.
as solvent. Mass spectra: EIMS, ionization energy 70 eV, Finnigan-Mat-GCQ ion
tramp instrument).
Results of the in vitro evaluation indicate that the chloroform extract was active
against all the fungi tested, and F. graminearum and M. phaseolina were the most
sensitive species. The n-hexane extract was inactive against the fungi tested and
methanol extract inhibited M. phaseolina only (Vogt et al. 2013).
The differences in the inhibition effect of the extracts may be due to the lignans
compounds present in L. divaricata, which had similarity to the chloroform solvent.
In relation with the n-hexane extract, lower inhibition activity indicates that there
were interactions among nonpolar inactive structures (Jasso de Rodrı́guez
et al. 2011).
Previously antifungal activity was described in L. divaricata. Svetaz et al. (2010)
studied L. divaricata ethanolic extract against dermatophytes of high incidence in
superficial infections. Author’s results were similar to the inhibitions obtained with
chloroform extract by our group.
In the chloroform extract from L. divaricate, we detected the presence of
flavonoids and lignans. Three compounds were isolated using chromatographic
methods and identified by spectroscopic methods in this extract: Apigenine-7methylether, nordihydroguaiaretic acid, and 3,4-dihydroxy-3,4-dimethoxy-6,7cyclolignan. The latter compound is described for the first time in the species and
it was the most active against F. graminearum on in vitro tests (Fig. 20.1).
On infected pots, this compound was more effective than L. divaricata
chloroformic extract reducing damping-off preemergence in 14 % (5 day after
emergence) and postemergence in 11 % (15 days postemergence). Disease developed extensively in roots and subcrown internodes and less in leaf sheaths of
15 days wheat plants. Data showed that treatment with this compound significantly
reduced severity of symptoms of F. graminearum crown rot as compared with the
non-treated controls.
Fig. 20.1 Chemical
structure of 3,4-dihydroxy3,4-dimethoxy-6,7cyclolignan isolated from
Larrea divaricata Cav
mkumar9@amity.edu
20
Biocontrol Activity of Medicinal Plants from Argentina
20.7
427
Conclusions
The use of plant products for the management of plant diseases has achieved greater
significance in recent years due to its readily available nature, antimicrobial activity, easy biodegradability, and lower phytotoxicity, besides inducing resistance in
host. The species studied are part of the traditional flora of the central region of
Argentina, and the results help to characterize and extend the available information
on the biological activities of the same. It is important to continue investigating the
biological properties of these species and identify the active compounds that are
present in the extracts.
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mkumar9@amity.edu
Index
A
Abacopteris multilineata, 80
Abelmoschus moschatus, 30
Abiotic stresses, 167
Abscisic acid (ABA), 61, 173
Acacia sp., 347
A. baileyana, 347
A. floribunda, 347
A. podalyriifolia, 347
Acaligenes sp., 75
Acaulospora sp., 9, 26, 28, 29, 91
A. cavernata, 25
A. laevis, 294
A. nicolsonii, 25
A. scrobiculata, 25
A. spinosa, 25
Acetobacter sp., 263, 398
A. diazotrophicus, 391
Achromobacter xylosoxidans, 8, 95, 182
Achromobacter xylosoxidans + Azospirillum
lipoferum, 95
Achyrocline satureioides, 416, 419, 424, 425
Acidobacteria, 21–24
Acidobacterium, 75
Acidovorax sp., 234
Acinetobacter sp., 3, 22, 24, 263
A. calcoaceticus, 21, 22, 312
Aconitum sp., 233
Acorus calamus, 137, 233
Acremonium alternatum, 241
Acrodontium crateriforme, 241
Actinobacteria, x, 22–24, 353
Actinomycetes, 22
A. delicate, 25
A. denticulate, 26
Adhatoda vasica, 80, 141, 233
Aecidium withaniae, 236
Aegle marmelos, 137
Aeromonas hydrophila, 75
Agapanthus africanus, 420
Agathosma betulina, 23, 29
Agrobacterium sp., 2, 22, 24, 74, 144, 234, 251,
330, 383
Ajmalicine, 5, 64, 293
Ajuga bracteosa, 22, 24
Alcaligenes (Ralstonia), 330
Alcaligenes sp., 3, 113, 263
Alkaloids, 33, 54, 60, 64, 342
Allenrolfea occidentalis, 208
Allium
A. cepa L., 80, 424
A. sativum, 80, 233
Allorhizobium sp., 2, 3, 74, 248, 306
Aloe
A. barbadensis, 27, 233
A. vera, 23–25, 116, 138, 233
A. vera (L.) Burm.f, 142
Alphaproteobacteria, 76
Alternaria sp., 346, 348, 401
A. alternata, 236, 398
A. brassicicola, 26
A. destruens, 349
A. porri, 347
A. solani, 388, 406
A. tenuissima, 236
Althaea officinalis, 237
Amaranthus caudatus, 185
Ambispora leptoticha, 25
Ambrosia artemisiifolia, 48
AM colonisation, 32
© Springer International Publishing Switzerland 2015
D. Egamberdieva et al. (eds.), Plant-Growth-Promoting Rhizobacteria (PGPR) and
Medicinal Plants, Soil Biology 42, DOI 10.1007/978-3-319-13401-7
mkumar9@amity.edu
431
432
Index
1-Aminocyclopropane-1-carboxylate (ACC)
deaminase, 51, 82, 149, 254, 297
Aminthas sp., 72
Ammi majus, 233
Ammolei majus, 201
Ammoniacal content, 361
Ammonium molybdate, 393
Ampelomyces quisqualis, 241
Amplified ribosomal DNA restriction
analysis, 370
Andrographis paniculata, 25, 139, 233, 350
Andrographis paniculata Nees, 291
Anethum graveolens L., 237, 291, 292
Aneurinibacillus aneurinilyticus, 401
Angelica
A. dahurica, 33
A. sinensis, 21, 22
Annona squamosa, 23, 80
Anthropogenic activities, 323
Antiallergic properties, 418
Antiasthmatic, 417, 418
Antibiosis, 242
Antibiotics, 255
Anticancer, 353
Antimycotics, 342
Antioxidants, 33, 135, 327, 353
Antirheumatic, 418
Apigenine-7-methylether, 426
Aporrectodea
A. caliginosa, 75, 76
A. longa, 72
Arabidopsis sp., 177
A. thaliana, x, 4, 314
Arachis hypogaea, 143, 150
Arbuscular mycorrhizal (AM) fungi, 26, 33, 64
Archaeospora sp., 29
A. leptoticha, 26
Archangium sp., 23
Arctium lappa, 237
A. rehmi, 25
Argyranthemum frutescens, 80
Arnica montana, 25
Artemisia
A. annua, 26, 28, 186, 293
A. annum, 233
A. dracunculus, 237
Artemisia annua L., 291
Arthrobacter sp., 3, 44, 74, 81, 113, 144, 263,
289, 295, 330, 386
Ascomycetes, 347
Ascorbic acid, 171
Asparagus racemosus, 140, 233
Aspergillus sp., 117, 222, 346, 392
A. flavipes, 347
A. flavus, 236, 415
A. fumigatus, 23, 30
A. niger, 30, 236, 347
A. parasiticus, 415
A. verocosa, 236
Aspidosperma sp., 417
A. quebracho blanco, 415, 417, 424, 425
Astragalus membranaceus, 23, 24
Astringent, 418
Atractylodes lancea, 22, 25, 29
Atriplex halimus, 201
Atropa sp.
A. acuminata, 233
A. belladonna, 217, 328
Aureobasidium sp., 347
Auxins, 45
Azadirachta indica, 25, 80, 140, 142,
243, 344
Azoarcus sp., 75, 263, 391
Azorhizobium sp., 2, 3, 74, 248, 306
Azospirillum sp., x 3, 8–10, 23, 24, 44, 46, 71,
99, 113, 114, 116, 117, 144, 148, 149,
152, 178, 221, 248, 252, 254, 263, 289,
292, 293, 306, 312, 330, 386, 391, 405
A. brasilense, 50, 59, 63–65, 92, 148, 149,
183, 265, 276, 279, 290–293
A. lipoferum, 46, 95, 97, 177
Azospirillum sp. AM fungi, 292
Azotobacter sp., 2, 3, 8, 23, 24, 44, 46, 71, 113,
116, 118, 144, 221, 248, 252, 263, 289,
330, 386, 391, 405
A. chroococcum, 46, 59, 64, 97
A.chroococcum, 177, 290–293
B
Bacilli, 252
Bacillus sp., 3, 8, 9, 21–23, 44, 74, 75, 113,
116, 117, 144, 177, 221, 242, 251,
263, 289, 295, 306, 312, 330, 383,
386, 398, 405
B. amyloliquefaciens, 4, 6, 177, 405
B. benzoevorans, 76
B. cereus, 6, 64, 76, 175, 292, 383
B. coagulans, 60, 64, 291, 294
B. lentus, 50, 296
B. licheniformis, 8, 21, 22, 76, 383
B. macroides, 76
B. megaterium, 21, 22, 46, 76, 177, 292,
293, 312, 405
B. mycoides, 6
B. pasteurii, 6
B. polymyxa, 59, 64, 77, 112, 181
B. pumilus, 6, 8, 21, 22, 30, 76, 120,
182, 296
B. sphaericus, 6
mkumar9@amity.edu
Index
433
B. subtilis, 3, 4, 6, 8, 10, 30, 58, 59, 63–65,
76, 144, 177, 265, 276, 290–293, 310,
383, 405
B. subtilis GB03, 65
Bacopa monnieri, 26, 137, 171, 172, 233, 296
Bacteroidetes, x, 22–24
Basil, 291
Begonia malabarica, 294, 332
Begonia malabarica Lam., 309
Begonia sp., 79
B. malabarica, 60, 64
Beijerinckia sp., 8, 263
Benzopyranones, 342
Berberis aristata, 233
Betaproteobacteria, 76
Beta vulgaris, 146
Biocontrol, 29
Biofertilisers, 29, 53, 136, 247, 407
Biopesticides, 136
Biostimulants, 247
Bipolaris sp., 346, 348
Blue green algae, 71
Boerhaavia diffusa, 233
Borago officinalis, 237
Boswellia serrata, 233
Botrytis cinerea, 10, 241
Bowiea volubilis, 327
Bradyrhizobium sp., 2, 3, 8, 58, 59, 64, 74, 248,
289–291, 306, 386
B. japonicum, 175
Brassica
B. napus, 151
B. oxyrrhina, 151
Brassinosteroids, 61
Brevibacillus sp., 330
Brevibacterium halotolerans, 8
Brugmansia candida, 64, 185, 328
Bunge (red sage), 292
Bunium persicumi, 142
Burkholderia sp., 3, 8, 10, 44, 75, 113, 144,
221, 234, 252, 263, 289, 330,
386, 398
B. cepacia, 401
B. gladioli, 30, 292, 293, 295
2, 3-Butandiol, 255
Butanediol, 51
C
Calendula officinalis, 21, 22
Calotropis
C. gigantea, 80, 347
C. procera, 80
Camphor, 64
Camptotheca acuminata, 31, 33
Candida
C. albicans, 346
C. guilliermondii, 348
Capsicum annuum, x, 80, 146, 151, 233
Carica papaya, 233
Carvacrol, 64
Cassia
C. alata, 26, 27
C. angustifolia, 140, 220
C. auriculata, 23
C. occidentalis, 26, 27, 30
C. senna, 233
C. sophera, 26, 27
Castanospermum australe, 33
Catalase (CAT), 48, 173
Catharanthus roseus, L., 23, 24, 33, 46, 64, 91,
93, 99, 116, 140, 143, 171, 172, 177,
208, 220, 233, 290, 291, 293, 332, 327
Caulobacter sp., 2, 44, 74
Cellulomonas sp., 81, 289
Cellulosimicrobium cellulans, 76
Centella asiatica, 25–27, 139, 186, 233
Cephaelis ipecacuanha, 233
Cephaliophora tropica, 76
Ceratoides lanata, 208
Cercidiphyllum japonicum, 26
Chaetomium sp., 347, 348
C. globosum, 345
Chiraunji, 232
Chitinase, 82, 399
Chloroflexi, 22, 23
Chloroform, 419
Chlorophyll, 49
Chlorophytum
C. arundinaceum, 233
C. borivilianum, 171
Chondromyces sp., 23
Chromobacterium sp., 2, 44, 74, 383
Chrysanthemum indicum L., 294
Chuvanna arali, 24
Cinchona sp., 233
C. officinalis, 218
C. pubescens, 218
C. rubra, 218
1,8-Cineole, 64
Cinnamic acid, 65
Cinnamomum zeylanicum, 138
cis-rose oxide, 59
cis-sabinene hydrate, 59, 64
cis-thujone, 56, 64
Citronellol, 59, 64
mkumar9@amity.edu
434
Index
Cladosporium sp., 348
C. cladosporoides, 343
Clavibacter sp., 234
Cleome rutidosperma, 138
Clitoria ternatea, 30
Clone library, 366
Clostridium sp., 289
Codonopsis pilosula, 21
Coelomycetes, 347
Coffea arabica L., 147
Coffea robusta L., 147
Co-inoculation, 274
Coleus
C. barbatus, 140
C. forskohlii, 116, 147, 177, 218, 233, 291,
294, 344
Coleus forskohlii Briq, 293
Coleus sp., 79
C. amboinicus, 33
C. forskohlii, 23, 24, 32, 89, 92–95, 97, 99
Colletotrichum sp., 222, 345, 346, 348
C. falcatum, 347
C. gloeosporioides, 26
C. truncatum, 349, 398
Commiphora wightii, 138, 233
Common basil, 291
Common sage, 292
Corallococcus sp., 23
Corchorus olitorius, 202
Coriandrum sativum, 91, 237
Corynebacterium sp., 23, 116
C. flavescens, 182
Coscinium fenestratum, 345
Costus speciosus, 328
Cotton lavender, 292
Crocetin, 5
Cryptococcus laurentii, 23, 29
Cucurbitacin, 50
Cucurbita pepo var. sterica, 237
Cupressus sempervirens, 147
Curculigo orchioides, 27, 28, 233
Curcuma
C. aromatica, 80
C. longa, 233, 350
C. mangga, 26
Curvularia sp., 348
C.cragrotidis, 236
C. lunata, 347
Cyamopsis tertagonoloba, 79
Cymbopogon flexuosus, 99
Cynara cardunculus, 32, 146
Cystobacteria, x
Cystobacter sp., 23
Cytokinins, 61
D
Dactylaria biseptata, 76
Datura
D. innoxia, 172
D. metal, 80
D. stramonium, 142
Daucus carota L., 424
Dematophora necatrix, 389, 401, 406
Denaturant gradient gel electrophoresis
(DGGE), 366–367
Dendrobium sp., 349
Dephosphorylation, 61
Derris elliptica, 24
Derxia sp., 263
Descurainia sophia, 237
DGGE. See Denaturant gradient gel
electrophoresis (DGGE)
2,4-diacetylphloroglucinol (DAPG), 240
Dichanthelium lanuginosum, 29
3,4-dihydroxy-3,4-dimethoxy-6,7-cyclolignan,
426
Dill, 291
Dioscorea sp., 219, 233
D. bulbifera, 172
D.dregeana, 172
Dioscorea zingiberensis, 25
DNA reassociation, 364
Drechslera sp., 345
Duboisia myoporoides, 233
Dyella marensis, 405
E
Echinacea purpurea, 25
Eclipta
E. alba, 23, 141, 233
E. prostrata, 28
Eisenia
E. foetida, 72, 75, 78
E. lucens, 75
Eiseniella tetraedra, 72
Embelia ribes, 141
Emblica officinalis, 27, 137, 142
Endophytic fungi, 26
Endosymbiosis, 92, 101
Enterobacter sp., 3, 22–24, 81, 113, 116, 221,
248, 251, 252, 263, 289, 295, 398
E. aerogenes, 30, 180, 292, 295
E. cloacae, 4
E. cloacae JM22, 314
Enterococcus faecalis, 57, 58
EO components, 281
Ephedra sinica, 21, 23
10-epi-γ-eudesmol, 59, 64
mkumar9@amity.edu
Index
435
Eragrostis curvula, 201
Erica coccinea, 139
Erwinia sp., 3, 44, 74, 221, 234
E. amylovora, 10
E. carotovora, 177, 241
E. tracheiphila, 50
Erysiphe
E. artemisiae, 236
E. beceleate, 236
E. cichoracearum, 236
E. communis, 236
E. hypersici, 236
Escherichia coli, 57, 58, 346
Eschscholzia californica, 5
Ethnosphere, 217
Ethyl acetate, 350
Ethylene, 61, 63
Eucomis autumnalis, 327
Eudrillus eugeniae, 72
Euphorbia
E. heterophylla, 138
E. pekinensis, 24, 25
Euphoria longan, 27
Euptelea pleiosperma, 26
Eurotiomycetes, 76
Exiguobacterium oxidotolerans, 186, 296
F
Fagopyrum esculentum, 233
Ferulic acid, 65
Fibers, 232
Firmicutes, 22–24, x
FISH. See Fluorescence in situ hybridization
(FISH)
Flavimonas oryzihabitans, 6
Flavobacteria, 76
Flavobacterium sp., 3, 44, 74, 289
Flavonoids, 33, 60, 64, 342
Fluorescence in situ hybridization (FISH), 372
Fluorescent pseudomonads, 45, 75
Frankia sp., 2, 391
Free radical scavenging, 281
Fritillaria thunbergii, 22, 24
Fungicides, 413
Fusarium sp., 6, 10, 24, 25, 80, 222, 236, 348
F. chlamydosporum, 32, 218
F. culmorum, 236
F. graminearum, 419, 426
F. moniliforme, 79
F. oxysporum, 26, 100, 236, 347, 388,
398, 401
F. oxysporum f. sp. cucumerinum, 6
F. proliferatum, 349
F. solani, 218, 236, 345, 419
F. verticillioides, 419
G
Galega sp., 386
G. officinalis, 208
Gallic acid, 65
Gamma-terpinene, 64
Gemmatimonadetes, 22, 23
Geodermatophilaceae, 24
Geodermatophilus obscurus, 23
Geotrichum sp., 76
G. candidum, 10
Geraniol, 64
Geranium dissectum L., 291, 292
Germanium, 291, 292
Gibberellic acid, 51, 145, 208
Gibberellins, 61, 206
Gigaspora sp., 26, 28, 91
Gi. albida, 25, 32
Gi. margarita, 26, 97
G. margarita, 331
Ginseng plants, 22, 27
Gliocladium virens, 241
Gliricidia sepium, 80
Glomerella sp., 348
Glomeromycota, 29
Glomus sp., 26–29, 91, 100
G. aggregatum, 25, 26, 64, 100, 291, 294
G. albidum, 26
G. ambisporum, 26
G. bagyarajii, 91, 92
G. claroideum, 25, 26, 100
G. clarum, 25, 26
G. constrictum, 25, 26
G. coronatum, 26
G. dimorphicum, 26
G. etunicatum, 291, 294
G. fasciculatum, 25, 26, 32, 92, 93, 95, 97,
218, 290, 291, 293, 294
G. flavisporum, 26
G. geosporum, 25–28, 386
G. hyderabadensis, 26
G. intraradices, 25–27, 29, 32, 53, 59, 64,
97, 100, 101, 291–294, 296, 329
G. lamellosum, 291, 292
G. macrocarpum, 25, 291, 293, 294
G. maculosum, 25
G. magnicaule, 26
G. microaggregatum, 25
G. microcarpum, 27, 28
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436
Index
Glomus sp. (cont.)
G. monosporum, 25, 26, 97
G. mosseae, 25–27, 53, 60, 64, 93, 97, 101,
291–294
G. multicaule, 25
G. reticulatum, 26
G. rubiforme, 25, 386
G. verruculosum, 26
G. versiforme, 25
G. viscosum, 26, 386
G. walkeri, 292, 293
Gloriosa superba, 138
Gluconacetobacter, 263
Gluconobacter diazotrophicus, 312
Glutathione, 171
Glycine sp., 2
G. max, 117, 347, 386
Glycyrrhiza glabra L., 219, 233, 237, 291, 294
γ-proteobacteria, 76
Gram-negative bacteria, 22
Groundnut, 150
GTP-binding proteins, 61
Guignardia sp., 348
G. cammillae, 349
Gum, 232
Gymnema sylvestre, 138, 233
H
Hedychium spicatum, 233
Heisteria concinna, 343
Helianthus
H. annuus, 327
H. tuberosus, 28
Hemidesmus indicus, 25, 137
Heracleum candicans, 233
Herbaspirillum sp., 252, 263
H. seropedicae, 312
Hexane extract, 419
Hippophae rhamnoides, 26, 405
HM-contaminated, 324
Hoagland’s nutrient, 278
Holarrhena antidysenterica, 139
Honeysuckle, 291
Hordeum vulgare L., 424
Hormonema ssp. homogenates, 64
Humicola sp., 345
Hydrocyanic acid (HCN), 174
Hydrogen cyanide, 118
3-Hydroxy-2-butanone (acetoin), 255
Hyoscyamine, 5, 54, 64, 329
Hyoscyamus
H. muticus, 27, 56
H. niger, 49, 55, 219
Hyoscyamus niger L., 64
Hyoscyamus sp. muticus, 233
Hypericum perforatum, 237, 327
Hypericum silenoides Juss, 22, 24
Hyphomycetes, 347
Hyphomycrobium sp., 74
Hyponectria sp., 29
Hypoxia, 169
I
Immobilization, 247
Immunosuppressant, 353
Indian coleus, 291
Indian ginseng, 292
Indigofera
I. aspalathoides, 28
I. tinctoria, 24, 28
Indole-3-acetic acid, 395
Indole acetic acids, 51, 61, 82, 145
Intracellular PGPR (iPGPR), 384
Inula racemosa, 233
iPGPR. See Intracellular PGPR (iPGPR)
Ipomoea batatas, 80
Iron chelation, 73
Isoflavones, 33
ISR-eliciting, 401
Italian cypress, 147
J
Jasmonic acid, 61
Jatropha
J. curcas, 80, 171, 172
J. podagrica, 111
Jatropha curcas L., 147
Jerusalem artichoke, 146
Juglans regia, 233
Juniperus sp., 233
K
Karaya gum, 232
Kinases, 61
Klebsiella sp., 113, 118, 248, 263,
306, 398
K. mobilis, 184
K. pneumoniae, 7
Kluyvera ascorbata, 183
Kocuria varians, 118
Kribbella
K. alba, 22, 24
K. flavida, 22, 24
K. karoonensis, 22, 24
mkumar9@amity.edu
Index
437
L
Lactuca sativa, 53, 151
Lactuca sativa L., 424
Lamiophlomis rotata, 23
Larrea
L. ameghinoi, 416
L. cuneifolia, 415, 416, 419, 424, 425
L. divaricata, 415, 416, 419
L. nitida, 416
L. tridentata, 415, 416
Lasiodiplodia sp., 348
Launaea nudicaulis, 146
Lavandula angustifolia L., 237, 291, 292
Lavender, 291
Lawsonia inermis, 139
Lecanoromycetes, 76
Length heterogeneity (LH) PCR, 371–372
Lepidium sativum L., 424
Leptadenia reticulata, 26, 28
Leptosphaerulina chartarum, 347
Leveillula
L. guttiferatum, 236
L. malvacearum, 236
LH PCR. See Length heterogeneity (LH) PCR
Lignolytic fungus, 77
Limonene, 275
Lipoxygenase (LOX), 186
Liquorice, 219, 233, 237, 291, 294
Lonicera confusa, 291, 294
Lumbricus
L. polyphemus, 72
L. rubellus, 75
L. terrestris, 72, 75, 76
Luteolin, 309
Lycium barbarum, 26
Lycopersicon esculentum, x, 420, 424
Lysinibacillus
L. fusiformis, 405
L. xylanilyticus, 383
M
Macrophomina phaseolina, 30, 100, 101, 222,
398, 419
Madagascar periwinkle, 291
Magnolia cylindrica, 26, 28
Malva sylvestris, 237
Marasmius sp., 348
Marjoram, 291
Materia Medica, 20
Matricaria chamomilla, 21, 22, 172, 205, 233,
290, 295, 326
Maytenus sp., 418
M. vitis-idaea, 415, 418
MBC. See Minimal bactericidal concentration
(MBC)
Mediterranean, 381
Melissa officinalis, 172
Melissa officinalis L., 237
Meloidogyne incognita, 218
Mentha
M. arvensis, 290, 291, 326
M. piperita, 63, 64, 140, 237, 266
M. pulegium, 237
Menthone, 64
Mesorhizobium sp., 2, 3, 74, 144, 248, 253, 306
Mesua ferrea, 140
Metagenomics, 360, 372–374
Methanol, 350, 419
Methyl jasmonate, 61, 63
Mexican marigold, 292
MIC. See Minimal inhibitory concentration
(MIC)
Microarrays, 374–375
Microbacterium sp., 8, 9, 75, 76
M. oxydans, 76
Micrococcus sp., 23, 44, 74, 116, 289
M. luteus, 21, 22
Micromonospora sp., 76
Mimosa pudica, 27, 350
Minimal bactericidal concentration (MBC), 57
Minimal inhibitory concentration (MIC), 57
Minthostachys
M. mollis, 280
M. verticillata, 415, 424
Mitragyna parvifolia, 26, 28
Momordica charantia, 80
Monoterpenes, 63, 264
Moringa oleifera, 80, 346
Moringa oleifera Lam, 143
Mucilaginibacter sp., 21
M. boryungensis, 21
M. myungsuensis, 21, 22
M. polysacchareus, 22
M. ximonensis, 21, 22
Mucor
M. mucedo, 236
M. piriformis, 10
Mucuna pruriens, 29, 139
Mycelia sterilia, 347
Mycobacterium sp., 221
Mycorrhizal, 329
Myxococcus sp., 23
N
N-Acyl-homoserine lactones, 255
Naregamia alata, 25
mkumar9@amity.edu
438
Index
Nerium indicum, 22, 80
n-hexane, 419
Nicotiana tabacum, 80
Nicotinamide adenine dinucleotide phosphate
(NADP), 297
nifH, 391
Nigrospora sp., 346
N. oryzae, 349
N. sphaerica, 347
Nitrogen fixation, 2
Nocardioides oleivorans, 79
Non-mycorrhizal, 31
Nothopanax scutellarium, 350
Nutraceutica, 135
O
Ochrobactrum sp., 252, 263
O. bacillus, 331
Ocimene, 275
Ocimenone, 275
Ocimum basilicum L., 50
Ocimum sp., 172, 291
O. basilicum, 33, 63, 65, 150, 151, 271,
272, 290, 291, 295, 386
O. sanctum, 23, 24, 26, 27, 91, 116, 141,
177, 348
Octolasion cyaneum, 72
Oenothera biennis, 233
Olea europaea, 172
Operational taxonomic unit (OTU), 368
Ophiopogon platyphyllum, 25
Ophthalmic, 418
Oregano, 292
Origanum
O. dictamnus, 292
O. majorana, 58
O. vulgare, 22, 24
Origanum majorana L., 64, 290, 291
Origanum majoricum, 59, 64
Origanum sp., 292
Ortho-dihydroxyphenols, 33, 64
Orthosiphon stamineus, 172
Oryza sativa, 80
OTU, Operational taxonomic unit (OTU)
Oxalis reclinata, 186
Oxylipin phytoprostanes, 63
P
Paecilomyces sp., 76
Paenibacillus sp., 21, 22, 75, 81, 178, 253, 289
P. polymyxa, 117
Paeonia suffruticosa, 26, 28
Palaearctic, 381
p-aminoacetophenonic acid, 352
Panax
P. ginseng, 25, 219
P. notoginseng, 25
P. pseudoginseng, 233
P. quinquefolius, 147, 186, 233
Pantoea sp., 22, 24, 234, 263
P. agglomerans, 7, 181
Papaver somniferum, 219, 233
Papulaspora sp., 348
Paraglomus sp., 29
Parthenium hysterophorus, 80, 81
Pectobacterium sp., 234
Pelargonium sp., 290, 292, 296
P. graveolens, 65
Penicillium sp., 10, 117, 346, 348, 392
P. citrinum, 236
P. digitatum, 26
P. pinophilum, 30
Peppermint, 275
Perionyx excavates, 72
Peroxidase, 48
Peroxidase (POD), 171
Persea americana, 146
Pestalotiopsis sydowiana, 347
Petunia sp., 79
Pezizomycetes, 76
PGPR. See Plant growth-promoting
rhizobacteria (PGPR)
Phanerochaete chrysosporium, 415
Phaseolus vulgaris, 180
Phellodendron amurense, 29
Phenerocrete crysosporium, 77
Phenolic acids, 342
Phenolic compounds, 65
Phenols, 64, 274
Phenyl-alanine ammonia-lyase (PAL), 173
Phlebia sp., 348
P. radiata, 415
Phoma sp., 343, 346, 348
P. exigua, 347
Phomopsis sp., 343, 346, 348
P. archeri, 347
Phosphate solubilization, 73
Phosphate solubilizing bacteria, 64
Phospholipases, 62, 63
Phospholipid fatty acid (PLFA), 364–365
Phragmites australis, 9
Phyllanthus
P. amarus, 137, 146, 233
P. emblica, 232
Phyllosphere, 217
Physalis minima, 25
Phytochelatins, 173
Phytohormones, 73, 114, 118, 247, 263
mkumar9@amity.edu
Index
439
Phytolacca acinosa, 23
Phytophthora sp., 10, 217, 401, 406
P. capsici, 79
P. cinnamomi, 218
P. quininea, 218
Phytoplasma sp., 234
Phytoremediation, 153
Phytostabilization, 330
Phytostimulators, 136, 248
Picrocrocin, 5
Picrorhiza sp., 404
P. kurroa, 233, 386, 388, 394, 404
Pinellia ternata, 25
Piper sp., 348
P. crocatum, 350
P. hispidum, 348
P. longum, 30, 139
P. nigrum, 146
P. retrofractum, 233
Piriformospora indica, 344
Pisum sativum, 65
Pithomyces sp., 348
Planctomycetes, 22, 23
Plantago
P. major, 220
P. ovata, 233
Plant growth-promoting rhizobacteria
(PGPR), 10
Plectranthus
P. amboinicus, 30
P. tenuiflorus, 21, 22
PLFA. See Phospholipid fatty acid (PLFA)
Pluchea
P. indica, 350
P. lanceolata, 172
Plumbago
P. indica, 140
P. zeylanica, 30, 140
Podophyllum sp., 404
P. emodi, 233
P. hexandrum, 386, 390, 394, 404, 406
Polyacrylamide gel, 366
Polyphenolic profile, 33
Polyphenol oxidase (PPO), 176
Poncirus trifoliata, 30
Pongamia pinnata, 80
Pontibacter sp., 22, 24
Pontoscolex corethrurus, 72
Populus euphratica, 172
Prospects and challenges, 10–11
Proteobacteria, x, 22–24, 76
Proteobacterium, 22, 23
Proteus sp., 3
Prunus africana, 28
Pseudomonades sp., 7
Pseudomonas sp., 3, 10, 21–24, 30, 44, 50, 60,
74–76, 113, 116–118, 120, 144, 177,
202, 208, 221, 234, 242, 248, 251, 252,
263, 289, 295, 296, 330, 383, 386, 392,
398, 405
P. aeruginosa, 30, 65
P. asplenii, 9
P. extremorientalis, 202, 205, 296
P. fluorescens, 6–8, 10, 45, 46, 48, 49, 54,
58, 59, 63–65, 118, 120, 144, 153,
175–177, 180, 183, 186, 208, 268, 275,
276, 279, 290–294, 296, 310
P. mendocina, 53
P. monteilii, 32, 291, 293
P. officinalis, 53
P. putida, 6, 8, 46, 49, 54, 59, 64, 175, 291,
292, 296
P. striata, 8, 97
P. syringae, 180
P. syringae pv. lachrymans, 6
P. syringae pv. phaseolicola, 6
P. tolaasii, 10, 253
Pseudoxanthomonas sp., 81
Psoralea corylifolia, 30
Pterocarpus santalinus, 206
Pueraria mirifica, 24
Pulegone, 64
Pyochelin, 251
Pyoverdin, 251
Pythium sp., 10
P. aphanidermatum, 388
P. ultimum, 79
Pytoalexins, 55
Pyxidicoccus sp., 23
Q
Quorum sensing (QS), vii
molecules, vi
signal, vi
Quercetin, 309
Quinones, 342
Quorum sensing, 1
R
Ralstonia sp., 234
R. solanacearum, 218
Rauvolfia
R. canescens, 5
R. serpentina, 27, 140, 220, 232, 233
R. tetraphylla, 27
Redoxin, 173
Reductase, 173
Rehmannia glutinosa, 23, 28
mkumar9@amity.edu
440
Index
Rheinheimera sp., 81
Rheum emodi, 233
Rhizobacteria, 1, 325
Rhizobia, 92
Rhizobium sp., 3, 7, 71, 101, 117, 144, 168,
175, 221, 248, 289, 306, 330, 386,
391, 398
R. leguminosarum, 6, 222
R. meliloti, 29
Rhizoctonia sp., 10
R. solani, 236, 241, 398, 401
Rhizopus solani, 236
Rhizoremediators, 136
Rhizosphere, 2, 33, 102, 112, 114, 174, 175,
248, 249, 305, 325, 382
Rhizospheric microorganism, 29
Rhodococcus sp., 76, 81, 221, 263
R. fascians, 218
Rhodotorula sp., 405
Richardia brasiliensis, 141
Roots, 232
Rosa multiflora, 32
Rose-scented geranium (Pelargonium sp.), 64
Rosewood, 232
Rosmarinus officinalis, 237
R-terpineol, 63
Rumex patientia, 22, 23
S
Saccharomycetes, 76
Salicornia pacifica, 208
Salicylic acid, 61, 251, 401
Salmonella typhi, 348
Salvia
S. militiorrhiza, 290
S. miltiorrhiza, 292, 293
S. miltiorrhiza Bunge, 64
S. officinalis L., 30, 33, 45, 56, 64, 237,
292, 293
Sandalwood oil, 232
Santalum album, 140, 143
Santolina chamaecyparissus, 292
Sapindus trifoliatus, 27
Saponins, 64
Saraca asoca, 137
Satureja hortensis, 201, 237
Saussurea lappa, 233
Schizophyllum sp., 348
Sclerocystis dussii, 97
Sclerotinia sclerotiorum, 350
Sclerotium sp., 348
S. rolfsii, 26, 388, 398, 401, 406, 419, 420
Scoparia dulcis, 138
Scopolamine, 5, 64
Scopulariopsis sp., 348
Scutellaria baicalensis, 27
Scutellospora sp., 26, 28, 29
S. aurigloba, 26
S. calospora, 25, 91
Scytalidium sp., 345
Serpentine, 5, 64
Serratia sp., 3, 22–24, 44, 74, 113, 116, 144,
252, 263, 289, 330
S. marcescens, 6, 30, 292, 293, 295
S. plymuthica, 254
Sida
S. acuta, 141
S. rhombifolia, 233
Siderophores, 44, 82, 115, 119–120, 174, 221,
251, 255, 325, 389, 395
Silybum marianum, 150, 233
Single strand conformation polymorphism
(SSCP), 369
Sinorhizobium sp., 3, 74, 248, 289, 306, 386
S. meliloti, 58, 59
β-Sitosterol, 309
Sivakaranthai, 292
Smilax sp., 27
Smooth-stem turnip, 151
Soil fungi, 27
Solanaceae, 55
Solanum
S. distichum, 21, 22
S. dulcamara, 237
S. melongena, 147
S. nigrum, 139
S. viarum, 64
S. xanthocarpum, 139
Solubilization, 393
Sordariomycetes, 76, 347
Sorghum bicolor, 27
Spermosphere, 217
Sphaeranthes amaranthoides, 295
Sphaeranthus amaranthoides (L.) Burm, 292
Sphaerotheca fuliginea, 236
Sphingobacteria, 76
Sphingobium sp., 22, 24
Sphingomonas sp., 76
Spigelia anthelmia, 139
Spinacia oleracea, 237
Spiroplasma sp., 75, 234
SSCP. See Single strand conformation
polymorphism (SSCP)
S. scutata, 25
Stachytarpheta cayennensis, 137
mkumar9@amity.edu
Index
441
Staphylococcus sp., 252
S. aureus, 57, 58, 346
S. epidermidis, 57, 58, 79
Stenotrophomonas sp., 22, 24, 81, 252, 263
Steroids, 342
Stevia rebaudiana, 59, 64, 293, 326
Stevia rebaudiana Bert., 292
Stevioside, 64
Stigmatella sp., 23
Streptococcus agalactiae, 57, 58
Streptomyces sp., 10, 28, 76, 79, 234, 242
S. acidiscabies, 153
S. caeruleus, 77
S. pactum, 29
Striga sp., 19
Strychnos nux-vomica, 139
Sunchoke, 146
Superoxide dismutase (SOD), 48, 171
S. verrucosa, 25, 26
Sweet leaf, 292
Swertia chirata, 138, 233
T. serpyllum, 237
Tinospora cordifolia, 139
Trachyspermum copticum, 27
trans-rose oxide, 59
trans-sabinene hydrate, 59, 64
Tremellomycetes, 76
T-RFLP. See Terminal restriction fragment
length polymorphism (T-RFLP)
Tribulus terrestris, 138
Trichoderma
T. harzianum, 60, 64, 97, 101, 291, 294
T. viride, 64, 77, 292, 293, 295
Trichoderma sp., 241, 242, 254, 386
Trichophaea abundans, 346
Trichosanthes kirilowii, 30
Tridax procumbens, 80, 138, 350
Trigonella foenumgraecum, 150
Triticum aestivum, 424
Tryptophan, 297
Tryptophan decarboxylase (TDC), 173
Typhonium giganteum, 22, 24
T
Tagetes minuta, 65, 273, 290, 292
Tagetone, 275
Tannins, 60, 64
Tanshinone, 64
Taxus
T. baccata, 233
T. chinensis, 26
Temperature gradient gel electrophoresis
(TGGE), 366–367
Terminalia
T. belerica, 232
T. bellirica, 137
T. chebula, 139, 232
Terminal restriction fragment length
polymorphism (T-RFLP), 367–368
Terpenoids, 281, 342
Terpinene-4-o1, 64
α-Terpineol, 64
Terriglobus sp., 21
T. roseus, 21
T. saanensis, 21, 22
Tetralones, 342
TGGE. See Temperature gradient gel
electrophoresis (TGGE)
Thyme, 292
Thymol, 64
Thymus
T. daenensis, 292
T. maroccanus, 172
U
Urginea indica, 233
V
Valeriana sp., 404
V. jatamansi, 386, 389, 394,
401, 404
V. wallichii, 233
Verbascum sp., 417
V. thapsus, 415
Vermicompost, 78
Verrucomicrobia, 22, 23
Verticillium sp., 24, 25
V. albo-atrum, 236
V. dahliae, 236
Vetiveria zizanioides, 137
Vicia faba, 5
Vinca rosea, 140
Vitex negundo, 80
Vitis vinifera, 151
W
Wild mint, 291
Withania
W. coagulans, 26, 28
W. somnifera, 30, 137, 143, 218, 233, 290,
292, 332, 386
Wormwood, 291
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442
X
Xanthomonas sp., 3, 234
Xanthones, 342
Xylariaceae, 349
Xylariales, 346
Xylaria sp., 343
Xylella sp., 234
Xylosoxidans sp., 312
Index
Z
Zea mays, L., 386, 424
Zingiber officinale, 80, 233
Ziziphora clinopodioides, 172
Ziziphus jujuba Mill. var. inermis, 26
Zoogloea sp., 263
mkumar9@amity.edu