Phytotaxa 340 (2): 101–127
http://www.mapress.com/j/pt/
Copyright © 2018 Magnolia Press
ISSN 1179-3155 (print edition)
Article
PHYTOTAXA
ISSN 1179-3163 (online edition)
https://doi.org/10.11646/phytotaxa.340.2.1
Plant diversity of the Heydari Wildlife Refuge in northeastern Iran, with a
checklist of vascular plants
ZOHREH ATASHGAHI1, HAMID EJTEHADI1,*, MANSOOR MESDAGHI2 & FERESHTEH GHASSEMZADEH1
1
Department of Biology, Faculty of Science, Ferdowsi University of Mashhad, 9177948974, Mashhad, Iran
Department of Range and Watershed Management, Faculty of Natural Resources and Environment, Ferdowsi University of Mashhad,
9177948974, Mashhad, Iran
*Corresponding author:hejtehadi@um.ac.ir
2
Abstract
Heydari Wildlife Refuge (HWR) is located in Binalood mountain range of the Razavi Khorassan Province in Northeastern
Iran. The area belongs to the central part of Khorassan-Kopet Dagh floristic province, which is a transitional zone between
different phytogeographical units in the Irano-Turanian region. We investigated the floristic composition, life-form spectrum
and the phytogeography of the area during 2014–2017 by collecting vascular plants and establishing 443 random-quadrats
in representative stands of different vegetation types. A total of 588 vascular plant taxa (species and subspecies) belonging to
304 genera and 65 families are recorded as native and naturalized in the study area. The richest plant families are Asteraceae
(40 genera/87 species), Fabaceae (15/72), Poaceae (33/60), Brassicaceae (33/49), Lamiaceae (19/32), and Apiaceae (18/27).
The genera Astragalus (44 species), Cousinia (17), and Allium (10) are the richest ones. However, the dominant canopy
cover belongs to Acantholimon, Astragalus, Artemisia, and Acanthophyllum species. Raunkiaer’s plant life-form spectrum in
the area is dominated by hemicryptophytes (41.50%) and therophytes (28.06%). The core flora of HWR has the Irano-Turanian origin; the widespread elements are also well represented in the study area. Based on the Sørensen dissimilarity index,
the HWR has about 50% dissimilarity to the adjacent areas. The study area is inhabited by several Iranian and/or KhorassanKopet Dagh endemic (19%), threatened (16%), and narrow-range plant species. The results indicate the importance of the
HWR in the plant diversity of NE Iran.
Keywords: Binalood, biogeography, conservation, endemism, flora, Khorassan
Introduction
Iran, with about 7300 vascular plant species (Akhani 2006, Govaerts 2001) in a 1.65 million square kilometers surface
area, is the second richest country after Turkey in SW Asia (Davis et al. 1994). Iran is predominantly covered by
mountain ranges and deserts. The geographic and habitat diversity result in diverse bioclimatic regions and consequently
a rich flora and vegetation diversity in the country. The flora of Iran is influenced by three main floristic regions of
the Old World, i.e. Irano-Turanian (IT), Euro-Siberian (ES), and Saharo-Sindian (SS) (Zohary 1973, Léonard 1988,
1993). The mountainous terrain of the NE Iran belongs to an independent floristic province of the IT region, named
“Khorassan-Kopet Dagh” (Memariani et al. 2016a). This area is primarily influenced by Central Irano-Turanian desert
elements of the south and southwest and by many local and regional endemic taxa exclusively originated in KhorassanKopet Dagh (KK) foothills and mountains. Furthermore, there are many widespread species; the flora of surrounding
Central Asian, Afghanistan, the Aralo-Caspian and ES regions enrich the plant diversity of KK (Fet 1994, Memariani
et al. 2016b).
Restoring biodiversity will probably increase ecosystem resistance to climate extremes, which were predicted to
become increasingly frequent as the global climate continues to change (Isbell 2015). Investigating the flora of a region
is a strategy to know its diversity, and thus the base for management programs and conservation of natural resources
(Encina-Domínguez et al. 2016). The awareness of the importance of exploring and preserving the floristic diversity
of protected areas has dramatically increased in the latest years (Akhani 1998, Jafari & Akhani 2008, Memariani et al.
2016a). There is still a major lack of basic knowledge of the plants themselves.
The Heydari Wildlife Refuge (HWR) is located in Razavi Khorassan province. It was designated a Wildlife Refuge
in 2002. According to the bioclimatic maps of Iran (Djamali et al. 2012) the area has an “Irano-Turanian bioclimate”.
Accepted by Alexander Sennikov: 29 Jan. 2018; published: 23 Feb. 2018
101
Despite its vast area and crucial position in the central part of KK floristic province, little is known about the floristic
composition of the HWR. More recently, there have been local floristic collections made by Joharchi in 2003, resulting
in the description of a new species, Cousinia amicorum Tscherneva, Joharchi & Ghahremaninejad (in Tscherneva et al.
2005). There are several occasional plant collections at the HWR recorded in “Flora Iranica” (Rechinger 1963–2015).
Nikan et al. (2012) studied the floristic composition of the semi-steppe habitats in Baharkish, a small area located in
the north of HWR and recorded 156 species from three sites under different grazing intensities. The objectives of this
study are: 1) to provide an annotated checklist of the plants and their life-forms, chorotypes and plant endemism in
HWR, 2) to compare species composition between HWR and the other areas previously studied in northeastern Iran
and 3) to encourage honouring the nature and protecting vegetation along with conserving the wildlife in the area.
Material and Methods
Floristic survey
Field surveys were conducted over a four-year period (2014–2017), during which approximately 3,000 vascular plant
specimens were collected. Collected plants plus those coming from random-quadrats, were dried and labeled precisely
for herbarium specimens. Plant specimens were identified using relevant Floras, mainly “Flora Iranica” (Rechinger
1963–2015), “Flora of Iran” (Assadi et al. 1988–2013) and complementary literatures (Tzvelev 1976, Maassoumi
2005, 2013, Ranjbar et al. 2008, Memariani et al. 2007, 2012, Mozaffarian 2012, Fritsch & Abbasi 2013, Tavakkoli
et al. 2014, Arjmandi et al. 2016). The floristic list was presented alphabetically following the APG IV (2016) for the
classification of angiosperms, PPG I (2016) for ferns, and Christenhusz et al. (2011) for gymnosperms. The chorotype
of each taxon was determined according to the distribution data extracted from the above-mentioned Floras and papers.
The terminology and delimitation of the main phytogeographical units (IT, Mediterranean, ES, and SS) were based on
classical works, particularly Zohary (1973). Following Akhani (1998), we considered the concept of Léonard (1988)
for phytogeographical subdivisions and provinces and the distributional groups were easily characterized either by
the geographical directions (i.e. ITE, C, W) or by the known geographical provinces (i.e. Khorassan-Kopet Dagh: ITKK).
Life-forms of the plants were determined according to Raunkiaer (1934). Threat categories were evaluated by the “Red
Data Book of Iran” (Jalili & Jamzad 1999) and Memariani et al. (2016b). Voucher specimens were mainly deposited
in the Herbarium of the Faculty of Science, Ferdowsi University of Mashhad (abbreviated here as FUM), and some
duplicates were transferred to the Herbarium of Ferdowsi University of Mashhad (FUMH) and Herbarium of Noshahr
Botanical Garden (abbreviated here as HNBG). Along with the floristic study, species canopy cover (percentage)
of vascular plants was measured in the random variable plots. The Sørensen index of similarity was measured to
evaluate the floristic similarity among the study area and three other studied territories in Khorassan-Kopet Dagh
floristic province, including Ghorkhod Protected Area (Memariani et al. 2016c), Fereizi (Memariani et al. 2009), and
Baghshangach (Ghahreman et al. 2006).
Study Area
Geography
Heydari Wildlife Refuge, with an area of 46350 ha, is situated in the latitudes of 36° 31´ to 36° 49´ N and longitudes
of 58° 29´ 7″ to 58° 45′ 55″ E, and is the largest wildlife refuge in Razavi Khorassan province, NE Iran. The elevation
ranges from 1400 to 2900 meters above sea level. There are 18 villages in the HWR, mostly in the surroundings, and
an uninhabited area (Figure 1). The HWR is a “no-hunting” area for the protection of animal populations, especially
urials (Ovis orientalis Gmelini), and has been designated and protected since 2002. A wildlife Refuge in Iran is an area
administered for the conservation of wildlife.
Climate
According to the nearest synoptic station of Quchan, HWR has a mean annual temperature of 12.7°C and a mean
annual precipitation of 315 mm, indicating a cold and arid climate. There is no synoptic station inside the HWR,
thus ombrothermic graphs are prepared using 20-year (1994–2014) data from three synoptic stations close to the area
(Figure 2). Among those, Quchan is the nearest one and according to our 4-year field surveying, its climate is more
similar to the one at the HWR. Precipitation period is autumn–winter–spring; in average, there are 6.5 dry months
(P < 2T). Due to the high elevations of the HWR (at least 1400 m), more precipitation and lower temperatures are
experienced in the study area. There are 23 springs and 6 permanent and seasonal rivers inside the area.
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FIGURE 1. A. Map of Iran in the Middle East (prepared in R 2016), the inset shows the position of HWR, B. Protected areas in NE
Iran according to Iranian environmental protection categories. HWR is indicated by green color and number 27 (modified from Bali &
Bahmanpoor 2012), C. Topographic map of HWR, showing villages surrounding the area (prepared by M. Javidi).
FIGURE 2. Climatic diagrams of three stations close to the HWR. Up-left: Neyshabour, Up-right: Golmakan-Chenaran, and Downleft: Quchan. Climatological data are obtained from the website of the meteorological organization of Iran (IRIMO 2016). Down-right:
geographical positions of three synoptic stations and HWR.
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Results
Floristic composition
The total number of 588 species and infraspecific taxa of vascular plants belonging to 304 genera and 65 families has
been collected and identified from the study area (Appendix I). Angiosperms include Dicots with 472 species, 243
genera, and 47 families followed by Monocots with 111 species, 57 genera, and 14 families. Gymnosperms include
three species, two genera and two families, and Ferns are represented by two species, two genera and two families.
The richest families are Asteraceae (40 genera/87 species), Fabaceae (15/72), Poaceae (33/60), Brassicaceae (33/49),
Lamiaceae (19/32), and Apiaceae (18/27) (Table 1).
TABLE 1. List of the most species-rich vascular plant families (with ≥ 10 species) in HWR.
Families
Asteraceae
Fabaceae
Poaceae
Brassicaceae
Lamiaceae
Apiaceae
Caryophyllaceae
Boraginaceae
Ranunculaceae
Rubiaceae
Rosaceae
Plantaginaceae
Polygonaceae
Caprifoliaceae
Amaryllidaceae
Genera
40
15
33
33
19
18
13
12
10
5
7
3
4
6
1
Species/infraspecific taxa
87
72
60
49
32
27
24
19
16
15
14
14
11
10
10
Number of genera with ≥ 4 species
6
3
3
1
1
2
1
2
1
1
1
1
1
1
1
The genera Astragalus Linnaeus (1753: 755) (44 species), Cousinia Cassini (1827: 503) (17 species), and Allium
Linnaeus (1753: 294) (10 species) are the richest ones; however, the species of Acantholimon Boissier (1846b: 69),
Astragalus, Artemisia Linnaeus (1753: 845), and Acanthophyllum Meyer (1831: 210) make the dominant canopy
cover in the area. Table 2 shows 32 genera presented by four or more species in the HWR. Figures 3 and 4 show the
characteristic landscapes and selected rare and threatened plants in the HWR.
Based on the Sørensen similarity index, the floristic composition of the HWR is 57.65, 47.48 and 47.81% similar
to the adjacent areas of Fereizi, Ghorkhod Protected Area, and Baghshangach, respectively.
TABLE 2. List of the most species-rich vascular plant genera with more than four species in HWR.
Genera
Astragalus
Cousinia
Allium
Alyssum
Veronica
Bromus
Galium
Scorzonera
Stipa
Euphorbia
Ferula
species
44
17
10
10
9
7
7
7
7
6
6
Genera
Poa
Polygonum
taraxacum
Cirsium
Hymenocrater
Valerianella
Acantholimon
Acanthophyllum
Bunium
Carex
Centaurea
species
6
6
6
5
5
5
4
4
4
4
4
Genera
Eremurus
Gagea
Hedysarum
Iris
lappula
Onobrychis
Ranunculus
Rochelia
Rosa
tragopogon
Genera (< 4 spp.)
species
4
4
4
4
4
4
4
4
4
4
272
Life-form
Hemicryptophytes (41.50%) and therophytes (28.06%) are the dominant life-forms in the HWR. Cryptophytes
(geophytes) having different regenerating bodies include 15.13% of the species. Finally, 11.39% and 3.91% of the
species are chamaephytes and phanerophytes, respectively (Figure 5).
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FIGURE 3. Characteristic landscapes in HWR; a: Juniperus polycarpos woodlands, b: mountain steppes of thorn-cushion formations, c:
Eremurus spectabilis in high mountain thorn-cushion steppes, d: Stipa-steppes, e: harvesting Gundelia tournefortii as a winter forage in
southern lowlands of HWR, f: grazing pressure near villages (Photos by a: M. Khaleqipoor, b–f: Z. Atashgahi).
Phytogeography
More than two-thirds of species (69.13%) in the area belong to the Irano-Turanian floristic region. Widespread elements
(11.84%), i.e. pluri-regional, sub-cosmopolitan and cosmopolitan species, make up a remarkable proportion of the
flora followed by tri-regionals (9.43%) and bi-regionals (9.26%) with a relatively wide distribution range. The EuroSiberian species have an inconsiderable frequency (0.34%) in the phytogeographical spectrum of the area (Figure 6).
The main subdivisions of Irano-Turanian elements are widespread IT (26.8%), Central IT (20.34%), IT elements
endemic to KK floristic province (16.38%), and Central-Eastern IT (11.16%) (Figure 7). Sixty-four species (10.88%)
are endemic to Iran; however, there are 115 sub-endemic or regional endemic taxa (19.56%) in the study area occurring
mainly in Iran and in one or both of adjacent countries, i.e. Turkmenistan and Afghanistan (Appendix I). Four-fifths
of endemic and sub-endemic plants (76 taxa) have been evaluated as threatened species. In total, 96 plant species
(16.33%) are threatened in HWR. Based on the previous data, Cousinia amicorum was the only known local endemic
of the HWR (Figure 4b–c), yet a new survey (Mehregan & Assadi 2016) shows the occurrence of the species in the
other Iranian parts of KK floristic province.
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FIGURE 4. Selected rare and threatened plants of HWR in their habitats; a: Helictotrichon turcomanicum, an endangered species in Iran,
b–c: Cousinia amicorum, an endangered and endemic species in their small habitat in the southern part of HWR, d: Nepeta binaloudensis,
an endangered, endemic, and medicinal plant inhabited on wet soils in the central parts of the study area, e: Astragalus esferayanicus, an
endangered, rare, and endemic species, f: Iris loczyi, a vulnerable plant on higher elevations, g: Phlomoides binaludensis, an endangered,
endemic species in NW foothills of HWR, close to the Chahab valley, h: Delphinium turkmenum Lipsky, endemic to Khorassan-Kopet Dagh,
and i: Acanthophyllum adenophorum, an endemic cushion plant, found in low foothills of the study area (Photos by: Z. Atashgahi).
Vegetation and physiognomy
Approximately 40 percent of the study area is covered by vegetation. The mountainous subalpine vegetation of the
area is dominated by thorn-cushion plants mainly as different combinations of Astragalus spp., Acantholimon spp.,
Acanthophyllum spp., and Onobrychis cornuta (Linnaeus 1763: 1060) Desvaux (1814: 81) (Figure 3 a–b). Acantholimon
erinaceum (Jaubert & Spach 1844: 163) Linczevski (in Komarov 1952: 370), Astragalus verus Olivier (1807: 342),
Acantholimon raddeanum Czerniakowska (1930: 276), and Acanthophyllum glandulosum Bunge ex Boissier (1867:
565) are the most frequent thorn-cushion species. In the lower elevations, the cushion plants are replaced by the steppe
flora of Artemisia and Artemisia-Astragalus. Meadow steppes are mainly described as Festuca valesiaca Schleicher
ex Gaudin (1811:242) and Elymus Linnaeus (1753: 83)-Stipa Linnaeus (1753: 78) steppes, or mosaic stands of leymus
Hochstetter (1848: 118) steppes in some west-facing slopes. leymus steppes are described as semi-dense patches of
up to 60% canopy cover. In the lower belt of the mountains, especially on the well-developed soils, there are mixtures
of Acantholimon erinaceum and Acanthophyllum adenophorum Freyn (1902–1903: 867) as cushion forms, as well as
Stipa caucasica Schmalhausen (1892: 293), S. hohenackeriana Trinius & Ruprecht (1842: 80), S. holosericea Trinius
(1831: 81) as perennial grasses (Figure 3 d).
The woodlands of Juniperus polycarpos Koch (1849: 303) var. turcomanica (Fedtschenko 1932: 14) Adams
(Adams et al. 2008) occur as small patches in the uplands of the HWR. The vast stands of these juniper woodlands in
the southwest of the area extend from the highest elevation (about 2900 m) to the lowest parts (about 1700 m) of the
Heydari River (Figure 3 a). The natural regeneration of juniper trees is observed in this stand; however, in the other
areas, the juniper woodlands are distributed as isolated stands or as single old-growth individual trees with no observable
seedlings. Open to semi-dense shrublands are formed in mesic valleys composed mainly of Cotoneaster spp., lonicera
nummulariifolia Jaubert & Spach (1843: 133), Ephedra major Host (1831: 671), and Berberis integerrima Bunge
(1844: 145).
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FIGURE 5. The life-form spectrum of the flora of HWR. Ch: chamaephyte, G.b: bulbous geophyte, G.c: cormous geophyte, G.t: tuberous
geophyte, G.r: rhizomatous geophyte, G.p: parasitic geophyte, He: hemicryptophyte, Ph: phanerophyte, and Th: therophyte.
FIGURE 6. The proportion of the phytogeographical groups in the flora of HWR. Tri-regional (include: IT-ES-M, IT-ES-SS, and IT-MSS), Bi-regional (include: IT-ES, IT-M, IT-SS, and ES-M), IT: Irano-Turanian, ES: Euro-Siberian, M: Mediterranean, SS: Sahara-Sindian,
COS: Cosmopolitan, SCO: Sub-cosmopolitan, and PL: Pluri-regional.
Marl foothills are mainly covered by halophytic species viz. Krascheninnikovia ceratoides (Linnaeus 1753:
979) Gueldenstaedt (1772: 555), Salsola arbusculiformis Drobow (1916: 142), and Reaumuria alternifolia Britten
(1916:110). The lands close to the summer villages, nomads’ pastures and areas along the side of roads are covered by
ruderal and invasive communities.
Discussion
The total number of 588 species and infraspecific taxa, 304 genera, and 65 families of vascular plants reported here
reveal the significance of the plant biodiversity of the area. Angiosperms include Dicots (472 spp., 243 genera and 47
families) followed by Monocots (111, 57 and 14), show the dominance of dicots (dicots to monocots ratio of four to
one) in the study area, typical to Iranian and Middle Asian floras (Kamakhina 1994). Gymnosperms and Ferns have
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a minor contribution to the floristic composition of the HWR. The richest plant families are Asteraceae, Fabaceae,
Poaceae, Brassicaceae, Lamiaceae, and Apiaceae. The majority of the species belong to small numbers of families.
These characteristics have also been reported for the floristic composition of the several areas in Iran (Ghahreman et al.
2006, Memariani et al. 2016a,c), of total flora of Iran (Ghahremaninejad & Nejad Falatoury 2016), and Turkmenistan
(Kamakhina 1994). Diverse terrains such as marl foothills, sliding slopes, rocks, streams, rivers, upland- villages and
available aquifers as well as meadows, and invasive plant communities make the HWR harboring a diverse flora.
The genera Astragalus, Cousinia, and Allium are the richest; however, the dominant vegetation cover belongs to
the Acantholimon, Astragalus, Artemisia and Acanthophyllum species. Characteristic mega-genera for the IT region
include Astragalus, Acanthophyllum, Acantholimon, Cousinia, Eremurus Marschall von Bieberstein (1810: 61), and
Eremostachys Bunge (1830: 414) (Manafzadeh et al. 2016). Astragalus is a characteristic IT element (Manafzadeh et
al. 2016) and according to Maassoumi (2005), the total number of taxa of this genus in Iran is 804 so this country is
one of the main center of speciation for this genus. Cousinia as one of the largest genera of Asteraceae and one of the
50 largest genera of flowering plants (Frodin 2004; López-Vinyallonga et al. 2009), has the highest species diversity
in the IT region and the mountains of Central Asia (López-Vinyallonga et al. 2009).
It has been reported that 22 (Jalili & Jamzad 1999) to 24% (Akhani 2006) of the plant taxa are endemic to
Iran. The average number of endemics per million hectares of the whole country is 10.46 species (Jalili & Jamzad
1999). The occurrence of two sub-endemic genera viz. Diaphanoptera Rechinger (1940: 41) (Caryophyllaceae) and
Sclerorhachis (Rechinger 1944: 4) Rechinger (1968: 242) (Asteraceae), and 64 Iranian endemic species in the HWR
demonstrates a high rate of plant endemism in such a small area. The total 66 plant taxa (11.22% of the flora of HWR)
are endemic to the KK floristic province, i.e. NE Iran and S Turkmenistan. The rate of the endemism in the KK is
about 14% of the total flora (Memariani et al. 2016a,b). Except for Ranunculus cicutarius Schlechtendal (1819: 25)
as a Euro-Siberian/Hyrcanian (ESHy) regionally endemic species, all other endemics in the HWR belong to the IT
region. The families over-represented in terms of endemics include Fabaceae, Asteraceae, and Lamiaceae. The genera
Astragalus and Cousinia have the highest number of endemic species in the HWR. According to the “Red Data Book
of Iran” (Jalili & Jamzad 1999), there is a similar picture for families and genera of the total flora of Iran.
Most of the endemics in the study area represent hemicryptophyte or chamaephyte life-forms. Hemicryptophytes
are the dominant life-form (41.50%) in the HWR followed by therophytes (28.06%). Cryptophytes (Geophytes), with
different regenerating bodies, present 15.13% of species. Finally, 11.39% and 3.91% of the species are chamaephytes
or phanerophytes, respectively. The cold and semi-arid climate of the HWR provide suitable conditions for the
occurance of hemicryptophytes. Approximately 20% of the flora of Iran (Jalili & Jamzad 1999) and 13% of the World’s
flora (Raunkiaer 1934) are annuals. Therefore, by comparison, the flora of HWR is rich in annuals. The number of
therophytes often decreases with increasing elevation as they become quite rare in the higher elevations. Nevertheless,
annual species of Polygonum Linnaeus (1753: 359) and Veronica Linnaeus (1753: 9) are well-represented in the subalpine flora of HWR. Although chamaephytes have a relatively low contribution to the life-form spectrum (11.39%),
they play a major role in the vegetation of the HWR as suffruticose and thorny cushion formations.
According to the classification of floristic regions (Zohary 1973, Takhtajan 1986, Léonard 1988, 1993), the study
area is located in the Irano-Turanian (IT) region. IT elements comprise more than 69% of the flora of the HWR.
Widespread elements (11.84%), i.e. pluri-regional, sub-cosmopolitan and cosmopolitan species, make up a remarkable
proportion of the flora. The IT region is differentiated from neighboring areas by the degree of continentality, seasonality
of precipitation, and winter temperature. Continentality is the most important bioclimatic factor responsible for floristic
differences between sub-regions of the IT region. The vast range of the IT region appears to be homogeneous in
physiognomy, but different vegetation types are extremely rich in taxonomic, genetic, and beta-diversity (Djamali et
al. 2012). Main subdivisions of IT elements in HWR are widespread IT (26.8%), Central IT (20.34%), IT elements
endemic to KK floristic province (16.38%), and Central-Eastern IT (11.16%). The IT region has long been regarded
as the source of many taxa, especially xerophytes, found in adjacent regions (Manafzadeh et al. 2013). The “donor”
character of the IT region, by which new species disperse into neighboring regions, renders it particularly important to
a conservation standpoint.
Juniperus polycarpos is considered a resistant pioneer tree species in the harsh climatic conditions of stony slopes
at elevations ranging from 1000 to 3500 m in Iran (Pirani et al. 2011). This plant is easily resistant to dry summers
and harsh winters. It forms open woodlands mixed with Amygdalus scoparia Spach (1843: 109) and Pistacia atlantica
Desfontaines (1799: 364) in the central and western parts of Iran (Zohary 1973), and also with Acer monspessulanum
Linnaeus (1753: 1056) in the northeast of Iran (Akhani 1998, Memariani 2016a, 2016c); however, J. polycarpos
associates with Cotoneaster Medikus (1789: 154), lonicera Linnaeus (1753: 173), and Ephedra Linnaeus (1753:
1040) species in the HWR. Indigenous people use J. polycarpos for the backbone of buildings, firewood, etc. In the
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past decades, removal of the canopy through clear-cutting was responsible for the changes of juniper woodlands to the
steppes in the NE Iran.
Many water resources in the area, such as temporary and permanent rivers, streams and springs, caused a unique
habitat for hydrophyte plants. Although most of such wet habitats do not have a major role in the whole vegetation of
the area, but they are important ecosystems with regard to biodiversity. The riparian vegetation in the HWR consists
of communities dominated mainly by Salix Linnaeus (1753: 1015) spp., Berberis integerrima, tamarix ramosissima
Ledebour (1829: 424), Rosa beggeriana Schrenk (1841: 73), and Calamagrostis pseudophragmites (Haller 1797: 11)
Koeler (1802: 106). The “Alatman River” and the Alatman earth-dam in the north of the HWR, surrounded densely
by Phragmites australis (Cavanilles 1799: 100) Trinius ex Steudel (1841: 324), have made a suitable habitat for
Zannichellia palustris Linnaeus (1753: 969) which is the only hydrophyte plant in the HWR.
Based on the Sørensen similarity Index, the floristic composition of HWR revealed the greatest similarity
(57.64%), to the flora of Fereizi (Memariani et al. 2009). The Fereizi area is closest in distance to the HWR comparing
with the two others; Ghorkhod Protected Area (Memariani et al. 2016c) and Baghshangach (Ghahreman et al. 2006)
have less than 50% similarity of the floristic composition to HWR. The Fereizi and Baghshangach are located in the
central Khorassan-Kopet Dagh in the Binalood mountain range, while the Ghorkhod P. A. is located in the western
Khorassan-Kopet Dagh. More studies on the floristic composition of different habitats in Binalood and Kopet Dagh
ranges may reveal the distinctiveness of the flora.
Anthropogenic and environmental changes decrease the resistance of ecosystem productivity to climate events
and drive biodiversity loss, which probably causes ecosystem instability (Isbell 2015). The HWR has traditionally
been used for grazing, harvesting for firewood, winter forage, and medical purposes. The most important medicinal
plants include: Nepeta binaloudensis Jamzad (1991: 25) (Figure 4 d), Hymenocrater Fischer & Meyer (1835: 39) spp.,
Stachys lavandulifolia Vahl (1790: 42), Ziziphora clinopodioides Lamarck (1791: 63), Ferula Linnaeus (1753: 246)
spp., Elwendia Linnaeus (1753: 243) spp., Astragalus spp., etc. Forage species as winter silages include Medicago
Linnaeus (1753: 778) spp., Onobrychis Miller (1754: 970) spp., trifolium Linnaeus (1753: 764) spp., grasses, and even
thorny species like Gundelia tournefortii Linnaeus (1753: 814) (Figure 3 e). The additional other ecosystem services
in the HWR contain clean water, hunting, climbing, tourism, etc. In recent years, the disturbing effect by the humans
has arisen due to the return of aboriginal inhabitants to rural areas with new housing, introduction of invasive species,
and increasing pressure of grazing (Figure 3 f). These disturbances have led to a more urgent necessity to organize
conservation activities and recording the floristic richness.
Furthermore, the HWR is housing many endemic, rare, vulnerable or endangered species. For example,
Helictotrichon turcomanicum Czopanov (1970: 23), a rare species, is reported as a second record in Iran after Memariani
et al. (2016c). The type locality for Cousinia amicorum is located in the study area. Carex serotina subsp. philocrena
Kukkonen (1984: 387) and linum album Kotschy ex Boissier (1846a: 27), mainly distributed in central and western
parts of Iran, are recorded as new to the flora of Khorassan. At least ten plant species such as Nepeta binaloudensis
(Figure 4 d) and Astragalus assadii Maassoumi & Podlech (in Podlech & Maassoumi 1987: 98) are endangered taxa.
Many species viz. Astragalus catacamptus Bunge (1870: 191), A. controversus Maassoumi & Podlech (in Podlech
& Maassoumi 1987: 98), etc. are vulnerable and facing a high risk of extinction in the wild in the medium-term
future (Figure 4, Appendix I). The HWR is the habitat of 114 species that are endemic to Iran or to the NE of Iran
and neighbouring countries (Turkmenistan and Afghanistan). The HWR is known as the “Heaven of Mouflons” for
supporting many herds of urials. Protection of the plant diversity of the HWR should be given urgent priority by
government and the people of this region.
Conclusion
The occurrence of 588 species and infraspecific taxa of vascular plants in a semi-arid, continental climate condition,
reveals the significance of the plant diversity of the Heydari Wildlife Refuge (HWR) in NE Iran. Diverse physiography
and habitats such as springs, rivers, shallow aquifers as well as meadows, reflect the HWR harboring a diverse flora.
The HWR with its high rate of plant endemism (19.56%) is home to two regionally endemic genera and 114 endemic
and sub-endemic plant species. Considering the conservation status and the life-form of the plants, most of the
endemics in the HWR are endangered or vulnerable which include hemicryptophytes or chamaephytes. Well-adapted
to cold and drought, hemicryptophytes are dominant life-forms followed by therophytes, in the HWR. Chamaephytes
as suffruticose or thorny cushions also play a major role in the vegetation, but minor in the life-form spectrum of the
HWR. The HWR is located in the center of Khorassan-Kopet Dagh (KK) province of Irano-Turanian (IT) floristic
PLANT DIVERSITy OF THE HEyDARI WILDLIFE
Phytotaxa 340 (2) © 2018 Magnolia Press • 109
region. Approximately 69% of the HWR’s flora encompasses IT elements. The “donor” character of the IT region to
the neighboring areas, is extensible to the HWR because it has approximately 50% floristic similarities to the adjacent
areas based on the Sørensen index, besides accommodating diverse elements of IT subdivisions. Judging from an
annotated list of floristic composition and diverse plant formations (cushion steppes, grasslands, sparse woodlands,
hydrophytes, etc.) resulted from this study, the HWR needs an urgent priority to the government and the aboriginals for
conserving and maintaining the title “Heaven of Mouflons” by supporting the urial herds’ habitat.
FIGURE 7. The numbers of Irano-Turanian elements in the flora of HWR. Delimitation and abbreviation of chorological subdivisions
are based on Akhani (1998) and Memariani et al. (2016a). IT (or ITOmni): Species distributed widely in the whole Irano-Turanian region or
with a wide range that cannot be categorized within the subdivisions defined in this work; ITKK: Mountainous areas in NE Iran and Kopet
Dagh range in southern Turkmenistan; ITKK-Afgh.: Mountainous areas in the NE Iran and Kopet Dagh range in the S Turkmenistan and also N
and NW Afghanistan; ITW: Preliminarily defined as the Anatolian and western Iranian montane and sub-montane flora; ITC: Species whose
distribution is confined to the montane and sub-montane areas and the steppes in Central Iran (southern slopes of the Alborz Range, eastern
slopes of the Zagros Range), mountains in NE Iran and S Turkmenistan (ITKK) and most of the west and central parts of Afghanistan; ITE:
Species occuring mainly in the Middle and Central Asia but with disjunct occurrences in one or a few localities in eastern KhorassanKopet Dagh; ITAlborz: Species exclusively distributed in the montane steppes along the Alborz Range.
Acknowledgements
We wish to thank the office of the Vice President for Research and Technology, Ferdowsi University of Mashhad for
financial support (grant number: 33474). Special thanks go to the staff of “Department of Environment” of Razavi
Khorassan Province for giving permission to collect the botanical specimens, and to the HWR’s guard officers,
especially Mr. Barakshahi, Hatami and Javanbakht for their invaluable coorporation in the field. We also wish to
acknowledge with appreciation V. Jafari, Z. Maleki, H. Atashgahi and S. Tavakoli for the field trips, and Dr. y. Nasseh
for identification of Astragalus spp., Dr. F. Memariani for identification of the grasses and confirming the chorotypes,
M.R. Joharchi for identification of several critical taxa, and M. Javidi for helping in the preparation of the maps.
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Tzvelev, N.N. (1976) Grasses of the Soviet Union. Nauka Publishers, Leningrad.
Vahl, M. (1790) Symbolae botanicae, sive plantarum, tam earum, quas in itinere, imprimis orientali. Part 1. Imprensis auctoris, excudebant
N. Möller et filius, Hauniae, 85 pp.
Zohary, M. (1973) Geobotanical Foundations of the Middle East. 2 vols. Gustav Fischer Verlag, Stuttgart, 765 pp.
114 • Phytotaxa 340 (2) © 2018 Magnolia Press
ATASHGAHI Et Al.
Appendix I. Checklist of vascular plants of the HWR. Life-forms: Ch (chamaephyte), G.b (bulbous geophyte),
G.c (cormous geophyte), G.t (tuberous geophyte), G.r (rhizomatous geophyte), G.p (parasitic geophyte), He
(hemicryptophyte), Ph (phanerophyte), Th (therophyte). Chorotypes according to Akhani (1998) and Memariani et
al. (2009, 2016a,b,c). IT: Irano-Turanian (for chorological subdivisions of IT elements, refer to Fig. 7); ES: EuroSiberian; M: Mediterranean; SS: Sahara-Sindian; COS: Cosmopolitan; SCO: Sub-cosmopolitan; PL: Pluri-regional.
Iranian endemics are marked by one and regional endemics by two asterisks. Threat categories are given only for
those species evaluated by Jalili & Jamzad (1999) [1] and Memariani et al. (2016b) [2] for plant species of Iran:
EN (Endangered), VU (Vulnerable), LR (Lower Risk), DD (Data Deficient), LC (Least Concern), and NT (Near
Threatened). All specimens are preserved in the Faculty of Science Herbarium, Ferdowsi University of Mashhad
(FUM). Some duplicates are deposited in the Herbarium of Ferdowsi University of Mashhad (FUMH) and Herbarium
of Noshahr Botanical Garden (HNBG).
No.
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
36
37
38
39
Families and species/infraspecific taxa
Amaranthaceae Juss. (including Chenopodiaceae Vent.)
Ceratocarpus arenarius L.
Chenopodium foliosum Asch.
Chenopodium glaucum L.
Dysphania botrys (L.) Mosyakin & Clemants (=Chenopodium
botrys L.)
Krascheninnikovia ceratoides (L.) Gueldenst.
Noaea mucronata (Forssk.) Asch. & Schweinf.
Salsola arbusculiformis Drobow
Spinacia turkestanica Iljin
Amaryllidaceae J.St.-Hil.
Allium ampeloprasum L.
Allium atroviolaceum Boiss.
Allium cristophii Trautv.
Allium ellisii Hook.f.
Allium kopetdagense Vved.
Allium kuhsorkhense R.M.Fritsch & Joharchi
Allium rubellum M.Bieb.
Allium scabriscapum Boiss.
Allium tenuicaule Regel
Allium xiphopetalum Aitch. & Baker
Apiaceae Lindl.
Bupleurum falcatum L.
Chaerophyllum macrospermum (Willd. ex Spreng.) Fisch. &
C.A.Mey. ex Hohen.
Conium maculatum L.
Elwendia afghanica (Beauverd) Pimenov & Kljuykov
Elwendia cylindrica (Boiss. & Hausskn.) Pimenov & Kljuykov
Elwendia intermedia (Korovin) Pimenov & Kljuykov
Elwendia persica (Boiss.) Pimenov & Kljuykov
Eryngium billardierei F.Delaroche
Eryngium bungei Boiss.
Falcaria vulgaris Bernh.
Ferula alliacea Boiss.
Ferula diversivittata Regel & Schmalh.
Ferula flabelliloba Rech.f. & Aellen
Ferula gummosa Boiss.
Ferula ovina (Boiss.) Boiss.
Ferula szowitziana DC.
Galagania tenuisecta (Regel & Schmalh.) M.G.Vassiljeva &
Pimenov
Heracleum persicum Desf. ex Fisch., C.A.Mey. & Avé-Lall.
Johrenia platycarpa Boiss.
Pimpinella tragium Vill.
Prangos latiloba Korovin
PLANT DIVERSITy OF THE HEyDARI WILDLIFE
Life-form
Chorotype
Threat
category
[Ref.]
Th
Th
Th
Th
IT C & E
PL
PL
PL
7200
7201
7202
7203, 8084
Ch
Ch
Ch
Th
IT-ES-M
IT-ES-M
IT KK-E
IT C & E
7204, 8082–3
7205, 8081
7206, 8080
7207
G.b
G.b
G.b
G.b
G.b
G.b
G.b
G.b
G.b
G.b
IT-ES-M
IT
IT KK *
IT KK *
IT KK
IT KK *
IT Cauc.-Turk.
IT W & C
IT KK-E
IT C & E
7208, 8079
7209
7210, 8079
7211
7212
7213, 7078, 8078
7214, 8077
7215, 7076
7216, 8075
7217, 8074
Ch
G.t
IT Omni
IT Omni
He
G.t
G.t
G.t
G.t
He
He
He
He
He
He
PL
IT KK-E
IT
IT KK-E
IT C & E
IT C
IT C
IT-ES-M
IT C *
IT C & E
IT KK *
He
He
He
G.t
IT C
IT C & E
IT W & C
IT KK-E
He
He
He
He
IT C
IT C*
IT-ES-M
IT C
LC [2]
VU [2]
LC [2]
NT [2]
Herbarium No.
7222, 8067, 8068
7223, 8066
7224
7218, 8071–3
7219, 8069–70
7220
7221, 8064
7225
7226, 8065
7227
7228
7229, 8063
VU [1], EN 7230
[2]
LR [1]
7231
7232, 8061, 8085
7233
7234
7235
7236, 8060
7237
7238, 8059
Phytotaxa 340 (2) © 2018 Magnolia Press • 115
No.
Families and species/infraspecific taxa
Life-form
Chorotype
40
Pseudotrachydium vesiculosoalatum (Rech.f.) Pimenov &
Kljuykov
Scandix stellata Banks & Sol.
Semenovia tragioides (Boiss.) Pimenov & V.N. Tikhom.
turgenia latifolia (L.) Hoffm.
Zeravschania aucheri (Boiss.) Pimenov
Ch
IT KK-Afgh.
Th
He
Th
He
IT-M
IT C
IT-M
IT C*
Zosima absinthifolia Link
Apocynaceae Juss.
Vincetoxicum pumilum Decne.
He
IT Omni
He
IT KK
41
42
43
44
45
46
Threat
category
[Ref.]
Herbarium No.
7239,
45496(FUMH)
7240, 8057–8
7241
7242
7243, 8055–6,
8062
7244
LR [1], LC
[2]
7245
G.t
IT W & C
7246, 8113
48
49
50
Araceae Juss.
Arum rupicola Boiss.
Asparagaceae Juss.
Asparagus breslerianus Schult. & Schult.f.
Bellevalia saviczii Woronow
Fessia khorassanica (Meikle) Speta
Ch
G.b
G.b
IT Omni
IT C
IT KK *
7247
7248, 8054
7249, 8052–3
51
Hyacinthus litwinovii Czerniak.
G.b
IT KK
52
53
G.b
G.r
IT-ES-M
IT KK-E
7251
7252, 8050
G.r
G.r
G.r
G.r
IT C
IT KK-E
IT
IT C & E*
7779
7780, 7784
7781
7782
G.r
IT E
7783
G.r
COS
7253
He
He
PL
IT
7254
7255
He
He
Ch
Ch
He
Th
He
Ch
Th
He
He
He
He
He
PL
IT KK-E
IT KK-Afgh.
PL
IT
IT-M
IT-ES EH
IT
IT W & C
PL
PL
IT KK
IT KK-E
IT
7256
8037-8038
7257, 8048–9
7258
7259
7260
7261
7262, 8047
7263, 8046, 8087
7264
7265
7266, 8045
7267
7268
76
77
Muscari neglectum Guss. ex Ten.
Polygonatum sewerzowii Regel
Asphodelaceae Juss.
Eremurus luteus Baker
Eremurus olgae Regel
Eremurus spectabilis M.Bieb.
Eremurus stenophyllus (Boiss. & Buhse) Baker (=Eremurus
stenophyllus subsp. stenophyllus)
Eremurus stenophyllus subsp. aurantiacus (Baker) Wendelbo
Aspleniaceae Newman
Asplenium ruta-muraria L.
Asteraceae Bercht. & J.Presl
Achillea arabica Kotschy
Achillea santolinoides subsp. wilhelmsii (K.Koch) Greuter
(=Achillea wilhelmsii K.Koch)
Arctium lappa L.
Arctium umbrosum (Bunge) Kuntze
Artemisia kopetdaghensis Krasch., Popov & Lincz. ex Poljakov
Artemisia scoparia Waldst. & Kitam.
Centaurea behen L.
Centaurea benedicta (L.) L. (=Cnicus benedictus L.)
Centaurea iberica Trevir. ex Spreng.
Centaurea virgata Lam.
Chardinia orientalis (L.) Kuntze
Cichorium intybus L.
Cirsium arvense (L.) Scop.
Cirsium bornmuelleri Sint. ex Bornm.
Cirsium pseudolappaceum Kharadze
Cirsium sorocephalum Fisch. & C.A.Mey. (=Cirsium
congestum Fisch. & C.A.Mey. ex DC.)
Cirsium vulgare (Savi) Ten.
Cousinia amicorum Tscherneva, Joharchi & Ghahrem.-Nejad
He
He
PL
IT KK *
78
79
Cousinia attariae Assadi & Joharchi
Cousinia bienertii Bunge
He
He
IT KK *
IT KK *
80
81
82
Cousinia concolor Bunge
Cousinia congesta Bunge
Cousinia deserti Bunge
He
He
He
IT KK-Alborz*
IT C
IT C
47
54
55
56
57
58
59
60
61
62
63
64
65
66
67
68
69
70
71
72
73
74
75
116 • Phytotaxa 340 (2) © 2018 Magnolia Press
DD [1], VU
[2]
LR [1], NT
[2]
LR [1]
VU [2]
VU [2]
EN [2]
DD [1], EN
[2]
DD [1]
7250, 8051
7269
7270,
45486(FUMH)
7271
7273
7272, 8043
7274, 8044
7275
ATASHGAHI Et Al.
No.
Families and species/infraspecific taxa
Life-form
Chorotype
83
84
85
86
87
88
Cousinia elata Boiss. & Buhse
Cousinia eryngioides Boiss.
Cousinia euchlora Bornm. & Rech.f.
Cousinia freynii Bornm. & Sint.
Cousinia lasiandra Bunge
Cousinia lasiolepis Boiss.
He
He
He
He
He
He
IT KK-Alborz*
IT C*
IT KK
IT KK *
IT C*
IT C*
89
90
91
92
93
Cousinia microcarpa Boiss.
Cousinia multiloba DC.
Cousinia smirnowii Trautv.
Cousinia stahliana Bornm. & Gauba
Cousinia verbascifolia Bunge
He
He
He
He
He
IT KK-Afgh.
IT C
IT KK *
IT KK *
IT KK *
94
95
96
Crepis pulchra L.
Crepis turcomanica Krasch.
Cyanus depressus (M.Bieb.) Soják (=Centaurea depressa
M.Bieb.)
Cymbolaena griffithii (A.Gray) Wagenitz
Echinops leiopolyceroides Mozaff.
Echinops orientalis Trautv.
Echinops ritrodes Bunge
Erigeron acris subsp. pycnotrichus (Vierh.) Grierson
Garhadiolus hedypnois Jaub. & Spach (=Garhadiolus
angulosus Jaub. & Spach)
Gundelia tournefortii L.
Helichrysum oocephalum Boiss.
Inula peacockiana (Aitch. & Hemsl.) Korovin
(=Codonocephalum peacockianum Aitch. & Hemsl.)
Inula rhizocephala Schrenk
Jurinea radians Boiss.
Jurinea sintenisii Bornm.
Th
G.r
Th
IT
IT KK
IT
Th
He
He
He
He
Th
IT
IT KK *
IT W & C
IT C
PL
IT
He
He
He
IT
IT C
IT
G.r
He
Ch
IT C & E
IT C*
IT KK
Th
Ch
G.t
He
Ch
He
He
He
Ch
He
IT-SS
IT
IT
IT-ES-M
IT C
IT W & C
IT
IT-M
IT C
PL
He
He
G.t
G.t
G.t
G.t
G.t
G.t
G.r
IT KK
IT-ES-M
IT Cauc.-Turk.
IT W & C
IT C
IT W & C*
IT Cauc.-Alburz
IT C
IT C
128
129
130
Koelpinia linearis Pall.
lactuca orientalis (Boiss.) Boiss. (=Scariola orientalis Boiss.)
lactuca persica Boiss.
lactuca serriola L.
launaea acanthodes (Boiss.) Kuntze
leontodon asperrimus (Willd.) Endl.
Onopordum leptolepis DC.
Picnomon acarna (L.) Cass.
Pulicaria gnaphalodes (Vent.) Boiss.
Rhaponticum repens (L.) Hidalgo (=Acroptilon repens (L.)
DC.)
Sclerorhachis platyrachis (Boiss.) Podlech ex Rech.f.
Scorzonera laciniata Jacq.
Scorzonera leptophylla (DC.) Krasch. & Lipsch.
Scorzonera phaeopappa (Boiss.) Boiss.
Scorzonera raddeana C.Winkl.
Scorzonera stenocephala Boiss.
Scorzonera szovitzii DC.
Scorzonera tunicata Rech.f. & Köie
Senecio paulsenii subsp. khorasanicus (Rech.f. & Aellen)
B.Nord.
Serratula latifolia Boiss.
Sonchus oleraceus (L.) L.
tanacetum khorassanicum (Krasch.) Parsa
He
Th
He
IT C
PL
IT KK *
131
tanacetum parthenium (L.) Sch.Bip.
He
PL
97
98
99
100
101
102
103
104
105
106
107
108
109
110
111
112
113
114
115
116
117
118
119
120
121
122
123
124
125
126
127
PLANT DIVERSITy OF THE HEyDARI WILDLIFE
Threat
category
[Ref.]
VU [1,2]
EN [2]
LR [1]
NT [2]
LR [1], NT
[2]
NT [2]
LC [2]
Herbarium No.
7276
7277, 8042
7278
7279
8124
7280, 8041,
45487–8(FUMH)
7281
7282
7283, 8039, 8040
7284
7285
7286
7287, 8036
7288
7289, 8035
7290
7291
7292, 8034
7293, 8032–3
7294
7295
7296
7297
DD [1]
DD [1], LC
[2]
7298
7299
7300, 8031
7301, 8030
7302, 8028
7303, 8029
7304
7305
7306
7307
7308
7309
7310
LC [2]
LR [1]
DD [1], NT
[2]
7311
7312
7316, 8146
7313, 8027, 8023
7317, 8026
7314, 8022
7315
8148
7318, 8025
7319
7320
7321, 8156
7322, 8155
Phytotaxa 340 (2) © 2018 Magnolia Press • 117
No.
Families and species/infraspecific taxa
Life-form
Chorotype
132
133
134
taraxacum afghanicum Soest
taraxacum microcephaloides Soest
taraxacum sonchoides (D.Don) Sch.Bip. (=taraxacum
montanum (C.A.Mey.) DC.)
taraxacum sp.
He
He
He
IT E
IT
IT
7323
7326
7329
taraxacum syriacum Boiss.
thevenotia persica DC.
tragopogon collinus DC.
tragopogon gaudanicus Boriss.
tragopogon montanus S.A.Nikitin
tragopogon vaginatus Ownbey & Rech.f.
tripleurospermum disciforme (C.A.Mey.) Sch.Bip.
tussilago farfara L.
Varthemia persica DC.
Xanthium spinosum L.
Xeranthemum longepapposum Fisch. & C.A.Mey.
Berberidaceae Juss.
Berberis integerrima Bunge
He
Th
He
He
He
He
Th
G.t
Ch
Th
Th
IT
IT C
IT C
IT C
IT C & E
IT W & C
IT
IT-ES-M
IT C
COS
IT
7324–5, 7327–8,
8147
7330–1
7332
7333, 8021, 8154
7334
7335, 8024
7336
7337, 8086
7338
7339
7340
7341
Ph
IT
Bongardia chrysogonum (L.) Spach
leontice leontopetalum L.
Biebersteiniaceae Schnizl.
Biebersteinia multifida DC.
Boraginaceae Juss.
Anchusa azurea Mill.
Asperugo procumbens L.
Buglossoides tenuiflora (L.f.) I.M.Johnst.
Caccinia macranthera (Banks & Sol.) Brand
Echium italicum L.
Heterocaryum szovitsianum (Fisch. & C.A.Mey.) A.DC.
lappula barbata (M.Bieb.) Gürke
lappula microcarpa (Ledeb.) Gürke
lappula sessiliflora Gürke
lappula sinaica (A.DC.) Asch. & Schweinf.
Myosotis stricta Link ex Roem. & Schult.
Nonnea caspica G. Don
Onosma dichroantha Boiss.
Onosma longiloba Bunge
Paracaryum heratense (Rech.f. & Riedl) Kamelin
Rochelia cardiosepala Bunge
Rochelia disperma (L.f.) K.Koch
Rochelia peduncularis Boiss.
Rochelia persica Bunge ex Boiss.
Brassicaceae Burnett
Aethionema carneum (Banks & Sol.) B.Fedtsch.
Aethionema trinervium (DC.) Boiss.
Alliaria petiolata (M.Bieb.) Cavara & Grande
Alyssum alyssoides (L.) L.
Alyssum dasycarpum Stephan ex Willd.
Alyssum desertorum Stapf
Alyssum heterotrichum Boiss.
Alyssum lanceolatum Baumg.
Alyssum linifolium Stephan ex Willd.
Alyssum singarense Boiss. & Hausskn.
Alyssum stapfii Vierh.
Alyssum szovitsianum Fisch. & C.A.Mey.
Alyssum turkestanicum Regel & Schmalh.
G.t
G.t
IT
IT-M
7342, 8018–20,
8122
7343, 8017
7344, 8016
G.t
IT
7345, 8088
He
Th
Th
Th
He
Th
Th
Th
Th
Th
Th
Th
He
He
He
Th
Th
Th
Th
IT-ES
PL
IT-M
IT
IT-M
IT
IT-M
IT
IT
IT
IT-ES-M
IT
IT W & C
IT KK-Alborz
IT KK-Afgh.
IT
IT C
IT
IT
7346
7347
7348
7349
7350
7613
7351, 8015, 8089
7352, 8012–4
7353
7354
7355
7356
7357
7358, 8011, 8090
7359
7360
7361, 8010
7362, 8009
7363, 8008, 8140
Th
Ch
He
Th
Th
Th
Th
Ch
Th
He
Th
Th
Th
IT
IT
IT-ES-M
IT-ES-M
IT
IT-ES-M
IT C
IT KK-Afgh.
IT-M
IT W
IT
IT C
IT C & E
7364, 8007
7365, 8006
8127
7366, 8005
7367
7368
7369
7370, 8001–4
7371, 8103
7372, 7998–8000
7373, 7997
7374, 7995–6
7375, 8091
135
136
137
138
139
140
141
142
143
144
145
146
147
148
149
150
151
152
153
154
155
156
157
158
159
160
161
162
163
164
165
166
167
168
169
170
171
172
173
174
175
176
177
178
179
180
181
182
118 • Phytotaxa 340 (2) © 2018 Magnolia Press
He
Threat
category
[Ref.]
Herbarium No.
ATASHGAHI Et Al.
No.
Families and species/infraspecific taxa
Life-form
Chorotype
183
184
Arabis nova Vill.
Asperuginoides axillaris (Boiss. & Hohen.) Rauschert
(=Buchingera axillaris Boiss. & Hohen.)
Barbarea plantaginea DC.
Brassica elongata Ehrh.
Camelina rumelica Velen.
Capsella bursa-pastoris (L.) Medik.
Chorispora tenella (Pall.) DC.
Clypeola jonthlaspi L.
Conringia clavata Boiss.
Conringia orientalis (L.) Dumort.
Crambe cordifolia subsp. kotschyana (Boiss.) Jafri (=Crambe
kotschyana Boiss.)
Descurainia sophia (L.) Webb ex Prantl
Diptychocarpus strictus (Fisch. ex M.Bieb.) Trautv.
Draba nuda (Bél.) Al-Shehbaz & M.Koch (=Drabopsis verna
K.Koch)
Erophila verna (L.) DC.
Erysimum badghisi (Korsh.) Lipsky ex N.Busch
Erysimum ischnostylum Freyn & Sint
Euclidium syriacum (L.) R.Br.
Fibigia suffruticosa (Vent.) Sweet
Goldbachia laevigata (M.Bieb.) DC.
Graellsia integrifolia (Rech.f.) Rech.f.
Th
Th
IT-ES-M
IT
He
He
Th
Th
Th
Th
Th
Th
He
IT
IT-ES-M
IT-ES-M
PL
IT Omni
IT-M
IT
IT-ES-M
IT
7378, 7994
7379
7380
7381
7382, 8119
7383, 7993
7384, 8118
7385, 7992
7386
Th
Th
Th
PL
IT-ES
IT-ES-M
7387
7388
7389, 8092
Th
He
He
Th
Ch
Th
He
PL
IT KK-Afgh.
IT KK-Afgh.
IT
IT C
IT
IT KK *
7390
7391
7392, 7989–91
7393
7394, 7988
7395
7396
lepidium draba L. (=Cardaria draba (L.) Desv.)
lepidium latifolium L.
lepidium litwinowii (Lipsky) Al-Shehbaz (=Stroganowia
litwinowii Lipsky)
litwinowia tenuissima (Pall.) Woronow ex Pavlov (=Euclidium
tenuissimum (Pall.) B.Fedtsch.)
Malcolmia africana (L.) R.Br.
Matthiola afghanica Rech. fil. & Koie
Matthiola alyssifolia Bornm.
Neotorularia dentata (Freyn & Sint.) Hedge & J. Léonard
Pachypterygium brevipes Bunge
Peltaria angustifolia DC.
Pseudoclausia turkestanica (Lipsky) A.V.Vassil.
Sisymbrium loeselii L.
Sisymbrium septulatum DC.
tauscheria lasiocarpa Fisch. ex DC.
thlaspi arvense L.
Capparaceae Juss.
Capparis spinosa L.
Caprifoliaceae Juss.
Cephalaria microcephala Boiss.
lomelosia olivieri (Coult.) Greuter & Burdet (=Scabiosa
olivieri Coult.)
lonicera nummulariifolia Jaub. & Spach
He
He
He
IT-ES
IT-ES-M
IT KK
Th
IT C & E
7400
Th
He
He
Th
Th
Th
He
Th
Th
Th
Th
IT-M-SS
IT KK-Afgh.
IT C & E
IT C
IT C & E
IT C
IT KK-E
IT-ES
IT
IT
PL
7401
7402, 8101
7403, 7984
7404
8102
7406, 8117
7407, 7982–3
7408
7409
7410
7411
Ph
SCO
7412
He
Th
IT C
IT
7460, 7953
7413
Ph
IT
Pterocephalus afghanicus Boiss.
Valeriana sisymbriifolia Vahl
Valerianella cymbocarpa C.A.Mey.
Valerianella oxyrhyncha Fisch. & C.A.Mey.
Valerianella plagiostephana Fisch. & C.A.Mey.
Valerianella szovitsiana Fisch. & C.A.Mey.
Valerianella tuberculata Boiss.
Caryophyllaceae Juss.
He
He
Th
Th
Th
Th
Th
IT C
IT W & C
IT
IT
IT
IT Omni
IT
7414, 7980–1,
4887(HNBG)
7461
7415, 7979
7416
7417, 7978
7418
7419, 7976
7420, 7977
185
186
187
188
189
190
191
192
193
194
195
196
197
198
199
200
201
202
203
204
205
206
207
208
209
210
211
212
213
214
215
216
217
218
219
220
221
222
223
224
225
226
227
228
229
PLANT DIVERSITy OF THE HEyDARI WILDLIFE
Threat
category
[Ref.]
LR [1]
LR [1], NT
[2]
NT [2]
Herbarium No.
7376, 8120
7377
7397, 7987
7398, 7986
7399, 7985
Phytotaxa 340 (2) © 2018 Magnolia Press • 119
No.
Families and species/infraspecific taxa
Life-form
Chorotype
230
231
232
233
234
235
236
237
Ch
Ch
Ch
Ch
Ch
Ch
Th
Th
IT KK
IT C & E
IT KK-Afgh.
IT C
IT C
IT KK-Afgh.
IT
IT
Ch
Ch
Ch
He
Th
Th
IT KK-Afgh.
IT KK
IT KK *
IT-M
IT
7428, 7969
7429, 8138
8125–6
7430
7431
7432, 7968
Th
IT
7433
Th
Th
He
Th
Th
He
Ch
He
Th
IT C & E
IT C
IT
IT-M
IT
IT-M
IT KK
IT W & C
IT C & E
7442
7434, 8093
7435, 7966–7
7436
7437, 7965
7438
7439, 7964, 8137
7440, 7963, 8094
7441, 7961–2
He
IT C
7443
G.c
G.c
IT W & C
IT C & E
7444, 7920
7445, 7960
He
He
He
Th (holoparasite)
Th (holoparasite)
SCO
IT C & E
IT-ES-M
PL
PL
7446, 8095
7447
7448
7452
7453, 7958
He
He
IT C
IT C & E
7449
7450
Ph
IT KK
7451, 7959,
1675(HNBG)
G.r
G.r
He
He
He
G.r
IT C & E
IT-ES-M
IT
IT-ES
PL
PL
7454
7455
8096
7456, 7458
7457, 7956
7459, 7954
Ph
IT-M
7462, 7951–2
272
Acanthophyllum adenophorum Freyn
Acanthophyllum glandulosum Bunge ex Boiss.
Acanthophyllum korshinskyi Schischk.
Acanthophyllum pachystegium Rech.f.
Bufonia oliveriana Ser.
Bufonia sintenisii Freyn
Cerastium dichotomum L.
Cerastium dichotomum subsp. inflatum Cullen (=Cerastium
inflatum Link ex Desf.)
Dianthus crinitus subsp. turcomanicus (Schischk.) Rech.f.
Dianthus polylepis Bien. ex Boiss.
Diaphanoptera khorasanica Rech.f.
Gypsophila sp.
Herniaria glabra L.
Holosteum umbellatum subsp. glutinosum (M.Bieb.) Nyman
(=Holosteum glutinosum (M.Bieb.) Fisch. & C.A.Mey.)
lepyrodiclis holosteoides (C.A.Mey.) Fenzl ex Fisch. &
C.A.Mey.
lepyrodiclis holosteoides × stellarioides
lepyrodiclis stellarioides Fisch. & C.A.Mey.
Mesostemma kotschyana (Fenzl ex Boiss.) Vved.
Minuartia hamata (Hausskn.) Mattf.
Minuartia meyeri (Boiss.) Bornm.
Silene bupleuroides L.
Silene indeprensa Schischk.
Silene swertiaefolia Boiss.
Stellaria alsinoides Boiss. & Buhse
Cleomaceae Bercht. & J.Presl
Cleome coluteoides Boiss.
Colchicaceae DC.
Colchicum kotschyi Boiss.
Colchicum robustum (Bunge) Stef.
Convolvulaceae Juss.
Convolvulus arvensis L.
Convolvulus dorycnium L.
Convolvulus lineatus L.
Cuscuta campestris yunck.
Cuscuta europaea L. (=Cuscuta brevistyla A.Braun ex A.Rich.)
Crassulaceae J.St.-Hil.
Pseudosedum multicaule (Boiss. & Buhse) Boriss.
Rosularia radicosa (Boiss. & Hohen.) Eggli
Cupressaceae Gray
Juniperus polycarpos K.Koch var. turcomanica
(B.Fedtsch.) R.P.Adams
Cyperaceae Juss.
Bolboschoenus schmidii (Raymond) Holub
Carex diluta M.Bieb.
Carex serotina subsp. philocrena (V.I.Krecz.) Kukkonen
Carex songorica Kar. & Kir.
Carex stenophylla Wahlenb.
Scirpoides holoschoenus (L.) Soják
Elaeagnaceae Juss.
Elaeagnus angustifolia L.
Ephedraceae Dumort.
Ephedra intermedia Schrenk & C.A.Mey.
Ph
IT C
273
Ephedra major Host
Ph
IT-ES-M
7463,
9278(HNBG)
7464, 7948–50,
1821(HNBG)
238
239
240
241
242
243
244
245
246
247
248
249
250
251
252
253
254
255
256
257
258
259
260
261
262
263
264
265
266
267
268
269
270
271
120 • Phytotaxa 340 (2) © 2018 Magnolia Press
Threat
category
[Ref.]
LC [2]
VU [1,2]
VU [1,2]
NT [2]
Herbarium No.
7421, 7975
7422, 7972–4
8158
7423
7424
7425, 7971
7426, 7970
7427
ATASHGAHI Et Al.
No.
Families and species/infraspecific taxa
Life-form
Chorotype
G.r
PL
7465, 7947
Th
He
He
Th
He
Th
IT C
IT
IT W & C
IT KK-E
IT C
IT
7466, 7946
7467, 7944–5
7468, 7942–3
7469
7470, 7939–41
7471
He
He
IT-M-SS
IT KK
281
282
Equisetaceae Michx
Equisetum ramosissimum Desf.
Euphorbiaceae Juss.
Euphorbia aucheri Boiss.
Euphorbia boissieriana (Woronow) Prokh.
Euphorbia bungei Boiss.
Euphorbia franchetii B.Fedtsch.
Euphorbia microsciadia Boiss.
Euphorbia szovitsii Fisch. & C.A.Mey.
Fabaceae Lindl.
Alhagi maurorum Medik. (=Alhagi camelorum DC.)
Astragalus (Incani) ackerbergensis Freyn & Sint.
283
284
285
Astragalus (Hololeuce) alyssoides Lam.
Astragalus (Erioceras) anacamptus Bunge
Astragalus (Caprini) assadii Maassoumi & Podlech
He
He
He
IT W & C
IT KK-Alborz*
IT KK *
286
287
288
289
290
291
292
Astragalus (Astragalus) basineri Trautv.
Astragalus (Sesamei) biovulatus Bunge
Astragalus (Onobrychioidei) brevidens Freyn & Sint.
Astragalus (Incani) caespititius Podlech
Astragalus (Annulares) campylorhynchus Fisch. & C. Mey.
Astragalus (Erioceras) catacamptus Bunge
Astragalus (Rhacophorus) cerasocrenus Bunge
He
Th
He
He
Th
He
He
IT KK-Afgh.
IT W & C
IT KK
IT C*
IT C & E
IT W & C*
IT KK
293
294
Astragalus (Hymenostegis) chrysostachys Boiss.
Astragalus (Erionotus) citrinus Bunge
Ch
He
IT W & C
IT C
295
Astragalus citrinus subsp. barrowianus (Aitch. & Baker)
Podlech
Astragalus (Ankylotus) commixtus Bunge
Astragalus (Caprini) controversus Maassoumi & Podlech
Astragalus (Erionotus) curvipes Trautv.
Astragalus (Dipelta) dipelta Bunge
Astragalus (trachycercis) durandianus Aitch. & Baker
Astragalus (Caprini) esferayanicus Podlech & Maassoumi
He
IT KK-Afgh.
Th
He
He
Th
He
He
IT
IT KK *
IT KK
IT C
IT C*
IT KK *
He
He
Ch
Th
He
IT C
IT KK *
IT KK *
IT C
IT C*
307
308
309
310
311
312
313
314
Astragalus (Caprini) gompholobium Bunge
Astragalus (Incani) gululsaranii Podlech
Astragalus (Ammodendron) hekmat-safaviae Ghahrem.
Astragalus (Sesamei) kerkukiensis Bornm.
Astragalus (Erioceras) khongensis Maassoumi, Joharchi &
Podlech
Astragalus (Acanthophace) lycioides Boiss.
Astragalus (Cystium) masenderanus Bunge
Astragalus (Incani) mercklinii Boiss. & Buhse
Astragalus (Caprini) nephtonensis Freyn
Astragalus (Oxyglottis) oxyglottis M.Bieb.
Astragalus (Cremoceras) pendulinus Popov & B.Fedtsch.
Astragalus (Ammodendron) podolobus Boiss.
Astragalus (Caprini) pseudoindurascens Sirj. & Rech.f.
Ch
He
He
He
Th
He
Ch
He
IT C*
IT C
IT C
IT KK-Afgh.
IT-M
IT KK
IT
IT KK *
315
Astragalus (Caprini) pseudokurrumensis Sirj. & Rech.f.
He
IT KK *
316
317
318
319
Astragalus (Anthylloidei) raddei Basil.
Astragalus (Oxyglottis) schmalhausenii Bunge
Astragalus (Astragalus) sieversianus Pall.
Astragalus (theiochrus) siliquosus Boiss.
He
Th
He
He
IT KK
IT C & E
IT KK-E
IT
274
275
276
277
278
279
280
296
297
298
299
300
301
302
303
304
305
306
PLANT DIVERSITy OF THE HEyDARI WILDLIFE
Threat
category
[Ref.]
VU [1], LC
[2]
VU [1]
VU [1]
EN [1], VU
[2]
LR [1]
LC [2]
VU [1]
VU [1], LC
[2]
Herbarium No.
7472
7474, 8098
7475
7476, 7937, 8157
7477
7478, 7936
7479
7480, 7935, 8133
7481
7482
7483, 7934, 8099
7473, 7938
7484, 7932
7485, 7930–1,
8129
7486
VU [1,2]
LC [2]
LR [1]
VU [1], EN
[2]
DD [2]
DD [1]
VU [1]
LR [1]
LC [2]
LR [1], VU
[2]
VU [1], DD
[2]
DD [2]
7487, 8096
7488
7489
7490, 7929
7491
7494, 8097
7495, 7928
7496
7497
7498
7499
7500, 7927, 7933
7501, 7927
7502, 8128
7503
7504
7505, 7926, 8130
7493
7506, 8131
7507
7508, 7924–5
7509
7510
7511, 7923
Phytotaxa 340 (2) © 2018 Magnolia Press • 121
No.
Families and species/infraspecific taxa
Life-form
Chorotype
320
321
322
323
324
325
326
327
328
329
Astragalus (ammodendron) sp.
Astragalus (Ankylotus) stalinskyi Sirj.
Astragalus (Malacothrix) suluklensis Freyn & Sint.
Astragalus (Dissitiflori) sumbari Popov
Astragalus (Platonychium) verus Olivier
Astragalus (Cytisodes) zoshkensis Ghahr.-Nejad
Cicer tragacanthoides Jaub. & Spach
Colutea buhsei (Boiss.) Shap.
Glycyrrhiza glabra L.
Glycyrrhiza triphylla Fisch. & C.A.Mey. (=Meristotropis
xanthioides Vassilcz.)
Hedysarum glabrifoliolatum Ranjbar
Hedysarum kopetdaghi Boriss.
Hedysarum renzii Rech.f.
Hedysarum wrightianum Aitch. & Baker
lathyrus inconspicuus L.
lotus corniculatus L.
Medicago lupulina L.
Medicago monantha (C.A.Mey.) Trautv. (=trigonella
monantha C.A.Mey.)
Medicago sativa L.
Melilotus officinalis (L.) Pall.
Onobrychis amoena Popov & Vved.
Onobrychis chorassanica Boiss.
Onobrychis cornuta (L.) Desv.
Onobrychis verae Sirj.
Ononis afghanica Sirj. & Rech.f.
Oxytropis binaludensis Vassilcz.
Oxytropis hypsophila Bunge
Ch
Th
He
He
Ch
Ch
He
Ph
G.r
G.r
IT C & E
IT KK *
LC [2]
IT KK
LC [2]
IT C
LR [1]
IT KK *
EN [2]
IT C
LR [1]
IT KK-Alborz-ESHy
IT-ES-M
LR [1]
IT C
7512
7513
7492, 8100, 7922
7514, 7921
7515
7516
7517, 7918
7518, 7917
7519
7520, 7916
He
He
He
He
Th
He
Th
Th
IT KK *
IT KK
IT C*
IT C
IT-M
PL
PL
IT
7521
7522
7523
7524, 7914
7525
7526, 7913
7527
7528
He
He
Ch
He
Ch
He
Ch
He
He
PL
IT-ES-M
IT C & E
IT KK-E
IT Omni
IT KK-Afgh.
IT KK-Afgh.
IT KK *
IT KK *
Oxytropis sp.
Oxytropis suavis Boriss.
trifolium pratense L.
trifolium repens L.
trifolium resupinatum L.
Vicia subvillosa (Ledeb.) Boiss.
Gentianaceae Juss.
Gentiana olivieri Griseb.
Geraniaceae Juss.
Erodium cicutarium (L.) L’Hér.
Geranium collinum Stephan ex Willd.
Geranium kotschyi Boiss.
Geranium rotundifolium L.
Hypericaceae Juss.
Hypericum helianthemoides (Spach) Boiss.
Hypericum scabrum L.
Iridaceae Juss.
Crocus michelsonii B. Fedtsch.
He
He
He
He
Th
G.r
IT KK *
IT-ES-M
IT-ES-M
IT-ES-M
IT C & E
G.r
IT
7546
Th
G.r
G.t
Th
IT-ES-M
IT-ES
IT C
IT-ES-M
7547, 7903
7548
7549, 7901–2
7550
He
He
IT C
IT W & C
7551
7552, 7899, 7900
G.c
IT KK
Gladiolus atroviolaceus Boiss.
Iris fosteriana Aitch. & Baker
Iris kopetdagensis (Vved.) B.Mathew & Wendelbo
Iris loczyi Kanitz
Iris songarica Schrenk
Ixioliriaceae Nakai
Ixiolirion tataricum (Pall.) Schult. & Schult.f.
Juglandaceae DC. ex Perleb
Juglans regia L.
G.b
G.t
G.t
G.r
G.r
IT-M
IT KK-Afgh.
IT KK-Afgh.
IT KK-E
IT C & E
G.b
IT
7559
Ph
PL
7560
330
331
332
333
334
335
336
337
338
339
340
341
342
343
344
345
346
347
348
349
350
351
352
353
354
355
356
357
358
359
360
361
362
363
364
365
366
367
122 • Phytotaxa 340 (2) © 2018 Magnolia Press
Threat
category
[Ref.]
Herbarium No.
NT [2]
LR [1]
DD [1]
DD [1]
DD [1,2]
DD [1], VU
[2]
7537, 7540
7539, 7541, 7912
7542
7543
7544
7545, 7904
NT [2]
LR [1], VU
[2]
VU [1]
7529
7530
7531
7532, 7911
7533, 7910
7534, 7908–9
7535, 7907
7536, 7905–6
7538
7553
7554
7555, 7898, 8135
7556, 7897
7557, 7896
7558
ATASHGAHI Et Al.
No.
Families and species/infraspecific taxa
Life-form
Chorotype
Threat
category
[Ref.]
Herbarium No.
He
He
He
SCO
SCO
PL
7561, 7957
7562, 7895
7563, 7892–4
Th
IT-ES-M
7564, 7880, 7878
Ch
Ch
IT C
IT KK-Alborz*
7566, 7891
7567, 7889–90,
7915
7568, 7888
7569
7570, 7886–7,
8143–4
7571, 7885
7572
7573
7574, 7884
7575
7576
7577
7578
7883
7580, 7882
7581
7582, 8142
372
373
Juncaceae Juss.
Juncus articulatus L.
Juncus gerardii Loisel.
Juncus inflexus L.
Lamiaceae Martinov
Clinopodium graveolens (M.Bieb.) Kuntze (=Acinos
graveolens (M.Bieb.) Link)
Hymenocrater bituminosus Fisch. & C.A.Mey.
Hymenocrater calycinus (Boiss.) Benth.
374
375
376
Hymenocrater elegans Bunge
Hymenocrater oxyodontus Rech.f.
Hymenocrater platystegius Rech.f.
Ch
Ch
Ch
IT KK-Alborz
IT C*
IT KK *
377
378
379
380
381
382
383
384
385
386
387
388
lagochilus cabulicus Benth.
lallemantia iberica (M.Bieb.) Fisch. & C.A.Mey.
lamium amplexicaule L.
leonurus turkestanicus V.I.Krecz. & Kuprian.
Marrubium vulgare L.
Mentha longifolia (L.) L.
Nepeta binaloudensis Jamzad
Nepeta pungens (Bunge) Benth.
Nepeta ucranica subsp. kopetdaghensis (Pojark.) Rech.f.
Phlomis cancellata Bunge
Phlomoides binaludensis Salmaki & Joharchi
Phlomoides labiosa (Bunge) Adylov, Kamelin & Makhm.
(=Eremostachys labiosa Bunge)
Phlomoides labiosiformis (Popov) Adylov, Kamelin & Makhm.
(=Eremostachys labiosiformis (Popov) Knorring)
Phlomoides molucelloides (Bunge) Salmaki
Salvia abrotanoides (Kar.) Sytsma (=Perovskia abrotanoides
Kar.)
Salvia chloroleuca Rech.f. & Aellen
Salvia virgata Jacq.
Scutellaria luteo-coerulea Bornm.
Sideritis montana L.
Stachys lavandulifolia Vahl
Stachys setifera C.A.Mey.
Stachys trinervis Aitch. & Hemsl.
teucrium polium L.
Ziziphora clinopodioides subsp. pseudodasyantha (Rech.f.)
Rech.f.
Ziziphora clinopodioides subsp. rigida (Boiss.) Rech.f.
Ziziphora tenuior L.
Liliaceae Juss.
Fritillaria gibbosa Boiss.
Gagea chomutovae (Pascher) Pascher
Gagea gageoides (Zucc.) Vved.
Gagea kunawurensis (Royle) Greuter (=Gagea stipitata
Merckl. ex Bunge, =Gagea ova Stapf)
Gagea reticulata (Pall.) Schult. & Schult.f.
tulipa biflora Pall.
tulipa micheliana Hoog
Linaceae DC. ex Perleb
linum album Kotschy ex Boiss.
linum austriacum L.
Malvaceae Juss.
Alcea rhyticarpa (Trautv.) Iljin
Ch
Th
Th
He
He
He
He
Th
He
He
He
He
IT C
IT-M
SCO
IT KK-E
PL
PL
IT KK *
IT C & E
IT KK
IT KK-Afgh.
IT KK *
IT KK-E
He
IT C
7583
G.t
Ch
IT W & C
IT C & E
He
He
He
Th
He
He
Ch
Ch
Ch
IT KK-Alborz
IT-M
IT KK
IT-ES-M
IT C
IT
IT KK-Afgh.
IT-M
IT-ES
7565
7579,
3222(HNBG)
7584, 7881, 8141
7585
7586
7587
7588, 7879
7589
7590
7591
7592
Ch
Th
IT-ES
IT Omni
7593, 7876
7594, 7877
G.b
G.b
G.b
G.b
IT C
IT C & E
IT W & C
IT
7595, 7875
7596
7597, 7874
7598, 8104–5
G.b
G.b
G.b
IT
IT C & E
IT KK-Alborz
7599, 7873
7600
7601, 7871–2
He
Ch
IT C*
IT-ES-M
He
IT KK-E
368
369
370
371
389
390
391
392
393
394
395
396
397
398
399
400
401
402
403
404
405
406
407
408
409
410
411
412
PLANT DIVERSITy OF THE HEyDARI WILDLIFE
DD [1]
LR [1]
EN [1,2]
NT [2]
EN [2]
NT [2]
LR [1]
7602
7603
7604
Phytotaxa 340 (2) © 2018 Magnolia Press • 123
No.
Families and species/infraspecific taxa
Life-form
Chorotype
413
Malva neglecta Wallr.
Nitrariaceae Lindl.
Peganum harmala L.
Onagraceae Juss.
Epilobium hirsutum L.
Epilobium minutiflorum Hausskn.
Orchidaceae Juss.
Anacamptis palustris (Jacq.) R.M.Bateman, Pridgeon &
M.W.Chase (=Orchis palustris Jacq.)
Orobanchaceae Vent.
leptorhabdos parviflora (Benth.) Benth.
Orobanche kotschyi Reut.
Orobanche stocksii Boiss.
Pedicularis pycnantha Boiss.
Pedicularis rechingeri Wendelbo
He
PL
7605, 7870
He
PL
7606
G.r
G.r
PL
IT
7607
7608, 7869
G.b
IT-ES-M
7609
Th
G.p
G.p
He
He
IT C & E
IT
IT C
IT C
IT KK *
7761, 8116
7611, 7867
8123
7765
45558(FUMH)
Phelipanche hohenackeri (Reut.) Soják
Phelipanche schultzii (Mutel) Pomel
Papaveraceae Juss.
Corydalis aitchisonii Popov
Corydalis chionophila Czerniak.
G.p
G.p
IT
IT-M
G.t
G.t
IT KK-Afgh.
IT KK
Fumaria vaillantii Loisel.
Glaucium elegans Fisch. & C.A.Mey.
Hypecoum pendulum L.
Papaver decaisnei Hochst. & Steud. ex Elkan
Roemeria hybrida (L.) DC.
Roemeria refracta DC.
Plantaginaceae Juss.
linaria khorasanensis Hamdi & Assadi
linaria odora (M.Bieb.) Fisch.
linaria simplex DC.
Plantago lanceolata L.
Plantago major L.
Veronica anagallis-aquatica L.
Veronica arguteserrata Regel & Schmalh.
Veronica beccabunga L.
Veronica biloba schreb. ex L.
Veronica campylopoda Boiss. (=Veronica capillipes Nevski)
Th
Th
Th
Th
Th
Th
IT-ES-M
IT C & E
IT-M
IT
IT-M-SS
IT
He
He
Th
He
He
G.r
Th
He
Th
Th
IT KK *
IT-ES
IT-M
IT-ES-M
SCO
IT
IT
PL
IT Omni
IT Omni
Veronica hederifolia L.
Veronica intercedens Bornm.
Veronica khorassanica Czerniak.
Veronica rubrifolia Boiss.
Plumbaginaceae Juss.
Acantholimon erinaceum (Jaub. & Spach) Lincz.
Acantholimon pterostegium Bunge
Acantholimon quinquelobum Bunge
Acantholimon raddeanum Czerniak.
Poaceae Barnhart
Aegilops crassa Boiss.
Aegilops triuncialis L.
Agropyron cristatum (L.) Gaertn. (=Agropyron pectinatum
(M.Bieb.) P.Beauv.)
Agropyron desertorum (Fisch. ex Link) Schult.
Alopecurus arundinaceus Poir.
Arrhenatherum kotschyi Boiss.
Boissiera squarrosa (Sol.) Nevski
Th
Th
He
Th
IT-ES-M
IT C & E
IT KK
IT
Ch
Ch
Ch
Ch
IT C & E
IT KK *
IT C*
IT KK-E
Th
Th
He
IT W & C
IT-M
PL
7637
7638
7639
He
He
He
Th
IT
PL
IT
IT-M
7640
7641, 8153
7642
7643, 7855
414
415
416
417
418
419
420
421
422
423
424
425
426
427
428
429
430
431
432
433
434
435
436
437
438
439
440
441
442
443
444
445
446
447
448
449
450
451
452
453
454
455
456
457
124 • Phytotaxa 340 (2) © 2018 Magnolia Press
Threat
category
[Ref.]
Herbarium No.
LR [1], NT
[2]
7610, 7868, 7766
7612
LR [1], NT
[2]
LR [1]
VU [2]
NT [2]
LR [1]
LC [2]
7614, 7868
7615
7616
7617
7618
7619, 7867, 8136
7620
7621, 8137
7762, 7788, 8115
7763, 7789–90
7764
7622, 7866
7623
7624
7625, 7865
7626
7627
7628, 7863–4,
8114
7629
7630
7631, 7862
7632, 7860–1
7633, 7859
7634
7635
7636, 7856–8
ATASHGAHI Et Al.
No.
Families and species/infraspecific taxa
Life-form
Chorotype
458
459
460
Bromus danthoniae Trin. ex C.A.Mey
Bromus japonicus Thunb.
Bromus kopetdagensis Drobow
Th
Th
He
PL
PL
IT KK-Alborz*
461
462
463
464
465
466
467
468
469
470
471
472
473
474
475
476
477
478
Bromus oxyodon Schrenk
Bromus pseudodanthoniae Drobow
Bromus tectorum L.
Bromus tomentellus Boiss.
Calamagrostis pseudophragmites (Haller f.) Koeler
Catabrosa aquatica (L.) P.Beauv.
Colpodium parviflorum Boiss. & Buhse
Cynodon dactylon (L.) Pers.
Dactylis glomerata L.
Elymus hispidus (Opiz) Melderis
Elymus longiaristatus (Boiss.) Tzvelev
Elymus repens (L.) Gould
Eremopoa persica (Trin.) Roshev.
Eremopyrum bonaepartis (Spreng.) Nevski
Eremopyrum distans (K.Koch) Nevski
Festuca valesiaca Schleich. ex Gaudin
Glyceria notata Chevall. (=Glyceria plicata (Fr.) Fr.)
Helictotrichon turcomanicum Czopanov
Th
Th
Th
He
He
He
He
He
He
He
He
He
Th
Th
Th
He
He
He
IT C & E
IT
PL
IT C & E
IT-ES-M
PL
IT
PL
PL
IT-ES-M
IT C
IT-ES-M
IT-M
IT
IT
IT-ES
PL
IT KK
479
480
481
482
483
484
485
486
487
488
489
490
491
492
493
494
495
496
497
498
499
500
501
502
503
504
505
506
507
508
509
510
Henrardia persica (Boiss.) C.E.Hubb.
Heteranthelium piliferum (Sol.) Hochst. ex Jaub. & Spach
Hordeum brevisubulatum (Trin.) Link
Hordeum bulbosum L.
Hordeum murinum L.
leymus tianschanicus (Drobow) Tzvelev
loliolum subulatum (Banks & Sol.) Eig
Melica ciliata L.
Melica persica Kunth
Phragmites australis (Cav.) Trin. ex Steud.
Piptatherum holciforme (M.Bieb.) Roem. & Schult.
Poa annua L.
Poa bulbosa L.
Poa pratensis L.
Poa sinaica Steud.
Poa trivialis L.
Poa versicolor Besser
Polypogon monspeliensis (L.) Desf.
Polypogon viridis (Gouan) Breistr.
Rhizocephalus orientalis Boiss.
Sclerochloa dura (L.) P.Beauv.
Setaria viridis (L.) P.Beauv.
Stipa arabica Trin. & Rupr.
Stipa caragana Trin.
Stipa caucasica Schmalh.
Stipa hohenackeriana Trin. & Rupr.
Stipa holosericea Trin.
Stipa lessingiana Trin. & Rupr.
Stipa sp.
taeniatherum caput-medusae (L.) Nevski
Vulpia myuros (L.) C.C.Gmel.
Vulpia persica (Boiss. & Buhse) Krecz. & Bobrov
Polygonaceae Juss.
Atraphaxis binaludensis S. Tavakkoli, Mozaff. & Kaz. Osaloo
Atraphaxis spinosa L.
Th
Th
He
He
Th
He
He
He
He
He
He
Th
He
He
He
He
He
Th
Th
Th
Th
Th
He
He
He
He
He
He
He
Th
Th
Th
IT W & C
IT
IT
IT-M
IT-M
IT
IT
IT-ES-M
IT
SCO
IT-M
SCO
IT-ES-M
PL
IT-SS
PL
IT
PL
PL
IT W & C
PL
PL
IT
IT Omni
IT
IT Omni
IT Cauc.-Turk.
IT-ES
IT-ES-M
IT-M
IT
Ch
Ch
IT KK *
IT
511
512
PLANT DIVERSITy OF THE HEyDARI WILDLIFE
Threat
category
[Ref.]
LR [1]
DD [1]
EN [2]
DD [2]
Herbarium No.
7644, 7854
7645
7646, 7850–3,
8149, 8107
7647
7648
7649, 7849
7650
7651, 7848
7652
7653
7654
7655, 7848
7656, 7844–7
7657
7658, 8106
7659
7660, 8108
7661
7662, 7843, 7839
7663
7664,
45697(FUMH)
7665, 7842
7666, 7841
7667
7668, 7840
7669
7670, 7838
7671
7672
7673, 7836–7
7674
7675
7676
7677, 8109
7678
7679
7680, 8150
7681, 8151
7682, 8152
7683
7684
7685
7686
7687, 7834
7688, 7833
7689, 7831–2
7690, 7830, 7835
7691, 7829
7692, 7828
7693
7694, 7826–7
7695
7696
7697, 7825
7698, 8145
Phytotaxa 340 (2) © 2018 Magnolia Press • 125
No.
Families and species/infraspecific taxa
Life-form
Chorotype
513
514
515
516
517
518
519
520
521
Polygonum afghanicum Meisn.
Polygonum arenastrum Boreau
Polygonum aviculare L.
Polygonum molliiforme Boiss.
Polygonum rottboellioides Jaub. & Spach
Polygonum thymifolium Jaub. & Spach
Pteropyrum aucheri Jaub. & Spach
Rumex chalepensis Mill.
Rumex crispus L.
Potamogetonaceae Bercht. & J.Presl
Zannichellia palustris L.
Primulaceae Batsch ex Borkh.
Androsace maxima L.
Dionysia tapetodes Bunge
Ranunculaceae Juss.
Adonis aestivalis L.
Anemone biflora var. petiolulosa (Juz.) Ziman (=Anemone
petiolulosa Juz.)
Ceratocephala falcata (L.) Pers.
Ceratocephala testiculata (Crantz) Besser
Clematis orientalis L.
Ch
Th
Th
Th
Th
Ch
Ch
He
He
IT C
SCO
COS
PL
IT C
IT C
IT C
IT
SCO
7699, 7824
7700
7701
7702, 7822–3
7703, 7820–1
7704, 7818–9
7705
7706
7707
G.r
COS
7708
Th
Ch
IT-ES-M
IT KK-Afgh.
7709, 8110
7710
Th
G.t
IT-ES-M
IT C & E
7711
7712, 7817, 8134
Th
Th
Ch
IT-ES-M
IT-ES-M
IT
Consolida orientalis (J.Gay) Schrödinger
Consolida rugulosa (Boiss.) Schrödinger
Delphinium turkmenum Lipsky
Eranthis longistipitata Regel
Nigella integrifolia Regel
Ranunculus aucheri Boiss. (=Ranunculus elbursensis var.
aucheri (Boiss.) Parsa)
Ranunculus buhsei Boiss.
Th
Th
G.r
G.t
Th
G.t
IT-M
IT C
IT KK *
IT KK-E
IT C & E
IT Omni
LR [1]
7713, 7816
7714, 7815
7715, 7814,
8413(HNBG)
7716
7717
7718
7719
7720
7721
G.r
IT Cauc.-Alburz
LR [1]
7722
522
523
524
525
526
527
528
529
530
531
532
533
534
535
536
Threat
category
[Ref.]
LC [2]
Herbarium No.
&C
G.t
G.t
ES Hy *
IT E-ES Hy
7723
7724
G.r
He
IT Omni
IT C
7725
7726
He
IT-ES-M
7727
Ph
IT-ES
7728
543
Ranunculus cicutarius Schltdl.
Ranunculus sewerzowii Regel (=Ranunculus leptorrhynchus
Aitch. & Hemsl.)
thalictrum isopyroides C.A.Mey.
thalictrum sultanabadense Stapf
Resedaceae Martinov
Reseda lutea L.
Rhamnaceae Juss.
Rhamnus pallasii Fisch. & C.A.Mey.
Rosaceae Juss.
Cotoneaster kotschyi (C.K.Schneid.) G.Klotz
Ph
IT
544
Cotoneaster ovatus Pojark.
Ph
IT KK-Alborz*
545
Ph
IT KK
546
Crataegus pseudoheterophylla Pojark. subsp. turcomanica
(Pojark.) K.I.Chr.
Crataegus spathulata Michx. (=Crataegus microcarpa Lindl.)
7730, 7809–12,
3145(HNBG)
7731, 7808, 8139,
3175(HNBG)
7732
Ph
ES Euxi.-Hy
547
548
549
Geum kokanikum Regel & Schmalh.
Potentilla nuda Boiss.
Prunus microcarpa C.A.Mey.
He
He
Ph
IT C & E
IT
IT W & C
550
Prunus pseudoprostrata (Pojark.) Rech.f.
Ch
IT KK-Alborz
551
Prunus spinosissima (Bunge) Franch. (=Amygdalus
spinosissima Bunge)
Rosa beggeriana Schrenk ex Fisch. & C.A.Mey.
Ph
IT C & E
Ph
IT C & E
537
538
539
540
541
542
552
126 • Phytotaxa 340 (2) © 2018 Magnolia Press
VU [2]
LR [1]
7733,
3285(HNBG)
7734
7735
7736, 7807,
3287(HNBG)
7737, 7805–6,
3255(HNBG)
7729, 7813
7738, 7804,
3170(HNBG)
ATASHGAHI Et Al.
No.
Families and species/infraspecific taxa
Life-form
Chorotype
553
554
Rosa canina L.
Rosa kokanica (Regel) Regel ex Juz.
Ph
Ph
IT-ES-M
IT C & E
555
556
Rosa persica Michx. ex Juss.
Sanguisorba minor Scop.
Rubiaceae Juss.
Asperula glomerata subsp. turcomanica (Pobed.) Ehrend. &
Schönb.-Tem.
Asperula setosa Jaub. & Spach
Callipeltis cucullaris (L.) DC.
Crucianella chlorostachys Fisch. & C.A.Mey.
Crucianella gilanica subsp. transcaspica (Ehrend.) Ehrend. &
Schönb.-Tem.
Galium aparine L.
Ch
He
IT C & E
IT-ES-M
7739
7740,
45440(FUMH)
7741
7742, 7803
Ch
IT
7743, 7801–2
Th
Th
Th
He
IT
IT-M
IT
IT
7744, 7799–800
7745, 7798
7746
7747, 7797
Th
PL
Th
He
He
Th
Th
Th
Ch
Ch
Ch
IT-SS
IT-M
IT KK *
IT-M
IT-ES-M
IT-ES-SS
IT C*
IT
IT
He
IT C & E
7757
Ph
Ph
IT
-
7759
7758, 8121
G.r
IT W & C
7760
He
He
He
IT
IT C
IT W & C
7767
7768, 7787
7769, 7786
He (biennial)
Th
IT-ES-M
COS
7770
7771
581
Galium ceratopodum Boiss.
Galium humifusum M.Bieb.
Galium pojarkovae Pobed.
Galium setaceum Lam.
Galium spurium L.
Galium tricornutum Dandy
Rubia florida Boiss.
Rubia rigidifolia Pojark.
Rubia tinctorum L.
Rutaceae Juss.
Haplophyllum acutifolium (DC.) G.Don
Salicaceae Mirb.
Salix excelsa S.G.Gmel.
Salix sp.
Santalaceae R.Br.
thesium kotschyanum Boiss.
Scrophulariaceae Juss.
Scrophularia striata Boiss.
Scrophularia variegata M.Bieb.
Verbascum cheiranthifolium Boiss.
Solanaceae Juss.
Hyoscyamus reticulatus L.
Solanum americanum Mill. (=Solanum nigrum L.)
Tamaricaceae Link
Reaumuria alternifolia (Labill.) Britten
7752,
45674(FUMH)
7748, 8112
7749, 7796, 8111
7750
7751
7794–5
7753
7754, 7792–3
7755, 7791
7756
Ch
IT
582
tamarix ramosissima Ledeb.
Ph
PL
7772,
6124(HNBG)
7773, 7785,
2301(HNBG)
Th
IT
7405
He
He
IT-ES
-
7774
7775
Ph
ES-M
7776
He
SCO
7777
Th
IT Omni
7778
557
558
559
560
561
562
563
564
565
566
567
568
569
570
571
572
573
574
575
576
577
578
579
580
583
584
585
586
587
588
Thymelaeaceae Juss.
Diarthron vesiculosum (Fisch. & C.A.Mey.) C.A.Mey.
Typhaceae Juss.
typha minima Funck
typha sp.
Ulmaceae Mirb.
Ulmus minor Mill.
Urticaceae Juss.
Urtica dioica L.
Violaceae Batsch
Viola occulta Lehm.
PLANT DIVERSITy OF THE HEyDARI WILDLIFE
Threat
category
[Ref.]
DD [1]
VU [2]
LR [1]
LR [1]
Herbarium No.
Phytotaxa 340 (2) © 2018 Magnolia Press • 127