LAZAROA 35: 19-35. 2014
doi: 10.5209/rev_LAZA.2014.v35.44196
ISSN: 0210-9778
Biogeographic trends of endemic and subendemic
flora in the western Iberian Peninsula under
scenarios of future climate change
João Rocha (*), Rubim Almeida da Silva (*), Francisco Amich (**),
Álvaro Martins (***), Paulo Almeida (***), José T. Aranha (****),
Isabel García-Cabral (***), Mónica Martins (***), Carlos Castro (*****)
& António L. Crespí (***)
Abstract: Rocha, J., Almeida da Silva, R., Amich, F., Martins, A., Almeida, P., Aranha, J.T., García-Cabral, I., Martins,
M., Castro, C. & Crespí, A.L. Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
under scenarios of future climate changes. Lazaroa 35: 19-35 (2014).
Altitude, temperature and precipitation are important environmental variables for the distribution of endemic plants.
Taking in account their present distribution, this work studies the distribution trends of 116 endemic and subendemic
species that occur on the western Iberian Peninsula and north-western Morocco, in different scenarios of future climate
change. It was possible to identify five groups of taxa in the present environmental conditions, four of which for the northern
part of the Iberian Peninsula. This range can partially be explained by the altitudinal variability of such area. The other
group distributes along the western of the Iberian Peninsula. Concerning future climate change scenarios, important changes
in species distribution, and a general south-north trend were obtained. Under harsher climatic changes, only the groups
that tolerate the most variable environmental conditions persist. Estimates of extinction rates of the studied taxa for the
next 75 years are also presented. The present methodology allows the application of ecological indicators (environmental
groups, in this case) to understand biogeographic trends.
Keywords: Species distribution models; environmental variability; Maxent; conservation
Resumen: Rocha, J., Almeida da Silva, R., Amich, F., Martins, A., Almeida, P., Aranha, J.T., García-Cabral, I., Martins,
M., Castro, C. & Crespí, A.L. Tendencias biogeográficas de flora endémica y subendémica en el oeste de la Península
Ibérica bajo escenarios de cambio climático futuro. Lazaroa 35: 19-35 (2014).
Altitud, temperatura y precipitación son variables ambientales importantes en la circunscripción de las distribuciones
biogeográficas de plantas endémicas. Tomando en cuenta su distribución actual, este trabajo estudia las tendencias de distribución de 116 especies endémicas y subendémicas que se producen en el oeste de la Península Ibérica y el noroeste de
Marruecos, en diferentes escenarios de cambio climático futuro. Se identificaron cinco grupos de taxones en las actuales
condiciones ambientales, de las cuales cuatro son para el norte de la Península Ibérica. Este rango se puede explicar parcialmente por la variabilidad altitudinal de dicha zona. El otro grupo se distribuye a lo largo del oeste de la Península
Ibérica. En cuanto a los futuros escenarios de cambio climático, se obtuvieron cambios importantes en la distribución de
las especies, y una tendencia general sur-norte. Bajo los cambios climáticos más severos, sólo los grupos que toleran las
condiciones de la mayoría de las variables ambientales persisten. También se presentan estimaciones de las tasas de extinción de los taxones estudiados para los próximos 75 años. La presente metodología permite la aplicación de los indicadores
ecológicos (grupos ecológicos, en este caso) para comprender las tendencias biogeográficcas.
Palabras clave: modelos de distribución de especies, variabilidad medioambiental, Maxent, conservación.
* Department of Biology, CIBIO/UP - Research Centre in Biodiversity and Genetic Resources & Faculty of Sciences, University
of Porto, Edifício FC4, Rua do Campo Alegre, S/N, 4169-007 Porto. Portugal.
** Evolution, Taxonomy and Conservation Group (ECOMED), Department of Botany, University of Salamanca, E-37008 Salamanca. Spain. Email: pacoamich@gmail.com
*** Department of Biology and Environment-CITAB, Botanical Garden and Herbarium, University of Trás-os-Montes e Alto
Douro, 5001-801 Vila Real. Portugal.
**** Department of Forest and Landscape-CITAB, University of Trás-os-Montes e Alto Douro, 5001-801 Vila Real. Portugal.
***** Department of Agronomy-CITAB, University of Trás-os-Montes e Alto Douro, 5001-801 Vila Real. Portugal.
19
LAZAROA 35: 19-35. 2014
João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
INTRODUCTION
DEZ-SANTANA & al., 2008; RUIZ-LABOURDETTE &
al., 2012) were the main reasons for preferentially using endemic species in these contributions.
Based on the higher sensibility of endemic
taxa to environmental changes, an approach to
future dynamic flows of this flora under climate
change scenarios is here proposed. A set of endemic taxa with different life forms and known
biogeographic distributions (and thus different
sensitivities to climate change) were selected.
The general requirement was their Iberian endemicity (some included taxa also occur in the
south-western France and in north-western Morocco).
A Species Distribution Model (SDM) was applied to describe the spatial relationship between
the species and their overall environmental variability in the geographic area (GUISAN & THUILLER, 2005; ELITH & LEATHWICK, 2009). After the
environmental characterization of these endemisms, grouped environmentally, a forecasting
analysis was developed under two predicted future scenarios of climate change, would allow a
dynamic picture of these environmental groups
of species to be obtained. The results achieved
will be a contribution to describe the biogeographic floristic dynamics of the flora of the western
Iberian Peninsula. At the same time, they will also
be useful to consolidate the management conservation policies for rare or more restricted flora in
western Iberian Peninsula.
Biogeographic behaviours of several genera
and species have been previously reported for the
Iberian Peninsula (OLALDE & al., 2002; PETIT &
al., 2002; VARGAS, 2003; MEJÍAS & al., 2007;
PARDO & al., 2008; GUZMÁN & VARGAS, 2009;
CRESPÍ & al., 2007; ROCHA & al., 2012a; ROCHA
& al., 2012b; ALMEIDA DA SILVA & al., 2014).
Based on these descriptions, two distinct dynamics were identified for the western Iberian Peninsula: one along the northern mountains
system, and another closer to the southern coast.
Endemic and non-endemic taxa, have been used
in these biogeographic descriptions. Yet, endemic
taxa are much more reliable descriptors of such
dynamics. In this sense, the hypothesis of centres
of endemicity being areas of special evolutionary
history, brings important implications for biogeographic performances (JETZ & al., 2004). The
most obvious refers to bioenvironmental restrictions, saying that endemic species with restricted
distributions will also respond to limited environmental amplitudes (KRUCKEBERG & RABINOWITZ,
1985). In this context, arises the question: could
the environmental characterizations of those areas
be a proper approach to explain the biogeographic
dynamics at a regional scale? Accepting the hypothesis aforementioned the mapping of areas of intense evolutionary activity, can well translate
endemic biogeographic trends, and can be extremely useful to describe recent floristic dynamics
at a regional level (YOUNG & al., 2002; CALSBEEK
& al., 2003; HOPPER & GIOIA, 2004).
The floristic distribution through the western
Iberian Peninsula has been studied and analysed
by several authors for different species or genera
(TABERLET & al., 1998; HEWITT, 1999; PETIT &
al., 2002; PEÑUELAS & BOADA, 2003; MEJÍAS &
al., 2007; PARDO & al., 2008; GUZMÁN & VARGAS, 2009; ROCHA & al., 2012a). Conservational
concerns (FERRIER & al., 2002; ENGLER & al.,
2004; THUILLER & al., 2005; RODRÍGUEZ & al.,
2007; BENITO & al., 2009; ROCHA & al., 2012b)
and taxa sensitivity to climate change (WOHLGEMUTH 1998; GUISAN & THEURILLAT, 2000; SANZELORZA, 2003; ELITH & al., 2006; HARRISON &
al., 2006; BENITO GARZÓN & al. 2007; HERNÁNLAZAROA 35: 19-35. 2014
MATERIAL AND METHODS
STUDY AREA AND DATA COLLECTION
The criterion used to limit the study area, was
based on the general geomorphology of the Iberian
Peninsula acording to RIVAS-MARTINEZ (1987) and
RIVAS-MARTINEZ & RIVAS-SÁENZ (2009), the Carpetan-Iberian-Leonese province has a natural border that separates the north from the south by the
Central Mountains System. The southern area was
defined by the Gado-Algarvian province.
The study area was refined taking in account
the capacity for grouping taxa and the speciation
20
João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
described for the south-western side of the Iberian Peninsula and north-western Morocco. This
effect was already pointed out by several authors
for other taxa (PARDO & al., 2008; GUZMÁN &
VARGAS, 2009; ROCHA & al., 2012a; ALMEIDA
DA SILVA & al., 2014). A western biogeographic
dynamics, limited by the biological Almerian
and Iberian System border (HERNÁNDEZ BERMEJO & SAÍNZ OLLERO, 1984), could explain the
expansion of the floristic cast along the western
part of Europe, from the Tanger-Cadiz-Algarve
bay.
In order to obtain a significant resolution of the
potential areas and their modelling (AUSTIN,
2007), it was used a species selection system that
would allow to maintain the balance between the
north and south quadrants, based on general and
regional floras (AMARAL FRANCO, 1971, 1984;
AMARAL FRANCO & ROCHA AFONSO, 1994, 1998,
2003; http://www.floraiberica.es; VALDÉS & al.,
1987; BLANCA & al., 2011).
Although there is no clear relation between
threatened species and the fact a species being endemic (according IUCN criteria, 2012), to obtain
the final list of taxa included in this work, the official threatened plant lists published for the Spanish - communities of Asturias, Castilla-León,
Extremadura and Andalusia (http://www.conservacionvegetal.org/legislacion.php?id_categoria=8)
- were consulted. For Portugal, there is still no list
of threatened species officially published (with the
exception of the ones included in the Directive
92/43/CEE). Some unpublished data of field prospections, was also analysed.
With this information, 116 taxa were selected
(see Table 1), based on three main criteria: a) species with a preferential distribution in the selected
area; b) proportionality in the distribution along
this area should be maintained (a similar number
of species in its middle northern and southern
part); and c) diversity of life forms.
To map their distributions occurrences were
geo-referenced using a 1 km2 grid resolution (according to the pixel resolution of the environmental variables data), as recommended by GUTIÉRREZ
& PONS (2006).
The locations of the species in the field, were
obtained from several herbaria (67% of the ga-
thered information) possessing data form specimens of the Western Iberian Peninsula (BRESA,
COI, HVR, LEB, LISE, LISI, LISU, MA, PO,
SALA - http://sweetgum.nybg.org/ih/ihmapsearch.php-). Complementary information was
taken from field expeditions and the Anthos
database (http://www.anthos.es) for areas without other available references. The life forms
classification was carried out using Raunkier´s
tipification, adapted from B RAUN -B LANQUET
(1979).
ENVIRONMENTAL CHARACTERIZATION AND
POTENTIAL DISTRIBUTIONS
Based on the occurrence of the species, an environmental assesment was made, using 68 environmental variables found in WORLDCLIM (http:
//www.worldclim.org/formats), and the thermic
and pluviometric WORLDCLIM application for their
analysis (http://www.worldclim.org/).
The achieved environmental matrix, in which
the thermic, pluviometric and altitudinal information was specified for each location, was also applied for similar characterizations (ROCHA & al.,
2012a; ROCHA & al., 2012b; ALMEIDA DA SILVA &
al., 2014). A similarity analysis (Unweight Pair
Group Average -UPGA- amalgamation and Manhattan City-block distances) was applied to establish environmentally similar groups. The obtained
groups of species, were characterized statistically
by multivariate analysis, after a previous standardization of the environmental matrix. These groups
were decisive for describing the biogeographic behaviour of the selected taxa.
The most discriminating environmental variables were obtained by Discriminate Canonical
Analysis (DCA), and its numerical parameters: the
F statistic (F-remove) and p-levels to describe the
distribution of the variable, Wilk´s Lambda as the
test to explain variance between variables, and tolerance (in this case, the squared multiple correlation). Finally, the representation of ranges by
environmental variables and group of species, was
represented by mean ± standard deviation/mean ±
1.96 standard deviation plots. The STATISTICA
v. 9.1 software was applied for these analyses and
graphic representations.
21
LAZAROA 35: 19-35. 2014
João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
Table 1
List of analyzed species, their general distributions in the study area (Dist: northern, N; southern, S), life forms
(according to Raunkier classification), and environmental group where they were included.
Species
Dist
Life forms
Environ. Group
Aconitum napellus subsp. castellanum
Adenocarpus argyrophyllus
Adenocarpus telonensis
Allium schmitzii
Allium victorialis
Anarrhinum duriminium
Anarrhinum longipedicellatum
Anthemis alpestris
Antirrhinum cirrhigerum
Antirrhinum linkianum
Anthyllis vulneraria subsp. iberica
Anthyllis vulneraria subsp. sampaiana
Arabis juresii
Arenaria querioides
Armeria humilis subsp. humilis
Armeria humilis subsp. odorata
Armeria linkiana
Armeria velutina
Aster aragonensis
Bufonia macropetala
Calendula suffruticosa subsp. lusitanica
Calicotome villosa
Carex asturica
Cistus libanotis
Cytisus arboreus subsp. baeticus
Cytisus grandiflorus subsp. cabezudoi
Dianthus langeanus
Digitalis purpurea subsp. amandiana
Diplotaxis siifolia subsp. vicentina
Drosophyllum lusitanicum
Echinospartum ibericum
Elaeoselinum foetidum
Erica lusitanica
Erophaca baetica
Erysimum merxmuelleri
Euphorbia polygalifolia subsp. polygalifolia
Euphorbia uliginosa
Festuca duriotagana
Festuca summilusitana
Galega cirujanoi
Galium glaucum subsp. australis
Genista ancistrocarpa
Genista berberidea
Genista carpetana
Genista hystrix
Genista micrantha
Genista polyanthos
Genista sanabrensis
Genista tournefortii
Genista triacanthos
C
C
S
NS
N
N
N
N
S
NS
N
NS
N
N
N
N
S
S
N
NS
NS
S
N
S
S
S
N
N
S
NS
N
S
NS
NS
S
N
N
NS
N
C
N
N
N
N
N
N
S
N
NS
NS
Geophyte
Microphanerophyte
Nanophanerophyte
Helophyte
Geophyte
Chamaephyte
Hemicriptophyte
Chamaephyte
Chamaephyte
Chamaephyte
Chamaephyte
Chamaephyte
Hemicriptophyte
Terophyte
Chamaephyte
Chamaephyte
Hemicriptophyte
Chamaephyte
Hemicriptophyte
Chamaephyte
Chamaephyte
Nanophanerophyte
Geophyte
Nanophanerophyte
Microphanerophyte
Nanophanerophyte
Chamaephyte
Hemicryptophyte
Terophyte
Geophyte
Nanophanerophyte
Hemicryptophyte
Nanophanerophyte
Hemicryptophyte
Chamaephyte
Chamaephyte
Chamaephyte
Hemicryptophyte
Hemicriptophyte
Hemicriptophyte
Hemicriptophyte
Nanophanerophyte
Nanophanerophyte
Chamaephyte
Nanophanerophyte
Chamaephyte
Nanophanerophyte
Nanophanerophyte
Chamaephyte
Nanophanerophyte
1C
1C
2
2
1C
2
1A
1C
2
2
1A
2
1C
1C
1B
1B
20
2
1C
1C
2
2
1B
2
2
2
1C
2
2
2
1C
2
2
2
1C
1C
2
2
1B
2
2
2
1A
1C
1C
1C
2
3
1C
2
LAZAROA 35: 19-35. 2014
22
João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
Species
Dist
Life forms
Environ. Group
Halimium calycinum
Halimium umbellatum subsp. umbellatum
Holcus annus subsp. duriensis
Holcus gayanus
Hyacinthoides mauritanica
Hymenostemma pseudanthemis
Iberis procumbens subsp. procumbens
Jasione cavanillesii
Jasione crispa subsp. mariana
Juncus emmanuelis
Lavandula viridis
Limonium algarvense
Limonium ovalifolium
Loeflingia baetica
Malva hispanica
Marsilea batardae
Mercurialis reverchonii
Narcissus asturiensis
Nothobartsia asperrima
Ononis broteriana
Ononis cintrana
Otospermum glabrum
Paradisea lusitanica
Pistorinia hispanica
Plantago monosperma subsp. discolor
Polygala baetica
Rhododendrum ponticum subsp. baeticum
Rhynchospora modesti-lucennoi
Santolina semidentata
Scrophularia sambucifolia
Scrophularia sublyrata
Selinum broteri
Sempervivum vicentei
Sideritis arborescens
Sideritis lurida
Silene acutifolia
Silene coutinhoi
Silene longicilia
Silene mariana
Silene marizii
Spergula viscosa
Stauracanthus genistoides
Succisella microcephala
Teucrium algarbiense
Teucrium salviastrum
Thapsia minor
Thapsia nitida
Thapsia transtagana
Thymelaea broteriana
Thymelaea lanuginosa
Thymus albicans
Thymus carnosus
Thymus villosus subsp. lusitanicus
Thymus zygis subsp. sylvestris
S
N
N
N
S
S
S
N
C
S
S
S
S
S
S
S
S
N
NS
NS
S
S
N
NS
N
S
NS
S
N
S
NS
N
N
S
NS
N
N
NS
S
N
N
S
C
S
N
NS
S
S
N
S
S
S
S
S
Chamaephyte
Chamaephyte
Terophyte
Terophyte
Geophyte
Terophyte
Chamaephyte
Chamaephyte
Chamaephyte
Helophyte
Chamaephyte
Hemicryptophyte
Chamaephyte
Terophyte
Chamaephyte
Helophyte
Chamaephyte
Geophyte
Chamaephyte
Terophyte
Terophyte
Terophyte
Geophyte
Terophyte
Chamaephyte
Chamaephyte
Microphanerophyte
Chamaephyte
Chamaephyte
Hemicriptophyte
Hemicriptophyte
Hemicriptophyte
Chamaephyte
Chamaephyte
Chamaephyte
Hemicriptophyte
Hemicriptophyte
Hemicriptophyte
Terophyte
Hemicriptophyte
Chamaephyte
Nanophanerophyte
Chamaephyte
Chamaephyte
Chamaephyte
Hemicriptophyte
Hemicriptophyte
Hemicriptophyte
Chamaephyte
Nanophanerophyte
Chamaephyte
Chamaephyte
Chamaephyte
Chamaephyte
2
1C
2
1C
2
2
2
3
2
2
2
2
2
2
2
2
2
1B
2
2
2
2
1C
1C
1C
2
2
2
1C
2
2
1C
3
2
1C
1B
2
2
2
1C
3
2
1C
2
1B
2
2
2
1C
2
2
2
2
2
23
LAZAROA 35: 19-35. 2014
João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
Species
Dist
Life forms
Environ. Group
Thymus villosus subsp. villosus
Thymus zygis subsp. zygis
Ulex argenteus
Ulex erinacenus
Ulex micranthus
Verbascum barnadesii
Verbascum litigiosum
Verbascum giganteum subsp. martinezii
Veronica mampodrensis
Veronica micrantha
Viola langeana
Xolantha globulariifolia
S
N
S
S
N
S
S
S
N
N
N
N
Chamaephyte
Chamaephyte
Nanophanerophyte
Chamaephyte
Nanophanerophyte
Hemicriptophyte
Hemicriptophyte
Hemicriptophyte
Chamaephyte
Chamaephyte
Hemicriptophyte
Hemicriptophyte
2
1C
2
2
1A
2
2
2
3
1C
1C
1C
The potential habitat distribution areas and
previsions for environmental groups and subgroups, were obtained with the MAXENT software,
v. 3.3.3e (http://www.cs.princeton.edu/~schapire/maxent/). MAXENT estimates the distribution
probability of a species occurrence, based on environmental constraints (PHILLIPS & al., 2006). It
only requires the data of the species presence, and
the environmental variables in GIS layers, for the
study area. The MAXENT software was used to estimate the probability of a potentially suitable habitat for species occurrence, varying from 0 to 1,
where 0 is the lowest and 1 the highest probability.
The modelling approach was validated based
on the probability that locations with a confirmed
presence of the species, ranked higher than a random background probability, also with a characteristic receiver-operating (ROC) plot (FIELDING
& BELL 1997), and an area under the curve
(AUC) approach (PHILLIPS & al. 2006). Locations
with a random background probability served as
pseudo-absences for all analyses in MAXENT (PHILLIPS & al., 2004; PHILLIPS & al., 2006).
The MAXENT jack-knife approach was used for
assessing the importance of the variable (YOST &
al., 2008). The training gain was calculated for
each variable as well as the drop in training gain
when the variable was omitted from the full
model (PHILLIPS & al., 2006).
For all models, the following parameters were
used: 10 repetitions with cross-validation, standard regularization multiplier (affects how focused or closely-fitted the output distribution is),
500 iterations (for further details on these para-
meters, see PHILLIPS (2010) and a threeshold of
0.5, meaning that only suitable habitat areas ranking higher than 0.5 of probability of occurrence
were chosen - to describe the most significant distribution areas. The output obtained (in ASCII
format) was then used as input for a GIS project
(ArcGIS software version 9.2 - ESRI, Redlands,
California, USA) as a floating-point grid (PETERSON & al. 2007), revealing the probability of the
occurrence of the species at each site and resulting in a continuous map.
LAZAROA 35: 19-35. 2014
MODELLING THE POTENTIAL FUTURE
DISTRIBUTIONS
The climate predictors were derived from a general circulation model (CCCMA: CGCM2) for
2080, under the IPCC emission scenarios (SRES;
A2a and B2a) for predicting future potential distribution areas (http://gisweb.ciat.cgiar.org/GCMPage;
RAMÍREZ & JARVIS, 2008). The scenarios A2a and
B2a represent two different possible situations of
greenhouse gas emissions. In comparison with
A2a, B2a has a lower rate of global warming, and
hence changes in temperature and precipitation
are less intense (http://forest.jrc.ec.europa.eu/climate-change/future-trends).
In order to confirm the previsions per environmental group, potential distribution areas and
previsions for both future scenarios were also
elaborated for each species individually. This
approach was necessary to confirm the result obtained for every environmental group, based on
the variability of information included in each
group.
24
João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
RESULTS
distinguish those five groups (Table 2). This last environmental variable describes the variability of
average precipitation among seasons along the year
(coefficient of variation between seasons).
The potential distribution map for the environmental groups is exposed in Figure 3. The concentration of habitats suitable for harbouring the
environmental groups is clearly different for
group 1 and 2, but regionally overlapped in the
north-eastern. The potential environmental distribution for group 1 (subgroups 1a, 1b and 1c) is
concentrated in the northern of the area, for group
2 is extended along the whole area (at low altitude). The potential occurrence of group 3 is also
located in the northern area, but at the highest altitudes of the Cantabrian mountain system.
In the case of group 1, the three potential distributions of subgroups 1a, 1b and 1c are evidently distinguished. Potential occurrence for
subgroup 1a is along the coast and at low altitudes
of north-western and north; subgroup 1b is restricted to the occident of the lusitanian-gallaecian
mountain system; and subgroup 1c is more concentrated in the most continental side of the
north-western and northern of the area.
The life form description of each environmental group and subgroup is exposed in Table 3. In
ENVIRONMENTAL CHARACTERIZATION AND
POTENTIAL DISTRIBUTIONS
The map detailing the present known distribution of taxa is shown in Figure 1 (for 2983 confirmed locations). A total 40% of the studied
species were concentrated in the north, 40% in
the south, 4% just in the center, and the remaining
16% along the area.
The similarity analysis on the environmental matrix is shown in the dendrogram of Figure 2a. Three
basic groups were primarily observed: groups 1, 2
and 3. The first one is subdivided in three subgroups: group 1a, 1b, and 1c. This classification is
deduced according to the CDA for the environmental matrix, for the most discriminant classification
(the highest F, highest Wilks´ lambda, and lowest pvalue) deduced from the dendrogram obtained from
the similarity analysis. The CDA for the environmental matrix classified into five environmental
groups (included here the three subdivisions of
group 1) is graphically represented in Figure 2b. Altitude (F=11.857, p-level<0.001) and precipitation
seasonality (bio 05, F=10.350, p-level<0.001) are
the most discriminant environmental variables to
Figure 1. – Distribution maps of populations occurrences for all the species analysed.
25
LAZAROA 35: 19-35. 2014
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
João Rocha & al.
a
b
Figure 2. – Multivariate analysis of the environmental matrix: (a) dendrogram obtained from the similarity analysis
of average environmental variables per taxon, with groups (Gr.) and subgroups (Sgr.) represented, and their maps
of current potential distribution; (b) graphic representation of DCA for the five groups (1 -1a, 1b, and 1c-, 2 and 3).
Table 2
Numerical values of CDA for the environmental matrix. Altitude (F=11.857, p-level<0.001) and precipitation
seasonality (bio 5, F=10.350, p-level<0.001) are the most discriminant environmental variables.
Wilks' Lambda
F-remove
(4,51)
p-level
Toler.
0,030243
0,026711
0,028414
0,030666
0,024746
10,21554
7,53363
8,82649
10,53671
6,04113
0,000004
0,000076
0,000017
0,000003
0,000466
0,409161
0,099515
0,066694
0,159397
0,186567
altitude
prec4
prec1
bio 5
tmin7
LAZAROA 35: 19-35. 2014
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João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
Figure 3. – Potential distribution areas for the bioclimatic groups: a) group 1a, b) group 1b, c) group 1c, d) group 2,
and e) group 3. All these bioclimatic groups are represented for the middle northern of the study area, in contrast
with the middle southern where just group 2 occurs.
terms of life forms, 9% were therophytes, 23%
hemicryptophytes, 6% geophytes, 42% chamaephytes, 14% nanophanerophytes, 3% microphanerophytes, and 3% helophytes.
Group 2 and subgroup 1c are the most diverse
in terms of life forms. In contrast, the rest of the
environmental groups are extremely restricted:
biannual (hemicriptophytes) or perennial herbaceous (geophytes and chamaephytes), or small
shrubs (nanophanerophytes) are the only forms
observed. These results could be associated with
the environmental variability obtained for groups
2 and 1c, both of them very similar about their altitudinal ranges (Figure 4).
MODELLING THE POTENTIAL FUTURE
DISTRIBUTIONS
Projections of potential distributions for environmental groups 2, for both 2080 scenarios,
show an evident shift towards the northern part
of the Iberian Peninsula (Figure 5). Groups 3 and
27
LAZAROA 35: 19-35. 2014
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
João Rocha & al.
Table 3
Percentages of life forms per environmental group (Tero, terophytes; Hemi, hemicriptophyte; Geop, geophytes;
Helo, helophytes; Cham, chamaephytes; Nano, nanopharerophytes; Micr, microphanerophytes).
Tero
0
0
27,27
72,73
0
Group 1a
Group 1b
Group 1c
Group 2
Group 3
Hemi
3,7
7,41
22,22
66,67
0
Geop
0
28,57
42,86
28,57
0
Helo
0
0
0
100
0
Cham
2,04
6,12
32,65
51,02
8,16
Nano
12,5
0
12,5
68,75
6,25
Micr
0
0
33,33
66,67
0
1, with subgroups 1a, 1b, and 1c, reflect significant decreases or even extinctions (group 3 for
both scenarios, and subgroup 1b for the A2a scenario) in the potential habitat distributions.
The current thermic and pluviometric characterization per envionmental group is explained in Table
4. Group 3 and subgroups 1a and 1c are clearly cooler than group 2 or subgroup 1b. This circumstance
is maintained for the future climatic change scenarios
A2a and B2a, where an increasing of 3º-4ºC and a
decreasing in 20% for annual precipitation are confirmed for all the environmental groups. These results are in accordance with previous previsions for
Mediterranean areas (LOARIE & al., 2009).
Figure 4. – Average altitude for the 1c and 2 bioclimatic
groups from eastern to western of the study area. Both
bioclimatic groups show a very similar and wide altitudinal range.
Table 4
Thermic and pluviometric values for the current situation and for the climate scenarios analysed (A2a and B2a)
in 2080, based on the annual average precipitation (P), annual lowest temperature (tmin) and annual highest
temperature (tmax), per environmental group.
Groups
Current
P (mm)
2080 A2a
2080 B2a
tmin (°C) tmax (°C) P (mm)
tmin (°C) tmax (°C) P (mm)
tmin (°C) tmax (°C)
1a
1b
1c
3
2
87
88
120
70
55
1
10
6
6
11
11
18
15
16
21
69
73
98
56
43
4
12
9
9
14
15
21
18
20
24
80
83
113
65
49
3
12
8
8
13
14
20
17
19
23
Table 5
Potential areas of the bioclimatic groups (Km2), under the current climatic conditions and for both future
climate scenarios (A2 and B2). Surfaces were also calculated based on the species distributions
of each group (with *).
Current
2080 A2a
2080 B2a
2080 A2a*
2080 B2a*
Group 1a
Group 1b
Group 1c
Group 2
Group 3
20495
2031
16050
595
5245
7234
0
703
1321
4624
116460
9021
50087
72291
86972
139247
72502
91485
76996
69256
4251
0
62
0
517
LAZAROA 35: 19-35. 2014
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João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
The surfaces occupied by the groups in the future scenarios are also very explicit (Table 5).
Group 3 and subgroup 1b will disappear (A2a) or
reduce severally their surfaces (B2a). For the
other groups substantial decreases are verified.
The largest group (group 2) is the most resistant,
keeping extensive areas in both scenarios.
The individual analysis of every species (for
the current climatic conditions and for the future
scenarios) is also exposed in Table 5. With the exception of groups 1c and 2 -where the areas previewed in both scenarios are much higher than
those previewed as a group (subgroup 1c), or with
opposite results (group 2)-, the other environmental groups show similar behaviors. The cases of
groups 1c and 2 could be explained by their environmental variability. In fact, the potential areas
deduced for both, are significantly higher than for
the others (1a, 1b and 3). This issue will force the
subdivision of groups 1c and 2, in order to obtain
a better description for future scenarios.
The significance of the changes observed for
the potential distribution per environmental group
and subgroup, in both climate change scenarios,
analysed by a CDA (Figure 6a-c), shows that the
highest average temperature in July (tmax7) exposes the most important variations between the
current and the future conditions. These variations are more relevant for the group 3 and the
subgroups 1, than for the group 2.
taxa. However, contributions using groups of species with similar ecological amplitudes (TERBRAAK & GREMMEN, 1987) or sets of endemic
species with different life forms (BROENNIMANN
& al., 2006), have reported promising results.
Three different types of behaviours were
found: two of them are represented by potential
distributions on the northern (groups 1 and 3), and
one along the analysed area (group 2). In group
1, three behaviours are distinguished for the northern potential habitats of the group 1, one of
them is restricted to potential habitats along the
coast (subgroup 1a), a second one for the most
occidental mountains (subgroup 1b), and the third
group describes dryer and continental potential
habitats (subgroup 1c).
Traditionally, the areas where the studied species are concentrated (both in the north and in the
southern biogeographic area) have been referred
as biological refugia (MÉDAIL & QUEZEL, 1997;
MORENO SAÍZ & SAÍNZ OLLERO, 1997; MORENO
SAÍZ & al., 1998; LOBO & al., 2001; GIMÉNEZ &
al., 2004).
These results help to understand the gene
flow proposed by several authors for the western
Iberian Peninsula (TABERLET & al., 1998;
OLALDE & al., 2002; PETIT & al., 2002; VARGAS,
2003; MEJÍAS & al., 2007; PARDO & al., 2008;
GUZMÁN & VARGAS, 2009; ROCHA & al., 2012a),
and to explain the significant geographic environmental connectivity along the western of the
Iberian Peninsula (group 2 and subgroup 1c).
The high concentration of endemic species in
northwestern Iberian Peninsula is explained by
the presence of distinct potential habitats for
mountains (group 3 and subgroup 1b) and north
coast (subgroup 1a). On the contrary the high
environmental variability for groups 1c and 2
with significant divergences between grouping
and specific predictions will demand more subdivisons. Additionally, the rapid response of all
the environmental groups to climate changes indicates an extremely thermic and pluviometric
dynamic. This rapid response could reflect a
very active gene flow, possibly as a result of the
characteristic intense climatic variability prevailing since the late Pliocene (OLDFIELD, 2005;
TZEDAKIS, 2007). These relevant changes have
DISCUSSION
Several authors have discussed an expected
northward displacement of the flora in result of
future climate changes (HUNTLEY & al., 1995;
COMES & KADEREIT, 1998; PUIG DE FÁBREGAS &
MENDIZABAL, 1998; WALTHER, 2003; JUMP & al.,
2006a, b; BENITO GARZÓN & al., 2008; RODRÍGUEZ SÁNCHEZ & ARROYO, 2008; ROCHA & al.,
2012b). Several modelling approaches have been
elaborated, with different ecological and geographic ranges for species (GUISAN & THEURILLAT,
2000; al. & al., 2003; ENGLER & al., 2004; RANDIN & al., 2006; RUIZ-LABOURDETTE & al., 2012).
Yet, all the mentioned cases, the modelling was
applied individually by taxon, and not to sets of
29
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João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
Figure 5. – Bioclimatic groups areas under the effect of future climate change scenarios A2 and B2 in 2080: a) group
1A for A2 scenario; b) group 1a for B2 scenario; c) group 1b for A2 scenario; d) group 1b for B2 scenario; e) group
1c for A2 scenario; f) group 1c for B2 scenario; g) group 2 for A2 scenario; h) group 2 for B2 scenario; i) group 3
for A2 scenario; j) group 3 for B2 scenario.
LAZAROA 35: 19-35. 2014
30
João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
Figure 6. – CDA graphic representation for the first two roots, a) for current and future climate change scenarios for
the five bioclimatic groups; b) for group 1 (1a, 1b and 1c) and group 3; and c) for group 2.
determined the migration of individuals across
western Europe (HEWITT, 1996; TABERLET & al.,
1998). Advances and setbacks, the access to different altitudinal levels, and the contact between
different types of biogeographic behavior have
been the main consequences of this intensive
biogeographic dynamic (GUTIÉRREZ LARENA &
al., 2002; HEWITT, 2004; FRAJMAN & OXELMAN,
2007; MÉDAIL & DIADEMA, 2009). In this sense,
the peninsular geomorphological variability has
acted as an extremely important distributing regulator in this biological process (SWANSON &
al., 1988; STALLINS, 2006). This dynamic biological and environmental correlation is now involved in the refugee discussion (MÉDAIL &
DIADEMA, 2009; GÓMEZ & LUNT, 2007; NIETO
FELINER, 2011, 2014). The lack of thermic and
pluviometric stability introduces the possibility
of dynamic refugia, in contrast with the static
idea of environmental areas where species will
find their potential habitat. In accordance with
this discussion, the endemic species especially
those with more restricted ecological amplitudes, will be biological indicators of this process.
The results obtained for future climatic change
scenarios show alarming thermic and pluviometric forecasts for the preservation of species. Special attention must be considered for the mountain
groups (group 3 and subgroup 1b), and north
Atlantic potential habitats, seriously threaten. Results such as those discussed here draw attention
to the importance of monitoring policies, to guarantee the preservation of the species with occurrence in the most sensitive environmental groups
and subgroups.
In the present work the groups, obtained by similarity of thermic, pluviometric and altitudinal
amplitudes of endemic and restricted subendemic
species contribute to describe the biogeographic
floristic dynamics of the flora of the western Iberian Peninsula. To know the geographic dynamic
of these environmental groups under future climate changes, will also be very useful for conservation purposes, or even to understand and
31
LAZAROA 35: 19-35. 2014
João Rocha & al.
Biogeographic trends of endemic and subendemic flora in the western Iberian Peninsula
explain quaternary phylogenetic routes (COMES
& KADEREIT, 1998; TABERLET & al., 1998;
OLALDE & al., 2002; VARGAS, 2003).
scenarios. A trend to north of the area, as well as
important transformations in the potential habitat
areas and the elimination of some of them, are the
most relevant consequences of this forecast.
These results allowed to understand the recent
gene flow across this area described by several
authors, but at the same time the environmental
groups here described seem useful biological indicators for recent biogeographic trends in western Iberian Peninsula.
CONCLUSIONS
The diversity of environmental groups and subgroups, which are significantly different on the
western Iberian Peninsula, reflects the potential habitat complexity of this region. Anyway, the continuity along these environmental clusters of
potential habitats along the study area is guaranteed
by the groups and subgroups detected. In this sense,
restricted and broader environmental amplitudes
are obtained for these environmental subgroups.
A very dynamic biogeographic behavior is deduced by these environmental groups and subgroups when exposed to future climate changes
ACKNOWLEDGEMENTS
João Rocha thanks FCT for a grant (SFRH/ BD/43167/
2008). The authors would like to express their gratitude to
Professor João Honrado (Department of Biology, Faculty of
Sciences, University of Porto) for his important contribution.
They also want to thank to two anonymous reviewers for the
comments made to the manuscript.
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Received: 29 January 2014
Accepted: 23 October 2014
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LAZAROA 35: 19-35. 2014