Proceedings of the Royal Society of Edinburgh, 89B, 135-146, 1986
Notes on the distribution, climate and flora of the sand deserts of
Iran and Afghanistan
H. Freitag
Arbeitsgruppe Morphologie und Systemarik der Pflanzen, Universitat Kassel,
Heinrich-Plett-Strasse 40, D-3500 Kassel, B.R.D.
Synopsis
An account is given of the distribution of the sand deserts in Iran, Afghanistan and Pakistan Baluchistan,
where they cover large surfaces on the plains at low and medium altitudes. Climatologically they differ
considerably from each other with respect to winter temperatures, but the latitudinal sequence is obscured
by elevation effects. About one half to one third of the species are strict psammophytes; structurally they
are the most important components of the different plant communities and in mobile sands usually no
other plants occur. Their phytogeographical and taxonomic relationships are discussed in detail and
attempts made to relate the distributional patterns to certain ecological factors. 66% of the species are truly
Irano-Turanian, 23% are endemics, mostly derivatives of Irano-Turanian species, 10% are SaharoArabian and 7% are biregionals. Further aspects pointed out are the representations of life forms of
families and genera. The results in the deserts studied give support to the concept of a coherent IranoTuranianfloristicregion. The southern deserts form a sub-unit of their own, characterised by high numbers
of endemics, some intruding Saharo-Arabian species and an absence of several otherwise common IranoTuranian species.
Introduction
Up till now, information about the ecology, flora, and vegetation of the sand deserts
in Iran and Afghanistan has been very scanty, as can be judged from the small entries
in the voluminous work of Zohary (1973). Even the remarkable progress of Flora
Iranica (Rechinger 1963-) has not altered the situation very much, as it includes only
few data about the ecology of species dealt with. Evidently, detailed studies on the
ecology of species and particularly on plant communities can only be carried out after
the taxonomic base has been laid down. The flora of the sand deserts is comparatively
poor in species, but it includes many critical species, especially in the genera Salsola,
Calligonum and Astragalus sect. Ammodendron, which are not yet dealt with in Flora
Iranica, or are still under dispute, as Calligonum. Besides, every thorough field
campaign yields species new to the Flora Iranica region or even species new to science.
The provisional account presented here is based on the author's own experience
from field work carried out during several years in all seasons, and on careful
evaluation of the pertinent literature. Whereas almost all sand deserts of Afghanistan
have been seen and studied between 1966 and 1970, the coverage of Iran is highly
incomplete, being limited to the sand areas in northern Central Iran in the provinces
Tehran, Semnan and W Khorasan, which were visited in 1976 and 1978. More
detailed floristic data are available only from certain sand deserts in the Kavir
National Park (Rechinger & Wendelbo 1976), the Touran Protected Area (Rechinger
136
H. Freitag
1977) and—most important as examples of the southern type—from the Dasht-e-Lut
and the Jaz Murian depression (Leonard 1981-85). It must be emphasised that the
flora of most remaining Iranian sand deserts is very fragmentarily known; this is
particularly true for the southernmost ones in Khuzestan.
During the preparation of this paper, it proved very useful to have had personal
taxonomic experience in several of the difficult groups, particularly the Chenopodiaceae.
Distribution and climatological conditions
Sandy habitats are widely distributed in the semideserts of Iran and Afghanistan.
This paper, however, deals only with the most extensive and typical kind of sandy
habitat, the real sand deserts or "sand seas". The very common local sand accumulations along most dry river beds and the shallow sand sheets covering many plains
are excluded; they are also inhabited by some widespread psammophilous plants, but
usually dominated by species of disturbed habitats or species of the plains. The only
important exception known to the author, the Dasht-e-Nawor, is discussed later in
this paper.
The sand seas consist of vast dunefields,with sands reaching a thickness of from a
few metres up to more than 100 metres. The surface is more or less mobile or
stabilised, depending upon the degree of aridity and anthropogenic influence. Even in
the remotest and most inaccessible parts, at least the dune crests are built of more or less
mobile sands. The dune structure is more or less irregular, caused by winds blowing
from different directions. More typical longitudinal dunes and barchans occur only
peripherally, where the former type seems to be related to the occurrence of some
taller (shrubby) dune vegetation, and the latter is usually completely devoid of
vegetation and may move several metres per year. Some authors (e.g. Bhimaya, cited
in Ehlers 1980) ascribe the formation of the sand seas to long-lasting desertification
processes, but there is only evidence for re-mobilisation of already more densely
vegetated dune fields with subsequent marginal expansion and rather small-scale
formation of new dunes by sands outblown from degraded gravelly plains. In fact, the
existing sand seas are either more or less active and continuing to grow in accordance
with the actual climate (that seems to be true for S Afghanistan and S Iran), or they
have originated during drier periods of the past and today they tend to be stabilised
by dense psammophytic vegetation. In either case they are the result of weathering,
transportation by water and accumulation by wind during many millenia.
Figure 1 gives the distribution of the sand deserts in a highly generalised manner
because of the irregular surface and the mosaic-like character of many individual
areas. Another delimitation problem occurs at the southern border of the sand desert
in NW Afghanistan as in adjacent Turkmenian Badghys, where the sand accumulations grade continuously into the likewise aeolic loess accumulations. The distribution of sand deserts in Iran and Afghanistan is widely determined by topography,
amount of precipitation and direction of the prevailing winds. They are located in
areas with less than 200 mm annual mean precipitation and most of them receive less
than 150 mm. The only exceptions are the sands in Khuzestan (S Iran), where
precipitation may reach 250 mm (as in some marginal parts of the Indian desert). The
The sand deserts of Iran and Afghanistan
137
spectacular regeneration of vegetation and sand fixation after initial mulching with
crude petrol from the Khuzestan oil fields clearly indicates less arid climatic
conditions, which are probably marginal for the formation of sand deserts. (It should
be noted that the course of the 200 mm isohyete in Figure 1 is not based on the
Climatic Atlas of Iran (1965), which gives very generalised and certainly too low
values for S Iran, but rather the map of Bobek (1952), which agrees much better with
the vegetation of the respective areas and the few available measurements.)
From Figure 1 it is evident that in Iran the sand deserts, except the sands of
Khuzestan and the depression of Jaz Murian, are confined to the central plateau.
Situated at altitudes of about 500-1200 m, they cover a surface of about 183,000 km2
(11% of Iran) with a percentage of c.34% in Esfahan and c.16% in Khorasan and
Kerman provinces (Bhimaya 1971, cited in Ehlers 1980). In contrast, their distribution in Afghanistan is peripheral. In N Afghanistan the southeastern corner of the
Turkmenian Kara Kum extends along the lowlands of the Amu-Darya at 300-400 m
altitude from Faryab to Kunduz provinces. In S Afghanistan the largest sand deserts
are located in Kandahar and Helmand provinces ("Registan") and in Chakhansoor at
altitudes of 500-1000 m, and from there they continue into Pakistani Baluchistan. The
absence of larger sand deserts from the likewise arid W Afghanistan is probably
related to the strong northern or northwestern 'wind of the 120 days', which carries its
heavy sand load further the S and SE.
A comparison of the diagrams on both sides of Figure 1 reveals that climatic
Figure 1. Distribution of sand deserts in Iran and Afghanistan, as related to the 200 mm isohyete, and
climate diagrams of selected stations (taken from Walter & Lieth 1960); data from various
sources, modified.
138
H. Freitag
conditions seem to be rather uniform all over the area. There are no significant
differences over long distances both in W-E and N-S directions, as may be seen from
the diagrams of Kisil Arvat in Turkmenia, Termez on the banks of the Amu-Darya,
and Esfahan in western C Iran. However, on closer inspection a quite steep but
discontinuous gradient in winter temperatures, exemplified by the absolute minima
and consequently also in the annual mean temperatures, becomes detectable: Nukuss
just S of Lake Aral ( - 2 6 0 ; 10-8), Esfahan (-200; 15-5), Chaman (-11-7; 18-8),
Seistan (-8-3; 20-6) and Chabahar ( + 7-2; 25-7). Despite almost equally hot and dry
summers, it must be expected that differences in frost resistance lead to floristic
differentiation, which indeed is very pronounced between N Afghanistan and N and
C Iran on one hand and S Iran, S Afghanistan and Pakistani Baluchistan on the other.
The striking uniformity of climate and subsequently of the flora from central Iran
northwards up to the Kara Kum is mainly due to the fact that the normal temperature
gradient does not become effective because of the higher elevation of the more
southern semideserts.
The psammophytic flora
General remarks
As everywhere in sandy habitats, plant species growing in the sand deserts of Iran
and Afghanistan are highly adapted to their special environment. The particular
stresses are burial by sand, desiccation by outblown roots, dying off of seedlings by
rapid exsiccation of the upper soil layer or by extremely high temperatures, etc. Much
less known are the advantages of comparatively high amounts of water stored in the
subsoil and the absence of higher salt contents. It is not surprising that most species
are highly specialised as psammophytes. The plant communities on mobile sands are
made up of only a very small number of extreme psammophytes. The more the sands
become stabilised, the more psammophytic species invade. Under natural conditions
without strong human pressure, they form open shrublands, surpassing the vegetation of most adjacent non-sandy habitats in their height, coverage and productivity.
Beside the true psammophytes, a growing number of more ubiquitous species occur,
but they remain subordinate. The only exceptions are the very few cases of old fossil
dunes with a completely stabilised surface and an advanced formation of a soil profile
usually indicated by the development of a gypsum horizon.
In Tables 1, 2a and 2b a first comprehensive list of the psammophytic flora of
the sand deserts of the Flora Iranica region is presented. It is based on repeated
screening of hundreds of vegetation inventories and other field notes, and on an
additional evaluation of the literature. Thefirstdraft, shown and discussed at the time
of the symposium, has been further improved by taking into consideration some
comments kindly given by Professor K. H. Rechinger. Nevertheless, the enumeration
should be considered as a first approach. Further studies, particularly in central and S
Iran, and in Pakistani Baluchistan may add more species or may lead to re-evaluations.
For considering a species as a genuine psammophyte, the strongest criteria have been
used. Here only a species strictly bound to sandy habitats all over its distributional
area is included. I am quite aware of the subjective component of using that narrow
The sand deserts of Iran and Afghanistan
139
concept because, besides the obligate psammophytes listed below, there are others
with a preference for sand deserts, but which also occur on quite different habitats:
Dendrostellera lessertii, Haplophyllum robustum, Schumannia karelinii, Salsola leptoclada and Euphorbia turcomanica. Quite a number of annuals are almost equally
common on stabilised sands, on loess soils and on sandy-gravelly alluvial soils of the
plains. Finally the lists have been re-checked against the tables of several Soviet
authors who dealt with the Turkmenian sand deserts, in particular Nechajeva et al.
(1973) and Korovin (1961).
Distributional types in the psammophytic flora
Despite the discontinuous distribution of the sand deserts, most psammophytes
evidently were and probably still are able to reach even the most remote sand fields.
Except for a few species (e.g. of Euphorbia, Chrozophora and Allium), their diaspores
are equipped with very effective anemochorous devices (wings, feathery appendices,
balloon-like vesicles, etc.) and the frequent and strong winds can carry them over long
distances. That makes psammophytes particularly suitable for phytogeographical
considerations, because their respective areas are generally more strictly controlled by
actual climatic factors than in many other species. Nevertheless, other ecological
factors as competition with other species (particularly of the same life form) and
history (age of the taxon and possibility of migrations during past periods with
different climates) are likewise effective. A very first but inevitably fragmentary
attempt to detect distributional pattern in the psammophytes of Iran was undertaken
by Hedge & Wendelbo (1978).
Widespread species (Table 1)
A remarkable high number of psammophytes are spread all over the sand deserts of
Iran, Afghanistan and adjacent areas. Species of all life forms belong here, but
annuals are more numerous. Evidently those species do not respond to the
considerable variation of temperature conditions within the area under concern.
Most of them do not extend further S or SW but are widespread in Soviet Middle
Asia (Srednaya Aziya). They are mostly representative of the Irano-Turanian floristic
element.
A much smaller group of species likewise extends far beyond the frontiers of Iran
and Afghanistan in both directions to the N and S. The area of these biregional IranoTuranian/Saharo-Arabian species includes at least large parts of Arabia as the eastern
sector of the Saharo-Arabian floristic region. Most individual species have their
centre of distribution either in the Irano-Turanian (e.g. Haloxylon persicum) or the
Saharo-Arabian region (e.g. Centropodia forsskalii).
Species with more restricted areas of distribution (Table 2a, b)
All psammophytes with distributional lines inside the area are listed in Table 2a, b,
together with their occurrences in the 5 geographical subunits: NW Afghanistan, N and
central Iran, S Iran, S Afghanistan, Pakistani Baluchistan, and central Afghanistan.
The first group comprises again Irano-Turanian species, which in contrast to those
140
H. Freitag
Table 1. Widespread psammophytic species (mostly Irano-Turanian elements; a
few biregional Irano-Turanian and Sahara-Arabian elements are marked
with +)
Shrubs, dwarf shrubs
Ammodendron conollyi Bunge (only Turkmenia and Iranian Baluchistan)
Calligpnum caput-medusae Schrenk
C. leucocladum (Schrenk) Bunge s.l. (incl. var. serratum Litv. & C. persicum Boiss.)
C. rubens Mattel
C. setosum Litv.
Convolvulus erinaceus Ledeb.
C. korolkovii Regel & Schmalh.
Ephedra strobilacea Bunge
+
Haloxylon persicum Bunge ex Boiss. & Buhse
Salsola richteri Kar. ex Litv.
Other perennials
Astragalus (Eremophysd) chivensis Bunge
+
Centropodia forsskalii (Vahl) Cope ( = Asthenatherum forsskalii)
Cistanche ambigua (Bunge) G. Beck
C.flava (C. A. Mey.) Korsh.
Haplophyllum bungei Trautv.
Heliotropium arguzioides Kar. & Kir.
H. micranthos (Pall.) Bunge (only Turkmenia and S Iran)
Stipagrostis pennata (Trin.) de Winter
Geophytes (ephemeroids)
Allium borszczowii Regel
A. fibrosum Regel
Carex physodes M. Bieb.
Ferula foetida (Bunge) Regel
Iris falcifolia Bunge
Annuals (and biennials)
Agriophyllum latifolium Fischer & C. A. Mey.
A. minus Fischer & C. A. Mey.
Astragalus (Oxyglottis) ammophilus Kar. & Kir.
* A. (Harpilobus) hauarensis Boiss.
Centaurea pulchella Ledeb. ( = Hyalea pulchella (Ledeb.) C. Koch)
Chrozophora gracilis Fischer & C. A. Mey.
+
C. hierosolymitana Spreng.
Cousinia bipinnata Boiss, s.l. (incl. C. oxiana Tschern. & C. turkmenorum Bornm.)
*Cutandia memphitica (Spreng.) Benth.
Euphorbia cheirolepis Fischer & C. A. Mey. ex Ledeb.
E. densa Schrenk
E. turczaninowii Kar. & Kir.
Horaninovia anomala (C. A. Mey.) Moq.
H. ulicina Fischer & C. A. Mey.
Kochia iranica (Bornm. & Hausskn.) Litv.
K. odontoptera Schrenk
Lappula semiglabra (Ledeb.) Guerke
Octoceras lehmannianum Bunge
Oligochaeta minima (Boiss.) Briq.
Salsola implicata Botsch.
S. praecox Litv.
*Schismus barbatus (L.) Thell.
+
Silene arabica Boiss.
S. nana Kar. & Kir.
Spirorhynchus sabulosus Kar. & Kir.
Tetracme recurvata Bunge
141
The sand deserts of Iran and Afghanistan
Table 2a. Psammophytic species with more restricted distribution
NW
Afgh.
N&C
Iran
S
Iran
S Afgh.
&Bal.
C
Afgh
IRANO-TURANIAN species
Shrubs, dwarf shrubs
Astragalus (Ammodendron) nigricans Barneby
Polygonum arianum Grig.
Acanthophyllum elatius Bunge
Ammothamnus lehmannii Bunge
Artemisia diffusa Kraschen.
Mausolea eriocarpa (Bunge) Poljak. ex Podl.
Calligonum microcarpum Borszcz.
Smirnowia turkestana Bunge
Zygophyllum eichwaldii C. A. Mey. in Eichw.
+
+
+
+
+
7
+
+
+
+
+
+
+
+
7
+
Other perennials
Jurinea derderioides C. Winkl.
Stipagrostis karelinii (Trin. & Rupr.) Tzvelev
Astragalus (Myobroma) flexus Fischer
Eremostachys regeliana Aitch. & Hemsl.
Heliotropium acutiflorum Kar. & Kir.
H. chorassanicum Bunge
H. transoxanum Bunge
+
+
+
+
+
+
+
+
+
+
+
+
+
Geophytes (ephemeroids)
Allium caspium (Pall.) M. Bieb.
A. sabulosum Stev. ex Bunge
Dorema sabulosum Litv.
Eminium lehmannii (Bunge) O. Kuntze
Merendera robusta Bunge
+
?
+
+
+
+
+
+
+
+
+
+
+
+
+
?
+
+
?
+
+
+
+
Annuals
Cousinia orlhacantha Tscherneva
Chamaesphacos ilicifolius Schrenk
Cithareloma lehmannii Bunge
Consolida camptocarpa (Fischer & C. A. Mey.)
Nevski
Corispermum lehmannianum Bunge
Euphorbia inderiensis Less, ex Kar. & Kir.
Launaea korovinii (Popov) Popov ex Pavlov
(+ )
(+)
cited in Table 1 fade out in central Iran and are absent from S Iran, S Afghanistan and
Baluchistan. Stipagrostis karelinii (not yet mentioned in Flora Iranica) in Figure 2
serves as an example. The reasons for the absence from the southern sand deserts are
difficult to explain. Some species seem to have problems coping with the harsher
environmental conditions, particularly with regard to their water balance or the
establishment of seedlings because of the higher temperatures during the shorter rainy
season and the less predictable rainfall. That could well explain the distribution of the
geophytes and many annuals. Other species are represented in the southern part of the
area by closely related vicariants (cited in Table 2b under endemics), which probably
evolved in periods of more pronounced isolation and may have developed more
effective adaptations to the southern environments. Such pairs of vicariant species
are Calligonum microcarpum and C. amoenum, Cithareloma lehmannii and C. registanicum, Eremostacys regeliana and E. ammophila, Ephedra strobilacea and E.
142
H. Freitag
Table 2b. Psammophytic species with more restricted distribution
NW
Afgh.
SAHARO-ARABIAN species
N&C
Iran
S
Iran
S Afgh.
&Bal.
c
Afgh.
Shrubs
Calligonum crinitum Boiss.
Other perennials
Cyperus conglomerates Rottb.
Pennisetum divisum (Gmel.) Henrard
Annuals
Eremobium aegyptiacum (Spreng.) Schweinf. &
Aschers.
Ifloga spicata (Forsskal) Schultz-Bip.
Launaea capitata (Spreng.) Dandy
Neurada procumbens L.
Savignya parviflora (Del.) Webb
Tribulus longipetalus Viv.
T. ochroleucus (Maire) Ozenda & Quezel
ENDEMIC species
Shrubs, dwarf shrubs
Astragalus (Ammodendrori) kavirensis Freitag
A. (Ammodendrori) aff. ahmed-adlii
A. (Ammodendrori) oligophyllus Boiss.
Calligonum amoenum Rech. f. & Schim.-Czeika
C. laristanicum Rech. f. & Schim.-Czeika
Ephedra microbracteata Ghahreman
Noaea griffithii Bunge
Astragalus (Ammodendron) aff. oligophyllus
Astragalus (Aegacantha) antheliophorus Demi
Other perennials
Heliolropium rudbaricum (Bornm.) Riedl
Aeluropus macrostachys Hack.
Astragalus (Eremophysa) registanicus Rech. f.
Eremostachys ammophila Rech. f.
Cousinia ammophila Rech. f.
Fibigia compacta Rech. f.
Piptatherum rechingeri (Bor) Freitag
Annuals
Cithareloma registanicum Rech. f.
Fagonia ovalifolia Hadidi
Heliotropium remotiflorum Rech. f. & Riedl
Arnebia latebracteata Riedl
Lappula leonardii Riedl
Launaea platyphylla Rech. f.
Psammogeton spec. nov.
microbracteata. In the area under review, most Irano-Turanian species of Table 2a
agree to their distribution patterns, but one group of specimens seems to be confined
to the sand deserts N of the mountain divide formed by the Hindukush-ParopamisusKopet Dagh system, and probably they never managed to cross it. Most characteristic examples of this group, which represents the Turanian sub-element, are Polygonum arianum (not recorded from Afghanistan before), Jurinea derderioides and
The sand deserts of Iran and Afghanistan
Figure 2.
143
Distribution of: Stipagrostis karelinii, an example of an Irano-Turanian species with a restricted
distribution absent from all southern deserts; and Pennisetum divisum, an example of an
widespread Saharo-Arabian species, extending into the southern deserts.
Cousinia orthacantha. Other species, so far only known from the Turkmenian sands,
may be found in the sand deserts at the Amu-Darya in NW Afghanistan, where
botanical field work was, and still is, almost impossible for political reasons. Most
probable candidates to be found there are Acanthophyllum korolkovii, Ammodendron
eichwaldii, several Astragalus species of the sections Ammodendron {A. badghysi, A.
excedens, A. unifoliatus) and Spryginiana (A. petunnikovii), Cousinia alata and C.
psammophila, Cryptodiscus ammophilus, Eremosparton aphyllum and E. flaccidum,
Ferula litwinowiana, Lipskyella annua, Salsola paletzkiana and Tournefortia sogdiana.
A second group is formed by Saharo-Arabian species (Table 2b), which occur only
in the southern sand deserts. They are less numerous, but a few of them are important
components of the respective plant communities, particularly Pennisetum divisum
(Fig. 2) and Cyperus conglomeratus. However, they are always outnumbered by
Irano-Turanian and endemic species, but admittedly the southernmost sand deserts in
Khuzestan, in the Jaz Murian depression and in Pakistani Baluchistan have not yet
been studied phytosociologically. No doubt, the more or less identical northern
borderline of the Saharo-Arabian species is determined directly or indirectly by low
winter temperatures. Other environmental factors are almost alike and all species
have the ability of long-range dispersal.
The third group is made up of endemic species. The 21 species (including 3 species
not yet described) are very unevenly distributed. NW Afghanistan has none, and the
bulk of the endemics are concentrated in the southern sand deserts. N and central Iran
and S Afghanistan have 2 endemic species in common {Astragalus oligophyllus and
Heliotropium rudbaricum). Both belong to very critical groups and their distribution is
incompletely known, so they might be found in other parts of the area. Taxonomically they are likewise closely allied to Irano-Turanian psammophytes. The southern
sand deserts have quite a number of endemics in common, but each area has its own
144
H. Freitag
set of narrow endemics. Most of the southern endemics are again offsprings from
Irano-Turanian psammophytes or at least psammophilous species. It is interesting
that a few endemics have without doubt originated from Saharo-Arabian stock, in
particular Fagonia ovalifolia, Launaea platyphylla and probably the more isolated
Aeluropus macrostachys. A very peculiar case is Noaea griffithii Bunge. It may be a
remnant of an old indigenous subtropical element comparable to Stocksia brahuica
which has a very similar distribution, albeit it grows along dry river beds.
The most remarkable and unusual case of local endemism in psammophytes is
displayed by the group Cousinia ammophila, Fibigia compacta, Astragalus (Aegacantha) antheliophorus and Piptatherum rechingeri. These 4 species are confined to the
rather small and shallow sand fields in the Dasht-e-Nawor depression in eastern central
Afghanistan. The sands cover less than 1 km2 at an altitude of c.3000 m and are
surrounded by high mountain ranges. The absence of even widespread and otherwise
common psammophytes and the evolution of that number of endemics can only be
understood in terms of highly effective and long-lasting topographical and ecological
isolation. In striking contrast to all the other endemic psammophytes, these species
did not evolve from progenitors already adapted to sandy habitats, but from species
of the lower alpine slope vegetation, with Cousinia multiloba, Fibigia membranacea,
Astragalus (Aegacantha) spec, and Piptatherum laterale on adjacent slopes being
respectively the closest relatives.
Concluding remarks
According to present-day knowledge, the number of true psammophytes in the
sand deserts of Iran and Afghanistan amounts to 106 species. They make up
approximately one half to one third of the total number of species to be found in these
habitats. With regard to distributional patterns (see Table 3), the overwhelming
majority of species (62%) belong to the Irano-Turanian element. This is followed by a
remarkably high percentage of endemics (22%) and a much smaller number of
Saharo-Arabian (9%) and biregional species (7%). The tabulation demonstrates the
Irano-Turanian character of the flora in the Iranian and Afghan lowlands and
plateaux, where almost all sand deserts are located. Their floristic separation from the
Transcaspian lowlands, the Turanian subregion, is much weaker than might be
expected. Very pronounced is the differentiation into a northern sector including N
and central Iran and N Afghanistan, and a southern sector with significant intrusions of
Saharo-Arabian species. More precise conclusions for the southern deserts must
Table 3. Distributional types and life forms in the psammophytes of Iran and
Afghanistan
Distributional type
Irano-Turanian
Ir.-Tur. & Saharo-Arabian
Saharo-Arabian
Endemics
Total
Shrubs,
dwarf shrubs
Other
perennials
Geophytes
Annuals,
biennials
18
1
1
9
14
1
2
7
6
—
—
—
28
5
7
7
29 = 27%
24 = 23%
6 = 6%
47 = 44%
Total
s. %
66
7
10
23
62
7
9
22
106=100%
145
The sand deserts of Iran and Afghanistan
await careful phytosocjological studies in southern Iran and in Baluchistan. The
percentage of the endemics is somewhat smaller than in most other habitat types. The
reason is seen in the anemochorous distribution of the species and their high degree of
adaptation to the special habitat. More than 80% of the endemics are restricted to the
southern deserts and, together with the occurrence of Saharo-Arabian plants and the
rather sudden thinning-out of some Irano-Turanian species, they underline the
distinct phytogeographical position of that southernmost part of the Irano-Turanian
region. However, it should be noted that the endemics, except for a very few species of
Saharo-Arabian or unknown origin, have originated from truly Irano-Turanian
progenitors, usually of a psammophytic character. That is also reflected in Table 4 by
the list of genera with higher numbers of endemics.
With respect to life forms (Table 3) it is noteworthy, but not surprising, that the
annuals (including biennials) dominate with almost one half of the species total,
followed by shrubs and dwarf shrubs with about one third and other perennials with
c. one quarter. Geophytes are poorly represented and occur only in the IranoTuranian group.
The family representation (Table 5) shows a predominance of the Fabaceae,
Asteraceae, Chenopodiaceae, Boraginaceae, Polygonaceae and Poaceae both in
species numbers and in structurally important components of the plant communities.
Fabaceae and Polygonaceae are each represented by 9 species of shrubs and dwarf
shrubs. They usually determine the shape and aspect of the respective associations.
Table 4. Genera with higher numbers of endemic psammophytes
Number of species
11
(5)
8
7
4
4
3
Genus
Astragalus
(sect. Ammodendron)
Calligonum
Heliotropium
Salsola
AIHum
Cousinia
Table 5. Family representation in the psammophytes of Iran and Afghanistan
Family
Fabaceae
Asteraceae
Chenopodiaceae
Boraginaceae
Polygonaceae
Poaceae
Brassicaceae
Euphorbiaceae
Zygophyllaceae
Alliaceae
Caryophyllaceae
Lamiaceae
Apiaceae
Other families
Shrubs,
dwarf shrubs
Other
perennials
Geophytes
Annuals,
biennials
9
2
3
—
9
—
1
—
1
—
1
—
—
3
3
2
—
6
—
6
—
—
—
—
—
2
—
5
—
—
—
—
—
—
—
—
—
4
—
2
9
9
4
—
2
7
6
3
—
2
1
1
1
2
Tot
14
13
12
10
9
8
8
6
4
4
3
3
3
9
146
H. Freitag
Boraginaceae and Poaceae have the highest number (6 species) of hemicryptophy tes,
which contribute significantly to the biomass of the plant communities and play a
most important part in sand fixation (Heliotropium, Stipagrostis). Asteraceae and
Chenopodiaceae have the highest number (9 species) of annual psammophytes,
besides some representatives of other life forms.
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