O4: Caspian hemipsammophytic grass-wormwood deserts on partly clayey sand soils with Artemisia lerchiana, Poa bulbosa, partly with Stipa sareptana and/or Stipa lessingiana

CountryKazakhstan
Province Caspian lowland – interfluvial region Volga-Ural, south-western of the lower Volga
References

Ivanov 1953b; Kljukin et al. 1968; Kunaev (Red.) 1982; Ladygina, Račkovskaja & Safronova (Red.) 1995a; Ladygina, Račkovskaja & Safronova (Red.) 1995b; Lavrenko 1962; Pjatin (Ed.) 1997; Prozorovskij 1940; Prozorovskij & Maleev 1947; Račkovskaja, Safronova & Chramcov 1990; Rodin & Rubcov 1956; Safronova 1975; Safronova 1980b; Sangadziev et al. 1974

Remarks

CONIF
BLD
BLE
SCL
LEG
ZONPALM
ARBFERN
D-HERB
M-HERB
AZONAL WOODY
AZONAL NON-WOODY
AQUATIC
PROBLEMATIC TAXA
Sum of taxa
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
6.60
M-HERB
2.40
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
Percentage of zonal taxa
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
73.33
M-HERB
26.67
Percentage of zonal woody angiosperms
BLD
NaN
BLE
NaN
SCL
NaN
LEG
NaN
ZONPALM
NaN
Sum of all taxa9.00
Sum of zonal taxa9.00
Sum of zonal woody angiosperms0.00
Sum of % SCL + LEGNaN
Sum of % D-HERB + M-HERB (ZONAL HERB)100.00

Vegetation types

No vegetation types.

EuroVegMap information

Title

Caspian hemipsammophytic grass-wormwood deserts on partly clayey sand soils with Artemisia lerchiana, Poa bulbosa, partly with Stipa sareptana and/or Stipa lessingianaa = alternating with O1; b = alternating with O2; c = alternating with O6; d = alternating with tall reed vegetation and salt meadows (Phragmites australis, Typha latifolia, Elymus repens, Aeluropus littoralis etc.) adjacent to lakes with fresh and brackish waters

Geographical distribution

Country/territory
Russia and Kazakhstan: Caspian lowland – interfluvial region Volga-Ural, south-western of the lower Volga
area covered
43670 km²
area frequency
13 polygons.

Scientific names of main plant communities and their most common synonyms (with author citation)

Poa bulbosa-Artemisia lerchiana, Stipa sareptana-Poa bulbosa-Artemisia lerchiana, Stipa lessingiana-Poa bulbosa-Artemisia lerchiana communities.

Structural feature of the main community(ies) (layers, life-forms, etc.)

Very species deficient vegetation type (10-15 species) with a loose (25-35 %) degree of cover (seldom 40-45 %). Artemisia lerchiana is accompanied by the codominant Poa bulbosa, and often by codominant grasses (Stipa sareptana, Stipa lessingiana). In the early spring ephemerals, ephemeroids and hemiephemeroids occur frequently. Summer and autumn annuals are rare.

Dominant and most frequent species in different layers

Tree layer
---
Shrub layer
---
Lianas
---
Herb layer
Artemisia lerchiana, Poa bulbosa, Stipa sareptana, Stipa lessingiana, Kochia prostrata, Bromus tectorum, Alyssum turkestanicum, Ceratocephala testiculata, Tulipa biflora among others
Moss layer (incl. lichens)
No details

Diagnostically important species

Artemisia lerchiana, Poa bulbosa, Stipa sareptana, Stipa lessingiana

Ecological variants

---

Geographical variants (geogr. differential species)

Stipa sareptana and Stipa caspia in the south of the intrafluvial region between the Volga and the Ural.

Natural accompanying vegetation (most important units in complex with the name giving mapping unit, scientific names)

Small area occurrences of Artemisia taurica stands in Artemisia deserts on salty soils of the kalmuk steppes, of north-Turanian halophytic dwarf semishrub vegetation (Halocnemum strobilaceum, Kalidium foliatum, Atriplex cana, Artemisia santonicum) on solonetz soils and vegetation-free salt pans; Artemisia lerchiana-Poa bulbosa communities with different Stipa species.

Adjoining climax and permanent vegetation (with numbers of mapping units)

desert steppes (M19, M18, M20, M21), northern dwarf semishrub deserts (O1, O2, O3, O5, O6), salt vegetation (P35), freshwater-tall reed swamps (R1), alluvial forests and scrubs (U42).

Land use, substitute communities

forestry (substitute communities, plantations of economic tree-species, scrub)
---
grassland (meadows, pastures, herb-rich communities)
Pastures.
arable land (characteristic weed communities)
---
settlements (typical ruderal vegetation)
---

Site conditions of the mapping unit

Landscape type, geomorphology
flat and weakly undulating plains where negative relief forms prevail
Altitudinal belt and/or altitudinal range
lowland; the absolute altitudinal range of -20 to +25 m
Geology (bedrock)
eolian sediments (Holocene)
Soil conditions
soil type, also the depth of fine textured earth (soil), stone content; (international nomenclature)
brown desert soils; (haplic and luvic sodic xerosols)
soil texture
loamy sand and sand
soil moisture, water balance
very dry
soil reaction
alkaline
soil fertility
oligotrophic
Climate incl. local climate
climate type (following Walter & Lieth)
VII3
average annual temperature
7-8 °C
average annual precipitation
200-250 mm
average temperature of the warmest month
July 24-26 °C
average temperature of the coldest month
January -12 to -10 °C
local climate or other climatic peculiarities
distinctively continental, arid.

Importance for nature protection

Present state and development trend of natural vegetation (degree of endangerment)
Natural Poa bulbosa-Artemisia lerchiana desert occupies larger areas in the European desert region.
endangered communities, species worthy of protection in natural vegetation
Poa bulbosa-Artemisia lerchiana communities with Stipa-species.
causes of endangerment
Intensive grazing.
required measures for protection and restitution
Regulation of grazing.

Localities of representative stands (loci typici) with state of protection

of the natural vegetation
between Caucasus and the lower course of the Ural.
of characteristic substitute communities worthy of protection
---

Most important references (author, year)

Ivanov 1953b; Kljukin et al. 1968; Kunaev (Red.) 1982; Ladygina, Račkovskaja & Safronova (Red.) 1995a; Ladygina, Račkovskaja & Safronova (Red.) 1995b; Lavrenko 1962; Pjatin (Ed.) 1997; Prozorovskij 1940; Prozorovskij & Maleev 1947; Račkovskaja, Safronova & Chramcov 1990; Rodin & Rubcov 1956; Safronova 1975; Safronova 1980b; Sangadziev et al. 1974

Compiled by

Z. Neuhäuslová based on documents by I. Safronova

Taxons

Taxon
CONIF
BLD
BLE
SCL
LEG
ZONPALM
ARBFERN
D-HERB
M-HERB
AZONAL WOODY
AZONAL NON-WOODY
AQUATIC
PROBLEMATIC TAXA
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
0.90
M-HERB
0.10
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
0.80
M-HERB
0.20
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
0.60
M-HERB
0.40
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
0.80
M-HERB
0.20
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
0.60
M-HERB
0.40
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
0.50
M-HERB
0.50
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
0.90
M-HERB
0.10
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
1.00
M-HERB
0.00
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00
CONIF
0.00
BLD
0.00
BLE
0.00
SCL
0.00
LEG
0.00
ZONPALM
0.00
ARBFERN
0.00
D-HERB
0.50
M-HERB
0.50
AZONAL WOODY
0.00
AZONAL NON-WOODY
0.00
AQUATIC
0.00
PROBLEMATIC TAXA
0.00