G. Shenbrot et B. Krasnov, HABITAT RELATIONSHIPS OF THE LIZARD FAUNA IN THE RAMON EROSION CIRQUE, NEGEV HIGHLANDS (ISRAEL), Journal of zoology, 241, 1997, pp. 429-440
Lizards were censused in the Ramon erosion cirque (Central Negev, Isra
el) in 1994 on 24 one-ha plots. Fifteen quantitative habitat variables
, describing soil and vegetation structure, were measured at 25 points
of each plot. Data were analysed to examine a classification of habit
at types based on lizard species composition and the sets of environme
nt variables influencing density of each lizard species. Three hundred
and fifty three individuals of 14 lizard species were recorded on the
sampling plots. Of these species, only one (Acanthodactylus boskianus
) was abundant, eight (Ptyodactyhus guttatus, Stenodactylus sthenodact
ylus, Mesalina guttulata, M. olivieri, Ophisops elegans, Ablepharus ki
taibellii, Chalcides ocellatus, Eurnesces schneiderii) were common, an
d five (Laudakia stellio, Pseudotrapelus sinaitus, Trapelus pallidus,
Hemidaetylus turcicus, tropiocolotes steudneri) were rare. Four main h
abitat types and two sub-types were distinguished: wadis among loess h
ills (I); rock outcrops among loess hills (II); rock outcrops among gr
avel plains (III); wadis among gravel plains (IVa); open gravel plains
(IVb), and sand dunes (IVc). Lizard density and biomass were greatest
(15-19 ind./ha; about 200 g/ha) in IVb, and IVc, and least(3.7 ind./h
a; 38 g/ha) in III. Lizard species richness and diversity were low (th
ree species) in IVc and higher and similar (6-10 species) in all other
habitat types. Among common and abundant species, densities of three
(A. boskianus, O. elagans, A. kitaibellii) were highly (30-60 % of den
sity dispersion) affected by habitat variables and densities of six (P
. guttatus, S. sthenodactylus M. guttulata, M. olivieri, C. ocellatus,
E. schneiderii) were weakly (13-30% of dispersion) affected. Densitie
s of S. sthenodactylus, A. boskianus, and M. guttulata were determined
mainly by soil structure, of M. olivieri and O. elegans mainly by str
ucture of annual vegetation, and of C. ocellatus, A. kitaibellii, and
E. schneiderii mainly by the structure of shrub vegetation. Density of
P. gutratus was determined by both soil and annual vegetation structu
re.