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Calandrella cinerea

warning Vulnerable
VU (A2b)

Update Time: Jan. 1, 2011, 7:39 a.m.

The Greater Short-toed Lark is classified as Vulnerable (VU) because of the continued decrease in its populations, estimated at more than 30% over 10 years. In the previous edition of the Red Book (2002), it was classified as Data Deficient (DD). The change in the status of the species reflects the decline in its population, as well as an improvement in the quality of data and assessment methods.
VU Current Regional Assessment | DD Previous Regional Assessment | LC Global Assessment

Presence In Israel Summer
Breeding In Israel Breeder
Migration Types Long Range
Zoographical Zones Mediterranean, Irano-Turanian
Landscape Types Plains & Valleys, Wide Wadis
Vegetation Types Cropland, Herbaceous
Vegetation Densities Low
Nest Locations Ground
Diet Types Herbivore
Foraging Grounds Ground
Body Sizes Small (up to 500g)
Threat Factors Habitat destruction in migration and wintering areas, Habitat loss and fragmentation, Nest destruction by agricultural activity, Tree planting

The Greater Short-toed Lark is a relatively small, pale lark with delicate streaking, which frequently forms flocks. Its plumage is relatively variable – some individuals are greyish-sandy, while others have a richer rustier hue. It has a relatively thick, but pointed bill and a delicate face pattern. Occasionally a dark patch appears on the sides of the breast. Flight call is hoarse and intermittent, frequently discloses its presence.

The Greater Short-toed Lark is a common passage migrant throughout Israel in spring and autumn. Breeds locally and in low densities in the Golan Heights, Eastern Galilee, on Mt. Gilboa and in the Jordan Valley, as well as in the Northern and Central Negev. The number of breeding pairs and their distribution varies greatly from year to year.

The Greater Short-toed Lark nests in open dry fields, often at the edges of cultivated fields as well as in desert plains with low vegetation.

No specific conservation measures have been taken for this species to date.

The Greater Short-toed Lark is a nomadic species that breeds in “green patches” in the Negev and at the edges of cultivated fields with suitable cultivation regimes. Detailed surveys are necessary for a better understanding of the factors limiting the population and suggesting ways of preserving the species.

  • פז, ע. 1986. עופות. מתוך אלון, ע. (עורך), החי והצומח של ארץ ישראל. כרך 6. הוצאת משרד הביטחון, ישראל.
  • פרלמן, י., אלתרמן, ש. וגרניט, ב. 2011. סקר עופות דוגרים בנחלים הפנימיים, אביב 2011. דו"ח מרכז הצפרות של החברה להגנת הטבע.
Contributed: Avner Rinot, Asaf Mayrose, Yoav Perlman, Lior Kislev, Nadav Israeli, Noam Weiss, Tuvia Kahn, Ezra Hadad

Current Occupancy Map

Current occupancy map by density
Data Missing Sporadic Limited Sites Low Density High Density
0 0 0 0 0

Distribution maps

The maps presented here provide visual information on the distribution of species in Israel from the past and present, and the changes in occupancy and breeding density during the comparison period. For further reading


Relative Abundance 2010-2020

Breeding density values in the current decade as determined from experts' opinion and observations from databases.

Relative Abundance 2010-2020 by density
Data Missing Sporadic Limited Sites Low Density High Density
8 12 12 21 19

Relative Abundance 1980-1990

Density values based primarily on the book The Birds of Israel (Shirihai 1996).

Relative Abundance 1980-1990 by density
Data Missing Sporadic Limited Sites Low Density High Density
5 14 14 17 22

Occupancy 1990-2020

The map shows differences in the species breeding distribution between the 1980's breeding map and the current weighted breeding evaluation. Negative value - species previously bred in the grid and is not presently breeding; positive value - species has not previously bred in the grid and is currently breeding.

Occupancy 1990-2020
Data Missing No Change Occupancy Increase Occupancy Decrease
6 35 1 9

Change in Relative Abundance 1990-2020

The map shows the changes in the relative abundance of a species in each of the distribution grids between the breeding map of the 1980s and the weighted current breeding evaluation. Negative values - decline in abundance; positive values - increase in abundance; zero - no change in abundance.

Change in Relative Abundance 1990-2020
80 to 100 50 20 to 30 No Change 30- to 20- 50- 100- to 80- Data Missing
0 4 2 22 12 14 11 16

Rarity
Vulnerability
Attractiveness
Endemism
Red number
Peripherality
IUCN category
Threat Definition according to the red book
() districts
Disjunctiveness:
% of protected sites

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