774 Y. Yom‐Tov et al.
FIG. 3 Connectivity of the mountain gazelle population in (a) core regions in the Mediterranean region and (b) central Israel, where connectivity of gazelle populations is particularly hampered, with the main barriers preventing free movement between populations. The connectivity index is a function of permeability for gazelle movement to adjacent populations (see text for full details, and Supplementary Table 1).
main areas of gazelle concentrations, (2) occasional obser- vations of gazelles routinely reported by Israel Nature and Parks Authority rangers (the database comprised 72,437 observations recorded during 1973–2018), and (3) observa- tions and counts of gazelles by AB and EH in the Jerusalem corridor and Judean Mountains and foothills, respectively (Fig. 2). For each core area we calculated the degree of fragmen-
tation in two stages. Initially we used a map of land use (Sorek & Perevolotsky, 2016) to identify human dominated landscapes (i.e. built environments, roads, railways), and ha- bitats that are permeable to gazelles such as natural vegeta- tion and agricultural fields. Each pixel (150 m2) was given a permeability score based on its property of enabling or hampering gazelle movement (see Supplementary Table 1 for permeability score values per land-use category). We then summed these scores outwards from each core area to create its connectivity area. For each connectivity area the perme- ability values were summed up to 6 km away from each core region, or up to a maximum of 6,000 permeability score units. In fragmented regions with high human disturbance, the 6,000 units threshold was reached before the 6 km limit, and thus the connectivity areas were smaller. We then cal- culated a connectivity index for each core area as (core area + connectivity area)/core area. Completely isolated core areas have an index value of 1, whereas higher index values indicate higher connectivity from the core areas outwards. Figure 3 displays the connectivity index for each core area, highlighting regions where gazelles reside and their con- nectivity.
This first stage did not take into consideration all possible
causes of fragmentation, such as fences,most ofwhich do not appear on the available maps. To account for such obstruc- tions, we consulted with regional Israel Nature and Parks Authority rangers. In cases where obstruction to free move- ment of gazelles exists we changed the category of each core area by altering the relevant permeability scores and recalcu- lating the connectivity index (Fig. 3). All spatial analysis was carried out in ArcMap 10.3 (Esri, Redlands, USA).
Threats
A combination of several major threats limits the growth of the Israeli gazelle population and/or causes its decline.
Habitat destruction and change
The impact of human settlements on gazelles may extend beyond dwellings and is considerably greater than the actual loss of suitable grazing land. Gazelles have been recorded to perceivehuman presence as a threat, with an increased flight distance with higher human presence and a positive corre- lation of vigilancewith extent of disturbance (Manor&Saltz, 2004, 2005). Gazelle pellet counts have indicated partial avoidance at least 700 m into natural habitats bordering human habitations (Manor&Saltz, 2005). Strong avoidance of human dwellings and their vicinity by gazelles has been confirmed using camera-traps (Sorek&Perevolotsky, 2016).
Oryx, 2021, 55(5), 771–778 © The Author(s), 2020. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S003060531900108X
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