204 M. A. Kichloo et al. The wide array of habitats across the landscape supports
a large population of carnivores and their prey base. The major carnivores in the region, apart from the common leopard, include the snow leopard Panthera uncia, Asiatic black bear Ursus thibetanus and Himalayan brown bear Ursus arctos isbellinus. The main prey species include the Himalayan goral Naemorhedus goral, Himalayan musk deer Moschus leucogaster, Himalayan ibex Capra sibirica, hangul Cervus hanglu hanglu, various smaller animals and numerous species of Galliformes (Hilaluddin & Naqash, 2013). Agriculture and livestock herding are the primary sources of income for the majority of the population in the area. The Bakerwals inhabit the National Park along with their large herds of sheep, goats, cows and horses that graze along the forest edges and meadows through the summer (April–September).
Methods
Sampling design We conducted questionnaire-based interviews with select members of local communities and Bakerwals over a 2-year time period, during 2017–2019. The questionnaire (following Oli et al., 1994; Supplementary Material 1), com- prised three parts: (1) socio-demographic data (name, age, gender, occupation and community) and respondent knowledge of wildlife, (2) details regarding livestock depre- dation as well as the practices used to mitigate such preda- tion, and (3) data regarding people’s perceptions towards carnivores on a five-point Likert scale (strong like, slight like, indifferent, slight dislike and strong dislike). We approached the respondents and introduced ourselves as students conducting a study on human–wildlife inter- actions in the National Park and its surroundings. We included in the study only those individuals who could correctly identify the common leopard from a series of pictures of different wild animals. Before the start of each interview, we obtained informed verbal consent from each respondent and we kept their identity confidential. To faciliate communication with respondents in their local language, the interviewing team was often accompanied by local people who were knowledgeable about wildlife, and by staff from the local wildlife department. We con- ducted the interviews (lasting a mean of 6 min) in local languages including Kashmiri, Gojri and Urdu. We pro- vided no financial incentives or monetary benefits to the respondents who participated in the survey.
Data analysis
We used descriptive statistics to analyse data on livestock mortality and depredation patterns. We examined the rela- tionship between livestock holdings, predation control
practices and respondent attitudes towards these practices using Spearman’s correlation. We measured the predation control practices as ranks and considered the Likert score to be an ordinal variable. For each predation control practice, we computed the correlation coefficient and related P-value with livestock holdings and Likert score as dependent variables, whereby livestock holdings equalled animal counts. We used an ordinal logistic regression to determine the key factors (e.g. age, gender, occupation, region, activity duration and livestock holdings) that in- fluence the attitudes of people towards leopards. We per- formed all statistical and graphical analysis in R 4.1.1 (R Core Team, 2022). Wecarried out the regression analysis using the clm function in the ordinal package in R (Chris- tensen, 2022), and assessed the overall measure of model fit using the function anova. We calculated pseudo-R2 values to test the goodness of model fit using the function nagerkerke from the package rcompanion (Mangiafico, 2023). We calculated the statistical significance of the live- stock holdings for the groups of respondents who had and had not experienced livestock depredation using a Mann– Whitney U test after we had checked the samples for nor- mality using a Shapiro–Wilk test. We used a rank biserial correlation to calculate the effect size of the results using the function rank_biserial from the package effectsize (Ben-Shachar et al., 2020).
Results
Weinterviewed 102 respondents (98 men, 4 women) in vari- ous villages/locations in the Dachan and Marwah regions of the National Park. Most of the respondents (52%) were aged 46–65 years, with a mean age of 49.7 years (Table 1). The principal occupation of the majority of the respondents was livestock rearing (52%) followed by agriculture/small landholders (32%) and government employees (forest and wildlife officials; 10%), and 6% of respondents practiced mixed occupations. Most of the interviewees were long- time users of the Park, and the mean activity period of re- spondents (i.e. the number of years during which they had visited the Park regularly) was 30.5 years (Table 1). Many of the respondents (42%) had visited the Park on a regu- lar basis for more than 30 years, followed by those with ac- tivity periods of 21–30 years (25%) and 10–20 years (31%). Only two respondents (2%) had regularly accessed the Park for less than 10 years. Of the total 102 respondents, 68 reported mixed livestock
holdings comprising sheep, goat, cows, oxen and horses. Amongst these, 43 respondents reported livestock predation by leopards on 71 separate occasions over a span of 2 years (during 2017–2019). Participants from the Rinae valley reported the highest number of depredation cases (30), followed by those from the Kiyar (22), Kibber (15) and
Oryx, 2024, 58(2), 202–209 © The Author(s), 2023. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S0030605323001278
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