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532 A. Uduman et al.


TABLE 2 Predictor variables included in regression models with their explanations and examples of survey questions used to infer variable data. The range of response values are given across both study sites. Survey section refers to the complete survey (SupplementaryMaterial 1).


Variable name


Reported depredation Socio-demographics


Cost


Knowledge of leopard ecology


General awareness of leopard tourism


Explanation & survey questions used to infer variable data1


EFA variable comprised of respondent age, number of dependants & time spent rearing cattle Monthly expenditure (LKR) on cattle


EFA variable comprised of respondents’ awareness of leopard-related tourism in Yala National Park & its economic value


Importance of conservation EFA variable comprised of respondents’ views on the conser- vation of Sri Lanka’s mammals, birds, reptiles & amphibians


Leopard sightings &/or signs Change in leopard sightings or signs over the last 3 years Worry


Government involvement 1EFA, exploratory factor analysis.


compared to the top-ranked model (the one with the lowest AICc) as plausible (Burnham & Anderson, 2002).


Results


Attitudes towards leopards Respondents in Palatupana had more negative attitudes to- wards leopards compared to those in Maskeliya (Table 1), most clearly evident by their level of agreement to attitude statements that pertained to cattle depredation and leopard populations. For example, 66%(40 of 61) of respondents in Palatupana indicated they would be happier if there were fewer leopards in the areas where they raised their cattle, compared to 12%(6 of 52) in Maskeliya (χ2 = 13.95, P,0.001). Similarly, 72%(44/61) of respondents in Palatupana strongly agreed they may have to kill leopards if these depredate their cattle, compared to 15%(8/52)in Maskeliya (χ2 = 13.15,P,0.001). Respondents in Palatupana strongly agreed that the na-


ture and wildlife of Sri Lanka are a national treasure and should be conserved (69%, 42 of 61), and that leopards should be respected for the economic value they bring to the country through wildlife tourism (51%, 31 of 61). This contrasted significantly with attitudes in Maskeliya (χ2 = 33.05,P,0.001 and χ2 = 27.78,P,0.001, respectively), where most respondents (c. 80%) gave neutral responses to these statements. The statement suggesting that respondents could tolerate the killing of a few of their cattle by leopards because the felids are wild animals trying to survive received a broad range of responses (indistinguishable from a


uniform distribution across the five categories: χ2 = 5.91, P= 0.206) from respondents in Palatupana, whereas the majority (77%, 40 of 52) of those in Maskeliya strongly disagreed. These differences in response distributions were highly significant (Fisher’sexact test:P,0.001). Supplementary Tables 1 and 2 provide full details of re- sponses to attitude statements in both communities.


Determinants of attitudes towards leopards


We found that determinants of attitudes towards leopards differed between the two study sites. There was no reported livestock depredation in Maskeliya, whereas 93% of respon- dents in Palatupana reported depredation. Variables includ- ed in the top model for Palatupana included respondents’ knowledge of leopard ecology, awareness of leopard tourism, opinions on the importance of conservation, and socio- demographics (Table 3). Parameter estimates were similar across models close to the top model (ΔAICc#2). Re- spondents who thought that the presence of leopards in the buffer zones of protected areas would increase encounters between leopards and cattle had more negative attitudes


(−3.41; 95%CI −5.77, −0.95;P = 0.008). Similarly, respon- dents who were more aware of leopard tourism had more


negative attitudes (−0.38; 95%CI −0.65, −0.11;P = 0.009). Respondents who thought that wildlife conservation in gen- eral was important had more positive attitudes (0.15; 95%CI 0.10, 0.21;P,0.001), as did those with high scores in the


socio-demographics metric (0.04; 95%CI −0.01, 0.10; P=0.09). The adjusted proportion of deviance accounted for by the top model was 46%. Models with ΔAICc#2 (compared to the top model) are presented in Table 3.


Oryx, 2022, 56(4), 528–536 © The Author(s), 2021. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S0030605321000247


Concerns of respondents about their own safety or that of their cattle after seeing a leopard


Desire for increased government involvement to facilitate an improvement in cattle rearing (e.g. vaccines or land leases)


Range


Variable type


Survey section


Proportion of cattle reported to have been killed by leopards 0.0–0.5 Continuous 4 1.1–10.0 Continuous 1


10,000– 100,000


EFA variable comprised of respondents’ knowledge of leopard endangerment, general movement & prey species


Continuous 3


1.5–10.0 Continuous 6 1.0–10.0 Continuous 6


1.0–10.0 Continuous 5 1–7


0–1 0–1


Continuous 4 Categorical 4


Categorical 4


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