Role of covariates in determining detection probability of leopard sign (Pt) on 2‐km‐long replicates of west Chure, based on covariates for probability of occurrence of leopard from the global model, (Global) = IO+R+N+PD+PS+WB+L+T
| Model | AIC | ΔAIC | w | Model Likelihood | K | 
|---|---|---|---|---|---|
| (Global) θ 0(·) θ 1(·) p(IO+N+L) θ 0 pi (·) | 614.8 | 0 | 0.5317 | 1 | 31 | 
| (Global) θ 0(·) θ 1(·) p(IO+N+L+R) θ 0 pi (·) | 616.68 | 1.88 | 0.2077 | 0.3906 | 32 | 
| (Global) θ 0(·) θ 1(·) p(IO+N+L+Samp_Eff) θ 0 pi (·) | 616.79 | 1.99 | 0.1966 | 0.3697 | 32 | 
| (Global) θ 0(·) θ 1(·) p(IO+N) θ 0 pi (·) | 621.02 | 6.22 | 0.0237 | 0.0446 | 30 | 
| (Global) θ 0(·) θ 1(·) p(IO+N+R) θ 0 pi (·) | 622.55 | 7.75 | 0.011 | 0.0208 | 31 | 
| (Global) θ 0(·) θ 1(·) p(IO+R) θ 0 pi (·) | 622.77 | 7.97 | 0.0099 | 0.0186 | 30 | 
| (Global) θ 0(·) θ 1(·) p(IO+N+Samp_Eff) θ 0 pi (·) | 623.02 | 8.22 | 0.0087 | 0.0164 | 31 | 
| (Global) θ 0(·) θ 1(·) p(IO+L) θ 0 pi (·) | 623.68 | 8.88 | 0.0063 | 0.0118 | 30 | 
| (Global) θ 0(·) θ 1(·) p(IO) θ 0 pi (·) | 625.59 | 10.79 | 0.0024 | 0.0045 | 29 | 
| (Global) θ 0(·) θ 1(·) p(IO+Samp_Eff) θ 0 pi (·) | 625.94 | 11.14 | 0.002 | 0.0038 | 30 | 
| (Global) θ 0(·) θ 1(·) p(R) θ 0 pi (·) | 662.42 | 47.62 | 0 | 0 | 29 | 
| (Global), θ 0(·) θ 1(·),p(L) θ 0 pi (·) | 668.29 | 53.49 | 0 | 0 | 29 | 
| (Global), θ 0(·) θ 1(·),p() θ 0 pi (·) | 670.11 | 55.31 | 0 | 0 | 28 | 
| (Global), θ 0(·) θ 1(·),p(N) θ 0 pi (·) | 671.97 | 57.17 | 0 | 0 | 29 | 
| (Global), θ 0(·) θ 1(·),p(Samp_EFF) θ 0 pi (·) | 672.08 | 57.28 | 0 | 0 | 29 | 
| , θ 0(·) θ 1(·),p() θ 0 pi (·) | 676.43 | 61.63 | 0 | 0 | 20 | 
: model‐averaged leopard occupancy; p = replicate‐level detectability; AIC = Akaike's information criterion, ΔAIC = difference in AIC value between the top model and the focal model; w = AIC weight; Model likelihood is −2 logarithm of the likelihood function evaluated at maximum; θ 0 = Pr (leopard presence in a replicate/grid occupied and which was absent in the previous replicate) and “θ 1” = Pr (leopard presence in a replicate/grid occupied and was present in the previous replicate); k = number of model parameters; Covariates: IO: management regime (grids inside and outside of the protected areas); R = terrain ruggedness averaged across each grid; N = nondifferent vegetative index averaged across each grid; PD = averaged human population density in each grid; PS = prey species (rhesus, barking deer, chital); WB = wild boar; L = livestock presence; Samp_Eff = sampling effort; T = tiger; + = covariates modeled additively; (·) = parameters are held constant. β‐coefficient estimates for IO, N, L = −4.97 (SE 1.34), −1.46(SE 0.47), 1.327 (SE 0.49), respectively.