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. 2021 Sep 21;11(20):13641–13660. doi: 10.1002/ece3.8105

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, Ψ^ (Global) = IO+R+N+PD+PS+WB+L+T

Model AIC ΔAIC w Model Likelihood K
Ψ^(Global) θ 0(·) θ 1(·) p(IO+N+L) θ 0 pi (·) 614.8 0 0.5317 1 31
Ψ^(Global) θ 0(·) θ 1(·) p(IO+N+L+R) θ 0 pi (·) 616.68 1.88 0.2077 0.3906 32
Ψ^(Global) θ 0(·) θ 1(·) p(IO+N+L+Samp_Eff) θ 0 pi (·) 616.79 1.99 0.1966 0.3697 32
Ψ^(Global) θ 0(·) θ 1(·) p(IO+N) θ 0 pi (·) 621.02 6.22 0.0237 0.0446 30
Ψ^(Global) θ 0(·) θ 1(·) p(IO+N+R) θ 0 pi (·) 622.55 7.75 0.011 0.0208 31
Ψ^(Global) θ 0(·) θ 1(·) p(IO+R) θ 0 pi (·) 622.77 7.97 0.0099 0.0186 30
Ψ^(Global) θ 0(·) θ 1(·) p(IO+N+Samp_Eff) θ 0 pi (·) 623.02 8.22 0.0087 0.0164 31
Ψ^(Global) θ 0(·) θ 1(·) p(IO+L) θ 0 pi (·) 623.68 8.88 0.0063 0.0118 30
Ψ^(Global) θ 0(·) θ 1(·) p(IO) θ 0 pi (·) 625.59 10.79 0.0024 0.0045 29
Ψ^(Global) θ 0(·) θ 1(·) p(IO+Samp_Eff) θ 0 pi (·) 625.94 11.14 0.002 0.0038 30
Ψ^(Global) θ 0(·) θ 1(·) p(R) θ 0 pi (·) 662.42 47.62 0 0 29
Ψ^(Global), θ 0(·) θ 1(·),p(L) θ 0 pi (·) 668.29 53.49 0 0 29
Ψ^(Global), θ 0(·) θ 1(·),p() θ 0 pi (·) 670.11 55.31 0 0 28
Ψ^(Global), θ 0(·) θ 1(·),p(N) θ 0 pi (·) 671.97 57.17 0 0 29
Ψ^(Global), θ 0(·) θ 1(·),p(Samp_EFF) θ 0 pi (·) 672.08 57.28 0 0 29
Ψ^, θ 0(·) θ 1(·),p() θ 0 pi (·) 676.43 61.63 0 0 20

Ψ^: 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.