Abstract

BackgroundThe reliability of long-term population estimates is crucial for conservation and management purposes. Most previous studies assume that count indices are proportionally related to abundance; however, this assumption may not hold when detection varies spatially and temporally. We examined seasonal variations in abundance of three bird species (Cabot’s Tragopan Tragopan caboti, Silver Pheasant Lophura nycthemera, and White-necklaced Partridge Arborophila gingica) along an elevational gradient, using N-mixture models that take into account imperfect detection in our bird data.MethodsCamera-trapping was used to monitor temporal activity patterns of these species at Guangdong Nanling National Nature Reserve from December 2013 to November 2017 (4 seasons per year). For abundance analysis (N-mixture modeling), we divided a year into 4 seasons, i.e. 3 months per season, and performed the analysis by season. Elevation was incorporated into the N-mixture model as a covariate that may affect abundance. We compared the N-mixture model with a null model (no covariate model) and selected the better model based on AIC values to make an inference.ResultsFrom 24 sampling sites, we obtained 6786 photographs of 8482 individuals of 44 bird species and 26 mammal species. Silver Pheasant was photographed much more frequently and showed higher temporal activity frequency than White-necklaced Partridge or Cabot’s Tragopan. Silver Pheasant was camera-captured most frequently in summer, and other two species in winters. All three species had two daytime activity peaks: between 6:00 a.m. and 10:00 a.m., and between 5:00 p.m. and 7:00 p.m., respectively. Our estimated abundance and detection probability from the N-mixture model were variable by season. In particular, all three species showed greater abundance in summer than in winter, and estimated abundance patterns of all three species were more similar with observed camera-trapping counts in summers. Moreover, in winter, elevation had a positive impact on abundance of Silver Pheasant and Cabot’s Tragopan, but not on White-necklaced Partridge.ConclusionsOur results demonstrate that the N-mixture model performed well in the estimation of temporal population abundance at local fixed permanent plots in mountain habitat in southern China, based on the modeling of repeated camera-trapping counts. The seasonal differences in abundance of the three endemic bird species and the strong effect of elevation on abundance of two species in winter were only indicative of variations in spatio-temporal distribution within species and between species. In identifying suitable habitat for endemic pheasants, the positive elevational effect also suggests that more attention should be paid to conservation of areas with higher elevation in the Nanling Mountains.

Highlights

  • The reliability of long-term population estimates is crucial for conservation and management pur‐ poses

  • Zou et al Avian Res (2019) 10:42 strong effect of elevation on abundance of two species in winter were only indicative of variations in spatio-temporal distribution within species and between species

  • In identifying suitable habitat for endemic pheasants, the positive elevational effect suggests that more attention should be paid to conservation of areas with higher elevation in the Nanling Mountains

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Summary

Introduction

The reliability of long-term population estimates is crucial for conservation and management pur‐ poses. Reliable long-term count data are crucial for conservation status assessment and spatio-temporal prediction of bird abundance or population size (Chandler et al 2009; Jakob et al 2014) This is true for Galliformes species in China (e.g. partridges, pheasants, grouses) for which abundance estimates are essential for assessing degrees of threat, determining the species’ conservation status (Lu 1991) and designing appropriate conservation strategies (Zhang et al 2003). Most monitoring programs for estimating endemic species population sizes assume that count indices are proportionally related to abundance (Carbone et al 2001; Rovero and Marshall 2009) These data are rarely exhaustive and can only be regarded as an index of true abundance, rather than as abundance per se. Pheasant population management policies require intensive sampling efforts and accurate estimating models, rather than mark–recapture or distance sampling

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