2021
DOI: 10.1016/j.ecolind.2021.108170
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Bias in estimated breeding-bird abundance from closure-assumption violations

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Cited by 13 publications
(25 citation statements)
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“…The MNCM, such as the related N-mixture model (Royle, 2004) and MRCM (Sutherland et al, 2016), implicitly assumes all sites are closed to movement during the survey window. The mobility of birds and previous analyses suggest that our data violate the closure assumption (Fogarty & Fleishman, 2021). However, if the closure assumption is relaxed, these models can accurately estimate superpopulation abundance, and covariate estimates in N-mixture models are robust to large and realistic amounts of within-survey movement (Fogarty & Fleishman, 2021).…”
Section: Multiple-region Mncmsmentioning
confidence: 72%
“…The MNCM, such as the related N-mixture model (Royle, 2004) and MRCM (Sutherland et al, 2016), implicitly assumes all sites are closed to movement during the survey window. The mobility of birds and previous analyses suggest that our data violate the closure assumption (Fogarty & Fleishman, 2021). However, if the closure assumption is relaxed, these models can accurately estimate superpopulation abundance, and covariate estimates in N-mixture models are robust to large and realistic amounts of within-survey movement (Fogarty & Fleishman, 2021).…”
Section: Multiple-region Mncmsmentioning
confidence: 72%
“…One advantage of using remotely sensed tagging data for analyses with the MSORD-SU model is that there is minimized negative bias in the derived phenological parameters [ 32 ]. Since detection of previously tagged birds in the study area is high ( ρ = 0.57 : 0.84) [ 56 ], low tagging effort is not expected to strongly influence arrival estimates. However, because our primary and secondary sampling periods are configured over a contiguous temporal range, mortality during secondary sampling periods is a source of negative bias in estimates of both and ρ [ 32 ].…”
Section: Discussionmentioning
confidence: 99%
“…Given the presence of bias in λ , the use of HMs for inferring the site use frequency λ use could be an alternative that provides reliable answers to many wildlife related questions. Site use frequency is effectively a product of population size and HRA, hence reflects both the true number of animals present N , as well as their movement pattern (Chandler et al, 2011; Nakashima, 2020; Fogarty and Fleishman, 2021). Our results suggest that HMs do not necessarily estimate λ use more accurately than λ .…”
Section: Discussionmentioning
confidence: 99%
“…There have been several studies that assess the performance of HMs under the violation of these assumptions (i-iv). While few authors have focused on the BernP so far, the BP model has been evaluated in more depth: Fogarty and Fleishman (2021) show that even small violations of the closure assumption lead to substantial bias in abundance estimated from BP. Moreover, accidental double counting of individuals, which can be viewed as false positive detections, resulted in strong positive biases in this model (Link et al, 2018).…”
Section: Introductionmentioning
confidence: 99%
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