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The dispersion and detection patterns of mtDNA‐assigned red fox Vulpes vulpes scats in Tasmania are anomalous

1. Models used for resource allocation in eradication programmes must be based on replicated data of known quality and have proven predictive accuracy, or they may provide a false indication of species presence and/or distribution. In the absence of data corroborating the presence of extant foxes Vu...

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Autores principales: Marks, Clive A, Obendorf, David, Pereira, Filipe, Edwards, Ivo, Hall, Graham P
Formato: Online Artículo Texto
Lenguaje:English
Publicado: John Wiley and Sons Inc. 2014
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC4301185/
https://www.ncbi.nlm.nih.gov/pubmed/25641979
http://dx.doi.org/10.1111/1365-2664.12278
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author Marks, Clive A
Obendorf, David
Pereira, Filipe
Edwards, Ivo
Hall, Graham P
author_facet Marks, Clive A
Obendorf, David
Pereira, Filipe
Edwards, Ivo
Hall, Graham P
author_sort Marks, Clive A
collection PubMed
description 1. Models used for resource allocation in eradication programmes must be based on replicated data of known quality and have proven predictive accuracy, or they may provide a false indication of species presence and/or distribution. In the absence of data corroborating the presence of extant foxes Vulpes vulpes in Tasmania, a habitat‐specific model based upon mtDNA data (Sarre et al. 2012. Journal Applied Ecology, 50, 459–468) implied that foxes were widespread. Overall, 61 of 9940 (0·6%) surveyed scats were assigned as mtDNA fox positive by the fox eradication programme (FEP). 2. We investigated the spatiotemporal distribution of the 61 mtDNA‐assigned fox scats and modelled the probability of replicating scat detection in independent surveys using detection dogs based upon empirically derived probabilities of scat detection success obtained by the FEP using imported fox scats. 3. In a prior mainland study, fox genotypes were recurrently detected in a consecutive four‐day pool of scats. In Tasmania, only three contemporaneously collected scat pairs of unknown genotype were detected by the FEP within an area corresponding to a conservatively large mainland fox home range (639 ha) in a decade. Nearest neighbour pairs were widely spaced (mean = 7·0 km; circular area = 153 km(2)) and generated after a mean of 281 days. 4. The majority of assigned mtDNA positive scats were found in urban and peri‐urban environments corresponding to small mainland fox home ranges (30–45 ha) that imply higher scat density and more certain replication. Using the lowest empirically determined scat detection success for dogs, the failure to replicate fox scat detection on 34 of 36 occasions in a large (639 ha) home range is highly improbable (P = 0·00001) and suggestive of Type I error. 5. Synthesis and applications. Type I error, which may have various sources, should be considered when scat mtDNA data are few, accumulated over many years, uncorroborated by observations of extant specimens, inadequately replicated in independent surveys within an expected spatiotemporal scale and reported in geographically isolated environments unlikely to have been colonized.
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spelling pubmed-43011852015-01-28 The dispersion and detection patterns of mtDNA‐assigned red fox Vulpes vulpes scats in Tasmania are anomalous Marks, Clive A Obendorf, David Pereira, Filipe Edwards, Ivo Hall, Graham P J Appl Ecol Detection and Management of Invasives 1. Models used for resource allocation in eradication programmes must be based on replicated data of known quality and have proven predictive accuracy, or they may provide a false indication of species presence and/or distribution. In the absence of data corroborating the presence of extant foxes Vulpes vulpes in Tasmania, a habitat‐specific model based upon mtDNA data (Sarre et al. 2012. Journal Applied Ecology, 50, 459–468) implied that foxes were widespread. Overall, 61 of 9940 (0·6%) surveyed scats were assigned as mtDNA fox positive by the fox eradication programme (FEP). 2. We investigated the spatiotemporal distribution of the 61 mtDNA‐assigned fox scats and modelled the probability of replicating scat detection in independent surveys using detection dogs based upon empirically derived probabilities of scat detection success obtained by the FEP using imported fox scats. 3. In a prior mainland study, fox genotypes were recurrently detected in a consecutive four‐day pool of scats. In Tasmania, only three contemporaneously collected scat pairs of unknown genotype were detected by the FEP within an area corresponding to a conservatively large mainland fox home range (639 ha) in a decade. Nearest neighbour pairs were widely spaced (mean = 7·0 km; circular area = 153 km(2)) and generated after a mean of 281 days. 4. The majority of assigned mtDNA positive scats were found in urban and peri‐urban environments corresponding to small mainland fox home ranges (30–45 ha) that imply higher scat density and more certain replication. Using the lowest empirically determined scat detection success for dogs, the failure to replicate fox scat detection on 34 of 36 occasions in a large (639 ha) home range is highly improbable (P = 0·00001) and suggestive of Type I error. 5. Synthesis and applications. Type I error, which may have various sources, should be considered when scat mtDNA data are few, accumulated over many years, uncorroborated by observations of extant specimens, inadequately replicated in independent surveys within an expected spatiotemporal scale and reported in geographically isolated environments unlikely to have been colonized. John Wiley and Sons Inc. 2014-08 2014-06-06 /pmc/articles/PMC4301185/ /pubmed/25641979 http://dx.doi.org/10.1111/1365-2664.12278 Text en © 2014 The Authors. Journal of Applied Ecology published by John Wiley & Sons Ltd on behalf of British Ecological Society. This is an open access article under the terms of the http://creativecommons.org/licenses/by-nc-nd/3.0/ License, which permits use and distribution in any medium, provided the original work is properly cited, the use is non‐commercial and no modifications or adaptations are made.
spellingShingle Detection and Management of Invasives
Marks, Clive A
Obendorf, David
Pereira, Filipe
Edwards, Ivo
Hall, Graham P
The dispersion and detection patterns of mtDNA‐assigned red fox Vulpes vulpes scats in Tasmania are anomalous
title The dispersion and detection patterns of mtDNA‐assigned red fox Vulpes vulpes scats in Tasmania are anomalous
title_full The dispersion and detection patterns of mtDNA‐assigned red fox Vulpes vulpes scats in Tasmania are anomalous
title_fullStr The dispersion and detection patterns of mtDNA‐assigned red fox Vulpes vulpes scats in Tasmania are anomalous
title_full_unstemmed The dispersion and detection patterns of mtDNA‐assigned red fox Vulpes vulpes scats in Tasmania are anomalous
title_short The dispersion and detection patterns of mtDNA‐assigned red fox Vulpes vulpes scats in Tasmania are anomalous
title_sort dispersion and detection patterns of mtdna‐assigned red fox vulpes vulpes scats in tasmania are anomalous
topic Detection and Management of Invasives
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC4301185/
https://www.ncbi.nlm.nih.gov/pubmed/25641979
http://dx.doi.org/10.1111/1365-2664.12278
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