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Methods of monitoring red foxes Vulpes vulpes and badgers Meles meles: are field signs the answer?

Identifieur interne : 000A51 ( Istex/Corpus ); précédent : 000A50; suivant : 000A52

Methods of monitoring red foxes Vulpes vulpes and badgers Meles meles: are field signs the answer?

Auteurs : Linda M. J. Sadlier ; Charlotte C. Webbon ; Philip J. Baker ; Stephen Harris

Source :

RBID : ISTEX:F3339F0C44A0CFC6D076C54A14CE89E69592EFB1

English descriptors

Abstract

1. A national monitoring scheme for recording the abundance of foxes and badgers in Britain would have to utilize a technique or techniques that could detect a wide range of animal densities in structurally different habitats. Furthermore, the likely reliance on volunteers for data collection means that these techniques must be easily applied by people with different levles of field expertise.

Url:
DOI: 10.1046/j.0305-1838.2003.00029.x

Links to Exploration step

ISTEX:F3339F0C44A0CFC6D076C54A14CE89E69592EFB1

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 A national monitoring scheme for recording the abundance of foxes and badgers in Britain would have to utilize a technique or techniques that could detect a wide range of animal densities in structurally different habitats. Furthermore, the likely reliance on volunteers for data collection means that these techniques must be easily applied by people with different levles of field expertise.</p>
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<b>2.</b>
 Direct methods that rely on counts of the animals themselves (e.g. capture‐mark‐recapture, radio‐tracking, spotlight counts) are generally unsuitable because of cost, manpower and licensing requirements, are not readily applied to all habitats and cannot easily be used by volunteers. However, density estimates derived from capture‐mark‐recapture and radio‐tracking methods are likely to represent the benchmark against which other estimates of abundance are measured.</p>
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<b>3.</b>
 The number of foxes killed per unit area is currently collated by non‐governmental organisations for some patterns of land use, e.g. game estates. No such data are available for badgers, as this species is legally protected in Britain. However, the applicability of hunting statistics for monitoring fox abundance is limited by differences in culling effort, the non‐independence of different culling practices applied in the same region, possible future changes in the legal status of different culling methods and changes in the ratio of land where foxes are and are not culled.</p>
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<b>4.</b>
 Indirect methods that rely on counts of the signs of the animals (e.g. droppings, breeding refugia) are less expensive than direct methods, can be applied to the range of habitats found in Britain and can easily be used by volunteers. To date, indirect methods have been utilised to derive estimates of relative animal density or the density of social groups. However, the major factor currently limiting the use of indirect methods is that their relationship with absolute animal density has not been validated. The preliminary results of two projects quantifying the use of field signs as a measure of absolute fox and badger abundance suggest that indirect methods could be applicable for monitoring changes in fox and badger numbers at a national scale.</p>
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<affiliation>School of Biological Sciences, University of Bristol, Woodland Road, Bristol BS8 1UG, UK</affiliation>
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<namePart type="given">PHILIP J.</namePart>
<namePart type="family">BAKER</namePart>
<affiliation>School of Biological Sciences, University of Bristol, Woodland Road, Bristol BS8 1UG, UK</affiliation>
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<name type="personal">
<namePart type="given">STEPHEN</namePart>
<namePart type="family">HARRIS</namePart>
<affiliation>School of Biological Sciences, University of Bristol, Woodland Road, Bristol BS8 1UG, UK</affiliation>
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<publisher>Blackwell Science Ltd</publisher>
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<placeTerm type="text">Oxford, UK</placeTerm>
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<dateIssued encoding="w3cdtf">2004-01</dateIssued>
<edition>Submitted 15 August 2002; returned for revision 17 February 2003; revision accepted 26 April 2003 Editor: DY</edition>
<copyrightDate encoding="w3cdtf">2004</copyrightDate>
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<languageTerm type="code" authority="rfc3066">en</languageTerm>
<languageTerm type="code" authority="iso639-2b">eng</languageTerm>
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<abstract>1. A national monitoring scheme for recording the abundance of foxes and badgers in Britain would have to utilize a technique or techniques that could detect a wide range of animal densities in structurally different habitats. Furthermore, the likely reliance on volunteers for data collection means that these techniques must be easily applied by people with different levles of field expertise.</abstract>
<abstract>2. Direct methods that rely on counts of the animals themselves (e.g. capture‐mark‐recapture, radio‐tracking, spotlight counts) are generally unsuitable because of cost, manpower and licensing requirements, are not readily applied to all habitats and cannot easily be used by volunteers. However, density estimates derived from capture‐mark‐recapture and radio‐tracking methods are likely to represent the benchmark against which other estimates of abundance are measured.</abstract>
<abstract>3. The number of foxes killed per unit area is currently collated by non‐governmental organisations for some patterns of land use, e.g. game estates. No such data are available for badgers, as this species is legally protected in Britain. However, the applicability of hunting statistics for monitoring fox abundance is limited by differences in culling effort, the non‐independence of different culling practices applied in the same region, possible future changes in the legal status of different culling methods and changes in the ratio of land where foxes are and are not culled.</abstract>
<abstract>4. Indirect methods that rely on counts of the signs of the animals (e.g. droppings, breeding refugia) are less expensive than direct methods, can be applied to the range of habitats found in Britain and can easily be used by volunteers. To date, indirect methods have been utilised to derive estimates of relative animal density or the density of social groups. However, the major factor currently limiting the use of indirect methods is that their relationship with absolute animal density has not been validated. The preliminary results of two projects quantifying the use of field signs as a measure of absolute fox and badger abundance suggest that indirect methods could be applicable for monitoring changes in fox and badger numbers at a national scale.</abstract>
<subject lang="en">
<genre>keywords</genre>
<topic>badger</topic>
<topic>fox</topic>
<topic>monitoring</topic>
<topic>sign surveys</topic>
</subject>
<relatedItem type="host">
<titleInfo>
<title>Mammal Review</title>
</titleInfo>
<genre type="journal">journal</genre>
<identifier type="ISSN">0305-1838</identifier>
<identifier type="eISSN">1365-2907</identifier>
<identifier type="DOI">10.1111/(ISSN)1365-2907</identifier>
<identifier type="PublisherID">MAM</identifier>
<part>
<date>2004</date>
<detail type="volume">
<caption>vol.</caption>
<number>34</number>
</detail>
<detail type="issue">
<caption>no.</caption>
<number>1‐2</number>
</detail>
<extent unit="pages">
<start>75</start>
<end>98</end>
<total>25</total>
</extent>
</part>
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<identifier type="istex">F3339F0C44A0CFC6D076C54A14CE89E69592EFB1</identifier>
<identifier type="DOI">10.1046/j.0305-1838.2003.00029.x</identifier>
<identifier type="ArticleID">MAM29</identifier>
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<recordContentSource>WILEY</recordContentSource>
<recordOrigin>Blackwell Science Ltd</recordOrigin>
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