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Tracking the decline of the once‐common butterfly: delayed oviposition, demography and population genetics in the hermit Chazara briseis

Identifieur interne : 001A03 ( Istex/Corpus ); précédent : 001A02; suivant : 001A04

Tracking the decline of the once‐common butterfly: delayed oviposition, demography and population genetics in the hermit Chazara briseis

Auteurs : T. Kadlec ; P. Vrba ; P. Kepka ; T. Schmitt ; M. Konvicka

Source :

RBID : ISTEX:8BF3639C03E23D19C54F46189842B73E0999E4A4

English descriptors

Abstract

Large populations, seemingly not at risk of extinction, can decline rapidly due to alteration of habitat. This appears to be the case of the butterfly Chazara briseis, which is declining in all of Central and Eastern Europe, even from apparently large areas of its steppe grassland habitats. We combined mark–recapture, allozyme electrophoresis and adult behaviour observation to study the last remaining metapopulation of this once‐widespread butterfly in the Czech Republic. The total population estimate was 1300 males and 1050 females in 10 colonies within a 70 km2 landscape. Adults were long‐lived, and inseminated females required several weeks before they started ovipositing. Models using realistic lengths of the preoviposition period estimated that due to background mortality, only 25–55% of the female census population lived long enough to contribute to the next generation. This demographic load was unlikely to be balanced by an increased fecundity. Allozyme electrophoresis of 22 loci revealed much higher allelic variation than in most other studies of butterflies living in small populations (mean heterozygosity: 20.7%). If expressed as per individual colony, the genetic variation did not correlate with population density, survival or longevity. This was probably due to frequent movements among colonies; during 8 weeks of adult flight, 5.1% of recaptured males and 3.6% of recaptured females moved between colonies. The high preoviposition mortality indicates that populations of this species must contain more individuals compared with populations not suffering this additional demographic load. The high allelic diversity of each single colony suggests that the population as a whole has not undergone genetic bottlenecks, but now may be facing risks of inbreeding depression due to allele frequency shifts and the possible increase of weakly deleterious alleles. In the past, high effective population sizes were maintained by frequent dispersal in dense networks of steppic grasslands. Generous habitat restoration is necessary to safeguard populations of this specialized, yet formerly common species.

Url:
DOI: 10.1111/j.1469-1795.2009.00318.x

Links to Exploration step

ISTEX:8BF3639C03E23D19C54F46189842B73E0999E4A4

Le document en format XML

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Martin Konvicka, Institute of Entomology, Czech Academy of Sciences, Branisovska 31, CZ‐370 05, Ceske Budejovice, Czech Republic. Tel: +420 38 777 5312
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<b>Appendix S1.</b>
Electrophoresis conditions for 17 enzyme systems analysed representing 22 loci for
<i>Chazara briseis</i>
(in order of EC‐No.). TC: Tris‐citrate pH=8.2 (Richardson
<i>et al</i>
., 1986), TG: Tris‐glycine pH=8.5 (Hebert & Beaton, 1993), TM: Tris maleic acid pH=7.0 (adjusted from TM pH=7.8 (Richardson
<i>et al</i>
., 1986)). All buffers were run at 200 V.</p>
<p>
<b>Appendix S2.</b>
Allele frequencies of the 17 polymorphic allozyme loci in six
<i>Chazara briseis</i>
samples in the Ceske Stredohori, NW Czech Republic.</p>
<p>As a service to our authors and readers, this journal provides supporting information supplied by the authors. Such materials are peer‐reviewed and may be re‐organized for online delivery, but are not copy‐edited or typeset. Technical support issues arising from supporting information (other than missing files) should be addressed to the authors.</p>
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, which is declining in all of Central and Eastern Europe, even from apparently large areas of its steppe grassland habitats. We combined mark–recapture, allozyme electrophoresis and adult behaviour observation to study the last remaining metapopulation of this once‐widespread butterfly in the Czech Republic. The total population estimate was 1300 males and 1050 females in 10 colonies within a 70 km
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<name type="personal">
<namePart type="given">M.</namePart>
<namePart type="family">Konvicka</namePart>
<affiliation>Faculty of Science, University Southern Bohemia, Ceske Budejovice, Czech Republic</affiliation>
<affiliation>Institute of Entomology, Czech Academy of Sciences, Ceske Budejovice, Czech Republic</affiliation>
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<publisher>Blackwell Publishing Ltd</publisher>
<place>
<placeTerm type="text">Oxford, UK</placeTerm>
</place>
<dateIssued encoding="w3cdtf">2010-04</dateIssued>
<edition>Received 18 April 2009; accepted 11 September 2009</edition>
<copyrightDate encoding="w3cdtf">2010</copyrightDate>
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<languageTerm type="code" authority="rfc3066">en</languageTerm>
<languageTerm type="code" authority="iso639-2b">eng</languageTerm>
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<extent unit="figures">5</extent>
<extent unit="tables">4</extent>
<extent unit="formulas">5</extent>
<extent unit="references">75</extent>
<extent unit="words">9194</extent>
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<abstract lang="en">Large populations, seemingly not at risk of extinction, can decline rapidly due to alteration of habitat. This appears to be the case of the butterfly Chazara briseis, which is declining in all of Central and Eastern Europe, even from apparently large areas of its steppe grassland habitats. We combined mark–recapture, allozyme electrophoresis and adult behaviour observation to study the last remaining metapopulation of this once‐widespread butterfly in the Czech Republic. The total population estimate was 1300 males and 1050 females in 10 colonies within a 70 km2 landscape. Adults were long‐lived, and inseminated females required several weeks before they started ovipositing. Models using realistic lengths of the preoviposition period estimated that due to background mortality, only 25–55% of the female census population lived long enough to contribute to the next generation. This demographic load was unlikely to be balanced by an increased fecundity. Allozyme electrophoresis of 22 loci revealed much higher allelic variation than in most other studies of butterflies living in small populations (mean heterozygosity: 20.7%). If expressed as per individual colony, the genetic variation did not correlate with population density, survival or longevity. This was probably due to frequent movements among colonies; during 8 weeks of adult flight, 5.1% of recaptured males and 3.6% of recaptured females moved between colonies. The high preoviposition mortality indicates that populations of this species must contain more individuals compared with populations not suffering this additional demographic load. The high allelic diversity of each single colony suggests that the population as a whole has not undergone genetic bottlenecks, but now may be facing risks of inbreeding depression due to allele frequency shifts and the possible increase of weakly deleterious alleles. In the past, high effective population sizes were maintained by frequent dispersal in dense networks of steppic grasslands. Generous habitat restoration is necessary to safeguard populations of this specialized, yet formerly common species.</abstract>
<subject lang="en">
<genre>keywords</genre>
<topic>allozyme electrophoresis</topic>
<topic>Lepidoptera</topic>
<topic>mark–recapture</topic>
<topic>metapopulation</topic>
<topic>minimum viable population</topic>
<topic>reproductive effort</topic>
<topic>Satyrinae</topic>
</subject>
<relatedItem type="host">
<titleInfo>
<title>Animal Conservation</title>
</titleInfo>
<genre type="journal">journal</genre>
<note type="content"> Appendix S1. Electrophoresis conditions for 17 enzyme systems analysed representing 22 loci for Chazara briseis (in order of EC‐No.). TC: Tris‐citrate pH=8.2 (Richardson et al., 1986), TG: Tris‐glycine pH=8.5 (Hebert & Beaton, 1993), TM: Tris maleic acid pH=7.0 (adjusted from TM pH=7.8 (Richardson et al., 1986)). All buffers were run at 200 V. Appendix S2. Allele frequencies of the 17 polymorphic allozyme loci in six Chazara briseis samples in the Ceske Stredohori, NW Czech Republic. As a service to our authors and readers, this journal provides supporting information supplied by the authors. Such materials are peer‐reviewed and may be re‐organized for online delivery, but are not copy‐edited or typeset. Technical support issues arising from supporting information (other than missing files) should be addressed to the authors. Appendix S1. Electrophoresis conditions for 17 enzyme systems analysed representing 22 loci for Chazara briseis (in order of EC‐No.). TC: Tris‐citrate pH=8.2 (Richardson et al., 1986), TG: Tris‐glycine pH=8.5 (Hebert & Beaton, 1993), TM: Tris maleic acid pH=7.0 (adjusted from TM pH=7.8 (Richardson et al., 1986)). All buffers were run at 200 V. Appendix S2. Allele frequencies of the 17 polymorphic allozyme loci in six Chazara briseis samples in the Ceske Stredohori, NW Czech Republic. As a service to our authors and readers, this journal provides supporting information supplied by the authors. Such materials are peer‐reviewed and may be re‐organized for online delivery, but are not copy‐edited or typeset. Technical support issues arising from supporting information (other than missing files) should be addressed to the authors. Appendix S1. Electrophoresis conditions for 17 enzyme systems analysed representing 22 loci for Chazara briseis (in order of EC‐No.). TC: Tris‐citrate pH=8.2 (Richardson et al., 1986), TG: Tris‐glycine pH=8.5 (Hebert & Beaton, 1993), TM: Tris maleic acid pH=7.0 (adjusted from TM pH=7.8 (Richardson et al., 1986)). All buffers were run at 200 V. Appendix S2. Allele frequencies of the 17 polymorphic allozyme loci in six Chazara briseis samples in the Ceske Stredohori, NW Czech Republic. As a service to our authors and readers, this journal provides supporting information supplied by the authors. Such materials are peer‐reviewed and may be re‐organized for online delivery, but are not copy‐edited or typeset. Technical support issues arising from supporting information (other than missing files) should be addressed to the authors.Supporting Info Item: Supporting info item - </note>
<identifier type="ISSN">1367-9430</identifier>
<identifier type="eISSN">1469-1795</identifier>
<identifier type="DOI">10.1111/(ISSN)1469-1795</identifier>
<identifier type="PublisherID">ACV</identifier>
<part>
<date>2010</date>
<detail type="volume">
<caption>vol.</caption>
<number>13</number>
</detail>
<detail type="issue">
<caption>no.</caption>
<number>2</number>
</detail>
<extent unit="pages">
<start>172</start>
<end>183</end>
<total>12</total>
</extent>
</part>
</relatedItem>
<identifier type="istex">8BF3639C03E23D19C54F46189842B73E0999E4A4</identifier>
<identifier type="DOI">10.1111/j.1469-1795.2009.00318.x</identifier>
<identifier type="ArticleID">ACV318</identifier>
<accessCondition type="use and reproduction" contentType="copyright">© 2009 The Authors. Journal compilation © 2009 The Zoological Society of London</accessCondition>
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<recordContentSource>WILEY</recordContentSource>
<recordOrigin>Blackwell Publishing Ltd</recordOrigin>
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