Effects of coupled natural and anthropogenic factors on the community structure of diadromous fish and shrimp species in tropical island streams
Identifieur interne : 001069 ( Istex/Corpus ); précédent : 001068; suivant : 001070Effects of coupled natural and anthropogenic factors on the community structure of diadromous fish and shrimp species in tropical island streams
Auteurs : Catherine L. Hein ; Andrew S. Pike ; Juan F. Blanco ; Alan P. Covich ; Frederick N. Scatena ; Charles P. Hawkins ; Todd A. CrowlSource :
- Freshwater Biology [ 0046-5070 ] ; 2011-05.
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- KwdEn :
Abstract
1. Overlapping river and road networks provide a framework for studying the complex interactions between natural and human systems, with river‐road intersections as focal areas of study. Roads can alter the morphology of stream channels, pose barriers to freshwater fauna, provide easy access to streams for humans and non‐native species and accelerate the expansion of urban development. 2. We determined what variables control the structure of diadromous fish and shrimp communities and assessed whether particular road crossings altered community structure in north‐eastern Puerto Rico. We identified 24 sites that represented a range of river and road sizes across two catchments that drain El Yunque National Forest in Puerto Rico. 3. The location of natural barriers and the size of stream pools were the most important variables for predicting six of fifteen fish and shrimp distributions. Predatory fishes were predicted to be limited to areas in the river network below large, steep waterfalls, whereas adult shrimp Atya lanipes (Atyidae) were predicted to be present above these waterfalls. The fish Awaous banana was predicted to be present in pools >11.6 m wide, whereas the shrimp Xiphocaris elongata was predicted to be present in pools <10.4 m wide. The distributions of nine species were predicted poorly, but three of these species were common and three were rare. 4. Although urban and agricultural land covers were among the top three predictors of five species distributions, they were probably good predictors because they were correlated with the natural gradient. Further study is necessary to disentangle natural and anthropogenic gradients. 5. Road crossings, 10 of which were culverts, were not dispersal barriers for fishes or shrimps. On average, species were present both upstream and downstream from road crossings at 68% of sites where they occurred. Absences upstream or downstream from road crossings occurred at 16% of sites each and likely resulted from a failure to detect species. 6. Several existing features of these catchments and taxa may aid in fish and shrimp conservation. The headwaters are protected by management practices of El Yunque National Forest, connectivity within the river network has been maintained, and the diadromous life history of these organisms makes them resilient to pulsed disturbances.
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DOI: 10.1111/j.1365-2427.2010.02537.x
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Overlapping river and road networks provide a framework for studying the complex interactions between natural and human systems, with river‐road intersections as focal areas of study. Roads can alter the morphology of stream channels, pose barriers to freshwater fauna, provide easy access to streams for humans and non‐native species and accelerate the expansion of urban development. 2. We determined what variables control the structure of diadromous fish and shrimp communities and assessed whether particular road crossings altered community structure in north‐eastern Puerto Rico. We identified 24 sites that represented a range of river and road sizes across two catchments that drain El Yunque National Forest in Puerto Rico. 3. The location of natural barriers and the size of stream pools were the most important variables for predicting six of fifteen fish and shrimp distributions. Predatory fishes were predicted to be limited to areas in the river network below large, steep waterfalls, whereas adult shrimp Atya lanipes (Atyidae) were predicted to be present above these waterfalls. The fish Awaous banana was predicted to be present in pools >11.6 m wide, whereas the shrimp Xiphocaris elongata was predicted to be present in pools <10.4 m wide. The distributions of nine species were predicted poorly, but three of these species were common and three were rare. 4. Although urban and agricultural land covers were among the top three predictors of five species distributions, they were probably good predictors because they were correlated with the natural gradient. Further study is necessary to disentangle natural and anthropogenic gradients. 5. Road crossings, 10 of which were culverts, were not dispersal barriers for fishes or shrimps. On average, species were present both upstream and downstream from road crossings at 68% of sites where they occurred. Absences upstream or downstream from road crossings occurred at 16% of sites each and likely resulted from a failure to detect species. 6. Several existing features of these catchments and taxa may aid in fish and shrimp conservation. The headwaters are protected by management practices of El Yunque National Forest, connectivity within the river network has been maintained, and the diadromous life history of these organisms makes them resilient to pulsed disturbances.</div></front></TEI><istex><corpusName>wiley</corpusName><author><json:item><name>CATHERINE L. HEIN</name><affiliations><json:string>Department of Watershed Sciences and Ecology Center, Utah State University, Logan, UT, U.S.A.</json:string></affiliations></json:item><json:item><name>ANDREW S. PIKE</name><affiliations><json:string>Department of Earth & Environmental Science, University of Pennsylvania, Philadelphia, PA, U.S.A.</json:string></affiliations></json:item><json:item><name>JUAN F. 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Overlapping river and road networks provide a framework for studying the complex interactions between natural and human systems, with river‐road intersections as focal areas of study. Roads can alter the morphology of stream channels, pose barriers to freshwater fauna, provide easy access to streams for humans and non‐native species and accelerate the expansion of urban development. 2. We determined what variables control the structure of diadromous fish and shrimp communities and assessed whether particular road crossings altered community structure in north‐eastern Puerto Rico. We identified 24 sites that represented a range of river and road sizes across two catchments that drain El Yunque National Forest in Puerto Rico. 3. The location of natural barriers and the size of stream pools were the most important variables for predicting six of fifteen fish and shrimp distributions. Predatory fishes were predicted to be limited to areas in the river network below large, steep waterfalls, whereas adult shrimp Atya lanipes (Atyidae) were predicted to be present above these waterfalls. The fish Awaous banana was predicted to be present in pools >11.6 m wide, whereas the shrimp Xiphocaris elongata was predicted to be present in pools >10.4 m wide. The distributions of nine species were predicted poorly, but three of these species were common and three were rare. 4. Although urban and agricultural land covers were among the top three predictors of five species distributions, they were probably good predictors because they were correlated with the natural gradient. Further study is necessary to disentangle natural and anthropogenic gradients. 5. Road crossings, 10 of which were culverts, were not dispersal barriers for fishes or shrimps. On average, species were present both upstream and downstream from road crossings at 68% of sites where they occurred. Absences upstream or downstream from road crossings occurred at 16% of sites each and likely resulted from a failure to detect species. 6. Several existing features of these catchments and taxa may aid in fish and shrimp conservation. 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Santa Cruz, CA 95060, U.S.A.</note><affiliation>Present address: National Marine Fisheries Service, Southwest Fisheries Science Center, 110 Shaffer Road, Santa Cruz, CA 95060, U.S.A.</affiliation><affiliation>Department of Earth & Environmental Science, University of Pennsylvania, Philadelphia, PA, U.S.A.</affiliation></author><author xml:id="author-3"><persName><forename type="first">JUAN F.</forename><surname>BLANCO</surname></persName><affiliation>Instituto de Biología, Universidad de Antioquia, Ciudad Universitaria, Medellín, Colombia, South America</affiliation></author><author xml:id="author-4"><persName><forename type="first">ALAN P.</forename><surname>COVICH</surname></persName><affiliation>Institute of Ecology, Odum School of Ecology, University of Georgia, Athens, GA, U.S.A.</affiliation></author><author xml:id="author-5"><persName><forename type="first">FREDERICK N.</forename><surname>SCATENA</surname></persName><affiliation>Department of Earth & Environmental Science, University of Pennsylvania, Philadelphia, PA, U.S.A.</affiliation></author><author xml:id="author-6"><persName><forename type="first">CHARLES P.</forename><surname>HAWKINS</surname></persName><affiliation>Department of Watershed Sciences and Ecology Center, Utah State University, Logan, UT, U.S.A.</affiliation></author><author xml:id="author-7"><persName><forename type="first">TODD A.</forename><surname>CROWL</surname></persName><note type="biography">Present address: National Science Foundation, Division of Environmental Biology, Arlington, VA 22230, U.S.A.</note><affiliation>Present address: National Science Foundation, Division of Environmental Biology, Arlington, VA 22230, U.S.A.</affiliation><affiliation>Department of Watershed Sciences and Ecology Center, Utah State University, Logan, UT, U.S.A.</affiliation></author></analytic><monogr><title level="j">Freshwater Biology</title><idno type="pISSN">0046-5070</idno><idno type="eISSN">1365-2427</idno><idno 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Overlapping river and road networks provide a framework for studying the complex interactions between natural and human systems, with river‐road intersections as focal areas of study. Roads can alter the morphology of stream channels, pose barriers to freshwater fauna, provide easy access to streams for humans and non‐native species and accelerate the expansion of urban development. 2. We determined what variables control the structure of diadromous fish and shrimp communities and assessed whether particular road crossings altered community structure in north‐eastern Puerto Rico. We identified 24 sites that represented a range of river and road sizes across two catchments that drain El Yunque National Forest in Puerto Rico. 3. The location of natural barriers and the size of stream pools were the most important variables for predicting six of fifteen fish and shrimp distributions. Predatory fishes were predicted to be limited to areas in the river network below large, steep waterfalls, whereas adult shrimp Atya lanipes (Atyidae) were predicted to be present above these waterfalls. The fish Awaous banana was predicted to be present in pools >11.6 m wide, whereas the shrimp Xiphocaris elongata was predicted to be present in pools <10.4 m wide. The distributions of nine species were predicted poorly, but three of these species were common and three were rare. 4. Although urban and agricultural land covers were among the top three predictors of five species distributions, they were probably good predictors because they were correlated with the natural gradient. Further study is necessary to disentangle natural and anthropogenic gradients. 5. Road crossings, 10 of which were culverts, were not dispersal barriers for fishes or shrimps. On average, species were present both upstream and downstream from road crossings at 68% of sites where they occurred. Absences upstream or downstream from road crossings occurred at 16% of sites each and likely resulted from a failure to detect species. 6. Several existing features of these catchments and taxa may aid in fish and shrimp conservation. The headwaters are protected by management practices of El Yunque National Forest, connectivity within the river network has been maintained, and the diadromous life history of these organisms makes them resilient to pulsed disturbances.</p></abstract><textClass xml:lang="en"><keywords scheme="keyword"><list><head>keywords</head><item><term>diadromous</term></item><item><term>distribution models</term></item><item><term>random forests</term></item><item><term>roads</term></item><item><term>tropical stream</term></item></list></keywords></textClass><textClass><keywords scheme="Journal Subject"><list><head>article-category</head><item><term>APPLIED ISSUES</term></item></list></keywords></textClass></profileDesc><revisionDesc><change when="2011-05">Published</change></revisionDesc></teiHeader></istex:fulltextTEI><json:item><extension>txt</extension><original>false</original><mimetype>text/plain</mimetype><uri>https://api.istex.fr/document/A99EF91E6C716FB699E70BE6FB3765ACF06B8C63/fulltext/txt</uri></json:item></fulltext><metadata><istex:metadataXml wicri:clean="Wiley, elements deleted: body"><istex:xmlDeclaration>version="1.0" encoding="UTF-8" standalone="yes"</istex:xmlDeclaration><istex:document><component version="2.0" type="serialArticle" xml:lang="en"><header><publicationMeta level="product"><publisherInfo><publisherName>Blackwell Publishing Ltd</publisherName><publisherLoc>Oxford, UK</publisherLoc></publisherInfo><doi origin="wiley" registered="yes">10.1111/(ISSN)1365-2427</doi><issn type="print">0046-5070</issn><issn type="electronic">1365-2427</issn><idGroup><id type="product" value="FWB"></id><id type="publisherDivision" value="ST"></id></idGroup><titleGroup><title type="main" sort="FRESHWATER BIOLOGY">Freshwater Biology</title></titleGroup></publicationMeta><publicationMeta level="part" position="05105"><doi origin="wiley">10.1111/fwb.2011.56.issue-5</doi><numberingGroup><numbering type="journalVolume" number="56">56</numbering><numbering type="journalIssue" number="5">5</numbering></numberingGroup><coverDate startDate="2011-05">May 2011</coverDate></publicationMeta><publicationMeta level="unit" type="article" position="17" status="forIssue"><doi origin="wiley">10.1111/j.1365-2427.2010.02537.x</doi><idGroup><id type="unit" value="FWB2537"></id></idGroup><countGroup><count type="pageTotal" number="14"></count></countGroup><titleGroup><title type="tocHeading1">Applied Issues</title><title type="articleCategory">APPLIED ISSUES</title></titleGroup><copyright>© 2010 Blackwell Publishing Ltd</copyright><eventGroup><event type="xmlConverted" agent="Converter:BPG_TO_WML3G version:2.4.8 mode:FullText" date="2011-04-04"></event><event type="publishedOnlineEarlyUnpaginated" date="2010-11-26"></event><event type="firstOnline" date="2010-11-26"></event><event type="publishedOnlineFinalForm" date="2011-04-04"></event><event type="xmlConverted" agent="Converter:WILEY_ML3G_TO_WILEY_ML3GV2 version:3.8.8" date="2014-01-26"></event><event type="xmlConverted" agent="Converter:WML3G_To_WML3G version:4.1.7 mode:FullText,remove_FC" date="2014-10-16"></event></eventGroup><numberingGroup><numbering type="pageFirst" number="1002">1002</numbering><numbering type="pageLast" number="1015">1015</numbering></numberingGroup><correspondenceTo>Catherine L. Hein, Climate Impacts Research Centre, Abisko Scientific Research Station, SE‐98107, Abisko, Sweden. E‐mail: <email>clhein@gmail.com</email></correspondenceTo><linkGroup><link type="toTypesetVersion" href="file:FWB.FWB2537.pdf"></link></linkGroup></publicationMeta><contentMeta><unparsedEditorialHistory>(Manuscript accepted 27 October 2010)</unparsedEditorialHistory><countGroup><count type="figureTotal" number="5"></count><count type="tableTotal" number="3"></count></countGroup><titleGroup><title type="main">Effects of coupled natural and anthropogenic factors on the community structure of diadromous fish and shrimp species in tropical island streams</title><title type="shortAuthors"><i>C. L. Hein</i> et al.</title><title type="short"><i>Stream communities on a tropical island</i></title></titleGroup><creators><creator creatorRole="author" xml:id="cr1" affiliationRef="#a1"><personName><givenNames>CATHERINE L.</givenNames><familyName>HEIN</familyName></personName></creator><creator creatorRole="author" xml:id="cr2" affiliationRef="#a2" noteRef="#fn1"><personName><givenNames>ANDREW S.</givenNames><familyName>PIKE</familyName></personName></creator><creator creatorRole="author" xml:id="cr3" affiliationRef="#a3"><personName><givenNames>JUAN F.</givenNames><familyName>BLANCO</familyName></personName></creator><creator creatorRole="author" xml:id="cr4" affiliationRef="#a4"><personName><givenNames>ALAN P.</givenNames><familyName>COVICH</familyName></personName></creator><creator creatorRole="author" xml:id="cr5" affiliationRef="#a2"><personName><givenNames>FREDERICK N.</givenNames><familyName>SCATENA</familyName></personName></creator><creator creatorRole="author" xml:id="cr6" affiliationRef="#a1"><personName><givenNames>CHARLES P.</givenNames><familyName>HAWKINS</familyName></personName></creator><creator creatorRole="author" xml:id="cr7" affiliationRef="#a1" noteRef="#fn2"><personName><givenNames>TODD A.</givenNames><familyName>CROWL</familyName></personName></creator></creators><affiliationGroup><affiliation xml:id="a1" countryCode="US"><unparsedAffiliation>Department of Watershed Sciences and Ecology Center, Utah State University, Logan, UT, U.S.A.</unparsedAffiliation></affiliation><affiliation xml:id="a2" countryCode="US"><unparsedAffiliation>Department of Earth & Environmental Science, University of Pennsylvania, Philadelphia, PA, U.S.A.</unparsedAffiliation></affiliation><affiliation xml:id="a3" countryCode="CO"><unparsedAffiliation>Instituto de Biología, Universidad de Antioquia, Ciudad Universitaria, Medellín, Colombia, South America</unparsedAffiliation></affiliation><affiliation xml:id="a4" countryCode="US"><unparsedAffiliation>Institute of Ecology, Odum School of Ecology, University of Georgia, Athens, GA, U.S.A.</unparsedAffiliation></affiliation></affiliationGroup><keywordGroup xml:lang="en"><keyword xml:id="k1">diadromous</keyword><keyword xml:id="k2">distribution models</keyword><keyword xml:id="k3">random forests</keyword><keyword xml:id="k4">roads</keyword><keyword xml:id="k5">tropical stream</keyword></keywordGroup><abstractGroup><abstract type="main" xml:lang="en"><title type="main">Summary</title><p>1. Overlapping river and road networks provide a framework for studying the complex interactions between natural and human systems, with river‐road intersections as focal areas of study. Roads can alter the morphology of stream channels, pose barriers to freshwater fauna, provide easy access to streams for humans and non‐native species and accelerate the expansion of urban development.</p><p>2. We determined what variables control the structure of diadromous fish and shrimp communities and assessed whether particular road crossings altered community structure in north‐eastern Puerto Rico. We identified 24 sites that represented a range of river and road sizes across two catchments that drain El Yunque National Forest in Puerto Rico.</p><p>3. The location of natural barriers and the size of stream pools were the most important variables for predicting six of fifteen fish and shrimp distributions. Predatory fishes were predicted to be limited to areas in the river network below large, steep waterfalls, whereas adult shrimp <i>Atya lanipes</i> (Atyidae) were predicted to be present above these waterfalls. The fish <i>Awaous banana</i> was predicted to be present in pools >11.6 m wide, whereas the shrimp <i>Xiphocaris elongata</i> was predicted to be present in pools <10.4 m wide. The distributions of nine species were predicted poorly, but three of these species were common and three were rare.</p><p>4. Although urban and agricultural land covers were among the top three predictors of five species distributions, they were probably good predictors because they were correlated with the natural gradient. Further study is necessary to disentangle natural and anthropogenic gradients.</p><p>5. Road crossings, 10 of which were culverts, were not dispersal barriers for fishes or shrimps. On average, species were present both upstream and downstream from road crossings at 68% of sites where they occurred. Absences upstream or downstream from road crossings occurred at 16% of sites each and likely resulted from a failure to detect species.</p><p>6. Several existing features of these catchments and taxa may aid in fish and shrimp conservation. The headwaters are protected by management practices of El Yunque National Forest, connectivity within the river network has been maintained, and the diadromous life history of these organisms makes them resilient to pulsed disturbances.</p></abstract></abstractGroup></contentMeta><noteGroup><note xml:id="fn1"><p> Present address: National Marine Fisheries Service, Southwest Fisheries Science Center, 110 Shaffer Road, Santa Cruz, CA 95060, U.S.A.</p></note><note xml:id="fn2"><p> Present address: National Science Foundation, Division of Environmental Biology, Arlington, VA 22230, U.S.A.</p></note></noteGroup></header></component></istex:document></istex:metadataXml><mods version="3.6"><titleInfo lang="en"><title>Effects of coupled natural and anthropogenic factors on the community structure of diadromous fish and shrimp species in tropical island streams</title></titleInfo><titleInfo type="abbreviated" lang="en"><title>Stream communities on a tropical island</title></titleInfo><titleInfo type="alternative" contentType="CDATA" lang="en"><title>Effects of coupled natural and anthropogenic factors on the community structure of diadromous fish and shrimp species in tropical island streams</title></titleInfo><name type="personal"><namePart type="given">CATHERINE L.</namePart><namePart type="family">HEIN</namePart><affiliation>Department of Watershed Sciences and Ecology Center, Utah State University, Logan, UT, U.S.A.</affiliation><role><roleTerm type="text">author</roleTerm></role></name><name type="personal"><namePart type="given">ANDREW S.</namePart><namePart type="family">PIKE</namePart><affiliation>Department of Earth & Environmental Science, University of Pennsylvania, Philadelphia, PA, U.S.A.</affiliation><description>Present address: National Marine Fisheries Service, Southwest Fisheries Science Center, 110 Shaffer Road, Santa Cruz, CA 95060, U.S.A.</description><role><roleTerm type="text">author</roleTerm></role></name><name type="personal"><namePart type="given">JUAN F.</namePart><namePart type="family">BLANCO</namePart><affiliation>Instituto de Biología, Universidad de Antioquia, Ciudad Universitaria, Medellín, Colombia, South America</affiliation><role><roleTerm type="text">author</roleTerm></role></name><name type="personal"><namePart type="given">ALAN P.</namePart><namePart type="family">COVICH</namePart><affiliation>Institute of Ecology, Odum School of Ecology, University of Georgia, Athens, GA, U.S.A.</affiliation><role><roleTerm type="text">author</roleTerm></role></name><name type="personal"><namePart type="given">FREDERICK N.</namePart><namePart type="family">SCATENA</namePart><affiliation>Department of Earth & Environmental Science, University of Pennsylvania, Philadelphia, PA, U.S.A.</affiliation><role><roleTerm type="text">author</roleTerm></role></name><name type="personal"><namePart type="given">CHARLES P.</namePart><namePart type="family">HAWKINS</namePart><affiliation>Department of Watershed Sciences and Ecology Center, Utah State University, Logan, UT, U.S.A.</affiliation><role><roleTerm type="text">author</roleTerm></role></name><name type="personal"><namePart type="given">TODD A.</namePart><namePart type="family">CROWL</namePart><affiliation>Department of Watershed Sciences and Ecology Center, Utah State University, Logan, UT, U.S.A.</affiliation><description>Present address: National Science Foundation, Division of Environmental Biology, Arlington, VA 22230, U.S.A.</description><role><roleTerm type="text">author</roleTerm></role></name><typeOfResource>text</typeOfResource><genre type="article" displayLabel="article"></genre><originInfo><publisher>Blackwell Publishing Ltd</publisher><place><placeTerm type="text">Oxford, UK</placeTerm></place><dateIssued encoding="w3cdtf">2011-05</dateIssued><edition>(Manuscript accepted 27 October 2010)</edition><copyrightDate encoding="w3cdtf">2011</copyrightDate></originInfo><language><languageTerm type="code" authority="rfc3066">en</languageTerm><languageTerm type="code" authority="iso639-2b">eng</languageTerm></language><physicalDescription><internetMediaType>text/html</internetMediaType><extent unit="figures">5</extent><extent unit="tables">3</extent></physicalDescription><abstract lang="en">1. Overlapping river and road networks provide a framework for studying the complex interactions between natural and human systems, with river‐road intersections as focal areas of study. Roads can alter the morphology of stream channels, pose barriers to freshwater fauna, provide easy access to streams for humans and non‐native species and accelerate the expansion of urban development. 2. We determined what variables control the structure of diadromous fish and shrimp communities and assessed whether particular road crossings altered community structure in north‐eastern Puerto Rico. We identified 24 sites that represented a range of river and road sizes across two catchments that drain El Yunque National Forest in Puerto Rico. 3. The location of natural barriers and the size of stream pools were the most important variables for predicting six of fifteen fish and shrimp distributions. Predatory fishes were predicted to be limited to areas in the river network below large, steep waterfalls, whereas adult shrimp Atya lanipes (Atyidae) were predicted to be present above these waterfalls. The fish Awaous banana was predicted to be present in pools >11.6 m wide, whereas the shrimp Xiphocaris elongata was predicted to be present in pools <10.4 m wide. The distributions of nine species were predicted poorly, but three of these species were common and three were rare. 4. Although urban and agricultural land covers were among the top three predictors of five species distributions, they were probably good predictors because they were correlated with the natural gradient. Further study is necessary to disentangle natural and anthropogenic gradients. 5. Road crossings, 10 of which were culverts, were not dispersal barriers for fishes or shrimps. On average, species were present both upstream and downstream from road crossings at 68% of sites where they occurred. Absences upstream or downstream from road crossings occurred at 16% of sites each and likely resulted from a failure to detect species. 6. Several existing features of these catchments and taxa may aid in fish and shrimp conservation. The headwaters are protected by management practices of El Yunque National Forest, connectivity within the river network has been maintained, and the diadromous life history of these organisms makes them resilient to pulsed disturbances.</abstract><subject lang="en"><genre>keywords</genre><topic>diadromous</topic><topic>distribution models</topic><topic>random forests</topic><topic>roads</topic><topic>tropical stream</topic></subject><relatedItem type="host"><titleInfo><title>Freshwater Biology</title></titleInfo><genre type="journal">journal</genre><subject><genre>article-category</genre><topic>APPLIED ISSUES</topic></subject><identifier type="ISSN">0046-5070</identifier><identifier type="eISSN">1365-2427</identifier><identifier type="DOI">10.1111/(ISSN)1365-2427</identifier><identifier type="PublisherID">FWB</identifier><part><date>2011</date><detail type="volume"><caption>vol.</caption><number>56</number></detail><detail type="issue"><caption>no.</caption><number>5</number></detail><extent unit="pages"><start>1002</start><end>1015</end><total>14</total></extent></part></relatedItem><identifier type="istex">A99EF91E6C716FB699E70BE6FB3765ACF06B8C63</identifier><identifier type="DOI">10.1111/j.1365-2427.2010.02537.x</identifier><identifier type="ArticleID">FWB2537</identifier><accessCondition type="use and reproduction" contentType="copyright">© 2010 Blackwell Publishing Ltd</accessCondition><recordInfo><recordContentSource>WILEY</recordContentSource><recordOrigin>Blackwell Publishing Ltd</recordOrigin></recordInfo></mods></metadata><serie></serie></istex></record>Pour manipuler ce document sous Unix (Dilib)
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