Serveur d'exploration sur le chêne en Belgique (avant curation)

Attention, ce site est en cours de développement !
Attention, site généré par des moyens informatiques à partir de corpus bruts.
Les informations ne sont donc pas validées.

Effects of Previous Land-Use on Plant Species Composition and Diversity in Mediterranean Forests

Identifieur interne : 000022 ( Pmc/Corpus ); précédent : 000021; suivant : 000023

Effects of Previous Land-Use on Plant Species Composition and Diversity in Mediterranean Forests

Auteurs : Yacine Kouba ; Felipe Martínez-García ; Ángel De Frutos ; Concepci N L. Alados

Source :

RBID : PMC:4580598

Abstract

At some point in their history, most forests in the Mediterranean Basin have been subjected to intensive management or converted to agriculture land. Knowing how forest plant communities recovered after the abandonment of forest-management or agricultural practices (including livestock grazing) provides a basis for investigating how previous land management have affected plant species diversity and composition in forest ecosystems. Our study investigated the consequences of historical “land management” practices on present-day Mediterranean forests by comparing species assemblages and the diversity of (i) all plant species and (ii) each ecological group defined by species’ habitat preferences and successional status (i.e., early-, mid-, and late-successional species). We compared forest stands that differed both in land-use history and in successional stage. In addition, we evaluated the value of those stands for biodiversity conservation. The study revealed significant compositional differentiation among stands that was due to among-stand variations in the diversity (namely, species richness and evenness) of early-, intermediate-, and late-successional species. Historical land management has led to an increase in compositional divergences among forest stands and the loss of late-successional forest species.


Url:
DOI: 10.1371/journal.pone.0139031
PubMed: 26397707
PubMed Central: 4580598

Links to Exploration step

PMC:4580598

Le document en format XML

<record>
<TEI>
<teiHeader>
<fileDesc>
<titleStmt>
<title xml:lang="en">Effects of Previous Land-Use on Plant Species Composition and Diversity in Mediterranean Forests</title>
<author>
<name sortKey="Kouba, Yacine" sort="Kouba, Yacine" uniqKey="Kouba Y" first="Yacine" last="Kouba">Yacine Kouba</name>
<affiliation>
<nlm:aff id="aff001">
<addr-line>Instituto Pirenaico de Ecología (CSIC), Zaragoza, Spain</addr-line>
</nlm:aff>
</affiliation>
</author>
<author>
<name sortKey="Martinez Garcia, Felipe" sort="Martinez Garcia, Felipe" uniqKey="Martinez Garcia F" first="Felipe" last="Martínez-García">Felipe Martínez-García</name>
<affiliation>
<nlm:aff id="aff002">
<addr-line>Departamento de Sistemas y Recursos Naturales, Escuela de Ingeniería de Montes, Forestal y del Medio Natural, Universidad Politécnica de Madrid, Madrid, Spain</addr-line>
</nlm:aff>
</affiliation>
</author>
<author>
<name sortKey="De Frutos, Angel" sort="De Frutos, Angel" uniqKey="De Frutos A" first="Ángel" last="De Frutos">Ángel De Frutos</name>
<affiliation>
<nlm:aff id="aff003">
<addr-line>Instituto Pirenaico de Ecología (CSIC), Jaca, Huesca, Spain</addr-line>
</nlm:aff>
</affiliation>
</author>
<author>
<name sortKey="Alados, Concepci N L" sort="Alados, Concepci N L" uniqKey="Alados C" first="Concepci N L." last="Alados">Concepci N L. Alados</name>
<affiliation>
<nlm:aff id="aff001">
<addr-line>Instituto Pirenaico de Ecología (CSIC), Zaragoza, Spain</addr-line>
</nlm:aff>
</affiliation>
</author>
</titleStmt>
<publicationStmt>
<idno type="wicri:source">PMC</idno>
<idno type="pmid">26397707</idno>
<idno type="pmc">4580598</idno>
<idno type="url">http://www.ncbi.nlm.nih.gov/pmc/articles/PMC4580598</idno>
<idno type="RBID">PMC:4580598</idno>
<idno type="doi">10.1371/journal.pone.0139031</idno>
<date when="2015">2015</date>
<idno type="wicri:Area/Pmc/Corpus">000022</idno>
<idno type="wicri:explorRef" wicri:stream="Pmc" wicri:step="Corpus" wicri:corpus="PMC">000022</idno>
</publicationStmt>
<sourceDesc>
<biblStruct>
<analytic>
<title xml:lang="en" level="a" type="main">Effects of Previous Land-Use on Plant Species Composition and Diversity in Mediterranean Forests</title>
<author>
<name sortKey="Kouba, Yacine" sort="Kouba, Yacine" uniqKey="Kouba Y" first="Yacine" last="Kouba">Yacine Kouba</name>
<affiliation>
<nlm:aff id="aff001">
<addr-line>Instituto Pirenaico de Ecología (CSIC), Zaragoza, Spain</addr-line>
</nlm:aff>
</affiliation>
</author>
<author>
<name sortKey="Martinez Garcia, Felipe" sort="Martinez Garcia, Felipe" uniqKey="Martinez Garcia F" first="Felipe" last="Martínez-García">Felipe Martínez-García</name>
<affiliation>
<nlm:aff id="aff002">
<addr-line>Departamento de Sistemas y Recursos Naturales, Escuela de Ingeniería de Montes, Forestal y del Medio Natural, Universidad Politécnica de Madrid, Madrid, Spain</addr-line>
</nlm:aff>
</affiliation>
</author>
<author>
<name sortKey="De Frutos, Angel" sort="De Frutos, Angel" uniqKey="De Frutos A" first="Ángel" last="De Frutos">Ángel De Frutos</name>
<affiliation>
<nlm:aff id="aff003">
<addr-line>Instituto Pirenaico de Ecología (CSIC), Jaca, Huesca, Spain</addr-line>
</nlm:aff>
</affiliation>
</author>
<author>
<name sortKey="Alados, Concepci N L" sort="Alados, Concepci N L" uniqKey="Alados C" first="Concepci N L." last="Alados">Concepci N L. Alados</name>
<affiliation>
<nlm:aff id="aff001">
<addr-line>Instituto Pirenaico de Ecología (CSIC), Zaragoza, Spain</addr-line>
</nlm:aff>
</affiliation>
</author>
</analytic>
<series>
<title level="j">PLoS ONE</title>
<idno type="eISSN">1932-6203</idno>
<imprint>
<date when="2015">2015</date>
</imprint>
</series>
</biblStruct>
</sourceDesc>
</fileDesc>
<profileDesc>
<textClass></textClass>
</profileDesc>
</teiHeader>
<front>
<div type="abstract" xml:lang="en">
<p>At some point in their history, most forests in the Mediterranean Basin have been subjected to intensive management or converted to agriculture land. Knowing how forest plant communities recovered after the abandonment of forest-management or agricultural practices (including livestock grazing) provides a basis for investigating how previous land management have affected plant species diversity and composition in forest ecosystems. Our study investigated the consequences of historical “land management” practices on present-day Mediterranean forests by comparing species assemblages and the diversity of (i) all plant species and (ii) each ecological group defined by species’ habitat preferences and successional status (i.e., early-, mid-, and late-successional species). We compared forest stands that differed both in land-use history and in successional stage. In addition, we evaluated the value of those stands for biodiversity conservation. The study revealed significant compositional differentiation among stands that was due to among-stand variations in the diversity (namely, species richness and evenness) of early-, intermediate-, and late-successional species. Historical land management has led to an increase in compositional divergences among forest stands and the loss of late-successional forest species.</p>
</div>
</front>
<back>
<div1 type="bibliography">
<listBibl>
<biblStruct>
<analytic>
<author>
<name sortKey="Barbero, M" uniqKey="Barbero M">M Barbero</name>
</author>
<author>
<name sortKey="Bonin, G" uniqKey="Bonin G">G Bonin</name>
</author>
<author>
<name sortKey="Loisel, R" uniqKey="Loisel R">R Loisel</name>
</author>
<author>
<name sortKey="Quezel, P" uniqKey="Quezel P">P Quézel</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Bengtsson, J" uniqKey="Bengtsson J">J Bengtsson</name>
</author>
<author>
<name sortKey="Nilsson, Sg" uniqKey="Nilsson S">SG Nilsson</name>
</author>
<author>
<name sortKey="Franc, A" uniqKey="Franc A">A Franc</name>
</author>
<author>
<name sortKey="Menozzi, P" uniqKey="Menozzi P">P Menozzi</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Vanbergen, Aj" uniqKey="Vanbergen A">AJ Vanbergen</name>
</author>
<author>
<name sortKey="Woodcock, Ba" uniqKey="Woodcock B">BA Woodcock</name>
</author>
<author>
<name sortKey="Watt, Ad" uniqKey="Watt A">AD Watt</name>
</author>
<author>
<name sortKey="Niemela, J" uniqKey="Niemela J">J Niemela</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Paillet, Y" uniqKey="Paillet Y">Y Paillet</name>
</author>
<author>
<name sortKey="Berges, L" uniqKey="Berges L">L Bergès</name>
</author>
<author>
<name sortKey="Hj Lten, J" uniqKey="Hj Lten J">J Hjältén</name>
</author>
<author>
<name sortKey="Odor, P" uniqKey="Odor P">P Odor</name>
</author>
<author>
<name sortKey="Avon, C" uniqKey="Avon C">C Avon</name>
</author>
<author>
<name sortKey="Bernhardt Romermann, M" uniqKey="Bernhardt Romermann M">M Bernhardt-Römermann</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Mather, As" uniqKey="Mather A">AS Mather</name>
</author>
<author>
<name sortKey="Fairbairn, J" uniqKey="Fairbairn J">J Fairbairn</name>
</author>
<author>
<name sortKey="Needle, Cl" uniqKey="Needle C">CL Needle</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Sciama, D" uniqKey="Sciama D">D Sciama</name>
</author>
<author>
<name sortKey="Augusto, L" uniqKey="Augusto L">L Augusto</name>
</author>
<author>
<name sortKey="Dupouey, J L" uniqKey="Dupouey J">J-L Dupouey</name>
</author>
<author>
<name sortKey="Gonzalez, M" uniqKey="Gonzalez M">M Gonzalez</name>
</author>
<author>
<name sortKey="Moares Dominguez, C" uniqKey="Moares Dominguez C">C Moares Domínguez</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Verheyen, K" uniqKey="Verheyen K">K Verheyen</name>
</author>
<author>
<name sortKey="Bossuyt, B" uniqKey="Bossuyt B">B Bossuyt</name>
</author>
<author>
<name sortKey="Hermy, M" uniqKey="Hermy M">M Hermy</name>
</author>
<author>
<name sortKey="Tack, G" uniqKey="Tack G">G Tack</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Flinn, Km" uniqKey="Flinn K">KM Flinn</name>
</author>
<author>
<name sortKey="Vellend, M" uniqKey="Vellend M">M Vellend</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Hermy, M" uniqKey="Hermy M">M Hermy</name>
</author>
<author>
<name sortKey="Verheyen, K" uniqKey="Verheyen K">K Verheyen</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Matuszkiewicz, Jm" uniqKey="Matuszkiewicz J">JM Matuszkiewicz</name>
</author>
<author>
<name sortKey="Kowalska, A" uniqKey="Kowalska A">A Kowalska</name>
</author>
<author>
<name sortKey="Kozlowska, A" uniqKey="Kozlowska A">A Kozłowska</name>
</author>
<author>
<name sortKey="Roo Zieli Ska, E" uniqKey="Roo Zieli Ska E">E Roo-Zielińska</name>
</author>
<author>
<name sortKey="Solon, J" uniqKey="Solon J">J Solon</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Lasanta, T" uniqKey="Lasanta T">T Lasanta</name>
</author>
<author>
<name sortKey="Arnaez, J" uniqKey="Arnaez J">J Arnáez</name>
</author>
<author>
<name sortKey="Errea, Mp" uniqKey="Errea M">MP Errea</name>
</author>
<author>
<name sortKey="Ortigosa, L" uniqKey="Ortigosa L">L Ortigosa</name>
</author>
<author>
<name sortKey="Ruiz Fla O, P" uniqKey="Ruiz Fla O P">P Ruiz-Flaño</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Carson, Wp" uniqKey="Carson W">WP Carson</name>
</author>
<author>
<name sortKey="Schnitzer, Sa" uniqKey="Schnitzer S">SA Schnitzer</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Gehring, C" uniqKey="Gehring C">C Gehring</name>
</author>
<author>
<name sortKey="Denich, M" uniqKey="Denich M">M Denich</name>
</author>
<author>
<name sortKey="Vlek, Plg" uniqKey="Vlek P">PLG Vlek</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Duguid, Mc" uniqKey="Duguid M">MC Duguid</name>
</author>
<author>
<name sortKey="Ashton, Ms" uniqKey="Ashton M">MS Ashton</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Smith, Kj" uniqKey="Smith K">KJ Smith</name>
</author>
<author>
<name sortKey="Keeton, Ws" uniqKey="Keeton W">WS Keeton</name>
</author>
<author>
<name sortKey="Twery, Mj" uniqKey="Twery M">MJ Twery</name>
</author>
<author>
<name sortKey="Tobi, Dr" uniqKey="Tobi D">DR Tobi</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Berhane, A" uniqKey="Berhane A">A Berhane</name>
</author>
<author>
<name sortKey="Totland, " uniqKey="Totland ">Ø Totland</name>
</author>
<author>
<name sortKey="Moe, Sr" uniqKey="Moe S">SR Moe</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Oliver, Cd" uniqKey="Oliver C">CD Oliver</name>
</author>
<author>
<name sortKey="Larson, Bc" uniqKey="Larson B">BC Larson</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Kouba, Y" uniqKey="Kouba Y">Y Kouba</name>
</author>
<author>
<name sortKey="Martinez Garcia, F" uniqKey="Martinez Garcia F">F Martínez-García</name>
</author>
<author>
<name sortKey="De Frutos, A" uniqKey="De Frutos A">A de Frutos</name>
</author>
<author>
<name sortKey="Alados, C" uniqKey="Alados C">C Alados</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Baeten, L" uniqKey="Baeten L">L Baeten</name>
</author>
<author>
<name sortKey="Hermy, M" uniqKey="Hermy M">M Hermy</name>
</author>
<author>
<name sortKey="Van Daele, S" uniqKey="Van Daele S">S Van Daele</name>
</author>
<author>
<name sortKey="Verheyen, K" uniqKey="Verheyen K">K Verheyen</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="De Frenne, P" uniqKey="De Frenne P">P De Frenne</name>
</author>
<author>
<name sortKey="Baeten, L" uniqKey="Baeten L">L Baeten</name>
</author>
<author>
<name sortKey="Graae, Bj" uniqKey="Graae B">BJ Graae</name>
</author>
<author>
<name sortKey="Brunet, J" uniqKey="Brunet J">J Brunet</name>
</author>
<author>
<name sortKey="Wulf, M" uniqKey="Wulf M">M Wulf</name>
</author>
<author>
<name sortKey="Orczewska, A" uniqKey="Orczewska A">A Orczewska</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Halpern, Cb" uniqKey="Halpern C">CB Halpern</name>
</author>
<author>
<name sortKey="Spies, Ta" uniqKey="Spies T">TA Spies</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Okland, T" uniqKey="Okland T">T Okland</name>
</author>
<author>
<name sortKey="Rydgren, K" uniqKey="Rydgren K">K Rydgren</name>
</author>
<author>
<name sortKey="Halvorsen, R" uniqKey="Halvorsen R">R Halvorsen</name>
</author>
<author>
<name sortKey="Storaunet, K" uniqKey="Storaunet K">K Storaunet</name>
</author>
<author>
<name sortKey="Rolstad, J" uniqKey="Rolstad J">J Rolstad</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Seiwa, K" uniqKey="Seiwa K">K Seiwa</name>
</author>
<author>
<name sortKey="Etoh, Y" uniqKey="Etoh Y">Y Etoh</name>
</author>
<author>
<name sortKey="Hisita, M" uniqKey="Hisita M">M Hisita</name>
</author>
<author>
<name sortKey="Masaka, K" uniqKey="Masaka K">K Masaka</name>
</author>
<author>
<name sortKey="Imaji, A" uniqKey="Imaji A">A Imaji</name>
</author>
<author>
<name sortKey="Ueno, N" uniqKey="Ueno N">N Ueno</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Battles, Jj" uniqKey="Battles J">JJ Battles</name>
</author>
<author>
<name sortKey="Shlisky, Aj" uniqKey="Shlisky A">AJ Shlisky</name>
</author>
<author>
<name sortKey="Barrett, Rh" uniqKey="Barrett R">RH Barrett</name>
</author>
<author>
<name sortKey="Heald, Rc" uniqKey="Heald R">RC Heald</name>
</author>
<author>
<name sortKey="Allen Diaz, Bh" uniqKey="Allen Diaz B">BH Allen-Diaz</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Dufrene, M" uniqKey="Dufrene M">M Dufrene</name>
</author>
<author>
<name sortKey="Legendre, P" uniqKey="Legendre P">P Legendre</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="De Caceres, M" uniqKey="De Caceres M">M De Cáceres</name>
</author>
<author>
<name sortKey="Font, X" uniqKey="Font X">X Font</name>
</author>
<author>
<name sortKey="Vicente, P" uniqKey="Vicente P">P Vicente</name>
</author>
<author>
<name sortKey="Oliva, F" uniqKey="Oliva F">F Oliva</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Farwig, N" uniqKey="Farwig N">N Farwig</name>
</author>
<author>
<name sortKey="Sajita, N" uniqKey="Sajita N">N Sajita</name>
</author>
<author>
<name sortKey="Bohning Gaese, K" uniqKey="Bohning Gaese K">K Böhning-Gaese</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Peterken, Gf" uniqKey="Peterken G">GF Peterken</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Kouba, Y" uniqKey="Kouba Y">Y Kouba</name>
</author>
<author>
<name sortKey="Camarero, Jj" uniqKey="Camarero J">JJ Camarero</name>
</author>
<author>
<name sortKey="Alados, Cl" uniqKey="Alados C">CL Alados</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Kouba, Y" uniqKey="Kouba Y">Y Kouba</name>
</author>
<author>
<name sortKey="Alados, Cl" uniqKey="Alados C">CL Alados</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Goodall, Dw" uniqKey="Goodall D">DW Goodall</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Alados, Cl" uniqKey="Alados C">CL Alados</name>
</author>
<author>
<name sortKey="Navarro, T" uniqKey="Navarro T">T Navarro</name>
</author>
<author>
<name sortKey="Komac, B" uniqKey="Komac B">B Komac</name>
</author>
<author>
<name sortKey="Pascual, V" uniqKey="Pascual V">V Pascual</name>
</author>
<author>
<name sortKey="Martinez, F" uniqKey="Martinez F">F Martinez</name>
</author>
<author>
<name sortKey="Cabezudo, B" uniqKey="Cabezudo B">B Cabezudo</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Castroviejo, S" uniqKey="Castroviejo S">S Castroviejo</name>
</author>
<author>
<name sortKey="Lainz, M" uniqKey="Lainz M">M Laínz</name>
</author>
<author>
<name sortKey="Gonzalez, Gl" uniqKey="Gonzalez G">GL González</name>
</author>
<author>
<name sortKey="Montserrat, Pf" uniqKey="Montserrat P">PF Montserrat</name>
</author>
<author>
<name sortKey="Flora, Iberica" uniqKey="Flora I">iberica Flora</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Barbier, S" uniqKey="Barbier S">S Barbier</name>
</author>
<author>
<name sortKey="Gosselin, F" uniqKey="Gosselin F">F Gosselin</name>
</author>
<author>
<name sortKey="Balandier, P" uniqKey="Balandier P">P Balandier</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Ramovs, Bv" uniqKey="Ramovs B">BV Ramovs</name>
</author>
<author>
<name sortKey="Roberts, Mr" uniqKey="Roberts M">MR Roberts</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Montserrat, M" uniqKey="Montserrat M">M Montserrat</name>
</author>
<author>
<name sortKey="Jose Maria" uniqKey="Jose Maria">José-María</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Peinado, M" uniqKey="Peinado M">M Peinado</name>
</author>
<author>
<name sortKey="Rivas Martinez" uniqKey="Rivas Martinez">Rivas-Martinez</name>
</author>
</analytic>
</biblStruct>
<biblStruct></biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Villar, L" uniqKey="Villar L">L Villar</name>
</author>
<author>
<name sortKey="Sese, Ja" uniqKey="Sese J">JA Sesé</name>
</author>
<author>
<name sortKey="Ferrandez, Jv" uniqKey="Ferrandez J">JV Ferrández</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Villar, L" uniqKey="Villar L">L Villar</name>
</author>
<author>
<name sortKey="Sese, Ja" uniqKey="Sese J">JA Sesé</name>
</author>
<author>
<name sortKey="Ferrandez, Jv" uniqKey="Ferrandez J">JV Ferrández</name>
</author>
</analytic>
</biblStruct>
<biblStruct></biblStruct>
<biblStruct></biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Pinheiro, J" uniqKey="Pinheiro J">J Pinheiro</name>
</author>
<author>
<name sortKey="Bates, D" uniqKey="Bates D">D Bates</name>
</author>
<author>
<name sortKey="Dedroy, S" uniqKey="Dedroy S">S DedRoy</name>
</author>
<author>
<name sortKey="Sarkar, D" uniqKey="Sarkar D">D Sarkar</name>
</author>
<author>
<name sortKey="R Core" uniqKey="R Core">R-core</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="De Caceres, M" uniqKey="De Caceres M">M De Cáceres</name>
</author>
<author>
<name sortKey="Legendre, P" uniqKey="Legendre P">P Legendre</name>
</author>
<author>
<name sortKey="Wiser, Sk" uniqKey="Wiser S">SK Wiser</name>
</author>
<author>
<name sortKey="Brotons, L" uniqKey="Brotons L">L Brotons</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Calvi O Cancela, M" uniqKey="Calvi O Cancela M">M Calviño-Cancela</name>
</author>
<author>
<name sortKey="Rubido Bara, M" uniqKey="Rubido Bara M">M Rubido-Bará</name>
</author>
<author>
<name sortKey="Van Etten, Ejb" uniqKey="Van Etten E">EJB van Etten</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Baselga, A" uniqKey="Baselga A">A Baselga</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Lasanta, T" uniqKey="Lasanta T">T Lasanta</name>
</author>
<author>
<name sortKey="Garcia Ruiz, Jm" uniqKey="Garcia Ruiz J">JM García-Ruiz</name>
</author>
<author>
<name sortKey="Perez Rontome, C" uniqKey="Perez Rontome C">C Pérez-Rontomé</name>
</author>
<author>
<name sortKey="Sancho Marcen, C" uniqKey="Sancho Marcen C">C Sancho-Marcén</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Schmiedinger, A" uniqKey="Schmiedinger A">A Schmiedinger</name>
</author>
<author>
<name sortKey="Kreyling, J" uniqKey="Kreyling J">J Kreyling</name>
</author>
<author>
<name sortKey="Steinbauer, Mj" uniqKey="Steinbauer M">MJ Steinbauer</name>
</author>
<author>
<name sortKey="Macdonald, Se" uniqKey="Macdonald S">SE Macdonald</name>
</author>
<author>
<name sortKey="Jentsch, A" uniqKey="Jentsch A">A Jentsch</name>
</author>
<author>
<name sortKey="Beierkuhnlein, C" uniqKey="Beierkuhnlein C">C Beierkuhnlein</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Fahey, Rt" uniqKey="Fahey R">RT Fahey</name>
</author>
<author>
<name sortKey="Puettmann, Kj" uniqKey="Puettmann K">KJ Puettmann</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Hart, Sa" uniqKey="Hart S">SA Hart</name>
</author>
<author>
<name sortKey="Chen, Hyh" uniqKey="Chen H">HYH Chen</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Vockenhuber, Ea" uniqKey="Vockenhuber E">EA Vockenhuber</name>
</author>
<author>
<name sortKey="Scherber, C" uniqKey="Scherber C">C Scherber</name>
</author>
<author>
<name sortKey="Langenbruch, C" uniqKey="Langenbruch C">C Langenbruch</name>
</author>
<author>
<name sortKey="Mei Ner, M" uniqKey="Mei Ner M">M Meißner</name>
</author>
<author>
<name sortKey="Seidel, D" uniqKey="Seidel D">D Seidel</name>
</author>
<author>
<name sortKey="Tscharntke, T" uniqKey="Tscharntke T">T Tscharntke</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Breugel, Mv" uniqKey="Breugel M">MV Breugel</name>
</author>
<author>
<name sortKey="Bongers, F" uniqKey="Bongers F">F Bongers</name>
</author>
<author>
<name sortKey="Martinez Ramos, M" uniqKey="Martinez Ramos M">M Martínez-Ramos</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Bartels, Sf" uniqKey="Bartels S">SF Bartels</name>
</author>
<author>
<name sortKey="Chen, Hyh" uniqKey="Chen H">HYH Chen</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Bartemucci, P" uniqKey="Bartemucci P">P Bartemucci</name>
</author>
<author>
<name sortKey="Messier, C" uniqKey="Messier C">C Messier</name>
</author>
<author>
<name sortKey="Canham, Cd" uniqKey="Canham C">CD Canham</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Messier, C" uniqKey="Messier C">C Messier</name>
</author>
<author>
<name sortKey="Parent, S" uniqKey="Parent S">S Parent</name>
</author>
<author>
<name sortKey="Bergeron, Y" uniqKey="Bergeron Y">Y Bergeron</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Szeicz, M" uniqKey="Szeicz M">M Szeicz</name>
</author>
<author>
<name sortKey="Macdonald, M" uniqKey="Macdonald M">M Macdonald</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Smith, Md" uniqKey="Smith M">MD Smith</name>
</author>
<author>
<name sortKey="Knapp, Ak" uniqKey="Knapp A">AK Knapp</name>
</author>
<author>
<name sortKey="Collins, Sl" uniqKey="Collins S">SL Collins</name>
</author>
</analytic>
</biblStruct>
<biblStruct>
<analytic>
<author>
<name sortKey="Kouba, Y" uniqKey="Kouba Y">Y Kouba</name>
</author>
<author>
<name sortKey="Alados, Cl" uniqKey="Alados C">CL Alados</name>
</author>
</analytic>
</biblStruct>
</listBibl>
</div1>
</back>
</TEI>
<pmc article-type="research-article">
<pmc-dir>properties open_access</pmc-dir>
<front>
<journal-meta>
<journal-id journal-id-type="nlm-ta">PLoS One</journal-id>
<journal-id journal-id-type="iso-abbrev">PLoS ONE</journal-id>
<journal-id journal-id-type="publisher-id">plos</journal-id>
<journal-id journal-id-type="pmc">plosone</journal-id>
<journal-title-group>
<journal-title>PLoS ONE</journal-title>
</journal-title-group>
<issn pub-type="epub">1932-6203</issn>
<publisher>
<publisher-name>Public Library of Science</publisher-name>
<publisher-loc>San Francisco, CA USA</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="pmid">26397707</article-id>
<article-id pub-id-type="pmc">4580598</article-id>
<article-id pub-id-type="doi">10.1371/journal.pone.0139031</article-id>
<article-id pub-id-type="publisher-id">PONE-D-15-06411</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Research Article</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>Effects of Previous Land-Use on Plant Species Composition and Diversity in Mediterranean Forests</article-title>
<alt-title alt-title-type="running-head">Previous Land-Use Effects on Forest Plant Composition and Diversity</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Kouba</surname>
<given-names>Yacine</given-names>
</name>
<xref ref-type="aff" rid="aff001">
<sup>1</sup>
</xref>
<xref rid="cor001" ref-type="corresp">*</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Martínez-García</surname>
<given-names>Felipe</given-names>
</name>
<xref ref-type="aff" rid="aff002">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>de Frutos</surname>
<given-names>Ángel</given-names>
</name>
<xref ref-type="aff" rid="aff003">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Alados</surname>
<given-names>Concepción L.</given-names>
</name>
<xref ref-type="aff" rid="aff001">
<sup>1</sup>
</xref>
</contrib>
</contrib-group>
<aff id="aff001">
<label>1</label>
<addr-line>Instituto Pirenaico de Ecología (CSIC), Zaragoza, Spain</addr-line>
</aff>
<aff id="aff002">
<label>2</label>
<addr-line>Departamento de Sistemas y Recursos Naturales, Escuela de Ingeniería de Montes, Forestal y del Medio Natural, Universidad Politécnica de Madrid, Madrid, Spain</addr-line>
</aff>
<aff id="aff003">
<label>3</label>
<addr-line>Instituto Pirenaico de Ecología (CSIC), Jaca, Huesca, Spain</addr-line>
</aff>
<contrib-group>
<contrib contrib-type="editor">
<name>
<surname>Gomory</surname>
<given-names>Dusan</given-names>
</name>
<role>Editor</role>
<xref ref-type="aff" rid="edit1"></xref>
</contrib>
</contrib-group>
<aff id="edit1">
<addr-line>Technical University in Zvolen, SLOVAKIA</addr-line>
</aff>
<author-notes>
<fn fn-type="conflict" id="coi001">
<p>
<bold>Competing Interests: </bold>
The authors have declared that no competing interests exist.</p>
</fn>
<fn fn-type="con" id="contrib001">
<p>Conceived and designed the experiments: YK CLA. Performed the experiments: YK CLA. Analyzed the data: YK AF. Contributed reagents/materials/analysis tools: YK FMG AF CLA. Wrote the paper: YK FMG AF CLA.</p>
</fn>
<corresp id="cor001">* E-mail:
<email>kouba_yacine@yahoo.fr</email>
</corresp>
</author-notes>
<pub-date pub-type="epub">
<day>23</day>
<month>9</month>
<year>2015</year>
</pub-date>
<pub-date pub-type="collection">
<year>2015</year>
</pub-date>
<volume>10</volume>
<issue>9</issue>
<elocation-id>e0139031</elocation-id>
<history>
<date date-type="received">
<day>12</day>
<month>2</month>
<year>2015</year>
</date>
<date date-type="accepted">
<day>7</day>
<month>9</month>
<year>2015</year>
</date>
</history>
<permissions>
<copyright-year>2015</copyright-year>
<copyright-holder>Kouba et al</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<license-p>This is an open access article distributed under the terms of the
<ext-link ext-link-type="uri" xlink:href="http://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License</ext-link>
, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited</license-p>
</license>
</permissions>
<self-uri content-type="pdf" xlink:type="simple" xlink:href="pone.0139031.pdf"></self-uri>
<abstract>
<p>At some point in their history, most forests in the Mediterranean Basin have been subjected to intensive management or converted to agriculture land. Knowing how forest plant communities recovered after the abandonment of forest-management or agricultural practices (including livestock grazing) provides a basis for investigating how previous land management have affected plant species diversity and composition in forest ecosystems. Our study investigated the consequences of historical “land management” practices on present-day Mediterranean forests by comparing species assemblages and the diversity of (i) all plant species and (ii) each ecological group defined by species’ habitat preferences and successional status (i.e., early-, mid-, and late-successional species). We compared forest stands that differed both in land-use history and in successional stage. In addition, we evaluated the value of those stands for biodiversity conservation. The study revealed significant compositional differentiation among stands that was due to among-stand variations in the diversity (namely, species richness and evenness) of early-, intermediate-, and late-successional species. Historical land management has led to an increase in compositional divergences among forest stands and the loss of late-successional forest species.</p>
</abstract>
<funding-group>
<funding-statement>YK was funded by a MAEC-AECID grant from the Spanish Agency for International Cooperation (
<ext-link ext-link-type="uri" xlink:href="http://www.aecid.es/EN/aecid">http://www.aecid.es/EN/aecid</ext-link>
). AF was financed by a JAE-DOC postdoctoral contract from the Spanish Research Council (CSIC) (
<ext-link ext-link-type="uri" xlink:href="http://www.csic.es/web/guest/home">http://www.csic.es/web/guest/home</ext-link>
) and Fondo Social Europeo(
<ext-link ext-link-type="uri" xlink:href="http://ec.europa.eu/esf/home.jsp?langId=en">http://ec.europa.eu/esf/home.jsp?langId=en</ext-link>
). The authors acknowledge financial support from the Spanish Ministry of Economy and Competitiveness and Innovation (research project: CGL2011-27259). This funder had no role in study design, data collection and analysis.</funding-statement>
</funding-group>
<counts>
<fig-count count="4"></fig-count>
<table-count count="4"></table-count>
<page-count count="15"></page-count>
</counts>
<custom-meta-group>
<custom-meta id="data-availability">
<meta-name>Data Availability</meta-name>
<meta-value>All relevant data are within the paper and its Supporting Information files.</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
<notes>
<title>Data Availability</title>
<p>All relevant data are within the paper and its Supporting Information files.</p>
</notes>
</front>
<body>
<sec sec-type="intro" id="sec001">
<title>Introduction</title>
<p>Most of today’s unmanaged Mediterranean forests were once under intensive management [
<xref rid="pone.0139031.ref001" ref-type="bibr">1</xref>
<xref rid="pone.0139031.ref003" ref-type="bibr">3</xref>
]. Since antiquity, those forests have been extensively cleared, and the rate of forest loss accelerated in the 18th and 19th C. [
<xref rid="pone.0139031.ref004" ref-type="bibr">4</xref>
]. In Euro-Mediterranean countries, in particular, many of the natural forests were coppiced for timber and firewood, which created coppices that differed in their management intensity and the time since coppicing had ceased.</p>
<p>On the other hand, changes in socioeconomics and production systems in the late 19th C. and early 20th C. resulted in the abandonment and subsequent afforestation (both spontaneously and through planting) of the poorest arable lands and many pastures [
<xref rid="pone.0139031.ref005" ref-type="bibr">5</xref>
<xref rid="pone.0139031.ref007" ref-type="bibr">7</xref>
]. In many regions, abandonment and forest encroachment occurred in several phases, which created a complex mix of forest stands that are at different stages of succession [
<xref rid="pone.0139031.ref008" ref-type="bibr">8</xref>
<xref rid="pone.0139031.ref010" ref-type="bibr">10</xref>
]. In Spain, as in many other European countries, the largest increase in forest cover on abandoned lands that had been used for agriculture or as pastures occurred in the second half of the 20th C. [
<xref rid="pone.0139031.ref011" ref-type="bibr">11</xref>
].</p>
<p>In the early 21st C., those human-altered forests have continued to bear the imprint of historical changes in land-use [
<xref rid="pone.0139031.ref009" ref-type="bibr">9</xref>
]. In particular, the type of prior land-use and intensity have had a strong influence on the characteristics of secondary forest stands [
<xref rid="pone.0139031.ref012" ref-type="bibr">12</xref>
,
<xref rid="pone.0139031.ref013" ref-type="bibr">13</xref>
], and the type of historical management has had a similarly strong effect on abandoned coppice stands [
<xref rid="pone.0139031.ref014" ref-type="bibr">14</xref>
,
<xref rid="pone.0139031.ref015" ref-type="bibr">15</xref>
]. Furthermore, historical logging, livestock grazing, and agriculture might have affected the diversity and composition of the plant communities in those forests [
<xref rid="pone.0139031.ref008" ref-type="bibr">8</xref>
,
<xref rid="pone.0139031.ref009" ref-type="bibr">9</xref>
,
<xref rid="pone.0139031.ref016" ref-type="bibr">16</xref>
]. The plant community differs depending on the time since human disturbance has ceased. Classifying the plant species (e.g. early-, intermediate-, and late-successional species) found within the successional stages can increase our understanding of the successional dynamics [
<xref rid="pone.0139031.ref008" ref-type="bibr">8</xref>
,
<xref rid="pone.0139031.ref017" ref-type="bibr">17</xref>
]. Investigating how plant species diversity and composition differ among forest stands that have different land-use histories and are at different successional stages can increase our understanding of the consequences of past land-use on plant communities in these forests and provides a basis for predicting the responses of the communities to future disturbances and environmental changes. Furthermore, given the increase in human-altered forests in the Mediterranean Basin [
<xref rid="pone.0139031.ref001" ref-type="bibr">1</xref>
], a greater understanding of the contribution that these forests can make to biodiversity conservation is crucial [
<xref rid="pone.0139031.ref018" ref-type="bibr">18</xref>
].</p>
<p>Plant diversity and compositional differences between primarily old growth forests and secondary growth forests [
<xref rid="pone.0139031.ref006" ref-type="bibr">6</xref>
,
<xref rid="pone.0139031.ref010" ref-type="bibr">10</xref>
,
<xref rid="pone.0139031.ref019" ref-type="bibr">19</xref>
,
<xref rid="pone.0139031.ref020" ref-type="bibr">20</xref>
] and between managed and unmanaged forests [
<xref rid="pone.0139031.ref004" ref-type="bibr">4</xref>
,
<xref rid="pone.0139031.ref021" ref-type="bibr">21</xref>
,
<xref rid="pone.0139031.ref022" ref-type="bibr">22</xref>
] have been well studied; however, published studies of formerly managed forests and secondary growth forests in Mediterranean environments are rare. Studies have emphasized the importance of anthropogenic disturbances in fostering the establishment of early-successional species to the disadvantage of forest specialists [
<xref rid="pone.0139031.ref023" ref-type="bibr">23</xref>
]. A recent review [
<xref rid="pone.0139031.ref014" ref-type="bibr">14</xref>
] found that a comparison between two types of forest management (even-aged vs. uneven-aged) did not provide a clear pattern that could predict the plant diversity response; however, other studies have shown that uneven-aged stands have the capacity to maintain high plant diversity [
<xref rid="pone.0139031.ref015" ref-type="bibr">15</xref>
].</p>
<p>Our study was conducted in oak forests that included formerly managed stands and secondary forest stands that differed in their structural properties. The main objective was to investigate the effects of previous forest management and agricultural activities (including livestock grazing) on contemporary forest plant communities. Specifically, we first assessed the effects of stand history (abandoned coppices vs. secondary growth stands), stand age (young vs. old), age structure of the forest stand (even-aged vs. uneven-aged stands), and the extent of the canopy cover on plant species composition. Secondly, we assessed whether those factors affected the species diversity (namely, species richness and evenness) of each ecological group defined by species’ habitat preferences and successional status (i.e. early-, intermediate-, and late-successional species). Previous studies have suggested that diversity as a measure of community response can be deceptive if there are increases or decreases in the number of species in the plant groups; e.g., increases in the abundances of early-successional species might obscure the loss of or decrease in late-successional species [
<xref rid="pone.0139031.ref015" ref-type="bibr">15</xref>
,
<xref rid="pone.0139031.ref024" ref-type="bibr">24</xref>
]. Thirdly, we evaluated the value of the oak stands for biodiversity conservation as reflected by their ability to support species that are associated with natural forests (i.e., late-successional species), which can be achieved using indicator species analysis [
<xref rid="pone.0139031.ref025" ref-type="bibr">25</xref>
,
<xref rid="pone.0139031.ref026" ref-type="bibr">26</xref>
] that allows the assessment of the strength of the relationship between species abundance and forest type. Previous studies have shown that the potential to develop into forests that are more natural is high in forests that have high diversity in late-successional species [
<xref rid="pone.0139031.ref027" ref-type="bibr">27</xref>
,
<xref rid="pone.0139031.ref028" ref-type="bibr">28</xref>
]. We hypothesized that differences in historical land-use have led to the development of forest stands that have contrasting successional trajectories, which increases the floristic differentiation among oak stands [
<xref rid="pone.0139031.ref018" ref-type="bibr">18</xref>
]. Furthermore, previous land management has reduced the diversity of forest specialists in those oak stands [
<xref rid="pone.0139031.ref001" ref-type="bibr">1</xref>
,
<xref rid="pone.0139031.ref018" ref-type="bibr">18</xref>
].</p>
</sec>
<sec sec-type="materials|methods" id="sec002">
<title>Materials and Methods</title>
<sec id="sec003">
<title>Ethics statement</title>
<p>All plant surveys were performed under permits issued by the municipal councils of Nueno and Arguis, and by the Director of the Parque Natural de la Sierra y Cañones de Guara, Aragón, Spain.</p>
</sec>
<sec id="sec004">
<title>Study area</title>
<p>The study was carried out in oak forests at a moderate elevation (800–1000 m a.s.l.) in the Central Pre-Pyrenees, Spain (between 42.32 N and 42.11 N, and 0.31 W and 0.04 W) (
<xref rid="pone.0139031.g001" ref-type="fig">Fig 1</xref>
). Most of the lithology is conglomerate, limestone, marl, and sandstone developed on Eocene flysch sedimentary formations. The climate is transitional sub-Mediterranean; i.e., influenced by continental effects from the north and by milder Mediterranean conditions from the south (i.e., the Ebro Basin). Mean annual precipitation is 1317 ± 302 mm (1915–2005) and mean annual temperature is 11.5 ± 2.8°C (1910–2005) [
<xref rid="pone.0139031.ref029" ref-type="bibr">29</xref>
].</p>
<fig id="pone.0139031.g001" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0139031.g001</object-id>
<label>Fig 1</label>
<caption>
<title>Study area.</title>
<p>The location of the study area in Spain (left panel), and the locations of the stands that were surveyed in the Central Pre-Pyrenees (right panel) (AB Abena, AG Arguis, AR Ara, BE Belsué, IB Ibort, IP Ipies, LU Lucera, NO Nocito, RA Rasal, RP Rapun).</p>
</caption>
<graphic xlink:href="pone.0139031.g001"></graphic>
</fig>
<p>The oak forests (mainly,
<italic>Quercus faginea</italic>
) of the Central Pre-Pyrenees are a mosaic of stands that differ in their structure and history. Based on historical land-use, those semi-deciduous oak forests are of two types: abandoned coppice stands (coppices that differed in historical coppicing intensities and time since management abandonment) and secondary growth stands (most of which were established on abandoned farmlands and pastures, primarily, in the second half of the 20th C. [
<xref rid="pone.0139031.ref030" ref-type="bibr">30</xref>
]). The overstorey canopy of those semi-deciduous oak stands was mostly
<italic>Q</italic>
.
<italic>faginea</italic>
interspersed with some scattered pines (
<italic>Pinus sylvestris</italic>
and
<italic>Pinus nigra</italic>
) and evergreen oak (
<italic>Quercus ilex</italic>
subsp.
<italic>ballota</italic>
). The understory comprised shrubs (mainly,
<italic>Quercus coccifera</italic>
,
<italic>Buxus sempervirens</italic>
,
<italic>Genista scorpius</italic>
,
<italic>Juniperus communis</italic>
), forbs (mainly,
<italic>Aphyllanthes monspeliensis</italic>
,
<italic>Arenaria montana</italic>
,
<italic>Achillea millefolium</italic>
), and graminoids (mainly,
<italic>Brachypodium pinnatum</italic>
,
<italic>Carex halleriana</italic>
,
<italic>Festuca rubra</italic>
,
<italic>Carex flacca</italic>
,
<italic>Bromus erectus</italic>
).</p>
</sec>
<sec id="sec005">
<title>Data collection</title>
<p>Based on historical land-use maps and aerial photographs from 1957 and 2006, we selected ten
<italic>Q</italic>
.
<italic>faginea</italic>
-dominated stands that were at different successional stages and had different land-use histories [
<xref rid="pone.0139031.ref029" ref-type="bibr">29</xref>
,
<xref rid="pone.0139031.ref030" ref-type="bibr">30</xref>
] (
<xref rid="pone.0139031.t001" ref-type="table">Table 1</xref>
). In 2009 and 2010, during the period of peak growth (May and June), vascular plant species were surveyed in the ten stands. Within each stand, three 500-m linear transects (N = 30 transects) were established. To estimate plant abundance, richness, and species composition within each transect, we used the Point-Intercept Method [
<xref rid="pone.0139031.ref031" ref-type="bibr">31</xref>
], which involves recording, at 40-cm intervals, the identity of all individuals that are in contact with a vertical nail [
<xref rid="pone.0139031.ref032" ref-type="bibr">32</xref>
].</p>
<table-wrap id="pone.0139031.t001" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0139031.t001</object-id>
<label>Table 1</label>
<caption>
<title>Characteristics of the ten
<italic>Quercus faginea</italic>
stands surveyed in the Central Pre-Pyrenees, Spain.</title>
</caption>
<alternatives>
<graphic id="pone.0139031.t001g" xlink:href="pone.0139031.t001"></graphic>
<table frame="hsides" rules="groups">
<colgroup span="1">
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
</colgroup>
<thead>
<tr>
<th align="left" rowspan="1" colspan="1">Abbreviation</th>
<th align="left" rowspan="1" colspan="1">Location</th>
<th align="left" rowspan="1" colspan="1">FORTYPE</th>
<th align="left" rowspan="1" colspan="1">AGE (year)</th>
<th align="left" rowspan="1" colspan="1">CVAGE (%)</th>
<th align="left" rowspan="1" colspan="1">CANCOV (%)</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" rowspan="1" colspan="1">AB</td>
<td align="left" rowspan="1" colspan="1">Abena</td>
<td align="left" rowspan="1" colspan="1">SF</td>
<td align="left" rowspan="1" colspan="1">Old (50)</td>
<td align="left" rowspan="1" colspan="1">EA (19)</td>
<td align="left" rowspan="1" colspan="1">47.7, 49.3, 48.4</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">AR</td>
<td align="left" rowspan="1" colspan="1">Ara</td>
<td align="left" rowspan="1" colspan="1">CS</td>
<td align="left" rowspan="1" colspan="1">Young (35)</td>
<td align="left" rowspan="1" colspan="1">EA (17)</td>
<td align="left" rowspan="1" colspan="1">39.8, 29.3, 29.6</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">AG</td>
<td align="left" rowspan="1" colspan="1">Arguis</td>
<td align="left" rowspan="1" colspan="1">CS</td>
<td align="left" rowspan="1" colspan="1">Old (50)</td>
<td align="left" rowspan="1" colspan="1">EA (10)</td>
<td align="left" rowspan="1" colspan="1">38.9, 47.1, 45.4</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">BE</td>
<td align="left" rowspan="1" colspan="1">Belsué</td>
<td align="left" rowspan="1" colspan="1">CS</td>
<td align="left" rowspan="1" colspan="1">Young (40)</td>
<td align="left" rowspan="1" colspan="1">UEA (43)</td>
<td align="left" rowspan="1" colspan="1">43.9, 47.2, 41.0</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">IB</td>
<td align="left" rowspan="1" colspan="1">Ibort</td>
<td align="left" rowspan="1" colspan="1">CS</td>
<td align="left" rowspan="1" colspan="1">Old (63)</td>
<td align="left" rowspan="1" colspan="1">EA (17)</td>
<td align="left" rowspan="1" colspan="1">75.4, 68.6, 63.6</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">IP</td>
<td align="left" rowspan="1" colspan="1">Ipies</td>
<td align="left" rowspan="1" colspan="1">CS</td>
<td align="left" rowspan="1" colspan="1">Old (64)</td>
<td align="left" rowspan="1" colspan="1">EA (15)</td>
<td align="left" rowspan="1" colspan="1">08.3, 15.9, 39.9</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">LU</td>
<td align="left" rowspan="1" colspan="1">Lucera</td>
<td align="left" rowspan="1" colspan="1">CS</td>
<td align="left" rowspan="1" colspan="1">Young (39)</td>
<td align="left" rowspan="1" colspan="1">EA (12)</td>
<td align="left" rowspan="1" colspan="1">53.5, 45.6, 60.9</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">NO</td>
<td align="left" rowspan="1" colspan="1">Nocito</td>
<td align="left" rowspan="1" colspan="1">SF</td>
<td align="left" rowspan="1" colspan="1">Old (56)</td>
<td align="left" rowspan="1" colspan="1">UEA (47)</td>
<td align="left" rowspan="1" colspan="1">50.4, 36.6, 44.4</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">RP</td>
<td align="left" rowspan="1" colspan="1">Rapun</td>
<td align="left" rowspan="1" colspan="1">CS</td>
<td align="left" rowspan="1" colspan="1">Old (69)</td>
<td align="left" rowspan="1" colspan="1">EA (9)</td>
<td align="left" rowspan="1" colspan="1">44.6, 46.6, 49.6</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">RA</td>
<td align="left" rowspan="1" colspan="1">Rasal</td>
<td align="left" rowspan="1" colspan="1">SF</td>
<td align="left" rowspan="1" colspan="1">Young (31)</td>
<td align="left" rowspan="1" colspan="1">UEA (31)</td>
<td align="left" rowspan="1" colspan="1">46.0, 41.2, 29.3</td>
</tr>
</tbody>
</table>
</alternatives>
<table-wrap-foot>
<fn id="t001fn001">
<p>FORTYPE: forest type; AGE: mean stand tree age; CVAGE: coefficient of variation of stand age; CANCOV: canopy cover; SF: secondary growth stand; CS: abandoned coppice stand; EA: even-aged stand; UEA: uneven-aged stand. CANCOV is reported for the three transects of each stand.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>We recorded all of the vascular plants that touched the nail and any overstorey species (including
<italic>Q</italic>
.
<italic>faginea</italic>
) that was above the nail (
<xref rid="pone.0139031.s001" ref-type="supplementary-material">S1 Appendix</xref>
). Plant species that could not be identified with certainty in the field were collected, pressed, and brought to the laboratory for identification by botanists. Species that have traits that make them difficult to distinguish were identified to genus, only. Plant nomenclature followed
<italic>Flora Iberica</italic>
[
<xref rid="pone.0139031.ref033" ref-type="bibr">33</xref>
]. The abundance of each plant species in each transect was calculated as the number of points where the species occurred. In each transect, canopy cover (CANCOV) was estimated based on the relative abundance (%) of woody species (including trees and large shrubs) that were ≥ 1.5 m tall. For each stand, we estimated the age of ~ 40 trees (for details on age estimations see [
<xref rid="pone.0139031.ref029" ref-type="bibr">29</xref>
]), calculated mean tree-age and the coefficient of variation of tree-age. Two binary variables were derived from the age data: AGE (young vs. old stands) and CVAGE (even-aged vs. uneven-aged stands). Forest type (FORTYPE; secondary growth stands vs. abandoned coppice stands) of each stand was based on observations in the field (see
<xref rid="pone.0139031.t001" ref-type="table">Table 1</xref>
).</p>
</sec>
<sec id="sec006">
<title>Grouping species by successional status</title>
<p>Analyses based on ecological groups can help to identify the mechanisms that underlie the tree species-plant diversity relationship [
<xref rid="pone.0139031.ref034" ref-type="bibr">34</xref>
]. In our study, species were clustered within one of three ecological groups based on species’ habitat preferences and successional status [
<xref rid="pone.0139031.ref023" ref-type="bibr">23</xref>
,
<xref rid="pone.0139031.ref035" ref-type="bibr">35</xref>
]: Early-successional species (ES), which are shade-intolerant pioneer species that reach maximum abundance in open-canopy and disturbed areas, Intermediate-successional species (IS), which occupy young to mature, open- or closed-canopy forests, but not excessively disturbed habitats, and late-successional species (LS), which are shade tolerant species that reach maximum abundance in mature, closed-canopy, forest interiors (
<xref rid="pone.0139031.s001" ref-type="supplementary-material">S1 Appendix</xref>
). To assign each plant species to one of the three ecological groups, we used information in the literature [
<xref rid="pone.0139031.ref033" ref-type="bibr">33</xref>
,
<xref rid="pone.0139031.ref036" ref-type="bibr">36</xref>
<xref rid="pone.0139031.ref040" ref-type="bibr">40</xref>
], experience in the field, and personal knowledge (Dr. Felipe Martínez-García, botanist).</p>
</sec>
<sec id="sec007">
<title>Statistical analyses</title>
<p>To quantify the effects of the explanatory variables (AGE, CVAGE, FORTYPE, and CANCOV) on species composition, we used a permutational multivariate analysis of variance (PERMANOVA), which is a multivariate, nonparametric analogue of the univariate analysis of variance (MANOVA). The species abundance data (all species included) were subjected to PERMANOVA using the Bray-Curtis distance measure and 10000 permutations. To identify patterns in the compositional variation of plant communities among stand types (i.e., young vs. old, even-aged vs. uneven-aged, secondary growth vs. abandoned coppice stands), we used unconstrained ordination, non-metrical multidimensional scaling (NMDS). In addition, to test for the effect of canopy cover, this variable was plotted as a smooth surface in an ordination diagram.</p>
<p>Differences in species richness and species evenness among stand types (i.e., young vs. old, even-aged vs. uneven-aged, secondary growth vs. abandoned coppice stands) and the relationship between these two measures of diversity and canopy cover were analyzed using ANCOVA, both for all species combined and for each ecological group. To account for spatial dependencies, stand location was included as a random factor in the ANCOVA models. Normality and homogeneity of variance were tested by examining the model residuals versus the fitted plots and the normal
<italic>q-q</italic>
plots of the models. The appropriate transformations were used as required.</p>
<p>Indicator species analyses were used to assess the strength of the correlations between plant species and the following forest classes that resulted from the interaction AGE × CVAGE × FORTYP: old even-aged secondary growth stands, old even-aged coppice stands, old uneven-aged secondary growth stands, young even-aged coppice stands, young uneven-aged secondary growth stands, and young uneven-aged coppice stands. Indicator species in each forest class were identified by calculating the indicator values [
<xref rid="pone.0139031.ref025" ref-type="bibr">25</xref>
] based on plant species abundance (all species included), then we assigned each selected species to an ecological group (i.e., early-, intermediate-, or late-successional species).</p>
<p>The statistical analyses were performed using the programming language R [
<xref rid="pone.0139031.ref041" ref-type="bibr">41</xref>
]. The PERMANOVA and the NMDS were performed using the R package ‘
<italic>vegan</italic>
’ [
<xref rid="pone.0139031.ref042" ref-type="bibr">42</xref>
], the ANCOVA was performed using the R package ‘
<italic>nlme</italic>
’ [
<xref rid="pone.0139031.ref043" ref-type="bibr">43</xref>
], and the Indicator Species Analysis was performed using the R package ‘
<italic>indicspecies</italic>
’ [
<xref rid="pone.0139031.ref044" ref-type="bibr">44</xref>
].</p>
</sec>
</sec>
<sec sec-type="results" id="sec008">
<title>Results</title>
<p>In the ten oak stands in the Central Pre-Pyrenees, we identified 206 vascular plant species (
<xref rid="pone.0139031.s001" ref-type="supplementary-material">S1 Appendix</xref>
). The most abundant species, which comprised 60% of all of the individuals recorded, were
<italic>Buxus sempervirens</italic>
(19.17%),
<italic>Brachypodium pinnatum</italic>
(13.38%),
<italic>Aphyllanthes monspeliensis</italic>
(8.93%),
<italic>Carex halleriana</italic>
(5.95%, IS),
<italic>Genista scorpius</italic>
(4.50%),
<italic>Carex flacca</italic>
(4.10%, IS), and
<italic>Festuca rubra</italic>
(3.61%).</p>
<p>The classification of plant species by successional status indicated that most (56%) of the 206 vascular plant species were ES species. Twenty-six percent and 18% of the plants were IS species and LS species, respectively.
<italic>Genista scorpius</italic>
(ES),
<italic>Teucrium chamaedrys</italic>
(ES),
<italic>Thymus vulgaris</italic>
(ES),
<italic>Buxus sempervirens</italic>
(IS),
<italic>Festuca rubra</italic>
(IS),
<italic>Amelanchier ovalis</italic>
(IS),
<italic>Aphyllanthes monspeliensis</italic>
(IS),
<italic>Brachypodium pinnatum</italic>
(IS), and
<italic>Rubia peregrina</italic>
(LS) were the most commonly occurring species (found in all transects) (
<xref rid="pone.0139031.s001" ref-type="supplementary-material">S1 Appendix</xref>
).</p>
<sec id="sec009">
<title>Factors affecting species composition</title>
<p>The PERMANOVA analysis revealed that plant species composition differed significantly between stand types (i.e., young vs. old, even-aged vs. uneven-aged, secondary growth vs. abandoned coppice stands). In addition, canopy cover “CANCOV” and plant species composition were significantly correlated.</p>
<p>The explanatory variables explained almost 40% of the variation in the composition of plant communities (
<xref rid="pone.0139031.t002" ref-type="table">Table 2</xref>
). “FORTYPE” explained the largest proportion (15.2%) of the compositional variation, followed by “CANCOV”, which explained 11% of the variation. “AGE” and “CVAGE” each explained ~ 7% of the variation.
<xref rid="pone.0139031.g002" ref-type="fig">Fig 2</xref>
shows the grouping of plant transects by stand type in the ordination space determined by the NMDS analysis.</p>
<table-wrap id="pone.0139031.t002" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0139031.t002</object-id>
<label>Table 2</label>
<caption>
<title>Non-parametric MANOVA test for the effects of explanatory variables on the plant species composition of ten
<italic>Quercus faginea</italic>
forest stands in the Central Pre-Pyrenees, Spain.</title>
</caption>
<alternatives>
<graphic id="pone.0139031.t002g" xlink:href="pone.0139031.t002"></graphic>
<table frame="hsides" rules="groups">
<colgroup span="1">
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
</colgroup>
<thead>
<tr>
<th align="justify" rowspan="1" colspan="1"></th>
<th align="justify" rowspan="1" colspan="1">
<italic>F</italic>
</th>
<th align="justify" rowspan="1" colspan="1">
<italic>R</italic>
<sup>
<italic>2</italic>
</sup>
</th>
<th align="justify" rowspan="1" colspan="1">
<italic>P</italic>
</th>
</tr>
</thead>
<tbody>
<tr>
<td align="justify" rowspan="1" colspan="1">AGE</td>
<td align="char" char="." rowspan="1" colspan="1">2.6</td>
<td align="char" char="." rowspan="1" colspan="1">0.072</td>
<td align="char" char="." rowspan="1" colspan="1"><0.001</td>
</tr>
<tr>
<td align="justify" rowspan="1" colspan="1">CVAGE</td>
<td align="char" char="." rowspan="1" colspan="1">2.6</td>
<td align="char" char="." rowspan="1" colspan="1">0.071</td>
<td align="char" char="." rowspan="1" colspan="1">0.004</td>
</tr>
<tr>
<td align="justify" rowspan="1" colspan="1">FORTYPE</td>
<td align="char" char="." rowspan="1" colspan="1">3.8</td>
<td align="char" char="." rowspan="1" colspan="1">0.152</td>
<td align="char" char="." rowspan="1" colspan="1"><0.001</td>
</tr>
<tr>
<td align="justify" rowspan="1" colspan="1">CANCOV</td>
<td align="char" char="." rowspan="1" colspan="1">7.6</td>
<td align="char" char="." rowspan="1" colspan="1">0.110</td>
<td align="char" char="." rowspan="1" colspan="1"><0.001</td>
</tr>
</tbody>
</table>
</alternatives>
<table-wrap-foot>
<fn id="t002fn001">
<p>AGE: Stand Age; CVAGE: coefficient of variation of stand age; FORTYPE: forest type; CANCOV: Canopy Cover. R
<sup>2</sup>
is the variance (%) explained by each variable.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<fig id="pone.0139031.g002" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0139031.g002</object-id>
<label>Fig 2</label>
<caption>
<title>Nonparametric multidimensional scaling (NMDS) ordinations.</title>
<p>NMDS diagrams indicating the groupings of the floristic transects by stand type of
<italic>Quercus faginea</italic>
in the Central Pre-Pyrenees, Spain: young vs. old stands, even aged vs. uneven aged stands, secondary growth stands vs. abandoned coppice stands. Canopy cover is indicated in the ordination diagram as a smooth surface (below right hand plot).</p>
</caption>
<graphic xlink:href="pone.0139031.g002"></graphic>
</fig>
</sec>
<sec id="sec010">
<title>Factors affecting the species diversity of each successional species group</title>
<p>Each of the four explanatory variables explained a significant amount of the variation in overall plant species richness and, collectively, they explained >70% of the total variance (
<xref rid="pone.0139031.t003" ref-type="table">Table 3</xref>
). Based on the variance explained by each variable, “FORTYP” was the most important variable, followed by “CANCOV”, “AGE”, and “CVAGE” (
<xref rid="pone.0139031.t003" ref-type="table">Table 3</xref>
).</p>
<table-wrap id="pone.0139031.t003" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0139031.t003</object-id>
<label>Table 3</label>
<caption>
<title>ANCOVA Test for the effects of four explanatory variables on plant species diversity (species richness and evenness) in ten oak stands in the Central Pre-Pyrenees, Spain.</title>
</caption>
<alternatives>
<graphic id="pone.0139031.t003g" xlink:href="pone.0139031.t003"></graphic>
<table frame="hsides" rules="groups">
<colgroup span="1">
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
</colgroup>
<thead>
<tr>
<th align="left" rowspan="1" colspan="1"></th>
<th align="left" rowspan="1" colspan="1"></th>
<th colspan="3" align="left" rowspan="1">Richness</th>
<th colspan="3" align="left" rowspan="1">Evenness</th>
</tr>
<tr>
<th align="left" rowspan="1" colspan="1"></th>
<th align="left" rowspan="1" colspan="1"></th>
<th align="left" rowspan="1" colspan="1">
<italic>R</italic>
<sup>
<italic>2</italic>
</sup>
</th>
<th align="left" rowspan="1" colspan="1">
<italic>F</italic>
</th>
<th align="left" rowspan="1" colspan="1">
<italic>P</italic>
</th>
<th align="left" rowspan="1" colspan="1">
<italic>R</italic>
<sup>
<italic>2</italic>
</sup>
</th>
<th align="left" rowspan="1" colspan="1">
<italic>F</italic>
</th>
<th align="left" rowspan="1" colspan="1">
<italic>P</italic>
</th>
</tr>
</thead>
<tbody>
<tr>
<td rowspan="4" align="right" colspan="1">AS</td>
<td align="left" rowspan="1" colspan="1">AGE</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.150</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>12.8</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold><0.001</bold>
</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.08</td>
<td align="char" char="." rowspan="1" colspan="1">0.770</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">CVAGE</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.107</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>9.2</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.006</bold>
</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.01</td>
<td align="char" char="." rowspan="1" colspan="1">0.980</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">FORTYPE</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.291</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>25.0</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold><0.001</bold>
</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.00</td>
<td align="char" char="." rowspan="1" colspan="1">0.459</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">CANCOV</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.160</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>13.7</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold><0.001</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.324</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>11.61</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.004</bold>
</td>
</tr>
<tr>
<td rowspan="4" align="right" colspan="1">ES</td>
<td align="left" rowspan="1" colspan="1">AGE</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.150</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>16.04</bold>
</td>
<td align="left" rowspan="1" colspan="1">
<bold><0.001</bold>
</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">2.68</td>
<td align="char" char="." rowspan="1" colspan="1">0.123</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">CVAGE</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.146</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>15.60</bold>
</td>
<td align="left" rowspan="1" colspan="1">
<bold><0.001</bold>
</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">3.25</td>
<td align="char" char="." rowspan="1" colspan="1">0.091</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">FORTYPE</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.326</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>34.72</bold>
</td>
<td align="left" rowspan="1" colspan="1">
<bold><0.001</bold>
</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.00</td>
<td align="char" char="." rowspan="1" colspan="1">0.985</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">CANCOV</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.156</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>16.98</bold>
</td>
<td align="left" rowspan="1" colspan="1">
<bold><0.001</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.291</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>11.88</bold>
</td>
<td align="left" rowspan="1" colspan="1">
<bold>0.003</bold>
</td>
</tr>
<tr>
<td rowspan="4" align="right" colspan="1">IS</td>
<td align="left" rowspan="1" colspan="1">AGE</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.17</td>
<td align="char" char="." rowspan="1" colspan="1">0.904</td>
<td align="left" rowspan="1" colspan="1"></td>
<td align="char" char="." rowspan="1" colspan="1">0.09</td>
<td align="char" char="." rowspan="1" colspan="1">0.764</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">CVAGE</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.122</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>5.35</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.029</bold>
</td>
<td align="left" rowspan="1" colspan="1"></td>
<td align="char" char="." rowspan="1" colspan="1">0.01</td>
<td align="char" char="." rowspan="1" colspan="1">0.981</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">FORTYPE</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.197</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>8.61</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.007</bold>
</td>
<td align="left" rowspan="1" colspan="1"></td>
<td align="char" char="." rowspan="1" colspan="1">1.04</td>
<td align="char" char="." rowspan="1" colspan="1">0.316</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">CANCOV</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.150</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>6.53</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.017</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.324</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>10.11</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.002</bold>
</td>
</tr>
<tr>
<td rowspan="4" align="right" colspan="1">LS</td>
<td align="left" rowspan="1" colspan="1">AGE</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.4</td>
<td align="char" char="." rowspan="1" colspan="1">0.538</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.97</td>
<td align="char" char="." rowspan="1" colspan="1">0.340</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">CVAGE</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.0</td>
<td align="char" char="." rowspan="1" colspan="1">0.962</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.293</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>10.2</bold>
</td>
<td align="char" char="." rowspan="1" colspan="1">
<bold>0.003</bold>
</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">FORTYPE</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">1.6</td>
<td align="char" char="." rowspan="1" colspan="1">0.219</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">1.03</td>
<td align="char" char="." rowspan="1" colspan="1">0.322</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">CANCOV</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.7</td>
<td align="char" char="." rowspan="1" colspan="1">0.412</td>
<td align="left" rowspan="1" colspan="1">-</td>
<td align="char" char="." rowspan="1" colspan="1">0.21</td>
<td align="char" char="." rowspan="1" colspan="1">0.648</td>
</tr>
</tbody>
</table>
</alternatives>
<table-wrap-foot>
<fn id="t003fn001">
<p>AS: all plant species; ES: Early-successional species; IS: Intermediate-successional species; LS: Late-successional species. Significant effects (P < 0.05) are shown in bold. R
<sup>2</sup>
is the variance (%) explained by each significant explanatory variable.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>Secondary growth stands that had been established on abandoned lands, young stands, and uneven-aged stands had the highest plant species richness (
<xref rid="pone.0139031.g003" ref-type="fig">Fig 3</xref>
), which was negatively correlated with “CANCOV” (
<xref rid="pone.0139031.g004" ref-type="fig">Fig 4</xref>
). Using successional species groups, the same trends in species richness were apparent among ES and IS species (
<xref rid="pone.0139031.t003" ref-type="table">Table 3</xref>
; Figs
<xref rid="pone.0139031.g003" ref-type="fig">3</xref>
and
<xref rid="pone.0139031.g004" ref-type="fig">4</xref>
), although the effect of “AGE” among IS species was not statistically significant (
<xref rid="pone.0139031.t003" ref-type="table">Table 3</xref>
). None of the explanatory variables had a significant effect on the species richness among LS species (
<xref rid="pone.0139031.t003" ref-type="table">Table 3</xref>
). Among ES and IS species, evenness was affected by “CANCOV” and, among LS species, “CVAGE” had a significant effect on species evenness (
<xref rid="pone.0139031.t003" ref-type="table">Table 3</xref>
). Species evenness among LS species was significantly higher in even-aged stands than it was in uneven-aged stands (
<xref rid="pone.0139031.g003" ref-type="fig">Fig 3</xref>
). Furthermore, evenness was positively correlated with “CANCOV” among ES species, but was negatively correlated with “CANCOV” among IS species (
<xref rid="pone.0139031.g004" ref-type="fig">Fig 4</xref>
).</p>
<fig id="pone.0139031.g003" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0139031.g003</object-id>
<label>Fig 3</label>
<caption>
<title>Influence of predictor variables on plant species diversity in ten oak stands in the Central Pre-Pyrenees, Spain.</title>
<p>Species richness and evenness (AS: all plant species; ES: Early-successional species; IS: Intermediate-successional species; LS: Late-successional species) as influenced by stand age “AGE” (O: old stands; Y: young stands), age structure of stand “CVAGE” (EA: even-aged stands; UEA: Uneven-aged stands), and forest type “FORTYPE” (SF: secondary growth stands; CS: abandoned coppice stands). Boxes that have the same letter did not differ significantly based on ANCOVA.</p>
</caption>
<graphic xlink:href="pone.0139031.g003"></graphic>
</fig>
<fig id="pone.0139031.g004" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0139031.g004</object-id>
<label>Fig 4</label>
<caption>
<title>Effects of canopy cover on plant diversity in ten oak stands in the Central Pre-Pyrenees, Spain.</title>
<p>Canopy cover (CANCOV) and species richness and evenness (AS: all plant species; ES: Early-successional species; IS: Intermediate-successional species; LS: Late-successional species).</p>
</caption>
<graphic xlink:href="pone.0139031.g004"></graphic>
</fig>
</sec>
<sec id="sec011">
<title>Indicator species</title>
<p>Overall, 70 species were significant (
<italic>p</italic>
< 0.05) indicator species, and most (39 species) were indicative of young uneven-aged coppice stands, followed by young uneven-aged secondary growth stands (12), old even-aged secondary growth stands (7), old uneven-aged secondary growth stands (7), and young even-aged coppice stands (4) (
<xref rid="pone.0139031.t004" ref-type="table">Table 4</xref>
,
<xref rid="pone.0139031.s002" ref-type="supplementary-material">S2 Appendix</xref>
). One significant indicator species was found in old even-aged coppice stands. LS indicator species occurred in all of the forest classes except old even-aged secondary growth- and coppice-stands; however, young uneven-aged coppice stands harbored the highest number of LS indicator species (
<xref rid="pone.0139031.t004" ref-type="table">Table 4</xref>
).</p>
<table-wrap id="pone.0139031.t004" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0139031.t004</object-id>
<label>Table 4</label>
<caption>
<title>The number of early- (ES), intermediate- (IS), and late-successional (LS) Indicator Species identified in each forest class found in the ten
<italic>Quercus faginea</italic>
forest stands surveyed in the Central Pre-Pyrenees, Spain.</title>
</caption>
<alternatives>
<graphic id="pone.0139031.t004g" xlink:href="pone.0139031.t004"></graphic>
<table frame="hsides" rules="groups">
<colgroup span="1">
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
<col align="left" valign="middle" span="1"></col>
</colgroup>
<thead>
<tr>
<th align="left" rowspan="1" colspan="1">Forest class</th>
<th align="left" rowspan="1" colspan="1">ES</th>
<th align="left" rowspan="1" colspan="1">IS</th>
<th align="left" rowspan="1" colspan="1">LS</th>
<th align="left" rowspan="1" colspan="1">Total</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" rowspan="1" colspan="1">Old even-aged secondary growth stands</td>
<td align="left" rowspan="1" colspan="1">2</td>
<td align="left" rowspan="1" colspan="1">5</td>
<td align="left" rowspan="1" colspan="1">0</td>
<td align="left" rowspan="1" colspan="1">7</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">Old even-aged coppice stands</td>
<td align="left" rowspan="1" colspan="1">1</td>
<td align="left" rowspan="1" colspan="1">0</td>
<td align="left" rowspan="1" colspan="1">0</td>
<td align="left" rowspan="1" colspan="1">1</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">Old uneven-aged secondary growth stands</td>
<td align="left" rowspan="1" colspan="1">3</td>
<td align="left" rowspan="1" colspan="1">2</td>
<td align="left" rowspan="1" colspan="1">2</td>
<td align="left" rowspan="1" colspan="1">7</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">Young uneven-aged secondary growth stands</td>
<td align="left" rowspan="1" colspan="1">3</td>
<td align="left" rowspan="1" colspan="1">8</td>
<td align="left" rowspan="1" colspan="1">1</td>
<td align="left" rowspan="1" colspan="1">12</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">Young even-aged coppice stands</td>
<td align="left" rowspan="1" colspan="1">1</td>
<td align="left" rowspan="1" colspan="1">2</td>
<td align="left" rowspan="1" colspan="1">1</td>
<td align="left" rowspan="1" colspan="1">4</td>
</tr>
<tr>
<td align="left" rowspan="1" colspan="1">Young uneven aged coppice stands</td>
<td align="left" rowspan="1" colspan="1">32</td>
<td align="left" rowspan="1" colspan="1">4</td>
<td align="left" rowspan="1" colspan="1">3</td>
<td align="left" rowspan="1" colspan="1">39</td>
</tr>
</tbody>
</table>
</alternatives>
<table-wrap-foot>
<fn id="t004fn001">
<p>Indicator species are those that had significant (
<italic>p < 0</italic>
.
<italic>05</italic>
) indicator values in the multilevel pattern analysis.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
</sec>
<sec sec-type="conclusions" id="sec012">
<title>Discussion</title>
<p>Our study has demonstrated the importance of previous land-use and forest management in shaping the development of plant species assemblages and the richness and evenness of plant species. Evidently, human-induced disturbances can have a strong influence on plant communities in forest ecosystems, which have been reported elsewhere [
<xref rid="pone.0139031.ref008" ref-type="bibr">8</xref>
,
<xref rid="pone.0139031.ref009" ref-type="bibr">9</xref>
,
<xref rid="pone.0139031.ref019" ref-type="bibr">19</xref>
].</p>
<sec id="sec013">
<title>Plant species composition</title>
<p>The oak stands differed significantly in species composition, which underscores the importance of considering compositional differences in addition to differences in diversity parameters [
<xref rid="pone.0139031.ref045" ref-type="bibr">45</xref>
]. The evenness of all species collectively did not differ significantly among stand types, which indicated that the differences in species composition were not because of differences in species abundances; rather, they were mainly due to differences in species richness. Furthermore, the high overall richness in young stands (vs. old stands), secondary growth stands (vs. abandoned coppice stands), and uneven-aged stands (vs. even-aged stands) suggest that the compositional dissimilarities were not due to species turnover, only, but were the result of species turnover and nestedness [
<xref rid="pone.0139031.ref046" ref-type="bibr">46</xref>
]. That is, part of the compositional differentiation is due to species replacement and another part is due to differences in richness between stands; i.e., the richest stands have species that are not present in the poorest stands [
<xref rid="pone.0139031.ref046" ref-type="bibr">46</xref>
].</p>
</sec>
<sec id="sec014">
<title>Plant species diversity</title>
<p>Overall species richness was significantly higher in secondary growth stands than it was in abandoned coppice stands, which might have been because of the high number of ES and IS species in the secondary growth stands, which drove the dissimilarities that were apparent in plant community composition between secondary growth stands and abandoned coppice stands (see above). In stands that developed on abandoned agricultural terraces, the persistence of old-field species might have contributed to the high total richness in these stands [
<xref rid="pone.0139031.ref008" ref-type="bibr">8</xref>
]. The secondary growth stands in our study area were established on formerly abandoned lands (i.e., agricultural terraces and pastures) that were on relatively flat land, and some were in valley bottoms where the soils have large amounts of nutrients and water [
<xref rid="pone.0139031.ref029" ref-type="bibr">29</xref>
,
<xref rid="pone.0139031.ref047" ref-type="bibr">47</xref>
]. Those conditions strongly favor shade-intolerant, ruderal, and competitive species [
<xref rid="pone.0139031.ref004" ref-type="bibr">4</xref>
], which can increase total richness.</p>
<p>The large number of ES colonizers was responsible for the high species richness in young oak stands, which might have contributed to the differences in the plant species composition of young and old stands (see above). ES species are the first to colonize disrupted or damaged ecosystems [
<xref rid="pone.0139031.ref009" ref-type="bibr">9</xref>
,
<xref rid="pone.0139031.ref048" ref-type="bibr">48</xref>
]. In our study, the disappearance (i.e., competitive exclusion) of ES species in the transition from one successional stage to another might have been responsible for the comparatively low overall species richness in old (> 50 yr) stands. The richness of ES and IS species was higher in uneven-aged stands than it was in even-aged stands, which might explain the dissimilarities in the plant community composition of even-aged and uneven-aged stands (see above). Those dissimilarities might have occurred because of the high resource availability caused by the formation of gaps in the canopy of uneven-aged stands [
<xref rid="pone.0139031.ref014" ref-type="bibr">14</xref>
], which can provide conditions that favor the establishment of ES and IS species [
<xref rid="pone.0139031.ref049" ref-type="bibr">49</xref>
]. In contrast, in even-aged stands, the structure of the overstorey canopy, the amount of interspecific competition, and the resources available on the forest floor change more dramatically and phases of development occur more uniformly than they do in uneven-aged stands, which might reduce the richness of shade-intolerant species [
<xref rid="pone.0139031.ref017" ref-type="bibr">17</xref>
], most of which are ES and IS species.</p>
<p>Overall species richness and the species richness of ES and IS species were negatively correlated with the extent of the canopy cover. Many studies have demonstrated the negative effect of canopy closure on shade-intolerant species [
<xref rid="pone.0139031.ref050" ref-type="bibr">50</xref>
,
<xref rid="pone.0139031.ref051" ref-type="bibr">51</xref>
]. The reduction in the availability of light as a forest canopy closes can reduce species richness and limit the growth and survival of many species that became established during the stand initiation stage, and allow LS species to persist, only [
<xref rid="pone.0139031.ref050" ref-type="bibr">50</xref>
,
<xref rid="pone.0139031.ref052" ref-type="bibr">52</xref>
]. Furthermore, the high abundance of the competitor shrub
<italic>Buxus sempervirens</italic>
in stands that have closed canopies might out-compete other shade-intolerant species by reducing the amount of resources (i.e., light, soil nutrients, water) in the understorey (the abundance of this competitor species was positively associated with the extent of the canopy cover). In our study, the explanatory variables did not explain a significant amount of the variation in the richness of LS species, which indicates that the number of LS species did not differ significantly between stand types. Similarly, [
<xref rid="pone.0139031.ref023" ref-type="bibr">23</xref>
] found that forest stands that differed in management intensity did not differ in the number of LS species. In the oak forests in the Central Pre-Pyrenees, the extent of canopy cover and ES species evenness were positively correlated, perhaps, because canopy closure increases interspecific competition, which can lead to the exclusion of rare species and increase the mortality rate of highly abundant ES species. Probably, the reduction in sunlight caused by canopy closure contributed to a reduction in the evenness of IS species [
<xref rid="pone.0139031.ref004" ref-type="bibr">4</xref>
]. Furthermore, that reduction might have been due to the greater dominance of the competitor shrub
<italic>B</italic>
.
<italic>sempervirens</italic>
in stands that had closed canopies.</p>
<p>The evenness of LS species was highest in even-aged stands, which have a more homogeneous structure and are more uniformly limiting in shade and microhabitats than are uneven-aged stands [
<xref rid="pone.0139031.ref014" ref-type="bibr">14</xref>
,
<xref rid="pone.0139031.ref053" ref-type="bibr">53</xref>
]. Under those conditions, interspecific competition inhibits the establishment of shade-intolerant species, but favors the establishment of LS species that can thrive in those environments [
<xref rid="pone.0139031.ref050" ref-type="bibr">50</xref>
,
<xref rid="pone.0139031.ref054" ref-type="bibr">54</xref>
<xref rid="pone.0139031.ref056" ref-type="bibr">56</xref>
], which can increase the abundance of uncommon LS species and, thereby, increase species evenness. Other studies have suggested that facilitation or release from inhibition by preceding successional species, or intrinsic characteristics such as arrival time, growth rate, and the absence of direct interaction with early species might lead to the establishment of LS species [
<xref rid="pone.0139031.ref012" ref-type="bibr">12</xref>
].</p>
</sec>
<sec id="sec015">
<title>Indicator species</title>
<p>Indicator species analysis revealed that, in the absence of old uneven-aged coppice stands in our study area, young uneven-aged coppice stands have a high value for biodiversity conservation. In addition to harboring the highest number of significant indicator species, those stands included a sizeable portion the LS indicator species (e.g.,
<italic>Brachypodium sylvaticum</italic>
,
<italic>Lathyrus linifolius</italic>
, and
<italic>Ranunculus repens</italic>
). We predict that LS species will progressively replace the ES and IS indicator species (e.g.,
<italic>Brachypodium distachyon</italic>
,
<italic>Plantago lanceolata</italic>
,
<italic>Dactylis glomerata</italic>
) identified in our study. The chronic fluctuations in resources that occur in the successional process might lead to the reordering of plant species: species loss and colonization by species that are better suited to the new environment (in this case, LS species) [
<xref rid="pone.0139031.ref057" ref-type="bibr">57</xref>
]. The uneven-aged secondary growth stands, only, harbored significant LS indicator species, and the highest number were in old uneven-aged secondary growth stands (i.e.,
<italic>Cornus sanguinea</italic>
,
<italic>Rubia peregrine</italic>
). Variation in the ages of trees in uneven aged stands increases the variety of habitats, which permits the coexistence of species that have different requirements [
<xref rid="pone.0139031.ref014" ref-type="bibr">14</xref>
,
<xref rid="pone.0139031.ref015" ref-type="bibr">15</xref>
]; however, the ability of those stands to provide habitat for LS species makes them very important for biodiversity conservation.</p>
</sec>
<sec id="sec016">
<title>Implications for biodiversity conservation</title>
<p>Agriculture, livestock grazing, and forest coppicing, which were once common types of land management in the Mediterranean Basin, were abandoned in many places in the late 19th C. and 20th C. After the abandonment of marginal agricultural lands, pastures, and coppices, forest stands that differed in land-use histories and structural properties developed. The coexistence of different types of stands can provide heterogeneous habitats that maximize biodiversity conservation at the regional scale [
<xref rid="pone.0139031.ref018" ref-type="bibr">18</xref>
]. Furthermore, although our study focused on the presence of plant species in previously disturbed oak forests, we recognize that these forests provide vital resources for fauna, ecosystem services, and forest products [
<xref rid="pone.0139031.ref058" ref-type="bibr">58</xref>
]. Therefore, the conservation of those oak stands might provide ecosystem and economic benefits (e.g., ecotourism) and should be promoted through government incentives and land-use regulations. The uneven-aged oak stands and, specifically, the abandoned uneven-aged coppice stands seem to represent a progression in the transition towards native forests, which increases their importance from a conservation perspective.</p>
</sec>
</sec>
<sec sec-type="supplementary-material" id="sec017">
<title>Supporting Information</title>
<supplementary-material content-type="local-data" id="pone.0139031.s001">
<label>S1 Appendix</label>
<caption>
<title>Plant species abundance.</title>
<p>Plant species abundance (mean ± SD) in the 10 oak forests surveyed in the Central Pre-Pyrenees, Spain. Successional status: ES, Early-successional species; IS, Intermediate-successional species; LS, Late-successional species.</p>
<p>(XLSX)</p>
</caption>
<media xlink:href="pone.0139031.s001.xlsx">
<caption>
<p>Click here for additional data file.</p>
</caption>
</media>
</supplementary-material>
<supplementary-material content-type="local-data" id="pone.0139031.s002">
<label>S2 Appendix</label>
<caption>
<title>Multilevel pattern analysis.</title>
<p>A test of the relationship between plant species and forest class in the 10 oak forests surveyed in the Central Pre-Pyrenees, Spain.</p>
<p>(DOCX)</p>
</caption>
<media xlink:href="pone.0139031.s002.docx">
<caption>
<p>Click here for additional data file.</p>
</caption>
</media>
</supplementary-material>
</sec>
</body>
<back>
<ack>
<p>We thank Arben Q. Alla, Gabriel Sangüesa-Barreda, Guillermo C. Bueno, Benjamin Komac, Maite Gartzia, Hugo Saiz, and Paloma Nuche for assistance in the field. Constructive comments from two anonymous reviewers and Bruce MacWhirter improved the manuscript. Y.K. was funded by a MAEC-AECID grant from the Spanish Agency for International Cooperation and Development, and A.F. was supported by a JAE-doc postdoctoral contract from the framework ‘‘Junta para la Ampliación de Estudios” (Spanish Ministry of Economy and Competitiveness), which was co-financed by the European Social Fund. This study was part of the research project CGL2011-27259 (Spanish Ministry of Economy and Competitiveness and Innovation), which was co-financed by the FEDER.</p>
</ack>
<ref-list>
<title>References</title>
<ref id="pone.0139031.ref001">
<label>1</label>
<mixed-citation publication-type="journal">
<name>
<surname>Barbero</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Bonin</surname>
<given-names>G</given-names>
</name>
,
<name>
<surname>Loisel</surname>
<given-names>R</given-names>
</name>
,
<name>
<surname>Quézel</surname>
<given-names>P</given-names>
</name>
.
<article-title>Changes and disturbances of forest ecosystems caused by human activities in the western part of the mediterranean basin</article-title>
.
<source>Vegetatio</source>
.
<year>1990</year>
;
<volume>87</volume>
:
<fpage>151</fpage>
<lpage>173</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref002">
<label>2</label>
<mixed-citation publication-type="journal">
<name>
<surname>Bengtsson</surname>
<given-names>J</given-names>
</name>
,
<name>
<surname>Nilsson</surname>
<given-names>SG</given-names>
</name>
,
<name>
<surname>Franc</surname>
<given-names>A</given-names>
</name>
,
<name>
<surname>Menozzi</surname>
<given-names>P</given-names>
</name>
.
<article-title>Biodiversity, disturbances, ecosystem function and management of European forests</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2000</year>
;
<volume>132</volume>
:
<fpage>39</fpage>
<lpage>50</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref003">
<label>3</label>
<mixed-citation publication-type="journal">
<name>
<surname>Vanbergen</surname>
<given-names>AJ</given-names>
</name>
,
<name>
<surname>Woodcock</surname>
<given-names>BA</given-names>
</name>
,
<name>
<surname>Watt</surname>
<given-names>AD</given-names>
</name>
,
<name>
<surname>Niemela</surname>
<given-names>J</given-names>
</name>
.
<article-title>Effect of land-use heterogeneity on carabid communities at the landscape scale</article-title>
.
<source>Ecography</source>
.
<year>2005</year>
;
<volume>1</volume>
:
<fpage>3</fpage>
<lpage>16</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref004">
<label>4</label>
<mixed-citation publication-type="journal">
<name>
<surname>Paillet</surname>
<given-names>Y</given-names>
</name>
,
<name>
<surname>Bergès</surname>
<given-names>L</given-names>
</name>
,
<name>
<surname>Hjältén</surname>
<given-names>J</given-names>
</name>
,
<name>
<surname>Odor</surname>
<given-names>P</given-names>
</name>
,
<name>
<surname>Avon</surname>
<given-names>C</given-names>
</name>
,
<name>
<surname>Bernhardt-Römermann</surname>
<given-names>M</given-names>
</name>
,
<etal>et al</etal>
<article-title>Biodiversity differences between managed and unmanaged forests: meta-analysis of species richness in Europe</article-title>
.
<source>Conservation biology</source>
.
<year>2010</year>
;
<volume>24</volume>
:
<fpage>101</fpage>
<lpage>112</lpage>
.
<comment>doi:
<ext-link ext-link-type="uri" xlink:href="http://dx.doi.org/10.1111/j.1523-1739.2009.01399.x">10.1111/j.1523-1739.2009.01399.x</ext-link>
</comment>
<pub-id pub-id-type="pmid">20121845</pub-id>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref005">
<label>5</label>
<mixed-citation publication-type="journal">
<name>
<surname>Mather</surname>
<given-names>AS</given-names>
</name>
,
<name>
<surname>Fairbairn</surname>
<given-names>J</given-names>
</name>
,
<name>
<surname>Needle</surname>
<given-names>CL</given-names>
</name>
.
<article-title>The course and drivers of the forest transition: the case of France</article-title>
.
<source>Journal of Rural Studies</source>
.
<year>1999</year>
;
<volume>15</volume>
:
<fpage>65</fpage>
<lpage>90</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref006">
<label>6</label>
<mixed-citation publication-type="journal">
<name>
<surname>Sciama</surname>
<given-names>D</given-names>
</name>
,
<name>
<surname>Augusto</surname>
<given-names>L</given-names>
</name>
,
<name>
<surname>Dupouey</surname>
<given-names>J-L</given-names>
</name>
,
<name>
<surname>Gonzalez</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Moares Domínguez</surname>
<given-names>C</given-names>
</name>
.
<article-title>Floristic and ecological differences between recent and ancient forests growing on non-acidic soils</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2009</year>
;
<volume>258</volume>
:
<fpage>600</fpage>
<lpage>608</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref007">
<label>7</label>
<mixed-citation publication-type="journal">
<name>
<surname>Verheyen</surname>
<given-names>K</given-names>
</name>
,
<name>
<surname>Bossuyt</surname>
<given-names>B</given-names>
</name>
,
<name>
<surname>Hermy</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Tack</surname>
<given-names>G</given-names>
</name>
.
<article-title>The land use history (1278–1990) of a mixed hardwood forest in western Belgium and its relationship with chemical soil characteristics</article-title>
.
<source>Journal of Biogeography</source>
.
<year>1999</year>
;
<volume>26</volume>
:
<fpage>1115</fpage>
<lpage>1128</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref008">
<label>8</label>
<mixed-citation publication-type="journal">
<name>
<surname>Flinn</surname>
<given-names>KM</given-names>
</name>
,
<name>
<surname>Vellend</surname>
<given-names>M</given-names>
</name>
.
<article-title>Recovery of forest plant communities in post-agricultural landscapes</article-title>
.
<source>Frontiers in Ecology and the Environment</source>
.
<year>2005</year>
;
<volume>3</volume>
:
<fpage>243</fpage>
<lpage>250</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref009">
<label>9</label>
<mixed-citation publication-type="journal">
<name>
<surname>Hermy</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Verheyen</surname>
<given-names>K</given-names>
</name>
.
<article-title>Legacies of the past in the present-day forest biodiversity: a review of past land-use effects on forest plant species composition and diversity</article-title>
.
<source>Ecological Research</source>
.
<year>2007</year>
;
<volume>22</volume>
:
<fpage>361</fpage>
<lpage>371</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref010">
<label>10</label>
<mixed-citation publication-type="journal">
<name>
<surname>Matuszkiewicz</surname>
<given-names>JM</given-names>
</name>
,
<name>
<surname>Kowalska</surname>
<given-names>A</given-names>
</name>
,
<name>
<surname>Kozłowska</surname>
<given-names>A</given-names>
</name>
,
<name>
<surname>Roo-Zielińska</surname>
<given-names>E</given-names>
</name>
,
<name>
<surname>Solon</surname>
<given-names>J</given-names>
</name>
.
<article-title>Differences in plant-species composition, richness and community structure in ancient and post-agricultural pine forests in central Poland</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2013</year>
;
<volume>310</volume>
:
<fpage>567</fpage>
<lpage>576</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref011">
<label>11</label>
<mixed-citation publication-type="journal">
<name>
<surname>Lasanta</surname>
<given-names>T</given-names>
</name>
,
<name>
<surname>Arnáez</surname>
<given-names>J</given-names>
</name>
,
<name>
<surname>Errea</surname>
<given-names>MP</given-names>
</name>
,
<name>
<surname>Ortigosa</surname>
<given-names>L</given-names>
</name>
,
<name>
<surname>Ruiz-Flaño</surname>
<given-names>P</given-names>
</name>
.
<article-title>Mountain pastures, environmental degradation, and landscape remediation: The example of a Mediterranean policy initiative</article-title>
.
<source>Applied Geography</source>
.
<year>2009</year>
;
<volume>29</volume>
:
<fpage>308</fpage>
<lpage>319</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref012">
<label>12</label>
<mixed-citation publication-type="book">
<name>
<surname>Carson</surname>
<given-names>WP</given-names>
</name>
,
<name>
<surname>Schnitzer</surname>
<given-names>SA</given-names>
</name>
.
<source>Tropical forest community ecology</source>
.
<publisher-loc>Oxford</publisher-loc>
:
<publisher-name>Wiley-Blackell</publisher-name>
<year>2008</year>
<fpage>491</fpage>
p.</mixed-citation>
</ref>
<ref id="pone.0139031.ref013">
<label>13</label>
<mixed-citation publication-type="journal">
<name>
<surname>Gehring</surname>
<given-names>C</given-names>
</name>
,
<name>
<surname>Denich</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Vlek</surname>
<given-names>PLG</given-names>
</name>
.
<article-title>Resilience of secondary forest regrowth after slash-and-burn agriculture in central Amazonia</article-title>
.
<source>Journal of Tropical Ecology</source>
.
<year>2005</year>
;
<volume>21</volume>
:
<fpage>519</fpage>
<lpage>527</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref014">
<label>14</label>
<mixed-citation publication-type="journal">
<name>
<surname>Duguid</surname>
<given-names>MC</given-names>
</name>
,
<name>
<surname>Ashton</surname>
<given-names>MS</given-names>
</name>
.
<article-title>A meta-analysis of the effect of forest management for timber on understory plant species diversity in temperate forests</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2013</year>
;
<volume>303</volume>
:
<fpage>81</fpage>
<lpage>90</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref015">
<label>15</label>
<mixed-citation publication-type="journal">
<name>
<surname>Smith</surname>
<given-names>KJ</given-names>
</name>
,
<name>
<surname>Keeton</surname>
<given-names>WS</given-names>
</name>
,
<name>
<surname>Twery</surname>
<given-names>MJ</given-names>
</name>
,
<name>
<surname>Tobi</surname>
<given-names>DR</given-names>
</name>
.
<article-title>Understory plant responses to uneven-aged forestry alternatives in northern hardwood—conifer forests</article-title>
.
<source>Canadian Journal of Forest Research</source>
.
<year>2008</year>
;
<volume>38</volume>
:
<fpage>1303</fpage>
<lpage>1318</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref016">
<label>16</label>
<mixed-citation publication-type="journal">
<name>
<surname>Berhane</surname>
<given-names>A</given-names>
</name>
,
<name>
<surname>Totland</surname>
<given-names>Ø</given-names>
</name>
,
<name>
<surname>Moe</surname>
<given-names>SR</given-names>
</name>
.
<article-title>Woody plant assemblages in isolated forest patches in a semiarid agricultural matrix</article-title>
.
<source>Biodiversity and Conservation</source>
.
<year>2013</year>
;
<volume>22</volume>
:
<fpage>2519</fpage>
<lpage>2535</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref017">
<label>17</label>
<mixed-citation publication-type="book">
<name>
<surname>Oliver</surname>
<given-names>CD</given-names>
</name>
,
<name>
<surname>Larson</surname>
<given-names>BC</given-names>
</name>
.
<source>Forest stand dynamics</source>
.
<publisher-loc>New York</publisher-loc>
:
<publisher-name>John Wiley&Sons</publisher-name>
<year>1996</year>
<fpage>520</fpage>
p.</mixed-citation>
</ref>
<ref id="pone.0139031.ref018">
<label>18</label>
<mixed-citation publication-type="journal">
<name>
<surname>Kouba</surname>
<given-names>Y</given-names>
</name>
,
<name>
<surname>Martínez-García</surname>
<given-names>F</given-names>
</name>
,
<name>
<surname>de Frutos</surname>
<given-names>A</given-names>
</name>
,
<name>
<surname>Alados</surname>
<given-names>C</given-names>
</name>
.
<article-title>Plant β-diversity in human-altered forest ecosystems: the importance of the structural, spatial, and topographical characteristics of stands in patterning plant species assemblages</article-title>
.
<source>European Journal of Forest Research</source>
.
<year>2014</year>
;
<volume>133</volume>
:
<fpage>1057</fpage>
<lpage>1072</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref019">
<label>19</label>
<mixed-citation publication-type="journal">
<name>
<surname>Baeten</surname>
<given-names>L</given-names>
</name>
,
<name>
<surname>Hermy</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Van Daele</surname>
<given-names>S</given-names>
</name>
,
<name>
<surname>Verheyen</surname>
<given-names>K</given-names>
</name>
.
<article-title>Unexpected understorey community development after 30 years in ancient and post-agricultural forests</article-title>
.
<source>Journal of Ecology</source>
.
<year>2010</year>
;
<volume>98</volume>
:
<fpage>1447</fpage>
<lpage>1453</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref020">
<label>20</label>
<mixed-citation publication-type="journal">
<name>
<surname>De Frenne</surname>
<given-names>P</given-names>
</name>
,
<name>
<surname>Baeten</surname>
<given-names>L</given-names>
</name>
,
<name>
<surname>Graae</surname>
<given-names>BJ</given-names>
</name>
,
<name>
<surname>Brunet</surname>
<given-names>J</given-names>
</name>
,
<name>
<surname>Wulf</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Orczewska</surname>
<given-names>A</given-names>
</name>
,
<etal>et al</etal>
<article-title>Interregional variation in the floristic recovery of post-agricultural forests</article-title>
.
<source>Journal of Ecology</source>
.
<year>2010</year>
;
<volume>99</volume>
:
<fpage>600</fpage>
<lpage>609</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref021">
<label>21</label>
<mixed-citation publication-type="journal">
<name>
<surname>Halpern</surname>
<given-names>CB</given-names>
</name>
,
<name>
<surname>Spies</surname>
<given-names>TA</given-names>
</name>
.
<article-title>Plant species diversity in natural and managed forests of the Pacific Northwest</article-title>
.
<source>Ecological Applications</source>
.
<year>1995</year>
;
<volume>5</volume>
:
<fpage>913</fpage>
<lpage>934</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref022">
<label>22</label>
<mixed-citation publication-type="journal">
<name>
<surname>Okland</surname>
<given-names>T</given-names>
</name>
,
<name>
<surname>Rydgren</surname>
<given-names>K</given-names>
</name>
,
<name>
<surname>Halvorsen</surname>
<given-names>R</given-names>
</name>
,
<name>
<surname>Storaunet</surname>
<given-names>K</given-names>
</name>
,
<name>
<surname>Rolstad</surname>
<given-names>J</given-names>
</name>
.
<article-title>Variation in environmental conditions, understorey species number, abundance and composition among natural and managed Picea abies forest stands</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2003</year>
;
<volume>177</volume>
:
<fpage>17</fpage>
<lpage>37</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref023">
<label>23</label>
<mixed-citation publication-type="journal">
<name>
<surname>Seiwa</surname>
<given-names>K</given-names>
</name>
,
<name>
<surname>Etoh</surname>
<given-names>Y</given-names>
</name>
,
<name>
<surname>Hisita</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Masaka</surname>
<given-names>K</given-names>
</name>
,
<name>
<surname>Imaji</surname>
<given-names>A</given-names>
</name>
,
<name>
<surname>Ueno</surname>
<given-names>N</given-names>
</name>
.
<article-title>Roles of thinning intensity in hardwood recruitment and diversity in a conifer, Criptomeria japonica plantation: A 5-year demographic study</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2012</year>
;
<volume>269</volume>
:
<fpage>177</fpage>
<lpage>187</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref024">
<label>24</label>
<mixed-citation publication-type="journal">
<name>
<surname>Battles</surname>
<given-names>JJ</given-names>
</name>
,
<name>
<surname>Shlisky</surname>
<given-names>AJ</given-names>
</name>
,
<name>
<surname>Barrett</surname>
<given-names>RH</given-names>
</name>
,
<name>
<surname>Heald</surname>
<given-names>RC</given-names>
</name>
,
<name>
<surname>Allen-Diaz</surname>
<given-names>BH</given-names>
</name>
.
<article-title>The effects of forest management on plant species diversity in a Sierran conifer forest</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2001</year>
;
<volume>146</volume>
:
<fpage>211</fpage>
<lpage>222</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref025">
<label>25</label>
<mixed-citation publication-type="journal">
<name>
<surname>Dufrene</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Legendre</surname>
<given-names>P</given-names>
</name>
.
<article-title>Species assemblages and indicator species: the need for a flexible asymmetrical approach</article-title>
.
<source>Ecological Monographs</source>
.
<year>1997</year>
;
<volume>67</volume>
:
<fpage>345</fpage>
<lpage>366</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref026">
<label>26</label>
<mixed-citation publication-type="journal">
<name>
<surname>De Cáceres</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Font</surname>
<given-names>X</given-names>
</name>
,
<name>
<surname>Vicente</surname>
<given-names>P</given-names>
</name>
,
<name>
<surname>Oliva</surname>
<given-names>F</given-names>
</name>
.
<article-title>Numerical reproduction of traditional classifications and automatic vegetation identification</article-title>
.
<source>Journal of Vegetation Science</source>
.
<year>2009</year>
;
<volume>20</volume>
:
<fpage>620</fpage>
<lpage>628</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref027">
<label>27</label>
<mixed-citation publication-type="journal">
<name>
<surname>Farwig</surname>
<given-names>N</given-names>
</name>
,
<name>
<surname>Sajita</surname>
<given-names>N</given-names>
</name>
,
<name>
<surname>Böhning-Gaese</surname>
<given-names>K</given-names>
</name>
.
<article-title>High seedling recruitment of indigenous tree species in forest plantations in Kakamega Forest, western Kenya</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2009</year>
;
<volume>257</volume>
:
<fpage>143</fpage>
<lpage>150</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref028">
<label>28</label>
<mixed-citation publication-type="journal">
<name>
<surname>Peterken</surname>
<given-names>GF</given-names>
</name>
.
<article-title>A method for assessing woodland flora for conservation using indicator species</article-title>
.
<source>Biological Conservation</source>
.
<year>1974</year>
;
<volume>6</volume>
:
<fpage>239</fpage>
<lpage>245</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref029">
<label>29</label>
<mixed-citation publication-type="journal">
<name>
<surname>Kouba</surname>
<given-names>Y</given-names>
</name>
,
<name>
<surname>Camarero</surname>
<given-names>JJ</given-names>
</name>
,
<name>
<surname>Alados</surname>
<given-names>CL</given-names>
</name>
.
<article-title>Roles of land-use and climate change on the establishment and regeneration dynamics of Mediterranean semi-deciduous oak forests</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2012</year>
;
<volume>274</volume>
:
<fpage>143</fpage>
<lpage>150</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref030">
<label>30</label>
<mixed-citation publication-type="journal">
<name>
<surname>Kouba</surname>
<given-names>Y</given-names>
</name>
,
<name>
<surname>Alados</surname>
<given-names>CL</given-names>
</name>
.
<article-title>Spatio-temporal dynamics of Quercus faginea forests in the Spanish Central Pre-Pyrenees</article-title>
.
<source>European Journal of Forest Research</source>
.
<year>2012</year>
;
<volume>131</volume>
:
<fpage>369</fpage>
<lpage>379</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref031">
<label>31</label>
<mixed-citation publication-type="journal">
<name>
<surname>Goodall</surname>
<given-names>DW</given-names>
</name>
.
<article-title>Some considerations in the use of point quadrats for the analysis of vegetation</article-title>
.
<source>Australian Journal of Scientific Research Ser B: Biological Sciences</source>
.
<year>1952</year>
;
<volume>5</volume>
:
<fpage>1</fpage>
<lpage>41</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref032">
<label>32</label>
<mixed-citation publication-type="journal">
<name>
<surname>Alados</surname>
<given-names>CL</given-names>
</name>
,
<name>
<surname>Navarro</surname>
<given-names>T</given-names>
</name>
,
<name>
<surname>Komac</surname>
<given-names>B</given-names>
</name>
,
<name>
<surname>Pascual</surname>
<given-names>V</given-names>
</name>
,
<name>
<surname>Martinez</surname>
<given-names>F</given-names>
</name>
,
<name>
<surname>Cabezudo</surname>
<given-names>B</given-names>
</name>
,
<etal>et al</etal>
<article-title>Do vegetation patch spatial patterns disrupt the spatial organization of plant species?</article-title>
<source>Ecological Complexity</source>
.
<year>2009</year>
;
<volume>6</volume>
:
<fpage>197</fpage>
<lpage>207</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref033">
<label>33</label>
<mixed-citation publication-type="book">
<name>
<surname>Castroviejo</surname>
<given-names>S</given-names>
</name>
,
<name>
<surname>Laínz</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>González</surname>
<given-names>GL</given-names>
</name>
,
<name>
<surname>Montserrat</surname>
<given-names>PF</given-names>
</name>
.
<name>
<surname>Flora</surname>
<given-names>iberica</given-names>
</name>
.
<source>Plantas vasculares de la Península Ibérica e Islas Baleares</source>
.
<volume>vols 1–8</volume>
,
<fpage>10</fpage>
<lpage>15</lpage>
,
<fpage>17</fpage>
<lpage>18</lpage>
,
<fpage>21</fpage>
<publisher-loc>Madrid</publisher-loc>
:
<publisher-name>Real Jardín Botánico, CSIC</publisher-name>
<year>2012</year>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref034">
<label>34</label>
<mixed-citation publication-type="journal">
<name>
<surname>Barbier</surname>
<given-names>S</given-names>
</name>
,
<name>
<surname>Gosselin</surname>
<given-names>F</given-names>
</name>
,
<name>
<surname>Balandier</surname>
<given-names>P</given-names>
</name>
.
<article-title>Influence of tree species on understory vegetation diversity and mechanisms involved—A critical review for temperate and boreal forests</article-title>
.
<source>Forest Ecology and Management</source>
.
<year>2008</year>
;
<volume>254</volume>
:
<fpage>1</fpage>
<lpage>15</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref035">
<label>35</label>
<mixed-citation publication-type="journal">
<name>
<surname>Ramovs</surname>
<given-names>BV</given-names>
</name>
,
<name>
<surname>Roberts</surname>
<given-names>MR</given-names>
</name>
.
<article-title>Response of plant functional groups within plantations and naturally regenerated forests in southern New Brunswick, Canada</article-title>
.
<source>Canadian Journal of Forest Research</source>
.
<year>2005</year>
;
<volume>35</volume>
:
<fpage>1261</fpage>
<lpage>1276</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref036">
<label>36</label>
<mixed-citation publication-type="book">
<name>
<surname>Montserrat</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>José-María</surname>
</name>
.
<source>Flora y Vegetación de la Sierra de Guara (prepirineo aragonés)</source>
.
<publisher-loc>Zaragoza</publisher-loc>
:
<publisher-name>Diputación General de Aragón</publisher-name>
<year>1986</year>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref037">
<label>37</label>
<mixed-citation publication-type="book">
<name>
<surname>Peinado</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Rivas-Martinez</surname>
</name>
.
<chapter-title>La vegetación de España</chapter-title>
<source>Colección Aula Abierta</source>
.
<publisher-loc>Madrid</publisher-loc>
:
<publisher-name>Universidad de Alcalá de Henares</publisher-name>
<year>1987</year>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref038">
<label>38</label>
<mixed-citation publication-type="other">Sainz H, Morla C, Costa M. Los Bosques Ibéricos. Una interpretación Geobotánica. Madrid Editorial Planeta. 1997</mixed-citation>
</ref>
<ref id="pone.0139031.ref039">
<label>39</label>
<mixed-citation publication-type="book">
<name>
<surname>Villar</surname>
<given-names>L</given-names>
</name>
,
<name>
<surname>Sesé</surname>
<given-names>JA</given-names>
</name>
,
<name>
<surname>Ferrández</surname>
<given-names>JV</given-names>
</name>
.
<source>Flora del Pirineo aragonés I</source>
.
<publisher-loc>Huesca</publisher-loc>
:
<publisher-name>Consejo de Protección de la Naturaleza de Aragón; Instituto de Estudios Altoaragoneses</publisher-name>
<year>2001</year>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref040">
<label>40</label>
<mixed-citation publication-type="book">
<name>
<surname>Villar</surname>
<given-names>L</given-names>
</name>
,
<name>
<surname>Sesé</surname>
<given-names>JA</given-names>
</name>
,
<name>
<surname>Ferrández</surname>
<given-names>JV</given-names>
</name>
.
<source>Flora del Pirineo aragonés II</source>
.
<publisher-loc>Huesca</publisher-loc>
:
<publisher-name>Consejo de Protección de la Naturaleza de Aragón; Instituto de Estudios Altoaragoneses</publisher-name>
<year>2003</year>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref041">
<label>41</label>
<mixed-citation publication-type="book">
<collab>Team RDC</collab>
.
<source>R: A Language and Environment for Statistical Computing</source>
.
<publisher-loc>Vienna, Austria</publisher-loc>
:
<publisher-name>R Foundation for Statistical Computing</publisher-name>
<year>2015</year>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref042">
<label>42</label>
<mixed-citation publication-type="other">Oksanen J, Blanchet G, Kindt R, Legendre P, Minchin PR, O'Hara RB, et al. vegan: Community Ecology Package. R package version 3.0–0. Available:
<ext-link ext-link-type="uri" xlink:href="http://cran.r-project.org/package=vegan">http://cran.r-project.org/package=vegan</ext-link>
. 2012</mixed-citation>
</ref>
<ref id="pone.0139031.ref043">
<label>43</label>
<mixed-citation publication-type="journal">
<name>
<surname>Pinheiro</surname>
<given-names>J</given-names>
</name>
,
<name>
<surname>Bates</surname>
<given-names>D</given-names>
</name>
,
<name>
<surname>DedRoy</surname>
<given-names>S</given-names>
</name>
,
<name>
<surname>Sarkar</surname>
<given-names>D</given-names>
</name>
,
<name>
<surname>R-core</surname>
</name>
.
<article-title>nlme: Linear and Nonlinear Mixed Effects Models</article-title>
.
<source>R package version 3.1–111</source>
.
<year>2013</year>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref044">
<label>44</label>
<mixed-citation publication-type="journal">
<name>
<surname>De Cáceres</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Legendre</surname>
<given-names>P</given-names>
</name>
,
<name>
<surname>Wiser</surname>
<given-names>SK</given-names>
</name>
,
<name>
<surname>Brotons</surname>
<given-names>L</given-names>
</name>
.
<article-title>Using species combinations in indicator value analyses</article-title>
.
<source>Methods in Ecology and Evolution</source>
.
<year>2012</year>
;
<volume>3</volume>
:
<fpage>973</fpage>
<lpage>982</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref045">
<label>45</label>
<mixed-citation publication-type="journal">
<name>
<surname>Calviño-Cancela</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Rubido-Bará</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>van Etten</surname>
<given-names>EJB</given-names>
</name>
.
<article-title>Do eucalypt plantations provide habitat for native forest biodiversity?</article-title>
<source>Forest Ecology and Management</source>
.
<year>2012</year>
;
<volume>270</volume>
:
<fpage>153</fpage>
<lpage>162</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref046">
<label>46</label>
<mixed-citation publication-type="journal">
<name>
<surname>Baselga</surname>
<given-names>A</given-names>
</name>
.
<article-title>The relationship between species replacement, dissimilarity derived from nestedness, and nestedness</article-title>
.
<source>Global Ecology and Biogeography</source>
.
<year>2012</year>
;
<volume>21</volume>
:
<fpage>1223</fpage>
<lpage>1232</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref047">
<label>47</label>
<mixed-citation publication-type="journal">
<name>
<surname>Lasanta</surname>
<given-names>T</given-names>
</name>
,
<name>
<surname>García-Ruiz</surname>
<given-names>JM</given-names>
</name>
,
<name>
<surname>Pérez-Rontomé</surname>
<given-names>C</given-names>
</name>
,
<name>
<surname>Sancho-Marcén</surname>
<given-names>C</given-names>
</name>
.
<article-title>Runoff and sediment yield in a semi-arid environment: the effect of land management after farmland abandonment</article-title>
.
<source>Catena</source>
.
<year>2000</year>
;
<volume>38</volume>
:
<fpage>265</fpage>
<lpage>278</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref048">
<label>48</label>
<mixed-citation publication-type="journal">
<name>
<surname>Schmiedinger</surname>
<given-names>A</given-names>
</name>
,
<name>
<surname>Kreyling</surname>
<given-names>J</given-names>
</name>
,
<name>
<surname>Steinbauer</surname>
<given-names>MJ</given-names>
</name>
,
<name>
<surname>Macdonald</surname>
<given-names>SE</given-names>
</name>
,
<name>
<surname>Jentsch</surname>
<given-names>A</given-names>
</name>
,
<name>
<surname>Beierkuhnlein</surname>
<given-names>C</given-names>
</name>
.
<article-title>A continental comparison indicates long-term effects of forest management on understory diversity in coniferous forests</article-title>
.
<source>Canadian Journal of Forest Research</source>
.
<year>2012</year>
;
<volume>42</volume>
:
<fpage>1239</fpage>
<lpage>1252</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref049">
<label>49</label>
<mixed-citation publication-type="journal">
<name>
<surname>Fahey</surname>
<given-names>RT</given-names>
</name>
,
<name>
<surname>Puettmann</surname>
<given-names>KJ</given-names>
</name>
.
<article-title>Ground-layer disturbance and initial conditions influence gap partitioning of understorey vegetation</article-title>
.
<source>Journal of Ecology</source>
.
<year>2007</year>
;
<volume>95</volume>
:
<fpage>1098</fpage>
<lpage>1109</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref050">
<label>50</label>
<mixed-citation publication-type="journal">
<name>
<surname>Hart</surname>
<given-names>SA</given-names>
</name>
,
<name>
<surname>Chen</surname>
<given-names>HYH</given-names>
</name>
.
<article-title>Understory Vegetation Dynamics of North American Boreal Forests</article-title>
.
<source>Critical Reviews in Plant Sciences</source>
.
<year>2006</year>
;
<volume>25</volume>
:
<fpage>381</fpage>
<lpage>397</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref051">
<label>51</label>
<mixed-citation publication-type="journal">
<name>
<surname>Vockenhuber</surname>
<given-names>EA</given-names>
</name>
,
<name>
<surname>Scherber</surname>
<given-names>C</given-names>
</name>
,
<name>
<surname>Langenbruch</surname>
<given-names>C</given-names>
</name>
,
<name>
<surname>Meißner</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Seidel</surname>
<given-names>D</given-names>
</name>
,
<name>
<surname>Tscharntke</surname>
<given-names>T</given-names>
</name>
.
<article-title>Tree diversity and environmental context predict herb species richness and cover in Germany's largest connected deciduous forest</article-title>
.
<source>Perspectives in Plant Ecology, Evolution and Systematics</source>
.
<year>2011</year>
;
<volume>13</volume>
:
<fpage>111</fpage>
<lpage>119</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref052">
<label>52</label>
<mixed-citation publication-type="journal">
<name>
<surname>Breugel</surname>
<given-names>MV</given-names>
</name>
,
<name>
<surname>Bongers</surname>
<given-names>F</given-names>
</name>
,
<name>
<surname>Martínez-Ramos</surname>
<given-names>M</given-names>
</name>
.
<article-title>Species Dynamics During Early Secondary Forest Succession: Recruitment, Mortality and Species Turnover</article-title>
.
<source>Biotropica</source>
.
<year>2007</year>
;
<volume>35</volume>
:
<fpage>610</fpage>
<lpage>619</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref053">
<label>53</label>
<mixed-citation publication-type="journal">
<name>
<surname>Bartels</surname>
<given-names>SF</given-names>
</name>
,
<name>
<surname>Chen</surname>
<given-names>HYH</given-names>
</name>
.
<article-title>Is understory plant species diversity driven by resource quantity or resource heterogeneity?</article-title>
<source>Ecology</source>
.
<year>2010</year>
;
<volume>91</volume>
:
<fpage>1931</fpage>
<lpage>1938</lpage>
.
<pub-id pub-id-type="pmid">20715612</pub-id>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref054">
<label>54</label>
<mixed-citation publication-type="journal">
<name>
<surname>Bartemucci</surname>
<given-names>P</given-names>
</name>
,
<name>
<surname>Messier</surname>
<given-names>C</given-names>
</name>
,
<name>
<surname>Canham</surname>
<given-names>CD</given-names>
</name>
.
<article-title>Overstory influences on light attenuation patterns and understory plant community diversity and composition in southern boreal forests of Quebec</article-title>
.
<source>Canadian Journal of Forest Research</source>
.
<year>2006</year>
;
<volume>36</volume>
:
<fpage>2065</fpage>
<lpage>2079</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref055">
<label>55</label>
<mixed-citation publication-type="journal">
<name>
<surname>Messier</surname>
<given-names>C</given-names>
</name>
,
<name>
<surname>Parent</surname>
<given-names>S</given-names>
</name>
,
<name>
<surname>Bergeron</surname>
<given-names>Y</given-names>
</name>
.
<article-title>Effects of overstory and understory vegetation on the understory light environment in mixed boreal forests</article-title>
.
<source>Journal of Vegetation Science</source>
.
<year>1998</year>
;
<volume>9</volume>
:
<fpage>511</fpage>
<lpage>520</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref056">
<label>56</label>
<mixed-citation publication-type="journal">
<name>
<surname>Szeicz</surname>
<given-names>M</given-names>
</name>
,
<name>
<surname>Macdonald</surname>
<given-names>M</given-names>
</name>
.
<article-title>Recent white spruce dynamics at the subarctic alpine treeline of north-western Canada</article-title>
.
<source>Journa of Ecology</source>
.
<year>1995</year>
;
<volume>83</volume>
:
<fpage>873</fpage>
<lpage>885</lpage>
.</mixed-citation>
</ref>
<ref id="pone.0139031.ref057">
<label>57</label>
<mixed-citation publication-type="journal">
<name>
<surname>Smith</surname>
<given-names>MD</given-names>
</name>
,
<name>
<surname>Knapp</surname>
<given-names>AK</given-names>
</name>
,
<name>
<surname>Collins</surname>
<given-names>SL</given-names>
</name>
.
<article-title>A framework for assessing ecosystem dynamics in response to chronic resource alterations induced by global change</article-title>
.
<source>Ecology</source>
.
<year>2009</year>
;
<volume>90</volume>
:
<fpage>3279</fpage>
<lpage>3289</lpage>
.
<pub-id pub-id-type="pmid">20120798</pub-id>
</mixed-citation>
</ref>
<ref id="pone.0139031.ref058">
<label>58</label>
<mixed-citation publication-type="journal">
<name>
<surname>Kouba</surname>
<given-names>Y</given-names>
</name>
,
<name>
<surname>Alados</surname>
<given-names>CL</given-names>
</name>
.
<article-title>Spatio-temporal dynamics of Quercus faginea forests in the Spanish Central Pre-Pyrenees</article-title>
.
<source>European Journal of Forest Research</source>
.
<year>2011</year>
;
<volume>131</volume>
:
<fpage>369</fpage>
<lpage>379</lpage>
.</mixed-citation>
</ref>
</ref-list>
</back>
</pmc>
</record>

Pour manipuler ce document sous Unix (Dilib)

EXPLOR_STEP=$WICRI_ROOT/Wicri/Bois/explor/CheneBelgiqueV1/Data/Pmc/Corpus
HfdSelect -h $EXPLOR_STEP/biblio.hfd -nk 000022 | SxmlIndent | more

Ou

HfdSelect -h $EXPLOR_AREA/Data/Pmc/Corpus/biblio.hfd -nk 000022 | SxmlIndent | more

Pour mettre un lien sur cette page dans le réseau Wicri

{{Explor lien
   |wiki=    Wicri/Bois
   |area=    CheneBelgiqueV1
   |flux=    Pmc
   |étape=   Corpus
   |type=    RBID
   |clé=     PMC:4580598
   |texte=   Effects of Previous Land-Use on Plant Species Composition and Diversity in Mediterranean Forests
}}

Pour générer des pages wiki

HfdIndexSelect -h $EXPLOR_AREA/Data/Pmc/Corpus/RBID.i   -Sk "pubmed:26397707" \
       | HfdSelect -Kh $EXPLOR_AREA/Data/Pmc/Corpus/biblio.hfd   \
       | NlmPubMed2Wicri -a CheneBelgiqueV1 

Wicri

This area was generated with Dilib version V0.6.27.
Data generation: Tue Feb 21 23:48:11 2017. Site generation: Wed Mar 6 16:29:49 2024