<?xml version="1.0" encoding="ISO-8859-1"?><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id>2007-3364</journal-id>
<journal-title><![CDATA[Therya]]></journal-title>
<abbrev-journal-title><![CDATA[Therya]]></abbrev-journal-title>
<issn>2007-3364</issn>
<publisher>
<publisher-name><![CDATA[Asociación Mexicana de Mastozoología A.C.]]></publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S2007-33642023000300329</article-id>
<article-id pub-id-type="doi">10.12933/therya-23-4991</article-id>
<title-group>
<article-title xml:lang="en"><![CDATA[Influence of forest type on the diversity, abundance, and naïve occupancy of the mammal assemblage in the southeastern Brazilian Atlantic Forest]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Soto-Werschitz]]></surname>
<given-names><![CDATA[Alejandra]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
<xref ref-type="aff" rid="Aaf"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Mandujano]]></surname>
<given-names><![CDATA[Salvador]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Passamani]]></surname>
<given-names><![CDATA[Marcelo]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
</contrib-group>
<aff id="Af1">
<institution><![CDATA[,Universidade Federal de Lavras Departamento de Ecologia e Conservação Laboratório de Ecologia e Conservação de Mamíferos]]></institution>
<addr-line><![CDATA[Lavras Minas Gerais]]></addr-line>
<country>Brazil</country>
</aff>
<aff id="Af2">
<institution><![CDATA[,Universidad de Los Andes Departamento de Biología ]]></institution>
<addr-line><![CDATA[Mérida Mérida]]></addr-line>
<country>Venezuela</country>
</aff>
<aff id="Af3">
<institution><![CDATA[,Instituto de Ecología. A.C. Red de Biología y Conservación de Vertebrados ]]></institution>
<addr-line><![CDATA[Xalapa Veracruz]]></addr-line>
<country>Mexico</country>
</aff>
<pub-date pub-type="pub">
<day>00</day>
<month>00</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="epub">
<day>00</day>
<month>00</month>
<year>2023</year>
</pub-date>
<volume>14</volume>
<numero>3</numero>
<fpage>329</fpage>
<lpage>341</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_arttext&amp;pid=S2007-33642023000300329&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_abstract&amp;pid=S2007-33642023000300329&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_pdf&amp;pid=S2007-33642023000300329&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p><![CDATA[The Brazilian Atlantic Forest has the highest rate of native vegetation destruction, which is one of the principal drivers of mammal extinctions. Therefore, reducing information gaps regarding diversity patterns, abundance, and habitat use is crucial to understand mammal persistence in fragmented landscapes. Our objective was to establish the &#947; diversity and to assess the extent to which the &#945;, and &#946; diversity, the relative abundance, and naïve occupation of medium and large-sized mammal communities differ between seasonal and ombrophilous forests. Between January 2019 and March 2020, we placed 22 camera traps in the Atlantic Forest of Minas Gerais. We calculate Hill's numbers using iNEXT.4steps package, the &#946;-diversity with the Betapart package, as well as the relative abundance index (RAI), and naïve occupancy (PAO). We used Kruskal-Wallis and Mann-Whitney statistical tests to compare the RAIs between different species and forest types. Finally, we calculated the correlation between the RAIs and PAOs. We found 32 species, principally from the orders Carnivora and Artiodactyla. The alpha diversity and evenness profiles were not different between the two forest types (seasonal q0 = 0.91, q1 = 0.99, q2 = 1, J = 0.83; ombrophilous q0 = 0.96, q1 = 0.99, q2 = 1, J = 0.85). The beta diversity was low (&#946;JAC = 0.37) which was mostly associated with species turnover (&#946;JTU = 0.34), while nestedness was almost non-existent (&#946;JNE = 0.02). The RAIs varied among mammalian species (H = 115.24, P = 0.000), with the highest values for Didelphis aurita (RAI = 4.55 ± 7.66) and Cuniculus paca (RAI = 2.35 ± 3.73) and the minor values for Speothos venaticus (RAI = 0.04 ± 0.24) and Galictis cuja (RAI = 0.06 ± 1.19). The RAIs of species was not significantly different between forests (U = 453.5; Z = 0.37; P = 0.70), and only Leopardus wiedii showed significant differences between forests (U = 84.5; P = 0.01). Most of the mammalian species had restricted occupancy to a few localities (&lt; 50 %). The species Eira barbara and Didelphis aurita had the highest PAOs in both forests (&gt; 50 %), and the species Tayassu pecari, Tamandua tetradactyla, and Speothos venaticus, the lowest values (5 %). We found a correlation of 75 % between the average RAI and naïve occupancy. The &#947; diversity was representative and consistent with the species found in the Atlantic Forest, and the relative abundance and naïve occupancy reflected the rarity of most species in the area. Additionally, the only difference between the two forests corresponds to species turnover. Therefore, we must conserve native remnants of both forests to ensure the existence of native mammals, mainly the most threatened species, to prevent more dramatic scenarios of local extinction in Minas Gerais.]]></p></abstract>
<abstract abstract-type="short" xml:lang="es"><p><![CDATA[La Mata Atlántica Brasileña presenta la mayor tasa de destrucción de vegetación nativa, causa principal de la extinción de mamíferos. Por lo tanto, reducir las lagunas de información relacionadas con los patrones de diversidad &#945;, &#946; y &#947;, abundancia, ocupación y uso de hábitat es una prioridad, para comprender la persistencia de mamíferos en paisajes fragmentados. Nuestro objetivo fue establecer la diversidad &#947;, y evaluar en qué medida la diversidad &#945; y &#946;, la abundancia relativa y la ocupación naïve de las comunidades de mamíferos medianos y grandes, contrastan entre bosques estacionales y ombrófilos. Entre enero (2019) y marzo (2020), colocamos 22 cámaras trampa en el Bosque Atlántico de Minas Gerais. Calculamos los números de Hill utilizando el paquete iNEXT.4steps, la &#946;-diversidad con el paquete Betapart, el índice de abundancia relativa (RAI) y la ocupación naïve (PAO). Utilizamos pruebas de Kruskal-Wallis y Mann-Whitney para comparar los RAI entre especies y bosques. Finalmente, calculamos la correlación entre los RAIs y PAOs. Registramos 32 especies, principalmente de los órdenes Carnivora y Artiodactyla. La diversidad alfa y los perfiles de uniformidad no difirieron entre bosques (estacional q0 = 0.91, q1 = 0.99, q2 = 1, J = 0.83; ombrófilo q0 = 0.96, q1 = 0.99, q2 = 1, J = 0.85). La beta-diversidad fue baja (&#946;JAC = 0.37), correspondiente al recambio de especies (&#946;JTU = 0.34), y a una anidación casi inexistente (&#946;JNE = 0.02). Los RAIs difirieron entre especies (H = 115.24, P = 0.000), los valores más altos fueron para Didelphis aurita (RAI = 4.55 ± 7.66) y Cuniculus paca (RAI = 2.35 ± 3.73), y los valores más bajos para Speothos venaticus (RAI = 0.04 ± 0.24) y Galictis cuja (RAI = 0.06 ± 1.19). Los RAIs no difirieron entre bosques (U = 453.5; Z = 0,37; P = 0.70), y exclusivamente Leopardus wiedii mostró diferencias significativas entre bosques (U = 84.5; P = 0.01). La mayoría de las especies presentaron una ocupación restringida (&lt; 50 %). Eira barbara y Didelphis aurita presentaron los valores más altos en ambos bosques (&gt; 50 %), mientras que Tayassu pecari, Tamandua tetradactyla y Speothos venaticus, los valores más bajos (5 %). Observamos una correlación del 75 % entre los RAIs y PAOs. La diversidad &#947; fue representativa de la riqueza de especies reportada para la Mata Atlántica. Los RAIs y PAOs reflejaron la rareza de la mayoría de las especies. Adicionalmente, la única diferencia entre los dos bosques correspondió a la rotación de especies. Por lo tanto, debemos conservar los remanentes nativos de ambos bosques para asegurar la existencia de los mamíferos nativos, principalmente las especies más amenazadas, para evitar escenarios más dramáticos de extinción local en la Mata Atlántica de Minas Gerais.]]></p></abstract>
<kwd-group>
<kwd lng="en"><![CDATA[Biodiversity]]></kwd>
<kwd lng="en"><![CDATA[Brazil]]></kwd>
<kwd lng="en"><![CDATA[conservation]]></kwd>
<kwd lng="en"><![CDATA[habitat use]]></kwd>
<kwd lng="en"><![CDATA[mammals]]></kwd>
<kwd lng="en"><![CDATA[relative abundance index]]></kwd>
</kwd-group>
</article-meta>
</front><back>
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