<?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>S2007-33642024000200202</article-id>
<article-id pub-id-type="doi">10.12933/therya-24-5970</article-id>
<title-group>
<article-title xml:lang="en"><![CDATA[Land-use change and habitat fragmentation of Leopardus pardalis in Highlands of Puebla, Mexico]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Hernández-Pérez]]></surname>
<given-names><![CDATA[Ezequiel]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
<xref ref-type="aff" rid="Aaf"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Lemus Rincón]]></surname>
<given-names><![CDATA[Sergio Gilmar]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Ayala-Hernández]]></surname>
<given-names><![CDATA[María M.]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Alemán-Sancheschúlz]]></surname>
<given-names><![CDATA[Gilberto]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
</contrib-group>
<aff id="Af1">
<institution><![CDATA[,Universidad Nacional Autónoma de México Facultad de Estudios Superiores Zaragoza Laboratorio de Geomática]]></institution>
<addr-line><![CDATA[ Tlaxcala]]></addr-line>
<country>Mexico</country>
</aff>
<aff id="Af2">
<institution><![CDATA[,Universidad Nacional Autónoma de México Facultad de Estudios Superiores Zaragoza Unidad Multidisciplinaria de Investigación Experimental Zaragoza]]></institution>
<addr-line><![CDATA[Ciudad de México ]]></addr-line>
<country>Mexico</country>
</aff>
<pub-date pub-type="pub">
<day>00</day>
<month>00</month>
<year>2024</year>
</pub-date>
<pub-date pub-type="epub">
<day>00</day>
<month>00</month>
<year>2024</year>
</pub-date>
<volume>15</volume>
<numero>2</numero>
<fpage>202</fpage>
<lpage>217</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_arttext&amp;pid=S2007-33642024000200202&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_abstract&amp;pid=S2007-33642024000200202&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_pdf&amp;pid=S2007-33642024000200202&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p><![CDATA[Ocelots are relatively tolerant to habitat modification. However, it has been observed that they may be sensitive to habitat loss and fragmentation as a result of human development. The Sierra Norte de Puebla is considered a potential habitat for ocelots and other tropical felines. However, it has suffered heavy loss and fragmentation of its natural ecosystems, which considerably affects habitat availability and quality. This study analyzed the land-use changes and habitat fragmentation in the distribution range of the ocelot in the Sierra Norte de Puebla, Mexico, from 1993 to 2020. Habitat suitability was determined using potential distribution models and vegetation and land-use maps from 1993, 2003, and 2020, obtained using supervised classification of Landsat images. The resulting maps were reclassified in terms of the habitat suitability for Leopardus pardalis according to their quality. Land-use changes and habitat loss were quantified with a transition matrix, and fragmentation was assessed using the Morphological Spatial Pattern Analysis tool of the program GUIDOS. These habitat fragments were quantified using the integral index of connectivity with the CONEFOR Sensinode program. We estimated that 22.2 % of the study area has suitable conditions for ocelots. From 1993 to 2020, the area covered by natural vegetation decreased 16 % at an annual rate of -2.4 %. During this period, the mean fragment size and shape index decreased; on the other hand, the number of fragments and the Euclidean distance between fragments increased. The percentages of edge, branch, and islet vegetation dropped from 1993 to 2003 but increased in 2020. The connectivity analysis indicated that two habitat fragments showed high values of the integral index of connectivity. The increase in anthropogenic cover and the habitat loss for L. pardalis between 1993 and 2020 affected mainly vegetation fragments considered optimal for the persistence of this species. In these ecosystems, agricultural and livestock practices are expanding vigorously, increasing edge habitats and decreasing the core area of habitat fragments. The areas that recorded the presence of ocelots have optimum conditions to serve as biological corridors in the Sierra Madre Oriental, particularly in the portion of the Sierra Norte de Puebla. The fragmentation of the ocelot habitat is of particular concern and should be addressed strategically for the long-term conservation of the ocelot and regional biodiversity.]]></p></abstract>
<abstract abstract-type="short" xml:lang="es"><p><![CDATA[Los ocelotes presentan cierta tolerancia a la modificación de su hábitat, sin embargo, se ha observado que pueden ser sensibles a la pérdida y fragmentación como resultado del desarrollo humano. La Sierra Norte de Puebla se considera con potencial para la distribución del ocelote y otros felinos tropicales; no obstante, la pérdida y fragmentación de sus ecosistemas es alta y genera un efecto significativo en la disponibilidad y calidad del hábitat. En este estudio se analizó el cambio de uso de suelo y la fragmentación del hábitat del ocelote en la Sierra Norte de Puebla, México de 1993 a 2020. Se determinó la idoneidad de hábitat del ocelote mediante modelos de distribución potencial y mapas de vegetación y uso de suelo de 1993, 2003 y 2020, obtenidos mediante una clasificación supervisada de imágenes Landsat. Los mapas derivados fueron reclasificados según la aptitud de hábitat de Leopardus pardalis de acuerdo con su calidad. Se cuantificó el cambio y pérdida de hábitat mediante una matriz de transición y se evalúo la fragmentación con la herramienta Morphological Spatial Pattern Analysis del programa GUIDOS. A estos fragmentos de hábitat se les cuantificó el Índice Integral de Conectividad con el programa CONEFOR Sensinode. 22.2 % de la superficie total de la zona de estudio tiene condiciones para la presencia del ocelote. De 1993 a 2020 la superficie de vegetación disminuyó 16% a una tasa de cambio de -2.4 %. Durante este periodo el tamaño medio del fragmento e índice de forma disminuyeron; en cambio, el número de fragmentos y la distancia euclidiana entre fragmentos se incrementaron. El porcentaje de borde, rama y relicto disminuyeron de 1993 a 2003, aunque aumentaron en 2020. El análisis de conectividad indicó que dos fragmentos de hábitat presentaron valores altos del índice de conectividad integral. El incremento en la superficie de las coberturas antrópicas y pérdida de hábitat de L. pardalis entre 1993 y 2020, se concentró en fragmentos de vegetación considerados óptimos para la persistencia de esta especie. En estos ecosistemas el avance de las prácticas agrícolas y ganaderas es alto, lo cual contribuye a un incremento en el hábitat de borde y una disminución en el área interior de los fragmentos de hábitat. Las áreas en las que se registró la presencia de ocelotes tienen las condiciones ideales para que éstas funcionen como corredores biológicos en la Sierra Madre Oriental, particularmente en la porción de la Sierra Norte de Puebla. La fragmentación del hábitat del ocelote es especialmente preocupante y necesita abordarse estratégicamente para la conservación a largo plazo, no solo del ocelote, sino de la biodiversidad de la región.]]></p></abstract>
<kwd-group>
<kwd lng="en"><![CDATA[Carnivores]]></kwd>
<kwd lng="en"><![CDATA[connectivity]]></kwd>
<kwd lng="en"><![CDATA[conservation]]></kwd>
<kwd lng="en"><![CDATA[deforestation]]></kwd>
<kwd lng="en"><![CDATA[optimal habitat]]></kwd>
<kwd lng="en"><![CDATA[landscape]]></kwd>
<kwd lng="en"><![CDATA[habitat loss]]></kwd>
</kwd-group>
</article-meta>
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