<?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>S2007-33642024000100103</article-id>
<article-id pub-id-type="doi">10.12933/therya-24-5947</article-id>
<title-group>
<article-title xml:lang="en"><![CDATA[Use of artificial water troughs by deer in the Maya forest, México]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Contreras-Moreno]]></surname>
<given-names><![CDATA[Fernando M.]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
<xref ref-type="aff" rid="Aaf"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Jesús-Espinosa]]></surname>
<given-names><![CDATA[Daniel]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Sánchez-Pinzón]]></surname>
<given-names><![CDATA[Khiavett G.]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Méndez-Tun]]></surname>
<given-names><![CDATA[José M.]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Cruz-Romo]]></surname>
<given-names><![CDATA[Lizardo]]></given-names>
</name>
<xref ref-type="aff" rid="Aff"/>
</contrib>
</contrib-group>
<aff id="Af1">
<institution><![CDATA[,World Wildlife Fund Inc  ]]></institution>
<addr-line><![CDATA[Ciudad de México ]]></addr-line>
<country>México</country>
</aff>
<aff id="Af2">
<institution><![CDATA[,Universidad Tecnológica de Calakmul  ]]></institution>
<addr-line><![CDATA[ Campeche]]></addr-line>
<country>México</country>
</aff>
<aff id="Af3">
<institution><![CDATA[,Grupo de Monitoreo Socioambiental  ]]></institution>
<addr-line><![CDATA[ Tabasco]]></addr-line>
<country>México</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>1</numero>
<fpage>103</fpage>
<lpage>111</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_arttext&amp;pid=S2007-33642024000100103&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_abstract&amp;pid=S2007-33642024000100103&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_pdf&amp;pid=S2007-33642024000100103&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p><![CDATA[Artificial water troughs have been implemented in the Calakmul region as a measure that contributes to the maintenance of wildlife populations during the drought season. The aim of this study was to estimate the use of artificial water troughs by three species of deer (Odocoileus virginianus, M. pandora, and Mazama temama) in the Maya Forest of Campeche in southeastern México. The study was carried out in the Calakmul Biosphere Reserve (CBR, in Spanish) in southeastern México. Seventy artificial water troughs were installed, most of them within the core areas of the CBR. Between December 2018 and August 2021, eight digital traps were placed in eight artificial water troughs to monitor the presence of deer. The Photographic Visit Index (PVI) was calculated, and the visit rates of each species were compared by sampling year for each monitoring station. Deer activity patterns were evaluated using circular statistics to assess whether there were differences between visiting times. Watson-Williams tests were performed during the different sampling months. The density of records was analyzed to identify the degree of overlap in the deer activity patterns. With a sampling effort of 4,672 nights/camera, we captured 477 records of O. virginianus, 229 of M. pandora, and three of M. temama using artificial water troughs in the CBR. Due to the scarce records of M. temama in water troughs, comparative analyses were performed only with the other two deer species. According to the PVI, in the case of O. virginianus, highly significant differences were found between the three sampling years (H= 12.575, df = 2, P &lt; 0.001); similarly, M. pandora showed highly significant differences between sampling years (H = 9.29, df = 2, P = 0.001). Regarding activity patterns, O. virginianus is mainly diurnal, with peaks of activity in the early hours of the day (8:00 h to 9:00 h). M. pandora was also mainly diurnal, showing the highest peaks of activity in the early hours of the day and before dusk. O. virginianus and M. pandora regularly visit water troughs, and the presence of deer in water troughs responds to their need to drink water for thermoregulation. The activity pattern of deer was mainly diurnal; it is safer for both species to move during the day because predators were recorded constantly in the study area. The degree of overlap recorded between O. virginianus and M. pandora suggests that both species are active at the same times of the day.]]></p></abstract>
<abstract abstract-type="short" xml:lang="es"><p><![CDATA[Los bebederos artificiales se han implementados en la región de Calakmul como una medida que contribuye al mantenimiento de las poblaciones de fauna silvestre, durante la época de estiaje. El objetivo de este estudio fue estimar el uso que tres especies de venados (Odocoileus virginianus, Mazama pandora y Mazama temama) hacen del agua en bebederos artificiales en la Selva Maya de Campeche en el sureste de México. El estudio se realizó en la Reserva de la Biosfera Calakmul (RBC), en el sureste de México. Se instalaron 70 bebederos artificiales, la mayoría de los cuales se ubican dentro de las zonas núcleo de la RBC. Entre los meses de diciembre de 2018 hasta agosto del 2021, se colocaron ocho cámaras trampas digitales en ocho bebederos artificiales, con el objetivo de verificar la presencia de venados. Se obtuvo el Índice Fotográfico de Visita (IFV), se compararon las tasas de visita de las especies en cada estación de monitoreo, por año de muestreo. Se evaluaron los patrones de actividad de los venados mediante estadística circular para identificar si existían diferencias entre los horarios de visitas. Durante los diferentes meses de muestreo se realizaron pruebas Watson-Williams. Se analizó la densidad de registros para identificar el grado de traslape en los patrones de actividad los venados. Con un esfuerzo de muestreo de 4,672 noches/cámara se obtuvieron 477 registros independientes de O. virginianus, 229 de M. pandora y tres M. temama que utilizan los bebederos artificiales en la CBR. Debido a los escasos registros de M. temama en bebederos los análisis comparativos se realizaron con las otras dos especies de venados. De acuerdo con el IFV, para O. virginianus, se observaron diferencias altamente significativas al comparar entre los tres años de muestreo (H=12.575, gl=2, P&lt;0.001), de igual forma M. pandora mostró diferencias altamente significativas al comparar los registros independientes entre años de muestreo (H = 9.29, gl = 2, P = 0.001). Con respecto a los patrones de actividad. Se encontró que O. virginianus es principalmente diurna, con picos de actividad en las primeras horas del día (8:00 a 9:00 h). M. pandora, fue principalmente diurna, obteniéndose los mayores picos de actividad en las primeras horas del día y antes del anochecer. Los bebederos son utilizados constantemente por O. virginianus y M. pandora. La presencia de venados en los bebederos responde a necesidad de termorregulación, para satisfacer sus necesidades hídricas. El patrón de actividad de los venados fue principalmente diurno, ya que es más seguro para ambas especies moverse durante el día, dado que en el área de estudio se registran de forma constante depredadores. El grado de traslape encontrado entre O. virginianus y M. pandora sugiere que ambas especies están activas en los mismos horarios.]]></p></abstract>
<kwd-group>
<kwd lng="en"><![CDATA[Calakmul]]></kwd>
<kwd lng="en"><![CDATA[game species]]></kwd>
<kwd lng="en"><![CDATA[mammals]]></kwd>
<kwd lng="en"><![CDATA[photo-trapping]]></kwd>
<kwd lng="en"><![CDATA[ungulate]]></kwd>
</kwd-group>
</article-meta>
</front><back>
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