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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Ecol. Evol.</journal-id>
<journal-title>Frontiers in Ecology and Evolution</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Ecol. Evol.</abbrev-journal-title>
<issn pub-type="epub">2296-701X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fevo.2022.1000168</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Ecology and Evolution</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Dental mesowear and microwear for the dietary reconstruction of Quaternary Southeast Asian serows and gorals</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Isarankura Na Ayudhya</surname> <given-names>Jakritip</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Merceron</surname> <given-names>Gildas</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/723355/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Wannaprasert</surname> <given-names>Thanakul</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Jaeger</surname> <given-names>Jean-Jacques</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/234001/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Chaimanee</surname> <given-names>Yaowalak</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/274514/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Shoocongdej</surname> <given-names>Rasmi</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Suraprasit</surname> <given-names>Kantapon</given-names></name>
<xref ref-type="aff" rid="aff5"><sup>5</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/879923/overview"/>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Department of Biology, Faculty of Science, Chulalongkorn University</institution>, <addr-line>Bangkok</addr-line>, <country>Thailand</country></aff>
<aff id="aff2"><sup>2</sup><institution>PALEVOPRIM, UMR 7262, CNRS-INEE, Universit&#x00E9; de Poitiers</institution>, <addr-line>Poitiers</addr-line>, <country>France</country></aff>
<aff id="aff3"><sup>3</sup><institution>Department of Archaeology, Faculty of Archaeology, Silpakorn University</institution>, <addr-line>Bangkok</addr-line>, <country>Thailand</country></aff>
<aff id="aff4"><sup>4</sup><institution>The Prehistoric Population and Cultural Dynamics in Highland Pang Mapha Project, Princess Maha Chakri Sirindhorn Anthropology Centre</institution>, <addr-line>Bangkok</addr-line>, <country>Thailand</country></aff>
<aff id="aff5"><sup>5</sup><institution>Center of Excellence in Morphology of Earth Surface and Advanced Geohazards in Southeast Asia (MESA CE), Department of Geology, Faculty of Science, Chulalongkorn University</institution>, <addr-line>Bangkok</addr-line>, <country>Thailand</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: G. Lynn Wingard, United States Geological Survey (USGS), United States</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Tzu-Ruei Yang, National Museum of Natural Science, Taiwan; Emmanuel Paul Gilissen, Royal Museum for Central Africa, Belgium</p></fn>
<corresp id="c001">&#x002A;Correspondence: Kantapon Suraprasit, <email>Kantapon.S@chula.ac.th</email></corresp>
<fn fn-type="other" id="fn004"><p>This article was submitted to Paleoecology, a section of the journal Frontiers in Ecology and Evolution</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>13</day>
<month>09</month>
<year>2022</year>
</pub-date>
<pub-date pub-type="collection">
<year>2022</year>
</pub-date>
<volume>10</volume>
<elocation-id>1000168</elocation-id>
<history>
<date date-type="received">
<day>21</day>
<month>07</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>24</day>
<month>08</month>
<year>2022</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2022 Isarankura Na Ayudhya, Merceron, Wannaprasert, Jaeger, Chaimanee, Shoocongdej and Suraprasit.</copyright-statement>
<copyright-year>2022</copyright-year>
<copyright-holder>Isarankura Na Ayudhya, Merceron, Wannaprasert, Jaeger, Chaimanee, Shoocongdej and Suraprasit</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/"><p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p></license>
</permissions>
<abstract>
<p>Serows and gorals (Bovidae, Caprinae) are emblematic antelopes distributed in Southeast Asia. They all are nearly threaten or vulnerable species nowadays despite having a more widespread distribution during the Pleistocene. Fossils of three native caprine species, i.e., a Sumatran serow <italic>Capricornis sumatraensis</italic>, Chinese goral <italic>Naemorhedus griseus</italic>, and Himalayan goral <italic>Naemorhedus goral</italic>, were recovered from four Pleistocene paleontological and archeological sites in Thailand, namely Pha Bong, Khok Sung, Tham Wiman Nakin, and Tham Lod Rockshelter. To investigate dietary changes of these Southeast Asian serows and gorals through the Quaternary, differences in feeding habits and habitat preferences between the Pleistocene and extant populations were examined using the hypsodonty index (HI) together with the mesowear II method and the dental microwear texture analysis (DMTA). The HI and mesowear-II results showed that Pleistocene and extant caprines were mixed feeders. For the Pleistocene caprine populations, the DMTA results suggested more browsing signals for <italic>C. sumatraensis</italic> than both <italic>Naemorhedus</italic> species that were mixed feeders similar to their extant populations. The DMTA demonstrated a considerable dietary overlap among the Pleistocene sympatric caprine populations. The dental microwear results also revealed that the extant <italic>C. sumatraensis</italic> is a leaf-dominant browser, while the extant <italic>N. griseus</italic> possibly feeds on seeds or tough food items. These data combined with previous stable carbon isotope analyses reinforce the idea that the restricted ranges of habitats for these extant serow and goral populations have possibly been driven by the Holocene climatic and environmental changes as well as the negative effects of human activities.</p>
</abstract>
<kwd-group>
<kwd>Caprinae</kwd>
<kwd>hypsodonty index</kwd>
<kwd>mesowear</kwd>
<kwd>DMTA</kwd>
<kwd>paleoecology</kwd>
<kwd>Pleistocene</kwd>
<kwd>Thailand</kwd>
</kwd-group>
<contract-sponsor id="cn001">Chulalongkorn University<named-content content-type="fundref-id">10.13039/501100002873</named-content></contract-sponsor>
<counts>
<fig-count count="5"/>
<table-count count="6"/>
<equation-count count="0"/>
<ref-count count="95"/>
<page-count count="17"/>
<word-count count="10892"/>
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</article-meta>
</front>
<body>
<sec id="S1" sec-type="intro">
<title>Introduction</title>
<p>Serows (<italic>Capricornis</italic>) and gorals (<italic>Naemorhedus</italic>), the family Bovidae and subfamily Caprinae, are ruminants with a goat-like or antelope-like appearance. Members of these two genera are present today in Southeast Asia, South Asia, and China (<xref ref-type="bibr" rid="B48">Lekagul and McNeely, 1988</xref>; <xref ref-type="bibr" rid="B93">Wilson and Mittermeier, 2011</xref>). Although taxonomic status and the existing number of species in these two genera have been matters for debate so far, four recognized species, i.e., Sumatran serows (<italic>Capricornis sumatraensis</italic>), red serows (<italic>Capricornis rubidus</italic>), Chinese gorals (<italic>Naemorhedus griseus</italic>), and Himalayan gorals (<italic>Naemorhedus goral</italic>), are likely to be valid based on most recent studies of morphological and molecular phylogenetic analyses (<xref ref-type="bibr" rid="B12">Bover et al., 2019</xref>; <xref ref-type="bibr" rid="B59">Mori et al., 2019</xref>; <xref ref-type="bibr" rid="B41">Joshi et al., 2022</xref>). These present-day serows and gorals are found in high-altitude areas such as steep limestone mountains, cliffs, and caves, at the elevation ranging from 200 to 3,000 m for Sumatran serows (<xref ref-type="bibr" rid="B48">Lekagul and McNeely, 1988</xref>; <xref ref-type="bibr" rid="B93">Wilson and Mittermeier, 2011</xref>) and from 900 to 4,000 m for those gorals (<xref ref-type="bibr" rid="B48">Lekagul and McNeely, 1988</xref>; <xref ref-type="bibr" rid="B19">Chaiyarat et al., 1999</xref>; <xref ref-type="bibr" rid="B8">Bhattacharya et al., 2012</xref>). These three caprine taxa are listed as endangered or near-threatened species and are protected by CITES Appendix I (<xref ref-type="bibr" rid="B26">Duckworth et al., 2008</xref>; <xref ref-type="bibr" rid="B25">Duckworth and MacKinnon, 2008</xref>; <xref ref-type="bibr" rid="B63">Phan et al., 2020</xref>).</p>
<p>However, only two caprine species, <italic>C. sumatraensis</italic> and <italic>N. griseus</italic>, are nowadays distributed in Thailand (<xref ref-type="fig" rid="F1">Figure 1</xref>). The former species is found in the southern, western, and northern parts of Thailand (<xref ref-type="bibr" rid="B18">Chairat, 2007</xref>; <xref ref-type="bibr" rid="B93">Wilson and Mittermeier, 2011</xref>; <xref ref-type="bibr" rid="B61">Nakasathien, 2017</xref>), whereas <italic>N. griseus</italic> is present only in the northern region where the coexistence of these two species occurs (<xref ref-type="bibr" rid="B14">Buranapim et al., 2014</xref>; <xref ref-type="bibr" rid="B69">Safoowong, 2015</xref>; <xref ref-type="bibr" rid="B38">Jangtarwan et al., 2020</xref>). Fossils of caprines were recovered from four paleontological and archeological sites of which the faunal ages range from the middle Pleistocene to the late Pleistocene (<xref ref-type="bibr" rid="B80">Suraprasit et al., 2016</xref>, <xref ref-type="bibr" rid="B78">2021a</xref>; <xref ref-type="bibr" rid="B10">Bocherens et al., 2017</xref>; <xref ref-type="bibr" rid="B91">Wattanapituksakul et al., 2018</xref>). Fossil evidence indicates that <italic>N. goral</italic> coexisted with <italic>C. sumatraensis</italic> and <italic>N. griseus</italic> in low-altitude areas of Thailand at the elevation below 800 m above mean sea level during the Pleistocene (<xref ref-type="bibr" rid="B87">Tougard, 1998</xref>, <xref ref-type="bibr" rid="B88">2001</xref>; <xref ref-type="bibr" rid="B75">Shoocongdej et al., 2007</xref>; <xref ref-type="bibr" rid="B10">Bocherens et al., 2017</xref>; <xref ref-type="bibr" rid="B91">Wattanapituksakul et al., 2018</xref>; <xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). Based on the stable carbon isotope analysis of mammalian tooth enamel, it has been suggested that environmental changes in Southeast Asia from the Pleistocene savannah to the Holocene rainforest have contributed to the extinction of some grassland-dwelling mammals (<xref ref-type="bibr" rid="B49">Louys and Robert, 2020</xref>). For instance, the extinction of <italic>N. goral</italic> in Thailand might have been driven by the reduction of open habitats during the Holocene (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). In addition to the replacement of open grassland landscapes by more closed rainforests, the decreasing number of wild caprine populations is mostly caused by anthropogenic activities such as overhunting and deforestation for timber trading or rice field expansion (<xref ref-type="bibr" rid="B29">Ellen et al., 2000</xref>; <xref ref-type="bibr" rid="B76">Sodhi et al., 2004</xref>; for more detailed information of caprines in Thailand, see in <xref ref-type="supplementary-material" rid="DS1">Supplementary material 1</xref>). This raises the importance of paleoecological studies to test how environmental changes and anthropogenic activities have driven the present-day species&#x2019; range contractions.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption><p>The distribution of extant and Pleistocene caprines in Southeast Asia, the eastern region of South Asia, and South China [modified after <xref ref-type="bibr" rid="B81">Suraprasit et al. (2020)</xref>]. Six paleontological and archeological sites in Southeast Asia mentioned in this study: 1 = Pha Bong, Mae Hong Son (<xref ref-type="bibr" rid="B10">Bocherens et al., 2017</xref>); 2 = Khok Sung, Nakhon Ratchasima (<xref ref-type="bibr" rid="B80">Suraprasit et al., 2016</xref>); 3 = Tham Wiman Nakin, Chaiyaphum (<xref ref-type="bibr" rid="B78">Suraprasit et al., 2021a</xref>); 4 = Tham Lod Rockshelter, Mae Hong Son (<xref ref-type="bibr" rid="B91">Wattanapituksakul et al., 2018</xref>); 5 = Boh Dambang, Cambodia (<xref ref-type="bibr" rid="B3">Bacon et al., 2018b</xref>); and 6 = Nam Lot, Laos (<xref ref-type="bibr" rid="B2">Bacon et al., 2018a</xref>). Extant populations of <italic>C. sumatraensis</italic> and <italic>N. griseus</italic> have overlapping distribution areas at the northern part of Thailand, Myanmar, and China.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-1000168-g001.tif"/>
</fig>
<p>The paleoecology of bovids has been extensively investigated during the past two decades, using several methods (e.g., analyses of the stable carbon/nitrogen isotopes in animals&#x2019; tissues, limb ecomorphometrics, and dental wear patterns), allowing paleontologists to have access to individual and populational life history traits (<xref ref-type="bibr" rid="B35">Green and Croft, 2018</xref>). Nonetheless, information on diet and habitat preferences of Pleistocene caprines in Thailand remains scarce and has been only obtained from the stable carbon isotope measurements of mammalian tooth enamel (<xref ref-type="bibr" rid="B64">Pushkina et al., 2010</xref>; <xref ref-type="bibr" rid="B10">Bocherens et al., 2017</xref>; <xref ref-type="bibr" rid="B77">Suraprasit et al., 2018</xref>, <xref ref-type="bibr" rid="B81">2020</xref>, <xref ref-type="bibr" rid="B83">2021b</xref>) and the dental mesowear-I analysis (<xref ref-type="bibr" rid="B37">Isarankura Na Ayudhya et al., 2021</xref>).</p>
<p>The Southeast Asian Pleistocene <italic>C. sumatraensis</italic> has been identified as a generalist foraging chiefly on either pure C<sub>3</sub> or C<sub>4</sub> plants in both closed forest and open grassland landscapes, in response to local environmental conditions based on stable carbon isotope studies (e.g., <xref ref-type="bibr" rid="B64">Pushkina et al., 2010</xref>; <xref ref-type="bibr" rid="B2">Bacon et al., 2018a</xref>,<xref ref-type="bibr" rid="B3">b</xref>; <xref ref-type="bibr" rid="B77">Suraprasit et al., 2018</xref>, <xref ref-type="bibr" rid="B81">2020</xref>). In extant populations from Thailand, Laos, and Indonesia, <italic>C. sumatraensis</italic> has been considered to be a pure C<sub>3</sub> feeder (<xref ref-type="bibr" rid="B64">Pushkina et al., 2010</xref>; <xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). However, the <italic>&#x03B4;</italic><sup>13</sup>C results showed that Pleistocene <italic>N. griseus</italic> and <italic>N. goral</italic> in Thailand were more specialized feeders focusing on either pure C<sub>4</sub> or mixed C<sub>3</sub>/C<sub>4</sub> plants (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). One specimen of extant <italic>N. griseus</italic> shows a mixed C<sub>3</sub>/C<sub>4</sub> diet, while the extant <italic>N. goral</italic> feeds on pure C<sub>3</sub> or mixed C<sub>3</sub>/C<sub>4</sub> plants (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). It is inferred from this isotope evidence that the extant caprine populations live in more restricted habitats than the Pleistocene ones. As all grasslands in the tropics are mostly covered by C<sub>4</sub> grasses and sedge today (<xref ref-type="bibr" rid="B70">Sage, 2004</xref>; <xref ref-type="bibr" rid="B28">Edwards and Still, 2008</xref>), the dichotomy between C<sub>3</sub> and C<sub>4</sub> diets may reflect the habitats used by animals (open vs. closed) but not the types of vegetation that they consumed (<xref ref-type="bibr" rid="B16">Cerling and Harris, 1999</xref>). Thus, the question is raised whether the extant gorals mainly graze on C<sub>3</sub> monocots, or otherwise browse in C<sub>3</sub> bushes, trees, and shrubs. In addition, the mesowear I analysis suggested a more browsing signal for <italic>C. sumatraensis</italic> but similar feeding habits for both species of <italic>Naemorhedus</italic> through the Pleistocene and Holocene (<xref ref-type="bibr" rid="B37">Isarankura Na Ayudhya et al., 2021</xref>), unlike the achievement of previously analyzed carbon isotope data (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>).</p>
<p>While stable carbon isotope ratios can identify the photosynthetic pathways (C<sub>3</sub> or C<sub>4</sub>) of the food vegetation resources, other proxies such as hypsodonty index (HI) together with mesowear II and dental microwear texture analysis (DMTA) indicate mechanical properties and inner compositions of foods in relation to ungulate feeding habits. The HI is a morphological study of a dental phenotype related to feeding habits and habitats through the evolutionary adaptation (<xref ref-type="bibr" rid="B39">Janis, 1988</xref>; <xref ref-type="bibr" rid="B40">Janis, 2008</xref>). Ungulates that feasibly live in open habitats tend to have high hypsodonty because of high consumption of silica-rich grasses and food contaminated with grits. Typically, the HI is often used to analyze in parallel with another proxy called mesowear for indicating feeding habits in a long temporal scale (<xref ref-type="bibr" rid="B45">Kaiser et al., 2013</xref>; <xref ref-type="bibr" rid="B74">Semprebon et al., 2019</xref>). Mesowear analysis refers to macroscopic tooth wear of attrition (tooth to tooth contact) and abrasion (tooth to food contact), according to the primary definition by <xref ref-type="bibr" rid="B33">Fortelius and Solounias (2000)</xref>. The mesowear indicates a lifelong habit of species represented by its average diet from a specific location in space and time (<xref ref-type="bibr" rid="B33">Fortelius and Solounias, 2000</xref>; <xref ref-type="bibr" rid="B1">Ackermans, 2020</xref>). Because of an easy accessibility, the mesowear analysis has been applied to the study of diets and habitats in several herbivores using various scoring systems (e.g., <xref ref-type="bibr" rid="B44">Kaiser et al., 2009</xref>; <xref ref-type="bibr" rid="B58">Mihlbachler et al., 2010</xref>; <xref ref-type="bibr" rid="B84">Taylor et al., 2013</xref>). One of the mesowear scoring systems used for illustrating dietary feeding habits of ungulates is a mesowear II method (<xref ref-type="bibr" rid="B67">Rivals and Semprebon, 2006</xref>; <xref ref-type="bibr" rid="B44">Kaiser et al., 2009</xref>). Mesowear-II examines the attrition-abrasion signal through two variables: occlusal relief (OR) and cusp shape (CS), combining into a single variable named as a mesowear score (MS) (<xref ref-type="bibr" rid="B44">Kaiser et al., 2009</xref>). Grass phytoliths as well as dust in diets result in more abrasion than soft foliage (<xref ref-type="bibr" rid="B4">Baker et al., 1959</xref>; <xref ref-type="bibr" rid="B22">Damuth and Janis, 2011</xref>). Therefore, teeth of grazing ungulates that mainly consume grasses or nearby ground-level vegetation are more prone to abrasions than those of browsing animals. Unlike mesowear, dental microwear can provide more detailed information about food in a short-term period and can demonstrate directly the nature of meals of the last few days to weeks of an individual before death (<xref ref-type="bibr" rid="B85">Teaford and Oyen, 1989</xref>; <xref ref-type="bibr" rid="B94">Winkler and Kaiser, 2011</xref>; <xref ref-type="bibr" rid="B23">Davis and Pineda-Munoz, 2016</xref>; <xref ref-type="bibr" rid="B86">Teaford et al., 2017</xref>). Dental microwear textures can track differences in abrasive particles such as biosilica in herbaceous monocots and/or test the tissue composition such as lignin in food items (<xref ref-type="bibr" rid="B90">Walker et al., 1978</xref>; <xref ref-type="bibr" rid="B73">Scott et al., 2006</xref>; <xref ref-type="bibr" rid="B72">Scott, 2012</xref>; <xref ref-type="bibr" rid="B5">Barron-Ortiz et al., 2014</xref>). The dental microwear texture is then characterized by using the scale-sensitive fractal analysis (SSFA) (<xref ref-type="bibr" rid="B73">Scott et al., 2006</xref>). Microwear analysis might provide additional information on short-time dietary patterns such as dietary seasonal switch, sex differences, and niche partitioning (<xref ref-type="bibr" rid="B15">Calandra and Merceron, 2016</xref>; <xref ref-type="bibr" rid="B24">DeSantis, 2016</xref>). Therefore, the combination between mesowear and microwear has often been used to fill the gap between short- and long-term scales for dietary reconstructions (e.g., <xref ref-type="bibr" rid="B68">Rivals et al., 2011</xref>; <xref ref-type="bibr" rid="B5">Barron-Ortiz et al., 2014</xref>; <xref ref-type="bibr" rid="B57">Mihlbachler et al., 2018</xref>). In the present study, we investigated dietary and habitat preferences of Pleistocene fossil caprines and their extant populations through the combination of the HI (evolutionarily related dietary proxies) together with the mesowear-II (long-term dietary proxies) and dental microwear texture analyses (short-term dietary proxies; <xref ref-type="bibr" rid="B23">Davis and Pineda-Munoz, 2016</xref>). Our results are compared with previous stable carbon isotope data and field observation studies of extant wild populations. The information on diets and feeding habits of these caprines is useful to deepen the understanding of their dietary adaptations through the Quaternary and may provide some clues to propose appropriate ecological guidelines for future conservation biology politics.</p>
</sec>
<sec id="S2" sec-type="materials|methods">
<title>Materials and methods</title>
<sec id="S2.SS1">
<title>Fossil specimens</title>
<p>Sixty-three fossil specimens were collected from four paleontological and archeological sites in Thailand: Pha Bong, Khok Sung, Tham Wiman Nakin, and Tham Lod Rockshelter, all of which cover the ages ranging from the middle to latest Pleistocene (for more detailed information, see <xref ref-type="supplementary-material" rid="DS1">Supplementary material 2</xref>). The number of fossil specimens in each locality is given in <xref ref-type="table" rid="T1">Table 1</xref>.</p>
<table-wrap position="float" id="T1">
<label>TABLE 1</label>
<caption><p>General information of four paleontological and archeological sites and the number of specimens in this study.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Localities</td>
<td valign="top" align="center">Ages</td>
<td valign="top" align="center">Elevation above mean sea level</td>
<td valign="top" align="left">Number of fossils</td>
<td valign="top" align="center">References</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Pha Bong</td>
<td valign="top" align="center">400&#x2013;300 ka, middle Pleistocene</td>
<td valign="top" align="center">280 m</td>
<td valign="top" align="left"><italic>N. goral</italic> (<italic>n</italic> = 10)</td>
<td valign="top" align="center"><xref ref-type="bibr" rid="B10">Bocherens et al., 2017</xref>; <xref ref-type="bibr" rid="B78">Suraprasit et al., 2021a</xref></td>
</tr>
<tr>
<td valign="top" align="left">Khok Sung</td>
<td valign="top" align="center">217 or 130 ka, middle Pleistocene</td>
<td valign="top" align="center">150 m</td>
<td valign="top" align="left"><italic>C. sumatraensis</italic> (<italic>n</italic> = 2)</td>
<td valign="top" align="center"><xref ref-type="bibr" rid="B79">Suraprasit et al., 2015</xref>, <xref ref-type="bibr" rid="B80">2016</xref>; <xref ref-type="bibr" rid="B27">Duval et al., 2019</xref></td>
</tr>
<tr>
<td valign="top" align="left">Tham Wiman Nakin</td>
<td valign="top" align="center">&#x003E;169 ka, middle Pleistocene</td>
<td valign="top" align="center">500 m</td>
<td valign="top" align="left"><italic>C. sumatraensis</italic> (<italic>n</italic> = 10)<break/> <italic>N. goral</italic> (<italic>n</italic> = 4)</td>
<td valign="top" align="center"><xref ref-type="bibr" rid="B30">Esposito et al., 1998</xref>, <xref ref-type="bibr" rid="B31">2002</xref>; <xref ref-type="bibr" rid="B87">Tougard, 1998</xref>, <xref ref-type="bibr" rid="B88">2001</xref>; <xref ref-type="bibr" rid="B78">Suraprasit et al., 2021a</xref></td>
</tr>
<tr>
<td valign="top" align="left">Tham Lod Rockshelter</td>
<td valign="top" align="center">32&#x2013;12 ka, late Pleistocene</td>
<td valign="top" align="center">640 m</td>
<td valign="top" align="left"><italic>C. sumatraensis</italic> (<italic>n</italic> = 7)<break/> <italic>N. griseus</italic> (<italic>n</italic> = 22)<break/> <italic>N. goral</italic> (<italic>n</italic> = 8)</td>
<td valign="top" align="center"><xref ref-type="bibr" rid="B75">Shoocongdej et al., 2007</xref>; <xref ref-type="bibr" rid="B51">Marwick and Gagan, 2011</xref>; <xref ref-type="bibr" rid="B91">Wattanapituksakul et al., 2018</xref></td>
</tr>
</tbody>
</table></table-wrap>
</sec>
<sec id="S2.SS2">
<title>Extant specimens</title>
<p>In this study, a total of 39 extant caprine specimens include <italic>C. sumatraensis</italic> (<italic>n</italic> = 22), <italic>N. griseus</italic> (<italic>n</italic> = 12), and <italic>N. goral</italic> (<italic>n</italic> = 5) issued from ten collections: (1) Khao Nang Ram Wildlife Research Center, Uthai Thani (KNR), (2) Om Koi Wildlife Breeding Center, Chiang Mai (OK), (3) Natural History Museum of Chulalongkorn University, Bangkok (CUMNH), (4) Zoological Museum of Kasetsart University, Bangkok (ZMKU), (5) Forestry Museum of Kasetsart University, Bangkok (FMKU), (6) National Science Museum, Pathum Thani (THNHM), (7) Natural History Museum (British Museum collection), United Kingdom (BM), (8) Naturhistorisches Museum Basel, Switzerland (NMB), (9) Mus&#x00E9;um National d&#x2019;Histoire Naturelle, France (MNHN), and (10) Zoologische Staatssammlung M&#x00FC;nchen, Germany (ZSM). Specimens from the zoo were excluded from this study because the diet and habitat of animals are not naturally controlled. This research has been approved for the use of wild specimens by the Department of National Park, Wildlife and Plant Conservation, Thailand (Permission number 0907.4/6178).</p>
</sec>
<sec id="S2.SS3">
<title>Hypsodonty index</title>
<p>To calculate the HI, the crown height of the lower third molar (m3) was divided by its width (<xref ref-type="bibr" rid="B39">Janis, 1988</xref>). As most of the m3 of extant individuals have remained embedded in the jaw bone, measurements of a tooth crown height might be underestimated. Therefore, the HI of isolated teeth of Pleistocene caprines <italic>C. sumatraensis</italic> (<italic>n</italic> = 7), <italic>N. griseus</italic> (<italic>n</italic> = 7), and <italic>N. goral</italic> (<italic>n</italic> = 6) was calculated and used as representatives of extant individuals.</p>
<p>The HI of mammals represents dental morphological characteristics throughout lifetime linked to their evolutionary adaptation (<xref ref-type="bibr" rid="B40">Janis, 2008</xref>). At the evolutionary time scales, the HI is commonly regarded as a species-specific parameter for interpreting progressively wear-inducing diets and environments for herbivorous mammals (<xref ref-type="bibr" rid="B45">Kaiser et al., 2013</xref>). In principle, high hypsodonty caused by the ingestion of abrasive dietary bolus (silica-bearing plant/grit digestion) is usually associated with mammals that occupy open habitats (<xref ref-type="bibr" rid="B39">Janis, 1988</xref>; <xref ref-type="bibr" rid="B22">Damuth and Janis, 2011</xref>). However, the combination of HI and mesowear has often been used to evaluate the accuracy of dietary interpretations (e.g., <xref ref-type="bibr" rid="B33">Fortelius and Solounias, 2000</xref>; <xref ref-type="bibr" rid="B44">Kaiser et al., 2009</xref>; <xref ref-type="bibr" rid="B34">Frazer and Theodor, 2011</xref>).</p>
</sec>
<sec id="S2.SS4">
<title>Mesowear II analysis</title>
<p>Samples for the mesowear II analysis include three extant species: <italic>C. sumatraensis</italic> (<italic>n</italic> = 22), <italic>N. griseus</italic> (<italic>n</italic> = 12), and <italic>N. goral</italic> (<italic>n</italic> = 5). Pleistocene specimens of the same taxa: <italic>C. sumatraensis</italic> (<italic>n</italic> = 19), <italic>N. griseus</italic> (<italic>n</italic> = 22), and <italic>N. goral</italic> (<italic>n</italic> = 22) were analyzed. The results obtained from mesowear II were compared with <xref ref-type="bibr" rid="B45">Kaiser et al. (2013)</xref>&#x2019;s datasets including 26 species of browsers, 20 species of grazers, and 29 species of mixed feeders (see <xref ref-type="supplementary-material" rid="DS1">Supplementary material 3</xref> for the full list of name and the number of extant specimens used in this study).</p>
<p>The OR and cusp(id) shape (CS), which were observed on the cutting edge of either the buccal cusp of an upper second molar or the lingual cuspid of a lower second molar, were used for mesowear analysis. Both anterior and posterior cusp(id)s were examined and only the sharper one was scored (<xref ref-type="bibr" rid="B33">Fortelius and Solounias, 2000</xref>). Unworn teeth, heavily worn teeth, and those with broken cusp(id)s were excluded from the analysis. The OR was classified as high or low, depending on how high the cusp(id)s uplift from the valley between them (<xref ref-type="bibr" rid="B54">Merceron et al., 2007</xref>; <xref ref-type="bibr" rid="B9">Blondel et al., 2010</xref>) (<xref ref-type="fig" rid="F2">Figure 2</xref>). The obtained value was calculated using the ImageJ program (v. 1.51k). The CS was recorded by characterizing the cusp(id) apices as sharp, round, or blunt, using a 10 &#x00D7; magnification hand lens (<xref ref-type="fig" rid="F2">Figure 2</xref>). The OR and CS were combined into a single parameter, so-called the MS (<xref ref-type="bibr" rid="B44">Kaiser et al., 2009</xref>). To investigate diets based on the MS, five different levels ranging from 0 to 4 have so far been recognized (<xref ref-type="bibr" rid="B44">Kaiser et al., 2009</xref>). A score of 0 is defined as the most attrition-dominated wear commonly found in leaf browsers, whereas a score of 4 reflects the most abrasion-dominated signal associated with grazing behavior (<xref ref-type="table" rid="T2">Table 2</xref>). The MS of each species was calculated based on the average values of all dental individuals (<xref ref-type="bibr" rid="B45">Kaiser et al., 2013</xref>).</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption><p>Criteria of occlusal reliefs (OR) and cusp shapes (CS) for caprine teeth based on the mesowear II method.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-1000168-g002.tif"/>
</fig>
<table-wrap position="float" id="T2">
<label>TABLE 2</label>
<caption><p>Interpretations of mesowear scores following <xref ref-type="bibr" rid="B44">Kaiser et al. (2009)</xref>.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Occlusal relief (OR)</td>
<td valign="top" align="center">Cusp shape (CS)</td>
<td valign="top" align="center">Mesowear score (MS)</td>
<td valign="top" align="center">Interpretation</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">High</td>
<td valign="top" align="center">Sharp</td>
<td valign="top" align="center">0</td>
<td valign="top" align="center">Lowest abrasion-Highest</td>
</tr>
<tr>
<td valign="top" align="left">High</td>
<td valign="top" align="center">Round</td>
<td valign="top" align="center">1</td>
<td valign="top" align="center">attrition</td>
</tr>
<tr>
<td valign="top" align="left">Low</td>
<td valign="top" align="center">Sharp</td>
<td valign="top" align="center">2</td>
<td valign="top" align="center">&#x2193;</td>
</tr>
<tr>
<td valign="top" align="left">Low</td>
<td valign="top" align="center">Round</td>
<td valign="top" align="center">3</td>
<td valign="top" align="center">Highest abrasion-Lowest</td>
</tr>
<tr>
<td valign="top" align="left">Low</td>
<td valign="top" align="center">Blunt</td>
<td valign="top" align="center">4</td>
<td valign="top" align="center">attrition</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn><p>The lowest score at 0 indicates the lowest abrasion reflecting a browsing habit. The highest score at 4 stands for the highest abrasion corresponding to a grazing habit.</p></fn>
</table-wrap-foot>
</table-wrap>
<p>The MS is more related to intrinsic factors and dietary feeding habits than environmental conditions (<xref ref-type="bibr" rid="B44">Kaiser et al., 2009</xref>). According to the dataset of <xref ref-type="bibr" rid="B45">Kaiser et al. (2013)</xref>, browsers have a low value of MS, while grazers have a high value of MS.</p>
</sec>
<sec id="S2.SS5">
<title>Dental microwear texture analysis</title>
<p>Caprine specimens for DMTA include extant <italic>C. sumatraensis</italic> (<italic>n</italic> = 15), <italic>N. griseus</italic> (<italic>n</italic> = 3), and <italic>N. goral</italic> (<italic>n</italic> = 3) as well as Pleistocene <italic>C. sumatraensis</italic> (<italic>n</italic> = 16), <italic>N. griseus</italic> (<italic>n</italic> = 22), and <italic>N. goral</italic> (<italic>n</italic> = 10). In complement with extant species of serows (<italic>Capricornis</italic>) and gorals (<italic>Naemorhedus</italic>), we also include a comparative dataset of 119 specimens belonging to three extant species of ruminants with known differences in feeding habits for our DMTA. These comparative specimens include a semi-wild cattle <italic>Bos taurus</italic> (<italic>n</italic> = 44), moose <italic>Alces alces</italic> (<italic>n</italic> = 50), and European bison <italic>Bison bonasus</italic> (<italic>n</italic> = 25). The semi-wild cattle from Camargue, Rhone delta, France, have dental microwear textures supporting the dominance of a grazing habit, whereas the moose from Biebrza in Poland is a browser (<xref ref-type="bibr" rid="B52">Merceron et al., 2021</xref>). The European bison from Bia&#x0142;owieza in Poland is identified as having a mixed feeder pattern (<xref ref-type="bibr" rid="B11">Borowski and Kossak, 1972</xref>; <xref ref-type="bibr" rid="B13">Bowyer et al., 2003</xref>; <xref ref-type="bibr" rid="B47">Kowalczyk et al., 2011</xref>). A full list of name and the number of extant specimens used for DMTA is given in <xref ref-type="supplementary-material" rid="DS1">Supplementary material 3</xref>.</p>
<p>Dental microwear analysis was preferentially performed on unbroken upper second molars, mesio-buccal facets of protocones; or metaconules if the former is broken or altered, or lower second molars, disto-buccal facets of protoconids; or hypoconids if the protoconid is broken or altered (<xref ref-type="bibr" rid="B66">Ramdarshan et al., 2017</xref>). Teeth were cleaned with acetone and molds were made using polyvinylsiloxane (Colt&#x00E8;ne/Whaledent AG, Altst&#x00E4;tten, Switzerland, ref 6015-ISO, Regular Body President, medium consistency). The silicone casts were cut and scanned with &#x201C;TRIDENT,&#x201D; a Leica DCM8 white confocal stereoscope with the 100 &#x00D7; objective lens (numerical aperture = 0.90, working distance = 0.90 mm) at the laboratory of PALEVOPRIM, University of Poitiers, France. The surfaces of 200 &#x00D7; 200 micrometers were extracted from the occlusal surfaces and aberrant peaks erased, using a template shown on the Leica Map software version 7.4.8737 (<xref ref-type="fig" rid="F3">Figure 3</xref>), following the protocol in <xref ref-type="bibr" rid="B56">Merceron et al. (2016)</xref>. Dental surfaces were analyzed through the SSFA using the Sfdx version 1.0.11 and Toothfrax version 1.0 beta 1.7 software (<xref ref-type="bibr" rid="B73">Scott et al., 2006</xref>). According to <xref ref-type="bibr" rid="B73">Scott et al. (2006)</xref>, four microwear texture variables were extracted from dental surfaces: complexity (Asfc), anisotropy (epLsar), heterogeneity (HAsfc), and textural fill volume (Tfv) (<xref ref-type="fig" rid="F4">Figure 4</xref>; <xref ref-type="table" rid="T4">Table 4</xref>).</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption><p>Dental microwear textures from the second molars of <bold>(A)</bold> extant <italic>C. sumatraensis</italic>, <bold>(B)</bold> Pleistocene <italic>C. sumatraensis</italic>, <bold>(C)</bold> extant <italic>N. griseus</italic>, <bold>(D)</bold> Pleistocene <italic>N. griseus</italic>, <bold>(E)</bold> extant <italic>N. goral</italic>, and <bold>(F)</bold> Pleistocene <italic>N. goral</italic>. Scale bars = 50 &#x03BC;m.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-1000168-g003.tif"/>
</fig>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption><p>Schematic illustration of microwear surfaces showing high and low values for four variables including complex textures, anisotropic textures, heterogeneous textures, and textural fill volume [modified from <xref ref-type="bibr" rid="B73">Scott et al. (2006)</xref> and <xref ref-type="bibr" rid="B55">Merceron et al. (2014)</xref>].</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-1000168-g004.tif"/>
</fig>
<p>To investigate dietary differences between extinct and extant caprines, we ran an analysis of variance (ANOVA) (after box-cox transformation), using SPSS version 22.0, together with the three reference species as mentioned above. <italic>Post-hoc</italic> tests, run after ANOVA, were done using Tukey&#x2019;s honest significant difference (HSD) and Fisher&#x2019;s least significant difference (LSD) (Bonferroni adjustment) tests to balance the type I and II errors (<xref ref-type="bibr" rid="B21">Cook and Farewell, 1996</xref>) (<xref ref-type="table" rid="T5">Table 5</xref>). Browsers usually have higher complexity and textural fill volume values, resulting from their consumption of hard objects (e.g., lignin-bearing woody tissues such as twigs, shoots, bark but also fruits with seeds) (<xref ref-type="bibr" rid="B73">Scott et al., 2006</xref>; <xref ref-type="bibr" rid="B72">Scott, 2012</xref>). Grazers mainly feed on herbaceous monocotyledons (mostly grasses, sedges and rushes), which contain higher silica phytolith content than dicots (<xref ref-type="bibr" rid="B73">Scott et al., 2006</xref>; <xref ref-type="bibr" rid="B72">Scott, 2012</xref>). The shearing of this foliage results in higher anisotropy and lower complexity for grazing species, while the crushing cation on hard food objects seen in browsers is considered to generate complex and isotropic textures on enamel surfaces (<xref ref-type="bibr" rid="B73">Scott et al., 2006</xref>; <xref ref-type="bibr" rid="B72">Scott, 2012</xref>).</p>
<p>However, it is noteworthy that leaf-browsing species may have a combination of low anisotropy with low to intermediate complexity such as <italic>Giraffa camelopardalis</italic> or <italic>A. alces</italic> or high anisotropy with low to intermediate complexity such as <italic>Capreolus capreolus</italic> (<xref ref-type="bibr" rid="B53">Merceron et al., 2018</xref>, <xref ref-type="bibr" rid="B52">2021</xref>). Analyzing the heterogeneity of complexity reflects a large diversity in feeding resources. Hence, leaf browsers or grazers would have lower heterogeneity than mixed feeders or browsers with a wide spectrum of food items and various mechanical properties (<xref ref-type="bibr" rid="B73">Scott et al., 2006</xref>; <xref ref-type="bibr" rid="B72">Scott, 2012</xref>).</p>
</sec>
</sec>
<sec id="S3" sec-type="results">
<title>Results</title>
<sec id="S3.SS1">
<title>Hypsodonty and mesowear II</title>
<p>The Pleistocene <italic>C. sumatraensis</italic> has the lowest HI of 2.77 and the lowest MS of 0.89 (<xref ref-type="fig" rid="F5">Figure 5</xref>). The Pleistocene <italic>N. goral</italic> has the highest HI of 3.95 and the Pleistocene <italic>N. griseus</italic> displayed the highest MS of 1.50. The dental morphology of <italic>C. sumatraensis</italic> that has lower molar crowns than other two goral species possibly suggests its dietary adaptation for more browsing habits.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption><p>A bivariate plot of hypsodonty index (HI) against mesowear score (MS). The comparative dataset of extant ungulates is derived from <xref ref-type="bibr" rid="B45">Kaiser et al. (2013)</xref>. Cs, extant <italic>C. sumatraensis</italic>, Ngr, extant <italic>N. griseus</italic>, Ngo, extant <italic>N. goral</italic>, CsP, Pleistocene <italic>C. sumatraensis</italic>, NgrP, Pleistocene <italic>N. griseus</italic>, and NgoP, Pleistocene <italic>N. goral</italic>.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-1000168-g005.tif"/>
</fig>
<p>In extant populations, <italic>C. sumatraensis</italic> has the lowest MS of 0.54 and <italic>N. goral</italic> shows the highest MS of 1.40 (<xref ref-type="table" rid="T3">Table 3</xref>). Both HI and MS have shown that the Pleistocene and extant <italic>C. sumatraensis</italic> falls within a 95% confidence ellipse for browsers, while <italic>Naemorhedus</italic> is out of it. All analyzed caprine taxa tend to be assembled in a 95% confidence ellipse for mixed feeders, overlapping with grazers for <italic>N. griseus</italic> and <italic>N. goral</italic> (<xref ref-type="fig" rid="F5">Figure 5</xref>). The degree of hypsodonty and mesowear-II results has shown the trend that the Pleistocene Southeast Asian caprines preferentially occupied open habitats, although <italic>C. sumatraensis</italic> has the lower HI and MS than the other two goral species. This probably reflects less grit digestion from the surrounding areas or living in a more closed habitat than <italic>Naemorhedus</italic>.</p>
<table-wrap position="float" id="T3">
<label>TABLE 3</label>
<caption><p>Hypsodonty index (HI) for species and mesowear score (MS) of extant and Pleistocene caprines.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Species</td>
<td valign="top" align="center"><italic>n</italic></td>
<td valign="top" align="center">HI &#x00B1; SE</td>
<td valign="top" align="center">MS</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" colspan="4"><bold>Extant</bold></td>
</tr>
<tr>
<td valign="top" align="left"><italic>C. sumatraensis</italic></td>
<td valign="top" align="center">22</td>
<td valign="top" align="center">2.77&#x002A;</td>
<td valign="top" align="center">0.54</td>
</tr>
<tr>
<td valign="top" align="left"><italic>N. griseus</italic></td>
<td valign="top" align="center">12</td>
<td valign="top" align="center">3.61&#x002A;</td>
<td valign="top" align="center">1.08</td>
</tr>
<tr>
<td valign="top" align="left"><italic>N. goral</italic></td>
<td valign="top" align="center">5</td>
<td valign="top" align="center">3.95&#x002A;</td>
<td valign="top" align="center">1.40</td>
</tr>
<tr>
<td valign="top" align="left" colspan="4"><bold>Pleistocene</bold></td>
</tr>
<tr>
<td valign="top" align="left"><italic>C. sumatraensis</italic></td>
<td valign="top" align="center">19</td>
<td valign="top" align="center">2.77 &#x00B1; 0.30</td>
<td valign="top" align="center">0.89</td>
</tr>
<tr>
<td valign="top" align="left"><italic>N. griseus</italic></td>
<td valign="top" align="center">22</td>
<td valign="top" align="center">3.61 &#x00B1; 0.37</td>
<td valign="top" align="center">1.50</td>
</tr>
<tr>
<td valign="top" align="left"><italic>N. goral</italic></td>
<td valign="top" align="center">22</td>
<td valign="top" align="center">3.95 &#x00B1; 0.28</td>
<td valign="top" align="center">1.00</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn><p>Asterisks refer to the average values of a species that are calculated based on the Pleistocene isolated teeth. The number of specimens analyzed (n) and standard error (SE) are given.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap position="float" id="T4">
<label>TABLE 4</label>
<caption><p>Descriptive statistics (mean and standard error, SE) of microwear textural parameters for Pleistocene and extant caprines and reference species.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Species</td>
<td valign="top" align="center"><italic>n</italic></td>
<td valign="top" align="center" colspan="2">Asfc</td>
<td valign="top" align="center" colspan="2">epLsar<xref ref-type="table-fn" rid="t4fn1">&#x002A;</xref></td>
<td valign="top" align="center" colspan="2">HAsfc</td>
<td valign="top" align="center" colspan="2">Tfv</td>
</tr>
<tr>
<td valign="top" align="center"></td>
<td valign="top" align="center"></td>
<td valign="top" align="center" colspan="2"><hr/></td>
<td valign="top" align="center" colspan="2"><hr/></td>
<td valign="top" align="center" colspan="2"><hr/></td>
<td valign="top" align="center" colspan="2"><hr/></td>
</tr>
<tr>
<td/>
<td/>
<td valign="top" align="center">Mean</td>
<td valign="top" align="center">SE</td>
<td valign="top" align="center">Mean</td>
<td valign="top" align="center">SE</td>
<td valign="top" align="center">Mean</td>
<td valign="top" align="center">SE</td>
<td valign="top" align="center">Mean</td>
<td valign="top" align="center">SE</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" colspan="10"><bold>Pleistocene</bold></td>
</tr>
<tr>
<td valign="top" align="left"><italic>C. sumatraensis</italic></td>
<td valign="top" align="center">16</td>
<td valign="top" align="center">2.64</td>
<td valign="top" align="center">0.35</td>
<td valign="top" align="center">2.82</td>
<td valign="top" align="center">0.46</td>
<td valign="top" align="center">0.33</td>
<td valign="top" align="center">0.03</td>
<td valign="top" align="center">38698.12</td>
<td valign="top" align="center">3939.84</td>
</tr>
<tr>
<td valign="top" align="left"><italic>N. griseus</italic></td>
<td valign="top" align="center">22</td>
<td valign="top" align="center">5.20</td>
<td valign="top" align="center">1.03</td>
<td valign="top" align="center">2.83</td>
<td valign="top" align="center">0.43</td>
<td valign="top" align="center">0.92</td>
<td valign="top" align="center">0.26</td>
<td valign="top" align="center">35163.48</td>
<td valign="top" align="center">3392.93</td>
</tr>
<tr>
<td valign="top" align="left"><italic>N. goral</italic></td>
<td valign="top" align="center">10</td>
<td valign="top" align="center">3.20</td>
<td valign="top" align="center">0.56</td>
<td valign="top" align="center">3.56</td>
<td valign="top" align="center">0.85</td>
<td valign="top" align="center">0.59</td>
<td valign="top" align="center">0.12</td>
<td valign="top" align="center">43971.79</td>
<td valign="top" align="center">3431.24</td>
</tr>
<tr>
<td valign="top" align="left" colspan="10"><bold>Extant</bold></td>
</tr>
<tr>
<td valign="top" align="left"><italic>C. sumatraensis</italic></td>
<td valign="top" align="center">15</td>
<td valign="top" align="center">2.14</td>
<td valign="top" align="center">0.31</td>
<td valign="top" align="center">2.78</td>
<td valign="top" align="center">0.44</td>
<td valign="top" align="center">0.42</td>
<td valign="top" align="center">0.05</td>
<td valign="top" align="center">39626.54</td>
<td valign="top" align="center">2238.82</td>
</tr>
<tr>
<td valign="top" align="left"><italic>N. griseus</italic></td>
<td valign="top" align="center">3</td>
<td valign="top" align="center">4.62</td>
<td valign="top" align="center">1.28</td>
<td valign="top" align="center">3.76</td>
<td valign="top" align="center">0.42</td>
<td valign="top" align="center">0.63</td>
<td valign="top" align="center">0.03</td>
<td valign="top" align="center">40602.04</td>
<td valign="top" align="center">1365.99</td>
</tr>
<tr>
<td valign="top" align="left"><italic>N. goral</italic></td>
<td valign="top" align="center">3</td>
<td valign="top" align="center">1.36</td>
<td valign="top" align="center">0.68</td>
<td valign="top" align="center">7.14</td>
<td valign="top" align="center">0.79</td>
<td valign="top" align="center">0.43</td>
<td valign="top" align="center">0.16</td>
<td valign="top" align="center">33136.44</td>
<td valign="top" align="center">4745.47</td>
</tr>
<tr>
<td valign="top" align="left" colspan="10"><bold>Reference species</bold></td>
</tr>
<tr>
<td valign="top" align="left"><italic>B. taurus</italic></td>
<td valign="top" align="center">44</td>
<td valign="top" align="center">1.57</td>
<td valign="top" align="center">0.14</td>
<td valign="top" align="center">5.17</td>
<td valign="top" align="center">0.31</td>
<td valign="top" align="center">0.42</td>
<td valign="top" align="center">0.04</td>
<td valign="top" align="center">38042.30</td>
<td valign="top" align="center">1487.57</td>
</tr>
<tr>
<td valign="top" align="left"><italic>A. alces</italic></td>
<td valign="top" align="center">50</td>
<td valign="top" align="center">4.02</td>
<td valign="top" align="center">0.45</td>
<td valign="top" align="center">2.36</td>
<td valign="top" align="center">0.26</td>
<td valign="top" align="center">0.73</td>
<td valign="top" align="center">0.10</td>
<td valign="top" align="center">30177.99</td>
<td valign="top" align="center">2598.65</td>
</tr>
<tr>
<td valign="top" align="left"><italic>Bison bonasus</italic></td>
<td valign="top" align="center">25</td>
<td valign="top" align="center">2.30</td>
<td valign="top" align="center">0.31</td>
<td valign="top" align="center">3.28</td>
<td valign="top" align="center">0.38</td>
<td valign="top" align="center">0.47</td>
<td valign="top" align="center">0.04</td>
<td valign="top" align="center">36507.70</td>
<td valign="top" align="center">2313.68</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="t4fn1"><p>Asterisks (&#x002A;) indicate values multiplied by 1000 (&#x00D7;1000). Asfc, complexity; epLsar, anisotropy; HAsfc, heterogeneity; Tfv, textural fill volume.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap position="float" id="T5">
<label>TABLE 5</label>
<caption><p><italic>Post-hoc</italic> test and pairwise multiple comparisons between caprines and reference species.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Species</td>
<td valign="top" align="center">CsP</td>
<td valign="top" align="center">NgrP</td>
<td valign="top" align="center">NgoP</td>
<td valign="top" align="center">Cs</td>
<td valign="top" align="center">Ngr</td>
<td valign="top" align="center">Ngo</td>
<td valign="top" align="center"><italic>Bos</italic></td>
<td valign="top" align="center"><italic>Alces</italic></td>
<td valign="top" align="center"><italic>Bison</italic></td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left"><bold>CsP</bold></td>
<td/>
<td/>
<td/>
<td/>
<td/>
<td valign="top" align="center"><bold>epLsar</bold></td>
<td valign="top" align="center"><bold>epLsar</bold></td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><bold>NgrP</bold></td>
<td valign="top" align="center"><underline>Asfc, HAsfc</underline></td>
<td/>
<td/>
<td valign="top" align="center"><bold>Asfc</bold></td>
<td/>
<td valign="top" align="center"><bold>epLsar</bold></td>
<td valign="top" align="center"><bold>Asfc, epLsar, HAsfc</bold></td>
<td/>
<td valign="top" align="center"><bold>Asfc</bold></td>
</tr>
<tr>
<td valign="top" align="left"><bold>NgoP</bold></td>
<td/>
<td valign="top" align="center"><underline>Asfc</underline></td>
<td/>
<td/>
<td/>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><bold>Cs</bold></td>
<td/>
<td valign="top" align="center"><underline>HAsfc</underline></td>
<td/>
<td/>
<td/>
<td valign="top" align="center"><bold>epLsar</bold></td>
<td valign="top" align="center"><bold>epLsar</bold></td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><bold>Ngr</bold></td>
<td/>
<td/>
<td/>
<td/>
<td/>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><bold>Ngo</bold></td>
<td/>
<td valign="top" align="center"><underline>Asfc</underline></td>
<td valign="top" align="center"><underline>epLsar</underline></td>
<td valign="top" align="center"><underline>epLsar</underline></td>
<td valign="top" align="center"><underline>epLsar</underline></td>
<td/>
<td/>
<td valign="top" align="center"><bold>epLsar</bold></td>
<td valign="top" align="center"><bold>epLsar</bold></td>
</tr>
<tr>
<td valign="top" align="left"><italic><bold>Bos</bold></italic></td>
<td/>
<td valign="top" align="center"><underline>HAsfc</underline></td>
<td valign="top" align="center"><underline>epLsar</underline></td>
<td/>
<td/>
<td/>
<td/>
<td valign="top" align="center"><bold>Asfc, epLsar</bold></td>
<td valign="top" align="center"><bold>epLsar</bold></td>
</tr>
<tr>
<td valign="top" align="left"><italic><bold>Alces</bold></italic></td>
<td valign="top" align="center"><underline>HAsfc, Tfv</underline></td>
<td valign="top" align="center"><underline>Tfv</underline></td>
<td valign="top" align="center"><underline>Tfv</underline></td>
<td valign="top" align="center"><underline>Asfc, HAsfc</underline></td>
<td/>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic><bold>Bison</bold></italic></td>
<td/>
<td valign="top" align="center"><underline>HAsfc</underline></td>
<td/>
<td/>
<td/>
<td/>
<td/>
<td/>
<td/>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn><p>Significant differences in microwear variables using Tukey&#x2019;s HSD appear in bold. Significant differences in microwear variables using Fisher&#x2019;s LSD are underlined. Cs, extant C. sumatraensis; CsP, Pleistocene C. sumatraensis; Ngo, extant N. goral; NgoP, Pleistocene N. goral; Ngr, extant N. griseus; NgoP, Pleistocene N. griseus. The abbreviations of microwear texture variables are the same as <xref ref-type="table" rid="T4">Table 4</xref>. A p-value of 0.05 or less (p &#x2264; 0.05) is considered statistically significant.</p></fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="S3.SS2">
<title>Dental microwear texture analysis</title>
<p>Descriptive statistics of fossil and extant caprines and <italic>post-hoc</italic> tests using the ANOVA are shown in <xref ref-type="table" rid="T4">Tables 4</xref>, <xref ref-type="table" rid="T5">5</xref>, respectively. According to the results of ANOVA, complexity, anisotropy, and heterogeneity of complexity have showed significant differences between species (with <italic>p</italic> &#x003C; 0.001, <italic>p</italic> &#x003C; 0.001, and <italic>p</italic> = 0.027, respectively). The browsing moose <italic>A. alces</italic> has the highest complexity of 4.02 and the lowest anisotropy of 2.36 &#x00D7; 10<sup>&#x2013;3</sup>. Conversely, the semi-wild grazing <italic>B. taurus</italic> has the lowest complexity of 1.57 and the highest anisotropy of 5.17 &#x00D7; 10<sup>&#x2013;3</sup>. The intermediate values of complexity and anisotropy are found in extant <italic>B. bonasus</italic>. The heterogeneity of complexity between extant <italic>B. taurus</italic> and <italic>B. bonasus</italic> displays a similar range of values, whereas <italic>A. alces</italic> has the highest value of 0.73. The textural fill volume of <italic>B. taurus</italic> shows the highest value, followed by <italic>B. bonasus</italic> and <italic>A. alces</italic> (<xref ref-type="table" rid="T4">Tables 4</xref>, <xref ref-type="table" rid="T5">5</xref> and see <xref ref-type="supplementary-material" rid="DS1">Supplementary material 4</xref> for both HSD and LSD tests including extinct and extant species). In comparison with the comparative species, the extant <italic>C. sumatraensis</italic> showed a significantly lower anisotropy than <italic>B. taurus</italic> (<xref ref-type="table" rid="T4">Tables 4</xref>, <xref ref-type="table" rid="T5">5</xref>). Both extant <italic>Naemorhedus</italic> species had a higher anisotropy than <italic>A. alces</italic> and <italic>B. bonasus</italic>, although a significant difference was found only in <italic>N. goral</italic>. The Pleistocene <italic>C. sumatraensis</italic> and <italic>N. griseus</italic> have significantly lower anisotropy, compared to those of extant <italic>B. taurus</italic>. The complexity of Pleistocene <italic>N. griseus</italic> is significantly higher than that of <italic>B. taurus</italic> and <italic>B. bonasus</italic>.</p>
<p>The DMTA has provided more detailed information for caprine diets in shorter temporal extent. Three extant Eurasian ruminant species whose dietary differences are recognized serve us as a standard comparison for the extinct species and some extant taxa. The high complexity and low anisotropy of extant <italic>A. alces</italic> are characteristic of browsing species, which include woody lignin-enriched elements in their diet (<xref ref-type="bibr" rid="B7">Berlioz et al., 2022</xref>). Conversely, the grazing <italic>B. taurus</italic> shows low complexity and high anisotropy, similar to several other African and Eurasian grazers (<xref ref-type="bibr" rid="B89">Ungar et al., 2007</xref>; <xref ref-type="bibr" rid="B71">Schulz et al., 2010</xref>; <xref ref-type="bibr" rid="B72">Scott, 2012</xref>; <xref ref-type="bibr" rid="B6">Berlioz et al., 2017</xref>). The anisotropy is related to the folivory, notably the ingestion of tough foliages requiring high slicing motion (<xref ref-type="bibr" rid="B73">Scott et al., 2006</xref>; <xref ref-type="bibr" rid="B72">Scott, 2012</xref>). When associated with low complexity, this evidence indicates the consumption of herbaceous silica-bearing monocots and the absence of woody material rich in lignin, which requires crushing to extract energy from cell content (<xref ref-type="bibr" rid="B72">Scott, 2012</xref>; <xref ref-type="bibr" rid="B56">Merceron et al., 2016</xref>). The intermediate values of complexity and anisotropy present in <italic>B. bonasus</italic> represent mixed feeding habits.</p>
<p>The extant <italic>C. sumatraensis</italic> has a browsing habit, as indicated by low complexity and anisotropy (<xref ref-type="table" rid="T4">Table 4</xref>). The extant <italic>N. goral</italic> shows a grazing signal based on microwear results but the low sample size prevents us to make definitive judgments. In any case, these dietary reconstructions are congruent with other existing ecological evidence. Although the dental microwear textures of extant <italic>N. griseus</italic> (<italic>n</italic> = 3) show a similar pattern of feeding habits with <italic>N. goral</italic>, the highest value of complexity and textural fill volume may represent more browsing habits for the former (<xref ref-type="table" rid="T4">Table 4</xref>). The small sample sizes of extant gorals for DMTA (<italic>n</italic> = 3 per species) should be taken into consideration and may require additional analyses.</p>
<p>The Pleistocene <italic>C. sumatraensis</italic> and <italic>N. griseus</italic> have significantly lower anisotropy than the extant <italic>B. taurus</italic> (<xref ref-type="table" rid="T5">Table 5</xref>), whereas the Pleistocene <italic>N. goral</italic> has slightly higher anisotropy than the extant <italic>A. alces</italic> and <italic>B. bonasus</italic> (<xref ref-type="table" rid="T4">Table 4</xref>). We infer that the Pleistocene <italic>C. sumatraensis</italic> and <italic>N. griseus</italic> likely fed on fewer herbaceous monocotyledons than <italic>N. goral</italic>. The Pleistocene <italic>C. sumatraensis</italic> has the lowest complexity, compared to other Pleistocene species (<xref ref-type="table" rid="T4">Table 4</xref>). In addition, the Pleistocene <italic>N. griseus</italic> has significantly higher complexity than the extant <italic>A. alces</italic> (<xref ref-type="table" rid="T4">Table 4</xref>), indicating the consumption of hard objects for the former (<xref ref-type="bibr" rid="B65">Ramdarshan et al., 2016</xref>). The Pleistocene <italic>N. griseus</italic> might have chiefly fed on harder food items such as seeds and lignified plant tissues, which require highly efficient crushing actions. However, the Pleistocene <italic>C. sumatraensis</italic> and two goral species were likely to be mixed feeders, but <italic>C. sumatraensis</italic> tended to feed on softer objects.</p>
</sec>
</sec>
<sec id="S4" sec-type="discussion">
<title>Discussion</title>
<sec id="S4.SS1">
<title>Niche partitioning between <italic>Capricornis</italic> and <italic>Naemorhedus</italic></title>
<p>Regarding the previous studies of extant caprine diets, <italic>C. sumatraensis</italic> in Thailand has high intakes of dicotyledons, especially soft shoots of trees, as exemplified by analyses of feces and stomach contents as well as by field observations, notably through bite marks on plants (<xref ref-type="bibr" rid="B18">Chairat, 2007</xref>; <xref ref-type="bibr" rid="B43">Junshum et al., 2010</xref>; <xref ref-type="bibr" rid="B61">Nakasathien, 2017</xref>). In contrast, <italic>N. griseus</italic> in Thailand (previously assigned to <italic>N. goral</italic>) mainly feeds on a higher percentage of monocotyledon grasses than <italic>C. sumatraensis</italic> does (<xref ref-type="bibr" rid="B19">Chaiyarat et al., 1999</xref>), suggesting mixed feeding habits for the former. Other dietary observations on the living caprine populations from northern Thailand have indicated that <italic>N. griseus</italic> feeds on fallen dry leaves and grasses (<xref ref-type="bibr" rid="B62">Nimitsin, 2012</xref>). <italic>N. goral</italic> from Kashmir, India feeds more frequently on herbaceous monocotyledons (grasses, sedges, rushes) than on dicotyledon shrubs and trees (<xref ref-type="bibr" rid="B42">Junaid et al., 2012</xref>), like <italic>N. griseus</italic> in Thailand. Moreover, <italic>N. goral</italic> from Binsar Wildlife Sanctuary in India contains the high ratio of grasses in feces (<xref ref-type="bibr" rid="B36">Ilyas and Khan, 2004</xref>), implying a grass-dominated mixed feeding habit.</p>
<p>The HI and mesowear II results have shown mixed feeding habits for both extant and Pleistocene caprines, congruent with the HI and mesowear I interpretations mentioned by <xref ref-type="bibr" rid="B37">Isarankura Na Ayudhya et al. (2021)</xref>. For the extant populations of <italic>Capricornis</italic> and <italic>Naemorhedus</italic>, our results based on the HI and MS are congruent with several previous studies on dietary interpretations of caprines (e.g., <xref ref-type="bibr" rid="B36">Ilyas and Khan, 2004</xref>; <xref ref-type="bibr" rid="B18">Chairat, 2007</xref>, <xref ref-type="bibr" rid="B62">Nimitsin, 2012</xref>). The results showed two possibilities of dietary interpretations in Pleistocene and extant <italic>C. sumatraensis</italic>, either mixed-feeding or browsing habits.</p>
<p>Dietary interpretations based on the DMTA results probably reflect inter- and intraspecific competition among the Pleistocene caprine populations. Based on the Tukey&#x2019;s HSD tests, there are no significant differences in microwear variables between the Pleistocene serows and gorals (<xref ref-type="table" rid="T5">Table 5</xref>), suggesting dietary overlaps among sympatric populations, at least in terms of food properties. When focusing on the less conservative Fisher&#x2019;s LSD tests, the Pleistocene <italic>N. griseus</italic> from Tham Lod Rockshelter shows significantly higher complexity and heterogeneity than the other Pleistocene <italic>C. sumatraensis</italic> in Thailand (<xref ref-type="table" rid="T4">Tables 4</xref>, <xref ref-type="table" rid="T5">5</xref>), reflecting more browsing habits for the former. Both Pleistocene and extant <italic>N. griseus</italic> has also the highest heterogeneity, compared to other analyzed caprines in this study (<xref ref-type="table" rid="T4">Tables 4</xref>, <xref ref-type="table" rid="T5">5</xref>), indicating more browsing habits. Small differences in dietary investigations using DMTA suggest that three Pleistocene caprine species might have shared food resources if they had coexisted.</p>
<p>However, as seen in their extant populations from western Sichuan in China, <italic>C. sumatraensis</italic> occupies steep slopes with high shrub density, while <italic>N. griseus</italic> tends to dwell in a high-altitude meadow (<xref ref-type="bibr" rid="B20">Chen et al., 2009</xref>). Although extant <italic>C. sumatraensis</italic> and <italic>N. griseus</italic> may have different habitat preferences, the interspecific competition in habitat use between both taxa is observed from the mountainous areas of Chiang Mai, northern Thailand (<xref ref-type="bibr" rid="B19">Chaiyarat et al., 1999</xref>; <xref ref-type="bibr" rid="B61">Nakasathien, 2017</xref>). The larger-sized and aggressive <italic>C. sumatraensis</italic> usually forces <italic>N. griseus</italic> out of coexisting areas (<xref ref-type="bibr" rid="B19">Chaiyarat et al., 1999</xref>; <xref ref-type="bibr" rid="B61">Nakasathien, 2017</xref>). For instance, these authors mentioned that one to six serow individuals that form herd (<xref ref-type="bibr" rid="B62">Nimitsin, 2012</xref>; <xref ref-type="bibr" rid="B61">Nakasathien, 2017</xref>) usually overcome a single or couple of <italic>N. griseus</italic> and successfully occupy the coexistence areas. The competition of natural resources between two extant caprine species might have led to the decreasing populations of a smaller-sized goral <italic>N. griseus</italic>. In contrast, studies on temporal activity patterns observed in extant caprine communities have revealed that gorals are likely to be active at the beginning of daytime from dawn to late morning, while serows are energetic after late afternoon to night (<xref ref-type="bibr" rid="B8">Bhattacharya et al., 2012</xref>; <xref ref-type="bibr" rid="B50">Lovari et al., 2020</xref>). It is presumable that although the dental microwear textures suggest small differences in dietary preferences between <italic>Capricornis</italic> (soft foliage) and <italic>Naemorhedus</italic> (harder food object), niche partitioning might have occurred in other different ways.</p>
</sec>
<sec id="S4.SS2">
<title>Ecological adaptations of caprines through time</title>
<p>As the degree of HI combined with mesowear II results showed similarities in feeding habits between these three Pleistocene and extant caprine taxa (<xref ref-type="table" rid="T6">Table 6</xref>), comparisons between stable carbon isotope data and DMTA provide more detailed ecological interpretations of each species through time.</p>
<table-wrap position="float" id="T6">
<label>TABLE 6</label>
<caption><p>Summary of dietary interpretations of Pleistocene and extant caprines based on dental wear pattern and stable carbon isotope studies.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left"></td>
<td valign="top" align="left">Species</td>
<td valign="top" align="left">Mesowear I with hypsodonty index (<xref ref-type="bibr" rid="B37">Isarankura Na Ayudhya et al., 2021</xref>)</td>
<td valign="top" align="left">Mesowear II with hypsodonty index (this study)</td>
<td valign="top" align="left">DMTA (this study)</td>
<td valign="top" align="left">Stable carbon isotopes of tooth enamel (literatures)</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left"><bold>Pleistocene</bold></td>
<td valign="top" align="left"><italic>C. sumatraensis</italic></td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Soft plant-dominated browsing habit<break/> Low heterogeneity of diets at intra-individual scale</td>
<td valign="top" align="left">Pure C<sub>4</sub> and C<sub>3</sub> signals from Boh Dambang populations in Cambodia (<xref ref-type="bibr" rid="B3">Bacon et al., 2018b</xref>)<break/> Pure C<sub>4</sub> and C<sub>3</sub> signals from Tham Wiman Nakin populations in Northeastern Thailand (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>)<break/> Pure C<sub>3</sub> signals from Khok Sung (Northeastern Thailand) and Nam Lot (northern Laos) populations (<xref ref-type="bibr" rid="B2">Bacon et al., 2018a</xref>; <xref ref-type="bibr" rid="B77">Suraprasit et al., 2018</xref>, <xref ref-type="bibr" rid="B81">2020</xref>)</td>
</tr>
<tr>
<td/>
<td valign="top" align="left"><italic>N. griseus</italic></td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Hard-item mixed feeding habit<break/> High heterogeneity of diets at intra-individual scale</td>
<td valign="top" align="left">Pure C<sub>4</sub> signals from Tham Lod Rockshelter populations in northern Thailand (<xref ref-type="bibr" rid="B83">Suraprasit et al., 2021b</xref>)</td>
</tr>
<tr>
<td/>
<td valign="top" align="left"><italic>N. goral</italic></td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Mixed feeding habit<break/> Intermediate heterogeneity of diets at intra-individual scale</td>
<td valign="top" align="left">Pure C<sub>4</sub> to mixed C<sub>3</sub>/C<sub>4</sub> signals from Tham Wiman Nakin populations in Northeastern Thailand (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>)<break/> Pure C<sub>4</sub> signals from Pha Bong populations in northern Thailand (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"><bold>Extant</bold></td>
<td valign="top" align="left"><italic>C. sumatraensis</italic></td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Soft leaf-dominated browsing habit<break/> Intermediate heterogeneity of diets at intra-individual scale</td>
<td valign="top" align="left">Pure C<sub>3</sub> signals from Thung Yai populations in Thailand and populations in Laos (<xref ref-type="bibr" rid="B64">Pushkina et al., 2010</xref>)<break/> Pure C<sub>3</sub> and possible C<sub>3</sub>/C<sub>4</sub> signals from populations in Thailand and in Sumatra Island, Indonesia (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>)</td>
</tr>
<tr>
<td/>
<td valign="top" align="left"><italic>N. griseus</italic></td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Hard-item mixed feeding habit<break/> High heterogeneity of diets at intra-individual scale</td>
<td valign="top" align="left">Pure C<sub>4</sub> to mixed C<sub>3</sub>/C<sub>4</sub> signals from populations in northern Thailand (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>)</td>
</tr>
<tr>
<td/>
<td valign="top" align="left"><italic>N. goral</italic></td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Mixed feeding habit</td>
<td valign="top" align="left">Mixed feeding habit<break/> Intermediate heterogeneity of diets at intra-individual scale</td>
<td valign="top" align="left">Pure C<sub>3</sub> to mixed C<sub>3</sub>/C<sub>4</sub> signals from populations in Himalayan, Nepal, and western China (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>)</td>
</tr>
</tbody>
</table></table-wrap>
<sec id="S4.SS2.SSS1">
<title>Capricornis sumatraensis</title>
<p>The Pleistocene <italic>C. sumatraensis</italic> had enamel <italic>&#x03B4;</italic><sup>13</sup>C results congruent with the DMTA analysis. The <italic>&#x03B4;</italic><sup>13</sup>C values of tooth enamel of <italic>C. sumatraensis</italic> from the late middle Pleistocene of Tham Wiman Nakin [range: &#x2212;12.8&#x2030; to +1.7&#x2030; and median: &#x2212;11.0&#x2030;; <xref ref-type="bibr" rid="B81">Suraprasit et al. (2020)</xref>] and from the late middle Pleistocene of Khok Sung [range: &#x2212;15.1&#x2030; to &#x2212;11.8&#x2030; and median: &#x2212;13.9&#x2030;; <xref ref-type="bibr" rid="B77">Suraprasit et al. (2018)</xref>] suggested that this species was a pure C<sub>3</sub> feeder and probably seasonally fed on C<sub>4</sub> plants. During the late Pleistocene, stable carbon isotopes in tooth enamel of <italic>C. sumatraensis</italic> from Tham Lod Rockshelter in northern Thailand [range: &#x2212;14.3&#x2030; to +1.9&#x2030; and median: &#x2212;12.2&#x2030;; <xref ref-type="bibr" rid="B83">Suraprasit et al. (2021b)</xref>], from Boh Dambang in Cambodia [range: &#x2212;13.2&#x2030; to +1.6&#x2030; and median: &#x2212;11.5&#x2030;; <xref ref-type="bibr" rid="B3">Bacon et al. (2018b)</xref>], and Nam Lot in northern Laos (range: &#x2212;14.6&#x2030; to &#x2212;13.0&#x2030; and median: &#x2212;13.8&#x2030;; <xref ref-type="bibr" rid="B2">Bacon et al., 2018a</xref>) suggested similar patterns in feeding habits between the middle and late Pleistocene <italic>C. sumatraensis</italic>. All the isotope evidence has implied that the Pleistocene <italic>C. sumatraensis</italic> mainly fed on C<sub>3</sub> plants and occasionally on C<sub>4</sub> plants in open canopy areas. The DMTA results of Pleistocene <italic>C. sumatraensis</italic> are congruent with the stable carbon isotope data. The lowest of complexity and heterogeneity of Pleistocene <italic>C. sumatraensis</italic>, compared to the other two gorals (<xref ref-type="table" rid="T4">Table 4</xref>), supported its feeding habit on soft plants with low heterogeneity of diets.</p>
<p>All the recent evidence (stable carbon isotopes, DMTA, and field observations) has suggested browsing habits for extant <italic>C. sumatraensis</italic> (e.g., <xref ref-type="bibr" rid="B18">Chairat, 2007</xref>; <xref ref-type="bibr" rid="B43">Junshum et al., 2010</xref>; <xref ref-type="bibr" rid="B61">Nakasathien, 2017</xref>; <xref ref-type="bibr" rid="B32">Faiznur et al., 2020</xref>; <xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). There are pure C<sub>3</sub> signals of tooth enamel <italic>&#x03B4;</italic><sup>13</sup>C values of extant <italic>C. sumatraensis</italic> populations from Thailand (&#x2212;17.8&#x2030; to &#x2212;8.8&#x2030; and median: &#x2212;15.9&#x2030;; <xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>) and from Sumatra (range: &#x2212;16.6&#x2030; to &#x2212;12.3&#x2030; and median: &#x2212;14.1&#x2030;; <xref ref-type="bibr" rid="B64">Pushkina et al., 2010</xref>; <xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). The DMTA analysis showed that the extant <italic>C. sumatraensis</italic> is a soft leaf-dominated browser and has intermediate heterogeneity of diets, as deduced from the lowest complexity and heterogeneity compared with other extant goral species (<xref ref-type="table" rid="T4">Table 4</xref>). The feeding habits of extant <italic>C. sumatraensis</italic> based on the DMTA and stable carbon isotope interpretations are relatively similar to those of Pleistocene populations (<xref ref-type="table" rid="T6">Table 6</xref>). Evidence from field observations such as nibble traces and feces (<xref ref-type="bibr" rid="B18">Chairat, 2007</xref>; <xref ref-type="bibr" rid="B43">Junshum et al., 2010</xref>; <xref ref-type="bibr" rid="B61">Nakasathien, 2017</xref>; <xref ref-type="bibr" rid="B32">Faiznur et al., 2020</xref>) supports the browsing habit in a closed forest for <italic>C. sumatraensis</italic>, congruent with the DMTA results in this study. Both of Pleistocene and extant <italic>C. sumatraensis</italic> might have had similar dietary feeding habits in browsing on soft foliage. However, the Pleistocene <italic>C. sumatraensis</italic> might have occupied a wider range of habitats than the extant one and have seasonally or occasionally fed on C<sub>4</sub> grasses when open canopies were available.</p>
</sec>
<sec id="S4.SS2.SSS2">
<title>Naemorhedus griseus</title>
<p>The <italic>&#x03B4;</italic><sup>13</sup>C of tooth enamel of <italic>N. griseus</italic> from the late Pleistocene of Tham Lod Rockshelter (range: &#x2212;7.1&#x2030; to +1.9&#x2030; and median: &#x2212;0.4&#x2030;) suggested the consumption of either mixed C<sub>3</sub>/C<sub>4</sub> and pure C<sub>4</sub> plants in open mixed habitats (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). The DMTA results of Pleistocene <italic>N. griseus</italic> had the highest complexity and heterogeneity compared to other Pleistocene caprine species (<xref ref-type="table" rid="T4">Table 4</xref>), indicating a mixed feeding habit with several dietary types of hard food items. During the Pleistocene, <italic>N. griseus</italic> tended to feed on more various and tougher plants and lived in a more open habitat canopy than <italic>C. sumatraensis</italic>.</p>
<p>In extant populations, one stable carbon isotope sample of <italic>N. griseus</italic> was only analyzed (&#x2212;3.3&#x2030;) and fell within the range of a mixed C<sub>3</sub>/C<sub>4</sub> feeder (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). The highest complexity and heterogeneity of three extant <italic>N. griseus</italic> individuals thus provide further information regarding the possibility of a tough plant-dominated mixed feeder for the species (<xref ref-type="table" rid="T4">Table 4</xref>). Moreover, the DMTA results suggested that the Pleistocene <italic>N. griseus</italic> probably lived in more open habitats than the extant populations, although additional samples are required to confirm our interpretation.</p>
</sec>
<sec id="S4.SS2.SSS3">
<title>Naemorhedus goral</title>
<p>The enamel <italic>&#x03B4;</italic><sup>13</sup>C values of <italic>N. goral</italic> from the middle Pleistocene of Pha Bong (range: &#x2212;2.6&#x2030; to +3.0&#x2030; and median: &#x2212;0.5&#x2030;), from the late middle Pleistocene of Tham Wiman Nakin (range &#x2212;3.5&#x2030; to +0.4&#x2030; and median: &#x2212;1.2&#x2030;), and from the late Pleistocene of Tham Lod Rockshelter (range: &#x2212;5.3&#x2030; to &#x2212;0.1&#x2030; and median: &#x2212;3.3&#x2030;) implied a C<sub>4</sub>-dominated grazer living in open grasslands (with sometimes a small amount of C<sub>3</sub> plants in diet) (<xref ref-type="bibr" rid="B10">Bocherens et al., 2017</xref>; <xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). The DMTA results showed that the Pleistocene <italic>N. goral</italic> had high anisotropy with intermediate complexity and heterogeneity compared to the other two contemporaneous caprine taxa (<xref ref-type="table" rid="T4">Table 4</xref>). This probably indicates that the Pleistocene <italic>N. goral</italic> was a C<sub>4</sub>-dominated grazer with intermediate heterogeneity of diets occupying an open habitat. Based on the dental microwear textures, our analysis has shown that extant <italic>N. goral</italic> has a mixture of plant-based diets with several food types, similar to the Pleistocene populations. The apparent discrepancy between stable carbon isotopes and DMTA might be the consequences of the consumption of fresh growing non-abrasive grasses with ingestion of grits or browsing behavior in response to local environmental conditions that occurred few weeks before death. However, several months to a year after the amelogenesis process could have had a chance to record such behavior in the stable carbon isotope composition of enamel prisms.</p>
<p>The extant populations of <italic>N. goral</italic> from Himalaya in Nepal and from western China (range: &#x2212;15.2&#x2030; to &#x2212;6.0&#x2030; and median: &#x2212;12.2&#x2030;) suggested the consumption of pure C<sub>3</sub> (possibly C<sub>3</sub> grasses) or mixed C<sub>3</sub> and C<sub>4</sub> plants with the habitat preference of a closed canopy (<xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>). The DMTA results of extant <italic>N. goral</italic> are congruent with the interpretation obtained from the stable carbon isotope records (<xref ref-type="table" rid="T6">Table 6</xref>). The highest anisotropy and the lowest complexity of extant <italic>N. goral</italic> indicate a grass feeding habit. Taking into account the low sample size, the extant populations of <italic>N</italic>. <italic>goral</italic> possibly feed on a higher amount of C<sub>3</sub> grasses or various food types and/or lived in more closed habitats than the Pleistocene ones.</p>
</sec>
</sec>
<sec id="S4.SS3">
<title>Climatic and environmental impacts on present-day caprine populations</title>
<p>The DMTA results have suggested that the dietary preferences for these three caprine species might have not changed much over the Pleistocene. According to the location of paleontological and archeological sites where the caprine fossils were analyzed in this study (<xref ref-type="fig" rid="F1">Figure 1</xref>), there is no discrepancy in dietary preferences observed among the Pleistocene populations across the latitudinal gradient. The Pleistocene caprines in the coexistence areas possessed mixed feeding behavior, although probably having differences in physical characteristics of foods (e.g., hardness). Isotopic, botanical, and faunal evidence revealed that, during the Pleistocene, mainland Southeast Asia was covered by forest-grassland mosaics with a variety of plant resources available for both grazers and browsers (e.g., <xref ref-type="bibr" rid="B17">Chaimanee, 1998</xref>; <xref ref-type="bibr" rid="B64">Pushkina et al., 2010</xref>; <xref ref-type="bibr" rid="B92">White et al., 2004</xref>; <xref ref-type="bibr" rid="B2">Bacon et al., 2018a</xref>,<xref ref-type="bibr" rid="B3">b</xref>; <xref ref-type="bibr" rid="B95">Yang and Grote, 2018</xref>; <xref ref-type="bibr" rid="B77">Suraprasit et al., 2018</xref>, <xref ref-type="bibr" rid="B82">2019</xref>, <xref ref-type="bibr" rid="B81">2020</xref>, <xref ref-type="bibr" rid="B78">2021a</xref>,<xref ref-type="bibr" rid="B83">b</xref>). During the Holocene, wetter and warmer conditions have contributed to the spread of rainforests and the dominance of C<sub>3</sub> plants in relation to the decline of C<sub>4</sub> grassland landscapes (<xref ref-type="bibr" rid="B46">Kershaw et al., 2001</xref>; <xref ref-type="bibr" rid="B92">White et al., 2004</xref>; <xref ref-type="bibr" rid="B60">Morley, 2012</xref>; <xref ref-type="bibr" rid="B49">Louys and Robert, 2020</xref>; <xref ref-type="bibr" rid="B81">Suraprasit et al., 2020</xref>, <xref ref-type="bibr" rid="B83">2021b</xref>).</p>
<p>Our dental microwear texture results supported the idea that the mosaic habitats of closed forests and open grasslands were present in Thailand during the Pleistocene. Differences in climatic and environmental conditions between the Pleistocene and Holocene have resulted in the ecological adaptation of grass-feeding mammals such as caprines, as it is the case for <italic>C. sumatraensis</italic>. However, we suggest that the anthropogenic activities and especially the agricultural development have had severe impacts on species distribution, spatial behavior, and home ranges of Southeast Asian caprines. Thus, the decreasing number of these present-day caprine populations should be taken into concern for the future conservation plans and management.</p>
</sec>
</sec>
<sec id="S5" sec-type="conclusion">
<title>Conclusion</title>
<p>This study provides insights into diets and feeding habits of Pleistocene and extant caprines in Southeast Asia based on the HI, mesowear II method, and DMTA. The first two approaches have indicated similar dietary preferences and feeding habits between Pleistocene and extant caprine populations, with notice of browsing signals in <italic>C. sumatraensis</italic>. Although the DMTA pointed out that each caprine species has some differences in dietary preferences (food hardness), this approach fails to clearly discriminate the feeding habits between Pleistocene and extant caprine populations. The Pleistocene and extant <italic>C. sumatraensis</italic> has a soft-plant browsing habit, while both goral species are mixed feeders (but <italic>N. griseus</italic> preferring harder food items than the other two species). Previous studies including the stomach content, mesowear I, and stable carbon isotope analyses, together with our DMTA have suggested that mosaic habitats of closed forests and open grasslands were widespread in Thailand during the Pleistocene, but became more limited and were replaced by the expansion of rainforests during the Holocene. This study advocates that the combination of applying HI with the mesowear II methods, stable carbon approaches, and DMTA to the paleoecological study of past and living caprine populations through time is useful for proposing their habitat conservation plans and this aspect should be further extended to other Southeast Asian endangered mammal species in the future.</p>
</sec>
<sec id="S6" sec-type="data-availability">
<title>Data availability statement</title>
<p>The original contributions presented in this study are included in the article/<xref ref-type="supplementary-material" rid="DS1">Supplementary material</xref>, further inquiries can be directed to the corresponding author.</p>
</sec>
<sec id="S7">
<title>Ethics statement</title>
<p>The animal study was reviewed and approved by Department of National Parks, Wildlife and Plant Conservation of Thailand (DNP).</p>
</sec>
<sec id="S8">
<title>Author contributions</title>
<p>JI, GM, TW, and KS conceived the research project, raised funds, and wrote the manuscript. J-JJ, YC, and RS conducted the field excavations and provided the fossil samples. JI, GM, and KS performed and directed the sampling, preparation, and analysis of the material. JI and KS were principal investigators for the project. All authors discussed the results and commented on the manuscript.</p>
</sec>
</body>
<back>
<sec id="S9" sec-type="funding-information">
<title>Funding</title>
<p>This project was funded by the 90<sup>th</sup> Anniversary of Chulalongkorn University Scholarship and the Overseas Research Experience Scholarship for Graduate Student, Graduate School, Chulalongkorn University.</p>
</sec>
<ack><p>We would like to thank the Department of National Parks, Wildlife and Plant Conservation of Thailand (DNP) and to the Department of Mineral Resources (DMR) for giving us access and permissions to the specimens. We also extend our thanks to Athiwat Wattanapituksakul for providing helpful information on archeological sites in Pang Mapha and for all facilities during our sample collection process. We further thank curators and members from institutes and museums: Chulalongkorn University Museum of Natural History (CUMNH), Zoological Museum of Kasetsart University (ZMKU), Forestry Museum of Kasetsart University (FMKU), National Science Museum of Thailand (NSM), and Zoologische Staatssammlung M&#x00FC;nchen (ZSM), for permitting us access to extant caprine specimens and for facilitating our sample collection. We are grateful to all members of the PALEVOPRIM laboratory (CNRS and University of Poitiers, France) for training JI at the University of Poitiers. We appreciate the feedback and valuable comments from the editor and reviewers, which indeed helped us to improve the quality of the manuscript.</p>
</ack>
<sec id="S10" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="S11" sec-type="disclaimer">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec id="S12" sec-type="supplementary-material">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fevo.2022.1000168/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fevo.2022.1000168/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Data_Sheet_1.PDF" id="DS1" mimetype="application/pdf" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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