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Table ¹: Comparison of analysis of variance results for skull (occlusal view) and mandible (side view) shape in Rhipidomys mastacalis from three vegetation classes in Brazil. Object asymmetry and correspondence methods were employed to assess asymmetry for skulls and mandibles, respectively. in Morphological symmetry of Rhipidomys mastacalis (Mammalia, Rodentia, Cricetidae) in fragmented habitats of the Atlantic Forest in Northeastern Brazil: a study on the influence of the environment on an endemic species
<p><b>Table ¹:</b> Comparison of analysis of variance results for skull (occlusal view) and mandible (side view) shape in <i>Rhipidomys mastacalis</i> from three vegetation classes in Brazil.Object asymmetry and correspondence methods were employed to assess asymmetry for skulls and mandibles,respectively.</p><table><tbody><tr><th><b>Shape procrustes ANOVA</b></th></tr></tbody><tbody><tr><th><b>Effect Sum of squares</b></th><td><b>Mean squares</b></td><td><b>Degrees of freedom</b></td><td><i>F statistic</i></td><td><i>p -Value</i></td><td><b>Pillai tr.</b></td><td><i>p -Value</i></td></tr><tr><th><b>Skulls</b></th></tr><tr><th><b>Forested vegetation</b></th></tr><tr><th>Individual</th><td>0.19908517</td><td>0.0004253957</td><td>468</td><td>22.36</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Side</th><td>0.00366522</td><td>0.0002036232</td><td>18</td><td>10.70</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Individual × side</th><td>0.00890443</td><td>0.0000190266</td><td>468</td><td>2.24</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Error 1</th><td>0.00825565</td><td>0.0000084935</td><td>972</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Occupancy mosaics in forested areas</b></th></tr><tr><th>Individual</th><td>0.37829478</td><td>0.0003965354</td><td>954</td><td>18.57</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Side</th><td>0.00547536</td><td>0.0003041869</td><td>18</td><td>14.25</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Individual × side</th><td>0.02037065</td><td>0.0000213529</td><td>954</td><td>1.89</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Error 1</th><td>0.02201359</td><td>0.0000113239</td><td>1944</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Cocoa plantations</b></th></tr><tr><th>Individual</th><td>0.0645902300</td><td>0.0001302222</td><td>496</td><td>5.18</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Side</th><td>0.0113531900</td><td>0.0007095741</td><td>16</td><td>28.23</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Individual × side</th><td>0.0124666800</td><td>0.0000251344</td><td>496</td><td>1.88</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Error 1</th><td>0.0136608800</td><td>0.0000133407</td><td>1024</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Mandibles</b></th></tr><tr><th><b>Forested vegetation</b></th></tr><tr><th>Individual</th><td>0.70443879</td><td>0.0012579264</td><td>560</td><td>8.10</td><td><0.0001</td><td>14.16</td><td><0.0001</td></tr><tr><th>Side</th><td>0.00549957</td><td>0.0002749783</td><td>20</td><td>1.77</td><td>0.0207</td><td>0.0207</td><td>0.0069</td></tr><tr><th>Individual × side</th><td>0.08696012</td><td>0.0001552859</td><td>560</td><td>2.46</td><td><0.0001</td><td>10.75</td><td><0.0001</td></tr><tr><th>Error 1</th><td>0.07312665</td><td>0.0000387718</td><td>1160</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Occupancy mosaics in forested areas</b></th></tr><tr><th>Individual</th><td>1.19843989</td><td>0.0011984399</td><td>1000</td><td>8.16</td><td><0.0001</td><td>14.70</td><td><0.0001</td></tr><tr><th>Side</th><td>0.01169771</td><td>0.0005848855</td><td>20</td><td>3.98</td><td><0.0001</td><td>0.74</td><td>0.0001</td></tr><tr><th>Individual × side</th><td>0.14685738</td><td>0.0001468574</td><td>1000</td><td>3.03</td><td><0.0001</td><td>11.21</td><td><0.0001</td></tr><tr><th>Error 1</th><td>0.09880745</td><td>0.0000484350</td><td>2040</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Cocoa plantations</b></th></tr><tr><th>Individual</th><td>0.3269927600</td><td>0.0004808717</td><td>680</td><td>4.52</td><td><0.0001</td><td>14.14</td><td><0.0001</td></tr><tr><th>Side</th><td>0.0143644400</td><td>0.0007182221</td><td>20</td><td>6.75</td><td><0.0001</td><td>0.86</td><td>0.0017</td></tr><tr><th>Individual × side</th><td>0.0723474900</td><td>0.0001063934</td><td>680</td><td>2.39</td><td><0.0001</td><td>10.41</td><td>0.0017</td></tr><tr><th>Error 1</th><td>0.0622041800</td><td>0.0000444316</td><td>1400</td><td>–</td><td>–</td><td>–</td><td>–</td></tr></tbody></table>
Table ²: Comparison of the results of analysis of variance on the shape of scapulae (occlusal view) and pelvis (side view) in Rhipidomys mastacalis from three vegetation classes in Brazil. Correspondence asymmetry was the only method used for asymmetry analysis. in Morphological symmetry of Rhipidomys mastacalis (Mammalia, Rodentia, Cricetidae) in fragmented habitats of the Atlantic Forest in Northeastern Brazil: a study on the influence of the environment on an endemic species
<p><b>Table ²:</b> Comparison of the results of analysis of variance on the shape of scapulae (occlusal view) and pelvis (side view) in <i>Rhipidomys mastacalis</i> from three vegetation classes in Brazil. Correspondence asymmetry was the only method used for asymmetry analysis.</p><table><tbody><tr><th><b>Shape procrustes ANOVA</b></th></tr></tbody><tbody><tr><th><b>Effect Sum of squares</b></th><td><b>Mean squares</b></td><td><b>Degrees of freedom</b></td><td><i>F statistic</i></td><td><i>p -Value</i></td><td><b>Pillai tr.</b></td><td><i>p -Value</i></td></tr><tr><th><b>Scapulae</b></th></tr><tr><th><b>Forested vegetation</b></th></tr><tr><th>Individual</th><td>0.0941373400</td><td>0.0010459705</td><td>90</td><td>3</td><td><0.0001</td><td>–</td><td>–</td></tr><tr><th>Side</th><td>0.0100439600</td><td>0.0010043960</td><td>2.88</td><td>0.0037</td><td>0.0003</td><td>–</td><td>–</td></tr><tr><th>Individual × side</th><td>0.0314069500</td><td>0.0003489662</td><td>90</td><td>5.89</td><td><0.0001</td><td>4.91</td><td><0.0001</td></tr><tr><th>Error 1</th><td>0.0118544100</td><td>0.0000592721</td><td>200</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Occupancy mosaics in forested areas</b></th></tr><tr><th>Individual</th><td>0.2064168200</td><td>0.0010320841</td><td>200</td><td>4.82</td><td><0.0001</td><td>7.15</td><td><0.0001</td></tr><tr><th>Side</th><td>0.0262808000</td><td>0.0026280796</td><td>10</td><td>12.28</td><td><0.0001</td><td>0.86</td><td>0.0022</td></tr><tr><th>Individual × side</th><td>0.0428160400</td><td>0.0002140802</td><td>200</td><td>2.68</td><td><0.0001</td><td>4.98</td><td><0.0001</td></tr><tr><th>Error 1</th><td>0.0335675700</td><td>0.0000799228</td><td>420</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Cocoa plantations</b></th></tr><tr><th>Individual</th><td>0.2508635400</td><td>0.0009291242</td><td>270</td><td>4.07</td><td><0.0001</td><td>7.11</td><td><0.0001</td></tr><tr><th>Side</th><td>0.0256608100</td><td>0.0025660812</td><td>10</td><td>11.24</td><td><0.0001</td><td>0.87</td><td><0.0001</td></tr><tr><th>Individual × side</th><td>0.0616394000</td><td>0.0002282941</td><td>270</td><td>3.10</td><td><0.0001</td><td>5.72</td><td><0.0001</td></tr><tr><th>Error 1</th><td>0.0412323300</td><td>0.0000736292</td><td>560</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Pelvis</b></th></tr><tr><th><b>Forested vegetation</b></th></tr><tr><th>Individual</th><td>0.0543411200</td><td>0.0004312787</td><td>126</td><td>4.63</td><td><0.0001</td><td></td><td></td></tr><tr><th>Side</th><td>0.0043155600</td><td>0.0003082544</td><td>14</td><td>3.31</td><td>0.0002</td><td></td><td></td></tr><tr><th>Individual × side</th><td>0.0117297800</td><td>0.0000930935</td><td>126</td><td>2.31</td><td><0.0001</td><td>6.07</td><td><0.0001</td></tr><tr><th>Error 1</th><td>0.0112943700</td><td>0.000040337</td><td>280</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Occupancy mosaics in forested areas</b></th></tr><tr><th>Individual</th><td>0.1059661700</td><td>0.0003440460</td><td>308</td><td>4.42</td><td><0.0001</td><td>9.69</td><td><0.0001</td></tr><tr><th>Side</th><td>0.0049395300</td><td>0.0003528236</td><td>14</td><td>4.53</td><td><0.0001</td><td>0.85</td><td>0.0311</td></tr><tr><th>Individual × side</th><td>0.0239852500</td><td>0.0000778742</td><td>308</td><td>2.00</td><td><0.0001</td><td>6.64</td><td><0.0001</td></tr><tr><th>Error 1</th><td>0.0251368400</td><td>0.0000390324</td><td>644</td><td>–</td><td>–</td><td>–</td><td>–</td></tr><tr><th><b>Cocoa plantations</b></th></tr><tr><th>Individual</th><td>0.1292837500</td><td>0.0003420205</td><td>378</td><td>5.68</td><td><0.0001</td><td>10.51</td><td><0.0001</td></tr><tr><th>Side</th><td>0.0043550500</td><td>0.0003110747</td><td>14</td><td>5.17</td><td><0.0001</td><td>0.84</td><td>0.0016</td></tr><tr><th>Individual × side</th><td>0.0227608400</td><td>0.0000602139</td><td>378</td><td>2.24</td><td><0.0001</td><td>6.17</td><td><0.0001</td></tr><tr><th>Error 1</th><td>0.0210413800</td><td>0.0000268385</td><td>714</td><td>–</td><td>–</td><td>–</td><td>–</td></tr></tbody></table>
TABLE 1 in Revision of the endemic South African genus Moegistorhynchus Macquart (Diptera: Nemestrinidae), with a species key, description of three new species and comments on pollination biology and biogeography
<p><b>TABLE 1.</b> Emergence times for the seven species of <i>Moegistorhynchus</i> and other co-occurring and functionally similar insect pollinators. Emergence times are based on museum specimen labels and observational records from iNaturalist.</p><table><tbody><tr><th>Taxa</th><th>Jan</th><th>Feb</th><th>Mar</th><th>Apr</th><th>May</th><th>Jun</th><th>Jul</th><th>Aug</th><th>Sep</th><th>Oct</th><th>Nov</th><th><b>Dec</b></th></tr><tr><th><i>M. braunsi</i> Bequaert</th></tr><tr><th><i>M. brevirostris</i> (Wiedemann)</th></tr><tr><th><i>M. strillii</i> <b>sp. nov.</b></th></tr><tr><th><i>M. longirostris</i> (Wiedemann)</th></tr><tr><th><i>M. manningi</i> <b>sp. nov.</b></th></tr><tr><th><i>M. perplexus</i> Bequaert</th></tr><tr><th><i>M. turneri</i> <b>sp. nov.</b></th></tr><tr><th>Nemestrinidae (e.g., <i>Prosoeca</i> species: <i>P. peringueyi</i> Lichtwardt (Manning & Goldblatt, 1997), <i>P. westermanni</i> Wiedemann, <i>P. rubicunda</i> Bezzi)</th></tr><tr><th>Tabanidae (e.g., <i>Philoliche rostrata</i> (Linnaeus) and <i>P. gulosa</i> (Wiedemann) (Manning & Goldblatt, 1997)</th></tr><tr><th>Hymenoptera (Apidae) (e.g., <i>Amegilla</i> sp.)</th></tr></tbody></table>
Table ¹: List of fruit species consumed by kinkajous in Pijao and San Juan. in Notes on the ecology, activity patterns and behavior of the kinkajou (Potos flavus)
<p><b>Table ¹:</b> List of fruit species consumed by kinkajous in Pijao and San Juan.</p><table><tbody><tr><th><b>Family</b></th><th><b>Species</b></th><th><b>Locality</b></th></tr></tbody><tbody><tr><th></th><td></td><td><b>Pijao</b></td><td><b>San Įuan</b></td></tr><tr><th>Anacardiaceae</th><td><i>Spondias mombin</i></td><td><b>–</b></td><td>X</td></tr><tr><th>Araliaceae</th><td><i>Dendropanax macrophyllum</i></td><td>X</td><td><b>–</b></td></tr><tr><th>Moraceae</th><td><i>Ficus brevibracteata</i></td><td>X</td><td><b>–</b></td></tr><tr><th></th><td><i>Ficus dendrocida</i></td><td><b>–</b></td><td>X</td></tr><tr><th></th><td><i>Poulsenia armata</i></td><td>X</td><td><b>–</b></td></tr><tr><th>Sapotaceae</th><td><i>Pouteria baehniana</i></td><td><b>–</b></td><td>X</td></tr><tr><th>Ulmaceae</th><td><i>Ampelocera albertiae</i></td><td>X</td><td><b>–</b></td></tr><tr><th>Urticaceae</th><td><i>Cecropia telealba</i></td><td>X</td><td><b>–</b></td></tr><tr><th></th><td><i>Cecropia membanacea</i></td><td><b>–</b></td><td>X</td></tr></tbody></table>
Table Z in Harpy eagle kill sample provides insights into the mandibular ontogenetic patterns of two-toed sloths (Xenarthra: Choloepus)
<p><b>Table Z:</b> Principal components’ factor loadings of eight mandibular measurements of <i>Choloepus</i> sp.</p><table><tbody><tr><th></th><th><b>PC¹</b></th><th><b>PCZ</b></th><th><b>PCƎ</b></th><th><b>PC4</b></th><th><b>PCS</b></th><th><b>PCƂ</b></th><th><b>PC7</b></th><th><b>PCB</b></th></tr></tbody><tbody><tr><th>BAC</th><td>−0.36419</td><td>−0.03257</td><td>−0.37585</td><td>−0.00685</td><td>0.21989</td><td>0.78839</td><td>0.12241</td><td>0.20027</td></tr><tr><th>BCC</th><td>−0.37306</td><td>−0.05151</td><td>−0.04782</td><td>0.07696</td><td>0.19834</td><td>0.01218</td><td>−0.59374</td><td>−0.67672</td></tr><tr><th>HCA</th><td>−0.33771</td><td>−0.40931</td><td>0.39166</td><td>0.70764</td><td>−0.04241</td><td>−0.03279</td><td>0.01090</td><td>0.24754</td></tr><tr><th>HCC</th><td>−0.35614</td><td>−0.02746</td><td>−0.63993</td><td>0.00627</td><td>−0.09856</td><td>−0.50959</td><td>−0.20713</td><td>0.38803</td></tr><tr><th>LAM</th><td>−0.35690</td><td>0.09563</td><td>0.39899</td><td>−0.44229</td><td>−0.55334</td><td>0.16929</td><td>−0.33608</td><td>0.24672</td></tr><tr><th>LCD</th><td>−0.31297</td><td>0.86221</td><td>0.17765</td><td>0.23890</td><td>0.18636</td><td>−0.10852</td><td>0.14633</td><td>0.04581</td></tr><tr><th>LMS</th><td>−0.35341</td><td>−0.25972</td><td>0.29043</td><td>−0.48950</td><td>0.58561</td><td>−0.26349</td><td>0.25401</td><td>0.08244</td></tr><tr><th>TML</th><td>−0.37024</td><td>−0.08940</td><td>−0.13581</td><td>−0.03065</td><td>−0.46577</td><td>−0.08763</td><td>0.62497</td><td>−0.46940</td></tr></tbody></table><p>See main text for measurement abbreviations.</p>
TABLE 1 in A new wave of Mesoamerican bumblebees? Revising the weisi-complex to reject numts and pseudospecies (Apidae: Bombus)
<p><b>TABLE 1.</b> Collections from which material has been examined.</p><table><tbody><tr><th>Abbreviation</th><th>Address</th></tr></tbody><tbody><tr><th>AMNH</th><td>American Museum of Natural History, New York, USA</td></tr><tr><th>BMEC</th><td>Bohart Museum of Entomology, University of California, Davis, California, USA</td></tr><tr><th>CAS</th><td>California Academy of Sciences, San Francisco, California, USA</td></tr><tr><th>CNIN</th><td>Colección Nacional de Insectos, Universidad Nacional Autónoma de México, D.F, México</td></tr><tr><th>ECOAB</th><td>El Colegio de la Frontera Sur, San Cristóbal de Las Casas, Chiapas, México</td></tr><tr><th>EMEC</th><td>Essig Museum Entomological Collection, University of California, Berkeley, California, USA</td></tr><tr><th>INHS</th><td>Illinois Natural History Survey, Champaign, Illinois, USA</td></tr><tr><th>LACM</th><td>Natural History Museum of Los Angeles, Los Angeles, California, USA</td></tr><tr><th>MNHP</th><td>Museum National d’Histoire Naturelle, Paris, France</td></tr><tr><th>MZFC</th><td>Museo de Zoología, Facultad de Ciencia UNAM, D. F. Mexico</td></tr><tr><th>NHMUK</th><td>Natural History Museum, London, UK</td></tr><tr><th>SDEI</th><td>Senckenberg Deutsches Entomologisches Institut, Senckenberg, Germany</td></tr><tr><th>SEMC</th><td>Snow Entomological Museum Collection, Lawrence, Kansas, USA</td></tr><tr><th>UCRC</th><td>University of California Riverside Entomology Research Museum, Riverside, California, USA</td></tr><tr><th>UDLAP</th><td>Universidad de las Américas, Puebla, México</td></tr><tr><th>USDA-ARS</th><td>Bee Biology and Systematics Laboratory, Utah State University, Logan, Utah, USA</td></tr><tr><th>USNM</th><td>United State National Entomological Collection, Washington DC, USA</td></tr><tr><th>VAB</th><td>Van Asperen de Boer, Amsterdam, Netherlands (now in Naturalis)</td></tr><tr><th>ZMHB</th><td>Museum für Naturkunde an der Humboldt-Universität, Berlin, Germany</td></tr><tr><th>ZMUC</th><td>Zoological Museum University of Copenhagen, Denmark</td></tr><tr><th>ZSM</th><td>Zoologische Staatssammlung München, Germany</td></tr></tbody></table>
Table ²: The surveyed Community Conservation Reserves in Meghalaya, (India). in New distribution and breeding record of Wroughton's free-tailed bat (Otomops wroughtoni) (Chiroptera: Molossidae) from Meghalaya, India
<p><b>Table ²:</b> The surveyed Community Conservation Reserves in Meghalaya, (India).</p><table><tbody><tr><th><b>Sl. no.</b></th><th><b>Name of Community Reserve</b></th><th><b>District</b></th></tr></tbody><tbody><tr><th>1</th><td>Ka Khloo Thangbru Umsymphu Community</td><td>East Jaintia</td></tr><tr><th></th><td>Reserve</td><td>Hills</td></tr><tr><th>2</th><td>Khloo Blai Sein Raij Tuber Community Reserve</td><td></td></tr><tr><th>3</th><td>Ka Khloo Pohblai Mooshutia Community Reserve</td><td></td></tr><tr><th>4</th><td>Ka Khloo Langdoh Kur Pyrtuh Community Reserve</td><td>West Jaintia</td></tr><tr><th>5</th><td>Umsum Pitcher Plant Community Reserve</td><td>Hills</td></tr><tr><th>6</th><td>Jirang Community Reserve</td><td>Ribhoi</td></tr><tr><th>7</th><td>Raid Nonglyngdoh/Pdah Kyndeng Community</td><td></td></tr><tr><th>Reserve</th></tr><tr><th>8</th><td>Nongsangu Community Reserve</td><td></td></tr><tr><th>9</th><td>Lum jusong Community Reserve</td><td></td></tr><tr><th>10</th><td>Raid Nongbri Community Reserve</td><td></td></tr><tr><th>11</th><td>Eman Asakgre Community Reserve</td><td>South Garo</td></tr><tr><th>12</th><td>Mikadogre Community Reserve</td><td>hills</td></tr><tr><th>13</th><td>Khloo Blai Chyrmang Sein Raij Kongwasan</td><td>West Jaintia</td></tr><tr><th></th><td>Chyrmang Kmai Community Reserve</td><td>Hills</td></tr><tr><th>14</th><td>Kpoh Eijah Community Reserve</td><td>West Khasi</td></tr><tr><th></th><td></td><td>Hills</td></tr><tr><th>15</th><td>Resu Haluapara Community Reserve</td><td>North Garo</td></tr><tr><th>16</th><td>Aruakgre Community Reserve</td><td>hills</td></tr><tr><th>17</th><td>Dumitdikgre Community Reserve</td><td>West Garo</td></tr><tr><th>18</th><td>Sasatgre Community Reserve</td><td>hills</td></tr><tr><th>19</th><td>Daribokgre Community Reserve</td><td>East Garo</td></tr><tr><th></th><td></td><td>hills</td></tr></tbody></table>
Table 5 in Morphometrics highlights subspecies differentiation of continental (Rangifer t. tarandus) and insular (Rangifer t. platyrhynchus) Norwegian reindeer
<p><b>Table 5:</b> Sexual dimorphism in metacarpal and metatarsal size and shape of the three insular Svalbard reindeer subpopulations.</p><table><tbody><tr><th><b>Skeletal elements</b></th><th></th><th><b>Metacarpal</b></th><th></th><th></th><th><b>Metatarsal</b></th><th></th></tr></tbody><tbody><tr><th><b>Morphometric parameters</b></th><td><b>Size</b></td><td><b>Shape</b></td><td><b>Size</b></td><td><b>Shape</b></td></tr><tr><th><b>Tests</b></th><td><b>W</b></td><td><b>p</b></td><td><b>F</b></td><td><b>p</b></td><td><b>W</b></td><td><b>p</b></td><td><b>F</b></td><td><b>p</b></td></tr><tr><th>Colesdalen GrØndalen Sassendalen</th><td>36 65 29</td><td><b>0.002 0.048 0.006</b></td><td>0.58 2.23 0.58</td><td>0.76 0.069 0.76</td><td>39 51 58</td><td><b>0.007 0.002</b> 0.37</td><td>1.32 3.48 0.37</td><td>0.28 <b>0.009</b> 0.9</td></tr></tbody></table><p>Results of Wilcoxon test (W statistic and p-value) for size and manova (F statistic and p-values) for shape. Bold values mean significant tests.</p>
Table ¹: Summary statistics for mandible measurements (in mm) of each age group of Choloepus (mean ± standard deviation [range] sample size). in Harpy eagle kill sample provides insights into the mandibular ontogenetic patterns of two-toed sloths (Xenarthra: Choloepus)
<p><b>Table ¹:</b> Summary statistics for mandible measurements (in mm) of each age group of <i>Choloepus</i> (mean ± standard deviation [range] sample size).</p><table><tbody><tr><th><b>Measurement</b></th><th><b>Age classes</b></th></tr></tbody><tbody><tr><th></th><td><b>Infant</b></td><td><b>Įuvenile</b></td><td><b>Subadult</b></td><td><b>Adult</b></td></tr><tr><th>BAC</th><td>44.08 ± 3.04 [40.7–47.92] 4</td><td>48.54 ± 2.65 [42.39–52.29] 15</td><td>54.46 ± 3.79 [50.78–59.2] 4</td><td>65.12 ± 3.28 [61.05–71.01] 9</td></tr><tr><th>BCC</th><td>20.57 ± 1.47 [18.76–22.35] 4</td><td>23.08 ± 1.33 [20.83–25.78] 16</td><td>26.51 ± 0.73 [25.53–27.25] 4</td><td>31.81 ± 1.59 [28.84–33.69] 9</td></tr><tr><th>HCA</th><td>12.84 ± 1.41 [9.66–15.12] 13</td><td>15.66 ± 1.74 [11.95–20.11] 18</td><td>17.48 ± 1.13 [16.32–18.88] 4</td><td>21 ± 1.25 [18.49–23.08] 9</td></tr><tr><th>HCC</th><td>8.16 ± 1.4 [6.01–10.29] 13</td><td>9.65 ± 1.23 [7.52–11.68] 15</td><td>13.08 ± 0.72 [12.11–13.83] 4</td><td>23.68 ± 0.98 [22.16–25.02] 9</td></tr><tr><th>LAM</th><td>17.74 ± 1.57 [14.58–20.44] 13</td><td>20.6 ± 1.15 [19.15–22.72] 18</td><td>24.11 ± 2.11 [21.29–26.3] 4</td><td>26.28 ± 1.67 [23.31–28.9] 9</td></tr><tr><th>LCD</th><td>8.69 ± 1.11 [7.48–11.43] 13</td><td>9.88 ± 0.75 [8.89–11.73] 18</td><td>11.43 ± 0.8 [10.7–12.54] 4</td><td>12 ± 1.07 [10.18–13.89] 9</td></tr><tr><th>LMS</th><td>14.78 ± 0.84 [13.52–16.22] 13</td><td>16.98 ± 0.54 [16–18.11] 18</td><td>18.74 ± 0.69 [17.72–19.15] 4</td><td>20.06 ± 0.71 [19.15–21.38] 9</td></tr><tr><th>TML</th><td>56.3 ± 3.76 [50.53–61.07] 13</td><td>64.9 ± 1.99 [62.81–68.57] 18</td><td>72.42 ± 2.12 [69.41–74.39] 4</td><td>86.67 ± 3.52 [81.7–91.93] 9</td></tr></tbody></table><p>See main text for measurement abbreviations.</p>
Table 4 in Morphometrics highlights subspecies differentiation of continental (Rangifer t. tarandus) and insular (Rangifer t. platyrhynchus) Norwegian reindeer
<p><b>Table 4:</b> Test of sexual dimorphism in mandibular teeth size and shape for each of the six populations/subpopoulations (significant statistical results (p <0.05) are presented in bold).</p><table><tbody><tr><th><b>Subspecies</b></th><th><b>Morphometric parameters</b></th><th><b>Size</b></th><th><b>Shape</b></th></tr></tbody><tbody><tr><th></th><td><b>Tests</b></td><td><b>W</b></td><td><b>p</b></td><td><b>F</b></td><td><b>p</b></td></tr><tr><th>Continental reindeer</th><td>Forollhogna</td><td>155</td><td><b>0.007</b></td><td>0.77858</td><td>0.5708</td></tr><tr><th><i>Rangifer t. tarandus</i></th><td>Hardangervidda</td><td>499</td><td>0.7389</td><td>0.66636</td><td>0.6504</td></tr><tr><th></th><td>KnutshØ</td><td>223</td><td>0.737</td><td>0.92948</td><td>0.4725</td></tr><tr><th>Insular Svalbard reindeer</th><td>Colesdalen</td><td>68</td><td>0.8793</td><td>1.3164</td><td>0.3037</td></tr><tr><th><i>Rangifer t. platyrhynchus</i></th><td>GrØndalen</td><td>25</td><td>0.2463</td><td>1.042</td><td>0.4372</td></tr><tr><th></th><td>Sassendalen</td><td>27</td><td>1</td><td>2.0517</td><td>0.1646</td></tr></tbody></table><p>Results of Wilcoxon test (W statistic and p-value) for size and manova (F statistic and p-values) for shape. Bold values mean significant tests.</p>
Table 3 in Morphometrics highlights subspecies differentiation of continental (Rangifer t. tarandus) and insular (Rangifer t. platyrhynchus) Norwegian reindeer
<p><b>Table 3:</b> Pairwise comparison of continental populations and insular reindeer subpopulations in isometric size and Log Shape Ratio for the distal and proximal parts of the metatarsal and metacarpal.</p><table><tbody><tr><th></th><th></th><th></th><th><b>Proximal</b></th><th></th><th></th><th><b>Distal</b></th><th></th><th></th></tr></tbody><tbody><tr><th></th><td></td><td><b>Hardangervidda</b> <b>a</b></td><td><b>Colesdalen</b></td><td><b>Grøndalen</b></td><td><b>Sassendalen</b></td><td><b>Hardangervidda</b> <b>a</b></td><td><b>Colesdalen</b></td><td><b>Grøndalen</b></td><td><b>Sassendalen</b></td></tr><tr><th>Metacarpe</th><td>Hardangervidda a</td><td><b>–</b></td><td>0.40141</td><td><b>0.00089</b></td><td><b>0.00451</b></td><td><b>–</b></td><td><b>0.012</b></td><td><b>0.024</b></td><td>0.066</td></tr><tr><th></th><td>Colesdalen</td><td><b>0.00018</b></td><td><b>–</b></td><td><b>0.02263</b></td><td><b>0.08285</b></td><td><b>1.9e-7</b></td><td><b>–</b></td><td>0.573</td><td>0.478</td></tr><tr><th></th><td>GrØndalen</td><td><b>0.00045</b></td><td>0.65390</td><td><b>–</b></td><td>0.72177</td><td><b>1.9e-7</b></td><td>0.99</td><td><b>–</b></td><td>0.670</td></tr><tr><th></th><td>Sassendalen</td><td><b>5.7e-6</b></td><td>0.12495</td><td><b>0.04323</b></td><td><b>–</b></td><td><b>1.9e-7</b></td><td>0.60</td><td>0.60</td><td><b>–</b></td></tr><tr><th>Metatarse</th><td>Hardangervidda a</td><td><b>–</b></td><td><b>1.2e-14</b></td><td><b>1.2e-14</b></td><td><b>7.3e-10</b></td><td><b>–</b></td><td>0.35</td><td>0.83</td><td>0.34</td></tr><tr><th></th><td>Colesdalen</td><td><b>0.023</b></td><td><b>–</b></td><td>0.83</td><td>0.83</td><td><b>7.7e-8</b></td><td><b>–</b></td><td>0.34</td><td>0.64</td></tr><tr><th></th><td>GrØndalen</td><td><b>0.023</b></td><td>1</td><td><b>–</b></td><td>0.87</td><td><b>5.5e-8</b></td><td>0.75</td><td><b>–</b></td><td>0.34</td></tr><tr><th></th><td>Sassendalen</td><td><b>4.2e-5</b></td><td><b>0.023</b></td><td><b>0.023</b></td><td><b>–</b></td><td><b>3.2e-8</b></td><td>0.25</td><td>0.1</td><td>–</td></tr></tbody></table><p>p-Value of the size comparisons are in the lower hemi-matrices while the p-values for LSR comparisons are in the upper hemi-matrices.Significant p-value are presented in bold.p-Value were corrected for multitest comparison for each pairwise analysis separately. <sup>a</sup> Continental population. Bold values mean significant tests.</p>
Table 2 in Morphometrics highlights subspecies differentiation of continental (Rangifer t. tarandus) and insular (Rangifer t. platyrhynchus) Norwegian reindeer
<p><b>Table 2:</b> Differences in mandibular teeth between the 6 populations/subpopulations of reindeer located in the continental Norway mainland and the insular Svalbard archipelago.</p><table><tbody><tr><th></th><th><b>Colesdalen</b></th><th><b>Forollhogna</b></th><th><b>Grøndalen</b></th><th><b>Hardangervidda</b></th><th><b>Knushø</b></th><th><b>Sassendalen</b></th></tr></tbody><tbody><tr><th>Colesdalen</th><td><b>–</b></td><td>4.8e-19</td><td>8.8e-3</td><td><b>2.4e-8</b></td><td>1.1e-6</td><td>2.4e-2</td></tr><tr><th>Forollhogna</th><td>0.812</td><td><b>–</b></td><td>3.4e-13</td><td><b>4.8e-15</b></td><td>1.1e-17</td><td>9.3e-11</td></tr><tr><th>GrØndalen</th><td>0.948</td><td>0.972</td><td><b>–</b></td><td><b>1.3e-13</b></td><td>2.7e-7</td><td>4.1e-2</td></tr><tr><th>Hardangervidda</th><td>2.00E-10</td><td>4.4e-15</td><td>9.7e-8</td><td><b>-</b></td><td>3.7e-5</td><td>3.1e-6</td></tr><tr><th>KnushØ</th><td>0.278</td><td>0.275</td><td>0.541</td><td><b>3.2e-11</b></td><td><b>–</b></td><td>6.4e-4</td></tr><tr><th>Sassendalen</th><td>0.073</td><td>0.089</td><td>0.166</td><td><b>1.4e-6</b></td><td>0.520</td><td>–</td></tr></tbody></table><p>Isometric size (below the diagonal) and shape (Log Shape Ratios, above the diagonal) pairwise differences. p-Values of Wilcoxon-tests for size and of Manovas for shape. p-Values <0.05 in bold.</p>
Table 2 in Using photo by-catch data to reliably estimate spotted hyaena densities over time
<p><b>Table 2:</b> Summary of spotted hyaena density estimates for the Hluhluwe and iMfolozi sections in the Hluhluwe-iMfolozi Park, KwaZulu-Natal, South Africa.</p><table><tbody><tr><th><b>Year</b></th><th><b>Hluhluwe density</b></th><th><b>Hluluwe LCL</b></th><th><b>Hluhluwe UCL</b></th><th><b>iMfolozi density</b></th><th><b>iMfolozi LCL</b></th><th><b>iMfolozi UCL</b></th></tr></tbody><tbody><tr><th>2013</th><td>17.59</td><td>11.74</td><td>26.36</td><td>21.41</td><td>15.38</td><td>29.82</td></tr><tr><th>2014</th><td>14.39</td><td>9.32</td><td>22.21</td><td>27.09</td><td>20.9</td><td>35.11</td></tr><tr><th>2015</th><td>9.78</td><td>4.41</td><td>21.69</td><td>12.98</td><td>9.18</td><td>18.37</td></tr><tr><th>2016</th><td>8.54</td><td>4.69</td><td>15.55</td><td>24.31</td><td>17.j26</td><td>34.23</td></tr><tr><th>2017</th><td>12.9</td><td>8.28</td><td>20.11</td><td>21.34</td><td>15.25</td><td>29.87</td></tr><tr><th>2018</th><td>14.6</td><td>9.88</td><td>21.58</td><td>27.27</td><td>20.34</td><td>36.56</td></tr><tr><th>Mean</th><td>12.97</td><td>8.05</td><td>21.25</td><td>22.40</td><td>16.21</td><td>30.66</td></tr><tr><th>Stdev</th><td>3.34</td><td>2.94</td><td>3.50</td><td>5.30</td><td>4.75</td><td>6.63</td></tr></tbody></table><p>The SECR analysis used a uniform 12,500 m buffer effective trapping area.LCL,lower confidence limit;UCL,upper confidence limit.Estimates are measured in hyaena per 100 km <sup>2</sup>.</p>
TABLE 3 in A new Oreolalax (Anura: Megophryidae) from the Hoang Lien Range, northwest Vietnam
<p><b>TABLE 3.</b> Morphometric measurements (in mm) of <i>Oreolalax adelphos</i> <b>sp. nov</b>. Abbreviations are defined in the Materials and methods. HT = holotype; PR = paratype.</p><table><tbody><tr><th><b>Specimens</b></th><th><b>ITBCZ 3619 (HT)</b></th><th><b>ITBCZ 3620 (PR)</b></th><th><b>ITBCZ 3621 (PR)</b></th></tr></tbody><tbody><tr><th>Sex</th><td>M</td><td>F</td><td>F</td></tr><tr><th>SVL</th><td>38.0</td><td>39.2</td><td>46.2</td></tr><tr><th>HL</th><td>15.0</td><td>14.8</td><td>19.0</td></tr><tr><th>HW</th><td>14.8</td><td>14.5</td><td>17.3</td></tr><tr><th>HH</th><td>6.7</td><td>6.2</td><td>7.9</td></tr><tr><th>SNT</th><td>6.8</td><td>6.3</td><td>8.1</td></tr><tr><th>IN</th><td>4.3</td><td>5.8</td><td>5.2</td></tr><tr><th>EN</th><td>4.1</td><td>3.8</td><td>4.0</td></tr><tr><th>NS</th><td>3.1</td><td>3.3</td><td>3.4</td></tr><tr><th>EYE</th><td>5.0</td><td>5.2</td><td>5.0</td></tr><tr><th>IOD</th><td>5.0</td><td>5.0</td><td>6.3</td></tr><tr><th>FEL</th><td>19.8</td><td>19.2</td><td>23.5</td></tr><tr><th>TIB</th><td>18.2</td><td>19.0</td><td>23.8</td></tr><tr><th>TaL</th><td>9.4</td><td>10.4</td><td>13.1</td></tr><tr><th>ML</th><td>11.2</td><td>12.9</td><td>13.1</td></tr><tr><th>PL</th><td>18.2</td><td>9.4</td><td>24.4</td></tr><tr><th>IPL</th><td>2.1</td><td>2.0</td><td>3.1</td></tr><tr><th>OPL</th><td>1.8</td><td>1.9</td><td>2.7</td></tr><tr><th>F1DSC</th><td>1.1</td><td>1.0</td><td>1.3</td></tr><tr><th>F3DSC</th><td>0.8</td><td>0.9</td><td>1.2</td></tr><tr><th>T4DSC</th><td>1.0</td><td>1.0</td><td>1.1</td></tr><tr><th>IML</th><td>1.3</td><td>1.7</td><td>2.4</td></tr><tr><th>PG</th><td>1.5</td><td>1.8</td><td>1.8</td></tr><tr><th>FG</th><td>1.3</td><td>1.8</td><td>2.0</td></tr></tbody></table>
TABLE 2. Mean uncorrected p in A new Oreolalax (Anura: Megophryidae) from the Hoang Lien Range, northwest Vietnam
<p><b>TABLE 2.</b> Mean uncorrected p-distance between <i>Oreolalax</i> species of the 16S rRNA gene. Mean values of genetic distance are given in the lower half of the table. The in-group mean uncorrected p-distances are shown on the diagonal and shaded in bold.</p><table><tbody><tr><th><b>ID</b></th><th><b>Species</b></th><th><b>1</b></th><th><b>2</b></th><th><b>3</b></th><th><b>4</b></th><th><b>5</b></th><th><b>6</b></th><th><b>7</b></th><th><b>8</b></th><th><b>9</b></th><th><b>10</b></th><th><b>11</b></th><th><b>12</b></th><th><b>13</b></th><th><b>14</b></th><th><b>15</b></th><th><b>16</b></th><th><b>17</b></th><th><b>18</b></th><th><b>19</b></th><th><b>20</b></th></tr></tbody><tbody><tr><th><b>1</b></th><td><i>Oreolalax adelphos</i> <b>sp. nov</b>.</td><td><b>0.14</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>2</b></th><td><i>Oreolalax chuanbeiensis</i></td><td>6.7</td><td><b>0.00</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>3</b></th><td><i>Oreolalax jingdongensis</i></td><td>3.0</td><td>6.4</td><td><b>0.06</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>4</b></th><td><i>Oreolalax liangbeiensis</i></td><td>1.3</td><td>7.3</td><td>3.6</td><td><b>NA</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>5</b></th><td><i>Oreolalax lichuanensis</i></td><td>7.9</td><td>10.6</td><td>10.0</td><td>11.4</td><td><b>2.20</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>6</b></th><td><i>Oreolalax longmenmontis</i></td><td>6.6</td><td>1.6</td><td>6.2</td><td>6.5</td><td>10.4</td><td><b>0.00</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>7</b></th><td><i>Oreolalax major</i></td><td>1.1</td><td>6.7</td><td>2.9</td><td>0.8</td><td>9.8</td><td>6.1</td><td><b>0.07</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>8</b></th><td><i>Oreolalax multipunctatus</i></td><td>6.4</td><td>3.7</td><td>8.1</td><td>8.9</td><td>11.8</td><td>3.1</td><td>8.0</td><td><b>0.14</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>9</b></th><td><i>Oreolalax nanjiangensis</i></td><td>6.4</td><td>0.9</td><td>6.7</td><td>7.2</td><td>10.7</td><td>1.4</td><td>6.7</td><td>3.8</td><td><b>0.00</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>10</b></th><td><i>Oreolalax omeimontis</i> 1</td><td>6.3</td><td>2.8</td><td>7.4</td><td>8.4</td><td>11.8</td><td>3.0</td><td>7.7</td><td>4.2</td><td>2.6</td><td><b>0.27</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>11</b></th><td><i>Oreolalax omeimontis</i> 2</td><td>9.9</td><td>10.1</td><td>9.6</td><td>10.1</td><td>12.6</td><td>8.8</td><td>9.5</td><td>10.3</td><td>9.9</td><td>10.9</td><td><b>0.37</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>12</b></th><td><i>Oreolalax pingii</i></td><td>5.9</td><td>10.0</td><td>8.6</td><td>9.8</td><td>4.4</td><td>8.4</td><td>8.0</td><td>11.1</td><td>9.8</td><td>11.2</td><td>10.7</td><td><b>NA</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>13</b></th><td><i>“ Oreolalax popei ”</i></td><td>7.6</td><td>2.1</td><td>8.0</td><td>8.6</td><td>11.9</td><td>0.0</td><td>8.1</td><td>4.2</td><td>1.8</td><td>3.2</td><td>10.4</td><td>11.5</td><td><b>NA</b></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>14</b></th><td><i>Oreolalax rhodostigmatus</i></td><td>5.7</td><td>8.8</td><td>9.0</td><td>9.9</td><td>12.2</td><td>6.9</td><td>8.1</td><td>10.3</td><td>9.3</td><td>10.8</td><td>11.0</td><td>10.8</td><td>10.3</td><td><b>2.80</b></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>15</b></th><td><i>Oreolalax rugosus</i></td><td>1.8</td><td>7.3</td><td>3.8</td><td>1.6</td><td>11.3</td><td>6.0</td><td>1.7</td><td>8.7</td><td>7.1</td><td>8.1</td><td>10.0</td><td>9.5</td><td>8.2</td><td>9.1</td><td><b>NA</b></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>16</b></th><td><i>Oreolalax schmidti</i></td><td>6.6</td><td>10.6</td><td>9.0</td><td>9.9</td><td>4.5</td><td>9.1</td><td>8.3</td><td>11.2</td><td>10.4</td><td>11.5</td><td>11.4</td><td>0.8</td><td>11.7</td><td>11.0</td><td>9.9</td><td><b>0.14</b></td><td></td><td></td><td></td><td></td></tr><tr><th><b>17</b></th><td><i>Oreolalax</i> sp.</td><td>3.0</td><td>7.1</td><td>4.0</td><td>3.8</td><td>11.3</td><td>5.5</td><td>3.4</td><td>7.9</td><td>6.9</td><td>8.0</td><td>9.9</td><td>9.9</td><td>8.0</td><td>9.4</td><td>3.7</td><td>10.1</td><td><b>NA</b></td><td></td><td></td><td></td></tr><tr><th><b>18</b></th><td><i>Oreolalax sterlingae</i></td><td>5.8</td><td>7.5</td><td>6.0</td><td>5.8</td><td>8.3</td><td>7.5</td><td>5.5</td><td>6.8</td><td>7.2</td><td>7.3</td><td>10.4</td><td>6.5</td><td>8.1</td><td>7.2</td><td>5.1</td><td>6.9</td><td>4.9</td><td><b>0.62</b></td><td></td><td></td></tr><tr><th><b>19</b></th><td><i>Oreolalax xiangchengensis</i></td><td>1.2</td><td>7.1</td><td>3.8</td><td>2.2</td><td>10.7</td><td>6.1</td><td>2.1</td><td>8.5</td><td>7.1</td><td>8.1</td><td>9.7</td><td>9.9</td><td>8.3</td><td>9.7</td><td>2.4</td><td>10.3</td><td>4.1</td><td>5.9</td><td><b>NA</b></td><td></td></tr><tr><th><b>20</b></th><td><i>Oreolalax</i> cf. <i>xiangchengensis</i></td><td>0.5</td><td>7.4</td><td>3.7</td><td>2.3</td><td>10.8</td><td>6.7</td><td>1.9</td><td>8.6</td><td>7.4</td><td>8.2</td><td>10.4</td><td>9.8</td><td>8.4</td><td>9.7</td><td>2.3</td><td>10.2</td><td>4.2</td><td>5.9</td><td>0.2</td><td>0.00</td></tr></tbody></table>
Table ¹: Data by year and by month, for the number of cameras, sampling days, sampling effort, and relative abundance index (RAI) of records for females and cubs. in Reproductive aspects of female Andean bears (Tremarctos ornatus) in the Chingaza massif, eastern range of the Colombian Andes
<p><b>Table ¹:</b> Data by year and by month, for the number of cameras, sampling days, sampling effort, and relative abundance index (RAI) of records for females and cubs.</p><table><tbody><tr><th><b>Year</b></th><th><b>Camera traps used</b></th><th></th><th></th><th><b>Sampling days per month (sampling effort per month)</b></th><th></th><th></th><th><b>Sampling days</b></th><th><b>Camera traps</b></th><th><b>Sampling effort</b></th></tr></tbody><tbody><tr><th><b>Reconyx Wildview</b></th><td><b>Bushnell</b></td><td><b>]</b></td><td><b>F</b></td><td><b>M</b></td><td><b>A</b></td><td><b>M</b></td><td><b>]</b></td><td><b>]</b></td><td><b>A</b></td><td><b>S</b></td><td><b>O</b></td><td><b>N</b></td><td><b>D</b></td><td><b>per year</b></td><td><b>per year</b></td><td><b>per year</b></td></tr><tr><th>2011</th><td>2</td><td>4</td><td>0</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>3 (18)</td><td>30</td><td>30</td><td>30</td><td>93</td><td>6</td><td>558</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>(180)</td><td>(180)</td><td>(180)</td><td></td><td></td><td></td></tr><tr><th>2012a</th><td>2</td><td>4</td><td>0</td><td>31</td><td>29</td><td>31</td><td>30</td><td>31</td><td>30</td><td>31</td><td>31</td><td>30</td><td>31</td><td>30</td><td>30</td><td>365</td><td>6</td><td>2190</td></tr><tr><th></th><td></td><td></td><td></td><td>(186)</td><td>(174)</td><td>(186)</td><td>(180)</td><td>(186)</td><td>(180)</td><td>(186)</td><td>(186)</td><td>(180)</td><td>(186)</td><td>(180)</td><td>(180)</td><td></td><td></td><td></td></tr><tr><th>2012b</th><td>0</td><td>0</td><td>12</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>30</td><td>30</td><td>60</td><td>12</td><td>720</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>(360)</td><td>(360)</td><td></td><td></td><td></td></tr><tr><th>2013</th><td>2</td><td>4</td><td>14</td><td>31</td><td>28</td><td>31</td><td>30</td><td>31</td><td>30</td><td>31</td><td>31</td><td>30</td><td>30</td><td></td><td></td><td>303</td><td>20</td><td>6060</td></tr><tr><th></th><td></td><td></td><td></td><td>(620)</td><td>(560)</td><td>(620)</td><td>(600)</td><td>(620)</td><td>(600)</td><td>(620)</td><td>(620)</td><td>(600)</td><td>(600)</td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>2014</th><td>0</td><td>2</td><td>9</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>3 (33)</td><td>30</td><td>33</td><td>11</td><td>363</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>(330)</td><td></td><td></td><td></td></tr><tr><th>2015a</th><td>0</td><td>2</td><td>9</td><td>31</td><td>28</td><td>31</td><td>30</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>120</td><td>11</td><td>1320</td></tr><tr><th></th><td></td><td></td><td></td><td>(341)</td><td>(308)</td><td>(341)</td><td>(330)</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>2015b</th><td>0</td><td>0</td><td>117</td><td></td><td></td><td></td><td></td><td>2 (234)</td><td>30</td><td>31</td><td>31</td><td>30</td><td>31</td><td>30</td><td>30</td><td>215</td><td>117</td><td>25,155</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>(3510)</td><td>(3627)</td><td>(3627)</td><td>(3510)</td><td>(3627)</td><td>(3510)</td><td>(3510)</td><td></td><td></td><td></td></tr><tr><th>2016</th><td>0</td><td>0</td><td>117</td><td>31</td><td>29</td><td>31</td><td>30</td><td>30</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>151</td><td>117</td><td>17,667</td></tr><tr><th></th><td></td><td></td><td></td><td>(3627)</td><td>(3393)</td><td>(3627)</td><td>(3510)</td><td>(3510)</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>Sum of sampling effort per month over</th><td>4774</td><td>4435</td><td>4774</td><td>4620</td><td>4550</td><td>4290</td><td>4433</td><td>4433</td><td>4308</td><td>4593</td><td>4263</td><td>4560</td><td>Total sampling effort</td><td>54,033</td></tr><tr><th>the years</th></tr><tr><th>Records of females with cubs (4 <b>–</b></th><td>1</td><td>2</td><td>1</td><td>3</td><td>1</td><td>0</td><td>0</td><td>0</td><td>0</td><td>2</td><td>0</td><td>4</td><td></td><td></td><td></td></tr><tr><th>7 months)</th></tr><tr><th>RAI of females with cubs (4 <b>–</b> 7 months)</th><td>0.21</td><td>0.45</td><td>0.21</td><td>0.65</td><td>0.22</td><td>0.00</td><td>0.00</td><td>0.00</td><td>0.00</td><td>0.44</td><td>0.00</td><td>0.88</td><td></td><td></td><td></td></tr><tr><th>Records of estimated births</th><td></td><td>1</td><td>0</td><td>1</td><td>0</td><td>0</td><td>7</td><td>3</td><td>2</td><td>0</td><td>3</td><td>3</td><td>0</td><td></td><td></td><td></td></tr><tr><th>RAI of estimated births</th><td></td><td></td><td>0.21</td><td>0.00</td><td>0.21</td><td>0.00</td><td>0.00</td><td>1.63</td><td>0.68</td><td>0.45</td><td>0.00</td><td>0.65</td><td>0.70</td><td>0.00</td><td></td><td></td><td></td></tr></tbody></table>
TABLE 3 in A new species of the genus Boulenophrys from South China (Anura, Megophryidae)
<p><b>TABLE 3.</b> Measurements (in mm) of the type series of <i>Boulenophrys pepe</i> <b>sp. nov</b>., * indicates the holotype.</p><table><tbody><tr><th></th><th>GEP a207*</th><th>SYS a009350</th><th>GEP a209</th><th>GEP a117</th></tr></tbody><tbody><tr><th><b>Sex</b></th><td>♂</td><td>♂</td><td>♂</td><td>♂</td></tr><tr><th><b>SVL</b></th><td>36.4</td><td>35.7</td><td>35.3</td><td>36.0</td></tr><tr><th><b>HDL</b></th><td>12.6</td><td>12.5</td><td>12.7</td><td>12.5</td></tr><tr><th><b>HDW</b></th><td>14.1</td><td>14.4</td><td>14.2</td><td>13.7</td></tr><tr><th><b>SNT</b></th><td>4.5</td><td>4.1</td><td>4.5</td><td>4.4</td></tr><tr><th><b>IND</b></th><td>4.3</td><td>4.9</td><td>4.6</td><td>4.3</td></tr><tr><th><b>IOD</b></th><td>3.9</td><td>4.1</td><td>4.1</td><td>4.0</td></tr><tr><th><b>ED</b></th><td>3.9</td><td>4.0</td><td>4.1</td><td>4.1</td></tr><tr><th><b>TD</b></th><td>2.1</td><td>2.5</td><td>2.5</td><td>2.4</td></tr><tr><th><b>HND</b></th><td>8.9</td><td>9.0</td><td>8.6</td><td>8.4</td></tr><tr><th><b>RAD</b></th><td>8.2</td><td>7.5</td><td>8.1</td><td>7.9</td></tr><tr><th><b>TIB</b></th><td>14.5</td><td>14.6</td><td>14.6</td><td>14.7</td></tr><tr><th><b>FTL</b></th><td>20.2</td><td>22.0</td><td>21.0</td><td>20.5</td></tr></tbody></table>
TABLE 2 in Two new species of Caribbiantes, with the redescription of the type species and a review of male genital patterns in Antillean Stenostygninae (Opiliones: Laniatores: Biantidae)
<p><b>TABLE 2.</b> Measurements (in mm) of the male holotype (H) and paratypes (P) of <i>Caribbiantes obtusus</i> sp. nov.</p><table><tbody><tr><th></th><th>H ♂α CZACC 3.3384</th><th>P ♂α CZACC 3.3388</th><th>P ♂α CZACC 3.3389</th><th>P ♂β CZACC 3.3386</th><th>P ♀ CZACC 3.3385</th><th>P ♀ CZACC 3.3387</th><th>P ♀ CZACC 3.3390</th></tr><tr><th><i>Dorsal scutum</i></th></tr></tbody><tbody><tr><th>DSL</th><td>1.8</td><td>1.8</td><td>1.8</td><td>1.7</td><td>1.9</td><td>2.0</td><td>1.8</td></tr><tr><th>DSMW</th><td>1.6</td><td>1.6</td><td>1.6</td><td>1.4</td><td>1.7</td><td>1.6</td><td>1.6</td></tr><tr><th>CL</th><td>0.8</td><td>0.7</td><td>0.7</td><td>0.6</td><td>0.7</td><td>0.7</td><td>0.7</td></tr><tr><th>CMW</th><td>1.4</td><td>1.5</td><td>1.4</td><td>1.3</td><td>1.4</td><td>1.3</td><td>1.3</td></tr><tr><th><i>Pedipalp length</i></th><td>4.0</td><td>3.9</td><td>3.2</td><td>3.5</td><td>4.0</td><td>3.9</td><td>3.2</td></tr><tr><th>Tr</th><td>0.3</td><td>0.3</td><td>0.3</td><td>0.3</td><td>0.3</td><td>0.3</td><td>0.3</td></tr><tr><th>Fe</th><td>1.5</td><td>1.4</td><td>1.2</td><td>1.3</td><td>1.4</td><td>1.4</td><td>1.2</td></tr><tr><th>Pa</th><td>0.7</td><td>0.7</td><td>0.6</td><td>0.7</td><td>0.8</td><td>0.8</td><td>0.6</td></tr><tr><th>Ti</th><td>0.8</td><td>0.7</td><td>0.5</td><td>0.6</td><td>0.7</td><td>0.7</td><td>0.5</td></tr><tr><th>Ta</th><td>0.7</td><td>0.7</td><td>0.5</td><td>0.6</td><td>0.7</td><td>0.7</td><td>0.5</td></tr><tr><th><i>Leg I length</i></th><td>6.0</td><td>6.0</td><td>5.1</td><td>5.4</td><td>5.9</td><td>6.0</td><td>5.1</td></tr><tr><th>Tr</th><td>0.3</td><td>0.3</td><td>0.2</td><td>0.2</td><td>0.2</td><td>0.2</td><td>0.2</td></tr><tr><th>Fe</th><td>1.4</td><td>1.4</td><td>1.3</td><td>1.2</td><td>1.4</td><td>1.3</td><td>1.1</td></tr><tr><th>Pa</th><td>0.4</td><td>0.4</td><td>0.3</td><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td></tr><tr><th>Ti</th><td>1.2</td><td>1.2</td><td>1.0</td><td>1.1</td><td>1.3</td><td>1.3</td><td>1.1</td></tr><tr><th>Mt</th><td>1.8</td><td>1.7</td><td>1.4</td><td>1.5</td><td>1.7</td><td>1.7</td><td>1.5</td></tr><tr><th>Ta</th><td>1.0</td><td>1.1</td><td>0.9</td><td>1.0</td><td>1.1</td><td>1.1</td><td>0.8</td></tr><tr><th><i>Leg II length</i></th><td>14.8</td><td>12.5</td><td>11.6</td><td>12.8</td><td>13.3</td><td>12.7</td><td>11.9</td></tr><tr><th>Tr</th><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td></tr><tr><th>Fe</th><td>3.8</td><td>3.1</td><td>3.5</td><td>3.4</td><td>3.5</td><td>3.3</td><td>3.4</td></tr><tr><th>Pa</th><td>0.6</td><td>0.7</td><td>0.5</td><td>0.6</td><td>0.7</td><td>0.6</td><td>0.6</td></tr><tr><th>Ti</th><td>3.0</td><td>2.7</td><td>2.3</td><td>2.6</td><td>2.8</td><td>2.6</td><td>2.4</td></tr><tr><th>Mt</th><td>4.2</td><td>3.4</td><td>3.1</td><td>3.4</td><td>3.7</td><td>3.4</td><td>3.1</td></tr><tr><th>Ta</th><td>2.8</td><td>2.2</td><td>1.9</td><td>2.4</td><td>2.2</td><td>2.4</td><td>2.1</td></tr><tr><th><i>Leg III length</i></th><td>9.5</td><td>9.1</td><td>7.7</td><td>8.6</td><td>9.5</td><td>9.2</td><td>8.4</td></tr><tr><th>Tr</th><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td><td>0.4</td></tr><tr><th>Fe</th><td>2.7</td><td>2.4</td><td>2.1</td><td>2.4</td><td>2.8</td><td>2.5</td><td>2.4</td></tr><tr><th>Pa</th><td>0.6</td><td>0.6</td><td>0.6</td><td>0.6</td><td>0.7</td><td>0.7</td><td>0.7</td></tr><tr><th>Ti</th><td>1.7</td><td>1.7</td><td>1.3</td><td>1.5</td><td>1.7</td><td>1.7</td><td>1.4</td></tr><tr><th>Mt</th><td>2.8</td><td>2.5</td><td>2.2</td><td>2.4</td><td>2.6</td><td>2.6</td><td>2.5</td></tr><tr><th>Ta</th><td>1.3</td><td>1.4</td><td>1.1</td><td>1.3</td><td>1.3</td><td>1.4</td><td>1.0</td></tr><tr><th><i>Leg IV length</i></th><td>13.9</td><td>12.2</td><td>10.7</td><td>12.1</td><td>13.6</td><td>13.1</td><td>11.7</td></tr><tr><th>Tr</th><td>0.5</td><td>0.5</td><td>0.5</td><td>0.5</td><td>0.5</td><td>0.5</td><td>0.5</td></tr><tr><th>Fe</th><td>4.0</td><td>3.3</td><td>3.1</td><td>3.6</td><td>4.0</td><td>3.7</td><td>3.5</td></tr><tr><th>Pa</th><td>1.0</td><td>0.8</td><td>0.7</td><td>0.7</td><td>0.8</td><td>0.8</td><td>0.7</td></tr><tr><th>Ti</th><td>2.5</td><td>2.2</td><td>1.9</td><td>2.1</td><td>2.5</td><td>2.5</td><td>2.2</td></tr><tr><th>Mt</th><td>4.0</td><td>3.6</td><td>3.3</td><td>3.6</td><td>4.0</td><td>3.8</td><td>3.5</td></tr><tr><th>Ta</th><td>1.9</td><td>1.9</td><td>1.3</td><td>1.6</td><td>1.9</td><td>1.9</td><td>1.3</td></tr></tbody></table>
Table ¹: Model performance in relation to predictor variables combinations and MaxEnt parameters for the two best models identified in our analysis. in Understanding habitat suitability and road mortality for the conservation of the striped hyaena (Hyaena hyaena) in Batna (East Algeria)
<p><b>Table ¹:</b> Model performance in relation to predictor variables combinations and MaxEnt parameters for the two best models identified in our analysis.</p><table><tbody><tr><th><b>Prediction set</b></th><th><b>FC</b></th><th><b>RM</b></th><th><b>P</b> <b>ROC</b></th><th><b>OR</b></th><th><b>AICc</b></th><th><b>ΔAICc</b></th><th><b>WAICc</b></th><th><b>Number of parameters**</b></th></tr></tbody><tbody><tr><th>313</th><td>lqp</td><td>0.7</td><td>0</td><td>0</td><td>752.875</td><td>1.226</td><td>0.0337</td><td>10</td></tr><tr><th>314*</th><td>lqp</td><td>1</td><td>0</td><td>0</td><td>751.649</td><td>0.000</td><td>0.057</td><td>7</td></tr></tbody></table><p>The selected model set (*) met the statistical significance and omission rate criteria during evaluation with train and test data.**Number of environmental variables. FC, feature class; RM, regularization multiplier; OR = omission rate; ΔAICc, Akaike information criterion corrected for small simple sizes; WAICc, weighted AICc.</p>
TABLE 1 in New Galumnidae (Acari, Oribatida) from the Merida and Zulia States, Venezuela
<p><b>TABLE 1</b>. Leg setation and solenidia of adult <i>Sacculogalumna zuliaensis</i> <b>sp. nov.</b>, <i>Pergalumna</i> (<i>Pergalumna</i>) <i>convergens</i> <b>sp. nov.</b> and <i>Carinogalumna meridaensis</i> sp. nov.</p><table><tbody><tr><th>Leg</th><th><i>Tr</i></th><th><i>Fe</i></th><th><i>Ge</i></th><th><i>Ti</i></th><th><i>Ta</i></th></tr></tbody><tbody><tr><th>I</th><td><i>v’</i></td><td><i>d, (l), bv”</i></td><td><i>(l), v’,</i> σ</td><td><i>(l), (v),</i> φ1, φ2</td><td><i>(ft), (tc), (it), (p), (u), (a), s, (pv), v’, (pl), l”,</i> ɛ, ω 1, ω 2</td></tr><tr><th>II</th><td><i>v’</i></td><td><i>d, (l), bv”</i></td><td><i>(l), v’,</i> σ</td><td><i>(l), (v),</i> φ</td><td><i>(ft), (tc), (it), (p), (u), (a), s, (pv),</i> ω1, ω2</td></tr><tr><th>III</th><td><i>v’</i></td><td><i>d, ev’</i></td><td><i>l’,</i> σ</td><td><i>l’, (v),</i> φ</td><td><i>(ft), (tc), (it), (p), (u), (a), s, (pv)</i></td></tr><tr><th>IV</th><td><i>v’</i></td><td><i>d, ev’</i></td><td><i>d, l’</i></td><td><i>l’, (v),</i> φ</td><td>ft”, (tc), (p), (u), (a), s, (pv)</td></tr></tbody></table><p>Note: Roman letters refer to normal setae, Greek letters to solenidia (except ɛ = famulus). Single quotation mark (<i>’</i>) designates setae on the anterior and double quotation mark (<i>”</i>) setae on the posterior side of a given leg segment; parentheses refer to a pair of setae.</p>
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