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Table 4 in Assessing grass carp (Ctenopharyngodon idella) occupancy and detection probability within Lake Erie from environmental DNA
<p><b>Table 4.</b> Percentage of positive eDNA replicate detections in each month and site in 2018 and 2019 in western Lake Erie (based on at least one positive detection on at least one marker and one replicate). All markers (GCTM10, GCTM 22, GCTM32) were used to calculate these proportions. Samples were collected monthly from June to November for each site. The number of telemetered grass carp detected within 7 days before sampling for eDNA is denoted in parentheses. Acoustic telemetry receivers in MB in 2018 were not available. DR = Detroit River, HP = Hot Ponds, and MB = Maumee Bay. NA denotes when acoustic telemetry receivers were not in operation.</p><table><tbody><tr><th>Year</th></tr><tr><th>Site</th><th>2018</th><th>2019</th></tr><tr><th></th><th>June</th><th>July</th><th>Aug</th><th>Sept</th><th>Oct</th><th>Nov</th><th>May</th><th>June</th><th>July</th><th>August</th><th>Oct</th><th>Nov</th></tr></tbody><tbody><tr><th>DR</th><td>0.0%</td><td>2.3%</td><td>2.3%</td><td>0.0%</td><td>0.0%</td><td>0.0%</td><td>4.5%</td><td>10.6</td><td>14.1</td><td>17.4%</td><td>14.1%</td><td>2.2%</td></tr><tr><td>(1)</td><td>(1)</td><td>(2)</td><td>(1)</td><td>(2)</td><td>(0)</td><td>(1)</td><td>% (1)</td><td>% (1)</td><td>(2)</td><td>(2)</td><td>(0)</td></tr><tr><th>HP</th><td>0.0%</td><td>0.1%</td><td>4.1%</td><td>2.2%</td><td>15.8%</td><td>0.0%</td><td>9.0%</td><td>1.5%</td><td>34.8</td><td>1.5%</td><td>15.8%</td><td>22.7%</td></tr><tr><td>(1)</td><td>(1)</td><td>(2)</td><td>(2)</td><td>(3)</td><td>(NA)</td><td>(2)</td><td>(2)</td><td>% (2)</td><td>(3)</td><td>(2)</td><td>(2)</td></tr><tr><th>MB</th><td>12.0%</td><td>0.0%</td><td>0.0%</td><td>0.0%</td><td>0.0%</td><td>0.0%</td><td>0.0%</td><td>6.1%</td><td>37.1</td><td>8.3%</td><td>8.3%</td><td>0.0%</td></tr><tr><td>(NA)</td><td>(NA)</td><td>(NA)</td><td>(NA)</td><td>(NA)</td><td>(NA)</td><td>(0)</td><td>(0)</td><td>% (0)</td><td>(0)</td><td>(0)</td><td>(0)</td></tr></tbody></table>
Table 1 in Pseudofilamentous desmids (Zygnematophyceae) from an Amazonian floodplain lake (Macapá, AP, Brazil)
<p><b>Table 1.</b> Seasonal occurrence of pseudofilamentous desmids at Curralinho Lake (FR: relative frequency; F: frequent; LC: less common; R: rare; BP: both periods, rainy and less rainy; RP: rainy period.</p><table><tbody><tr><th><b>Taxon</b></th><th><b>F.R. (%)</b></th><th><b>Category</b></th><th><b>Seasonal occurrence</b></th></tr></tbody><tbody><tr><th><i>Bambusina borreri</i> var. <i>borreri</i></th><td>58,33</td><td>F</td><td>BP</td></tr><tr><th><i>B. borreri</i> var. <i>brasiliense</i></th><td>50</td><td>F</td><td>BP</td></tr><tr><th><i>B. borreri</i> var. <i>majus</i></th><td>50</td><td>F</td><td>BP</td></tr><tr><th><i>Desmidium baileyi</i> var. <i>baileyi</i> f. <i>baileyi</i></th><td>33.33</td><td>LC</td><td>RP</td></tr><tr><th><i>D. elegans</i></th><td>50</td><td>F</td><td>BP</td></tr><tr><th><i>D. graciliceps</i> var. <i>graciliceps</i></th><td>16.66</td><td>LC</td><td>BP</td></tr><tr><th><i>D. graciliceps</i> var. <i>groenbladii</i></th><td>25</td><td>LC</td><td>BP</td></tr><tr><th><i>D. longatum</i></th><td>33.33</td><td>LC</td><td>BP</td></tr><tr><th><i>D. quadratum</i> var. <i>quadratum</i></th><td>16.66</td><td>LC</td><td>RP</td></tr><tr><th><i>D. quadratum</i> var. <i>constrictum</i></th><td>16.66</td><td>LC</td><td>RP</td></tr><tr><th><i>Groenbladia neglecta</i> var. <i>neglecta</i></th><td>58.33</td><td>F</td><td>BP</td></tr><tr><th><i>G. neglecta</i> var. <i>elongata</i></th><td>58.33</td><td>F</td><td>BP</td></tr><tr><th><i>Haplozyga armata</i> var. <i>armata</i></th><td>41.66</td><td>F</td><td>RP</td></tr><tr><th><i>Hyalotheca dissiliens</i> var. <i>dissiliens</i></th><td>41.66</td><td>F</td><td>BP</td></tr><tr><th><i>H. javanica</i></th><td>58.33</td><td>F</td><td>BP</td></tr><tr><th><i>Mateola curvata</i></th><td>8.33</td><td>R</td><td>RP</td></tr><tr><th><i>Phymatodocis nordstedtiniana</i> var. <i>nordstedtiniana</i> f. <i>minor</i></th><td>25</td><td>LC</td><td>BP</td></tr><tr><th><i>Spondylosium desmidiiforme</i></th><td>8.33</td><td>R</td><td>RP</td></tr><tr><th><i>S. pulchrum</i> var. <i>pulchrum</i></th><td>16.66</td><td>LC</td><td>BP</td></tr><tr><th><i>S. rectangulare</i> var. <i>rectangulare</i></th><td>41.66</td><td>F</td><td>BP</td></tr><tr><th><i>S. rectangulare</i> var. <i>goyazense</i></th><td>25</td><td>LC</td><td>BP</td></tr></tbody></table>
Table 1. Uncorrected distances among 31 in On the distribution and taxonomy of bats of the Myotis mystacinus morphogroup from the Caucasus region (Chiroptera: Vespertilionidae)
<p><b>Table 1</b>. Uncorrected distances among 31 haplotypes of the cytochrome <i>b</i> gene found in the bats of the <i>Myotis mystacinus</i> morphogroup from the Caucasus region.</p><table><tbody><tr><th>hap1</th><th>hap2</th><th>hap3</th><th>hap4</th><th>hap5</th><th>hap6</th><th>hap7</th><th>hap8</th><th>hap9</th><th>hap10 hap11 hap12 hap13 hap14 hap15 hap16 hap17 hap18 hap19 hap20 hap21 hap22 hap23 hap24 hap25</th><th>hap26 hap27 hap28</th><th>hap29 hap30</th></tr></tbody><tbody><tr><th>hap2 0.001</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></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>hap3 0.007</th><td>0.006</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><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap4 0.003</th><td>0.002</td><td>0.004</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><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap5 0.015</th><td>0.014</td><td>0.017</td><td>0.012</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><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap6 0.039</th><td>0.038</td><td>0.039</td><td>0.036</td><td>0.039</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><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap7 0.041</th><td>0.040</td><td>0.041</td><td>0.039</td><td>0.042</td><td>0.004</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><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap8 0.039</th><td>0.038</td><td>0.039</td><td>0.036</td><td>0.039</td><td>0.002</td><td>0.004</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><td></td><td></td><td></td><td></td></tr><tr><th>hap9 0.127</th><td>0.126</td><td>0.131</td><td>0.128</td><td>0.132</td><td>0.133</td><td>0.136</td><td>0.135</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><td></td><td></td><td></td></tr><tr><th>hap10 0.127</th><td>0.126</td><td>0.131</td><td>0.128</td><td>0.132</td><td>0.133</td><td>0.136</td><td>0.135</td><td>0.003</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><td></td><td></td></tr><tr><th>hap11 0.125</th><td>0.125</td><td>0.129</td><td>0.126</td><td>0.130</td><td>0.132</td><td>0.135</td><td>0.134</td><td>0.002</td><td>0.004</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><td></td></tr><tr><th>hap12 0.126</th><td>0.125</td><td>0.130</td><td>0.127</td><td>0.131</td><td>0.133</td><td>0.136</td><td>0.135</td><td>0.003</td><td>0.005</td><td>0.001</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>hap13 0.129</th><td>0.128</td><td>0.132</td><td>0.130</td><td>0.133</td><td>0.136</td><td>0.139</td><td>0.138</td><td>0.006</td><td>0.009</td><td>0.006</td><td>0.007</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>hap14 0.127</th><td>0.126</td><td>0.131</td><td>0.128</td><td>0.130</td><td>0.131</td><td>0.133</td><td>0.132</td><td>0.004</td><td>0.006</td><td>0.004</td><td>0.004</td><td>0.006</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>hap15 0.128</th><td>0.127</td><td>0.132</td><td>0.129</td><td>0.132</td><td>0.135</td><td>0.138</td><td>0.137</td><td>0.010</td><td>0.012</td><td>0.010</td><td>0.011</td><td>0.012</td><td>0.010</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>hap16 0.122</th><td>0.121</td><td>0.125</td><td>0.123</td><td>0.125</td><td>0.127</td><td>0.130</td><td>0.129</td><td>0.019</td><td>0.022</td><td>0.019</td><td>0.020</td><td>0.020</td><td>0.019</td><td>0.018</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>hap17 0.145</th><td>0.144</td><td>0.146</td><td>0.146</td><td>0.146</td><td>0.146</td><td>0.143</td><td>0.146</td><td>0.158</td><td>0.157</td><td>0.156</td><td>0.157</td><td>0.160</td><td>0.156</td><td>0.158</td><td>0.159</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>hap18 0.145</th><td>0.144</td><td>0.146</td><td>0.146</td><td>0.146</td><td>0.146</td><td>0.143</td><td>0.146</td><td>0.158</td><td>0.157</td><td>0.156</td><td>0.157</td><td>0.160</td><td>0.156</td><td>0.158</td><td>0.161</td><td>0.002</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>hap19 0.146</th><td>0.145</td><td>0.147</td><td>0.146</td><td>0.147</td><td>0.146</td><td>0.144</td><td>0.146</td><td>0.159</td><td>0.158</td><td>0.157</td><td>0.158</td><td>0.161</td><td>0.157</td><td>0.159</td><td>0.161</td><td>0.003</td><td>0.001</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>hap20 0.143</th><td>0.142</td><td>0.145</td><td>0.144</td><td>0.145</td><td>0.144</td><td>0.141</td><td>0.144</td><td>0.156</td><td>0.155</td><td>0.154</td><td>0.155</td><td>0.158</td><td>0.154</td><td>0.156</td><td>0.159</td><td>0.004</td><td>0.002</td><td>0.003</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>hap21 0.145</th><td>0.144</td><td>0.146</td><td>0.146</td><td>0.146</td><td>0.146</td><td>0.143</td><td>0.146</td><td>0.158</td><td>0.157</td><td>0.156</td><td>0.157</td><td>0.160</td><td>0.156</td><td>0.158</td><td>0.161</td><td>0.004</td><td>0.002</td><td>0.003</td><td>0.002</td><td>–</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap22 0.144</th><td>0.143</td><td>0.146</td><td>0.145</td><td>0.146</td><td>0.145</td><td>0.142</td><td>0.145</td><td>0.157</td><td>0.156</td><td>0.155</td><td>0.156</td><td>0.159</td><td>0.155</td><td>0.157</td><td>0.160</td><td>0.003</td><td>0.001</td><td>0.002</td><td>0.001</td><td>0.001</td><td>–</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap23 0.151</th><td>0.150</td><td>0.153</td><td>0.152</td><td>0.151</td><td>0.145</td><td>0.142</td><td>0.145</td><td>0.161</td><td>0.160</td><td>0.159</td><td>0.160</td><td>0.161</td><td>0.159</td><td>0.161</td><td>0.160</td><td>0.027</td><td>0.025</td><td>0.026</td><td>0.025</td><td>0.025</td><td>0.025</td><td>–</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap24 0.153</th><td>0.152</td><td>0.154</td><td>0.154</td><td>0.153</td><td>0.146</td><td>0.144</td><td>0.146</td><td>0.162</td><td>0.161</td><td>0.161</td><td>0.161</td><td>0.162</td><td>0.161</td><td>0.162</td><td>0.161</td><td>0.029</td><td>0.027</td><td>0.026</td><td>0.027</td><td>0.027</td><td>0.026</td><td>0.002</td><td>–</td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap25 0.153</th><td>0.152</td><td>0.154</td><td>0.154</td><td>0.153</td><td>0.146</td><td>0.144</td><td>0.146</td><td>0.163</td><td>0.162</td><td>0.161</td><td>0.162</td><td>0.163</td><td>0.161</td><td>0.163</td><td>0.162</td><td>0.029</td><td>0.027</td><td>0.028</td><td>0.027</td><td>0.027</td><td>0.026</td><td>0.004</td><td>0.005</td><td>–</td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>hap26 0.153</th><td>0.152</td><td>0.154</td><td>0.154</td><td>0.153</td><td>0.146</td><td>0.144</td><td>0.146</td><td>0.162</td><td>0.161</td><td>0.161 0.161</td><td>0.162</td><td>0.161</td><td>0.162</td><td>0.161</td><td>0.027</td><td>0.025</td><td>0.026</td><td>0.025</td><td>0.025</td><td>0.025</td><td>0.002</td><td>0.004</td><td>0.002</td><td>–</td><td></td><td></td><td></td><td></td></tr><tr><th>hap27 0.151</th><td>0.150</td><td>0.153</td><td>0.150</td><td>0.149</td><td>0.146</td><td>0.147</td><td>0.146</td><td>0.161</td><td>0.161</td><td>0.159</td><td>0.160</td><td>0.161</td><td>0.159</td><td>0.161</td><td>0.158</td><td>0.049</td><td>0.049</td><td>0.050</td><td>0.049</td><td>0.049</td><td>0.048</td><td>0.050</td><td>0.052</td><td>0.052</td><td>0.050</td><td>–</td><td></td><td></td><td></td></tr><tr><th>hap28 0.149</th><td>0.148</td><td>0.151</td><td>0.148</td><td>0.147</td><td>0.145</td><td>0.146</td><td>0.145</td><td>0.159</td><td>0.160</td><td>0.157</td><td>0.158</td><td>0.159</td><td>0.157</td><td>0.161</td><td>0.156</td><td>0.047</td><td>0.047</td><td>0.048</td><td>0.047</td><td>0.047</td><td>0.046</td><td>0.048</td><td>0.050</td><td>0.050</td><td>0.048</td><td>0.002</td><td>–</td><td></td><td></td></tr><tr><th>hap29 0.150</th><td>0.149</td><td>0.152</td><td>0.149</td><td>0.148</td><td>0.146</td><td>0.146</td><td>0.146</td><td>0.160</td><td>0.161</td><td>0.158</td><td>0.159</td><td>0.160</td><td>0.158</td><td>0.161</td><td>0.157</td><td>0.048</td><td>0.048</td><td>0.048</td><td>0.048</td><td>0.048</td><td>0.047</td><td>0.049</td><td>0.050</td><td>0.051</td><td>0.049</td><td>0.003</td><td>0.001</td><td>–</td><td></td></tr><tr><th>hap30 0.152</th><td>0.153</td><td>0.157</td><td>0.154</td><td>0.154</td><td>0.144</td><td>0.143</td><td>0.144</td><td>0.158</td><td>0.159</td><td>0.158</td><td>0.157</td><td>0.158</td><td>0.156</td><td>0.157</td><td>0.154</td><td>0.104</td><td>0.103</td><td>0.104</td><td>0.103</td><td>0.101</td><td>0.102</td><td>0.099</td><td>0.101</td><td>0.101</td><td>0.101</td><td>0.097</td><td>0.096</td><td>0.097</td><td>–</td></tr><tr><th>hap31 0.167</th><td>0.166</td><td>0.165</td><td>0.166</td><td>0.164</td><td>0.159</td><td>0.161</td><td>0.157</td><td>0.168</td><td>0.169</td><td>0.168</td><td>0.168</td><td>0.166</td><td>0.168</td><td>0.171</td><td>0.164</td><td>0.169</td><td>0.169</td><td>0.170</td><td>0.169</td><td>0.168</td><td>0.168</td><td>0.161</td><td>0.163</td><td>0.163</td><td>0.163</td><td>0.161</td><td>0.159</td><td>0.160</td><td>0.147</td></tr></tbody></table>
Table 3 in Assessing grass carp (Ctenopharyngodon idella) occupancy and detection probability within Lake Erie from environmental DNA
<p><b>Table 3.</b> Candidate set of hierarchical occupancy models used to estimate probability of grass carp eDNA occurrence among sites (ψ), the conditional probability of grass carp eDNA occurrence at a sampling locality within a site given that grass carp were present at the site (Θ), and the conditional probability of eDNA detection on replicate filters collected at a sampling locality given that the species is present at the sampling locality <i>(p</i>) from three sites in western Lake Erie sampled in 2018 and 2019. Covariates included location (site), time (Month) and probe type (GCTM10, GCTM22, GCTM32). Model comparison was evaluated with the Widely Applicable Information Criterion (WAIC).</p><table><tbody><tr><th>Model</th><th>WAIC</th><th>Δ WAIC</th><th>Lack of fit</th><th>Predicted Variance</th></tr></tbody><tbody><tr><th>ψ(Site)Θ(Site)p(.)</th><td>309.44</td><td>-</td><td>298.70</td><td>18.63</td></tr><tr><th>ψ(.)Θ(Site)p(.)</th><td>309.50</td><td>0.06</td><td>298.99</td><td>10.73</td></tr><tr><th>ψ(.)Θ(Month)p(.)</th><td>317.61</td><td>8.18</td><td>299.05</td><td>18.56</td></tr><tr><th>ψ(Season)Θ(.)p(.)</th><td>317.67</td><td>8.24</td><td>299.01</td><td>18.65</td></tr><tr><th>ψ(Month)Θ(.)p(.)</th><td>317.72</td><td>8.28</td><td>299.04</td><td>18.67</td></tr><tr><th>ψ(Season)Θ(Season)p(.)</th><td>317.84</td><td>8.40</td><td>299.04</td><td>18.79</td></tr><tr><th>ψ(.)Θ(Season)p(.)</th><td>317.74</td><td>8.31</td><td>299.07</td><td>18.66</td></tr><tr><th>ψ(Site)Θ(.)p(.)</th><td>317.94</td><td>8.51</td><td>299.04</td><td>18.90</td></tr><tr><th>ψ(.)Θ(.)p(.)</th><td>325.00</td><td>15.57</td><td>305.50</td><td>20.21</td></tr><tr><th>ψ(Season)Θ(Site)p(.)</th><td>325.41</td><td>15.98</td><td>305.49</td><td>19.91</td></tr><tr><th>ψ(Site + Season)Θ(.)p(.)</th><td>325.59</td><td>16.16</td><td>305.44</td><td>20.15</td></tr><tr><th>ψ(Site)Θ(Season)p(.)</th><td>325.72</td><td>16.29</td><td>305.48</td><td>20.23</td></tr><tr><th>ψ(Site + Season)Θ(Site + Season)p(.)</th><td>325.92</td><td>16.49</td><td>305.49</td><td>20.43</td></tr><tr><th>ψ(.)Θ(Site + Season)p(.)</th><td>326.37</td><td>16.94</td><td>305.52</td><td>20.84</td></tr><tr><th>ψ(Site)Θ(Month)p(.)</th><td>329.57</td><td>20.14</td><td>308.65</td><td>20.92</td></tr><tr><th>ψ(Month)Θ(Month)p(.)</th><td>330.14</td><td>20.71</td><td>308.66</td><td>21.84</td></tr><tr><th>ψ(Site + Season)Θ(Site)p(Probe)</th><td>377.63</td><td>68.20</td><td>276.90</td><td>100.72</td></tr><tr><th>ψ(Site + Season)Θ(.)p(Probe)</th><td>378.35</td><td>68.92</td><td>277.00</td><td>101.34</td></tr><tr><th>ψ(Site + Season)Θ(Site + Season)p(Probe)</th><td>378.42</td><td>68.99</td><td>277.00</td><td>101.41</td></tr><tr><th>ψ(Site + Season)Θ(Season)p(Probe)</th><td>378.55</td><td>69.12</td><td>277.09</td><td>101.46</td></tr><tr><th>ψ(Season)Θ(Site + Season)p(Probe)</th><td>379.41</td><td>69.98</td><td>277.28</td><td>102.10</td></tr><tr><th>ψ(Site)Θ(Site + Season)p(Probe)</th><td>379.62</td><td>70.19</td><td>277.40</td><td>102.21</td></tr><tr><th>ψ(.)Θ(Site + Season)p(Probe)</th><td>379.88</td><td>70.45</td><td>277.31</td><td>102.57</td></tr><tr><th>ψ(Site + Month)Θ(.)p(.)</th><td>383.56</td><td>74.13</td><td>282.86</td><td>100.69</td></tr><tr><th>ψ(Site + Month)Θ(Site + Month)p(.)</th><td>385.47</td><td>76.04</td><td>283.38</td><td>102.09</td></tr><tr><th>ψ(Site + Month)Θ(Site + Month)p(Probe)</th><td>386.95</td><td>77.52</td><td>282.90</td><td>104.05</td></tr><tr><th>ψ(.)Θ(Site + Month)p(.)</th><td>396.44</td><td>87.01</td><td>292.14</td><td>104.29</td></tr><tr><th>ψ(.)Θ(.)p(Probe)</th><td>396.45</td><td>87.01</td><td>292.14</td><td>104.29</td></tr></tbody></table>
Table 2 in On the distribution and taxonomy of bats of the Myotis mystacinus morphogroup from the Caucasus region (Chiroptera: Vespertilionidae)
<p><b>Table 2</b>. External, skull, and tooth dimensions (in millimetres) of the examined sample sets of the <i>Myotis mystacinus</i> morphogroup from the Caucasus region. See Section 2.3 for explanation of the dimension acronyms.</p><table><tbody><tr><th></th><th>Lineage I</th><th></th><th></th><th></th><th>Lineage II</th><th></th><th></th><th></th><th>Lineage IV</th><th></th><th></th><th></th><th>Lineage V</th><th>Lineage VI</th><th></th><th></th><th></th></tr></tbody><tbody><tr><th></th><td><i>M. mystacinus</i> s.str.</td><td></td><td></td><td><i>M. davidii</i></td><td></td><td></td><td></td><td><i>M.</i> cf. a <i>lcathoe</i></td><td></td><td></td><td><i>M. hyrcanicus</i></td><td><i>M. brandtii</i></td><td></td><td></td><td></td></tr><tr><th></th><td>n</td><td><b>M</b></td><td>min</td><td>max</td><td>SD</td><td>n</td><td><b>M</b></td><td>min</td><td>max</td><td>SD</td><td>n</td><td><b>M</b></td><td>min</td><td>max</td><td>SD</td><td></td><td>n</td><td><b>M</b></td><td>min</td><td>max</td><td>SD</td></tr><tr><th>LAt</th><td>7</td><td><b>34.94</b></td><td>34.40</td><td>36.10</td><td>0.648</td><td>12</td><td><b>34.98</b></td><td>33.4</td><td>37.2</td><td>1.012</td><td>17</td><td><b>32.34</b></td><td>30.1</td><td>34.2</td><td>0.941</td><td>32.4</td><td>5</td><td><b>35.16</b></td><td>34.4</td><td>35.7</td><td>0.503</td></tr><tr><th>LPol</th><td>7</td><td><b>5.09</b></td><td>4.70</td><td>5.40</td><td>0.279</td><td>12</td><td><b>5.83</b></td><td>5.2</td><td>6.3</td><td>0.345</td><td>17</td><td><b>4.29</b></td><td>4.1</td><td>4.6</td><td>0.145</td><td>4.4</td><td>4</td><td><b>5.45</b></td><td>5.2</td><td>5.9</td><td>0.311</td></tr><tr><th>LTib</th><td>7</td><td><b>16.30</b></td><td>15.60</td><td>16.90</td><td>0.465</td><td>12</td><td><b>16.73</b></td><td>15.9</td><td>17.9</td><td>0.508</td><td>17</td><td><b>14.17</b></td><td>12.3</td><td>15.3</td><td>0.699</td><td>14.1</td><td>1</td><td>15.6</td><td></td><td></td><td></td></tr><tr><th>LCr</th><td>7</td><td><b>13.56</b></td><td>13.16</td><td>14.37</td><td>0.439</td><td>12</td><td><b>13.86</b></td><td>13.42</td><td>14.56</td><td>0.331</td><td>17</td><td><b>12.88</b></td><td>12.48</td><td>13.22</td><td>0.227</td><td>12.66</td><td>13</td><td><b>14.06</b></td><td>13.66</td><td>14.57</td><td>0.276</td></tr><tr><th>LCb</th><td>7</td><td><b>12.97</b></td><td>12.52</td><td>13.71</td><td>0.428</td><td>12</td><td><b>13.11</b></td><td>12.72</td><td>13.73</td><td>0.296</td><td>17</td><td><b>12.30</b></td><td>11.84</td><td>12.74</td><td>0.267</td><td>12.06</td><td>13</td><td><b>13.44</b></td><td>12.92</td><td>14.03</td><td>0.295</td></tr><tr><th>LaZ</th><td>6</td><td><b>8.24</b></td><td>7.96</td><td>8.42</td><td>0.166</td><td>9</td><td><b>8.62</b></td><td>8.22</td><td>8.99</td><td>0.239</td><td>14</td><td><b>7.93</b></td><td>7.61</td><td>8.23</td><td>0.184</td><td>8.08</td><td>12</td><td><b>8.50</b></td><td>8.20</td><td>8.81</td><td>0.181</td></tr><tr><th>LaI</th><td>7</td><td><b>3.40</b></td><td>3.28</td><td>3.65</td><td>0.139</td><td>12</td><td><b>3.47</b></td><td>3.33</td><td>3.87</td><td>0.140</td><td>17</td><td><b>3.16</b></td><td>2.87</td><td>3.43</td><td>0.142</td><td>3.27</td><td>13</td><td><b>3.61</b></td><td>3.40</td><td>3.74</td><td>0.106</td></tr><tr><th>LaInf</th><td>7</td><td><b>3.25</b></td><td>2.96</td><td>3.53</td><td>0.176</td><td>12</td><td><b>3.39</b></td><td>3.13</td><td>3.58</td><td>0.131</td><td>17</td><td><b>3.21</b></td><td>3.01</td><td>3.42</td><td>0.116</td><td>3.13</td><td>13</td><td><b>3.52</b></td><td>3.38</td><td>3.67</td><td>0.081</td></tr><tr><th>LaN</th><td>7</td><td><b>6.60</b></td><td>6.28</td><td>6.93</td><td>0.242</td><td>12</td><td><b>6.81</b></td><td>6.52</td><td>7.27</td><td>0.219</td><td>17</td><td><b>6.25</b></td><td>5.94</td><td>6.50</td><td>0.138</td><td>6.14</td><td>13</td><td><b>6.89</b></td><td>6.66</td><td>7.14</td><td>0.120</td></tr><tr><th>AN</th><td>7</td><td><b>4.79</b></td><td>4.59</td><td>5.07</td><td>0.184</td><td>12</td><td><b>4.87</b></td><td>4.62</td><td>5.13</td><td>0.156</td><td>17</td><td><b>4.59</b></td><td>4.44</td><td>4.74</td><td>0.106</td><td>4.52</td><td>13</td><td><b>4.73</b></td><td>4.52</td><td>4.96</td><td>0.150</td></tr><tr><th>CC</th><td>6</td><td><b>3.33</b></td><td>3.17</td><td>3.57</td><td>0.148</td><td>12</td><td><b>3.46</b></td><td>3.20</td><td>3.62</td><td>0.138</td><td>17</td><td><b>3.18</b></td><td>3.05</td><td>3.33</td><td>0.087</td><td>3.27</td><td>13</td><td><b>3.39</b></td><td>3.27</td><td>3.62</td><td>0.095</td></tr><tr><th>M3M3</th><td>6</td><td><b>5.34</b></td><td>5.09</td><td>5.49</td><td>0.140</td><td>12</td><td><b>5.43</b></td><td>5.12</td><td>5.74</td><td>0.163</td><td>16</td><td><b>5.14</b></td><td>4.91</td><td>5.34</td><td>0.102</td><td>5.18</td><td>13</td><td><b>5.34</b></td><td>5.08</td><td>5.76</td><td>0.174</td></tr><tr><th>IM3</th><td>7</td><td><b>6.28</b></td><td>6.06</td><td>6.68</td><td>0.228</td><td>12</td><td><b>6.13</b></td><td>5.97</td><td>6.29</td><td>0.096</td><td>17</td><td><b>5.90</b></td><td>5.58</td><td>6.18</td><td>0.147</td><td>6.01</td><td>12</td><td><b>6.47</b></td><td>6.23</td><td>6.91</td><td>0.198</td></tr><tr><th>CM3</th><td>7</td><td><b>5.24</b></td><td>5.06</td><td>5.68</td><td>0.233</td><td>12</td><td><b>5.08</b></td><td>4.96</td><td>5.23</td><td>0.092</td><td>17</td><td><b>4.89</b></td><td>4.67</td><td>5.11</td><td>0.107</td><td>4.92</td><td>13</td><td><b>5.29</b></td><td>5.08</td><td>5.71</td><td>0.171</td></tr><tr><th>P4M3</th><td>7</td><td><b>3.90</b></td><td>3.68</td><td>4.16</td><td>0.152</td><td>12</td><td><b>3.92</b></td><td>3.76</td><td>4.05</td><td>0.094</td><td>17</td><td><b>3.67</b></td><td>3.50</td><td>3.79</td><td>0.090</td><td>3.63</td><td>12</td><td><b>3.78</b></td><td>3.42</td><td>4.27</td><td>0.236</td></tr><tr><th>M1M3</th><td>7</td><td><b>3.20</b></td><td>3.00</td><td>3.45</td><td>0.146</td><td>12</td><td><b>3.14</b></td><td>3.05</td><td>3.21</td><td>0.054</td><td>17</td><td><b>3.02</b></td><td>2.84</td><td>3.58</td><td>0.157</td><td>2.97</td><td>12</td><td><b>3.09</b></td><td>2.74</td><td>3.42</td><td>0.195</td></tr><tr><th>M1M2</th><td>7</td><td><b>2.48</b></td><td>2.32</td><td>2.65</td><td>0.107</td><td>12</td><td><b>2.43</b></td><td>2.32</td><td>2.49</td><td>0.058</td><td>17</td><td><b>2.32</b></td><td>2.20</td><td>2.43</td><td>0.068</td><td>2.31</td><td>12</td><td><b>2.37</b></td><td>2.15</td><td>2.68</td><td>0.136</td></tr><tr><th>CP4</th><td>7</td><td><b>2.54</b></td><td>2.43</td><td>2.77</td><td>0.116</td><td>12</td><td><b>2.44</b></td><td>2.32</td><td>2.55</td><td>0.080</td><td>17</td><td><b>2.35</b></td><td>2.23</td><td>2.49</td><td>0.083</td><td>2.45</td><td>12</td><td><b>2.54</b></td><td>2.35</td><td>2.82</td><td>0.165</td></tr><tr><th>P2P3</th><td>7</td><td><b>0.76</b></td><td>0.68</td><td>0.82</td><td>0.049</td><td>12</td><td><b>0.65</b></td><td>0.51</td><td>0.74</td><td>0.057</td><td>17</td><td><b>0.72</b></td><td>0.59</td><td>0.77</td><td>0.055</td><td>0.72</td><td>12</td><td><b>0.80</b></td><td>0.71</td><td>0.92</td><td>0.067</td></tr><tr><th>LMd</th><td>6</td><td><b>9.79</b></td><td>9.52</td><td>10.45</td><td>0.342</td><td>12</td><td><b>9.67</b></td><td>9.46</td><td>9.96</td><td>0.169</td><td>14</td><td><b>9.32</b></td><td>8.93</td><td>9.63</td><td>0.202</td><td>9.31</td><td>12</td><td><b>10.09</b></td><td>9.76</td><td>10.42</td><td>0.219</td></tr><tr><th>ACo</th><td>6</td><td><b>2.67</b></td><td>2.53</td><td>2.89</td><td>0.149</td><td>12</td><td><b>2.74</b></td><td>2.57</td><td>2.97</td><td>0.114</td><td>16</td><td><b>2.74</b></td><td>2.61</td><td>2.94</td><td>0.085</td><td>2.61</td><td>11</td><td><b>2.82</b></td><td>2.58</td><td>2.98</td><td>0.128</td></tr><tr><th>IM3</th><td>7</td><td><b>6.65</b></td><td>6.34</td><td>7.14</td><td>0.257</td><td>12</td><td><b>6.50</b></td><td>6.39</td><td>6.61</td><td>0.092</td><td>17</td><td><b>6.25</b></td><td>5.94</td><td>6.49</td><td>0.136</td><td>6.34</td><td>12</td><td><b>6.79</b></td><td>6.43</td><td>7.22</td><td>0.233</td></tr><tr><th>CM3</th><td>7</td><td><b>5.59</b></td><td>5.34</td><td>5.97</td><td>0.218</td><td>12</td><td><b>5.52</b></td><td>5.35</td><td>5.82</td><td>0.126</td><td>17</td><td><b>5.26</b></td><td>5.01</td><td>5.48</td><td>0.126</td><td>5.24</td><td>13</td><td><b>5.71</b></td><td>5.47</td><td>6.11</td><td>0.188</td></tr><tr><th>P4M3</th><td>7</td><td><b>4.20</b></td><td>3.89</td><td>4.45</td><td>0.174</td><td>12</td><td><b>4.20</b></td><td>4.08</td><td>4.29</td><td>0.076</td><td>17</td><td><b>3.99</b></td><td>3.79</td><td>4.13</td><td>0.091</td><td>3.95</td><td>12</td><td><b>4.09</b></td><td>3.82</td><td>4.58</td><td>0.268</td></tr><tr><th>M1M3</th><td>7</td><td><b>3.50</b></td><td>3.18</td><td>3.63</td><td>0.163</td><td>12</td><td><b>3.49</b></td><td>3.37</td><td>3.61</td><td>0.071</td><td>17</td><td><b>3.32</b></td><td>3.13</td><td>3.42</td><td>0.087</td><td>3.53</td><td>12</td><td><b>3.45</b></td><td>3.16</td><td>3.79</td><td>0.194</td></tr><tr><th>CP4</th><td>7</td><td><b>2.28</b></td><td>2.18</td><td>2.54</td><td>0.122</td><td>12</td><td><b>2.15</b></td><td>2.04</td><td>2.28</td><td>0.085</td><td>17</td><td><b>2.12</b></td><td>1.98</td><td>2.24</td><td>0.078</td><td>2.15</td><td>12</td><td><b>2.33</b></td><td>2.20</td><td>2.54</td><td>0.117</td></tr><tr><th>P2P3</th><td>7</td><td><b>0.87</b></td><td>0.81</td><td>0.98</td><td>0.066</td><td>12</td><td><b>0.78</b></td><td>0.71</td><td>0.85</td><td>0.038</td><td>17</td><td><b>0.82</b></td><td>0.74</td><td>0.90</td><td>0.051</td><td>0.82</td><td>12</td><td><b>0.91</b></td><td>0.85</td><td>0.98</td><td>0.044</td></tr><tr><th>LCn</th><td>7</td><td><b>0.85</b></td><td>0.80</td><td>0.90</td><td>0.044</td><td>12</td><td><b>0.95</b></td><td>0.90</td><td>1.01</td><td>0.031</td><td>17</td><td><b>0.82</b></td><td>0.73</td><td>0.91</td><td>0.040</td><td>0.82</td><td>12</td><td><b>0.83</b></td><td>0.74</td><td>0.95</td><td>0.053</td></tr><tr><th>LaCn</th><td>7</td><td><b>0.67</b></td><td>0.61</td><td>0.75</td><td>0.046</td><td>12</td><td><b>0.69</b></td><td>0.61</td><td>0.75</td><td>0.040</td><td>17</td><td><b>0.63</b></td><td>0.58</td><td>0.68</td><td>0.034</td><td>0.65</td><td>12</td><td><b>0.68</b></td><td>0.63</td><td>0.80</td><td>0.045</td></tr><tr><th>P3</th><td>7</td><td><b>0.35</b></td><td>0.29</td><td>0.39</td><td>0.031</td><td>12</td><td><b>0.31</b></td><td>0.22</td><td>0.39</td><td>0.046</td><td>17</td><td><b>0.36</b></td><td>0.29</td><td>0.43</td><td>0.032</td><td>0.35</td><td>12</td><td><b>0.37</b></td><td>0.30</td><td>0.42</td><td>0.035</td></tr><tr><th>P3</th><td>7</td><td><b>0.39</b></td><td>0.37</td><td>0.43</td><td>0.030</td><td>12</td><td><b>0.34</b></td><td>0.30</td><td>0.38</td><td>0.027</td><td>17</td><td><b>0.38</b></td><td>0.29</td><td>0.43</td><td>0.036</td><td>0.38</td><td>12</td><td><b>0.42</b></td><td>0.36</td><td>0.47</td><td>0.034</td></tr><tr><th>ACin</th><td>7</td><td><b>0.13</b></td><td>0.06</td><td>0.17</td><td>0.041</td><td>12</td><td><b>0.10</b></td><td>0.04</td><td>0.21</td><td>0.045</td><td>17</td><td><b>0.14</b></td><td>0.10</td><td>0.17</td><td>0.023</td><td>0.14</td><td>8</td><td><b>0.26</b></td><td>0.20</td><td>0.31</td><td>0.041</td></tr><tr><th>P4</th><td>7</td><td><b>1.25</b></td><td>1.09</td><td>1.37</td><td>0.088</td><td>12</td><td><b>1.28</b></td><td>1.18</td><td>1.35</td><td>0.052</td><td>17</td><td><b>1.07</b></td><td>0.97</td><td>1.16</td><td>0.048</td><td>1.22</td><td>12</td><td><b>1.23</b></td><td>1.09</td><td>1.38</td><td>0.092</td></tr><tr><th>M1</th><td>7</td><td><b>1.47</b></td><td>1.40</td><td>1.63</td><td>0.089</td><td>12</td><td><b>1.42</b></td><td>1.30</td><td>1.48</td><td>0.053</td><td>17</td><td><b>1.36</b></td><td>1.18</td><td>1.47</td><td>0.064</td><td>1.38</td><td>12</td><td><b>1.44</b></td><td>1.26</td><td>1.58</td><td>0.092</td></tr><tr><th>M2</th><td>7</td><td><b>1.61</b></td><td>1.53</td><td>1.74</td><td>0.070</td><td>12</td><td><b>1.59</b></td><td>1.46</td><td>1.65</td><td>0.056</td><td>17</td><td><b>1.56</b></td><td>1.46</td><td>1.65</td><td>0.047</td><td>1.56</td><td>12</td><td><b>1.58</b></td><td>1.45</td><td>1.72</td><td>0.089</td></tr><tr><th>M3</th><td>7</td><td><b>1.54</b></td><td>1.43</td><td>1.60</td><td>0.053</td><td>12</td><td><b>1.47</b></td><td>1.37</td><td>1.55</td><td>0.053</td><td>17</td><td><b>1.41</b></td><td>1.34</td><td>1.50</td><td>0.047</td><td>1.42</td><td>12</td><td><b>1.43</b></td><td>1.32</td><td>1.61</td><td>0.097</td></tr></tbody></table>
Table 2 in Clonal mechanisms that matter in Agave fourcroydes and A. sisalana invasions in drylands: implications for their management
<p><b>Table 2.</b> Standardized coefficients of the best-fitting Generalized Linear Mixed Models (GLMMs) explaining bulbil rooting success under the monitored conditions (natural conditions, and experimental plots). Three predictor variable types were considered (intrinsic mother plant and bulbil traits, and extrinsic bulbil traits). Species identity and plots were included as random factors. The best model was ranked according to AIC (Akaike Information Criterion) value (See also Table S5). Non-data cells indicate variables not included in a particular model.</p><table><tbody><tr><th></th><th>Intrinsic mother plant Extrinsic bulbil Extrinsic bulbil</th><th>Random factor</th></tr></tbody><tbody><tr><th>Sets of bulbils data</th><td>Intercept</td><td>traits Rosette Scape diameter height</td><td>traits Height</td><td>traits Position Buried</td><td>significance Species Plot identity</td></tr><tr><th>Monitored under natural conditions</th><td>0.936***</td><td>−0.064</td><td>0.034</td><td></td><td>0.799***</td><td>ns</td><td></td></tr><tr><th>Greenhouse plots</th><td>−3.805***</td><td></td><td></td><td>0.835***</td><td>3.427***</td><td>ns</td><td>ns</td></tr><tr><th>Natural conditions plots</th><td>−0.481***</td><td>0.124</td><td></td><td></td><td>1.897***</td><td>ns</td><td>ns</td></tr></tbody></table><p>Significance: *** <i>p-values</i> <0.001. ns: no significance</p>
Table 1 in Clonal mechanisms that matter in Agave fourcroydes and A. sisalana invasions in drylands: implications for their management
<p><b>Table 1.</b> Sampling goals, work stages and summary of data collected.</p><table><tbody><tr><th>Sampling goal</th><th>Phenology of flowering and bulbils and production of basal shoots</th><th>Estimation of bulbil production*</th><th>Estimation of shoot production from rhizomes</th><th>Estimation of rooting rates of bulbils under natural conditions</th><th>Estimation of the rooting rates of bulbils in experimental plots (greenhouse and natural conditions)*</th><th>Phenology of shoots production and rate of establishment of new individuals (rooted bulbils vs shoots from rhizomes)</th></tr></tbody><tbody><tr><th>Sampling unit</th><td>60 individuals (30 from Agave fourcroydes and 30 from | <i>A. sisalana</i>)</td><td>60 individuals (30 from Agave fourcroydes and 30 from <i>A. sisalana</i>)</td><td>8 individuals (4 from Agave fourcroydes, 4 from <i>A. sisalana</i>)</td><td>1,184 bulbils (582 from Agave fourcroydes, 602 from <i>A. sisalana</i>; 590 from early fall, 594 from late fall)</td><td>1,440 bulbils, 24 <i>from each of 60</i> individuals (30 from <i>Agave fourcroydes</i>, and 30 from <i>A. sisalana</i>)</td><td>10 plots 10 × 10 m</td></tr><tr><th>Monitored individual nature</th><td>Reproductive individuals with incipient floral scapes emerging from the rosette</td><td>Reproductive individuals with floral scapes at the stage of maximum bulbils production</td><td>Juvenile, i.e., prominent but not reproductive individuals</td><td>Mature bulbils fallen from the floral scapes</td><td>Mature bulbils fallen from the floral scapes</td><td>New young individuals</td></tr><tr><th>Traits measured</th><td>Height and</td><td>Height and</td><td>Number of</td><td>Height (cm)</td><td>Height (cm)</td><td>Origin: from</td></tr><tr><td>diameter of the rosette (cm) Height and</td><td>diameter of the rosette (cm) Height and</td><td>rhizomes Number of emerged shoots</td><td>Diameter (cm) Number of leaves</td><td>Diameter (cm) Number of leaves</td><td>rhizomes or rooted bulbils Presence of</td></tr><tr><td>diameter of the floral scape (cm)</td><td>diameter of the floral scape (cm)</td><td>from rhizomes</td><td>Number of preformed roots</td><td>Number of preformed roots</td><td>contractile roots</td></tr><tr><td>Number of scape branches</td><td>Number of bulbils by scape branches</td><td></td><td>Position (vertical or horizontal)</td><td>Rooted</td><td></td></tr><tr><td>% of branches with floral buds</td><td>Number of fallen bulbils</td><td></td><td>Buried or not</td><td></td><td></td></tr><tr><td>% of branches with flowers</td><td></td><td></td><td>Rooted</td><td></td><td></td></tr><tr><th>% of branches with bulbils</th></tr><tr><th>% of branches with fruits</th></tr><tr><th>% of branches with fallen bulbils</th></tr><tr><th>Number of basal shoots (born directly from the rosette)</th></tr><tr><th>Monitoring dates and frequency</th><td>February 2015– May 2016 (monthly)</td><td>October 2015</td><td>May–July 2015</td><td>October 2015– October 2016 (monthly)</td><td>January 2016– May 2016</td><td>February 2015– February 2016 (monthly)</td></tr></tbody></table><p>* The individuals selected for these two studies were the same.</p>
Table 2 in Assessing grass carp (Ctenopharyngodon idella) occupancy and detection probability within Lake Erie from environmental DNA
<p><b>Table 2.</b> Gene region, primer, and probe sequences used to amplify GCTM10,GCTM22, and GCTM32 for grass carp.</p><table><tbody><tr><th>Gene</th><th>Primers and Probes</th><th>Sequence</th></tr></tbody><tbody><tr><th>ND2</th><td>Forward</td><td>5′- CCYTACGTACTCGCAATTCTAC -3′</td></tr><tr><th>ND2</th><td>Reverse</td><td>5′- GTGGTGGTGTTGGGCTATTA -3′</td></tr><tr><th>ND2</th><td>Probe</td><td>5′- VIC- ACCCTAACCTTTGCTAGCTCCCAC -MGBNFQ-3′</td></tr><tr><th>COII</th><td>Forward</td><td>5′- CCGACTCCTAGAAACAGATCAC -3′</td></tr><tr><th>COII</th><td>Reverse</td><td>5′- GGGACAGCTCAGGAATGTAATA -3′</td></tr><tr><th>COII</th><td>Probe</td><td>5′- 56-FAM- CCAGTTCGT/ZEN/GTCCTAGTATCTGCCGA -3IABkFQ -3′</td></tr><tr><th>COIII</th><td>Forward</td><td>5′- CCACGGACTACACGTCATTATT -3′</td></tr><tr><th>COIII</th><td>Reverse</td><td>5′-GATGTTCGGATGTAAAGTGGTATTG -3′</td></tr><tr><th>COIII</th><td>Probe</td><td>5′-NED- TTCCTAGCTGTTTGCCTTCTCCGT -MGBNFQ-3′</td></tr></tbody></table>
Table 1 in Catching carp: a review of bigheaded carp capture strategies
<p><b>Table 1.</b> Summary of active and passive sampling gears and attributes used to capture bigheaded carp (<i>Hypophthalmichthys</i> spp.) across larval, juvenile, and adult life stages.</p><table><tbody><tr><th>Approach</th><th>Gear</th><th>Life stage</th><th>Units</th><th>Gear attributes</th></tr></tbody><tbody><tr><th>Active</th><td>Push net</td><td>Eggs, Larvae</td><td>density</td><td>Single or dual conical nets, 0.5 m diameter, 2.0 m long, 0.8 mm mesh</td></tr><tr><td>Nueston net</td><td>Eggs, Larvae</td><td>density</td><td>1 × 2 m, 500 µm mesh</td></tr><tr><td>Surface plankton net</td><td>Eggs, Larvae</td><td>density</td><td>0.5 diameter opening, 2-m length, 500 µm mesh</td></tr><tr><td>Bongo net</td><td>Eggs, Larvae</td><td>density</td><td>0.6 cm diameter opening, 333 µm mesh</td></tr><tr><td>Cast net</td><td>Juvenile</td><td>per cast</td><td>2.7 m diameter; 10 mm mesh</td></tr><tr><td>Seine–Beach</td><td>Juvenile</td><td>per haul</td><td>10 m length, 3–5 mm mesh</td></tr><tr><td>Seine–Purse</td><td>Juvenile</td><td>per haul</td><td>122 × 3.05 m, with 2.5 cm mesh</td></tr><tr><td>Seine–Contracted</td><td>Juvenile, Adult</td><td>per haul</td><td>Varying set lengths; mesh size range 1.6–5.1 cm</td></tr><tr><td>Trawl–Paupier</td><td>Juvenile, Adult</td><td>CPUE</td><td>Standard amperage adjusted to conductivity, 30 Hz, 15%, 2–4 × 1.5 m frame, 38 mm stretched body mesh to 6 mm mesh cod</td></tr><tr><td>Trawl–Electrified</td><td>Juvenile, Adult</td><td>CPUE</td><td>Amperage adjusted to conductivity, 30 Hz, 15%, 2.13 × 0.9 m frame, 38 mm stretched body mesh to 6 mm mesh cod</td></tr><tr><td>Trawl–Dozer</td><td>Juvenile, Adult</td><td>CPUE</td><td>Two seam; 4.8 m wide × 4.5 m long with 18 mm stretch mesh. Bag 1.8 m; Mesh, 3 mm</td></tr><tr><td>Electrofishing–AC</td><td>Juvenile, Adult</td><td>CPUE</td><td>3-phase, 3 Kw, 230-V, 60 hz; 100–250 V, 3–10 amps, 60–120 hz, 25% Duty cycle, 60–80 pulses/s</td></tr><tr><td>Electrofishing–DC</td><td>Juvenile, Adult</td><td>CPUE</td><td>180–1000 V, 15–60 Hz, 25–50% duty cycle</td></tr><tr><td>Hydroacoustic</td><td>Adult</td><td>density</td><td>Two horizontal-orientated split-beam transducers, 5 pings/s, pulse duration of 0.40 ms, 70 kHz (5 beam angle)–200 kHz (6.6 beam angle)</td></tr><tr><td>Trammel net–Driven</td><td>Adult</td><td>CPUE</td><td>Height, 1.8–3.6 m; Inner panel, 2.5–7.6 cm; Outer panel, 20–34 cm, varying set lengths</td></tr><tr><td>Gill net–Driven</td><td>Adult</td><td>CPUE</td><td>Height, 1.8–3.6 m; Mesh size range:2.54–25.4 cm; Varying set lengths</td></tr><tr><th>Passive</th><td>Drift net</td><td>Eggs, Larvae</td><td>density</td><td>0.5 diameter opening, 2-m length, 750 µm mesh, 1-m below surface water</td></tr><tr><td>Bongo net</td><td>Eggs, Larvae</td><td>density</td><td>0.6 cm diameter opening, 333 µm mesh</td></tr><tr><td>Light traps</td><td>Larvae</td><td>trap night</td><td>Cloverleaf array; 25.0 cm tall with 5.0 mm entry slots. Collection pan with 6 holes cover by 250 µm mesh</td></tr><tr><td>Minnow trap</td><td>Larvae, juvenile</td><td>net night</td><td>Trap dimensions, 42 × 19 × 22 cm, baited</td></tr><tr><td>Mini fyke net</td><td>Juvenile</td><td>net night</td><td>4.5 × 0.6 m lead, 0.6 × 1.2 m trap 3 mm mesh; some tandem sets</td></tr><tr><td>Hoop net</td><td>Adult</td><td>net night</td><td>Diameter, 0.6–1.8 m; Mesh range, 3.8–10 cm; Some tandem sets</td></tr><tr><td>Stop log net</td><td>Adult</td><td>net night</td><td>25 × 25 cm wood frames; 0.9 m hoops; 1.9 cm mesh</td></tr><tr><td>Fyke net</td><td>Adult</td><td>net night</td><td>0.9 m × 1.8 m frame with 15.2 m × 1.4 m lead, 1.8 to 3.8 cm bar mesh</td></tr><tr><td>Pound net</td><td>Adult</td><td>net night</td><td>Trap dimensions, 6.1 × 3.1 × 3.1 m; 100 m lead and wings</td></tr><tr><td>Trammel net</td><td>Adult</td><td>CPUE</td><td>Height, 1.8–3.6 m; Inner panel, 2.5–7.6 cm; Outer panel, 20–34 cm, varying set lengths</td></tr><tr><td>Gill net</td><td>Adult</td><td>CPUE</td><td>Height, 1.8–3.6 m; Mesh size range: 2.54–25.4 cm; Varying set lengths</td></tr></tbody></table>
Table 2 in Risk screening of non-native freshwater fishes in Yunnan Province, China
<p><b>Table 2.</b> Non-native freshwater fish species assessed with the Aquatic Species Invasiveness Screening Kit (AS-ISK) for Yunnan Province</p><table><tbody><tr><th>Species name</th><th>A priori categorisation</th><th>Screening component</th><th></th><th>Confidence</th></tr><tr><th>BRA</th><th>BRA+CCA</th><th></th><th>CL</th><th>CF</th></tr><tr><th>Score</th><th>Outcome</th><th>Score</th><th>Outcome</th><th>Delta</th><th>Total</th><th>BRA</th><th>CCA</th><th>Total</th><th>BRA</th><th>CCA</th></tr></tbody><tbody><tr><th><i>Acheilognathus chankaensis</i></th><td>N</td><td>10</td><td>Medium</td><td>8</td><td>Medium</td><td>−2</td><td>3.4</td><td>3.4</td><td>3.5</td><td>0.85</td><td>0.85</td><td>0.88</td></tr><tr><th><i>Acheilognathus macropterus</i></th><td>N</td><td>−2</td><td>Low</td><td>−4</td><td>Low</td><td>−2</td><td>3.3</td><td>3.3</td><td>3.2</td><td>0.81</td><td>0.82</td><td>0.79</td></tr><tr><th><i>Acipenser baerii</i></th><td>Y</td><td>26</td><td>High</td><td>32</td><td>High</td><td>6</td><td>3.0</td><td>3.0</td><td>2.8</td><td>0.74</td><td>0.74</td><td>0.71</td></tr><tr><th><i>Ameiurus nebulosus</i></th><td>Y</td><td>29</td><td>High</td><td>35</td><td>High</td><td>6</td><td>3.0</td><td>3.0</td><td>2.8</td><td>0.75</td><td>0.76</td><td>0.71</td></tr><tr><th><i>Anguilla anguilla</i></th><td>N</td><td>0</td><td>Low</td><td>−2</td><td>Low</td><td>−2</td><td>3.0</td><td>3.0</td><td>3.0</td><td>0.77</td><td>0.77</td><td>0.75</td></tr><tr><th><i>Anguilla japonica</i></th><td>N</td><td>−2</td><td>Low</td><td>−4</td><td>Low</td><td>−2</td><td>3.1</td><td>3.2</td><td>3.0</td><td>0.79</td><td>0.80</td><td>0.75</td></tr><tr><th><i>Carassius cuvieri</i></th><td>Y</td><td>24</td><td>High</td><td>28</td><td>High</td><td>4</td><td>3.1</td><td>3.1</td><td>2.8</td><td>0.78</td><td>0.79</td><td>0.71</td></tr><tr><th><i>Clarias gariepinus</i></th><td>Y</td><td>39.5</td><td>High</td><td>47.5</td><td>High</td><td>8</td><td>3.1</td><td>3.1</td><td>2.8</td><td>0.77</td><td>0.78</td><td>0.71</td></tr><tr><th><i>Ctenopharyngodon idella</i></th><td>Y</td><td>29.5</td><td>High</td><td>33.5</td><td>High</td><td>4</td><td>3.3</td><td>3.3</td><td>3.2</td><td>0.83</td><td>0.84</td><td>0.79</td></tr><tr><th><i>Cultrichthys erythropterus</i></th><td>N</td><td>22.5</td><td>High</td><td>24.5</td><td>High</td><td>2</td><td>3.2</td><td>3.3</td><td>3.0</td><td>0.81</td><td>0.82</td><td>0.75</td></tr><tr><th><i>Gambusia affinis</i></th><td>Y</td><td>39</td><td>High</td><td>41</td><td>High</td><td>2</td><td>3.1</td><td>3.1</td><td>3.0</td><td>0.78</td><td>0.78</td><td>0.75</td></tr><tr><th><i>Hypomesus olidus</i></th><td>N</td><td>16</td><td>Medium</td><td>16</td><td>Medium</td><td>0</td><td>3.2</td><td>3.2</td><td>3.0</td><td>0.79</td><td>0.80</td><td>0.75</td></tr><tr><th><i>Hypophthalmichthys molitrix</i></th><td>Y</td><td>24</td><td>High</td><td>30</td><td>High</td><td>6</td><td>3.3</td><td>3.3</td><td>3.0</td><td>0.83</td><td>0.84</td><td>0.75</td></tr><tr><th><i>Hypophthalmichthys nobilis</i></th><td>Y</td><td>26</td><td>High</td><td>32</td><td>High</td><td>6</td><td>3.3</td><td>3.4</td><td>3.0</td><td>0.84</td><td>0.85</td><td>0.75</td></tr><tr><th><i>Hyporhamphus intermedius</i></th><td>N</td><td>7</td><td>Medium</td><td>7</td><td>Medium</td><td>0</td><td>3.2</td><td>3.2</td><td>3.0</td><td>0.80</td><td>0.80</td><td>0.75</td></tr><tr><th><i>Hypostomus plecostomus</i></th><td>Y</td><td>51</td><td>High</td><td>59</td><td>High</td><td>8</td><td>3.0</td><td>3.0</td><td>3.0</td><td>0.75</td><td>0.74</td><td>0.75</td></tr><tr><th><i>Ictalurus punctatus</i></th><td>Y</td><td>36.5</td><td>High</td><td>42.5</td><td>High</td><td>6</td><td>3.0</td><td>3.0</td><td>2.7</td><td>0.75</td><td>0.76</td><td>0.67</td></tr><tr><th><i>Labeo rohita</i></th><td>N</td><td>10</td><td>Medium</td><td>14</td><td>Medium</td><td>4</td><td>3.1</td><td>3.2</td><td>3.0</td><td>0.79</td><td>0.79</td><td>0.75</td></tr><tr><th><i>Megalobrama amblycephala</i></th><td>N</td><td>10</td><td>Medium</td><td>10</td><td>Medium</td><td>0</td><td>3.4</td><td>3.4</td><td>3.3</td><td>0.84</td><td>0.84</td><td>0.83</td></tr><tr><th><i>Micropterus salmoides</i></th><td>Y</td><td>35</td><td>High</td><td>43</td><td>High</td><td>8</td><td>3.1</td><td>3.2</td><td>2.5</td><td>0.79</td><td>0.81</td><td>0.63</td></tr><tr><th><i>Mylopharyngodon piceus</i></th><td>Y</td><td>29</td><td>High</td><td>35</td><td>High</td><td>6</td><td>3.3</td><td>3.3</td><td>3.0</td><td>0.82</td><td>0.83</td><td>0.75</td></tr><tr><th><i>Neosalanx taihuensis</i></th><td>N</td><td>24.5</td><td>High</td><td>22.5</td><td>High</td><td>−2</td><td>3.4</td><td>3.4</td><td>3.0</td><td>0.85</td><td>0.86</td><td>0.75</td></tr><tr><th><i>Oncorhynchus mykiss</i></th><td>Y</td><td>29</td><td>High</td><td>37</td><td>High</td><td>8</td><td>3.0</td><td>3.0</td><td>2.8</td><td>0.75</td><td>0.75</td><td>0.71</td></tr><tr><th><i>Oreochromis aureus</i></th><td>Y</td><td>49</td><td>High</td><td>61</td><td>High</td><td>12</td><td>3.1</td><td>3.1</td><td>2.7</td><td>0.77</td><td>0.78</td><td>0.67</td></tr><tr><th><i>Oreochromis mossambicus</i></th><td>Y</td><td>44.5</td><td>High</td><td>56.5</td><td>High</td><td>12</td><td>2.9</td><td>3.0</td><td>2.8</td><td>0.75</td><td>0.75</td><td>0.71</td></tr><tr><th><i>Oreochromis niloticus</i></th><td>Y</td><td>47</td><td>High</td><td>59</td><td>High</td><td>12</td><td>2.9</td><td>3.0</td><td>2.5</td><td>0.74</td><td>0.75</td><td>0.63</td></tr><tr><th><i>Parabramis pekinensis</i></th><td>N</td><td>5.5</td><td>Medium</td><td>3.5</td><td>Medium</td><td>−2</td><td>3.3</td><td>3.3</td><td>3.0</td><td>0.81</td><td>0.82</td><td>0.75</td></tr><tr><th><i>Paramisgurnus dabryanus</i></th><td>N</td><td>13.5</td><td>Medium</td><td>17.5</td><td>High</td><td>4</td><td>3.2</td><td>3.2</td><td>3.0</td><td>0.80</td><td>0.80</td><td>0.75</td></tr><tr><th><i>Piaractus brachypomus</i></th><td>Y</td><td>8</td><td>Medium</td><td>12</td><td>Medium</td><td>4</td><td>3.1</td><td>3.1</td><td>3.0</td><td>0.77</td><td>0.77</td><td>0.75</td></tr><tr><th><i>Prochilodus lineatus</i></th><td>N</td><td>11</td><td>Medium</td><td>17</td><td>Medium</td><td>6</td><td>3.1</td><td>3.1</td><td>3.0</td><td>0.76</td><td>0.77</td><td>0.75</td></tr><tr><th><i>Protosalanx hyalocranius</i></th><td>N</td><td>14.5</td><td>Medium</td><td>12.5</td><td>Medium</td><td>−2</td><td>3.1</td><td>3.1</td><td>2.8</td><td>0.76</td><td>0.77</td><td>0.71</td></tr><tr><th><i>Rhinogobius cliffordpopei</i></th><td>Y</td><td>37</td><td>High</td><td>43</td><td>High</td><td>6</td><td>3.1</td><td>3.1</td><td>2.8</td><td>0.76</td><td>0.77</td><td>0.71</td></tr><tr><th><i>Salmo trutta</i></th><td>Y</td><td>18</td><td>High</td><td>12</td><td>Medium</td><td>−6</td><td>2.9</td><td>2.9</td><td>3.0</td><td>0.73</td><td>0.72</td><td>0.75</td></tr><tr><th><i>Sarcocheilichthys nigripinnis</i></th><td>N</td><td>3</td><td>Medium</td><td>3</td><td>Medium</td><td>0</td><td>3.5</td><td>3.5</td><td>3.2</td><td>0.86</td><td>0.87</td><td>0.79</td></tr><tr><th><i>Siniperca chuatsi</i></th><td>N</td><td>14.5</td><td>Medium</td><td>18.5</td><td>High</td><td>4</td><td>3.0</td><td>3.0</td><td>2.8</td><td>0.74</td><td>0.74</td><td>0.71</td></tr><tr><th><i>Tinca tinca</i></th><td>Y</td><td>21</td><td>High</td><td>27</td><td>High</td><td>6</td><td>3.1</td><td>3.1</td><td>3.0</td><td>0.77</td><td>0.77</td><td>0.75</td></tr><tr><th><i>Toxabramis swinhonis</i></th><td>N</td><td>16.5</td><td>Medium</td><td>16.5</td><td>Medium</td><td>0</td><td>3.3</td><td>3.4</td><td>3.2</td><td>0.84</td><td>0.84</td><td>0.79</td></tr><tr><th>A priori categorisation (N: non-invasive; Y: invasive); Screening component (BRA: Basic Risk Assessment, BRA+CCA: BRA+ Climate Change Assessment, Delta: BRA+CCA score minus BRA score); Confidence (CL: confidence level, CF: confidence factor); Outcome (Low: score <1, Medium: 1 ≤ score <17.25, High: score ≥ 17.25)</th></tr></tbody></table>
Table 1 in Prevalence and new genotypes of Enterocytozoon bieneusi in sheltered dogs and cats in Sichuan province, southwestern China
<p><b>Table 1.</b> Prevalence and genotypes of <i>E. bieneusi</i> in sheltered dogs from different cities and sources in Sichuan province, southwestern China.</p><table><tbody><tr><th>City</th><th>Source</th><th>No. examined</th><th>No. positive</th><th>Prevalence (%)</th><th>OR (95% CI)</th><th><i>p-</i> value</th><th>Genotypes (<i>n</i>)</th></tr></tbody><tbody><tr><th></th><td></td><td></td><td></td><td>(95% CI)</td><td></td><td></td><td></td></tr><tr><th>Chengdu</th><td>Shuangliu</td><td>158</td><td>16</td><td>10.1% (5.4–14.8)</td><td>Reference</td><td></td><td>CD9 (8); PtEb IX (7); SCD-1 (1)</td></tr><tr><th></th><td>Wenjiang</td><td>250</td><td>80</td><td>32.0% (26.2–37.8)</td><td>4.176</td><td>0.000</td><td>CD9 (79); PtEb IX (1)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>(2.336–7.468)</td><td></td><td></td></tr><tr><th>Ya’ an</th><td>Yucheng</td><td>228</td><td>36</td><td>15.8% (11.1–20.5)</td><td>1.664</td><td>0.112</td><td>CD9 (4); PtEb IX (32)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>(0.888–3.117)</td><td></td><td></td></tr><tr><th>Panzhihua</th><td>Dongqu</td><td>44</td><td>2</td><td>4.5% (<i>—</i> 1.6–10.7)</td><td>0.423</td><td>0.264</td><td>CD9 (1); PtEb IX (1)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>(0.093–1.913)</td><td></td><td></td></tr><tr><th>Guangyuan</th><td>Lizhou</td><td>44</td><td>2</td><td>4.5% (<i>—</i> 1.6–10.7)</td><td>0.423</td><td>0.264</td><td>Type IV (1); SCD-2 (1)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>(0.093–1.913)</td><td></td><td></td></tr><tr><th>Total</th><td></td><td>724</td><td>136</td><td>18.8% (15.9–21.6)</td><td></td><td></td><td>CD9 (92); PtEb IX (41);</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>Type IV (1); SCD-1 (1); SCD-2 (1)</td></tr></tbody></table>
Table 2 in Prevalence and new genotypes of Enterocytozoon bieneusi in sheltered dogs and cats in Sichuan province, southwestern China
<p><b>Table 2.</b> Prevalence and genotypes of <i>E. bieneusi</i> in sheltered cats from different cities and sources in Sichuan province, southwestern China.</p><table><tbody><tr><th>City</th><th>Source</th><th>No. examined</th><th>No. positive</th><th>Prevalence</th><th>OR (95% CI)</th><th><i>p-</i> value</th><th>Genotypes (<i>n</i>)</th></tr></tbody><tbody><tr><th></th><td></td><td></td><td></td><td>(%) (95% CI)</td><td></td><td></td><td></td></tr><tr><th>Chengdu</th><td>Shuangliu</td><td>85</td><td>13</td><td>15.3% (7.6–22.9)</td><td>Reference</td><td></td><td>CD9 (10); D (2); PtEb IX (1)</td></tr><tr><th>Ya’ an</th><td>Yucheng</td><td>23</td><td>3</td><td>13.0% (<i>—</i> 0.7–26.8)</td><td>0.831 (0.215–3.203)</td><td>0.788</td><td>CD9 (1); D (2)</td></tr><tr><th>Panzhihua</th><td>Dongqu</td><td>48</td><td>6</td><td>12.5% (3.1–21.9)</td><td>0.791 (0.280–2.237)</td><td>0.791</td><td>Type IV (6)</td></tr><tr><th>Total</th><td></td><td>156</td><td>22</td><td>14.1% (8.6–19.6)</td><td></td><td></td><td>CD9 (11); Type IV (6);</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>D (4); PtEb IX (1)</td></tr></tbody></table>
Table 2 in Leishmaniasis and phlebotomine sand flies in Oman Sultanate
<p><b>Table 2.</b> Captures made using sticky traps in locations mentioned in Figures 1 and 2. ³ = males, ♀ = females, ³ + ♀ = males and females, s/m 2 = density of sandflies (per m 2 of sticky paper).</p><table><tbody><tr><th>Location</th><th></th><th>Sharqiyah</th><th></th><th></th><th></th><th>Dh2</th><th></th><th></th><th></th><th>Dh3</th><th></th><th></th><th></th><th>Dh5</th><th></th><th></th><th>Dh6</th><th></th><th>Total Dhofar</th></tr></tbody><tbody><tr><th>Species</th><td>³</td><td>♀</td><td>³ + ♀</td><td>s/m2</td><td>³</td><td>♀</td><td>³ + ♀ s/m2</td><td>³</td><td>♀</td><td>³ + ♀</td><td>s/m2</td><td>³</td><td>♀</td><td>³ + ♀</td><td>s/m2</td><td>³</td><td>♀</td><td>³ + ♀</td><td>s/m2</td><td>³</td><td>♀</td><td>³ + ♀ s/m2</td></tr><tr><th><i>Phlebotomus</i></th><td>35</td><td>14</td><td>49</td><td>1.16</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><td></td></tr><tr><th><i>papatasi</i></th></tr><tr><th><i>Phlebotomus</i></th><td>2</td><td>2</td><td>4</td><td>0.09</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>45</td><td>4</td><td>49</td><td>0.84</td><td>45</td><td>4</td><td>49</td><td>2.13</td></tr><tr><th><i>bergeroti</i></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></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><i>Phlebotomus</i></th><td></td><td>2</td><td>2</td><td>0.05</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><td></td></tr><tr><th><i>duboscqi</i></th></tr><tr><th><i>Phlebotomus</i></th><td>3</td><td></td><td>3</td><td>0.07</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>31</td><td>4</td><td>35</td><td>0.60</td><td>31</td><td>4</td><td>35</td><td>1.52</td></tr><tr><th><i>alexandri</i></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></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><i>Phlebotomus</i></th><td></td><td></td><td></td><td></td><td>4</td><td></td><td>4</td><td>1.43</td><td></td><td>4</td><td>4</td><td>0.51</td><td>2</td><td></td><td>2</td><td>0.42</td><td>1</td><td>1</td><td>2</td><td>0.03</td><td>7</td><td>5</td><td>12</td><td>0.52</td></tr><tr><th><i>saevus</i></th></tr><tr><th><i>Phlebotomus</i></th><td>8</td><td></td><td>8</td><td>0.19</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>7</td><td>3</td><td>10</td><td>0.17</td><td>7</td><td>3</td><td>10</td><td>0.43</td></tr><tr><th><i>sergenti</i></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></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><i>Grassomyia</i></th><td></td><td>2</td><td>2</td><td>0.05</td><td></td><td>1</td><td>1</td><td>0.36</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>1</td><td>1</td><td>0.04</td></tr><tr><th><i>dreyfussi</i></th></tr><tr><th><i>Sergentomyia</i></th><td>4</td><td>4</td><td>8</td><td>0.19</td><td>27</td><td>30</td><td>57</td><td>20.36</td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td>22</td><td>50</td><td>72</td><td>1.23</td><td>49</td><td>80</td><td>129</td><td>5.60</td></tr><tr><th><i>fallax</i></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></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><i>Sergentomyia</i></th><td>29</td><td>9</td><td>38</td><td>0.90</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>5</td><td>2</td><td>7</td><td>0.12</td><td>5</td><td>2</td><td>7</td><td>0.30</td></tr><tr><th><i>cincta</i></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></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><i>Sergentomyia</i></th><td>67</td><td>39</td><td>106</td><td>2.51</td><td>1</td><td>8</td><td>9</td><td>3.21</td><td></td><td>3</td><td>3</td><td>0.38</td><td></td><td></td><td></td><td></td><td>8</td><td>6</td><td>14</td><td>0.24</td><td>9</td><td>17</td><td>26</td><td>1.13</td></tr><tr><th><i>christophersi</i></th></tr><tr><th><i>Sergentomyia</i></th><td>5</td><td>4</td><td>9</td><td>0.21</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><td></td></tr><tr><th><i>clydei</i></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></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><i>Sergentomyia</i></th><td>50</td><td>21</td><td>71</td><td>1.68</td><td>2</td><td>8</td><td>10</td><td>3.57</td><td>1</td><td>6</td><td>7</td><td>0.89</td><td>1</td><td></td><td>1</td><td>0.21</td><td>52</td><td>26</td><td>78</td><td>1.34</td><td>56</td><td>40</td><td>96</td><td>4.17</td></tr><tr><th><i>tiberiadis</i></th></tr><tr><th><i>Sergentomyia</i></th></tr><tr><th><i>africana</i></th></tr><tr><th><i>Sergentomyia</i></th><td>13</td><td>12</td><td>25</td><td>0.59</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><td></td></tr><tr><th><i>baghdadis</i></th></tr><tr><th><i>Sergentomyia</i></th><td>1</td><td>2</td><td>3</td><td>0.07</td><td>1</td><td></td><td>1</td><td>0.36</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>1</td><td></td><td>1</td><td>0.04</td></tr><tr><th><i>(Sintonius) sp.</i></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></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th>Undetermined</th><td>3</td><td></td><td>3</td><td>0.07</td><td>1</td><td></td><td>1</td><td>0.36</td><td></td><td>1</td><td>1</td><td>0.13</td><td></td><td></td><td></td><td></td><td>4</td><td>4</td><td>8</td><td>0.14</td><td>5</td><td>5</td><td>10</td><td>0.43</td></tr><tr><th>Total</th><td>220</td><td>111</td><td>331</td><td>7.85</td><td>36</td><td>47</td><td>83</td><td>29.64</td><td>1</td><td>14</td><td>15</td><td>1.91</td><td>3</td><td>0</td><td>3</td><td>0.63</td><td>175</td><td>100 275</td><td>4.71</td><td>215 161</td><td>376 16.32</td></tr></tbody></table>
Table 1 in Molecular characterization and protective efficacy of a new conserved hypothetical protein of Eimeria tenella
<p><b>Table 1.</b> Protective effect of r <i>Et</i> CHP protein on <i>E. tenella</i> infection.</p><table><tbody><tr><th>Group</th><th>Average body</th><th>Mean lesion scores</th><th>Oocyst shedding</th><th>Percentage reduction</th></tr></tbody><tbody><tr><th></th><td>weight gains (g)</td><td></td><td>per bird (<i>×</i> 10 7)</td><td>of oocyst excretion (%)</td></tr><tr><th>Unchallenged control</th><td>258.62 ± 70.26c</td><td>0.00 ± 0.00a</td><td>0.00 ± 0.00a</td><td>100d</td></tr><tr><th>Challenged control</th><td>180.87 ± 45.38a</td><td>3.20 ± 0.83c</td><td>4.43 ± 0.99c</td><td>0.00a</td></tr><tr><th>r <i>Et</i> CHP-50 <b>μ</b> g</th><td>226.25 ± 24.47b</td><td>1.75 ± 0.95b</td><td>2.10 ± 0.88b</td><td>54.07 ± 11.76c</td></tr><tr><th>r <i>Et</i> CHP-100 <b>μ</b> g</th><td>235.25 ± 23.44bc</td><td>1.20 ± 0.44b</td><td>3.26 ± 2.47bc</td><td>31.99 ± 29.35b</td></tr></tbody></table><p><sup>a–d</sup> Values with different letters in the same column are significantly different (<i>P</i> <0.05) according to the ANOVA Duncan test.</p>
Table 2 in Morphological updates and molecular description of Heterosentis holospinus Amin, Heckmann, & Ha, 2011 (Acanthocephala, Arhythmacanthidae) in the Pacific Ocean off Vietnam
<p><b>Table 2.</b> Chemical composition of Gallium (LMIS) cut hooks of <i>Heterosentis holospinus</i>.*</p><table><tbody><tr><th></th><th></th><th>Cross section cuts</th><th></th><th>Longitudinal cuts**</th></tr></tbody><tbody><tr><th></th><td>Tip cuts</td><td>Mid cut</td><td></td><td></td><td></td></tr><tr><th>Element</th><td>Edge***</td><td>Edge</td><td>Center</td><td>Arch***</td><td>Base</td></tr><tr><th>Sodium (Na)</th><td><b>0.28</b></td><td>0.13</td><td>0.43</td><td><b>0.04</b></td><td>0.14</td></tr><tr><th>Magnesium (Mg)</th><td><b>0.07</b></td><td>0.21</td><td>0.77</td><td><b>0.45</b></td><td>0.07</td></tr><tr><th>Phosphorous (P)</th><td><b>5.76</b></td><td>10.30</td><td>16.92</td><td><b>18.79</b></td><td>20.76</td></tr><tr><th>Sulfur (S)</th><td><b>25.57</b></td><td>28.15</td><td>4.41</td><td><b>1.14</b></td><td>1.06</td></tr><tr><th>Potassium (K)</th><td><b>0.00</b></td><td>0.00</td><td>0.05</td><td><b>0.33</b></td><td>0.48</td></tr><tr><th>Calcium (Ca)</th><td><b>12.91</b></td><td>18.70</td><td>40.41</td><td><b>48.66</b></td><td>60.53</td></tr></tbody></table><p><sup>*</sup> Listed in WT%. Common protoplasm (C, O, N) elements and processing elements (Au, Pd, Ga) are omitted from the table.</p><p><sup>**</sup> We also checked the longitudinal cuts for chlorine (Cl). The worm had low levels (0.11 and 0.09) of the ion which are NOT reliable. <sup>***</sup> Bolded figures are used to generate the corresponding spectra (Figs. 7, 8).</p>
Table 3 in New species and new records of camallanid nematodes (Nematoda, Camallanidae) from marine fishes and sea snakes in New Caledonia
<p><b>Table 3.</b> Comparison of measurements of <i>Camallanus carangis</i> four-stage larvae from fish and reptilian hosts in New Caledonia.</p><table><tbody><tr><th>Host <i>Parupeneus</i></th><th><i>Chirocentrus</i></th><th><i>Laticauda</i></th></tr></tbody><tbody><tr><th></th><td><i>indicus</i></td><td><i>dorab</i></td><td><i>saintgironsi *</i></td></tr><tr><th>No. of specimens</th><td>1</td><td>1</td><td>1</td></tr><tr><th>Body length (in mm)</th><td>3.13</td><td>4.12</td><td>1.31</td></tr><tr><th>Body width</th><td>136</td><td>109</td><td>122</td></tr><tr><th>Buccal capsule – length</th><td>84</td><td>105</td><td>102</td></tr><tr><th>Buccal capsule – width</th><td>69</td><td>69</td><td>90</td></tr><tr><th>No. of ridges</th><td>17</td><td>?</td><td>18</td></tr><tr><th>Basal ring – length</th><td>12</td><td>21</td><td>24</td></tr><tr><th>Basal ring – width</th><td>51</td><td>51</td><td>54</td></tr><tr><th>Length of prongs</th><td>78</td><td>123</td><td>117</td></tr><tr><th>Oesoph. cup – length</th><td>18</td><td>24</td><td>18</td></tr><tr><th>Oesoph. cup – width</th><td>21</td><td>21</td><td>21</td></tr><tr><th>Musc. oesoph. – length</th><td>435</td><td>571</td><td>517</td></tr><tr><th>Musc. oesoph. – width</th><td>63</td><td>60</td><td>45</td></tr><tr><th>Gland. oesoph. – length</th><td>394</td><td>490</td><td>435</td></tr><tr><th>Gland. oesoph. – width</th><td>72</td><td>60</td><td>45</td></tr><tr><th>Musc./gland. oesoph.</th><td>1:091</td><td>1:0.86</td><td>1:0.84</td></tr><tr><th>length ratio</th><td></td><td></td><td></td></tr><tr><th>% of buc. c. and</th><td>2</td><td>28</td><td>81</td></tr><tr><th>oesoph. of body</th><td></td><td></td><td></td></tr><tr><th>Tail</th><td>72</td><td>147</td><td>54</td></tr></tbody></table><p><sup>*</sup> Sea-snake (Reptilia).</p>
Table 2 in New species and new records of camallanid nematodes (Nematoda, Camallanidae) from marine fishes and sea snakes in New Caledonia
<p><b>Table 2.</b> Comparison of measurements of <i>Camallanus carangis</i> females from marine fishes in New Caledonia.</p><table><tbody><tr><th>Host</th><th><i>Atule</i></th><th><i>Carangoides</i></th><th><i>Selar</i></th><th><i>Parupeneus</i></th><th><i>Pristipomoides</i></th><th><i>Epinephelus</i></th></tr></tbody><tbody><tr><th></th><td><i>mate</i></td><td><i>dinema</i></td><td><i>crumenophthalmus</i></td><td><i>cyclostomus</i></td><td><i>filamentosus</i></td><td><i>retouti</i></td></tr><tr><th>No. of specimens 1 (grav.)</th><td>2 (subgr.)</td><td>3 (gr., subgr.)</td><td>2 (subgr.)</td><td>1 (subgr.)</td><td>1 (subgr.)</td></tr><tr><th>Body length (in mm)</th><td>14.93</td><td>4.75 –7.00</td><td>14.63–17.00</td><td>10.23–11.13</td><td>14.89</td><td>10.95</td></tr><tr><th>Body width</th><td>340</td><td>163–245</td><td>381–517</td><td>340–408</td><td>313</td><td>354</td></tr><tr><th>Buccal capsule – length</th><td>195</td><td>159–180</td><td>186–225</td><td>159</td><td>150</td><td>183</td></tr><tr><th>Buccal capsule – width</th><td>198</td><td>144–180</td><td>204–233</td><td>144</td><td>159</td><td>195</td></tr><tr><th>No. of ridges</th><td>32</td><td>37–40</td><td>35–50</td><td>?</td><td>32</td><td>44</td></tr><tr><th>Basal ring – length</th><td>30</td><td>27</td><td>24–36</td><td>21–24</td><td>24</td><td>30</td></tr><tr><th>Basal ring – width</th><td>111</td><td>96</td><td>108–117</td><td>96–99</td><td>90</td><td>108</td></tr><tr><th>Length of tridents</th><td>141</td><td>135</td><td>195–240</td><td>105–195</td><td>141</td><td>153</td></tr><tr><th>Oesoph. cup – length</th><td>27</td><td>24–30</td><td>30–39</td><td>33</td><td>15</td><td>36</td></tr><tr><th>Oesoph. cup – width</th><td>36</td><td>30–36</td><td>39–45</td><td>36</td><td>33</td><td>30</td></tr><tr><th>Musc. oesoph. – length</th><td>1550</td><td>721–1047</td><td>1333–1850</td><td>816–979</td><td>911</td><td>1469</td></tr><tr><th>Musc. oesoph. – width</th><td>136</td><td>90</td><td>123–177</td><td>122–136</td><td>163</td><td>122</td></tr><tr><th>Gland. oesoph. – length</th><td>1333</td><td>653–911</td><td>1156–1659</td><td>775–925</td><td>993</td><td>1156</td></tr><tr><th>Gland. oesoph. – width</th><td>136</td><td>96–99</td><td>114–190</td><td>122–163</td><td>163</td><td>136</td></tr><tr><th>Musc./gland. oesoph.</th><td>1:0.86</td><td>1:0.87–0.91</td><td>1:0.87–0.98</td><td>1:0.94–0.95</td><td>1:1.09</td><td>1:0.79</td></tr><tr><th>length ratio</th></tr><tr><th>% of buc. c. and oesoph.</th><td>21</td><td>22–40</td><td>18–25</td><td>17–19</td><td>14</td><td>26</td></tr><tr><th>of body</th></tr><tr><th>Excretory pore</th><td>1401</td><td>707–911</td><td>1591</td><td>?</td><td>?</td><td>1224</td></tr><tr><th>Vulva from ant. end (in</th><td>7.51</td><td>2.56–3.93</td><td>7.13–8.80</td><td>4.92</td><td>7.00</td><td>5.74</td></tr><tr><th>mm)</th></tr><tr><th>% of vulva of body</th><td>50</td><td>54–56</td><td>49–55</td><td>48</td><td>47</td><td>52</td></tr><tr><th>Tail</th><td>272</td><td>90–136</td><td>225</td><td>144–147</td><td>177</td><td>190</td></tr></tbody></table>
Table 1 in New species and new records of camallanid nematodes (Nematoda, Camallanidae) from marine fishes and sea snakes in New Caledonia
<p><b>Table 1.</b> Comparison of measurements of <i>Camallanus carangis</i> males from marine fishes in New Caledonia.</p><table><tbody><tr><th>Host</th><th><i>Atule mate</i></th><th><i>Carangoides fulvoguttatus</i></th><th><i>Cephalopholis sonnerati</i></th><th><i>Epinephelus retouti</i></th></tr></tbody><tbody><tr><th>No. of specimens</th><td>2</td><td>1</td><td>3</td><td>1</td></tr><tr><th>Body length (in mm)</th><td>12.17–13.67</td><td>6.90</td><td>9.93–11.32</td><td>frag. 5.40</td></tr><tr><th>Body width</th><td>299–354</td><td>218</td><td>258–326</td><td>258</td></tr><tr><th>Buccal capsule – length</th><td>165–189</td><td>162</td><td>183–186</td><td>159</td></tr><tr><th>Buccal capsule – width</th><td>159–189</td><td>156</td><td>156–183</td><td>165</td></tr><tr><th>No. of ridges</th><td>33–35</td><td>38</td><td>34–35</td><td>40</td></tr><tr><th>Basal ring – length</th><td>21–24</td><td>27</td><td>27–33</td><td>27</td></tr><tr><th>Basal ring – width</th><td>90–105</td><td>90</td><td>96–102</td><td>93</td></tr><tr><th>Length of tridents</th><td>150</td><td>150</td><td>171–219</td><td>153</td></tr><tr><th>Oesoph. cup – length</th><td>21–30</td><td>30</td><td>30–36</td><td>36</td></tr><tr><th>Oesoph. cup – width</th><td>24–33</td><td>39</td><td>36–39</td><td>30</td></tr><tr><th>Musc. oesoph. – length</th><td>1183–1414</td><td>1020</td><td>1333–1170</td><td>1102</td></tr><tr><th>Musc. oesoph. – width</th><td>122–136</td><td>81</td><td>122–136</td><td>84</td></tr><tr><th>Gland. oesoph. – length</th><td>1156–1333</td><td>857</td><td>1034–1238</td><td>1673</td></tr><tr><th>Gland. oesoph. – width</th><td>136</td><td>96</td><td>122–136</td><td>90</td></tr><tr><th>Musc./gland. oesoph. length ratio</th><td>1:0.94–0.98</td><td>1:084</td><td>1:0.88–0.93</td><td>1:0.79</td></tr><tr><th>% of buc. c. and oesoph. of body</th><td>21</td><td>30</td><td>23–24</td><td>–</td></tr><tr><th>Excretory pore</th><td>1047–1387</td><td>?</td><td>1115–1251</td><td>?</td></tr><tr><th>Right spicule</th><td>306–309</td><td>300</td><td>294–312</td><td>–</td></tr><tr><th>Tail</th><td>75–81</td><td>102</td><td>84–117</td><td>–</td></tr></tbody></table>
Table 1 in Proximate composition and its seasonal variations of the muscle tissue of Channa striata from Krishna river, Andhra Pradesh
<p><b>Table 1:</b> Variations of biochemical composition of muscle. <i>C</i>. <i>striata</i> (females)</p><table><tbody><tr><th><b>Seasons</b></th><th><b>Months Protein 2021-2022</b></th><th><b>Fat</b></th><th><b>Moisture</b></th><th><b>Ash</b></th></tr></tbody><tbody><tr><th>South West Monsoon</th><td>June</td><td>22.9</td><td>5.1</td><td>81.5</td><td>1.75</td></tr><tr><td>July</td><td>23.5</td><td>4.9</td><td>82.6</td><td>1.87</td></tr><tr><td>August</td><td>24.3</td><td>4.3</td><td>83.8</td><td>1.99</td></tr><tr><td>September</td><td>23.8</td><td>4.5</td><td>83.4</td><td>2.03</td></tr><tr><th>Post Monsoon</th><td>October November</td><td>22.8 21.5</td><td>4.8 5.2</td><td>83 82</td><td>2.12 2.19</td></tr><tr><th>North East Monsoon</th><td>December January February</td><td>20.4 21.5 21.2</td><td>5.4 4.9 4.6</td><td>82.1 82.3 82.2</td><td>2.01 1.96 1.81</td></tr><tr><th>Summer</th><td>March</td><td>21.8</td><td>4.5</td><td>80.2</td><td>1.79</td></tr><tr><td>April</td><td>22.3</td><td>4.6</td><td>81.5</td><td>1.61</td></tr><tr><td>May</td><td>22.4</td><td>5.2</td><td>80.5</td><td>1.75</td></tr><tr><th></th><td>Min.</td><td>20.4</td><td>4.3</td><td>80.2</td><td>1.61</td></tr><tr><th></th><td>Max.</td><td>24.3</td><td>5.4</td><td>83.8</td><td>2.19</td></tr><tr><th></th><td>Avg. 22.36±2.24.83±0.582.09±5.91.90±0.06</td></tr></tbody></table>
Table 4 in Water quality, yield and cost-benefit analysis of rain water ponds of Cuttack district: A comparison between Indian major carp and GIFT Tilapia
<p><b>Table 4:</b> Growth and production of IMC poly-culture & GIFT mono-sex tilapia in T1 & T2 (2018-19)</p><table><tbody><tr><th><b>Parameters</b></th><th><b>Growth-production data T1 T2</b></th></tr></tbody><tbody><tr><th>Initial avg. weight (g)</th><td>19</td><td>8</td></tr><tr><th>Final avg. weight (g)</th><td>816</td><td>1333</td></tr><tr><th>Survival rate (%)</th><td>91</td><td>93.75</td></tr><tr><th>Production (kg/pond/9 months)</th><td>3383</td><td>8000</td></tr><tr><th>Total production (kg/ha/9 months)</th><td>8457.5</td><td>20000</td></tr></tbody></table>
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