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Table 1 in Effect Of Parental Care On The Duration Of Larval Development And Offspring Survival In Nicrophorus Mexicanus Matthews (Coleoptera: Silphidae)
<p><b>Table 1.</b> Percentage of offspring survival in <i>N. mexicanus</i> in the three experimental groups. ni = number initial of larvae hatching for group. L1 = first instar larvae, L2 = second instar larvae, L3 = third instar larvae, pp = prepupae, p = pupae.</p><table><tbody><tr><th></th><th>Offspring Survival (%)</th><th>)</th></tr></tbody><tbody><tr><th>Treatment groups</th><td>ni</td><td>L1­L2 L3­PP PP­P</td></tr><tr><th>1) Control: parental care</th><td>390</td><td>97</td><td>90 70</td><td>70</td></tr><tr><th>2) With Brood­mass. Parents removed pre­hatching</th><td>468</td><td>95</td><td>89 60</td><td>60</td></tr><tr><th>3) Without care parental: with fresh meat, brood­mass</th><td>351</td><td>90</td><td>77 28</td><td>28</td></tr><tr><th>no present and parents removed pre­hatching</th><td></td><td></td><td></td><td></td></tr></tbody></table>
Table 2 in Larval Morhology Of Hydrotarsus Falkenström: Generic Characteristics, Description Of H. Compunctus (Wollaston), And Analysis Of Relationships With Other Members Of The Tribe Hydroporini (Coleoptera: Dytiscidae, Hydroporinae)
<p><b>Table 2.</b> Selected ratios of third instars of <i>Hydrotarsus</i> Falkenström (HDT), <i>Hydroporus</i> Clairville (HDR) and <i>Sanfilippodytes</i> Franciscolo (SAN); <i>n</i> = number of species studied.</p><table><tbody><tr><th>Features1</th><th>Genera</th></tr><tr><th>HDT (<i>n</i> = 1)</th><th>HDR (<i>n</i> = 15)</th><th>SAN (<i>n</i> = 1)</th></tr></tbody><tbody><tr><th>HL/HW</th><td>1.11–1.13</td><td>1.06–1.27</td><td>1.27</td></tr><tr><th>Ant L/HW</th><td>0.56–0.61</td><td>0.61–0.74</td><td>0.64</td></tr><tr><th>Ant L/Mx plp L</th><td>1.17–1.26</td><td>1.15–1.49</td><td>1.13</td></tr><tr><th>Mx plp L/Lb plp L</th><td>1.14–1.24</td><td>1.00–1.29</td><td>1.20</td></tr><tr><th>A2 L/A3 L</th><td>0.98–1.04</td><td>0.84–1.18</td><td>0.91</td></tr><tr><th>A3′ L/A4 L</th><td>0.56–0.63</td><td>0.59–0.85</td><td>0.89</td></tr><tr><th>MX2 L/MX1 L</th><td>0.81–0.85</td><td>0.74–1.01</td><td>0.95</td></tr><tr><th>LB2 L/LB1 L</th><td>0.96–0.97</td><td>0.96–1.25</td><td>1.15</td></tr><tr><th>FC L/HL</th><td>0.76–0.77</td><td>0.75–0.80</td><td>0.75</td></tr><tr><th>Metaleg L/HW</th><td>2.17</td><td>2.37–2.64</td><td>2.51</td></tr><tr><th>Siphon L/LASL</th><td>0.17</td><td>0.25–0.41</td><td>0.37</td></tr><tr><th>Uro1 L/LASL</th><td>1.42–1.49</td><td>0.75–1.86</td><td>1.18</td></tr><tr><th>Uro (1 + 2) L/LASL</th><td>3.10–3.31</td><td>1.49–3.73</td><td>2.62</td></tr><tr><th>Uro1 L/HW</th><td>0.71</td><td>0.62–1.09</td><td>0.81</td></tr><tr><th>Uro (1 + 2) L/HW</th><td>1.55–1.57</td><td>1.18–2.19</td><td>1.79</td></tr><tr><th>Uro1 L/Uro2 L</th><td>0.82–0.84</td><td>0.88–1.29</td><td>0.81</td></tr><tr><th>Uro1 L/Uro2′ L</th><td>0.86–0.88</td><td>0.91–1.37</td><td>0.90</td></tr><tr><th>LASL/HW</th><td>0.47–0.50</td><td>0.54–0.83</td><td>0.68</td></tr></tbody></table><p><sup>1</sup> Ant, antenna; FC, frontoclypeus; Lb plp, labial palpus; Mx plp, maxillary palpus; otherwise as defined in Alarie (1997) and Alarie et al. (1997).</p>
Table 2 in Effect Of Parental Care On The Duration Of Larval Development And Offspring Survival In Nicrophorus Mexicanus Matthews (Coleoptera: Silphidae)
<p><b>Table 2.</b> Significant differences in the variation the number of offspring surviving to adult emergence between three experimental groups.</p><table><tbody><tr><th>Compared groups</th><th></th><th></th><th></th><th></th><th></th><th></th></tr></tbody><tbody><tr><td>Difference</td><td>SE</td><td>Q</td><td>Q0.05 P <0­05</td></tr><tr><th>1 vs 3 1 vs 2</th><td>28.13–12.78 = 15.35 28.13–25.93 = 2.2</td><td>4.77 4.68</td><td>3.218 0.47</td><td>2.394 2.394</td><td>*</td></tr><tr><th>2 vs 3</th><td>25.93–12.78 = 13.15</td><td>4.77</td><td>2.75</td><td>2.394</td><td>*</td></tr><tr><th>Experimental groups</th><td>1</td><td></td><td>2</td><td>3</td><td></td></tr><tr><th>average ranges sample size</th><td>28.13 15</td><td></td><td>25.93 14</td><td>12.78 15</td><td></td></tr></tbody></table><p>* indicate a significant difference.</p>
Table 1 in Ecology Of Amblycerus Crassipunctatus Ribeiro-Costa (Coleoptera: Bruchidae) In Seeds Of Humiriaceae, A New Host Family For Bruchids, With An Ecological Comparision To Other Species Of Amblycerus
<p><b>Table 1.</b> Number of eggs and exit holes of <i>Amblycerus crassipunctatus</i> on and in fruits of Vantanea minor.</p><table><tbody><tr><th>Fruit</th><th>Number of</th><th>Emerged</th><th>% emerged</th></tr></tbody><tbody><tr><th>number</th><td>eggs/fruit</td><td>adults</td><td>adults</td></tr><tr><th>1</th><td>1</td><td>0</td><td>0</td></tr><tr><th>2</th><td>0</td><td>0</td><td>0</td></tr><tr><th>3</th><td>0</td><td>0</td><td>0</td></tr><tr><th>4</th><td>0</td><td>0</td><td>0</td></tr><tr><th>5</th><td>0</td><td>0</td><td>0</td></tr><tr><th>6</th><td>0</td><td>0</td><td>0</td></tr><tr><th>7</th><td>0</td><td>0</td><td>0</td></tr><tr><th>8</th><td>2</td><td>0</td><td>0</td></tr><tr><th>9</th><td>1</td><td>1</td><td>100</td></tr><tr><th>10</th><td>2</td><td>2</td><td>100</td></tr><tr><th>11</th><td>5</td><td>1</td><td>20</td></tr><tr><th>12</th><td>0</td><td>0</td><td>0</td></tr><tr><th>13</th><td>0</td><td>0</td><td>0</td></tr><tr><th>14</th><td>3</td><td>1</td><td>33.33</td></tr><tr><th>15</th><td>4</td><td>0</td><td>0</td></tr><tr><th>16</th><td>0</td><td>0</td><td>0</td></tr><tr><th>17</th><td>3</td><td>0</td><td>0</td></tr><tr><th>18</th><td>0</td><td>0</td><td>0</td></tr><tr><th>19</th><td>2</td><td>1</td><td>50</td></tr><tr><th>20</th><td>1</td><td>1</td><td>100</td></tr><tr><th>21</th><td>8</td><td>0</td><td>0</td></tr><tr><th>Total</th><td>32</td><td>7</td><td>21.87%</td></tr></tbody></table>
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Table 1 in A New Record Of Cononotus Lanchesteri Van Dyke (Coleoptera: Pyrochroidae: Agnathinae) In Washington State, With Notes On Habitat
<p><b>Table 1.</b> Dates of collection and number of <i>Cononotus lanchesteri</i> collected during pitfall collection intervals.</p><table><tbody><tr><th>Dates</th><th>Number of specimens</th></tr></tbody><tbody><tr><th>20–28 March 1998</th><td>1</td></tr><tr><th>18–25 April 1998</th><td>1</td></tr><tr><th>1–8 May 1998</th><td>1</td></tr><tr><th>8–15 May 1998</th><td>2</td></tr><tr><th>26 August–5 September 1998</th><td>1</td></tr><tr><th>9–16 April 1999</th><td>1</td></tr><tr><th>11–25 June 1999</th><td>1</td></tr></tbody></table>
TABLE 1 in Setting the record straight: a re-examination of ants (Hymenoptera: Formicidae) from Cyprus deposited at the Museum of Zoology of Athens
<p><b>TABLE 1.</b> List of localities of examined material.</p><table><tbody><tr><th>Number</th><th>District</th><th>Locality</th><th>Latitude</th><th>Longitude</th><th>Altitude (m)</th><th>Habitat</th></tr></tbody><tbody><tr><th>1</th><td>Akrotiri UK SBA</td><td>Lemessos, Akrotiri, Lady's Mile beach</td><td>34.5962</td><td>33.0073</td><td>2</td><td>phrygana (Mediterranean shrubland) and sand dunes</td></tr><tr><th>2</th><td>Akrotiri UK SBA</td><td>Lemessos, Akrotiri, Western beach</td><td>34.5898</td><td>32.9502</td><td>15</td><td>not specified</td></tr><tr><th>3</th><td>Limassol</td><td>Lemessos, Agia Mavri</td><td>34.8461</td><td>32.8687</td><td>720</td><td><i>Platanus</i> sp. (plane), next to riverbank</td></tr><tr><th>4</th><td>Limassol</td><td>Lemessos, Fasoula</td><td>34.7263</td><td>33.0364</td><td>250</td><td>phrygana, scarce trees</td></tr><tr><th>5</th><td>Limassol</td><td>Lemessos, Koilani</td><td>34.85</td><td>32.8509</td><td>980</td><td>vineyard, next to phrygana</td></tr><tr><th>6</th><td>Limassol</td><td>Lemessos, Lofou</td><td>34.8175</td><td>32.8751</td><td>750</td><td>not specified</td></tr><tr><th>7</th><td>Limassol</td><td>Lemessos, Pissouri, Trachonas 1</td><td>34.6472</td><td>32.6951</td><td>225</td><td>300 m from the sea, phrygana with <i>Ceratonia siliqua</i> (carob)</td></tr><tr><th>8</th><td>Limassol</td><td>Lemessos, Pissouri, Trachonas 2</td><td>34.6636</td><td>32.6892</td><td>820</td><td><i>Pinus brutia</i> (Calabrian pine) forest</td></tr><tr><th>9</th><td>Limassol</td><td>Lemessos, Platres, to Kalidonion waterfalls</td><td>34.8984</td><td>32.8671</td><td>1270</td><td>not specified</td></tr><tr><th>10</th><td>Nicosia</td><td>Lefkosia, Kotsiatis, near the bridge</td><td>35.0128</td><td>33.3524</td><td>270</td><td>not specified</td></tr><tr><th>11</th><td>Nicosia</td><td>Lefkosia, Lythrodontas, Gyalias dam</td><td>34.9713</td><td>33.2856</td><td>420</td><td>not specified</td></tr><tr><th>12</th><td>Paphos</td><td>Pafos, Chloraka, Azia resort</td><td>34.8106</td><td>32.3949</td><td>21</td><td>park close to the sea</td></tr><tr><th>13</th><td>Paphos</td><td>Pafos, Kato Pafos, Faros</td><td>34.7606</td><td>32.4058</td><td>15</td><td>phrygana, 200 m from sea</td></tr><tr><th>14</th><td>Paphos</td><td>Pafos, Lara, Ag. Georgios</td><td>34.9106</td><td>32.3265</td><td>30</td><td>phrygana next to road, 10 m from sea</td></tr><tr><th>15</th><td>Paphos</td><td>Pafos, Lara, White River beach</td><td>34.9118</td><td>32.3265</td><td>12</td><td>sand dunes, 10 m from the sea</td></tr><tr><th>16</th><td>Paphos</td><td>Pafos, Pegeia, Kampinariou</td><td>34.8881</td><td>32.3804</td><td>287</td><td>phrygana next to road, close to houses</td></tr><tr><th>17</th><td>Paphos</td><td>Pafos, Pegeia, Oktovriou</td><td>34.8865</td><td>32.383</td><td>253</td><td>park close to the sea</td></tr><tr><th>18</th><td>Paphos</td><td>Pafos, Pegeia, Pikni forest</td><td>34.8966</td><td>32.3702</td><td>375</td><td><i>Pinus halepensis</i> (Aleppo pine) forest</td></tr><tr><th>19</th><td>Paphos</td><td>Pafos, Skoulli riv.</td><td>34.9791</td><td>32.4568</td><td>90</td><td>not specified</td></tr></tbody></table>
TABLE 1 in Morphology, biology and phylogeny of Xenos gadagkari sp. nov. (Strepsiptera: Xenidae): an endoparasite of Polistes wattii (Hymenoptera: Vespidae)
<p><b>TABLE 1.</b> Numbers of stylopized wasps, compared to healthy wasps, in nests at late the colony phase. All nests were collected from IISER Mohali Campus.</p><table><tbody><tr><th><b>Nest No</b></th><th><b>Date of Collection</b></th><th><b>Healthy Male (No externally visible parasite)</b></th><th><b>Stylopized Male</b></th><th><b>Healthy Female (No externally visible parasite)</b></th><th><b>Stylopized Female</b></th></tr></tbody><tbody><tr><th>1</th><td>27-09-2021</td><td>46</td><td>8</td><td>32</td><td>0</td></tr><tr><th>2</th><td>24-11-2021</td><td>7</td><td>2</td><td>12</td><td>1</td></tr><tr><th>3</th><td>24-11-2021</td><td>1</td><td>0</td><td>35</td><td>3</td></tr><tr><th>4</th><td>19-12-2021</td><td>5</td><td>0</td><td>107</td><td>3</td></tr><tr><th>5</th><td>09-10-2022</td><td>8</td><td>1</td><td>34</td><td>4</td></tr><tr><th>6</th><td>18-10-2022</td><td>19</td><td>6</td><td>46</td><td>16</td></tr></tbody></table>
Table 1 in Taxonomic revision of the New World members of the trapdoor spider genus Ummidia Thorell (Araneae, Mygalomorphae, Halonoproctidae)
<p><b>Table 1.</b> Summary of <i>Ummidia</i> New World diversity documenting locality and latitude/longitude for each type locality. * Locality data for the type specimen of <i>Ummidia audouini</i> is given only as "North America" so the latitude and longitude shown and displayed in Map 1 are from male exemplar specimen UMM194 from Ecru, Mississippi.</p><table><tbody><tr><th>Species</th><th>Locality</th><th>Latitude/Longitude</th></tr></tbody><tbody><tr><td><i>Ummidia audouini</i></td><td>North America</td><td>34.3403 -89.0141 *</td></tr><tr><td><i>Ummidia neilgaimani</i> sp. nov.</td><td>Charlotte County, Virginia</td><td>36.7698 -78.6356</td></tr><tr><td><i>Ummidia gingoteague</i> sp. nov.</td><td>Accomack County, Virginia</td><td>37.9083 -75.3568</td></tr><tr><td><i>Ummidia carabivora</i></td><td>Chapel Hill, North Carolina</td><td>35.9131 -79.0557</td></tr><tr><td><i>Ummidia rongodwini</i> sp. nov.</td><td>Calhoun County, Alabama</td><td>33.8795 -85.7889</td></tr><tr><td><i>Ummidia okefenokee</i> sp. nov.</td><td>Charlton County, Georgia</td><td>30.8056 -82.3371</td></tr><tr><td><i>Ummidia richmond</i> sp. nov.</td><td>Miami-Dade County, Florida</td><td>25.605 -80.3566</td></tr><tr><td><i>Ummidia macarthuri</i> sp. nov.</td><td>Washington County Arkansas</td><td>35.8167 -94.395</td></tr><tr><td><i>Ummidia beatula</i></td><td>Dallas County, Texas</td><td>32.6472 -96.7913</td></tr><tr><td><i>Ummidia colemanae</i> sp. nov.</td><td>San Patricio County, Texas</td><td>28.0852 -97.2647</td></tr><tr><td><i>Ummidia funerea</i></td><td>Edinburg, Texas</td><td>26.3005 -98.1623</td></tr><tr><td><i>Ummidia rosillos</i> sp. nov.</td><td>Brewster County, Texas</td><td>29.5385 -103.2323</td></tr><tr><td><i>Ummidia mercedesburnsae</i> sp. nov.</td><td>Culberson County, Texas</td><td>31.8945 -104.6331</td></tr><tr><td><i>Ummidia paulacushingae</i> sp. nov.</td><td>Mesa County, Colorado</td><td>39.0636 -108.5518</td></tr><tr><td><i>Ummidia modesta</i></td><td>Dona Ana County, New Mexico</td><td>32.338 -106.7661</td></tr><tr><td><i>Ummidia waunekaae</i> sp. nov.</td><td>Bernalillo County, New Mexico</td><td>35.1303 -106.5521</td></tr><tr><td><i>Ummidia gertschi</i> sp. nov.</td><td>Cochise County, Arizona</td><td>31.8842 -109.206</td></tr><tr><td><i>Ummidia timcotai</i> sp. nov.</td><td>Globe, Gila County, Arizona</td><td>33.3940 -110.7864</td></tr><tr><td><i>Ummidia gabrieli</i> sp. nov.</td><td>La Paz, Baja California Sur, Mexico</td><td>24.0345 -110.227</td></tr><tr><td><i>Ummidia pesiou</i> sp. nov.</td><td>Sonora, Mexico</td><td>29.0894 -110.6947</td></tr><tr><td><i>Ummidia rodeo</i> sp. nov.</td><td>Durango, Mexico</td><td>25.1081 -104.5556</td></tr><tr><td><i>Ummidia pustulosa</i></td><td>Amula (now Jalisco), Mexico</td><td>20.6934 -103.356</td></tr><tr><td><i>Ummidia huascazaloya</i> sp. nov.</td><td>Hidalgo, Mexico</td><td>20.2762 -98.5169</td></tr><tr><td><i>Ummidia anaya</i> sp. nov.</td><td>Hidalgo, Mexico</td><td>20.3884 -99.0275</td></tr><tr><td><i>Ummidia cuicatec</i> sp. nov.</td><td>Oaxaca, Mexico</td><td>17.7984 -96.9519</td></tr><tr><td><i>Ummidia brandicarlileae</i> sp. nov.</td><td>Yucatan, Mexico</td><td>20.0603 -88.2654</td></tr><tr><td><i>Ummidia zebrina</i></td><td>Guatemala</td><td>15.2812 -90.3420</td></tr><tr><td><i>Ummidia riverai</i> sp. nov.</td><td>Baja Verapaz, Guatemala</td><td>15.1631 -90.2316</td></tr><tr><td><i>Ummidia frankellerae</i> sp. nov.</td><td>Cayo, Belize</td><td>16.733 -88.986</td></tr><tr><td><i>Ummidia zilchi</i></td><td>San Salvador, El Salvador</td><td>13.6921 -89.219</td></tr><tr><td><i>Ummidia hondurena</i> sp. nov.</td><td>Honduras</td><td>14.5036 -86.3206</td></tr><tr><td><i>Ummidia yojoa</i> sp. nov.</td><td>Dept. of Cortes, Honduras</td><td>14.8715 -87.9821</td></tr><tr><td><i>Ummidia matagalpa</i> sp. nov.</td><td>Matagalpa, Nicaragua</td><td>12.9207 -85.9172</td></tr><tr><td><i>Ummidia rugosa</i></td><td>Costa Rica</td><td>9.7703 -83.7751</td></tr><tr><td><i>Ummidia carlosviquezi</i> sp. nov.</td><td>Puntarenas, Costa Rica</td><td>8.7125 -83.0051</td></tr><tr><td><i>Ummidia varablanca</i> sp. nov.</td><td>Heredia, Costa Rica</td><td>10.0024 -84.1216</td></tr><tr><td><i>Ummidia quepoa</i> sp. nov.</td><td>Puntarenas, Costa Rica</td><td>9.4828 -84.0948</td></tr><tr><td><i>Ummidia cerrohoya</i> sp. nov.</td><td>Los Santos, Panama</td><td>7.2986 -80.0014</td></tr><tr><td><i>Ummidia erema</i></td><td>Panama Canal Zone, Panama</td><td>9.1520 -79.8467</td></tr><tr><td><i>Ummidia quijichacaca</i> sp. nov.</td><td>Cundinamarca, Colombia</td><td>4.6049 -74.0565</td></tr><tr><td><i>Ummidia tibacuy</i> sp. nov.</td><td>Cundinamarca, Colombia</td><td>4.3283 -74.5081</td></tr><tr><td><i>Ummidia asperula</i></td><td>Maiquetia, Venezuela</td><td>10.5778 -66.9973</td></tr><tr><td><i>Ummidia neblina</i> sp. nov.</td><td>Amazonas, Venezuela</td><td>1.2395 -65.6675</td></tr><tr><td><i>Ummidia tunapuna</i> sp. nov.</td><td>St. George, Trinidad and Tobago</td><td>10.6638 -61.3950</td></tr><tr><td><i>Ummidia salebrosa</i></td><td>St Vincent</td><td>13.2536 -61.187</td></tr><tr><td><i>Ummidia nidulans</i></td><td>St. Elizabeth, Jamaica</td><td>17.9244 -77.6869</td></tr><tr><td><i>Ummidia glabra</i></td><td>Brazil</td><td>-14.1241 -51.9029</td></tr></tbody></table>
Supplementary Table S1 & Table S2
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Table 1 in Parahiraciini (Hemiptera, Fulgoromorpha, Issidae): one new genus, two new species and three new subtribes
<p><b>Table 1.</b> Taxa sampling, collecting locations and GenBank accession numbers used for the phylogenetic study.</p><table><tbody><tr><th>Species name</th><th>Collecting location</th><th>Gene 18S</th><th>Gene 28S (D3-D5)</th><th>Gene 28S (D6-D7)</th><th>COXI</th><th>Cytb</th></tr></tbody><tbody><tr><td><i>Fortunia</i> sp.</td><td>China, Yunnan, Xishuangbanna, Mengla, Menglun, 21°24'398"N, 101°16'754"E, 705 ± 21 m</td><td>KX761487</td><td>KX761527</td><td>KX761518</td><td>KX761498</td><td>KX761509</td></tr><tr><td><i>Flavina hainana</i> (Wang & Wang, 1999)</td><td>China, Hainan, Jianfengling</td><td>KX702824</td><td>KX761453</td><td>MN381846</td><td></td><td>KX702912</td></tr><tr><td><i>Gelastyrella litaoensis</i> Yang, 1994</td><td>China, Hainan, Bawangling</td><td>KX702823</td><td>KX761452</td><td>KX702811</td><td>KX761461</td><td>KX702911</td></tr><tr><td><i>Macrodarumoides petalinus</i> Che, Zhang & Wang, 2012</td><td>China, Guangxi, Baise, Jinzhongshan, Songshuping</td><td>KX702827</td><td></td><td>KX702856</td><td>KX702926</td><td>KX702880</td></tr><tr><td><i>Neodurium hamatum</i> Wang & Wang, 2011</td><td>China, Yunnan, Xishuangbanna, Mengla, Menglun, 21°24'398"N, 101°16'754"E, 705 ± 21 m</td><td>KX702818</td><td>KX761446</td><td>MN381844</td><td>KX702920</td><td></td></tr><tr><td><i>Tetricodissus pandlineus</i> Wang, Bourgoin & Zhang, 2015</td><td>China, Yunnan, Xishuangbanna, Mengla, Nanshahe, 21°36'12.1"N, 101°34'23.9"E, 826 ± 43 m</td><td>KX702817</td><td>KX761445</td><td>KX702807</td><td></td><td>KX702907</td></tr><tr><td><i>Tetricodes songae</i> Zhang & Chen, 2009</td><td>China, Guizhou, Kuankuoshui, 1500 m</td><td>KX702841</td><td>KX761457</td><td></td><td>KX702925</td><td>KX702916</td></tr><tr><td><i>Pusulissus</i> sp.</td><td>Vietnam, Vinh Phuc, Tam Dao, 21°26'47"N, 105°38'38"E, 748 m</td><td>KX761479</td><td></td><td>KX761485</td><td>KX761471</td><td>KX761475</td></tr><tr><td><i>Pusulissus coronomensis</i> sp. nov.</td><td>China, Guangxi, Hezhou, Qichong, 24°13'6"N, 110°48'34"E, 180 m</td><td>MT772139</td><td>MT772137</td><td>MT772136</td><td>MT774094</td><td>MT774093</td></tr><tr><td><i>Pusulissus phiaoacensis</i> sp. nov.</td><td>Vietnam, Phia Oac, 1050 m</td><td>MW201961</td><td></td><td></td><td>MT774095</td><td>MT774092</td></tr><tr><td><i>Rhombissus</i> sp.</td><td>China, Shaanxi, Zhouzhi, Houzhenzi, 1050 m</td><td>MN381855</td><td>MN381852</td><td>MN381850</td><td></td><td>MN332231</td></tr><tr><td><i>Duplexissus punctatulus</i> Wang, Zhang & Bourgoin, 2019</td><td>China, Yunnan, Xishuangbanna, Mengla, Menglun</td><td>KX761490</td><td>KX761531</td><td>KX761520</td><td>KX761501</td><td>KX761512</td></tr><tr><td><i>Hemisphaerius lysanias</i> Fennah, 1978</td><td>Vietnam, Khanh Hoa Province, Hon-Ba massif, 12°13'20"N, 109°06'00"E</td><td>KX702833</td><td>KX761404</td><td>KX702860</td><td>KX702933</td><td>KX702883</td></tr><tr><td><i>Hemisphaerius coccinelloides</i> (Burmeister, 1834)</td><td>Philippines, Los Banos, UP Hortarium, 14°09'53"N, 121°14'14"E</td><td>KX702834</td><td>KX761405</td><td>KX702861</td><td>KX702934</td><td>KX702884</td></tr><tr><td><i>Sarima bifurca</i> Meng & Wang, 2016</td><td>China, Yunnan, Xishuangbanna, Mengla</td><td>KX702819</td><td>KX761447</td><td>KX702808</td><td>KX702921</td><td>KX761552</td></tr></tbody></table>
Table 5 in Guide to the Vascular Flora of the Savannas and Flatwoods of Shaken Creek Preserve and Vicinity (Pender & Onslow Counties, North Carolina, U. S. A.)
<p>Table 5. Summary of vascular plant taxa collected or reported from savannas, flatwoods, or sandhills in Shaken Creek Preserve or the vicinity (i.e., in Sandy Run and/or within a 2-mile radius of Shaken Creek Preserve). The first number in each three-number series indicates the number of taxa collected or reported from Shaken Creek Preserve. The second number in each series indicates the number of additional taxa collected or reported from the vicinity of, but not in, Shaken Creek Preserve. The third number in each series, which appears in parentheses, is the sum of the preceding two numbers and indicates the total number of taxa collected or reported from either Shaken Creek Preserve or the vicinity. (The lone exotic taxon is Pinus elliottii Engelm. var. elliottii, which was planted by a timber company in a flatwoods in Shaken Creek Preserve prior to the site’s purchase by The Nature Conservancy.)</p><table><tbody><tr><th>Group</th><th>Families</th><th>Genera</th><th>Species and Subspecies/Varieties</th></tr><tr><th>Native</th><th>Exotic</th><th>Total</th></tr></tbody><tbody><tr><td>Total</td><td>83, 7 (90)</td><td>204, 27 (231)</td><td>449, 102 (551)</td><td>1, 0 (1)</td><td>450, 102 (552)</td></tr></tbody></table>
TABLE 1 in A new species of Coelidiana Oman (Hemiptera: Cicadellidae: Neocoelidiinae) from Brazil with key to Brazilian species, description of immature stages, and notes about parasitoids and host plant
<p><b>TABLE 1.</b> Measurements in millimeters of <i>Coelidiana aroeira</i> <b>sp. nov.</b> nymph instars. (n= number of specimens analyzed)</p><table><tbody><tr><th>Instar</th><th>Thorax Head length length</th><th>Abdomen length</th><th>Body length</th><th>Pronotum length</th><th>Head width</th><th>Pronotum width</th></tr></tbody><tbody><tr><th>First (n=5)</th><td>0.30-0.42</td><td>0.30-0.50</td><td>0.80-1.30</td><td>1.40-2.14</td><td>0.10</td><td>0.42-0.72</td><td>0.40-0.72</td></tr><tr><th>Second (n=12)</th><td>0.37-0.53</td><td>0.59-0.78</td><td>1,03-1,87</td><td>2.20-3.15</td><td>0.16-0.18</td><td>0.66-0.75</td><td>0.66-0.75</td></tr><tr><th>Third (n=12)</th><td>0.44-0.68</td><td>0.64-1.00</td><td>1.52-2.45</td><td>3.40-4.00</td><td>0.16-0.25</td><td>0.80-0.95</td><td>0.80-1.00</td></tr><tr><th>Fourth (n=6)</th><td>0.50-0.70</td><td>1.00-1.20</td><td>2.10-2.60</td><td>4.00-4.40</td><td>0.20-0.30</td><td>1.00-1.20</td><td>1.20-1.30</td></tr><tr><th>Fifth (n=9)</th><td>0.55-0.75</td><td>1.10-1.45</td><td>2.35-3.56</td><td>4.35-5.60</td><td>0.25-0.30</td><td>1.00-1.20</td><td>1.15-1.30</td></tr></tbody></table>
TABLE 5 in Revisiting the description of Atractoscion macrolepis (Perciformes: Sciaenidae): Another argument for comprehensive taxonomy
<p><b>TABLE 5.</b> Frequency distribution of the number of second dorsal fin rays in <i>Atractoscion aequidens</i> and <i>A. macrolepis</i>.</p><table><tbody><tr><th>Species</th><th></th><th></th><th>2nd Dorsal fin rays (2DR)</th><th></th><th></th></tr></tbody><tbody><tr><th></th><td>24</td><td>25</td><td>26</td><td>27</td><td>28</td><td>29</td></tr><tr><th><i>Atractoscion aequidens</i></th><td></td><td></td><td>6</td><td>15</td><td>9</td><td>3</td></tr><tr><th><i>Atractoscion macrolepis</i></th><td>1</td><td>6</td><td>17</td><td>27</td><td>1</td><td></td></tr></tbody></table>
TABLE 1 in The Okuru skink (Oligosoma carinacauda sp. nov) of South Westland, New Zealand-simply elusive or extinct?
<p><b>TABLE 1.</b> Comparison of morphometric and meristic features between <i>O. carinacauda</i> <b>sp. nov.</b> and similar species.</p><table><tbody><tr><th><b>Character</b></th><th><i>O. carinacauda</i></th><th><i>O. inconspicuum</i></th><th><i>O. repens</i></th><th><i>O. burganae</i></th><th><i>O. tekakahu</i></th><th><i>O. toka</i></th><th><i>O. aureocola</i></th><th><i>O. polychroma</i></th></tr><tr><th><b>sp. nov.</b></th></tr></tbody><tbody><tr><th><b>Mean TL/SVL</b></th><td>1.25</td><td>1.16 n=14</td><td>1.28 n=2</td><td>1.00 n=1</td><td>N/A</td><td>1.16 n=3</td><td>N/A</td><td>1.16 n=19</td></tr><tr><th><b>(intact tail)</b></th></tr><tr><th><b>MS</b></th><td>29</td><td>26–32</td><td>30–34</td><td>30–34</td><td>30</td><td>30–34</td><td>30–31</td><td>26–31</td></tr><tr><th><b>VS</b></th><td>82</td><td>67–86</td><td>68–81</td><td>70–82</td><td>68</td><td>77–88</td><td>80–84</td><td>63–81</td></tr><tr><th><b>Lamellae</b></th><td>18/19</td><td>17–23</td><td>19–23</td><td>18–23</td><td>16</td><td>17–23</td><td>24–26</td><td>17–26</td></tr><tr><th><b>HL/HW</b></th><td>1.63</td><td>1.25–1.63</td><td>1.34–1.60</td><td>1.28–1.48</td><td>1.44</td><td>1.37–1.53</td><td>1.45–1.51</td><td>1.44– 1.93</td></tr><tr><th><b>SVL/HW</b></th><td>12.04</td><td>7.50–11.63</td><td>9.09–10.84</td><td>9.45–11.61</td><td>9.88</td><td>9.20–11.98</td><td>9.42–9.83</td><td>8.31–12.93</td></tr><tr><th><b>Projecting</b></th><td>No</td><td>Sometimes</td><td>Sometimes</td><td>No</td><td>Yes</td><td>Yes</td><td>Yes</td><td>Usually</td></tr><tr><th><b>scale(s) in ear</b></th><td></td><td></td><td></td><td></td><td></td><td></td><td></td><td></td></tr><tr><th><b>opening</b></th></tr><tr><th><b>Tail keeled</b></th><td>Yes</td><td>Sometimes</td><td>No</td><td>No</td><td>No</td><td>No</td><td>No</td><td>No</td></tr><tr><th><b>Supraoculars</b></th><td>3</td><td>4</td><td>3</td><td>3,4</td><td>3,4</td><td>3</td><td>3</td><td>3,4</td></tr></tbody></table>
TABLE 2 in Revisiting the description of Atractoscion macrolepis (Perciformes: Sciaenidae): Another argument for comprehensive taxonomy
<p><b>TABLE 2.</b> Factor loadings, eigenvalues and the variation (individually and cumulatively) explained by the first five principal components in the Principal Components Analysis of 23 transformed morphometric variables examining morphological variation among <i>Atractoscion aequidens</i> and <i>A. macrolepis</i>. Only Principal Components with eigenvalues> 1 are reported.</p><table><tbody><tr><th>Variable</th><th></th><th></th><th>Principal Components</th><th></th><th></th></tr></tbody><tbody><tr><th></th><td>PC1</td><td>PC2</td><td>PC3</td><td>PC4</td><td>PC5</td></tr><tr><th><i>TL’</i></th><td>0.667</td><td>-0.213</td><td>-0.057</td><td>0.184</td><td>0.186</td></tr><tr><th><i>FL’</i></th><td>0.510</td><td>-0.118</td><td>-0.098</td><td>-0.073</td><td>0.401</td></tr><tr><th><i>BD’</i></th><td>0.590</td><td>-0.046</td><td>0.420</td><td>0.198</td><td>0.008</td></tr><tr><th><i>1DFL’</i></th><td>0.554</td><td>-0.079</td><td>0.155</td><td>0.353</td><td>-0.190</td></tr><tr><th><i>2DFL’</i></th><td>-0.036</td><td>0.203</td><td>0.749</td><td>0.444</td><td>-0.031</td></tr><tr><th><i>CPL’</i></th><td>-0.504</td><td>0.217</td><td>-0.107</td><td>0.215</td><td>0.377</td></tr><tr><th><i>UCLL’</i></th><td>0.791</td><td>-0.055</td><td>-0.206</td><td>0.077</td><td>-0.042</td></tr><tr><th><i>MCL’</i></th><td>0.931</td><td>-0.194</td><td>-0.049</td><td>0.054</td><td>-0.043</td></tr><tr><th><i>LCLL’</i></th><td>0.475</td><td>-0.073</td><td>-0.287</td><td>0.331</td><td>0.518</td></tr><tr><th><i>AFB’</i></th><td>0.416</td><td>0.568</td><td>-0.193</td><td>-0.099</td><td>-0.380</td></tr><tr><th><i>AFL’</i></th><td>0.926</td><td>-0.036</td><td>-0.059</td><td>-0.056</td><td>-0.078</td></tr><tr><th><i>PFB’</i></th><td>0.444</td><td>0.722</td><td>-0.152</td><td>0.144</td><td>-0.179</td></tr><tr><th><i>PFL’</i></th><td>0.871</td><td>0.008</td><td>-0.003</td><td>0.055</td><td>0.092</td></tr><tr><th><i>PLFB’</i></th><td>0.047</td><td>0.820</td><td>-0.137</td><td>0.218</td><td>-0.214</td></tr><tr><th><i>PLFL’</i></th><td>0.877</td><td>-0.201</td><td>-0.027</td><td>-0.019</td><td>-0.125</td></tr><tr><th><i>PPL’</i></th><td>0.707</td><td>0.025</td><td>0.394</td><td>-0.169</td><td>0.182</td></tr><tr><th><i>HL’</i></th><td>0.934</td><td>-0.072</td><td>0.071</td><td>-0.216</td><td>0.012</td></tr><tr><th><i>LDL’</i></th><td>0.895</td><td>0.054</td><td>0.063</td><td>-0.290</td><td>0.026</td></tr><tr><th><i>IOW’</i></th><td>0.173</td><td>0.695</td><td>0.215</td><td>-0.483</td><td>0.146</td></tr><tr><th><i>OD’</i></th><td>0.854</td><td>0.175</td><td>-0.175</td><td>0.086</td><td>-0.030</td></tr><tr><th><i>SNL’</i></th><td>-0.033</td><td>0.792</td><td>0.177</td><td>-0.311</td><td>0.280</td></tr><tr><th><i>GFL’</i></th><td>0.392</td><td>0.715</td><td>-0.031</td><td>0.232</td><td>0.096</td></tr><tr><th><i>PSF’</i></th><td>-0.344</td><td>0.777</td><td>-0.107</td><td>0.184</td><td>0.159</td></tr><tr><th>Eigenvalue</th><td>9.296</td><td>4.024</td><td>1.283</td><td>1.232</td><td>1.068</td></tr><tr><th>% Total variation</th><td>40.42</td><td>17.50</td><td>5.58</td><td>5.36</td><td>4.64</td></tr><tr><th>Cumulative %</th><td>40.42</td><td>57.91</td><td>63.49</td><td>68.85</td><td>73.49</td></tr></tbody></table>
TABLE 1 in Revisiting the description of Atractoscion macrolepis (Perciformes: Sciaenidae): Another argument for comprehensive taxonomy
<p><b>TABLE 1.</b> The morphometric, meristic and otolith variables considered in the comparison of <i>Atractoscion aequidens</i> and <i>A. macrolepis</i> in the current study. Means and ranges (in parenthesis) of both raw measurements and proportions (prop.), with body variables expressed as a proportion of standard length (SL), head variables (*) as a proportion of head length (HL) and otolith variables as a proportion of fork length (FL), are presented for the morphometric and otolith variables. Modes and ranges are presented for the meristic counts and counts of otolith processes. Samples sizes (<i>n</i>) are indicated for each variable.</p><table><tbody><tr><th>Variable</th><th></th><th><i>Atractoscion aequidens</i></th><th></th><th><i>Atractoscion macrolepis</i></th></tr></tbody><tbody><tr><th></th><td><i>n</i></td><td>Mean (min.–max.)</td><td>Mean prop. (min.–max.)</td><td><i>n</i></td><td>Mean (min.–max.)</td><td>Mean prop. (min.–max.)</td></tr><tr><th>Morphometrics</th></tr><tr><th>SL</th><td>33</td><td>522.2 (323.0–825.0)</td><td>–</td><td>52</td><td>334.0 (229.9–556.0)</td><td>–</td></tr><tr><th>TL</th><td>31</td><td>603.7 (381.0–958.0)</td><td>1.18 (1.16–1.30)</td><td>52</td><td>401.3 (279.6–663.0)</td><td>1.20 (1.16–1.24)</td></tr><tr><th>FL</th><td>33</td><td>580.8 (364.0–913.0)</td><td>1.11 (1.05–1.14)</td><td>52</td><td>381.5 (268.8–629.0)</td><td>1.14 (1.01–1.19)</td></tr><tr><th>BD</th><td>33</td><td>105.6 (68.4–165.7)</td><td>0.20 (0.17–0.23)</td><td>52</td><td>73.4 (48.7–123.6)</td><td>0.22 (0.17–0.24)</td></tr><tr><th>1DFL</th><td>33</td><td>73.4 (46.8–115.8)</td><td>0.14 (0.11–0.16)</td><td>52</td><td>52.6 (35.0–87.1)</td><td>0.16 (0.13–0.26)</td></tr><tr><th>2DFL</th><td>33</td><td>175.2 (75.4–298.6)</td><td>0.33 (0.14–0.38)</td><td>52</td><td>111.9 (68.8–205.1)</td><td>0.34 (0.19–0.37)</td></tr><tr><th>CPL</th><td>33</td><td>79.8 (50.3–125.7)</td><td>0.15 (0.13–0.17)</td><td>52</td><td>47.4 (29.6–77.8)</td><td>0.14 (0.12–0.19)</td></tr><tr><th>UCLL</th><td>32</td><td>100.0 (62.4–158.7)</td><td>0.19 (0.15–0.21)</td><td>52</td><td>72.9 (47.2–122.1)</td><td>0.22 (0.19–0.25)</td></tr><tr><th>MCL</th><td>32</td><td>60.8 (41.5–87.7)</td><td>0.12 (0.10–0.13)</td><td>52</td><td>48.5 (33.2–75.8)</td><td>0.15 (0.13–0.17)</td></tr><tr><th>LCLL</th><td>32</td><td>94.8 (63.4–145.9)</td><td>0.19 (0.11–0.21)</td><td>51</td><td>66.2 (42.7–111.0)</td><td>0.20 (0.13–0.22)</td></tr><tr><th>AFB</th><td>33</td><td>43.9 (29.3–71.7)</td><td>0.08 (0.08–0.09)</td><td>52</td><td>29.3 (14.6–47.6)</td><td>0.09 (0.06–0.10)</td></tr><tr><th>AFL</th><td>33</td><td>59.9 (38.6–90.1)</td><td>0.12 (0.10–0.13)</td><td>52</td><td>44.2 (28.7–71.0)</td><td>0.13 (0.12–0.15)</td></tr><tr><th>PFB</th><td>33</td><td>17.8 (12.6–27.7)</td><td>0.03 (0.03–0.04)</td><td>52</td><td>12.7 (4.2–21.2)</td><td>0.04 (0.02–0.05)</td></tr><tr><th>PFL</th><td>33</td><td>82.7 (52.3–125.2)</td><td>0.16 (0.15–0.17)</td><td>52</td><td>61.7 (37.6–103.9)</td><td>0.19 (0.14–0.20)</td></tr><tr><th>PLFB</th><td>33</td><td>18.4 (12.5–30.0)</td><td>0.04 (0.03–0.04)</td><td>52</td><td>12.1 (3.1–22.9)</td><td>0.04 (0.01–0.04)</td></tr><tr><th>PLFL</th><td>33</td><td>73.1 (47.8–111.8)</td><td>0.14 (0.12–0.16)</td><td>52</td><td>53.0 (37.5–82.1)</td><td>0.16 (0.14–0.18)</td></tr><tr><th>PPL</th><td>33</td><td>168.7 (104.9–271.4)</td><td>0.32 (0.29–0.34)</td><td>52</td><td>113.3 (76.8–186.5)</td><td>0.34 (0.32–0.36)</td></tr><tr><th>HL</th><td>33</td><td>146.4 (94.5–229.0)</td><td>0.28 (0.26–0.30)</td><td>52</td><td>103.4 (70.5–166.9)</td><td>0.31 (0.29–0.33)</td></tr><tr><th>LDL*</th><td>33</td><td>81.7 (52.3–128.0)</td><td>0.56 (0.53–0.59)</td><td>52</td><td>56.9 (37.3–91.8)</td><td>0.55 (0.53–0.58)</td></tr><tr><th>IOW*</th><td>33</td><td>32.1 (17.9–52.2)</td><td>0.22 (0.16–0.24)</td><td>52</td><td>20.8 (11.3–34.0)</td><td>0.20 (0.16–0.23)</td></tr><tr><th>OD*</th><td>33</td><td>20.0 (14.9–28.3)</td><td>0.14 (0.09–0.17)</td><td>52</td><td>15.9 (7.5–23.0)</td><td>0.16 (0.11–0.18)</td></tr><tr><th>SNL*</th><td>33</td><td>43.2 (26.2–69.5)</td><td>0.29 (0.23–0.31)</td><td>52</td><td>27.0 (13.9–46.2)</td><td>0.26 (0.20–0.28)</td></tr><tr><th>GFL*</th><td>32</td><td>15.9 (10.0–23.8)</td><td>0.11 (0.08–0.13)</td><td>52</td><td>11.8 (3.2–18.8)</td><td>0.11 (0.04–0.14)</td></tr><tr><th>PSF*</th><td>32</td><td>23.9 (12.4–38.4)</td><td>0.16 (0.13–0.20)</td><td>52</td><td>13.7 (3.6–28.2)</td><td>0.13 (0.05–0.17)</td></tr><tr><th>Meristics</th></tr><tr><th>1DS</th><td>33</td><td>10</td><td>–</td><td>52</td><td>10</td><td>–</td></tr><tr><th>2DS</th><td>33</td><td>1</td><td>–</td><td>52</td><td>1</td><td>–</td></tr><tr><th>2DR</th><td>33</td><td>27 (26–29)</td><td>–</td><td>52</td><td>27 (24–28)</td><td>–</td></tr><tr><th>AFS</th><td>33</td><td>2</td><td>–</td><td>52</td><td>2</td><td>–</td></tr><tr><th>AFR</th><td>33</td><td>9</td><td>–</td><td>52</td><td>9 (9–10)</td><td>–</td></tr><tr><th>P</th><td>33</td><td>17 (16–18)</td><td>–</td><td>52</td><td>18 (16–19)</td><td>–</td></tr><tr><th>LL</th><td>15</td><td>72, 73, 74 (71–75)</td><td>–</td><td>31</td><td>70 (68–74)</td><td>–</td></tr><tr><th>Otoliths</th></tr><tr><th>OH</th><td>16</td><td>6.8 (5.1–8.7)</td><td>0.014 (0.011–0.016)</td><td>27</td><td>7.5 (5.6–9.7)</td><td>0.015 (0.013–0.036)</td></tr><tr><th>OL</th><td>17</td><td>14.3 (10.9–7.7)</td><td>0.030 (0.024–0.041)</td><td>27</td><td>14.7 (11.0–18.1)</td><td>0.030 (0.025–0.071)</td></tr><tr><th>OCD</th><td>17</td><td>3.9 (2.6–6.3)</td><td>0.008 (0.006–0.013)</td><td>27</td><td>3.5 (2.3–4.8)</td><td>0.007 (0.005–0.016)</td></tr><tr><th>OrCD</th><td>17</td><td>6.3 (4.9–7.7)</td><td>0.013 (0.010–0.018)</td><td>27</td><td>6.4 (4.3–8.3)</td><td>0.013 (0.010–0.028)</td></tr><tr><th>TOTC</th><td>17</td><td>6.3 (4.5–8.0)</td><td>0.013 (0.011–0.018)</td><td>27</td><td>6.8 (4.8–8.2)</td><td>0.014 (0.011–0.035)</td></tr><tr><th>TOBC</th><td>17</td><td>13.2 (9.7–16.8)</td><td>0.028 (0.023–0.039)</td><td>27</td><td>13.5 (9.8–16.9)</td><td>0.028 (0.023–0.062)</td></tr><tr><th>WC</th><td>17</td><td>1.9 (1.1–2.6)</td><td>0.004 (0.003–0.006)</td><td>27</td><td>2.0 (1.3–2.7)</td><td>0.004 (0.003–0.008)</td></tr><tr><th>OW</th><td>17</td><td>6.1 (4.3–7.4)</td><td>0.013 (0.010–0.022)</td><td>27</td><td>6.1 (1.1–8.6)</td><td>0.013 (0.002–0.028)</td></tr><tr><th>Processes</th><td>17</td><td>5 (3–10)</td><td></td><td>27</td><td>2, 3, 4 (0–8)</td><td></td></tr></tbody></table>
TABLE 4 in Revisiting the description of Atractoscion macrolepis (Perciformes: Sciaenidae): Another argument for comprehensive taxonomy
<p><b>TABLE 4.</b> Standardised coefficients of the 16 transformed morphometric variables for the canonical root, and the eigenvalues and cumulative variance explained by this root, extracted from the Discriminant Functions Analysis separating <i>Atractoscion aequidens</i> and <i>A. macrolepis</i>.</p><table><tbody><tr><th>Variable</th><th>Standardised coefficient</th></tr></tbody><tbody><tr><th><i>TL’ BD’ 2DFL’ CPL’ MCL’ LCLL’ AFBL’ AFL’ PFB’ PFL’ PLFL’ HL’ OD’ SNL’ PSF’ GFL’</i></th><td>-0.287 0.177 -0.239 -0.252 0.612 -0.685 -0.353 0.302 0.470 0.603 -0.455 0.644 -0.367 -0.593 -0.361 0.495</td></tr><tr><th>Eigenvalue Cumulative proportion</th><td>7.337 100%</td></tr></tbody></table>
Table 4 in Temperate grassy wetlands of South Africa: Description, classification and explanatory environmental factors
<p><b>Table 4</b> Description of vegetation types of temperate grassy wetlands.</p><table><tbody><tr><th>No.</th><th>Wetland vegetation type</th><th>No. comm.</th><th>Dominant species</th><th>Vegetation structure</th><th>Environmental conditions</th><th>Distribution</th><th>Comments</th><th>Species diversity</th></tr></tbody><tbody><tr><th>1</th><td>Waterbiesie</td><td>2</td><td><i>Eleocharis dregeana, Leersia</i></td><td>Dense, medium tall sedges or</td><td>Mostly pans, gleyed clay soils,</td><td>Inland parts of Eastern South</td><td><i>Leersia hexandra</i> is the most common</td><td>Median 6</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>dregeana</i></td><td>grasses (20–50 cm tall)</td><td>seasonally or permanently wet</td><td>Africa</td><td>wetland grass in South Africa</td><td>(1–23)</td></tr><tr><th>2</th><td>Pond sedge wetlands</td><td>1</td><td><i>Carex acutiformis</i></td><td>Dense medium tall sedges (30–80</td><td>Mostly valley bottom wetlands, on</td><td>Inland parts of Eastern South</td><td>The species <i>Carex acutiformis</i> is</td><td>Median 4</td></tr><tr><th></th><td></td><td></td><td></td><td>cm tall)</td><td>clay or peat, permanently wet</td><td>Africa, mostly around the</td><td>widely distributed and it is not clear</td><td>(1–18)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>escarpment</td><td>whether it is indigenous to South</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>Africa</td><td></td></tr><tr><th>3</th><td>Grassy everlasting</td><td>1</td><td><i>Aristida junciformis,</i></td><td>Dense short grassland (20–50 cm tall)</td><td>Seasonally or temporarily wet</td><td>Inland parts of Eastern South</td><td>Conspicuous because of the presence</td><td>Median 13</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Helichrysum aureonitens</i></td><td></td><td>grasslands, mostly on loam soils</td><td>Africa, most common around the</td><td>of the everlasting <i>Helichrysum</i></td><td>(5–24)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Drakensberg</td><td><i>aureonitens</i></td><td></td></tr><tr><th>4</th><td>Highveld mixed</td><td>6</td><td><i>Cyperus denudatus,</i></td><td>Dense medium tall to tall sedge or</td><td>Various habitats, mostly in valley</td><td>Widespread in Eastern South</td><td>Few communities are dominated by</td><td>Median 8</td></tr><tr><th></th><td>sedge wetlands</td><td></td><td><i>Schoenoplectus brachyceras,</i></td><td>grassland (20–120 cm tall)</td><td>bottom wetlands and floodplains, on</td><td>Africa, but also in the Cape</td><td>grasses, but the wetter communities</td><td>(1–22)</td></tr><tr><th></th><td></td><td></td><td><i>Juncus effusus</i></td><td></td><td>clay or loam soils of different wetness</td><td></td><td>by sedges and rushes</td><td></td></tr><tr><th>5</th><td>Eragrostis</td><td>1</td><td><i>Eragrostis planiculmis</i></td><td>Dense tall grassland (80–120 cm)</td><td>Temporarily to seasonally wet clay soils</td><td>Inland parts of Eastern South</td><td></td><td>Median 9</td></tr><tr><th></th><td>planiculmis wetlands</td><td></td><td></td><td></td><td></td><td>Africa</td><td></td><td>(3–19)</td></tr><tr><th>6</th><td>Chichi mixed</td><td>2</td><td><i>Arundinella nepalensis,</i></td><td>Dense tall grassland (80–120 cm) or</td><td>Temporarily to seasonally wet loam</td><td>Inland parts of Eastern South</td><td>The bush ‘Chichi’ or ‘Ouhout’ becomes</td><td>Median 11</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Leucosidea sericea</i></td><td>short grassland with shrubs up to 3 m.</td><td>soils, mostly in mountainous terrain</td><td>Africa, most common around the</td><td>dominant in disturbed grasslands, but</td><td>(3–24)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Drakensberg</td><td>also in floodplains and seepages</td><td></td></tr><tr><th>7</th><td>Rooivleigrass</td><td>3</td><td><i>Hemarthria altissima,</i></td><td>Open to dense, medium tall grassland</td><td>Mostly around the edge of pans or</td><td>Inland parts of eastern South</td><td></td><td>Median 9</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Cyperus marginatus,</i></td><td>or sedgeland (30–60 cm)</td><td>valley bottom wetlands, on temporarily</td><td>Africa, extending into the Western</td><td></td><td>(2–34)</td></tr><tr><th></th><td></td><td></td><td><i>Paspalum dilatatum</i></td><td></td><td>to seasonally wet loam soils</td><td>Free State</td><td></td><td></td></tr><tr><th>8</th><td>Red grass wetlands</td><td>1</td><td><i>Themeda triandra</i></td><td>Dense short grassland (20–50 cm tall)</td><td>Temporarily wet grassland areas</td><td>Widespread across the Highveld</td><td>The grass <i>Themeda triandra</i></td><td>Median 11</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>and around the Drakensberg</td><td>represents the most dominant grass</td><td>(3–26)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>species in the upland areas of the</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>Highveld region, and it can deal</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>reasonably well with inundation</td><td></td></tr><tr><th>9</th><td>Cyperus fastigiatus</td><td>1</td><td><i>Cyperus fastigiatus</i></td><td>Dense tall sedgeland (100–180 cm</td><td>Permanently wet areas in valley bottom</td><td>Throughout the country, including</td><td>Different forms of the species occur,</td><td>Median 6</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td>tall)</td><td>wetlands, either on clay or peat</td><td>the Cape and tropical areas, but</td><td>especially in the tropical areas</td><td>(1–16)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>absent from the drier areas</td><td></td><td></td></tr><tr><th>10</th><td>Silver spike grass</td><td>4</td><td><i>Imperata cylindrica,</i></td><td>Medium tall to tall mixed</td><td>Temporarily to seasonally wet,</td><td>Mostly in the Northern Highveld,</td><td><i>Imperata cylindrica</i> is commonly</td><td>Median 10</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Miscanthus junceus</i></td><td>grasslands (50–120 cm)</td><td>mostly sandy areas</td><td>Northern KwaZulu-Natal and in the</td><td>found in disturbed soils, for example</td><td>(2–30)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Cape</td><td>in road verges</td><td></td></tr><tr><th>11</th><td>Eragrostis plana</td><td>1</td><td><i>Eragrostis plana</i></td><td>Open to dense medium tall</td><td>Temporarily or seasonally wet loam</td><td>Inland parts of Eastern South Africa</td><td>Often an indicator of disturbance</td><td>Median 11</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td>grassland</td><td>or clay soils</td><td>as well as the Cape</td><td></td><td>(4–27)</td></tr><tr><th>12</th><td>Common bullrush</td><td>1</td><td><i>Typha capensis</i></td><td>Dense tall reedlands</td><td>Seasonally to permanently wet clay or</td><td>Common in Northern South Africa,</td><td>The dominant species occurs often in</td><td>Median 4.5</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td></td><td>peat soils, often with high nutrient</td><td>Natal and the Cape</td><td>urban wetlands as it can deal very</td><td>(1–18)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>loads</td><td></td><td>well with pollution and high nutrient</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>loads</td><td></td></tr><tr><th>13</th><td>Common reed</td><td>1</td><td><i>Phragmites australis</i></td><td>Open to dense tall reedlands</td><td>Many different habitats, mostly</td><td>Throughout the whole country</td><td>One of the most competitive wetland</td><td>Median 4</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td></td><td>seasonally to permanently wet, also</td><td></td><td>plants. Benefits from high nutrient</td><td>(1–30)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>dealing well with salinity</td><td></td><td>loads and stabilized water levels.</td><td></td></tr></tbody></table>
Table 2 in Ultrastructure of somatic embryo development and plant propagation for Lachenalia montana
<p><b>Table 2</b> Enhancement of somatic embryos and germination frequency in cell suspension culture from friable embryogenic callus (FEC) of L. montana.</p><table><tbody><tr><th>Sucrose (g L <i>−</i> 1) + PGR (μM) in solid MS medium</th><th>PGR (μM) in liquid MS medium</th><th>Liquid MS medium (MSL)</th><th>Number of SEs/SCV developmental stage</th><th>Germination (%)</th></tr></tbody><tbody><tr><th>6 weeks of culture</th><td>4 weeks of culture</td><td>2 weeks of culture</td><td>Globular</td><td>Different stages of embryo*</td><td></td></tr><tr><th>35 + 10 picloram + 2 BA</th><td>1 picloram</td><td>MSL</td><td>10.0 e</td><td>6.4 e</td><td>0</td></tr><tr><td>1 2,4-D</td><td>MSL</td><td>14.4 cd</td><td>9.0 cd</td><td>0</td></tr><tr><td>1 2,4-D + 0.5 BA</td><td>MSL</td><td>15.0 cd</td><td>9.8 cd</td><td>7.2 e</td></tr><tr><td>1 2,4-D + 0.5 <i>m</i> TR</td><td>MSL</td><td>7.8 f</td><td>6.0 e</td><td>8.6 de</td></tr><tr><td>1 2,4-D + 0.5 TDZ</td><td>MSL</td><td>18.0 b</td><td>12.4 b</td><td>14.0 ab</td></tr><tr><th>35 + 10 2,4-D + 2 TDZ</th><td>1 picloram</td><td>MSL</td><td>6.8 fg</td><td>3.0 f</td><td>0</td></tr><tr><td>1 2,4-D</td><td>MSL</td><td>16.0 cd</td><td>6.8 e</td><td>0</td></tr><tr><td>1 2,4-D + 0.5 BA</td><td>MSL</td><td>18.4 b</td><td>10.0 c</td><td>11.4 c</td></tr><tr><td>1 2,4-D + 0.5 <i>m</i> TR</td><td>MSL</td><td>10.2 e</td><td>6.8 e</td><td>14.3 ab</td></tr><tr><td>1 2,4-D + 0.5 TDZ</td><td>MSL</td><td>21.4 a</td><td>14.6 a</td><td>15.2 a</td></tr></tbody></table><p>PGR = Plant growth regulator. <sub>MSL</sub> = Liquid MS medium.SEs = Somatic embryos.SCV = Settled cell volume.*Different stages of embryo = pear-shaped, early torpedo-shaped, torpedoshaped and cotyledonary-stage embryos. Values with the means derived from 5 replicate (each 500 mg FEC) with 1000 μL SCV of embryogenic suspension cells per replicate. Mean values followed by same letters in each column are not significantly different according to the Duncan's multiple range test at 5% level.</p>
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