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214 results for “Mountain areas”
FIGURE 37 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 37. Altitudinal variation in males of Neritius abyssinicus. Specimens from higher elevations (left) are significantly larger than those from lower altitudes (right) (Table 4) and are slightly differently coloured. Scale bar represents 1 cm.
FIGURE 2 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 2. Habitats at collecting sites. a: Sheko Forest (1570 m); b: Makira Forest (1615 m); c: Dembi Forest (1260 m); d: Bebeka Plantation (1370 m).
FIGURE 3 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 3. Habitats at collecting sites. a: Komba Forest (1860 m); b: Hana Wetland (2425 m); c: Bamboo Forest (2620 m).
FIGURE 35 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 35. Eyprepocnemis plorans ibandana, Dembi Forest (1260 m), Ethiopia. Scale bar represents 1 cm.
FIGURE 10 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 10. Anoedopoda lamellata, Bonga Village (1700 m), Ethiopia (same specimen). Scale bar represents 1 cm.
FIGURE 4 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 4. Habitats at collecting sites. a: Shorori Wetland (1610 m); b: waterfall at Dembi Forest (1260 m); c: inside the bamboo forest at Bamboo Forest (2620 m).
FIGURE 11 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 11. Stridulatory file of Peropyrrhicia. The short prominence on the right tegmen, to which the file is rubbing during song, is shown (bottom right).
FIGURE 24 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 24. Habitus of male (holotype) and female (paratype) Peropyrrhicia attilioi n. sp., Komba Forest (1990 m), Ethiopia. Scale bar represents 1 cm.
FIGURE 9 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 9. Thyridorhoptrum baileyi, Dembi Forest (1260 m), Ethiopia (same specimen). Scale bar represents 1 cm.
FIGURE 32 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 32. Oxya hyla brachypterous form, Shorori wetland (1610 m), Ethiopia. Scale bar represents 1 cm.
FIGURE 25 in Orthoptera (Insecta: Tettigonioidea, Pyrgomorphoidea, Acridoidea) of Kafa Biosphere Reserve, Bale Mountains National Park and other areas of conservation interest in Ethiopia
FIGURE 25. Habitats of Peropyrrhicia attilioi n. sp., Komba Forest (1990 m), Ethiopia. The specimens were collected on lichens and on leaves of Phoenix palms up to three meters high.
FIGURES 13–19 in Soil mites of the families Ascidae, Blattisociidae and Melicharidae (Acari: Mesostigmata) from mountainous areas of Colombia
FIGURES 13–19. Protogamasellus caleraensis sp. nov. Female. 13. Chelicera; 14. Epistome; 15. Hypostome and proximal palp segments; 16. Dorsal view; 17. Ventral view; 18. Spermathecal apparatus; 19. Tarsus III.
FIGURES 29–34 in Soil mites of the families Ascidae, Blattisociidae and Melicharidae (Acari: Mesostigmata) from mountainous areas of Colombia
FIGURES 29–34. Proctolaelaps colombianus sp. nov. Female. 29. Chelicera; 30. Epistome; 31. Hypostome and proximal palp segment; 32. Dorsal idiosoma; 33. Ventral idiosoma; 34. Tarsus IV.
FIGURES 7–12 in Soil mites of the families Ascidae, Blattisociidae and Melicharidae (Acari: Mesostigmata) from mountainous areas of Colombia
FIGURES 7–12. Gamasellodes intermedius sp. nov. Female. 7. Chelicera; 8. Epistome; 9. Hypostome and proximal palp segments; 10. Dorsal view; 11. Ventral view; 12. Tarsus II.
FIGURES 1–6 in Soil mites of the families Ascidae, Blattisociidae and Melicharidae (Acari: Mesostigmata) from mountainous areas of Colombia
FIGURES 1–6. Gamasellodes andinus sp. nov. Female. 1. Chelicera; 2. Epistome; 3. Hypostome and proximal palp segments; 4. Dorsal view; 5. Ventral view; 5a. Variation of sternal shield 6. Tarsus II.
FIGURES 20–25 in Soil mites of the families Ascidae, Blattisociidae and Melicharidae (Acari: Mesostigmata) from mountainous areas of Colombia
FIGURES 20–25. Cheiroseius mesae sp. nov. Female. 20. Chelicera; 21. Epistome; 22. Hypostome and proximal palp segments; 23. Dorsal idiosoma; 24. Ventral idiosoma; 25. Spermathecal apparatus.
TABLE 1 in Diversity of wood-decaying fungi in Zixishan area (Hengduan Mountains), Yunnan Province, China
<p><b>TABLE 1.</b> Names, sample numbers and corresponding GenBank accession numbers of the taxa used in this study.</p><table><tbody><tr><th>Species name</th><th>Sample no.</th><th>GenBank Accession No. ITS</th><th>References</th></tr></tbody><tbody><tr><th><i>Aleurodiscus isabellinus</i></th><td>CLZhao 21151</td><td>OM955789</td><td>Present study</td></tr><tr><th><i>A. isabellinus</i></th><td>He 5294</td><td>MH109053</td><td>Tian <i>et al.</i> (2018)</td></tr><tr><th><i>A. mirabilis</i></th><td>CLZhao 6781</td><td>OM955790</td><td>Present study</td></tr><tr><th><i>A. mirabilis</i></th><td>He 3730</td><td>KX306878</td><td>Dai & He (2017)</td></tr><tr><th><i>Antrodia xantha</i></th><td>CLZhao 6685</td><td>OM955795</td><td>Present study</td></tr><tr><th><i>A. xantha</i></th><td>Dai 12984</td><td>MG787578</td><td>Unpublished</td></tr><tr><th><i>Butyrea japonica</i></th><td>CLZhao 7218</td><td>OM955796</td><td>Present study</td></tr><tr><th><i>B. japonica</i></th><td>SFC20170823-29</td><td>MN973797</td><td>Lee <i>et al.</i> (2020)</td></tr><tr><th><i>Byssomerulius corium</i></th><td>CLZhao 6910</td><td>OM955797</td><td>Present study</td></tr><tr><th><i>B. corium</i></th><td>Wu 1207-55</td><td>MZ636932</td><td>Chen <i>et al.</i> (2021)</td></tr><tr><th><i>Ceriporia nanlingensis</i></th><td>CLZhao 7208</td><td>OM955803</td><td>Present study</td></tr><tr><th><i>C. nanlingensis</i></th><td>Dai8173</td><td>JX623942</td><td>Jia <i>et al.</i> (2014)</td></tr><tr><th><i>C. pseudocystidiata</i></th><td>CLZhao 7682</td><td>OM955808</td><td>Present study</td></tr><tr><th><i>C. pseudocystidiata</i></th><td>Cui6878</td><td>JX623943</td><td>Jia <i>et al.</i> (2014)</td></tr><tr><th><i>Ceriporiopsis semisupina</i></th><td>CLZhao 7426</td><td>OM955809</td><td>Present study</td></tr><tr><th><i>Ce. semisupina</i></th><td>Chen 3327</td><td>MZ636937</td><td>Chen <i>et al.</i> (2021)</td></tr><tr><th><i>Cerrena zonata</i></th><td>CLZhao 7676</td><td>OM955819</td><td>Present study</td></tr><tr><th><i>Cer. zonata</i></th><td>Dai7821</td><td>KC485529</td><td>Yuan (2014)</td></tr><tr><th><i>Coltricia crassa</i></th><td>CLZhao 7157</td><td>OM955820</td><td>Present study</td></tr><tr><th><i>C. crassa</i></th><td>Dai 15163</td><td>KU360679</td><td>Bian & Dai (2015)</td></tr><tr><th><i>Crepatura ellipsospora</i></th><td>CLZhao 6851</td><td>OM955821</td><td>Present study</td></tr><tr><th><i>C. ellipsospora</i></th><td>CLZhao 697</td><td>MK343695</td><td>Ma & Zhao (2019)</td></tr><tr><th><i>Crustodontia chrysocreas</i></th><td>CLZhao 21107</td><td>OM955826</td><td>Present study</td></tr><tr><th><i>C. chrysocreas</i></th><td>CBS 125889</td><td>MH864087</td><td>Vu <i>et al.</i> (2019)</td></tr><tr><th><i>Crustomyces subabruptus</i></th><td>CLZhao 21086</td><td>OM955828</td><td>Present study</td></tr><tr><th><i>Cr. subabruptus</i></th><td>K(M):249975</td><td>MZ159685</td><td>Unpublished</td></tr><tr><th><i>Cyanosporus submicroporus</i></th><td>CLZhao 6920</td><td>OM955827</td><td>Present study</td></tr><tr><th><i>C. submicroporus</i></th><td>Cui 18156</td><td>MW182186</td><td>Liu <i>et al.</i> (2022)</td></tr><tr><th><i>Dentipellicula leptodon</i></th><td>CLZhao 6818</td><td>OM955830</td><td>Present study</td></tr><tr><th><i>D. leptodon</i></th><td>CBS 125879</td><td>MH864083</td><td>Vu <i>et al.</i> (2019)</td></tr><tr><th><i>Diplomitoporus flavescens</i></th><td>CLZhao 7009</td><td>OM955844</td><td>Present study</td></tr><tr><th><i>D. flavescens</i></th><td>IBL66</td><td>MZ410695</td><td>Unpublished</td></tr><tr><th><i>Fomitopsis pinicola</i></th><td>CLZhao 7716</td><td>OM955845</td><td>Present study</td></tr><tr><th><i>F. pinicola</i></th><td>Cui 10312</td><td>KR605781</td><td>Han <i>et al.</i> (2016)</td></tr><tr><th><i>Fuscoporia chinensis</i></th><td>CLZhao 21152</td><td>OM955848</td><td>Present study</td></tr><tr><th><i>F. chinensis</i></th><td>Dai 15713</td><td>MN816721</td><td>Chen <i>et al.</i> (2020)</td></tr><tr><th><i>Gloeocystidiellum porosum</i></th><td>CLZhao 6984</td><td>OM955849</td><td>Present study</td></tr><tr><th><i>G. porosum</i></th><td>CBS 189.56</td><td>MH857576</td><td>Vu <i>et al.</i> (2019)</td></tr><tr><th><i>Heterobasidion insulare</i></th><td>CLZhao 6829</td><td>OM955850</td><td>Present study</td></tr><tr><th><i>H. insulare</i></th><td>Dai 13933</td><td>MT146489</td><td>Yuan <i>et al.</i> (2021)</td></tr><tr><th><i>Hydnophanerochaete odontoidea</i></th><td>CLZhao 6785</td><td>OM955750</td><td>Present study</td></tr><tr><th><i>H. odontoidea</i></th><td>CLZhao 4036</td><td>MH784927</td><td>Shen <i>et al.</i> (2018)</td></tr><tr><th><i>Hydnoporia corrugata</i></th><td>CLZhao 7171</td><td>OM955854</td><td>Present study</td></tr><tr><th><i>Hy. corrugata</i></th><td>HHB 19233</td><td>MW740292</td><td>Unpublished</td></tr><tr><th><i>Hy. yasudae</i></th><td>CLZhao 21214</td><td>OM955855</td><td>Present study</td></tr><tr><th><i>Hy. yasudae</i></th><td>Miettinen X2653</td><td>MK514597</td><td>Miettinen <i>et al.</i> (2019)</td></tr><tr><th><i>Hymenochaete cruenta</i></th><td>CLZhao 21195</td><td>OM955856</td><td>Present study</td></tr><tr><th><i>H. cruenta</i></th><td>He 766</td><td>JQ279595</td><td>He & Dai (2012)</td></tr><tr><th><i>H. minor</i></th><td>CLZhao 7197</td><td>OM955857</td><td>Present study</td></tr><tr><th><i>H. minor</i></th><td>He 933</td><td>JQ279555</td><td>He & Dai (2012)</td></tr><tr><th><i>H. rheicolor</i></th><td>CLZhao 6801</td><td>OM955858</td><td>Present study</td></tr><tr><th><i>H. rheicolor</i></th><td>Cui 8317</td><td>JQ279529</td><td>He & Dai (2012)</td></tr><tr><th><i>H. xerantica</i></th><td>CLZhao 7141</td><td>OM955861</td><td>Present study</td></tr><tr><th><i>H. xerantica</i></th><td>Cui 9209</td><td>JQ279519</td><td>He & Dai (2012)</td></tr><tr><th><i>Hyphoderma cremeoalbum</i></th><td>CLZhao 17007</td><td>OM955862</td><td>Present study</td></tr><tr><th><i>H. cremeoalbum</i></th><td>NH 11538</td><td>DQ677492</td><td>Larsson (2007)</td></tr><tr><th><i>H. crystallinum</i></th><td>CLZhao 15841</td><td>MW917165</td><td>Present study</td></tr><tr><th><i>H. crystallinum</i></th><td>CLZhao 18459</td><td>MW917166</td><td>Guan & Zhao (2021a)</td></tr><tr><th><i>H. fissuratum</i></th><td>CLZhao 6731</td><td>MT791331</td><td>Present study</td></tr><tr><th><i>H. fissuratum</i></th><td>CLZhao 6726</td><td>MT791330</td><td>Ma <i>et al.</i> (2021)</td></tr><tr><th><i>H. floccosum</i></th><td>CLZhao 17215</td><td>MW301687</td><td>Present study</td></tr><tr><th><i>H. floccosum</i></th><td>CLZhao 17129</td><td>MW301683</td><td>Guan & Zhao (2021a)</td></tr><tr><th><i>H. membranacea</i></th><td>CLZhao 5844</td><td>MW917167</td><td>Present study</td></tr><tr><th><i>H. membranacea</i></th><td>CLZhao 6971</td><td>MW917168</td><td>Guan & Zhao (2021a)</td></tr><tr><th><i>H. microporoides</i></th><td>CLZhao 8695</td><td>MW917170</td><td>Present study</td></tr><tr><th><i>H. microporoides</i></th><td>CLZhao 6857</td><td>MW917169</td><td>Guan & Zhao (2021b)</td></tr><tr><th><i>H. moniliforme</i></th><td>CLZhao 21162</td><td>OM955863</td><td>Present study</td></tr><tr><th><i>H. moniliforme</i></th><td>Wu 0211-46</td><td>KC928284</td><td>Yurchenko & Wu (2015)</td></tr><tr><th><i>H. mopanshanense</i></th><td>CLZhao 6498</td><td>MT791329</td><td>Present study</td></tr><tr><th><i>H. mopanshanense</i></th><td>CLZhao 6493</td><td>MT791328</td><td>Ma <i>et al.</i> (2021)</td></tr><tr><th><i>H. sinense</i></th><td>CLZhao 7963</td><td>MW301679</td><td>Present study</td></tr><tr><th><i>H. sinense</i></th><td>CLZhao 7981</td><td>MW301680</td><td>Guan & Zhao (2021b)</td></tr><tr><th><i>H. tenuissimum</i></th><td>CLZhao 16210</td><td>MW443050</td><td>Present study</td></tr><tr><th><i>H. tenuissimum</i></th><td>CLZhao 7003</td><td>MW443048</td><td>Guan & Zhao (2021b)</td></tr><tr><th><i>H. transiens</i></th><td>CLZhao 1667</td><td>MT955166</td><td>Present study</td></tr><tr><th><i>H. transiens</i></th><td>NH 12304</td><td>DQ677504</td><td>Larsson (2007)</td></tr><tr><th><i>Hyphodermella zixishanensis</i></th><td>CLZhao 7412</td><td>MZ305282</td><td>Present study</td></tr><tr><th><i>Hy. zixishanensis</i></th><td>CLZhao 7124</td><td>MZ305276</td><td>Wang <i>et al.</i> (2021b)</td></tr><tr><th><i>Hy. aurantiaca</i></th><td>CLZhao 10521</td><td>MW209029</td><td>Present study</td></tr><tr><th><i>Hy. aurantiaca</i></th><td>CLZhao 10500</td><td>MW209025</td><td>Wang & Zhao (2021a)</td></tr><tr><th><i>Hyphodontia tropica</i></th><td>CLZhao 6714</td><td>OM955867</td><td>Present study</td></tr><tr><th><i>Hyp. tropica</i></th><td>CLZhao 6716</td><td>OM955868</td><td>Present study</td></tr><tr><th><i>Leptoporus mollis</i></th><td>CLZhao 7427</td><td>OM955917</td><td>Present study</td></tr><tr><th><i>L. mollis</i></th><td>Dai 21062</td><td>MW377302</td><td>Liu <i>et al.</i> (2023)</td></tr><tr><th><i>Lyomyces cremeus</i></th><td>CLZhao 7281</td><td>OM955918</td><td>Present study</td></tr><tr><th><i>L. cremeus</i></th><td>CLZhao 7244</td><td>OM955921</td><td>Present study</td></tr><tr><th><i>L. cremeus</i></th><td>CLZhao 7285</td><td>OM955919</td><td>Present study</td></tr><tr><th><i>L. cremeus</i></th><td>CLZhao 2812</td><td>MN945973</td><td>Zhao & Cui (2013)</td></tr><tr><th><i>L. cremeus</i></th><td>CLZhao 7294</td><td>OM955920</td><td>Present study</td></tr><tr><th><i>L. cremeus</i></th><td>CLZhao 4138</td><td>MN945974</td><td>Zhao & Cui (2013)</td></tr><tr><th><i>L. crustosus</i></th><td>CLZhao 6897</td><td>OM955922</td><td>Present study</td></tr><tr><th><i>L. crustosus</i></th><td>CLZhao 7274</td><td>OM955923</td><td>Present study</td></tr><tr><th><i>L. orientalis</i></th><td>CLZhao 7132</td><td>OM955926</td><td>Present study</td></tr><tr><th><i>L. orientalis</i></th><td>KAS-GEL 3376</td><td>DQ340325</td><td>Yurchenko <i>et al.</i> (2017)</td></tr><tr><th><i>L. vietnamensis</i></th><td>CLZhao 7100</td><td>OM955927</td><td>Present study</td></tr><tr><th><i>L. vietnamensis</i></th><td>TNM F9073</td><td>JX175044</td><td>Yurchenko & Wu (2015)</td></tr><tr><th><i>Megasporia major</i></th><td>CLZhao 7064</td><td>OM955928</td><td>Present study</td></tr><tr><th><i>M. major</i></th><td>GC 1407-21</td><td>KY688205</td><td>Chen <i>et al.</i> (2018)</td></tr><tr><th><i>Peniophora versiformis</i></th><td>CLZhao 7051</td><td>OM955931</td><td>Present study</td></tr><tr><th><i>P. versiformis</i></th><td>CBS 361.54</td><td>MH857362</td><td>Vu <i>et al.</i> (2019)</td></tr><tr><th><i>Peniophorella fissurata</i></th><td>CLZhao 7290</td><td>OM955718</td><td>Present study</td></tr><tr><th><i>Pe. fissurata</i></th><td>CLZhao 9421</td><td>MN864260</td><td>Guan <i>et al.</i> (2020)</td></tr><tr><th><i>Pe. praetermissa</i></th><td>CLZhao 21158</td><td>OM955719</td><td>Present study</td></tr><tr><th><i>Pe. praetermissa</i></th><td>NH 7827</td><td>DQ647460</td><td>Hallenberg <i>et al.</i> (2007)</td></tr><tr><th><i>Pe. pubera</i></th><td>CLZhao 7509</td><td>OM955722</td><td>Present study</td></tr><tr><th><i>Pe. pubera</i></th><td>NH 10512</td><td>DQ647505</td><td>Hallenberg <i>et al.</i> (2007)</td></tr><tr><th><i>Pe. rude</i></th><td>CLZhao 7142</td><td>OM955723</td><td>Present study</td></tr><tr><th><i>Pe. rude</i></th><td>Wu 0104-3</td><td>DQ647495</td><td>Hallenberg <i>et al.</i> (2007)</td></tr><tr><th><i>Pe. subpraetermissa</i></th><td>CLZhao 6882</td><td>OM955728</td><td>Present study</td></tr><tr><th><i>Pe. subpraetermissa</i></th><td>Wu 950627</td><td>DQ647493</td><td>Hallenberg <i>et al.</i> (2007)</td></tr><tr><th><i>Phanerochaete concrescens</i></th><td>CLZhao 7002</td><td>OM955732</td><td>Present study</td></tr><tr><th><i>P. concrescens</i></th><td>He 4657</td><td>MT235662</td><td>Unpublished</td></tr><tr><th><i>P. pruinosa</i></th><td>CLZhao 7713</td><td>MZ435347</td><td>Present study</td></tr><tr><th><i>P. pruinosa</i></th><td>CLZhao 7712</td><td>MZ435346</td><td>Wang & Zhao (2021b)</td></tr><tr><th><i>P. rhizomorpha</i></th><td>CLZhao 10470</td><td>MZ435348</td><td>Present study</td></tr><tr><th><i>P. rhizomorpha</i></th><td>CLZhao 10477</td><td>MZ435349</td><td>Wang & Zhao (2021b)</td></tr><tr><th><i>P. sordida</i></th><td>CLZhao 7486</td><td>OM955733</td><td>Present study</td></tr><tr><th><i>P. sordida</i></th><td>He 5400</td><td>MT235676</td><td>Unpublished</td></tr><tr><th><i>Phlebia acerina</i></th><td>CLZhao 7664</td><td>OM955744</td><td>Present study</td></tr><tr><th><i>P. acerina</i></th><td>HHB 11146</td><td>KP135372</td><td>Floudas & Hibbett (2015)</td></tr><tr><th><i>Phlebiopsis crassa</i></th><td>CLZhao 7130</td><td>OM955764</td><td>Present study</td></tr><tr><th><i>Ph. crassa</i></th><td>FP 102496</td><td>AY219341</td><td>De Koker <i>et al.</i> (2003)</td></tr><tr><th><i>Ph. yunnanensis</i></th><td>CLZhao 7367</td><td>OM955788</td><td>Present study</td></tr><tr><th><i>Ph. yunnanensis</i></th><td>CLZhao 3900</td><td>MH744141</td><td>Zhao <i>et al.</i> (2019)</td></tr><tr><th><i>Porodaedalea chinensis</i></th><td>CLZhao 7487</td><td>OM955768</td><td>Present study</td></tr><tr><th><i>P. chinensis</i></th><td>Dai 16864</td><td>KX852282</td><td>Dai <i>et al.</i> (2017)</td></tr><tr><th><i>Postia caesia</i></th><td>CLZhao 6904</td><td>OM955769</td><td>Present study</td></tr><tr><th><i>Po. caesia</i></th><td>K(M) 31967</td><td>AY599567</td><td>Yao <i>et al.</i> (2005)</td></tr><tr><th><i>Scytinostroma phaeosarcum</i></th><td>CLZhao 21302</td><td>OM955775</td><td>Present study</td></tr><tr><th><i>S. phaeosarcum</i></th><td>CBS 728.81</td><td>MH861463</td><td>Vu <i>et al.</i> (2019)</td></tr><tr><th><i>Skeletocutis nivea</i></th><td>CLZhao 7034</td><td>OM955776</td><td>Present study</td></tr><tr><th><i>S. nivea</i></th><td>FD-5</td><td>KP135331</td><td>Floudas & Hibbett (2015)</td></tr><tr><th><i>S. pseudo-odora</i></th><td>CLZhao 6938</td><td>OM955777</td><td>Present study</td></tr><tr><th><i>S. pseudo-odora</i></th><td>Dai 16527</td><td>KY245961</td><td>Fan <i>et al.</i> (2017)</td></tr><tr><th><i>Steccherinum nitidum</i></th><td>CLZhao 7198</td><td>MZ713646</td><td>Present study</td></tr><tr><th><i>S. nitidum</i></th><td>KHL 11903</td><td>JN710560</td><td>Miettinen <i>et al.</i> (2012)</td></tr><tr><th><i>Stereum hirsutum</i></th><td>CLZhao 7420</td><td>OM955779</td><td>Present study</td></tr><tr><th><i>St. hirsutum</i></th><td>CBS 108532</td><td>MH862810</td><td>Vu <i>et al.</i> (2019)</td></tr><tr><th><i>St. sanguinolentum</i></th><td>CLZhao 6856</td><td>OM955780</td><td>Present study</td></tr><tr><th><i>S. sanguinolentum</i></th><td>CLZhao 7581</td><td>OM955786</td><td>Present study</td></tr><tr><th><i>Tyromyces kmetii</i></th><td>CLZhao 7305</td><td>OM955787</td><td>Present study</td></tr><tr><th><i>T. kmetii</i></th><td>Dai 12403</td><td>KF698747</td><td>Unpublished</td></tr></tbody></table><p>......continued on the next page</p><p>......continued on the next page</p>
Subspecies and Distribution. U. a. arctos Linnaeus, 1758 — Europe and W Russia. U. a. alascensis Merriam, 1896 — most of Alaska (excluding Alaska Peninsula, SE panhandle & Kodiak Island group). U. a. beringianus Middendorff, 1853 — NE Russia (Kamchatka Peninsula & N Kuril Islands northward through the Koryak Autonomous District, and along W coast of the Sea of Okhotsk). U. a. collaris Cuvier, 1824 — Russia (Siberia, from E of the Yenisey River to the Bering Sea, but excluding Kamchatka and more southern parts of the Russian Far East), N Mongolia. U. a. dalli Merriam, 1896 — SE Alaska (N of Alexander Archipelago). U. a. gyas Merriam, 1902 — Alaska peninsula. U. a. horribilis Ord, 1815 —W Canada (Yukon, North-West Territories, British Columbia & Alberta), inland W USA (extirpated from S Wyoming to Mexico). U. a. isabellinus Horsfield, 1826 — N India, Pakistan, Afghanistan, N to Kazakhstan and Mongolia (Gobi Desert). U. a. lasiotus Gray, 1867 — Russia (Southern Kuril Islands, Sakhalin, Ussuri/Amur river region of the Russian Far East), NE China, North Korea, and Japan (Hokkaido). U. a. middendorffi Merriam, 1896 — Alaska (Kodiak Island & nearby islands). U. a. pruinosus Blyth, 1853 — Tibetan Plateau, China, N Nepal. U. a. sitkensis Merriam, 1896 — SE Alaska (Alexander Archipelago & adjacent coastal area). U. a. stikeenensis Merriam, 1914 — W Canada (W British Columbia), and formerly W USA (W Washington and Oregon). U. a. syriacus Hemprich & Ehrenberg, 1828 — Middle East, from Turkey to Iran (extirpated in Syria), Caucasus mountains of Russia, Georgia, Armenia and Azerbaijan. in Ursidae
Subspecies and Distribution. U. a. arctos Linnaeus, 1758 — Europe and W Russia. U. a. alascensis Merriam, 1896 — most of Alaska (excluding Alaska Peninsula, SE panhandle & Kodiak Island group). U. a. beringianus Middendorff, 1853 — NE Russia (Kamchatka Peninsula & N Kuril Islands northward through the Koryak Autonomous District, and along W coast of the Sea of Okhotsk). U. a. collaris Cuvier, 1824 — Russia (Siberia, from E of the Yenisey River to the Bering Sea, but excluding Kamchatka and more southern parts of the Russian Far East), N Mongolia. U. a. dalli Merriam, 1896 — SE Alaska (N of Alexander Archipelago). U. a. gyas Merriam, 1902 — Alaska peninsula. U. a. horribilis Ord, 1815 —W Canada (Yukon, North-West Territories, British Columbia & Alberta), inland W USA (extirpated from S Wyoming to Mexico). U. a. isabellinus Horsfield, 1826 — N India, Pakistan, Afghanistan, N to Kazakhstan and Mongolia (Gobi Desert). U. a. lasiotus Gray, 1867 — Russia (Southern Kuril Islands, Sakhalin, Ussuri/Amur river region of the Russian Far East), NE China, North Korea, and Japan (Hokkaido). U. a. middendorffi Merriam, 1896 — Alaska (Kodiak Island & nearby islands). U. a. pruinosus Blyth, 1853 — Tibetan Plateau, China, N Nepal. U. a. sitkensis Merriam, 1896 — SE Alaska (Alexander Archipelago & adjacent coastal area). U. a. stikeenensis Merriam, 1914 — W Canada (W British Columbia), and formerly W USA (W Washington and Oregon). U. a. syriacus Hemprich & Ehrenberg, 1828 — Middle East, from Turkey to Iran (extirpated in Syria), Caucasus mountains of Russia, Georgia, Armenia and Azerbaijan.
Distribution. Two disjunct areas across the lowland rainforest belt of W Africa (Guinea, Sierra Leone, Liberia, Ivory Coast, Ghana, Togo & Benin) and C Africa through the Congo Basin (Cameroon, Gabon, Republic of the Congo, DR Congo, Central African Republic & extreme SW Sudan), and five very small disjunct populations in mountainous areas in C Kenya. in Bovidae
Distribution. Two disjunct areas across the lowland rainforest belt of W Africa (Guinea, Sierra Leone, Liberia, Ivory Coast, Ghana, Togo & Benin) and C Africa through the Congo Basin (Cameroon, Gabon, Republic of the Congo, DR Congo, Central African Republic & extreme SW Sudan), and five very small disjunct populations in mountainous areas in C Kenya.
Subspecies and Distribution. S. s. scrofa Linnaeus, 1758 — W Europe, from Denmark, Germany, Poland, and Czech Republic to N Italy and N Iberian Peninsula; possibly also Albania. The taxonomic status of animals in Austria, Switzerland, Slovenia, and Slovakia is unclear but presumably these populations are included in scrofa, as are the populations of Sweden, Finland, and the Baltic states. However, restocking of once depleted populations, for example in Italy, has likely involved the introduction and mixing of this subspecies with other subspecies, such as attila. S. s. affinis Gray, 1847 — S India and Sri Lanka. S. s. algirus Loche, 1867 — Tunisia, Algeria, and Morocco, on the coastal side of the mountains or in the low montane areas. S. s. attila Thomas, 1912 — Hungary, Ukraine, C & S Belarus, Romania, Moldova, and S Russia towards the N flank of the Caucasus, but not including the Transcaucasian countries of Georgia, Armenia, and Azerbaijan. The range possibly extends as far S as the Mesopotamian Delta in Iraq, in which case it would likely include W & SW Iran, and possibly E Turkey and Syria, where it borders with lybicus. Such a range could not be easily reconciled with a statement by Groves that "the difference between pigs from N and S of the Caucasus is quite striking; Transcaucasian boars are certainly not attila." This subspecies may also extend into C Asia and include Kazakhstan, Uzbekistan, and Turkmenistan, but no data exist to support this. S. s. baeticus Thomas, 1912 — originally described from Coto Donana, S Spain, and later merged with meridionalis; also S Portugal. Unless evidence is found that these Italian and Iberian populations are the relics of a much larger formerly contiguous range, this subspecies should be kept as distinct. S. s. coreanus Heude, 1897 — Korean Peninsula. S. s. eristatus Wagner, 1839 — Himalayas S to C India and E to Indochina (N of the Kra Isthmus). S. s. davidi Groves, 1981 — the arid zone from E Iran to Gujarat, including Pakistan and NW India, and perhaps N to Tajikistan. S. s. leucomystax Temminck, 1842 — main Is ofJapan (Honshu, Shikoku, Kyushu, Nakadori, Hiburijima, Tojima, Kushima, and other smaller Is). S. s. lybicus Gray, 1868 — Bulgaria, Greece, Turkey, Syria, Jordan, Israel, Palestine, in the past also in Lybia, and Egypt. The former Yugoslavia was included in its range, which would suggest that now Slovenia, Serbia, Croatia, Bosnia and Herzegovina, Montenegro, and Kosovo are within the range of this subspecies, although the exact boundaries are unclear. Pigs from Albania have been assigned to S. s. scrofa. S. s. majori De Beaux & Festa, 1927 — C & S Italian Peninsula. S. s. menidionalis Forsyth Major, 1882 — Corsica and Sardinia, with the proviso that the two populations are very likely to be introduced or feral. S. s. moupinensis Milne-Edwards, 1871 — China, S to Vietnam and W to Sichuan. S. s. nigripes Blanford, 1875 — the flanks of the Tianshan mountains in Kyrgyzstan and NW China (Xinjiang). An animal photographed in NE Iran (Golestan) looked like this subspecies. S. s. nukiuanus Kuroda, 1924 — Iriomote, Ishigaki, Okinawa, Tokunoshima, Amamioshima, and Kakerome Is in the Ryukyu chain in extreme S Japan, though some of these populations have hybridized with introduced domesticates. S. s. sibiricus Staffe, 1922 — Mongolia and Transbaikal (S & E of Lake Baikal). S. s. tawvanus Swinhoe, 1863 — Taiwan. S. s. ussuricus Heude, 1888 — far E Russia and the Manchurian region (China). Korean populations were previously included in this subspecies, but based on new evidence, the Korean taxon seems more similar to moupinensis. S. s. vittatus Boie, 1828 — Malay Peninsula, S of the Isthmus of Kra, the offshore islands of Terutai and Langkawi, Sumatra, Riau Archipelago, Java, Bali, and a range of smaller islands around these, including Babi, Bakong, Batam, Bawean, Bengkalis, Bintan, Bulan, Bunguran, Cuyo, Deli, Durian, Enggano, Galang, Jambongan, Karimon (Riau Is), Kundur, Lagong, Laut, Lingga, Lingung, Mapor, Moro Kecil, North Pagai, Nias, Panaitan, Payong, Penang, Pinie, Rupat, Siantan, Siberut, Simeulue, Singkep, Sugi, Sugi Bawa, Telibon, Tinggi, Tuangku, and the Tambelan Is. This species was originally present from the British Is in the extreme W, through Eurasia from S Scandinavia to S Siberia, extending as far E as Korea and Japan, and SE into some of the Sunda Is and Taiwan. In the S the species ranged along the Nile Valley to Khartoum, and N of the Sahara in Africa, more orless following the continental coasts of S, E, and SE Asia. Within this range it was absent only from extremely dry deserts, e.g. the driest regions of Mongolia and in China W of Sichuan; and alpine zones, such as the high altitudes of Pamir and Tien Shan. In recent centuries, the range of S. scrofa has changed dramatically because of hunting and changes in available habitat. The species disappeared from the British Is in the 17" century, from Denmark in the 19" century, and was greatly reduced in range and numbers in the 20" century from areas as distant as Tunisia, Sudan, Germany, and Russia. Following these severe declines, there were some slight population recoveries in Russia, Italy, Spain, and Germany in the mid-20™ century, and natural and assisted range expansions in Denmark and Sweden. The species has also been inadvertently reintroduced in various locations in the Great Britain via escapees of mixed origin from commercial farming enterprises. Ex-S. scrofa stocks also occur as introduced feral populations in various other parts of the world, including Australia, New Zealand, the eastern Malay Archipelago, and in North, Central, and South America. In all of these areas they are now generally recognized as a major pest. in Suidae
Subspecies and Distribution. S. s. scrofa Linnaeus, 1758 — W Europe, from Denmark, Germany, Poland, and Czech Republic to N Italy and N Iberian Peninsula; possibly also Albania. The taxonomic status of animals in Austria, Switzerland, Slovenia, and Slovakia is unclear but presumably these populations are included in scrofa, as are the populations of Sweden, Finland, and the Baltic states. However, restocking of once depleted populations, for example in Italy, has likely involved the introduction and mixing of this subspecies with other subspecies, such as attila. S. s. affinis Gray, 1847 — S India and Sri Lanka. S. s. algirus Loche, 1867 — Tunisia, Algeria, and Morocco, on the coastal side of the mountains or in the low montane areas. S. s. attila Thomas, 1912 — Hungary, Ukraine, C & S Belarus, Romania, Moldova, and S Russia towards the N flank of the Caucasus, but not including the Transcaucasian countries of Georgia, Armenia, and Azerbaijan. The range possibly extends as far S as the Mesopotamian Delta in Iraq, in which case it would likely include W & SW Iran, and possibly E Turkey and Syria, where it borders with lybicus. Such a range could not be easily reconciled with a statement by Groves that "the difference between pigs from N and S of the Caucasus is quite striking; Transcaucasian boars are certainly not attila." This subspecies may also extend into C Asia and include Kazakhstan, Uzbekistan, and Turkmenistan, but no data exist to support this. S. s. baeticus Thomas, 1912 — originally described from Coto Donana, S Spain, and later merged with meridionalis; also S Portugal. Unless evidence is found that these Italian and Iberian populations are the relics of a much larger formerly contiguous range, this subspecies should be kept as distinct. S. s. coreanus Heude, 1897 — Korean Peninsula. S. s. eristatus Wagner, 1839 — Himalayas S to C India and E to Indochina (N of the Kra Isthmus). S. s. davidi Groves, 1981 — the arid zone from E Iran to Gujarat, including Pakistan and NW India, and perhaps N to Tajikistan. S. s. leucomystax Temminck, 1842 — main Is ofJapan (Honshu, Shikoku, Kyushu, Nakadori, Hiburijima, Tojima, Kushima, and other smaller Is). S. s. lybicus Gray, 1868 — Bulgaria, Greece, Turkey, Syria, Jordan, Israel, Palestine, in the past also in Lybia, and Egypt. The former Yugoslavia was included in its range, which would suggest that now Slovenia, Serbia, Croatia, Bosnia and Herzegovina, Montenegro, and Kosovo are within the range of this subspecies, although the exact boundaries are unclear. Pigs from Albania have been assigned to S. s. scrofa. S. s. majori De Beaux & Festa, 1927 — C & S Italian Peninsula. S. s. menidionalis Forsyth Major, 1882 — Corsica and Sardinia, with the proviso that the two populations are very likely to be introduced or feral. S. s. moupinensis Milne-Edwards, 1871 — China, S to Vietnam and W to Sichuan. S. s. nigripes Blanford, 1875 — the flanks of the Tianshan mountains in Kyrgyzstan and NW China (Xinjiang). An animal photographed in NE Iran (Golestan) looked like this subspecies. S. s. nukiuanus Kuroda, 1924 — Iriomote, Ishigaki, Okinawa, Tokunoshima, Amamioshima, and Kakerome Is in the Ryukyu chain in extreme S Japan, though some of these populations have hybridized with introduced domesticates. S. s. sibiricus Staffe, 1922 — Mongolia and Transbaikal (S & E of Lake Baikal). S. s. tawvanus Swinhoe, 1863 — Taiwan. S. s. ussuricus Heude, 1888 — far E Russia and the Manchurian region (China). Korean populations were previously included in this subspecies, but based on new evidence, the Korean taxon seems more similar to moupinensis. S. s. vittatus Boie, 1828 — Malay Peninsula, S of the Isthmus of Kra, the offshore islands of Terutai and Langkawi, Sumatra, Riau Archipelago, Java, Bali, and a range of smaller islands around these, including Babi, Bakong, Batam, Bawean, Bengkalis, Bintan, Bulan, Bunguran, Cuyo, Deli, Durian, Enggano, Galang, Jambongan, Karimon (Riau Is), Kundur, Lagong, Laut, Lingga, Lingung, Mapor, Moro Kecil, North Pagai, Nias, Panaitan, Payong, Penang, Pinie, Rupat, Siantan, Siberut, Simeulue, Singkep, Sugi, Sugi Bawa, Telibon, Tinggi, Tuangku, and the Tambelan Is. This species was originally present from the British Is in the extreme W, through Eurasia from S Scandinavia to S Siberia, extending as far E as Korea and Japan, and SE into some of the Sunda Is and Taiwan. In the S the species ranged along the Nile Valley to Khartoum, and N of the Sahara in Africa, more orless following the continental coasts of S, E, and SE Asia. Within this range it was absent only from extremely dry deserts, e.g. the driest regions of Mongolia and in China W of Sichuan; and alpine zones, such as the high altitudes of Pamir and Tien Shan. In recent centuries, the range of S. scrofa has changed dramatically because of hunting and changes in available habitat. The species disappeared from the British Is in the 17" century, from Denmark in the 19" century, and was greatly reduced in range and numbers in the 20" century from areas as distant as Tunisia, Sudan, Germany, and Russia. Following these severe declines, there were some slight population recoveries in Russia, Italy, Spain, and Germany in the mid-20™ century, and natural and assisted range expansions in Denmark and Sweden. The species has also been inadvertently reintroduced in various locations in the Great Britain via escapees of mixed origin from commercial farming enterprises. Ex-S. scrofa stocks also occur as introduced feral populations in various other parts of the world, including Australia, New Zealand, the eastern Malay Archipelago, and in North, Central, and South America. In all of these areas they are now generally recognized as a major pest.
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