:ŽƵƌŶĂůŽĨdŚƌĞĂƚĞŶĞĚdĂdžĂͮǁǁǁ͘ƚŚƌĞĂƚĞŶĞĚƚĂdžĂ͘ŽƌŐͮϮϲ:ĂŶƵĂƌLJϮϬϭϱͮϳ;ϭͿ͗ϲϳϲϰʹϲϳϳϯ

K—ÊăãƒÊ¥Dƒ½ç—ƒÃEƒã®Êă½WƒÙ»͕^ƒÙƒóƒ»͕Dƒ½ƒùÝ®ƒ

ÊÃÃçÄ®‘ƒã®ÊÄ ZŽƌLJ͘Žǁϭ͕ZŽďŝŶtĞŶ:ŝĂŶŐEŐŝĂŵϮΘZĂŵďůŝŚŵĂĚϯ

/^^EϬϵϳϰͲϳϵϬϳ;KŶůŝŶĞͿ 1 /^^EϬϵϳϰͲϳϴϵϯ;WƌŝŶƚͿ Naturalis Biodiversity Center, P.O. Box 9517, 2300 RA Leiden, The Netherlands 2 EĂƟŽŶĂůŝŽĚŝǀĞƌƐŝƚLJĞŶƚƌĞ͕EĂƟŽŶĂůWĂƌŬƐŽĂƌĚ͕ϭůƵŶLJZŽĂĚ͕^ŝŶŐĂƉŽƌĞϮϱϵϱϲϵ͕ZĞƉƵďůŝĐŽĨ^ŝŶŐĂƉŽƌĞ 3v^ĂƌĂǁĂŬ&ŽƌĞƐƚƌLJŽƌƉŽƌĂƟŽŶ͕>ŽƚϮϭϴ͕<>͕:ĂůĂŶdĂƉĂŶŐ͕<ŽƚĂ^ĞŶƚŽƐĂ͕ϵϯϮϱϬ<ƵĐŚŝŶŐ͕^ĂƌĂǁĂŬDĂůĂLJƐŝĂ KWE^^ 1 ƌŽƌLJ͘ĚŽǁϮϯϬΛLJĂŚŽŽ͘ĐŽ͘ƵŬ;ĐŽƌƌĞƐƉŽŶĚŝŶŐĂƵƚŚŽƌͿ͕2 LJĂŶƌŽďŝŶΛŚŽƚŵĂŝů͘ĐŽŵ͕3 ƌĂŵďůŝĂŚŵĂĚΛƐĂƌĂǁĂŬĨŽƌĞƐƚƌLJ͘ĐŽŵ

ďƐƚƌĂĐƚ͗dŚŝƐƉĂƉĞƌƉƌĞƐĞŶƚƐƌĞĐŽƌĚƐŽĨKĚŽŶĂƚĂĐŽůůĞĐƚĞĚŝŶ:ƵůLJϮϬϭϮŝŶDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͕^ĂƌĂǁĂŬ͕DĂůĂLJƐŝĂ͘ƚŽƚĂůŽĨϰϴ ƐƉĞĐŝĞƐĨƌŽŵŶŝŶĞĨĂŵŝůŝĞƐǁĞƌĞĐŽůůĞĐƚĞĚ͘dŚƌĞĞƐƉĞĐŝĞƐǁĞƌĞŶĞǁƚŽƐĐŝĞŶĐĞ͕ŽŶĞŽĨǁŚŝĐŚŚĂƐĂůƌĞĂĚLJďĞĞŶĚĞƐĐƌŝďĞĚĂƐProdasineura yulanŽǁΘEŐŝĂŵ͕ǁŚŝĐŚŵĂLJďĞĞŶĚĞŵŝĐƚŽDĂůƵĚĂŵ͘/ŶĂĚĚŝƟŽŶ͕DĂůƵĚĂŵŝƐŽŶůLJƚŚĞƐĞĐŽŶĚůŽĐĂůŝƚLJƌĞĐŽƌĚĞĚŝŶ^ĂƌĂǁĂŬĨŽƌĨŽƵƌ ƉŽŽƌůLJŬŶŽǁŶƐƉĞĐŝĞƐ͗Pachycypha aurea, Macrogomphus decemlineatus, Brachygonia ophelia and Brachygonia puella͘dǁŽŽĨƚŚĞƐĞ ƐƉĞĐŝĞƐ͕Macrogomphus decemlineatus and Brachygonia ophelia͕ĂƌĞƌĞĐŽƌĚĞĚĨŽƌƚŚĞĮƌƐƚƟŵĞŝŶ^ĂƌĂǁĂŬŝŶŵŽƌĞƚŚĂŶϭϬϬLJĞĂƌƐ

<ĞLJǁŽƌĚƐ͗KĚŽŶĂƚĂ͕ĚƌĂŐŽŶŇŝĞƐ͕ĚĂŵƐĞůŇŝĞƐ͕DĂůƵĚĂŵ͕ĞƚŽŶŐ͕^ĂƌĂǁĂŬ͕DĂůĂLJƐŝĂ͕ŶĞǁƐƉĞĐŝĞƐ

ďƐƚƌĂŬĂŚĂƐĂDĞůĂLJƵ͗<ĞƌƚĂƐŝŶŝŵĞŶŐĞŵƵŬĂŬĂŶƌĞŬŽĚKĚŽŶĂƚĂLJĂŶŐĚŝŬƵŵƉƵůĚĂůĂŵďƵůĂŶ:ƵůĂŝĚŝdĂŵĂŶEĞŐĂƌĂDĂůƵĚĂŵ͕^ĂƌĂǁĂŬ͕ DĂůĂLJƐŝĂ͘^ĞũƵŵůĂŚϰϴƐƉĞƐŝƐĚĂƌŝƉĂĚĂƐĞŵďŝůĂŶĨĂŵŝůŝƚĞůĂŚĚŝŬƵŵƉƵůŬĂŶ͘dŝŐĂƐƉĞƐŝƐĂĚĂůĂŚďĂŚĂƌƵŬĞƉĂĚĂƐĂŝŶƐ͕ƐĂƚƵĚĂƌŝƉĂĚĂŶLJĂƚĞůĂŚ ĚŝŚƵƌĂŝŬĂŶƐĞďĂŐĂŝProdasineura yulanŽǁΘEŐŝĂŵ͕LJĂŶŐŵƵŶŐŬŝŶĞŶĚĞŵŝŬŬĞƉĂĚĂDĂůƵĚĂŵ͘dĂŵďĂŚĂŶƉƵůĂ͕DĂůƵĚĂŵĂĚĂůĂŚƚĞŵƉĂƚ ŬĞĚƵĂĚŝ^ĂƌĂǁĂŬLJĂŶŐŵĞƌĞŬŽĚŬĂŶĞŵƉĂƚƐƉĞƐŝƐLJĂŶŐŬƵƌĂŶŐĚŝŬĞƚĂŚƵŝ͗Pachycypha aurea, Macrogomphus decemlineatus, Brachygonia ophelia and Brachygonia puella͘ ƵĂ ĚĂƌŝƉĂĚĂ ƐƉĞƐŝƐ ŝŶŝ͕ Macrogomphus decemlineatus and Brachygonia ophelia͕ ĚŝƌĞŬŽĚŬĂŶ ƵŶƚƵŬ ƉĞƌƚĂŵĂŬĂůŝĚŝ^ĂƌĂǁĂŬĚĂůĂŵŵĂƐĂůĞďŝŚĚĂƌŝƉĂĚĂϭϬϬƚĂŚƵŶ͘

/ĐƟŶŽŐŽŵƉŚƵƐĂĐƵƚƵƐ

NOT DATA LEAST NEAR CRITICALLY EXTINCT VULNERABLE ENDANGERED EXTINCT EVALUATED DEFICIENT CONCERN THREATENED ENDANGERED IN THE WILD NE DD LC NT VU EN CR EW EX

K/͗ŚƩƉ͗ͬͬĚdž͘ĚŽŝ͘ŽƌŐͬϭϬ͘ϭϭϲϬϵͬ:Ždd͘ŽϰϭϬϳ͘ϲϳϲϰͲϳϯͮŽŽĂŶŬ͗ƵƌŶ͗ůƐŝĚ͗njŽŽďĂŶŬ͘ŽƌŐ͗ƉƵď͗&ϬϵϬͲϮϲ&ͲϰϳͲϵϭϳͲϭϭϬϵϱ&ϲϵ

ĚŝƚŽƌ͗ůďĞƌƚKƌƌ͕'ƌŝĸƚŚhŶŝǀĞƌƐŝƚLJ͕EĂƚŚĂŶ͕ƵƐƚƌĂůŝĂ͘ ĂƚĞŽĨƉƵďůŝĐĂƟŽŶ͗Ϯϲ:ĂŶƵĂƌLJϮϬϭϱ;ŽŶůŝŶĞΘƉƌŝŶƚͿ

DĂŶƵƐĐƌŝƉƚĚĞƚĂŝůƐ͗DƐηŽϰϭϬϳͮZĞĐĞŝǀĞĚϮϰ:ƵůLJϮϬϭϰͮ&ŝŶĂůƌĞĐĞŝǀĞĚϯϭĞĐĞŵďĞƌϮϬϭϰͮ&ŝŶĂůůLJĂĐĐĞƉƚĞĚϬϰ:ĂŶƵĂƌLJϮϬϭϱ

ŝƚĂƟŽŶ͗Žǁ͕Z͕͘͘Z͘t͘:͘EŐŝĂŵ͕ΘZ͘ŚŵĂĚ;ϮϬϭϱͿ͘KĚŽŶĂƚĂŽĨDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͕^ĂƌĂǁĂŬ͕DĂůĂLJƐŝĂ. Journal of Threatened Taxaϳ;ϭͿ͗ϲϳϲϰʹϲϳϳϯ; ŚƩƉ͗ͬͬ Ědž͘ĚŽŝ͘ŽƌŐͬϭϬ͘ϭϭϲϬϵͬ:Ždd͘ŽϰϭϬϳ͘ϲϳϲϰͲϳϯ

ŽƉLJƌŝŐŚƚ͗ ©ŽǁĞƚĂů͘ϮϬϭϱ͘ƌĞĂƟǀĞŽŵŵŽŶƐƩƌŝďƵƟŽŶϰ͘Ϭ/ŶƚĞƌŶĂƟŽŶĂů>ŝĐĞŶƐĞ͘:ŽddĂůůŽǁƐƵŶƌĞƐƚƌŝĐƚĞĚƵƐĞŽĨƚŚŝƐĂƌƟĐůĞŝŶĂŶLJŵĞĚŝƵŵ͕ƌĞƉƌŽĚƵĐƟŽŶ ĂŶĚĚŝƐƚƌŝďƵƟŽŶďLJƉƌŽǀŝĚŝŶŐĂĚĞƋƵĂƚĞĐƌĞĚŝƚƚŽƚŚĞĂƵƚŚŽƌƐĂŶĚƚŚĞƐŽƵƌĐĞŽĨƉƵďůŝĐĂƟŽŶ͘

&ƵŶĚŝŶŐ͗ None.

ŽŵƉĞƟŶŐ/ŶƚĞƌĞƐƚ͗dŚĞĂƵƚŚŽƌƐĚĞĐůĂƌĞŶŽĐŽŵƉĞƟŶŐŝŶƚĞƌĞƐƚƐ͘

ƵƚŚŽƌĞƚĂŝůƐ͗ZÊÙù͘ÊóŝƐĂƌĞƐĞĂƌĐŚĂƐƐŽĐŝĂƚĞĂƚEĂƚƵƌĂůŝƐŝŽĚŝǀĞƌƐŝƚLJĞŶƚƌĞ͕>ĞŝĚĞŶ͕ƚŚĞEĞƚŚĞƌůĂŶĚƐ͘,ŝƐƌĞƐĞĂƌĐŚŝŶƚĞƌĞƐƚƐĂƌĞŝŶƚŚĞĨĂƵŶŝƐƟĐƐĂŶĚ ƚĂdžŽŶŽŵLJŽĨƐŝĂŶKĚŽŶĂƚĂ͘,ĞŚĂƐĞdžƚĞŶƐŝǀĞĞdžƉĞƌŝĞŶĐĞŽĨǁŽƌŬŝŶŐŝŶ^ŽƵƚŚĞĂƐƚƐŝĂ͕ĞƐƉĞĐŝĂůůLJŝŶŽƌŶĞŽ͘Zʐ®Ät›Ä:®ƒÄ¦E¦®ƒÃǁŽƌŬƐŝŶƚŚĞEĂƟŽŶĂů ŝŽĚŝǀĞƌƐŝƚLJĞŶƚƌĞ͕^ŝŶŐĂƉŽƌĞ͘,ĞŝƐĂŶKĚŽŶĂƚĂĞdžƉĞƌƚŝŶ^ŝŶŐĂƉŽƌĞĂŶĚŚĂƐƌĞĐĞŶƚůLJƐƚĂƌƚĞĚƚŽĂƐƐŝƐƚŝŶKĚŽŶĂƚĂƌĞƐĞĂƌĐŚŝŶ^ĂƌĂǁĂŬ͘ZƒÃ½®«Ãƒ— is an ĞĐŽůŽŐŝƐƚǁŝƚŚƚŚĞ^ĂƌĂǁĂŬ&ŽƌĞƐƚƌLJŽƌƉŽƌĂƟŽŶ͘

ƵƚŚŽƌŽŶƚƌŝďƵƟŽŶ͗ZŝĚĞŶƟĮĐĂƟŽŶĂŶĚŝŶĨŽƌŵĂƟŽŶŽŶƚŚĞKĚŽŶĂƚĂĐŽůůĞĐƚĞĚ͕ĐŽůůĞĐƟŽŶŽĨƐƉĞĐŝŵĞŶƐ͘Zt:EĐŽůůĞĐƟŽŶŽĨƐƉĞĐŝŵĞŶƐĂŶĚƉŚŽƚŽŐƌĂƉŚLJ͘Z ďĂĐŬŐƌŽƵŶĚŝŶĨŽƌŵĂƟŽŶĂŶĚŵĂƉŝŶ&ŝŐƵƌĞϭ͘

ĐŬŶŽǁůĞĚŐĞŵĞŶƚƐ͗dŚĞĮƌƐƚƚǁŽĂƵƚŚŽƌƐǁŽƵůĚůŝŬĞƚŽƚŚĂŶŬƚŚĞ^ĂƌĂǁĂŬ&ŽƌĞƐƚƌLJŽƌƉŽƌĂƟŽŶĂŶĚ^ĂƌĂǁĂŬ&ŽƌĞƐƚĞƉĂƌƚŵĞŶƚĨŽƌŐƌĂŶƟŶŐƉĞƌŵŝƐƐŝŽŶƚŽĐŽůͲ ůĞĐƚKĚŽŶĂƚĂŝŶ^ĂƌĂǁĂŬ͕ƚŚĞƐƚĂīŽĨDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͕ŝŶƉĂƌƟĐƵůĂƌƚŚĞƉĂƌŬǁĂƌĚĞŶĂƚƚŚĞƟŵĞŽĨƚŚĞŝƌǀŝƐŝƚ͕dŽůŽLJ<ĞƌŝƉŝŶDƵŶƐĂŶŐ͕ĨŽƌƚŚĞŝƌĂƐƐŝƐƚĂŶĐĞ͕ ĂŶĚƚŚĞƉĞŽƉůĞŽĨZƵŵĂŚdĂŶũŽŶŐĂƌƵĨŽƌƉƌŽǀŝĚŝŶŐĂĐĐŽŵŵŽĚĂƟŽŶĂŶĚŚŽƐƉŝƚĂůŝƚLJ͘ůďĞƌƚKƌƌĂŶĚƚǁŽĂŶŽŶLJŵŽƵƐƌĞĨĞƌĞĞƐŵĂĚĞĐŽŵŵĞŶƚƐŽŶƚŚĞƉĂƉĞƌƚŚĂƚ ŚĂǀĞŐƌĞĂƚůLJŝŵƉƌŽǀĞĚŝƚ͘^ƉĞĐŝĂůƚŚĂŶŬƐĂƌĞĚƵĞƚŽtĂƚƐŽŶƐĂŝĂŶĂŬ:ŝŬĂĂŶĚDĂƚŚĞǁĂŶĂŬ^ĂŵĂƚĨŽƌƚŚĞŝƌĂƐƐŝƐƚĂŶĐĞŝŶƚŚĞĮĞůĚ͘

6764 KĚŽŶĂƚĂŽĨDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͕DĂůĂLJƐŝĂ ŽǁĞƚĂů͘

/EdZKhd/KE dŚĞƌĞ ĂƌĞ ŽŶůLJ ƉƵďůŝƐŚĞĚ ƌĞĐŽƌĚƐ ŽĨ ĞŝŐŚƚ ƐƉĞĐŝĞƐ ŽĨ KĚŽŶĂƚĂƚŚĂƚĐĂŶďĞƚƌĂĐĞĚƚŽĞƚŽŶŐŝǀŝƐŝŽŶƚŚĂƚǁĞ WĞĂƚƐǁĂŵƉĨŽƌĞƐƚƐĂƌĞǁĂƚĞƌůŽŐŐĞĚǁĞƚůĂŶĚĂƌĞĂƐ͕ ĂƌĞ ĂǁĂƌĞ ŽĨ͕ Ăůů ŝŶ >ĂŝĚůĂǁ ;ϭϵϭϰ͕ ϭϵϮϬͿ ĂŶĚ Ăůů ĨƌŽŵ ǁŝƚŚǀĞƌLJůŽǁůĞǀĞůƐŽĨŶƵƚƌŝĞŶƚĂŶĚĚŝƐƐŽůǀĞĚŽdžLJŐĞŶ͘ ^ĂƌŝďĂƐ͗ Libellago hyalina ;^ĞůLJƐ͕ ϭϴϱϵͿ͖ Rhinocypha WĞĂƚ ƐǁĂŵƉ ĨŽƌĞƐƚ ŝƐ Ă ƵŶŝƋƵĞ ĞĐŽƐLJƐƚĞŵ ǁŚĞƌĞ cucullata ^ĞůLJƐ͕ϭϴϳϯ͖Euphaea subcostalis ^ĞůLJƐ͕ϭϴϳϯ͖ ƐƉĞĐŝĂů ŇŽƌĂ ĂŶĚ ĨĂƵŶĂ ŚĂǀĞ ĞǀŽůǀĞĚ ĂŶĚ ĂĚĂƉƚĞĚ ƚŽ Euphaea tricolor ^ĞůLJƐ͕ϭϴϱϵ͖ůĂƩŽŶĞƵƌĂĂŶĂůŝƐ;^ĞůLJƐ͕ ƚŚĞ ƐĞĞŵŝŶŐůLJ ŚĂƌƐŚ ĞŶǀŝƌŽŶŵĞŶƚ͘  DŽƌĞ ƚŚĂŶ ϲϬй ϭϴϲϬͿ͖ Heliaeschna idae ;ƌĂƵĞƌ͕ ϭϴϲϱͿ͖ Gynacantha ŽĨ ƚŚĞ ǁŽƌůĚ͛Ɛ ƚƌŽƉŝĐĂů ƉĞĂƚ ƐǁĂŵƉ ĨŽƌĞƐƚƐ ĂƌĞ ŝŶ dohrni <ƌƺŐĞƌ͕ϭϴϵϵ͖ĂŶĚMicrogomphus chelifer ;^ĞůLJƐ͕ ^ŽƵƚŚĞĂƐƚƐŝĂǁŝƚŚƚŚĞŵŽƐƚĞdžƚĞŶƐŝǀĞĂƌĞĂƐďĞŝŶŐŝŶ ϭϴϱϴͿ͘  /ƚ ǁĂƐ ĂŐĂŝŶƐƚ ƚŚŝƐ ďĂĐŬŐƌŽƵŶĚ ƚŚĂƚ Ă ƐƵƌǀĞLJ ŽƌŶĞŽĂŶĚ^ƵŵĂƚƌĂ;hEWϮϬϬϲͿ͘WŽƐĂĞƚĂů͘;ϮϬϭϭͿ ŽĨ ƚŚĞ ŽĚŽŶĂƚĞ ĨĂƵŶĂ ŽĨ DĂůƵĚĂŵ EĂƟŽŶĂů WĂƌŬ ǁĂƐ ĚĞŵŽŶƐƚƌĂƚĞĚƚŚĂƚĂƐŝŐŶŝĮĐĂŶƚƉƌŽƉŽƌƟŽŶŽĨ^ŽƵƚŚĞĂƐƚ ĐŽŶĚƵĐƚĞĚ ŝŶ :ƵůLJ ϮϬϭϮ ďLJ ƚŚĞ ĮƌƐƚ ƚǁŽ ĂƵƚŚŽƌƐ ǁŝƚŚ ƐŝĂ͛Ɛ ǀĞƌƚĞďƌĂƚĞ ĨĂƵŶĂ ĐĂŶ ďĞ ĨŽƵŶĚ ŝŶ ƉĞĂƚ ƐǁĂŵƉ ĂƐƐŝƐƚĂŶĐĞ ĨƌŽŵ ƚŚĞ WƌŽƚĞĐƚĞĚ ƌĞĂƐ ĂŶĚ ŝŽĚŝǀĞƌƐŝƚLJ ĨŽƌĞƐƚƐĂŶĚƚŚĂƚƉƌĞƐĞƌǀĂƟŽŶŽĨƚŚĞƐĞĨŽƌĞƐƚƐŝƐĐƌƵĐŝĂů ŽŶƐĞƌǀĂƟŽŶhŶŝƚŽĨƚŚĞ^&͘ ŝŶ ĐŽŶƐĞƌǀŝŶŐ Ă ŶƵŵďĞƌ ŽĨ ƚŚƌĞĂƚĞŶĞĚ ƚĂdžĂ͕ ĞƐƉĞĐŝĂůůLJ ƐƉĞĐŝĂůŝnjĞĚĮƐŚƐƉĞĐŝĞƐ͘WĞĂƚƐǁĂŵƉĨŽƌĞƐƚƐ͕ŚŽǁĞǀĞƌ͕ ĂƌĞ ŽŌĞŶ ƌĞŐĂƌĚĞĚ ĂƐ ƵŶƉƌŽĚƵĐƟǀĞ ǁĂƐƚĞůĂŶĚƐ͕ ĂŶĚ DdZ/>^EDd,K^ ƐƵīĞƌ ĨƌŽŵ ĂŶƚŚƌŽƉŽŐĞŶŝĐ ŝŵƉĂĐƚƐ ƐƵĐŚ ĂƐ ůŽŐŐŝŶŐ ĂŶĚĐŽŶǀĞƌƐŝŽŶƚŽĂŐƌŝĐƵůƚƵƌĂůƵƐĞǁŚŝůĞƌĞĐĞŝǀŝŶŐůŝƩůĞ ĚƵůƚKĚŽŶĂƚĂǁĞƌĞĐŽůůĞĐƚĞĚƵƐŝŶŐŚĂŶĚŚĞůĚŶĞƚƐ ĂƩĞŶƟŽŶĨƌŽŵĐŽŶƐĞƌǀĂƟŽŶŝƐƚƐ͘dŚĞĚĞŐƌĂĚĂƟŽŶĂŶĚ ŽŶƐŝdžĚĂLJƐĨƌŽŵϲ ƚŽϭϭ:ƵůLJϮϬϭϮ͘dŚĞŵĂŝŶĂƌĞĂƐŽĨ ŚĂďŝƚĂƚ ůŽƐƐ ŽĨ ƉĞĂƚ ƐǁĂŵƉƐ ŝŶ ^ŽƵƚŚĞĂƐƚ ƐŝĂ ŽǀĞƌ ĐŽůůĞĐƟŽŶǁĞƌĞ͗^ƵŶŐĂŝDĂůƵĚĂŵŶĞĂƌZƵŵĂŚdĂŶũŽŶŐ ƚŚĞ ůĂƐƚ ĨĞǁ ĚĞĐĂĚĞƐ ŚĂƐ ďĞĞŶ ƵŶƉƌĞĐĞĚĞŶƚĞĚ͖ ŝƚ ŝƐ ĂƌƵ ;ŽƵƚƐŝĚĞ ƚŚĞ ŶĂƟŽŶĂů ƉĂƌŬ ďŽƵŶĚĂƌLJͿ͖ ^ƵŶŐĂŝ ĞƐƟŵĂƚĞĚ ƚŚĂƚ ŽŶůLJ ĐĂ͘ ϯϳй ŽĨ ŚŝƐƚŽƌŝĐĂů ƉĞĂƚ ƐǁĂŵƉ DĂůƵĚĂŵ ŝŶƐŝĚĞ ƚŚĞ ŶĂƟŽŶĂů ƉĂƌŬ͕ ƚŚŝƐ ŝƐ ƌĞĨĞƌƌĞĚ ƚŽ ĨŽƌĞƐƚƌĞŵĂŝŶƐŝŶƚŚĞƌĞŐŝŽŶ;WŽƐĂĞƚĂů͘ϮϬϭϭͿ͘ ďĞůŽǁĂƐhůƵ;ƵƉƌŝǀĞƌͿDĂůƵĚĂŵ͖ŝŶƐǁĂŵƉĂĚũĂĐĞŶƚƚŽ͕ ,ŝƐƚŽƌŝĐĂůůLJ^ĂƌĂǁĂŬĂŶĚ^ĂďĂŚŚĂĚĐĂ͘ϭϳ͕ϰϲϬŬŵ2 ĂŶĚ ƐŵĂůů ƐƚƌĞĂŵƐ ŇŽǁŝŶŐ ŝŶƚŽ hůƵ DĂůƵĚĂŵ ;/ŵĂŐĞƐ ŽĨ ƉĞĂƚ ƐǁĂŵƉ ĨŽƌĞƐƚ ďƵƚ ŽŶůLJ ĐĂ͘ ϯϲй ŽĨ ŝƚ ƌĞŵĂŝŶƐ͘ ϭʹϯͿ͘KŶƚŚĞ^ƵŶŐĂŝDĂůƵĚĂŵ͕ƐĂŵƉůŝŶŐǁĂƐĐŽŶĚƵĐƚĞĚ dǁŽ ŽĨ ^ĂƌĂǁĂŬ͛Ɛ ůŽŶŐĞƌ ĞƐƚĂďůŝƐŚĞĚ ŶĂƟŽŶĂů ƉĂƌŬƐ ĨƌŽŵ Ă ďŽĂƚ͘  ^ĂŵƉůŝŶŐ ŝŶ ƐǁĂŵƉ ĂŶĚ ƐŵĂůů ƐƚƌĞĂŵƐ ĐŽŶƚĂŝŶƐŝŐŶŝĮĐĂŶƚĂƌĞĂƐŽĨƉĞĂƚƐǁĂŵƉĨŽƌĞƐƚ͗>ŽĂŐĂŶ ŇŽǁŝŶŐ ŝŶƚŽ ^ƵŶŐĂŝ DĂůƵĚĂŵ ǁĂƐ ĐŽŶĚƵĐƚĞĚ ŽŶ ĨŽŽƚ͘ ƵŶƵƚEĂƟŽŶĂůWĂƌŬŝŶDŝƌŝŝǀŝƐŝŽŶ͕ŐĂnjĞƩĞĚŝŶϭϵϵϬ͕ dŚĞƐĂŵƉůŝŶŐƐŝƚĞƐĂƌĞƐŚŽǁŶŝŶ&ŝŐ͘ϭ͘ ĂŶĚDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬŝŶĞƚŽŶŐŝǀŝƐŝŽŶ͕ŐĂnjĞƩĞĚ ^ƉĞĐŝŵĞŶƐǁĞƌĞƉƌĞƐĞƌǀĞĚĞŝƚŚĞƌďLJƚƌĞĂƚŵĞŶƚǁŝƚŚ ŝŶϮϬϬϬ͘DĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬŝƐĂďŽƵƚϰϯ͕ϭϰϳŚĂŝŶ ĂĐĞƚŽŶĞ Žƌ ŝŵŵĞƌƐŝŽŶ ŝŶ ĞƚŚĂŶŽů͘  dŚĞ ƐƉĞĐŝŵĞŶƐ ĂƌĞ ƐŝnjĞ;^ĂƌĂǁĂŬ&ŽƌĞƐƚƌLJŽƌƉŽƌĂƟŽŶϮϬϭϯͿ͘dŚĞƉĂƌŬŝƐ ĐƵƌƌĞŶƚůLJŚĞůĚŝŶĞŝƚŚĞƌƚŚĞEĂƚƵƌĂůŝƐŝŽĚŝǀĞƌƐŝƚLJĞŶƚƌĞ ůŽĐĂƚĞĚ ŽŶ ƚŚĞ DĂůƵĚĂŵ WĞŶŝŶƐƵůĂ ĂŶĚ ŝƐ ƉĂƌƚ ŽĨ ƚŚĞ ŝŶ>ĞŝĚĞŶ͕ƚŚĞZĂŋĞƐDƵƐĞƵŵŽĨŝŽĚŝǀĞƌƐŝƚLJZĞƐĞĂƌĐŚ ŇŽŽĚƉůĂŝŶŽĨƚŚĞ>ƵƉĂƌĂŶĚ^ĂƌŝďĂƐƌŝǀĞƌƐ;,ĂnjĞďƌŽĞŬΘ Ăƚ EĂƟŽŶĂů hŶŝǀĞƌƐŝƚLJ ŽĨ ^ŝŶŐĂƉŽƌĞ͕ Žƌ ƚŚĞ ǁŽƌŬŝŶŐ DŽƌƐŚŝĚŝϮϬϬϬͿ͘ĞĨŽƌĞƚŚĞĞƐƚĂďůŝƐŚŵĞŶƚŽĨƚŚĞƉĂƌŬ͕ ĐŽůůĞĐƟŽŶƐŽĨƚŚĞĮƌƐƚƚǁŽĂƵƚŚŽƌƐ͘ ƚŚĞ ĂƌĞĂ ǁĂƐ ŚĂƌǀĞƐƚĞĚ ĨŽƌ ƟŵďĞƌ ĨƌŽŵ ϭϵϱϱ͕ ŵĂŝŶůLJ ĨŽƌ ƌĂŵŝŶ ;Gonystylus bancanus - dŚLJŵĞůĂĞĂĐĞĂĞͿ ƵŶƟůůŽŐŐŝŶŐĐŽŶĐĞƐƐŝŽŶƐĞdžƉŝƌĞĚŝŶϭϵϵϵ;tŽŶŐϮϬϬϯͿ͘ hƐŝŶŐƌĞŵŽƚĞƐĞŶƐŝŶŐĂŶĚ'/^ƚĞĐŚŶŽůŽŐLJ͕tŽŶŐ;ϮϬϬϯͿ ƐŚŽǁĞĚ ƚŚĂƚ ŶĂƚƵƌĂů ƵŶĚŝƐƚƵƌďĞĚ ĨŽƌĞƐƚƐ ƌĞŵĂŝŶŝŶŐ ŝŶ ƚŚĞ ŶĂƟŽŶĂů ƉĂƌŬ ĐŽŶƐƟƚƵƚĞĚ ŽŶůLJ ĂďŽƵƚ ϯ͘Ϯϵй ŽĨ ƚŚĞƚŽƚĂůƉĂƌŬĂƌĞĂ͖ŵƵĐŚŽĨƚŚĞƌĞŵĂŝŶŝŶŐĂƌĞĂŝƐƐƟůů ĨŽƌĞƐƚĞĚ͕ǁŝƚŚƚŚĞĨŽƌĞƐƚŝŶǀĂƌŝŽƵƐƐƚĂƚĞƐŽĨĚŝƐƚƵƌďĂŶĐĞ͘ DĂůƵĚĂŵ EĂƟŽŶĂů WĂƌŬ ŝƐ Ă ƌĞĨƵŐĞ ĨŽƌ ƐŽŵĞ ŽĨ ^ĂƌĂǁĂŬ͛ƐŵŽƐƚŝŵƉŽƌƚĂŶƚĂŶŝŵĂůƉŽƉƵůĂƟŽŶƐ͘džĂŵƉůĞƐ ĂƌĞƚŚĞZĞĚͲďĂŶĚĞĚ>ĂŶŐƵƌWƌĞƐďLJƟƐŵĞůĂůŽƉŽƐĐƌƵĐŝŐĞƌ ǁŚŝĐŚ ŝƐ ƉƌŽďĂďůLJ ůŝŵŝƚĞĚ ĞŶƟƌĞůLJ ƚŽ DĂůƵĚĂŵ͕ ƚŚĞ ŽƌŶĞŽ ĞŶĚĞŵŝĐ WƌŽďŽƐĐŝƐ DŽŶŬĞLJ Nasalis larvatus ĂŶĚ ƚŚĞ ƌĂƌĞ ^ƚŽƌŵ͛Ɛ ^ƚŽƌŬ Ciconia stormi ;,ĂnjĞďƌŽĞŬ ΘDŽƌƐŚŝĚŝϮϬϬϬͿ͘KĚŽŶĂƚĂŚĂĚŶŽƚďĞĞŶƐƵƌǀĞLJĞĚŝŶ ZŽďŝŶtĞŶ:ŝĂŶŐEŐŝĂŵ

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Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2015 | 7(1): 6764–6773 ϲϳϲϱ KĚŽŶĂƚĂŽĨDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͕DĂůĂLJƐŝĂ ŽǁĞƚĂů͘ ZŽďŝŶtĞŶ:ŝĂŶŐEŐŝĂŵ © ZŽďŝŶtĞŶ:ŝĂŶŐEŐŝĂŵ ©

/ŵĂŐĞϮ͘^ŵĂůůƚƌŝďƵƚĂƌLJƐƚƌĞĂŵŽĨ^ƵŶŐĂŝDĂůƵĚĂŵ͘ /ŵĂŐĞϯ͘ĨŽƌĞƐƚƚƌĂŝůŝŶhůƵDĂůƵĚĂŵ͘

&ŝŐƵƌĞϭ͘>ŽĐĂƟŽŶŽĨZƵŵĂŚdĂŶũŽŶŐĂƌƵĂŶĚƐĂŵƉůŝŶŐƐŝƚĞƐŝŶDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͘

Z^h>d^ LJŐŽƉƚĞƌĂ ƌŐŝŽůĞƐƟĚĂĞ ƚŽƚĂůŽĨϰϴƐƉĞĐŝĞƐĨƌŽŵŶŝŶĞĨĂŵŝůŝĞƐǁĞƌĞĐŽůůĞĐƚĞĚ͘ ;ŝͿPodolestes chrysopus^ĞůLJƐ͕ϭϴϴϵ;/ŵĂŐĞϰͿͶdŚĞ DĂƚĞƌŝĂůůŝƐƚĞĚŝƐďLJĚĂƚĞƚŚĞŶŝŶĂůƉŚĂďĞƟĐĂůŽƌĚĞƌďLJ ŽŶůLJ ƌĞĐĞŶƚ ƌĞĐŽƌĚƐ ŽĨ ƚŚŝƐ ƐƉĞĐŝĞƐ ĂƌĞ ĨƌŽŵ ǁĞƐƚĞƌŶ ĐŽůůĞĐƚŽƌƐ͛ƐƵƌŶĂŵĞ͘ŽůůĞĐƚŽƌƐ͗tͲtĂƚƐŽŶĂŶĂŬƐĂŝ͖ ^ĂƌĂǁĂŬ;ŽǁΘZĞĞůƐϮϬϭϭ͖ŽǁϮϬϭϮͿ͘/ƚŝƐŽƚŚĞƌǁŝƐĞ ZͲZŽƌLJŽǁ͖ZEͲZŽďŝŶEŐŝĂŵ͘ůĂƐƐŝĮĐĂƟŽŶĨŽůůŽǁƐ ŬŶŽǁŶĨƌŽŵůŽĐĂƟŽŶƐŝŶŶŽƌƚŚǁĞƐƚĞƌŶ<ĂůŝŵĂŶƚĂŶ;^ĞůLJƐ ŝũŬƐƚƌĂĞƚĂů͘;ϮϬϭϯͿĞdžĐĞƉƚƚŚĂƚƚŚĞƌŐŝŽůĞƐƟĚĂĞĂƌĞ ϭϴϴϵ͖>ŝĞŌŝŶĐŬϭϵϯϱͿ͖ĂƌĞĐŽƌĚĨƌŽŵƌƵŶĞŝ;dŚŽŵƉƐŽŶΘ ƌĞĐŽŐŶŝnjĞĚ ĨŽůůŽǁŝŶŐ <ĂůŬŵĂŶ Θ dŚĞŝƐĐŚŝŶŐĞƌ ;ϮϬϭϯͿ ǀĂŶdŽůϭϵϵϯͿŝŶĨĂĐƚƌĞĨĞƌƐƚŽŵŝƐŝĚĞŶƟĮĞĚP. harrissoni ĂŶĚŝũŬƐƚƌĂĞƚĂů͘;ϮϬϭϰͿ͘ ĂŶĚƚŚĂƚĨƌŽŵ>ĂďƵĂŶŝŶ^ĞůLJƐ;ϭϴϴϵͿŝƐůŝŬĞůLJƚŽďĞŽŶĞ

6766 Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2015 | 7(1): 6764–6773 KĚŽŶĂƚĂŽĨDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͕DĂůĂLJƐŝĂ ŽǁĞƚĂů͘ ZŽƌLJŽǁ © ZŽďŝŶtĞŶ:ŝĂŶŐEŐŝĂŵ © /ŵĂŐĞϰ͘Podolestes chrysopus;ŵĂůĞͿ͘dŚŝƐŝƐĂƉĞĂƚƐǁĂŵƉ ƐƉĞĐŝĂůŝƐƚĂŶĚŝƐĨŽƵŶĚĂƚŽŶůLJƚǁŽŽƚŚĞƌƵŶƉƌŽƚĞĐƚĞĚƐŝƚĞƐŝŶ ^ĂƌĂǁĂŬ͘ /ŵĂŐĞϱ͘PodolestesŶĞǁƐƉĞĐŝĞƐ;ĨĞŵĂůĞͿ͘

ŽĨŵĂŶLJĐĂƐĞƐǁŚĞƌĞƐƉĞĐŝŵĞŶƐǁĞƌĞůĂďĞůůĞĚĂĐĐŽƌĚŝŶŐ ĨĞŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭĨĞŵĂůĞ͕ ƚŽƚŚĞƉŽƌƚĨƌŽŵǁŚŝĐŚƚŚĞLJǁĞƌĞƐĞŶƚďĂĐŬƚŽƵƌŽƉĞ ϴ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ Ϯ ŵĂůĞƐ͕ ϵ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ Ϯ ŵĂůĞƐ͕ ƌĂƚŚĞƌ ƚŚĂŶ ĐŽůůĞĐƟŶŐ ƐŝƚĞ͘ ϰ ŵĂůĞƐ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϱ ϵ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ĨĞŵĂůĞ͕ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ ϭ ŵĂůĞ͕ ϭ ŵĂůĞƐ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϭ ĨĞŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ĨĞŵĂůĞ͕ ϴ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ ϯ ŵĂůĞƐ͕ ϭ ĨĞŵĂůĞ͕ ϴ͘ǀŝŝ͘ϮϬϭϮ͕ ;ŝŝͿ Pachycypha aurea >ŝĞŌŝŶĐŬ͕ ϭϵϱϬ Ͷ DĂůƵĚĂŵ ZE͖ϭĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭ EĂƟŽŶĂůWĂƌŬŝƐƚŚĞƐĞĐŽŶĚƐŝƚĞŝŶ^ĂƌĂǁĂŬǁŚĞƌĞƚŚŝƐ ŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭĨĞŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ ƉŽŽƌůLJ ŬŶŽǁŶ ƐƉĞĐŝĞƐ ŚĂƐ ďĞĞŶ ĨŽƵŶĚ͕ ƚŚĞ ŽƚŚĞƌ ŝƐ Ă ϭĨĞŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭĨĞŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭ ŶŽŶͲƉƌŽƚĞĐƚĞĚ ƐŝƚĞ ŶĞĂƌ <ƵĐŚŝŶŐ ;Žǁ Θ ZĞĞůƐ ϮϬϭϭͿ͖ ŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϮŵĂůĞƐ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ŝƚŝƐŽƚŚĞƌǁŝƐĞŬŶŽǁŶĨƌŽŵĐĞŶƚƌĂů<ĂůŝŵĂŶƚĂŶ͘ϭŵĂůĞ͕ ;ŝŝͿ Podolestes harrissoni >ŝĞŌŝŶĐŬ͕ ϭϵϱϯ Ͷ tŝĚĞůLJ 7.vii.2012, RN. ĚŝƐƚƌŝďƵƚĞĚĂĐƌŽƐƐ^ĂƌĂǁĂŬĂŶĚƌƵŶĞŝ͕ďƵƚĐŽŶĮŶĞĚƚŽ ƉĞĂƚ ƐǁĂŵƉ ĨŽƌĞƐƚ͘ ϭ ŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϵ ŵĂůĞƐ͕ ϭ WůĂƚLJĐŶĞŵŝĚŝĚĂĞ ĨĞŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϯŵĂůĞƐ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ ;ŝͿ Coeliccia ƐƉĞĐŝĞƐ Ͷ dŚĞ ƐƚĂƚƵƐ ŽĨ ƚŚĞ Coeliccia ϵ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ϭĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ ƐƉĞĐŝĞƐĨŽƵŶĚĂƚDĂůƵĚĂŵ ŝƐƐƟůůƵŶĚĞƌŝŶǀĞƐƟŐĂƟŽŶ͖ŝƚ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ŵĂLJŵĞƌĞůLJďĞƚŚĞǁŝĚĞƐƉƌĞĂĚC. nigrohamata >ĂŝĚůĂǁ͕ ;ŝŝŝͿ Podolestes orientalis ^ĞůLJƐ͕ ϭϴϲϮ Ͷ dŚĞ ŵŽƐƚ ϭϵϭϴ͕ ǁŚŝĐŚ ŝƚ ĐůŽƐĞůLJ ƌĞƐĞŵďůĞƐ͕ ďƵƚ C. nigrohamata ĞƵƌLJƚŽƉŝĐ ĂŶĚ ǁŝĚĞƐƉƌĞĂĚ ŽĨ ƚŚĞ Podolestes ƐƉĞĐŝĞƐ͕ ŝƐ ŶŽƚ ŶŽƌŵĂůůLJ ĨŽƵŶĚ ŝŶ ƉĞĂƚ ƐǁĂŵƉ ĨŽƌĞƐƚ͘ ϭ ŵĂůĞ͕ ĨŽƵŶĚ ŝŶ Ă ǀĂƌŝĞƚLJ ŽĨ ƐǁĂŵƉLJ ƐŝƚƵĂƟŽŶƐ͘  ϭ ĨĞŵĂůĞ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϭĨĞŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ ϭ ĨĞŵĂůĞ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ Ϯ ŵĂůĞƐ͕ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ;ŝŝͿ ͞ůĂƩŽŶĞƵƌĂ͟ ĂƵƌĂŶƟĂĐĂ ;^ĞůLJƐ͕ ϭϴϴϲͿ ;/ŵĂŐĞ ;ŝǀͿPodolestesŶĞǁƐƉĞĐŝĞƐ;/ŵĂŐĞϱͿͶWŽƐƐŝďůLJƚŚĞ ϲͿͶ^ĞĞŝũŬƐƚƌĂĞƚĂů͘ ;ϮϬϭϰͿĨŽƌĂĚŝƐĐƵƐƐŝŽŶŽĨƐŝĂŶ ƐŵĂůůĞƐƚPodolestesƐƉĞĐŝĞƐŬŶŽǁŶ͘&ĞŵĂůĞƐǁĞƌĞĨŽƵŶĚ ͞ůĂƩŽŶĞƵƌĂ”. ϲ ŵĂůĞƐ͕ ϭ ĨĞŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ Ϯ ƉĞƌĐŚĞĚĂƚǁĂŝƐƚŚĞŝŐŚƚŝŶĐůŽƐĞĚĐĂŶŽƉLJĨŽƌĞƐƚǁŝƚŚŽƵƚ ŵĂůĞƐ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϭĨĞŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ ŶĞĂƌďLJĨƌĞĞǁĂƚĞƌ͘dŚĞƐŽůĞŵĂůĞĨŽƵŶĚǁĂƐƉĞƌĐŚĞĚ ϮŵĂůĞƐ͕ϭĨĞŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭĨĞŵĂůĞ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕ ŝŶĂƐŵĂůůŚŽůĞĚƵŐŝŶƚŽƚŚĞĚĂŵƉƉĞĂƚ͕ƉƌĞƐƵŵĂďůLJďLJ t͖ Ϯ ŵĂůĞƐ͕ ϭ ĨĞŵĂůĞ͕ ϵ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ ϯ ŵĂůĞƐ͕ ϭ ĂĞĂƌĚĞĚWŝŐSus barbatus͕ǁŝƚŚŽƵƚĨƌĞĞǁĂƚĞƌ͖ǁŚĞŶ ĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϮŵĂůĞƐ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ ĚŝƐƚƵƌďĞĚŝƚŇĞǁĂǁĂLJďƵƚƌĞƚƵƌŶĞĚĂĨĞǁŵŝŶƵƚĞƐůĂƚĞƌ͕ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖Ϯ ŵĂůĞƐ͕ ϭ ĨĞŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ϭ ĂŶĚ ĂĐƚĞĚ ĂƐ ŝĨ ŝƚ ǁĂƐ ŚŽůĚŝŶŐ Ă ƚĞƌƌŝƚŽƌLJ Ăƚ ƚŚĞ ŚŽůĞ͘ ŵĂůĞ͕ϮĨĞŵĂůĞƐ͕ϭϭ͘ǀŝ͘ϮϬϭϮ͕ZE͘ tĂƚĞƌǁĂƐŽŶůLJĨŽƵŶĚĐĂ͘ϭϱĐŵďĞůŽǁƚŚĞďŽƩŽŵŽĨƚŚĞ ;ŝŝŝͿOnychargia atrocyana;^ĞůLJƐ͕ϭϴϲϱͿͶOnychargia ŚŽůĞ͘ϮĨĞŵĂůĞƐ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ǁĂƐĨŽƌŵĞƌůLJƉůĂĐĞĚŝŶƚŚĞŽĞŶĂŐƌŝŽŶŝĚĂĞ͕ƐĞĞŝũŬƐƚƌĂ et al. ;ϮϬϭϰͿ͘ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ŚůŽƌŽĐLJƉŚŝĚĂĞ ;ŝǀͿProdasineura yulanŽǁΘEŐŝĂŵ͕ϮϬϭϯͶ^ĞĞ ;ŝͿ Libellago hyalina ;^ĞůLJƐ͕ ϭϴϱϵͿ Ͷ Ϯ ŵĂůĞƐ͕ ϭ ŽǁΘEŐŝĂŵ;ϮϬϭϯͿ͘ ĨĞŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϭ

Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2015 | 7(1): 6764–6773 6767 KĚŽŶĂƚĂŽĨDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͕DĂůĂLJƐŝĂ ŽǁĞƚĂů͘

ƐǁĂŵƉĂŶĚŬĞƌĂŶŐĂƐͿĨŽƌĞƐƚ͘ϭŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϯ ŵĂůĞƐ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϮŵĂůĞƐ͕ϭĨĞŵĂůĞ;͍Ϳ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕t͖Ϯ ŵĂůĞƐ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ;ǀŝŝŝͿ Ischnura senegalensis ;ZĂŵďƵƌ͕ ϭϴϰϮͿ Ͷ ϭ ŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ;ŝdžͿ Mortonagrion indraneil Žǁ͕ ϮϬϭϭ Ͷ >ŝŬĞ Podolestes harrisoni͕ ƚŚŝƐ ƐƉĞĐŝĞƐ ŝƐ ǁŝĚĞůLJ ĚŝƐƚƌŝďƵƚĞĚ ŝŶ^ĂƌĂǁĂŬĂŶĚƌƵŶĞŝ͕ďƵƚŝƐĐŽŶĮŶĞĚƚŽƉĞĂƚƐǁĂŵƉ ĨŽƌĞƐƚ͘ ϭ ŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϯ ŵĂůĞƐ͕ Ϯ ĨĞŵĂůĞƐ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕ ZŽďŝŶtĞŶ:ŝĂŶŐEŐŝĂŵ t͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖Ϯ © ŵĂůĞƐ͕ϭĨĞŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭĨĞŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ /ŵĂŐĞϲ͘͞ůĂƩŽŶĞƵƌĂ͟ĂƵƌĂŶƟĂĐĂ;ŵĂůĞͿ͘ RN. ;džͿ Pseudagrion coomansi >ŝĞŌŝŶĐŬ͕ ϭϵϯϳ Ͷ ϭ ŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ŵĂůĞ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ŵĂůĞ͕ ŽĞŶĂŐƌŝŽŶŝĚĂĞ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ĨĞŵĂůĞ͕ ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ ϰ ŵĂůĞƐ͕ ϭ ;ŝͿ Amphicnemis annae >ŝĞŌŝŶĐŬ͕ ϭϵϰϬ Ͷ  ƉĞĂƚ ĨĞŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ƐǁĂŵƉ ĨŽƌĞƐƚ ƐƉĞĐŝĂůŝƐƚ͕ ǁŝĚĞůLJ ĚŝƐƚƌŝďƵƚĞĚ ŝŶ ŶŽƌƚŚͲ ;džŝͿPseudagrion microcephalum;ZĂŵďƵƌ͕ϭϴϰϮͿͶ ǁĞƐƚĞƌŶ <ĂůŝŵĂŶƚĂŶ͕ ^ĂƌĂǁĂŬ ĂŶĚ ƌƵŶĞŝ͘ ϯ ŵĂůĞƐ͕ ϭ ϭŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ ĨĞŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϯĨĞŵĂůĞƐ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ϭĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϯŵĂůĞƐ͕ϮĨĞŵĂůĞƐ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ϭŵĂůĞ͕ϭĨĞŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ ŶŝƐŽƉƚĞƌĂ Z͘ Aeshnidae ;ŝŝͿ Amphicnemis wallacii ^ĞůLJƐ͕ ϭϴϲϯ Ͷ ϭ ŵĂůĞ͕ ;ŝͿ Gynacantha dohrni <ƌƺŐĞƌ͕ ϭϴϵϵ Ͷ ϭ ŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ϮĨĞŵĂůĞƐ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϯŵĂůĞƐ͕ ;ŝŝͿ Heliaeschna idae ;ƌĂƵĞƌ͕ ϭϴϲϱͿ Ͷ dŚŝƐ ůĂƌŐĞ ϭĨĞŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ƐƉĞĐŝĞƐ ǁĂƐ ĂďƵŶĚĂŶƚ ĚƵƌŝŶŐ ƚŚĞ ƐĂŵƉůŝŶŐ ƉĞƌŝŽĚ͘ /ƚ ;ŝŝŝͿ Amphicnemis ƐƉĞĐŝĞƐ ĐĨ dactylostyla >ŝĞŌŝŶĐŬ͕ ŝƐ ƚLJƉŝĐĂůůLJ ƌĞŐĂƌĚĞĚ ĂƐ Ă ĐƌĞƉƵƐĐƵůĂƌ ƐƉĞĐŝĞƐ͕ ďƵƚ Ăƚ ϭϵϱϯͶdŚĞƐƚĂƚƵƐŽĨĨŽƌŵƐĂůůŝĞĚƚŽA. dactylostyla and DĂůƵĚĂŵŝƚǁĂƐŽďƐĞƌǀĞĚŇLJŝŶŐĂůůĚĂLJ͕ĞǀĞŶŝŶďƌŝŐŚƚ ͘ŵĂƌƟŶŝZŝƐ͕ϭϵϭϭŝŶ^ĂƌĂǁĂŬŝƐƚŚĞƐƵďũĞĐƚŽĨĂŶŽŶͲ ƐƵŶůŝŐŚƚŝŶƉĂƌƚƐŽĨƚŚĞĨŽƌĞƐƚǁŚĞƌĞƚŚĞĐĂŶŽƉLJŚĂĚďĞĞŶ ŐŽŝŶŐŝŶǀĞƐƟŐĂƟŽŶ͘ϯŵĂůĞƐ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ŽƉĞŶĞĚ ĞdžƚĞŶƐŝǀĞůLJ ďLJ ƉĂƐƚ ůŽŐŐŝŶŐ ĂĐƟǀŝƟĞƐ͘ ϭ ŵĂůĞ͕ ;ŝǀͿArchibasis melanocyana;^ĞůLJƐ͕ϭϴϳϳͿͶďƵŶĚĂŶƚ ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕ ŽŶƐƚƌĞƚĐŚĞƐŽĨhůƵDĂůƵĚĂŵ͘ϭŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭ ZE͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭĨĞŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ ŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϯŵĂůĞƐ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϱŵĂůĞƐ͕ϭ t͖ ϭ ŵĂůĞ͕ ϭ ĨĞŵĂůĞ ;ŝŶ ƚĂŶĚĞŵͿ͕ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ĨĞŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭϭŵĂůĞƐ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ;ǀͿ Archibasis viola >ŝĞŌŝŶĐŬ͕ ϭϵϰϵ Ͷ ϭ ŵĂůĞ͕ ;ŝŝŝͿOligoaeschna foliacea>ŝĞŌŝŶĐŬ͕ϭϵϲϴͶϭŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϮŵĂůĞƐ͕ϭĨĞŵĂůĞ͕ ϮĨĞŵĂůĞƐ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ;ŝǀͿ Tetracanthagyna plagiata ;tĂƚĞƌŚŽƵƐĞ͕ ϭϴϳϳͿ ;ǀŝͿ Ceriagrion cerinorubellum ;ƌĂƵĞƌ͕ ϭϴϲϱͿ Ͷ ϭ ͶϭĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ŵĂůĞ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭĨĞŵĂůĞ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ ϵ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ŵĂůĞ͕ ϭ ĨĞŵĂůĞ͕ ϵ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ Ϯ 'ŽŵƉŚŝĚĂĞ ŵĂůĞƐ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ϭĨĞŵĂůĞ;ŝŶƚĂŶĚĞŵͿ͕ ;ŝͿ/ĐƟŶŽŐŽŵƉŚƵƐĂĐƵƚƵƐ;>ĂŝĚůĂǁ͕ϭϵϭϰͿ;/ŵĂŐĞϳͿͶ 10.vii.2012, RN. ϰŵĂůĞƐ͕ϮĨĞŵĂůĞƐ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϮŵĂůĞƐ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕ ;ǀŝŝͿ Ceriagrion ŶĞǁ ƐƉĞĐŝĞƐ Ͷ  ƐƉĞĐŝĞƐ ƚŚĂƚ ZE͖ ϭ ŵĂůĞ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ Ϯ ŵĂůĞƐ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ ϭ ĐůŽƐĞůLJ ƌĞƐĞŵďůĞƐ C. cerinorubellum͕ ĚŝīĞƌŝŶŐ ŝŶ ƚŚĞ ĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϮŵĂůĞƐ͕ ĂůŵŽƐƚ ĞŶƟƌĞůLJ ƌĞĚ ĂďĚŽŵĞŶ ĂŶĚ ĚĞƚĂŝůƐ ŽĨ ƚŚĞ ĂŶĂů 11.vii.2012, RN. ĂƉƉĞŶĚĂŐĞƐ͘ ^ŝŶĐĞ ŝƚƐ ĚŝƐĐŽǀĞƌLJ Ăƚ DĂůƵĚĂŵ ŝƚ ŚĂƐ ;ŝŝͿ /ĐƟŶŽŐŽŵƉŚƵƐ ĚĞĐŽƌĂƚƵƐ ŵĞůĂĞŶŽƉƐ ;^ĞůLJƐ͕ ĂůƐŽďĞĞŶĨŽƵŶĚĂƚƚǁŽƐŝƚĞƐŝŶƌƵŶĞŝ;EŐŝĂŵ͕ŽǁΘ ϭϴϱϴͿͶϭŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϬ͕Z͘ ŚŽŽŶŐŝŶƉƌĞƉĂƌĂƟŽŶͿ͘/ƚĂƉƉĞĂƌƐƚŽďĞĂƐƉĞĐŝĂůŝƐƚŽĨ ;ŝŝŝͿ Macrogomphus decemlineatus ;^ĞůLJƐ͕ ϭϴϳϴͿ ƉĞĂƚ ƐǁĂŵƉ ĂŶĚ ŬĞƌĂƉĂ ;ŝŶƚĞƌŵĞĚŝĂƚĞ ďĞƚǁĞĞŶ ƉĞĂƚ Ͷ tĞ ĂƌĞ ŶŽƚ ĂǁĂƌĞ ŽĨ ĂŶLJ ƉƵďůŝƐŚĞĚ ƌĞĐŽƌĚ ŽĨ ƚŚŝƐ

6768 Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2015 | 7(1): 6764–6773 KĚŽŶĂƚĂŽĨDĂůƵĚĂŵEĂƟŽŶĂůWĂƌŬ͕DĂůĂLJƐŝĂ ŽǁĞƚĂů͘ ZŽďŝŶtĞŶ:ŝĂŶŐEŐŝĂŵ © ZŽďŝŶtĞŶ:ŝĂŶŐEŐŝĂŵ ©

/ŵĂŐĞϳ͘/ĐƟŶŽŐŽŵƉŚƵƐĂĐƵƚƵƐ;ŵĂůĞͿ͘/ƚǁĂƐǀĞƌLJĂďƵŶĚĂŶƚĂůŽŶŐ /ŵĂŐĞϴ͘ƌĂĐŚLJŐŽŶŝĂŽƉŚĞůŝĂ;ĨĞŵĂůĞͿ͘dŚŝƐŝƐƚŚĞĮƌƐƚƌĞĐŽƌĚŽĨƚŚĞ ^ƵŶŐĂŝDĂůƵĚĂŵ͘ ƐƉĞĐŝĞƐŝŶ^ĂƌĂǁĂŬƐŝŶĐĞϭϵϭϬ͘

ƐƉĞĐŝĞƐŚĂǀŝŶŐďĞĞŶĐŽůůĞĐƚĞĚŝŶ^ĂƌĂǁĂŬƐŝŶĐĞƚŚĂƚŝŶ EĂƟŽŶĂůWĂƌŬŝƐƚŚĞƐĞĐŽŶĚƐŝƚĞŝŶ^ĂƌĂǁĂŬǁŚĞƌĞƚŚŝƐ >ĂŝĚůĂǁ;ϭϵϭϰͿŽĨƚǁŽŵĂůĞƐĐŽůůĞĐƚĞĚĨƌŽŵ͞<ƵĐŚŝŶŐ͟ŝŶ ƉŽŽƌůLJ ŬŶŽǁŶ ƐƉĞĐŝĞƐ ŚĂƐ ďĞĞŶ ĨŽƵŶĚ͖ ƚŚĞ ŽƚŚĞƌ ƐŝƚĞ DĂLJϭϴϵϲ͘dŚĞƐƉĞĐŝĞƐŝƐŬŶŽǁŶĨƌŽŵŽƌŶĞŽ͕^ƵŵĂƚƌĂ͕ ŝƐ ŝŶLJŽ WĞŶLJŝůĂŵ ƉƌŽƉŽƐĞĚ ŶĂƟŽŶĂů ƉĂƌŬ ŝŶ ŝŶƚƵůƵ ĞůŝƚƵŶŐ ĂŶĚ ƉĞŶŝŶƐƵůĂƌ DĂůĂLJƐŝĂ͕ ďƵƚ ŝƐ ƐĞůĚŽŵ ŝǀŝƐŝŽŶ;ŽǁΘhŶŐŐĂŶŐϮϬϭϬͿ͘/ƚŝƐĂůƐŽŬŶŽǁŶĨƌŽŵ ƌĞĐŽƌĚĞĚ͘ϮŵĂůĞƐ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ <ĂůŝŵĂŶƚĂŶ dĞŶŐĂŚ ĂŶĚ ĞůŝƚƵŶŐ͘ ϯ ŵĂůĞƐ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ϮŵĂůĞƐ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϮŵĂůĞƐ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕t͖Ϯ DĂĐƌŽŵŝŝĚĂĞ ŵĂůĞƐ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϮŵĂůĞƐ͕ ;ŝͿ Macromia cincta ZĂŵďƵƌ͕ ϭϴϰϮ Ͷ ϭ ŵĂůĞ͕ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ϵ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ ϭ ŵĂůĞ͕ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ ϭ ŵĂůĞ͕ ;ŝǀͿ ŚĂůLJďĞŽƚŚĞŵŝƐ ŇƵǀŝĂƟůŝƐ >ŝĞŌŝŶĐŬ͕ ϭϵϯϯ Ͷ Ϯ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ŵĂůĞƐ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϮŵĂůĞƐ͕ϲ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ŵĂůĞ͕ ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϯ ŵĂůĞƐ͕ Corduliidae 11.vii.2012, RN. ;ŝͿ Hemicordulia tenera >ŝĞŌŝŶĐŬ͕ ϭϵϯϬ Ͷ ϭ ŵĂůĞ͕ ;ǀͿ Nannophya pygmaea ZĂŵďƵƌ͕ ϭϴϰϮ Ͷ ϭ ϲ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϮŵĂůĞƐ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϱŵĂůĞƐ͕ϭĨĞŵĂůĞ ŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ Ϯ ŵĂůĞƐ͕ ;ŝŶ ƚĂŶĚĞŵͿ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ ϭ ŵĂůĞ͕ ϴ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ ϭ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕t͘ ŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϲŵĂůĞƐ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ ;ǀŝͿ EĞƵƌŽƚŚĞŵŝƐ ŇƵĐƚƵĂŶƐ ;&ĂďƌŝĐŝƵƐ͕ ϭϳϵϯͿ Ͷ ϭ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕Z͘ ;ǀŝŝͿ Orchithemis pruinans ;^ĞůLJƐ͕ ϭϴϳϴͿ Ͷ ϭ ŵĂůĞ͕ >ŝďĞůůƵůŝĚĂĞ 10.vii.2012, RN. ;ŝͿ Brachygonia oculata ;ƌĂƵĞƌ͕ ϭϴϳϴͿ Ͷ ϭ ŵĂůĞ͕ ;ǀŝŝŝͿ Orchithemis pulcherrima ƌĂƵĞƌ͕ ϭϴϳϴ Ͷ ϭ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ŵĂůĞ͕ ϭ ĨĞŵĂůĞ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ ϭ ŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭĨĞŵĂůĞ͕ϳ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ ;ŝdžͿ Orchithemis xanthosoma >ĂŝĚůĂǁ͕ ϭϵϭϭ Ͷ Ϯ ϮŵĂůĞƐ͕ϮĨĞŵĂůĞƐ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ϴ͘ǀŝŝ͘ϮϬϭϮ͕ ŵĂůĞƐ͕ ϭ ĨĞŵĂůĞ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϯ ŵĂůĞƐ͕ ϳ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ϯĨĞŵĂůĞƐ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕t͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕t͖ ZE͖ ϭ ŵĂůĞ͕ ϴ͘ǀŝŝ͘ϮϬϭϮ͕ t͖ ϭ ŵĂůĞ͕ ϵ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ϭĨĞŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭŵĂůĞ͕ϮĨĞŵĂůĞƐ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ ŵĂůĞ͕ ϵ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ ϭ ŵĂůĞ͕ ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ ϭ ŵĂůĞ͕ t͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭĨĞŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕t͘ 11.vii.2012, RN. ;ŝŝͿBrachygonia opheliaZŝƐ͕ϭϵϭϬ;/ŵĂŐĞϴͿͶdŚĞ ;džͿ Orthetrum chrysis ;^ĞůLJƐ͕ ϭϴϵϭͿ Ͷ ϭ ŵĂůĞ͕ ůĂƐƚƉƵďůŝƐŚĞĚƌĞĐŽƌĚŽĨƚŚŝƐƐƉĞĐŝĞƐĨƌŽŵ^ĂƌĂǁĂŬǁĂƐ ϴ͘ǀŝŝ͘ϮϬϭϮ͕t͖ ŵĂĚĞŝŶ<ƵĐŚŝŶŐŝǀŝƐŝŽŶŝŶϭϵϭϬ;>ĂŝĚůĂǁϭϵϮϬͿ͕ŵĂŬŝŶŐ ;džŝͿ Orthetrum sabina ;ƌƵƌLJ͕ ϭϳϳϯͿ Ͷ ϭ ŵĂůĞ͕ ƚŚŝƐ ƚŚĞ ĮƌƐƚ ƌĞĐŽƌĚ ŽĨ ƚŚĞ ƐƉĞĐŝĞƐ ĨƌŽŵ ƚŚĞ ƐƚĂƚĞ ĨŽƌ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ ŵŽƌĞƚŚĂŶϭϬϬLJĞĂƌƐ͘/ƚŝƐĂůŽĐĂůůLJŽĐĐƵƌƌŝŶŐƐƉĞĐŝĂůŝƐƚ ;džŝŝͿ Pornothemis serrata <ƌƺŐĞƌ͕ ϭϵϬϮ Ͷ ϭ ŵĂůĞ͕ ŽĨůŽǁƉ,ƐǁĂŵƉĨŽƌĞƐƚ͕ŬŶŽǁŶƚŽŽĐĐƵƌĂĐƌŽƐƐŽƌŶĞŽ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ Z͖ Ϯ ŵĂůĞƐ͕ ϲ͘ǀŝŝ͘ϮϬϭϮ͕ ZE͖ ϭ ĨĞŵĂůĞ͕ ĂŶĚŝŶƉĞŶŝŶƐƵůĂƌDĂůĂLJƐŝĂ͕ďƵƚǁŝƚŚǀĞƌLJĨĞǁƌĞĐŽƌĚƐ͘ϭ ϳ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕Z͖ϭŵĂůĞ͕ϭϬ͘ǀŝŝ͘ϮϬϭϮ͕ ŵĂůĞ͕ϵ͘ǀŝŝ͘ϮϬϭϮ͕ZE͖ϭĨĞŵĂůĞ͕ϭϭ͘ǀŝŝ͘ϮϬϭϮ͕ZE͘ Z͘ ;ŝŝŝͿBrachygonia puella>ŝĞŌŝŶĐŬ͕ϭϵϯϳͶDĂůƵĚĂŵ ;džŝŝŝͿ Rhodothemis rufa ;ZĂŵďƵƌ͕ ϭϴϰϮͿ Ͷ ϭ ŵĂůĞ͕

Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2015 | 7(1): 6764–6773 6769 Odonata of Maludam National Park, Malaysia Dow et al.

7.vii.2012, RN. DISCUSSION (xiv) Rhyothemis fulgens Kirby, 1889 — This species was treated as a junior synonym of R. pgymaea (Brauer, The results from this first Odonata collection in 1867) by Ris (1913), a course followed by almost all Maludam National Park are very encouraging, the subsequent authors, but is clearly distinct from true 48 species recorded offer a snapshot of the diversity R. pygmaea, differing substantially in the male anal present in the park; further surveys will surely uncover appendages; it appears that R. pygmaea occurs east of additional species. With a number of rare and specialist the Wallace line and that all records from west of the species, including three previously unknown to science, Wallace line actually refer to R. fulgens. This subject will it is already clear that Maludam National Park is an be treated in detail elsewhere (Dow in preparation). important area for odonate conservation and research 1 male, 6.vii.2012, RN; 1 male, 1 female (in tandem), in northern Borneo. One of the new species has 7.vii.2012, RN; 1 male, 10.vii.2012, RN. already been described in Dow & Ngiam (2013). Only (xv) Rhyothemis obsolescens Kirby, 1889 — 1 male, a single male specimen of this species, Prodasineura 6.vii.2012, RD. yulan, was collected. Description of the other two (xvi) Tyriobapta laidlawi Ris, 1919 — 3 males, new species (Podolestes new species cf. atomarius and 6.vii.2012, RD; 1 male, 6.vii.2012, RN; 1 male, 7.vii.2012, Ceriagrion new species) is in preparation. Besides the RD; 1 male, 7.vii.2012, RN; 2 males, 8.vii.2012, WA; 1 new species found, other important records were also male, 9.vii.2012, WA; 2 males, 1 female, 9.vii.2012, RD; made, including only the second record in Sarawak for 1 male, 9.vii.2012, RN; 1 male, 1 female, 10.vii.2012, Pachycypha aurea and Brachygonia puella, and the first WA; 2 males, 10.vii.2012, RD; 1 male, 10.vii.2012, RN; 2 record in Sarawak for over 100 years for Macrogomphus males, 11.vii.2012, WA. decemlineatus and Brachygonia ophelia. Due to time (xvii) Urothemis signata insignata (Selys, 1872) — 2 constraints and low water levels, the upper reaches males, 1 female, 6.vii.2012, RD; 1 female, 6.vii.2012, RN; of Ulu Maludam, where there are more pristine forest 1 male, 8.vii.2012, WA; 1 male, 11.vii.2012, WA; 1 male, areas, were not explored; this is a priority area for future 11.vii.2012, RN. work. (xviii) Zyxomma petiolatum Rambur, 1842 — 1 male, Species collected at Maludam National Park and 9.vii.2012, RN; 1 male, 10.vii.2012, RD. considered to be worthy of special attention from a conservation viewpoint, at least in Sarawak, are summarised in Table 1. For explanation of terms such as Data Deficient, Area of Occurrence etc., see

Table 1. Species collected in Maludam National Park in 2012 and potentially of conservation concern either within Sarawak, or globally.

Species Conservation concern Only one other, non-protected, site is known in Sarawak for this species. Outside of Sarawak it is only currently known Pachycypha aurea from a few sites in Kalimantan Tengah. Podolestes new species cf. atomarius Only known from Maludam National Park.

Podolestes harrissoni A peat swamp forest specialist species whose Extent of Occurrence has been seriously reduced. Only two other sites in Sarawak are known for this species; both are non-protected. Outside of Sarawak it is only Podolestes chrysopus known from old records from north-western Kalimantan. Amphicnemis annae A peat swamp forest specialist species whose Extent of Occurrence has been seriously reduced.

Ceriagrion new species Only known from Maludam National Park and two sites in Brunei.

Mortonagrion indraneil A peat swamp forest specialist species whose Extent of Occurrence has been seriously reduced.

Prodasineura yulan Only known from Maludam National Park. Currently listed as Near Threatened on the IUCN Red List, because of specialized habitat and a declining extent of Ictinogomphus acutus occurrence Macrogomphus decemlineataus Maludam National Park is the only location in Sarawak from which this species is currently known. Currently assessed as Data Deficient for the IUCN Red List, but likely to be re-assessed in a higher threat category as an Brachygonia ophelia extremely local low pH swamp forest specialist species. In Sarawak only currently known from Maludam National Park. Brachygonia puella Within Sarawak only one other site in is currently known for this species.

6770 Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2015 | 7(1): 6764–6773 Odonata of Maludam National Park, Malaysia Dow et al.

IUCN (2012). There is still insufficient data to make with peat swamp forest Odonata from Sumatra or its concrete statements about the rarity or otherwise of satellite islands; although some records from Sumatra many odonate species in Sarawak. However, any peat and Belitung must be from peat swamp forest, but swamp forest specialist species confined to Borneo can details of habitat are lacking from most records. From be reasonably assumed to be of serious conservation peninsular Malaysia data from peat swamp forest can concern, as peat swamp forest is undoubtedly an be found in Choong & Cheah (2013: Ayer Hitam in extremely threatened forest type in South-east Asia, Johor), Dow et al. (2010, 2012: the Sungai Bebar area known to have undergone a serious and continuing in Pahang) and Norma Rashid et al. (2001: Tasek Bera decline in its extent, and in the quality of what remains in Pahang; most records in this publication appear to be (e.g. Wong 2013, Posa et al. 2011); probably the only from open habitats around the margin of the lake Tasek truly pristine peat swamp habitats remaining on the Bera rather than from within the peat swamp forest that island are in Brunei. Moreover, as very little peat swamp borders part of the lake). forest is protected in Sarawak, peat swamp specialist Although there is an urgent need for far more data species occurring in the state have few secure refuges from the remaining peat swamp forest areas of Borneo, and are of significant conservation concern. sufficient data is now available to make some preliminary There are relatively few publications dealing observations about the specialist odonate fauna of peat specifically with the Odonata of peat swamp forest swamp forest of different parts of the island. and other low pH swamp forest formations in Borneo. For Anisoptera the available data suggests that many Orr (2001) includes records from peat swamp forest of the specialist species have relatively large ranges, some in Belait district of western Brunei, as do Thompson even extending beyond Borneo. However some of the & van Tol (1993). Considerable extra data from peat more widely distributed species, perhaps most notably swamp forest in northern Belait District was generated Brachygonia ophelia, are extremely local in occurrence. in 2013 as part of the Belait Biodiversity Action Plan We are not aware of any specialist anisopteran species project (Dow & Choong unpublished); this data will be confined to peat swamp forest in just one partof published in due course. Dow & Silvius (2014) deals Borneo. However it should be noted that many species with the peat swamp forests of Central Kalimantan, from the families Aeshnidae, Gomphidae, Macromiidae Indonesian Borneo; many records in Lieftinck (1953a,b) and Corduliidae are so difficult to sample in Borneo that must actually be from similar habitat, but details are it is entirely possible that some restricted range peat lacking. Yagi & Kitagawa (2001) presented records from swamp specialists have not yet been detected. degraded peat swamp forest in the Klias peninsula on For the more weakly flying Zygoptera the situation is the west coast of Sabah. For Sarawak, Dow & Unggang very different. In genera generally recognized as having (2010) discussed the odonate fauna of low pH swamp many swamp forest specialist species, e.g., Podolestes, forest at Binyo Penyilam in Bintulu Division, Dow & Amphicnemis and Mortonagrion, all the peat swamp Reels (2011) presented records from a peat swamp specialist species found in Borneo are endemic to the forest remnant in Kuching Division, and Dow & Reels island. Additionally the available evidence suggests that (2013) includes records from Sama Jaya Nature Reserve a number of the Bornean Platycnemididae formerly in Kuching Division (where the habitat may be best placed in Protoneuridae, e.g., members of Elattoneura characterized as kerapa – intermediate between peat sensu lato and Prodasineura, are specialists of low pH swamp and kerangas forest), from peat swamp forest at streams; of these only “Elattoneura” (sic) aurantiaca the Universiti Malaysia Sarawak campus in Samarahan and “Elattoneura” (sic) coomansi Lieftinck, 1937 are Division, and a few records from extremely disturbed known to occur outside of Borneo. peat swamp forest from the Simunjan area further west Within Borneo many of the peat swamp specialist in the same administrative division. As-yet-unpublished Zygoptera appear to have restricted ranges. Most of the data is also available from Loagan Bunut National Park Zygoptera known or believed likely to be peat swamp in Miri Division, and from highly disturbed peat swamp or other low pH swamp forest specialists occurring in forest habitats in the vicinity of Marudi in the lower Central Kalimantan appear to be confined to the peat Baram area of the same division. In Sundaland outside lands of southern Borneo (See Dow & Silvius (2014) of Borneo substantial areas of peat swamp forest and Dow (2014): Podolestes atomarius Lieftinck, occur in Sumatra and, to a lesser extent, in peninsular 1950; P. furcifer Lieftinck, 1950; Coeliccia new species; Malaysia; for these areas even less data is available. We “Elattoneura” erythromma Lieftinck, 1953;Prodasineura are not aware of any publications dealing specifically abbreviata Lieftinck, 1951; P. quadristigma Lieftinck,

Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2015 | 7(1): 6764–6773 6771 Odonata of Maludam National Park, Malaysia Dow et al.

1951; Prodasineura new species; Amphicnemis erminea classification and survey of taxonomic richness (Addenda 2013). Lieftinck, 1953; A. pandanicola Lieftinck, 1953; A. Zootaxa 3703: 1–82; http://dx.doi.org/10.11646/zootaxa.3703.1.9 Dijkstra, K.-D.B., V.J. Kalkman, R.A. Dow, F.R. Stokvis & J. van Tol platystyla Lieftinck, 1953; Amphicnemis triplex Dow, (2014). Redefining the damselfly families: the first comprehensive 2014 and an as-yet-un-named Amphicnemis species). molecular phylogeny of Zygoptera (Odonata). Systematic Entomology 39(1): 68–96; http://dx.doi.org/10.1111/syen.12035 As these low lying areas are almost isolated from Dow, R.A. (2012). Odonata collected at Gunung Pueh, Kuching Division, similar habitats in other parts of the island by extensive Sarawak, Malaysia in October 2012. International Dragonfly Fund mountain ranges, the high degree of endemicity to the Report 54: 1–21. Dow, R.A. (2014). Amphicnemis triplex sp. nov. from Central region may not be surprising. However even in northern Kalimantan, Indonesia (Odonata: Coenagrionidae). Odonatologica Borneo, many peat swamp specialist species appear to 43(1/2): 67–77. have small ranges. Amphicnemis madelenae Laidlaw, Dow, R.A., C.Y. Choong & Y.F. Ng (2010). A review of the genus Amphicnmemis in Peninsular Malaysia and Singapore, 1913 is only known from northwestern Kalimantan with descriptions of two new species (Odonata: Zygoptera: (Lieftinck 1954) and Kuching Division in Sarawak (e.g., Coenagrionidae). Zootaxa 2605: 45–55. Dow & Reels 2011, 2013). The status of a number of Dow, R.A., Y.F. Ng & C.Y. Choong (2012). Odonata of Sungai Bebar, Pahang, Malaysia, with four species recorded for the first time from forms allied to A. martini Ris, 1911 is unclear, but some mainland Asia. Journal of Threatened Taxa 4(3): 2417–2426; http:// may be distinct species with small ranges; at least one dx.doi.org/10.11609/JoTT.o3041.2417–26 of these is a peat swamp specialist. An unnamed peat Dow, R.A. & R.W.J. Ngiam (2013). Prodasineura yulan (Odonata: Zygoptera: Platycnemididae), a new species from Sarawak. Zootaxa swamp species of Coeliccia known from two sites in 3670(1): 87–90; http://dx.doi.org/10.11646/zootaxa.3670.1.8 Kuching and Samarahan divisions (Dow & Reels 2011, Dow, R.A. & G.T. Reels (2011). Odonata from a remnant patch of disturbed peatswamp forest on the outskirts of Kuching, west 2013) has not been found at Maludam or further Sarawak. Agrion 15(2): 50–51. east, while Coeliccia macrostigma Laidlaw, 1918 is Dow, R.A. & G.T. Reels (2013). Previously unpublished Odonata a peat swamp forest specialist only known from the records from Sarawak, Borneo. Part I. Kuching Division excluding Kubah National Park, and Samarahan Division. Faunistic Studies in lower Baram area (where virtually no suitable habitat South-East Asian and Pacific Island Odonata 3: 1–25. remains) and Belait District in Brunei. Two of the new Dow, R.A. & M. Silvius (2014). Results of an Odonata survey carried species found at Maludam (Podolestes new species and out in the peatlands of Central Kalimantan, Indonesia, in 2012. Faunistic Studies in South-East Asian and Pacific Island Odonata 7: Prodasineura yulan) have not been found anywhere else. 1–37. Podolestes chrysopus is only reliably known from north- Dow, R.A. & J. Unggang (2010). The Odonata of Binyo Penyilam, a west Kalimantan and Sarawak as far east as Maludam. unique tropical wetland area in Bintulu Division, Sarawak, Malaysia. Journal of Threatened Taxa 2(13): 1349–1358; http://dx.doi. However, Pachycypha aurea, which is a peat swamp org/10.11609/JoTT.o2478.1349-58 forest specialist, appears to have a wide distribution Hazebroek, H.P. & A.K.A. Morshidi (2000). National Parks of Sarawak. from Kalimantan Tengah to western Sarawak. We can Natural History Publications (Borneo), Malaysia, 502pp. IUCN (2012). IUCN Red List Categories and Criteria: Version 3.1. Second tentatively conclude that there is a “hot spot” for peat edition. Gland, Switzerland and Cambridge, UK: IUCN, iv+32pp. swamp Zygoptera endemicity and diversity in southern Kalkman, V.J. & G. Theischinger (2013). Generic revision of Kalimantan and possibly another in northwestern Argiolestidae (Odonata), with four new genera. International Journal of Odonatology 16(1): 1–52; http://dx.doi.org/10.1080/13 Kalimantan and southwestern Sarawak. What appears 887890.2012.749450 certain is that additional peat swamp specialist species Laidlaw, F.F. (1914). Contributions to a Study of the Dragonfly Fauna of Borneo. Part II. The Gomphinae and Chlorogomphinae. Proceedings remain undiscovered in the many poorly sampled parts of the Zoological Society of London, 1914: 51–63, plate I. of the lowlands of Borneo. As very little peat swamp Laidlaw, F.F. (1920). Contributions to the study of the dragonfly fauna forest has totally protected status in Borneo, many of of Borneo. Part IV. A list of species known to occur in the island. Proceedings of the Zoological Society of London, 1920: 311–342. the peat swamp specialist Odonata face an uncertain Lieftinck, M.A. (1935). New and little known Odonata of the Oriental future. and Australian Regions. Treubia 15(2): 175–207. Lieftinck, M.A. (1953a). Additions to the odonate fauna of the Indo- Australian archipelago. Treubia 22(1): 233–269. Lieftinck, M.A. (1953b). New dragonflies (Odonata) from Borneo, with REFERENCES notes on their habits and larvae. Treubia 22(2): 381–406. Lieftinck, M.A. (1954). Handlist of Malaysian Odonata. A catalogue of the dragonflies of the Malay Peninsula, Sumatra, Java and Choong, C.Y. & D.S. Cheah (2013). Odonata of Ayer Hitam Forest Borneo, including the adjacent small islands. Treubia (Suppl.) 22: Reserve, Johor, Peninsular Malaysia. Faunistic Studies in South-East i–xiii+202pp. Asian and Pacific Island Odonata 2: 1–11. Norma-Rashid, Y., A. Mohd-sofian & M. Zakaria-Ismail (2001). Dijkstra, K.D.B., G. Bechly, S.M. Bybee, R.A. Dow, H.J. Dumont, G. Diversity and distribution of Odonata (dragonflies and damselflies) Fleck, R.W. Garrison, M. Hämäläinen, V.J. Kalkman, H. Karube, in the freshwater swamp lake Tasek Bera, Malaysia. Hydrobiologica M.L. May, A.G. Orr, D.R. Paulson, A.C. Rehn, G. Theischinger, 459: 135–146. J.W.H. Trueman, J. van Tol, N. von Ellenrieder & J. Ware (2013). The Orr, A.G. (2001). An annotated checklist of the Odonata of Brunei with classification and diversity of dragonflies and damselflies (Odonata). ecological notes and descriptions of hitherto unknown males and In: Zhang, Z.Q. (ed.). Animal biodiversity: An outline of higher-level larvae. International Journal of Odonatology 4(2): 167–220.

6772 Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2015 | 7(1): 6764–6773 Odonata of Maludam National Park, Malaysia Dow et al.

Posa, M.R.C, L.S. Wijedasa & R.T. Corlett (2011). Biodiversity and Thompson, D.J. & J. van Tol (1993). Damselflies and dragonflies from Conservation of Tropical Peat Swamp Forests. BioScience 61(1): four forest types in Brunei. Brunei Museum Journal 8: 57–72. 49–57. UNDP (2006). Malaysia’s Peat Swamp Forests. Conservation and Ris, F. (1913). Libellulinen 7. Collections Zoologiques du Baron Edm. Sustainable use. United Nations Development Programme (UNDP), De Selys Longchamps. Catalogue Systématique et Descriptif 15: Malaysia, iv+33pp. 837–964, plate VII. Wong, J.L.M. (2003). Status of Peat Swamp Forest in Sarawk. Sarawak Foresty Corporation (2013). http://www.sarawakforestry. Malaysia / The Netherlands Joint Working Group on Sustainable com/htm/snp-np.html. Accessed 01 December 2013. Forest Management. Lee Miing Press Sdn. Bhd. Kuching, Sarawak, Selys Longchamps, E. de (1889). Odonates de Sumatra comprenant Malaysia, 40pp. les espèces recueillies à Pulo Nias par M. le Dr. E. Modigliani. Annali Yagi, T. & T. Kitagawa (2001). A survey of the dragonflies in the Klias Museo Civico Storia Naturale Genova 27: 444–484. and Binsulok Forest Reserves, Sabah, Malaysia. Nature and Human Activities 6: 31–39.

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