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Final Report - Asian Development Bank

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22<br />

TA 4721-PRC: Preparing the Shaanxi-Qinling Mountains Integrated Ecosystem Management Project<br />

<strong>Final</strong> <strong>Report</strong> Appendix 5<br />

5. Data Gaps and Unresolved Issues<br />

a. Detailed Summary of Qinling Biodiversity<br />

88. The Qinling mountain ecosystem has been recognized for decades by many authorities and<br />

government at all levels as an extraordinary natural resource. Volumes have been written about the<br />

importance of the ecosystem and hundreds of scientific and popular manuscripts have been<br />

published, mainly in the Chinese, on various discrete issues. Only for Giant Panda have long-term<br />

research programs been undertaken and summary results published in formats relevant to<br />

conservation management. For other species and groups of species the research efforts and<br />

literature are fragmented, probably due to the scarcity of funding for applied long-term field research.<br />

Thus there is often detailed knowledge of the biology or ecology of a given species (e.g. the group<br />

sizes of Sichuan Golden Monkeys or Golden Takin and their seasonal distributions), but there is<br />

seldom adequate synthesis. This also results in part from the lack of funding for synthesis of past<br />

efforts and lessons learned. Two examples of the need for consolidation and interpretation of<br />

scientific information are: (i) summary of the three Giant Panda censuses and interpretation with<br />

respect to conservation of all recorded fauna besides Giant Panda; and (ii) summary of the semiannual<br />

transect surveys carried out by WWF and SFD in terms of implications for species<br />

management and recovery, and overall conservation biology of the Qinling. A third pressing need is<br />

for a consolidation of all Qinling research projects and publications related to biota and presentation of<br />

the results by species, community, vegetation type and other relevant categories. These efforts<br />

should look critically at past research projects to learn lessons that can guide future research.<br />

b. Crested Ibis<br />

89. Detailed studies have been completed mainly for the Giant Panda, Golden Takin, Sichuan<br />

Golden Monkey, and Crested Ibis. Of these four species, the one most urgently in need of<br />

conservation action is Crested Ibis. While the wild population on the south slope of the Qinling is<br />

increasing in size, it is the only wild population known in China. The two reasons listed by the Species<br />

Survival Commission of IUCN for reintroduction of captive animals to the wild are to augment the wild<br />

population and to increase genetic diversity of the wild population. The first of these reasons is<br />

applicable throughout virtually all of the former range of Crested Ibis where the species is extinct. The<br />

second reason might be applicable as well, although at least one researcher has reported<br />

abnormalities in the Yang County population that suggest inbreeding depression. The captive<br />

populations are self sustaining and reintroduction is under consideration in China and Japan.<br />

Reintroduction planning should focus on the captive population at Zhouzhi County to re-establish wild<br />

populations on the north slope of the Qinling and at select wetland nature reserves throughout the<br />

species former range.<br />

c. Non-charismatic and Globally Threatened Species<br />

90. Table 11 lists 37 species from the Qinling that are globally threatened, nine of which have<br />

been recorded on the Project Area. Of the nine, Chinese Giant Salamander is Critically Endangered.<br />

It has not been adequately addressed by research or by species management or recovery plans.<br />

Chinese Giant Salamander is farmed in the Qinling for food markets but its conservation in the wild<br />

remains ineffective due to habitat destruction (clear, clean mountain rivers) and hunting pressure.<br />

91. Two endangered species have been reported on the Project Area, Asiatic Wild Dog and<br />

Chinese Shrew Mole. Neither has been researched in the Qinling and no conservation management<br />

or species recovery plans address these species.<br />

92. Six globally vulnerable species have been recorded on the Project Area, two of which are<br />

members of the “big four” and have been adequately researched and addressed by conservation<br />

plans. The remaining four species (Chinese Softshell, Serow, Malaysian Porcupine, and Asiatic Black<br />

Bear) have not been adequately researched in the wild. Wild populations of Chinese Softshell and<br />

Asiatic Black Bear are under severe pressure from hunting/collecting for food markets. Chinese<br />

Softshell is farmed and wild terrapins are captured to supplement farm populations.<br />

93. In addition to the nine globally threatened species on the Project Area, 26 of the remaining<br />

28 globally threatened species in the Qinling are not among the “big four” and have not been<br />

adequately researched or addressed by conservation or recovery plans.

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