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Final Report - Asian Development Bank

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een a significant lack of research and development into the needs of wild or controlled release programs<br />

through which the value of captive breeding could be exploited through the establishment of a secure wild<br />

population. There needs to be significant field research into habitat availability and food sources to<br />

ascertain what habitat management is necessary to achieve successful reintroductions.<br />

(v) Diversity in Target Species Biodiversity inventories of Qinling protected areas are generally<br />

thorough except for invertebrate taxa. Of the 38 globally threatened species in the Qinling, 34 species are<br />

non-migratory. The big “four” species receive most research and conservation attention: Giant Panda,<br />

Golden Takin, Sichuan Golden Monkey, and Crested Ibis. The remaining 30 species have been little<br />

studied and are seldom the target of conservation programs. These include 11 species of indigenous<br />

plants, six species of wetland vertebrates (four amphibians and two reptiles), one upland bird and one<br />

wetland bird, and eleven mammals. Study of 11 indigenous plants should also be a priority for<br />

simultaneous species recovery and ecosystem restoration. One plant species (Brown Moccasin Flower) is<br />

Critically Endangered, the most threatened of IUCN Red List categories.<br />

43. The globally threatened amphibians include Chinese Giant Salamander (Critically<br />

Endangered 12 ), a flagship species for mountain wetlands in China. While restoration of forests will<br />

indirectly benefit Qinling wetland habitats of Chinese Giant Salamander, more direct intervention is<br />

needed because of the pressure on Qinling rivers for gold mining and abstraction for transfer to other<br />

basins. Great investments have been made in commercial rearing of Chinese Giant Salamander, but these<br />

have not been matched by investments in field conservation. The 11 mammals include two species that<br />

will not directly benefit from habitat protection for Giant Panda: Desert Cat (Vulnerable) and <strong>Asian</strong> Wild<br />

Dog (Endangered). These species have different habitat needs and these will require dedicated study and<br />

management projects.<br />

(v) Captive Propagation. Conservation biology increasingly focuses on science-based management of<br />

people, habitats, and ecosystems. One successful conservation project in Shaanxi Province is the<br />

collaborative effort of SFD and WWF to conserve the Giant Panda by protecting and restoring its forest<br />

habitats and movement corridors in the Qinling Mountains ecosystem. There is, however, a tendency to<br />

approach conservation of wildlife in China from the perspective of captive propagation. Examples are<br />

Giant Panda, Crested Ibis, species of sturgeon and other fishes, and two sub-species of tiger. While<br />

successes have been achieved in captive breeding of some of these species, none of these programs has<br />

yet led to significant conservation gains for wild populations. Giant Panda and Crested Ibis numbers are<br />

increasing in the Qinling Mountains because of successful habitat management---not because of release of<br />

captive bred animals. Fisheries biologists world-wide have concluded that release of captive-bred fish<br />

from hatcheries can cause more problems than it solves. Russia has shown that habitat protection is the<br />

key to tiger conservation and all efforts are made to avoid taking Siberian Tigers into captivity. The<br />

captive rearing approach is taken world-wide only as a “last chance” strategy when numbers of a species<br />

have declined to a level where extinction in the wild is certain. The Qinling eco-region does not need<br />

more captive rearing and breeding programs to save threatened wildlife. Rather, as in the case of the<br />

Giant Panda, habitat protection and restoration is the priority for future investment based on scientific<br />

knowledge of the requirements of the species targeted for conservation.<br />

iv) Proposed Project Area<br />

44. The Project area comprises 458 km 2 (less than 1% of the Qinling Mountains) and is located on<br />

the northern slope of the Qinling Mountains adjacent to Louguantai Township. It is located in Zhouzhi<br />

County, 50km south and west of Xian with a travel time from Xian of less than one hour. The Project<br />

area includes: (i) the Tianyu River and the Chiyu River Valleys, (ii) the hill and plain area to the north of<br />

the Qinling Mountains, (iii) the existing Louguantai Historical and Cultural Area, (iv) a Hot Springs<br />

12<br />

Yet still harvested from the wild to build captive breeding programs for the local restaurant trade with apparent<br />

impunity from law enforcement

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