Wildlife of
Xizang Zizhiqu

Primary Threats

• Warming on the Tibetan Plateau melts glaciers and changes snowpack, altering runoff that feeds alpine wetlands and river valleys important for black-necked cranes. Permafrost thaw and road damage lead to more construction that breaks up habitat. Shrub spread and plant shifts lower food for Tibetan gazelle and kiang.
• New and bigger roads, power lines, and quarrying break up open steppe and mountain passes used by snow leopard prey and Tibetan antelope. Such infrastructure also eases poaching and disturbance, and fences block seasonal moves in Changtang and northern TAR.
• Hard-rock mining and associated exploration (including new access tracks, camps, and tailings) can degrade alpine grasslands and pollute headwater catchments. In remote basins, even small mines can have outsized impacts because recovery is slow in cold, arid high-elevation environments.
• Land change is rare at very high elevations, but local loss is large in river valleys and lower mountain areas where towns, tourist sites, and farms cluster. In southeast forest gorges, loss and breaking up of habitat hurt small-range species (red panda, forest pheasants) more than wide-ranging steppe animals.
• Hydropower planning and river engineering in major basins (notably the Yarlung Tsangpo/Brahmaputra system) can modify flow regimes, disrupt riparian habitats, and affect fish and wetland dynamics. Wetland drainage or water diversion around towns and pasture bases can reduce breeding habitat for black-necked cranes and other waterbirds.
• Snow leopards and wolves kill yaks, sheep, and goats, causing people to kill predators in return and push for lethal control near large reserves. Bears raid crops and property in forests and ecotone areas, hurting households that rely on a short growing season.
• While large-scale commercial hunting has declined, opportunistic illegal hunting persists in remote rangelands (e.g., targeting ungulates for meat), and retaliatory killing of predators remains a risk. Accessibility increases from new roads can elevate hunting pressure in previously hard-to-reach areas.
• Historic demand for Tibetan antelope shahtoosh and ongoing markets for musk (musk deer) and furs create incentives for poaching, particularly along transport corridors and near border trade routes. Enforcement has improved, but high value and remoteness maintain residual risk.
• Wastewater and solid waste from rapidly growing tourism nodes (e.g., around major lakes and scenic corridors) can contaminate alpine wetlands and lakes where dilution is limited. Localized heavy-metal and acid drainage risks occur near mines and ore-processing sites, threatening headwater streams.
• Rangeland productivity can be reduced by sustained high grazing pressure in some pastoral areas, compounded by drought years. Collection of fuelwood in treeline ecotones and intensive harvesting of high-value medicinal plants (where unmanaged) can degrade fragile alpine vegetation communities.
• Disease transmission between domestic livestock and wild ungulates (e.g., respiratory infections, brucellosis-like syndromes, and other pathogens) is a concern where herds overlap with kiang, bharal (blue sheep), and wild yak. Dog-associated diseases and stray dog predation/disturbance can also affect ground-nesting birds and small mammals near settlements.
• Tourism growth (vehicle convoys, trekking, pilgrimage traffic, drone use) increases disturbance at key wildlife sites, especially wetlands used by black-necked cranes and high passes used by ungulates. Winter disturbance can be particularly costly energetically for wildlife in extreme cold and low-oxygen conditions.
• Large-scale commercial logging has been curtailed in many areas, but localized illegal cutting and fuelwood extraction in the southeast's montane forests can still degrade habitat structure and increase erosion risk in steep gorges.
• Expansion is geographically limited by elevation and climate, but valley-bottom cropland and greenhouse agriculture can encroach on riparian corridors and wetlands, reducing habitat for waterbirds and creating conflict points with wildlife attracted to crops.
• Invasives are less widespread at very high elevations, but disturbed corridors (roadsides, town margins) can introduce non-native or weedy species that alter local plant communities. Stocking or accidental introduction of non-native fish into cold lakes/streams can affect native highland aquatic communities where it occurs.
• Urban growth is concentrated around Lhasa and major county seats, where construction footprints, new ring roads, and peri-urban development increase pressure on nearby river corridors and wetlands and raise demand for sand/gravel extraction from riverbeds.
• Fishing pressure is generally low compared to lowland China, but localized overharvest in accessible rivers and lakes (especially near towns and tourist areas) can reduce native fish populations; combined with flow modification, this can affect broader aquatic food webs.