Wildlife of
Shanxi Sheng

Primary Threats

• Coal mining, both underground and open-pit, plus waste piles, ground sinking and mine roads break up Lüliang/Taihang foothill habitats, pollute rivers with silt and heavy metals, and block mountain wildlife (including leopards and ungulate prey). Reclaimed land often replaces native plant patches with simple plantings.
• Past and current emissions from coal, coke making, and heavy industry cause long-term air pollution, harming plants and people, and causing acid rain. Industrial wastewater and mine drainage raise salt and metal levels in Yellow River and Fen River tributaries, stressing aquatic life and wetland food webs for waterbirds.
• Conversion and intensive use of valley bottoms for agriculture and urban/industrial land reduce wetlands, riparian belts, and lowland steppe remnants-key habitats for migratory waterbirds and foraging corridors between mountain blocks. Mountain forests are increasingly 'edge-dominated' due to road building and dispersed settlements.
• Expressways, rail lines, power corridors, and expanding wind/solar installations on ridgelines and plateaus increase fragmentation and collision/disturbance risk for large birds (e.g., storks, raptors), and open access into previously remote forest and shrubland used by sensitive species.
• Water scarcity is a limiting factor on the Loess Plateau; groundwater pumping and surface-water withdrawals for cities, industry, and irrigation reduce environmental flows in smaller tributaries and can shrink/seasonally dry wetlands, concentrating pollutants and limiting fish/amphibian reproduction.
• Check dams, river channelization, reservoirs, and flood-control works (common in loess catchments) alter sediment transport and seasonal flow pulses; while helpful for erosion control, they can simplify riparian habitat structure and reduce connectivity between floodplain wetlands and rivers used by breeding/stopover birds.
• Orchards and terraced cropland expansion in some counties, plus intensified fertilizer/pesticide use in valley agriculture, increase nutrient runoff to rivers/reservoirs and reduce native grass-shrub mosaics important for ground-nesting birds and small-mammal prey bases.
• Fuelwood collection in some rural areas, grazing pressure in steppe/forest-steppe margins, tourism at scenic mountain sites, and frequent vehicle traffic on forest roads can disrupt breeding of ground/understory birds (e.g., pheasants) and displace large mammals from preferred areas.
• Although illegal, snaring and opportunistic hunting persist in some mountainous areas, affecting pheasants, ungulates, and carnivores; prey depletion can indirectly constrain recovery of apex predators like the North China leopard.
• Local demand and supply chains can incentivize collection of raptors, songbirds, and some reptiles/amphibians, and create incentives for poaching of protected fauna despite enforcement; trade pressure is often highest near transport corridors and urban markets.
• Warming and increasingly variable precipitation on the Loess Plateau intensify drought stress, increase the frequency of extreme rainfall/erosion events, and can shift the steppe-forest boundary upslope; these changes affect spring water availability, wildfire risk, and breeding success for species dependent on stable riparian/understory moisture.
• Introduced or widely planted non-native species used in historical revegetation (notably black locust, Robinia pseudoacacia, in some areas) can form simplified stands that reduce native understory diversity; invasive ruderal plants along disturbed riverbanks and mine lands can outcompete native grasses/forbs, reducing habitat quality for steppe-associated fauna.
• Close interfaces among livestock, free-ranging dogs, and wildlife in mountain villages increase risks of pathogen spillover (e.g., canine diseases affecting carnivores) and can complicate recovery of predators and mesocarnivores where vaccination/management of domestic animals is limited.