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Chinese Journal of Applied Ecology ›› 2026, Vol. 37 ›› Issue (5): 1374-1382.doi: 10.13287/j.1001-9332.202605.013

• Special Features of Stable Isotope Ecology • Previous Articles     Next Articles

Effects of alpine meadow degradation on soil stable nitrogen isotope and its drivers.

WANG Qirui1,2, ZHOU Chunli3, ZHANG Chunqing4, Pengcuoji5, WANG Guiqiang1,2, MA Zifeng1,2, LI Yikang1*   

  1. 1Northwest Institute of Plateau Biology, Chinese Academy of Sciences, Xining 810008, China;
    2University of Chinese Academy of Sciences, Beijing 100049, China;
    3The Third Middle School of Liling City, Zhuzhou 412299, Hunan, China;
    4Huangyuan County Grassland Station, Xining 812199, China;
    5College of Ecological Environment and Resources, Qinghai Minzu University, Xining 810007, China
  • Received:2025-09-02 Accepted:2026-04-03 Online:2026-05-18 Published:2026-11-18

Abstract: The degradation of alpine meadow profoundly alters soil nitrogen (N) cycling. However, the stability of soil N pools and the response mechanisms of δ15N across different degradation stages remain unclear. In an alpine meadow of Maqin County, Qinghai Province, China, we investigated the effects of degradation on soil stable nitrogen isotopes (δ15N) and their driving factors. Four degradation stages were identified: non-degraded grass meadow (ND), Kobresia humilis + Kobresia pygmaea meadow (SD), thickened turf layer of K. pygmaea meadow (MD), and “black-soil beach” with secondary bare land (HD). The results showed that aboveground biomass significantly decreased with increasing degradation intensity, with biomass in the HD stage reduced to 56.5% of that in the ND stage. Degradation significantly reduced soil pH, electrical conductivity, and soil moisture in the 0-30 cm layer, and altered the vertical distribution pattern of soil C/N. Soil total nitrogen (TN) and microbial biomass nitrogen (MBN) declined markedly with increasing degradation, particularly in the surface soil (0-5 cm), with reductions of 57.8% and 70.6%, respectively. Meadow degradation significantly influenced the distribution of δ15N. In the SD and MD stages, δ15N values increased with soil depth, whereas in the HD stage they became homogenized. The difference in δ15N between surface and deep soil layers (Δδ15N) first decreased and then increased with degradation, approaching zero in the HD stage, indicating a highly open N cycle and homogenization of soil N across the profile. Random forest analysis revealed that the dominant drivers of δ15N varied among degradation stages. Ammonium (NH4+-N) dominated in the ND stage, soil pH in the SD and MD stages, and MBN in the HD stage. Surface soil δ15N was significantly negatively correlated with pH, electrical conductivity, soil moisture, C/N, TN, MBN, and NH4+-N, suggesting that degradation influenced N cycling primarily by altering surface soil environmental condition. In summary, alpine meadow degradation significantly affected soil N pools and N transformation efficiency by altering aboveground biomass and soil physicochemical properties. Δδ15N could serve as an effective indicator of the openness of ecosystem N cycling and degradation stage.

Key words: alpine meadow, degradation succession, soil nitrogen content, stable nitrogen isotope