Resources Science, Volume. 42, Issue 5, 991(2020)

Spatiotemporal change of habitat quality in ecologically sensitive areas of eastern Qinghai-Tibet Plateau: A case study of the Hehuang Valley, Qinghai Province

Jie ZHU1, Jian GONG1,2、*, and Jingye LI1
Author Affiliations
  • 1School of Public Administration, China University of Geosciences, Wuhan 430074, China;
  • 2Key Laboratory of Rule of Law Research, Ministry of Natural Resources, Wuhan 430074, China
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    Figures & Tables(12)
    Geographical location and elevation of the Hehuang Valley
    Landscape type distribution of the study area
    Distribution of habitat quality of the Hehuang Valley, 1995-2015
    Habitat quality index changes in different regions
    Hotspots and coldspots of habitat quality of the Hehuang Valley
    Correlation between landscape pattern and habitat quality of the Hehuang Valley
    • Table 1. Flow transfer matrix

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      Table 1. Flow transfer matrix

      景观类型 1景观类型 2景观类型 3流出
      景观类型 1C12i=13j=31CijC13i=13j=31CijC12+13i=13j=31Cij
      景观类型 2C21i=13j=31CijC23i=13j=31CijC21+23i=13j=31Cij
      景观类型 3C31i=13j=31CijC32i=13j=31CijC31+32i=13j=31Cij
      流入C21+31i=13j=31CijC12+32i=13j=31CijC13+23i=13j=31Ciji=13j=13Cij-Cii
    • Table 2. Threat factors

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      Table 2. Threat factors

      威胁因子最大影响距离/km权重衰退类型
      建设用地8.001.00exponential
      国道6.001.00linear
      省道4.000.85linear
      高速公路2.000.80linear
      铁路2.000.80linear
      耕地4.000.70exponential
    • Table 3. Sensitivity of habitat types to each threat factor

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      Table 3. Sensitivity of habitat types to each threat factor

      地类名称生境适宜度建设用地国道省道高速公路铁路耕地
      林地1.000.800.800.800.800.750.70
      草地1.000.750.800.800.800.750.70
      水域0.800.700.650.650.650.600.65
      耕地0.400.400.400.400.400.300.25
      未利用地0.000.000.000.000.000.000.00
    • Table 4. Flow matrix of landscape type transformation, 1995-2015 (%)

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      Table 4. Flow matrix of landscape type transformation, 1995-2015 (%)

      1995年景观类型2015年景观类型
      草地耕地建设用地林地水域未利用地流出
      草地1.880.202.780.080.875.82
      耕地2.351.651.540.180.105.82
      建设用地0.030.180.020.020.010.26
      林地3.960.470.210.200.295.13
      水域0.050.090.020.120.030.31
      未利用地1.360.290.070.480.052.24
      流入7.752.912.164.940.531.3019.58
    • Table 5. Landscape metrics of the study area

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      Table 5. Landscape metrics of the study area

      年份景观破碎化指数
      NP/个PD/(个/hm2LPI/%AREA_MN/hm2DIVISION/%
      1995713720.2310.6298494.238097.25
      2005805822.8410.2255437.748497.58
      2015959727.2110.7360367.549997.59
      年份景观形状指数景观多样性指数
      ED/(m/hm2LSICONTAG/%SHDISHEI
      199513.986368.036858.12951.37700.7685
      200514.763071.683857.82271.38280.7717
      201515.579675.518057.06281.40370.7834
    • Table 6. Classification of habitat quality index values of the study area, 1995-2015

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      Table 6. Classification of habitat quality index values of the study area, 1995-2015

      等级1995年2005年2015年
      面积/km2占比/%面积/km2占比/%面积/km2占比/%
      2947.668.362880.008.163283.349.31
      中等4616.1713.094295.9112.184063.5811.52
      良好3233.359.173158.928.962829.078.02
      优等24476.5969.3924938.9370.7025097.7871.15
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    Jie ZHU, Jian GONG, Jingye LI. Spatiotemporal change of habitat quality in ecologically sensitive areas of eastern Qinghai-Tibet Plateau: A case study of the Hehuang Valley, Qinghai Province[J]. Resources Science, 2020, 42(5): 991

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    Paper Information

    Received: Sep. 6, 2019

    Accepted: --

    Published Online: Apr. 15, 2021

    The Author Email: GONG Jian (gongjian@cug.edu.cn)

    DOI:10.18402/resci.2020.05.16

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