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基于CLUE-S和InVEST模型的苏州市生境质量评估及预测

唐娇娇 余成 张委伟 陈德超

唐娇娇,余成,张委伟,等.基于CLUE-S和InVEST模型的苏州市生境质量评估及预测[J].环境工程技术学报,2023,13(1):377-385 doi: 10.12153/j.issn.1674-991X.20210657
引用本文: 唐娇娇,余成,张委伟,等.基于CLUE-S和InVEST模型的苏州市生境质量评估及预测[J].环境工程技术学报,2023,13(1):377-385 doi: 10.12153/j.issn.1674-991X.20210657
TANG J J,YU C,ZHANG W W,et al.Habitat quality assessment and prediction in Suzhou based on CLUE-S and InVEST models[J].Journal of Environmental Engineering Technology,2023,13(1):377-385 doi: 10.12153/j.issn.1674-991X.20210657
Citation: TANG J J,YU C,ZHANG W W,et al.Habitat quality assessment and prediction in Suzhou based on CLUE-S and InVEST models[J].Journal of Environmental Engineering Technology,2023,13(1):377-385 doi: 10.12153/j.issn.1674-991X.20210657

基于CLUE-S和InVEST模型的苏州市生境质量评估及预测

doi: 10.12153/j.issn.1674-991X.20210657
基金项目: 国家自然科学基金项目(41801148,41701477)
详细信息
    作者简介:

    唐娇娇(1995—),女,硕士研究生,主要从事环境规划与管理研究,2278918228@qq.com

    通讯作者:

    陈德超(1972—),男,教授,博士,主要从事环境规划与管理研究,dcchen2002@163.com

  • 中图分类号: X826

Habitat quality assessment and prediction in Suzhou based on CLUE-S and InVEST models

  • 摘要:

    评估城市化进程中土地利用变化下的生境质量演变,对于构建综合生态规划体系、应对全球可持续发展的重大挑战具有重要意义。基于苏州市2010年和2018年遥感影像解译的土地利用数据和社会经济等数据,选取高程、坡度、到公路的距离、人口密度等驱动因子,采用CLUE-S模型模拟多情景下2030年土地利用变化,并通过生态系统服务评估与权衡(InVEST)模型评估过去并预测未来的生境质量时空演变,探讨土地利用变化对生境质量的影响。结果表明:最优拟合尺度为400 m×400 m,Kappa系数达到0.854 5,模型能够很好地模拟研究区未来的土地利用格局;苏州市2030年生态保护情景下的生境质量优于2018年,而2030年自然增长情景下的生境质量差于2010年和2018年;从空间分布看,苏州市中心城区、工业较集中和人口活动强度大的地区生境质量差,太湖周边等水系发达地区生境质量较好。因此,未来研究区在发展经济的同时,更要注重生态保护,实现高质量发展。

     

  • 图  1  研究区域行政区划

    Figure  1.  Administrative division of the study area

    图  2  不同模拟尺度下各地类ROC变化

    Figure  2.  Changes in ROC of each land use type under different simulation scales

    图  3  苏州市2018年实际土地利用与模拟土地利用对比

    Figure  3.  Comparison of actual land use and simulated land use in Suzhou City in 2018

    图  4  苏州市2030年不同情景下土地利用模拟结果

    Figure  4.  Land use simulation results of different scenarios in Suzhou City in 2030

    图  5  苏州市过去、现状和未来不同情景下生境质量空间分布

    Figure  5.  Spatial distribution of past, present and future habitat quality in Suzhou under different scenarios

    表  1  各土地利用类型转换矩阵

    Table  1.   Transformation matrix of each land use type

    土地利用类型耕地水域建设用地其他用地
    耕地1111
    水域1111
    建设用地1111
    其他用地1111
      注:1表示可以相互转换。
    下载: 导出CSV

    表  2  胁迫因子的最大影响距离及其权重

    Table  2.   Maximum influence distance and weight of stress factors

    胁迫因子最大影响距离/km权重距离衰减函数
    耕地10.5线性
    建设用地2.50.7指数
    下载: 导出CSV

    表  3  生境适宜度及其对不同胁迫因子的敏感度

    Table  3.   Habitat suitability and its sensitivity to different stress factors

    土地利用类型生境适宜度敏感度
    耕地建设用地
    耕地0.50.30.5
    水域1.00.80.7
    建设用地000
    其他用地0.20.30.4
    下载: 导出CSV

    表  4  土地覆被模拟结果与现状数据对比

    Table  4.   Comparison of land cover simulation results and current data

    土地利用类型模拟正确的栅格数总栅格数模拟正确格栅数占比/%
    耕地16 96918 96989.46
    水域17 27619 19090.03
    建设用地12 45814 30787.07
    其他用地1 5021 64491.36
    合计48 20554 11089.09
    下载: 导出CSV

    表  5  2030年不同情景模拟下土地利用面积及占比

    Table  5.   Land use area and proportion under different scenarios in 2030

    土地利用
    类型
    2018年现状2030年
    自然增长情景
    2030年
    生态保护情景
    面积/km2占比/%面积/km2占比/%面积/km2占比/%
    耕地3 050.04 35.052 688.1831.052 849.9232.91
    水域3 070.4035.463 040.5735.123 068.9635.44
    建设用地2 289.1226.442 657.0130.692 469.7628.53
    其他用地263.043.05271.843.14268.963.12
    下载: 导出CSV

    表  6  各等级生境质量面积与占比

    Table  6.   Area and proportion of each grade of habitat quality

    等级生境质量指数2010年2018年2030年自然增长情景2030年生态保护情景
    面积/km2占比/%面积/km2占比/%面积/km2占比/%面积/km2占比/%
    0~0.21 045.6012.082 548.6429.442 503.2028.922 007.3623.18
    较差0.2~0.42 752.4831.792 644.9630.551 980.1622.872 277.6026.33
    中等0.4~0.62 159.2024.93914.5610.56462.405.341 425.6016.46
    较好0.6~0.8265.603.07448.325.181 375.0415.88473.445.46
    0.8~1.02 434.7228.132 101.1224.272 336.8026.992 473.6028.57
    下载: 导出CSV
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