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1980—2020年永定河流域景观格局动态变化及驱动力分析

曹丽慧 郎琪 雷坤 王殿武 杨坤 杨文浩

曹丽慧,郎琪,雷坤,等.1980—2020年永定河流域景观格局动态变化及驱动力分析[J].环境工程技术学报,2023,13(1):143-153 doi: 10.12153/j.issn.1674-991X.20210881
引用本文: 曹丽慧,郎琪,雷坤,等.1980—2020年永定河流域景观格局动态变化及驱动力分析[J].环境工程技术学报,2023,13(1):143-153 doi: 10.12153/j.issn.1674-991X.20210881
CAO L H,LANG Q,LEI K,et al.Analysis on landscape pattern dynamics and driving force in Yongding River Basin from 1980 to 2020[J].Journal of Environmental Engineering Technology,2023,13(1):143-153 doi: 10.12153/j.issn.1674-991X.20210881
Citation: CAO L H,LANG Q,LEI K,et al.Analysis on landscape pattern dynamics and driving force in Yongding River Basin from 1980 to 2020[J].Journal of Environmental Engineering Technology,2023,13(1):143-153 doi: 10.12153/j.issn.1674-991X.20210881

1980—2020年永定河流域景观格局动态变化及驱动力分析

doi: 10.12153/j.issn.1674-991X.20210881
基金项目: 国家水体污染控制与治理科技重大专项项目(2018ZX071-110-02)
详细信息
    作者简介:

    曹丽慧(1997—),男,硕士研究生,主要从事土壤养分资源与景观生态研究,caolihui1997@163.com

    通讯作者:

    郎琪(1988—),女,副研究员,主要从事流域水生态健康评估与生态退化机制研究,langqi1988@163.com

  • 中图分类号: X522

Analysis on landscape pattern dynamics and driving force in Yongding River Basin from 1980 to 2020

  • 摘要:

    为研究高原—山区—平原—滨海生态要素梯级流动特性的流域景观格局动态变化规律,以永定河流域1980—2020年7期Landsat遥感影像为主要数据源,综合运用景观面积动态分析、景观格局指数和数理统计等方法分析了近40年来永定河流域景观格局演变特征,并揭示其驱动因子。结果表明:1)1980—2020年流域土地利用类型以耕地、林地、草地为主,面积占比约90%;近40年,耕地、草地面积分别减少1 376.38、463.42 m2,建设用地、林地面积增加,综合土地利用动态度在2015—2020年变化最大。2)在类型水平上,建设用地斑块破碎程度明显降低,其余用地类型变化不明显;景观水平上,香农多样性指数(SHDI)由1.29增至1.35,香农均匀度指数(SHEI)由0.67增至0.75,景观整体结构趋向复杂,异质性增加,团聚程度下降,景观破碎化加剧。3)流域景观格局变化受社会经济因素、自然因素和政策因素共同影响,其中社会经济发展为主要驱动力,经济发展和城乡人口结构变化是景观格局变化的主要驱动因子。

     

  • 图  1  研究区水系与地形

    Figure  1.  Rivers and topographic condition of the study area

    图  2  1980—2020年永定河流域各时期土地利用类型空间分布

    Figure  2.  Spatial distribution of land use types in Yongding River Basin in different periods from 1980 to 2020

    图  3  1980—2020年土地利用转移状况空间分布

    Figure  3.  Spatial distribution of land use change from 1980 to 2020

    图  4  永定河流域类型水平景观格局变化

    Figure  4.  Landscape pattern change of Yongding River Basin at type level

    图  5  1980—2018年研究区社会经济发展状况

    Figure  5.  Socio-economic development of the study area from 1980 to 2018

    图  6  1980—2018年研究区气候环境变化

    Figure  6.  Climate and environmental changes in the study area from 1980 to 2018

    表  1  景观指数的选取及作用

    Table  1.   Selection and function of landscape index

    景观指数在景观中的作用
    斑块数量(NP)反映斑块数量多少,NP增多景观破碎度升高,反之降低
    斑块平均面积(MPS)反映某一类型斑块平均面积,MPS增大,
    斑块破碎度降低
    最大斑块指数(LPI)反映最大斑块占景观面积比例,LPI大则景观破碎度降低,反之升高
    相似临近百分比(PLADJ)反映斑块类型在景观中的比例,若斑块类型达到最大程度散布,PLADJ最小
    面积加权分维数 (FRAC_AM)反映斑块形状的复杂性,FRAC_AM越靠近1,形状愈简单;越靠近2,形状愈复杂
    斑块结合度指数(COHESION)反映景观类型自然连接性,当斑块类型
    分布聚集,COHESION增加
    蔓延度指数(CONTAG)反映不同斑块间聚集和延展程度,高蔓延度表明景观类型连接性较好
    散布并列指数(IJI)反映各斑块类型间总体散布与并列情况,IJI增大,表明斑块分布趋向均匀,彼此临近
    香农多样性指数(SHDI)反映景观要素和景观要素所占比例变化,SHDI增大,表明景观系统中土地利用越丰富,
    破碎化程度越高
    香农均匀度指数(SHEI)SHEI趋近1,表明景观中没有优势类型,斑块
    分布均匀,有最大多样性
    下载: 导出CSV

    表  2  永定河流域1980—2020年土地利用类型面积及占比

    Table  2.   Area and proportion of land use types in Yongding River Basin from 1980 to 2020

    年份耕地林地草地水域建设用地未利用地
    面积/km2占比/%面积/km2占比/%面积/km2占比/%面积/km2占比/%面积/km2占比/%面积/km2占比/%
    198021 865.0345.1510 246.7621.1612 572.6925.96992.832.052 553.975.27193.380.40
    199521 633.5444.6710 006.2520.6612 706.6026.24999.402.062 880.885.95197.990.41
    200021 624.5744.6610 005.2020.6612 699.5826.23996.722.062 901.315.99197.110.41
    200521 342.2144.0710 013.8420.6812 771.8326.37927.511.923 153.006.51216.110.45
    201021 378.6344.1610 219.6221.1112 736.5226.31850.381.763 026.386.25196.600.41
    201520 879.3043.1210 175.7721.0112 763.1326.36915.991.893 485.537.20205.170.42
    202020 488.6542.3110 619.0421.9312 109.2725.01882.591.824 163.958.60161.430.33
    下载: 导出CSV

    表  3  1980—2020年永定河流域土地利用转移矩阵

    Table  3.   Land use transfer matrix of Yongding River Basin from 1980 to 2020

    土地利用类型耕地林地草地水域建设用地未利用地2020年合计
    耕地19 466.02504.32442.24103.521 331.2119.0121 866.32
    林地231.019 495.23365.2516.22136.131.0210 244.86
    草地483.56580.6511 206.3329.35257.3214.2112 571.42
    水域135.3322.0244.18722.5652.2116.32992.62
    建设用地126.5410.2330.2210.852 378.540.002 556.38
    未利用地43.016.2420.132.0210.11111.02192.53
    1980年合计20 485.4710 618.6912 108.35884.524 165.52161.5848 424.13
    下载: 导出CSV

    表  4  永定河流域1980—2020年土地利用动态度变化

    Table  4.   Dynamic degree change of land use in Yongding River Basin from 1980 to 2020 % 

    年份区间单一土地利用动态度综合土地利用动态度
    耕地林地草地水域建设用地未利用地
    1980—1995−0.07−0.160.070.040.850.160.06
    1995—2000−0.010.00−0.01−0.050.14−0.090.01
    2000—2005−0.260.020.11−1.391.731.930.15
    2005—20100.030.41−0.061.66−0.80−1.810.10
    2010—2015−0.47−0.090.041.543.030.870.23
    2015—2020−0.370.87−1.02−0.733.89−4.260.46
    下载: 导出CSV

    表  5  永定河流域景观水平景观格局指数

    Table  5.   Landscape pattern index of Yongding River Basin at landscape level

    年份LPI/%IJI/%CONTAG/%SHDISHEI
    19807.1457.9060.471.290.67
    19957.0957.9260.191.310.67
    20007.0857.9260.171.310.67
    20057.0958.0359.991.320.68
    20106.9256.9760.311.310.67
    20156.8965.6756.181.330.74
    20206.6766.3355.861.350.75
    下载: 导出CSV

    表  6  旋转后主成分因子载荷

    Table  6.   Principal component factor load after rotation

    指标因子人均GDPGDP第三产业产值第二产业产值第一产业产值城镇人口农村人口年蒸发量人口总数年均气温相对湿度年均降水量
    主成分10.9970.9940.9850.9780.9690.959−0.944−0.9260.8280.801−0.1190.276
    主成分20.0220.0420.0060.0800.2270.1770.168−0.0880.3260.3400.6800.648
    下载: 导出CSV
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  • 收稿日期:  2021-12-29

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