赵丽,,
陶金源,
张蓬涛
河北农业大学国土资源学院 保定 071000
基金项目: 河北省社会科学基金项目HB18GL053
详细信息
作者简介:陈雅倩, 主要研究方向为土地资源规划与利用。E-mail:chenyaqiann@163.com
通讯作者:赵丽, 主要研究方向为土地利用与评价、土地生态。E-mail:zhaoli1302@126.com
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出版历程
收稿日期:2019-12-09
录用日期:2020-03-31
刊出日期:2020-07-01
Habitat quality evaluation before and after unused land development based on InVEST model: A case study of Tang County
CHEN Yaqian,ZHAO Li,,
TAO Jinyuan,
ZHANG Pengtao
College of Land and Resources, Hebei Agricultural University, Baoding 071000, China
Funds: the Social Science Fund ProjectHB18GL053
More Information
Corresponding author:ZHAO Li, E-mail: zhaoli1302@126.com
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摘要
摘要:生境质量评价对生物多样性保护有至关重要的作用,为探究未利用地开发对唐县生境质量的影响,本文运用InVEST模型中的Habitat Quality模块分析2000年、2007年和2016年河北省唐县未利用地开发前后的生境质量变化情况。研究表明:1)2000—2016年,未利用地开发方向主要以草地、林地和耕地为主,未利用地比例从100%(以2000年未利用地面积为基数)减少到33.70%,草地、林地和耕地比例从0分别增加到27.43%、21.30%和10.46%。2)唐县未利用地斑块所占景观面积比逐年减少,其平均斑块面积由开发前的94.73 hm2减少到开发后的6.15 hm2;林地、水域和草地所占景观面积比例增加。未利用地开发后均匀度指数和多样性指数都有所增加,各景观组分所占面积比例差异减小,生态系统稳定性提高。3)未利用地开发后,研究区生境质量明显提升,生境质量得分由2000年的0.09上升到2007年的0.28,2016年又上升到0.39。研究结果可以为制定合理的土地规划以及土地开发工作中的生境及生物多样性保护等提供科学依据。
关键词:InVEST模型/
唐县/
未利用地/
景观指数/
生境质量
Abstract:At present, habitat quality is under constant threat due to the impact of human activities. Therefore, it is particularly important to assess habitat quality status and trends. In this study, the Habitat Quality module of InVEST model was used to analyze the impact of unused land development on habitat quality in Tang County, China in 2000, 2007, and 2016. The results showed that 1) from 2000 to 2016, the development direction for unused land was mainly grassland, forest land, and cultivated land. The proportion of unused land decreased from 100% (based on the unused land area in 2000) to 33.70%, whereas the proportion of grassland, forest land, and cultivated land increased from 0% to 27.43%, 21.30%, and 10.46%, respectively. 2) The proportion of unused land patches in the landscape area of Tang County decreased year by year. The average patch area decreased from 94.73 hm2 before development to 6.15 hm2 after development, and the forest land, water area, and grassland proportions in the landscape area increased. Furthermore, the evenness and diversity indexes increased after the unused land was developed and ecosystem stability improved. 3) After the exploitation of unused land, the habitat quality in the study area significantly improved, and the habitat quality score increased from 0.09 in 2000 to 0.28 in 2007, and then to 0.39 in 2016. The habitat quality high value areas were mainly located in the middle of the study area and northwest of Qijiazuo Town, the southern part of Huangshikou Town and the northern part of Yangjiao Town. However, the habitat quality in Chuanli Town, Juncheng Town, and Luozhuang Town, and in the southern region was lower. This study analyzed the impact of unused land development on habitat quality, and the results provide a scientific basis for making reasonable land planning decisions and for protecting habitat and biodiversity during land development.
Key words:InVEST model/
Tang County/
Unused land/
Landscape index/
Habitat quality
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图1唐县地理位置及高程图
Figure1.Position and elevation map of Tang County
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图2唐县未利用地开发前后生境质量空间分布图
Figure2.Spatial distribution of habitat quality before and after unused land exploitation in Tang County
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表1景观指数及其生态学含义
Table1.Landscape indexes and their ecological meaning
景观指数Landscape index | 生态学含义Ecological meaning |
斑块数量 Number of patches | 景观中斑块总数, 值越大表明景观异质性越高, 同时景观破碎度也越高。 The total number of patches in the landscape; the larger the value, the higher the heterogeneity of landscape and the higher the degree of landscape fragmentation. |
斑块密度 Patch density | 单位面积上某种类型斑块的个数, 反映斑块的密集程度。 The number of patches of some type per unit area, it reflects the density of plaques. |
平均斑块面积 Mean patch area | 景观总面积与斑块数量的比值, 值越大景观破碎度越低。 The ratio of the total landscape area to the number of patches; the larger the value, the lower the degree of landscape fragmentation. |
最大斑块指数 Largest patch index | 某一斑块类型中的最大斑块占据整个景观面积的比例, 其值的大小决定着景观中的优势种、内部种的丰度等生态特征, 反映人类活动的方向和强弱。 The proportion of the largest patch of a certain patch type of the whole landscape area, and its value determines the dominant species in the landscape, the abundance of internal species and other ecological characteristics, and reflects the direction and strength of human activities. |
斑块所占景观面积比 Area percent of patch to landscape | 某一斑块类型的总面积占整个景观面积的百分比, 反映景观中模地或优势景观元素。 The percentage of the total area of a certain patch type in the whole landscape area, it reflects the mold land or dominant landscape elements in the landscape. |
均匀度指数 Shannon’s evenness index | 反映景观组成的均匀度和优势度, 其值越大, 表明斑块类型越多或各景观组分所占比例越接近。 Reflecting the uniformity and dominance of landscape composition, the greater the value, the more types of patches or the closer the proportion of each landscape component. |
多样性指数 Shannon’s diversity index | 表示土地利用斑块类型的丰富程度, 反映土地生态系统结构的合理程度。 It represents the richness of land use patch type and reflects the reasonable degree of land ecosystem structure. |
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表2威胁源的最大影响距离、权重和空间衰退类型
Table2.Maximum distance of influence, weight and type of decay over space of threat factors
威胁因子 Threat factor | 最大影响距离 Max distance of influence (km) | 权重 Weight | 空间衰退类型 Type of decay over space |
城镇和农村居民点用地Urban and rural settlements | 1.0 | 1.0 | 线性Linear |
交通用地Transportation land | 0.5 | 0.6 | 线性Linear |
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表3不同土地利用类型生境适宜度及其对各威胁源的敏感度
Table3.Habitat suitability and sensitivity to various threat sources of different land use types
土地利用类型 Land use type | 生境质量得分 Habitat quality score | 威胁因子Threat factor | |
城镇和农村居民点用地 Urban and rural settlements | 交通用地 Transportation land | ||
耕地Cultivated land | 0.4 | 0.3 | 0 |
林地Forest land | 1.0 | 0.9 | 0 |
草地Grassland | 0.6 | 0.3 | 0.2 |
城镇和农村居民点用地Urban and rural settlements | 0 | 0 | 0.8 |
交通用地Transportation land | 0 | 0 | 0.8 |
水域Water area | 0.9 | 0.9 | 0.2 |
未利用地Unused land | 0.1 | 0.1 | 0.6 |
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表4唐县未利用地开发前(2000年)、开发后(2007年和2016年)土地利用转移矩阵
Table4.Transfer matrix of land use before (2000) and after (2007 and 2016) exploitation of unused land in Tang County?
年份 Year | 类型 Type | 耕地 Cultivated land | 林地 Forest land | 草地 Grassland | 城镇和农村居民点用地 Urban and rural settlements | 交通用地 Transportation land | 水域 Water area | 未利用地 Unused land |
2000—2007 | 未利用地Unused land | 11.34 | 14.01 | 17.72 | 3.83 | 0.69 | 0.45 | 51.96 |
2007—2016 | 耕地Cultivated land | 40.08 | 7.09 | 24.49 | 7.32 | 1.77 | 0.95 | 18.30 |
林地Forest land | 0.83 | 73.18 | 8.96 | 0.19 | 0.05 | 0.03 | 16.76 | |
草地Grassland | 10.32 | 16.51 | 43.81 | 3.50 | 0.81 | 0.20 | 24.85 | |
城镇和农村居民点 Urban and rural settlements | 7.04 | 1.66 | 20.20 | 52.93 | 5.83 | 1.31 | 11.03 | |
交通用地Transportation land | 2.90 | 0.11 | 15.40 | 27.83 | 8.74 | 10.41 | 34.61 | |
水域Water area | 3.70 | 0.92 | 18.34 | 6.33 | 6.58 | 59.87 | 4.26 | |
未利用地Unused land | 7.08 | 13.96 | 28.22 | 3.41 | 0.62 | 0.17 | 46.54 | |
2000—2016 | 未利用地Unused land | 10.46 | 21.30 | 27.43 | 5.49 | 0.99 | 0.63 | 33.70 |
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表5唐县未利用地开发前(2000年)、开发后(2007年和2016年)类型水平景观指数变化
Table5.Landscape indexes changes at type level before (2000) and after (2007 and 2016) exploitation of unused land in Tang County
地类 Type | 最大斑块指数 Largest patch index (%) | 斑块所占景观面积比 Area percent of patch to landscape (%) | 平均斑块面积 Mean patch area (hm2) | ||||||||||||
2000 | 2007 | 2016 | 2000 | 2007 | 2016 | 2000 | 2007 | 2016 | |||||||
耕地Cultivated land | 0.66 | 1.76 | 11.34 | 10.46 | 3.51 | 3.76 | |||||||||
林地Forest land | 4.25 | 4.97 | 14.00 | 21.27 | 6.31 | 3.48 | |||||||||
草地Grassland | 4.65 | 3.84 | 17.72 | 27.45 | 3.82 | 3.89 | |||||||||
城镇和农村居民点 Urban and rural settlements | 0.59 | 0.29 | 3.83 | 5.50 | 1.77 | 1.72 | |||||||||
交通用地Transportation land | 0.11 | 0.03 | 0.69 | 0.99 | 1.65 | 0.63 | |||||||||
水域Water area | 0.12 | 0.14 | 0.47 | 0.64 | 1.03 | 1.29 | |||||||||
未利用地Unused land | 95.94 | 20.24 | 4.51 | 100.00 | 51.95 | 33.69 | 94.73 | 11.87 | 6.15 |
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表6唐县未利用地开发前(2000年)、开发后(2007年和2016年)景观水平景观指数变化
Table6.Landscape indexes changes at landscape level before (2000) and after (2007 and 2016) exploitation of unused land in Tang County
年份 Year | 斑块数量 Patches number | 斑块密度 Patch density | 均匀度指数 Shannon’s evenness index | 多样性指数 Shannon’s diversity index |
2000 | 961 | 1.06 | 0 | 0 |
2007 | 15 881 | 17.50 | 0.70 | 1.35 |
2016 | 24 232 | 26.69 | 0.78 | 1.52 |
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表7唐县未利用地开发前(2000年)、开发后(2007年和2016年)各等级生境比例及生境平均值
Table7.Percentage of each habitat level and average value of habitat quality before (2000) and after (2007 and 2016) unused land exploitation in Tang County
生境质量得分 Habitat quality score | 比例Proportion (%) | ||
2000 | 2007 | 2016 | |
0~0.2 | 100.00 | 66.16 | 49.07 |
> 0.2~0.4 | 9.62 | 8.86 | |
> 0.4~0.6 | 12.79 | 24.04 | |
> 0.6~0.8 | 0.38 | 0.42 | |
> 0.8~1.0 | 11.05 | 17.61 | |
生境质量平均值 Average value of habitat quality | 0.09 | 0.28 | 0.39 |
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