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Remote Sensing for Natural Resources    2023, Vol. 35 Issue (4) : 201-213     DOI: 10.6046/zrzyyg.2022274
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County-scale land use/land cover simulation based on multiple models
HE Suling1,2,3(), HE Zenghong1,2,3, PAN Jiya1,2,3, WANG Jinliang1,2,3()
1. Faculty of Geography, Yunnan Normal University, Kunming 650500, China
2. Key Laboratory of Resources and Environmental Remote Sensing for Universities in Yunnan, Kunming 650500, China
3. Center for Geospatial Information Engineering and Technology of Yunnan Province, Kunming 650500, China
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Abstract  

Land use/land cover (LULC) simulation is essential for research on changes in land use. Based on the Google Earth Engine (GEE) platform, this study extracted the high-precision LULC information of Luquan County from 1991 to 2021 and analyzed the spatio-temporal evolution pattern. Then, this study analyzed the factors driving LULC changes using a random forest model and compared the simulation results of Luquan County obtained using the cellular automata-Markov (CA-Markov), land change modeler (LCM), future land use simulation (FLUS), and patch-generating land use simulation (PLUS). Finally, this study forecast the LULC change scenario in Luquan County in 2027 using the optimal model. The results show that: ① From 1991 to 2021, the spatial LULC pattern of Luquan County was dominated by forestland, grassland, and farmland. The areas of farmland and waterbodies increased by 89.26 km2 and 27.72 km2, respectively, the areas of forestland, construction land, and bare land increased continuously by 724.25 km2, 21.08 km2, and 13.67 km2, respectively, and the grassland decreased at an annual average rate of 29.20 km2; ② The LULC in Luquan County was primarily influenced by topographic conditions (elevation and slope); ③ The simulation effects of the four LULC models were in the order of PLUS > FLUS > CA-Markov > LCM, with Kappa coefficient of 0.63, 0.58, 0.46 and 0.35, respectively and the overall accuracy of 0.78, 0.75, 0.66 and 0.58, respectively; ④ The spatial LULC pattern in Luquan County in 2027 will share similarities with that in 2021. From 2021 to 2027, the areas of farmland land, grassland, and water bodies will decrease at a rate of 40.21 km2/a, 4.51 km2/a, and 0.70 km2/a, respectively, while the forestland, construction land, and bare land will expand by 265.52 km2, 4.85 km2, and 2.08 km2, respectively.

Keywords LULC      random forest      multi-model      Luquan County     
ZTFLH:  P94  
Issue Date: 21 December 2023
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Suling HE
Zenghong HE
Jiya PAN
Jinliang WANG
Cite this article:   
Suling HE,Zenghong HE,Jiya PAN, et al. County-scale land use/land cover simulation based on multiple models[J]. Remote Sensing for Natural Resources, 2023, 35(4): 201-213.
URL:  
https://www.gtzyyg.com/EN/10.6046/zrzyyg.2022274     OR     https://www.gtzyyg.com/EN/Y2023/V35/I4/201
Fig.1  Location of the study area
Fig.2  Comparison of different LULC products
Fig.3  Drivers of land use/land cover change
土地类型 耕地 林地 草地 水体 建设用地 裸地
耕地 1 1 1 1 1 1
林地 1 1 0 0 1 1
草地 1 1 1 1 1 1
水体 0 1 1 1 0 1
建设用地 1 1 1 1 1 1
裸地 0 1 1 1 0 1
Tab.1  Transfer rules between different land types
景观指数 公式 指标描述与意义
聚集度(AI) A I = g i j m a x g i j 式中gij为景观类型的相似邻接斑块数目。AI反映景观要素斑块的聚集程度,值越大,景观破碎度越低
平均斑块面积(AREA_MN) A R E A _ M N = A N 式中A为景观总面积; N为所有斑块数量。AREA_MN为反映景观结构的有效指标,值越大,景观破碎度越低
蔓延度(CONTAG) C O N T A G = 1 + i = 1 n j = 1 n p i f i j i = 1 n f i j l n p i f i j i = 1 n f i j 2 l n n × 100 式中pi为第i类斑块所占的面积百分比; fij为第i类和第j类斑块毗邻的数量; n为斑块总数。CONTAG反映景观斑块类型的团聚程度或延展趋势,值越大,景观破碎度越低
边缘密度(ED) E D = i n E i A × 10 - 6 式中Ei为第i类斑块边界总长度。ED越大,景观破碎度越高
景观形状指数(LSI) L S I = 0.25 i n e j i * A 式中 e i j *为景观斑块类型ji之间的边缘总长度。LSI反映景观斑块要素的形状。LSI越大,景观破碎度越高
斑块密度(PD) P D = i n N i A 式中Ni为第i类景观斑块数量。PD值越高,景观破碎度越高
Tab.2  Typical landscape indices for measuring landscape fragmentation
Fig.4  Temporal and spatial changes of LULC in Luquan from 1991 to 2021
地类 高程 坡度 年均降水 年均温度 距主要道路的距离 距主要河流的距离 人口密度
耕地 0.24 0.19 0.19 0.13 0.10 0.09 0.07
林地 0.22 0.17 0.15 0.16 0.11 0.12 0.07
草地 0.25 0.15 0.14 0.16 0.10 0.12 0.07
水域 0.37 0.30 0.05 0.04 0.03 0.09 0.13
建设用地 0.24 0.16 0.09 0.14 0.13 0.10 0.14
裸地 0.49 0.06 0.15 0.09 0.08 0.05 0.07
Tab.3  Importance of different drivers on LULC changes
地类 CA-Markov LCM FLUS PLUS
生产精度 用户精度 生产精度 用户精度 生产精度 用户精度 生产精度 用户精度
耕地 0.74 0.51 0.77 0.45 0.68 0.67 0.70 0.70
林地 0.74 0.89 0.60 0.85 0.85 0.85 0.87 0.87
草地 0.37 0.37 0.33 0.31 0.56 0.57 0.63 0.63
水域 0.46 0.77 0.35 0.60 0.41 0.73 0.61 0.88
建设用地 0.09 0.36 0.23 0.43 0.26 0.27 0.40 0.41
裸地 0.07 0.12 0.25 0.33 0.50 0.46 0.45 0.46
Kappa系数 0.46 0.35 0.58 0.63
总体精度 0.66 0.58 0.75 0.78
Tab.4  Accuracy of different land use/land cover simulation models
Fig.5  The area of different LULC types in Luquan County in 2021 simulated by the four models
Fig.6  The spatial pattern of LULC in Luquan County in 2021 simulated by 4 models
Fig.7  The LULC landscape fragmentation index simulated by the 4 models
Fig.8  Spatial distribution pattern and area of LULC in Luquan County in 2027
Fig.9  Landscape indices of different LULCs in Luquan County in 2021
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