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Remote Sensing for Natural Resources    2025, Vol. 37 Issue (1) : 113-121     DOI: 10.6046/zrzyyg.2023271
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Identification of land use conflicts and zoning regulation in Nanchang City, China
WANG Jianping(), CHEN Meiqiu()
College of Land Resources and Environment, Jiangxi Agricultural University/ Research Center on Rural Land Resources Use and Protection, Jiangxi Agricultural University, Nanchang 330045, China
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Abstract  

The rapid social and economic development and the trend of human migration to large- and mid-size cities, especially provincial capitals, have significantly intensified land use conflicts. The coordination among production, living, and ecological spaces is significant for sustainable, regional social and economic development. This study created a multi-purpose suitability assessment model from the perspective of the production, living, and ecological functions, identified the production, living, and ecological suitability, as well as the intensity of potential land use conflicts, in Nanchang City, China while considering land space background and planning objectives for differentiated regional regulation. The results indicate that over 65% of areas in the city are suitable for production and living. Areas with ecological, productive, and living suitability differ in spatial distribution and structural composition and exhibit pronounced overlaps. This indicates potential land use conflicts. The conflict identification results reveal that the areas with severe, strong, moderate, and weak land use conflicts account for 0.53%, 18.81%, 5.77%, and 5.67%, respectively. Given the different spatial distributions, area proportions, and characteristics of areas with potential land use conflicts, differentiated regulations are required. Based on comprehensive considerations of the conflict identification results and the functional zoning stated in the Nanchang City Land and Space Master Plan (2021—2035), this study determined nine major zones for differentiated regulation. This study made some preliminary attempts in zoning regulation against land use conflicts while considering both land use suitability and the requirements for social and economic development. The results of this study will provide a scientific basis for identifying land use conflicts and optimizing land space layout in other similar cities.

Keywords land use conflict      multi-purpose suitability      production, living, and ecological functions      zoning regulation      Nanchang City     
ZTFLH:  F205  
  TP79  
Issue Date: 17 February 2025
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Jianping WANG
Meiqiu CHEN
Cite this article:   
Jianping WANG,Meiqiu CHEN. Identification of land use conflicts and zoning regulation in Nanchang City, China[J]. Remote Sensing for Natural Resources, 2025, 37(1): 113-121.
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https://www.gtzyyg.com/EN/10.6046/zrzyyg.2023271     OR     https://www.gtzyyg.com/EN/Y2025/V37/I1/113
Fig.1  Map of the study area
目标层 因素层 指标 因子分级及分值 权重
1 3 5 7 9
生产
适宜
坡度/(°) (25,+∞) (15,25] (6,15] (2,6] (-∞,2] 0.053 7
自然条件 海拔/m [-22,0]∪[800,+∞) (500,800) (250,500] (100,250] (0,100] 0.035 1
坡向 阴坡 半阴坡 半阳坡 阳坡 0.031 5
距离河流距离/m (2 000,+∞) (1 500,2 000] (1 000,1500] (500,1 000] (0,500] 0.040 8
开发便利度 距道路距离/m (5 000,+∞) (3 500,5 000] (2 000,3 500] (500,2 000] (0,500] 0.030 2
距居民点距离/m (5 000,+∞) (3 500,5 000] (2 000,3 500] (500,2 000] (0,500] 0.043 2
土地利用
现状
用地类型(三调地类编码) 05,07,08,09 00,03,04,12
及其他
10,11 06 01,02,1202 0.055 2
人均耕地面积(亩?(? 1 亩≈666.67 m2)/人) [0,0.05] (0.05,1] (1,1.5] (1.5,2] (2,+∞) 0.036 8
利用水平 单位耕地面积粮食产量/(kg·hm-1) [0,2 000] (2 000,4 000] (4 000,7 000] (7 000,10 000] (10 000,+∞) 0.052 1
生活
适宜

自然条件
坡度/(°) (25,+∞) (15,25] (6,15] (2,6] (-∞,2] 0.031 2
海拔/m [-22,0]∪(1 000,+∞) (800,1 000] (600,800] (400,600] (0,400] 0.024 5
土地利用
现状
用地类型(三调
地类编码)
12,00,01,1102 02,03,04 06,09 10,11及其他 05,07,08 0.022 4
与城镇中心的距离/m (5 000,+∞) (3 500,5 000] (2 000,3 500] (500,2 000] (0,500] 0.048 6
人口密度(人/hm2) (0,500]∪(7 000,+∞) (5 000,7 000] (3 000,5 000] (1 000,3 000] (500,1 000] 0.042 5
公共服务 与教育基础设施的
距离/m
(5 000,+∞) (3 500,5 000] (2 000,3 500] (500,2 000] (0,500] 0.041 6
与医疗设施的距离/m (5 000,+∞) (3 500,5 000] (2 000,3 500] (500,2 000] (0,500] 0.060 1
生态
适宜
自然条件 坡度/(°) (25,+∞) (15,25] (6,15] (2,6] (-∞,2] 0.030 2
海拔/m (1 000,+∞) (800,1 000] (600,800] (400,600] [-22,400] 0.031 9
景观破碎度 规则性差 规则性较差 规则性一般 规则性较好 规则性好 0.061 2
环境质量 植被指数 [0,0.05] (0.05,0.1] (0.1,0.3] (0.3,0.5] (0.5,+∞) 0.060 6
生物丰度 [0,1 259] (1 259,3 568] (3 568,7 136] (7 136,11 613] (11 613,+∞) 0.051 2

区位因素
与建设用地的距离/m (0,500] (500,2 000] (2 000,3 500] (3 500,5 000] (5 000,+∞) 0.070 9
距水体距离/m (5 000,+∞) (3 500,5 000] (2 000,3 500] (500,2 000] (0,500] 0.044 5
Tab.1  Multi-objective suitability evaluation index system and weight table of Nanchang City
一级冲突
类型区
二级冲突
类型区代码
二级冲突
类型区
“三生”适宜性组合
生产 生活 生态
用地适宜区(P) P1 生产适宜区 最适宜 较/一般/弱/不适宜 较/一般/弱/不适宜
较适宜 一般/弱/不适宜 一般/弱/不适宜
P2 生活适宜区 较/一般/弱/不适宜 最适宜 较/一般/弱/不适宜
一般/弱/不适宜 较适宜 一般/弱/不适宜
P3 生态适宜区 较/一般/弱/不适宜 较/一般/弱/不适宜 最适宜
一般/弱/不适宜 一般/弱/不适宜 较适宜
剧烈冲突区(HC) HC1 生产与生活剧烈冲突区 最适宜 最适宜 较/一般/弱/不适宜
HC2 生产与生态剧烈冲突区 最适宜 较/一般/弱/不适宜 最适宜
HC3 生活与生态剧烈冲突区 较/一般/弱/不适宜 最适宜 最适宜
HC4 “三生”剧烈冲突区 最适宜 最适宜 最适宜
强烈冲突区(SC) SC1 生产与生活中度冲突区 较适宜 较适宜 一般/不适宜/弱适宜
SC2 生产与生态强烈冲突区 较适宜 一般/不适宜/弱适宜 较适宜
SC3 生活与生态强烈冲突区 一般/不适宜/弱适宜 较适宜 较适宜
SC4 “三生”强烈冲突区 较适宜 较适宜 较适宜
中度冲突区(MC) MC1 生产与生活中度冲突区 一般适宜 一般适宜 不适宜/弱适宜
MC2 生产与生态中度冲突区 一般适宜 不适宜/弱适宜 一般适宜
MC3 生活与生态中度冲突区 不适宜/弱适宜 一般适宜 一般适宜
MC4 “三生”中度冲突区 一般适宜 一般适宜 一般适宜
微弱冲突区(LC) LC 微弱冲突区 一般适宜 弱/不适宜 弱/不适宜
弱/不适宜 一般适宜 弱/不适宜
弱/不适宜 弱/不适宜 一般/弱/不适宜
Tab.2  Empirical model of land use conflict identification
Fig.2  Spatial distribution of production, life and ecological suitability in Nanchang
适宜性等级 生产适宜性 生活适宜性 生态适宜性
面积/hm2 比例/% 面积/hm2 比例/% 面积/hm2 比例/%
最适宜 148 043.47 20.58 52 242.66 7.26 60 483.13 8.41
较适宜 261 413.48 36.33 201 816.26 28.05 163 820.13 22.77
一般适宜 169 848.58 23.61 213 672.35 29.70 104 812.65 14.57
弱适宜 105 498.56 14.66 167 532.29 23.28 53 983.64 7.50
不适宜 34 695.90 4.82 84 236.44 11.71 336 400.45 46.75
Tab.3  Statistics of production living and ecological suitability results
Fig.3  Identification results of potential land use conflict in Nanchang
一级冲
突类型
面积/hm2 比例/% 二级冲
突类型
面积/ hm2 比例/%
P 498 054.77 69.22 P1 263 220.44 36.58
P2 94 367.48 13.12
P3 140 466.85 19.52
HC 3 777.73 0.53 HC1 3 481.87 0.48
HC2 119.52 0.02
HC3 172.48 0.02
HC4 3.87 0.00
SC 135 348.99 18.81 SC1 75 041.20 10.43
SC2 37 758.39 5.25
SC3 12 196.35 1.70
SC4 10 353.05 1.44
MC 41 523.38 5.77 MC1 22 268.29 3.09
MC2 7 532.12 1.05
MC3 4 256.37 0.59
MC4 7 466.59 1.04
LC 40 795.12 5.67 LC 40 795.12 5.67
Tab.4  Result statistics of potential land use conflict areas
分区调
控类型
分区依据 主导用
地类型
面积/hm2 占比/% 调控措施
优先治理-城乡发展
区PM1
南昌大都市/安义绿色发展区/进贤综合发展区+剧烈冲突区/强烈冲突区 建设用地 33 267.99 4.62 优先治理,刚性与弹性的结合,一方面贯彻建设用地总量控制与永久基本农田保护,另一方面预留一定面积作为弹性用地,防止潜在土地利用冲突转化为现实
优先治理-粮食发展
区PM2
赣江下游粮食主产区/锦江流域粮食主产区/抚河流域粮食主产区/军山湖沿岸富硒农业区+剧烈冲突区/强烈冲突区 耕地、园地、其他农用地 82 352.32 11.45 优先治理,治理要点优先保护永久基本农田,HC3与SC3紧邻生活区的可划分为弹性城镇发展区
优先治理-生态保护
区PM3
鄱阳湖生态核心区/梅岭-峤岭/军山湖+剧烈冲突区/强烈冲突区 草地、林地、未利用地、水域 23 543.67 3.27 生态优先,HC1与HC2中连片性较好的划入耕地范围,严格管控建设用地扩张
重点治理-城乡发展
区KM1
南昌大都市/安义绿色发展区/进贤综合发展区+中度冲突区 建设用地 7 988.28 1.11 挖掘城市空间资源,防止优质耕地被建设用地占用,引导该区域发展设施农业和高价值经济作物来提升农业竞争力
重点治理-粮食发展
区KM2
赣江下游粮食主产区/锦江流域粮食主产区/抚河流域粮食主产区/军山湖沿岸富硒农业区+中度冲突区 耕地、园地、其他农用地 22 745.45 3.16 重点治理,治理要点优先保留生产适宜性,其他优化空间环境矛盾
重点治理-生态保护
区KM3
鄱阳湖生态核心区/梅岭-峤岭/军山湖+剧烈冲突区/强烈冲突区 草地、林地、未利用地、水域 10 586.07 1.47 生态优先,HC1与HC2中连片性较好的划入耕地范围,严格管控建设用地扩张
稳步推进-城乡发展
区SP1
南昌大都市/安义绿色发展区/进贤综合发展区+微弱冲突区/用地适宜区 建设用地 118 697.52 16.50 稳步持续推进城乡发展
稳步推进-粮食发展
区SP2
赣江下游粮食主产区/锦江流域粮食主产区/抚河流域粮食主产区/军山湖沿岸富硒农业区+微弱冲突区/用地适宜区 耕地、园地、其他农用地 265 407.20 36.89 稳步持续推进粮食种植
稳步推进-生态保护
区SP3
鄱阳湖生态核心区/梅岭-峤岭/军山湖+微弱冲突区/用地适宜区 草地、林地、未利用地、水域 154 911.50 21.53 可持续保护生态环境
Tab.5  Nanchang district regulation
Fig.4  Types of land use conflict regulation in Nanchang City
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