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半岛丘陵区城市周边永久基本农田划定研究——以山东省海阳市为例

本站小编 Free考研考试/2022-01-01

张雅芹1,,
闫弘文1,,,
赵贤锋2,
孙世清3
1.山东师范大学地理与环境学院 济南 250300
2.烟台市国土资源局 烟台 264003
3.海阳市国土资源局 海阳 265100
基金项目: 山东省海阳市政府采购项目HYHAYT2016-486

详细信息
作者简介:张雅芹, 研究方向为土地评估规划与开发整理。E-mail:2366479731@qq.com
通讯作者:闫弘文, 研究方向为土地评估规划与开发整理。E-mail:preyan@163.com
中图分类号:F301.24

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出版历程

收稿日期:2017-11-04
录用日期:2018-02-05
刊出日期:2018-07-01

Permanent prime farmland demarcation in city periphery in peninsula hill areas: A case of Haiyang City in Shandong Province

ZHANG Yaqin1,,
YAN Hongwen1,,,
ZHAO Xianfeng2,
SUN Shiqing3
1. College of Geography and Environment, Shandong Normal University, Jinan 250300, China
2. Yantai Municipal Bureau of Land and Resources, Yantai 264003, China
3. Haiyang Municipal Bureau of Land and Resources, Haiyang 265100, China
Funds: the Procurement Project of the Haiyang Municipal Government, Shandong Province, ChinaHYHAYT2016-486

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Corresponding author:YAN Hongwen, E-mail: preyan@163.com


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摘要
摘要:基本农田红线是土地利用总体规划“三线”划定的重中之重,城市周边永久基本农田的划定是基本农田红线划定工作中的难点。本研究以半岛丘陵区山东省海阳市为例,以“三线”协同划定的思想为切入点,采用生态优先、建设用地严格举证、优质耕地尽量划入永久基本农田和市场配置资源的思路,将生态安全网络构建、建设用地适宜性评价、耕地质量综合评价等多种方法有机结合,并对土地评价和立地分析(LESA)方法进行改进,通过Arcgis空间分析功能,综合划定海阳市城市周边永久基本农田。结果表明:1)生态安全网络中耕地面积为12.11 hm2,优先建设区与重点建设区中已举证的耕地面积为154.99 hm2,此部分耕地均不适宜划入永久基本农田。2)根据耕地综合质量分值将耕地划分为4个等级,其中,优先划入型和适宜划入型耕地,自然质量和立地条件均比较优越,可划定为永久基本农田,重点调控型和后备资源型耕地则不宜划入;其中优先划入型耕地面积为458.05 hm2,将其中427.82 hm2划入永久基本农田,适宜划入型耕地面积为771.83 hm2,将其中500.67 hm2划入永久基本农田。3)划定后城市周边永久基本农田面积1 305.22 hm2,新划入永久基本农田的耕地面积为928.49 hm2,占城市周边耕地总面积的60.26%,永久基本农田保护率提高了42.66%,永久基本农田中耕地的国家利用等平均值(9.04)高于全市耕地平均利用等别(9.56),且坡度均低于15°。4)城市周边生态安全用地、永久基本农田、建设用地空间布局更加优化,有利于城市的有序发展和土地的可持续利用。本研究采用基于改进的LESA评价方法,并综合考虑生态安全用地、永久基本农田和建设用地的空间布局,丰富了永久基本农田划定方法,达到了海阳市城市周边永久基本农田划定目标;同时研究结果具有较强的实用性,为海阳市永久基本农田的保护和土地利用总体规划“三线”划定工作提供了科学依据。
关键词:半岛丘陵区/
城市周边/
永久基本农田/
生态安全网络/
建设用地适宜性/
耕地自然质量/
LESA体系/
“三线”协同
Abstract:The red lines of prime farmlands constitute the top priority of the "Tri-Line" demarcation of general land use planning. The demarcation of permanent prime farmlands in city periphery has been of great significance for controlling city unlimited sprawl, stabilizing farmland area and ensuring food security of the country. Using Haiyang City in Shandong Province as a case study, this study developed a land planning strategy for the study area based on the "Tri-Line"-coordinating demarcation process. The study adopted procedures of ecological priority, strict construction land evidence, positive demarcation of high-quality cultivated land and market resources allocation to integrate ecological safety network, suitable evaluation of construction land and comprehensive evaluation of cultivated land to demarcate the permanent prime farmland in the study area. To comprehensively evaluate the cultivated land quality, the land evaluation and site assessment (LESA) method was improved, and ArcGIS was used to analyze spatial distribution of cultivated land patch. The results showed that the area of cultivated lands in ecological safety network was 12.11 hm2, and those in the priority construction region and important construction region was 154.99 hm2, both were not suitable for permanent prime farmland. The cultivated land in the city periphery was divided into 4 grades based on comprehensive quality scores. The priority area and suitable area were designated as permanent prime farmland, where the natural quality and site condition were superior. Then the controlled area and reserved area were not included in this division. About 458.05 hm2land was in the priority region, of which 427.82 hm2 of the cultivated land was classified as permanent prime farmland. About 771.83 hm2 land was classified as suitable area, of which 500.67 hm2 was permanent prime farmland. After demarcation, the area of permanent prime farmland around Haiyang City was 1 305.22 hm2, of which newly cultivated land formed 928.49 hm2, accounting for 60.26% of the total cultivated land around the city. Overall, permanent prime farmland protection rate increased by 42.66%. The average use index of cultivated land in permanent prime farmland (9.04) was higher than that of cultivated land in the whole city (9.56), and the slope of the permanent prime farmland was less than 15°. 4) The layout of ecological security land, permanent prime farmland and construction land around the city was more optimized in favor of the orderly development of the city and the sustainable use of the land. In summary, based on the improved LESA evaluation method and comprehensive consideration of layout space of ecological security land, permanent prime farmland and construction land, the study enriched the demarcation method of permanent prime farmlands and achieved permanent prime farmland demarcation in Haiyang City. At the same time, the results of the study were practicable and provided the scientific basis for the protection of permanent prime farmlands and the application of "Tri-Line" demarcation in general land use planning.
Key words:Peninsula hill area/
City periphery/
Permanent prime farmland/
Ecological safety network/
Construction land suitability/
Cultivated land natural quality/
LESA system/
"Tri-Line" coordination

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图1海阳市城市周边生态安全网络布局
Figure1.Ecological security network layout of city periphery in Haiyang City


下载: 全尺寸图片幻灯片


图2海阳市城市周边建设用地适宜性评价分区
Figure2.Zoning map of construction land suitability evaluation in city periphery of Haiyang City


下载: 全尺寸图片幻灯片


图3海阳市城市周边耕地自然质量(a)、立地条件(b)、土地评价和立地分析(LESA) (c)分值图
Figure3.Score graphs of natural quality (a), site conditions (b), land evaluation and site assessment (LESA) (c) of cultivated land in city periphery of Haiyang City


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图4海阳市城市周边永久基本农田空间布局
Figure4.Permanent prime farmland layout of city periphery of Haiyang City


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表1海阳市建设用地适宜性评价指标体系
Table1.Index system of construction land suitability evaluation in Haiyang City
因子类型
Factor type
因子
Factor
类型
Type
适宜性分值
Suitability score
权重
Weight
强限制性因子
Strong restrictive factors
现状基本农田
Current prime farmland
是Yes 0
否No 1
生态红线
Ecological red line
是Yes 0
否No 1
行洪通道
Flood discharge channel
是Yes 0
否No 1
采空塌陷
Goaf collapse
严重区Serious area 0
非严重区Non-serious area 1
较强限制性因子
Secondary strong restrictive factors
一般农用地
General agriculture land
高于平均等Above average 60 0.32
低于平均等Below average 80
园地、林地、人工草地
Garden, woodland, artificial grassland
90
其他Others 100
坡度
Slope (°)
> 15 40 0.30
8~15 60
2~8 80
< 2 100
突发地质灾害
Emergency geological hazard
高High 40 0.20
中Medium 60
低Low 80
无None 100
土地利用综合分区
Land use comprehensive zoning
一般乡镇General township 50 0.18
重点乡镇Important township 70
城区City 90


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表2海阳市耕地自然质量评价指标体系
Table2.Index system of cultivated land natural quality evaluation in Haiyang City
目标层
Aim layer
准则层
Criteria layer
计算方法
Calculation method
因素作用分
Factor action score
权重
Weight
自然条件
Natural conditions
有效土层厚度
Effective soil thickness (cm)
农用地质量分等规程
Regulation for gradation on agriculture land quality
分级赋分
Grading assignment
0.30
表层土壤质地
Topsoil texture
农用地质量分等规程
Regulation for gradation on agriculture land quality
分级赋分
Grading assignment
0.10
障碍层次
Barrier level (cm)
农用地质量分等规程
Regulation for gradation on agriculture land quality
分级赋分
Grading assignment
0.10
土壤有机质含量
Soil organic matter content (g·kg-1)
农用地质量分等规程
Regulation for gradation on agriculture land quality
分级赋分
Grading assignment
0.06
地形坡度
Terrain slope (°)
农用地质量分等规程
Regulation for gradation on agriculture land quality
分级赋分
Grading assignment
0.21
灌溉保证率
Irrigation guarantee rate (%)
农用地质量分等规程
Regulation for gradation on agriculture land quality
分级赋分
Grading assignment
0.23


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表3海阳市耕地立地条件评价指标体系
Table3.Index system of cultivated land site condition assessment in Haiyang City
目标层
Aim layer
准则层
Criteria layer
指标层
Index layer
计算方法
Calculation method
因素作用分
Factor action score
权重
Weight
立地条件
Site conditions
区位条件
Location conditions
耕地到交通主干道距离
Distance of arable land to main road
GIS缓冲分析
GIS buffering analysis
Fi=1001-r (r=di/d) 0.13
耕地到中心城镇距离
Distance of arable land to central town
GIS缓冲分析
GIS buffering analysis
Fi=1001-r (r=di/d) 0.14
耕地到农村居民点的距离
Distance of arable land to village
GIS缓冲分析
GIS buffering analysis
Fi=1001-r (r=di/d) 0.12
耕作条件
Tillage conditions
耕地连片性
Extent of arable land connectivity
GIS缓冲分析
GIS buffering analysis
Fi=100[(Ei-Emin)/(Emax-Emin)] 0.18
农业结构调整可能性
Possibility of agricultural restructure
GIS叠加分析
GIS overlay analysis
分级赋分Grading assignment 0.11
耕地斑块形状指数
Index of arable land shape
Esi=4S1/2/L Fi=100[(Esi-Esimin)/(Esimax-Esimin)] 0.15
生态条件
Ecological conditions
生态安全程度
Extent of ecological security
GIS叠加分析
GIS overlay analysis
分级赋分
Grading assignment
0.09
地质灾害易发程度
Geological hazard susceptibility
GIS叠加分析
GIS overlay analysis
分级赋分
Grading assignment
0.08
??Fi为因子i的作用分值, r为相对距离, di为单元距扩散源的实际距离, d为扩散源的影响半径, Ei为缓冲后耕地图斑面积, Esi为耕地斑块形状指数, S为评价单元耕地图斑面积, L为评价单元耕地图斑周长; EsiminEsimax为耕地斑块形状指数的最小值和最大值。Fi is the effect score of factor i; r is the relative distance; di is the actual distance of the unit from the diffusion source; d is the impact radius of the diffusion source; Ei is the area of cultivated land after buffering; Esi is the morphological index of cultivated land; S is the cultivated land area of the evaluation unit; L is the cultivated land perimeter of the evaluation unit; Esimin and Esimax are the minimum and maximum values of the morphological index of cultivated land.


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表4海阳市城市周边建设用地适宜性评价分区统计
Table4.Zoning statistics of construction land suitability evaluation in city periphery of Haiyang City
建设用地类型Construction land type 地块面积Land area (hm2) 面积比例Area ratio (%)
禁止建设区Forbidden construction region 1 414.65 19.59
限制建设区Limited construction region 803.66 11.13
扩展建设区Extended construction region 920.99 12.76
重点建设区Important construction region 3 047.95 42.22
优先建设区Priority construction region 1 032.65 14.30
合计Total 7 219.90 100.00


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表5海阳市耕地土地评价和立地分析(LESA)综合评价结果及类型划分
Table5.Comprehensive evaluation results and type classification of land evaluation and site assessment (LESA) in city periphery of Haiyang City
耕地类型Cultivated land type LESA 地块面积Land area (hm2) 面积比例Area ratio (%)
优先划入型Priority area 81.96~93.63 458.05 25.59
适宜划入型Suitable area 75.38~81.95 771.83 43.12
重点调控型Controlled area 68.94~75.37 464.44 25.94
后备资源型Reserved area 55.63~68.93 95.73 5.35
总计Total 1 790.04 100.00


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