1. 宁波大学 地理与空间信息技术系,浙江,宁波,315211
2. 青岛市环境保护科学研究院,山东,青岛,266003
纸质出版:2019
移动端阅览
韩世豪, 梅艳国, 叶持跃, 等. 基于最小累积阻力模型的福建省南平市延平区生态安全格局构建[J]. 水土保持通报, 2019,39(2):192-198.
Han Shihao, Mei Yanguo, Ye Chiyue, et al. Construction of Ecological Security Pattern in Yanping District of Nanping City, Fujian Province Based on Minimum Cumulative Resistance Model[J]. Bulletin of Soiland Water Conservation, 2019, 39(2): 192-198.
韩世豪, 梅艳国, 叶持跃, 等. 基于最小累积阻力模型的福建省南平市延平区生态安全格局构建[J]. 水土保持通报, 2019,39(2):192-198. DOI: 10.13961/j.cnki.stbctb.2019.02.031.
Han Shihao, Mei Yanguo, Ye Chiyue, et al. Construction of Ecological Security Pattern in Yanping District of Nanping City, Fujian Province Based on Minimum Cumulative Resistance Model[J]. Bulletin of Soiland Water Conservation, 2019, 39(2): 192-198. DOI: 10.13961/j.cnki.stbctb.2019.02.031.
[目的
]
对城市综合生态安全格局进行构建,为城市总体规划和城市生态规划等专题研究提供科学参考。[方法
]
以福建省南平市延平区为研究对象,在划定生态保护红线的基础上选择生态源地,以地形坡度、土地覆盖和植被覆盖为阻力因子,应用最小累积阻力模型,以生态阻力面直方图分布的突变点2 983和9 268为界,分别构筑延平区底线型、缓冲型和理想型生态安全格局。[结果
]
延平区生态源地,即底线型生态格局用地面积为534.51 km
2
,占延平区面积的20.10%;缓冲型和理想型生态安全格局用地面积分别为771.17和1 592.79 km
2
,占到延平区的29.00%和59.89%。结合这3种不同安全水平的生态安全格局,进一步明确了生态源地间的13条生态廊道和5个关键生态节点,共同组合形成了延平区综合生态安全格局。[结论
]
在生态保护红线的基础上,结合延平区山水型城市的特点,确定了不同安全水平的生态用地分布格局、生态廊道和关键生态节点,形成了延平区综合生态安全格局。
[Objective] The construction of a urban integrated ecological security pattern was studied in order to provide scientific references for special studies such as urban master planning and urban ecological planning.[Methods] Taking Yanping District of Nanping City
Fujian Province as the research object
the ecological source land was selected on the basis of the ecological protection red line. The terrain gradient
land cover and vegetation cover were used as the resistance factors
and the minimum cumulative resistance model was applied to the mutation point of the ecological resistance surface histogram distribution. 2 983 and 9 268 are the boundaries
and the bottom line type
buffer type and ideal ecological security pattern of Yanping District are constructed respectively.[Results] The ecological source area of Yanping District
namely the bottom line ecological pattern
covered an area of 534.51 km2
accounting for 20.10% of the Yanping District. The buffered and ideal ecological security pattern covered an area of 771.17 km2 and 1 592.79 km2 respectively
and accounting for 29.00% and 59.89% of Yanping District. Combining three different levels of safety and ecological security
the 13 ecological corridors and 5 key ecological nodes between the ecological sources were further clarified
and the comprehensive ecological security pattern of Yanping District was formed.[Conclusion] On the basis of the ecological protection red line
combined with the characteristics of Yanping District which is a landscape-type city
the ecological land distribution patterns of different safety levels
ecological corridors and key ecological nodes are determined
and the comprehensive ecological security pattern of Yanping District is formed.
彭建,赵会娟,刘焱序,等.区域生态安全格局构建研究进展与展望[J].地理研究,2017,36(3):407-419.
Naveh Z. From biodiversity to ecodiversity:A landscape-ecology approach to conservation and restoration[J]. Restoration Ecology, 2010,2(3):180-189.
Bloom D E, Canning D, Fink G. Urbanization and the wealth of nations[J]. Science, 2008,319(5864):772-775.
Mundia C N, Murayama Y. Modeling spatial processes of urban growth in African cities:A case study of Nairobi City[J]. Urban Geography, 2010,31(2):259-272.
蒋艳灵,刘春腊,周长青,等.中国生态城市理论研究现状与实践问题思考[J].地理研究,2015,34(12):2222-2237.
崔胜辉,洪华生,黄云凤,等.生态安全研究进展[J].生态学报,2005,25(4):861-868.
李月辉,胡志斌,高琼,等.沈阳市城市空间扩展的生态安全格局[J].生态学杂志,2007,26(6):875-881.
欧定华,夏建国,张莉,等.区域生态安全格局规划研究进展及规划技术流程探讨[J].生态环境学报,2015,24(1):163-173.
习近平.在主持十八届中央政治局第六次集体学习时的讲话要点[R].北京:新华社,2013.
俞孔坚,王思思,李迪华.区域生态安全格局:北京案例[M].北京:中国建筑工业出版社,2012.
陈星,周成虎.生态安全:国内外研究综述[J].地理科学进展,2005,24(6):8-20.
俞孔坚.生物保护的景观生态安全格局[J].生态学报,1999,19(1):8-15.
Yu Kongjian. Security patterns and surface model in landscape ecological planning[J]. Landscape and Urban Planning,1996,36(1):1-17.
蒙吉军,朱利凯,杨倩,等.鄂尔多斯市土地利用生态安全格局构建[J].生态学报,2012,32(21):6755-6766.
彭建,赵会娟,刘焱序,等.区域水安全格局构建:研究进展及概念框架[J].生态学报,2016,36(11):3137-3145.
周锐,王新军,苏海龙,等.平顶山新区生态用地的识别与安全格局构建[J].生态学报,2015,35(6):2003-2012.
李晖,易娜,姚文璟,等.基于景观安全格局的香格里拉县生态用地规划[J].生态学报,2011,31(20):5928-5936.
潘竟虎,刘晓.疏勒河流域景观生态风险评价与生态安全格局优化构建[J].生态学杂志,2016,35(3):791-799.
俞孔坚,王思思,李迪华,等.北京市生态安全格局及城市增长预景[J].生态学报,2009,29(3):1189-1204.
吴健生,张理卿,彭建,等.深圳市景观生态安全格局源地综合识别[J].生态学报,2013,33(13):4125-4133.
李晶,蒙吉军,毛熙彦.基于最小累积阻力模型的农牧交错带土地利用生态安全格局构建:以鄂尔多斯市准格尔旗为例[J].北京大学学报:自然科学版,2013,49(4):707-715.
张兰兰.夹缝中求生的第二新城:评说南平市延平新城总体规划[J].中华建设,2015(6):30-33.
Knaapen J P, Scheffer M, Harms B. Estimating habitat isolation in landscape planning[J]. Landscape and Urban Planning, 1992,23(1):10-16.
Pain G, Baudry J, Burel F. Land Pop:un outil d'étude de la structure spatiale des populations animals fragmentées[J]. Revue Internationale de Géomatique, 2000,10:89-106.
陈利顶,傅伯杰,徐建英,等.基于"源-汇"生态过程的景观格局识别方法:景观空间负荷对比指数[J].生态学报,2003,23(11):2406-2413.
黎晓亚,马克明,傅伯杰,等.区域生态安全格局:设计原则与方法[J].生态学报,2004,24(5):1055-1062.
林勇,樊景凤,温泉,等.生态红线划分的理论和技术[J].生态学报,2016,36(5):1244-1252.
徐德琳,邹长新,徐梦佳,等.基于生态保护红线的生态安全格局构建[J].生物多样性,2015,23(6):740-746.
王洁,李锋,钱谊,等.基于生态服务的城乡景观生态安全格局的构建[J].环境科学与技术,2012,35(11):199-204.
叶玉瑶,苏泳娴,张虹鸥,等.生态阻力面模型构建及其在城市扩展模拟中的应用[J].地理学报,2014,69(4):485-496.
朱强,俞孔坚,李迪华.景观规划中的生态廊道宽度[J].生态学报,2005,25(9):2406-2412.
李卫锋,王仰麟,彭建,等.深圳市景观格局演变及其驱动因素分析[J].应用生态学报,2004,15(8):1403-1410.
乌尼图,岳德鹏,张亦超,等.基于3S技术的城乡区域生态节点的识别与分析[J].环境科学与技术,2014,37(2):184-189.
陆禹,佘济云,陈彩虹,等.基于粒度反推法的景观生态安全格局优化:以海口市秀英区为例[J].生态学报,2015,35(19):6384-6393.
0
浏览量
1061
下载量
15
CSCD
关联资源
相关文章
相关作者
相关机构
京公网安备11010802024621