PDF Download

[1]LI Jing,ZHU Yongming,ZHANG Hui,et al.Dynamic Recognition of Source Area of Landscape Ecological Security Pattern in Beidaihe New District[J].Research of Soil and Water Conservation,2016,23(06):340-344,351.

Copy

Dynamic Recognition of Source Area of Landscape Ecological Security Pattern in Beidaihe New District

Research of Soil and Water Conservation[ISSN 1005-3409/CN 61-1272/P] Volume: 23 Number of periods: 2016 06 Page number: 340-344,351 Column: Public date: 2016-12-28

Title:: Dynamic Recognition of Source Area of Landscape Ecological Security Pattern in Beidaihe New District

Author(s):: LI Jing, ZHU Yongming, ZHANG Hui, ZHANG Guijun; College of Land and Resources, Agricultural University of Hebei, Baoding, Hebei 071001, China

Keywords:: environmental science; recognition of source area; dynamic; Beidaihe New District

CLC:: F590

DOI:: -

Abstract:: Source area is the foundation of constructing ecological landscape security pattern. Taking into account the effect of time dynamics, we propose a new methodology to improve source area recognition in order to lay foundations for the reasonable construction of ecological landscape security pattern. With the aid of software such as Fragstats 3.4,ArcGIS 10.0,Conefor Sensinode 2.2 and InVEST 2.2.0, we present a dynamic evaluation of landscape patch quality in three specific periods, respectively 1991, 2001 and 2013 in Beidaihe New District. All the final results of evaluation are divided into five levels, representing with numbers 1 to 5(the smaller the level, the better the quality of the patch). Afterwards, the classification results of the three years are superimposed, and the patches in level 1 and 2 are selected as the source area for landscape ecological security pattern in 2013. It turns out that the total source area in Beidaihe New District is 73.34 km², accounting for 14.25% of the total area of Beidaihe New District. Among them, the patch of level 1 is 37.44 km², which makes up 7.27% of the total area of Beidaihe New District; the patch of level 2 is 35.90 km², presenting 6.97% of the total area of Beidaihe New District. The patches of source area mainly distribute in Aquatic Bureau and Seven Caspian Sea and surroundings, southeast of Liutaizhuang town and south of State-owned Forest. It is extremely essential to focus on the management and protection of these areas.

References:: [1] 李秉成.中国城市生态环境问题及可持续发展[J].干旱区资源与环境,2006,20(2):2-6.
[2] 姬晓娜,朱泮民.生态旅游区的景观生态问题及其调控[J].生态学杂志,2007,26(11):1884-1889.
[3] 蒋欣.试论城市化发展进程中的生态环境问题及对策:以长株潭城市群为例[J].生态经济,2009(9):167-170.
[4] 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.
[5] 张虹波,刘黎明.土地资源生态安全研究进展与展望[J].地理科学进展,2006,25(5):77-85.
[6] 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.
[7] 李绥,石铁矛,付士磊,等.南充城市扩展中的景观生态安全格局[J].应用生态学报,2011,22(3):734-740.
[8] 王亮.崇明岛景观生态安全格局分析[J].国土与自然资源研究,2007(2):54-55.
[9] 王建英,李江风,邹利林,等.生态约束下的湖泊旅游用地布局[J].应用生态学报,2012,23(10):2871-2877.
[10] 李咏红,香宝,袁兴中,等.区域尺度景观生态安全格局构建:以成渝经济区为例[J].草地学报,2013,21(1):19-24.
[11] Adriaensen F, Chardon J P, De Blust G, et al. The application of ‘least-cost’ modeling as a functional landscape model[J]. Landscape and Urban Planning, 2003,64(4):233-247.
[12] 董雅文,周雯,周岚,等.城市化地区生态防护研究:以江苏省,南京市为例[J].城市研究,1999,2(2):6-10.
[13] 邓红兵,陈春娣,刘昕,等.区域生态用地的概念及分类[J].生态学报,2009,29(3):1519-1524.
[14] 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.
[15] 熊春泥,魏虹,兰明娟.重庆市都市区绿地景观的连通性[J].生态学报,2008,28(5):2237-2244.
[16] Heather Tallis, Taylor Ricketts, Anne Guerry, et al. InVEST 2.2.0 User’s Guide[Z]. The Natural Capital Project, Stanford, 2011.
[17] 吴季秋.基于CA-Markov和InVEST模型的海南八门湾海湾生态综合评价[D].海口:海南大学,2002.
[18] 刘志伟.基于InVEST的湿地景观格局变化生态响应分析:以杭州湾南岸地区为例[D].杭州:浙江大学,2014.
[19] 唐蜜.县域生态系统非木材林木产品服务功能评估研究:以四川省宝兴县为例[D].四川雅安:四川农业大学,2010.
[20] 谢高地,甄霖,鲁春霞,等.一个基于专家知识的生态系统服务价值化方法[J].自然资源学报,2008,23(5):911-919.

Similar References:

Memo

Last Update: 1900-01-01