重庆市主城区景观动态及格局特征分析
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摘要
城市化正对当今世界产生深刻的影响,中国的城市化已经进入加速发展时期。中国的城市生态面临着严峻的挑战,城市景观受到越来越多的关注。重庆是长江中上游的经济、文化、交通中心,自1997年设立直辖市以来,经济飞速发展,城市面貌日新月异,城市景观发生了巨大的变化,以其主城区尤为明显。重庆市以建造“山水园林城市”为城市规划目标,城市绿地既是解决城市生态环境问题的手段,也是城市建设的目标。
     本文以重庆市主城区为研究对象,利用1995年和2002年两年的土地利用图,在GIS软件中进行重新分类,并且分别提取出城镇景观、非城镇景观、绿地景观。首先比较了直辖前后主城区景观、城镇景观、非城镇景观、绿地景观的动态变化,分析城市化对主城区的影响。然后在多个粒度下分析主城区景观、城镇景观、非城镇景观、绿地景观的格局特征,探讨各个景观的粒度变化规律。利用移动步长法,在不同的幅度下分析了主城区景观的空间异质性。最后,选用多个连通性指数分析主城区绿地景观的连通性,比较各指数的优劣,并且分析绿地景观中的斑块对其连通性的重要性,找出对连通性最关键的斑块。主要得到以下结果:
     (1)8年间,主城区景观整体变化很小,但城镇景观变化较大。城镇景观变得简单、紧凑、均匀。主城区景观的变化是由城镇景观引起。但城镇景观的面积占主城区比例较小,因此对整体景观特征影响较弱。绿地景观几乎无变化,相对城镇景观的迅速增长,绿地建设已经滞后,需要加强建设。
     (2)城镇景观、非城镇景观、主城区景观、绿地景观的粒度效应不尽相同。其中,非城镇景观与主城区景观粒度效应一致,绿地景观与其它三类景观粒度效应差异较大。城镇景观、非城镇景观、主城区景观在120m之前变化不大,绿地景观在240m出现明显的转折。
     (3)幅度变化影响着主城区景观格局特征空间异质性的表现。随着幅度增大,斑块密度、分维数和多样性指数的最大值减少,聚集度指数的最小值增大。其中,斑块密度受幅度影响最大。各指数最大值域由点状逐渐扩大为面状。在1km的小幅度下,可以发现主城区斑块密度最高、多样性最高、聚集度最差、分维数最大的小范围区域。在4km的分析幅度下,则能较真实反映主城区的异质性全貌。
     (4)最大斑块密度在小幅度下分布于九龙坡区南部和北碚区东北部,在大幅度下位于沙坪坝区和巴南区东南部。分维数最大的区域在巴南区的西北部和九龙坡区的南部、渝北区的北部,说明这些地方斑块最不规则,景观复杂。聚集度最大的区域在巴南区和渝北区,主要的土地利用类型是农业用地。多样性指数最高的区域分布于两江沿岸,土地利用类型主要是城镇用地,但同时也有水体、绿地、农业用地,景观结构复杂。
     (5)通过连通性指数的比较,发现COHESION、CONNECT、IIC、PC4个指数值能反映绿地景观连通性的实际状况。尤其是IIC、PC,具有可以实际应用等优越性。指数计算的结果说明重庆市主城区绿地景观连通性较差。
     (6)重庆市主城区绿地景观主要由少数巨型斑块和大量小型斑块组成。巨型斑块之间相互分离,小斑块分散。重庆市主城区的绿地景观连通性较差与景观组成密切相关。对于绿地景观的连通性而言,巨型斑块的重要性最大,但是小型斑块的重要性也不容忽视。
     (7)对绿地景观连通性重要值最大的斑块主要分布于主城区的几大山脉上,具有较好的生态系统服务功能。因此,在进行绿地规划时,首先要保护重要斑块,同时要考虑在巨型斑块之间构建小斑块,形成连通性廊道。
Urbanization has profoundly transformed natural landscapes throughout the world. With accelerating urbanization in china, the ecological environment in cities confronted huge challenge, city landscapes were play more and more attention. Chongqing was one of center cities in economic, civilization and communication in mid-higher Yangtze River. After 1997, the economic of Chongqing developed rapidly and the appearance of city was never-ending changes and improvement. The landscape of Chongqing, especially in the metropolitan region has changed greatly. "Landscape garden city "was the target of planning of Chongqing, Greenland landscape was not only the method to solve the problem in environment, but also the object of construction.
     The metropolitan region of Chongqing was the study area. Land use images in 1995 and 2002 have been reclassified by GIS software. The building landscape, non-building landscape and Greenland landscape have been cut from the land use images respectively. Firstly, For analysting the effect of urbanization on landscape pattern, the dynamics of the building landscape, non-building landscape, landscape of metropolitan region and Greenland landscape have been quantified between 1995 and 2002. Secondly, patterns of building landscape, non-building landscape, the metropolitan region and Greenland landscape have been measured under multi-grain to understand the scale effect in every landscape. Third, the heterogeneity of the landscape of metropolitan region has been researched under multi-extent by "moving window". Finally, several connectivity indices have been used to measure the connectivity of Greenland landscape. All indices were compared, and two indices were selected to compute the important value of patches in Greenland landscape, for finding the key patches. The results and conclusion as below:
     (1)Non-building landscape had hardly any change, while building landscape changed greatly. Building landscape grew simpler, even and compact. The landscape of metropolitan region had little change, which was significantly influenced by building landscape. Because area of building landscape was lower proportion in metropolitan region, the influence was not obvious. Greenland landscape had hardly any change too. Compared to the development of building landscape, the development of Greenland landscape has fallen behind, so it needs more attention.
     (2)The scale effect of building landscape, non-building landscape, landscape of metropolitan region and Greenland landscape were not identical. The non-building landscape and the landscape of metropolitan region had the same scale effect. There were greatly differences between Greenland landscape and the other three landscapes. The building landscape, non-building landscape and landscape of metropolitan region have been not affected when grain was less than 120m. Greenland landscape varied intensely when grain was 240m.
     (3)The extent had effect on the appearance of heterogeneity of landscape pattern of metropolitan region. As increasing in extent, the max of Patch density, Fractal Dimension Index, Shannon's Diversity Index decreased, the minimum value of Contagion Index increased. Patch density had more influenced than other indexes. The shape of the highest values of all indexes grew large, from point to surface. Under small extent 1km, the figures of spatial heterogeneity of indexes respectively displayed areas which Patch density was highest, Shannon's Diversity Index was highest, Contagion Index was lowest, Fractal Dimension Index was highest. Under extent 4km, the figures of spatial heterogeneity of indexes can show the spatial heterogeneity of the landscape of metropolitan area of Chongqing.
     (4)Under small extent, the max of PD distributed in the southern of Jiulongpo and northeastern of Beibei. Under big extent, the max of PD distributed in Shapinba and southeastern of Banan. The max of FRAC disturbed in northwestern of Banan, southern of Jiulongpo and northern of YUbei, where was not regular and most complex. The max of CONTAG disturbed in Banan and Yubei, where type of land use was agriculture land. The max of SHDI disturbed in shore of Jialing river and Yangtze river, where type of land use included building landscape, water, Greenland, agriculture land.
     (5)Eleven connectivity indices have been compared. COHESION、CONNECT、IIC、PC can display precisely the connectivity of Greenland landscape. The values of the four indices showed that the connectivity of Greenland landscape is not very good. Among the four indices, IIC、PC were the new connectivity indices for overcoming defects of other indices. They had been proved by researches.
     (6)The results showed, the Greenland landscape was consisted of few large patches and many little patches. The huge patches separated to each other while little patches scattered everywhere. The construction of Greenland landscape was related to the connectivity. The important values of huge patches for connectivity of Greenland landscape was more than others types of patches. It was the first object that must be considered in planning. The important of little patches can not be ignored.
     (7)The most important patches were exhibited with figure in paper. These patches lied in mountains in metropolitan region and provided various well ecosystem services. As above, the better way, which to increase the Greenland value in urban ecological and environment management is to increase the connectivity of patches, both small and huge patches when planning Greenland landscape in metropolitan region of Chongqing city.
引文
[1]Kang F H, Nakagoshi N. Spatial-temporal gradient analysis of urban green spaces inJinan.China.Landscape and Urban Planning,2006,78:147-164.
    
    [2]Gobster P H, Westphal L M. The human dimensions of urban greenways: planning forrecreation and related experiences. Landscape and Urban Planning,2004,68:147-165.
    
    [3]Kong F H, Yin H W, Nakagoshi N. Using GIS and landscape metrics in the hedonic pricemodeling of the amenity value of urban green space: A case study in Jinan City, China.Landscape and Urban Planning,2007,79:240-252.
    
    [4]周志翔,邵天一,万鹏等.城市绿地空间格局及其环境效应.生态学报,2004,24(2):186-192.
    
    [5]White M D, Greer K A. The effects of watershed urbanization on the stream hydrology andriparian vegetation of Los Penasquitos Creek, California. Landscape and UrbanPlanning,2006,74:125-138.
    
    [6]杨柳,马克明,郭青海等.城市化对水体非点源污染的影响.环境科学,25(6):32-39.
    
    [7]张金屯,Pouyat R.“城-郊-乡”生态样带森林土壤重金属变化格局.中国环境科 学,1997,17(5):410-413.
    
    [8]Green D A, Baker M G. Urbanization impacts on habitat and bird communities in a Sonorandesert ecosystem.Landscape and Urban Planning, 2003,63:225-239.
    
    [9]Hara Y.Takeuchi K, Okubo S. Urbanization linked with past agricultural landuse patterns inthe urban fringe of a deltaic Asian mega-city: A case study in Bangkok.Landscape andUrban Planning, 2005,73:16-28.
    
    [10]张涛,李惠敏,韦东等.城市化过程中余杭市森林景观空间格局的研究.复旦学报 (自),2002,41(1):83-88.
    
    [11]章家恩,饶卫民,肖红生等.基于RS与GIS的城市化过程中农业用地景观格局变化研究. 华南农业大学学报(自),2005,26(4):106-109.
    
    [12]曾辉,江子瀛,喻红等.深圳市龙华地区快速城市化过程中的景观结构研究Ⅲ农业用地结 构及异质性分析.北京大学学报(自).2000,36(2):221-230.
    
    [13]Murakami A, Zain A, MTakeuchi, K, et al. Trends in urbanization and patterns of land use inthe Asian mega cities Jakarta, angkok, and Metro Manila.Landscape and UrbanPlanning,2005,70:251-259.
    
    [14]郭栎,夏北成,刘蔚秋等.城市化进程中广州市景观格局的时空变化与梯度分析.应用生 态学报,2006,17(9):1671-1676.
    
    [15]王辉,周睿,毕晓丽等.泾河流域平凉市城市化影响下景观格局梯度分析.生态学杂 志,2006,25(12):1476-1480.
    
    [16]李杨帆,朱晓东,潘涛.苏南快速城市化地区景观生态优化调控研究.生态学杂 志.2006.25(2):207-211.
    
    [17]邬建国.景观生态学——格局、过程、尺度与等级.北京,高等教育出版设,2000.
    
    [18]Selinger R L, Grevilliot F ,Muller S. Structure of plant communities and landscape patternsin alluvial meadows of two flood plains in the north-east of France.LandscapeEcology, 1999,14:213-229.
    
    [19]Biirgi M. A case study of forest change in the Swiss lowlands. Landscape Ecology,1999, 14:567-575.
    
    [20]Saveraid E H, Debinski D M, Kindscher K et al. A comparison of satellite data and landscapevariables in predicting bird species occurrences in the Greater Yellowstone Ecosystem, USA.Landscape Ecology,2001,16:71-83.
    
    [21]角嫒梅,马明国,肖笃宁等.干旱区农业绿洲景观格局研究.农村生态环境,2003,19(1):22- 26.
    
    [22]唐礼俊.佘山风景区景观空间格局分析.地理学报,1998,53(5):429-437.
    
    [23]余世孝,郭泺.山东泰山地区景观结构变化及其分形分析.生态学报,2005,25(1):129-134.
    
    [24]刘红玉,张世奎,吕宪国.三江平原湿地景观结构的时空变化.地理学报,2004,59(3):391- 400.
    
    [25]曾辉,孔宁宁,李书娟.卧龙自然保护区认为活动对景观结构的影响.生态学 报,2001,21(12):1994-2001.
    
    [26]Turner M G Spatial and temporal analysis of landscape pattern, landscape Ecology,1990,4:21-30.
    
    [27]Jenerette G D, Wu J G. Analysis and simulation of land-use change in the centralArizona-Phoenix region, USA. Landscape ecology, 2001,21:611-626.
    
    [28]Luck M and Wu J G. A gradient analysis of urban landscape pattern: A case study from thephoenix metropolitan region, Arizona, USA. Landscape ecology, 2002,17:327-339.
    
    [29]Marc Antrop. Changing patterns in the urbanized countryside of Western Europe. LandscapeEcology,2000(15):257-270.
    
    [30]DiBari N J. Evaluation of five landscape-level metrics for measuring the effects ofurbanization on landscape structure: the case of Tucson, Arizona, USA. Landscape andurban Pianning,2007(79):208-313.
    
    [31]Weng Y.-C. Spatiotemporal changes of landscape pattern in response to urbanization.Landscape Urban Planning,2007, doi:10.1016/j.landurbplan.2007.01.009
    
    [32]Yu X J, Ng C N. Spatial and temporal dynamics of urban sprawl along two urban-ruraltransects: A case study of Guangzhou,China. Landscape and urban planning,2007(79):96-??109.
    
    [33]肖笃宁,赵羿,孙中伟等.沈阳西郊景观格局变化的研究.应用生态学报,1990,1(1):75-84.
    
    [34]田光进,张增祥,张国平.基于遥感与GIS的海口市景观格局动态演化.生态学 报,2002,22(7):1028-1034.
    
    [35[曾辉,江子瀛.深圳市龙华地区快速城市化过程中的景观结构研究——城市建设用地结 构及异质性特征分析.应用生态学报,2000,11(4):567-572.
    
    [36]曾辉,江子瀛,孔宁宁等.快速城市化景观格局的空间自相关特征分析——以深圳市龙华 地区为例.2000,36(6):824-831.
    
    [37]张明娟,刘茂松,徐驰等.南京市区景观破碎化过程中的斑块规模结构动态.生态学杂 志,2006,25(11):1358-1363.
    
    [38]Turner M G,O'Neill R V. Effects of changing spatial scale on the analysis of Lanscapepattern. Landscape ecology,1989,3:153-162.
    
    [39]He F, Legendre P. Diversity pattern and spatial scale: A study of a tropical rain forest ofMalaysia. Environmental & Ecological Statistics,1994,1:265-286.
    
    [40]O'Neill R V,Hunsaker C T,Timmins S P,et al.Scale problems in reporting landscape patternat the regional scale.Landscape Ecology,1996,11:169-180.
    
    [41]Qi Y, Wu J. Effects of changing spatial resolution on the results of landscape pattern analysisusing spatial autocorrelation indices. Landscape Ecology,1996,11:39-49.
    
    [42]Saura S, Martinez-Millan J. Sensitivity of landscape pattern metrics to map spatial extent.Photogrammatic Engineering & Remote Sensing,2001,67:1027-1036.
    
    [43]Saura S. Effects of remote sensor spatial resolution and data aggregation on selectedfragmentation indices.Landscape Ecology,2004,19:197-209.
    
    [44]Wu J.Hierarchy and scaling: Extrapolating information along a scaling ladder. CanadianJournal of Remote Sensing,1999,25:367-380.
    
    [45]Wu J,Jelinski D, Luck M, et al. Multi-scale analysis of landscape heterogeneity: scalevariance and pattern metrics. Geographical Information Science,2000,6:6-19.
    
    [46]Wu J, Shen W, Sun W, et al. Empirical patterns of the effects of changing scale on landscapemetrics. Landscape Ecology,2002,17:761-782.
    
    [47]Wu J. Effects of changing scale in landscape pattern analysis: scaling relations. LandscapeEcology,2004,19:125-138.
    
    [48]Buyantuyev A, Wu J G. Effects of thematic resolution on landscape pattern analysis.landscape ecology,2007,22:7-13.
    
    [49]李晓兵,陈云浩.基于多尺度遥感测量的区域土地覆盖格局研究.植被生态学 报,2003,27(5):577-586.
    
    [50]赵文武,傅伯杰,陈利顶.景观指数的粒皮变化效应.第四纪研究,2003,23(3):327-333.
    
    [51]申卫军,邬建国.空间粒度变化对景观格局分析的影响.生态学报,2003,23(12):2507- 2519.
    
    [52]布仁仓,李秀珍.尺度分析对景观格局指标的影响.应用生态学报,2003,14(12):2181- 2186.
    
    [53]丹峰.IKONOS影像景观格局特征尺度的小波与半方差分析.生态学报,2003,23(3):405- 413.
    
    [54]谈文琦,徐建华,岳文泽.城市景观空间自相关与自相似的尺度特征研究.生态学杂志, 2005,24(6):627-630.
    
    [55]岳文泽,徐建华,谈文琦.城市景观格局的空间尺度分析.生态科学,2005,24(2):102-106.
    
    [56]岳文泽,徐建华,谈文琦.城市景观多样性的空间尺度分析——以上海市外环线以内区域 为例.生态学报,2005,25(1):123-128.
    
    [57]常学礼,张德干,杨持.农牧交错区沙地景观空间格局的间隙度分析.中国沙漠,1999,19 (增1):12-17.
    
    [58]申卫军,邬建国,任海.空间幅度变化对景观格局分析的影响.生态学报,2003,23(4):2220- 2231.
    
    [59]徐建华,岳文泽,谈文琦.城市景观格局尺度效应的空间统计规律——以上海中心城区 为例.地理学报,2004,59(6):1058-1067.
    
    [60]岳文泽,徐建华,徐丽华.不同尺度下城市景观综合指数的空间变异特征研究.应用生态 学报,2005,16(11):2054-2059.
    
    [61]龚建周,夏北成,李楠.广州市土地覆被格局异质性的尺度与等级特征.地理学报,2006, 61(8):873-881.
    
    [62]吴人韦.城市绿地的分类.中国园林,1999,15:59-62.
    
    [63]车生泉,王洪轮.城市绿地研究综述.上海交通大学学报(农业科学版),2001,19(3):229- 234.
    
    [64]Jim C Y, Chen S S. Comprehensive greenspace planning based on landscape ecologyprinciples in compact Nanjing city,China.Landscape and Urban Planning,2003,65:95-116.
    
    [65]Augest Heckscher. Open space-the life of American city. New York:Harper Row,1984.
    
    [66]郑淑颖,管东生,马灵芳等.广州城市绿地斑块的破碎化分析.中山大学学报(自然科学 版):2000,39(2):109-113.
    
    [67]高峻,杨名静,陶康华.上海城市绿地景观格局的分析研究冲国园林,2000,16(67):53-56.
    
    [68]何兴元,陈玮,徐文铎等.沈阳城区绿地生态系统景观结构与异质性分析.应用生态学 报,2003,14(12):2085-2089.
    
    [69]肖荣波,周志翔,王鹏程.武钢工业区绿地景观格局分析及综合评价.生态学??报,2004,24(9):1924-1930.
    
    [70]周志翔,邵天一,王鹏程.武钢厂区绿地景观类型空间结构及滞尘效应.生态 报,2002,22(12):2036-2040.
    
    [71]周志翔,邵天一,唐万鹏等.城市绿地空间格局及其环境效应——以宜昌市中心城区为例. 生态学报,2004,24(2):186-182.
    
    [72]周廷刚,郭达志.基于GIS的城市绿地景观空间结构研究——以宁波市为例.生态 报,2003,23(5):901-907.
    
    [73]尹海伟,孔繁花.济南市城市绿地时空梯度分析.生态学报,2005,25(11):3010-3018.
    
    [74]欧阳志云,王如松,李伟峰.北京市环城绿化隔离带生态规划.生态学报,2005,25(5):965- 974.
    
    [75]李锋,王如松.城市绿地系统的生态服务功能评价、规划与预测研究——以扬州市为例. 生态学报,2003,23(9):1929-1936.
    
    [76]吴丽娟,周亮,王新杰等.北京城市绿地系统景观多样性分析.北京林业大学学报, 2007,29(2):88-93.
    
    [77]陈芳,周志翔,肖荣波等.城市工业区绿地生态服务功能的计量评价——以武汉钢铁公司 厂区绿地为例.生态学报,2006,26(7):2229-2236.
    
    [78]Chang C R, Li M H, Chang S D. A preliminary study on the local cool-island intensity ofTaipei city parks.Landscape and Urban Planning,2007(80):386-395.
    
    [79]Jim C Y. A planning strategy to augment the diversity and biomass of roadside trees in urbanHong Kong.Landscape and Urban Planning,1999,44:13-32.
    
    [80]Breuste J H. Decision making, planning and design for the conservation of indigenousvegetation within urban development.Landscape and Urban Planning,2004,68:439-452.
    
    [81]Sandstr(?)om U G, Angelstam P ,Mikusi'nski G. Ecological diversity of birds in relation to thestructure of urban green space.Landscape and Urban Planning,2006,77:39-53.
    
    [82]Christina G C, Klaus S. Are urban green spaces optimally distributed to act as places forsocial integration? Results of a geographical information system (GIS) approach for urbanforestry research.Forest Policy and Economics,2004,6:3-13.
    
    [83]TyrvBinen L. The amenity value of the urban forest: an application of the hedonic pricingmethod.Landscape and Urban Planning,1997,37:211-222.
    
    [84]Bjerke T, Thrane C. Vegetation density of urban parks and perceived appropriateness forrecreation.Urban Forestry & Urban Greening ,2006,5:35-44.
    
    [85]Jorgensen A, Hitchmough J, Dunnett N. Woodland as a setting for housing-appreciation andfear and the contribution to residential satisfaction and place identity in Warrington NewTown, UK.Landscape and Urban Planning,2007,79:273-287.
    
    [86]Taylor P, Fahrig I.Henein K,et al. Connectivity is a vital element of landscape structure.Oikos,1993, 68 (3):571-573.
    
    [87]Philippe C, Burel F. The role of spatio-temporal patch connectivity at the landscape level: anexample in a bird distribution. Landscape Urban Planning, 1997,38: 37-43.
    
    [88]Metzger J P, Ddcamps H. The structural connectivity threshold: an hypothesis inconservation biology at the landscape scale.Acta Ecologia,1997,18(1):1-12.
    
    [89]Bunn A G, Urban D L, Keitt T H. Landscape connectivity:A conservation application ofgraph theory. Journal of Environmental Management,2000,59:265-278.
    
    [90]Mason J, Moorman C, Hess G, et al. Designing suburban greenways to provide habitat forforest-breeding birds. Landscape and Urban Planning,2007,80:153-164.
    
    [91]Bryant M M. Urban landscape conservation and the role of ecological greenways at local andmetropolitan scales. Landscape and Urban planning,2006,76:23-44.
    
    [92]Ribeiro L, Bar~ao T. Greenways for recreation and maintenance of landscape quality:fivecase studies in Portugal. Landscape and Urban Planning,2006,76:79-97.
    
    [93]Gobster P H., Westphal L M. The human dimensions of urban greenways: planning forrecreation and related experiences. Landscape and Urban Planning,2004,68:147-165.
    
    [94]Fuller T, Sarkar S. LQGraph: A software package for optimizing connectivity inconservation planning. Enviromental Modelling & Software,2006,21:750-755.
    
    [95]Ferrari J R., Lookingbill T R., Neel M C. Two measures of landscape-graph connectivity:assessment across gradients in area and configuration.Landscape Ecology,2007,22:1315-1323.
    
    [96]Pascual-Hortal L, Saura S. Comparison and development of new graph-based landscapeconnectivity indices: towards the priorization of habitat patches and corridors forconservation. Landscape Ecology,2006,21:959-967.
    
    [97]岳文祥,叶庆华.景观连通性模型及其应用.地理学报,2002,57(1):67-75.
    
    [98]王玉沽,李俊祥,吴健平等.上海浦东新区城市化过程景观格局变化分析.应用生态学 报,2006,17(1):36-40.
    
    [99]DiBari J N. Evaluation of five landscape-level metrics for measuring the effects ofurbanization on landscape structure: the case of Tucson,Arizona,USA. Landscape and UrbanPlanning, 2007,79,308-313.
    
    [100]McGarigal K,Cushman S A, Neel M C, et al. FRAGSTATS: Spatial Pattern AnalysisProgram for Categorical Maps, Computer software program produced by the authors at theUniversity of Massachusetts, Amherst. 2002.Available at:http://www.umass.edu/landeco/research/fragstats/fragstats.html
    
    [101]Zhu M, Nan J, Li J L,et al. The effects of sensor spatial resolution and changing grain sizeon fragmentation indices in urban landscape.International Journal of Remote sensing,2006,27(21):4791-4805.
    
    [102]朱明.基于景观格局尺度效应分析的上海市土地利用城市化水平测度.南京大学博士 论文,2006.
    
    [103]陈彩虹,胡锋,张落成等.南京市城乡交错带景观格局研究.应用生态学 报,2003,14(8):1363-1368.
    
    [104]柯美红.东山县景观空间格局研究.集美大学学报(自),2005,10(1):75-82.
    
    [105]Zhu M, Xu J G,Nan J, et al. Impacts of road corridors on urban landscape pattern: agradient analysis with changing grain size in Shanghai, China. Landscape ecology,2006,21:723-734.
    
    [106]肖笃宁,布仁仓,李秀珍等.生态空间理论与景观异质性.生态学报,1997,17(5):455- 456.
    
    [107]Kolasa J , Picketts T A. Ecological Heterogeneity.New York : Spring-Verlag , 1991.
    
    [108]Li H , Reynolds J F. On definition and quantification of heterogeneity. Oikos , 1995 , 73 :280-284.
    
    [109]Dutilleul P, Lengendre P. Spatial heterogeneity against heteroscedasticity : an ecologicalparadigm versus a statistical concept. Oikos , 1993 ,66 :152-171.
    
    [110]Pickett S T A, Cadenasso M L. Landscape ecology:spatial heterogeneity in ecologicalsystems.Science,1995,269:331-334.
    
    [111]蒋文伟,刘彤,丁丽霞.景观生态空间异质性的研究进展.浙江林学院学报,2003,20(3): 311-214.
    
    [112]朱明,徐建刚,李建龙.上海市景观格局梯度分析的空间幅度效应.生态学杂 志,2006,25(10):1214-1217.
    
    [113]肖寒,欧阳志云,赵景柱等.海南岛景观空间结构分析.生态学报,2001,21(1):20-27.
    
    [114]邱杨,张金屯,郑凤英等.景观生态学的核心:生态学系统的时空异质性.生态学杂志, 2000,19(2):42-49.
    
    [115]Pascual-Hortal L, Saura S. Impact of spatial scale on the identification of critical habitatpatches for the maintenance of landscape connectivity, Landscape Urban Planning, 2007,doi:10.1016/j.landurbplan.2007.04.003
    
    [116] Sutherland G D,Harestad A S, Price K,et al. Scaling of natal dispersal Distance in Terrestrialbirds and mammals. Conservation Ecology,4(1):16.[online]URL:http://www.consecol.org/vol4/iss1/art16
    
    [117]Pascual-Hortal L, Saura S. A new habitat availability index to integrate connectivity in??landscape conservation planning: Comparison with existing indices and application to a casestudy, Landscape Urban Planning ,2007,doi:10.1016/j.landurbplan.2007.03.005
    
    [118]魏斌,王景旭,张涛.城市绿地生态效果评价方法的改进.城市环境与城市生 态,1997,10(4):54-55.
    
    [119]周廷刚,郭达志.基于GIS的城市绿地景观引力场研究——以宁波市为例.生态 报,2004,24(6):1157-1163.
    
    [120]陈芳,周志翔,肖荣波等.城市工业区绿地生态服务功能的计量评价——以武汉钢铁公 司厂区绿地为例.生态学报,2006,26(7):2229-2236.
    
    [121]Chang C R, Li M H.Chang S D. Apreliminary study on the local cool-island intensity ofTaipei city Parks. Landscape and Urban Planning,2007,80:386-395.
    
    [122]Balmford A, Moore J L, Brooks T, et al. Conservation conflicts across Africa. Science,2001291,2616-2619.
    
    [123]Cornelis J, Hermy M. Biodiversity relationship in urban and suburban parks in Flanders.Lnadscape and urban Planning,2004,69,385-401.
    
    [124]Jim C Y. A planning strategy to augment the diversity and biomass of roadside trees inurban Hong Kong. Lndascape and Urban planning,1998,44:13-32.
    
    [125]MoErtberg U, Wallentinus H G. Red-listed forest bird species in an urban environmentassessment of green space corridors. Landscape and Urban Planning,2000,50:215-226.
    
    [126]Jim C Y, Liu H T. Species diversity of three major urban forest types in Guangzhou City,China. Forest Ecology and Management.2001,146,99-114.
    
    [127]Alvey A A. Promoting and preserving biodiversity in the urban forest. Urban Forest &Urban Greening,2006,5:195-201.
    
    [128]Wei Z, Xue L, Zhang L L. Urban forest in Jinan City: Distribution, classification andecological significance.Catena,2007,69:44-50.

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