康保县景观格局变化及其生态效应分析
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
景观是人类生活的载体,人类的一切社会活动和经济活动都是在一定的区域景观内进行。人类活动是形成景观,构建自然和人工管理斑块组成镶嵌体的重要动力。人类是景观变化的原始动力,也由此导致了目前的生态危机(Naveh,1995)。对景观格局变化研究,是进行景观生态学评价、景观生态设计管理等的基础,尤其在生态环境脆弱的地区,对于促进该地区的生态环境的改善和可持续发展具有重要理论与现实意义。
     康保县地处河北省坝上高原,是我国北方农牧交错带中段的典型地区,是生态环境的典型脆弱区。因此,研究其景观格局变化,并探讨变化的驱动力因素以及生态效应,对于改善本区生态环境,充分认识人类活动的利弊,促进坝上地区资源的合理利用,保障生态和粮食安全无疑具有重要意义。
     本文以康保县1987年、2000年、2005年三期Landsat-TM/ETM遥感影像为基础,从综合自然地理学、景观生态学的角度出发,在遥感(RS)、地理信息系统(GIS)等技术的支持下,结合康保县的区域特征,对康保县景观格局的变化进行分析,并在此基础上定性分析了该地区景观格局变化的驱动力,最后结合气候气象资料、野外实测数据及相关资料对景观格局变化的生态效应进行了分析。结果表明:
     (1)1987年研究区主要景观类型为耕地、草地、建设用地;2000年研究区主要景观类型为耕地、草地、林地和建设用地;2005年主要景观类型也为耕地、草地、林地和建设用地。通过对这三年的景观类型面积的相互对比可以看出,耕地面积不断减少,林地、草地面积呈大幅度增长,尤其在2000年至2005年这一研究区间内变化比较剧烈,建设用地面积也呈现出增加的趋势,未利用地面积先增加后减少。
     (2)基于单一土地利用类型动态度模型和综合土地利用动态度模型的分析结果,研究区整体景观变化速度较大。18年间,林地和草地都有了一定幅度的增长,尤其在2000年至2005年,林地的动态度高达38.48%,草地的动态度也达8.47%,建设用地也一定程度的增加,但变化幅度小于林地和草地;耕地不断减少,动态度为--4.69%。
     (3)通过景观类型转移矩阵分析可知,耕地面积大幅度减少,林地、草地面积大幅度增加,建设用地、未利用地均有一定程度的增加,水域面积持续减少。景观类型转移以耕地——草地,耕地——林地,林地——草地为主,且这些景观类型间的相互转化均是双向的。
     (4)利用景观格局指数对康保县景观格局变化进行分析,结果显示:1987年至2005年,康保县各景观要素斑块中,耕地、林地、建设用地、未利用地的斑块数量增加,草地、水域的斑块数量有少量的减少;1987年至2000年,耕地、林地、未利用地平均斑块面积向小型化发展,破碎度增加,而草地、建设用地的斑块向大型化发展;2000年至2005年,林地、草地、建设用地、水域的平均斑块面积有所增加,耕地、未利用地的平均斑块面积持续减少。1987年至2005年,各要素斑块的景观形状指数除未利用地外,全部都有了一定程度的降低,这说明斑块形状的复杂程度降低。在景观水平上,康保县景观的斑块数和密度都有所增加,多样性指数(SHDI)、均匀度指数(SHEI)均在增加,优势度(D)在减小,这说明康保县景观各要素的分配正在变得均匀,且景观异质性增加。蔓延度(CONTAG)在减小,平均斑块分维数(FRAC_MN)接近1,这说明康保县人类对景观的干扰程度较大,斑块相似性较强,破碎化程度变高。
     (5)对于本研究区,景观格局变化的最基本的驱动因素在2000年之前是自然因素和人口因素;到2000年之后,政策因素(退耕还林草政策)便成为康保县景观格局变化的最主要的因素。
     (6)景观格局的变化也反过来影响着自然环境以及人类的生产活动,本文利用野外实测数据较详细地分析了景观格局的变化(退耕还林草)对研究区域内土壤的影响。结果表明,在一定程度上,发现退耕还林草能够提高土壤养分水平,起到了较好的土壤生态效应,使得土壤质量在不同程度上得以恢复和提高;并且对减缓土壤风蚀起到了积极的作用。另外,景观格局的变化也将在一定程度上影响该地区的小气候和生物种类的变化。
Landscape is the carrier of human life,All the social activities of human and economic activities are certain to carry out the regional landscape. Human activity is the formation of the landscape, Construction management of natural and artificial patch mosaic composed of an important driving force. Human beings are the primary driving force for landscape change, this also led to the current ecological crisis(Naveh,1995) . Change of landscape pattern is the evaluation of landscape ecology, landscape management, eco-design basis.In particular, a fragile ecological environment in the region, In the region to promote the improvement of ecological environment and sustainable development has an important theoretical and practical significance.
     Kangbao County is located in Bashang plateau of Hebei Province, is the agro-pastoral transitional zone in northern China the middle of a typical region and typical of the fragile ecological environment in the district. So Study the landscape pattern change, and to explore the factors driving force of change and the ecological effects, for improving the ecological environment in this area, fully understand the pros and cons of human activities, promote the rational use of resources in Bashang region, the protection of ecological and food security is undoubtedly of great significance.
     This article based on three remote sensing image Landsat-TM/ETM in 1987,2000,2005. From the view of the integrated physical geography, landscape ecology , with the support of remote sensing (RS), geographic information systems (GIS) technology and so on, combined with the regional characteristics of kangbao country, analysised the changes in landscape pattern of kangbao country, qualitative analysised the driving force of change of landscape pattern in the region, finally ,combined with climate weather data, field measured data and relevant information, analysised the ecological effects of Landscape pattern changes. The results showed that:
     (1)In 1987,Arable land, grassland, land for construction purposes are the main landscape types in this region; In 2000, Arable land, grassland, forest and construction land are the main landscape types in this region; In 2005,the same as 2000.By the contrast of the area of different types of landscape in these three years, we can see: the area of arable land steadily decline, woodland, grassland showed a substantial increase, especially this region has a dramatic change in 2000-2005, construction land area showed an increasing trend, an area of unused land to reduce the increase.
     (2)Based on the analysis of the single type of land use dynamic degree model and the integrated dynamic model of land use, the region has the larger speed of the overall landscape changes. 18 years,the woodlands and grasslands have a certain growth rate, especially in 2000 to 2005,the dynamic degree of woodland is 38.48%, the dynamic degree of grassland is 8.47%, construction land is also a certain degree of increase, However, changes in less than woodland and grassland, Steady decline in arable land, the dynamic degree is - 4.69%.
     (3)Through the analysis of the transfer matrix of landscape types,we can see: Substantial reduction in arable land’s area, a significant increase in Woodland and grassland’s area, construction land, unused land has increased to some extent, the waters continued to decrease in size. The main transfer of landscape types are arable land - grassland, arable land - forest, woodland– grassland, and these landscape types are of each other into a two-way.
     (4)Use the andscape pattern indices to analysis the kangbao country’s changes in landscape pattern, the results show that: 1987—2005, elements of the landscape patch in kangbao country, the number of arable land, forest land, construction land, unused land increase, the number of grassland,water has a small reduction;1987—2000,the average patch area of arable land, woodland, unused land go to the small-scale, increasing fragmentation; the patch of grassland and land for construction go to the big-scale. At the landscape level, the number of patches and density increase;SHDI, SHEI increase, D decrease; It said County Mingkang the distribution of the elements of the landscape is becoming even,and landscape heterogeneity increased.
     (5)The basic drivers of Landscape pattern changes were Natural factors and demographic factors before 2000;after 2000, Policy factors are the main factors.
     (6)Changes in landscape pattern in turn affects the production of the natural environment and human activities, In this paper,we use the field measured data to analysis the impact of changes in landscape pattern (returning farmland to forest or grassland) to the soil region, the results show that: To some extent, Returning farmland to forest and grass can improve soil nutrient levels, played a better ecological effect of soil; And to mitigate soil erosion has played a positive role; In addition, Changes in landscape pattern will also affect the region's climate and the types of living creature.
引文
[1]李哈滨景观生态学—生态学领域的新概念构架生态学进展1988,5(l):23—33.
    [2]肖笃宁.景观生态学的发展和应用.生态学杂志.1988,7(6):43—48.
    [3]赵雪,赵文智,宝音等.河北坝上脆弱生态环境及整治[M] .北京:中国环境科学出版社,1997. 1 - 16
    [4]王卫,王丽萍,高伟明等.首都生态圈可持续发展透视[M] .河北人民出版社,2001. 172 - 176.
    [5] Naveh, Z. and Lieberman,A.S.,1984,Landscape Ecology. Theory and Application, Springer_Verlag.356
    [6] Forman, R.T.T. and M. Godron. Landscape Ecology[M]. John Wiley & Sons, New York.1986.
    [7]肖笃宁等.当代景观生态学研究进展和展望[J].地理科学,1997,17(4):356~439.
    [8]何东进,洪伟,胡海清.景观生态学的基本理论及中国景观生态学的研究进展[J]. 2003, 25(2):276-282.
    [9] ISIWeb of Knowledge ( http: / /portal. isiknowledge. com. Data was retrieved and analyzed on December 19, 2007) .
    [10]傅伯杰,吕一河,陈利顶,苏常红,姚雪玲,刘宇.国际景观生态学研究新进展[J].生态学报,2008,28(2):798-804
    [11] Bastian O. 2001. Landscape ecology: Towards a unified discipline[J]. Landscape Ecology.16:757-766
    [12] Opdam P,Foppen R ,Vos C. 2002. Bridging the gap between ecology and spatial planning in landscape ecology [J].Landsc.Ecol , 16 :767~779
    [13] Chen W B, Xiao D N , Li X Z. Classification, application and creation of landscape indices.
    [14] King A. Translating models across scales in the landscape. In: Turner M G, Gardner R H, eds
    [15] Ims R A. Experimental landscape eco logy. In: Wiens J A , Moss M R, eds. Issues in landscape ecology. Snowmass Village: International Association for Landscape Ecology,1999
    [16]曹宇,肖笃宁,赵羿,等.近十年来中国景观生态学文献分析[J].应用生态学报,2001,12 (3) :474~477.
    [17] LiX-Z.2000.Understanding of the contemporary focus on landscape ecology from 15th LE annual meeting American. ActaEcolSin(生态学报),20(6):1113~1115(inChinese)
    [18]肖笃宁,布仁仓,李秀珍.生态空间理论与景观异质性[J].生态学报,1997,17(5):453~461
    [19]陈利顶,刘洋,吕一河,冯晓明,傅伯杰景观生态学中的格局分析:现状、困境与未来[J].生态学报,2008,28(11):5521-5531
    [20] Haase D. Development and perspectives of landscape ecology. Landscape Ecology, 2004, 19: 5672569.
    [21]曹宇,欧阳华,肖笃宁,等.基于APACK的额济纳天然绿洲景观空间格局分析.自然资源学报, 2004, 19 (6) : 776~785.
    [22] Hulshoff R M. Landscape indices describing a Dutch landscape. Landscape Ecology, 1995, 10 (2) : 1012111.
    [23]陈文波,肖笃宁,李秀珍.景观指数分类、应用及构建研究.应用生态学报, 2002, 13 (1) : 121~125.
    [24] Li H, Wu J. Use and misuse of landscape indices. Landscape Ecology, 2004, 19: 3892399.
    [25] Fu B J, Lu Y H. The p rogress and perspectives of landscape ecology in China. Progress in Physical Geography, 2006, 30: 2322244.
    [26] Zhang S, Zhang J, Li F, et al. Vector analysis theory on landscape pattern (VATLP) . EcologicalModelling, 2006, 193: 4922502.
    [27]陈利顶,傅伯杰,赵文武.“源”“汇”景观理论及其生态学意义.生态学报, 2006, 26 (5) : 1444-1449.
    [28]吕一河,陈利顶,傅伯杰.景观格局与生态过程的耦合途径分析.地理科学进展, 2007, 26 (3) : 1-10.
    [29] TurnerM G. Landscape ecology in North America: past, p resent, and future. Ecology, 2005, 86 (8) : 196721974.
    [30]张秋菊,傅伯杰,陈利顶.关于景观格局演变研究的几个问题.地理科学, 2003, 23 (3) : 264~270.
    [31] LAUSCH A,HERZOG F.Applicability of landscape metrics for the monitoring of landscape change : issue of scale , resolution and interpretability[J].Ecological Indicators,2002,2:3-15.
    [32] RAO K S,REKHA P.Land use dynamics and landscape change pattern in a typical micro watershed in the mid elevation zone of central Himalaya,India[J].Agriculture,Ecosystems and Environment, 2001.86:1 13-123.
    [33] Riiters K H, O′Neill R V, Hunsacker C T, et al. A factor analysis oflandscape pattern and structure metrics. Landscape Ecology, 1995, 10: 232.39.
    [34] Li H, Wu J. Use and misuse of landscape indices. Landscape Ecology, 2004, 19: 3892399.
    [35]曹新向.开封市水域景观格局演变研究.河南大学硕士学位论文,2004
    [36]曾辉,喻红,郭庆华.深圳市龙华地区城镇建设用地动态模型建设与模拟研究.生态学报,2000,20(3):243-249.
    [37]周成虎,孙战利,谢一春.地理元胞自动机研究.北京科学出版社,
    [38]许风娟.济南南部近郊区景观动态变化及其生态效应分析.山东师范大学硕士学位论文,2006.
    [39] KentM. Biogeography and landscape ecology. Progress in Physical Geography, 2007, 31 (3) : 345 - 355.
    [40] Bu R-C(布仁仓) ,Li X-Z(李秀珍) , Hu Y-M (胡远满) , et al .2004. Analyzing the agreement of maps through spatial aggregations. Acta Ecol Sin (生态学报) ,24 (4) :659-665 (in Chinese)
    [41] Song D-M(宋冬梅) ,Xiao D-N(肖笃宁) ,Zhang Z-C(张志诚) , etal . 2003. Landscape changes of Minqin oasis in Gansu Province and it‘s driving force. Chin J A ppl Ecol (应用生态学报) ,14 (4) :535-539 (in Chinese)
    [42] Meng P(孟平) ,Jia B2Q (贾宝全) ,Zhang J2S (张劲松) . 2004.Characterization of landscape changes in Taihang Mountain in China :A cae studies of Jiyuan City ,Henan Province. Acta Ecol Sin (生态学报) ,24 (4) :826~830 (in Chinese)
    [43] Wang X2L (王秀兰) ,Bao Y2H(包玉海) . 1999. Study on the methods of land use dynamic change research. Prog Geogr (地理科学进展) ,18 (1) :81~87 (in Chinese)
    [44]张金屯,邱扬,郑凤英.景观格局的数量研究方法[J].山地学报.2000,18(4):346-352
    [45]傅伯杰,吕一河,陈利顶.国际景观生态学研究新进展[J].生态学报.2008,2:798-804
    [46]王晓燕,徐志高,杨明义,等.黄土高原小流域景观多样性动态分析.应用生态学报,2004,15(2):273-277.
    [47]邬建国.景观生态学——格局、过程、尺度与等级[M].北京:高等教育出版社,2000.
    [48]汪雪格.吉林西部生态景观格局变化与空间优化研究.吉林大学博士学位论文.2008.
    [49]王宪礼,肖笃宁,布仁仓等.辽河三角洲湿地的景观格局分析[J].生态学报.1997,17(3):317-323
    [50]肖笃宁,布仁仓,李秀珍.生态空间理论与景观异质性[J].见:肖笃宁主编,景观生态学研究进展.湖南科学技术出版社.1999,P15-22
    [51]许风娟.济南南部近郊区景观动态变化及其生态效应分析.山东师范大学硕士学位论文,2006.
    [52] LAMBIN E F, TURNERB B L, GEISTA H J , et al. The causes of land-use and land-cover change :moving beyond the myths[J].Global Environmental Change ,2001,11:261-269.
    [53]朱会义,何书金,张明.环海地区土地利用变化的驱动力分析[J].地理研究,2001,20(6):669-678.
    [54]伍光和,蔡运龙.综合自然地理学.北京:高等教育出版社,2004.1-377
    [55]王书转,赵先贵.陕西省耕地面积变化趋势及其驱动因子研究.干旱区研究,2006,23(1):139-143
    [56]任志远.土地利用变化及驱动因素分析——以内蒙古准格尔旗为例.干旱区研究,2003,20(3):202-205
    [57]任志远,李晶,王晓峰.城郊土地利用变化与区域生态安全动态[M].科学出版社.2006.
    [58]傅伯杰,陈利顶,蔡运龙,李秀彬等,环渤海地区土地利用变化及可持续利用研究[M].科学出版社.2004.
    [59]姜艳等,徐丽萍.不同退耕模式林草初夏小气候效应[ J ].干旱地区农业研究, 2007, 3 (25) : 165-166.
    [60]程杰,高亚军.云雾山封育草地土壤养分变化特征.草地学报,2007,15(3):273~277
    [61]马琨,马斌,何宪平,罗登科,徐志有,牟彦荣.宁夏南部山区不同土地类型土壤养分的分布特征研究.农业科学研究,2006,27(2):1-5
    [62]盛学斌,孙建中,刘云霞.坝上地区土地利用与覆被变化对土壤养分的影响.农村生态环境,2002,18(4):10-14
    [63]常学礼.坝上地区沙漠化过程对景观格局影响的研究.中国沙漠, 1996, 16(3): 221-226
    [64]孙鸿烈等.中国生态环境建设地带性原理与实践[M].北京:科学出版社,2004:245–266
    [65]卜兆宏,刘绍清.土壤流失量及其参数实测的新方法[J].土壤学报,1995,32(2): 210-219.
    [66]韩永伟,韩建国,张蕴薇,等.农牧交错带草地植被的水土保持作用研究[J].水土保持学报,2004,18(4):24-28.
    [67]中国科学院南京土壤研究所,1978:土壤理化分析.588页,上海科学技术出版社
    [68]毛留喜.北方农牧交错带[M].北京:气象出版社,2002:1–8
    [69]慈龙骏.我国荒漠化发展趋势及防治对策[N].科技日报,1998-06-03.
    [70]展鹏飞.基于3S的伏牛山自然保护区景观格局变化研究.河南大学研究生硕士论文.2007

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700