奈曼旗沙质草地植被—裸沙动态特征研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
土地沙漠化是人类面临的重大全球生态环境问题之一,造成了严重的环境恶化和经济贫困,威胁着人类社会的生存和发展。我国沙漠广布,是世界上受沙漠化危害最为严重的国家之一,沙漠化的研究对于中国具有十分重要的意义。植被变化和风沙活动是半干旱地区两种主要的地表过程,影响着沙漠化发展的方向。深入研究植被和裸沙的空间分布及其动态特征为阐明植被变化和风沙活动的相互关系提供基础,为进一步解释半干旱区地表变化的规律及其机制提供依据。
     基于以上的考虑,本文以半干旱地区植被变化和风沙活动明显的奈曼旗沙质草地为例,在景观生态学理论的指导下,采用遥感与地理信息系统等手段,结合野外调查,对以下内容进行研究。
     1.对研究区遥感影像进行分析,结合实地考察归纳总结得到奈曼旗沙质草地植被和裸沙的空间分布类型主要有如下三种:相对均匀型,梯度型,几何型。相对均匀型指植被斑块和裸沙斑块在空间分布上比较均匀,植被或裸沙地的空间分布没有明显的集中或渐变特征。梯度型主要是指从完全裸沙地到植被集中区,植被和裸沙的空间分布具有明显的梯度渐变过程,主要分布在河流和湖泊附近。几何型指具有几何形状的农田植被与裸沙地在空间上的分布形式。
     2.对奈曼旗沙质草地植被和裸沙空间分布进行深入研究发现:奈曼旗沙质草地植被-裸沙空间分布主要集中在连续的几个NDVI值之间,不同分布类型峰值的大小和半峰宽各不同。植被破碎化主要发生在两个NDVI区段内。在斑块破碎化过程中植被为基质,裸沙斑块状分布与高植被梯度型分布的斑块变形程度相似。植被和裸沙细密度均匀分布类型中斑块变形高于其他类型。低植被梯度分布型中斑块的变形不明显。
     3.对同一NDVI值斑块的空间分布特征分析发现:同一NDVI值内,存在着斑块数量随着斑块面积的增加而呈幂函数减小,随斑块周长的增加而呈幂函数增加的规律,且斑块数量越多时该规律表现越明显。
     4.对典型样带近二十年植被-裸沙空间分布的面积曲线,斑块密度曲线,形状指数曲线的动态特征参数进行分析,发现植被-裸沙动态变化具有三种主要模式。模式一为1987年到1992年斑块面积快速集中在较窄的NDVI值之间,并快速向低NDVI移动,斑块形状快速简单化;1992年到2002年斑块面积较慢集中较窄的NDVI值之间,快速向高NDVI移动;2002年到2009年斑块面积缓慢集中较窄的NDVI值之间,缓慢向低NDVI移动,斑块形状缓慢简单化。模式二为1987年到1992年斑块面积缓慢分散在较宽的NDVI值之间,缓慢向低NDVI移动,斑块形状快速简单化;1992年到2002年斑块面积快速集中在较窄的NDVI值之间,快速右移向高NDVI移动,斑块形状缓慢简单化;2002年到2009年斑块面积较快分散在较宽的NDVI值之间,缓慢向低NDVI移动,斑块形状缓慢简单化。模式三为1987年到1992年斑块面积分布基本不变,缓慢向低NDVI移动,斑块形状快速简单化;1992年到2002年斑块面积快速分散在较宽的NDVI值之间,快速向高NDVI移动,斑块形状缓慢简单化;2002年到2009年斑块面积快速集中在较窄的NDVI值之间,缓慢向高NDVI移动,斑块形状较慢复杂化。
     5对奈曼旗沙质草地植被-裸沙动态的驱动力分析发现:气候因素中大风、降水量和蒸发量变化与植被-裸沙空间分布动态的相关性较大;人为因素的影响不大,但与年末牲畜栅栏头数和农牧民纯收入具有一定的相关性。并对Lancaster气象模型进行了验证。
Desertification is one of the major global environmental problems that human faced, It has caused serious environmental degradation and economic deprivation and even hazard the survival and development of human society. Desert widely distributed in China and it is one of the countries that damaged seriously by desertification. Therefore, desertification has great significance to China. Vegetation change and sand activity is two major surface processes in semi-arid regions, affecting desertification development. For clarifying the relationship between vegetation changes and sand activities and further explaining the variation of the surface and mechanism in Semi-arid areas, this paper studied the vegetation coverage together with spatial distribution and dynamic Characteristics of the bare sand deeply.
     Based on the considerations above, it takes sandy grassland in Naiman Banner, which has apparent vegetation change and drift activity, for example. This paper is under the guidance of landscape ecology, using remote sensing and geographic information systems and field investigation to research on the following contents.
     1. From analysis of remote sensing image in study area combine with the field investigation, it can conclude the sandy grassland vegetation and spatial distribution of the bare sand in Naiman Banner, there are three main types as follows: relatively uniform type, gradient type, geometry type. Relatively uniform type refers to vegetation patches and bare sand patches distribute uniformly in space and the dirtibution is no obvious concentration or gradient characteristics. Gradient-based mainly refers the completely bare sand move to vegetation clusters areas. The distribution of vegetation and bare sand has obvious gradient gradual process.It mainly distributed in the vicinity of rivers and lakes. Geometry type means with geometric shape of the field vegetation and form of the bare sand in the spatial distribution.
     2. From the reasearch on the vegetation coverage together with spatial distribution and dynamic characteristics of the bare sand in Naiman Banner, we found that: Sandy grassland vegetation - bare sand distribution in Naiman Banner concentrated mainly in a few NDVI values, peak size and half-peak breadths of distribution types vary from unit to unit. Vegetation - bare sand fragmentation occurred mainly in two NDVI sections. The vegetation is basis in patch fragmentation process, bare sand and patchy distribution and patch of High vegetation - bare of sand gradient type distribution similar to their deformation. Plaque deformation in vegetation and uniform density type of bare sand higher than other types. Plaque deformation in Low vegetation - bare patch of sand in the gradient distribution is not relatively significant.
     3. From the analysis features about the spatial distribution of same NDVI values for plaque we found that: the Area and patch number of the same NDVI values for plaque has power function relationship, index of location parameters is negative; Patch perimeter and area of the same NDVI values for plaque aslo has power function relationship, index of location parameters is Positive.
     4. From the analysis of area curve about vegetation - the spatial distribution of bare sand, patch density curve, the shape of the dynamic characteristic parameter exponential curve in typical sample with nearly two decades, we found that vegetation - bare sand dynamics has three main modes. Mode 1 for the 1987 to 1992 concentrated fastly between a more narrow NDVI values and took rapid movement to the low NDVI values, simplification of plate was fast. From 1992 to 2002, it focused slowly between the more narrow NDVI values and moved rapidly to high NDVI; From 1992 to 2002, it slower focused between the more narrow NDVI values and moved slowly to low NDVI values, simplification of plate was slow. Mode 2 for the 1987 to 1992 concentrated slowly between a more wide NDVI values and took slow movement to the low NDVI values, simplification of plate was fast. From 1992 to 2002, it focused fastly between the more narrow NDVI values and moved rapidly to high NDVI; simplification of plate was slow.From 2002 to 2009, it focused rapidly between the more wide NDVI values and moved slowly to low NDVI values, simplification of plate was slow. Mode 3 for the 1987 to 1992, it basically unchanged and took slow movement to the low NDVI values, simplification of plate was fast. From 1992 to 2002, it focused fastly between the more wide NDVI values and moved rapidly to high NDVI; simplification of plate was slow.From 2002 to 2009, it focused rapidly between the more narrow NDVI values and moved slowly to high NDVI values, complication of plate was slowish.
     5. From the analysis on driving force of Sandy grassland vegetation - bare sand dynamics in Naiman Banner, we found that climate change is the the main reason for vegetation - bare sand Changes, In particular, wind, precipitation and evaporation. Human activities on Sandy grassland vegetation - bare sand dynamics in Naiman Banner also has some impact, but not obvious.
引文
[1]唐灿,孟晖河西走廊地区土地荒漠化问题分析[J],中国地质灾害与防治学报1999,10(4):47-55.
    [2] Abahussain A. A, Abdu A. S., A Zubari WK,et al. Desertification in the Arab Region: analysis of current status and trends, Journal of Arid Environment, 2002, 51(4):521~545
    [3]寇有观,萧术.卫星遥感在我国土地资源调查的作用[J].中国航天,1998,(4):7-11.
    [4]董光荣,吴波慈龙骏等。我国荒漠化现状、成因与防治对策[J].中国沙漠. 1999,(4):318-332.
    [5] Buckley, 1987,The effecrt of sparse vegetation on the transport dune sand by wind, Natrur, 325(6103): 426-428.
    [6]黄富强,牛海山,王明星,王跃思,丁国栋.毛乌素裸沙植被覆盖率与风蚀输沙率定量关系.地理学报,2001,56(6) :700~710.
    [7]夏建新,植被覆盖条件下地表输沙率模型[J],应用基础与工程科学学报,2006,14(2):218-227.
    [8]屈建国,丁国梁,植物配置格局对土壤风蚀的影响研究[M].2007
    [9] Grainger, A., Smith, M., Squires V. R. et al Desertification and climate change: the case for greater convergence [J], Mitigation and adaptation strategies for global change, 2000, 5: 361-377.
    [10]高志海,魏怀东,丁峰. TM影像沙漠化解泽与成图技术研究[J].遥感技术与应用,2002,17(6):293-298.
    [11]肖笃宁.景观生态学—理论方法及应用[M].北京:中国林业出版社,1991.
    [12]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,2000,163~221.
    [13]傅伯杰,陈利顶,马克明等.景观生态学原理及应用[M].北京:科学出版社,2002.
    [14]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,2007,2-18.
    [15] Ayoub A. T. 1998. Extent, severity and causative factors of land degradation in the Sudan [J]. Journal of Arid Environments, 38: 397-409.
    [16]蔡体久.基于遥感和的荒漠化程度定量评价研究[D].北京:北京林业大学博士学位论文,2002.
    [17]范文义.荒漠化程度评价高光谱遥感信息模型[J].林业科学,2002.
    [18]王伯荪,彭少麟.植被生态学-群落与生态系统[M].北京:中国环境科学出版社,1997.
    [19]中国科学院内蒙古草原生态系统定位站.草原生态系统研究[M].北京:科学出版社,1985.
    [20]李博.内蒙古地带性植被的基本类型及其生态地理规律[J].内蒙古大学学报(自然科学),1962.
    [21]植被生态学研究编辑委员会.植被生态学研究[M].北京:科学出版社,1994.
    [22]冯起,程国程.我国裸沙水分分布状况及其意义[J].土壤学报,1999,36(5):226-236.
    [23]吕达仁主编.内蒙古半干旱草原土壤-植被-大气相互作用[M].北京:气象出版社,2005.
    [24]吴正.裸裸沙貌与治沙工程学[M].北京:科学出版社,2003.
    [25]史培军,严平,袁艺.中国北方裸沙活动的驱动力分析[J].第四纪研究,2001,21(1):41-47.
    [26]刘玉璋,董光荣,李长治.影响土壤风蚀主要因素的风洞试验研究[J].中国沙漠,1992,(4):41-48.
    [27]贺大良.关于风速和输沙律的几个问题[J].中国沙漠,1993,13(2):14-17.
    [28]常学礼,杨持.科尔沁裸沙降水量波动对草场植被组成和初级生产力影响的研究[J].中国草地,2000,(3):7-16.
    [29]史培军,李晓兵,周武光.利用“3S”技术检测我国北方气候变化的植被响应[J].第四纪研究, 2000,20(3):220-228.
    [30]高尚玉,史培军,哈斯等.我国北方裸沙灾害加剧的成因及其发展趋势[J].自然灾害学报,2000,9(3):31-37.
    [31]张德二.我国历史时期以来降尘的天气气候学初步分析[J].中国科学,1984,24(3):278-288.
    [32]张德二,陆风.我国北方的冬季沙尘暴[J].第四纪研究,1999,(5):441-447.
    [33]戴雪荣,李吉均,俞立中等.末次间冰期甘肃沙尘暴演化历史的黄土记录分析[J].地理学报, 1999,54(5):445-453.
    [34] Townshend J R G. Global data sets for land applications from the advance very high resolution radiometer: An introduction [J]. International Journal of Temote Sensing, 1994,(15):3319-3332.
    [35] Forman R T T, Godron M. Landscape Ecology [M]. New York: John Wiley&Sons. 1986.
    [36] Forman R T T. Cambridge University Press [M]. Land Mosaics: the ecology of landscapes and regions.1995.
    [37] Wu J, Levin S A.. A spatial patch dynamic modeling approach to pattern and process in an annual grassland. Ecological Monographs.1994. 64(4): 447-464.
    [38] Wiens JA. The science and practice of landscape ecology [A].In: Klopatek TM, GardnerRH,eds. Landscape Ecological Analysis: Issues and Applications[C]. New York: Springer Verlag. 1999. 372-383.
    [39]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,2007,2-18.
    [40]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,2000,163~221.
    [41]肖笃宁.景观生态学—理论方法及应用[M].北京:中国林业出版社,1991.
    [42]傅伯杰,陈利顶,马克明等.景观生态学原理及应用[M].北京:科学出版社,2002.
    [43]李振山,王怡,贺丽敏.半干旱区植被-裸沙动力过程耦合研究:Ⅰ.模型.中国沙漠,2009,29(1):23-30.
    [44]邬建国.现代生态学讲座(Ⅲ)科学进展与热点论题[M].北京:高等教育出版社,2007,362-379
    [45]朱震达,王涛.中国北方的土地沙漠化问题.科技导报[J]. 1991,4:55-58.
    [46] JingYun F., YongChang S., HongYan L.,et al. Vegetation-Climate Relationship and ItsApplication in the Division of Vegetation Zone in China [J]. Acta Botanica Sinica. 2002, 44 (9) : 1105-1122
    [47] Ayoub A. T. 1998. Extent, severity and causative factors of land degradation in the Sudan [J]. Journal of Arid Environments, 38: 397-409.
    [48] Fredrickson E., K. M. Havstad, R. Estell and P. Hyder. 1998. Perspectives on desertification: south-western United States [J]. Journal of Arid Environments, 39:171-297.
    [49]田长彦,宋郁东,胡明芳.新疆荒漠化现状,成因及对策[J].中国沙漠, 1999.19:214-217.
    [50]赵哈林,张桐会,吴薇等.科尔沁裸沙沙漠化过程及其恢复机理[M].北京:海洋出版社,2003.
    [51]朱震达,刘恕.中国的荒漠化及其治理[M].北京:科学出版社,1998.
    [52] Puigdefabregas J. and Mendizabal T. Perspectives on desertification: western Mediterranean [J]. Journal of Arid Environments, 1998.39: 209-224.
    [53]董光荣,高尚玉,金炯.青海共和盆地土地沙漠化与防治途径[M].北京:科学出版社,1993.
    [54]葛小东,李振山.科尔沁裸沙近水区域沙漠化空间分布规律初步研究[J].中国沙漠,2009,29(3):404-408.
    [55]常学礼,高玉葆,何兴东等.科尔沁裸沙流动裸沙景观破碎化和荒漠化过程分析[J].南开大学学报(自然科学版),2006,39:84-89.
    [56] Zalidis G. S., Stamatiadis, V. Takavakoglou,et al. Impacts of agricultural practices on soil and water quality in the Mediterranean region and proposed assessment methodology [J]. Agriculture, Ecosystems and Environment, 2002, 88:137-146.
    [57] Ludwig J. A., E. Muldavin and K. R. Blanche. Vegetation change and surface erosion in desert grasslands of Otero Mesa, Southern New Mexico [J]: 1982-1985.American Midland Naturalist, 2000, 144:273-285.
    [58] Sullivan S. The impacts of people and livestock on topographically diverse open wood-and shrub-lands in arid north-west Namibia [J]. Global Ecology and Biogeogaphy, 1999.8: 257-277.
    [59]张萍,哈斯等.呼伦贝尔沙质草原风蚀坑积沙区的植被分带性[J].自然资源学,2008, 23(2):237-244.
    [60] Dech J P, Maun A M, Pazner M I. Blowout dynamics on Lake Huron sand dunes: analysis of digital multispectral data from colour air photos [J]. Catena, 2005, 60:165–180.
    [61] Duran O, Silva M V N, Bezerra L J C, Herrmann H J, Maia L P. Measurements and numerical simulations of the degree of activity and vegetation cover on parabolic dunes in north-eastern Brazil [J]. Geomorphology, 2008, 102: 460–471.
    [62]王怡,李振山,陈悠.半干旱区植被-裸沙动力过程耦合研究:Ⅱ.模拟.中国沙漠,2009,29(1):30-38.
    [63]陈悠,李振山,王怡.半干旱区植被-裸沙动力过程耦合研究:Ⅲ.应用.中国沙漠,2009,29(1): 38-45.
    [64]王怡.裸沙-植被动力学耦合过程模拟研究[D].北京:北京大学硕士论文,2007.
    [65]包慧娟,沙漠化地区可持续发展研究-以科尔沁裸沙奈曼旗地区为例[M].长春:中国科学院研究生院博士学位论文,2004.
    [66]朱震达,陈广庭等.中国土地沙质荒漠化[M].北京:北京:科学出版社,1994:46、98、107、166-169.
    [67]吴薇.近50 a来科尔沁地区沙漠化土地的动态监测结果与分析[J].中国沙漠,2003, 23(6):646-651.
    [68]内蒙古自治区统计局.内蒙古自治区统计年鉴[M].北京:中国统计出版社,1987-2008.
    [69] Bagnold, R. A. The Physics of Blown Sand and Desert Dunes[M]. London: Chapman and Hall. 1941.
    [70]李爱敏,韩致文,许健等. 21世纪初科尔沁裸沙沙漠化土地变化趋势[J].地理学报,2006,61(9):978-984.
    [71]陈述彭、赵英时主编.遥感地学分析[M].北京:测绘出版杜,1990.
    [72]孙涛,李纪人,杜龙江.塔里木河下游应急输水前后生态变化遥感监测分析中国水利水电[J].科学研究院学报.2004,2(3):179-183.
    [73]张芸香,郭晋平森林景观斑块密度及边缘密度动态研究[J].生态学杂志,2001,20 (1):18-21.
    [74] Hastings M.H. Georges.Fractals Oxford University Press, 1993.
    [75]辛晓平,徐斌,单保庆等.恢复演替中草地斑块动态及尺度转换分析[J].生态学报,2000, 20(4):587-593.
    [76]赵哈林,张桐会,吴薇等.科尔沁沙地沙漠化过程及其恢复机理[M].北京:海洋出版社,2003.
    [77] Lancaster N., et al. A test of a climatic index of dune mobility using measurements from the southwestern United States [J]. Earth Surface Processes and Landforms. 2000,25:197-207. .

© 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