顾及空间因素的协克吕格土壤环境评价模型研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
随着工农业生产的发展,耕地土壤污染问题越来越突出,特别是耕地土壤重金属和农药等有机物污染尤为突出,对土壤环境各项污染因子进行评价、预测就显得尤为重要。本文以地统计学方法为基础,提出顾及地形等空间因素的协克吕格模型,使之更符合土壤环境实际情况,能够更加准确反应土壤污染程度的空间变异性,并应用南方某市的土壤监测数据,分别对内梅罗污染指数评价模型、克吕格模型和顾及空间因素的协克吕格模型的评价效益进行比较,得出顾及空间因素的协克吕格模型较优的结论。本文的具体工作及结论有:
     (1)以内梅罗指数为模型,对土壤重金属中Pb进行综合评价。根据该方法得出研究区域内各个子区的土壤污染等级,并对该结果进行评价。
     (2)以地统计学中普通克吕格方法做为土壤污染空间变异的统计模型,对土壤重金属中Pb在研究区域内进行综合评价,在研究区得到Pb的空间变异规律。并对该结果进行评价。结果表明:在大尺度下,由于受地形地貌等空间因素的影响,普通克吕格方法的误差较大,不能很好的反映土壤污染的空间变异性。
     (3)针对普通克吕格方法在大尺度上的不适应性,提出改进方法,即对研究区域先进行高程采样,得到DEM模型,再利用遥感图像对研究区域进行河流水系提取。最后根据上述等空间因素,对研究区进行分区,把大尺度的研究区最终分形为中尺度,小尺度,最终得到顾及空间因素的协克吕格模型。对土壤重金属中Pb在研究区域内进行综合评价,得到Pb的空间变异规律。
     (4)对上述三种评价模型的结果的精度进行评价。最终得出在研究区域为大尺度的情况下,顾及空间因素的协克吕格土壤环境评价模型是精度最高、预测能力最好的模型。
According to the evaluation diffculties of soil pollution, Kriging interpolation is improved in this thesis. It makes it suitable to the reality of the soil environment, and can be able to more accurately reflect the extent of spatial variability of the soil pollution.This thesis takes some southern areas as an example, considers factors such as DEM, river, and the earth's surface, and uses this method to interpolate. At the same time, it contrast the Neimeiluo pollution index model, the ordinary Kriging model and DEM Kriging model, then get a much better space count model. The main contents are:
     (1) Nemero index for the model of heavy metals was used in the soil Pb comprehensive evaluation. According to the study, we can obtain the soil pollution levels of the various sub-areas, and the results were evaluated.
     (2) Kriging method was used to evaluate the spatial variability of the Pb in the study areas. From the results, it can be concluded as following: in the large scale, because of the topography, and other spatial factors, ordinary Kriging methods can not well reflected the spatial variability of the soil pollution.
     (3) Because of the inapplicability of the ordinary Kriging, an improved method was developed in this thesis. The regional elevation sampling and remote sensing images ware studied to form DEM model and extract river line. Finally, the study area was divided into smaller areas according those facts. Then the modle based on Cokringing and spatial facts was used to get Pb on the comprehensive evaluation of spatial variability.
     (4) Compareing the accuracy of the evaluate results of the three models at last. Throught comparison, the third method is the best.
引文
[1]陈同斌.土壤污染将成为中国的世纪难题[J].科技文萃.2005:30-32.
    [2]刘海林.需要引起人们重视的农村土壤污染问题[J].环境教育.2007:25-27.
    [3]陈怀满.环境十壤学[M].北京:科学出版社.2005:216.
    [4]施加春.浙北环太湖平原不同尺度土壤重金属污染评价与管理信息系统构建[D].2006:8-9.
    [5]夏家琪,骆永明.关于土壤污染的概念和3类评价指标的探讨[J].生态与农村环境学报,2006,22(1):87-90.
    [6]高凤霞.土壤污染状况与防治的几点建议[J].科技资讯,2007,(17):139.
    [7]刘多森,曾志远.土壤和环境研究中的数学方法与建模[M].北京:农业出版社,1987:399.
    [8]Gambardella C.A.,Moorman T.B.,Novak J.M.,et al.Field-scale variability of soil properties in central Iowa soils[J].Soil Sci.Soc.Am.J,1994,58:1501-1511.
    [9]郑一,王学军,刘瑞民,陶澍.天津地区土壤多环芳烃的克吕格插值与污染评价[J].中国环境科学,2003,23(2):113-116.
    [10]陈怀满等著.土壤中化学物质的行为与环境质量[M].北京:科学出版社,2002:8-12.
    [11]丁菁.尼梅罗污染指数法在排污口邻近海域水环境质量评价中的应[J].福建水产,2006.3:1-2
    [12]兰文辉,安海燕.环境水质评价方法的分析与探讨[J].干旱环境监测,2002,16(3):167-169.
    [13]《海洋监测质量保证手册》编委会.《海洋监测质量保证手册》[M].北京:中国海洋出版社,2000:2-4.
    [14]Campbell JB.Spatial variation of sand content and pH withinsingle contiguous delineation of two soil mapping units[J].Soil Sci.Am.J.,1978,(42):460-464.
    [15]Yost RS,Uehara G,Fox RL.Geostatistical analysis of soilchemical properties of large land areas.I.Semivariograms[J].Soil Sci.Soc.Am.J.,1982,(46):1028-1037.
    [16]Ardabanlioglu O,Oztas T,Evren S,et al..Spatialvariability of exchangeable sodium,electrical conductivity,soil pH and boron content in salt-and sodium-affected areas of thelgdir plain(Turkey) [J].Journal of Arid Environments,2003,(54):495-503
    [17]Paz-Gonzalez A,Castro M T T,Vieira S R.Geostatisticalanalysis of heavy metal in a one-hectare plot under naturalvegetation in a serpentine area[J].Canadian Journal of Sol]Science,2002,81(3):469-479.
    [18]Cattle J A,McBrantney A B,Minasny B.Kriging methodevaluation for assessing the spatial distribution of urban soil lead contamination [J].Journal of Environmental Quality,2002,31:1576-1588.
    [19]Goovaerts·P,Webster R,Dubois J P.Assessing the risk of soil contamination in the Swiss Jura using indicator geostatistics[J].Environmental and Ecological Statistics,1997,(4):31-48.
    [20]McGratha D,Zhang C,Cartona O T.Geostatistical analyses and hazard assessment on soil lead in Silvermines area,Ireland [J].Environmental Pollution,2004,(127):229-238.
    [21]Oliver M A.Kriging:A method of estimation for environmental and rare disease data[M].London:Geological Society Special Publications,1997.
    [22]Hwang S-A,Fitzgerald E F,Cayo M,et al.Assessing environmental exposure to PCBs among Mohawks at Akwesasne through the use of geostatistical methods[J].Environmental Research,1999,(80):19-199.
    [23]侯景儒.地质统计学发展现状及对若干问题的讨论[J].黄金地质,1996,2(1):1-11.
    [24]赵士鹏,金伦.地统计学及其在土壤环境背景值制图中的应用[J].中国环境监测,1992,8(5):61-64.
    [25]李毅,门旗,罗英.土壤水分空间变异性对灌溉决策的影响研究[J].干旱地区农业研究,2000,18(2):80-85.
    [26]李毅,王文焰,王全九.土壤空间变异性研究[J].水土保持学报,2002,16(1):68-71.
    [27]龚元石,廖超子,李保国.土壤含水量和容重的空间变异及其分形特征[J].土壤学报,1998,35(1):10-15.
    [28]白红军,余国营,王国平.地统计学在湿地土壤养分空间异质性研究中的应用[J].农业环境保护,2001,20(5):311-314.
    [29]朱益玲,刘洪斌,谢德体,等.江津紫色土壤养分空间变异性研究——地统计 学法[J].西南农业大学学报,2002,24(3):207-210.
    [30]朱益玲,刘洪斌,江希流.江津市紫色土中N、P养分元素区域空间变异性研究[J].环境科学,2004,25(1):138-143.
    [31]刘付程,史学正,潘贤章,等.太湖流域典型地区土壤磷素含量的空间变异特征[J].地理科学,2003,23(1):77-81.
    [32]刘付程,史学正,于东升,等.太湖流域典型地区土壤全氮含量的空间变异特征[J].地理研究,2004,23(1):63-70.
    [33]苏伟,聂宜民,胡晓洁,等.农田土壤微量元素的空间变异及Kriging估值[J].华中农业大学学报,2004,23(2):222-226.
    [34]郑一,王学军,刘瑞民,等.天津地区土壤多环芳烃的克吕格插值与污染评价[J].中国环境科学,2003,23(2):113-116.
    [35]陈慧选,吴持平,吴家华,等.应用地质统计法对土壤环境重金属最佳估值的研究[J].农业环境与发展,1994,3:19-22.
    [36]汪景宽,赵永存,张旭东,等.海伦县土壤重金属含量的空间变异性研究[J].土壤通报,2003,34(5):398-403.
    [37]郑袁明,陈同斌,陈煌,等.北京市近郊区土壤镍的空间结构及分布特征[J].地理学报,2003,58(3):470-476.
    [38]XU S,TAOS.Co regionalization analysis of heavy metals in the surface soil of Inner Mongolia[J].The Science of the Total Environmental,2004,320(1):73-87.
    [39]胡克林,李保国,陈德立.区域潜层地下水埋深和水质的空间变异性特征[J].水科学进展,2000,11(4):408-414.
    [40]牛文杰.贝叶斯同位置协同克里金(Bayesian collocated CoKriging)估值法的研究[J].计算机辅助设计与图形学学报,2002,14(4):333-335.
    [41]邬伦等著.地理信息系统——原理、方法和应用[M].北京:科学出版社,2001.
    [42]黄勇,郭庆荣,任海,万洪富.地统计学在土壤重金属研究中的应用及展望[J].生态环境2004,13(4).681-684.
    [43]施加春.浙北环太湖平原不同尺度土壤重金属污染评价与管理信息系统构建[D].2006.8-9.
    [44]兰文辉,安海燕.环境水质评价方法的分析与探讨[J].干旱环境监测,2002,16(3).167-169.
    [45]孙英君.地统计学方法进展研究[J].地球科学进展,2004,19(2):296-273.
    [46]张仁铎.空间变异理论及应用[M].北京:科学出版社.2005,65-68.
    [47]孙英君.地统计学方法进展研究[J].地球科学进展,2004,19(2):296-273.
    [48]张仁铎.空间变异理论及应用[M].北京:科学出版社.2005,70-76.
    [49]Goovaerts P.Geostatistics for Natural Resources Evaluation[M].New York:Oxford University Press,1997.
    [50]孙英君.地统计学方法进展研究[J].地球科学进展,2004,19(2):296-273.
    [51]Deutsch,Journel.GSL IB2Geostatistical Software Library and Use' s Guide(2nd)[M].New York:Oxford University Press,1998.
    [52]张仁铎.空间变异理论及应用[M].北京:科学出版社.2005,36-37.
    [53]李洪宁.基于互联网地理信息系统的城市空气质量发布与分析[J].环境保护,2002,1:33-34.
    [54]王学军.空间分析技术与地理信息系统的结合[J].地理研究,1997,16(3):70-74.
    [55]冯克忠,万庆,励惠国.基于组件技术的GIS广义空间分析[J].地球信息科学,2003,5(1):62-66.
    [56]李哈滨,王政权,王庆成.空间异质性定量研究理论与方法[J].应用生态学报.1998,12,19(6).
    [57]史舟,金辉明,李艳,李洪义.地统计软件包的开发及在土壤空间变异中的应用[J].水土保持学报.2005,19(5):170-173.
    [58]王桂红,杨勇,刘向锋.基于GIS的土壤资源信息系统研究与开发[J].农业网路信息.2005,4:39-41.
    [59]××市环境科学研究所××省生态环境与土壤研究所.××市土壤污染状况探查研究[M].2006-02.
    [60]中华人民共和国国家环境保护局、国家技术监督局.GBl5618-1995中华人民共和国国家标准[M].北京:中国标准出版社,1996-03-01
    [61]Cambardella C.A.,Moorman T.B.,Novak J.M.,et al.Field-scale variability of soil properties in central Iowa soils[J].Soil Sci.Soc.Am.J,1994,58:1501-1511.
    [62]刘哲民.宝鸡土壤重金属污染及其防治[J].干旱区资源与环境,2005.3,19(2):101-104.
    [63]张征,刘淑春.地下水环境评价中分布参数随机性的空间统计分析[J].环境科学学报,1999,19(4):410-414.
    [64]张征,鞠硕华,韩守江,等.水环境评价参数空间变异模拟数学原理与方法[J].工程勘查,2002,5:17-19.
    [65]孟健,马小明.Kriging空间分析法及其在城市大气污染中的应用[J].数学 的实践与认识,2002,32(2):309-312.
    [66]张乃明,李保国,胡克林.太原污灌区土壤重金属与盐分含量的空间分布特征[J].环境科学学报,2001,21(3):349-353.
    [67]李晓燕,张树文,王宗明,等.吉林省德惠市土壤特性空间变异特征于格局[J].地理学报,2004,59.
    [68]秦耀东.土壤物理学[M].高等教育出版社,2002:203-205.
    [69]刘付程,史学正,于东升,等.太湖流域典型地区土壤全氮的空间变异特征[J].地理研究,2004,23(1):63-71.
    [70]郑袁明,陈煌,陈同斌,郑国砥,吴泓涛,周建利.北京市土壤中Cr,Ni 含量的空间结构与分布特征[J].第四纪研究,2003,7.
    [71]Deutsch C V,Journel A G.GSLIB:Geostatistical Software Li-brary and User's Guide[M].New York:Oxford UniversityPress,1992,71-72.
    [72]Journel W Xu,T Tran.Integrating seismic data in reservoir mod-eling:The collocated CoKriging alternative[J].Society Petroleum Engineers,1992,Paper 24742:833-842.
    [73]P Doyen,T Guidish.Monte-Carlo simulation of lithology from seismic data in a channel sand reservoir[J].Society Petroleum Engineers,1989,Paper 19588:715-721.
    [74]Cambardella C.A.,Moorman T.B.,Novak J.M.,et al.Field-scale variability of soil properties in central Iowa soils[J].Soil Sci.Soc.Am.J,1994,58:1501-1511.
    [75]冯洋,刘洪斌,王正银,武伟,王世平.土壤重金属铅的空间变异性研究——以重庆市吴滩镇为例[J].中国生态农业学报,2006,1,14(1):104-107.
    [76]××市环境科学研究所××省生态环境与土壤研究所.××市土壤污染状况探查研究[M].2006-02.
    [77]冯锦霞.基于GIS与地统计学的土壤重金属元素空间变异分析[D],2007,10-30.

© 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