摘要
准确的土壤盐分空间变异信息是防治土壤盐碱化和制定科学种植规划的重要依据。本文根据电磁型近地传感器EM38测定的土壤表征电导率(EC_a),研究有限最大似然法(REML)在地统计建模趋势去除中的应用,基于线性混合模型将趋势与残差分离,然后利用泛克立格开展海涂围垦区水稻田土壤盐分的空间变异性研究。结果表明,本研究区土壤盐分存在强烈的空间变异性且呈一定的空间分布趋势;REML方法拟合的二次多项式模型可较好的表征土壤盐分的空间分布趋势,在去除趋势的同时,选用指数模型对残差的半方差函数进行拟合;基于泛克立格插值的交叉检验结果可见,该方法可得到较小的预测误差,且标准离差比平均值参数接近理想值,REML方法大大提高了模型的精度;就地统计空间插值结果可看出,土壤盐分呈出从西北角向东北角、从周边向中心渐变的空间分布特征,且与土壤排水条件表现出较好的耦合性。
Accurate map of soil salinity is great important for controlling soil salinization and making rational decisions for management. The apparent electrical conductivity(EC_a) was measured by the Geonics EM38 sensor at 192 points in a paddy rice field in reclaimed coastal saline land in Zhejiang Province, China. We discovered a strong spatial trend in the data, which we treated as a quadratic trend surface with correlated random residuals, evaluated the coefficients of the trend and the parameters of the covariance of the residuals by restricted maximum likelihood(REML), and then kriged the EC_a on to a fine grid for mapping by universal kriging, using the estimated covariance parameters and taking into account the form of the trend. All combinations of models and kriging methods gave small mean errors(ME), as expected kriging was unbiased. The mean squared deviation ratios(MSDR), which ideally should equal 1,varied more. The combination with an MSDR closest to 1 was UK with the exponential variogram estimated by REML;its MSDR was 1.03. We used this combination to map the predicted EC_a and associated errors. The horizontal distribution of salinization was characteristic of higher salinity in the northwestward side than the southeast side, or higher in the central part than the edge part. Besides, there existed coupling effect between the soil salinity and the drainage condition.
引文
[1]管孝艳,王少丽,高占义,等.盐渍化灌区土壤盐分的时空变异特征及其与地下水埋深的关系.生态学报,2012,32(4):1202-1210.
[2]刘国顺,常栋,叶协锋,等.基于GIS的缓坡烟田土壤养分空间变异研究.生态学报,2013,33(8):2586-2595.
[3]章亭洲,马晓航,许光辉.我国地带性土壤中产蛋白酶细菌生态分布研究.应用生态学报,1991,2(4):339-343.
[4]高福元,赵成章,卓马兰草.高寒退化草地不同海拔梯度狼毒种群分布格局及空间关联性.生态学报,2014,34(3):605-612.
[5]GUO Y,SHI Z,LI H Y,et al.Application of digital soil mapping methods to identify salinity management classes in coastal lands of central China.Soil Use and Management,2013,29:445-456.
[6]OLIVER M A,WEBSTER R.A tutorial guide to geostatistics:Computing and modelling variograms and kriging.Catena.2014,112:56-69.
[7]ODEH I O A,MCBRATNEY A B,CHITTLEBOROUGH D J.Spatial prediction of soil properties from landform attributes derived from a digital elevation model.Geoderma,1994,63:197-214.
[8]LARK R M,CULLIS B R,WELHAM S J.On spatial prediction of soil properties in the presence of a spatial trend:the empirical best linear unbiased predictor(E-BLUP)with REML.European Journal of Soil Science,2006,57:787-799.
[9]MATHERON G.Le krigeage universal.Cahiers du Centre de Morphologie Mathématique,No 1.Ecole des Mines de Paris,Fontainebleau,1969.
[10]WEBSTER R,OLIVER M A.Geostatistics for Environmenta l Scientists(second edition).John Wiley&Sons,Chichester,2007.
[11]PATTERSON H D,THOMPSON R.Recovery of inter-bloc k information when block sizes are unequal.Biometrika,1971,58:545-554.
[12]MINASNY B,MCBRATNEY A B.Spatial prediction of soi l properties using EBLUP with the Matern covariance function.Geoderma,2007,140:324-336.
[13]CHAI X R,SHEN C Y,YUAN X Y,et al.Spatial prediction of soil organic matter in the presence of different external trends with REML-EBLUP[J].Geoderma,2008,148(2):159-166.
[14]LI H Y,SHI Z,WEBSTER W,et al.Mapping the three-dimensional variation of soil salinity in a rice-paddy soil.Geoderma,2013,195-196:31-41.
[15]YAO R J,YANG J S.Quantitative evaluation of soil salinity and its spatial distribution using electromagnetic induction method.Agricultural Water Management,2010,97(12):1961-1970.
[16]CRESSIE N A C.Statistics for Spatial Data.Revised edition.John Wiley&Sons,New York,1993.
[17]GERBBERS R and ADAMCHUK V I.Precision agriculture and food security.Science.2010,327:828-831.
[18]杨谦,王晓晴,孙孝林,等.基于REML的普通克里格和回归克里格在土壤属性空间预测中的比较[J].土壤通报,2018,49(2):154-163.