农业工程学报
農業工程學報
농업공정학보
2014年
21期
249-255
,共7页
杨勇%梅杨%张楚天%张若兮%廖祥森
楊勇%梅楊%張楚天%張若兮%廖祥森
양용%매양%장초천%장약혜%료상삼
土壤%重金属%监测%时空克里格%时空变异函数%时空预测
土壤%重金屬%鑑測%時空剋裏格%時空變異函數%時空預測
토양%중금속%감측%시공극리격%시공변이함수%시공예측
soils%heavy metals%monitoring%spatio-temporal kriging%spatio-temporal semivariogram%spatio-temporal prediction
土壤重金属或其他生态环境属性在时间和空间上均存在连续性和变异性,而目前的研究忽略了它们在时间维的变异。为了在预测时使用多时期采样数据,该文提出使用时空克里格方法对土壤重金属进行时空建模及预测,着重介绍了经验半方差值的计算、理论变异模型的形式及参数拟合、时空克里格估值算法、估值方差和精度随邻近点数量的变化及时空克里格制图。以武汉市青山区土壤重金属为例介绍了时空克里格建模及预测的流程。结果表明,时空克里格方法能够很好地描述土壤重金属在空间、时间和时空上3个部分的变异特征,能够利用其他时期的数据对预测时间点的属性进行插值,而多时期的属性空间分布图能够很好地反映土壤重金属的分布变化规律。该研究可为资源环境生态时空建模及预测研究提供参考。
土壤重金屬或其他生態環境屬性在時間和空間上均存在連續性和變異性,而目前的研究忽略瞭它們在時間維的變異。為瞭在預測時使用多時期採樣數據,該文提齣使用時空剋裏格方法對土壤重金屬進行時空建模及預測,著重介紹瞭經驗半方差值的計算、理論變異模型的形式及參數擬閤、時空剋裏格估值算法、估值方差和精度隨鄰近點數量的變化及時空剋裏格製圖。以武漢市青山區土壤重金屬為例介紹瞭時空剋裏格建模及預測的流程。結果錶明,時空剋裏格方法能夠很好地描述土壤重金屬在空間、時間和時空上3箇部分的變異特徵,能夠利用其他時期的數據對預測時間點的屬性進行插值,而多時期的屬性空間分佈圖能夠很好地反映土壤重金屬的分佈變化規律。該研究可為資源環境生態時空建模及預測研究提供參攷。
토양중금속혹기타생태배경속성재시간화공간상균존재련속성화변이성,이목전적연구홀략료타문재시간유적변이。위료재예측시사용다시기채양수거,해문제출사용시공극리격방법대토양중금속진행시공건모급예측,착중개소료경험반방차치적계산、이론변이모형적형식급삼수의합、시공극리격고치산법、고치방차화정도수린근점수량적변화급시공극리격제도。이무한시청산구토양중금속위례개소료시공극리격건모급예측적류정。결과표명,시공극리격방법능구흔호지묘술토양중금속재공간、시간화시공상3개부분적변이특정,능구이용기타시기적수거대예측시간점적속성진행삽치,이다시기적속성공간분포도능구흔호지반영토양중금속적분포변화규률。해연구가위자원배경생태시공건모급예측연구제공삼고。
Soil plays a very important role in the food chain, and hence is a very important pathway through which humans come into contact with most pollutants. Therefore, there is considerable interest in the best way to monitor the quality of the soil to ensure that it is managed sustainably. However, when the need to monitor the status of soil heavy metals for one area continuously occurs, the sampling and analysis procedures are expensive and time-consuming. Therefore, space-time interpolation is necessary because we can use previous soil sampling points to predict present spatial distribution with fewer soil samples. In this paper, spatio-temporal kriging was utilized to model and predict the spatio-temporal distribution of soil heavy metals. The main objectives of this study were 1) to explore the methods of obtaining an experimental spatio-temporal semivariogram; 2) to fit models for experimental spatio-temporal semivariogram;3) to perform the algorithm of spatio-temporal kriging interpolation; 4) to evaluate the accuracy and uncertainty of spatio-temporal kriging under the conditions of different neighborhoods; and 5) to predict the spatio-temporal distribution of soil heavy metals of a study area using spatio-temporal kriging. The study area was east of Qingshan district, Wuhan city, Hubei province, China. To monitor the degree of soil contamination, we collected topsoil samples from the study area every year from 2011 to 2014. The number of soil samples from 2011, 2012, 2013, and 2014 were 45, 48, 55, and 48, respectively. The concentrations of cadmium (Cd), copper (Cu), lead (Pb), and zinc (Zn) were analyzed and used as experimental data. For Cd, Cu, and Zn, soil concentrations showed a constant increase from 2010 to 2014. However, the concentrations of Pb showed an increase from 2010 to 2013, followed by a small decrease in 2014. The results of K-S tests showed that Cd, Pb, and Cu did not follow a normal distribution, however, Zn followed a normal distribution. Therefore, the data of Cd, Pb, and Cu were transformed to their common logarithms to achieve a normal distribution. As the results of experimental spatio-temporal semivariance, the T parts of semivariograms for LogCd, LogCu, and LogPb were modeled with a linear model, for Zn was modeled with an exponential model;The S and ST parts of semivariograms for LogCd, LogCu, LogPb, and Zn were modeled with a spherical model. The method of fitting models was the genetic algorithm proposed by the author in 2011. With the results of theoretical variation semivariogram models of LogCd, LogCu, LogPb, and Zn, spatio-temporal kriging were performed. To determine the influence created by the number of neighborhoods, we decided to predict the unmeasured ST point using 4 to 20 of the nearest ST sampling points around the predicted ST site. The results showed that including more neighborhoods could result in less prediction variance. However, more neighborhoods might not produce less RMSE. In addition, ordinary kriging was performed using the same year sampling points while generating a spatial distribution for one year. The results of comparison RMSE generated by ordinary kriging and spatio-temporal kriging showed that spatio-temporal kriging can produce higher prediction accuracy than ordinary kriging. The results of spatio-temporal distribution generally reveal a tendency of Cd, Cu, and Zn concentrations to spread from the south-western part to the whole study area over time, while Pb contamination tends to concentrate mostly on the northern and western parts. The paper showed the computational process of spatio-temporal kriging and its application to soil heavy metals. The results showed that spatio-temporal kriging can improve the prediction accuracy with the help of multi-temporal data.