利用可见近红外漫反射光谱评价土壤石油污染的空间变异性。

Somsubhra Chakraborty, David C Weindorf, Yuanda Zhu, Bin Li, Cristine L S Morgan, Yufeng Ge, John Galbraith
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引用次数: 19

摘要

可见近红外(VisNIR)漫反射光谱(DRS)是一种快速、无损地检测土壤中总石油烃(TPH)污染的存在和数量的方法。该研究证明了VisNIR DRS在野外用于近距离感知并绘制土壤中TPH污染的面积范围的可行性。更具体地说,我们评估了惩罚样条回归和地质统计学两种方法的结合是否可以提供有效的方法来评估土壤TPH的空间变异性,该方法使用的是美国路易斯安那州中部80公顷原油泄漏土壤的VisNIR DRS数据。首先,通过结合46个污染和未污染土壤样品的实验室TPH值以及这些样品的VisNIR反射光谱的一阶导数,校准了一个惩罚样条模型来预测土壤中的TPH污染。校正后的惩罚样条模型的r(2)、RMSE和偏差分别为0.81、0.289 log(10) mg kg(-1)和0.010 log(10) mg kg(-1)。随后,使用惩罚样条模型预测了80 ha研究地点收集的128个土壤样品的土壤TPH含量。当从128个样本中随机选择验证子集(n = 10)进行评估时,惩罚样条模型表现令人满意(r(2) = 0.70;残差预测偏差= 2.0)。在剩余的118个预测用于生成实验半方差图和图之后,使用相同的验证子集来评估点克里格插值。实验半变异曲线拟合为指数模型,表明土壤TPH具有较强的空间依赖性[r(2) = 0.76, nugget = 0.001 (log(10) mg kg(-1))(2), sill = 1.044 (log(10) mg kg(-1))(2)]。Kriging插值充分插值了TPH, r(2)和RMSE值分别为0.88和0.312 log(10) mg kg(-1)。此外,在克里格图中,TPH分布与研究地点的预期TPH变异性相匹配。由于VisNIR预测和地质统计学的结合应用有望识别土壤中TPH污染的空间格局,因此未来的研究需要对石油污染土壤的空间变异性进行评估。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Assessing spatial variability of soil petroleum contamination using visible near-infrared diffuse reflectance spectroscopy.

Visible near-infrared (VisNIR) diffuse reflectance spectroscopy (DRS) is a rapid, non-destructive method for sensing the presence and amount of total petroleum hydrocarbon (TPH) contamination in soil. This study demonstrates the feasibility of VisNIR DRS to be used in the field to proximally sense and then map the areal extent of TPH contamination in soil. More specifically, we evaluated whether a combination of two methods, penalized spline regression and geostatistics could provide an efficient approach to assess spatial variability of soil TPH using VisNIR DRS data from soils collected from an 80 ha crude oil spill in central Louisiana, USA. Initially, a penalized spline model was calibrated to predict TPH contamination in soil by combining lab TPH values of 46 contaminated and uncontaminated soil samples and the first-derivative of VisNIR reflectance spectra of these samples. The r(2), RMSE, and bias of the calibrated penalized spline model were 0.81, 0.289 log(10) mg kg(-1), and 0.010 log(10) mg kg(-1), respectively. Subsequently, the penalized spline model was used to predict soil TPH content for 128 soil samples collected over the 80 ha study site. When assessed with a randomly chosen validation subset (n = 10) from the 128 samples, the penalized spline model performed satisfactorily (r(2) = 0.70; residual prediction deviation = 2.0). The same validation subset was used to assess point kriging interpolation after the remaining 118 predictions were used to produce an experimental semivariogram and map. The experimental semivariogram was fitted with an exponential model which revealed strong spatial dependence among soil TPH [r(2) = 0.76, nugget = 0.001 (log(10) mg kg(-1))(2), and sill 1.044 (log(10) mg kg(-1))(2)]. Kriging interpolation adequately interpolated TPH with r(2) and RMSE values of 0.88 and 0.312 log(10) mg kg(-1), respectively. Furthermore, in the kriged map, TPH distribution matched with the expected TPH variability of the study site. Since the combined use of VisNIR prediction and geostatistics was promising to identify the spatial patterns of TPH contamination in soils, future research is warranted to evaluate the approach for mapping spatial variability of petroleum contaminated soils.

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来源期刊
Journal of Environmental Monitoring
Journal of Environmental Monitoring 环境科学-分析化学
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