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Modeling fertilization impacts on nitrate leaching and groundwater contamination with HYDRUS-1D and MT3DMS
Paddy and Water Environment ( IF 2.2 ) Pub Date : 2020-03-18 , DOI: 10.1007/s10333-020-00796-6 Han Zhang , Ruxing Yang , Shanshan Guo , Qiling Li
Paddy and Water Environment ( IF 2.2 ) Pub Date : 2020-03-18 , DOI: 10.1007/s10333-020-00796-6 Han Zhang , Ruxing Yang , Shanshan Guo , Qiling Li
Agriculture is recognized as the major source of groundwater nitrate (NO3−) contamination; yet quantifying its effects is still challenging in large, due to the difficulty to track the transformation and fates of agricultural nitrogen (N) in soils and aquifers. In this study, a HYDRUS-1D model was adopted to explore water content and NO3− distribution in the unsaturated zone above groundwater table in an agricultural area. The resulting estimates of water flux and NO3− leaching through the unsaturated zone were used as input data in the application of the groundwater flow model Visual MODFLOW and mass transport model MT3DMS via a concentration recharge boundary. Nitrate leaching occurred mainly between May and September, accounting for 64% of the annual total. Four fertilizer application scenarios were developed, and their effects were compared in predictive simulations of groundwater NO3− concentrations using MT3DMS and quantitative analysis of NO3−-contaminated areas, the spatial and temporal distribution of groundwater NO3− concentration using ArcGIS. Predictions in the business as usual (scenario 1) showed that NO3− continued to accumulate in groundwater in the study area, with the maximum increased from 14 to 18 mg L−1 in 10 years. In the scenario 2 (2% increase in fertilizer application rate), peak groundwater NO3− was expected to exceed 20 mg L−1 in 2027. However, in both scenarios 3 (2% reduction in fertilizer application) and 4 (4% reduction in fertilization), the maximal NO3− concentrations were predicted to be lower than 12 mg L−1 in 2027. The integration of HYDRUS-1D, MT3DMS and GIS models offers a powerful tool for evaluating agricultural management impacts on aquifer water quality.
中文翻译:
使用HYDRUS-1D和MT3DMS模拟施肥对硝酸盐淋失和地下水污染的影响
农业是公认的地下水硝酸盐的主要来源(NO 3 - )污染; 然而,由于难以追踪土壤和含水层中农业氮(N)的转化和命运,因此量化其影响仍然面临很大挑战。在这项研究中,一个HYDRUS-1D模型获得通过探索水含量和NO 3 -中地下水位之上的非饱和区分布在农业区。将所得的水通量和NO的估计3 -在地下水流模型Visual MODFLOW和传质模型MT3DMS中,通过浓度补给边界将通过非饱和带的淋洗作为输入数据。硝酸盐浸出主要发生在5月至9月之间,占全年总量的64%。四个肥料应用场景被开发,它们的作用在地下水的预测模拟NO进行比较3 -使用MT3DMS和NO的定量分析浓度3 - -contaminated区域,地下水的时空分布NO 3 -使用ArcGIS浓度。在业务预测如常(方案1)表明,NO 3 -继续在研究区域的地下水中积累,在10年中最大值从14 mg L -1增加到18 mg L -1。在方案2(在施用量2%增加),峰地下水NO 3 -已超过了20毫克的L -1在2027年但是,在这两种情况下(在施肥减少2%)3和4(4%在施肥减少),最大NO 3 -浓度预测要低于12毫克的L -1 2027年HYDRUS-1D,MT3DMS和GIS模型提供了对含水层水质评价农业管理影响的强大工具的集成。
更新日期:2020-03-18
中文翻译:
使用HYDRUS-1D和MT3DMS模拟施肥对硝酸盐淋失和地下水污染的影响
农业是公认的地下水硝酸盐的主要来源(NO 3 - )污染; 然而,由于难以追踪土壤和含水层中农业氮(N)的转化和命运,因此量化其影响仍然面临很大挑战。在这项研究中,一个HYDRUS-1D模型获得通过探索水含量和NO 3 -中地下水位之上的非饱和区分布在农业区。将所得的水通量和NO的估计3 -在地下水流模型Visual MODFLOW和传质模型MT3DMS中,通过浓度补给边界将通过非饱和带的淋洗作为输入数据。硝酸盐浸出主要发生在5月至9月之间,占全年总量的64%。四个肥料应用场景被开发,它们的作用在地下水的预测模拟NO进行比较3 -使用MT3DMS和NO的定量分析浓度3 - -contaminated区域,地下水的时空分布NO 3 -使用ArcGIS浓度。在业务预测如常(方案1)表明,NO 3 -继续在研究区域的地下水中积累,在10年中最大值从14 mg L -1增加到18 mg L -1。在方案2(在施用量2%增加),峰地下水NO 3 -已超过了20毫克的L -1在2027年但是,在这两种情况下(在施肥减少2%)3和4(4%在施肥减少),最大NO 3 -浓度预测要低于12毫克的L -1 2027年HYDRUS-1D,MT3DMS和GIS模型提供了对含水层水质评价农业管理影响的强大工具的集成。