罗巧, 李勇, 吴金水. 亚热带典型农业小流域井水水质季节变化与空间分布特征[J]. 中国生态农业学报(中英文), 2016, 24(6): 829-836.
引用本文: 罗巧, 李勇, 吴金水. 亚热带典型农业小流域井水水质季节变化与空间分布特征[J]. 中国生态农业学报(中英文), 2016, 24(6): 829-836.
LUO Qiao, LI Yong, WU Jinshui. Seasonal dynamics and spatial distribution of well water quality in a small typical agricultural catchment in subtropical China[J]. Chinese Journal of Eco-Agriculture, 2016, 24(6): 829-836.
Citation: LUO Qiao, LI Yong, WU Jinshui. Seasonal dynamics and spatial distribution of well water quality in a small typical agricultural catchment in subtropical China[J]. Chinese Journal of Eco-Agriculture, 2016, 24(6): 829-836.

亚热带典型农业小流域井水水质季节变化与空间分布特征

Seasonal dynamics and spatial distribution of well water quality in a small typical agricultural catchment in subtropical China

  • 摘要: 井水是亚热带农业区域农民的饮用水源, 其水质状况直接影响到当地农民的身体健康。本文选取亚热带典型农业小流域中井水铵态氮(NH4+-N)、硝态氮(NO3--N)、总氮(TN)和总磷(TP)为研究对象, 采用地统计学方法, 分析其季节变化和空间分布特征。结果表明, 研究区农户井水中NH4+-N、NO3--N、TN和TP含量在全年4个季节的平均值分别为0.05~0.10 mg(N)·L-1、3.0~4.9 mg(N)·L-1、3.4~5.1 mg(N)·L-1和0.03~0.17 mg(P)·L-1, 超标率分别为2.3%、10.4%、9.5%和7.9%。在季节动态变化上, NH4+-N在全年变化不显著(P>0.05), 这主要与土壤的吸附有关; 而NO3--N、TN和TP均在夏季达到最高, 春季最低, 并且两个季节之间的变化具有显著性(P<0.05), 这主要与农业施肥活动和降水条件有关。在空间变异性上, NH4+-N、NO3--N、TN和TP含量在各季节的块金值与基台值的比值都为0, 并且各变量在各季节的变程各不相同, 说明这4个变量在各季节分别在不同尺度范围内表现出较强的空间自相关性。在空间分布上, NH4+-N、NO3--N、TN和TP含量都具有斑块状分布, 而斑块的位置、大小和形状各不相同。NO3--N和TN在全年的空间分布与研究区地形和土地利用方式有关, 在东南部和西南部地势较低的水稻种植区含量较高, 而在北部地势较高的林地含量较低。而NH4+-N和TP的空间变异系数高于NO3--N和TN, 这主要是由于NH4+-N易被土壤吸附, 而磷素在土壤中易被固定, 迁移较困难, 导致NH4+-N和TP在不同地方的含量差异比较大。地形、水文气候条件、土壤类型、土地利用方式和农业施肥等是造成亚热带农业区域井水水质季节动态变化和空间分布格局差异的主要因素。

     

    Abstract: Well water is the main source of drinking water in subtropical agricultural regions in China, and its quality is critical for human health. In this paper, we carried out a geostatistical analysis to investigate the seasonal changes and spatial variability in the concentrations of ammonium nitrogen (NH4+-N), nitrate nitrogen (NO3--N), total nitrogen (TN) and total phosphorus (TP) in domestic well water in a typical agricultural catchment in southern China. Our results showed that the average concentrations of NH4+-N, NO3--N, TN and TP in spring, summer, autumn and winter of 2013–2014 were in the ranges of 0.050.10 mg(N)·L-1, 3.04.9 mg(N)·L-1, 3.45.1 mg(N)·L-1 and 0.030.17 mg(P)·L-1, respectively. The observed concentrations of NH4+-N, NO3--N, TN and TP exceeded the national standards in terms of frequency by 2.3%, 10.4%, 9.5% and 7.9%, respectively. Temporally, NO3--N, TN and TP were significantly (P < 0.05) higher in summer and lower in spring, mainly resulting from paddy rice fertilization and precipitation. On the contrary, there was no significant difference in seasonal concentrations for NH4+-N, mainly due to soil retention. In terms of spatial variability, these four variables were strongly auto-correlated in space and with different spatial ranges for different seasons. In terms of spatial distribution, the high NH4+-N, NO3--N, TN and TP concentrations were distributed as patches, even though their locations, sizes and shapes varied from one another. The concentrations of NO3--N and TN were high in the southeast and southwest of the catchment, where rice was cultivated in the low topography. But the concentrations of NO3--N and TN were low in the north, where there was forest plantation on the high topography. This result suggested that the spatial distribution of NO3--N and TN in well water were related to topography and land use type in the catchment. The spatial coefficients of variation of NH4+-N and TP were higher than those of NO3--N and TN. This was mainly attributed to the strong adsorption and immobilization of NH4+-N and phosphate in the soil matrix, resulting in the differences in NH4+-N and TP concentrations at different locations. The main factors affecting the seasonal change and spatial variability of well water quality in subtropical agriculture region were topography, regional hydrological and climatic conditions, soil types, land use types and agricultural fertilization.

     

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