村镇饮用水源地污染关键区识别

    Key area identification of pollution sources of drinking water sources in rural areas

    • 摘要: 为直接识别村镇饮用水源地污染关键区,以遥感影像分类技术提取水源地土地利用类型,基于水源地各类非点源污染源源强系数,根据不同污染因子贡献率采用指数超标法计算各污染因子权值,确定各类污染源的污染影响程度和分析水源地各子流域污染浓度,以地表水环境指标值为界限值进行识别。以安基山水源地2011年污染状况为研究对象,选择农村居民区、农田、矿山为污染源,采用化学需氧量、氨氮、总氮和总磷作为主要污染因子,应用ArcGIS软件划分水源地为19个子流域,在各子流域内综合考虑各类污染源的影响程度,以地表Ⅲ类、Ⅳ类和Ⅴ类水的指标值为界限划分水源地污染等级区,划分结果为:子流域8、14、16和17为正常区,子流域9、10和13为一般污染关键区,子流域2为次污染关键区,子流域1、3、4、5、6、7、11、12、15、18和19为污染关键区。该研究可为村镇饮用水源地污染关键区识别提供新的方法。

       

      Abstract: Abstract: In the upstream of water sources, many pollutants are output from key pollution areas of water sources, and thus identifying key pollution areas of water sources is a key to protection and pollution control of rural drinking water source. In this paper, a method to directly identify key pollution areas was proposed and applied to investigate the pollution situation of rural drinking water sources in Anjishan reservoir area in 2011. Residential areas, farmlands, mines, and other land use types were identified as the pollution sources based on image classification techniques of remote sensing. Hydrology analysis tools for ArcGIS software were used to determine catchment of Anjishan basin. Batch Sub watershed Delineation tool combined with the distribution of the main pollution sources was used to divide Anjishan basin into 19 sub watershed, and land use areas for each sub watershed were summarized. In rural areas, Anjishan reservoir area was mainly affected by pollutants from non-point sources. So, farmland, aquaculture sewage, mines and rural life were considered as main pollution sources of this area. For these sources, COD (chemical oxygen demand), NH3-N (ammonia nitrogen), TN (total nitrogen) and TP (total phosphorus) were the main pollution factors. Source strength coefficient of each factor for each source was obtained from national reports and amended with survey data. Exceeds bid index method was adopted to calculate the weights of pollution factors based on their contributions rates, and degree of pollution was also calculated based on the weights. The pollution degree of water source for each sub watershed was calculated through degree of pollution of each pollution source and its corresponding land use area. The pollution degree of each sub watershed was converted to pollution concentration based on annual rainfall. Environmental quality standards for surface water in China are often used to assess the condition of water sources. In the standard, Class III is for secondary area of centralized drinking water, class IV is for industrial water and recreational water without direct contact to human body, and class V is for agricultural and landscape water. According to the weight of each pollution factor, the surface water environment index standard S was amended. By comparing the pollution concentration and the amended standard values, the sub watersheds was classified into 5 grades including normal area (S is 0-1.35), general pollution key area (S is 1.35-2.04), secondary key pollution area (S is 2.04-2.75), and key pollution area (>2.75). Among the 19 sub watershed, 4 watershed areas were identified as normal area including watershed 8, 14, 16 and 17; 3 general pollution key areas were 9, 10 and 13; the second key pollution areas were 2; and key pollution areas were 1, 3, 4, 5, 6, 7, 11, 12, 15, 18 and 19. The sub watershed 5, 6, 11 and 12 were identified to be polluted seriously. It indicated that the pollution of drinking water sources in Anjishan was mostly from farmland runoff and residential life. The study suggests that the new method is viable for key pollution area identification of rural drinking water sources.

       

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