NON-POINT SOURCE POLLUTIONS IN TYPICAL RIVER BASINS IN HILLY AND MOUNTAINOUS AREAS AND PLAIN RIVER NETWORK AREA IN CHINA
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摘要: 由于城镇化进程的差异,不同区域流域面源污染也存在较大差异,为研究典型流域城镇和非城镇面源污染规律及环境效应,选取长江流域丘陵山区(重庆市永川区)和平原河网区(江苏省常州市金坛区)为研究对象,分析不同地貌下城镇面源污染和非城镇面源污染的时空分布特征,并结合降雨特征探究了降雨与城镇和非城镇面源污染物的相关性。结果表明:在长江流域,丘陵山区和平原河网区城镇面源污染占比均远高于非城镇,在丘陵山区降雨较少的冬季(11月—次年3月)差异更显著。两区域对不同面源污染物指标的月度响应不同,丘陵山区的不同形态氮和磷浓度均略高于平原河网区。丘陵山区城镇不同形态磷浓度最高值出现在12月,而非城镇的最高值则出现在8月,平原河网区不同形态磷浓度最高值均出现在11月。此外,两区域秋冬季节非城镇的CODMn高于城镇区域。降雨与两区域非城镇大多数面源污染物指标呈正相关,说明降雨是非城镇面源污染的主要影响因子之一,但降雨与不同面源污染物相关性有长期响应和瞬时作用之分,表现在10年内年平均降雨量与两区域大多数非城镇面源污染指标呈正相关,而采样期间降雨量则与多数平原河网区城镇面源污染指标呈正相关。研究结果揭示了城镇面源污染在长江流域丘陵山区和平原河网区的面源污染中占据的较重分量,厘清城镇和非城镇面源污染的时空分布特征和污染规律对科学防控面源污染具有重要意义。Abstract: Due to the differences in the process and extent of urbanization, large differences of non-point source pollution appeared in different regions. To study the distribution characteristics and environmental effects of urban and non-urban non-point source pollution in typical river basins, this study selected two typical hilly and mountainous areas of the Yangtze River basin (Yongchuan District, Chongqing) and plain river network area (Jintan District, Changzhou, Jiangsu) as research objects. The spatial and temporal distribution characteristics of urban and non-urban non-point source pollution in different landforms were analyzed. Combined with rainfall characteristics, the correlation between rainfall and urban and non-urban non-point source pollutants was explored. The results showed that the proportion of urban non-point source pollution was much higher than that in non-urban areas in the two regions, especially in winter (from November to March) when there is less rainfall in the hilly and mountainous area. The monthly responses of those two regions to non-point source pollutants were different. Generally, the concentrations of different forms of nitrogen and phosphorus in the hilly and mountainous area were slightly higher than those in plain river network area. In the hilly and mountainous area, the highest nitrogen and phosphorus concentrations of different forms in urban areas appeared in December, while the highest concentrations in non-urban areas appeared in August. However, the highest nitrogen and phosphorus concentrations of different forms in plain river network area appeared in November. In addition, the permanganate index of non-urban areas was higher than that of urban areas in autumn and winter. Rainfall is positively correlated with most non-urban non-point source pollutants in the two regions, indicating that rainfall is one of the main influencing factors of non-urban non-point source pollution. However, the correlation between rainfall and different non-point source pollutants can be divided into long-term response and instantaneous effect. 10-year average annual rainfall is positively correlated with most non-urban non-point source pollutants in the two regions, while rainfall during the sampling time is positively correlated with most urban non-point source pollutants in plain river network area. This study reveals the non-negligible role of urban non-point source pollution in the hilly and mountainous area and the plain river network area. Analyzing the spatial and temporal distribution characteristics and emission characteristics of non-point source pollutants from different sources is important for scientific prevention and control of non-point source pollution.
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Key words:
- non-point source pollution /
- urban /
- typical watershed /
- rainfall /
- water quality
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[1] 谢晖,邱嘉丽,董建玮,等.流域水文模型在面源污染模拟与管控中的应用研究进展[J].生态学报,2022,42(15):6076-6091. [2] 杨林章,冯彦房,施卫明,等.我国农业面源污染治理技术研究进展[J].中国生态农业学报,2013,21(1):96-101. [3] 吴永红,胡正义,杨林章.农业面源污染控制工程的"减源-拦截-修复"(3R)理论与实践[J].农业工程学报,2011,27(5):1-6. [4] 武淑霞,刘宏斌,刘申,等.农业面源污染现状及防控技术[J]. 中国工程科学,2018,20(5):23-30. [5] 生态环境部,国家统计局,农业农村部. 关于发布《第二次全国污染源普查公报》的公告[EB/OL]. [2020-06-09].https://www.mee.gov.cn/xxgk2018/xxgk/xxgk01/202006/t20200610_783547.html. [6] 连心桥,朱广伟,杨文斌,等.强降雨对平原河网区入湖河道氮、磷影响[J].环境科学,2020,41(11):4970-4980. [7] 刘忠翰,贺彬,王宜明,等.滇池不同流域类型降雨径流对河流氮磷入湖总量的影响[J].地理研究,2004,23 (5):593-604. [8] 欧阳威,刘迎春,冷思文,等.近三十年非点源污染研究发展趋势分析[J].农业环境科学学报,2018,37(10):2234-2241. [9] 赵星辰,许海,俞洁等.城镇分布对新安江水系及千岛湖营养盐浓度的影响[J].环境科学研究,2022,35(4):864-876. [10] 罗海平,何志文,胡学英.城镇化对种植业面源污染影响的中介效应分析[J].中国生态农业学报(中英文),2021,29(9):1625-1635. [11] 钱君龙,府灵敏.用过硫酸盐氧化法同时测定水中的总氮和总磷[J].环境科学,1987,8(1): 81-84. [12] 夏利林. 降雨和坡度对三峡库区耕地和撂荒地氮磷流失的影响研究[D].重庆:重庆三峡学院,2023. [13] 樊桐桐,王冬梅,张泽洲,等.放水冲刷条件下工程边坡产流产沙及氮磷输出特征[J].水土保持学报,2023,37(4):101-109,117. [14] 朱玉凡.不同污染特征城市颗粒物氧化潜势与健康效应特征及其来源解析[D].兰州:兰州大学,2023. [15] 施卫明,王远,闵炬.中国农业面源污染防控研究进展与工程案例[J].土壤学报,2023,60(5):1309-1323. [16] 蒙小俊.农业面源污染研究进展[J].中南农业科技,2023,44(9):237-240. [17] 易绍荣,冯雪娇,王宗伟,等.基于SWAT的河套灌区氮磷面源污染时空变化研究[J].农业环境科学学报,2023,42(11):2550-2559.
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