| 巢湖富营养化的历程、空间分布与治理策略(1984-2013年) |
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| 引用本文： | 张民,孔繁翔.巢湖富营养化的历程、空间分布与治理策略(1984-2013年)[J].湖泊科学,2015,27(5):791-798. |
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| 作者姓名： | 张民 孔繁翔 |
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| 作者单位： | 中国科学院南京地理与湖泊研究所湖泊与环境国家重点实验室, 南京 210008,中国科学院南京地理与湖泊研究所湖泊与环境国家重点实验室, 南京 210008 |
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| 基金项目： | 国家水体污染控制与治理科技重大专项(2012ZX07103002)、国家自然科学基金项目(31200353,31470520)和中国科学院南京地理与湖泊研究所“一三五”战略发展规划项目(NIGLAS2012135010)联合资助. |
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| 摘 要： | 通过文献调研,分析巢湖富营养化的历程及其与合肥市社会、经济与人口发展的关系,同时利用遥感解译和野外调查监测方法分析2012和2013年巢湖主要富营养化指标及蓝藻水华的空间分布特征,并进一步探讨各个阶段湖泊治理措施对巢湖富营养化过程的影响.研究发现:近30年间,1984-1994年是巢湖水质的主要恶化阶段,在1990s中期巢湖的富营养化达到了近30年的峰值,这主要是经济快速发展、污染治理投入有限所致;1995-2007年,巢湖的水质逐步改善,恢复到1980s中期略高的水平,这得益于"九五"和"十五"期间的大量投入,对污、废水进行处理,限制了污染物直接入湖;但是2008年以来,巢湖的水质改善效果并不明显,富营养化维持在较高水平波动,这可能是因为合肥市经济快速发展背景下,原有的污、废水处理后入湖的减排方式已经不能进一步有效削减巢湖的污染负荷.巢湖富营养化在空间分布上呈现西高东低的渐变趋势,这主要是由西部主要入湖河流污染所致.通过对比2012和2013年的空间分布数据发现,2013年主要入湖污染河流河口水质相对2012年均有所好转,其中十五里河河口的好转比南淝河河口明显.综合长期及全湖富营养化水平的变化分析,现阶段巢湖富营养化的治理亟需改变经济发展模式,调整产业结构,实施污废水尾水提标改造、畜禽养殖污染控制和面源污染控制等控源工程,以进一步降低巢湖的富营养化程度.
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| 关 键 词： | 巢湖 富营养化 时空分布 湖泊治理 |
| 收稿时间： | 9/4/2014 12:00:00 AM |
| 修稿时间： | 1/6/2015 12:00:00 AM |
The process, spatial and temporal distributions and mitigation strategies of the eutrophication of Lake Chaohu (1984-2013) |
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| ZHANG Min and KONG Fanxiang.The process, spatial and temporal distributions and mitigation strategies of the eutrophication of Lake Chaohu (1984-2013)[J].Journal of Lake Science,2015,27(5):791-798. |
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| Authors: | ZHANG Min and KONG Fanxiang |
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| Institution: | State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China and State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China |
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| Abstract: | In the present study, we analyzed the eutrophication process in Lake Chaohu and its correlation with socioeconomic and population development in Hefei city. We also investigated the spatial and temporal distribution characteristics of total nitrogen, total phosphorus, ammonia nitrogen, permanganate index and cyanobacterial blooms in 2012 and 2013 in Lake Chaohu. The results showed that the water quality of Lake Chaohu started to deteriorate in 1984, and down to the worst in 1994 due to the increasing pollution and lacking of capital investment. During the period of 1995-2007, the water quality was getting better because of the limitation of direct waste water and sewage draining into the lake. After year 2008, the water quality did not show significant improvement and maintained a high level of eutrophication. In terms of spatial distributions, eutrophication in Lake Chaohu presented obviously different patterns: eutrophication level gradually degrades from the west to the east, which attributes to the source of pollution from the primary three rivers(Nanfei River, Shiwuli River and Pai River) in the west. The results from investigation also showed that the pollution from these rivers was less in 2013 than that in 2012, and the reduction in Shiwuli River was more apparent than that in Nanfei River. However, the reduction of pollution in the whole lake was not significant. Our findings suggest that in order to further reduce pollution, it is necessary to change economic development pattern and industrial structures and execute targeted pollution source control. |
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| Keywords: | Lake Chaohu eutrophication spatial and temporal distributions lake management |
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