东江干流惠州段沉积物—水界面无机氮交换通量及影响因素研究
[Abstract]:Dongjiang River is an important drinking water source in Guangdong Province and Hong Kong Special Administrative Region. Its quality of water is directly related to the people's lives and economic development of Guangzhou, Shenzhen and Hong Kong. In recent years, with the rapid economic development and the acceleration of urbanization, a large number of nitrogen-rich domestic and industrial and agricultural wastewater discharged into Dongjiang River has affected the East. Water quality in the main stream of the river. Excessive discharge of nitrogen will lead to the decline of water environmental quality and eutrophication. At the same time, the endogenous pollution caused by the accumulation of large amounts of nitrogen into the river sediments has become increasingly prominent, which has aroused widespread concern of scholars at home and abroad. The characteristics of nitrogen release, transport and transformation in sediments were discussed. The nitrogen exchange flux and influencing factors at the sediment-water interface were studied. It is of great significance to control the pollution of the main stream of the Dongjiang River and protect the high quality water sources of the Dongjiang River. In March 14, six sampling sites were selected to study the nitrogen content, water quality assessment, nitrogen exchange flux at the sediment-water interface, and laboratory simulation tests were carried out to analyze the influencing factors of nitrogen migration and transformation at the sediment-water interface. The main conclusions are as follows: (1) The water quality of the main stream of Dongjiang River (Huizhou Section) is in good condition for most of the time, and TN water quality is poor, which basically meets Class IV-V (lake, reservoir, N count), and some points are inferior Class V; the concentration of ammonia nitrogen is generally not high, the value of sampling points is less than 0.5mg/L in most of the time, and the water quality basically meets Class II requirements; The concentration range of nitrite nitrogen was 0.001-0.071 mg/L. The results showed that nitrate nitrogen was the main pollutant in the water body and belonged to light pollution. Ammonia nitrogen and nitrite nitrogen were clean state, and the nitrite nitrogen was clean. The annual ammonia-nitrogen exchange fluxes at the sediment-water interface in the prefecture section are all positive, indicating that the sediments in the main stream of the Dongjiang River (Huizhou section) are the source of ammonia-nitrogen. The exchange flux between sediment and overlying water slows down and ammonia-nitrogen exchange flux decreases gradually. The exchange flux of nitrate-nitrogen at the sediment-water interface is different from that of ammonia-nitrogen, and the exchange flux of nitrate-nitrogen is small. The sediment is not always used as the source or sink of nitrate-nitrogen, but often occurs sink-source conversion. (3) Simulation of exchange flux in sediment-water system. The results show that with the increase of temperature, the ammonia nitrogen produced by water mineralization increases, and the dissolved oxygen is consumed, which prevents nitrification. The release rate of ammonia nitrogen under anaerobic conditions is higher than that under aerobic conditions, which is beneficial to the release of ammonia nitrogen from sediments. The lower the pH value, the greater the concentration of hydrogen ion in the water, the stronger the exchange effect, the more ammonia nitrogen released from the sediment, which aggravates the nitrogen load in the overlying water and decreases the ammonia-nitrogen exchange capacity in the opposite direction. Under alkaline conditions, the ammonia-nitrogen in the water body decreases, and the ammonia-nitrogen concentration between the sediment and the water body increases. The results show that nitrate is the main pollutant in overlying water and sediment is an important internal source of ammonia nitrogen. Under the condition of insufficient dissolved oxygen in sediment, nitrate is reduced to increase the concentration of ammonia nitrogen in sediment and sediment becomes the source of ammonia nitrogen. The reduction of ammonia and the release of ammonia nitrogen from sediments are beneficial to the reduction of oxygen and the over acid conditions.
【学位授予单位】:吉首大学
【学位级别】:硕士
【学位授予年份】:2016
【分类号】:X52
【相似文献】
相关期刊论文 前10条
1 С.И.Андреев;邢子起;;太平洋沉积物堆积与铁锰结核生长的速度[J];海洋地质译丛;1990年03期
2 王雨春,万国江,黄荣贵,邹申清,陈刚才;湖泊现代化沉积物中磷的地球化学作用及环境效应[J];重庆环境科学;2000年04期
3 黄礼贤,廖森标;粤西海区海水与沉积物中石油含量分布特征[J];海洋环境科学;1984年03期
4 R.N.Dubois;傅命佐;;关于波浪状况、沉积物结构和海面上升之间关系的一种见解[J];海洋地质译丛;1983年03期
5 于雯泉;钟少军;蒲晓强;刘飞;徐丽君;;胶州湾李村河口区沉积物酸可挥发硫化物的环境响应[J];中国石油大学学报(自然科学版);2007年06期
6 Ю.П.Беэродных;朱佛宏;;陆架区含锡石及含金沉积物的类型和组成[J];海洋地质译丛;1982年02期
7 Ю.Л.赫鲁斯塔列夫;罗定;;南海西陆架和陆坡沉积物的矿物学[J];海洋地质译丛;1987年06期
8 万国江;;云贵高原深水湖库环境过程及水源保护途径[J];中国工程科学;2009年05期
9 李铁松;放射性~(210)Pb方法的地理学应用实例[J];四川师范学院学报(自然科学版);1994年03期
10 X.Liu;W.E.Galloway;王晓钦;;定量测定北海盆地第三系沉积物补给[J];国外油气勘探;1999年02期
相关会议论文 前1条
1 肖化云;刘丛强;;沉积物对成湖前土壤碳、氮比值的影响[A];中国矿物岩石地球化学学会第九届学术年会论文摘要集[C];2003年
相关博士学位论文 前5条
1 吕晓霞;黄海沉积物中氮的粒度结构及在生物地球化学循环中的作用 [D];中国科学院研究生院(海洋研究所);2003年
2 刘建国;全新世渤海泥质区的沉积物物质组成特征及其环境意义[D];中国科学院研究生院(海洋研究所);2007年
3 董爱国;黄、东海海域沉积物的源汇效应及其环境意义[D];中国海洋大学;2011年
4 张瑞虎;长江口沉积物记录的全新世沉积环境和东亚夏季风演变研究[D];华东师范大学;2011年
5 周晓静;东海陆架细颗粒沉积物组成分布特征及其物源指示[D];中国科学院研究生院(海洋研究所);2009年
相关硕士学位论文 前10条
1 熊蕾;东江干流惠州段沉积物—水界面无机氮交换通量及影响因素研究[D];吉首大学;2016年
2 古丽;渤、黄、东海沉积物中硫化物的研究[D];中国海洋大学;2011年
3 曹文卿;东、黄海沉积物中磷的形态研究[D];中国海洋大学;2006年
4 马红波;渤海沉积物中氮的赋存形态及其在循环中的作用[D];中国科学院海洋研究所;2001年
5 塔金璐;渤黄海粘土粒级沉积物地球化学记录对物源和沉积环境的释读[D];中国海洋大学;2014年
6 李玲伟;沉积物—水界面交换和黄河输入对渤海营养盐的影响[D];中国海洋大学;2010年
7 叶青;斋堂岛南部海域沉积物特征及物源分析[D];中国海洋大学;2014年
8 戴慧敏;济州岛西南泥质区不同粒级沉积物的元素地球化学特征及物源分析[D];中国海洋大学;2005年
9 吴晓娜;西湖沉积物中磷的形态及迁移转化的沉积剖面研究[D];浙江大学;2006年
10 程净净;南黄海中部泥质区沉积物声学物理特性研究[D];国家海洋局第一海洋研究所;2011年
,本文编号:2242669
本文链接:https://www.wllwen.com/kejilunwen/huanjinggongchenglunwen/2242669.html