欢迎登录材料期刊网

材料期刊网

高级检索

为探索城郊污染河道底泥磷释放的控制技术,选择无锡市城郊河道长广溪不同污染类型河段(农田区、农田支流区、生活区、工业区、一期修复区、二期修复区、一期修复支流区),采集底泥原状泥柱,进行锁磷剂和黄沙覆盖控磷技术处理,室内培养3周,测定磷的控制效果.结果发现,长广溪不同污染类型河段底泥中磷的释放速率具有明显差异,农田区、农田支流区、生活区、工业区、一期修复区、二期修复区、一期修复支流区的底泥磷的释放速率分别为:0?767、0?383、0?317、0?672、0?370、0?027、0?458μg P·m-2·d-1.除二期修复区外,所有河段的水体磷含量及底泥释放量均较高,生态修复时有必要进行底泥磷释放控制,其中农田区及工业区底泥污染最重,磷的释放速率也最高.锁磷剂和黄沙覆盖对所有河段底泥的磷释放均有较强的控制作用,锁磷剂的控制效率在81.25%—100%之间,黄沙的控制效率在62.50%—93.24%之间;对于农田区、农田支流区、一期修复区及一期修复支流区河段,黄沙和锁磷剂均能有效将底泥磷释放控制到较低水平,满足河道磷控制的目标,但对于工业区和生活区河段,只有锁磷剂能够达到控制目标,黄沙的控制效果不理想.研究表明,在太湖流域的城郊污染河道的生态修复中,锁磷剂和黄沙均可作为底泥磷控制材料使用,黄沙在部分类型水体可以替代锁磷剂,而锁磷剂的效果稳定,作用持久,操作简便,是相对更好的底泥控磷材料.

For exploring urban pollution of river sediment phosphorus release control technology, choosing different pollution sections of Changguangxi River ( include Farmland pollution section, farmland tributary section, sewage polluted section, industrial pollution section, First?term restoration section, Second?term restoration section, First?term restoration tributary section) in wuxi suburb, collected sediment cores to lab, and applied phoslock and sand ( 2 cm thickness) to test their utility of sediment phosphorus release control. The results showed that, because of the different pollution type and pollution degree of different types river in the Chang Guangxi, phosphorus release rate from sediment have obvious difference. Beside the Second?term restoration section, all of the phosphorus contents and sediment release rates were high. Therefore, it is very necessary to control the sediment phosphorus release before the ecological restoration engineering. In all the sections, Phoslock and sand capping effectively control the sediment release of phosphorus, with the efficiency for Phoslock of between 81.25% and 100%, and for sand capping between 62.50% and 93.24%. Beside sewage polluted section and industrial pollution section, the sand capping and Phoslock can effectively control sediment phosphorus release phosphorus to low enough and meet the goals of phosphorus control. This study shows that, during the ecological restoration in rivers locates at Taihu catchment, both Phoslock and sand capping were powerful for sediment phosphorus control. Sand capping can replace Phoslock in quite a lot of pollution types. But anyway, the effect of Phoslock is a relative more stable, durable, easy to operate, phosphorus control material in this region.

参考文献

[1] 赵生才.我国湖泊富营养化的发生机制与控制对策[J].地球科学进展,2004(01):138-140.
[2] 林晓,刘婧,徐厚坤.富营养化水体中磷的控制方法初探[J].城镇供水,2003(02):39-40.
[3] 李慧韫,张天胜.磷和水体富营养化(待续)[J].日用化学品科学,2002(05):12-14.
[4] 华凤林.湖泊富营养化与底质磷释放[J].环境监测管理与技术,1993(04):18-20,37.
[5] 秦伯强,杨柳燕,陈非洲,朱广伟,张路,陈宜瑜.湖泊富营养化发生机制与控制技术及其应用[J].科学通报,2006(16):1857-1866.
[6] S?ndergaard M;Jensen J P;Jeppesen E .Retention and internal loading of phosphorus in shallow,eutrophic lakes[J].The Scientific World Journal,2001,1:427-442.
[7] 张维亮,吴相利.无锡市长广溪国家城市湿地公园开发研究[J].国土与自然资源研究,2007(04):57-58.
[8] 黄成才,杨芳.湿地公园规划设计的探讨[J].中南林业调查规划,2004(03):26-29.
[9] 陈卫,徐丽丽.城市湿地公园人工过滤系统的构建--以长广溪湿地公园为例[J].湿地科学与管理,2009(01):30-33.
[10] 陈华 .化学沉淀法除磷与生物法除磷的比较[J].上海环境科学,1997,16(6):33-35.
[11] 顾小红,黄种买,虞启义.污水除磷技术的现状及发展趋势[J].再生资源研究,2002(03):33-35.
[12] 俞栋,谢有奎,方振东,杨娟.污水除磷技术的现状与发展[J].重庆工业高等专科学校学报,2004(01):9-12.
[13] 吴燕,安树林.废水除磷方法的现状与展望[J].天津工业大学学报,2001(01):74-78.
[14] Malcolm Robb;Bruce Greenop;Zoe Goss;Grant Douglas;John Adeney .Application of Phoslock~(TM), an innovative phosphorus binding clay, to two Western Australian waterways: preliminary findings[J].Hydrobiologia,2003(1/3):237-243.
[15] 孙珮石;朱宝平;胡永康.(锁磷剂)污染水体除磷性能研究[A].北京,2004
[16] 余先旭,孙珮石,朱宝平,胡永康.锁磷剂(PHOSLOCK)的污水除磷实验研究[J].资源环境与工程,2005(04):333-335.
[17] 余先旭,孙珮石,朱宝平,胡永康.锁磷剂(Phoslock)对滇池水体的除磷试验研究[J].贵州环保科技,2006(01):6-9.
[18] 叶恒朋,陈繁忠,盛彦清,秦向春,盛国英,傅家谟.覆盖法控制城市河涌底泥磷释放研究[J].环境科学学报,2006(02):262-268.
[19] 丁文明,黄霞,张力平.水合氧化镧吸附除磷的试验研究[J].环境科学,2003(05):110-113.
[20] 张大群,曹井国,姜亦增.三种除磷药剂的除磷性能比较[J].中国给水排水,2011(05):75-76.
[21] Sebastian Meis;Bryan M. Spears;Stephen C. Maberly;Rupert G. Perkins .Assessing the mode of action of Phoslock~? in the control of phosphorus release from the bed sediments in a shallow lake (Loch Flemington, UK)[J].Water research: A journal of the international water association,2013(13):4460-4473.
[22] 钱君龙;张连弟;乐美麟 .过硫酸盐消化法测定土壤全氮全磷[J].土壤,1990,22(5):258-262.
[23] 陈伟民;黄祥飞;周万平.湖泊生态系统观测方法[M].北京:中国环境科学出版社,2005
[24] 国家环境保护总局.水和废水监测分析方法(第四版)[M].北京:中国环境科学出版社,2002
[25] GB 3838-2002.地表水环境质量标准[S].北京:中国环境科学出版社,2002.
[26] 姜敬龙,吴云海.底泥磷释放的影响因素[J].环境科学与管理,2008(06):43-46.
[27] 聂祥,林彰文,顾继光,韩博平.南亚热带中小型水库沉积物中磷的形态与释放特征[J].生态环境,2008(03):903-908.
[28] U.S. EPA .Selecting remediation techniques for contaminated sediment. EPA-823-B93-001[R].,1993.
[29] 方宇翘 .河流底泥污染类型标准的制定[J].环境科学研究简报,1989,10(1):26-30.
[30] 廖文根,彭静,铁灵芝.太湖水体的磷负荷分析[J].水利学报,1994(11):77.
[31] Holdren G C;David E .Armstrong,factors affecting phosphorus release from intact lake sediments cores[J].Environmental Science and Technology,1980,14(1):79-87.
[32] Ingall E;Jahnke R .Evidence for enhanced phosphorus regeneration from marine sediments overlain by oxygen depleted waters[J].Geochimica et Cosmochimica Acta,1994,58(11):2571-2575.
[33] 于世繁 .白洋淀底质磷的释放及与水体中磷的关系[J].环境科学,1995,16(增刊):30-34.
[34] 尹大强;覃秋荣;阎航 .环境因子对五里湖沉积物磷释放的影响[J].湖泊科学,1994,6(3):240-244.
[35] 吴根福,吴雪昌,金承涛,宣晓东,李梅姿.杭州西湖底泥释磷的初步研究[J].中国环境科学,1998(02):107-110.
[36] 韩伟明 .底泥释放及其对杭州西湖富营养化的影响[J].湖泊科学,1993,5(1):71-76.
[37] 李卫东,刘云根,田昆,梁启斌,刘惠芳.Phoslock应用于滇池富营养化水体污染净化的研究[J].安徽农业科学,2010(34):19456-19458.
上一张 下一张
上一张 下一张
计量
  • 下载量()
  • 访问量()
文章评分
  • 您的评分:
  • 1
    0%
  • 2
    0%
  • 3
    0%
  • 4
    0%
  • 5
    0%