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梯级水库建设对怒江与澜沧江沉积物氮形态分布的影响
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  • 英文篇名:Effect of cascade reservoir construction on nitrogen distribution in sediments of Nujiang River and Lancang River
  • 作者:朱晓声 ; 郭小娟 ; 王耀耀 ; 何金艳 ; 杨正健 ; 纪道斌 ; 马骏 ; 刘德富
  • 英文作者:ZHU Xiao-sheng;GUO Xiao-juan;WANG Yao-yao;HE Jin-yan;YANG Zheng-jian;JI Dao-bin;MA Jun;LIU De-fu;College of Hydraulic and Environmental Engineering, China Three Gorges University;Hubei Key Laboratory of Ecological Restoration of River-lakes and Algal Utilization, Hubei University of Technology;
  • 关键词:梯级水库 ; 沉积物 ; 氮形态 ; 怒江 ; 澜沧江
  • 英文关键词:cascade reservoir;;sediment;;Nitrogen form;;Nujiang River;;Lancang River
  • 中文刊名:ZGHJ
  • 英文刊名:China Environmental Science
  • 机构:三峡大学水利与环境学院;湖北工业大学土木建筑与环境学院河湖生态修复与藻类利用湖北省重点实验室;
  • 出版日期:2019-07-20
  • 出版单位:中国环境科学
  • 年:2019
  • 期:v.39
  • 基金:国家重点研发计划(2016YFC0402204);; 国家自然科学基金资助项目(51879099,91647207,51709096)
  • 语种:中文;
  • 页:ZGHJ201907040
  • 页数:9
  • CN:07
  • ISSN:11-2201/X
  • 分类号:304-312
摘要
为探究梯级水库建设对沉积物氮形态分布的影响,通过分级浸取方法得到沉积物的离子交换态氮(IEF-N)、弱酸提取态氮(WAEF-N)、强碱提取态氮(SAEF-N)以及强氧化剂提取态氮(SOEF-N),对比研究了有梯级水库建设的澜沧江和干流无水电站建设的怒江沉积物中氮形态的分布特征,分析了可转化态氮的主要影响因素.结果表明,两条流域沉积物赋存环境存在差异,进而使沉积物的理化性质呈现明显的差异,最终导致沉积物可转化态氮的含量及空间分布也不同,澜沧江沉积物可转化态氮的含量高于怒江,且澜沧江的空间变化也大于怒江,怒江IEF-N、WAEF-N、SAEF-N与SOEF-N含量范围分别为1.56~2.55,16.91~46.42,1.83~10.66,486.61~719.27mg/kg,澜沧江IEF-N、WAEF-N、SAEF-N与SOEF-N含量范围分别为1.55~14.35,20.77~83.08,1.36~92.15,562.61~1404.82mg/kg.两条河流的可转化态氮含量大小排列顺序一致,均为SOEF-N>WAEF-N>SAEF-N>IEF-N,怒江与澜沧江上游自然河段可转化态氮含量及空间分布基本一致,但在澜沧江的梯级水库段上,4种可转化态氮空间分布特征发生了较明显的变化,产生这种现象的原因主要是水库的建设导致了沉积物理化性质的改变,总有机碳、粒度、氧化还原电位对可转化态氮的影响不同.
        In order to investigate the effect of cascade reservoir construction on the distribution of nitrogen forms in sediments, the ion exchangeable nitrogen(IEF-N), the weak acid extractable nitrogen(WAEF-N), the strong alkaline extractable nitrogen(SAEF-N) and the strong oxidant extractable nitrogen(SOEF-N) of sediments were obtained by the sequential extraction method, and were compared to study the distribution characteristics of nitrogen forms in the sediments of Lancang River with cascade reservoir construction and Nujiang River with no hydropower station in the main stream. The main influencing factors of convertible nitrogen were analyzed. The results showed that there were differences in the occurrence environment of sediments between the two basins, and the physical and chemical properties of sediments were obviously different, and the content and spatial distribution of converted nitrogen in sediments were also different. The content of transformed nitrogen in the sediments of Lancang River were greater than that of Nujiang River, and the spatial variation of Lancang River were also greater than that of Nujiang River. The contents of IEF-N, WAEF-N, SAEF-N and SOEF-N in Nujiang River were 1.56~2.55 mg/kg and 16.91~46.42 mg/kg, respectively. The contents of IEF-N, WAEF-N, SAEF-N and SOEF-N in Lancang River were 1.55~14.35 mg/kg, 20.77~83.08 mg/kg, 1.36~92.15 mg/kg and 562.61~1404.82 mg/kg, respectively, and the contents of Lanchang River were 1.55~14.35 mg/kg, 1.36~92.15 mg/kg, 562.61~1404.82 mg/kg, 20.77~8.08 mg/kg, 1.36~92.15 mg/kg and 562.61~1404.82 mg/kg, respectively. The order of convertible nitrogen content between the two rivers were the same, which were SOEF-N>WAEF-N>SAEF-N>IEF-N, Nujiang River and the upper reached of Lancang River. The content and spatial distribution of convertible nitrogen were basically the same, but on the cascade reservoir section of Lancang River, The spatial distribution characteristics of four kinds of converted nitrogen have changed obviously. The main reason for this phenomenon was that the construction of reservoir leads to the change of physical and chemical properties of sediments, total organic carbon and particle size. The effect of redox potential on convertible nitrogen were different.
引文
[1]Wang P F,Li Z,Chao W,et al.Nitrogen distribution and potential mobility in sediments of three typical shallow urban lakes in China[J].Environmental Engineering Science,2009,26(10):1511-1521.
    [2]Wang R,Huang T,Wei WU.Different factors on nitrogen and phosphorus self-purification ability from an urban Guandu-Huayuan river[J].Journal of Lake Sciences,2016,28(1):105-113.
    [3]陈朱虹,陈能汪,吴殷琪,等.河流库区沉积物-水界面营养盐及气态氮的释放过程和通量[J].环境科学,2014,(9):3325-3335.Chen Z H,Chen N W,Wu Y Q,et al.Release process and flux of nutrients and gaseous nitrogen between sediment and water interface in river reservoir area[J].Environmental Science,2014,(9):3325-3335.
    [4]马红波,宋金明,吕晓霞,等.渤海沉积物中氮的形态及其在循环中的作用[J].地球化学,2003,32(1):48-54.Ma H P,Song J M,Lv X X,et al.Nitrogen forms and their functions in recycling of the Bohai Sea sediments[J].Geochimica,2003,32(1):48-54.
    [5]Wang P D,Zhao L,Wang C,et al.Nitrogen distribution and potential mobility in sediments of three typical shallow urban lakes in China[J].Environmental Engineering Science,2009,26(10):1511-1521.
    [6]王雯雯,王书航,姜霞,等.蠡湖沉积物不同形态氮赋存特征及其释放潜力[J].中国环境科学,2017,(1):292-301.Wang W W,Wang S H,Jiang X,et al.Occurrence characteristics and release potential of nitrogen fractions in sediment of Lihu Lake[J].China Environmental Science,2017(1):292-301.
    [7]吕晓霞,宋金明,袁华茂,等.南黄海表层沉积物中氮的潜在生态学功能[J].生态学报,2004,24(8):1635-1642.Lv X X,Song J M,Yuan H M,et al.The potential ecological roles of nitrogen in the surface sediments of the South Yel low Sea[J].Acta Ecologica Sinica,2004,24(8):1635-1642.
    [8]潘伟亮,何强,艾海男,等.重庆典型区域雨水管道沉积物中氮磷污染特征分析[J].环境科学学报,2015,35(1):257-261.Pan W L,He Q,Ai H N,et al.Analysis on characteristics of nitrogen and phosphorus in storm sewer sediments in Chongqing City[J].Acta Scientiae Circumstantiae,2015,35(1):257-261.
    [9]Denis L,Grenz C,ALLIOTé,et al.Temporal variability in dissolved inorganic nitrogen fluxes at the sediment-water interface and related annual budget on a continental shelf(NW Mediterranean)[J].Oceanologica Acta,2001,24(1):85-97.
    [10]戴纪翠,宋金明,李学刚,等.胶州湾沉积物中氮的地球化学特征及其环境意义[J].第四纪研究,2007,27(3):347-356.Dai J C,Song J M,Li X G,et al.Geochemical characteristics of nitrogen and their environmental significance in Jaozhou Bay sediments[J].Quaternary Sciences,2007,27(3):347-356.
    [11]吉芳英,颜海波,何强,等.龙景湖龙景沟汇水区沉积物-水界面氮形态空间分布特征[J].中国环境科学,2015,35(10):3101-3107.Ji F Y,Yan H B,He Q,et al.Distribution of nitrogen speciation at the sediment-water interface in Longjinggou Catchment Area of Longjinghu Lake[J].China Environmental Science,2015,35(10):3101-3107.
    [12]López-Tarazón JA,López P,Lobera G,et al.Suspended sediment,carbon and nitrogen transport in a regulated Pyrenean river[J].Science of the Total Environment,2015,540:133.
    [13]Huo S,Zhang J,Xi B,et al.Distribution of nitrogen forms in surface sediments of lakes from different regions,China[J].Environmental Earth Sciences,2014,71(5):2167-2175.
    [14]刘波,周锋,王国祥,等.沉积物氮形态与测定方法研究进展[J].生态学报,2011,(22):6947-6958.Liu B,Zhou F,Wang G X,et al.Research progress on forms of nitrogen and determination in the sediments[J].Acta Ecologica Sinica,2011,(22):6947-6958.
    [15]王功芹,朱珠,张硕.海州湾表层沉积物中氮的赋存形态及其生态意义[J].环境科学学报,2016,36(2):450-457.Wang G Q,Zhu Z,Zhang S,Nitrogen forms in the surface sediment of Haizhou Bay and their ecological significance[J].Acta Scientiae Circumstantiae,2016,36(2):450-457.
    [16]张雷,秦延文,郑丙辉,等.三峡入库河流大宁河回水区浸没土壤及消落带土壤氮形态及分布特征[J].环境科学,2009,30(10):2884-2890.Zhang L,Qin Y W,Zheng B H,et al.Nitrogen forms and its distribution character in immerged and water-levelfluctuating zone soils of the backwater reach from Input river of Three Gorges Reservoir[J].Environmental Science,2009,30(10):2884-2890.
    [17]国家环境保护总局.水和废水监测分析方法[M].4版.北京:中国环境科学出版社,2009.State Environmental Protection Administration of China.Methods for monitoring and analysis of water and wastewater(fourth edition)[M].Beijing:Chinese Environmental Science Press,2009.
    [18]赵海超,王圣瑞,焦立新,等.洱海沉积物中不同形态氮的时空分布特征[J].环境科学研究,2013,26(3):235-242.Zhao H C,Wang S R,Jiao L X,et al.Characteristics of temporal and spatial distribution of the nitrogen forms in the sediments of Erhai Lake[J].Research of Environmental Sciences,2013,26(3):235-242.
    [19]Wang S,Jin X,Jiao L,et al.Nitrogen Fractions and Release in the Sediments from the Shallow Lakes in the Middle and Lower Reaches of the Yangtze River Area,China[J].Water Air&Soil Pollution,2008,187(1-4):5-14.
    [20]颜海波.龙景湖沉积物氮形态分布特征及源-汇关系[D].重庆:重庆大学,2015.Yan H B.Distribution characteristics of nitrogen forms in sediments of Longjing Lake and their source-sink relationship[D]:University Of Chongqing,2015.
    [21]刘心愿,宋林旭,纪道斌,等.蓄水前后三峡库区香溪河沉积物磷形态分布特征及释放通量估算[J].环境科学,2018,(9):4169-4178.Liu X Y,Song L X,Ji D B,et al.Distribution characteristics and release fluxes of phosphorus forms in Xiangxi Bay sediments in the Three Gorges Reservoir before and after impoundment[J].Environmental Science,2018(9):4169-4178.
    [22]王圣瑞,金相灿,焦立新.不同污染程度湖泊沉积物中不同粒级可转化态氮分布[J].环境科学研究,2007,20(3):52-57.Wang S R,Jin X C,Jiao L X.Distribution of transferable nitrogen in different grain size from the different trophic level lake sediments[J].Research of Environmental Sciences,2007,20(3):52-57.
    [23]戴纪翠,宋金明,郑国侠,等.胶州湾沉积物氮的环境生物地球化学意义[J].环境科学,2007,28(9):1924-1928.Dai J C,Song J M,Zheng G X,et al.Environmental biogeochemical significance of nitrogen in Jiaozhou Bay sediments[J].Environmental Science,2007,28(9):1924-1928.
    [24]王圣瑞,赵海超,王娟,等.有机质对湖泊沉积物不同形态氮释放动力学影响研究[J].环境科学学报,2012,32(2):332-340.Wang S R,Zhao H C,Wang J,et al.The effects of organic matter on the release kinetics of nitrogen with different forms in the Lake sediments[J].Acta Scientiae Circumstantiae,2012,32(2):332-340.
    [25]Usero J,Gamero M,Morillo J,et al.Comparative study of three sequential extraction procedures for metals in marine sediments[J].Environment International,1998,24(4):487-496.
    [26]宋金明.中国近海生物地球化学[M].济南:山东科学技术出版社,2004.Song J M.Offshore biogeochemistry of China[M].Jinan:Shandong Science and Technology Press,2004.
    [27]李正阳,袁旭音,王欢,等.西苕溪干流水体、悬浮物和表层沉积物中营养盐分布特征与水质评价[J].长江流域资源与环境,2015,24(7):1150-1156.Li Z Y,Yuan X Y,Wang H,et al.Characteristics of nutrient distribution and water quality evaluation in Xitiaoxi main stream,suspended solids and surface sediments[J].Resources and Environment in the Yangtze Basin,2015,24(7):1150-1156.
    [28]Song J M.Offshore biogeochemistry of China[M].Shandong Science and Technology Press,2004.
    [29]Xiaoxia L,Song J.Regional Geochemical Characteristics of Nitrogen in the Southern Yellow Sea Surface Sediment[J].Journal of Marine Systems,2005,56(1/2):17-27.
    [30]王圣瑞,焦立新,金相灿,等.长江中下游浅水湖泊沉积物总氮、可交换态氮与固定态铵的赋存特征[J].环境科学学报,2008,28(1):37-43.Wang S R,Jiao L X,Jin X C,et al.Occurrence characteristics of Total nitrogen,exchangeable nitrogen and fixed ammonium in sediments of shallow Lakes in the Middle and Lower reaches of the Yangtze River[J].Acta Scientiae Circumstantiae,2008,28(1):37-43.
    [31]Mortimer C H.Chemical exchanges between sediments and water in the Great Lakes-Speculations on probably regulatory mechanisms,Limnol[J].Limnology and Oceanography,1971,16(2):387-404.
    [32]郑国侠,宋金明,孙云明,等.Characteristics of nitrogen forms in the surface sediments of southwestern Nansha Trough,South China Sea[J].中国海洋湖沼学报(英文版),2008,26(3):280-288.Zheng G X,Song J M,Song Y M,et al.Characteristics of nitrogen forms in the surface sediments of southwestern Nansha Trough,South China Sea[J].Journal of Oceanology and Limnology,2008,26(3):280-288.
    [33]延霜.水体-沉积物界面氮迁移转化的生物化学过程[D].西安:西安建筑科技大学,2010.Yan S.Biochemical process of nitrogen Transport and Transformation between Water body and sediment Interface[D].Xi'an:Xi'an University of Architecture and Technology,2010.
    [34]汪淼,王圣瑞,焦立新,等.滇池沉积物内源氮释放风险及控制分区[J].中国环境科学,2016,36(3):798-807.Wang M,Wang S R,Jiao L X,et al.The risk and control division of endogenous nitrogen release in Dianchi Lake sediment[J].China Environmental Science,2016,36(3):798-807.
    [35]鲍根德.太平洋西部深海沉积物中有机质、氮、磷的初步研究[J].沉积学报,1987,5(1):114-124.Bao G D.A preliminary study on organic matter,nitrogen and phosphorus in Deep-sea sediments of the Western Pacific Ocean[J].Acta Sedimentologica Sinica,1987,5(1):114-124.

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