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太湖梅梁湾水体及沉积物中微囊藻毒素含量垂向分布特征
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  • 英文篇名:Vertical distribution characteristics of microcystin concentration in water and sediment of Meiliang Bay,Lake Taihu
  • 作者:舒秀波 ; 谢丽强 ; 万翔 ; 姚磊 ; 薛庆举 ; 李金娟
  • 英文作者:SHU Xiubo;XIE Liqiang;WANG Xiang;YAO Lei;XUE Qingju;LI Jinjuan;College of Resources and Environmental Engineering,Guizhou University;State Key Laboratory of Lake Science and Environment,Nanjing Institute of Geography and Limnology,Chinese Academy of Sciences;Univesity of Chinese Academy of Sciences;
  • 关键词:太湖 ; 梅梁湾 ; 微囊藻毒素 ; 水体 ; 沉积物 ; 垂向分布
  • 英文关键词:Lake Taihu;;Meiliang Bay;;microcystin;;water;;sediment;;vertical distribution
  • 中文刊名:湖泊科学
  • 英文刊名:Journal of Lake Sciences
  • 机构:贵州大学资源与环境工程学院;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;中国科学院大学;
  • 出版日期:2019-07-06
  • 出版单位:湖泊科学
  • 年:2019
  • 期:04
  • 基金:国家自然科学基金项目(41877486);; 国家水体污染控制与治理科技重大专项(2018ZX07208-008,2017ZX07203-004-04);; 中国科学院科技服务网络计划(KFJ-STS-ZDTP-038-3)联合资助
  • 语种:中文;
  • 页:88-99
  • 页数:12
  • CN:32-1331/P
  • ISSN:1003-5427
  • 分类号:X524
摘要
为探究太湖梅梁湾水体及沉积物中微囊藻毒素(MC-LR、MC-RR、MC-YR)含量的垂向分布特征,于2018年5月采集梅梁湾6个点位表层水、上覆水、混合水、间隙水以及柱状沉积物样品,并采用超高效液相色谱-串联质谱法分析样品中微囊藻毒素的含量.分析结果表明:水体中(表层水、上覆水、混合水以及间隙水) MC-LR、MC-RR、MC-YR的浓度范围分别为11.80~1297.14、2.50~818.40、1.80~176.00 ng/L,表层水、上覆水以及混合水中MC-LR的浓度高于MC-RR和MCYR,MC-RR和MC-YR之间差别较小,而间隙水中MCs三种异构体浓度大小顺序为:MC-LR>MC-RR>MC-YR;垂向分布上,间隙水中MCs异构体(MC-LR、MC-RR、MC-YR)浓度均远高于表层水、上覆水以及混合水,表层水MCs异构体浓度略高于上覆水,混合水MCs异构体浓度介于表层水和上覆水之间.对沉积物的研究发现,1~10 cm表层沉积物中MC-LR、MC-RR、MC-YR含量范围分别为0.60~26.95、0~0.90、0~8.10 ng/g,且1~10 cm层中MCs三种异构体平均含量大小顺序为:MC-LR>MC-YR>MC-RR,其中MC-LR、MC-RR、MC-YR的检出率分别为100%、70%、92%;垂向分布上,MC-RR含量较低且变化不大,而MC-YR和MC-LR含量均随沉积物深度的增加先升高后降低.相关性分析结果表明,表层水和混合水中MCs与总磷浓度呈显著正相关,而与总氮浓度无显著相关性;上覆水、间隙水以及沉积物中MCs与总氮、总磷浓度均呈显著正相关.
        In order to explore the vertical distribution characteristics of microcystin( MC-LR,MC-RR,MC-YR) concentration in the water body and sediment of Meiliang Bay,surface water,overlying water,mixed water,interstitial water and columnar sediment samples at six points were collected in May 2018,and the microcystin concentrations were analyzed by ultra-high performance liquid chromatography-tandem mass spectrometry( UPLC-MS/MS). The results indicated that the MC-LR,MC-RR,MC-YR concentrations in water( surface water,overlying water,mixed water and interstitial water) ranged from 11. 80-1297. 14,2. 50-818.40,1.80-176.00 ng/L,respectively. The MC-LR concentration in surface water,overlying water and mixed water were higher than MC-RR and MC-YR concentrations,but there were no significant difference between MC-RR and MC-YR concentration. The order of MC concentrations isomer in interstitial water was: MC-LR > MC-RR > MC-YR. The MC concentrations isomer( MC-LR,MC-RR,MC-YR) in interstitial water were all far higher than those in surface water,overlying water and mixed water in vertical profiles of water,the MC isomer concentrations in surface water were slightly higher than those in overlying water. The MC isomer concentrations in mixed water were between surface water and overlying water. The MC-LR,MC-RR and MC-YR contents in sediment with a depth of 10 cm ranged from 0.60-26.95,0-0.90 and 0-8.10 ng/g,respectively,and the order of the average content of three MC isomers in the 1-10 cm layer was MC-LR > MC-YR > MC-RR. The detection rates of MC-LR,MC-RR and MC-YR were 100%,70% and 92%,respectively. In the vertical distribution of sediment,the MC-RR concentration was low and showed little change,the overall trend of MC-YR and MC-LR contents increased first and then decreased with the increasing of the sediment depth. The results of correlation analysis indicated that MC isomer concentrations in surface water and mixed water were positively correlated with total phosphorus( TP) concentration,respectively,but did not show correlation with total nitrogen( TN)concentration. The MC concentrations in overlying water,interstitial water and sediment were positively correlated with TN and TP concentrations,respectively.
引文
[1] Falconer IR. Tumor promotion and liver injury caused by oral consumption of cyanobacteria. Environ Toxic Water,1991,6(2):177-184. DOI:10.1002/tox.2530060207.
    [2] Meriluoto J,Spoof L,Codd GA eds. Handbook of cyanobacterial monitoring and cyanotoxin analysis. Chichester:John Wiley&Sons,2017:526-537. DOI:10.1002/9781119068761.
    [3] Dziga D,Wasylewski M,Wladyka B et al. Microbial degradation of microcystins. Chem Res Toxicol,2013,26(6):841-852. DOI:10.1021/tx4000045.
    [4] Chen W,Song L,Peng L et al. Reduction in microcystin concentrations in large and shallow lakes:Water and sedimentinterface contributions. Water Research,2008,42(3):763-773. DOI:10.1016/j.watres.2007.08.007.
    [5] Jia J,Luo W,Lu Y et al. Bioaccumulation of microcystins(MCs)in four fish species from Lake Taihu,China:Assessment of risks to humans. Science of the Total Environment,2014,487(1):224-234. DOI:10. 1016/j. scitotenv. 2014.04.037.
    [6] Zhang J,Wang Z,Song Z et al. Bioaccumulation of microcystins in two freshwater gastropods from a cyanobacteria-bloom plateau lake,Lake Dianchi. Environmental Pollution,2012,164(1):227-234. DOI:10.1016/j.envpol.2012.01.021.
    [7] Zhang D,Xie P,Chen J et al. Determination of microcystin-LR and its metabolites in snail(Bellamya aeruginosa),shrimp(Macrobrachium nipponensis)and silver carp(Hypophthalmichthys molitrix)from Lake Taihu,China. Chemosphere,2009,76(7):974-981. DOI:10.1016/j.chemosphere.2009.04.034.
    [8] Zhang D,Xie P,Liu Y et al. Transfer,distribution and bioaccumulation of microcystins in the aquatic food web in Lake Taihu,China,with potential risks to human health. Science of the Total Environment,2009,407(7):2191-2199. DOI:10.1016/j.scitotenv.2008.12.039.
    [9] Xu Q,Chen W,Gao G. Seasonal variations in microcystin concentrations in Lake Taihu,China. Environ Monit Assess,2008,145(1-3):75-79. DOI:10.1007/s10661-007-0016-5
    [10] Song L,Chen W,Peng L et al. Distribution and bioaccumulation of microcystins in water columns:A systematic investigation into the environmental fate and the risks associated with microcystins in Meiliang Bay,Lake Taihu. Water Research,2007,41(3):2853-2864. DOI:10.1016/j.watres.2007.02.013.
    [11] Gao ZM,Zhao ZH,Zhang B et al. Seasonal variation of microcystins concentration and influencing factors in Meiliang Bay,Lake Taihu. Ecology and Environmental Sciences,2011,20(6/7):1063-1067.[高振美,赵中华,张波等.太湖梅梁湾水体微囊藻毒素含量的季节变化特征及其影响因素研究.生态环境学报,2011,20(6/7):1063-1067.]
    [12] Wang L,Li XY,Xue WT et al. Review on research progress of microcystins detection. Food Science,2005,26(Z):136-138.[王蕾,李小艳,薛文通等.微囊藻毒素检测方法研究进展.食品科学,2005,26(Z):136-138.]
    [13] Water resources department of the Taihu basin Jiangsu provincial department of water resources,Zhejiang provincial department of water resources,Shanghai municipal water bureau eds. Taihu health report. 2017.[水利部太湖流域管理局,江苏省水利厅,浙江省水利厅,上海市水务局.太湖健康状况报告. 2017.]
    [14] Ke ZX,Xie P,Guo LG et al. Effects of large bio-manipulation fish pen on community structure of crustacean zooplankton in Meiliang Bay of Taihu Lake. Chinese Journal of Applied Ecology,2012,23(8):2270-2276. DOI:10.13287/j.1001-9332.2012.0317.[柯志新,谢平,过龙根等.太湖梅梁湾大型控藻围栏对浮游甲壳动物群落结构的影响.应用生态学报,2012,23(8):2270-2276.]
    [15] Jing XC,Tu QY eds. The standard methods in lake eutrophication investigation:The second edition. Beijing:China Environmental Science Press,1990:229-230.[金相灿,屠清瑛.湖泊富营养化调查规范:第2版.北京:中国环境科学出版社,1990:229-230.]
    [16] Bao SD ed. Agricultural soil analysis:The third edition. Beijing:China Agricultural Press,1981:30-33.[鲍士旦.土壤农化分析:第3版.北京:中国农业出版社,1981:30-33.]
    [17] Su X,Steinman AD,Xue Q et al. Evaluating the contamination of microcystins in Lake Taihu,China:The application of equivalent total MC-LR concentration. Ecological Indicators,2018,89:445-454. DOI:10.1016/j.ecolind.2017.11.042.
    [18] Chen W,Li L,Gan N et al. Optimization of an effective extraction procedure for the analysis of microcystins in soils and lake sediments. Environmental Pollution,2006,143(2):241-246. DOI:10.1016/j.envpol.2005.11.030.
    [19] Wang JJ,Yang J,Xian QM et al. Characteristic of microcystin distributions and its relationships with environmental factors in Lake Taihu. J Lake Sci,2011,23(4):513-519. DOI:10.18307/2011.0404.[王经结,杨佳,鲜啟鸣等.太湖微囊藻毒素时空分布特征及与环境因子的关系.湖泊科学,2011,23(4):513-519.]
    [20] Arnold TN,Oldham CE. Trace-element contamination of a shallow wetland in Western Australia. Marine&Freshwater Research,1997,48(6):531-539. DOI:10.1071/MF96088.
    [21] Zhu W,Li M,Dai X et al. Differences in vertical distribution of Microcystis morphospecies composition in a shallow hypertrophic lake(Lake Taihu,China). Environmental Earth Sciences,2015,73(9):1-10. DOI:10. 1007/s12665-014-3826-0.
    [22] Ihle T,Jhnichen S,Benndorf J. Wax and wane of Microcystis(Cyanophyceae)and microcystins in lake sediments:A case study in Quitzdorf Reservoir(Germany). Journal of Phycology,2010,41(3):479-488. DOI:10. 1111/j. 1529-8817.2005.00071.x.
    [23] Bostrm B,Pettersson AK,Ahlgren I. Seasonal dynamics of a cyanobacteria-dominated microbial community in surface sediments of a shallow,eutrophic lake. Aquatic Sciences,1989,51(2):153-178. DOI:10.1007/BF00879300.
    [24] Tsujimura S,Tsukada H,Nakahara H et al. Seasonal variations of Microcystis populations in sediments of Lake Biwa,Japan. Hydrobiologia,2000,434(1/2/3):183-192. DOI:10.1023/A:1004077225916.
    [25] Wang CB. Study on the dynamic and affecting factors of Microcystis and microcystin in sediment[Dissertation]. Beijing:University of Chinese Academy of Sciences,2014.[王纯波.微囊藻及其毒素在沉积物中的动态变化及影响因素研究[学位论文].北京:中国科学院大学,2014.]
    [26] Lahti K,Rapala J,Frdig M et al. Persistence of cyanobacterial hepatotoxin,microcystin-LR in particulatematerial and dissolved in lake water. Water Research,1997,31(5):1005-1012. DOI:10.1016/S0043-1354(96)00353-3.
    [27] Song H,Coggins LX,Reichwaldt ES et al. The importance of lake sediments as a pathway for Microcystin dynamics in shallow eutrophic lakes. Toxins,2015,7(3):900-918. DOI:10.3390/toxins7030900.
    [28] Ye W,Tan J,Liu X et al. Temporal variability of cyanobacterial populations in the water and sediment samples of Lake Taihu as determined by DGGE and real-time PCR. Harmful Algae,2011,10(5):472-479. DOI:10.1016/j. hal.2011.03.002.
    [29] Ma QQ,Wang B,Zhang ZY et al. Study on heavy metals pollution in sediments from North of Taihu Lake and its biological toxicity. Asian Journal of Ecotoxicology,2016,11(3):204-210. DOI:10. 7524/AJE. 1673-5897. 20150901001.[马青清,王博,张责研等.太湖北部表层沉积物重金属污染及其生物毒性研究.生态毒理学报,2016,11(3):204-210.]
    [30] Miller MJ,Critchley MM,Hutson J et al. The adsorption of cyanobacterial hepatotoxins from water onto soil during batch experiments. Water Research,2001,35(6):1461-1468. DOI:10.1016/S0043-1354(00)00419-X.
    [31] Grützmacher G,Wessel G,Klitzke S et al. Microcystin elimination during sediment contact. Environmental Science&Technology,2010,44(2):657-662. DOI:10.1021/es9016816.
    [32] Wu X,Xiao B,Li R et al. Mechanisms and factors affecting sorption of microcystins onto natural sediments. Environmental Science&Technology,2011,45(7):2641-2647. DOI:10.1021/es103729m.
    [33] Lu M,Zhang WG,Shi YX et al. Vertical variations of metals and nutrients in sediments from northern Taihu Lake and the influencing factors. J Lake Sci,2003,15(3):213-220. DOI:10.18307/2003.0304.[陆敏,张卫国,师育新等.太湖北部沉积物金属和营养元素的垂向变化及其影响因素.湖泊科学,2003,15(3):213-220.]
    [34] Zhao XQ,Yang LY,Yu ZY et al. Temporal and spatial distribution of physicochemical characteristics and nutrients in sediments of Lake Taihu. J Lake Sci,2007,19(6):698-704. DOI:10.18307/2007.0612.[赵兴青,杨柳燕,于振洋等.太湖沉积物物理化性质及营养盐的时空变化.湖泊科学,2007,19(6):698-704.]
    [35] Wang FW. Temporal and spatial variations of physico-chemical characteristics in sediments of Lake Taihu,China[Dissertation]. Guangzhou:Jinan University,2011.[王锋文.太湖沉积物物理化学性质时空变化特征研究[学位论文].广州:暨南大学,2011.]
    [36] Su X,Xue Q,Steinman AD et al. Spatiotemporal dynamics of microcystin variants and relationships with environmental parameters in Lake Taihu,China. Toxins,2015,7(8):3224-3244. DOI:10.3390/toxins7083224.
    [37] Park HD,Sasaki Y,Maruyama T et al. Degradation of the cyanobacterial hepatotoxin microcystin by a new bacterium isolated from a hypertrophic lake. Environmental Toxicology,2010,16(4):337-343. DOI:10.1002/tox.1041.
    [38] Yan H,Deng YM,Zou H et al. Isolation and activity of bacteria for the biodegradation of microcystins. Environmental Science,2004,25(6):336-339. DOI:10.13227/j.hjkx.2004.06.010.[闫海,邓义敏,邹华等.降解微囊藻毒素菌种的筛选和活性研究.环境科学,2004,25(6):336-339.]
    [39] Jones GJ,Orr PT. Release and degradation of microcystin following algaecide treatment of a Microcystis aeruginosa bloom in a recreational lake,as determined by HPLC and protein phosphatase inhibition assay. Water Research,1994,28(4):871-876. DOI:10.1016/0043-1354(94)90093-0.
    [40] Van DB,Verspagen JM,Lürling M et al. The ecological stoichiometry of toxins produced by harmful cyanobacteria:an experimental test of the carbon-nutrient balance hypothesis. Ecology Letters,2010,12(12):1326-1335. DOI:10.1111/j.1461-0248.2009.01383.x.
    [41] Chen W,Song L,Gan N et al. Sorption,degradation and mobility of microcystins in Chinese agriculture soils:Risk assessment for groundwater protection. Environmental Pollution,2006,144(3):752-758. DOI:10. 1016/j. envpol. 2006.02.023.
    [42] Rinta-Kanto JM,Konopko EA,Debruyn JM et al. Lake Erie Microcystis:Relationship between microcystin production,dynamics of genotypes and environmental parameters in a large lake. Harmful Algae,2009,8(5):665-673. DOI:10.1016/j.hal.2008.12.004.
    [43] Lee TA,Rollwagen-Bollens G,Bollens SM et al. Environmental influence on cyanobacteria abundance and microcystin toxin production in a shallow temperate lake. Ecotoxicology&Environmental Safety,2015,114:318-325. DOI:10.1016/j.ecoenv.2014.05.004.
    [44] Wan X,Tai YP,Wang R et al. Distribution patterns of microcystins-producing Microcystis and microcystin-LR during blooms in drinking watersource areas of Lake Erhai. Acta Scientiae Circumstantiae,2017,37(6):2040-2047. DOI:10.13671/j.hjkxxb.2017.0037.[万翔,邰义萍,王瑞等.洱海水华期间饮用水源区产毒微囊藻和微囊藻毒素-LR的分布特征.环境科学学报,2017,37(6):2040-2047.]
    [45] Wu WX. Unique spatiotemporal distribution of total and toxic Microcystis populations in water and sediments in Lake Taihu[Dissertation]. Shanghai:East China University of Science and Technology,2016.[吴文仙.太湖水体和底泥中总微囊藻与产毒微囊藻丰度的分布特征[学位论文].上海:华东理工大学,2016.]
    [46] Zhang YL,Yang LY,Qing BQ et al. Spatial distribution of COD and the correlations with other parameters in the northern region of Lake Taihu. Environmental Science,2008,29(6):1457-1462. DOI:10.13671/j.hjkxxb.2017.0037.[张运林,杨龙元,秦伯强等.太湖北部湖区COD浓度空间分布及与其他要素的相关性研究.环境科学,2008,29(6):1457-1462.]
    [47] Wang JG,Zou H,Zhang Q et al. Spatial and temporal distribution of microcystin in Taihu Lake. Research of Environmental Sciences,2014,27(7):696-703.[王靖国,邹华,张强等.太湖微囊藻毒素的时空分布特征.环境科学研究,2014,27(7):696-703.]
    [48] Yuan LJ,Liao QG,Zhang L et al. Seasonal and spatial variations of microcystins and their relationships with physiochemical and biological factors in Poyang Lake. Environmental Science,2018,39(1):450-459. DOI:10. 13227/j. hjkx.201708227.[袁丽娟,廖且根,张莉等.鄱阳湖微囊藻毒素时空分布格局及其与理化和生物因子的关系.环境科学,2018,39(1):450-459.]
    [49] Wang LZ,Hu QF,Hu Y et al. Changes and cause analysis of water level characteristic factors in Taihu Lake during period from 1954 to 2013. Journal of Hohai University:Natural Sciences,2016,44(1):14-19.[王磊之,胡庆芳,胡艳等.1954-2013年太湖水位特征要素变化及成因分析.河海大学学报:自然科学版,2016,44(1):14-19.]

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