巢湖水体重金属污染评价及水中重金属污染的植物修复研究
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摘要
巢湖是我国五大淡水湖之一,对周边地区的经济发展和人民生活都起着举足轻重的作用。近年来,由于工农业生产的发展,巢湖水体污染日益严重,直接影响着人民的生活质量,威胁着人类健康。对巢湖水体的污染状况进行评价,已迫在眉睫。
     为了了解巢湖水体重金属的污染现状,沉积物中各污染物的潜在生态危害程度,追溯水域污染历史,研究随年代变化的污染梯度及规律,本文通过对巢湖湖区及部分出入湖支流水、沉积物和水生植物中重金属元素(Cd、Cr、Pb、Cu、Zn、Mn、Fe)的含量进行了采样测定,评价了其污染状况。并对沉积物中重金属的空间分布进行了调查研究,利用潜在生态风险指数法对其进行了综合性评价分析。同时为了更好的了解表层沉积物中重金属的形态分布特征及其生物可利用性,研究其对生物的毒性大小,采用BCR三步提取法对巢湖水体表层沉积物中重金属(Cd、Pb、Cu、Cr、Zn、Fe、Mn)的形态分布特征及其生物可利用性进行了分析。
     1.研究结果表明,巢湖流域水体中的重金属元素含量均未超出地表水环境质量标准Ⅲ类标准。水生植物对重金属元素也都有不同程度的富集能力,据富集系数评价表明,植物对Cd、Mn、Cu的富集能力相对强些;且对重金属的生物积累量随所处环境中该元素含量的增加而有所增大。
     2.测定的巢湖水体沉积物重金属中,Zn、Cd的含量比背景值要高点,部分支流中的重金属含量比湖区要高,以西半湖的南淝河污染较为严重,并已出现复合污染的趋势。利用潜在生态风险指数法对沉积物中重金属污染的评价结果显示,对巢湖生态风险构成危害程度最大的重金属是Cd,少数样点属严重生态危害。多种重金属潜在生态危害指数则表明南淝河达到严重生态危害程度。同时沉积物中重金属的垂直分布特征研究表明,一般规律是在0-8cm段污染出现峰值,且随采样深度的增加重金属含量有递减的趋势。
     3.形态分析表明,重金属元素Cu、Cr、Zn、Fe主要以残渣态存在,其中Cu、Fe平均占总量的60%以上。而Mn、Cd主要以水溶态、可交换态与碳酸盐结合态存在,Pb则以氧化物结合态和有机态为主。这种形态分布特征决定了Mn、Cd、Pb有较大的释放潜力,远远大于其他四种金属,生物可利用性较大,具有较大的潜在危害。另外,Zn的形态变化特征还表明,人类活动对其存在影响,可能存在点源污染。
     4.重金属复合污染是主要水体污染类型之一。为了探明蜈蚣草修复水体重金属复合污染的能力,本文还采用水培试验研究了在分别添加不同浓度铅、镉、条件下三种重金属的积累以及对水体重金属的去除能力。结果表明:随着重金属离子供应浓度的增加,不同条件下,蜈蚣草体内重金属含量不同,均随着生长介质中重金属水平的提高而上升;表明蜈蚣草对这3种重金属离子有一定的耐受性,并有不同程度的吸收,pb~(2+)、Cd~(2+)和Cr~(6+)去除率最高分别为38.9%、31.5%和35.2%。总的来看,蜈蚣草对三者的复合污染有一定的耐性。这说明,蜈蚣草是一种可能有潜力用于混合污染水体修复的耐性植物。
Chaohu Lake is one of the five largest fresh lakes in China.In order to know the pollution condition of heavy metals in the water,sediments and aquatic plants of Chaohu Lake,the spatial distribution of heavy metals and the potential ecological hazard in the sediments of Chaohu Lake,a survey was conducted to evaluate the contents of heavy metals(Cd,Cr,Pb,Cu,Zn,Mn,Fe) in the water,sediments and aquatic plants of Chaohu Lake.Pollution degree of heavy metals was also evaluated based on the Potential Ecological Risk Index.And for knowing the modality distribution characteristic of heavy metals in surface sediments of Chaohu Lake,a study was conducted to estimate the contents of heavy metals' different modalities.
     The results indicated that the content of the heavy metals in the water in the investigated areas meet classⅢcriterion for surface water evaluation.Different kinds of aquatic plants in the sampling sites had different enrichment by the different heavy metals. According to the assessment of enrichment coefficient,the average enrichment coefficient of Cd,Cu,Mn contamination in aquatic plants was relatively higher than the other.
     The results also indicated that the sediments in rivers(esp.the Nanfei River) flowing into lakes were polluted more seriously than that in lakes by heavy metals.In the terms of concentration,the analyzed heavy metals followed a decreasing order of Fe>Mn>Zn>Cr>Pb>Cu>Cd.The potential ecologic risk index was used to evaluate metals pollution in the sediments of Chaohu Lake.By means of the risk assessment methodology,based on available data,it was demonstrated that Nanfei River was exposed to a very high potential ecological risk.Among the analyzed heavy metals Cd exhibited the highest pollution degree.Few section belonged to very high potential ecology risk.And the vertical distributions of pollutants in sediments were investigated.The highest concentration was in layer 0-8cm in depth.The results showed that the heavy metals concentration decreased with the increasing sampling depth.
     This paper investigated the speciation of heavy metals in selected contaminated surface sediments from water body by the BCR three-step sequential extraction procedure. The results showed that heavy metals(Cu,Cr,Zn,Fe) were associated mainly with residual form.Among these heavy metals,more than 60%of Cu,Fe.Pb were associated mainly with the Fe-Mn oxides bound form and the organic form.And more easily mobilized forms(the acid exchangeable form and the carbonate bound form) of Mn,Cd were dominant.While the percentage of the exchangeable Cd that was easily bioavailable was the highest.Compared with other metals,Cd,Mn and Pb in Lake Chaohu were more bioavailable,though the total concentrations of the three metals were not higher than others. It also found that the modality distribution of Zn was obviously influenced by human activities.
     Combination contamination of heavy metals is one of the important soil contamination types.A greenhouse experiment was carried out to determine the degree of tolerance of Pteris vittata L.to Pb,Cd and Cr and whether it could be applied to phytoremediation an revegetation of water contaminated with heavy metals.Results shown that:Concentrations of heavy metals in Pteris vittata L.all increased progressively with the increase of supply levels.Pteris vittata L.had good tolerance and could absorb the heavy metals mentioned above in various degrees.The Pb~(2+),Cd~(2+),and Cr~(6+) removal rates were 38.9%,31.5%and 35.2%.So,it was suggested that Pteris vittata L.was a potential pant for remedy Pb,Cd and Cr contaminated water.
引文
[1]简敏菲,游海,倪才英.鄱阳湖饶河段重金属污染水平与迁移特性[J].湖泊科学.2006,18(2):127-133.
    [2]简敏菲,弓晓峰,游海,等.鄱阳湖水土环境及其水生维管束植物重金属污染[J].长江流域资源与环境.2004,13(6):589-593.
    [3]A.IKEM,N.O.EGIEBOR and K.NYAVOR.Trace elements in water,fish and sediment from Tuskegee Lake,Southeastern USA[J].Water,Air,and Soil Pollution,2003,149:51-75.
    [4]陈怀满,郑春荣,王慎强,等.不同来源重金属污染的土壤对水稻的影响[J].农村生态环境.2001,17(2):35-40.
    [5]赵新华,马伟芳,等.玉米修复河道疏浚底泥重金属-有机复合污染的根际效应[J].农业环境科学学报.2006,25(1):100-106.
    [6]王庆仁,崔岩山,董艺婷.植物修复-重金属污染土壤整治有效途径[J].生态学报.2001,21(2):326-331.
    [7]X524 X131.2.邹晓东.南四湖水域重金属污染物分布特征及其存在形态的研究:[硕士学位论文].山东:山东大学,20040519.
    [8]奚旦立,孙裕生,刘秀英.环境监测[M].北京:高等教育出版社,1995:6.
    [9]陈静生,周家义.中国水环境重金属研究[M].北京:中国环境科学出版社,1992,168-170.
    [10]刘红磊,尹澄清.城市湖泊表层沉积物中的重金属污染现状及其稳定度分析-以武汉墨水湖为例[J].生态毒理学报.2007,2(2):214-219.
    [11]X524 X17.滑丽萍.湖泊底泥中磷与重金属污染评价及其植物修复:[硕士学位论文].北京:首都师范大学,20060501.
    [12]Wojciech Tylmann.Lithological and geochemical record of anthropogenic changes in recent sediments of a small and shallow lake(Lake Pusty Staw,northern Poland)[J].Journal of Paleolimnology(2005)33:313-325.
    [13]尚英男,倪师军,张成江,等.成都市河流表层沉积物重金属污染及潜在生态风险评价[J].生态环境.2005,14(6):827-829.
    [14]贾振邦,赵智杰,杨小毛,等.洋涌河、茅洲河和东宝河沉积物中重金属的污染及评价[J].环境化学.2001,20(3):212-219.
    [15]李仁英,杨浩,陈捷,等.盘龙江口滇池沉积物重金属的分别及污染评价[J].土壤.2006,38(2):186-191.
    [16]弓晓峰,陈春丽,周文斌,等.鄱阳湖底泥中重金属污染现状评价[J].环境科学.2006,27(4):732-736.
    [17]陈守莉,王平祖,秦明周,等.太湖流域典型湖泊积沉物中重金属污染的分布特征[J].江苏农业 学报.2007,23(2):124-130.
    [18]王荔娟,于瑞莲,胡恭任,等.晋江感潮河段表层沉积物重金属污染特征[J].华侨大学学报(自然科学版).2008,29(1):148-151.
    [19]吴光红,朱兆洲,刘二保,等.天津城市排污河道沉积物中重金属含量及分布特征[J].环境科学.2008,29(2):413-420.
    [20]刘恩峰,沈吉,朱郁新,等.太湖表层沉积物重金属元素的来源分析[J].湖泊科学.2004,16(2):113-119.
    [21]岳东,张辉,卫磊,等.苏州河沉积物中Zn、Cu、Hg的形态分布研究及沉积特点初探[J].矿物岩石地球化学通报.2008,27(1):57-62.
    [22]Wojciech Tylmann.Lithological and geochemical record of anthropogenic changes in recent sediments of a small and shallow lake(Lake Pusty Staw,northern Poland)[J].Journal of Paleolimnology(2005) 33:313-325.
    [23]Mc Cauley.;Dennis J.;De Greave G M.;Linton T K.Sediment quality guidelines and assessment:overview and research needs[J].Environmental Science & Policy,2000,(3):33-44.
    [24]金相灿.沉积物污染化学[M].北京:中国环境科学出版社,1992,327-356.
    [25]Miiller G.Index of geoaccumulation in sediments of the Rhine River[J].Geojournal,1969,2(3):108-118.
    [26]郁亚娟,黄宏,王晓栋.淮河沉积物中重金属的测定和污染评价[J].环境科学研究.2003,16(6):26-28.
    [27]贾振邦,梁涛,林健枝,等.香港河流重金属污染及潜在生态危害研究[J].北京大学学报(自然科学版).1997,33(4):485-492.
    [28]贾振邦,周华,赵智杰,等.应用地积累指数评价太子河沉积物中重金属污染[J].北京大学学报(自然科学版).2000,36(4):525-530.
    [29]袁惠民,陈文生.红枫湖沉积物中主要重金属潜在生态危害性评价[J].贵州环保科技.1997,3(3):39-43.
    [30]Lars Hakanson.An Ecological Risk Index for Aquatic Pollution Control-A Sediment logical Approach[J].Water Research,1980,14(8):975-986.
    [31]黄宏,郁亚娟,王晓栋,等.淮河沉积物中重金属污染及潜在生态危害评价[J].环境污染与防治.2004,26(3):207-208.
    [32]陆引罡,黄建国,滕应,等.重金属富集植物车前草对镍的响应[J].水土保持学报.2004,18(1):108-114.
    [33]戴秀丽,孙成.太湖沉积物中重金属污染状况及分布特征探讨[J].上海环境科学.2001,20(2):71-74.
    [34]文湘华.水体沉积物重金属质量基准研究[J].环境化学.1993,12(5):334-341.
    [35]范成新,朱育新,吉志军,等.太湖宜溧河水系沉积物的重金属污染特征[J].湖泊科学.2002,14(3):235-241.
    [36]方涛,刘剑彤,张晓华,等.河湖沉积物中酸挥发性硫化物对重金属吸附及释放的影响[J].环境科学学报.2002,22(3):324-328.
    [37]文湘华,Herbert E.Allen.乐安江沉积物酸可挥发硫化物含量及溶解氧对重金属释放特性的影响[J].环境科学.1997,18(4):32-35.
    [38]金相灿,荆一风.湖泊污染底泥疏竣工程技术-滇池草海底泥疏挖及处置[J].环境科学研究.1999,12(5):9-12.
    [39]刘霞,刘树庆.土壤重金属形态分布特征与生物效应的研究进展[J].农业环境科学学报.2006,25(增刊):407-410.
    [40]刘俊华,王文华,彭安.土壤中汞生物有效性的研究[J].农业环境保护.2000,19(4):216-220.
    [41]Kot A.,Namiesiiik J..The role of speciation in analytical chemistry[J].Trends in Analysis Chemistry.2004,19(2+3):69-79.
    [42]张立,袁旭音,邓旭.南京玄武湖底泥重金属形态与环境意义[J].湖泊科学.2007,19(1):63-69.
    [43]弓晓峰,黄志中,张静,等.鄱阳湖湿地重金属形态分布及植物富集研究[J].环境科学研究.2006,19(3):34-40.
    [44]王海,王春霞,王子健.太湖表层沉积物中重金属的形态分析[J].环境化学.2002,2l(5):430-435.
    [45]毕春娟,陈振楼,许世远.上海白龙港排污口附近潮滩沉积物中重金属总量及其化学形态分析[J].海洋环境科学.2002,21(4):1-5.
    [46]TG115-314.冯素萍.小清河(济南段)底泥沉积物痕量重金属形态分析:[硕士学位论文].山东:山东大学,19991001.
    [47]王新伟,何江,李朝生.黄河包头段沉积物中生物可给态重金属分布研究[J].环境科学研究.2002,15(1):20-30.
    [48]冯素萍,鞠莉,沈永,等.沉积物中重金属形态分析方法研究进展[J].化学分析计量.2006,15(4):72-74.
    [49]Tessier A,Campbell P G C,Bission M.Sequential extraction procedure for the speciation of particulate trace metals[J].Anal Chem,1979,51:844-851.
    [50]Quevauviller P H,Rauret G,Lopez-Sanehez J F,et al.Certification of trace metal extractable contents in a sediment reference material(CRM 601) following a three-step sequential extraction procedure[J].Sci Total Environ,1997,205:223-234.
    [51]Gomez Ariza J L,Giraldez I,Sanchez-Rodas D,et al.Comparison of the feasibility of three extraction procedures for trace metal partitioning in sediments from south-west Spain[J].Sci Total Environ,2OOO,246:271-283.
    [52]Patricia Smiehowski.Griselda Polla.Dario Gomez.Metal fractionation of atmospheric aerosols via sequential chemical extraction:a review[J].Anal Bioanal Chem(2005)381:302-316.
    [53]Slobodan Miko,Goran Dum,Renata Adamcova,et al.Heavy metal distribution in karst soils from Croatia and Slovakia[J].Environmental Geology(2003) 45:262- 272.
    [54]Patricia Smichowski,Griselda Polla,Dario Gomez.Metal fractionation of atmospheric aerosols via sequential chemical extraction:a review[J].Anal Bioanal Chem(2005)381:302-316.
    [55]刘恩峰,沈吉,朱育新.重金属元素BCR提取法及在太湖沉积物研究中的应用[J].环境科学研究.2005,18(2):57-60.
    [56]何江,王新伟,李朝生,等.黄河包头段水-沉积物系统中重金属的污染特征[J].环境科学学报.2003,23(1):53-57.
    [57]Adriano D C,Wenzel W W and Blum W E H.Role of phytoremediation in the establishment of a global soil remediation network[A].In:Proceedings International Seminar on Use Plants for Environmental Remediation[C].Kosaikaikan,Tokyo,Japan,1997,:3-25.
    [58]Raskin I,Smith R D and Salt D E.Phytoremediation of metals:using plants to remove pollutants from the environment[J].Current Opinion in Biotechnology,1997,8:221-226.
    [59]杨肖娥,龙新宪,倪吾钟.超积累植物吸收重金属的生理及分子机制[J].植物营养与肥料学报.2002,8(1):8-15.
    [60]丁园.重金属污染土壤的治理方法[J].环境与开发.2000,15(2):25-28.
    [61]韦朝阳,陈同斌.重金属超富集植物及植物修复技术研究进展[J].生态学报.2001,21(7),1196-1203.
    [62]夏星辉,陈静生.土壤重金属污染治理方法研究进展[J].环境科学.1997,3,72-75.
    [63]周国华.被污染土壤的植物修复研究[J].物探与化探.2003,27(6),473-476.
    [64]叶春和.土壤污染的植物修复技术:现状与前景[J].山东科学.2004,17(1):45-50.
    [65]Yetis O,Doleklm F,et al.The removal of pb(Ⅱ) by phanerochaete chrysosporium[J].Wat Res.2000,34(16),4090-4100.
    [66]蒋晓云,曾光明,黄国和,等.白腐的研究进展及其在重金属修复中的展望[J].中国生物工程杂志.2005:118-121.
    [67]X522.李红霞.河道底泥中重金属和有机物的植物去除及资源化:[硕士学位论文].天津:天津大学,20050701.
    [68]康维钧,孙汉文等.环境重金属污染水体及土壤的生态毒理诊断及修复研究进展[J].河北工业科技.2006,23(1):61-64.
    [69]CHANEY R L,MINNIE M,LI Y M,Phytoremediation of soil metals[J].Current Opinion in Biotechnology.1997,8:279-284.
    [70]韦朝阳,陈同斌.重金属污染植物修复技术的研究与应用现状[J].地球科学进展.2002,17(6):833-839.
    [71]USEPA.Introduction to Phytoremediation.EPA/600/R-99/107,Washington D C,2000.
    [72]Sebastien Roy,Suzanne Labelle,Punita Mehta,et al.Phytoremediation of heavy metal and PAH-contaminated brownfield sites[J].Plant and Soil.(2005)272:277-290.
    [73]李海华,刘建武,李树人,等.土壤-植物系统中重金属污染及农作物富集研究进展[J].河南农业大学学报.2000,34(1):30-34.
    [74]Raskin I,Kumer N P,Dushenkov S,et al.Bioconcentration of heavy metal by plants[J].Current Opinion in Biotechnology.1994,5:285-290.
    [75]张蕾,李红霞,马伟芳,等.黑麦草对复合污染河道疏浚底泥修复的研究[J].农业环境科学学报.2006,25(1):107-112.
    [76]郑春荣,孙兆海,周东美,等.土壤Pb、Cd污染的植物效应Ⅱ-Cd污染对水稻生长和Cd含量的影响[J].农业环境科学学报.2004,23(5):872-876.
    [77]陈怀满,郑春荣,等.不同来源重金属污染的土壤对水稻的影响[J].农村生态环境.2001,17(2):35-40.
    [78]周东美,郝秀珍,薛艳,等.污染土壤的修复技术研究进展[J].生态环境.2004,13(2):234-242.
    [79]陈同斌,韦朝阳.砷超富集植物蜈蚣草及其对砷的富集特征[J].科学通报.2002,47(3).
    [80]周国华.被污染土壤的植物修复研究[J].物探与化探.2003,27(6):473-476.
    [81]王松良,郑金贵等.13种小白菜基因型对Cd、Pb、As累积特性比较[J].福建农林大学学报.2005,34(3):304-308.
    [82]李华,程芳琴,王爱英等.三种水生植物对Cd污染水体的修复研究[J].山西大学学报(自然科学版).2005,28(3):325-327.
    [83]王红旗,李华,陆泗进.羽叶鬼针草对Pb的吸收特性及修复潜力[J].环境科学.2005,26(16):143-147.
    [84]韩志萍.利用芦竹修复重金属污染湿地的研究[J].环境污染治理技术与设备.2005,6(8):30-33.
    [85]渠荣遴,李德森,等.水体重金属污染的植物修复研究(Ⅳ)-种苗过滤去除水中重金属铜[J].农业环境科学学报.2003,22(2):167-169.
    [86]Glass D.Associations.Inc.US and International Markets for phytoremediation[J].Washington D C,1999-2000.
    [87]田胜尼,刘登义等.香根草和鹅观草对Cu、Pb、Zn及其复合重金属的耐性研究[J].生物学杂志.2004,21(3):15-26.
    [88]吴龙华,骆永明,章海波.有机络合强化植物修复的环境风险研究-I.EDTA对复合污染土壤中TOC和重金属动态变化的影响[J].土壤.2001,4:189-192.
    [89]Krizek B A,Prost V,Joshi R M,Stoming T,Glenn T C.Developing transgenic Arabidopsis plants to be metalspecific bioindicators[J].Environ Toxicol Chem.2003,22:175-181.
    [90]徐昕,陶思源,郝林.用转基因植物修复重金属污染的土壤[J].植物学通报.2004,21(5): 595-607.
    [91]J.Hernandez-Allica,J.M.Becerril,et al.Assessment of the efficiency of a metal phytoextraction process with biological indicators of soil health[J].Plant and Soil(2006) 281:147-158.
    [92]刘晓光,缪锦来等.天津市清静黄河口河岸翅碱蓬的重金属富集特性[J].应用与环境生物学报.2006,12(1):25-29.
    [93]宋春霞等.植物在污水土地处理中的作用研究[J].化工装备技术.2004,25(2):56-58.
    [94]阎伍玖,张建春,纪敏.巢湖流域河水中N,P盐分组成特征分析[J].土壤侵蚀与水土保持学报.1999,5(2):35-38.
    [95]G.P.Shang,J.C.Shang.Spatial and Temporal Variations of Eutrophication in Western Chaohu Lake,China[J].Environ Monit Assess(2007)130:99-109.
    [96]X143(271) X524.王静雅.成都市湖塘沉积物重金属元素环境地球化学研究及城市污染史初析:[硕士学位论文].成都:成都理工大学,20050601.
    [97]彭安,朱建国主编.稀土元素的环境化学及生态效应[J].北京:中国环境科学出版社,2003:13-14.
    [98]Querauviller P H,Rriepiuk B.Single and sequential extraction in sediments and soils[J].Intern.J.Environ.Anal.Chem.,1993,51,231.
    [99]姜利兵,张建强.土壤重金属污染的形态分析及生物有效性探讨[J].工业安全与环保.2007,33(2):4-6.
    [100]傅以刚,黄亚,张亚雷,等.3种水生植物对水溶液中乐果的降解作用研究[J].农业环境科学学报.2006,25(1):90-94.
    [101]吕兰军.鄱阳湖水及其沉积物中的重金属调查[J].上海环境科学.1994,(5):17-21.
    [102]龚霞,刘淑娟,曹维鹏,等.鄱阳湖及支流底泥中重金属形态研究[J].江西农业大学学报.2006,28(4):620-624.
    [103]李发荣.滇池入湖河道底质污染及防治对策研究[J].环境科学导刊.2007,26(3):5-7.
    [104]滑丽萍,华珞,高娟,等.中国湖泊底泥的重金属污染评价研究[J].土壤.2006,38(4):366-373.
    [105]万金保,闫伟伟,谢婷.鄱阳湖流域乐安河重金属污染水平[J].湖泊科学.2007,19(4):421-427.
    [106]向勇,缪启龙,丰江帆.太湖底泥中重金属污染及潜在生态危害评价[J].南京气象学院学报.2006,29(5):700-705.
    [107]宋玉芳等.重金属对土壤中萝卜种子发芽与根伸长抑制的生态毒性[J].生态学杂志.2001,20(3):4-8.
    [108]程南宁,李巍,冉光兴,等.浙江东钱湖底泥污染物分布特征与评价[J].湖泊科学.2007,19(1):58-62.
    [109]王军,陈振楼,王初,等.上海市崇明岛城镇河流沉积物重金属累积与环境风险[J].应用生态学报.2007,18(7):1518-1522.
    [110]王永华,钱少猛,徐南妮,等.巢湖东区底泥污染物分布特征及评价[J].环境科学研 究.2004,17(6):22-26.
    [111]黄亮,李伟,吴莹,等.长江中游若干湖泊中水生植物体内重金属分布[J].环境科学研究.2002,15(6):1-4.
    [112]姚书春,李世杰.巢湖富营养化过程的沉积记录[J].沉积学报.2004,22(2):343-347.
    [113]杨宏伟,张毅.黄河(喇嘛湾段)沉积物中铜、铅、锌、镉的化学形态研究[J].中国环境监测.2002,18(5):3-16.
    [114]T.G.Kazi,M.K.Jamali,G.H.Kazi,et al.Evaluating the mobility of toxic metals in untreated industrial wastewater sludge using a BCR sequential extraction procedure and a leaching test[J].Anal Bioanal Chem(2005)383:297-304.
    [115]曹维鹏,罗明标,丁建桦.鄱阳湖重要支流底泥中重金属形态研究[J].东华理工学院学报.2006,29(1):66-73.
    [116]徐争启,倪师军,庹先国,等.火焰原子吸收光谱法分析沉积物中重金属元素的形态[J].分析试验室.2006,25(4):1-4.
    [117]陈建斌.水体中重金属离子的形态及其对生物富集影响[J].微量元素与健康研究.2003,20(4):46-49.
    [118]韩春梅,王林山,巩宗强,等.土壤中重金属形态分析及其环境学意义[J].生态学杂志.2005,24(12):1499-1502.
    [119]梁彦秋,潘伟,刘婷婷,等.沈阳张士污灌区土壤重金属元素形态分析[J].环境科学与管理.2006,31(2):43-45.

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