重金属铬(Ⅵ)和铅对南京土壤中赤子爱胜蚓生长及繁殖的影响

王婉华, 陈丽红, 刘征涛, 王晓南, 张聪. 重金属铬(Ⅵ)和铅对南京土壤中赤子爱胜蚓生长及繁殖的影响[J]. 环境化学, 2015, 34(10): 1839-1844. doi: 10.7524/j.issn.0254-6108.2015.10.2015042102
引用本文: 王婉华, 陈丽红, 刘征涛, 王晓南, 张聪. 重金属铬(Ⅵ)和铅对南京土壤中赤子爱胜蚓生长及繁殖的影响[J]. 环境化学, 2015, 34(10): 1839-1844. doi: 10.7524/j.issn.0254-6108.2015.10.2015042102
WANG Wanhua, CHEN Lihong, LIU Zhengtao, WANG Xiaonan, ZHANG Cong. Effects of chromium (Ⅵ) and lead on the growth and reproduction of Eisenia Fetida in Nanjing soils[J]. Environmental Chemistry, 2015, 34(10): 1839-1844. doi: 10.7524/j.issn.0254-6108.2015.10.2015042102
Citation: WANG Wanhua, CHEN Lihong, LIU Zhengtao, WANG Xiaonan, ZHANG Cong. Effects of chromium (Ⅵ) and lead on the growth and reproduction of Eisenia Fetida in Nanjing soils[J]. Environmental Chemistry, 2015, 34(10): 1839-1844. doi: 10.7524/j.issn.0254-6108.2015.10.2015042102

重金属铬(Ⅵ)和铅对南京土壤中赤子爱胜蚓生长及繁殖的影响

  • 基金项目:

    国家环境保护公益性行业科研专项(201109032)

    环境基准与风险评估国家重点实验室自由探索基金(SKLECRA2014OFP06)资助.

Effects of chromium (Ⅵ) and lead on the growth and reproduction of Eisenia Fetida in Nanjing soils

  • Fund Project:
  • 摘要: 以南京化学工业园的土壤为研究对象, 分析土壤中重金属Cr(Ⅵ)和Pb对赤子爱胜蚓(Eisenia fetida)生长及繁殖的影响.结果表明, 与对照组比较, 暴露28 d时, 较低浓度的Cr(Ⅵ)(4—8 mg·kg-1)和Pb(1000—1500 mg·kg-1)能促进赤子爱胜蚓的生长发育, 而较高浓度的Cr(Ⅵ)(32—64 mg·kg-1)和Pb(3000 mg·kg-1)则显著抑制赤子爱胜蚓的生长发育;赤子爱胜蚓的产茧量随着Cr(Ⅵ)和Pb浓度的升高被显著抑制, 其中, Cr(Ⅵ)抑制赤子爱胜蚓产茧量的EC50(半数有效浓度)、NOEC(无观察效应浓度)和LOEC(最低观察效应浓度)分别为22.86 (20.56—25.42)、8、16 mg·kg-1.Pb抑制赤子爱胜蚓产茧量的EC50、NOEC和LOEC分别为2280.34 (2200.90—2362.65)、1500、2000 mg·kg-1;与人工土壤中Cr(Ⅵ)和Pb对赤子爱胜蚓产茧量的28 d-EC50有显著性差异.
  • 加载中
  • [1] 陈炳卿, 孙长颖. 食品污染与健康[M]. 北京:化学工业出版社, 2002:149-152
    [2] Molnar L, Fischer E, Kallay M. Laboratory studies on the effect, uptake and distribution of chromium in Eisenia foetida(Annelida, Oligochaeta)[J]. Zoologischer Anzeiger, 1989, 223:57-66
    [3] Richard F C, Bourg A C M. Aqueous geochemistry of chromium: a review[J]. Water Research, 1991, 25(7):807-816
    [4] Coleman R N. Chromium toxicity: effects on microorganisms with special reference to the soil matrix. In: Nriagu J O, Nieboer E(Eds). Chromium in Natural and Human Environments[M]. Wiley-Interscience, New York, 1988:335-350
    [5] Cary E E. Chromium in air soil and natural waters. In: Langard S(Ed). Biological and Environmental Aspects of Chromium, Topics in Environmental Health[M]. Elsevier Biomedical Press, Amsterdam, 1982:49-64
    [6] Chapman H D. Diagnostic criteria for plant s and soils[M]. Berkeley: University of California, 1973
    [7] Hunter J G, Vergnano O. Trace-element toxicities in oat plants[J]. Annals of Applied Biology, 1953, 40(4):761-776
    [8] Parr P D, Tatlor F G. Germination and growth effects of hexavalent chromium in Orocol TL (a corrosion inhibitor) on Phaseolus vulgaris[J]. Environment International, 1982, 7(3):197-202
    [9] Yang Y, Paterson E, Campbell C. Accumulation of heavy metal in urban soils and impacts on microorganism[J]. Environmental Science, 2001, 22(3): 44-48
    [10] Grakovskii V G, Frid A S, Timokhin P A. Evaluation of soil pollution by heavy metals and arsenic in Chelyabinsk Oblat[J]. Eurasian Soil Science, 1997, 30(1):74-81
    [11] Terelak H, Stuczynski T, Piotrowska M. Heavy metals in agricultural soils in Poland [J]. Polish Journal of Soil Science, 1997, 30(2):35-42
    [12] 陈丽红, 刘征涛, 方征, 等. 老化土壤中铅对赤子爱胜蚓生长及繁殖的影响[J]. 环境科学, 2014, 35(4):274-278
    [13] Xu J, Ke X, Krogh P H. Evaluation of growth and reproduction as indicators of soil metal toxicity to the Collembolan, Sinella curviseta[J]. Insect Science, 2009, 16: 57-63
    [14] 成杰民, 解敏丽, 朱宇恩. 赤子爱胜蚓对3种污染土壤中Zn及Pb的活化机理研究[J]. 环境科学研究, 2008, 21(5):91-97
    [15] Lock K, Janssen C R. Test designs to assess the influence of soil characteristics on the toxicity of copper and lead to the oligochaete Enchytraeus albidus[J]. Ecotoxicology, 2001, 10(3):137-144
    [16] Nelson Beyer W, Cromartie E J. A survey of Pb, Cu, Zn, Cd, As and Se earthworms and soil from diverse sites[J]. Environmental Monitoring and Assessment, 1987, 8(1):27-36
    [17] OECD. Guidelines for testing of chemicals. test 222: earthworm reproduction test[S]. Paris: Organization for Economic Coporation and Development, 2004
    [18] OECD. OECD series on testing and assessment No. 54. Current Approaches in the Statistical Analysis of Ecotoxicity Data: A Guidance to Application[S].
    [19] 陈英旭. pH、温度对Cr(Ⅵ)减少动力学的影响[J]. 环境科学, 1992, 13(3): 7-10
    [20] 王婉华, 陈丽红, 方征, 等. 土壤铬(Ⅵ)对赤子爱胜蚓的生态毒性效应[J]. 环境科学研究, 2013, 26(6):653-657
    [21] 徐明岗, 纳明亮, 张建新, 等. 红壤中Cu、Zn、Pb 污染对蔬菜根伸长的抑制效应[J]. 中国环境科学, 2008, 28(2):153-157
    [22] Kabala C, Singh B R. Fractionation and mobility of copper, lead, and zinc in soil profiles in the vicinity of a copper smelter[J]. Journal of Environment Quality, 2001, 30(2): 485-492
    [23] 寇士伟, 吴锦标, 谢素, 等. 红薯对Pb、Cd 的吸收累积特征及根际土壤Pb、Cd 形态分布研究[J]. 农业环境科学学报, 2011, 30(4):677-683
  • 加载中
计量
  • 文章访问数:  1340
  • HTML全文浏览数:  1282
  • PDF下载数:  451
  • 施引文献:  0
出版历程
  • 收稿日期:  2015-04-21
  • 刊出日期:  2015-10-15
王婉华, 陈丽红, 刘征涛, 王晓南, 张聪. 重金属铬(Ⅵ)和铅对南京土壤中赤子爱胜蚓生长及繁殖的影响[J]. 环境化学, 2015, 34(10): 1839-1844. doi: 10.7524/j.issn.0254-6108.2015.10.2015042102
引用本文: 王婉华, 陈丽红, 刘征涛, 王晓南, 张聪. 重金属铬(Ⅵ)和铅对南京土壤中赤子爱胜蚓生长及繁殖的影响[J]. 环境化学, 2015, 34(10): 1839-1844. doi: 10.7524/j.issn.0254-6108.2015.10.2015042102
WANG Wanhua, CHEN Lihong, LIU Zhengtao, WANG Xiaonan, ZHANG Cong. Effects of chromium (Ⅵ) and lead on the growth and reproduction of Eisenia Fetida in Nanjing soils[J]. Environmental Chemistry, 2015, 34(10): 1839-1844. doi: 10.7524/j.issn.0254-6108.2015.10.2015042102
Citation: WANG Wanhua, CHEN Lihong, LIU Zhengtao, WANG Xiaonan, ZHANG Cong. Effects of chromium (Ⅵ) and lead on the growth and reproduction of Eisenia Fetida in Nanjing soils[J]. Environmental Chemistry, 2015, 34(10): 1839-1844. doi: 10.7524/j.issn.0254-6108.2015.10.2015042102

重金属铬(Ⅵ)和铅对南京土壤中赤子爱胜蚓生长及繁殖的影响

  • 1.  中国环境科学研究院, 国家环境保护化学品生态效应与风险评估重点实验室, 环境基准与 风险评估国家重点实验室, 北京, 100012;
  • 2.  中海油环保服务有限公司, 天津, 300452
基金项目:

国家环境保护公益性行业科研专项(201109032)

环境基准与风险评估国家重点实验室自由探索基金(SKLECRA2014OFP06)资助.

摘要: 以南京化学工业园的土壤为研究对象, 分析土壤中重金属Cr(Ⅵ)和Pb对赤子爱胜蚓(Eisenia fetida)生长及繁殖的影响.结果表明, 与对照组比较, 暴露28 d时, 较低浓度的Cr(Ⅵ)(4—8 mg·kg-1)和Pb(1000—1500 mg·kg-1)能促进赤子爱胜蚓的生长发育, 而较高浓度的Cr(Ⅵ)(32—64 mg·kg-1)和Pb(3000 mg·kg-1)则显著抑制赤子爱胜蚓的生长发育;赤子爱胜蚓的产茧量随着Cr(Ⅵ)和Pb浓度的升高被显著抑制, 其中, Cr(Ⅵ)抑制赤子爱胜蚓产茧量的EC50(半数有效浓度)、NOEC(无观察效应浓度)和LOEC(最低观察效应浓度)分别为22.86 (20.56—25.42)、8、16 mg·kg-1.Pb抑制赤子爱胜蚓产茧量的EC50、NOEC和LOEC分别为2280.34 (2200.90—2362.65)、1500、2000 mg·kg-1;与人工土壤中Cr(Ⅵ)和Pb对赤子爱胜蚓产茧量的28 d-EC50有显著性差异.

English Abstract

参考文献 (23)

返回顶部

目录

/

返回文章
返回