研究报告

不同土壤类型下杂交籼稻地上部器官对重金属镉和铅的富集特征

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  • 1南京农业大学 应用生态研究所, 江苏 南京 210095; 2中国农业科学院 作物科学研究所, 北京 100081; *通讯联系人, E-mail: zhangweij@caas.net.cn

收稿日期: 1900-01-01

  修回日期: 1900-01-01

  网络出版日期: 2010-03-10

Accumulation Characteristics of Cadmium and Lead in Aboveground Organs of Indica Hybrid Rice as Affected by Different Soil Types

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  • 1 Institute of Applied Ecology, Nanjing Agricultural University, Nanjing 210095, China; 2 Institute of Crop Science, Chinese Academy of Agricultural Sciences, Beijing 100081, China; *Corresponding author, E-mail: zhangweij@caas.net.cn

Received date: 1900-01-01

  Revised date: 1900-01-01

  Online published: 2010-03-10

摘要

于2008年选用江苏省两种典型土壤(潮土和水稻土),采用盆栽试验研究杂交籼稻K优818地上部不同器官对土壤重金属镉(Cd)和铅(Pb)的富集特征。结果显示,水稻地上部不同器官对土壤Cd和Pb的富集特征差异显著,总体上呈现茎鞘>叶片>大米的趋势。水稻土栽培下重金属对水稻株高、单穗重等的抑制效应显著强于潮土,且抑制效应随土壤重金属浓度的升高而增强。与对照相比,当外源Cd和Pb的浓度为7 mg/kg和900 mg/kg时,单穗重降幅最大,分别下降了28.4%和36.6%。不同土壤类型下,重金属的生物有效性差异明显,水稻土栽培下水稻各器官的Cd与Pb含量显著高于潮土。

本文引用格式

范中亮,季辉,杨菲,吴琦,张卫建 . 不同土壤类型下杂交籼稻地上部器官对重金属镉和铅的富集特征[J]. 中国水稻科学, 2010 , 24(2) : 183 -188 . DOI: 10.3969/j.issn.1001-7216.2010.02.13

Abstract

Pot experiments were conducted to investigate the accumulation characteristics of Cd and Pb in aboveground organs of indica hybrid rice(K you 818) in two typical soils (paddy soil and alluvial soil) in 2008. There were significant differences in the concentrations of Cd and Pb in different aboveground organs, following an order of stem and sheath>leaves>milled rice(P<0.05). The inhibitory effects of the two heavy metals on plant height and single panicle weight were significantly greater in the paddy soil than those in the alluvial soil. In addition, the inhibitory intensity increased with the rising concentrations of the heavy metals. In comparison to the control, the single panicle weight showed the largest declines of 28.4% and 36.6% while the concentrations of exogenous Cd and Pb reached 7 mg/kg and 900 mg/kg, respectively. The bioavailability of the heavy metals exhibited significant differences between the two soil types. Consequently, the concentrations of Cd and Pb in various rice organs were significantly higher in the paddy soil than those in the alluvial soil (P<0.05).

参考文献

[1]Buchauer M J. Contamination of soil and vegetation near a zinc smelter by zinc, cadmium, copper and lead. Environ Sci Technol, 1973, 7(2): 131-135.
[2]Alloway B J, Steinnes E. Anthropogenic additions of cadmium to soils//McLaughlin M J, Singh B R. Cadmium in Soils and Plants. Dordrecht: Kluwer Academic Publishers, 1999: 97-123.
[3]赵其国, 周炳中, 杨浩. 江苏省环境质量与农业安全问题研究. 土壤, 2002, 34(1): 1-8.
[4]刘洪莲, 李艳慧, 李恋卿, 等. 太湖地区某地农田土壤及农产品中重金属的分布及风险评价. 农业与环境学报, 2006, 6(5): 60-63.
[5]USEPA. Part-503 Standards for the use or disposal of sewage sludge. Federal Register, 1993, 58: 9387-9404.
[6]Chang A C, Page A L. Cadmium uptake for Swiss chard grown on composted sewage sludge-treated field plots: Plateau or time bomb. J Environ Qual, 1997, 26(1): 11-19.
[7]王凯荣, 郭 焱, 何电源, 等. 重金属污染对稻米品质影响的研究. 农业环境保护, 1993, 12(6): 254-257.
[8]阎雨平, 蔡士悦, 史艇. 广东赤红壤、红壤重金属镉污染的农作物污染效应及其临界含量研究. 环境科学与技术, 1992, 6(1): 6-11.
[9]王凯荣. 镉对不同基因型水稻生长毒害影响的比较研究. 农村生态环境, 1996, 12(3): 18-23.
[10]陈铨荣. 利用放射性115Cd研究水稻对镉的吸收和分配. 环境科学, 1978(3): 4-7.
[11]康立娟, 赵成爱, 李呐. 铅在砂壤水稻土/水稻体系中污染效应及累积规律的研究. 吉林农业大学学报, 2000, 22(2): 68-70.
[12]洪谷政夫. 土壤污染的机理与解析. 正川, 于晶译. 北京:高等教育出版社, 1988.
[13]莫 争, 王春霞. 重金属Cu、Pb、Zn、Cr、Cd在水稻植株中的富集和分布. 环境化学, 2002, 21(2): 110-116.
[14]成颜君, 龚伟群, 李恋卿, 等. 2种杂交水稻对2种不同土壤中Cd吸收与分配的比较. 农业环境科学学报, 2008, 27(5): 1895-1900.
[15]鲁如坤. 土壤农业化学分析方法. 北京: 科学出版社, 2000: 205-226.
[16]赵步洪, 张洪熙, 杨建昌, 等. 杂交水稻不同器官镉浓度与累积量. 中国水稻科学, 2006, 20(3): 306-312.
[17]杨春刚, 朱智伟, 牟仁祥, 等. 重金属镉对水稻生长影响和矿质元素代谢的关系. 中国农学通报, 2005, 21(11): 176-178.
[18]吴燕玉, 余国营. Cd Pb Cu Zn As复合污染对水稻的影响. 农业环境保护, 1998, 17(2): 49-54.
[19]盂昭福, 薛澄泽, 张增强, 等. 土壤中复合污染的表征. 农业环境保护, 1999, 18(2): 87-91.
[20]赵志强, 牛军峰. 环境中有害金属植物修复的生理机制及进展. 环境科学研究, 2000, 13(5): 54-57.
[21]牟仁祥, 陈铭学, 朱智伟, 等. 水稻重金属污染研究进展. 生态环境, 2004, 13(3): 417-419.
[22]崔玉静, 赵中秋, 陈世宝, 等. 镉在土壤-植物-人体系统中迁移积累及其影响因子. 生态学报, 2003, 23(10): 2133-2140.
[23]Eriksson J, Oborn I, Jansson G, et al. Factors influencing Cd-content in crops: Results from Swedish field investigations. Swed J Agric Res, 1996, 26(3): 125-133.
[24]McLaughlin M J, Palmer L T, Tiller K G, et al. Increased soil salinity causes elevated cadmium concentrations in field-grown potato tubers. J Environ Qual, 1994, 23: 1013-1018.
[25]Mench M, Baize D, Mocquot B. Cadmium availability to wheat in five soil series from the Yonne district, Burgundy, France. Environ Pollut, 1997, 95: 93-103.
[26]Sukreeyapongse O, Holme P E, Strobel B W, et al. pH-dependent release of cadmium, copper, and lead from natural and sludge-amended soils. J Environ Qual, 2002, 31: 1901-1909.
[27]Kurz H, Schulz R, Romheld V. Phytoremediation of thallium and cadmium from contaminated soils: Possibilities and limitations//Proceedings of International Seminar on Use Plants for Environmental Remediation. Tokyo: Council for Promotion of Utilization of Organic Materials, 1997: 120-132.
[28]Morghan J T. Accumulation of cadmium and selected elements in flax seed grown on a calcareous soil. Plant & Soil, 1993, 150(1): 61-68.
[29]马朝红, 曾德生. 土壤中镉对水稻生长的影响. 湖北农业科学, 1992(2): 26-30.
[30]Youngberg B L. Differential responses of Australian wheat cultivars to cadmium concentration in wheat grain. Aust J Agric Res, 1991, 46(5): 873-886.
[31]Page A L, Bingham F T, Nelson C. Cadmium absorption and growth of various plant species as influenced by solution cadmium concentration. J Environ Qual, 1972, 28: 288-291.
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