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不同类型土壤小麦-水稻轮作体系施用含重金属污泥的环境效应
引用本文:任婧,程苗苗,李瑞,刘玲,吴龙华,刘鸿雁,骆永明.不同类型土壤小麦-水稻轮作体系施用含重金属污泥的环境效应[J].应用生态学报,2012,23(2):376-382.
作者姓名:任婧  程苗苗  李瑞  刘玲  吴龙华  刘鸿雁  骆永明
作者单位:1. 贵州大学农学院,贵阳550025;中国科学院南京土壤研究所土壤环境与污染修复重点实验室,南京210008
2. 中国科学院南京土壤研究所土壤环境与污染修复重点实验室,南京,210008
3. 贵州大学农学院,贵阳,550025
4. 中国科学院南京土壤研究所土壤环境与污染修复重点实验室,南京210008;贵州大学资源与环境工程学院,贵阳550003
基金项目:中国科学院知识创新工程重要方向项目(KSCX2-YW-G053);苏州市社会发展项目(SS201025);教育部211重点学科建设项目(211kst200902)资助
摘    要:采用贵州黄壤、石灰土和浙江水稻土,通过盆栽试验探讨了在3种土壤上施用含不同浓度重金属的污泥对小麦、水稻生长及锌(Zn)镉(Cd)吸收性的影响.结果表明:不同土壤施用同种污泥所产生的重金属污染风险不同,在黄壤和水稻土上施用高浓度重金属污泥对作物的污染风险较高.一次施用Zn、Cd浓度分别为1789、8.47 mg·kg-1的污泥1.6%,使黄壤小麦籽粒中Zn、Cd浓度分别达109、0.08 mg· kg-1;第二次施用后种植水稻,糙米中Zn、Cd浓度达52.0、0.54 mg·kg-1.而施用污泥后石灰性土壤的两种作物其可食部分均无重金属污染风险.土壤醋酸铵提取态Zn是影响麦粒和糙米中Zn浓度的主要因素,而土壤醋酸铵提取态Cd对麦粒和糙米中Cd浓度无明显影响.施用高浓度重金属污泥使3种土壤Zn、Cd全量显著提高,且两次施用后土壤全量Zn均超过国家土壤环境质量二级标准.

关 键 词:污泥  土壤  小麦-水稻轮作  重金属

Environmental effects of applying heavy metal-containing municipal sewage sludge on wheat-rice rotation system on different types of soil
Ren Jing,Cheng Miao-Miao,Li Rui,Liu Ling,Wu Long-Hua,Liu Hong-Yan,Luo Yong-Ming.Environmental effects of applying heavy metal-containing municipal sewage sludge on wheat-rice rotation system on different types of soil[J].Chinese Journal of Applied Ecology,2012,23(2):376-382.
Authors:Ren Jing  Cheng Miao-Miao  Li Rui  Liu Ling  Wu Long-Hua  Liu Hong-Yan  Luo Yong-Ming
Institution:College of Agronomy, Guizhou University, Guiyang, China. jren@issas.ac.cn
Abstract:A pot experiment with the yellow soil and limestone soil from Guizhou province, and paddy soil from Zhejiang Province was conducted to study the impacts of applying municipal sewage sludge containing different concentrations of heavy metals on the wheat and rice growth and their Zn and Cd absorption. The risks of the crop heavy metals pollution caused by the application of the same sludge differed with tested soils. On the yellow soil and paddy soil, applying the sludge containing high concentration heavy metals induced higher pollution risks to the crops. Applying the sludge 1.6% in dry mass and containing 1789 mg x kg(-1) of Zn and 8.47 mg x kg(-1) of Cd to yellow soil made the Zn and Cd concentrations in wheat grains reached 109 and 0.08 mg x kg(-1), and after the second time application of the same dosage of this sludge after rice planting, the Zn and Cd concentrations in brown rice reached 52.0 and 0.54 mg x kg(-1), respectively. However, applying the sludge to calcareous soil had no pollution risk to the edible parts of wheat and rice. Soil NH4OAc-extractable Zn was the main factor affecting the Zn concentration in wheat grain and brown rice, but soil NH4OAc-extractable Cd had less effect on the Cd concentration in wheat grain and brown nce. Applying the sludge containing high concentration Zn and Cd to the three soils made the concentrations of total Zn and Cd in the soils increased significantly, and after the first time and the second time of the application, the total Zn concentration in the soils all exceeded the 2nd level of the national soil environmental quality standards.
Keywords:sewage sludge  soil  wheat-rice rotation  heavy metal  
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