Remediation Technology Against Heavy Metal Pollution in Farmland Soil with Different Pollution Levels

doi:10.11924/j.issn.1000-6850.casb16040167

Abstract

Abstract: With heavy metal pollution of farmland is more and more serious, crops’ quality and yield decline continuously and cause harm to the health of human beings. But pollution status of different regions has great differences. Taking different restoration measures in terms of different pollution levels of soil can not only improve repair efficiency, but also cut the cost. This paper expounds the effective prevention and remediation methods for farmland soil with different pollution levels. For the moderately and slightly polluted farmland, we mainly take prevention measures as planting resistance control-plant enrichment, passivation-plant resistance controlling and agronomic strengthening; for the heavily polluted farmland, we mainly take prevention measures as planting resistance control-efficient passivation, planting enrichment-other high efficiency technology, physical remediation etc. Now the study on remediation techniques for different levels of heavy metal pollution is still insufficient. We need to develop concrete and feasible remediation technology for different levels of heavy metal pollution systematically.

Chen Liangmei,Ma Youhua,Wang Chensisi,Li Jiangxia,Ye Wenling,Wu Linchun and Cui Junyi. Remediation Technology Against Heavy Metal Pollution in Farmland Soil with Different Pollution Levels[J]. Chinese Agricultural Science Bulletin, 2016, 32(32): 94-99.

References

[1] 彭星辉,谢晓阳.稻田镉(Cd)污染的土壤修复技术研究进展[J].湖南农业科学,2007(2):67-69.
[2] 蔡美芳,李开明,谢丹平,等.我国耕地土壤重金属污染现状与防治对策研究[J].环境科学与技术,2014,37(120):223-230.
[3] Bhargava A, Carmona F F, Bhargava M, et al. Approaches for enhanced phytoextraction of heavy metals[J].Journal of Environmental Management,2012,105:103-120.
[4] Lageman R. Electrore clamation application in the Netherlands[J].Environmental Science Technology,1993,27(13):2648-2650.
[5] 吴佳,谢明吉,杨倩.砷污染微生物修复的进展研究[J].环境科学,2011,32(3):817-824.
[6] Cai Meifang, Li Kaiming, XieDanping, et al. The status and protection strategy of farmland soils polluted by heavy metals[J].Environmental Science & Technology,2014,37(120):223-230.
[7] Feng Fengling, Cheng Jiemin, Wang Dexia. Potential application of earthworm for the phytore mediation of soils contaminated by heavy metals[J].Chinese Journal of Soil Science,2006,37(4):808-814.
[8] 周建利,陈同斌.我国城郊菜地土壤和蔬菜重金属污染研究现状与展望[J].湖北农学院学报,2002,22(5):476-480.
[9] Webb,M. Cadmiyn.British Medical Bulletin[J].Environmental Research,1975;31:46-50.
[10] Kjellstrom T, Nordberg G F. A kinetic model of cadmium metabolism in the humanbeing[J].Environmental Research,1978;16:246-269.
[11] Lagerwerff J V, Armiger W H, Specht A w. Uptake of lead by alfalfa and corn form soil and air[J].Soil Sci,1973,115:45-460.
[12] 韩禹.重金属对食品的污染危害及控制污染的建议[J]吉林蔬菜专家论坛,2010,04:85-86.
[13] Arthur E, Crews H, Morgan C. Optimizing plant genetic strategies for minimizing environmental contamination in the food chain[J].International Journal of Phytoremediation,2000,2:1-21.
[14] Ci Dunwei, Jiang Dong, Dai Tingbo, et al. Effect of Cd stress on lipid peroxidation and Cd Upstake and translocation in wheat seeding[J].Journal of Triticale Crops,2009,29(3):508-513.
[15] 吴亮,孙波.不同品种对水稻铅汞耐性和富集能力的影响[J].土壤,2014,46(6):1061-1068.
[16] Liu W T, Zhou Q X, An J, et al. Variations in cadmium accumulation among Chinese cabbage cultivars and screening for Cd-safe cultivars[J].Journal of Hazardous Materials,2010,173:737-743.
[17] Liu W T, Zhou Q X, Zhang Y L, et al. Lead accumulation in different Chinese cabbage cultivars and screening for pollution-safe cultivars[J].Journal of Environmental Management,2010,91:781-788.
[18] AssuncaoA, Bookum W, Nelissen H, et al. Differential metal specific tolerance and accumulation patterns among Thlaspi caerulescens populations originating from different soil types[J].New Phytologist,2003,159(2):411-419.
[19] 蒋彬.超积累植物在治理土壤重金属污染中的应用[J].昭通师范高等专科学校学报,2002,24(5):32-34.
[20] Ma L Q, Kenneth MK, Tu C, et al. A fern that hyperaccumulates arsenic[J].Nature,2001,409(6820):579.
[21] 于玲玲,朱俊艳,黄青青,等.油菜-水稻轮作对作物吸收累积镉的影响[J].环境科学与技术,2014,37(1):1-6.
[22] 黑亮,吴启堂,龙新宪,等.东南景天和玉米套种对Zn污染污泥的处理效应[J].环境科学,2007,28(4):852-858.
[23] 邓腾灏博,谷海红,仇荣亮.钢渣施用对多金属复合污染土壤的改良效果及水稻吸收重金属的影响[J].农业环境科学学报,2011,30(3):455-460.
[24] Cao X D, Ma L Q, Chen M, et al. Phosphate-induced metal immobilization in a contaminated site[J].Environmental Pollution,2003,122(1):19-28.
[25] Van Herwijnen R, Hutchings TR, Al-Tabbaa A, et al. Remediation of metal contaminated soil with mineral-amended composts[J].Environmental Pollution,2007,150:347-354.
[26] Lombi E, Zhao FJ, Zhang G, et al. In situ fixation of metals in soils using bauxite residue: chemical assessment[J].Environmental Pollution,2002,118:435-443.
[27] 王陈丝丝,马友华,于倩倩,等.钝化剂对农田土壤重金属形态与其稳定性影响研究[J]中国农学通报,2016(1):172-177.
[28] Tiwari S, Kumari B, Singh SN. Evaluation of metal mobility/immobility in fly ash induced by bacterial strains isolated from the rhizospheric zone of Typha latifolia growing on fly ash dumps[J].Bioresource Technology,2008,99:1305-1310.
[29] Janou?ková M, Pavlíková D, Vosátka M. Potential contribution of arbuscular my corrhiza to cadmium immobilization in soil[J].Chemosphere,2006,65:1959-1965.
[30] Van PaassenLA. Biogrout, ground improvement by microbialial induced carbonate precipitation[D].Delft University of Technology,2009.
[31] 王新花,赵晨曦,潘响亮.基于微生物诱导碳酸钙沉淀(MICP)的铅污染生物修复[J].地球与环境,2015,43(1):1672-9250.
[32] Van Roy S, Vanbroekhoven K, Dejonghe W, et al. Immobilization of heavy metals inthe saturated zone by sorption and in situ bioprecipitation processes[J].Hydrometallurgy,2006,83:195-203.
[33] Achal V, Pan X, Zhang D. Remediation of copper-contaminaed soil by Kocuria flava CR1, based on microbially induced calcite precipitation[J].Ecological Engineering,2011,37(10):161-165.
[34] 王萌,陈世宝,等.纳米修复剂对溶液中重金属的吸附机制及镉污染土壤修复效果[D]中国农业科学院,2012.
[35] 王激清,茹淑华,苏德纯.氮肥形态和螯合剂对印度芥菜和高积累镉油菜吸收镉的影响[J].农业环境科学学报,2004,23(4):625-629.
[36] Kulli B, Balmer M, Krebs R, et al. Theinfluenceof nitrilotriacetateon heavymetaluptake oflettuce and ryegrass[J].J.Environ.Qual.,1999,28:6-10.
[37] RobinsonB.H. Thenickel hyper accumulator plant Alys-sumber to loni as a potential agent for phytoremediation and phytomining of nickel[J].J.Geochem.Explo,1997,59:75-86.
[38] JacobD.L., OteM.L. Influence of Typhalatifolia and fertilization on metal mobility in two different Pb-Zn mine tailing stypes[J].Sci.TotalEnviro.,2004,333:19-24.
[39] WildeE.W. Phyto extraction of lead from firing range soil by Vetiver grass[J].Chemosphere,2005,61:1451-1457.
[40] 王林,周启星.农艺措施强化重金属污染土壤的植物修复[J].中国生态农业学报,2008,16(3):772-777.
[41] EnsleyB D, Blaylock M J, Dushenkov S, et al. In-ducinghyperaccumulationofmetalsinplantshoots[P]U.S.Patent5917117.Dateissued:1999-06-29.
[42] 马铁铮,马友华,徐露露,等.农田土壤重金属污染的农业生态修复技术[J].农业资源与环境学报,2013,30(5):39-43.
[43] Rajkumar M, Ae N, Prasad M N, et al. Potential of siderophore-producing bacteria for improving heavy metal phytoextraction[J].Trends Biotechnol,2010,28(3):142-149.
[44] Tripathi M, Munot H P, Shouche Y, et al. Isolation and functional characterization of siderophore-producing lead-and cadmium-resistant Pseudomonas putida KNP9[J].Current microbiology,2005,50(5):233-237.
[45] Neubauer U, Furrer G, Schulin R. Heavy metal sorption on soil minerals affected by the siderophore desferrioxamine B: the role of Fe (III) (hydr) oxides and dissolved Fe (III)[J].European journal of soil science,2002,53(1):45-55.
[46] Komarek M, Tlustoa P, Sz^kovaa J, et al. The use of maize and poplarin chelant-enhanced phytoextraction of lead from contaminated agricultural soil[J].Chemosphere,2007,67:640451.
[47] 熊璇,唐浩,黄沈发,等.重金属污染土壤植物修复强化技术研究进展[J].环境科学与技术,2012,35(6):185-193.
[48] 瞿丽雅,付舜珍,刘鹂,等.汞污染土壤的改善研究[J].贵州师范大学学报:自然科学版,2004,22(2): 49-51.
[49] Cao A, Carucci A, Lai T, et al. Effect of biodegradable chelating agents on heavy metals phytoextraction with Mirabilis jalapa and on its associated bacteria[J].European Journal of Soil Biology,2007,43:200-206,
[50] 吴燕玉,陈涛,张学询.沈阳张士灌区Cd污染生态研究[J].生态学报,1989,9(1):21-26.
[51] 余志,黄代宽.重金属污染土壤修复治理技术概述[J].环保科技,2013(4):46-48.