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石灰钝化法原位修复酸性镉污染菜地土壤

本站小编 Free考研考试/2021-12-31

李明1,,
陈宏坪1,
王子萱1,
杨新萍1
1.南京农业大学资源与环境科学学院,南京 210095
基金项目: 公益性行业(农业)科研专项(201403014)




In-situ lime immobilization of cadmium in vegetable field of acid soil zone

LI Ming1,,
CHEN Hongping1,
WANG Zixuan1,
YANG Xinping1
1.College of Resources and Environmental Science,Nanjing Agricultural University,Nanjing 210095,China

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摘要:在湖南省湘潭县酸性(pH=5.47±0.64)镉污染((1.06±0.08) mg·kg-1)菜地,进行为期1年的田间修复实验。研究施用石灰类钝化剂(石灰石或生石灰)对菜地土壤镉(Cd)的有效性、当地常见蔬菜可食部位Cd含量的影响,分析蔬菜种植过程中农业投入品对表层土壤(20 cm)Cd积累的影响,确定Cd污染菜地蔬菜安全生产的措施。结果表明:与对照相比,施加4 500 kg·hm-2 CaCO3或3 000 kg·hm-2 CaO分别使土壤pH升高了1.48和1.73,土壤有效态Cd含量分别降低了87.8%和78.1%;叶菜类、根茎类、茄果类和豆类蔬菜可食部位Cd含量分别降低了5.9%~70.5%、59.8%~65.8%、4.0%~50.0%和35.0%~76.4%,但施用4 500 kg·hm-2 CaCO3或3 000 kg·hm-2 CaO不能使叶菜类、茄果类蔬菜中Cd含量降低到相应的国家食品安全标准限值(叶菜类蔬菜,0.2 mg·kg-1 ;茄果类蔬菜,0.05 mg·kg-1)以下;蔬菜种植过程中施用的基肥、灌溉水、CaCO3或CaO不会导致表层土壤Cd含量增加。在酸性Cd污染菜地施用CaCO3或CaO、并种植低Cd积累蔬菜,可以实现蔬菜的安全生产。
关键词: 蔬菜/
/
石灰石/
生石灰/
田间实验

Abstract:A field experiment was conducted in a vegetable land with an elevated cadmium (Cd) concentration in the soil of Xiangtan county, Hunan province. The effects of application of CaCO3 or CaO on Cd availability in vegetable soil, the Cd concentrations in edible parts of different local vegetables, and the effect of continuous application of agricultural input on Cd accumulation in the upper 20 cm layer of soil in vegetable land were investigated. An appropriate technology for safe production of vegetable in Cd-polluted farmland was proposed. The application of 4 500 kg·hm-2 CaCO3 or 3 000 kg·hm-2 CaO increased soil pH by 1.48 and 1.73, but decreased the CaCl2-extractable Cd by 87.8% and 78.1%, respectively, as compared to the control. The application of CaCO3 or CaO significantly decreased Cd concentration in edible part of the leafy vegetables, rootstalk, solanaceous fruit and legume vegetables with a reduction range from 5.9% to 70.5%, 59.8% to 65.8%, 4.0% to 50.0% and 35.0% to 76.4%, respectively. However, Cd concentrations of both leafy vegetables and solanaceous fruit vegetables still exceeded the Chinese maximum permissible limits for Cd (0.2 mg·kg-1 for leafy vegetables and 0.05 mg·kg-1 for solanaceous fruit vegetables) even though the application of 4 500 kg·hm-2 CaCO3 or 3 000 kg·hm-2 CaO in the experiment. The use of agricultural inputs including fertilizer, irrigation water and lime (CaCO3 or CaO) has no obvious effects on the accumulation of Cd in the topsoils. The present results suggest that planting low Cd-accumulating varieties in combination with application of CaCO3 or CaO could produce safe vegetables in moderate Cd contaminated field.
Key words:vegetable/
cadmium/
limestone/
quicklime/
field experiment.

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[1] BOUSSEN S, SOUBRANDO M, BRIL H, et al.Transfer of lead, zinc and cadmium from mine tailings to wheat (Triticum;aestivum) in carbonated Mediterranean (Northern Tunisia) soils[J].Geoderma,2013,192(1):227-236 10.1016/j.geoderma.2012.08.029
[2] YE X, LI H, MA Y, et al.The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties[J].Journal of Soils & Sediments,2014,14(8):1407-1416 10.1007/s11368-014-0901-9
[3] CHAIN E.Ethyl carbamate and hydrocyanic acid in food and beverages:Scientific opinion of the panel on contaminants[J].EFSA Journal,2007,5(10):1-44 10.2903/j.efsa.2007.551
[4] ZHAO F J, MA Y, ZHU Y G, et al.Soil contamination in China: Current status and mitigation strategies[J].Environmental Science & Technology,2014,49(2):750-759 10.1021/es5047099
[5] 董同喜, 杨海雪, 李花粉, 等. 华北农田小麦-玉米轮作体系下土壤重金属积累特征研究[J]. 农业资源与环境学报,2014,31(4):355-365
[6] 茹淑华, 耿暖, 张国印, 等. 河北省典型蔬菜产区土壤和蔬菜中重金属累积特征研究[J]. 生态环境学报,2016,25(8):1407-1411
[7] 曾希柏, 李莲芳, 梅旭荣. 中国蔬菜土壤重金属含量及来源分析[J]. 中国农业科学,2007, 40(11):2507-2517
[8] 王旭. 广东省蔬菜重金属风险评估研究[D]. 武汉: 华中农业大学,2012
[9] 余江. 菜园土壤重金属污染特征及蔬菜食用安全性评价[D]. 厦门: 集美大学,2010
[10] 沈彤, 刘明月, 贾来, 等. 长沙地区蔬菜重金属污染初探[J]. 湖南农业大学学报,2005, 31(1):87-90
[11] WANG L X, GUO Z H, XIAO X Y, et al.Heavy metal pollution of soils and vegetables in the midstream and downstream of the Xiangjiang River, Hunan Province[J].Journal of Geographical Sciences,2008,18(3):353-362 10.1007/s11442-008-0353-5
[12] 环境保护部. 中国人群暴露参数手册:成人卷[M]. 北京: 中国环境科学出版社,2013
[13] 串丽敏, 赵同科, 郑怀国, 等. 土壤重金属污染修复技术研究进展[J]. 环境科学与技术, 2014,37(S2):213-222
[14] 周莉, 郑向群, 丁永祯, 等. 农田镉砷污染防控与作物安全种植技术探讨[J]. 农业环境科学学报,2017,36(4):613-619
[15] PING L I, WANG X, ZHANG T, et al.Effects of several amendments on rice growth and uptake of copper and cadmium from a contaminated soil[J].Journal of Environmental Sciences,2008,20(4):449-455 10.1016/S1001-0742(08)62078-1
[16] 袁金华, 徐仁扣. 生物质炭对酸性土壤改良作用的研究进展[J].土壤,2012,44(4):541-547
[17] CHEN S B, ZHU Y G, MA Y B.The effect of grain size of rock phosphate amendment on metal immobilization in contaminated soils[J].Journal of Hazardoous Materials,2006,134(1/2/3):74-79 10.1016/j.jhazmat.2005.10.027
[18] 曹心德, 魏晓欣, 代革联, 等. 土壤重金属复合污染及其化学钝化修复技术研究进展[J]. 环境工程学报,2011,5(7):1441-1453
[19] 肖细元, 杨淼, 郭朝晖, 等. 改良剂对污染土壤上蔬菜生长及吸收重金属的影响[J]. 环境科学与技术,2012,35(8):41-46
[20] 徐明岗, 张青, 曾希柏. 改良剂对黄泥土镉锌复合污染修复效应与机理研究[J]. 环境科学,2007,28(6):1361-1366
[21] PARADELO R, VIRTO I, CHENU C.Net effect of liming on soil organic carbon stocks: A review[J].Agriculture Ecosystems & Environment,2015,202:98-107 10.1016/j.agee.2015.01.005
[22] ZHU H, CHEN C, XU C, et al.Effects of soil acidification and liming on the phytoavailability of cadmium in paddy soils of central subtropical China[J].Environmental Pollution,2016,219:99-106 10.1016/j.envpol.2016.10.043
[23] 环境保护部. 土壤环境质量标准:GB 15618-1995[S]. 北京: 中国环境科学出版社,1995
[24] 郭安宁, 段桂兰, 赵中秋, 等. 施加碳酸钙对酸性土壤微生物氮循环的影响[J]. 环境科学,2017,38(8):3483-3488 10.13227/j.hjkx.201701145
[25] 王艳红, 李盟军, 唐明灯, 等. 石灰和泥炭配施对叶菜吸收Cd的阻控效应[J]. 农业环境科学学报,2013,32(12):2339-2344
[26] 曾廷廷, 蔡泽江, 王小利, 等. 酸性土壤施用石灰提高作物产量的整合分析[J]. 中国农业科学,2017,50(13):2519-2527
[27] 鲍士旦. 土壤农化分析[M]. 北京: 中国农业出版社,2000
[28] HOUBA V J G, TEMMINGHOFF E J M, GAIKHORST G A, et al.Soil analysis procedures using 0.01 M calcium chloride as extraction reagent[J].Communications in Soil Science & Plant Analysis,2000,31(9/10):1299-1396 10.1080/00103620009370514
[29] MCGRATH S P, CUNLIFFE C H.A simplified method for the extraction of the metals Fe, Zn, Cu, Ni, Cd, Pb, Cr, Co, and Mn from soils and sewage sludges[J].Journal of the Science of Food & Agriculture,2010,36(9):794-798 10.1002/jsfa.2740360906
[30] ZHAO F J, MCGRATH S P, CTOSLAND A R.Comparison of three wet digestion methods for the determination of plant sulphur by inductively coupled plasma atomic emission spectroscopy[J].Communications in Soil Science & Plant Analysis,1994,25(3/4):407-418 10.1080/00103629409369047
[31] 中华人民共和国卫生和计划生育委员会, 国家食品药品监督管理总局. 食品安全国家标准食品中污染物限量:GB 2762-2017[S]. 北京: 中国标准出版社,2017
[32] 王美, 李书田. 肥料重金属含量状况及施肥对土壤和作物重金属富集的影响[J]. 植物营养与肥料学报,2014,20(2):466-480
[33] MCBRIDE M B, TYLER L D, HOVDE D A.Cadmium adsorption by soils and uptake by plants as affected by soil chemical properties[J].Soil Science Society of America Journal, 1981,45(4):739-744 10.2136/sssaj1981.03615995004500040013x
[34] 熊礼明. 石灰对土壤吸附镉行为及有效性的影响[J]. 环境科学研究,1994,7(1):35-38
[35] 刘昭兵, 纪雄辉, 彭华, 等. 不同类型钙化合物对污染土壤水稻吸收累积Cd,Pb的影响及机理[J]. 农业环境科学学报,2010,29(1):78-84
[36] 王凯荣, 张玉烛, 胡荣桂. 不同土壤改良剂对降低重金属污染土壤上水稻糙米铅镉含量的作用[J]. 农业环境科学学报,2007,26(2):476-481
[37] 王艳红, 李盟军, 唐明灯, 等. 石灰和泥炭配施对叶菜吸收Cd的阻控效应[J]. 农业环境科学学报,2013,32(12):2339-2344
[38] BANGIRA C, LOEPPERT R H, MOORE T J, et al.Relative effectiveness of CaCO3, and Ca(OH)2, in minimizing metals solubility in contaminated sediment[J].Journal of Soils & Sediments,2016,17(6):1-10 10.1007/s11368-016-1641-9
[39] 赵小虎, 刘文清, 张冲, 等. 蔬菜种植前施用石灰对土壤中有效态重金属含量的影响[J]. 广东农业科学,2007 (7):47-49
[40] 刘丽, 吴燕明, 周航, 等. 大田条件下施加组配改良剂对蔬菜吸收重金属的影响[J]. 环境工程学报,2015,9(3):1489-1495
[41] 任露陆, 吴文成, 陈显斌, 等. 碳酸钙与氢氧化钙修复重金属污染土壤效果差异研究[J]. 环境科学与技术,2016,39(5):22-27
[42] 李素霞, 韦司棋, 刘云霞. 3种改良剂对氮镉互作下小白菜产量和品质的影响[J]. 西南农业学报,2015,28(4):1709-1712
[43] 孟赐福, 吴益伟. 施用石灰对红壤旱地土壤酸度和油菜产量的影响[J]. 中国油料作物学报,1995,17(2):39-43
[44] 敖俊华, 黄振瑞, 江永, 等. 石灰施用对酸性土壤养分状况和甘蔗生长的影响[J]. 中国农学通报,2010,26(15):266-269
[45] ZHOU H, YANG W T, ZHOU X, et al.Accumulation of heavy metals in vegetable species planted in contaminated soils and the health risk assessment[J].International Journal of Environmental Research & Public Health,2016,13(3):289-300 10.3390/ijerph13030289
[46] GRANT C A, CLARKE J M, DUGUID S, et al.Selection and breeding of plant cultivars to minimize cadmium accumulation[J].Science of the Total Environment,2008,390(2/3):301-310 10.1016/j.scitotenv.2007.10.038
[47] 龚梦丹, 顾燕青, 王小雨, 等. 杭州市菜地蔬菜重金属污染评价及其健康风险分析[J]. 浙江农业学报,2015,27(6):1024-1031
[48] KELLER C, MARCHETTI M, ROSSI L, et al.Reduction of cadmium availability to tobacco (Nicotiana tabacum) plants using soil amendments in low cadmium-contaminated agricultural soils: A pot experiment[J].Plant & Soil,2005,276(2):69-84 10.1007/s11104-005-3101-y
[49] 郭利敏, 艾绍英, 唐明灯, 等. 不同改良剂对土壤-叶菜系统Cd迁移累积的调控作用[J]. 农业环境科学学报,2010,29(8):1520-1525
[50] 倪中应, 石一珺, 谢国雄, 等. 石灰降低酸性农田农产品中重金属积累的效果[J]. 现代农业科技,2018 (1):176-177
[51] 廖敏, 黄昌勇, 谢正苗.pH对镉在土水系统中的迁移和形态的影响[J]. 环境科学学报, 1999,19(1):81-86
[52] 丁凌云, 蓝崇钰, 林建平, 等. 不同改良剂对重金属污染农田水稻产量和重金属吸收的影响[J]. 生态环境学报,2006,15(6):1204-1208
[53] 刘香香. 广东省4种蔬菜中镉与土壤镉污染相关性及阈值研究[D]. 武汉: 华中农业大学, 2012
[54] SIX L, SMOLDERS E.Future trends in soil cadmium concentration under current cadmium fluxes to European agricultural soils[J].Science of the Total Environment,2014, 485-486(3):319-328 10.1016/j.scitotenv.2014.03.109
[55] 闫湘, 王旭, 李秀英, 等. 我国水溶肥料中重金属含量、来源及安全现状[J]. 植物营养与肥料学报,2016,22(1):8-18
[56] MOOLENAAR S W, LEXMOND T M.Heavy-metal balances of agro-ecosystems in the Netherlands[J].Netherlands Journal of Agricultural Science,1998,46(2):171-192
[57] WEISSENGRUBER L, MOLLER K, PUSCHENREITER M, et al.Long-term soil accumulation of potentially toxic elements and selected organic pollutants through application of recycled phosphorus fertilizers for organic farming conditions[J].Nutrient Cycling in Agroecosystems,2018, 110(3):427-449 10.1007/s10705-018-9907-9
[58] 蒋永吉. 不同镉污染农田的原位修复研究[D]. 杨凌: 西北农林科技大学,2017
[59] 王林, 秦旭, 徐应明, 等. 污灌区镉污染菜地的植物阻隔和钝化修复研究[J]. 农业环境科学学报,2014,33(11):2111-2117
[60] 王期凯, 郭文娟, 孙国红, 等. 生物炭与肥料复配对土壤重金属镉污染钝化修复效应[J]. 农业资源与环境学报,2015,32(6):583-589



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石灰钝化法原位修复酸性镉污染菜地土壤

李明1,,
陈宏坪1,
王子萱1,
杨新萍1
1.南京农业大学资源与环境科学学院,南京 210095
基金项目: 公益性行业(农业)科研专项(201403014)
关键词: 蔬菜/
/
石灰石/
生石灰/
田间实验
摘要:在湖南省湘潭县酸性(pH=5.47±0.64)镉污染((1.06±0.08) mg·kg-1)菜地,进行为期1年的田间修复实验。研究施用石灰类钝化剂(石灰石或生石灰)对菜地土壤镉(Cd)的有效性、当地常见蔬菜可食部位Cd含量的影响,分析蔬菜种植过程中农业投入品对表层土壤(20 cm)Cd积累的影响,确定Cd污染菜地蔬菜安全生产的措施。结果表明:与对照相比,施加4 500 kg·hm-2 CaCO3或3 000 kg·hm-2 CaO分别使土壤pH升高了1.48和1.73,土壤有效态Cd含量分别降低了87.8%和78.1%;叶菜类、根茎类、茄果类和豆类蔬菜可食部位Cd含量分别降低了5.9%~70.5%、59.8%~65.8%、4.0%~50.0%和35.0%~76.4%,但施用4 500 kg·hm-2 CaCO3或3 000 kg·hm-2 CaO不能使叶菜类、茄果类蔬菜中Cd含量降低到相应的国家食品安全标准限值(叶菜类蔬菜,0.2 mg·kg-1 ;茄果类蔬菜,0.05 mg·kg-1)以下;蔬菜种植过程中施用的基肥、灌溉水、CaCO3或CaO不会导致表层土壤Cd含量增加。在酸性Cd污染菜地施用CaCO3或CaO、并种植低Cd积累蔬菜,可以实现蔬菜的安全生产。

English Abstract






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