电化学联合H2O2氧化淋洗修复典型化工厂遗留地铬污染土壤

刘亦博; 成杰民

doi:10.12030/j.cjee.201801094

环境工程学报

电化学联合H2O2氧化淋洗修复典型化工厂遗留地铬污染土壤

刘亦博, 成杰民. 电化学联合H2O2氧化淋洗修复典型化工厂遗留地铬污染土壤[J]. 环境工程学报, 2018, 12(7): 2066-2074. doi: 10.12030/j.cjee.201801094

引用本文:

刘亦博, 成杰民. 电化学联合H2O2氧化淋洗修复典型化工厂遗留地铬污染土壤[J]. 环境工程学报, 2018, 12(7): 2066-2074. doi: 10.12030/j.cjee.201801094

LIU Yibo, CHENG Jiemin. Electrochemical and H2O2 oxidation with leaching to remove chromium from contaminated soil in a typical chemical deserted plant[J]. Chinese Journal of Environmental Engineering, 2018, 12(7): 2066-2074. doi: 10.12030/j.cjee.201801094

Citation:

LIU Yibo, CHENG Jiemin. Electrochemical and H2O2 oxidation with leaching to remove chromium from contaminated soil in a typical chemical deserted plant[J]. Chinese Journal of Environmental Engineering, 2018, 12(7): 2066-2074. doi: 10.12030/j.cjee.201801094

电化学联合H2O2氧化淋洗修复典型化工厂遗留地铬污染土壤

刘亦博^1,,
成杰民¹

1.
山东师范大学地理与环境学院，济南 250300
基金项目:
国家自然科学基金资助项目（41471255）

山东省自然科学基金资助项目（ZR2016YL002）

Electrochemical and H2O2 oxidation with leaching to remove chromium from contaminated soil in a typical chemical deserted plant

LIU Yibo^1,,
CHENG Jiemin¹

1.
College of Geography and Environment, Shandong Normal University, Jinan 250300, China
Fund Project:

摘要: 选取的济南某化工厂遗留地土壤主体为褐土类，年均降水量在685 mm左右，铬污染场地面积约34万m2，土量约105.4万m3。为筛选出最佳氧化条件，研究了4个厂区铬污染土壤的理化性质和污染状况，探讨了通电时间、通电电压、氧化剂质量分数、土液比和pH对Cr(Ⅲ)转化成Cr(Ⅵ)比率和总铬去除率的影响。结果表明：4个厂区土壤酸碱性不同；万吨铬盐生产车间和北部厂区有机质含量较高，其他2个厂区较低；总铬含量在863.3~14 403.8 mg·kg-1之间，均严重超出国家标准；铬污染活性指数I在0.007 8~0.292 9之间，铬污染活性指数均较低；最佳通电时间选择为20 min，通电电压为10 V，H2O2质量分数为1%，土液比为2:3，pH为8。经修复，4个厂区剩余总铬浓度分别为363.68、258.09、6 938.31和495.45 mg·kg-1，最大总铬去除率分别可达到87.59%、73.95%、51.83%和42.61%，其中万吨铬盐生产车间土壤中总铬残留值可达到国家土壤环境质量二级标准(GB 15618-2008)修订稿中的居住用地标准，铬盐生产车间和北部厂区可达到修订稿中的商业用地标准。
- 铬 /
- 土壤修复 /
- 电化学氧化 /
- 化学淋洗
Abstract: A typical chemical deserted plant in Jinan was selected in this paper, and the main soil type is cinnamon, the annual precipitation here is about 685 mm, the area of chromium contaminated site is about 340 000 m2, and the volume of soil is about 1 054 000 m3. In order to screen out the optimum oxidation conditions, the physicochemical properties and pollution status of chromium contaminated soil in four sites has been studied, and the effect of power time, electric voltage, mass fraction of H2O2, solid to liquid mass ratio and pH on the transformation of Cr(Ⅲ) into Cr(Ⅵ) and the removal rate of total Cr have been discussed. The results showed that the acidity and alkalinity of soil in the four sites was different. The organic matter content of ten thousand tons chromic salt workshop and north section of the plant was higher than that of the other two sites. The content of total Cr was in the range from 863.3 to 14 403.8 mg ·kg-1, which exceed the national standard seriously. The chromium pollution activity index I was low which were between 0.007 8 and 0.292 9. The optimal conditions were a power time of 20 min, electric voltage of 10 V, mass fraction of H2O2 of 1%, solid to liquid mass ratio of 2:3 and a pH of 8. After remediation, the remaining concentration of total Cr in the four sites was 363.68, 258.09, 6 938.31 and 495.45 mg·kg-1, respectively, and the maximum removal rate reached 87.59% , 73.95%, 51.83% and 42.61%. The total Cr residue in the soil of ten thousand tons chromic salt workshop reached the standard of residential land in the revised version of the National Soil Environmental Quality Class II Standard (GB 15618-2008). At the same time, chromic salt workshop and north section of the plant reached the revised version of the commercial land standards.
- chromium /
- soil remediation /
- electrochemical oxidation /
- chemical leaching

[1]	DAI R, YU C, LIU J,et al.Photo-oxidation of Cr(III)-citrate complexes forms harmful Cr(Ⅵ)[J].Environmental Science & Technology,2010,44(18):6959-6964 10.1021/es100902y
[2]	KOTAS J, STASICKA Z.Chromium occurrence in the environment and methods of its speciation[J].Environmental Pollution,2000,107(3):263-283 10.1016/S0269-7491(99)00168-2
[3]	WUANA R A, QKIEIMEN F E.Heavy metals in contaminated soils: A review of sources, chemistry, risks and best available strategies for remediation[J].ISRN Ecology,2011,2090-4614:1-20 10.5402/2011/402647
[4]	FU R B, WEN D D,XIA X,et al.Electrokinetic remediation of chromium (Cr)-contaminated soil with citric acid (CA) and polyaspartic acid (PASP) as electrolytes[J].Chemical Engineering Journal,2017,316:601-608 10.1016/j.cej.2017.01.092
[5]	RANIERI E, FRATIN U, PETRELLA A, et al.Ailanthus altissima and phragmites australis for chromium removal from a contaminated soil[J].Environmental Science and Pollution Research,2016,23(16):15983-15989 10.1007/s11356-016-6804-0
[6]	CHIANG L C, CHANG J E, WEN T C.Indirect oxidation effect in electrochemical oxidation treatment of land fill leachate[J].Water Research,1995,29(2):671-678 10.1016/0043-1354(94)00146-x
[7]	COMNINELLIS C, BATTISTI A D.Electrocatalysis in anodic oxidation of organics with simultaneous oxygen evolution[J].Journal De Chimie Physique,1996,93(4):673-679 10.1051/jcp/1996930673
[8]	王春荣, 李炟, 胡建龙, 等. 电化学氧化除氨氮过程中羟基自由基及中间产物定量分析[J]. 中国环境科学, 2012,32(2):238-241
[9]	VLYSSIDES A, BARAMPOUTI E M,MAI S,et al.Degradation of methylparathion in aqueous solution by electrochemical oxidation[J].Environment Science & Technology,2004,38(22):6125-6131 10.1021/es049726b
[10]	PANIZZA M, CERISOLA G.Removal of colour and COD from wastewater containing acid blue 22 by electrochemical oxidation[J].Journal of Hazardous Materials,2008,153(1/2):83-88 10.1016/j.jhazmat.2007.08.023
[11]	李世业, 成杰民.化工厂遗留地铬污染土壤化学淋洗修复研究[J]. 土壤学报,2015,52(4):870-878
[12]	贾之慎, 邬建敏, 唐孟成. 比色法测定Fenotn反应产生的羟自由基[J]. 生物化学与生物物理进展,1996,23(2):184-186
[13]	吴桐. 电动修复铬污染高岭土及铬渣污染土试验研究[D]. 北京：中国地质大学（北京）,2014
[14]	韩卫清. 电化学氧化法处理生物难降解有机化工废水的研究[D]. 南京：南京理工大学,2007
[15]	FONSECA B, PAZOS M,TAVARES T,et al.Removal of hexavalent chromium of contaminated soil by coupling electrokinetic remediation and permeable reactive biobarriers[J].Environmental Science & Pollution Research International,2012,19(5):1800-1808 10.1007/s11356-011-0694-y
[16]	王兴润, 刘雪, 颜湘华, 等. 铬渣污染土壤清洗剂筛选研究[J]. 环境科学研究,2010,23(11):1405-1409
[17]	李新, 刘勇弟, 孙贤波, 等.UV/H₂O₂法对印染废水生化出水中不同种类有机物的去除效果[J].环境科学, 2012,33(8):2728-2734

点击查看大图

计量

文章访问数: 2123
HTML全文浏览数: 1907
PDF下载数: 278
施引文献: 0

电化学联合H2O2氧化淋洗修复典型化工厂遗留地铬污染土壤

刘亦博^1,,
成杰民¹

1. 山东师范大学地理与环境学院，济南 250300

基金项目:

国家自然科学基金资助项目（41471255）

山东省自然科学基金资助项目（ZR2016YL002）

关键词:

摘要: 选取的济南某化工厂遗留地土壤主体为褐土类，年均降水量在685 mm左右，铬污染场地面积约34万m2，土量约105.4万m3。为筛选出最佳氧化条件，研究了4个厂区铬污染土壤的理化性质和污染状况，探讨了通电时间、通电电压、氧化剂质量分数、土液比和pH对Cr(Ⅲ)转化成Cr(Ⅵ)比率和总铬去除率的影响。结果表明：4个厂区土壤酸碱性不同；万吨铬盐生产车间和北部厂区有机质含量较高，其他2个厂区较低；总铬含量在863.3~14 403.8 mg·kg-1之间，均严重超出国家标准；铬污染活性指数I在0.007 8~0.292 9之间，铬污染活性指数均较低；最佳通电时间选择为20 min，通电电压为10 V，H2O2质量分数为1%，土液比为2:3，pH为8。经修复，4个厂区剩余总铬浓度分别为363.68、258.09、6 938.31和495.45 mg·kg-1，最大总铬去除率分别可达到87.59%、73.95%、51.83%和42.61%，其中万吨铬盐生产车间土壤中总铬残留值可达到国家土壤环境质量二级标准(GB 15618-2008)修订稿中的居住用地标准，铬盐生产车间和北部厂区可达到修订稿中的商业用地标准。

English Abstract

Electrochemical and H2O2 oxidation with leaching to remove chromium from contaminated soil in a typical chemical deserted plant

LIU Yibo^1,,
CHENG Jiemin¹

1. College of Geography and Environment, Shandong Normal University, Jinan 250300, China

Fund Project:

Keywords:

Abstract: A typical chemical deserted plant in Jinan was selected in this paper, and the main soil type is cinnamon, the annual precipitation here is about 685 mm, the area of chromium contaminated site is about 340 000 m2, and the volume of soil is about 1 054 000 m3. In order to screen out the optimum oxidation conditions, the physicochemical properties and pollution status of chromium contaminated soil in four sites has been studied, and the effect of power time, electric voltage, mass fraction of H2O2, solid to liquid mass ratio and pH on the transformation of Cr(Ⅲ) into Cr(Ⅵ) and the removal rate of total Cr have been discussed. The results showed that the acidity and alkalinity of soil in the four sites was different. The organic matter content of ten thousand tons chromic salt workshop and north section of the plant was higher than that of the other two sites. The content of total Cr was in the range from 863.3 to 14 403.8 mg ·kg-1, which exceed the national standard seriously. The chromium pollution activity index I was low which were between 0.007 8 and 0.292 9. The optimal conditions were a power time of 20 min, electric voltage of 10 V, mass fraction of H2O2 of 1%, solid to liquid mass ratio of 2:3 and a pH of 8. After remediation, the remaining concentration of total Cr in the four sites was 363.68, 258.09, 6 938.31 and 495.45 mg·kg-1, respectively, and the maximum removal rate reached 87.59% , 73.95%, 51.83% and 42.61%. The total Cr residue in the soil of ten thousand tons chromic salt workshop reached the standard of residential land in the revised version of the National Soil Environmental Quality Class II Standard (GB 15618-2008). At the same time, chromic salt workshop and north section of the plant reached the revised version of the commercial land standards.

全文HTML

参考文献 (17)

下载: 全尺寸图片幻灯片

返回文章

用微信扫码二维码

分享至好友和朋友圈

电化学联合H2O2氧化淋洗修复典型化工厂遗留地铬污染土壤

Electrochemical and H2O2 oxidation with leaching to remove chromium from contaminated soil in a typical chemical deserted plant

计量

出版历程

电化学联合H2O2氧化淋洗修复典型化工厂遗留地铬污染土壤

English Abstract

Electrochemical and H2O2 oxidation with leaching to remove chromium from contaminated soil in a typical chemical deserted plant

全文HTML

目录