两种修复模式下CAHs污染地下水的原位对照

宋久浩, 吴乃瑾, 李培中, 张骥, 李翔, 荣立明, 王海见, 宋云

中国环境科学 ›› 2022, Vol. 42 ›› Issue (10) : 4668-4675.

PDF(846 KB)
PDF(846 KB)
中国环境科学 ›› 2022, Vol. 42 ›› Issue (10) : 4668-4675.
水污染与控制

两种修复模式下CAHs污染地下水的原位对照

  • 宋久浩, 吴乃瑾, 李培中, 张骥, 李翔, 荣立明, 王海见, 宋云
作者信息 +

In-situ comparation of CAHs contaminated groundwater under two remediation strategies

  • SONG Jiu-hao, WU Nai-jin, LI Pei-zhong, ZHANG Ji, LI Xiang, RONG Li-ming, WANG Hai-jian, SONG Yun
Author information +
文章历史 +

摘要

为探究氯代脂肪烃(CAHs)污染地下水原位修复的长效性及环境的长期响应,选择华北某废弃化工厂污染区,开展了生物刺激、零价铁(ZVI)-生物刺激耦合中试对照试验,系统对比了2种修复模式下CAHs的降解效率及地下水生物化学参数的动态变化规律.结果表明,修复后长达4~5a内总CAHs含量均降至50 μg/L以下,耦合修复策略提高了CAHs的整体降解效率且未出现浓度反弹,同时可更快速地改善地下环境,为潜在降解菌的生长提供有利条件.两种修复方式对地下水细菌多样性的长期影响基本一致,均有利于向脱硫菌门Desulfobacterota和绿弯菌门Chloroflexi演化.最终生物刺激区总细菌数量高于耦合修复区约1个数量级,但后者地下水中的脱卤球菌属Dehalococcoidia数量(2.1~35)×103copies/mL反而高于前者(8.3~9.1)×103copies/mL,这更有利于CAHs的彻底脱氯.

Abstract

To explore the long-term effectiveness and environmental response of in-situ remediation of chlorinated aliphatic hydrocarbon (CAHs) contaminated groundwater, a pilot comparison experiment of biostimulation and zero valent iron (ZVI)-biological stimulation coupling remediation strategies was carried out in a polluted area of an abandoned chemical plant in North China. The degradation efficiency of CAHs and the dynamic variations of biochemical parameters for groundwater under these two remediation modes were systematically compared. Total CAHs decreased to less than 50μg/L within 4~5 years after remediation under the two strategies. The coupling remediation strategies increased the overall degradation efficiency of CAHs without concentration rebound and improved the groundwater environment and provided favorable conditions for the growth of potential degrading bacteria. The long-term effects on the bacterial diversity of groundwater by using these two remediation strategies were basically the same, which were conducive to the evolution to Desulfobacterota and Chloroflexi. Finally, the total number of bacteria in the biostimulation pilot area was about one order of magnitude higher than the coupling remediation pilot area, but the number of dehalococcoidia in the latter groundwater (2.1~35)×103 copies/mL was higher than the former (8.3~9.1)×103 copies/mL, which was more conducive to the complete dechlorination of CAHs.

关键词

地下水修复 / 零价铁 / 氯代脂肪烃 / 生物刺激 / 生物多样性

Key words

biodiversity / biostimulation / chlorinated aliphatic hydrocarbon / groundwater remediation / zero valent iron

引用本文

导出引用
宋久浩, 吴乃瑾, 李培中, 张骥, 李翔, 荣立明, 王海见, 宋云. 两种修复模式下CAHs污染地下水的原位对照[J]. 中国环境科学. 2022, 42(10): 4668-4675
SONG Jiu-hao, WU Nai-jin, LI Pei-zhong, ZHANG Ji, LI Xiang, RONG Li-ming, WANG Hai-jian, SONG Yun. In-situ comparation of CAHs contaminated groundwater under two remediation strategies[J]. China Environmental Science. 2022, 42(10): 4668-4675
中图分类号: X523   

参考文献

[1] Dai C, Zhou Y, Peng H, et al.Current progress in remediation of chlorinated volatile organic compounds:a review[J].Journal of Industrial and Engineering Chemistry, 2018,65:106-119.
[2] 陆强,李辉,林匡飞,等.上海浦东某氯代烃场地地下水污染现状调查[J].环境科学学报, 2016,36(5):1730-1737.Lu Q, Li H, Lin K F, et al.Investigation of chlorinated hydrocarbons in groundwater from a typical contaminated site in Pudong District, Shanghai[J].Acta Scientiae Circumstantiae, 2016,36(5):1730-1737.
[3] Wei Y, Wu S, Yang S, et al.Biodegradable surfactant stabilized nanoscale zero-valent iron for in situ treatment of vinyl chloride and 1,2-dichloroethane[J].Journal of Hazardous Materials, 2012,211-212:373-380.
[4] Fan D, Lan Y, Tratnyek P G, et al.Sulfidation of iron-based materials:a review of processes and implications for water treatment and remediation[J].Environmental Science & Technology, 2017,51:13070-13085.
[5] Wang X, Xin J, Yuan M, et al.Electron competition and electron selectivity in abiotic, biotic, and coupled systems for dechlorinating chlorinated aliphatic hydrocarbons in groundwater:A review[J].Water Research, 2020,183:116060.
[6] He F, Li Z, Shi S, et al.Dechlorination of excess trichloroethene by bimetallic and sulfidated nanoscale zero-valent iron[J].Environmental Science & Technology, 2018,52(15):8627-8637.
[7] Tang H, Wang J, Zhang S, et al.Recent advances in nanoscale zero-valent iron-based materials:Characteristics, environmental remediation and challenges[J].Journal of Cleaner Production, 2021, 319:128641.
[8] Bhattacharjee S, Ghoshal S.Phase Transfer of palladized nanoscale zerovalent iron for environmental remediation of trichloroethene[J].Environmental Science & Technology, 2016,50(16):8631-8639.
[9] Doong R, Saha S, Lee C, et al.Mesoporous silica supported bimetallic Pd/Fe for enhanced dechlorination of tetrachloroethylene[J].RSC Advances, 2015,5(110):90797-90805.
[10] Chen S, Bedia J, Li H, et al.Nanoscale zero-valent iron@mesoporous hydrated silica core-shell particles with enhanced dispersibility, transportability and degradation of chlorinated aliphatic hydrocarbons[J].Chemical Engineering Journal, 2018,343:619-628.
[11] Garcia A, Boparai H, Chowdhury A, et al.Sulfidated nano zerovalent iron (S-nZVI) for in situ treatment of chlorinated solvents:A field study[J].Water Research, 2020,174:115594.
[12] Zhang Y, Ozcer P, Ghoshal S.A comprehensive assessment of the degradation of C1and C2 chlorinated hydrocarbons by sulfidated nanoscale zerovalent iron[J].Water Research, 2021,201:117328.
[13] Smits T H M, Devenoges C, Szynalski K, et al.Development of a real-time PCR method for quantification of the three genera Dehalobacter, Dehalococcoides, and Desulfitobacterium in microbial communities[J].Journal of Microbiological Methods, 2004,57(3):369-378.
[14] Hatt J K, Ritalahti K M, Ogles D M, et al.Design and application of an internal amplification control to improve dehalococcoides mccartyi 16s rrna gene enumeration by qPCR[J].Environmental Science & Technology, 2013,47:11131-11138.
[15] Rosell M, Palau J, Mortan S H, et al.Dual carbon-chlorine isotope fractionation during dichloroelimination of 1,1,2-trichloroethane by an enrichment culture containing Dehalogenimonas sp.[J].The Science of the total environment, 2018,648:422-429.
[16] Mortan S H, Martin-Gonzalez L, Vicenta T, et al.Detoxification of 1,1,2-trichloroethane to ethene in a bioreactor co-culture of Dehalogenimonas and Dehalococcoides mccartyi strains[J].Journal of Hazardous Materials, 2017,331:218-225.
[17] Kocur C M D, Lomheim L, Molenda O, et al.Long-term field study of microbial community and dechlorinating activity following carboxymethyl cellulose-stabilized nanoscale zero-valent iron injection[J].Environmental Science & Technology, 2016,50(14):7658-7670.
[18] Wang S Y, Chen S C, Lin Y C, et al.Acidification and sulfide formation control during reductive dechlorination of 1,2-dichloroethane in groundwater:Effectiveness and mechanistic study[J].Chemosphere, 2016,160:216-229.
[19] Dong H, Li L, Lu Y, et al.Integration of nanoscale zero-valent iron and functional anaerobic bacteria for groundwater remediation:A review[J].Environ.Int., 2019,124:265-277.
[20] Herrero J, Puigserver D, Nijenhuis I, et al.Combined use of ISCR and biostimulation techniques in incomplete processes of reductive dehalogenation of chlorinated solvents[J].Science of the Total Environment, 2019,648:819-829.
[21] Vogel M, Nijenhuis I, Lloyd J, et al.Combined chemical and microbiological degradation of tetrachloroethene during the application of Carbo-Iron at a contaminated field site[J].S Science of the Total Environment, 2018,628-629:1027-1036.
[22] 袁梦姣,王晓慧,赵芳,等.零价铁与微生物耦合修复地下水的研究进展[J].中国环境科学, 2021,41(3):1119-1131.Yuan M J, Wang X H, Zhao F, et al.Research progress of zero-valent-iron microbial coupled system in remediating contaminated groundwater[J].China Environmental Science, 2021,41(3):1119-1131.
[23] 孙鸣璐,董军,张梦玥,等.乳化纳米铁(EZVI)强化地下水氯代烃还原脱氯[J].中国环境科学, 2022,42(6):2690-2696.Sun M L, Dong J, Zhang M Y, et al.Enhanced reductive dechlorination of chlorinated hydrocarbons in groundwater by emulsified zero-valent iron[J].China Environmental Science, 2022, 42(6):2690-2696.
[24] GB/T 148482017地下水质量标准[S].GB/T 148482017 Groundwater quality standard[S].
[25] 孙仲平,吴乃瑾,杨苏才,等.微生物降解污染地下水中三氯乙烯的微宇宙试验研究[J].环境工程技术学报, 2021,11(2):298-306.Sun Z P, Wu N J, Yang S C, et al.Microcosm study on the Bioremediation of Trichloroethylene contaminated groundwater[J].Journal of Environmental Engineering Technology, 2021,11(2):298-306.
[26] 吴乃瑾,宋云,魏文侠,等.微米铁复合生物碳源对地下水中1,2-二氯乙烷的高效去除[J].环境科学, 2019,40(3):1302-1309.Wu N J, Song Y, Wei W X, et al.High efficiency removal of 1,2-dichloroethane from groundwater by microscale zero-valent iron combined with biological carbon source[J].Environmental Science, 2019,40(3):1302-1309.
[27] 孙仲平,吴乃瑾,魏文侠,等.电子供体刺激下厌氧微生物对1,2-二氯乙烷的降解效果[J].环境科学研究, 2018,31(8):1431-1438.Sun Z P, Wu N J, Wei W X, et al.Effect of anaerobic microbial degradation of 1, 2-dichloroethane stimulated by electron donor[J].Research of Environmental Sciences, 2018,31(8):1431-1438.
[28] Nobre R C M, Nobre M M M.Natural attenuation of chlorinated organics in a shallow sand aquifer[J].Journal of Hazardous Materials, 2004,110(1):129−137.
[29] Nobre R, Nobre M, Campos T, et al.In-situ biodegradation potential of 1,2-DCA and VC at sites with different hydrogeological settings[J].Journal of Hazardous Materials, 2017,340(1):417-426.
[30] Lee Y C, Kwon T S, Yang J S, et al.Remediation of groundwater contaminated with DNAPLs by biodegradable oil emulsion[J].Journal of Hazardous Materials, 2007,140(1/2):340-345.
[31] Macé C, Desrocher S, Gheorghiu F, et al.Nanotechnology and groundwater remediation:A step forward in technology understanding[J].Remediation Journal, 2010,16(2):23-33.
[32] Wei Y T, Wu S C, Chihming C, et al.Influence of nanoscale zero-valent iron on geochemical properties of groundwater and vinyl chloride degradation:a field case study[J].Water Research, 2010, 44(1):131.
[33] Guan X, Sun Y, Qin H, et al.The limitations of applying zero-valent iron technology in contaminants sequestration and the corresponding countermeasures:The development in zero-valent iron technology in the last two decades (1994~2014)[J].Water Research, 2015,75:224-248.
[34] 陈梦舫,骆永明,宋静,等.场地含水层氯代烃污染物自然衰减机制与纳米铁修复技术的研究进展[J].环境监测管理与技术, 2011, 23(3):85-89.Chen M F, Luo Y M, Song J, et al.Natural attenuation mechanisms and the status of nano-iron technology for the remediation of chlorinated solvents in groundwater[J].The Administration and Technique of Environmental Monitoring, 2011,23(3):85-89.
[35] Zhuang P, Pavlostathis S G.Effect of temperature, pH and electron donor on the microbial reductive dechlorination of chloroalkenes[J].Chemosphere, 1995,31:3537-3548.
[36] Mccarty P L, Chu M Y, Kitanidis P K.Electron donor and pH relationships for biologically enhanced dissolution of chlorinated solvent DNAPL in groundwater[J].European Journal of Soil Biology, 2007,43:276-282.
[37] Molenda O, Quaile A T, Edwards E A.Dehalogenimonas sp.Strain WBC-2genome and identification of its trans-dichloroethene reductive dehalogenase, TdrA[J].Applied & Environmental Microbiology, 2015,82(1):40-50.

基金

国家重点研发计划项目(2018YFC1801400);国家自然科学基金资助项目(41907159);中国博士后科学基金资助项目(2017M610806)

PDF(846 KB)

Accesses

Citation

Detail

段落导航
相关文章

/