The abiotic natural attenuation of 1,2-dibromoethane mediated by FeS
GU Chun-yun1, LIAO Gao-ming2, DENG Yi-rong2, MA Jie1
1. State Key Laboratory of Heavy Oil Processing, Beijing Key Lab of Oil & Gas Pollution Control, College of Chemical Engineering and Environment, China University of Petroleum-Beijing, Beijing 1022494, China; 2. Guangdong Provincial Key Laboratory of Environmental Management and Remediation of Contaminated Sites, Guangdong-Hong Kong-Macao Environmental Quality Collaborative Innovation Laboratory, Guangdong Provincial Academy of Environmental Science, Guangzhou 510045, China
Abstract:The reduction degradation of 1,2-dibromoethane (EDB) by FeS in anaerobic environment was studied. The experimental data showed that FeS could effectively degrade EDB under anaerobic conditions. The degradation reaction conformed to the pseudo-first-order reaction kinetics. The corrected kobs value was (0.065±0.003) d-1 (R2=0.91). The degradation half-life was 11days. FeS were characterized by BET, X-ray photoelectron spectroscopy (XPS), X-ray diffraction (XRD) and scanning electron microscope-energy spectroscopy (SEM-EDS). The results showed that FeS had a large specific surface area, which increased the number of reaction sites and thus enhanced the reduction degradation of EDB by FeS. In addition, FeS transformed to goethite and greigite during the reduction reaction. The degradation rate of EDB increased with increases in concentrations of sulfide (HS-) and FeS. At high pH, the reduction degradation of EDB by FeS was faster. In addition, the presence of transition metal ions Co2+ and Cu2+ could promote the degradation of EDB by FeS, while the presence of Mn2+ could inhibit the degradation of EDB. In general, the presence of FeS in the ground can achieve abiotic natural attenuation of EDB in EDB-contaminated groundwater sites.
Falta R W. The potential for ground water contamination by the gasoline lead scavengers ethylene dibromide and 1,2-dichloroethane[J]. Ground Water Monitoring and Remediation, 2004,24(3):76-87.
[2]
Falta R W, Bulsara N, Henderson J K, et al. Leaded gasoline additives still contaminate groundwater[J]. Environmental Science & Technology, 2005,39:378A-384A.
[3]
康晓钧,姜月华,李云,等.苏南某市A1加油站渗漏污染特征及启示[J]. 地下水, 2013,35(3):65-68. Kang X Y, Jiang Y H, Li Y, et al. Characteristics and implications of leakage pollution of A1gas station in a city of southern Jiangsu Province[J]. Groundwater, 2013,35(3):65-68.
[4]
Ma J, Li H, Spiese R, et al. Vapor intrusion risk of lead scavengers 1,2-dibromoethane (EDB) and 1,2-dichloroethane (DCA)[J]. Environmental Pollution, 2016,213:825-832.
[5]
马欣程,徐红霞,孙媛媛,等.氯代烃污染场地生物自然衰减修复研究进展[J]. 中国环境科学, 2022,42(11):5285-5298. Ma X C, Xu H X, Sun Y Y, et al. Research progress on biotic natural attenuation for the remediation of chlorinated hydrocarbon-contaminated sites[J]. China Environmental Science, 2022,42(11):5285-5298.
[6]
Aulenta F, Majone M, Tandoi V. Enhanced anaerobic bioremediation of chlorinated solvents:environmental factors influencing microbial activity and their relevance under field conditions[J]. Journal of Chemical Technology & Biotechnology, 2006,81:1463-1474.
[7]
Frascari D, Zanaroli G, Danko A S. In situ aerobic cometabolism of chlorinated solvents:a review[J]. Journal of Hazardous Materials, 2015,283:382-399.
[8]
Brown R A, Wilson J T, Ferrey M. Monitored natural attenuation forum:The case for abiotic MNA[J]. Remediation Journal, 2007, 17:127-137.
[9]
He Y T, Wilson J T, Su C, et al. Review of abiotic degradation of chlorinated solvents by reactive iron minerals in aquifers[J]. Groundwater Monitoring & Remediation, 2015,35(3):57-75.
[10]
Lan Y, Elwood Madden A S, Butler E C. Transformation of mackinawite to greigite by trichloroethylene and tetrachloroethylene[J]. Environmental Science Processes & Impacts, 2016,18:1266-1273.
[11]
Jeong H Y, Hayes K F. Impact of transition metals on reductive dechlorination rate of hexachloroethane by mackinawite[J]. Environmental Science & Technology, 2003,37(20):4650-4655.
[12]
Butler E C, Hayes K F. Kinetics of the transformation of trichloroethylene and tetrachloroethylene by iron sulfide[J]. Environmental Science & Technology, 1999,33(12):2021-2027.
[13]
Butler E C, Hayes K F. Effects of Solution Composition and pH on the reductive dechlorination of hexachloroethane by iron sulfide[J]. Environmental Science & Technology, 1998,32(9):1276-1284.
[14]
Choi J, Choi K, Lee W. Effects of transition metal and sulfide on the reductive dechlorination of carbon tetrachloride and 1,1,1-trichloroethane by FeS[J]. Journal of Hazardous Materials, 2009,162:1151-1158.
[15]
廖高明,马杰,谷春云,等.污染场地卤代烃非生物自然衰减研究进展[J]. 环境科学研究, 2021,34:742-754. Liao G M, Ma J, Gu C Y, et al. Research progress on abiotic natural attenuation of halogenated hydrocarbons at contaminated sites[J]. Research of Environmental Sciences, 2021,34:742-754.
[16]
BUTLER E C, HAYES K F. Factors influencing rates and products in the transformation of trichloroethylene by iron sulfide and iron metal[J]. Environ. Sci. Technol, 2001,35:3884-3891.
[17]
Butler E C, Hayes K F. Kinetics of the transformation of halogenated aliphatic compounds by iron sulfide[J]. Environmental Science & Technology, 2000,34(3):422-429.
[18]
Jeong H Y, Hayes K F. Reductive dechlorination of tetrachloroethylene and trichloroethylene by mackinawite (FeS) in the presence of metals:Reaction rates[J]. Environmental Science & Technology, 2007, 41(18):6390-6396.
[19]
Lee W, Batchelor B. Abiotic reductive dechlorination of chlorinated ethylenes by iron-bearing soil minerals. 2. Green rust[J]. Environmental Science & Technology, 2002,36(24):5348-5354.
[20]
Pham H T, Suto K, Inoue C. Trichloroethylene transformation in aerobic pyrite suspension:Pathways and kinetic modeling[J]. Environmental Science & Technology, 2009,43(17):6744-6749.
[21]
Herbert Jr R B, Benner S G, Pratt A R, et al. Surface chemistry and morphology of poorly crystalline iron sulfides precipitated in media containing sulfate-reducing bacteria[J]. Chemical Geology, 1998,144:87-97.
[22]
Mullet M, Boursiquot S, Abdelmoula M, et al. Surface chemistry and structural properties of mackinawite prepared by reaction of sulfide ions with metallic iron[J]. Geochimica et Cosmochimica Acta, 2002, 66(5):829-836.
[23]
Amir A, Lee W. Enhanced reductive dechlorination of tetrachloroethene during reduction of cobalamin (III) by nano-mackinawite[J]. Journal of Hazardous Materials, 2012,235:359-356.
[24]
He Y T, Wilson J T, Wilkin R T. Impact of iron sulfide transformation on trichloroethylene degradation[J]. Geochimica et Cosmochimica Acta, 2010,74:2025-2039.
[25]
Lan Y, Butler E C. Iron-sulfide-associated products formed during reductive dechlorination of carbon tetrachloride[J]. Environmental Science & Technology, 2016,50:5489-5497.
[26]
Hanoch R J, Shao H, Butler E C. Transformation of carbon tetrachloride by bisulfide treated goethite, hematite, magnetite, and kaolinite[J]. Chemosphere, 2006,63:323-34.
[27]
Hassan S M. Reduction of halogenated hydrocarbons in aqueous media:I. Involvement of sulfur in iron catalysis[J]. Chemosphere, 2000,40:1357-1363.
[28]
Kim E J, Kim J H, Chang Y S, et al. Effects of metal ions on the reactivity and corrosion electrochemistry of Fe/FeS nanoparticles[J]. Environmental Science & Technology, 2014,48:4002-4011.
[29]
Jeong H Y, Anantharaman K, Hyun S P, et al. pH impact on reductive dechlorination of cis-dichloroethylene by Fe precipitates:an X-ray absorption spectroscopy study[J]. Water Research, 2013,47:6639-6649.
[30]
Danielsen K M, Hayes K F. pH dependence of carbon tetrachloride reductive dechlorination by magnetite[J]. Environmental Science & Technology, 2004,38(18):4745-4752.