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1.2- Dibromoethane degradation

Poelarends GJ, JET van Hylckama Vlieg, JR Marches , LM Freitas dos Santos, DB Janssen (1999) Degradation of 1,2-dibromoethane hy Mycobacterium sp. strain GPL J Bacteriol 181 2050-2058. [Pg.86]

Biotic and abiotic degradation of 1,2-dibromoethane in surface waters is slow relative to volatilization of the compound to the atmosphere (ERA 1987b). 1,2- Dibromoethane is resistant to hydrolysis (Jaber et al. 1984) the hydrolytic half-life of the compound has been reported to range from 2.5 years (Vogel and Reinhard 1982) to 13.2 years (HSDB 1989). As a result of its hydrolytic stability and the limited biological activity in subsurface soils, 1,2- dibromoethane leached to groundwater is expected to persist for years. [Pg.93]

Lai M, Monig J, Asmus K-D. 1986. Free radical induced degradation of 1,2-dibromoethane. Generation of free Br atoms. Free Rad Res Comms 1 235-241. [Pg.123]

Pignatello JJ. 1987. Microbial degradation of 1,2-dibromoethane in shallow aquifer materials. J Environ Qual 16 307-312. [Pg.128]

Guengerich, F.P. (1994) Metabolism and genotoxicity of dihaloalkanes. Adv. Pharmacol., 27,211-236 Guha, S.N., Schoneich, C. Asmus, K.D. (1993) Free radical reductive degradation of vic-dibromoalkanes and reaction of bromine atoms with polyunsaturated fatty acids possible involvement of Br(.) in the 1,2-dibromoethane-induced lipid peroxidation. Arch. Biochem. [Pg.664]

Vinyl bromide may form in air as a degradation product of 1,2-dibromoethane. It may also be released to the environment from facilities which manufacture or use vinyl bromide as a flame retardant for acrylic fibres. Vinyl bromide has been qualitatively identified in ambient air samples (United States National Library of Medicine, 1998a)... [Pg.924]

What Products Do You Expect from Microbial Degradation of 1,2-Dibromoethane (EDB )... [Pg.710]

The bacterial population was apparently already adapted to some of the compounds such as phenol, 4-chlorophenol, and 1,2-dibromoethane at the start of the experiment, and these substrates were therefore rapidly degraded. [Pg.340]

Freitas dos Santos, L.M., D.J. Leak, and A.G. Livingstone. 1996. Enrichment of mixed cultures capable of aerobic degradation of 1,2-dibromoethane. Appl. Environ. Microbiol. 62 4675-4677. [Pg.856]

Weintraub, R.A. Jex, G.W. Moye, H.A. "Degradation of 1,2-Dibromoethane in Florida Ground Water and Soil, American Chemical Society 189th National Meeting, PEST 110, Florida, 1985. [Pg.196]

Table 2.8 compares hydrolysis half-lives with half-lives for reaction with sulfur-based nucleophiles for several halogenated aliphatics. These data show that the environmental half-lives for substrates such as 1-bromohexane and 1,2-dibromoethane can be substantially reduced in the presence of HS and polysulfides. Enhanced degradation of 2-bromopropane and 1,1,1-trichloroethane, as well as chloroform and carbon tetrachloride (results not shown) was not observed, suggesting that steric hindrance significantly impedes reaction with the sulfur based nucleophiles (Haag and Mill, 1988a). [Pg.141]

Weintraub RA, Jex GW, Moye HA (1986). Chemical and microbial degradation of 1,2-dibromoethane (EDB) in Florida ground water, soil, and sludge. In Evaluation of Pesticides in Ground Water (eds. WY Garner, RC Honeycutt, HN Nigg). Washington, DC ... [Pg.535]

Pignatello, J.J. Microbial Degradation of 1,2-Dibromoethane in Shallow Aquifer Materials, J. Environ. Qual, 16(4) 307-312 (1987). [Pg.288]


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