Volatile chloro‐ and bromocarbons in coastal waters1

Contaminated coastal waters can contain nanomolar levels of C 1 and C 2 halocarbons originating through in situ synthesis from chlorine and through waste discharge. Haloforms are the major volatile products formed from chlorine. In freshwaters, CHCl 3 dominates with lesser amounts of CHBr 3 and the...

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Bibliographic Details
Published in:Limnology and Oceanography
Main Authors: Helz, George R., Hsu, Rong Y.
Format: Article in Journal/Newspaper
Language:English
Published: Wiley 1978
Subjects:
Online Access:http://dx.doi.org/10.4319/lo.1978.23.5.0858
https://api.wiley.com/onlinelibrary/tdm/v1/articles/10.4319%2Flo.1978.23.5.0858
https://aslopubs.onlinelibrary.wiley.com/doi/pdf/10.4319/lo.1978.23.5.0858
Description
Summary:Contaminated coastal waters can contain nanomolar levels of C 1 and C 2 halocarbons originating through in situ synthesis from chlorine and through waste discharge. Haloforms are the major volatile products formed from chlorine. In freshwaters, CHCl 3 dominates with lesser amounts of CHBr 3 and the mixed Cl–Br haloforms; however, above about 5 g · kg −1 salinity, CHBr 3 is virtually the only product when typical chlorine doses (10–100 µ M) are used. On a molar basis, >4% conversion of chlorine to haloforms was observed in some experiments. Samples from the Back River estuary (Maryland), which receives effluent from a very large urban wastewater treatment plant, contained CH 2 Cl 2 , CHCl 3 , CCl 4 , CCl 2 = CHCl, and CCl 2 =CCl 2 at concentrations exceeding 1 nM. Even when winter ice cover minimized loss by volatilization, downstream mixing was nonconservative, suggesting that chemical or biological degradation processes occur. Under normal circumstances, however, volatilization followed by chemical degradation in the atmosphere is probably the most important loss mechanism. Data on possible biologic effects of these compounds are critically needed.