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contributor authorMaria José Farré
contributor authorBonnie Lyon
contributor authorGlen A. de Vera
contributor authorDaniel Stalter
contributor authorWolfgang Gernjak
date accessioned2017-12-30T12:54:26Z
date available2017-12-30T12:54:26Z
date issued2016
identifier other%28ASCE%29EE.1943-7870.0001022.pdf
identifier urihttp://138.201.223.254:8080/yetl1/handle/yetl/4243228
description abstractAdsorbable organic halogens (AOX) were measured at the outlet (AOXo) and after 24 h contact time with residual disinfectant (AOX24  h) for 10 samples obtained from 7 drinking water treatment plants (WTPs) that employ chlorine-based disinfectants. AOXo ranged from 0.75 to 7.60 μM (26.2–266.0  μg Cl/L) and increased by up to 170% after 24 h contact time. The results were also compared with AOX formation potential (AOXFP) measured in the laboratory for the samples collected prior to disinfection at the same WTPs. In general, AOX24  h and AOXFP values varied by less than ±20%. A suite of disinfection byproducts (DBPs) were individually measured to elucidate the AOX composition. Trihalomethanes and haloacetic acids explained the largest fraction of AOX; however, the percentage of AOX not accounted for by measured DBPs varied greatly between samples (14.5–62.0%). Additionally, the fate of AOXFP was assessed across the seven WTPs. On average, coagulation removed 67±7% of AOXFP across the WTPs, while dual media filtration did not substantially remove AOXFP. The effect of ozone on AOXFP varied between WTPs, while biological activated carbon filtration removed 33±13% AOXFP. The ratio of known versus unknown AOXFP did not change across the WTPs.
publisherAmerican Society of Civil Engineers
titleAssessing Adsorbable Organic Halogen Formation and Precursor Removal during Drinking Water Production
typeJournal Paper
journal volume142
journal issue3
journal titleJournal of Environmental Engineering
identifier doi10.1061/(ASCE)EE.1943-7870.0001022
page04015087
treeJournal of Environmental Engineering:;2016:;Volume ( 142 ):;issue: 003
contenttypeFulltext


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