4.8 Article

Fate of 1,4-dioxane in the aquatic environment: From sewage to drinking water

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WATER RESEARCH
卷 48, 期 -, 页码 406-419

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PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.watres.2013.09.057

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1,4-Dioxane; Bank filtration; Drinking water; Surface water; Effluent; SPE

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Potential health effects of 1,4-dioxane and the limited data on its occurrence in the water cycle command for more research. In the current study, mobility and persistence of 1,4-dioxane in the sewage-, surface-, and drinking water was investigated. The occurrence of 1,4-dioxane was determined in wastewater samples from four domestic sewage treatment plants (STP). The influent and effluent samples were collected during weekly campaigns. The average influent concentrations in all four plants ranged from 262 +/- 32 ng L-1 to 834 +/- 480 ng L-1, whereas the average effluent concentrations were between 267 +/- 35 ng L-1 and 62,260 +/- 36,000 ng L-1. No removal of 1,4-dioxane during water treatment was observed. Owing to its strong internal chemical bonding, 1,4-dioxane is considered non-biodegradable under conventional bio-treatment technologies. The source of increased 1,4-dioxane concentrations in the effluents was identified to originate from impurities in the methanol used in the postanoxic denitrification process in one of the STPs. In view of poor biodegradation in STPs, surface water samples were collected to establish an extent of 1,4-dioxane pollution. Spatial and temporal distribution of 1,4-dioxane in the Rivers Main, Rhine, and Oder was examined. Concentrations reaching 2200 ng L-1 in the Oder River, and 860 ng L-1 in both Main and Rhine River were detected. The average monthly load of 1,4-dioxane in the Rhine River was calculated to equal to 172 kg d(-1). In all rivers, concentration of 1,4-dioxane increased with distance from the spring and was found to negatively correlate with the discharge of the river. Additionally, bank filtration and drinking water samples from two drinking water facilities were analyzed for the presence of 1,4-dioxane. The raw water contained 650 ng L-1-670 ng L-1 of 1,4-dioxane, whereas the concentration in the drinking water fell only to 600 ng L-1 and 490 ng L-1, respectively. Neither of the purification processes employed was able to reduce the presence of 1,4-dioxane below the precautionary guideline limit of 100 ng L-1 set by the German Federal Environmental Agency. (C) 2013 Elsevier Ltd. All rights reserved.

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