Continuous-flow laboratory simulation of stream water quality changes downstream of an untreated wastewater discharge.
| dc.contributor.author | Finnegan, Chris J. | - |
| dc.contributor.author | van Egmond, R. A. | - |
| dc.contributor.author | Price, O. R. | - |
| dc.contributor.author | Whelan, M. J. | - |
| dc.date.accessioned | 2012-05-31T23:04:48Z | |
| dc.date.available | 2012-05-31T23:04:48Z | |
| dc.date.issued | 2009-04-01T00:00:00Z | - |
| dc.description.abstract | In regions of the world with poor provision of wastewater treatment, raw sewage is often discharged directly into surface waters. This paper describes an experimental evaluation of the fate of two organic chemicals under these conditions using an artificial channel cascade fed with a mix of settled sewage and river water at its upstream end and operated under continuous steady-state conditions. The experiments underpin an environmental risk assessment methodology based on the idea of an “impact zone” (IZ) – the zone downstream of wastewater emission in which water quality is severely impaired by high concentrations of unionised ammonia, nitrite and biochemical oxygen demand (BOD). Radiolabelled dodecane-6-benzene sulphonate (DOBS) and aniline hydrochloride were used as the model chemical and reference compound respectively. Rapid changes in 14C counts were observed with flow-time for both these materials. These changes were most likely to be due to complete mineralisation. A dissipation half-life of approximately 7.1 h was observed for the 14C label with DOBS. The end of the IZ was defined as the point at which the concentration of both unionised ammonia and nitrite fell below their respective predicted no-effect concentrations for salmonids. At these points in the cascade, approximately 83 and 90% of the initial concentration of 14C had been removed from the water column, respectively. A simple model of mineral nitrogen transformations based on Michaelis–Menten kinetics was fitted to observed concentrations of NH4, NO2 and NO3. The cascade is intended to provide a confirmatory methodology for assessing the ecological risks of chemicals under direct discharge con | en_UK |
| dc.identifier.citation | C.J. Finnegan, R.A. van Egmond, O.R. Price, M.J. Whelan, Continuous-flow laboratory simulation of stream water quality changes downstream of an untreated wastewater discharge, Water Research, Volume 43, Issue 7, April 2009, Pages 1993-2001 | - |
| dc.identifier.issn | 0043-1354 | - |
| dc.identifier.uri | http://dx.doi.org/10.1016/j.watres.2009.01.031 | - |
| dc.identifier.uri | http://dspace.lib.cranfield.ac.uk/handle/1826/3462 | |
| dc.language.iso | en_UK | - |
| dc.publisher | Elsevier Science B.V., Amsterdam. | en_UK |
| dc.subject | Direct discharge | en_UK |
| dc.subject | LAS | en_UK |
| dc.subject | Degradation | en_UK |
| dc.subject | Laboratory simulation study | en_UK |
| dc.subject | Ammonia | en_UK |
| dc.subject | Nitrite | en_UK |
| dc.subject | River | en_UK |
| dc.title | Continuous-flow laboratory simulation of stream water quality changes downstream of an untreated wastewater discharge. | en_UK |
| dc.type | Article | - |