Mixing effects in the river downstream from pollution discharge point

Author:

Bielski Andrzej1ORCID

Affiliation:

1. Department of Water Supply, Sewerage and Environmental Monitoring, Faculty of Environmental Engineering, Cracow University of Technology

Abstract

This paper follows the propagation of pollution in a river with a rectangular cross-section of the river bed and a variable cross-sectional velocity. The calculations were made for steady flows and steady pollutant concentrations. To approximate the velocity distribution in the river bed a set of equations for current and vorticity functions was solved. The distribution of pollutant concentrations in the river was calculated from a bidirectional advection and turbulent diffusion equation. Analysis of the distribution of concentrations leads to the conclusion that the effects of transverse advection associated with a lateral inflow of pollutants disappear relatively quickly. Therefore, the distribution of concentrations in cross sections further downstream from the point of pollutant discharge can be determined quite accurately just from an advection-diffusion model, with no transverse advection effects included. Such a level of accuracy is usually sufficient to assess the impact of a pollution source on the aquatic environment. The transverse mixing of pollutants in the stream proceeds slowly and creates a large mixing zone in which the concentrations of pollutants (low but still significant for water quality) can be detected in cross-sections that are remote from the pollutant discharge point. Transverse advection may be ignored while calculating concentrations in remote cross sections at straight watercourse sections and in steady state conditions.

Publisher

Cracow University of Technology

Reference23 articles.

1. Bielski, A. (2003). Advection with two-way dispersion of pollutants in unsteady state in water environment. Technical Transactions, 3: 347–373.

2. Bielski, A. (2012a). Advection transport of river pollutants with bidirectional diffusion in the plane perpendicular to the direction of flow. Ochrona Środowiska, 34(2): 19–24.

3. Bielski, A. (2012b). Transport of pollutants in a the river with bi-directional diffusion. Engineering and Protection of Environment, 15(3): 307–332.

4. Ceka, A. (2011). Water framework directive and mixing zone guidelines, Swedish University of Agricultural Sciences, Faculty of Natural Resources and Agricultural Sciences, Department of Aquatic Sciences and Assessment, Uppsala.

5. CORMIX2 (December 1991). An Expert system for hydrodynamic mixing zone analysis of conventional and toxic multiport diffuser discharges, EPA/600/3-91/073.

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