Abstract

Experiments focused on pollution transport and dispersion phenomena in conditions of low flow (low water depth and velocities) in sewers with bed sediment and deposits are presented. Such conditions occur very often in sewer pipes during dry weather flows. Experiments were performed in laboratory conditions. To simulate real hydraulic conditions in sewer pipes, sand of fraction 0.6–1.2 mm was placed on the bottom of the pipe. In total, we performed 23 experiments with 4 different thicknesses of sand sediment layers. The first scenario is without sediment, the second is with sediment filling 3.4% of the pipe diameter (sediment layer thickness = 8.5 mm), the third scenario represents sediment filling 10% of the pipe diameter (sediment layer thickness = 25 mm) and sediment fills 14% of the pipe diameter (sediment layer thickness = 35 mm) in the last scenario. For each thickness of the sediment layer, a set of tracer experiments with different flow rates was performed. The discharge ranges were from (0.14–2.5)·10−3 m3·s−1, corresponding to the range of Reynolds number 500–18,000. Results show that in the hydraulic conditions of a circular sewer pipe with the occurrence of sediment and deposits, the value of the longitudinal dispersion coefficient Dx decreases almost linearly with decrease of the flow rate (also with Reynolds number) to a certain limit (inflexion point), which is individual for each particular sediment thickness. Below this limit the value of the dispersion coefficient starts to rise again, together with increasing asymmetricity of the concentration distribution in time, caused by transient (dead) storage zones.

Highlights

  • Transport of substances in flowing water is in principle the result of two basic phenomena: advection and dispersion

  • Results show that in the hydraulic conditions of a circular sewer pipe with the occurrence of sediment and deposits, the value of the longitudinal dispersion coefficient Dx decreases almost linearly with decrease of the flow rate to a certain limit, which is individual for each particular sediment thickness

  • The peak velocity up was used for the dispersion coefficient evaluation according to Equations (3)–(5) and the centroid velocity uc was used for determination of all other parameters

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Summary

Introduction

Transport of substances in flowing water is in principle the result of two basic phenomena: advection and dispersion. For example, longitudinal dispersion causes the decrease of pollution concentration and its distribution in time. Special situations occur very often in real sewer systems at time of low flows during dry weather periods. Flow in such sewer systems can be characterised with specific hydraulic conditions: low discharges (especially during night-time) and sediment and deposit formation. Sediments on the pipe bottom change the pipe (streambed) hydraulic roughness, but in cases of the same discharge cause a reduction in flow depth [1], which leads to flow with low Reynolds numbers, i.e., close to the laminar flow regime. There is a need to improve dispersion models with regard to the specific hydraulic conditions in partially filled sewer pipes with free surface flow, respecting real conditions (sediment occurrence)

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