Transformations of Carbon and Sulfur Wastewater Components Under Aerobic–Anaerobic Transient Conditions in Sewer Systems

Wastewater quality changes in the carbon and sulfur cycles in pressure sewers and in a gravity sewer that followed a pressure sewer were studied. The primary focus was on changes in chemical oxygen demand (COD) components during transport, which were investigated using oxygen uptake rate measurements and volatile fatty acid analyses. Sulfide formation in the pressure sewers and sulfide oxidation in the gravity sewer were also studied. Anaerobic hydrolysis, which resulted in a net production of readily biodegradable substrate in the pressure sewers, was quantified. A process model description, which included the main aerobic and anaerobic processes in the water phase and in the biofilm, was presented; model parameters were determined based on calibration. This simulation procedure made it possible to consider integrated aspects of hydrogen sulfide and variations in COD components in sewers such as odor and sewer corrosion by hydrogen sulfide and the inadequacy of advanced wastewater treatment because of the input of low-quality wastewater. It is possible to include wastewater quality changes and, thereby, process aspects for sewer design and operation.

[1]  Thorkild Hvitved-Jacobsen,et al.  Wastewater quality changes during transport in sewers — An integrated aerobic and anaerobic model concept for carbon and sulfur microbial transformations , 1998 .

[2]  T. Hvitved-Jacobsen,et al.  Transformations of wastewater organic matter in sewers under changing aerobic/anaerobic conditions , 1998 .

[3]  Thorkild Hvitved-Jacobsen,et al.  Sulfide production and wastewater quality in pressure mains , 1998 .

[4]  Thorkild Hvitved-Jacobsen,et al.  Volatile fatty acids and sulfide in pressure mains , 1995 .

[5]  Per Halkjær Nielsen,et al.  Conceptual Model for Production and Composition of Exopolymers in Biofilms , 1997 .

[6]  T. Hvitved-Jacobsen,et al.  Experimental procedures characterizing transformations of wastewater organic matter in the Emscher river, Germany , 1994 .

[7]  Neil A. Webster,et al.  Odor and corrosion control in sanitary sewerage systems and treatment plants , 1989 .

[8]  B. Teichgräber,et al.  Modeling of aerobic wastewater transformations under sewer conditions in the Emscher River, Germany , 1998 .

[9]  T. Hvitved-Jacobsen,et al.  Influence of oxygen on biofilm growth and potential sulfate reduction in gravity sewer biofilm , 1994 .

[10]  A. E. Greenberg,et al.  Standard methods for the examination of water and wastewater : supplement to the sixteenth edition , 1988 .

[11]  Thorkild Hvitved-Jacobsen,et al.  A Process and Model Concept for Microbial Wastewater Transformations in Gravity Sewers , 1998 .

[12]  Willi Gujer,et al.  Estimation of kinetic parameters of heterotrophic biomass under aerobic conditions and characterization of wastewater for activated sludge modeling , 1992 .

[13]  Niels Aagaard Jensen Empirical modeling of air-to-water oxygen transfer in gravity sewers , 1995 .

[14]  W. Gujer,et al.  Activated sludge model No. 3 , 1995 .

[15]  Thorkild Hvitved-Jacobsen,et al.  Effect of Sulfate and Organic Matter on the Hydrogen Sulfide Formation in Biofilms of Filled Sanitary Sewers , 1988 .

[16]  R. Reid,et al.  The Properties of Gases and Liquids , 1977 .