Catchment & sewer network simulation model to benchmark control strategies within urban wastewater systems

https://doi.org/10.1016/j.envsoft.2015.12.013Get rights and content

Highlights

  • Plant-wide Benchmark simulation model is extended to include the catchment and sewer system.

  • The extended model describes the generation and transport of wastewater.

  • New evaluation criteria are defined for benchmarking control strategies/structural modifications.

  • Case studies depicting the usefulness/application of the model are performed.

Abstract

This paper aims at developing a benchmark simulation model to evaluate control strategies for the urban catchment and sewer network. Various modules describing wastewater generation in the catchment, its subsequent transport and storage in the sewer system are presented. Global/local overflow based evaluation criteria describing the cumulative and acute effects are presented. Simulation results show that the proposed set of models is capable of generating daily, weekly and seasonal variations as well as describing the effect of rain events on wastewater characteristics. Two sets of case studies explaining possible applications of the proposed model for evaluation of: 1) Control strategies; and, 2) System modifications, are provided. The proposed framework is specifically designed to allow for easy development and comparison of multiple control possibilities and integration with existing/standard wastewater treatment models (Activated Sludge Models) to finally promote integrated assessment of urban wastewater systems.

Introduction

It has become increasingly clear that wastewater treatment plants (WWTPs) are strongly interconnected to other elements (sewer network, receiving media) within the urban wastewater system (UWS) and the evaluation of WWTP control strategies should be tackled in a more holistic manner (Rauch et al., 2002, Bach et al., 2014). For this reason, there is a need to move “outside the fence” of the WWTP and develop integrated tools for model-based evaluation and control of the UWS (Benedetti et al., 2013). This goal has inspired a large number of scientific contributions that attempt to investigate different aspects of integrated modelling. For example, Benedetti et al. (2004) and Vanrolleghem et al. (2005) tackled important issues such as model integration and model compatibility. Another important aspect has been model complexity reduction to allow for long term simulations (Erbe and Schütze, 2005, Fu et al., 2009a). The latter and the increase in computational power promoted the use of Monte Carlo simulations and the study of input uncertainty propagation through the model either during the model development process or during model use (e.g. Astaraie-Imani et al., 2012, Benedetti et al., 2008, Benedetti et al., 2010, Freni et al., 2011, Fu et al., 2009b). Long term simulations can be conducted as well, including the study of integrated control (e.g. Fu and Butler, 2012, Weijers et al., 2012). Finally, studies of the fate of particular compounds such as sulfur compounds (Jiang et al., 2010), greenhouse gas emissions (Guo et al., 2012) and micro-pollutants (Vezzaro et al., 2014, Snip et al., 2014) were also performed.

One of the major areas of application for integrated models is control. Integrated control has been studied for some years and the main benefits of using such an approach are demonstrated in several studies (e.g. Harremoës et al., 1994, Schütze et al., 2002, Vanrolleghem et al., 2005, Langeveld et al., 2013). With the future clearly pointing towards integrated management of the UWS, the need for development of efficient integrated control strategies is growing. In this context, we believe that a benchmarking tool can be extremely beneficial to develop and test control strategies in the UWS. Within sewer systems, Borsányi et al. (2008) conducted a benchmarking study using real-time control strategies applied to two virtual sewer systems. In the WWTP community, benchmarking control strategies has been very successful. Benchmark Simulation Models (BSM1, BSM1-LT and BSM 2) and associated spin-off products (influent generator, ADM1 implementation, sensor models, evaluation criteria etc.) have demonstrated to be valuable tools in the field of WWTP optimization and have been widely used in both industry and academia (Gernaey et al., 2014). Nevertheless, there is a lack of benchmarking tools that allow objective comparison of control strategies in urban catchments and sewer systems. Therefore: 1) Rigorous development/evaluation of control strategies in the WWTP (Gernaey et al., 2014) is based on influent generators (Gernaey et al., 2011, Flores-Alsina et al., 2014, Martin and Vanrolleghem, 2014), and such influent generators are not suitable for modelling control strategies upstream of the WWTP; and, 2) In many cases, integrated UWS control strategies cannot be developed and evaluated on a single simulation platform.

The objective of this paper is to develop a catchment and sewer network model to benchmark control strategies. The catchment model reproduces the generation of wastewater through the combination of four different sub-models (Domestic (DOM), Industrial (IND), Stormwater (SW) and Infiltration to sewers (INF)). The sewer model describes wastewater transport (TRANSPORT) as well as the sudden increase of particulates during the beginning of a rain event following a period of drought (FIRST FLUSH) and the retention of wastewater (especially during rain events) using storage tanks to avoid combined sewer overflows (STORAGE). A set of evaluation criteria are used to assess the overflow discharged into the receiving waters. The criteria can be applied for a specific overflow location (Local) or for the entire system (Global). The criteria can be further classified into those describing: 1) cumulative effects; and, 2) acute effects on the receiving water system. As a receiving water model is not used in this study, these criteria are only indirect indicators of the effect of overflow discharges on river systems. Additionally, case studies demonstrating the possible applications of the tool for analysing the impact of: 1) local/global control strategies; and, 2) system modifications, are presented and discussed in detail. The proposed framework is specifically designed to allow for development and comparison of multiple control strategies, and allows easy interfacing with existing wastewater treatment (benchmark) models to finally promote integrated assessment of catchment, sewer network and WWTP performance.

Section snippets

System characteristics and general model description

A hypothetical system with a similar structure as the catchment described in ATV A 128 (ATV, 1992) is used as a case study. Fig. 1 illustrates the catchment configuration and its main characteristics. The total catchment area (Ac) is 540 ha and comprises 80,000 population equivalents (PEc). Dry weather flow is scaled up to be similar to the BSM2 influent characteristics (18,500 m3/d) (Gernaey et al., 2014). The three main contributors to dry weather flow are: 1) domestic sources with a daily

Catchment model

The catchment model is largely inspired by the BSM2 dynamic influent pollutant disturbance scenario generator (DIPDSG) (Gernaey et al., 2011) and uses many of its salient model blocks for simulating the dynamics of flow rate and pollutant load generation. The generation of wastewater at each sub-catchment (SCi) is achieved by combining the contributions from: 1) domestic (DOMi); 2) industry (INDi); 3) infiltration to sewers (INFi); and, 4) stormwater (SWi). The pollutants considered are

Sewer network model

The sewer model is comprised of three different elements: 1) a transport sub-model (TRANSPORT) to describe the effect of the sewer system on both flow rate and pollutants; 2) a first flush sub-model (FIRST FLUSH) mimicking the sudden increase of particulates at the beginning of rain events following a period of drought; and, 3) different types of storage tank sub-models (STORAGE) acting as buffers to prevent discharge of rainwater into rivers during rain events. These three sub-models are used

Evaluation criteria

The following evaluation criteria are used for studying the behaviour of the system and the effects of various control strategies/system modifications on its performance. The evaluation considers various overflow locations in the sewer system and also the overflow at the WWTP bypass. Subscript “i” denotes the criteria for a specific overflow location.

  • 1.

    Yearly overflow frequency (Novf,i) (events/year): The total number of overflow events per year occurring at a given overflow location. Two

Case studies

This section presents simulation results from implementing different scenarios using the catchment and sewer network model (see Table 3). The evaluated control alternatives employ storage tanks as control handles. The control actuators are generally valves/gates/pumps that regulate the outflow from these storage tanks. Examples of the evaluation of both local and global (sewer & catchment system) control strategies are presented here. The strategies are:

  • Reducing the bypass at the WWTP (C1);

Discussion

The catchment and sewer extension to the BSM WWTP model has been described in detail in this paper. The model has successfully described the dynamics of wastewater generation from various sources (domestic, industrial) during dry weather and rain periods. Additionally, infiltration to the sewers is also included. A sewer network model that can simulate the transport of the generated wastewater has been implemented. The model can also describe the first flush of the particulate (sewer)

Conclusions

The presented model will enable practitioners/researchers to evaluate integrated control strategies/structural modifications (within catchment and sewer system) using overflow based evaluation criteria. The key findings of the presented study can be summarized in the following points:

  • 1)

    The catchment model is capable of generating (dry/wet weather) flow rate and pollution loads (soluble/particulate) through the combination of four different sub-models (DOM, IND, INF, SW). These sub-models

Acknowledgements

Dr. Flores-Alsina and Mr. Saagi gratefully acknowledge the financial support provided by the People Program (Marie Curie Actions) of the European Union's Seventh Framework Programme FP7/2007–2013 under REA agreement 329349 (PROTEUS) and 289193 (SANITAS) respectively. The authors gratefully acknowledge the feedback provided by Professor Peter A. Vanrolleghem, Canada Research Chair in Water Quality Modelling, Université Laval, Quebec, Canada during the development of the model.

References (45)

  • C. Martin et al.

    Analysing, completing, and generating influent data for WWTP modelling: a critical review

    Environ. Model. Soft.

    (2014)
  • L.J.P. Snip et al.

    Modelling the occurrence, transport and fate of pharmaceuticals in wastewater systems

    Environ. Model. Soft.

    (2014)
  • M. Talebizadeh et al.

    Influent generator for probabilistic modeling of nutrient removal wastewater treatment plants

    Environ. Model. Soft.

    (2016)
  • P. Vanrolleghem et al.

    Modelling and real-time control of the integrated urban wastewater system

    Env. Mod. Soft.

    (2005)
  • L. Vezzaro et al.

    A model library for dynamic transport and fate of micropollutants in integrated urban wastewater and stormwater systems

    Environ. Model. Soft.

    (2014)
  • E.I.P. Volcke et al.

    Continuity-based model interfacing for plant-wide simulation: a general approach

    Wat. Res.

    (2006)
  • ATV

    A 128-Richtlinien für die Bemessung und Gestaltung von Regenentlastungsanlagen in Mischwasserkanälen

    (1992)
  • L. Benedetti et al.

    Probabilistic modelling and evaluation of wastewater treatment plant upgrades in a water quality based evaluation context

    J. Hydr-inf.

    (2010)
  • L. Benedetti et al.

    Modelling and monitoring of integrated urban wastewater systems: review on status and perspectives

    Wat. Sci. Tech.

    (2013)
  • L. Benedetti et al.

    Model Connectors for Integrated Simulations of Urban Wastewater Systems. Sewer Networks and Processes within Urban Water Systems

    (2004)
  • P. Borsányi et al.

    Modelling real time control options on benchmark sewer systems

    J. Env. Eng. Sci.

    (2008)
  • D. Butler et al.

    Urban Drainage

    (2011)
  • Cited by (30)

    • Dynamic control of urban sewer systems to reduce combined sewer overflows and their adverse impacts

      2019, Journal of Hydrology
      Citation Excerpt :

      Nevertheless, structural measures are still used when the space and financial capacities are permitted (Nasri and Haynes, 2015). Even though, the non-structural measures are used to overcome the issues from CSOs, multiple interactions in various sub-systems such as, catchments, sewer systems, wastewater treatment plant and receiving water bodies make the control of urban wastewater system a greater challenge (Saagi et al., 2016, 2018). In addition, the dynamic behavior of flow and wastewater quality in sewer systems make the scenario more complex (Rathnayake and Tanyimboh, 2015).

    • Population mobility and urban wastewater dynamics

      2018, Science of the Total Environment
    View all citing articles on Scopus
    View full text