Abstract:During the design of a water resource recovery facility, it is becoming industry practice to use simulation software to assist with process design. Aeration is one of the key components of the activated sludge process, and is one of the most important aspects of modelling wastewater treatment systems. However, aeration systems are typically not modelled in detail in most wastewater treatment process modelling studies. A comprehensive dynamic aeration system model has been developed that captures both air suppl… Show more
“…3E-H) and the peak of the overall oxygen demand concentration was expressed as the mean of the daily maximum, Site #1 had about 278 mg-O 2 /L of the oxygen demand whilst Site #2 and Site #3 had 402 mgO 2 /L and 592 mg-O 2 /L respectively. Since these concentrations were scattered over the 3 sites, use of default values for oxygen demand might not be an attractive option to perform precise plant design, unlike the research by Schraa et al (2017) and USEPA [3]. Indeed, the ratio of the maximum value of the daily maximum to the mean value of the daily average were also distinct over the three sites.…”
Section: Hourly Concentration Of the Influent Biodegradable Substancesmentioning
confidence: 95%
“…For the air supply system and the oxygen transfer, the topics have been intensively studied. For instance, with respect to model-ling the aeration system and its energy consumption, Schraa et al (2017) developed a fully dynamic model around the aeration header network to simulate the air distribution, and evaluated its limitations with various optimisation options and influent loadings [3]. Juan-Garcia et al (2018) modified their study to the plant controlling systems by integrating a biokinetic model having oxygen uptake phenomena [4].…”
Section: Introductionmentioning
confidence: 99%
“…The above-mentioned guidelines only provide default design-daily-average concentrations of BOD 5 and Total Kjeldahl Nitrogen (TKN) with thumb rules to adapt the parameters to the plant design. For example, Schraa et al (2017) and US Environmental Protection Agency (USEPA) selected 150~200 mg-BOD/L and 30~40 mg-N/L as the default BOD 5 concentration and total TKN concentration respectively [3]. With respect to the oxygen demand in design-daily-maximum, the guidelines suggest calculating the load in proportion to the inflow rate of the design-dailyaverage.…”
Ascertaining peak oxygen demand is crucial for plant designers to determine blower capacities of wastewater treatment plants in planning phase. To obtain this technical information without cumbersome influent sampling and analysis, a set of field-test activated sludge reactors equipped with DO and nitrate-N sensors was installed at 3 sites and continuously operated for a couple of months in each field. Under the controlled aeration and hydraulics of the reactors, the hourly influent oxygen demands were back-calculated as biodegradable constituents using the IWA-Activated Sludge Model #1. The daily maximum concentrations (rounded to last for 1-hour) of biodegradable organics and nitrogen were ranged between 45~258 mg-COD/L and 10.4~32.3 mg-N/L in Site #1; 119~244 mg-COD/L and 28.3~38.7 mg-N/L in Site #2; 194~552 mg-COD/L and 30.2~51.7 mg-N/L in Site #3 respectively. The marginal blower capacities to maintain at least 1.0 mg-O 2 /L of DO in the daily maximum oxygen demand were estimated based on the datasets using the statistical method, Extreme Value Distribution analysis. To maintain the DO concentration for 99 days out of 100 days of the plant operations, the blower capacity was supposed to be designed as high as 1.4~2.2 times than those of the blower calculated from the daily average concentration.
“…3E-H) and the peak of the overall oxygen demand concentration was expressed as the mean of the daily maximum, Site #1 had about 278 mg-O 2 /L of the oxygen demand whilst Site #2 and Site #3 had 402 mgO 2 /L and 592 mg-O 2 /L respectively. Since these concentrations were scattered over the 3 sites, use of default values for oxygen demand might not be an attractive option to perform precise plant design, unlike the research by Schraa et al (2017) and USEPA [3]. Indeed, the ratio of the maximum value of the daily maximum to the mean value of the daily average were also distinct over the three sites.…”
Section: Hourly Concentration Of the Influent Biodegradable Substancesmentioning
confidence: 95%
“…For the air supply system and the oxygen transfer, the topics have been intensively studied. For instance, with respect to model-ling the aeration system and its energy consumption, Schraa et al (2017) developed a fully dynamic model around the aeration header network to simulate the air distribution, and evaluated its limitations with various optimisation options and influent loadings [3]. Juan-Garcia et al (2018) modified their study to the plant controlling systems by integrating a biokinetic model having oxygen uptake phenomena [4].…”
Section: Introductionmentioning
confidence: 99%
“…The above-mentioned guidelines only provide default design-daily-average concentrations of BOD 5 and Total Kjeldahl Nitrogen (TKN) with thumb rules to adapt the parameters to the plant design. For example, Schraa et al (2017) and US Environmental Protection Agency (USEPA) selected 150~200 mg-BOD/L and 30~40 mg-N/L as the default BOD 5 concentration and total TKN concentration respectively [3]. With respect to the oxygen demand in design-daily-maximum, the guidelines suggest calculating the load in proportion to the inflow rate of the design-dailyaverage.…”
Ascertaining peak oxygen demand is crucial for plant designers to determine blower capacities of wastewater treatment plants in planning phase. To obtain this technical information without cumbersome influent sampling and analysis, a set of field-test activated sludge reactors equipped with DO and nitrate-N sensors was installed at 3 sites and continuously operated for a couple of months in each field. Under the controlled aeration and hydraulics of the reactors, the hourly influent oxygen demands were back-calculated as biodegradable constituents using the IWA-Activated Sludge Model #1. The daily maximum concentrations (rounded to last for 1-hour) of biodegradable organics and nitrogen were ranged between 45~258 mg-COD/L and 10.4~32.3 mg-N/L in Site #1; 119~244 mg-COD/L and 28.3~38.7 mg-N/L in Site #2; 194~552 mg-COD/L and 30.2~51.7 mg-N/L in Site #3 respectively. The marginal blower capacities to maintain at least 1.0 mg-O 2 /L of DO in the daily maximum oxygen demand were estimated based on the datasets using the statistical method, Extreme Value Distribution analysis. To maintain the DO concentration for 99 days out of 100 days of the plant operations, the blower capacity was supposed to be designed as high as 1.4~2.2 times than those of the blower calculated from the daily average concentration.
“…The intensity of mixing leads to enhanced mass exchange in the AT, hence directly influencing the concentration of residual polluting matter in the effluent. The knowledge of actual reactor MRT can prevent incomplete biochemical reactions in ASP and help in growth of desirable microorganisms [14,23,33]. With the optimal combination of operating parameters, optimized ASP performance can be achieved that result in minimum BOD and COD of the treated effluent [34].…”
Section: Effects Of Varying Operational Parameters On Biological Treamentioning
confidence: 99%
“…Several RTD studies performed on ASP shows that the AT acts as a complete mixing tank and excessive air supply is needed to ensure the aerobic condition, provided by air diffusion systems or surface aerators. The rate of aeration often leads to high circulation rates and back-mixing, and affect the sludge particle size and its distribution in the reactor [14][15][16]. These reactors have been often represented with one parameters and two parameters RTD models [17,18].…”
Hydrodynamic study of Activated Sludge Process (ASP) is important to optimize the reactor performance and detect anomalies in the system. Residence time distribution (RTD) study has been performed using LiCl as tracer on a pilot scale aeration tank (AT) and ASP, treating the pulp and paper mill effluent. The hydraulic performance and treatment efficiency of the AT and ASP at different operating parameters like residence time, recycle rate was investigated. Flow anomalies were identified and based on the experimental data empirical models was suggested to interpret the hydrodynamics of the reactors using compartment modelling technique. The analysis of the RTD curves and the compartment models indicated increase in back-mixing ratio as the mean hydraulic retention time (MHRT) of the tank was increased. Bypassing stream was observed at lower MHRT. The fraction of dead zone in the tank increased by approximate 20-25% with increase in recycle rate. The fraction of the stagnant zone was found well below 5% for all performed experiments, which was under experimental error. The substrate removal of 91% for Chemical oxygen demand and 96% for Biochemical oxygen demand were observed for the ASP working at a hydraulic mean residence time 39 h MRT with a 20% recycling of activated sludge.
Aeration systems often lack the efficiency to maintain a desired residual dissolved oxygen (DO) concentration in the tank in part because little consideration is given to the dynamic daily and seasonal loading conditions. Although advanced aeration controllers exist, the majority of plants have DO set points typically based on common practice and literature values rather than site‐specific conditions, which can result in DO set points higher than those necessary to meet treatment objectives. DO set point reduction strategies have primarily been proposed through either static or dynamic simulations. In this study, the substantial improvements associated with DO set point reduction are demonstrated at full scale. A yearlong characterization of full‐scale aeration dynamics captured the effect of diurnal and seasonal fluctuations on oxygen transfer and energy demand and so facilitated the estimation of the potential savings of DO reduction strategies. Full‐scale validation provided direct evidence of DO reduction strategies inducing an overall enhancement of oxygen transfer efficiency along the different bioreactors, while confirming that energy savings as high as 20% were feasible. This study quantifies the influence of oxygen transfer efficiency on operating choices and site‐specific conditions (control strategy, loading conditions, and influent flow variability).
Practitioner points
We quantified the energy reduction and cost savings associated with a DO reduction in an aeration tank.
For each 0.2 mg/L of DO decreased, the average power demand reduction per unit water treated exceeded 17%.
Field measurements of dynamic alpha values eliminate the uncertainty in estimating aeration energy and cost savings from DO variations.
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