To improve the operational economy of sewage pumping stations, this paper combines the total volume of the drainage network and sewage pumping station to optimize the effective volume of the pumping station reservoir to reduce operating costs without overflow. Taking a residential area in Ningbo city as the study area, the drainage system was simulated based on Infoworks ICM to obtain the changes of sewage under different volumes of pumping station reservoirs. By combining the daily electricity costs of the pump station, pump start-stop times, and flood depth, the fuzzy optimization method was applied to optimize the effective volume of sewage pumping station reservoirs, selecting the optimal solution to reduce operating costs. A sensitivity analysis of the three factors, pump flow rate, the total population, and drainage network volume, was conducted, and the results showed that under the optimal scenario, the optimal effective volume of the pumping station reservoir increases with the increase in pump flow rate, drainage network volume, and total population. This study can provide theoretical support for the optimization of drainage pumping station reservoir volume as well as economical operation.

  • The study utilized InfoWorks ICM software to optimize the sewage pumping station reservoir's volume, considering factors such as electricity prices and sewage patterns.

  • Cost savings were significant, with optimizations reducing daily electricity costs by up to 15.89% and pump operations by 13.33%.

  • It highlighted a positive link between optimal reservoir volume and factors such as pump flow rates, network volumes, and population size.

The sewage pumping station plays a crucial role in water pollution treatment, serving as an indispensable component of municipal drainage systems responsible for collecting and discharging urban wastewater. The sewage pumping station has the characteristics of a single large discharge and long seasonal operation time (Gong & Zhu 2022). The operation of the system is almost entirely driven by electricity (Rinas et al. 2018), with pumps as the main power system, in constant operation, the load will gradually increase, and the corresponding energy consumption will increase. Although reducing the power output of the pump can reduce the loss rate, it will also increase the maintenance cost. According to statistics, the energy consumption of sewage pumping stations accounts for 20–30% of the sewage treatment system, which has brought heavy operating costs to enterprises (Badruzzaman et al. 2016).

At present, the optimization research of sewage pumping stations mainly focuses on the optimization of pump start-stop times (Ostojin et al. 2011) and energy consumption (Piri et al. 2021), which mainly involves algorithms and control strategies. Darsono & Labadie (2007) adopted the optimal control system based on a neural network to realize the optimal coordinated scheduling of discharge in the dynamic combined pumping station system and achieved good results in the local pumping station. Gorjian Jolfaei et al. (2019) proposed a new intelligent controller that generates pump switching commands through a series of rules, which is applied to Infoworks ICM and its built-in RTC editor, reducing daily power costs by 21% compared with traditional controllers. Improving conventional switching to achieve energy optimization and cost savings is a major challenge. Nonetheless, an effective pump scheduling program is a viable and economical way to save pumping costs. This is because there is no need to destroy existing infrastructure and existing pumps and piping can still contribute to our daily water supply.

Wang et al. (2021) took the time-varying electricity price as consideration, selected the number of units operating at each pumping station as a decision variable to establish a pumping station optimization model, and solved it with integer programming, which has significant economic benefits. Dadar et al. (2021) proposed a genetic algorithm optimization and used MATLAB software to verify the relationship between pump running time and flow rate under optimal energy consumption, which improved the power consumption efficiency of the pump and reduced the energy consumption by about 15 ∼ 20%. Yi & Wenhao (2023) set the research goal of minimizing the operation cost of a pumping station within the drainage cycle, combined with a genetic algorithm, and established a nonlinear mathematical model. Taking the Guazhou Pumping Station in Yangzhou, Jiangsu Province as an example, by optimizing the start-stop times of the pump, the electricity cost of the optimized scenario was respectively saved by 15.34 and 4.40% compared with the conventional scenario. Makaremi et al. (2017) proposed an adaptive NSGA-II algorithm for pump optimization with multi-objective constraint by using energy cost minimization and pump switching minimization as two objective functions. In the optimization process, a trade-off is made between the energy costs and the total number of pump switches, so that the total energy consumption is concentrated mainly in the medium load period and secondly in the low load period. They concluded that the total number of pump switches can be reduced by 69% while the energy cost increases by up to 10%. The above strategies have succeeded in increasing the computational efficiency of the applied optimization algorithms while providing computational tools for real-time applications, concurrently, the algorithms in question are becoming increasingly intricate. Currently, the research in multi-objective optimization is limited, particularly in terms of balancing competing objectives. The primary aim of the multi-objective model is to enhance the trade-offs between energy consumption and maintenance costs. The optimization process for pump scheduling seeks to equilibrate these two factors effectively, balancing energy costs against pump maintenance expenditures.

With increasing urban populations leading to rising sewage discharge volumes, the economical operation of sewage pumping stations becomes ever more critical in reducing enterprise costs. This study selected a residential area in Ningbo City as the study area, modeled the sewage network using Infoworks ICM software, and gathered data on the electric power consumption of the pump, electricity price standards, pump station drainage, pump start-stop times, and manhole flood depths. In order to minimize energy costs and maintenance costs associated with the pumping station, it is imperative to take into account the flood depth of the manhole, to ensure that the normal operation of the drainage system, and the emergence of overflow events. Consequently, the daily electricity cost, pump start-stop frequency, and flood depth are designated as preferred objectives. By integrating single-day electricity price fluctuations, study area sewage discharge patterns, and drainage network topologies, this study employed the fuzzy optimization method (Zadeh 1965) and multi-objective optimization methods (Bellman & Zadeh 1970) to analyze and optimize the effective volume of sewage pumping stations (Barán et al. 2005), aiming to decrease operational costs associated with sewage pumping stations.

Numerical model

Infoworks ICM software uses the one-dimensional hydrodynamic model to simulate the hydraulic conditions of domestic sewage, industrial wastewater, and other wastewater in sewage pipelines, which can output simulation data so that the hydraulic condition of existing or designed sewage networks can be evaluated, providing a data-driven effort for the optimization of sewage pumping station.

According to the physical exploration data, part of the as-built drawings and on-site research data, standardized data entry and topology correction are carried out to ensure the accuracy of the data and the connectivity of the system through repeated inspections and realize the establishment of the pipe network model. Based on the basic data of the drainage pipe network, sub-catchment division is carried out using the Tyson polygon method, and sewage events are set up based on the amount of sewage discharged by residents in the study area and the daily sewage change coefficient.

Fuzzy optimization method

Optimizing sewage pumping stations involves various considerations, such as managing the daily electricity costs, minimizing pump start-stop times to prolong equipment lifespan and reduce maintenance expenses, and maximizing drainage system storage capacity while preventing overflow incidents. Consequently, sewage pumping station optimization presents a multi-objective challenge (Yagi & Shiba 1999) that necessitates multi-objective comparative analysis to transform it into a single-objective optimization task (Wang et al. 2023). In this research, utilizing the fuzzy optimization method (Shan et al. 2021), the daily electricity cost, pump start-stop frequency, and flood depth are designated as preferred objectives (Borges et al. 2016), and different effective volumes of the pumping station are assessed to categorize options and calculate the relative superiority of each (Zimmermann 2011). The scenario exhibiting the highest relative superiority (Woldt et al. 1996) is chosen as the optimal solution (Huo et al. 2023), leading to the identification of the most efficient and effective volume for the sewage pumping station.

The calculation of the relative superiority includes the following steps:

(1) For a system with n scenarios to be selected and m evaluation indicators for each scenario, we construct its target eigenvalue matrix
(1)

The data of the evaluation indicators are the target eigenvalues. K in the matrix Xmn represents the result data set of selected evaluation indicators obtained by simulation calculation for each scheme, that is . L in the matrix Xmn indicates that for each selected evaluation indicator, the resulting data set of the evaluation indicator obtained by the simulation calculation of all schemes, that is .

(2) The relative superiority of each objective is calculated as follows:
(2)
where rij is the relative superiority of target i in scenario j; is the maximum eigenvalue of target i in the decision set; and is the minimum eigenvalue of target i in the decision set.
Since the selected evaluation indicators have different magnitudes, using Equation (2) to normalize , is obtained. K in the Rmn matrix represents the relative superiority set after normalization of the result data of the selected evaluation indicators obtained from the simulation calculation for each scheme, that is . L in the Rmn matrix represents the set of relative superiority of each selected evaluation indicator after normalization of the selected evaluation indicator of each scheme, that is . Then we obtain the target relative superiority matrix Rmn.
(3)
(3) Ranking and weighting of the importance of objectives. In the optimization process, objective weights (Wi) are determined to assess the significance of the preferred objectives. This study employs the methodology of multi-objective comparison to establish the weights of the evaluation objectives. Initially, each preferred target is prioritized based on importance, utilizing a fuzzy scale ranging from ‘equally important’ to ‘incomparable’ to compare their relative significance against one another. The order of importance is illustrated in Figure 1, with the most crucial target considered as incomparable to others and its importance gradually intensifying in the comparison process (Zadeh 1965). For instance, the relative importance (uij) of the first-ranked target is 0.5, indicating equal importance to itself. When a target is incomparable to the m'th target, its relative importance (uij) is 1, signifying incomparable importance. The remaining levels of importance are interpolated linearly between 0.5 and 1.0, facilitating the derivation of the target weights (W′).
(4)
Figure 1

Importance-fuzzy tone linear relationship graph.

Figure 1

Importance-fuzzy tone linear relationship graph.

Close modal
Using Equation (4) to normalize the importance, the weight of the i’th preferred target over the other targets can be obtained, i.e.
(5)
where Wi denotes the weight of target i, i = 1, 2, … , m. The M in vector W represents a set of selected preferred objectives for a project that requires multi-objective optimization; the O in vector W represents the weight value of the selected preferred objectives relative to other targets.
(4) Calculate the relative superiority uj of scenario j
(6)
where p is the Euclidean distance parameter, which takes the value of 2 in this study. According to the principle of maximum relative superiority, the optimal research scenario can be determined.

Table 1 lists all the simulation cases in this study, of which Case A1 is used to study the actual sewage flow in the area and the optimization of the effective volume of the pumping station reservoir. Cases Bs and Cs are used to study the effect of pump flow on the effective volume of the cistern; Cs to Es are used to study the effect of population size on the effective volume of the cistern of the sewage pumping station. For conditions As to Es, three different sewerage network volumes are set to study the effect of sewerage network volume on the effective volume of the sewage pumping station.

Table 1

Parameters of nodes in the drainage network

NodeNode typeDepth of node (m)
manhole −1.72 
manhole −1.76 
manhole −2.20 
manhole −3.00 
manhole −2.60 
manhole −2.67 
manhole −2.70 
manhole −2.75 
manhole −2.85 
pump −3.65 
NodeNode typeDepth of node (m)
manhole −1.72 
manhole −1.76 
manhole −2.20 
manhole −3.00 
manhole −2.60 
manhole −2.67 
manhole −2.70 
manhole −2.75 
manhole −2.85 
pump −3.65 

Drainage system model

In this study, a residential community in Ningbo City was selected, which has a relatively independent drainage system that is hardly affected by the surrounding area. The total area of the zone is about 24,000 m2 and the population is about 1,400. The per capita daily sewage discharge for this study was 215 L (Chen et al. 2022). The drainage network of this area is connected to the sewage pumping station, the pump flow Q = 0.118 m3/s, the inlet pipe diameter of the pumping station is 500 mm, the bottom elevation of the outlet pipe is −1.20 m, the size of the reservoir upstream of the pumping station is 4.18 × 3.11 × 6.65 m3, and the electricity cost of the area is taken as the charge of time-sharing tariffs of Ningbo city. The pipeline's base data were imported in Infoworks ICM, and the topology of the network was simplified based on ensuring the connectivity of the system to obtain a one-dimensional wastewater system model and sub-catchment delineation using the Tyson polygon method, and the model was calibrated against actual drainage information. The topology of the sewage pumping station and its upstream drainage network in the study area are shown in Figure 2. The information of nodes and pipes are shown in Tables 1 and 2, respectively.
Table 2

Parameters of drainage pipes

PipePipe diameter (m)Pipe length (m)Slope
PA-B 0.30 8.30 0.004 
PB-D 0.30 56.60 0.003 
PC-D 0.40 7.90 0.003 
PD-I 0.40 63.30 0.003 
PE-F 0.40 7.10 0.002 
PF-H 0.40 55.30 0.002 
PG-H 0.40 9.10 0.002 
PH-I 0.50 36.70 0.003 
PI-J 0.50 40.30 0.003 
PipePipe diameter (m)Pipe length (m)Slope
PA-B 0.30 8.30 0.004 
PB-D 0.30 56.60 0.003 
PC-D 0.40 7.90 0.003 
PD-I 0.40 63.30 0.003 
PE-F 0.40 7.10 0.002 
PF-H 0.40 55.30 0.002 
PG-H 0.40 9.10 0.002 
PH-I 0.50 36.70 0.003 
PI-J 0.50 40.30 0.003 
Figure 2

Topology of the sewage pumping station and its upstream drainage network.

Figure 2

Topology of the sewage pumping station and its upstream drainage network.

Close modal

Effective volume range

The operation of pumps is intricately linked to the regulating capacity of the reservoir. The effective volume of a pumping station reservoir refers to the space between the highest designated level of the reservoir (Start Pump Level) and its lowest designated level (Stop Pump Level). Determinants of the effective volume include the bottom elevation of the outlet pipe, cistern specifications, and pump flow rate, with the range conforming to the following criteria: the effective volume should exceed the maximum 5-minute water discharge of a pump; the stop pump level must surpass the centerline of the pump discharge pipe; the stop pump level should not fall below the bottom elevation of the cistern plus 300 mm; and the start pump level must not exceed the top elevation of the cistern minus 300 mm. The bottom elevation of the effluent pipe of the sewage pumping station in this study is −1.20 m. The dimensions of the cistern upstream of the pumping station are 4.18 × 3.11 × 6.65 m3, which results in an effective volume range of the pumping station (35.40, 47.45), as shown in Figure 3.
Figure 3

Section view of the drainage pumping station.

Figure 3

Section view of the drainage pumping station.

Close modal

Analysis of simulated data

The Infoworks ICM software was utilized for simulating and analyzing the drainage system within the study area. This simulation aims to provide insights into the drainage conditions of the pumping station, including pump start-stop frequency and flooding depth under varying effective volumes of the sewage pumping station reservoir. Additionally, local time-based tariffs are integrated to calculate the daily electricity expenses associated with operating the sewage pumping station. The daily electricity cost comprises the total electricity consumption during a day of pump operation. This calculation considers the electricity price based on local time-based tariffs and charges, where the electricity consumed per pump operation cycle is computed as f = W × t × c, where W represents the electric power consumption of the pump and c denotes the unit electricity price during pump operation. Flood depth signifies the water level in manholes, a fixed manhole in the drainage network selected for this study; the maximum flood depth of this fixed manhole reached in the operating cycle was determined to calculate; any flood depth of manhole in the drainage network equal to or greater than zero triggers a bubbling event, which has been omitted from the data summary in this study. The wastewater pumping station functions on a seven-day cycle, necessitating all parameters to be evaluated and compared based on a single cycle.

The fluctuation of pump station discharge and flood depth in the manhole over a single day with a pump station reservoir effective volume of 42.17 m3 is depicted in Figure 4. Notably, on that day, the pumps operated four times: the first and second pumps ran during off-peak hours, while the third pump operated during peak hours, and the fourth pump spanned both off-peak and peak hours. Therefore, the daily electricity costs of the pumping station and the associated pump operations are intricately linked to the periods corresponding to local electricity prices. Specifically, during off-peak hours, the pumping station utilized electricity at the lowest cost.
Figure 4

Fluctuation of daily electricity price, relative flow rate against mean flow rate, discharge of pumping station, and flood depth change.

Figure 4

Fluctuation of daily electricity price, relative flow rate against mean flow rate, discharge of pumping station, and flood depth change.

Close modal

In the study area, continuous sewage discharge leads to an increase in flood depth in manholes and water levels in the pumping station reservoir when the pumping station ceases operation. As sewage discharge rises, these levels escalate until they reach the start pumping level, prompting the pumping station to commence sewage discharge. Consequently, flood depths in manholes and reservoir levels drop significantly upon pump activation. On a particular day, the pumping station began operations four times correlating with substantial flood depths at the start pumping level. Pump start and stop times throughout the day exhibit non-uniform distributions, influenced by variations in daily sewage volume within the region. Notably, during the transition from the 1st to 2nd stoppage, the coefficient of variation for sewage exceeds 1, indicating higher variability compared to the subsequent transition. This implies that sewage flow in the former period surpasses that in the latter one. The sewage dynamics within the service area profoundly impact pumping station operations. During peak sewage periods, the drainage network experiences rapid elevation, necessitating more frequent pumping station operations.

Optimization of the pumping station

This study selected a total of 11 different effective volumes of the reservoir, that is, there are 11 options to be selected, and each option has 3 evaluation indicators, respectively, for the daily electricity costs of the pumping station, the frequency of pump start-stop times, and flood depth, to construct the target eigenvalue matrix
To account for variations in the characteristics of each target, it is essential to standardize the values of each target. Equation (2) is employed to compute the relative superiority degree of each target, facilitating the derivation of the target matrix's relative superiority degrees
after analyzing the operational scenario of the pumping station, and considering its economic influence.

Following consultations with pertinent practitioners and experts, as well as an analysis of relevant data, the prioritized ranking of the three assessment criteria is as follows: It is observed that the daily electricity cost carries greater importance compared to the number of pump start-stop frequencies, whereas flood depth serves as a metric for assessing overflow risks and holds lower significance than pump operations. After trial calculations, we concluded that the results are convergent with daily electricity cost of the pumping station (u11 = 0.8), number of pump starts and stops (u12 = 0.7), and flood depth (u13 = 0.8). Substituting these values into Equation (6) results in W′ = (1, 0.42857, 0.25). Upon normalization, the weight values for each target become W = (0.5957, 0.2553, 0.1489). Equation (8) is then applied to compute the relative superiority degree for each scenario.

Figure 5 illustrates the comparison of data for each preferred scenario under the condition of a pumping station reservoir effective volume of 42.17 m3 over an operating cycle of 7 days. The daily electricity cost of the pumping station amounts to 160.03 RMB, marking the lowest among all scenarios and achieving a 15.9% cost saving at its maximum efficiency. The number of pump start-stop times totals 26, representing a 13.3% reduction from the maximum frequency. Moreover, the flood depth in the manhole is −0.409 m, falling below the levels observed in other scenarios and avoiding overflow incidents. Following the fuzzy optimization method, the optimal scenario is determined based on the largest relative superiority degree. Consequently, Scenario 7 emerges as the most superior option according to this principle, indicating that the sewage pumping station is optimized with an effective volume of 42.17 m3.
Figure 5

Data comparison of the optimal solution of the sewage pumping station.

Figure 5

Data comparison of the optimal solution of the sewage pumping station.

Close modal

Sensitivity analysis

Utilizing data from the existing drainage system, pump flow characteristics, total service area population, and drainage network volume are examined as key factors for optimizing the sewage pumping station reservoir effective volume. Cases As–Es used in this section are shown in Table 3. Within this study, the drainage network volumes were determined to be 29.90, 39.12, and 43.94 m3 for sewage pumping station effective volume optimization scenarios. Ensuring that the effective volume exceeds the maximum 5-min water discharge of the largest pump, Case Bs with a pump flow rate of 0.094 m3/s falls within an effective volume range of (28.20, 47.45). Conversely, Cases Cs–Es with pump flow rates of 0.070 m3/s are associated with effective volume ranges of (21.00, 47.45). The electric power consumption of the pump varies based on different flow rates (0.118, 0.094, and 0.070 m3/s) and corresponding power ratings of 45, 41, and 36 kW, respectively. By applying the fuzzy optimization method to optimize the pumping station's effective volume across all operational conditions, the optimal scenario for each case can be identified.

Table 3

List of simulation cases

CasesTotal populationPump flow rate (m3/s)Drainage network volume (m3)Pumping station reservoir volume (m3)
As 1,400 0.118 29.90 35.40–47.45 
39.12 
43.94 
Bs 1,400 0.094 29.90 28.20–47.45 
39.12 
43.94 
Cs 1,400 0.070 29.90 21.00–47.45 
39.12 
43.94 
Ds 2,200 0.070 29.90 21.00–47.45 
39.12 
43.94 
Es 3,000 0.070 29.90 21.00–47.45 
39.12 
43.94 
CasesTotal populationPump flow rate (m3/s)Drainage network volume (m3)Pumping station reservoir volume (m3)
As 1,400 0.118 29.90 35.40–47.45 
39.12 
43.94 
Bs 1,400 0.094 29.90 28.20–47.45 
39.12 
43.94 
Cs 1,400 0.070 29.90 21.00–47.45 
39.12 
43.94 
Ds 2,200 0.070 29.90 21.00–47.45 
39.12 
43.94 
Es 3,000 0.070 29.90 21.00–47.45 
39.12 
43.94 

When the study area's total population is 1,400 people and the pump flow rates are 0.118, 0.094, and 0.070 m3/s (Case As–Bs), all cases are optimized and the observation reveals that with a constant service area population and drainage network volume, the optimal effective volume of the pumping station reservoir increases as the pump flow rate grows. Figure 6 illustrates that under constant service area population and drainage network volume, higher pump flow rates result in fewer start-stop times in the optimal scenario, reduced daily electricity costs for the pumping station, increased flood depths in manholes, and elevated risks of overflow events within the drainage system.
Figure 6

Influence of pump flow on pumping station optimization: (a) and (b) drainage network volume = 29.90 m3; (c) and (d) drainage network volume = 39.12 m3; (e) and (f) drainage network volume = 43.94 m3.

Figure 6

Influence of pump flow on pumping station optimization: (a) and (b) drainage network volume = 29.90 m3; (c) and (d) drainage network volume = 39.12 m3; (e) and (f) drainage network volume = 43.94 m3.

Close modal

During periods of pump inactivity at the sewage pumping station, the continuous discharge of sewage by residents causes both the drainage network and pumping station reservoir levels to rise. In the optimal scenario, when the pump flow diminishes, the effective volume of the pumping station decreases correspondingly. Under consistent sewage discharge conditions, faster pump activation leads to decreased reservoir levels at the pumping station and subsequently lower water levels within the drainage network. A smaller effective volume for the pumping station correlates with a reduction in the maximum flood depth of the drainage network.

In cases Cs–Es with a pump flow rate of 0.070 m3/s, the total population of the service area is specified as 1,400, 2,200, and 3,000, respectively. Through the optimization and analysis, it is evident that under constant pump flow and drainage network volume, an increase in the total population of the service area leads to a higher daily sewage generation volume, consequently necessitating a larger optimal effective volume for the pumping station. Figure 7 illustrates that with consistent pump flow and drainage network volume, a rise in the total service area population results in the following outcomes within the optimal scenario: increased daily electricity costs for the pumping station, higher frequency of pump start-stop times, greater flood depths in inspection wells, and heightened risks of overflow events within the drainage system.
Figure 7

Influence of total population of the service area on pumping station optimization: (a) and (b) drainage network volume = 29.90 m3; (c) and (d) drainage network volume = 39.12 m3; (e) and (f) drainage network volume = 43.94 m3.

Figure 7

Influence of total population of the service area on pumping station optimization: (a) and (b) drainage network volume = 29.90 m3; (c) and (d) drainage network volume = 39.12 m3; (e) and (f) drainage network volume = 43.94 m3.

Close modal
With the total population and pump flow rates remaining constant (Cases As–Es), the increase in the volume of the drainage network will result in an increase in the optimum effective volume requirement for the pump station reservoirs. Under identical sewage discharge conditions and pumping station drainage capacity, the expansion of the drainage pipe network volume enhances water storage capacity within the drainage system, necessitating a larger effective volume for the pumping station reservoir to raise the overall drainage system storage capacity. As depicted in Figure 8, within the optimal scenario, with a fixed total population of the service area and consistent pump flow, a larger drainage network volume corresponds to a reduction in the number of pump start-stop times. Additionally, when the total service area population is increased while the pump flow decreases, this relationship reinforces the observed trend.
Figure 8

Influence of drainage network volume on pumping station optimization: (a) impact on the optimal effective volume for the pumping station reservoir and (b) impact of the pump start-stop times.

Figure 8

Influence of drainage network volume on pumping station optimization: (a) impact on the optimal effective volume for the pumping station reservoir and (b) impact of the pump start-stop times.

Close modal

This study leveraged the InfoWorks ICM software to simulate the sewage network within the study area, focusing on analyzing and optimizing the effective volume of the sewage pumping station reservoir. The optimization process integrated the fuzzy optimization method and a multi-objective optimization method, considering variables such as daily electricity price fluctuations, service area sewage discharge patterns, and drainage network topologies. By addressing pump flow, total population, and drainage pipe network volume, a sensitivity analysis was conducted for sewage pumping station reservoir effective volume optimization, leading to the following conclusions:

  • 1. Applying the fuzzy optimization method involved weighing factors such as upstream drainage network topology, daily drainage variations, electric power consumption of the pump, electricity cost kurtosis, and sewage overflow risks. By assigning weights to each optimization objective and selecting the option with the highest relative superiority degree as the optimal scenario, the ideal effective volume for the sewage pumping station reservoir could be determined.

  • 2. Under standard drainage system operations without overflow incidents, implementing the optimization scenario resulted in substantial cost savings for the pumping station, with up to a 15.89% reduction in daily electricity expenses and a 13.33% decrease in pump start-stop times. This optimized approach effectively lowered sewage pumping station operating costs while streamlining the effective volume optimization process.

  • 3. The study revealed that the optimal effective volume of the pumping station correlates positively with increased pump flow rates, drainage network volumes, and total service area populations.

The authors gratefully appreciate the financial support from the National Key R&D Program of China (No. 2022YFC3203200), the Ningbo Key R&D Programs and ‘Listed and Commanded’ Projects (No. 2023Z216), and Project on Technical Study on Operation Assessment and Optimization of Stormwater and Sewerage Pumping Stations.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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