The increasing issue of aging water pipes highlights the need for a long-term renewal investment plan to respond effectively within constrained resources. This study proposes an optimization method designed to minimize life cycle costs while considering the structural safety of pipes and economic efficiency in pipe renewals. The method consists of two prediction models: artificial neural network (ANN)-based corrosion prediction models and ANN-based failure rate prediction models. This study uses these models to develop a dynamic programming (DP)-based optimization method that meets annual budget constraints. It applies successfully to a target area of conveyance pipe networks. Moreover, the findings demonstrate that adhering to annual budget constraints allows water utilities to allocate their budgets efficiently, facilitating strategic investments within set yearly limits. These findings offer substantial promise as foundational technologies for the asset management of water supply infrastructures, highlighting their potential for future applicability and value.

  • Developed artificial neural network models for corrosion and failure rate prediction achieved usability with high correlation coefficient.

  • Renewal investment plan optimization method based on dynamic programming was proposed and demonstrated in a cast study area.

  • The case study verified that the proposed method enables more efficient water pipe management at lower costs than existing methods.

One critical component of social overhead capital, essential for human survival, is the transmission and conveyance pipes of the drinking water supply systems. These pipes deteriorate over time due to various physical, environmental, and operational factors (Kleiner & Rajani 2002). The deterioration of water pipes undermines the original purpose of delivering safe, high-quality tap water with consistent pressure without insufficient quantity. Furthermore, the deterioration of water pipes can lead to structural problems, resulting in direct and indirect losses and potentially damaging other infrastructure (Abdel-Mottaleb et al. 2019; Assad & Bouferguene 2021). Therefore, ensuring proper installation, conducting regular inspections, and performing repair and maintenance tasks, including cleaning, replacement, or rehabilitation throughout the pipe's lifespan, are crucial to maintaining the performance of buried pipes above the target level. Additionally, water utilities require an investment plan to systematically execute these tasks within limited resources.

Dandy & Engelhardt (2006) proposed a comprehensive approach to developing a water pipe renewal plan, emphasizing three crucial factors: structural safety of the pipes, economic efficiency of renewal, and water quality. Among three factors, water quality mainly relates to replacing small-diameter distribution pipes with extended residence times. Therefore, when replacing large-diameter transmission or conveyance pipes, greater emphasis is placed on the structural safety of the pipes and the economic efficiency of renewal rather than water quality. As the water transmission and conveyance network represent most of the expenses needed to maintain the water supply system, water utility managers facing budget constraints must opt for the most cost-effective investment alternative (Kleiner & Rajani 2022). Nonetheless, in practical scenarios, managers traditionally employ a less efficient approach, wherein they replace pipes that have exceeded a predetermined period of use or replace a set percentage of pipes annually (Fitchett et al. 2020). Traditional methods not only lead to inefficient allocation of limited resources but also pose challenges for ensuring the long-term sustainability of the water supply system (Taiwo et al. 2023).

Regarding predicting the appropriate renewal period for water pipes, methods can generally be categorized into two approaches: physical condition assessment and statistical analysis. The physical approach involves diagnosing the structural characteristics of the pipes, such as corrosion depth and material degradation, to predict lifespan (Kleiner & Rajani 2001). For example, models like the safety factor (SF) concept evaluate structural safety by examining the relationship between residual tensile strength and applied load (Deb et al. 2002). Recent advancements include artificial neural network (ANN) models to predict corrosion depth accurately (Kim et al. 2023). On the other hand, statistical approaches analyze historical damage and leakage data to predict future failure rates. These methods range from early age-based models (Shamir & Howard 1979) to more advanced machine learning techniques, such as random forest and support vector machines (Giraldo-Gonzalez & Rodriguez 2020). Recent studies have further refined these methods by addressing challenges such as imbalanced datasets. For example, Beig Zali et al. (2024) proposed a semi-supervised clustering approach to enhance classification accuracy in pipe failure prediction by leveraging domain knowledge with unsupervised learning, demonstrating superior performance compared with traditional class imbalance techniques. Although machine learning methods have improved predictive accuracy, challenges remain due to real-time condition assessment data limitations and the potential mismatch between model predictions and actual pipe conditions.

Various decision support systems have been developed to address the challenges faced thus far. Most systems utilize methods for predicting an appropriate renewal time, which can be based on factors such as failure rates, service life, or the life cycle cost of the pipe. Loganathan et al. (2002), Shin et al. (2016), and Zhang et al. (2019) recommend replacing the pipe when it reaches a specific time threshold. Other approaches involve prioritizing pipe replacements based on risk assessments, reliability indices, or the condition assessment score of the pipes (Rahman et al. 2014; Haider et al. 2015; De Sousa-Pereira et al. 2020). Alternatively, some systems focus on replacing pipes to meet reliability or key performance indicators (Alegre et al. 2014; Liu et al. 2020).

Unfortunately, because the methods proposed to date approach pipe renewal from an incomplete perspective, the advantages or applicability of a method that simultaneously considers various aspects are unknown. As previous researchers have mentioned, determining the timing of pipe renewal by comprehensively considering various elements ensures the sustainability of water utilities. This study specifically focuses on creating a method that facilitates investment decisions for renewing over 500 mm large-diameter conveyance pipe networks, primarily addressing structural safety and economic efficiency. To this end, this study developed ANN-based models for predicting corrosion depth to estimate the structural safety of pipes and ANN-based models to predict failure rate for assessing the economic efficiency of pipe renewal. Based on the developed two prediction models, a dynamic programming (DP)-based method was designed to optimize the renewal investment of the conveyance pipe network. This method minimizes the life cycle cost of the entire network while working within the financial constraints of the water utility. By applying this developed method to a real-world network, this study demonstrates its practicality in supporting investment decisions related to renewal. This proposed management strategy empowers decision-makers to pinpoint the ideal time for pipe renewal, all while effectively minimizing costs and ensuring the safety of pipes.

This study develops a renewal investment plan optimization method to achieve the research objective. This method comprises four steps: data investigation, development of prediction models using ANN, derivation of prediction results, and optimization of an investment plan, as illustrated in the flowchart in Figure 1.
Figure 1

Flowchart of a method to renewal investment plan optimization.

Figure 1

Flowchart of a method to renewal investment plan optimization.

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Structural safety of pipes based on corrosion prediction models

This study estimated the structural safety of water conveyance pipes using SF, as depicted in Equation (1) (Deb et al. 2002):
(1)
where SF is a safety factor, σstrength represents a residual strength of pipe (N/m2), and σstress represents applied stress acting on a pipe (N/m2).
The residual strength of pipes was derived based on the relational equation established by Bae et al. (2008), which correlates a corrosion ratio with residual strength, as presented in Equation (2). Pc represents the ratio of residual thickness to initial thickness. The ANN model predicts the residual thickness based on various pipeline characteristics. This predicted residual thickness is then used to calculate the stress acting on the pipe.
(2)
where Pc is the corrosion ratio between residual thickness and initial pipe thickness (%), a is a coefficient (−4,573.2 was used for steel pipe (SP), and −3,776.8 was used for ductile iron pipe (DIP)), and b is a coefficient (4,520.3 was used for steel pipe (SP), and 4,132.1 was used for ductile iron pipe (DIP)).

This study developed ANN-based corrosion prediction models to acquire a corrosion ratio for calculating the SF. The choice of ANN was driven by its ability to capture complex, non-linear relationships between variables, making it particularly suitable for datasets with intricate patterns. ANN is more adept at learning from multidimensional data where multiple interacting factors influence the outcome. In developing these models, this study utilized pitting corrosion depth data collected from specimens of pipes with a diameter of 500 mm or more from various locations in the Republic of Korea spanning the years 1980 to 2021. During an analysis of collected data, any corrosion depth measurements that registered as 0 mm or exceeded the standard pipe thickness were identified as outliers and subsequently excluded from the sample. Table 1 shows the detailed number of remaining samples after removing outliers.

Table 1

Number of samples and collected data for developing corrosion prediction models

ModelsNumber of samplesCorrosion influence factors
SP external 212 Pipe–soil potential difference, soil resistivity, soil pH, water contents, Cl contents, SO42− contents 
SP internal 180 Water pH, Langelier saturation index (LI) 
DIP external 229 Soil resistivity, soil pH, water contents, Cl contents, SO42− contents 
DIP internal 234 Water pH, LI 
ModelsNumber of samplesCorrosion influence factors
SP external 212 Pipe–soil potential difference, soil resistivity, soil pH, water contents, Cl contents, SO42− contents 
SP internal 180 Water pH, Langelier saturation index (LI) 
DIP external 229 Soil resistivity, soil pH, water contents, Cl contents, SO42− contents 
DIP internal 234 Water pH, LI 

The output of prediction models was designated to represent corrosion depth, while inputs encompassed pipe-related information, including pipe age, pipe diameter, and factors influencing corrosion depth. Model training and validation datasets were partitioned in an 8:2 ratio, with data from the study area reserved for model testing. To determine hyperparameters of models, this study conducted a grid search, a method that exhaustively explores parameter combinations in a structured manner. Hyperparameters subjected to this search included the number of hidden layers (ranging from 2 to 5), the number of nodes in hidden layers (ranging from 2 to 7), learning rate (10−2, 10−3, 10−4, and 10−5), and threshold (10−1, 10−2, 10−3, and 10−4). The sigmoid function was employed as the activation function. Additionally, this study adopted an early stopping technique to prevent overfitting. This technique halts the training process at a specific point during the epoch repetition. The chosen early stopping criterion was when the validation error trend shifted from decreasing to increasing. After predicting the corrosion depth of a pipe within a specific environment and age using corrosion prediction models, a residual strength was calculated according to Equation (2). The method for calculating the applied stress is detailed in the supplementary material.

Economic efficiency of renewal of pipes

The benefit-cost (BC)-centered method proposed by Kim et al. (2019) examined economic efficiency in renewing pipes. Equation (3) represents an equation for calculating BC.
(3)
where BC is the benefit-cost ratio, t is the analysis year (t = 1, 2, … ,T), r is the real discount rate (=0.045), Br(t) is a benefit from reduction of repair cost for pipe failure at t year (USD/y), Bl(t) is a benefit from damage cost by living water outage (USD/y), Bc(t) is a benefit from damage cost by commercial water outage (USD/y), Bi(t) is a benefit from damage cost by industrial water outage (USD/y), and Cr(t) is a renewal cost at t year (USD/y).
This study assessed the extent of damage resulting from a single pipe failure, subsequently calculating benefits associated with the reduction in failure incidents due to renewal. Equations (4)–(7) show benefits categorized into four types. Firstly, if deteriorated pipes are not renewed, it is expected that damage caused by failures will occur. By replacing pipes, the water utility can mitigate the damage that would occur if the pipes were not replaced. The first benefit stemmed from the reduced cost of damage incurred by pipe replacement. The remaining three benefits were determined based on the specific purpose of water usage. When the failure led to the interruption of the living water supply, a benefit was calculated using the replacement cost method. Similarly, when the failure disrupted the commercial water supply, a benefit was determined as the cost of the unsupplied tap water. In cases where the industrial water supply was affected, a benefit was assessed by considering the value of the marginal product. This value represented the cost incurred due to the inability to manufacture products resulting from the water shortage.
(4)
(5)
(6)
(7)
where FR(t,m)WO is the failure rate of pipe m at t year without renewal (failure/km yr), FR(t,m)WI is the failure rate of pipe m at t year with renewal (failure/km yr), m is a target pipe (m = 1, 2, … , M), L(m) is the length of pipe m (m), RC(m) is the repair cost of pipe m (USD/failure), PS is the number of people who experienced outage (people), ts is the water outage time (h/failure), SC is the substitution cost of living water per person (USD/person d), WU is the amount of commercial water use (m3/d), CC is the unit cost of commercial water (USD/m3), SQ is supply shortage (m3/failure), and VMP is the value of the marginal product (USD/m3).
The assumption of this study regarding pipe replacement is that pipes are exchanged for new pipes of the same diameter and material. Equation (8) illustrates an equation used for cost calculation, wherein the cost of pipe renewal is established by applying the unit replacement cost associated with the diameter of the pipe to be replaced.
(8)
where Cr(t) is the renewal cost at t year (USD/y), Crm(t, m) is the renewal cost of pipe m at t year (USD/y), m is the target pipe (m = 1, 2, … , M), UC(m) is the unit renewal cost of pipe m (USD/m), L(m) is the length of pipe m (m), t is the analysis year (t = 1, 2, … , T), and r is the real discount rate (=0.045).

Failure rate prediction models, essential for benefit calculation, were also constructed using an ANN, similar to corrosion prediction models addressed earlier. To build these models, failure history data from pipes with a diameter of 500 mm or more from 1980 to 2021 across the Republic of Korea was utilized. Failures caused by external factors were excluded from the failure history data. Table 2 shows the number of samples and collected data for developing failure rate prediction models. Unlike corrosion prediction models, all available failure data without excluding outliers were included. The model's output was designated as a failure rate, while its input consisted of pipe-related data such as age, diameter, and other pertinent factors. The model development approach mirrored that used for corrosion prediction models.

Table 2

Number of samples and collected data for developing failure rate prediction models

ModelsTotal length (km)Number of failuresFailure influencing factors
SP 2,765.25 723 Installation year (pipe age), diameter, buried depth, topography, coating/lining material, repair history 
DIP 2,005.55 346 
ModelsTotal length (km)Number of failuresFailure influencing factors
SP 2,765.25 723 Installation year (pipe age), diameter, buried depth, topography, coating/lining material, repair history 
DIP 2,005.55 346 

Optimization of renewal plan considering life cycle costs of pipes

Water pipe failures can be categorized into circular breaks, joint failures, longitudinal failures, and corrosion, with various contributing factors (Barton et al. 2019). Additionally, the size of the failure may vary depending on whether the installation process is appropriate (Grigg 2017), making it reasonable to employ distinct maintenance techniques depending on the failure's magnitude (Taiwo et al. 2023). Nevertheless, realistically predicting the size of failures, such as leaks, bursts, deflections, bends, corrosion pits, and circumferential cracks, is a formidable challenge. Consequently, this study establishes a plan assuming that pipes identified as prone to damage by the failure prediction model will be repaired and used. In contrast, pipes with SF below 1.0 will be replaced.

This study employed DP as an optimization algorithm to optimize a renewal investment plan. DP, the method developed by Richard Ernest Bellman, stands as a unique approach for solving optimization problems and addressing multi-stage decision-making scenarios involving continuous decisions (Bellman 1957). In this method, each decision at every stage adheres to Bellman's Principle of Optimality, which dictates that ‘subsequent decision-making should remain optimal based on the state resulting from the initial decision-making, regardless of the optimal policy and sequence of decisions made at the initial state’ (Bellman & Deryfus, 2015). While other optimization techniques, such as genetic algorithms (GAs), are widely used, DP was chosen due to its deterministic nature and ability to efficiently handle problems with strict constraints, such as those involving budget limits. An optimal renewal plan, as determined by DP, was defined as a plan aimed at minimizing the life cycle costs of the pipe networks. Although the life cycle costs encompass planning, designing, constructing, operating, maintaining, and decommissioning facilities, this study did not consider the costs associated with planning, designing, and removing facilities. This decision was made because the costs for planning, designing, and removing facilities were significantly lower than the operating and maintaining costs. Equations (9)–(11) calculated life cycle costs for the entire network.
(9)
(10)
(11)
where Cr(t) is the renewal cost at t year (USD/y), Co(t) is the operation and maintenance cost at t year (USD/y), Crm(t,m) is the renewal cost of pipe m at t year (USD/y), m is the target pipe (m = 1, 2, … , M), UC(m) is the unit renewal cost of pipe m (USD/m), L(m) is the length of pipe m (m), t is the analysis year (t = 1, 2, … , T), r is the real discount rate (=0.045), Com(t,m) is the operation and maintenance cost of pipe m at t year (USD/y), FRm(t,m) is the failure rate of pipe m at t year (failure/km yr), RC(m) is the repair cost of pipe m (USD/failure), and ICF is the indirect cost factor (=3.0).

One rule and one restriction were established for planning. A rule determines which pipes are eligible for renewal and consists of two selection options. The first selection option takes into account the safety of the pipes. Renewal is not considered when the SF at a specific point in time is greater than 3.0. Replacement is an option when the SF ranges from 1.0 to 3.0, and pipes are unquestionably replaced when the SF falls below 1.0. The second selection option pertains to the cost efficiency of renewal. Renewal is not carried out when the BC at a specific point in time is less than 1.0, but it is pursued when the BC exceeds 1.0. Although pipes should be replaced when the SF is less than 1.0, there may be cases where renewal cannot be performed due to a BC less than 1.0. This study prioritizes the SF standard over the BC standard to prevent such problems from occurring.

One restriction imposed is an annual budget constraint. To ensure the sustainability of water utilities, this study considers the available budget's limitations. Equation (12) acts as a constraint, ensuring that the total renewal costs for each year remain within the allocated budget. The logical AND operation checks whether all annual costs meet this condition, combining the results across multiple years to ensure that no year exceeds the budget limit. This constraint guarantees that the renewal process adheres to the financial limitations imposed by the budget.
(12)
where Cr(t) is the renewal cost at t year (USD/y), Crm(t,m) is the renewal cost of pipe m at t year (USD/y), m is the target pipe (m = 1, 2, … , M), and t is the analysis year (t = 1, 2, … , T).
Figure 2 illustrates the structure of an optimization method developed in this study for renewal investment planning based on DP. According to predefined rules, each pipe can be renewed or abandoned in the first year. With a total of M pipes under consideration, the potential scenarios can amount to 2M. Among these, a plan that meets all constraints and incurs the lowest cost is identified as optimal for the first year. Planning for the second year builds upon an optimal plan of the first year, selecting the lowest life cycle cost plan from all possible cases by the second year. This process, employing the principle of DP, is repeated annually up to year T to identify an optimal plan for each subsequent year.
Figure 2

Structure of the developed optimization method based on DP.

Figure 2

Structure of the developed optimization method based on DP.

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This study set analysis scenarios to compare the developed method with other methods, as shown in Table 3.

Table 3

Analysis scenarios

ScenarioDescriptionsRemarks
Do nothing – 
Replace pipes with a specified period (30 years) Commonly used method 
Replace pipes when SF is less than 1.0 Control plan 
Replace pipes when BC is at maximum value Control plan 
Replace pipes using the optimization model Developed in this study 
ScenarioDescriptionsRemarks
Do nothing – 
Replace pipes with a specified period (30 years) Commonly used method 
Replace pipes when SF is less than 1.0 Control plan 
Replace pipes when BC is at maximum value Control plan 
Replace pipes using the optimization model Developed in this study 

Additionally, indicators in studies such as Brito et al. (2020) and Ramos-Salgado et al. (2020) were used to assess plans devised by each method. The first of these indicators is the infrastructure value index (IVI) proposed by Alegre & Coelho (2013). IVI was calculated using Equation (13), which represents an asset-oriented strategy. To calculate the IVI, expected useful life was defined as the period from initial burial until the SF reaches 1.0. The remaining period from the current point until the SF reaches 1.0 was calculated as the residual useful life. Subsequently, a comparison was made between the 40-year average SF and the probability of failure for the entire pipe network. Finally, the total investment amount over 40 years was compared to determine the more cost-effective plan.
(13)
where IVI(t) is the infrastructure value index at t year (%), m is the target pipe (m = 1, 2, … , M), t is the analysis year (t = 1, 2, … , T), rcm,t is the renewal cost of pipe m at t year (USD/y), rulm,t is the residual useful life of pipe m at t year (y), and eulm is the expected useful life of pipe m (y).

To obtain an optimal renewal plan that fulfills the objective function and constraint conditions, this study develops a coded program using Microsoft Visual C + +. Initially, the program calculates the number of cases meeting the SF requirements for each pipe and the economic evaluation results by aggregating the annual instances. The program then assesses whether the total costs incurred across all pipes satisfy the constraints. Furthermore, it carries over the number of compliant cases for examination to the following year. This iterative process continues until the predetermined endpoint is reached, ultimately yielding the minimum life cycle cost for all pipes as the optimal solution.

Development of prediction models

This study developed ANN-based corrosion and failure rate prediction models using corrosion and failure-related data and pipe characteristic data collected throughout the Republic of Korea.

Corrosion prediction models

The proposed corrosion prediction models show a correlation coefficient of 0.85 or higher, indicating that well-developed models capable of accurately capturing the trends in actual data were achieved. Table 4 displays hyperparameter combinations that demonstrate high accuracy while avoiding model overfitting and also presents the correlation coefficient and error for each model. The correlation coefficient was calculated using the Pearson correlation formula, which measures the strength of the linear relationship between predicted and actual values. RMSE was calculated using the standard formula for root mean square error, which quantifies the average difference between predicted and observed values to assess model accuracy. Figure 3 visually illustrates the strong correlation between the predicted and actual values, confirming the model's predictive accuracy.
Table 4

Optimized hyperparameters and performance of each corrosion prediction model

ModelsNumber of nodesLearning rateThresholdCorrelation coefficient (r)
Root mean square error (mm)
TrainingValidationTrainingValidation
SP External (8, 3, 3) 10−4 10−2 0.933 0.941 0.174 0.199 
SP Internal (7, 4, 2) 10−3 10−2 0.957 0.948 0.384 0.396 
DIP External (9, 5, 2) 10−4 10−3 0.862 0.903 0.204 0.175 
DIP Internal (7, 5, 3) 10−4 10−3 0.911 0.854 0.355 0.413 
ModelsNumber of nodesLearning rateThresholdCorrelation coefficient (r)
Root mean square error (mm)
TrainingValidationTrainingValidation
SP External (8, 3, 3) 10−4 10−2 0.933 0.941 0.174 0.199 
SP Internal (7, 4, 2) 10−3 10−2 0.957 0.948 0.384 0.396 
DIP External (9, 5, 2) 10−4 10−3 0.862 0.903 0.204 0.175 
DIP Internal (7, 5, 3) 10−4 10−3 0.911 0.854 0.355 0.413 
Figure 3

Scatter plot for corrosion depth prediction model. (a) SP external, (b) SP internal, (c) DIP external, and (d) DIP internal.

Figure 3

Scatter plot for corrosion depth prediction model. (a) SP external, (b) SP internal, (c) DIP external, and (d) DIP internal.

Close modal
Figure 4 illustrates the results of predicting the corrosion depth of the pipe under various environments, including the average values of influencing factors of the collected corrosion depth, the conditions that most promote corrosion, and the conditions that most suppressive corrosion. The dataset used in this study consists of discrete measurements of pipeline corrosion depth collected from various locations across the country, each with different pipe ages and environmental conditions. The model predicts future corrosion depth by holding other conditions constant and varying only the pipe age. The most corrosive environment refers to the condition where the highest corrosion rate was observed in the data. In contrast, the least corrosive environment corresponds to the condition with the slowest corrosion rate. The average environment represents a moderate corrosion rate based on the dataset. These classifications are derived from actual field data. Figure 4 illustrates the predicted corrosion depth under these varying conditions, reflecting the observed differences in corrosion rates.
Figure 4

Predicted corrosion depth according to the environment. Left-top: SP external, Right-top: SP internal, Left-bottom: DIP external, Right-bottom: DIP internal.

Figure 4

Predicted corrosion depth according to the environment. Left-top: SP external, Right-top: SP internal, Left-bottom: DIP external, Right-bottom: DIP internal.

Close modal

As a result of utilizing the average values of factors influencing corrosion to predict corrosion depth, models demonstrated that internal corrosion depth exceeds that of external corrosion. This study's data, focusing on large-diameter pipes, primarily involves samples from the upper part of the water supply chain, where water flows rapidly and in large volumes. These results suggest an erosive effect that compounds the corrosion issue. Additionally, this study found that overall corrosion depth in DIP was higher than in SP. SPs exhibited a high initial corrosion rate, which gradually decreased over time, whereas DIPs started with a lower corrosion rate that increased over time. The differing corrosion behaviors between SP and DIP can be attributed to their coating materials. Most DIPs examined were coated with cement mortar. At the same time, SPs typically had an epoxy resin coating, according to a study by Kim et al. (2018) on large-diameter pipes in the Republic of Korea, which aligns with the findings of this study, cement mortar coatings were estimated to have a lifespan of around 40 years. In contrast, epoxy resin coatings lasted about 60 years. Therefore, the deeper corrosion observed in DIPs relative to SPs is likely due to the shorter lifespan of their coating material.

For instance, in the case of SP under an average corrosion environment, combined internal and external corrosion depths were predicted to reach a maximum of 6 mm after 40 years of burial. The pipe thickness of a 1,500 mm diameter SP is approximately 15.0 mm (MOE 2010), indicating a local minimum pipe thickness of about 40% after 40 years of burial. Simply put, the pipe's tensile strength is proportionate to the pipe thickness, and the SF decreases to approximately 40% after around 40 years. This study utilized developed corrosion prediction models and applied stress derived from the pipe's environmental conditions to assess the structural safety of the pipeline.

Failure rate prediction models

Failure rate prediction models for SP and DIP were also developed using an ANN. Table 5 displays hyperparameter combinations and the performance of each model. All models exhibited a correlation coefficient of 0.90 or higher, indicating that well-developed models capable of accurately capturing the trends in actual data were achieved.

Table 5

Optimized hyperparameters and performance of each failure rate prediction model

ModelsNumber of nodesLearning rateThresholdCorrelation coefficient (r)
Root mean square error (failure/km yr)
TrainingValidationTrainingValidation
SP (8, 4, 2) 10−3 10−2 0.944 0.920 0.054 0.078 
DIP (9, 3, 2) 10−3 10−2 0.906 0.917 0.104 0.096 
ModelsNumber of nodesLearning rateThresholdCorrelation coefficient (r)
Root mean square error (failure/km yr)
TrainingValidationTrainingValidation
SP (8, 4, 2) 10−3 10−2 0.944 0.920 0.054 0.078 
DIP (9, 3, 2) 10−3 10−2 0.906 0.917 0.104 0.096 

Figure 5 illustrates the results of predicting the failure rate of the pipe under various scenarios, including the average values of the collected failure influencing factors, the conditions that most promote failure, and the conditions that most suppressive failure.
Figure 5

Predicted failure rate according to the environment. Left: SP, Right: DIP.

Figure 5

Predicted failure rate according to the environment. Left: SP, Right: DIP.

Close modal

For SPs, the predicted failure rate typically shows a pattern where the rate increases sharply after a certain period. Despite some variations based on the conditions affecting failure, this rapid escalation in failure rate generally occurs after 20 years of burial. Conversely, DIPs exhibit an immediate rapid increase in the failure rate upon burial under failure-promoting conditions, with a tendency for this rate to rise continuously under other conditions.

Previously, the corrosion depth of DIP was greater than that of SP. However, the average failure rate was found to be lower for DIP compared to SP. DIP requires a thicker pipe thickness to achieve similar tensile strength even with the same pipe diameter. In Korea, for 1,000 mm pipes, the standard pipe thickness for SP is 10 mm, while for DIP, it is 16 mm (MOE 2010). This difference in basic pipe thickness is believed to explain the greater corrosion depth, but the failure rate is lower in DIP. Additionally, SP mainly uses welding, while DIP uses mechanical jointing. The worker's skill level often influences the construction status in welding, and it is suggested that the higher failure rate of SP, compared to DIP, may be linked to numerous failures, mainly leakages, occurring in buried SP during periods of insufficient construction technique in the past.

Case study

Based on the developed prediction models, a renewal investment optimization method developed in this study was applied in the target area in the Republic of Korea.

Target area: KJ conveyance pipe network

The KJ conveyance pipe network was selected as the target area for establishing an optimal renewal investment plan due to its high proportion of aging pipes (32.3% exceeding 30 years of service) and a significant history of failures. To conduct the analysis, detailed data regarding the network were collected from official records maintained by the water utility managing the KJ region. The data included information on pipe material, diameter, installation year, and failure history. The preprocessed data were then partitioned into training and testing datasets to develop predictive models, ensuring that testing data were not used during model training. Environmental conditions influencing pipe performance, such as soil type, water quality, and topography, were also collected and matched to the corresponding pipe segments. This comprehensive dataset was the foundation for calculating the SF and BC values and applying the developed optimization method. Table 6 presents the detailed characteristics of the KJ conveyance network, and Figure 6 provides a visual representation of the study area. The storage facilities within the network primarily support the industrial complex, while residential and commercial areas are supplied with water through an interconnected network of water tanks.
Table 6

Details of the target area (KJ conveyance pipe network)

ClassificationDetails
Installation year 1972–2001 
Pipe material and diameter SP: 600–1,000 mm, DIP: 500 mm 
Failure history (from 1980 to 2021) SP: 32 failures, DIP: 32 failures 
Pipe length SP: 69.97 km, DIP: 32.33 km 
Water supply Approximately 70,000 m3 /d 
ClassificationDetails
Installation year 1972–2001 
Pipe material and diameter SP: 600–1,000 mm, DIP: 500 mm 
Failure history (from 1980 to 2021) SP: 32 failures, DIP: 32 failures 
Pipe length SP: 69.97 km, DIP: 32.33 km 
Water supply Approximately 70,000 m3 /d 
Figure 6

KJ multi-regional water supply pipes, the target area.

Figure 6

KJ multi-regional water supply pipes, the target area.

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Renewal investment plans by scenarios

Figure 7 illustrates renewal investment plans derived for each scenario. Table 7 summarizes the total investment costs and the corresponding effects for each plan.
Table 7

Costs needed and expected performance of renewal scenarios

ScenarioTotal costs for 40 years (Million USD)Annual average safety factor (−)Annual average failure rate (failure/km·yr)Annual average IVI (−)IVI at end point (−)IVI changes (Start point to end point) (−)
79.38 0.92 0.64 0.16 0.00 ▾ 0.39 
58.02 1.64 0.39 0.34 0.31 ▾ 0.07 
55.82 2.63 0.22 0.43 0.51 ▴ 0.12 
48.17 2.00 0.45 0.34 0.30 ▾ 0.09 
53.75 2.56 0.18 0.51 0.62 ▴ 0.23 
ScenarioTotal costs for 40 years (Million USD)Annual average safety factor (−)Annual average failure rate (failure/km·yr)Annual average IVI (−)IVI at end point (−)IVI changes (Start point to end point) (−)
79.38 0.92 0.64 0.16 0.00 ▾ 0.39 
58.02 1.64 0.39 0.34 0.31 ▾ 0.07 
55.82 2.63 0.22 0.43 0.51 ▴ 0.12 
48.17 2.00 0.45 0.34 0.30 ▾ 0.09 
53.75 2.56 0.18 0.51 0.62 ▴ 0.23 
Figure 7

Costs of each scenario and change of IVI for 40 years (2023–2062).

Figure 7

Costs of each scenario and change of IVI for 40 years (2023–2062).

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In Figure 7, Scenario A, representing the ‘do nothing’ approach, exhibited escalating maintenance costs amounting to 79.38 million USD over 40 years. This was due to the absence of renewal investment, leading to increased failure incidents and higher repair costs. This highlights that neglecting the renewal of aging pipes increases long-term costs and exposes water utilities to significant operational risks. On the other hand, Scenarios B, C, and D, where various renewal strategies were implemented, partially mitigated maintenance costs by reducing the frequency and severity of failures. However, these scenarios also demonstrated notable budget concentration in specific years, as large-scale pipe replacements were conducted during the planned replacement periods. This irregular budget allocation challenges water utilities regarding investment efficiency and financial planning.

Among the alternative plans, Scenario D emerged as the least costly option, with a total expenditure of 48.17 million USD over 40 years. In this scenario, pipe replacement was limited to segments with confirmed economic feasibility (BC > 1.0). The analysis revealed that replacements were primarily focused on larger-diameter pipes located at the top of the supply process, where failures caused substantial damage. Conversely, smaller-diameter pipes at the bottom of the supply chain were often neglected, resulting in minor but persistent damage. Although Scenario D minimized major damages at a lower cost, it was deemed less favorable from a water supply service perspective due to its potential impact on consumers.

Scenarios C and E utilized structural safety (SF) as a decision criterion, mandating replacement when the SF fell below 1.0. Scenario E, however, applied a budget constraint of 2,000 USD annually through DP, leading to consistent annual investment. This approach enabled water utilities to allocate resources efficiently over the 40-year period, avoiding the budget spikes observed in Scenario C. As a result, Scenario E achieved the highest IVI of 0.62 and the lowest average failure rate, making it the most balanced and sustainable plan among all scenarios.

In contrast to the irregular costs of other renewal methods, Scenario E effectively spread the investment across the entire analysis period, ensuring that water utilities could maintain high structural safety and asset value while minimizing risks to the pipe network. While Scenario E incurred slightly higher costs than economically focused plans like Scenario D, its ability to consistently maintain pipe safety and IVI underscores its stability and long-term viability.

Figure 8 outlines the action plans derived from applying the optimally evaluated Scenario E to the target area, highlighting the specific pipes that require renewal and their priority levels. The renewal plan prioritizes pipes near Purification Plant A, as these pipes are located at the start of the supply process, and their failure could lead to widespread disruptions across the network. This strategic prioritization underscores the necessity of addressing high-risk pipes first to maintain the stability and reliability of the entire system.
Figure 8

Optimal action plan for the target area (Scenario E).

Figure 8

Optimal action plan for the target area (Scenario E).

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Applying the developed method to the KJ conveyance pipe network demonstrates its effectiveness in achieving long-term sustainability. Specifically, the optimized Scenario E provides a balanced approach by adhering to an annual budget constraint of 2,000 USD while addressing economic efficiency and structural safety. By systematically renewing pipes based on their SFs and BC ratios, this method ensures consistent investment across the 40-year analysis period, avoiding the budgetary spikes observed in other scenarios. This approach provides multiple additional benefits compared to traditional methods, making it a more effective and sustainable solution for water utility management. First, the water utility can manage its pipes economically by minimizing life cycle costs while maintaining reliable service delivery. By adhering to a consistent annual investment plan, the utility can avoid unnecessary expenditure spikes and ensure financial stability over the long term. Second, this approach enhances structural safety within the pipe network. Systematically addressing pipes with critical safety risks in a timely manner significantly reduces the likelihood of catastrophic failures that could disrupt water supply services and incur substantial repair costs. Lastly, the prioritization strategy embedded in this method offers a clear and practical roadmap for renewal activities. This enables the water utility to allocate resources more effectively and plan operations more efficiently, ensuring that the most critical sections of the network are addressed first while maintaining overall network stability.

The increasing accumulation of aging pipes highlights the need for their effective management. In particular, in the case of conveyance pipes with large pipe diameters, more active management strategies are needed because the ripple effects in the event of failure are significant. This study introduces an optimization method for renewal investment plans based on DP. This approach simultaneously considers the structural safety of pipes and economic efficiency of renewal, areas traditionally addressed separately, and validates the methodology through a case study.

First, this study develops ANN-based models to predict pipe corrosion, assessing the structural safety of pipes. Failure rate prediction models are also developed to evaluate the economic efficiency of pipe renewal. Both models validated strong predictive capability, with correlation coefficients exceeding 0.85, indicating high accuracy in representing the collected data. DIP typically exhibited greater corrosion depth than SP, while SP showed a higher failure rate than DIP. This discrepancy was attributed to differences in pipe thickness and construction ability during periods of insufficient construction capacity.

Building on the developed corrosion and failure rate prediction models, this study evaluated the pipes' structural safety and the pipe renewal's economic efficiency. Subsequently, this study devised an optimization method to minimize life cycle costs while adhering to annual investment budget constraints, which was applied to a case study area. The renewal investment strategy formulated using the developed method proved more effective than the plan using a commonly used method, offering superior safety and economic advantages. The developed method achieved the highest IVI of 0.62, a metric for assessing renewal investment plan performance, and recorded the lowest average failure rate. This underscores its significant benefit in reducing risk within the conveyance pipe network. Moreover, the analysis revealed that leveraging annual budget constraints enables water utilities to manage their budgets efficiently, ensuring effective investment within predetermined limits each year.

Lastly, Scenario A demonstrated the economic benefits of pursuing the renewal of pipes by any means compared to abandoning them due to maintenance costs. This finding underscores the importance of devising proactive investment plans to renovate aging water infrastructure. Various frameworks have recently been developed to manage water infrastructures effectively within the asset management paradigm. The method introduced in this study can serve as a foundational technology for future asset management initiatives. This study presents limitations that necessitate further research to enhance the developed model. This study focused exclusively on the safety of conveyance pipes and the economic feasibility of renewal, overlooking water quality factors crucial for pipe renewal objectives. Given that distribution pipes also represent a significant area for investment, future studies could enhance the method by incorporating water quality considerations of the distribution network, thereby addressing current limitations.

Data cannot be made publicly available; readers should contact the corresponding author for details.

The authors declare there is no conflict.

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Author notes

These two authors contributed equally to this work.

This is an Open Access article distributed under the terms of the Creative Commons Attribution Licence (CC BY 4.0), which permits copying, adaptation and redistribution, provided the original work is properly cited (http://creativecommons.org/licenses/by/4.0/).

Supplementary data