The Special Region of Yogyakarta is one of the areas impacted by the 2006 earthquake which damaged vital infrastructures, including water distribution networks (WDN). The vulnerability of these networks increases because the design process does not consider the mitigation strategy of natural disasters. This region does not have any tools to estimate the infrastructure vulnerability for underground lifeline facilities, including WDN. Therefore, this study aimed to develop a framework to generate a Seismic Vulnerability Index for Water Distribution Network (SVI-WDN) for the Special Region of Yogyakarta which has been known to be exposed to many earthquake incidences. The framework presents a process to develop a SVI-WDN which consist of three steps. First step, to obtain the criteria, sub-criteria, their value range and the corresponding score for each value. Second step, to normalize the sub-criteria score. The third step, to obtain the criteria and sub-criteria weight by using the analytical hierarchy process (AHP). Lastly, the calculation of a vulnerability index for water distribution. Additional steps for visualizing the index are by generating a geographical information system map representing index value. Thus, this study presents a reproducible framework that can assist water authorities to prioritize the water distribution pipe segment which requires more intensive handling and maintenance.

  • To develop a conceptual framework for a seismic vulnerability index for water distribution network.

  • Weighting method in this study uses AHP and involves three group of experts, they are a government official, academics and a water supply specialist.

  • The vulnerability index was visualized through a geographical information system (GIS) map.

  • The index can be used to prioritize the pipe segment which requires intensive handling and maintenance.

Graphical Abstract

Graphical Abstract

The Special Region of Yogyakarta is one of the areas located in the fire ring zone, which has a high risk of disasters due to primary hazards such as earthquakes, tsunamis, and volcano eruptions (Muntafi et al. 2020). These hazards cause the most severe impact, with extended casualties emphasizing the failure of infrastructures in the post-disaster period (Eastman et al. 1995). During this period, water supply infrastructures are also most vulnerable and required. According to Li (2007), facilities such as water intake, treatment, and distribution pipe networks, are prone to several disasters. This was consistent (Ratnapradipa et al. 2012; Hlavinek et al. 2008), where earthquakes caused severe effects by rupturing water infrastructures, pipes, spare parts, and materials. Damage to the water supply infrastructure also creates shortages, leading to various diseases such as cholera, typhoid, and diarrhoea (Alexoudi et al. 2007). This requires a vulnerability assessment method to avoid severe damage to water supply infrastructure. The methods that are required for assessment method are classified into four categories, (a) Index-based method, (b) geographical information system (GIS)-based decision support tools, (c) visualization tools, and (d) dynamic computer models (Satta 2014). An index-based approach provides a single unitless aggregated value for vulnerability level expression. This value simplifies complex and interacting parameters, leading to its usefulness and easy understanding for management tools (Balica et al. 2012). Many previous studies also used the index method to estimate the vulnerability level of a system (Hosseini & Mirza-Hessabi 1999; Balica et al. 2012; Adhikary et al. 2018; Sekovski et al. 2020; Baig et al. 2021).

In the development of an index, the estimation of the criteria/sub-criteria is very important, although no suitable method was observed for weight determination (Böhringer & Jochem 2011). This determination method is often obtained through the availability of data, as well as the relationship pattern between parameters and time constraints (Sutadian et al. 2017). In this process, two methods are commonly used, namely statistical and participatory techniques. In Zardari et al. (2015), the procedure of weight identification was unclear through the statistical method, leading to the higher values of insignificant criteria. This method subsequently requires a high number of sample sizes, which are commonly problematic in cases with limited data availability (Hutcheson & Sofroniou 1999). It also mostly assumes linear relationships among selected criteria/sub-criteria, which is often uncommon in related cases. Meanwhile, the participatory methods, e.g., Delphi and AHP techniques, are highly popular for index estimation. According to Franklin & Hart (2007) and Hartwich (1998), Delphi was described as an expensive method with a time-consuming process, compared to other related techniques (Zardari et al. 2015). For AHP, a pairwise comparison sequence is mostly used on the relative values ​​between two criteria/sub-criteria. It also has similar accurate results as Delphi and is described as an easy-to-use process carried out in a relatively short time (Sutadian et al. 2017). Based on these methodological benefits and drawbacks, this study selected the index-based method developed by the participatory approach of AHP. Many reports also developed the vulnerability index for water supply systems (Nojima 2008; Karamouz et al. 2010), which was only implemented in specific regions or countries. This regional restriction led to unguaranteed implementations in other areas. Therefore, this study aims to develop a seismic vulnerability index for water distribution network (SVI-WDN) framework for the Special Region of Yogyakarta. This SVI-WDN framework is a tool aimed achieving a consensus among many aspects, which eventually produce a single value (index) representing the vulnerability status of water distribution systems. Outcomes from the SVI-WDN will be the handling prioritization of pipe segments in the study area. The structure of this report is observed as follows: (A) the importance of SVI and the index development methods, (B) the occurrences of earthquakes in the Special Region of Yogyakarta and their impact on water infrastructure based on a previous incident (the 2006 earthquake), (C) the literature review of the existing seismic vulnerability assessment and outputs on the criteria and sub-criteria mostly relevant in representing the level of SVI, and (D) a detailed description of the AHP application, to develop the seismic vulnerability index.

Occurrence of the Yogyakarta earthquake disaster and its impact on water infrastructure

The Special Region of Yogyakarta is prone to earthquakes as a 6.3 magnitude occurrence was experienced in 2006, causing a total loss of Rp. 85.6 billion. The epicenter of the earthquake was 3.7 km south of the city of Yogyakarta at the depth of 33 km. The earthquake was triggered by the movement of the Opak fault, which extends from the southern to the northern parts of this region. According to the IRBI (Indonesian Disaster Risk Index), the province of the Special Region of Yogyakarta has a moderate risk disaster index with an earthquake frequency of 133 times/year. This was the second largest frequency after the landslide disaster in 2021. Compared to other Indonesian provinces, the frequency of earthquake occurrences in Yogyakarta is very high. Figure 1 shows that the area with a high-risk category for earthquakes is approximately 27.32% of the total area of Yogyakarta Province.
Figure 1

Earthquake risk map in the Special Region of Yogyakarta (BNPB 2021).

Figure 1

Earthquake risk map in the Special Region of Yogyakarta (BNPB 2021).

Close modal

Based on Figure 1, the damage incurred by the pipeline network included the activities of installation, replacement, as well as repair of pipes and bridges. In Yogyakarta, 10,952 damage points were observed, costing around Rp. 5 billion. The size of the damaged pipe also had a diameter of 50 to 250 mm. Other damaged areas were shallow wells and much industrial spring water broncaptering. These were the two primary water sources for 70–95% of inhabitants (BAPPENAS and Worldbank 2006). The service area belonging to the Water Utilities of Yogyakarta City was also highly affected with the highest damaged pipe.

Development of seismic vulnerability index for water distribution network

A conceptual framework was developed by reviewing the existing seismic vulnerability assessment criteria from various studies. In this case, SVI-WDN emphasized all the applicable reliable aspects in the Special Region of Yogyakarta, Indonesia. The vulnerability score for sub-criteria is classified based on the severity level shown by a sub-criterion with certain values. The weighting of sub-criteria is based on the AHP method. From sub-criteria vulnerability score and weight, seismic vulnerability index can be calculated. The conceptual framework for SVI-WDN is shown in Figure 2.
Figure 2

Conceptual framework for SVI-WDN.

Figure 2

Conceptual framework for SVI-WDN.

Close modal

Using the AHP method, the major steps in weight determination are as follows:

  • a.

    Establish a hierarchy.

  • b.

    Calculate the sub-criteria weight and SVI-WDN.

  • c.

    Visualize the index into the GIS map.

Figure 3 shows the detailed steps to develop the conceptual SVI-WDN framework. In this process, the first questionnaire obtained opinions and approval on criteria, sub-criteria, and their scores. Meanwhile, the second questionnaire was distributed to determine the aggregated weight or importance level of every sub-criterion. The weight for all sub-criteria and criteria was also applied to the study area. with a GIS map showing the vulnerability of the water distribution network.
Figure 3

Flow chart of SVI-WDN development.

Figure 3

Flow chart of SVI-WDN development.

Close modal

There were three criteria found in the existing literature, namely physical, environmental and operational criteria. The physical criteria included the externals properties of the piping network. Meanwhile, the environmental aspects mainly dealt with the external factors influencing WDN's performance, with the operational criteria focusing on the activities required to continuously initiate the water supply system, toward providing the necessary service. Another review was conducted to ensure that the selected criteria and sub-criteria represented the study area's physical, environmental, and operational characteristics by excluding contradictions.

Establish a hierarchy

An extensive literature review including journal articles, regulations, standards, technical guidances and reports was conducted to identify the initial criteria, sub-criteria, and value range of SVI-WDN. In this case, sub-criteria score was classified into various scales. However, some studies did not classify a criterion due to the assessment of vulnerability using only the sub-criteria.

According to Nojima (2008), Adhikary et al. (2018), and Zohra et al. (2012) seismic vulnerability was examined for lifeline infrastructures. Other reports also explained multi-disaster vulnerability assessment in different disaster-prone countries, including Japan, Canada, Algeria, and Italy. The proposed experimental methods included statistical estimation, a hierarchal fuzzy expert system, multi-criteria decision-making, and hydraulic modelling. Table 1 presents the criteria and sub-criteria from these literature reviews; seven studies analysed the vulnerability index for global water infrastructure.

Table 1

Criteria and sub-criteria of existing studies of vulnerability in water supply system

AuthorObjectCriteriaSub-criteriaRange
Nojima (2008)  Distribution pipe  Pipe diameter Ø > 1,100 mm 
700 mm < Ø ≤ 1,000 mm 
500 mm < Ø < 600 mm 
300 mm < Ø < 450 mm 
200 mm < Ø < 250 mm 
100 mm < Ø < 150 mm 
Ø < 75 mm 
 Pipe material/joint type Cast Iron Pipe 
Ductile Cast Iron Pipe (Standard joint: Type A, K, and T) 
Ductile Cast Iron Pipe (Aseismic joint: Type S and S-II) 
Welded-joint Steel Pipe 
Screw-joint Steel Pipe 
Polyvinyl Chloride Pipe 
Asbestos Cement Pipe 
Adhikary et al. (2018)  Distribution pipeline  Pipe diameter Ø > 1,000 mm 
450 mm < Ø < 1,000 mm 
250 mm < Ø < 450 mm 
150 mm < Ø < 250 mm 
75 mm < Ø < 150 mm 
Ø < 75 mm 
Pipe material Ductile Iron 
Cast Iron 
Steel 
Polyvinyl chloride 
Asbestos Cement 
Settlement and landslide No Risk 
Average Risk 
Important Risk 
Seismic intensity (MMI) MMI < 8 
8 < MMI < 9 
9 < MMI < 10 
10 < MMI < 11 
11 < MMI 
Liquefaction 0 ≤ PL < 5 
5 ≤ PL < 15 
15 ≤ PL 
Fault crossing 2–4 nodes 
Zohra et al. (2012)  Distribution pipes  Pipe diameter Ø > 1,000 mm 
450 mm < Ø < 1,000 mm 
250 mm < Ø < 450 mm 
150 mm < Ø < 250 mm 
75 mm < Ø < 150 mm 
Ø < 75 mm 
Pipe material Ductile cast iron 
Cast iron 
PVC 
Steel 
Galvanized steel 
Asbestos cement 
PEHD 
Intersection pipe fault No intersection 
One intersection several 
Intersections 
Settlement/landslide No risk 
Average risk 
Important risk 
Type ground Deposit Soil: Alluvium: very soft 
Deposit Soil: Diluvium: soft 
Weathered Rock: Medium 
Moderate Weathered Rock: Medium 
Slightly/No Weathered Rock: Stiff/Hard 0.50 
Seismic intensity (MMI) MMI < 8 
8 < MMI < 9 
9 < MMI < 10 
10 < MMI < 11 
11 ≤ MMI 
Liquefaction 0 ≤ PL < 5 
5 ≤ PL < 15 
15 ≤ PL 
Laucelli et al. (2014); Laucelli & Giustolisi (2015Distribution pipes  Pipe material Steel 
Ductile iron 
Cast iron 
Asbestos cement 
Concrete 
Diameter 100 mm (4 in.)–300 mm (12 in.), 
> 300 mm (12 in.) 
Joint type Welded joint 
Flange joints 
Caulked joints 
Soils Database EXNET 
Yan & Vairavamoorthy (2003)  Distribution pipe Physical Pipe age 1952–1992 
Pipe diameter 300–500 mm 
Pipe material Unlined Cast Iron 
Lined Cast Iron 
Environment Road loading Very Busy 
Busy 
Very Busy 
Soil condition – 
Surrounding/settlement Excellent 
Very Good 
Good 
Quite Good 
Medium 
Poor 
Fares & Zayed (2008)  Distribution system Physical Material Cast Iron 
Cast Iron Post War 
PVC 
Ductile Iron 
Pipe age – 
Diameter – 
Protection method – 
Environmental Soil type – 
Water table level – 
Daily traffic – 
Operational Breakage rate – 
Hydraulic factor – 
Water quality – 
Leakage – 
Post failure Cost of repair – 
Damage to surroundings/business – 
distribution, Loss of protection – 
Type of service area – 
Godfrey et al. (2002)  Distribution system  Pipe material PVC 
Flexible Polyethylene (PE) 
Asbestos Cement (AC) 
Steel (ST) 
Ductile Iron (DI) 
Galvanized Iron (GI) 
Pipe diameter 50–800 mm 
Pipe length 5–4,000 m 
Pipe age 10–40 years (Short life) 
40–100 years (Long life) 
Leakage data 1–5 records of leakage 
Discontinuity 1–8 recorded discontinuities 
AuthorObjectCriteriaSub-criteriaRange
Nojima (2008)  Distribution pipe  Pipe diameter Ø > 1,100 mm 
700 mm < Ø ≤ 1,000 mm 
500 mm < Ø < 600 mm 
300 mm < Ø < 450 mm 
200 mm < Ø < 250 mm 
100 mm < Ø < 150 mm 
Ø < 75 mm 
 Pipe material/joint type Cast Iron Pipe 
Ductile Cast Iron Pipe (Standard joint: Type A, K, and T) 
Ductile Cast Iron Pipe (Aseismic joint: Type S and S-II) 
Welded-joint Steel Pipe 
Screw-joint Steel Pipe 
Polyvinyl Chloride Pipe 
Asbestos Cement Pipe 
Adhikary et al. (2018)  Distribution pipeline  Pipe diameter Ø > 1,000 mm 
450 mm < Ø < 1,000 mm 
250 mm < Ø < 450 mm 
150 mm < Ø < 250 mm 
75 mm < Ø < 150 mm 
Ø < 75 mm 
Pipe material Ductile Iron 
Cast Iron 
Steel 
Polyvinyl chloride 
Asbestos Cement 
Settlement and landslide No Risk 
Average Risk 
Important Risk 
Seismic intensity (MMI) MMI < 8 
8 < MMI < 9 
9 < MMI < 10 
10 < MMI < 11 
11 < MMI 
Liquefaction 0 ≤ PL < 5 
5 ≤ PL < 15 
15 ≤ PL 
Fault crossing 2–4 nodes 
Zohra et al. (2012)  Distribution pipes  Pipe diameter Ø > 1,000 mm 
450 mm < Ø < 1,000 mm 
250 mm < Ø < 450 mm 
150 mm < Ø < 250 mm 
75 mm < Ø < 150 mm 
Ø < 75 mm 
Pipe material Ductile cast iron 
Cast iron 
PVC 
Steel 
Galvanized steel 
Asbestos cement 
PEHD 
Intersection pipe fault No intersection 
One intersection several 
Intersections 
Settlement/landslide No risk 
Average risk 
Important risk 
Type ground Deposit Soil: Alluvium: very soft 
Deposit Soil: Diluvium: soft 
Weathered Rock: Medium 
Moderate Weathered Rock: Medium 
Slightly/No Weathered Rock: Stiff/Hard 0.50 
Seismic intensity (MMI) MMI < 8 
8 < MMI < 9 
9 < MMI < 10 
10 < MMI < 11 
11 ≤ MMI 
Liquefaction 0 ≤ PL < 5 
5 ≤ PL < 15 
15 ≤ PL 
Laucelli et al. (2014); Laucelli & Giustolisi (2015Distribution pipes  Pipe material Steel 
Ductile iron 
Cast iron 
Asbestos cement 
Concrete 
Diameter 100 mm (4 in.)–300 mm (12 in.), 
> 300 mm (12 in.) 
Joint type Welded joint 
Flange joints 
Caulked joints 
Soils Database EXNET 
Yan & Vairavamoorthy (2003)  Distribution pipe Physical Pipe age 1952–1992 
Pipe diameter 300–500 mm 
Pipe material Unlined Cast Iron 
Lined Cast Iron 
Environment Road loading Very Busy 
Busy 
Very Busy 
Soil condition – 
Surrounding/settlement Excellent 
Very Good 
Good 
Quite Good 
Medium 
Poor 
Fares & Zayed (2008)  Distribution system Physical Material Cast Iron 
Cast Iron Post War 
PVC 
Ductile Iron 
Pipe age – 
Diameter – 
Protection method – 
Environmental Soil type – 
Water table level – 
Daily traffic – 
Operational Breakage rate – 
Hydraulic factor – 
Water quality – 
Leakage – 
Post failure Cost of repair – 
Damage to surroundings/business – 
distribution, Loss of protection – 
Type of service area – 
Godfrey et al. (2002)  Distribution system  Pipe material PVC 
Flexible Polyethylene (PE) 
Asbestos Cement (AC) 
Steel (ST) 
Ductile Iron (DI) 
Galvanized Iron (GI) 
Pipe diameter 50–800 mm 
Pipe length 5–4,000 m 
Pipe age 10–40 years (Short life) 
40–100 years (Long life) 
Leakage data 1–5 records of leakage 
Discontinuity 1–8 recorded discontinuities 

Based on Table 1, subsequent selections were conducted by considering all the criteria and sub-criteria relevant to the area and condition of the Yogyakarta water supply system. Several sub-criteria were also filtered based on two factors, namely relevancy and data availability. Moreover, the excluded sub-criteria from Table 1 or another source included (1) liquefaction, (2) Repair rate, (3) intersection pipe fault (Zohra et al. 2012; Adhikary et al. 2018), (4) number of repairs, (5) peak ground velocity (PGV), (6) road loading, (7) water table level, (8) daily traffic, (9) cost of repair, (10) damage to surroundings (11) loss of protection, and (12) type of service area (Yan & Vairavamoorthy 2003; Fares & Zayed 2008). Liquefaction was inrelevant due to following: liquefaction was a relatively minor event in Yogyakarta, and the system managed by water utility companies was mostly installed in the city or sub-district capital, which was from the incidence of landslides. Data road loading and daily traffic were also not considered because the pipe burial location was at the roadside or sidewalk. Based on data unavailability, the other irrelevant sub-criteria were subsequently excluded. The values for pressure, leakage record, water quality, and discontinuity were obtained from other literature sources related to Indonesian WDN. According to the structural analysis and connectivity, the vulnerability index was calculated to identify the susceptible parts (Pinto et al. 2010). This indicated the requirement of vulnerability, to represent a score used for index calculations in a formula (Eastman et al. 1995). The utilized value ranges in this development included vulnerability (Zohra et al. 2012) and several regulations related to local and international pipe standards. In this experiment, various scores were assigned to the range value of the sub-criteria, where the lowest and highest estimations had low and great effects (not vulnerable and highly vulnerable), respectively. After filtration through the two initially grouped factors, the sub-criteria were re-grouped into environmental, physical, and operational standards. Table 2 shows the selected criteria and sub-criteria.

Table 2

Criteria and sub-criteria used in this study

CriteriaSub-criteriaRangeScoreDescription
A. Physical A1. Pipe diameter (Zohra et al. 2012Ø > 1,000 mm The pipes created affects the susceptibility to the heavy shock caused by human activities or a natural disaster, such as an earthquake. This indicates the smaller the pipe diameter, the more susceptible the risk of shock. 
600 mm < Ø ≤ 1,000 mm 
450 mm < Ø < 600 mm 
250 mm < Ø < 450 mm 
150 mm < Ø < 250 mm 
100 mm < Ø < 150 mm 
Ø < 100 mm 
A2. Pipe material (Godfrey et al. 2002; Zohra et al. 2012HDPE The pipes created from various materials fail in numerous ppatterns. According to Godfrey et al. (2002), pipe materials determined the levels of vulnerability. The materials of Reinforced Cement Concrete (RCC) and cast iron (CI) also had a higher vulnerability risk than AC and PVC (asbestos cement) and (polyvinyl chloride). Meanwhile, PVC and high-density polyvinyl chloride (HDPE) had the lowest vulnerability risk. Failure due to corrosion was also more common in cast iron pipes than in other materials. 
PVC 
Steel 
Asbestos cement 
Cast iron 
Ductile cast iron 
Galvanized steel 
A3. Pipe age (Godfrey et al. 2002< 10 years Age and corrosion accentuate damage in segmented pipelines and iron-made pipes. Age also determines their strength with the friction between the water and the pipe wall occurring due to the continuous flow, thinned out the pipe wall. 
10 ≤ years < 40 
40 ≤ years < 75 
75 ≤ years < 100 
> 100 years 
A4. Pipe length (Godfrey et al. 2002< 100 m Pipe length is known as continuous pipelines. which materials correlate with the welding method. According to previous studies, this pipeline was less vulnerable than segmented jointed materials. 
100 ≤ m < 750 
750 ≤ m < 2,000 
> 2,000 m 
A5. Protection method Protection Lined and protected pipes are less susceptible to corrosion and also decrease the material's thickness by creating stress concentration. 
No protection 
A6. Joint type (Zohra et al. 2012Ductile cast iron aseismic joint Some joints fail prematurely. Also, screwed and threaded steel fails more frequently than other joints. 
Welded-joint steel 
Ductile as iron standard join 
Polyvinyl chloride 
Cast iron 
Asbestos cement 
Screw-joint steel 
B. Environmen-tal B1. Fault No intersection Surface fault areas create local permanent ground deformation. This means the closer the pipelines to the fault areas, the more vulnerability to damage. 
1 Intersection 
> 1 Intersection 
B2. Settlement/Landslide (Zohra et al. 2012Non-populated areas The surface load of the embedded pipe is even greater in populated areas where almost all of the ground surface is covered by other infrastructure or roads. Densely populated areas are also more vulnerable to water supply interruptions. 
Mid densely populated areas 
Densely populated areas 
B3. Seismic intensity (Zohra et al. 2012MMI < 8 Seismic activity affects a large area and causes widespread damage. It also increases pipe stress, leading to damage-based pressure surges. (Karamouz et al. 2010). 
8 ≤ MMI < 9 
9 ≤ MMI < 10 
10 ≤ MMI < 11 
11 ≤ MMI 
B4. Type soil (Zohra et al. 2012Slightly/No Weathered Rock: Hard Putra et al. (2019) stated that corrosion caused pipe failure. This condition occurs due to physical and chemical reactions between pipe material and soil. Therefore, the identification of the solid properties is very necessary to estimate the potential degree of pipe corrosion. 
Moderate Weathered Rock: Medium 
Weathered Rock: Medium 
Deposit soil: diluvium: soft 
Deposit soil (alluvium: very soft) 
C. Operational C1. Breakage history (Nojima 2008Pipeline with no breakage history The breakage history defines a pipeline with damage. This is classified as vulnerable and vice versa. 
Pipeline with breakage history 
C2. Pressure (Specifications of the water treatment installation unit 2014< 6 atm Fire is likely to occur due to an earthquake, where a distribution system provides sufficient pressure on the consumers (Kanta & Brumbelow 2013). 
6 ≤ atm < 8 
> 8 atm 
C3. Leakage record (Maintenance of drinking water supply system 2016< 20% Leaks erode linings and increase soil moisture in the pipe zone. 
> 20% 
C4. Water quality (Standard Methods for Water Company Performance 2016≥ 80% Aggressive water promotes pipe corrosion. This indicates that the pH of non-aggressive water should be between 6.5 to 8.5. However, the aggression is often determined by the pH and other water quality parameters, such as alkalinity and the presence of carbonates. This proves that the range of values reflects the percentage of the sample compliant with the standard. 
60 ≤ %< 80 
40 ≤ %< 60 
20 ≤ %< 40 
<20% 
C5. Discontinuity (Standard Methods for Water Company Performance 2016Intermittent Continuous and intermittent supply pipes deliver water to the customers for 24 hours and less, respectively. This intermittent delivery is due to the issue of water availability or the inability of the hydraulic capacities to meet the required demand. 
Continue 
CriteriaSub-criteriaRangeScoreDescription
A. Physical A1. Pipe diameter (Zohra et al. 2012Ø > 1,000 mm The pipes created affects the susceptibility to the heavy shock caused by human activities or a natural disaster, such as an earthquake. This indicates the smaller the pipe diameter, the more susceptible the risk of shock. 
600 mm < Ø ≤ 1,000 mm 
450 mm < Ø < 600 mm 
250 mm < Ø < 450 mm 
150 mm < Ø < 250 mm 
100 mm < Ø < 150 mm 
Ø < 100 mm 
A2. Pipe material (Godfrey et al. 2002; Zohra et al. 2012HDPE The pipes created from various materials fail in numerous ppatterns. According to Godfrey et al. (2002), pipe materials determined the levels of vulnerability. The materials of Reinforced Cement Concrete (RCC) and cast iron (CI) also had a higher vulnerability risk than AC and PVC (asbestos cement) and (polyvinyl chloride). Meanwhile, PVC and high-density polyvinyl chloride (HDPE) had the lowest vulnerability risk. Failure due to corrosion was also more common in cast iron pipes than in other materials. 
PVC 
Steel 
Asbestos cement 
Cast iron 
Ductile cast iron 
Galvanized steel 
A3. Pipe age (Godfrey et al. 2002< 10 years Age and corrosion accentuate damage in segmented pipelines and iron-made pipes. Age also determines their strength with the friction between the water and the pipe wall occurring due to the continuous flow, thinned out the pipe wall. 
10 ≤ years < 40 
40 ≤ years < 75 
75 ≤ years < 100 
> 100 years 
A4. Pipe length (Godfrey et al. 2002< 100 m Pipe length is known as continuous pipelines. which materials correlate with the welding method. According to previous studies, this pipeline was less vulnerable than segmented jointed materials. 
100 ≤ m < 750 
750 ≤ m < 2,000 
> 2,000 m 
A5. Protection method Protection Lined and protected pipes are less susceptible to corrosion and also decrease the material's thickness by creating stress concentration. 
No protection 
A6. Joint type (Zohra et al. 2012Ductile cast iron aseismic joint Some joints fail prematurely. Also, screwed and threaded steel fails more frequently than other joints. 
Welded-joint steel 
Ductile as iron standard join 
Polyvinyl chloride 
Cast iron 
Asbestos cement 
Screw-joint steel 
B. Environmen-tal B1. Fault No intersection Surface fault areas create local permanent ground deformation. This means the closer the pipelines to the fault areas, the more vulnerability to damage. 
1 Intersection 
> 1 Intersection 
B2. Settlement/Landslide (Zohra et al. 2012Non-populated areas The surface load of the embedded pipe is even greater in populated areas where almost all of the ground surface is covered by other infrastructure or roads. Densely populated areas are also more vulnerable to water supply interruptions. 
Mid densely populated areas 
Densely populated areas 
B3. Seismic intensity (Zohra et al. 2012MMI < 8 Seismic activity affects a large area and causes widespread damage. It also increases pipe stress, leading to damage-based pressure surges. (Karamouz et al. 2010). 
8 ≤ MMI < 9 
9 ≤ MMI < 10 
10 ≤ MMI < 11 
11 ≤ MMI 
B4. Type soil (Zohra et al. 2012Slightly/No Weathered Rock: Hard Putra et al. (2019) stated that corrosion caused pipe failure. This condition occurs due to physical and chemical reactions between pipe material and soil. Therefore, the identification of the solid properties is very necessary to estimate the potential degree of pipe corrosion. 
Moderate Weathered Rock: Medium 
Weathered Rock: Medium 
Deposit soil: diluvium: soft 
Deposit soil (alluvium: very soft) 
C. Operational C1. Breakage history (Nojima 2008Pipeline with no breakage history The breakage history defines a pipeline with damage. This is classified as vulnerable and vice versa. 
Pipeline with breakage history 
C2. Pressure (Specifications of the water treatment installation unit 2014< 6 atm Fire is likely to occur due to an earthquake, where a distribution system provides sufficient pressure on the consumers (Kanta & Brumbelow 2013). 
6 ≤ atm < 8 
> 8 atm 
C3. Leakage record (Maintenance of drinking water supply system 2016< 20% Leaks erode linings and increase soil moisture in the pipe zone. 
> 20% 
C4. Water quality (Standard Methods for Water Company Performance 2016≥ 80% Aggressive water promotes pipe corrosion. This indicates that the pH of non-aggressive water should be between 6.5 to 8.5. However, the aggression is often determined by the pH and other water quality parameters, such as alkalinity and the presence of carbonates. This proves that the range of values reflects the percentage of the sample compliant with the standard. 
60 ≤ %< 80 
40 ≤ %< 60 
20 ≤ %< 40 
<20% 
C5. Discontinuity (Standard Methods for Water Company Performance 2016Intermittent Continuous and intermittent supply pipes deliver water to the customers for 24 hours and less, respectively. This intermittent delivery is due to the issue of water availability or the inability of the hydraulic capacities to meet the required demand. 
Continue 

The criteria, sub-criteria and their related scores were examined through questionnaire analysis with the experts, which contained government officials, academics, as well as water utilities and supply system specialists. This questionnaire contained agreement or disagreement questions, with the criteria and sub-criteria derived from literature reviews. The experts were also permitted to suggest the new criteria/sub-criteria and modify their value ranges. To determine the final criteria, sub-criteria, and value range for SVI-WDN, two screening procedures were established. Firstly, only the criteria and sub-criteria. selected by more than 50% of experts were used in the SVI-WDN calculation. Secondly, analyses were conducted by examining the experts' inputs in the response column. In this case, the similar inputs suggested by more than two experts were included in the list of criteria/sub-criteria/range values.

Furthermore, variation was observed in the values of the sub-criteria, as shown in Table 2. Since the scales are different, the criteria need to be normalized before multiplication by their weights. This contained a score of 1 to 7, with the vulnerability level description displayed in Table 3.

Table 3

Normalized sub-criteria score and the vulnerability level

Normalized sub-criteria scoreVulnerability level
Extremely Vulnerable 
Highly Vulnerable 
Vulnerable 
Moderately Vulnerable 
Slightly Vulnerable 
Less Vulnerable 
Not Vulnerable 
Normalized sub-criteria scoreVulnerability level
Extremely Vulnerable 
Highly Vulnerable 
Vulnerable 
Moderately Vulnerable 
Slightly Vulnerable 
Less Vulnerable 
Not Vulnerable 

A normalized sub-criteria score was obtained using the following formula:
(1)
where N(xi) the normalized score of sub-criteria; xi the score of sub-criteria i based on the case study data min (x) and max (x) the minimum and maximum scores of sub-criteria i, respectively; while min (y) and max (y) the minimum and maximum intended normalized sub-criteria score.

Calculate the sub-criteria weight

To calculate the sub-criteria weight, a pairwise comparison matrix was initially developed by combining several sub-criteria and various assigned scales to rate the stakeholders' perceptions (Supriadi et al. 2018). In this study, the 1–9 point scale was used to express the level of relative importance among sub-criteria. This scale was selected due to being easy to use, simple, and straightforward (Zhang et al. 2019). Table 4 presents the 1–9 scale, which exhibited the level of importance. For example, scales 1 and 9 showed that sub-criteria i was equally important and extremely more important compared to j, respectively. Conversely, a scale of 1/9 indicated that i was extremely less important to j.

Table 4

Level of importance scale for a pairwise comparison matrix (Saaty 1990)

Level of ImportanceDefinition
Extremely more important 
Very strongly more important 
Strongly more important 
Moderately more important 
Equally important 
1/3 Moderately less important 
1/5 Strongly less important 
1/7 Very strongly less important 
1/9 Extremely less importance 
2, 4, 6, 8 Importance of the above intervals 
Level of ImportanceDefinition
Extremely more important 
Very strongly more important 
Strongly more important 
Moderately more important 
Equally important 
1/3 Moderately less important 
1/5 Strongly less important 
1/7 Very strongly less important 
1/9 Extremely less importance 
2, 4, 6, 8 Importance of the above intervals 

According to Saaty (1990) the pairwise comparison matrix only considered the sub-criteria grouped similar criteria. This proved that the matrix was differentiated into three groups, namely physical, environmental and operational criteria.

With the dimension of N × N for each criterion, the pairwise comparison matrix was created, where N is the number of compared sub-criteria In this process, the participants were only instructed to fill the upper diagonal part of the matrix, since the lower sector had the positive reciprocal value of the upper triangle. For example, when the sub-criteria i compared to j has a scale of 9, is subsequently observed for the comparison of j-i. Table 5 shows the detailed pairwise comparison matrix.

Table 5
 
 

To determine the order of priority, this matrix underwent a normalization process. The AHP method also needs to be equipped with the calculation of the consistency index and ratio (CI and CR), to determine the CL (consistency level) of user input. When the CR ≤ 0.1, the user's answers were optimally consistent with the resulting solution (Saaty, 1990).

Individual priorities were also aggregated to obtain a set of weights determined by a group judgement. To determine each sub-criteria weight, the experts'/stakeholders' decisions were individually calculated and combined using the geometric mean Equation (2). The selection of the geometric mean was based on its consideration as a more consistent method in pairwise comparison matrix (Forman & Peniwati, 1998):
(2)
where wn is weight scale from every stakeholder and wi the weight of sub-criteria i.
According to (Eastman et al. 1995) the vulnerability index score was calculated using Equation (3):
(3)
where the seismic vulnerability index (SVI), wi the weight of i, and the normalized score of sub-criteria i.

The SVI was implemented in the study area by identifying the condition of the pipe segment based on the sub-criteria. The score was then assigned to this segment before calculating the normalized value seismic vulnerability level was calculated.

Visualize the index into a GIS map

Visualization helps in easily providing an overview of unimaginable modelling or formula. For example, the use of vulnerability maps helps in easy communication with the planning ideas, improves knowledge transfer, and promotes wider community inclusion in decision-making (Satta 2014). Besides the limitations to calculating the VI (vulnerability index), the proposed framework also visualizes the index, using a GIS. This was in line with Adhikary et al. (2018), in which a vulnerability index was calculated and visualized using GIS, as shown in Figure 4(a) and 4(b). This confirmed that GIS was used to show the results of an SVI assessment and WDN classification, which were beneficial in supporting decision-making for pipeline evaluation and rehabilitation. This framework was also an excellent tool in developing disaster adaptation strategies and action planning, to improve mitigation and damage reduction plans in urban contexts. These specifically emphasized the geographical and spatial factors significantly affecting seismic risk.
Figure 4

Example of a Seismic Vulnerability Map: (a) Seismic vulnerability index (SVI) for earthquake MMI <8. (b) Seismic Vulnerability Index (SVI) for earthquake 9 < MMI < 10 (Adhikary et al. 2018).

Figure 4

Example of a Seismic Vulnerability Map: (a) Seismic vulnerability index (SVI) for earthquake MMI <8. (b) Seismic Vulnerability Index (SVI) for earthquake 9 < MMI < 10 (Adhikary et al. 2018).

Close modal

This study presents the conceptual framework for developing a SVI-WDN in the Special Region of Yogyakarta, Indonesia. The SVI-WDN aims to assist water authorities to prioritize the pipe segment handling and maintenance considering many physical, environmental and operational aspects. The index-based method was subject to local conditions, so far studies of the vulnerability index for water distribution network were generated outside Indonesia. This is the first study that presents a vulnerability index for water distribution network in Indonesia. Indonesia particularly the Special Region of Yogyakarta has the unique characteristics of water distribution network and area, therefore it is crucial to develop a specific index for the Special Region of Yogyakarta. There were three criteria and 15 sub-criteria for representing conditions of water distribution networks and their environment which were derived from diverse literature. Each sub-criteria have values range and corresponding scores to describe the vulnerability level. Experts for this study consist of government officials, academics and a water supply specialist. The Analytical Hierarchy Process (AHP) was implemented to determine weight for selected criteria and sub-criteria. The vulnerability index was an aggregation of the normalized score that was multiplied by the weight of sub-criteria.

This study offers new insight into vulnerability index development for water distribution networks in the Special Region of Yogyakarta, Indonesia, which has not been researched in the past. However, this framework was designed to be limited for a certain region and only to the earthquake hazard. Therefore, future work will focus on incorporating a robustness analysis to test the applicability of the criteria and their weight to be implemented to other regions in Indonesia. Furthermore, the framework will be extended to include multi-disaster as Indonesia is a country which experiences many fatal disasters.

We would like to thank the Program of Thesis Recognition Grant (Rekognisi Tugas Akhir) from the Directorate of Research, University of Gadjah Mada, Indonesia for fully funding for this research.

This work was supported by the Program of Thesis Recognition Grant.

All authors contributed to the process of literature collection and review as well as design a conceptual framework. All author has read and approved the final manuscript.

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

The authors declare there is no conflict.

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