Abstract
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.
HIGHLIGHTS
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
INTRODUCTION
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
Earthquake risk map in the Special Region of Yogyakarta (BNPB 2021).
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
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.
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.
Criteria and sub-criteria of existing studies of vulnerability in water supply system
Author . | Object . | Criteria . | Sub-criteria . | Range . |
---|---|---|---|---|
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 (2015) | Distribution 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 |
Author . | Object . | Criteria . | Sub-criteria . | Range . |
---|---|---|---|---|
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 (2015) | Distribution 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.
Criteria and sub-criteria used in this study
Criteria . | Sub-criteria . | Range . | Score . | Description . |
---|---|---|---|---|
A. Physical | A1. Pipe diameter (Zohra et al. 2012) | Ø > 1,000 mm | 1 | 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 | 2 | |||
450 mm < Ø < 600 mm | 3 | |||
250 mm < Ø < 450 mm | 4 | |||
150 mm < Ø < 250 mm | 5 | |||
100 mm < Ø < 150 mm | 6 | |||
Ø < 100 mm | 7 | |||
A2. Pipe material (Godfrey et al. 2002; Zohra et al. 2012) | HDPE | 1 | 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 | 2 | |||
Steel | 3 | |||
Asbestos cement | 4 | |||
Cast iron | 5 | |||
Ductile cast iron | 6 | |||
Galvanized steel | 7 | |||
A3. Pipe age (Godfrey et al. 2002) | < 10 years | 1 | 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 | 2 | |||
40 ≤ years < 75 | 3 | |||
75 ≤ years < 100 | 4 | |||
> 100 years | 5 | |||
A4. Pipe length (Godfrey et al. 2002) | < 100 m | 1 | 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 | 2 | |||
750 ≤ m < 2,000 | 3 | |||
> 2,000 m | 4 | |||
A5. Protection method | Protection | 1 | Lined and protected pipes are less susceptible to corrosion and also decrease the material's thickness by creating stress concentration. | |
No protection | 2 | |||
A6. Joint type (Zohra et al. 2012) | Ductile cast iron aseismic joint | 1 | Some joints fail prematurely. Also, screwed and threaded steel fails more frequently than other joints. | |
Welded-joint steel | 2 | |||
Ductile as iron standard join | 3 | |||
Polyvinyl chloride | 4 | |||
Cast iron | 5 | |||
Asbestos cement | 6 | |||
Screw-joint steel | 7 | |||
B. Environmen-tal | B1. Fault | No intersection | 1 | 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 | 2 | |||
> 1 Intersection | 3 | |||
B2. Settlement/Landslide (Zohra et al. 2012) | Non-populated areas | 1 | 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 | 2 | |||
Densely populated areas | 3 | |||
B3. Seismic intensity (Zohra et al. 2012) | MMI < 8 | 1 | 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 | 2 | |||
9 ≤ MMI < 10 | 3 | |||
10 ≤ MMI < 11 | 4 | |||
11 ≤ MMI | 5 | |||
B4. Type soil (Zohra et al. 2012) | Slightly/No Weathered Rock: Hard | 1 | 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 | 2 | |||
Weathered Rock: Medium | 3 | |||
Deposit soil: diluvium: soft | 4 | |||
Deposit soil (alluvium: very soft) | 5 | |||
C. Operational | C1. Breakage history (Nojima 2008) | Pipeline with no breakage history | 1 | The breakage history defines a pipeline with damage. This is classified as vulnerable and vice versa. |
Pipeline with breakage history | 2 | |||
C2. Pressure (Specifications of the water treatment installation unit 2014) | < 6 atm | 1 | 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 | 2 | |||
> 8 atm | 3 | |||
C3. Leakage record (Maintenance of drinking water supply system 2016) | < 20% | 1 | Leaks erode linings and increase soil moisture in the pipe zone. | |
> 20% | 2 | |||
C4. Water quality (Standard Methods for Water Company Performance 2016) | ≥ 80% | 1 | 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 | 2 | |||
40 ≤ %< 60 | 3 | |||
20 ≤ %< 40 | 4 | |||
<20% | 5 | |||
C5. Discontinuity (Standard Methods for Water Company Performance 2016) | Intermittent | 1 | 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 | 2 |
Criteria . | Sub-criteria . | Range . | Score . | Description . |
---|---|---|---|---|
A. Physical | A1. Pipe diameter (Zohra et al. 2012) | Ø > 1,000 mm | 1 | 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 | 2 | |||
450 mm < Ø < 600 mm | 3 | |||
250 mm < Ø < 450 mm | 4 | |||
150 mm < Ø < 250 mm | 5 | |||
100 mm < Ø < 150 mm | 6 | |||
Ø < 100 mm | 7 | |||
A2. Pipe material (Godfrey et al. 2002; Zohra et al. 2012) | HDPE | 1 | 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 | 2 | |||
Steel | 3 | |||
Asbestos cement | 4 | |||
Cast iron | 5 | |||
Ductile cast iron | 6 | |||
Galvanized steel | 7 | |||
A3. Pipe age (Godfrey et al. 2002) | < 10 years | 1 | 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 | 2 | |||
40 ≤ years < 75 | 3 | |||
75 ≤ years < 100 | 4 | |||
> 100 years | 5 | |||
A4. Pipe length (Godfrey et al. 2002) | < 100 m | 1 | 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 | 2 | |||
750 ≤ m < 2,000 | 3 | |||
> 2,000 m | 4 | |||
A5. Protection method | Protection | 1 | Lined and protected pipes are less susceptible to corrosion and also decrease the material's thickness by creating stress concentration. | |
No protection | 2 | |||
A6. Joint type (Zohra et al. 2012) | Ductile cast iron aseismic joint | 1 | Some joints fail prematurely. Also, screwed and threaded steel fails more frequently than other joints. | |
Welded-joint steel | 2 | |||
Ductile as iron standard join | 3 | |||
Polyvinyl chloride | 4 | |||
Cast iron | 5 | |||
Asbestos cement | 6 | |||
Screw-joint steel | 7 | |||
B. Environmen-tal | B1. Fault | No intersection | 1 | 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 | 2 | |||
> 1 Intersection | 3 | |||
B2. Settlement/Landslide (Zohra et al. 2012) | Non-populated areas | 1 | 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 | 2 | |||
Densely populated areas | 3 | |||
B3. Seismic intensity (Zohra et al. 2012) | MMI < 8 | 1 | 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 | 2 | |||
9 ≤ MMI < 10 | 3 | |||
10 ≤ MMI < 11 | 4 | |||
11 ≤ MMI | 5 | |||
B4. Type soil (Zohra et al. 2012) | Slightly/No Weathered Rock: Hard | 1 | 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 | 2 | |||
Weathered Rock: Medium | 3 | |||
Deposit soil: diluvium: soft | 4 | |||
Deposit soil (alluvium: very soft) | 5 | |||
C. Operational | C1. Breakage history (Nojima 2008) | Pipeline with no breakage history | 1 | The breakage history defines a pipeline with damage. This is classified as vulnerable and vice versa. |
Pipeline with breakage history | 2 | |||
C2. Pressure (Specifications of the water treatment installation unit 2014) | < 6 atm | 1 | 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 | 2 | |||
> 8 atm | 3 | |||
C3. Leakage record (Maintenance of drinking water supply system 2016) | < 20% | 1 | Leaks erode linings and increase soil moisture in the pipe zone. | |
> 20% | 2 | |||
C4. Water quality (Standard Methods for Water Company Performance 2016) | ≥ 80% | 1 | 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 | 2 | |||
40 ≤ %< 60 | 3 | |||
20 ≤ %< 40 | 4 | |||
<20% | 5 | |||
C5. Discontinuity (Standard Methods for Water Company Performance 2016) | Intermittent | 1 | 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 | 2 |
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.
Normalized sub-criteria score and the vulnerability level
Normalized sub-criteria score . | Vulnerability level . |
---|---|
7 | Extremely Vulnerable |
6 | Highly Vulnerable |
5 | Vulnerable |
4 | Moderately Vulnerable |
3 | Slightly Vulnerable |
2 | Less Vulnerable |
1 | Not Vulnerable |
Normalized sub-criteria score . | Vulnerability level . |
---|---|
7 | Extremely Vulnerable |
6 | Highly Vulnerable |
5 | Vulnerable |
4 | Moderately Vulnerable |
3 | Slightly Vulnerable |
2 | Less Vulnerable |
1 | Not Vulnerable |
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.
Level of importance scale for a pairwise comparison matrix (Saaty 1990)
Level of Importance . | Definition . |
---|---|
9 | Extremely more important |
7 | Very strongly more important |
5 | Strongly more important |
3 | Moderately more important |
1 | 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 Importance . | Definition . |
---|---|
9 | Extremely more important |
7 | Very strongly more important |
5 | Strongly more important |
3 | Moderately more important |
1 | 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.
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).

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
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).
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).
CONCLUSION
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.
ACKNOWLEDGEMENT
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.
FUNDING
This work was supported by the Program of Thesis Recognition Grant.
AUTHOR CONTRIBUTION
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.
DATA AVAILABILITY STATEMENT
All relevant data are included in the paper or its Supplementary Information.
CONFLICT OF INTEREST
The authors declare there is no conflict.