This study evaluated the experience of implementing water safety plans (WSPs) in Vietnam. WSPs were introduced in Vietnam by the World Health Organization (WHO) in collaboration with the Ministry of Construction in 2006 and have been a mandatory requirement for municipal water supplies since 2012. Using a mixed-methods approach, we collected data on the perceived benefits and challenges of WSP implementation from 23 provincial water companies between August and November 2021. Potential public health benefits of improved water quality were a key motivation; 87% of the water utilities were also motivated by the risk of climate change and prepared response plans to climate-related extreme events as part of WSPs. A decrease in E. coli and an improvement in disinfectant residual in treated water were reported by 61 and 83% of the water supplies, respectively. Sixty-five percent of the water supplies also reported improved revenue and cost recovery. Key barriers to WSP implementation were a lack of WSP guidance suitable for the local context (87%) and insufficient funds for WSP implementation (43%). Our study highlights the need for improved support and capacity building along with locally suited guidance on WSP implementation and audit.

  • Increasing water pollution, emerging climate change, process of equitization, and expansion of service areas are important impacts on water safety plan (WSP).

  • WSP has led to tangible benefits. The WSP is a useful vehicle for climate change adaptations, improve resilience.

  • The commitment from Government and from water utilities is strong.

  • The critical financial barriers, training needs, and support in WSP need to be addressed.

Graphical Abstract

Graphical Abstract
Graphical Abstract

The World Health Organization (WHO) recommends water safety plans (WSPs) as a means to ensure the safety of drinking water (WHO 2004). WSPs consist of a comprehensive risk assessment and risk management approach to prevent contamination of drinking water, from catchment to consumers (WHO 2005, 2009). WSPs are key tools for sustained safe drinking water access (Kanyesigye et al. 2019) and the achievement of Sustainable Development Goal (SDG) target 6.1. The achievement of this target is measured using indicator 6.1.1, which emphasizes the proportion of the population using safely managed drinking water services. Safely managed water is defined as an improved source located on premises, available when needed and free from fecal and priority chemical contamination (WHO 2017).

As of 2017, WSPs have been developed and implemented in 93 countries worldwide (WHO & IWA 2017). Kumpel et al. (2018) investigated the effectiveness of WSP implemented in 99 water supply utilities in 12 countries from the Asia-Pacific region. This study identified both benefits from WSPs and challenges in their implementation, including financial constraints and insufficient capacity. Gunnarsdóttir et al. (2012) investigated the benefits of WSPs and critically analyzed the requirements for successful implementation and operation in Iceland, one of the first countries to adopt systematic preventive management for drinking water safety. The results showed several benefits of the WSP implementation process including changing the attitude of the staff to water safety and the culture within utilities. The lack of documentation and lack of regular internal and external audits were key obstacles to implementation of the WSP. The most important elements of success were the intensive training of staff and participation of staff in the whole process. The authors concluded that it was important to have simple and well-structured guidelines, and good cooperation with the health authorities (Gunnarsdóttir et al. 2012).

In Vietnam, WSPs were first introduced in 2006 by the WHO, collaborating with Vietnam's Ministry of Construction (MOC), and selected provincial water utilities, focusing on introducing the approach and capacity building. From 2007 to 2009, three provincial water supply utilities of Hai Duong, Thua Thien-Hue, and Vinh Long, providing water supply services in provincial capital cities, implemented trial WSPs. Based on the initial successes, between 2010 and 2012, WHO and MOC expanded WSP training and implementation at four other provincial water supply utilities of Hai Phong, Quang Ninh, Khanh Hoa, and Ba Ria-Vung Tau. A review of these first WSP experiences showed that implementation of WSPs helped to improve urban water supply services (ATI, MOC 2021).

The Ministry of Health (MOH) and Vietnam Water Supply and Sewerage Association (VWSA) are key players in promotion of WSPs in Vietnam. The MOH is in charge of the development of drinking water standards, and regulations for external monitoring of the water systems in all urban and rural areas in Vietnam. The VWSA has been developing human resources through capacity building in WSPs, and by developing the Vietnamese version of WSP Manual (Nguyen et al. 2021).

At the end of 2012, WSPs became a mandatory requirement for municipal water systems in Vietnam. In November 2021, for the first time, WSPs have been required in rural water supply systems by the National Strategy for Rural Water Supply and Sanitation for the period up to 2030 (GoV 2021). However, the level of understanding of WSP implementation at provincial water utilities varies widely. Some utilities have been active in developing, implementing, and updating their WSP, with participation of their staff and involvement of provincial authorities. Other utilities have developed a WSP, but its implementation is limited. Some provincial utilities and most rural water supply enterprises do not have a good understanding of WSPs (GoV 2021). WSP updating is not often carried out, while internal and external WSP auditing does not yet exist.

Increasing threats from water pollution and water source deterioration related to emerging changes in climate demonstrate a need to improve WSP implementation and strategy in the country. Water quality incidents in water supply systems in Vietnam show the need to improve risk management. Furthermore, the process of privatizing water by attracting private equity, which took place intensively between 1996 and 2015, has slowed down more recently; the expansion of service areas of provincial water utilities replacing unqualified rural water supply systems may have impacted WSP implementation.

This study aimed to assess WSP implementation at the provincial water supply utilities in Vietnam to understand the extent to which full implementation is being realized, the benefits of WSP implementation reported by utilities, and the constraints and challenges to WSP implementation.

The study was undertaken between August and November 2021 using a mixed-methods approach of surveys and in-depth interviews to collect information from key individuals who played a major role in WSP implementation at the water utilities.

Utility-level data was collected from 23 provincial water supply companies, which were key water service providers in provincial capitals and surrounding areas, in 21 provinces representing all 7 economic regions of Vietnam, as shown in Table 1. Utilities were chosen based on their location representing each economic region, the system capacity, as well as comparative level of development of the utility and of the province. According to the Resolution No. 1210/2016/UBTVQH13 by the Vietnam National Assembly Standing Committee, the cities in Vietnam are classified into six categories, from special to 5th, based on the criteria: (1) Location, function, role, structure, and level of socio-economic development; (2) population size; (3) population density; (4) ratio of non-agricultural workers; and (5) level of infrastructure development and urban architecture and landscape. The cities of special and first categories are considered more advanced than others (Figure 1).
Table 1

Selected provincial water utilities for the study

No.RegionsProvincesCitiesCategory of urban center
North East Phu Tho Viet Tri 
Bac Giang Bac Giang II 
Quang Ninh Ha Long 
North West Son La Son La II 
Hoa Binh Hoa Binh III 
Red River Delta Hanoi Hanoi Special 
Vinh Phuc Vinh Yen II 
Hai Duong Hai Duong 
Hai Phong Hai Phong 
Nam Dinh Nam Dinh 
North Central Region Ha Tinh Ha Tinh II 
South Central Region Quang Nam Tam Ky II 
Danang Danang 
Khanh Hoa Nha Trang 
South East Ho Chi Minh city Ho Chi Minh city Special 
Binh Duong Thu Dau Mọt 
Ba Ria-Vung Tau Vung Tau 
South West (Mekong Delta) An Giang Long Xuyên 
Bac Lieu Bac Lieu II 
Vinh Long Vinh Long II 
Hau Giang Vi Thanh II 
No.RegionsProvincesCitiesCategory of urban center
North East Phu Tho Viet Tri 
Bac Giang Bac Giang II 
Quang Ninh Ha Long 
North West Son La Son La II 
Hoa Binh Hoa Binh III 
Red River Delta Hanoi Hanoi Special 
Vinh Phuc Vinh Yen II 
Hai Duong Hai Duong 
Hai Phong Hai Phong 
Nam Dinh Nam Dinh 
North Central Region Ha Tinh Ha Tinh II 
South Central Region Quang Nam Tam Ky II 
Danang Danang 
Khanh Hoa Nha Trang 
South East Ho Chi Minh city Ho Chi Minh city Special 
Binh Duong Thu Dau Mọt 
Ba Ria-Vung Tau Vung Tau 
South West (Mekong Delta) An Giang Long Xuyên 
Bac Lieu Bac Lieu II 
Vinh Long Vinh Long II 
Hau Giang Vi Thanh II 
Figure 1

Location of surveyed provincial water utilities. ▴ Location of urban centers (capital cities) in provinces.

Figure 1

Location of surveyed provincial water utilities. ▴ Location of urban centers (capital cities) in provinces.

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The surveyed companies are listed in Table 2. The utilities selected represent the different management types of water supply utilities: public (100% state-own, one member company limited); fully equitized or private; not yet fully equitized, or joint stock company (JSC). Table 2 presents the different sources of funding for the water supply utilities. The general information related to system capacity and population served in each utility is shown in Table 3. The total capacities fluctuated from 22,000 to 2,400,000 m3/d with population to be served from 141 thousand to 8.8 million people. The number of connections in the water supply utilities is presented in Table 4. The data gathered from the survey were triangulated with data from the in-deep interviews, and financial reports 2021 published on the company's websites.

Table 2

Ownership type and source of funding at surveyed water utilities

No.RegionsName of utilitySurveyed utility No.Ownership and type of enterprise
Source of funding (%)
Source of income
State-own (One member Ltd)Fully equitized/PrivatedPartly equitized/JSCStateOthersWater tariff (%)Others (%)
North East Phu Tho Water Supply JSC 01   24 76 97.24 2.76 
Bac Giang Water Supply JSC 02   51 49 97.41 2.59 from construction and installation business 
Quang Ninh Water Supply JSC 03   96.16 3.84 96.74 1.37 from construction and installation; 1.89 from others 
North West Son La Water Supply JSC 04   100 95.51 2.63 from construction and installation; 1.86 from others 
Hoa Binh Water Supply JSC 05   100 91.77 8.11 from construction and installation; 0.12 from others 
Red River Delta Hanoi Water Co. Ltd 06   100 96.73 2.38 from construction and installation; 0.9 from others 
Hanoi Water Supply JSC No. 2 07   100 90.63 8.75 from construction and installation; 0.62 from others 
Duong river Water Supply JSC 08   100 100  
Vinh Phuc Water Supply and Drainage JSC No. 1 09   100 95.64 3.71 from construction and installation; 0.65 from others 
Hai Duong Water Supply JSC 10   65 35 97.43 2.32 from construction and installation; 0.26 from others 
Hai Phong Water Supply JSC 11   80.58 19.42 97.68 0.56 from construction and installation; 1.75 from others 
Nam Dinh Water Supply JSC 12   49.5 50.5 95.25 3.82 from construction and installation; 0.93 from others 
North central Ha Tinh Water Supply JSC 13   97.77 2.23 >95% <5% from construction and installation 
South central Quang Nam Water Supply, Drainage and Construction JSC 14   100 56.23 34.4 from real estate; 3.82 from construction and installation; 5.56 from others 
Danang Water Supply JSC 15   60.1 39.9 99.22 0.78 
Khanh Hoa Water Supply and Drainage JSC 16   N/A N/A >95% <5% from construction and installation 
South East Sai Gon Water Supply Co. Ltd 17   100 95.75 4.25 
Binh Duong Water and Environment JSC (BIWASE) 18   100 62 Solid waste: 17%; Wastewater: 2%; Others: 19% 
Ba Ria-Vung Tau Water Supply JSC 19   46.78 53.22 98.97 0.62% from construction and installation;
0.41% from others 
South West (Mekong Delta) An Giang Power and Water Supply JSC 20   87.72 12.28 22.09 76.31% from power tariff; 1.11% from real estate; 0.49% from others 
Bac Lieu Water Supply JSC 21   98.65 1.35 96.7 2.6% from construction and installation; 0.7% from others 
Vinh Long Water Supply JSC 22   51 49 90.52 6.4% from construction and installation; 3.08% from others 
Hau Giang Water Supply, Sewerage and Urban Projects JSC 23   46.33 53.67 45.58 54.42% from service 
No.RegionsName of utilitySurveyed utility No.Ownership and type of enterprise
Source of funding (%)
Source of income
State-own (One member Ltd)Fully equitized/PrivatedPartly equitized/JSCStateOthersWater tariff (%)Others (%)
North East Phu Tho Water Supply JSC 01   24 76 97.24 2.76 
Bac Giang Water Supply JSC 02   51 49 97.41 2.59 from construction and installation business 
Quang Ninh Water Supply JSC 03   96.16 3.84 96.74 1.37 from construction and installation; 1.89 from others 
North West Son La Water Supply JSC 04   100 95.51 2.63 from construction and installation; 1.86 from others 
Hoa Binh Water Supply JSC 05   100 91.77 8.11 from construction and installation; 0.12 from others 
Red River Delta Hanoi Water Co. Ltd 06   100 96.73 2.38 from construction and installation; 0.9 from others 
Hanoi Water Supply JSC No. 2 07   100 90.63 8.75 from construction and installation; 0.62 from others 
Duong river Water Supply JSC 08   100 100  
Vinh Phuc Water Supply and Drainage JSC No. 1 09   100 95.64 3.71 from construction and installation; 0.65 from others 
Hai Duong Water Supply JSC 10   65 35 97.43 2.32 from construction and installation; 0.26 from others 
Hai Phong Water Supply JSC 11   80.58 19.42 97.68 0.56 from construction and installation; 1.75 from others 
Nam Dinh Water Supply JSC 12   49.5 50.5 95.25 3.82 from construction and installation; 0.93 from others 
North central Ha Tinh Water Supply JSC 13   97.77 2.23 >95% <5% from construction and installation 
South central Quang Nam Water Supply, Drainage and Construction JSC 14   100 56.23 34.4 from real estate; 3.82 from construction and installation; 5.56 from others 
Danang Water Supply JSC 15   60.1 39.9 99.22 0.78 
Khanh Hoa Water Supply and Drainage JSC 16   N/A N/A >95% <5% from construction and installation 
South East Sai Gon Water Supply Co. Ltd 17   100 95.75 4.25 
Binh Duong Water and Environment JSC (BIWASE) 18   100 62 Solid waste: 17%; Wastewater: 2%; Others: 19% 
Ba Ria-Vung Tau Water Supply JSC 19   46.78 53.22 98.97 0.62% from construction and installation;
0.41% from others 
South West (Mekong Delta) An Giang Power and Water Supply JSC 20   87.72 12.28 22.09 76.31% from power tariff; 1.11% from real estate; 0.49% from others 
Bac Lieu Water Supply JSC 21   98.65 1.35 96.7 2.6% from construction and installation; 0.7% from others 
Vinh Long Water Supply JSC 22   51 49 90.52 6.4% from construction and installation; 3.08% from others 
Hau Giang Water Supply, Sewerage and Urban Projects JSC 23   46.33 53.67 45.58 54.42% from service 
Table 3

Key parameters of surveyed provincial water utilities

NoRegionUtility's CodeName of utilitySystem capacity (m3/d)Population served (person)Connections
Total numberApartment (multiple taps)Household (single taps)Public (shared) tapInstitutionCommercialIndustrialOthers
North East Phu Tho Water Supply JSC 120,000 580,500 147,350  142,253  2,872    
Bac Giang Water Supply JSC 40,000 216,000 61,106 16 60,00 100 469 281 240  
Quang Ninh Water Supply JSC 240,050 1,000,000 269,644  244,174  2,429 22,869 28 IPs and 144 customers connected to water meters of the IP  
North West Son La Water Supply JSC     95%  2.2% 2.45% 0.35%  
Hoa Binh Water Supply JSC 45,000  48,933 40,000  900 8,000 32  
Red River Delta Hanoi Water Co Ltd 750,000 3,200,000 543,655  536,111  7,544    
Hanoi Water Supply JSC N. 2   226,555 123 221,565  4,867    
Duong river Water Supply JSC 300,000 3,000,000 Wholesale to customers through 41 water meters        
Vinh Phuc Water Supply and Drainage JSC No. 1  156,800 40,379 39,220 680 175 289  
10 Hai Duong Water Supply JSC 154,000 2,000,000 247,079        
11 Hai Phong Water Supply JSC 390,000 1,400,000 38,156 41 33,195  1,711 810 2,318 81 
12 Nam Dinh Water Supply JSC 105,600 638,700 144,020 01 141,902 869 246 1,002  
North central region 13 Ha Tinh Water Supply JSC 85,000 400,000 94,235  92,100  2,135    
South central region 14 Quang Nam Water Supply and Drainage JSC 115,000 450,000 74,111  72,126  1,985    
15 Danang Water Supply JSC 286,000 1,119,686 305,070  201,346 24,406 33,558 33,558 30,507 Rural area: 15,254 
16 Khanh Hoa Water Supply and Drainage JSC 135,000 526,000 150,000  88,412  8,573 30,362 7,655  
South East 17 Sai Gon Water Supply Co. Ltd 2,400,000 8,837,544 1,600,000        
18 Binh Duong Water and Environment JSC 760,000–997,000 2,000,000 317,746  302,966  1,782 2,479 10,519  
19 Ba Ria-Vung Tau Water Supply JSC 180,000 865,764 149,711  138,140  1,656 7,401 2,514  
South West (Mekong Delta) 20 An Giang Power and Water Supply JSC 261,200 1,180,000 514,517  514,517      
21 Bac Lieu Water Supply JSC 22,000 141,000 28,332  27,992  278 62   
22 Vinh Long Water Supply JSC 67,300 337,802 76,620 16 68,824 1,150 6,243 387  
23 Hau Giang Water Supply, Sewerage and Urban Projects JSC 43,375  65,478  56,333  811 2,835 300 5,199 
NoRegionUtility's CodeName of utilitySystem capacity (m3/d)Population served (person)Connections
Total numberApartment (multiple taps)Household (single taps)Public (shared) tapInstitutionCommercialIndustrialOthers
North East Phu Tho Water Supply JSC 120,000 580,500 147,350  142,253  2,872    
Bac Giang Water Supply JSC 40,000 216,000 61,106 16 60,00 100 469 281 240  
Quang Ninh Water Supply JSC 240,050 1,000,000 269,644  244,174  2,429 22,869 28 IPs and 144 customers connected to water meters of the IP  
North West Son La Water Supply JSC     95%  2.2% 2.45% 0.35%  
Hoa Binh Water Supply JSC 45,000  48,933 40,000  900 8,000 32  
Red River Delta Hanoi Water Co Ltd 750,000 3,200,000 543,655  536,111  7,544    
Hanoi Water Supply JSC N. 2   226,555 123 221,565  4,867    
Duong river Water Supply JSC 300,000 3,000,000 Wholesale to customers through 41 water meters        
Vinh Phuc Water Supply and Drainage JSC No. 1  156,800 40,379 39,220 680 175 289  
10 Hai Duong Water Supply JSC 154,000 2,000,000 247,079        
11 Hai Phong Water Supply JSC 390,000 1,400,000 38,156 41 33,195  1,711 810 2,318 81 
12 Nam Dinh Water Supply JSC 105,600 638,700 144,020 01 141,902 869 246 1,002  
North central region 13 Ha Tinh Water Supply JSC 85,000 400,000 94,235  92,100  2,135    
South central region 14 Quang Nam Water Supply and Drainage JSC 115,000 450,000 74,111  72,126  1,985    
15 Danang Water Supply JSC 286,000 1,119,686 305,070  201,346 24,406 33,558 33,558 30,507 Rural area: 15,254 
16 Khanh Hoa Water Supply and Drainage JSC 135,000 526,000 150,000  88,412  8,573 30,362 7,655  
South East 17 Sai Gon Water Supply Co. Ltd 2,400,000 8,837,544 1,600,000        
18 Binh Duong Water and Environment JSC 760,000–997,000 2,000,000 317,746  302,966  1,782 2,479 10,519  
19 Ba Ria-Vung Tau Water Supply JSC 180,000 865,764 149,711  138,140  1,656 7,401 2,514  
South West (Mekong Delta) 20 An Giang Power and Water Supply JSC 261,200 1,180,000 514,517  514,517      
21 Bac Lieu Water Supply JSC 22,000 141,000 28,332  27,992  278 62   
22 Vinh Long Water Supply JSC 67,300 337,802 76,620 16 68,824 1,150 6,243 387  
23 Hau Giang Water Supply, Sewerage and Urban Projects JSC 43,375  65,478  56,333  811 2,835 300 5,199 
Table 4

Reasons and solutions to overcome the regularly fail to meet the National technical regulation on domestic water quality

NoCode of water utilitiesParameters which regularly fail to meet the National technical regulation on domestic water qualityReasonsSolutions
No. 02 COD (KMnO4Raw water is river/surface water which receives the industrial wastewater. • Adding PAC,
• Chlorination of the raw water. 
No. 03 pH = 4.0–5.0 The company exploits many water sources, this case exploits groundwater in Ha Long and Cam Pha underground wells, which may be contaminated with acid from coal mining. The company has mixed underground well water with the treated water of Dien Vong water treatment plant with a pH of 7.0–7.5. 
No. 04 Hardness This city is mountainous area. The company exploits groundwater. Therefore, the underground water contains high minerals and ions Ca2+, Mg2+, etc. Hardness is removed by lime. 
Nitrate (NO3Due to the inadequacy between the threshold values in QCVN 01:2009/BYT and QCVN 01-1:2018/BYT:
• QCVN 01:2009/BYT: NO3 = 50 mg/l (equivalent to NO3-N = 50/4.4 = 11.3 mg/l).
• Meanwhile QCVN 01-1:2018/BYT: NO3-N = 2 mg/l.
Therefore, the norm of NO3-N according to QCVN 01-1:2018 always exceeds the allowable threshold. 
Proposing MOH to review the nitrate parameter. 
No. 14 Chloride (ClThe company exploits surface water from the Vu Gia-Thu Bon river basin (at the time of salinization) Finding an alternative raw water supply. 
No. 23 Coliforms and free chlorine residual (Cl2) at the end of the water pipe The pipeline network is quite long, the management of the network has not been optimized. Hence, ingress of contaminated water occurs. • Increasing the chlorine at the water treatment plant to 0.7–0.9 mg/1.
• At the same time, regularly clean and disinfect the faucet head, flush the households' water tank, etc. 
NoCode of water utilitiesParameters which regularly fail to meet the National technical regulation on domestic water qualityReasonsSolutions
No. 02 COD (KMnO4Raw water is river/surface water which receives the industrial wastewater. • Adding PAC,
• Chlorination of the raw water. 
No. 03 pH = 4.0–5.0 The company exploits many water sources, this case exploits groundwater in Ha Long and Cam Pha underground wells, which may be contaminated with acid from coal mining. The company has mixed underground well water with the treated water of Dien Vong water treatment plant with a pH of 7.0–7.5. 
No. 04 Hardness This city is mountainous area. The company exploits groundwater. Therefore, the underground water contains high minerals and ions Ca2+, Mg2+, etc. Hardness is removed by lime. 
Nitrate (NO3Due to the inadequacy between the threshold values in QCVN 01:2009/BYT and QCVN 01-1:2018/BYT:
• QCVN 01:2009/BYT: NO3 = 50 mg/l (equivalent to NO3-N = 50/4.4 = 11.3 mg/l).
• Meanwhile QCVN 01-1:2018/BYT: NO3-N = 2 mg/l.
Therefore, the norm of NO3-N according to QCVN 01-1:2018 always exceeds the allowable threshold. 
Proposing MOH to review the nitrate parameter. 
No. 14 Chloride (ClThe company exploits surface water from the Vu Gia-Thu Bon river basin (at the time of salinization) Finding an alternative raw water supply. 
No. 23 Coliforms and free chlorine residual (Cl2) at the end of the water pipe The pipeline network is quite long, the management of the network has not been optimized. Hence, ingress of contaminated water occurs. • Increasing the chlorine at the water treatment plant to 0.7–0.9 mg/1.
• At the same time, regularly clean and disinfect the faucet head, flush the households' water tank, etc. 

The survey form (attached in Supplementary material) was prepared to collect general information related to system capacity, number of users, type of utility ownership, and various aspects of the WSP implementation. Utilities were asked about their motivations and barriers for developing WSP and whether any of the changes to the WSP had been made since its first development. The survey included questions on climate considerations and financial challenges faced during WSP development and implementation. The perceived benefits of implementing WSP, WSP auditing (both internal and external), and resources available for WSP training from external agencies were also investigated.

Survey results were collected in Vietnamese, translated to English and analyzed using Microsoft Excel. Frequency tables were prepared for each survey response to identify themes.

Motivations and barriers for developing WSP

Motivations

Figure 2 shows what the utilities considered to be the motivations for developing WSPs. The main motivations were potential improvement in water quality/public health, potential improvement in cost recovery, and interest of CEO/management, where all 23 utilities agreed. Besides, the mandatory requirement and impact of climate change also were important motivations, agreed by 20 (87%) utilities. While disaster preparedness was agreed by 22 (96%) utilities out of the 23 surveyed utilities. Mandatory requirement was not recognized as a motivation factor by 2 water utilities. One was providing wholesale water to another provincial water utility for distribution. Another was providing water service for different areas including urban and rural in a province.
Figure 2

Motivation for developing WSP at surveyed Vietnamese provincial water utilities.

Figure 2

Motivation for developing WSP at surveyed Vietnamese provincial water utilities.

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Barriers

The barriers to developing WSP are shown in Figure 3. The lack of guiding materials suited to the local context accounted for the largest proportion reported by 20 utilities (87%). The second most commonly identified barrier was the lack of funds to implement WSPs noted by 15 (65%) utilities. Other barriers were the lack of understanding of WSP and the lack of technical capacity to develop and implement WSPs, where 6 of 23 (26%) utilities selected the answer.
Figure 3

Barriers to developing WSP at provincial water utilities in Vietnam.

Figure 3

Barriers to developing WSP at provincial water utilities in Vietnam.

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One of the important barriers to apply WSP is the lack of understanding of WSPs by the utility's leaders. As WSP steering committees at provincial level have not been created, and regulation on compulsory application of WSP has not been issued, some water companies have not yet started to develop WSPs. For example, the private company with a wholesale water service to Hanoi of 300,000 m3/d does not implement a WSP.

Another barrier identified is where a water utility managing different water systems in different areas. Provincial water companies in Vietnam have looked to expand their service to surrounding areas, including rural areas taking water from different sources. This has created additional challenges for WSP implementation as more and more varied risks must be managed compared with utility with a single water source and concentrated service area.

The changes to the WSP after the first development

Eighteen (78%) of utilities made changes to the WSP after the first development. The changes made to the WSPs were diverse depending on the actual operating situation of the companies. Ten utilities (43%) reported updating, adjusting and supplementing their WSP every year or after a major change in infrastructure, management, and operation processes. Thirteen (57%) of the utilities reported changes made to their WSP after emergency or other unforeseen incidents. One company issued its first WSP in 2017 and revised this in 2019 after working with the Ministry of Construction's WSP inspection team.

Five companies developed, issued, and adjusted the emergency response plan or incident handling scenarios to describe solutions to deal with emergency incidents and possible risks. These addressed hazards in the process of water production and ensuring they could meet the goal of ensuring water safety from the source to consumers.

Ten companies reviewed the operating process of the water treatment and water supply network on an annual basis. They also strengthened solutions for monitoring water source safety, applying water treatment technology, and improving the water quality monitoring system. Investments were also made in automatic equipment for system operation, and detecting leakage in the network.

One company enhanced the awareness of leaders and staff in the implementation of their WSP through applying remote preventive measures and applying new technology in production. In addition, the coordination of all levels of government and relevant departments in the protection of water sources and water supply systems and advocacy on WSP to encourage people to help protect water sources and water supply works were undertaken by the company.

Climate considerations

Twenty (87%) of the surveyed utilities identified climate change as a motivation for developing their WSP as shown in Figure 4. They also were able to identify the current and future climate hazards or hazardous events during WSP development and had access to climate-related expertise. It is important to note that, while implementing the WSP, 22 (96%) of the surveyed utilities have prepared the response plans for climate-related threats such as heavy rain, typhoon, long-term dry spells, drought, or sea level rise.
Figure 4

Climate consideration in WSP implementation at Vietnamese provincial water utilities.

Figure 4

Climate consideration in WSP implementation at Vietnamese provincial water utilities.

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Financial considerations

The utilities' financial capacity for developing WSP

The survey collected data on companies' financial capacity to implement WSPs. The results show that only 13 (57%) of the utilities have sufficient financial resources while the remaining 10 have shortfalls in financial resources for WSP implementation. One company spent 24.4 billion VND ($10.5 million) to implement a WSP for a system with a capacity of 120,000 m3/d, serving 580,500 population, after submission the WSP to the Provincial People's Committee for approval. The cost for the implementation of WSP was around 430 billion VND ($18.5 million) for company No. 13 with a system capacity of 85,000 m3/d and 400,000 people to be served.

Some utilities from the cities of second urban category considered that the financial support for implementation of WSP should be taken from the State budget, but as yet they have not received these funds. The Government is now addressing this. An important political will change came in 2021 with Circular No. 44/2021/TT-BTC dated 18 June 2021 by the Ministry of Finance on Water tariff structure and water pricing principles to ensure that WSP expenses have been accounted for in the water tariff structure (MoF 2021).

One public company estimated that it lacked 10% of the total budget to implement its WSP while the JSC company considered that it would need 50% of the budget from external means to support WSP. There was no information related to the total budget for the implementation WSP, showing that WSP was not conducted as an individual activity at the surveyed water utility.

Several companies explained that a large budget would be required in order to carry out the WSP. The utilities must perform WSP in several stages. One company explained that the utility could fund the installation of water quality monitoring equipment, and improving technologies in water treatment plants, but would need external support and cooperation from the government for strategic safe water supply works such as raw water reservoirs and clean water reservoirs.

Effect of the lacking of funding for developing WSP

Five effects of the lack of funding, as reported by utilities, are shown in Figure 5. The two most common effects reported by 14 (63%) of companies were corrective actions on control measures and assessing the full range of hazardous events. The next most common factors reported by 12 (52%) of utilities were monitoring within the system linked to critical limits and establishing new control measures for hazardous events. The factor least affected by the lack of funding was the validation of control points, which was only reported by 8 (35%) of the companies.
Figure 5

Effects of the lack of funding for developing WSP.

Figure 5

Effects of the lack of funding for developing WSP.

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Perceived benefits of implementing WSPs

Infrastructure improvements made as part of WSP

The reported benefits from WSP implementation and the improvement of infrastructure are shown in Figure 6. A number of utilities have improved the water infrastructure from source to customer, including raw water intake (21 or 91% of utilities), water treatment plant (96%), service reservoir (78%), and distribution network (96%). The infrastructure improvement included upgrading of existing facilities and/or construction of new water works and reported by utilities of different capacities, from small (40,000 m3/d) to large (2,400,000 m3/d) and in cities of different urban categories, from II to ‘special’.
Figure 6

The situation of the main water works improvements in Vietnamese water utilities.

Figure 6

The situation of the main water works improvements in Vietnamese water utilities.

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Operational improvements made as part of WSP

Figure 7 demonstrates the operational improvements in utilities made as a result of the WSP. The activities included water quality monitoring, operational monitoring at treatment plants, development of standard operating procedures, staff training, and emergency response plans. These activities were found in all the surveyed utilities. Environmental protection/catchment management was applied at 22 (96%) of the surveyed utilities.
Figure 7

The situation of the operational improvements in water utilities.

Figure 7

The situation of the operational improvements in water utilities.

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Water quality control in the surveyed utilities

Seventeen utilities were surveyed regarding their systems for water quality control and compliance with the QCVN 01-1:2018/BYT – National technical regulation on domestic water quality issued by the MOH.

Capacity of the utilities' water quality analysis laboratory
The capacity of the utilities' water quality analysis laboratory is shown in Figure 8. Six utilities (29%) have been granted ISO 9000 certification and 10 (35%) utilities have ISO 17025 certification, with a further 2 utilities either waiting for accreditation or applying for ISO 17025 certification.
Figure 8

Capacity of the utilities' water quality analysis laboratory. (Note: VILAS – Vietnam Laboratory Accreditation Scheme).

Figure 8

Capacity of the utilities' water quality analysis laboratory. (Note: VILAS – Vietnam Laboratory Accreditation Scheme).

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Water quality monitoring undertaken by the utilities

As shown in Figure 9, all the surveyed utilities carried out internal auditing of water quality analysis with 99 parameters of groups A and B. Group A includes two microorganism parameters (coliforms, E. coli, or thermotolerant coliforms) and six sensory and inorganic parameters (arsenic, free chlorine residual, turbidity, color, odor and taste, pH). The frequency of water quality analysis for group A parameters is required not less than once per month. Group B includes 2 microorganism parameters, 26 inorganic parameters, 47 organic parameters, 14 disinfectants and by-products parameters, and 2 irradiation parameters. The frequency of water quality analysis for group B is required not less than once every 6 months.
Figure 9

The situation of performing water quality analysis in the utilities.

Figure 9

The situation of performing water quality analysis in the utilities.

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External auditing of group A and group B parameters is implemented in 12 (71%) of the surveyed utilites. This high ratio indicates adherence to the regulations on water quality control.

Water quality assurance in relation to the National technical regulation on domestic water quality
The situation of water quality assurance according to the National technical regulation on domestic water quality (QCVN 01-1:2018/BYT) is demonstrated in Figure 10. Only 12 (71%) of the utilities regularly meet the National technical regulation on domestic water quality. This raises concerns regarding the performance of some of the utilities in supplying safe drinking water to their customers.
Figure 10

The situation of water quality assurance according to the National technical regulation on domestic water quality.

Figure 10

The situation of water quality assurance according to the National technical regulation on domestic water quality.

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The parameters that are not met regularly are diverse and include COD (KMnO4), pH, hardness, nitrate (NO3), chloride (Cl), and coliforms and free chlorine residual (Cl2) at the end of the water pipe. The reasons and proposed solutions by the utilities are displayed in Table 4.

Water quality improvements made as part of WSP

Most of the surveyed utilities confirmed that WSP implementation directly led to improvements in treated water quality. The parameters to assess the water quality improvement were E. coli, thermotolerant (fecal) coliforms, chlorine residual, and turbidity, as shown in Figure 11. The improvement in turbidity and chlorine residual was reported by 20 (87%) and 19 (83%) companies, respectively. Improvement of E. coli and fecal coliform parameters was reported by 14 (61%) and 13 (57%) companies, respectively.
Figure 11

Water quality improvement as part of WSP.

Figure 11

Water quality improvement as part of WSP.

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Improvement of other parameters: iron, manganese, arsenic, and ammonium were reported by two companies where raw water source was groundwater.

The implementation of a WSP resulted in new actions on water quality control in the water utilities. For example, most utilities now record and archive the data of water quality from the water treatment plant and from household surveillance. Some utilities also archive the customers' complaint records. The treated water samples at all the water utilities have met the National Water Quality Regulation (NWQR) in terms of surveyed parameters. Some utilities performed very well in terms of meeting treated water quality regulations. Turbidity in treated water was below 0.3 NTU at two water utilities. One utility reported inspecting the water quality through different treatment stages that were not previously done. One utility confirmed the stability of the residual chlorine at household's tap water. Improvement of water quality also led to a reduction of number of complaints from customers.

WSP implementation led to improved revenue and cost recovery for the utilities

Of the 23 surveyed utilities, 15 (65%) of the surveyed utilities have confirmed the WSP implementation led to improvement in revenue generation and cost recovery.

Nine utilities indicated that preventing or minimizing risks such as reducing the time of water outage due to incidents. They considered this important in ensuring water quality, maintaining stable water supply pressure and flowrate or continuous water supply leading to increased customers' satisfaction and changing customers' awareness of other water sources. This was felt to lead to increased revenue, and contribute to the protection of water sources and water supply systems. Eight utilities indicated that the WSP helped in reducing non-revenue water, leading to increased revenue and opportunities to recover investment costs.

Two utilities indicated that predicting possible risks in advance, thereby developing a methodical response plan to overcome incidents will reduce costs for repairs. In addition, one company built up an automatic monitoring system from the water treatment plant to the water supply network, hence improving revenue and recovery project investment capital. The reducing and optimization of production costs by improving technology, reducing electricity and chemicals costs, as well as controlling the water treatment process, were mentioned by the three utilities.

WSP auditing

Internal WSP auditing was carried out in 20 (88%) of the utilities (Figure 12). In contrast, external WSP audit was reported in only 10 (43%) of the utilities. The recommendations during WSP audits have been acted upon by 13 utilities (57%) of the utilities surveyed.
Figure 12

WSP audits.

The recommendations based on WSP auditing were diverse. Eight utilities were given recommendations to regularly adjust, update data, and review and evaluation of the effectiveness of their WSP after an incident, or to develop specific detailed plans with appropriate scenarios to handle incidents. Four utilities received recommendations to strengthen the monitoring and protection of water sources, strengthen communication and public awareness on the WSP, improving the supervision and operation of the water supply system, and improving the quality of water supply services from production, transmission, and distribution. Other recommendations included recommending that a water utility managing different water systems in different areas should pilot a WSP in a selected system, and then replicate in other systems. Experience sharing on WSP among water utilities was also recommended by the surveyed water utilities.

Training

Figure 13 shows the experience of utilities with WSP training. 17 (74%) of the surveyed utilities have received WSP training from WHO Vietnam, Ministry of Construction, or VWSA. Twelve (52%) utilities have received more than one WSP training. Sixteen utilities reported having a good understanding of the need for WSP and its concepts based on the training. Eight (35%) of the utilities received training on WSP auditing, and developed a good understanding of the WSP auditing process.
Figure 13

Training on WSP.

Figure 13

Training on WSP.

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Discussion

This study demonstrates that water utilities consider multiple benefits associated with the implementation of WSPs, but that substantial challenges remain in increasing the uptake and use of WSPs. The utilities surveyed have found WSPs useful in improving water quality, and in identifying and implementing improvements in operation and maintenance, environmental protection, and water quality protection. These are all anticipated improvements derived from implementing WSPs (WHO 2005) and suggest that the approach yields benefits in low- and middle-income countries as well as in high-income countries (Rickert et al. 2019). It is also important to note that utilities also saw benefits in revenue and cost-recovery in their companies. This is corroborated by studies in other countries that improved water safety management yields financial and operational benefits (WHO & IWA 2018).

It is interesting to note that most of the utilities have programmes to update WSPs on a regular basis and in response to major upgrades or incidents. This indicates that the training and guidance have been effective in communicating the importance of using WSPs as a living document and the importance of responding to changing conditions. This regular updating is also reflected by the view that climate change is a key driver for action on WSPs, as water quality can be anticipated to vary increasingly as rainfall intensifies and temperatures increase. As noted by Khan et al. (2015), WSPs provide an effective mechanism for managing future climate threats and climate considerations need to be fully integrated into water safety planning in the future. However, as noted by Nijhawan & Howard (2022), more data is required to understand how climate change may affect water safety and therefore determine what actions may be required to maintain safety.

It is also clear that while internal auditing is well-developed, external auditing remains relatively limited and this suggests more investment is required to improve the overall regulation of the water sector. WSPs have been now officially integrated as a mandatory procedure for the operation of water companies by the Vietnamese Government.

Financial constraints appear to represent the major barrier to implementation and wider uptake of WSPs in Vietnam. This is likely to pose a binding constraint on smaller utilities unless support from the Government is more forthcoming. It will be important, however, that if this is done clear outcomes are agreed between Government and the utilities to ensure actions lead to improved water safety management. It may be that result-based financing, pegging a proportion of the payments to deliverables offers one way to provide reassurance to government on value for money (Howard & White 2020).

In order to enhance the role and efficiency of WSPs, an updated version of a Circular on mandatory WSP implementation and WSP audit would be an important motivating factor. Besides, it will be necessary to provide better coordination, guidance, and capacity building support from the government to the utilities. This should be complemented by awareness raising about WSPs to local stakeholders. Our findings suggest that a provincial level Steering Committee on WSP should be created and maintained, as there are a number of issues beyond the scope of individual water utilities to be covered.

Regular training on WSP implementation and auditing for the water supply utilities should be continued and expanded. Our findings also suggest that support on preparation of detailed and appropriate guidelines suitable for each locality on WSP implementation, especially support in in-depth training on risk/hazards assessment is important. This should also address the needs of utilities that are providing water to multiple communities of different sizes and using different sources of water. A guideline for the internal and external WSP auditing is also needed urgently to provide confidence in these processes. Furthermore, regulatory documentation such as a new Circular by the Ministry of Construction on WSP auditing following that guideline would be an important WSP motivation factor, and bring more benefits from efficient WSP implementation.

There has already been a discussion of Certification on WSP based on the external WSP auditing led by VWSA with other stakeholders. Further discussion on this initiative is needed. The VWSA plays an important role as a third-party focal point to facilitate the WSP implementation and dissemination to its members, the water utilities, both those provincial utilities and those responsible for provision of services in rural areas.

Our study demonstrates that overall WSP implementation in the surveyed utilities in Vietnam has been good and that has led to tangible benefits to the utilities and to their customers. The water supplied is safer and WSPs have led to programmes of improvement and investment in water safety. The WSPs are a useful vehicle for addressing climate change concerns and can help the water sector in the country plan, make investments to support adaptation, and improve their resilience. The commitment from Government, utilities, and national professional bodies is strong and provides a sound basis for further expansion of WSPs. However, the critical financial barriers identified will need to be addressed if wider uptake is to be promoted, particularly in smaller and more rural utilities. Costs of developing and implementing WSPs should be counted in connections with other utility expenditures for common benefits, and this could be an interesting topic for further studies. There remain ongoing training needs and for better local guidance to be developed to support utilities effectively implement WSPs. The new regulations on WSPs are an important step in encouraging uptake and implementation, but this may need to be supported by programmes of investment in utilities to ensure that they have the human, technical, and financial resources needed for water safety management.

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

The authors declare there is no conflict.

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Supplementary data