Guide in Developing Water Safety Plan for Health Facilities
In this document:
- •Introduction of the Guidelines
- •II. WATER SUPPLY SYSTEM and PROCESS DESCRIPTION
- •REVIEW AND AUDIT TEMPLATE: REVIEW AND AUDIT
80 tables · ~7k words
Document Info

TABLE OF CONTENTS
| TITLE | Page | |
|---|---|---|
| Definition of Terms / Acronyms | 2 | |
| Introduction of the Guidelines | 3 | |
| Key Introduction to Health Care Facilities | 5 | |
| I. | Assemble a WSP Team | 6 |
| II | Describe the Water Supply System | 7 |
| III | Identify Hazards and Hazardous Events, and Assess the Risk | 13 |
| IV | Determine and Validate Control Measures, Reassess and Prioritize the Risks | 27 |
| V | Improve/Upgrade Plan | 50 |
| VI | Define Monitoring of the Control Measures | 52 |
| VII | Verify the Effectiveness of the WSP | 55 |
| VIII | Develop Management Procedures | 56 |
| IX | Develop Support Programs | 58 |
| X | Conduct WSP System Review | 59 |
| XI | Revise WSP following an Incident | 60 |
| Annex A |
Definition of Terms/ Acronyms
Control Measure – any action or activity that can be used to prevent, reduce or eliminate a water supply quality/safety hazard to a tolerable level
Corrective Action – action to be taken when the results of monitoring at a control point indicate a loss of control
DENR – Department of Environment and Natural Resources
DOH – Department of Health
Hazard – physical, biological (microbiological) or chemical agents that can cause harm to public health
Hazardous Event – an event that introduces hazards to, or fails to remove them from, the water supply HCF – Health Care Facility
LGU – Local Government Unit
NWRB – National Water Resources Board
PNSDW – Philippine National Standard for Drinking Water
PoE – Point of Entry
PoU – Point of Use
Raw Risk – risk determined without considering existing control measures
Residual Risk – risk determined after considering/validating existing control measures
Risk – the likelihood of identified hazards causing harm in exposed populations in a specified timeframe including the magnitude of that harm and/or the consequence
SOP – Standard Operating Procedures
Support Programs – organization-wide programs which are required to support the delivery of quality water by the organization and any contractors used.
WSP – Water Safety Plan
WHO – World Health Organization
Introduction of the Guidelines
Water Safety Plan (WSP) is first introduced by the World Health Organization (WHO) to address issues and problems due to unsafe quality of drinking-water. The WSP approach involves the application of a comprehensive risk assessment and management approach that encompasses all steps in the water supply system from the catchment to consumers. This concept is a cost effective and preventive strategy that ensures safety and quality of drinking water(1) .
At present, the WHO has created a guiding document for the creation of WSP for buildings which includes water safety planning for hospitals (2). The need for the development and implementation of WSP in health care facilities is crucial due to the number of outbreaks recorded that were linked to ingestion of contaminated drinking-water. Moreover, hospitals cater vulnerable population who are immunocompromised that maybe exposed to unsafe drinking-water which further aggravates the patients' health condition (2). Some identified pathogens that caused these outbreaks were Legionella spp., and Pseudomonas aureginosa (3) .
Hospitals generally tapped with the municipal water service providers for their source of drinking-water. However, even though series of treatment was done prior to distribution of water among consumers, problems arise because of the faulty and corroded biofilm laden pipelines that serve as a point of entry for unwanted microorganisms (3). The contaminated water then may be consumed by patients through drinking, irrigation of wounds, or even inhalation (2). Hence, the need for WSP is very important.
In the Philippines, through the initiative of the Department of Health, issued a policy that requires all water service providers to devise and implement WSPs specifically designed on the existing water system (4). The evolving advancement on the medical practice in the country as evidenced by the increasing number of the different types of hospitals and health care facilities call for the need to a cautious monitoring of these establishments.
On an Administrative Order No. 2012-0012 issued by DOH, the different classification of hospitals and other health care facilities in the country were defined as to type of (1) ownership: government owned hospital and private which is established through donations, investments, etc. of any individual, corporations, and organizations; (2) scope of services: (1) general hospital which caters all forms of illnesses, diseases, injuries and deformities, and (2) specialty hospital that specializes in a particular disease or condition or in one type of patient.
Furthermore, the general hospitals are subdivided into three more levels which specifically describe the functional capacity of the facility. The development of WSP for healthcare facilities e.g. hospitals is a milestone on consistently addressing the need for the safe access to drinking-water. Thus, this guideline provides a step-by-step process on the formulation of WSP tailored fit on hospital setting which will also serve as a model for other health care facilities on the formulation of their own WSPs.
Key Introduction to Health Care Facilities (HCF)
In conducting a detailed and comprehensive assessment of a health care facility the following information are critical:
-
- Description/Overview of the HCF
- a. Name of the HCF
- b. Location or Address
- c. Type of HCF (see Administrative Order 2012-0012a)
- d. Year established
- e. Bed capacity
- f. Number of staffs (regular and contractual)
- g. Floor and lot area
- h. Number of floors
-
- Water sources (all which is applicable)
- a. Water district
- b. LGU-managed
- c. Community-managed
- d. HCF-owned deep well
- e. Privately- managed
-
- Waste Management System
- a. Wastewater
- b. Solid waste
- c. Health care waste
-
- Power Supply
- a. Two-phase
- b. Three-phase
- c. Stand-by-generator (include kVA)
1. Assemble a WSP Team
Convening a team is a critical requirement for the formulation and implementation of a WSP for the hospital. Identifying the roles and responsibilities of each of the team members is crucial on the success of WSP execution. A WSP coordinator must be identified to facilitate the overall coordination and monitoring of the WSP implementation. In order to signify management support for the WSP, an office order signed by the head of the Health Care Facility (HCF) must be included in the WSP.
Assigning a WSP coordinator is crucial for the success of the WSP implementation. Such person should be responsible in convening the selected members for the overall team. The coordinator must also have or acquire a good knowledge of the technical facilities in the building (in such case of the health care facility) and their daily work should be related to the facility. The primary task then of the coordinator is to coordinate the process of WSP development and implementation among the team members hence, technical knowledge in drinking-water and/or sanitation may be useful but not necessarily required. Moreover, the coordinator has the sole responsibility of ensuring the continuous monitoring and implementation of the WSP in place thus a building manager would be a good option for the WSP coordinator role.
On the other hand, the team members should be a mix of technical experts in various fields such as but not limited to design, operation, and management of drinking-water supplies, engineering, plumbing, and public health risk assessment. Also, the team should have been represented by people from the end users/consumers. The following are some of the stakeholders1 that might contribute to the water quality: (1) Water supply providers; (2) Waste management service providers; (3) Suppliers; (4) LGU; (5) Concerned national agencies e.g., DOH, DENR, NWRB (6) Nearby community; (7) Water users in the HCF; and (8) Others.
Below is a sample of a WSP team structure which can serve as a guide in designating the roles and responsibilities of the selected WSP coordinator, technical experts, and team members.
1 If water source is owned by HCF, the HCF will identify the stakeholder from source to user premises. If water is provided by water service provider, the HCF will identify the stakeholders from point of entry to user premises only.
2. Describe the Water Supply System
A detailed description of the water system is required to assist the succeeding risk assessment process. It must provide a comprehensive plan which covers the nature and quality of water supplied to the building up to the consumer. As part of describing the system, the HCFs must identify the different users of water in their facility. The users may include the patients, watchers, guests/visitor and employees. The different uses for which the users utilize the water must also be identified as different uses entails different level of water quality needed. The use may be for general purpose (e.g. drinking, cooking, flushing, washing, bathing, gardening, fire protection) or HCF-specific (e.g. dialysis, autoclaving).
In addition, the WSP should provide sufficient information to identify where the system is vulnerable to hazardous events, relevant types of hazard, and control measures. The following are critical information that must be included in the description:
- a. Results of mandatory water quality parameters based on latest PNSDW2 .
- b. Known or suspected changes in source water quality relating to weather or other conditions;
- c. Information relating to the water treatment such as:
- Type of treatment (filtration, sedimentation, coagulation, chlorination, reverse osmosis, ion exchange, UV, ozonation, etc.)
- Chemicals used (volume per month,
- Year installed per treatment facility
- Contaminants being removed per treatment facility
- Treatment facility location in the HCF
- Capacity of the water treatment facility
- Volume of water being treated per treatment facility;
- d. Information relating to the storage of water such as:
- Type of storage (ground, elevated)
- Technology applied (fill and draw, floating, pneumatic)
- Height of storage (for elevated tank) Description of storage tank location Number, Volume and shape of storage tank
- Material composition of storage tank
2 For water source owned by HCF, the HCF will be responsible for water quality testing of its water supply system based on the latest PNSDW and per level of water service. For water source from water service provider, the HCF will be responsible for testing from point of entry/after the meter to entire water supply system in the HCF premises based on the latest PNSDW (under Building category).
- Frequency of cleaning;
- e. Information relating to the water distribution network such as:
- Diameter, Length of pipe network
- Material used
- Water quality from the tap; and
- f. Description of all the materials that comes in contact with water
2.1. Source Water Description
The following are the possible sources of water supply for the hospital HCF
a. Water district (Level III Water System)
It is a local corporate entity that operates and maintains a water supply system in one or more provincial cities or municipalities. It is classified as a government-owned and controlled corporation, existing under the authority of The Provincial Water Utilities.
b. LGU – managed water utility (Level III Water System)
It is a source of water in which the local government unit (municipal/city level) manages, controls, and maintains the operation of the water utility. It caters number of households up to the community level.
c. Privately-managed water utility (Level III Water System)
It is a source of water in which the private sector manages, controls, and maintains the operation of the water utility. It caters number of households up to the community level.
d. Community-managed water utility (Level III Water System)
It is a source of water in which the community association manages, controls, and maintains the operation of the water utility. It caters number of households up to the community level.
e. HCF- owned deep well
It is a well with depth greater than 20 meters constructed in areas characterized by aquifers or water-bearing formations generally located at a depth of more than 20 meters below ground surface.
f. Water refilling stations
This source of drinking water may come in the form of using the Jerry can as water container or through a water dispenser.
2.2. Typical components of water systems inside a typical HCF
The use of a schematic diagram is utilized using illustrations to show how water flows inside the HCF. This provides a simple understanding of the water supply system which shall be vital in the succeeding modules.

Figure. 2.2.1. Schematic layout of Components of water systems inside a typical HCF
The figure above shows the typical elements of the water system being utilized inside a HCF. The abovementioned water supply systems are to be described in full detail. The following are the information necessary to describe the system:
| Details to be provided (if applicable) | |
|---|---|
| Water Source | a) Water supply provider (average volume billed/consumed per |
| year, latest water quality results – Point of Entry) | |
| b) Deep-well information (depth, diameter, year constructed, | |
| casing material, water quality) | |
| c) Pumping equipment (capacity, horsepower rating, year installed) | |
| Water Treatment | a) Type of treatment (filtration, sedimentation, coagulation, |
| chlorination, reverse osmosis, ion exchange, UV, | |
| ozonation, etc.) | |
| b) Chemicals used (volume per month, | |
| c) Year installed per treatment facility | |
| d) Contaminants being removed per treatment facility | |
| e) Treatment facility location in the HCF | |
| f) Capacity of the water treatment facility | |
| g) Volume of water being treated per treatment facility | |
| Storage | a) Type of storage (ground, elevated) |
| b) Technology applied (fill and draw, floating, pneumatic) | |
| c) Height of storage (for elevated tank) | |
| d) Description of storage tank location | |
| e) Number, Volume and shape of storage tank | |
| f) Material composition of storage tank | |
| g) Frequency of cleaning | |
| Distribution | a) Diameter, Length of pipe network |
| b) Material used | |
| c) Water quality from the tap | |
| User Premises | a) User practices on handling drinking water (e.g. storage, |
| dispenser, tap) | |
| Others | b) Hot and cold water system |
| c) Non-drinking water system (e.g. flushing, cleaning, laundry) |
2.3. Process Flow Diagram
In contrast, process flow diagrams utilize symbols to reflect the different stages in the water supply system. For simplicity and consistency, standard flow diagrams symbols are generally used (Tool 2.3.1) to construct the flow diagram.
Tool 2.3.1. Process Flow Diagram Symbols
| Flow Diagram Symbol | Definition of Symbol |
|---|---|
| Operation: Indicates when there is an operation or group of operations that result in intentional change in the water. | |
| Inspection: Represents an inspection or decision, for example, water supply is examined or is verified. | |
| Storage: Where water is stored. | |
| Transport: Occurs when the water is moved from one place to another. | |
| Combined activity: Indicates activities performed either concurrently or by the same operator at the same location. Any combination of symbols may be used. Example shown indicates a combined operation and inspection. |
Tool 2.3.2. Process Flow Diagram Sample (Process Flow Diagram of Tapped Water From Water District)
| Step Process | Description | Responsibility |
|---|---|---|
| $\overline{}$ | WD source | BCWD |
| Water Meter | Eng'g./BCWD | |
| $\otimes$ | Check Valve | Plumber |
| Distribution line | Eng'g. /Plumber | |
| Booster pump | Electrician/operator | |
| Pressurized tank | Eng'g./pllumber | |
| Distribution line | Eng'g./Plumber | |
| Monitoring | Eng'g./Plumber | |
| Consumer | Plumber | |
| Filtration process | End user/plumber | |
| Reverse Osmosis Process | End user/Plumber |
| Step Process | Description | Responsibility |
|---|---|---|
| UV Light | End user | |
| Distribution line | End user/ plumber | |
| Ф | Monitoring | Dialysis (end user)/Outsource |
| Consumer | End user | |
| Cistern Tank | Eng'g./Plumber | |
| Booster pump | Electician/plumber | |
| $\otimes$ | Manipulated Valve ( Note: Optional use when deep well pump busted) | Eng'g./plumber |
| Overhead storage tank | Eng'g./plumber |
3. Identify Hazards and Hazardous Events, and Assess the Risk
Based on the constructed flow diagram, the potential hazards and hazardous events that may take place on the water system form the source of water (PoE) up to the point of use must be identified by the WSP team. Several factors are considered in the identification of the hazards which include the quality of the raw water, and the equipment used on the water system. The identification of the hazards and hazardous event may be conducted through existing records, historical events, local knowledge, and onsite visits that can affect the safety of the water supply. The team should consider all the potential biological, physical, and chemical hazards (as discussed below) that could be linked with the water supply.
The hazards are classified into chemical and/or microbiological categories. After the identification of the hazards was done, hazard analysis is conducted to evaluate and prioritize the risks that may contribute to adverse health effects. The WSP team can utilize the semiquantitative risk assessment to calculate for the priority score for each of the identified hazard. The objective of this is to rank which hazardous events requires immediate intervention. The likelihood and severity was derived from the team's technical knowledge and expertise, historical data and relevant guidelines. Moreover, the WSP team determined a cut-off point, which is risk score of 5, above which all hazards will be retained for further consideration. There is little value in expending a great deal of effort considering very small risks.
Potential microbiological hazards indicated in the WSP may include:
- Bacteria Salmonella, Shigella, V. Cholerae, Y. enterocolita, C. jejuni, E.coli, Legionella, Mycobacterium spp., Pseudomonas aeruginosa
- Viruses – Hepatitis A & E, Norwalk, Rotavirus, Poliovirus
- Protozoa – Entamoeba histolytica, Giardia lamblia, Cryptosporidium parvum
- Helminths – roundworms, tapeworms, flukes
- Fungi Aspergillus, Fusarium, Exophilia
Potential chemical hazards indicated in the WSP may include:
- Inorganic constituents with health significance Antimony, Arsenic, Barium, Boron, Cadmium, Chromium, Cyanide, Lead, Mercury
- Organic constituents with health significance Benzene, Toluene, Zylenes, Styrene, Polynuclear Aromatic Hydrocarbons (PAHs)
- Organic constituents from agricultural pollution (pesticides)
- Disinfectants and disinfectant by-products
Hazardous events arise from non-compliance of the hospital administration on the established sanitation standard operating procedures poor equipment maintenance as well.
Tool 3.1. Typical Hazards and Hazardous Events in Purified Water Process
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category |
|---|---|---|
| Point of Entry to the | Compromised and unsafe | Microbiological Chemical |
| Building (Source of raw | use of contaminated water | |
| water) | from source |
| Intrusion and use of | Microbiological Chemical | ||
|---|---|---|---|
| contaminated water for | |||
| processing due to use of | |||
| non-food grade pipe and | |||
| adhesive materials | |||
| Contamination of water | Chemical | ||
| due to deterioration of | |||
| pipes | |||
| Incorrect operation and | Microbiological | ||
| interruption of treatment | Chemical | ||
| on PoE | |||
| Inadequate maintenance of | Microbiological Chemical | ||
| PoE treatment | |||
| Overdosing with treatment | Chemical | ||
| chemicals or release of | |||
| treatment chemicals into | |||
| distribution systems | |||
| Possible building-specific | Contamination of water | Microbiological | |
| sources of water and | from tank caused by | ||
| associated treatment (e.g. | accumulated dirt and | ||
| raw water storage) | microorganisms that grow | ||
| from the tank | |||
| from the tank such as lead | |||
| Microbiological Chemical | |||
| drinking and non-drinking | contaminated water for | ||
| purposes | processing due to use of | ||
| Cross connection of | Microbiological | ||
| Water pipelines both for | Contamination due to leaching toxic materials Intrusion and use of non-food grade pipe and adhesive materials | Chemical |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category |
|---|---|---|
| different water quality | Chemical | |
| (drinking and non-drinking | ||
| water supply) resulting to | ||
| leakage of chemicals and | ||
| possible intrusion of | ||
| contaminated water |
| Devices for heating and supplying hot water | Insufficient maintenance and monitoring of the | Chemical Microbiological |
|---|---|---|
| equipment Deterioration of materials | Chemical | |
| and fixtures leading to | ||
| leaching of toxic materials | ||
| such as lead | ||
| Low water temperatures in | Microbiological | |
| hot-water storage vessels | ||
| supports microbial growth | ||
| Hot water piping system | Poor temperature control | Microbiological |
| supports microbial growth | ||
| such as Legionella | ||
| Insufficient maintenance of | Chemical | |
| the pipelines resulting to | ||
| scaling and corrosion | ||
| Deterioration of pipes | Chemical | |
| leading to leaching of lead | ||
| to water supply | ||
| Stagnation and low water | Microbiological | |
| flows (hot system) | ||
| Cold water piping system | Insufficient maintenance of | Chemical |
| the pipelines resulting to | ||
| scaling and corrosion | ||
| Deterioration of pipes | Chemical | |
| leading to leaching of lead | ||
| to water supply | ||
| Stagnation and low water | Microbiological | |
| flows (cold system) | ||
| Poor temperature control | microbiological | |
| supports microbial growth | ||
| Equipment for point of use | Poor maintenance of PoU | Microbiological |
| (PoU) | equipment supports | |
| microbial growth and/or | ||
| corrosion | ||
| Inadequate backflow | Chemical | |
| prevention on PoU | ||
| equipment | ||
| Aerosol formation | Microbiological | |
| providing potential |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category |
|---|---|---|
| exposure to respiratory | ||
| disease due to poor | ||
| equipment maintenance | ||
| Improper connection of | Microbiological | |
| PoU devices and | ||
| equipment | ||
| Water treatment systems at | Incorrect installation of | Chemical |
| PoU | water treatment systems | |
| Insufficient maintenance | Chemical Microbiological | |
| and monitoring of the | ||
| equipment | ||
| Excessive doses of | Chemicals | |
| treatment chemicals e.g. | ||
| chlorine |
Tool 3.2. Risk Assessment Method
After all the potential hazards are identified, a hazard analysis should be conducted to evaluate the severity of the risks or health effects of the hazards. The risk assessment should take into account the number and vulnerability of exposed people and the type of exposure. A simple risk scoring matrix for prioritization is used.
The computed risk score in this module will be the raw risk scoring. Raw risk is defined as the risk before anything is done to mitigate or manage it (i.e. before controls are in place). The raw risk only takes into account the likelihood and severity of the hazardous event without taking into consideration any of the existing controls in the facility.
Table 3.2.1. Semi-Quantitative Risk Matrix (Source: Deere et. al. 2001)
| Severity / Consequence | ||||||
|---|---|---|---|---|---|---|
| Risk Factor Matrix | Insignificant No Impact/ Not Detectable Rating 1 | Minor Compliance Impact Rating 2 | Moderate Aesthetic Impact Rating 3 | Major Regulatory Impact Rating 4 | Catastrophic Public Health Impact Rating 5 | |
| Almost Certain Once a day Rating 5 | 5 | 10 | 15 | 20 | 25 | |
| Likely Once a week Rating 4 | 4 | 8 | 12 | 16 | 20 | |
| Moderate Once a month Rating 3 | 3 | 6 | 9 | 12 | 15 | |
| Unlikely Once a year Rating 2 | 2 | 4 | 6 | 8 | 10 | |
| Rare Once every 5 years Rating 1 | 1 | 2 | 3 | 4 | 5 | |
| Risk Score | <6 | 6-9 | 10-15 | >15 | ||
| Risk Rating | Low | Medium | High | Very High |
Table 3.2.2. Examples of definitions of likelihood and severity categories that can be used in risk scoring
| Item | Definition | Rating |
|---|---|---|
| Likelihood categories | ||
| Almost certain | Once per day | 5 |
| Likely | Once per week | 4 |
| Moderately likely | Once per month | 3 |
| Unlikely | Once per year | 2 |
| Rare | Once every 5 years | 1 |
| Severity categories |
| Catastrophic | Potentially lethal to all people using the building, | 5 |
|---|---|---|
| including vulnerable groups e.g. | ||
| immunocompromised patients, infants, ant the | ||
| elderly), following acute exposure | ||
| Major | Potentially harmful to all people using the | 4 |
| building following acute exposure | ||
| Moderate | Potentially harmful to vulnerable groups (e.g. | 3 |
| immunocompromised patients, infants and the | ||
| elderly) following chronic exposure | ||
| Minor | Potentially harmful to all people using the | 2 |
| building following chronic exposure | ||
| Insignificant | No impact or not detectable | 1 |
The next table shows a sample risk assessment method to identify which among the potential/existing hazards require immediate intervention. The matrix provides a quick overview of the impact that a certain hazard could contribute if not properly addressed or intervened.
Tool 3.3. Sample Template and Contents for Hazard Identification and Risk Assessment
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | LIKELIHOOD | SEVERITY | RAW RISK SCORE | RAW RISK RATING |
|---|---|---|---|---|---|---|
| Point of Entry to the Building (Source of raw | Compromised and unsafe use of contaminated water from source | Microbiological Chemical | 4 | 5 | 20 | Very High |
| water) | Intrusion and use of contaminated water for processing due to use of non-food grade pipe and adhesive materials | Microbiological Chemical | 4 | 5 | 20 | Very High |
| Contamination of water due to deterioration of pipes | Chemical | 3 | 4 | 12 | High | |
| Incorrect operation and interruption of treatment on PoE | Microbiological Chemical | 3 | 5 | 15 | High |
| Inadequate maintenance of PoE treatment | Microbiological Chemical | 4 | 5 | 20 | Very High |
|---|---|---|---|---|---|
| ----------------------------------------- | ----------------------------- | --- | --- | ---- | ----------- |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | LIKELIHOOD | SEVERITY | RAW RISK SCORE | RAW RISK RATING |
|---|---|---|---|---|---|---|
| Overdosing with treatment chemicals or release of treatment chemicals into distribution systems | Chemical | 4 | 4 | 16 | Very High | |
| Possible buildingspecific sources of water and associated treatment (e.g. raw water storage) | Contamination of water from tank caused by accumulated dirt and microorganisms that grow from the tank | Microbiological | 5 | 5 | 25 | Very High |
| Contamination due to leaching toxic | Chemical | 4 | 4 | 16 | High | |
|---|---|---|---|---|---|---|
| materials from the tank such as lead | Cnemical | 4 | 4 | 10 | High | |
| Water pipelines both for drinking and non-drinking purposes | Intrusion and use of contaminated water for processing due to use of non-food grade pipe and adhesive materials | Microbiological Chemical | 4 | 5 | 20 | Very High |
| Cross connection of different water quality (drinking | Microbiological Chemical | 1 | 5 | 5 | Low | |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | LIKELIHOOD | SEVERITY | RAW RISK SCORE | RAW RISK RATING |
| and non-drinking water supply) resulting to leakage of chemicals and possible intrusion of contaminated |
water
| Devices for heating and supplying hot water (Note: may or may not be | Insufficient maintenance and monitoring of the\nequipment | Chemical Microbiological | 4 | 5 | 20 | Very High |
|---|---|---|---|---|---|---|
| present) | Deterioration of materials and fixtures leading to leaching of toxic materials such as lead | Chemical | 3 | 4 | 12 | High |
| Low water temperatures in hot-water storage vessels supports microbial growth | Microbiological | 2 | 5 | 10 | High | |
| Hot water piping system (Note: may or may not be present) | Poor temperature control supports microbial growth such as Legionella | Microbiological | 3 | 5 | 15 | High |
| Insufficient maintenance of the pipelines resulting | Chemical | 4 | 4 | 16 | Very High | |
| Process Steps (Components of | Hazardous Event(s) (Source of Hazard) | Hazard Category | LIKELIHOOD | SEVERITY | RAW RISK SCORE | RAW RISK RATING |
| Water System) | ||||||
|---|---|---|---|---|---|---|
| to scaling and corrosion | ||||||
| Deterioration of pipes leading to leaching of lead to water supply | Chemical | 1 | 4 | 4 | Low | |
| Stagnation and low water flows (hot system) | Microbiological | 4 | 5 | 20 | Very High | |
| Cold water piping system (Note: may or may not be present) | Insufficient maintenance of the pipelines resulting to scaling and corrosion | Chemical | 4 | 4 | 16 | Very High |
| Deterioration of pipes leading to leaching of lead to water supply | Chemical | 1 | 4 | 4 | Low | |
| Stagnation and low water flows (cold system) | Microbiological | 4 | 5 | 20 | Very High |
| Poor temperature control supports microbial growth | microbiological | 4 | 5 | 20 | Very High | |
|---|---|---|---|---|---|---|
| Equipment for point of use (PoU) | Poor maintenance of PoU equipment supports microbial growth and/or corrosion | Microbiological | 4 | 5 | 20 | Very High |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | LIKELIHOOD | SEVERITY | RAW RISK SCORE | RAW RISK RATING |
| Inadequate backflow prevention on PoU equipment | Chemical | 3 | 5 | 15 | High | |
| Aerosol formation providing potential exposure to respiratory disease due to poor equipment maintenance | Microbiological | 3 | 5 | 15 | High | |
| Improper connection of PoU | Microbiological | 3 | 5 | 15 | High |
| devices and equipment | ||||||
|---|---|---|---|---|---|---|
| Water treatment systems at PoU | Incorrect installation of water treatment systems | Chemical | 1 | 5 | 5 | Low |
| Insufficient maintenance and monitoring of the equipment | Chemical Microbiological | 4 | 5 | 20 | Very High | |
| Excessive doses of treatment chemicals e.g. chlorine | Chemicals | 3 | 4 | 12 | High |
4. Determine and Validate Control Measures, Reassess, and Prioritize the Risks
Once the raw risks for each hazardous event have been identified, the existing control measure will need to be verified to recalculate the raw risk resulting to the residual risk rating. In definition, control measures are any action of activity that can be used to prevent, reduce or eliminate a water supply quality/safety hazard to tolerable level. This may take the form of:
- Preventing entry of contaminants to the water
- Removal of hazards from water
- Inactivation of pathogens
- Maintaining quality of water during distribution
Once validation of effectiveness, these control measures help reduce the risk rating of the hazardous events leading to the new risk score termed as the residual risk score. This residual risk score serves as basis in prioritizing which of the hazardous events need to be addresses short-term, medium-term and long-term. The higher the residual risk score, the more it needs to be addressed immediately.
The tables below show the different control measures which may be adopted by the HCFs for each type of hazardous events and how the residual risk score is calculated.
Tool 4.1. Control Measures for the Identified Hazards in the Hospital Water System
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | Raw Risks | Control Measure(s) |
|---|---|---|---|---|
| Point of Entry to the Building (Source of raw | Compromised and unsafe use of contaminated water from source | Microbiological Chemical | Very High | Use only of potable water that passed the PNSDW standards |
| water) | Intrusion and use of contaminated water for processing due to use of nonfood grade pipe and adhesive materials | Microbiological Chemical | Very High | Use DOH recommended pipelines and adhesive materials |
| Contamination of water due to deterioration of pipes | Chemical | High | Replace pipes with DOH recommended materials | |
| Incorrect operation and interruption of treatment on PoE | Microbiological Chemical | High | Daily monitoring of operation Assign staff to perform maintenance Installation of alarms for key processes Provision of standby generator in case of power interruptions |
| Inadequate maintenance of PoE treatment | Microbiological Chemical | Very High | Assign staff to perform maintenance Ensure processes are maintained according to manufacturer's instructions |
|---|---|---|---|
| Overdosing with treatment chemicals or release of treatment chemicals into distribution systems | Chemical | Very High | Ensure dosing equipment and storages are maintained Avoid overdesigning chemical storage capacities |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | Raw Risks | Control Measure(s) |
|---|---|---|---|---|
| Possible | Contamination of water from | Microbiological | Scheduled cleaning of water storage tanks | |
| building | tank caused by accumulated | |||
| specific sources | dirt and microorganisms that | Very High | ||
| of water and | grow from the tank | |||
| associated | Contamination due to | Chemical | Replace storage tank with DOH approved material | |
| treatment (e.g. | leaching toxic materials from | |||
| raw water | the tank such as lead | High | ||
| storage) | ||||
| Water pipelines | Intrusion and use of | Microbiological | Use of DOH approved pipes and adhesive materials | |
| both for drinking | contaminated water for | Chemical | ||
| and non-drinking | processing due to use of | Very High | ||
| purposes | nonfood grade pipe and | |||
| adhesive materials |
| Cross connection of different water quality (drinking and non-drinking water supply) resulting to leakage of chemicals and possible intrusion of contaminated water | Microbiological Chemical | Low | Ensure separation from water systems and appropriate labeling and marking of pipework and fittings | |
|---|---|---|---|---|
| Devices for heating and | Insufficient maintenance and monitoring of the equipment | Chemical Microbiological | Very High | Assign staff to perform maintenance |
| supplying hot water (Note: may or may not be | Deterioration of materials and fixtures leading to leaching of toxic materials such as lead | Chemical | High | Replace materials and fixtures with DOH approved materials |
| present) | Low water temperatures in hot-water storage vessels supports microbial growth | Microbiological | High | Adjust heater temperature Ensure sufficient energy delivery |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | Raw Risks | Control Measure(s) |
|---|---|---|---|---|
| -------------------------------------------------- | ------------------------------------------ | -------------------- | ----------- | -------------------- |
| Check heater thermostat | ||||
|---|---|---|---|---|
| Maintain temperatures above 50 o C in distribution system | ||||
| Maintain temperatures above 60 o C in storage vessels | ||||
| Install temperature reduction devices as close as possible to PoU | ||||
| Insulate system | ||||
| Avoid stagnation and low flow areas | ||||
| Ensure sufficient capacity for maximum flows | ||||
| Hot water piping | Poor temperature control | Microbiological | Insulate cold and hot water pipes | |
| system (Note: | supports microbial growth | High | ||
| may or may not | such as Legionella | Keep systems physically separate | ||
| be present) | Insufficient maintenance of | Chemical | Assign staff to perform maintenance | |
| the pipelines resulting to | Very High | |||
| scaling and corrosion | ||||
| Deterioration of pipes leading | Chemical | Replace pipes with DOH approve materials | ||
| to leaching of lead to water | Low | |||
| supply |
| Stagnation | and | low | water | Microbiological | Avoid overdesigning capacities | ||
|---|---|---|---|---|---|---|---|
| flows (hot system) | Very High | Isolate areas that are not used for extended periods |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | Raw Risks | Control Measure(s) |
|---|---|---|---|---|
| Remove dead legs and minimize length of branch pipes | ||||
| Cold water | Insufficient maintenance of | Chemical | Assign staff to perform maintenance | |
| piping system | the pipelines resulting to | Very High | ||
| (Note: may or | scaling and corrosion | Replace pipes with DOH approve materials | ||
| may not be | Deterioration of pipes leading | Chemical | Replace pipes with DOH approve materials | |
| present) | to leaching of lead to water | Low | ||
| supply |
| Stagnation and low water flows (cold system) | Microbiological | Avoid overdesigning capacities | ||
|---|---|---|---|---|
| Remove the causes of fluctuation (e.g. high peak water demand, fire drills) | ||||
| Very High | Prevent negative pressures | |||
| Flush systems that are not used frequently | ||||
| Isolate areas that are not used for extended periods | ||||
| Remove dead legs and minimize length of branch pipes | ||||
| Poor temperature control | Microbiological | Insulate cold and hot water pipes | ||
| supports microbial growth | Very High | Keep systems physically separate | ||
| Equipment for point of use (PoU) | Poor maintenance of PoU equipment supports microbial growth and/or corrosion | Microbiological | Very High | Assign staff to perform maintenance |
| Inadequate backflow prevention on PoU equipment | Chemical | High | Minimize connections and provide backflow prevention where required | |
| Process Steps (Components of Water System) | Hazardous Event(s) (Source of Hazard) | Hazard Category | Raw Risks | Control Measure(s) |
| Aerosol contamination on sewerage or septic systems | Microbiological | Install water traps in sewage lines | ||
|---|---|---|---|---|
| sewerage of septic systems | High | Filter double traps in high-risk environment | ||
| Prevent contamination from septic tanks | ||||
| Improper connection of PoU devices and equipment | Microbiological | High | Ensure proper establishment of connection for all POU equipment and devices | |
| Water treatment | Incorrect installation of water | Chemical | Choose quality materials | |
| systems at PoU | treatment systems | Low | Follow local or international choice and construction rules | |
| Use active protection of pipes (e.g. sacrificial anodes, anticorrosion products) | ||||
| Insufficient maintenance and monitoring of the equipment | Chemical Microbiological | Very High | Assign staff to perform maintenance | |
| Excessive doses of treatment | Chemicals | Ensure dosing equipment and storages are maintained | ||
| chemicals e.g. chlorine | High | Avoid overdesigning chemical storage capacities | ||
| Minimize cross-connections and provide backflow prevention where required |
Tool 4.2. Sample Template and Content for Determining and Validating Control Measures, Reassessing and Prioritizing Risks
| Process | HAZARDOUS EVENT | TYPE OF HAZARD | RAW RISK | EXISTING CONTROL MEASURES | VALIDATION OF CONTROL MEASURES | RESIDUAL RISK | ||||
|---|---|---|---|---|---|---|---|---|---|---|
| Steps (Component s of Water System) | ||||||||||
| Point of Entry to the Building (Source of raw water) | Compromised and unsafe use of contaminated water from source | Microbiolo gical Chemical | 4 | 5 | 20 | Use only of potable water that passed the PNSDW standards | Water supply tapped with service provider (water quality compliant) | 1 | 5 | 5 Low |
| Intrusion and use of contaminated water for processing due to use of nonfood grade pipe and adhesive materials | Microbiolo gical Chemical | 4 | 5 | 20 | Use DOH recommended pipelines and adhesive materials | Pipes and materials accredited by DOH | 1 | 5 | 5 Low |
| Contamination of water due to deterioration of pipes | Chemical | 3 | 4 | 12 | Replace pipes with DOH recommended materials | Pipes replaced with accredited materials | 1 | 5 | 5 Low | |
|---|---|---|---|---|---|---|---|---|---|---|
| Process | HAZARDOUS | TYPE OF | RAW RISK | EXISTING CONTROL | VALIDATION OF CONTROL | RESIDUAL RISK |
| Process | HAZARDOUS EVENT | TYPE OF HAZARD | RAW RISK | EXISTING CONTROL MEASURES | VALIDATION OF CONTROL MEASURES | RESIDUAL RISK | ||||
|---|---|---|---|---|---|---|---|---|---|---|
| Steps (Component s of Water System) | ||||||||||
| Incorrect operation and interruption of treatment on PoE | Microbiolo gical Chemical | 3 | 5 | 15 | Daily monitoring of operation Assign staff to perform maintenance Installation of alarms for key processes Provision of standby generator in case of power interruptions | Missing data on the monitoring sheet No assigned personnel to perform maintenance Alarms installed on key processes No generator for backup electricity | 3 | 5 | 15 High |
| Inadequate maintenance of PoE treatment | Microbiolo gical Chemical | 4 | 5 | 20 | Assign staff to perform maintenance Ensure processes are maintained according to manufacturer's instructions | No assigned personnel to perform maintenance Missing information of the monitoring sheet | 4 | 5 | 20 Very High |
|---|---|---|---|---|---|---|---|---|---|
| Overdosing with treatment chemicals or | Chemical | 4 | 4 | 16 | Ensure dosing equipment and storages are | Proper dose of chlorine recorded and maintained | 1 | 5 | 5 Low |
| Process | HAZARDOUS | TYPE OF | R | AW RIS | SK | EXISTING CONTROL | VALIDATION OF CONTROL | RESIDUAL RISK | |||
|---|---|---|---|---|---|---|---|---|---|---|---|
| Steps | EVENT | HAZARD | MEASURES | MEASURES | _ | l | |||||
| (Component s of Water System) | LIKELIHOOD | SEVERITY | RAW RISK SCORE | LIKELIHOOD | RISK SCORE | RESIDUALRISK RATING | |||||
| release of treatment chemicals into | maintained Avoid | ||||||||||
| distribution systems | overdesigning chemical storage capacities |
| Possible | Contamination | Microbiolo | Scheduled cleaning of | Cleaning schedule not | 5 | 5 | ||||
|---|---|---|---|---|---|---|---|---|---|---|
| buildingspecific sources of water and associated treatment (e.g. raw water storage) | of water from tank caused by accumulated dirt and microorganism s that grow from the tank | gical | 5 | 5 | 25 | water storage tanks | properly done | 25 Very High | ||
| Contamination due to leaching toxic materials from the tank such as lead | Chemical | 4 | 4 | 16 | Replace storage tank with DOH approved material | Storage tank not approved by DOH | 4 | 4 | 16 Very High | |
| Water pipelines both for drinking and non | Intrusion and use of contaminated water for processing due | Microbiolo gical Chemical | 4 | 5 | 20 | Use of DOH approved pipes and adhesive materials | Pipes replaced with accredited materials | 1 | 5 | 5 Low |
| Process | RAW RISK | RESIDUAL RISK | ||||
|---|---|---|---|---|---|---|
| Steps (Component s of Water System) | HAZARDOUS EVENT | TYPE OF HAZARD | EXISTING CONTROL MEASURES | VALIDATION OF CONTROL MEASURES | ||||||
|---|---|---|---|---|---|---|---|---|---|---|
| drinking purposes | to use of nonfood grade pipe and adhesive materials | |||||||||
| Cross connection of different water quality (drinking and non-drinking water supply) resulting to leakage of chemicals and possible intrusion of contaminated water | Microbiolo gical Chemical | 1 | 5 | 5 | Ensure separation from water systems and appropriate labeling and marking of pipework and fittings | Proper labeling of systems noted | 1 | 5 | 5 Low |
| Devices for | Insufficient | Chemical | Assign staff to perform | No definite staff assigned for | ||||||
|---|---|---|---|---|---|---|---|---|---|---|
| heating and | maintenance | Microbiolo | maintenance | maintenance | 20 | |||||
| supplying | and | gical | 4 | 5 | 20 | 4 | 5 | Very | ||
| hot water | monitoring of | High | ||||||||
| the equipment |
| Process | HAZARDOUS | TYPE OF | RAW RISK | EXISTING CONTROL | VALIDATION OF CONTROL | RESIDUAL RISK | |||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| Steps | EVENT | HAZARD | MEASURES | MEASURES | |||||||
| (Component | |||||||||||
| s of Water | |||||||||||
| System) | |||||||||||
| Deterioration | Chemical | Replace materials and | DOH materials used and in | ||||||||
| of materials | fixtures with DOH | place | |||||||||
| and fixtures | approved materials | ||||||||||
| leading to | 3 | 4 | 12 | 1 | 5 | 5 | |||||
| leaching of | Low | ||||||||||
| toxic materials | |||||||||||
| such as lead | |||||||||||
| Low water | Microbiolo | Adjust heater | Not frequently monitored | ||||||
|---|---|---|---|---|---|---|---|---|---|
| temperatures | gical | temperature | |||||||
| in hot-water | |||||||||
| storage vessels | Ensure sufficient | ||||||||
| supports | energy delivery | ||||||||
| microbial | |||||||||
| growth | Check heater | ||||||||
| thermostat | |||||||||
| 2 | 5 | 10 | 2 | 4 | 8 | ||||
| Maintain temperatures | Medium | ||||||||
| above 50 o C in | |||||||||
| distribution system | |||||||||
| Maintain temperatures | |||||||||
| above 60 o C in | |||||||||
| storage vessels | |||||||||
| Process | HAZARDOUS | TYPE OF | RAW RISK | EXISTING CONTROL | VALIDATION OF CONTROL | RESIDUAL RISK | |||
|---|---|---|---|---|---|---|---|---|---|
| Steps | EVENT | HAZARD | MEASURES | MEASURES | |||||
| (Component s of Water System) |
| Hot water piping system (Note: may or may not be present) | Poor temperature control supports microbial growth such as Legionella | Microbiolo gical | 3 | 5 | 15 | Install temperature reduction devices as close as possible to PoU Insulate system Avoid stagnation and low flow areas Ensure sufficient capacity for maximum flows Insulate cold and hot water pipes Keep systems physically separate | Insulation in place and properly separated | 1 | 5 | 5 Low |
|---|---|---|---|---|---|---|---|---|---|---|
| Insufficient | Chemical | Assign staff to perform | No definite staff assigned | 16 | ||||||
| maintenance of the pipelines | 4 | 4 | 16 | maintenance | 4 | 4 | Very High |
| Process Steps | HAZARDOUS EVENT | TYPE OF HAZARD | RAW RISK | EXISTING CONTROL MEASURES | VALIDATION OF CONTROL MEASURES | RESIDUAL RISK | |||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| (Component s of Water System) | |||||||||||
| resulting to scaling and corrosion | |||||||||||
| Deterioration of pipes leading to leaching of lead to water supply | Chemical | 1 | 4 | 4 | Replace pipes with DOH approve materials | DOH approved materials in place | 1 | 4 | 4 Low | ||
| Stagnation and low water flows (hot system) | Microbiolo gical | 4 | 5 | 20 | Avoid overdesigning capacities Isolate areas that are not used for extended periods | Water flow design appropriately constructed | 1 | 5 | 5 Low |
| Remove dead legs and minimize length of branch pipes | ||||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| Cold water piping system | Insufficient maintenance of the | Chemical | 4 | 4 | 16 | Assign staff to perform maintenance | No definite staff assigned for maintenance | 4 | 4 | 16 Very |
| (Note: may or may not | pipelines resulting to | Replace pipes with DOH approve | High |
| Process | HAZARDOUS | TYPE OF | RAW RISK | EXISTING CONTROL | VALIDATION OF CONTROL | RESIDUAL RISK | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Steps | EVENT | HAZARD | MEASURES | MEASURES | |||||||||
| (Component | |||||||||||||
| s of Water | |||||||||||||
| System) | |||||||||||||
| be present) | scaling and | materials | |||||||||||
| corrosion |
| Deterioration of pipes leading to leaching of lead to water supply | Chemical | 1 | 4 | 4 | Replace pipes with DOH approve materials | Pipes replace with DOH approved materials | 1 | 4 | 4 Low |
|---|---|---|---|---|---|---|---|---|---|
| Stagnation and low water flows (cold system) | Microbiolo gical | 4 | 5 | 20 | Avoid overdesigning capacities Remove the causes of fluctuation (e.g. high peak water demand, fire drills) Prevent negative pressures Flush systems that are not used frequently Isolate areas that are not used for extended | Water flow design appropriately constructed | 1 | 5 | 5 Low |
| Process | RAW RISK | RESIDUAL RISK | ||
|---|---|---|---|---|
| Steps (Component s of Water System) | HAZARDOUS EVENT | TYPE OF HAZARD | EXISTING CONTROL MEASURES | VALIDATION OF CONTROL MEASURES | ||||||
|---|---|---|---|---|---|---|---|---|---|---|
| periods Remove dead legs and minimize length of branch pipes | ||||||||||
| Poor temperature control supports microbial growth | Microbiolo gical | 4 | 5 | 20 | Insulate cold and hot water pipes Keep systems physically separate | Insulation in place and properly separated | 1 | 5 | 5 Low | |
| Equipment for point of use (PoU) | Poor maintenance of PoU equipment supports microbial growth and/or corrosion | Microbiolo gical | 4 | 5 | 20 | Assign staff to perform maintenance | No definite staff assigned for maintenance | 4 | 4 | 16 Very High |
| Inadequate backflow prevention on PoU | Chemical | 3 | 5 | 15 | Minimize connections and provide backflow prevention where required | Connections minimized and adequately controlled | 1 | 5 | 5 Low |
|---|---|---|---|---|---|---|---|---|---|
| equipment |
| Process | HAZARDOUS EVENT | TYPE OF HAZARD | RAW RISK | EXISTING CONTROL MEASURES | VALIDATION OF CONTROL MEASURES | RESIDUAL RISK | |||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| Steps (Component s of Water System) | |||||||||||
| Aerosol contamination on sewerage or septic systems | Microbiolo gical | 3 | 5 | 15 | Install water traps in sewage lines Filter double traps in high-risk environment Prevent contamination from septic tanks | Water traps adequately and properly installed | 1 | 5 | 5 Low | ||
| Improper connection of PoU devices and equipment | Microbiolo gical | 3 | 5 | 15 | Ensure proper establishment of connection for all | Connection of POU devices secured | 1 | 5 | 5 Low |
| POU equipment and devices | ||||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| Water treatment systems at PoU | Incorrect installation of water treatment systems | Chemical | 1 | 5 | 5 | Choose quality materials Follow local or international choice and construction rules Use active protection of pipes (e.g. sacrificial anodes, anticorrosion | Correct and recommended materials constituted the designed structure | 1 | 5 | 5 Low |
| Process | HAZARDOUS | TYPE OF | RAW RISK | EXISTING CONTROL | VALIDATION OF CONTROL | RESIDUAL RISK | |||
|---|---|---|---|---|---|---|---|---|---|
| Steps | EVENT | HAZARD | MEASURES | MEASURES | |||||
| (Component | |||||||||
| s of Water | |||||||||
| System) | |||||||||
| products) | |||||||||
| Insufficient maintenance | Chemical Microbiolo | Assign staff to perform maintenance | No definite assigned staff for maintenance | 4 | 5 | 20 | |||
|---|---|---|---|---|---|---|---|---|---|
| and | gical | 4 | 5 | 20 | Very | ||||
| monitoring of | High | ||||||||
| the equipment | |||||||||
| Excessive | Chemicals | Ensure dosing | Required doses administered | 1 | 5 | 5 | |||
| doses of | equipment and | correctly | |||||||
| treatment | storages are | Low | |||||||
| chemicals e.g. | maintained | ||||||||
| chlorine | |||||||||
| Avoid overdesigning | |||||||||
| 3 | 4 | 12 | chemical storage | ||||||
| capacities | |||||||||
| Minimize | |||||||||
| crossconnections and | |||||||||
| provide backflow | |||||||||
| prevention where | |||||||||
| required |
5. Improve/Upgrade Plan
Devising an improvement or upgrade plan is important to ensure that the quality of the water in the system is a priority and always taken into consideration. It involves review of existing operating procedures for activities, implementation of new operating procedures or infrastructure changes to upgrade existing control measures. Example of an improvement plan is formulation of program to control cross connection problems e.g. contamination of water supply.
The initial step in the identification of an improvement and/or upgrade is to consider the following factors: (a) cost; (b) practicality; (c) timelines; and (d) likelihood of success. If there is more than one identified need for improvement, priorities should be selected considering the level of unaddressed risk. The plan should also establish a schedule of short, medium, and long term activities. Moreover, it is crucial to put in place a mechanism for monitoring and reporting on implementation of the plan.
Tool. 5.1. Sample Improvement/Upgrade Plan
| Process Steps (Components of Water System) | ACTION | IDENTIFIED SPECIFIC IMPROVEMENT PLAN | RESPONSIBLE UNIT/PERSON | COST | FUNDING SOURCE | DUE | STATUS |
|---|---|---|---|---|---|---|---|
| Storage Tank | Implement measures to replace rusted steel storage tank | Replacement of storage tank from steel tank to stainless steel tank | Engineering Unit | P 50,000 | 1 st qtr 2017 | On-going | |
| Inadequate maintenance and monitoring of equipment due to insufficient staff | Additional staff for monitoring and maintenance of equipment | Hiring and training of additional staffs for monitoring and performance of maintenance (operational and preventive) of equipment | Administrative Unit | P 8,000 per month x 5-8 Staffs | 1 st qtr of 2017 | On-going |
6. Define Monitoring of the Control Measures
Proper documentation and monitoring of the processes involved is critical on the implementation of WSP. The procedures are established to oversee existing deviations and facilitate immediate interventions. The monitoring scheme includes the following questions which should be thoroughly assessed and evaluated: (1) What will be monitored; (2) How it will be monitored; (3) Where it will be monitored; (4) When and how often will it be monitored; (5) Who will do the monitoring; (6) What corrective action should be done.
In conducting operational monitoring, a planned and structured approach should be in place to appropriately manage any deviations that might occur during operations. It might include simple field measurements such as monitoring of the disinfectant residuals, turbidity, color, temperature, odor and other physical characteristics. The principle of having the simple measurements rather than the complex laboratory based evaluation is that a quick assessment on possible deviations can help initiate immediate response for corrective action. Corrective actions are actions which need to be taken when the results of monitoring at a control point indicate to a loss of control.
In addition, definite critical limits should also be in place in order for the assessor to easily decide if a certain measure has exceeded or lose the normal recommended value for it. Most of the critical limits are based on the limits defined in the latest PNSDW though some may be established by the HCF.
The table below shows a sample template of what are supposed to be included in the formulation of a monitoring scheme/structure.
Tool 6.1. Monitoring Requirements and Corrective Action
| Process Steps (Component s of Water System) | Critical Limits | What to Monitor | Where to Monitor | How | Frequency (When) | Who | Corrective Action |
|---|---|---|---|---|---|---|---|
| Source | PNSDW permissible limit | Microbial/ bacteriological water quality | Pumping Station | Microbial/ bacteriological tests | Monthly | Pump operator/ DOH accredited laboratory | Chlorination Investigate possible source |
| Treatment | Residual chlorine must be within 0.3ppm - 1.5ppm | Residual chloride monitoring | Source, midpoint and farthest point of the distribution network | Residual chlorine monitoring test kit | Daily | Pump Operator | Adjust chlorine dosage and retesting |
| Storage | Annual cleaning of reservoir / storage tanks | Cleaning of reservoir and storage facilities | Reservoir and storage tanks | Visual Inspection | Annually | Pump Operator | Regular cleaning |
| Distribution | 0.4 ppm | Residual chlorine | Tap | Test kit | Daily | Maintenance | Adjustment |
|---|---|---|---|---|---|---|---|
| testing | of chlorine | ||||||
| dosage Re | |||||||
| compute | |||||||
| chlorine | |||||||
| demand |
7. Verify the Effectiveness of the WSP
Verification provides reassurance that the WSP is effective. Moreover, this step confirms that the support programs are implemented and the hazard analysis is updated. It also serves as evidence that the hazard levels are within the acceptable levels. Results of the verification procedures should be communicated among the team through meetings.
The verification procedure of the HCF water supply system includes three components; water quality testing3 , water safety plan internal auditing and user satisfaction. For the water quality testing, water samples are tested based from the latest PNSDW. On the other hand, WSP internal audits are necessary in preparation for an external audit by the regulatory agency or by an independent auditor. Internal audit shall cover the following items: (a) operational monitoring, (b) improvement plans, (c) compliance monitoring, (d) management plans, (e) supporting programmes, (f) responsible team and (g) frequency of internal audit. In addition, user's satisfaction may also be conducted to determine any feedback from the employees, patients, watchers, and visitors. The following shall be defined for user's satisfaction: (a) responsible unit, (b) frequency of monitoring and (c) methodology of getting information from user.
Below are sample templates on specific verification activities that may be conducted by the WSP team.
3 If source is owned by HCF, the HCF will be responsible for water quality testing of its water supply system. If source is from water service provider, the HCF will be responsible for testing from point of entry/after the meter to entire water supply system in the HCF premises.
8. Develop Management Procedures
Development of Standard Operating Procedures (SOPs) is crucial in order to provide the staffs and employees with guidelines for the performance of their day-to-day duties and responsibilities. There are different conditions from which procedures need to be established for the continuous operation of the water supply in the HCF namely for normal condition, incidents and emergency conditions.
For normal conditions, this involves the regular tasks and how these are conducted for the water supply system. Among some of the tasks which need procedures include maintenance of storage tanks, preparation of disinfectants, water sampling, etc.
Incident conditions are instances wherein the activity is not conducted regularly but occur immediately as part of the facilities' operation and will require quick response from the facility owner. Examples of this which will need establishment of procedures are repair of burst pipes and equipment malfunction.
Lastly, there are the emergency conditions which may be due to force majeure (e.g. disease outbreak, earthquake, flood, power outage, etc.) or man-made (e.g. sabotage, terrorist attack). In most instances, the procedures for these conditions have been established by various agencies (e.g. NDRRMC, DOH, Red Cross, etc.) and will just be adopted for sitespecific application.
Among the key items which need to be included when establishing and reviewing any of the standard procedures are the following:
- Availability
- Relation to defined control measure/s and significant risks
- Accessibility of procedure
- Responsible unit
Also, it is important that for every procedure, the communication plan is included to ensure that the procedure is made known to the responsible units and its intended stakeholders.
Tool 8.1. Sample Templates for Management Procedures
| Required SOPs | Available Yes/No | Timeline for completion (if not yet available) | Responsible Unit | Location of the document |
|---|---|---|---|---|
| A. Normal Condition | ||||
| 1. Water source or point of entry | Laboratory/ | |||
| 1.1 Water sampling | Yes | Med Tech | Cabinet 1.2 | |
| 2. Water treatment | No | Maintenance | ||
| 2.1 Mixing chlorine | rd Quarter, 2016 3 | - | ||
| 3. Storage | Maintenance | Cabinet 2.5 | ||
| 3.1 Cleaning storage tank | Yes | |||
| 4. Distribution lines | Yes | Maintenance/ | Cabinet 3.1 | |
| 4.1 Repair of leak | Plumber | |||
| B. Incidents/Corrective actions | ||||
| 1. Source | No | 3rd quarter, 2016 | To be identified | - |
| 2. Treatment | No | |||
| 3. Storage | No | |||
| 4. Distribution | No | |||
| C . Emergency | ||||
| 1. Disease outbreak | Yes | Admin Office | Cabinet 4.4 |
9. Develop Support Programs
Support programs are activities that assist in the implementation of WSPs and essential to ensure the quality of water. These programs contribute to the overall safety of the hospital particularly on providing safe drinking-water for the consumers. Moreover, supporting programs provide knowledge and skills among staffs, operators, employees and users of the HCF, and commitment to the WSP approach and capacity to manage systems to deliver safe water. The key action for this step is for the WSP Coordinator and the team to identify the needed supporting programs for implementing the WSP approach, then reviews and if necessary revise the existing programs and develop additional supporting programs to address the identified gaps.
Examples of training may cover the following:
-
- Hygienic use of water supplies
-
- Hygienic practices in maintaining water supplies, water-using devices and equipment
-
- Hygienic practices in performing repairs
-
- Calibration of monitoring equipment
-
- Instructions on access to equipment and modification of systems
-
- Training requirement for maintenance staff
Tool 9.1. Sample Template for Developing a Support Program
| Activities | Justification | Objective/ Targets | Schedule | Budget | Responsible |
|---|---|---|---|---|---|
| 7 ICTI VICES | Objective, rangets | (2016) | Duager | Unit | |
| Training/ |
| Quarterly | P 10,000 | Admin | |
| Orientation | • WSP | Office / HR | |||
| members | Unit | ||||
| Calibration of | • Measuring | Annual | P 20,000 | Admin | |
| equipment | devices | Office/ | |||
| O&M | ||||
| Operation | • Equipment | Monthly | P 50,000 | Admin | |
| and |
| Office/ | |||
| maintenance | • Kits | O&M | |||
|
10. Conduct WSP Systems Review
One of the immediate responsibilities of the WSP coordinator is the periodic review of the WSP. Results based from the verification process of the WSP document should be thoroughly analyzed to apply accurate decisions on whether to change the existing WSP or not. Ideally, WSPs are reviewed ideally every three (3) to five (5) years and in cases where changes to the water system like repair of existing equipment or process is applied, change in the source of water, and in cases of emergencies, incident or near miss. The WSP system should also be critically reassessed for possible action to include in the improvement/upgrade plan section of the document.
Tool 10.1. Sample Template in Implementing a WSP Systems Review
| Activity | Purpose or Reason | Schedule | Responsible unit |
|---|---|---|---|
| Review of WSP | - To evaluate level of risks from operational monitoring results, new changes in the water supply system and HCF organization, lessons learned from incidents, results of audit - To provide recommendations on whether to | Quarterly | WSP Team |
| retain, revise or update WSP |
11. Revise WSP Following an Incident
The implementation of a comprehensive WSP will help greatly on the reduction of the risk on the occurrence of waterborne diseases and/or other related complaints. Existence of a WSP does not give the assurance that incidents may not occur hence, the need for WSP review is vital after an emergency, confirmed incidents or near misses or for unforeseen events. The reassessment or investigation of the incident provide opportunities for improvement and therefore the team shall create new protocols or revised the existing WSP after the conduct of the review and investigation.
Tool 11.1 List of questions to ask following an emergency, incident or near miss ✓
What was the cause of the problem?
- ✓ Was the cause a hazard already identified in the WSP hazard & risk assessment?
- ✓ How was the problem first identified or recognized?
- ✓ What were the most essential actions required and were they carried out?
- ✓ If, relevant, was appropriate and timely action taken to warn consumers and protect their health?
- ✓ What communication problems arose and how were they addressed?
- ✓ What were the immediate and long-term consequences of the emergency?
- ✓ How can risk assessment / procedures / training / communications be improved?
- ✓ How well did the emergency response plan function?
Tool 11.2 Following an incident, emergency or near miss the following checklist may be useful to revise the WSP
- ✓ Accountabilities of WSP and key personnel are updated
- ✓ Review whether the management procedures were appropriate for the incident and if not, revise accordingly
- ✓ Standard operating procedures and required equipment are readily available and relevant
- ✓ Does the risk assessment need revise?
- ✓ Do procedures / training / communications need improving?
- ✓ Has the problem shown the need for an improvement of program?
| Activity | Purpose or Reason | Schedule | Responsible unit |
|---|---|---|---|
| Revision of | To incorporate significant results | Normal condition: | WSP Team |
| WSP | of risk analysis derived from operational monitoring, new changes in the water supply system and HCF organization, lessons learned from incidents, and audit recommendations | Every second quarter of the year Following an incident: anytime |
Annex A: Sample Templates for Steps 1-11
INTRODUCTION
Key Points to consider in making the Introduction, but should not be limited to the following:
| Details | |||
|---|---|---|---|
| 1. | About the HCF | ||
| a. | Name of HCF | ||
| b. | Location or address | ||
| c. | Type of HCF (see DOH Category) | ||
| d. | Year established | ||
| e. | Bed capacity | ||
| f. | Number of staff (regular, contractual) | ||
| g. | Floor Area and Lot Area | ||
| h. | Number of Floors | ||
| 2. Water Sources (all which is applicable) | |||
| a. | Water district | ||
| b. | LGU-managed | ||
| c. | Community-managed | ||
| d. | HCF-owned deep well | ||
| e. | Privately-managed | ||
| 3. | Waste Management System |
| a. | Wastewater | ||
|---|---|---|---|
| b. | Solid Waste | ||
| c. | Health Care Waste | ||
| 4. | Power supply | ||
| a. | Two-phase | ||
| b. | Three-phase | ||
| c. | Stand-by Generator (include kVA) |
I. WSP Team WATER SAFETY PLAN TEAM STRUCTURE

WATER SAFETY PLAN TEAM
| Name | Organization / Department | Job Title / WSP Role | Responsibility | Telephone No. |
|---|---|---|---|---|
Identify the stakeholders who might contribute to the water quality which may include the following:
-
- Water supply providers
-
- Waste management service providers
-
- Suppliers
-
- LGU (e.g. MHO/CHO, MENRO/CENRO, MEO/CEO, etc.)
-
- Concerned national agencies (e.g. DOH, DENR, NWRB, etc.)
-
- Nearby community
-
- Water Users in the HCF
-
- Others
II. WATER SUPPLY SYSTEM and PROCESS DESCRIPTION
Key Points to consider in making the Water Supply System and Process Description, but should not be limited to the following:
| Details to be provided (if applicable) | |||
|---|---|---|---|
| Water Source | d) Water supply provider (average volume billed/consumed per | ||
| year, latest water quality results – Point of Entry) | |||
| e) Deep-well information (depth, diameter, year constructed, | |||
| casing material, water quality) | |||
| f) Pumping equipment (capacity, horsepower rating, year | |||
| installed) | |||
| Water Treatment | h) Type of treatment (filtration, sedimentation, coagulation, | ||
| chlorination, reverse osmosis, ion exchange, UV, | |||
| ozonation, etc.) | |||
| i) Chemicals used (volume per month, | |||
| j) Year installed per treatment facility | |||
| k) Contaminants being removed per treatment facility | |||
| l) Treatment facility location in the HCF | |||
| m) Capacity of the water treatment facility | |||
| n) Volume of water being treated per treatment facility | |||
| Storage | h) Type of storage (ground, elevated) | ||
| i) Technology applied (fill and draw, floating, pneumatic) | |||
| j) Height of storage (for elevated tank) | |||
| k) Description of storage tank location | |||
| l) Number, Volume and shape of storage tank | |||
| m) Material composition of storage tank | |||
| n) Frequency of cleaning | |||
| Distribution | d) Diameter, Length of pipe network | ||
| e) Material used | |||
| f) Water quality from the tap | |||
(NOTE: Mention water quality targets if the source is HCF-owned water system. For supplied by water service provider, request a copy of their water quality targets.)
(Sample template only)
| Provide Average number per day | ||||||
|---|---|---|---|---|---|---|
| Users | a) Patients (admitted and out-patient) | |||||
| b) Watchers | ||||||
| c) Guest / Visitor | ||||||
| d) Employees (regular, contractual) | ||||||
| State which of the uses are applicable | ||||||
| Uses | a) General use (drinking, cooking, flushing, washing, bathing, | |||||
| gardening, fire protection, etc.) | ||||||
| b) Special use (dialysis, autoclaving, etc.) |
TEMPLATE: FLOW DIAGRAM
| Process Step | Symbol | Org./ Dept. Responsible |
|---|---|---|
Legend:
| Process step |
|---|
| Chemical process |
| Storage / Reservoir / Catchment |
| Transport step |
| Consumer |
| "As Needed" basis process step |
| Connector |
HAZARD IDENTIFICATION AND RISK ASSESSMENT
TEMPLATE: HAZARD IDENTIFICATION AND RISK ASSESSMENT (identify as many hazardous events, per process step, as possible)
| PROCESS | HAZARDOUS | TYPE OF | LIKELIHOOD | SEVERITY | RAW RISK | RAW RISK |
|---|---|---|---|---|---|---|
| STEP | EVENT | HAZARD | LIKELIHOOD | SEVERILI | SCORE | RATING |
DETERMINE AND VALIDATE CONTROL MEASURES, REASSESS AND PRIORITIZE THE RISKS
TEMPLATE: Determine and Validate Control Measures, Reassess and Prioritize the Risk (all hazardous events in Module 3 must be reflected here in Module 4)
| RAW RISK | RESIDUAL RISK | ||||||
|---|---|---|---|---|---|---|---|
| PROCESS STEP | HAZARDOUS EVENT | TYPE OF HAZARD | EXISTING CONTROL MEASURES | VALIDATION OF CONTROL MEASURES | |||
IMPROVEMENT / UPGRADE PLAN
TEMPLATE: IMPROVEMENT / UPGRADE PLAN
(NOTE: Establish improvement plans for those hazardous events with significant residual risk ratings only)
| PROCESS | ACTION | IDENTIFIED | RESPONSIBLE | COST | FUNDING | DUE | STATUS |
|---|---|---|---|---|---|---|---|
| STEP | SPECIFIC | UNIT/PERSON | SOURCE | ||||
| IMPROVEMENT | |||||||
| PLAN | |||||||
MONITORING OF THE CONTROL MEASURES (OPERATIONAL MONITORING)
TEMPLATE: MONITORING OF THE CONTROL MEASURES
| Process Step | Critical Limits | What to Monitor | Where to Monitor | How | Frequency (When) | Who | Corrective Action |
|---|---|---|---|---|---|---|---|
VII. VERIFICATION
TEMPLATES: VERIFICATION
| Verification Activity | Location of Activity | Type of Activity | Frequency of Activity | Analyst | Recipient of Analysis | Action on Failing Result | Recipient of Result (3 rd party) |
|---|---|---|---|---|---|---|---|
| 1. Water Quality Parameters | |||||||
| 2. Microbiological | |||||||
| 3. Arsenic | |||||||
| 4. Cadmium | |||||||
| 5. Lead | |||||||
| 6. Nitrate | |||||||
| 7. Benzene | |||||||
| 8. Color | |||||||
| 9. Turbidity | |||||||
| 10. Iron | |||||||
| 11. pH | |||||||
| 12. Manganese | |||||||
| 13. Chloride | |||||||
| 14. Sulfate | |||||||
| 15. Total Dissolved Solids (TDS) |
| Type of Audit | Scope | Schedule | Who will conduct? | Documents to be checked |
|---|---|---|---|---|
| Internal | ||||
| Audit |
| Methodology for determining user satisfaction | Frequency of feedback | Responsible unit | Records generated |
|---|---|---|---|
| Survey | |||
| Complaints |
MANAGEMENT PROCEDURES TEMPLATE: MANAGEMENT PROCEDURES
| Required SOPs | Available Yes/No | Timeline for completion (if not yet available) | Responsible Unit | Location of the document |
|---|---|---|---|---|
| A. Normal Condition | ||||
| B. Incidents/Corrective actions | ||||
| C. Emergency | ||||
SUPPORTING PROGRAMS
TEMPLATE: SUPPORTING PROGRAMS
| Objective/ Targets | Schedule | Budget | Responsible Unit |
|---|---|---|---|
REVIEW AND AUDIT TEMPLATE: REVIEW AND AUDIT
| Activity | Purpose or Reason | Schedule | Responsible unit |
|---|---|---|---|
VI. REVISE THE WSP FOLLOWING AN INCIDENT
TEMPLATE: REVISION OF WSP
| Activity | Purpose or Reason | Schedule | Responsible unit |
|---|---|---|---|