Population and Public Health Division, Ministry of Health and Long-Term Care
Effective: January 1, 2018 or upon date of release
The Ontario Public Health Standards: Requirements for Programs, Services, and Accountability (Standards) are published by the Minister of Health and Long-Term Care under the authority of section 7 of the Health Protection and Promotion Act (HPPA) to specify the mandatory health programs and services provided by boards of health. 1,2 The Standards identify the minimum expectations for public health programs and services. Boards of health are accountable for implementing the Standards including the protocols and guidelines that are referenced in the Standards. Guidelines are program and topic-specific documents which provide direction on how boards of health shall approach specific requirement(s) identified within the Standards.
The Ministry of Health and Long-Term Care (the ministry) oversees the Small Drinking Water Systems Regulation under the Health Protection and Promotion Act (HPPA). 2,3 This regulation sets out the requirements that must be followed by the owners and operators of each small drinking water system (SDWS), such as minimum water testing for Escherichia coli and total coliforms. 3 Owners and operators of SDWS are responsible for keeping drinking water safe and meeting their regulatory requirements.
Under the SDWS Regulation, public health inspectors (PHIs) are responsible for conducting site-specific risk assessments of every SDWS in the province. 3 Based on the assessment, PHIs determine what owners and operators must do to keep their drinking water safe and issue a directive for each system, which may include requirements such as water testing, treatment and training. This reflects the use of a customized approach for each SDWS depending on the level of risk, rather than a set of 'one-size-fits-all' requirements.
The purpose of this document is to provide guidance to boards of health and, in particular, to PHIs, in developing and issuing directives to owners of SDWS in accordance with section 7 of the SDWS Regulation. 3 The site-specific requirements outlined in the directives are in addition to the minimum requirements specified in the SDWS Regulation under the HPPA. 2,3
This document is not intended to provide legal advice or to be a substitute for the professional judgment of public health inspectors. Public health inspectors should consult with legal counsel as appropriate when issuing directives to owners of Small Drinking Water Systems.
This section identifies the standards and requirements to which this guideline relates.
Requirement 1: The board of health shall:
Requirement 3: The board of health shall ensure the availability of education and training for owners/operators of small drinking water systems and recreational water facilities in accordance with the Operational Approaches for Recreational Water Guideline, 2018 (or as current); the Recreational Water Protocol, 2018 (or as current); the Safe Drinking Water and Fluoride Monitoring Protocol, 2018 (or as current); and the Small Drinking Water Systems Risk Assessment Guideline, 2018 (or as current).
Requirement 6: The board of health shall inform the public about unsafe drinking water conditions and provide the necessary information to respond appropriately in accordance with the Safe Drinking Water and Fluoride Monitoring Protocol, 2018 (or as current) and the Small Drinking Water Systems Risk Assessment Guideline, 2018 (or as current).
Requirement 8: The board of health shall ensure 24/7 availability to receive reports of and respond to:
The public health approach to protecting drinking water is based on assessing and identifying potential risks associated with a SDWS. Following a risk assessment, basic requirements are set to assist the owner/operator in adequately maintaining and supervising the provision of drinking water. As described in the Safe Drinking Water and Fluoride Monitoring Protocol, 2018 (or as current) , 4 the activities which must be conducted as part of the risk assessment process of a small drinking water system include: Conduct a site-specific visit of the small drinking water system;
As part of the risk assessment process, other activities may include:
The board of health shall ensure that the following approach is used in the assessment of Small Drinking Water Systems. This includes:
Directives must include, at minimum, the following sections:
The directive may be organized in the following format:
The Risk Categorization (RCat) tool was developed by the ministry specifically for sitespecific risk assessments of small drinking water systems. The tool is intended to assist PHIs in conducting on-site risk assessments for the purposes of determining whether SDWS are operating in a manner which provides safe water. The RCat tool is comprised of a series of questions which identify the security of the water source and system, and results in risk ratings of the source of water, treatment system and distribution system. It has been designed to consider all parts of the SDWS from source water to consumer, using a multi-barrier approach to protecting drinking water.
The ratings are used to assign one of following risk categories for the system:
The requirements for water treatment are based on the findings of the risk assessment and inspection process, the possibility of contamination in the source water and a history of water test results. This section describes the water treatment actions which are required in each situation to ensure the safety of the drinking water supply.
For small drinking water systems that provide drinking water that is derived from a secure ground water source, and where the water sampling and testing results indicate a condition of 0 total coliforms per 100 millilitres and no Escherichia coli , for multiple samples, treatment may not be required.
For small drinking water systems that use a ground water source that may contain bacteria and viruses but is not likely to contain cysts or oocysts, the necessary actions are to:
For small drinking water systems that use a ground water source that may contain bacteria, viruses, cysts or oocysts and surface water is suspected of entering the well, the necessary actions are to:
For small drinking water systems that use a surface water source that may contain bacteria, viruses, cysts or oocysts, the necessary actions are to:
If applicable, the owner/operator may also have to:
Where point of entry or point of use treatment devices are used in addition to treatment outlined in section 2.2 to 2.4, the necessary actions are to:
For small drinking water systems that use other sources (e.g., hauled water), treatment requirements are to be used in accordance with sections 2.1 to 2.4.
For small drinking water systems that use NSF/ANSI 55 Class A UV Systems that have a built-in fail-safe design that terminates the discharge of water if the system is not performing to the NSF standard, the frequency of testing required as per Table 2 may be reduced by up to 50%. *
This section will assist in determining the required scheduling of sampling and testing for bacteria (total coliforms and Escherichia coli ) to be included in a directive where the entire system is not posted. In determining the schedule and frequency of sampling, the following factors shall considered:
Where there is a new small drinking water system or where a system has less than one year's history of sampling and testing, it is necessary to take samples at the minimum rate of one sample per month or at a frequency greater than one sample per month as indicated in Table 2 and Table 3.
Table 2: Recommended frequency of bacterial sampling for Escherichia coli and total coliforms for all small drinking water systems without testing history
| Risk Category | Treatment Provided | Frequency of sampling water after being treated or otherwise directed for consumption |
|---|---|---|
| Low | No | One sample every three months |
| Low | Yes | One sample every three months |
| Moderate | No | One sample monthly |
| Moderate | Yes | One sample every two months |
| High | No | One sample every week |
| High | Yes | One sample every two weeks |
Table 3 is to be used in addition to Table 2 to determine the required frequency of sampling for small drinking water systems with distribution systems.
Table 3: Recommended sampling frequency for systems with distribution systems, by level of risk
| Applies to | Secondary Treatment | Number and Frequency of Sampling | Number and Frequency of Sampling | Number and Frequency of Sampling |
|---|---|---|---|---|
| Applies to | Secondary Treatment | Low Risk | Moderate Risk | High Risk |
| 2-10 Connections* | Yes or no | One sample monthly | One sample monthly | One sample monthly |
| 11-100 Connections | Yes | One sample monthly | One sample monthly | One sample every two weeks |
| ≥ 101 Connections | Yes | One sample from the treated water supply and one sample for every 100 connections or part thereof from the distribution system monthly | One sample from the treated water supply and one sample for every 100 connections or part thereof from the distribution system every two weeks | One sample from the treated water supply and one sample for every 100 connections or part thereof from the distribution system every week |
Samples are required to be collected at locations where the sampling would be representative of the water quality of the majority of the system.
Unless the PHI provides otherwise, for a system that uses point of entry treatment units and has more than one unit, samples are to be taken from locations downstream of the point of entry treatment units on a rotational basis. The rotation is to be set so that after a sample is taken from a location downstream of a particular point of entry treatment unit, another sample is not taken from that same unit, until samples have been taken from locations downstream of all the other point of entry treatment units.
For any water supply where a chemical or radiological agent is suspected, further assessment of the potential sources of the contaminant and additional testing for the suspected chemical or radiological agent is required.
However, where testing results indicate that the level of chemical or radiological agent is below the limits in the Ontario Drinking Water Quality Standards or where the contaminants are naturally occurring and not expected to increase, no further sampling is required of the small drinking water system. Appropriate notification of users of the conditions of the drinking water must be provided.
Where contaminants are identified and have the potential to fluctuate in a manner that may cause an increased risk to the health of the users, a schedule for regular sampling and testing is required. This information provides surveillance data to monitor any potential increased risk to the users of the water supply.
Where filtration is to be used on a system, turbidity is to be tested at a frequency in accordance with the risk level and configuration of the system.
Where primary or secondary disinfection is to be used, the chlorine residual is to be tested at a frequency of once every 24 hours or adjusted in accordance with the risk level and configuration of the system.
Subsection 7 (6) of the SDWS Regulation provides that directives may require the posting and maintenance of warning signs. 3 Direction may be given which requires the placement of a sign that states: "Public Notice: Do not drink this water" when posting the entire small drinking water system or specific service connections. The owner/operator should be informed that they are expected to conduct routine checks to confirm signs continue to be posted, in a good state of repair and they are easily readable.
Subsection 10 (2) of the SDWS Regulation requires that records of maintenance and operational tests be made available to the PHI on request. 3 The PHI may request additional records as deemed necessary.
Training for operators is important because it ensures they are aware of their responsibilities under the regulations and are able to maintain the supply of safe water to users.
At a minimum, training must include awareness of the normal operation of the system in order to respond appropriately to adverse test results or other conditions that may affect the safety of the drinking water. Table 4 describes the minimum recommendations for core competencies and training requirements for operators of different types of systems.
Table 4: Operator Training in Core Competencies
| Knowledge Areas | System Source and Treatment Type | System Source and Treatment Type | System Source and Treatment Type | System Source and Treatment Type | System Source and Treatment Type |
|---|---|---|---|---|---|
| Knowledge Areas | Posted System (Signage) | Secure Groundwater (no treatment required) | Ground Water and/or Surface Water (UV light, filtration* and chemical disinfection) | Distribution System (secondary disinfection) | Other Sources (e.g. water haulage vehicle) |
| Knowledge Areas | Recommended Courses (based on knowledge areas)** | Recommended Courses (based on knowledge areas)** | Recommended Courses (based on knowledge areas)** | Recommended Courses (based on knowledge areas)** | Recommended Courses (based on knowledge areas)** |
| Knowledge Areas | Educational Materials Only | Intro Course for 319 (online or half day) | Basics for 319 or equivalent | Advanced for 319 or equivalent | Educational Materials Only |
| Knowledge of general protection requirements (notification of users). | | | |||
| Knowledge of ground water basics, well basics, best management practices. | | ||||
| Knowledge of general protection requirements (water source, source water protection issues, potential of system failure, impacts of system failure, notification of users). | | |
| Knowledge Areas | System Source and Treatment Type | System Source and Treatment Type | System Source and Treatment Type | System Source and Treatment Type | System Source and Treatment Type |
|---|---|---|---|---|---|
| Knowledge Areas | Posted System (Signage) | Secure Groundwater (no treatment required) | Ground Water and/or Surface Water (UV light, filtration* and chemical disinfection) | Distribution System (secondary disinfection) | Other Sources (e.g. water haulage vehicle) |
| Knowledge Areas | Recommended Courses (based on knowledge areas)** | Recommended Courses (based on knowledge areas)** | Recommended Courses (based on knowledge areas)** | Recommended Courses (based on knowledge areas)** | Recommended Courses (based on knowledge areas)** |
| Knowledge Areas | Educational Materials Only | Intro Course for 319 (online or half day) | Basics for 319 or equivalent | Advanced for 319 or equivalent | Educational Materials Only |
| Knowledge of proper sampling techniques and lab submission process (why the sample is taken, where it is to be taken, when and who to call if an adverse result/observation happens, what the sample results mean). | | | | ||
| Ability to operate and understand why and how the treatment equipment works and what to do if the treatment fails. | | | |||
| Ability to maintain the operation of the equipment to, at minimum, manufacturer's recommended instructions. | Required if the system is not supported by a service company with appropriately trained staff | Required if the system is not supported by a service company with appropriately trained staff | |||
| Knowledge of distribution systems (how to sample, maintenance, and manage what to do if a distribution system breaks). | |
http://www.health.gov.on.ca/en/pro/programs/publichealth/oph_standards/protoc olsguidelines.aspx