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NSW Health Response Protocol: for the management of physical and chemical quality

This protocol is derived from the Australian Drinking Water Guidelines, 2004 (the
Guidelines) to be used by Public Health Units (PHU) and water utilities to guide their joint
response following the detection of physical and chemical water characteristics that exceed
the Guidelines.
Under Section 10D of the Public Health Act 1991, the Chief Health Officer has the power to
issue advice, for the benefit of the public, concerning the safety of available drinking water
and any possible risks to health involved in the consumption of that water. This may include
a recommendation for the provision of an alternative supply of water or a "do not drink"
advice. These powers are delegated to Public Health Unit Directors. A supplier of drinking
water must issue to the public the advice provided under the Public Health Act, if so
directed.
The Australian Drinking Water Guidelines, 2004 have set aesthetic and health related
guideline values for physical and chemical characteristics. Aesthetic guideline values are
set at the concentration that ensures water is aesthetically pleasing in terms of taste and
odour, and can be used without causing corrosion of plumbing or staining. Health-related
guideline values are set at the concentration that, based on current knowledge, does not
result in any significant risk to the health of the consumer over a lifetime of consumption.
Further information on the physical and chemical quality of drinking water is available in the
Guidelines (Chapters 6 and 10).
Where both aesthetic and health-related guideline values are exceeded, consider healthrelated
characteristics first and then aesthetic characteristics.

a) Action on the exceedance of guideline values

The water utility is responsible for carrying out all necessary investigation and resampling as

specified in this response protocol.

1. The water utility and the Public Health Unit (PHU) should be notified of the

contamination by the testing laboratory.

2. The water utility and the PHU should determine if a potential acute health risk exists.

Consider the type of guideline value (health-related or aesthetic) exceeded, the

concentration, and potential causes such as a major contamination event or

treatment failure. Further information is available in the fact sheets for physical and

chemical water quality in the Guidelines.

3. If a potential acute health risk exists, the water utility should consult with the PHU and

the Department of Energy Utilities and Sustainability (DEUS) regional inspector

regarding immediate action such as rectification, alternative supply, public warnings,

and investigation and sampling. The PHU should contact the Water Unit.

4. If no acute health risk is present the water utility should conduct an investigation, in

consultation with the local PHU and the DEUS regional inspector, to determine the

possible sources of contamination. These might include a treatment breakdown or

malfunction (eg. chemical overdose), a mains break, corrosion, interruption to the

supply, surges in supply, or deliberate or accidental contamination of the system.

The investigation may include a visual inspection of the system and associated

service reservoirs by trained personnel. When found, the source of contamination

should be rectified.

5. The water utility should resample at the same site upon advice from the PHU using

NSW Health Repeat/Additional Labels, unless specific project labels are issued. The

sample should be submitted to a NSW Health Laboratory or a NATA accredited

laboratory for analysis. Make sure that the laboratory knows that this is a repeat

samples investigating possible contamination.

6. If the repeat sample meets the guideline value resume normal sampling.

7. If the repeat sample exceeds the guideline value use available data to assess risk

(section b).

8. If the risk assessment does not indicate an ongoing risk, resume normal sampling.

9. If the risk assessment indicates an ongoing risk, the water utility should consult with

the PHU and the DEUS regional inspector regarding rectification (eg. flushing,

system maintenance, etc.), alternative supply, public warnings, and investigation and

sampling. PHU Environmental Health Officers and Director should contact the Water

Unit.

b) Risk assessment and considerations for public notification:

Risk assessment

The Water Utility, PHU, and DEUS regional inspector should consider the following when

conducting the risk assessment:

• Routine sampling frequency. Water utilities that collect two routine chemistry

samples per year for the affected supply system should discuss, with the PHU, the

need for a sampling investigation either through a project or change in the routine

sampling frequency.

• Statistical analysis of available data or sampling investigation results.

o For health-related guideline exceedances, calculate the 95th percentile of

results over (at least) the last twelve months.

o For aesthetic guideline exceedances, calculate the mean of results over (at

least) the last twelve months.

• Exposure

o Estimate daily water consumption levels.

o Determine if the samples are representative of water that is actually

consumed?

o Exposure duration (how long have people been consuming the water?

20

• Have there been any complaints about water quality or health?

• Are flow-on effects possible? Such as low pH causing lead and copper contamination

through corrosion of plumbing.

• Are any vulnerable populations receiving the water? (i.e. dialysis patients,

immunocompromised, infants, etc.)

Further information on conducting health risk assessments is available in Section 3.2.3

(page 3-6) of the Guidelines and Appendix 4 of the enHealth Guidelines for assessing

human health risks from environmental hazards.

Public notification considerations

The PHU, Water Unit and/or Chief Health Officer will consider the following when

determining the need for public notification, a do not drink advice, or an alternative supply:

• The outcomes of the risk assessment.

• Whether proper sample collection and analysis techniques were used

• Whether a NATA accredited laboratory analysed the samples

• Availability of an alternative supply

• Notification of consumers that may receive carted water from the affected

system.

Also see the flowchart.

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