Recycled water sampling technique

This factsheet describes the procedures to be followed to sample non-potable waters and the adequate preservation and transport of samples to determine the microbial and chemical quality. The factsheet provides guidance for both samples taken on site and samples collected and transported to be analysed in the laboratory. 

Recycled (non-potable) water sources include:

  • greywater, 
  • treated wastewater, 
  • industrial wastewater (trade waste waters) and 
  • sewage (yellow water and black water).
To determine the microbiological and chemical quality of recycled water it must be sampled and analysed in accordance with:
  • AS/NZS 5667.10:1998 Water Quality Sampling Part 10; Guidance on Sampling of wastewaters
  • AS/NZS 4276.7:2007 Water microbiology Escherichia coli and Thermotolerant coliforms - Membrane filtration method. 
  • AS/NZS 4276.14: 2014 Water microbiology Detection of Salmonella spp. 
  • APHA 22nd Edition 9244E (2012) Standard Methods for the Examination of Water and Wastewater
  • Surface water sampling methods and analysis — technical appendices Standard operating procedures for water sampling methods and analysis, Department of Water WA (2009)
All recycled water samples are to be analysed by a National Association of Testing Authority (NATA) registered laboratory. 

Safety Procedures

There are potential health hazards associated with the use of recycled water. The risk of diseases arises from the pathogens that may be present in raw sewage which are removed to varying degrees during treatment processes.

Persons engaged in any operation involving recycled water (including sampling) should ensure they:

  • Wash hands well with soap before eating, drinking or smoking, and when finished working with wastewater or the recycled water.

  • Do not consume food or drink, and do not smoke while working with wastewater or recycled water.

  • Wear / use suitable clothing and safety equipment appropriate to the task being undertaken.

  • Clothing and equipment should be washed after use

  • Do not wash hands with or drink wastewater or recycled water, and avoid inhalation of spray.

General Rules of Sampling:

  • Spot samples are usually taken manually and are useful to estimate the compliance with recycled water quality standards not related to average quality. 
  • Samples must be representative of the sampling point to be examined. Whenever practicable, permanent sampling locations should be established. Review Department of Health approval conditions and the Recycled Water Quality Management Plan to confirm sample points.
  • Frequency of sampling and parameters to be sampled shall be as specified in the validation and verification monitoring during the commissioning of the recycled water scheme. The same applies for the ongoing monitoring, based on the Exposure Risk Level of the Guidelines for the Use of Recycled Water in WA.
  • Sampling should be taken from a point beyond the treatment and disinfection process and as close to the point of reuse as possible, unless otherwise stipulated in the approval for use.
  • If there is any reason to suspect that contamination has occurred during sampling, discard the sample and take another in a fresh bottle.
  • Before and after sampling the equipment should be cleaned with detergent and water to avoid cross contamination.
  • Sample points should be labelled for easy identification of personnel responsible for sampling.
  • Frequent reviews of the sampling point locations need to be made. Any changes in the WWTP treatment process or in the recycling scheme (extension/modifications) shall be notified to the Department of Health.
  • The Department of Health is the only agency responsible to allocate site codes for Recycling Schemes.
  • The concentration of parameters in recycled water will vary due random and systematic changes. Whenever practicable an on-line automatic instrument shall be used (e.g. measurement of chlorine, turbidity, pH, dissolved oxygen). 
  • Sample requirements for specific parameters commonly tested in recycled water are presented in Table 1.

Also:

  • Take extreme care to avoid contaminating the sample container and the wastewater sample.
  • Only remove the bottle from the plastic bag to complete the label details OR when it is time to sample.
 Do Not   Always
  • Eat, drink or smoke when sampling. 
  • Touch the inside of the bottle.
  • Rinse the bottle.
  • Put caps on the ground while sampling.
  • Transport wastewater samples with other samples, (e.g. drinking water or environmental samples).
  • Wear gloves.
  • Take care to avoid contact with the wastewater
  • Confirm sample point location and use correct site code
  • Label the bottle before sampling.
  • Take pH measurement first and record the concentration in the laboratory form
  • Take the free chlorine measurement first and record the concentration in the laboratory form

Sample Bottles

For recycled water, plastic bottles are recommended for the majority of parameters. However, some analysis such as pesticides, hydrocarbons and detergents require glass bottles. The collected volume shall not be less than 100mL

Sample Bottle Labeling

The following information should be provided on all sample bottles:
  • Sender reference number.
  • Site code.
  • Point of Collection/Source – Site description.
  • Site location.
  • Date and time of collection.
  • Transport temperature (4oC or ambient).
  • Comments or relevant details that may influence the sampling quality 
  • On site pH measurement.
  • On site free chlorine measurement.
  • Authority or Company Name.

Sample Preservation and Transportation

The most common way of preservation is to keep the recycled water samples between 0oC and 4oC in a dark area. Bacteriological samples should be collected into pre-chilled bottles and be transported in a chilled, not frozen, state between 0°C and 4°C. Freezer blocks should be used, not loose ice.

Samples should arrive in the laboratory no later than 24 hours after collection. Whenever possible, samples should arrive at the laboratory on the day of collection, preferably before 2pm.

On site pH Measurement

The relative concentration of chlorine species in water is affected by pH. Increase in pH requires a greater chlorine contact time to achieve the desired pathogen log inactivation by chlorine.

The measurement of pH can be done by using pH probes or pH indicator strips.

pH probes

pH probes are suitable if they are correctly maintained and regularly calibrated (monthly). Calibration/maintenance procedures of the pH probes need to be included in the Recycled Water Quality Management Plan to ensure validity and reliability of the instrument measurement. Instruments without proper maintenance and calibration will give poor readings.

pH indicator strips

Strips are a quick, simple and cost effective option to record pH measurement. Strips are ready for immediate use and are maintenance free. Strips cover different pH ranges from the universal ranges 0 to 14 or 1 to 10 to more specific ranges. If used please ensure
  • The strips must cover at least the 6-10 pH range. 
  • Test strips that have two colour pads per pH level are preferred over single tone dispenser reels, single tone test strips, or other indicator papers. This assists staff with colour blindness to accurately read the pH value.
  • pH values taken in-situ shall be recorded on the lab request form 
  • Only use test strips before expiration date
  • Hi heat or humidity could shorten expected shelf life of the strips. Follow manufacturer ‘s storage recommendations.
  • Follow manufacturer’s instructions for their use

On site Chlorine Measurement

Where schemes are chlorinated it is important that the level of chlorine is measured prior to sampling. A sufficient chlorine dose must be added to allow for the chlorine demand reactions to occur, and to ensure that there is an adequate free chlorine residual available to disinfect the recycled water effectively. If the reading shows the free chlorine level is low this should be investigated and restored before sampling is carried out. 

Chlorine dosing systems, ideally with flow-proportional automatic dosing and feedback loops should be used to achieve target chlorine residual and provide rapid responses to any changes in flow and water quality. Chlorine sensors should be used to continuously measure hypochlorous acid (HOCl) and temperature in recycled water to determine free chlorine concentration.

On site chlorine measurement can be done using the DPD (diethyl paraphenylene diamine) liquid reagent. There are different test kits and instruments commercially available for analysing the chlorine residual. Examples include but are not limited to colour-wheel test kits, comparators, digital colorimeters and photometers. Calibration/maintenance procedures of the instruments need to be included in the Recycled Water Quality Management Plan to ensure validity and reliability of the instrument measurement. Instruments without proper maintenance and calibration will give poor free chorine readings.

Tap Samples

  1. Turn the on tap full and allow the water to run to waste for 2 minutes. This flushes the interior of the nozzle and discharges stagnant water from the pipe.
  2. Turn off the tap and sterilise the spout by heating it with a blow lamp, gas torch or by igniting a piece of cotton wool soaked in methylated spirits until any water in the tap boils
  3. Cool the tap by allowing the water to run to waste for a few seconds.
  4. Adjust the tap to deliver a gentle stream of water.
  5. Clearly label the bottle. (See Sample Bottle Labelling for further details).
  6. Hold the bottle in one hand and remove the screw cap with the other. Hold the cap open side down and keep it close to the bottle.
  7. Fill the bottle to within 5mm from the top by holding it under the tap taking care to avoid splashing.
  8. Carefully replace the cap.
  9. Place the bottle into a biohazard bag and seal.

Samples should arrive in the laboratory no later than 24 hours after collection. Whenever possible, samples should arrive at the laboratory on the day of collection, preferably before 2pm.

Documentation

The Water Examination Laboratory requires all samples to be accompanied by a correctly filled out WB (blue) form:
  • Make sure that the pH and the level of chlorine are recorded on the form.
  • Write on sample collection report: copy to Water Unit, Department of Health Western Australia. 

Site Code Number

A site code number is a computerised identification number that must identify all samples and accompanying documentation. Site codes are only assigned by the Department of Health. The basic site code numbers have:
  • Three-digit Wastewater Treatment Plant (WWTP) ID 
  • Two-digit Primary Recipient ID
  • One-digit Secondary Recipient ID
  • Two digit sample type code ID as indicated below

WWTP Primary recipient Secondary recipient Sample type ID
AAX/ XX X XX


For more information regarding site codes please contact the Water Unit.
Table 1: Recycled water sampling requirements for common analysed parameters
Parameter (units) Volume required Type of bottle ** ^ Preservation Maximum sample holding time
Turbidity(NTUs)
  • 250 mL
  • Fill bottle just below shoulder
  • Plastic or glass
  • Refrigerate at 1–4 °C
  • Do not freeze
  • 24 hours
pH (pH units)
  • 125 mL
  • Fill bottle to the top to exclude air
  • Sample must be free of air bubbles
  • Plastic.
  • Bottle cap must have a teflon liner
  • Refrigerate at 1–4 °C
  • Do not freeze
  • 6 hours In situ test is preferable to
Chlorine Residual (mg/L)
  • 500 mL
  • Plastic or glass
  • Monitored in-situ by on-line sensors
  • Immediate analysis is preferable
  • Maximum holding time is 5 minutes
  • Keep sample out of direct sunlight
BOD (mg/L)
  • 1 L
  • Fill bottle to the top to exclude air. Sample must be free of air bubbles
  • Plastic or glass brown (amber)
  • Refrigerate at 1–4 °C
  • Store in the dark
  • Do not freeze
  • Analyse as soon as possible after collection or within 24 hours if sample is refrigerated at 1-4°C
Suspended Solids (mg/L)
  • 1 L
  • Fill to the shoulder of bottle
  • Plastic
  • Refrigerate at 1–4 °C
  • Do not freeze
  • Analyse as soon as possible after collection or within 24 hours if sample is refrigerated at 1-4 °C
  • Do not hold samples longer than 7 days
Total Nitrogen (mg/L)
  • 200 mL
  • Fill bottle just below shoulder
  • Plastic
  • Refrigerate at 1–4 °C or freeze
  • Store in the dark
  • Analyse within 24 hours if sample is kept refrigerated at 1- 4 °C
  • Analyse within 30 days if kept frozen below -20 °C
  • Alternative holding time is 7 days at 4 °C
Total Phosphorus (mg/L)
  • 200 mL
  • Fill bottle just below shoulder
  • Plastic
  • Refrigerate at 1–4 °C or freeze
  • Store in the dark
  • Immediate analysis is preferable
  • Analyse within 24 hours if sample is kept refrigerated at 1-4 °C
  • Analyse within 30 days if kept frozen below -20 °C
  • Alternative holding time is 7 days at 4 °C
Microbiological (including coliphage) (cfu/100mL)
  • 100 mL per microbial analysis
  • 200 mL is required for the
  • AS for coliforms and E.coli, and total plate count
  • Fill to below shoulder of bottle
  • Sterilised plastic or glass
  • Use new precleaned sterilised bottles
  • Store in the dark
  • Refrigerate at 1–4 °C
  • 24 hours
  • Immediate analysis is preferable

Notes to accompany Table 1

  • Appropriate plastic bottles are high-density polyethylene (HDPE), polypropylene, polycarbonate or a fluoropolymer (e.g. Teflon).
  • Whenever possible plastic is preferred for occupational health and safety issues.
  • NTU: nephelometric turbidity units
  • cfu: coliform forming units
  • ** Ensure sample bottle is pre-rinsed three times with sample water (3 × 20 mL) before final collection.
  • ^ Use new pre-cleaned bottles
  • Samples for TN and TP determination can be collected in the same 250 mL container.
  • All parameters in the table are unfiltered samples for laboratory analysis

More information

  • Water Unit, Environmental Health Directorate
    Telephone: 9222 2000
    Postal address: Department of Health, PO Box 8172, Perth Business Centre WA 6849
    Email: ehinfo@health.wa.gov.au
Last reviewed: 29-10-2020
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