| Req ID | Category | Intent | Legal Status | Name | Subdomain(s) | Context | Conditions | Confidence |
|---|---|---|---|---|---|---|---|---|
| #Q001 | administrative | operational | recommended | Consultation of individual guideline technical documents | drinking water | Health Canada updates this document regularly, but you should always consult individual guideline technical documents and guidance documents on the website Water Quality - Reports and Publications for the most current information. | high | |
| #Q002 | monitoring | health | recommended | E. coli monitoring approach | drinking water | E. coli should be monitored in conjunction with other indicators, as part of a source-to-tap approach to producing drinking water of an acceptable quality. | high | |
| #Q003 | monitoring | operational | recommended | Total coliforms monitoring in distribution system | drinking water | Total coliforms should be monitored in the distribution system because they are used to indicate changes in water quality. | high | |
| #Q004 | monitoring | operational | recommended | Total coliforms measurement at treatment plant | drinking water | In water leaving a treatment plant, total coliforms should be measured in conjunction with other indicators to assess water quality; the presence of total coliforms indicates a serious breach in treatment. | In water leaving a treatment plant | high |
| #Q005 | corrective_action | operational | recommended | Total coliforms detection investigation | drinking water | Detection of total coliforms from consecutive samples from the same site or from more than 10% of the samples collected in a given sampling period should be investigated. | Detection of total coliforms from consecutive samples from the same site or from more than 10% of the samples collected in a given sampling period | high |
| #Q006 | administrative | operational | mandatory | Exemption from filtration decision | drinking water | The decision to exempt a waterworks from filtration should be made by the appropriate authority based on site-specific considerations, including historical and ongoing monitoring data. | high | |
| #Q007 | design | operational | recommended | Filtration systems design and operation | drinking water | Filtration systems should be designed and operated to reduce turbidity levels as low as reasonably achievable and strive to achieve a treated water turbidity target from individual filters of less than 0.1 NTU. | high | |
| #Q008 | corrective_action | operational | recommended | Membrane unit integrity investigation | drinking water | Measurements greater than 0.1 NTU for a period greater than 15 minutes from an individual membrane unit should immediately trigger an investigation of the membrane unit integrity. | Measurements greater than 0.1 NTU for a period greater than 15 minutes from an individual membrane unit | high |
| #Q009 | treatment | health | guidance | Additional log removal for Enteric protozoa | drinking water | Depending on the source water quality, a greater log removal and/or inactivation may be required. | Depending on the source water quality | high |
| #Q010 | administrative | operational | mandatory | Aluminum MAC and OG application | drinking water | The MAC and OG apply to all drinking water supplies (including groundwater) and are to be applied as locational running annual averages. | high | |
| #Q011 | monitoring | operational | recommended | Ammonia monitoring in distribution system | drinking water | Levels of ammonia, either naturally present in the source water or added as part of a disinfection strategy, can affect water quality in the distribution system (e.g., nitrification) and should be monitored. | high | |
| #Q012 | treatment | health | mandatory | Bromate reduction and disinfection effectiveness | drinking water | Efforts to reduce bromate concentrations must not compromise the effectiveness of disinfection. | high | |
| #Q013 | treatment | health | recommended | Bromate formation control strategy | drinking water | The recommended strategy is controlling the ozonation process; use of certified treatment chemicals and; appropriate handling and storage of hypochlorite. | high | |
| #Q014 | monitoring | operational | recommended | Raw water bromide monitoring | drinking water | Quarterly monitoring of raw water bromide is recommended to allow correlation to bromate or brominated DBPs. | high | |
| #Q015 | monitoring | health | recommended | Cadmium sampling location | drinking water | Sampling should be done at the tap to reflect average exposure similar to sampling done for lead. | high | |
| #Q016 | operational | health | guideline | Cadmium exposure minimization approach | drinking water | The best approach to minimize exposure to cadmium from drinking water is to replace galvanized steel and components. | high | |
| #Q017 | operational | health | recommended | Chlorate formation control | drinking water | As chlorate is difficult to remove once formed, its formation should be controlled by respecting the maximum feed dose of 1.2 mg/L of chlorine dioxide and managing /monitoring formation in hypochlorite solutions. | high | |
| #Q018 | operational | health | recommended | Chlorite formation control | drinking water | Chlorite formation should be controlled by respecting the maximum feed dose of 1.2 mg/L of chlorine dioxide and managing /monitoring formation in hypochlorite solutions. | high | |
| #Q019 | monitoring | health | recommended | Copper sampling location | drinking water | Water samples should be taken at the tap. | high | |
| #Q020 | corrective_action | health | recommended | Alternate drinking water source for infant formula (Cyanobacterial toxins) | drinking water | As a precautionary measure, where levels of total microcystins in treated water are detected above a reference value of 0.4 µg/L, the public in the affected area should use an alternate suitable source of drinking water (such as bottled water) to reconstitute infant formula. | where levels of total microcystins in treated water are detected above a reference value of 0.4 µg/L | high |
| #Q021 | monitoring | health | recommended | Dichlorobenzenes individual isomer analysis | drinking water | In cases where total dichlorobenzenes are measured and concentrations exceed the most stringent value (0.005 mg/L), the concentrations of the individual isomers should be established. | In cases where total dichlorobenzenes are measured and concentrations exceed the most stringent value (0.005 mg/L) | high |
| #Q022 | administrative | health | mandatory | Dimethoate and omethoate additive approach | drinking water | An additive approach should be taken in which the sum of the detected concentrations of dimethoate and omethoate (expressed as a dimethoate equivalent value) does not exceed the MAC for dimethoate. | high | |
| #Q023 | treatment | health | mandatory | 1,4-Dioxane treatment technologies | drinking water | Treatment technologies such as advanced oxidation processes and synthetic adsorbents need to be considered. | high | |
| #Q024 | operational | aesthetic | recommended | Separate unsoftened supply for hardness | drinking water | Where a water softener is used, a separate unsoftened supply for cooking and drinking purposes is recommended. | Where a water softener is used | high |
| #Q025 | operational | health | recommended | Lead levels ALARA | drinking water | Lead levels should be kept as low as reasonably achievable. | high | |
| #Q026 | monitoring | health | recommended | Lead sampling location | drinking water | Sampling should be done at the tap to reflect average exposure. | high | |
| #Q027 | operational | health | guideline | Lead exposure minimization approach | drinking water | The best approach to minimize exposure to lead from drinking water is to remove the full lead service line. | high | |
| #Q028 | operational | health | recommended | Awareness of malathion degradation byproducts | drinking water | When using oxidation or advanced oxidation processes for malathion removal, water utilities should be aware of the potential for the formation of degradation by products. | When using oxidation or advanced oxidation processes for malathion removal | high |
| #Q029 | monitoring | health | recommended | Nitrate monitoring in distribution system | drinking water | Systems using chloramine disinfection or that have naturally occurring ammonia should monitor the level of nitrate in the distribution system. | Systems using chloramine disinfection or that have naturally occurring ammonia | high |
| #Q030 | monitoring | health | recommended | Nitrate testing for well owners | drinking water | Homeowners with a well should test concentration of nitrate in their water supply. | Homeowners with a well | high |
| #Q031 | monitoring | health | recommended | Nitrite monitoring in distribution system | drinking water | Systems using chloramine disinfection or that have naturally occurring ammonia should monitor the level of nitrite in the distribution system. | Systems using chloramine disinfection or that have naturally occurring ammonia | high |
| #Q032 | monitoring | health | recommended | Nitrite testing for well owners | drinking water | Homeowners with a well should test concentration of nitrite in their water supply. | Homeowners with a well | high |
| #Q033 | treatment | health | recommended | NDMA formation prevention | drinking water | Levels should be kept low by preventing formation during treatment. | high | |
| #Q034 | monitoring | health | guidance | PFAS type examination | drinking water | If measurements of PFAS in drinking water are approaching or exceed the 30 ng/L objective, it may be useful to examine the types of PFAS that are present in the greatest concentrations. | If measurements of PFAS in drinking water are approaching or exceed the 30 ng/L objective | high |
| #Q035 | treatment | health | recommended | PFAS ALARA treatment | drinking water | When treatment is required, it is also recommended that treatment plants strive to maintain PFAS concentrations in drinking water as low as reasonably achievable (ALARA). | When treatment is required | high |
| #Q036 | operational | health | recommended | Separate unsoftened supply for sodium | drinking water | where a sodium-based water softener is used, a separate unsoftened supply for cooking and drinking purposes is recommended. | where a sodium-based water softener is used | high |
| #Q037 | operational | health | recommended | Trihalomethanes ALARA maintenance | drinking water | Utilities should make every effort to maintain concentrations as low as reasonably achievable without compromising the effectiveness of disinfection. Recommended strategy is precursor removal. | high | |
| #Q038 | operational | aesthetic | recommended | Plumbing flushing for zinc | drinking water | plumbing should be thoroughly flushed before water is consumed. | high | |
| #Q039 | monitoring | health | recommended | Radiological screening analysis | drinking water | Drinking water samples should initially be screened against a gross alpha radiation level of 0.5 Bq/L (becquerel/litre) and a gross beta level of 1 Bq/L.. | high | |
| #Q040 | monitoring | health | mandatory | Individual radionuclide analysis requirement | drinking water | Individual radionuclide analysis is only necessary when one (or both) of these are exceeded. | when one (or both) of these are exceeded | high |
| #Q041 | administrative | health | mandatory | Multiple radionuclide MAC ratio sum limit | drinking water | If more than one radionuclide in Table 1 is detected, the sum of the ratios of the observed concentration to their corresponding MAC should not exceed 1. | If more than one radionuclide in Table 1 is detected | high |
| #Q042 | corrective_action | health | recommended | Chloral hydrate investigation | drinking water | levels above 0.2 mg/L may indicate a concern for health effects and should be investigated. | levels above 0.2 mg/L | high |
| #Q043 | prohibition | health | recommended | Avoidance of potassium chloride treated water | drinking water | those with kidney disease or other conditions, such as heart disease, coronary artery disease, hypertension or diabetes, and those who are taking medications that interfere with normal body potassium handling should avoid the consumption of water treated by water softeners using potassium chloride. | those with kidney disease or other conditions, such as heart disease, coronary artery disease, hypertension or diabetes, and those who are taking medications that interfere with normal body potassium handling | high |
| #Q044 | operational | health | recommended | Chemical treatment impact on disinfection | drinking water | Any measure taken to reduce concentrations of chemical substances should not compromise the effectiveness of disinfection. | When taking measures to reduce chemical concentrations | high |
| #Q045 | operational | operational | recommended | Ammonia limit for nitrification prevention | drinking water | To help prevent nitrification, limit excess free ammonia entering the distribution system to below 0.1 mg/L, and preferably below 0.05 mg/L, measured as nitrogen. | To prevent nitrification in the distribution system | high |
| #Q046 | operational | health | recommended | Chlorine dioxide maximum feed dose limit | drinking water | A maximum feed dose of 1.2 mg/L of chlorine dioxide should not be exceeded to control the formation of chlorite and chlorate. | When using chlorine dioxide for disinfection | high |
| #Q047 | operational | operational | recommended | Distribution system entry turbidity recommendation | drinking water | To ensure effectiveness of disinfection and for good operation of the distribution system, it is recommended that water entering the distribution system have turbidity levels of 1.0 NTU or less. | At the point of entry to the distribution system | high |
| #Q048 | operational | operational | recommended | Groundwater turbidity level recommendation | drinking water | For systems that use groundwater, turbidity should generally be below 1.0 NTU. | For systems utilizing groundwater sources | high |
| Req ID | Category | Intent | Legal Status | Name | Subdomain(s) | Limit Type | Limit Value | Context | Conditions | Confidence |
|---|---|---|---|---|---|---|---|---|---|---|
| #P001 | microbiological | treatment | guideline | Enteric protozoa: Giardia and Cryptosporidium | drinking water | treatment_goal | 3 log | Treatment goal: Minimum 3 log removal and/or inactivation of cysts and oocysts | high | |
| #P002 | microbiological | treatment | guideline | Enteric viruses | drinking water | treatment_goal | 4 log | Treatment goal: Minimum 4 log reduction (removal and/or inactivation) of enteric viruses | high | |
| #P003 | microbiological | health | guideline | Escherichia coli (E. coli) | drinking water | MAC | 0 per 100 mL | MAC: None detectable per 100 mL | medium | |
| #P004 | microbiological | operational | guideline | Total coliforms | drinking water | MAC | 0 per 100 mL | MAC of none detectable/100 mL in water leaving a treatment plant and in non-disinfected groundwater leaving the well | in water leaving a treatment plant and in non-disinfected groundwater leaving the well | medium |
| #P005 | physical | treatment | guideline | Turbidity (Conventional and direct filtration) | drinking water | requirement | <= 0.3 NTU | Treatment limits for individual filters or units | in at least 95% of measurements either per filter cycle or per month; never to exceed 1.0 NTU. | high |
| #P006 | physical | treatment | guideline | Turbidity (slow sand and diatomaceous earth filtration) | drinking water | requirement | <= 1.0 NTU | Treatment limits for individual filters or units | in at least 95% of measurements either per filter cycle or per month; never to exceed 3.0 NTU. | high |
| #P007 | physical | treatment | guideline | Turbidity (membrane filtration) | drinking water | requirement | <= 0.1 NTU | Treatment limits for individual filters or units | in at least 99% of measurements per operational filter period or per month. | high |
| #P008 | chemical | health | guideline | Aluminum | drinking water | MAC | 2.9 mg/L | MAC (mg/L) | apply to all drinking water supplies (including groundwater) and are to be applied as locational running annual averages. | high |
| #P009 | chemical | operational | guideline | Aluminum | drinking water | OG | 0.1 mg/L | OG: 0.1 | high | |
| #P010 | chemical | health | guideline | Antimony | drinking water | MAC | 0.006 mg/L | MAC (mg/L) | high | |
| #P011 | chemical | health | guideline | Arsenic | drinking water | MAC | 0.010 mg/L | 0.010 ALARA | high | |
| #P012 | chemical | health | guideline | Atrazine | drinking water | MAC | 0.005 mg/L | MAC (mg/L) | high | |
| #P013 | chemical | health | guideline | Barium | drinking water | MAC | 2.0 mg/L | MAC (mg/L) | high | |
| #P014 | chemical | health | guideline | Benzene | drinking water | MAC | 0.005 mg/L | MAC (mg/L) | high | |
| #P015 | chemical | health | guideline | Benzo[a]pyrene | drinking water | MAC | 0.00004 mg/L | 0.000 04 | high | |
| #P016 | chemical | health | guideline | Boron | drinking water | MAC | 5 mg/L | MAC (mg/L) | high | |
| #P017 | chemical | health | guideline | Bromate | drinking water | MAC | 0.01 mg/L | MAC (mg/L) | high | |
| #P018 | chemical | health | guideline | Chlorate | drinking water | MAC | 1 mg/L | MAC (mg/L) | high | |
| #P019 | chemical | aesthetic | guideline | Chloride | drinking water | AO | <= 250 mg/L | AO: <= 250 | high | |
| #P020 | chemical | health | guideline | Chlorite | drinking water | MAC | 1 mg/L | MAC (mg/L) | high | |
| #P021 | radiological | operational | guideline | Gross alpha radiation | drinking water | requirement | 0.5 Bq/L | Drinking water samples should initially be screened against a gross alpha radiation level of 0.5 Bq/L | high | |
| #P022 | radiological | operational | guideline | Gross beta radiation | drinking water | requirement | 1 Bq/L | and a gross beta level of 1 Bq/L | high | |
| #P023 | chemical | health | mandatory | Lead | drinking water | MAC | 0.005 mg/L | MAC is for total lead. ALARA (As Low As Reasonably Achievable). | Sampling should be done at the tap to reflect average exposure. | high |
| #P024 | chemical | health | guideline | Per-and polyfluoroalkyl substances (PFAS) | drinking water | treatment_goal | 0.00003 mg/L | Objective: 0.00003 mg/L (30 ng/L) ALARA. | Applies to the sum of 25 specified PFAS. | high |
| #P025 | chemical | health | mandatory | Nitrate | drinking water | MAC | 45 mg/L | 45 mg/L as nitrate; equivalent to 10 mg/L as nitrate-nitrogen. | high | |
| #P026 | physical | operational | guideline | pH | drinking water | AO | 7.0-10.5 dimensionless | Aesthetic Objective range. | high | |
| #P027 | chemical | operational | guidance | Free Ammonia | drinking water | OG | < 0.1 mg/L | Measured as nitrogen to prevent nitrification. | Preferably below 0.05 mg/L. | high |
| #P028 | chemical | health | guidance | Chloral hydrate | drinking water | treatment_goal | 0.2 mg/L | Levels above 0.2 mg/L may indicate a concern for health effects and should be investigated. | high | |
| #P029 | chemical | health | mandatory | Cyanobacterial toxins (Microcystins) | drinking water | MAC | 0.0015 mg/L | MAC is for total microcystins (intra- and extra-cellular). | If total microcystins are detected above 0.4 µg/L, alternate water should be used for infant formula. | high |
| #P030 | chemical | health | mandatory | Copper | drinking water | MAC | 2 mg/L | MAC for total copper protects against gastrointestinal, liver, and kidney effects. | Samples should be taken at the tap. | high |
| #P031 | chemical | health | guideline | Bromoxynil | drinking water | MAC | 0.03 mg/L | MAC (mg/L) | high | |
| #P032 | chemical | health | guideline | Cadmium | drinking water | MAC | 0.007 mg/L | MAC (mg/L) | Sampling should be done at the tap | high |
| #P033 | chemical | health | guideline | Carbon tetrachloride | drinking water | MAC | 0.002 mg/L | MAC (mg/L) | Inhalation and dermal absorption during showering included | high |
| #P034 | chemical | operational | guidance | Chlorine (Distribution range) | drinking water | requirement | 0.04-2.0 mg/L | Free chlorine concentrations in most Canadian drinking water distribution systems | high | |
| #P035 | chemical | operational | guideline | Chlorine dioxide (Maximum feed dose) | drinking water | requirement | <= 1.2 mg/L | A maximum feed dose of 1.2 mg/L of chlorine dioxide should not be exceeded | to control the formation of chlorite and chlorate | high |
| #P036 | chemical | health | guideline | Chlorpyrifos | drinking water | MAC | 0.09 mg/L | MAC (mg/L) | high | |
| #P037 | chemical | health | guideline | Chromium | drinking water | MAC | 0.05 mg/L | MAC for total chromium | high | |
| #P038 | physical | aesthetic | guideline | Colour | drinking water | AO | <= 15 TCU | AO: <= 15 TCU | high | |
| #P039 | chemical | aesthetic | guideline | Copper (Aesthetic Objective) | drinking water | AO | 1 mg/L | AO based on taste and water discolouration | high | |
| #P040 | chemical | health | guideline | Cyanide | drinking water | MAC | 0.2 mg/L | MAC (mg/L) | high | |
| #P041 | chemical | health | guideline | Dicamba | drinking water | MAC | 0.11 mg/L | MAC (mg/L) | high | |
| #P042 | chemical | health | guideline | 1,4-Dichlorobenzene | drinking water | MAC | 0.005 mg/L | MAC (mg/L) | high | |
| #P043 | chemical | aesthetic | guideline | 1,4-Dichlorobenzene (Aesthetic) | drinking water | AO | <= 0.001 mg/L | AO based on odour | high | |
| #P044 | chemical | health | guideline | 1,2-Dichloroethane | drinking water | MAC | 0.005 mg/L | MAC (mg/L) | high | |
| #P045 | chemical | health | guideline | Dichloromethane | drinking water | MAC | 0.05 mg/L | MAC (mg/L) | high | |
| #P046 | chemical | health | guideline | 2,4-Dichlorophenoxy acetic acid (2,4-D) | drinking water | MAC | 0.1 mg/L | MAC (mg/L) | high | |
| #P047 | chemical | health | guideline | Dimethoate | drinking water | MAC | 0.02 mg/L | MAC is for dimethoate | Sum of dimethoate and omethoate should not exceed this MAC | high |
| #P048 | chemical | health | guideline | 1,4-Dioxane | drinking water | MAC | 0.050 mg/L | MAC (mg/L) | high | |
| #P049 | chemical | health | guideline | Diquat | drinking water | MAC | 0.05 mg/L | MAC (mg/L) | high | |
| #P050 | chemical | health | guideline | Ethylbenzene | drinking water | MAC | 0.14 mg/L | MAC (mg/L) | high | |
| #P051 | chemical | aesthetic | guideline | Ethylbenzene (Aesthetic) | drinking water | AO | 0.0016 mg/L | AO based on odour | high | |
| #P052 | chemical | health | guideline | Fluoride | drinking water | MAC | 1.5 mg/L | MAC (mg/L) | high | |
| #P053 | chemical | health | guideline | Glyphosate | drinking water | MAC | 0.28 mg/L | MAC (mg/L) | high | |
| #P054 | chemical | health | guideline | Haloacetic acids (Total) | drinking water | MAC | 0.08 mg/L | Total of MCA, DCA, TCA, MBA, and DBA | Locational running annual average of quarterly samples | high |
| #P055 | physical | aesthetic | guidance | Hardness (Poor Quality Threshold) | drinking water | requirement | > 200 mg/L | Water with a hardness greater than 200 mg/L is considered poor | primarily based on calcium and magnesium | high |
| #P056 | physical | aesthetic | guidance | Hardness (Unacceptable Threshold) | drinking water | requirement | > 500 mg/L | hardness in excess of 500 mg/L is generally unacceptable for domestic use | high | |
| #P057 | chemical | aesthetic | guideline | Hydrogen Sulphide | drinking water | AO | <= 0.05 mg/L | AO: <= 0.05 | Can occur from reduction of sulphates by bacteria | high |
| #P058 | chemical | aesthetic | guideline | Iron | drinking water | AO | <= 0.1 mg/L | AO: <= 0.1 | high | |
| #P059 | chemical | health | guideline | Malathion | drinking water | MAC | 0.29 mg/L | MAC (mg/L) | high | |
| #P060 | chemical | health | guideline | Manganese | drinking water | MAC | 0.12 mg/L | MAC (mg/L) | high | |
| #P061 | chemical | aesthetic | guideline | Manganese (Aesthetic) | drinking water | AO | <= 0.02 mg/L | AO: <= 0.02 | high | |
| #P062 | chemical | health | guideline | Mercury | drinking water | MAC | 0.001 mg/L | MAC (mg/L) | high | |
| #P063 | chemical | health | guideline | MCPA | drinking water | MAC | 0.35 mg/L | MAC (mg/L) | high | |
| #P064 | chemical | aesthetic | guideline | MTBE | drinking water | AO | <= 0.015 mg/L | AO based on odour | high | |
| #P065 | chemical | health | guideline | Metribuzin | drinking water | MAC | 0.08 mg/L | MAC (mg/L) | high | |
| #P066 | chemical | health | guideline | NTA | drinking water | MAC | 0.4 mg/L | MAC (mg/L) | high | |
| #P067 | chemical | health | guideline | Nitrite | drinking water | MAC | 3 mg/L | 3 mg/L as nitrite | high | |
| #P068 | chemical | health | guideline | NDMA | drinking water | MAC | 0.00004 mg/L | 0.000 04 mg/L | high | |
| #P069 | chemical | health | guideline | Pentachlorophenol | drinking water | MAC | 0.06 mg/L | MAC (mg/L) | high | |
| #P070 | chemical | health | guideline | Selenium | drinking water | MAC | 0.05 mg/L | MAC (mg/L) | high | |
| #P071 | chemical | aesthetic | guideline | Sodium | drinking water | AO | <= 200 mg/L | AO based on taste | Strict sodium reduced diets threshold: 20 mg/L | high |
| #P072 | chemical | health | guideline | Strontium | drinking water | MAC | 7.0 mg/L | MAC (mg/L) | high | |
| #P073 | chemical | aesthetic | guideline | Sulphate | drinking water | AO | <= 500 mg/L | AO based on taste and corrosion | High levels above 500 mg/L can cause diarrhoea | high |
| #P074 | physical | aesthetic | guideline | Total dissolved solids (TDS) | drinking water | AO | <= 500 mg/L | AO based on taste | TDS above 500 mg/L results in excessive scaling | high |
| #P075 | chemical | aesthetic | guideline | Pentachlorophenol (Aesthetic Objective) | drinking water | AO | <= 0.03 mg/L | AO based on odour; levels above the AO would render drinking water unpalatable. | high | |
| #P076 | chemical | health | guideline | Tetrachloroethylene | drinking water | MAC | 0.01 mg/L | MAC takes into consideration all exposures from drinking water, which include ingestion, as well as inhalation and dermal absorption. | high | |
| #P077 | chemical | health | guideline | Toluene | drinking water | MAC | 0.06 mg/L | MAC takes into consideration all exposures from drinking water, which include ingestion, as well as inhalation and dermal absorption. | high | |
| #P078 | chemical | aesthetic | guideline | Toluene (Aesthetic Objective) | drinking water | AO | 0.024 mg/L | AO based on odour. | high | |
| #P079 | chemical | health | guideline | Trichloroethylene | drinking water | MAC | 0.005 mg/L | MAC takes into consideration all exposures from drinking water, which include ingestion, as well as inhalation and dermal absorption. | high | |
| #P080 | chemical | health | guideline | 2,4,6-Trichlorophenol | drinking water | MAC | 0.005 mg/L | high | ||
| #P081 | chemical | aesthetic | guideline | 2,4,6-Trichlorophenol (Aesthetic Objective) | drinking water | AO | <= 0.002 mg/L | AO based on odour; levels above the AO would render drinking water unpalatable. | high | |
| #P082 | chemical | health | guideline | Trihalomethanes (THMs) | drinking water | MAC | 0.1 mg/L | Refers to the total of chlorodibromomethane, chloroform, bromodichloromethane and bromoform. | high | |
| #P083 | chemical | health | guideline | Uranium | drinking water | MAC | 0.02 mg/L | MAC is for total uranium and is protective in relation to both chemical and radiological hazards. | high | |
| #P084 | chemical | health | guideline | Vinyl chloride | drinking water | MAC | 0.002 mg/L | ALARA. Based on analytical achievability. | high | |
| #P085 | chemical | health | guideline | Xylenes (total) | drinking water | MAC | 0.09 mg/L | MAC takes into consideration all exposures from drinking water, which include ingestion, as well as inhalation and dermal absorption. | high | |
| #P086 | chemical | aesthetic | guideline | Xylenes (total) (Aesthetic Objective) | drinking water | AO | 0.02 mg/L | AO is based on odour. | high | |
| #P087 | chemical | aesthetic | guideline | Zinc (Aesthetic Objective) | drinking water | AO | <= 5.0 mg/L | AO based on taste. | high | |
| #P088 | radiological | health | guideline | Ionizing Radiation Reference Level | drinking water | requirement | 1 mSv/year | The MACs are derived from a reference level corresponding to a radiation dose of 1 millisievert per year (mSv/year). | high | |
| #P089 | radiological | health | guideline | Radionuclide Mixture Ratio | drinking water | requirement | <= 1 dimensionless | If more than one radionuclide in Table 1 is detected, the sum of the ratios of the observed concentration to their corresponding MAC should not exceed 1. | Applies when multiple radionuclides are detected. | high |
| #P090 | physical | operational | recommended | Turbidity (Entering distribution system) | drinking water | requirement | <= 1.0 NTU | To ensure effectiveness of disinfection and for good operation of the distribution system | Water entering the distribution system | high |
| #P091 | physical | operational | guideline | Turbidity (Groundwater systems) | drinking water | requirement | < 1.0 NTU | For systems that use groundwater | high | |
| #P092 | physical | treatment | recommended | Turbidity (Individual filter target) | drinking water | treatment_goal | < 0.1 NTU | Filtration systems should be designed and operated to reduce turbidity levels as low as reasonably achievable | Strive to achieve target from individual filters | high |
| #P093 | chemical | health | guidance | Cyanobacterial toxins (Infant reference value) | drinking water | requirement | 0.4 µg/L | Precautionary measure for bottle-fed infants | Where levels of total microcystins in treated water are detected above this value | high |
| #P094 | chemical | health | mandatory | Nitrate (as Nitrogen) | drinking water | MAC | 10 mg/L | MAC expressed as nitrate-nitrogen | high | |
| #P095 | chemical | health | mandatory | Nitrite (as Nitrogen) | drinking water | MAC | 1 mg/L | MAC expressed as nitrite-nitrogen | high | |
| #P096 | microbiological | operational | mandatory | Total coliforms (Investigation trigger) | drinking water | requirement | > 10 % | Detection of total coliforms should be investigated | from more than 10% of the samples collected in a given sampling period in distribution/storage system | high |
| #P097 | physical | operational | mandatory | Turbidity (Membrane investigation trigger time) | drinking water | requirement | > 15 minutes | Trigger an immediate investigation of the membrane unit integrity | Measurements greater than 0.1 NTU for a period greater than 15 minutes from an individual membrane unit | high |
| Req ID | Category | Name | Context | Confidence |
|---|---|---|---|---|
| #D001 | A | acceptability (parameter type) | high | |
| #D002 | ALARA | as low as reasonably achievable | high | |
| #D003 | AO | aesthetic objective | high | |
| #D004 | CDW | Federal-Provincial-Territorial Committee on Drinking Water | high | |
| #D005 | D | disinfectant (parameter type) | high | |
| #D006 | DBP | disinfectant by-product (parameter type) | high | |
| #D007 | HPC | heterotrophic plate count | high | |
| #D008 | I | inorganic chemical (parameter type) | high | |
| #D009 | MAC | maximum acceptable concentration | high | |
| #D010 | NTU | nephelometric turbidity units | high | |
| #D011 | O | organic chemical (parameter type) | high | |
| #D012 | OG | operational guidance value | high | |
| #D013 | P | pesticide (parameter type) | high | |
| #D014 | QMRA | quantitative microbial risk assessment | high | |
| #D015 | T | treatment-related (parameter type) | high | |
| #D016 | TCU | true colour units | high | |
| #D017 | Guidelines | maximum acceptable concentrations or treatment goals | high | |
| #D018 | Objective | established taking into account available treatment technology and analytical methods in order to reduce exposure through drinking water | high | |
| #D019 | Bq/L | becquerel/litre | high | |
| #D020 | mSv/year | millisievert per year | high | |
| #D021 | Problem formulation | a high-level summary of the scientific data needed to determine a path forward for a specific parameter or issue | high | |
| #D022 | Aesthetic objectives | Aesthetic objectives (e.g., for taste or odour) are provided when they play a role in determining whether consumers will consider the water drinkable. | high | |
| #D023 | Operational guidance values | Operational guidance values are provided when a substance may interfere with or impair a treatment process or technology (e.g., turbidity interfering with chlorination or UV disinfection) or adversely affect drinking water infrastructure (e.g., corrosion of pipes). | high | |
| #D024 | Haloacetic acids - Total (HAAs) | Refers to the total of monochloroacetic acid (MCA), dichloroacetic acid (DCA), trichloroacetic acid (TCA), monobromoacetic acid (MBA) and dibromoacetic acid (DBA) | high | |
| #D025 | Trihalomethanes (THMs) | Refers to the total of chlorodibromomethane, chloroform, bromodichloromethane and bromoform | high | |
| #D026 | Guidance document | advice provided to convey operational or management information related to a substance or issue of concern | high | |
| #D027 | Enterococci | bacteriological indicator of fecal contamination | high | |
| #D028 | E. coli | an indicator of fecal contamination that is used as a tool to verify the quality of the drinking water | high | |
| #D029 | Total coliforms | used as a tool to determine how well the drinking water treatment system is operating and to indicate water quality changes in the distribution system | high | |
| #D030 | Total dissolved solids (TDS) | primarily composed of calcium, magnesium, sodium, potassium, carbonate, bicarbonate, chloride, and sulphate | high | |
| #D031 | Per-and polyfluoroalkyl substances (PFAS) | Synthetic chemicals used in consumer products and fire-fighting foams for their water and oil repellant properties. | high | |
| #D032 | Methaemoglobinaemia | blue baby syndrome | high |