| #Q001 | design | treatment | recommended | Ion Exchange Pilot Studies | drinking water | Pilot studies should be conducted in order to verify the effectiveness of ion exchange technology for site-specific water quality. | When considering ion exchange technology for selenium removal. | high |
| #Q002 | design | health | recommended | Ion Exchange Resin Selection | drinking water | To minimize nitrosamine formation, attention should be paid when selecting strong-base ion exchange resins (Kimoto et al., 1980; Najm and Trussell, 2001). | When selecting strong-base ion exchange resins. | high |
| #Q003 | treatment | operational | mandatory | RO Feed Water Pretreatment | drinking water | A pretreatment of the feed water is required to prevent scaling and fouling of the RO membranes. | When using reverse osmosis (RO) membrane systems. | high |
| #Q004 | treatment | treatment | mandatory | RO Product Water Post-treatment | drinking water | The product water typically requires post-treatment, consisting of pH and alkalinity adjustments. | When using reverse osmosis (RO) membrane systems. | high |
| #Q005 | treatment | treatment | mandatory | RO Post-treatment Corrosion Control | drinking water | In most cases, post-treatment corrosion control measures need to be undertaken. | Following reverse osmosis (RO) treatment. | high |
| #Q006 | design | operational | mandatory | Activated Alumina Chemical Handling Consideration | drinking water | Utilities need to consider the chemical handling and disposal requirements prior to selecting this treatment technology (U.S. EPA, 1989, 1998). | Prior to selecting activated alumina treatment technology. | high |
| #Q007 | design | treatment | mandatory | Electrodialysis Pilot Testing | drinking water | Utilities planning to utilize electrodialysis for the reduction of selenium, total dissolved solids and other trace metals would require pilot plant testing of the feed water in order to verify the effectiveness of selenium removal. | Utilities planning to utilize electrodialysis. | high |
| #Q008 | treatment | treatment | recommended | Ferric Oxide Media pH Adjustment | drinking water | At pH values greater than 8.0 to 8.5, pH adjustment is recommended to ensure adsorption capacity is maintained. | When using ferric oxide media at pH values greater than 8.0 to 8.5. | high |
| #Q009 | treatment | operational | recommended | Avoidance of Additional Treatment on Municipal Water | drinking water | Generally, it is not recommended that drinking water treatment devices be used to provide additional treatment to municipally treated drinking water. | For municipally treated drinking water at the residential scale. | high |
| #Q010 | monitoring | treatment | recommended | Well Water Pre-installation Testing | drinking water | Before a treatment device is installed, the well water should be tested to determine general water chemistry and to verify the concentration of selenium. | Before installing a residential treatment device on a private well. | high |
| #Q011 | monitoring | treatment | recommended | Testing for Competing Ions | drinking water | The testing should also include assessing the presence and concentration of competing ions (e.g., sulphate, nitrate, chloride) and organic matter in the water, which could interfere with selenium removal. | Before installing a residential treatment device on a private well. | high |
| #Q012 | treatment | operational | mandatory | Device Maintenance and Replacement | drinking water | Devices can lose removal capacity through usage and time and need to be maintained and/or replaced. | Over the operational lifespan of residential drinking water treatment devices. | high |
| #Q013 | operational | operational | recommended | Consumer Verification of Component Longevity | drinking water | Consumers should verify the expected longevity of the components in their treatment device as per the manufacturer's recommendations. | When using residential drinking water treatment devices. | high |
| #Q014 | design | health | recommended | Use of Certified Devices | drinking water | Health Canada does not recommend specific brands of drinking water treatment devices, but it strongly recommends that consumers use devices that have been certified by an accredited certification body as meeting the appropriate NSF/ANSI drinking water treatment unit standards. | When selecting residential drinking water treatment devices. | high |
| #Q015 | administrative | operational | mandatory | Accreditation of Certification Organizations | drinking water | Certification organizations provide assurance that a product conforms to applicable standards and must be accredited by the Standards Council of Canada (SCC). | For certification organizations verifying NSF/ANSI standards in Canada. | high |
| #Q016 | treatment | operational | guidance | Residential RO Feed Water Pretreatment | drinking water | A consumer may need to pretreat the influent water to reduce fouling and extend the service life of the membrane. | When using reverse osmosis (RO) drinking water treatment systems at residential scale. | high |
| #Q017 | operational | operational | mandatory | Ion Exchange Resin Regeneration | drinking water | Once the resin has reached its capacity (i.e., when all the resin sites are occupied by the contaminant ion), the resin must be regenerated to reverse the process. | Once ion exchange resin capacity is reached. | high |
| #Q018 | operational | operational | mandatory | Activated Alumina Bed Regeneration | drinking water | When adsorption sites on the activated alumina surface become filled, the bed must be regenerated. | When adsorption sites on activated alumina are filled. | high |
| #Q019 | operational | operational | mandatory | Activated Alumina Operational Considerations | drinking water | When employing activated alumina technology, operational issues that must be considered include the degradation of activated alumina through the regeneration process and the fouling of the activated alumina bed, resulting in an increase in headloss across the media bed. | When employing activated alumina technology. | high |
| #Q020 | operational | reporting | mandatory | RO Concentrate Disposal | drinking water | the concentrate discharge must be disposed of appropriately. | Disposal of reject water/brine from RO systems. | high |
| #Q021 | design | health | mandatory | NSF/ANSI Standard 61 Selenium Leaching Limit | drinking water | When materials are certified to the standard, the concentration of selenium must not exceed the single product allowable concentration of 0.005 mg/L (NSF/ANSI, 2011a). | For materials certified to NSF/ANSI Standard 61. | high |
| #Q022 | design | treatment | mandatory | NSF/ANSI Residential Device Performance Requirement | drinking water | Drinking water treatment devices certified to NSF/ANSI Standards 53, 58 and 62 specifically for selenium removal, must be capable of reducing the concentration of selenium in water from an influent (challenge) concentration of 0.1 mg/L (added as 0.05 mg/L for Se(IV) and 0.05 mg/L for Se(VI)) to a maximum final (effluent) concentration of 0.05 mg/L (NSF/ANSI, 2009a,b, 2011b). | When devices are certified specifically for selenium removal under NSF/ANSI 53, 58, or 62. | high |
| #Q023 | design | treatment | mandatory | NSF/ANSI 62 TDS Surrogate Performance Requirement | drinking water | Treatment devices certified to NSF/ANSI Standard 62 using TDS as a surrogate, must achieve a minimum TDS reduction of 99.0% from an influent (challenge) concentration of 1000 mg/L(NSF/ANSI, 2009b). | When devices are certified using TDS as a surrogate under NSF/ANSI 62. | high |
| #Q024 | prohibition | treatment | mandatory | Small System BAT Restriction | drinking water | Conventional coagulation/filtration and lime softening processes are not defined as BATs for small systems unless these treatment processes are currently in place (U.S. EPA, 1991c). | For small water systems evaluating Best Available Technologies (BATs) for selenium removal. | high |
| #Q025 | design | treatment | guideline | Residential RO Point-of-Use Limitation | drinking water | RO systems certified to NSF/ANSI Standard 58 (Reverse Osmosis Drinking Water Treatment Systems) are intended for point-of-use installation only. | When using residential RO systems certified to Standard 58. | high |
| #Q026 | design | treatment | guideline | Residential Distillation Point-of-Use Limitation | drinking water | Distillation systems certified to NSF/ANSI Standard 62 (Drinking Water Distillation Systems) are also intended for point-of-use installation only. | When using residential distillation systems certified to Standard 62. | high |
| #Q027 | design | treatment | recommended | Ion Exchange Se(IV) Speciation Consideration | drinking water | The ion exchange behaviour of the monovalent biselenite form (HSeO3−) and divalent form (SeO32−) should be considered, as the monovalent anion is less preferred than the divalent anion (Maneval et al., 1985). | When considering the ion exchange removal of Se(IV). | high |
| #Q028 | operational | operational | mandatory | Manganese Greensand Bed Regeneration | drinking water | When the manganese greensand bed is exhausted, the bed is regenerated to restore its oxidizing capacity. | When using manganese greensand filtration and the bed is exhausted. | high |
| #Q029 | operational | operational | mandatory | Activated Alumina Surveillance and Maintenance | drinking water | The technology requires adequate surveillance and maintenance, including the use of concentrated acids (sulphuric acid or hydrochloric acid) and base (sodium hydroxide) for regeneration of activated alumina. | When employing activated alumina technology. | high |