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Document ID ca-dtdgcdwq-2022-12-23-4 Title Draft technical document guidelines for Canadian drinking water quality - Antimony: Analytical and treatment considerations URL https://www.canada.ca/en/health-canada/programs/consultation-draft-technical-document-guidelines-canadian-drinking-water-quality-antimony/analytical-treatment-considerations.html Jurisdiction /ca Subdomain(s) Drinking water, Water treatment, Analytical methods Language en Status completed Analyzed at 2026-03-19 09:18:16.475202+00:00 Relevance Provides draft technical guidance on analytical methods and treatment for antimony.

Q Qualitative Requirements (14)

Req ID Category Intent Legal Status Name Subdomain(s) Context Conditions Confidence
#Q001administrativeoperationalrecommendedLaboratory Sampling Requirements Discussiondrinking waterDrinking water utilities should discuss sampling requirements with the accredited laboratory conducting the analysis to ensure that quality control procedures are met and that MRLs are low enough to ensure accurate monitoring at concentrations below the proposed MAC.When setting up antimony analysis with accredited laboratorieshigh
#Q002monitoringreportingmandatoryTotal Antimony Analysis Requirementdrinking waterAnalysis of total antimony is needed for comparison to the proposed MAC.When comparing sample results against the maximum acceptable concentration (MAC)high
#Q003monitoringoperationalrecommendedDissolved Antimony Field Filtrationdrinking waterIn order to determine dissolved antimony concentrations, samples should be filtered at the time of collection (not at the laboratory) and the filtrate should be acidified to pH < 2 with concentrated nitric acid.When determining dissolved antimony concentrationshigh
#Q004designtreatmentrecommendedBench and Pilot-Scale Testing Recommendationdrinking waterPilot- and bench-scale testing is recommended to ensure the source water can be successfully treated and to optimize operating conditions.When selecting an appropriate municipal-scale treatment process for antimonyhigh
#Q005treatmentoperationalmandatoryReverse Osmosis Post-Treatment pH and Alkalinity Adjustmentdrinking waterTherefore, the product water pH must be adjusted and alkalinity may need to be increased to avoid corrosion issues in the distribution system such as the leaching of lead and copper (Schock and Lytle, 2011; U.S. EPA, 2012).When utilizing reverse osmosis (RO) membrane filtration processeshigh
#Q006designtreatmentmandatoryCombined Treatment Pilot Testingdrinking waterGiven that only bench-scale studies are available, it is critical to conduct bench- and pilot-scale studies prior to full-scale implementation to ensure the effectiveness of combined treatment and its optimal operating conditions.Prior to full-scale implementation of combined treatment processes (coagulation followed by ultrafiltration)high
#Q007monitoringtreatmentrecommendedPre-Installation Source Water Testingdrinking waterBefore a treatment unit is installed, the water should be tested to determine the general water chemistry and antimony concentration in the source water.Prior to the installation of a residential drinking water treatment unithigh
#Q008monitoringoperationalrecommendedPeriodic Residential Treatment Unit Testingdrinking waterPeriodic testing by an accredited laboratory should be conducted on both the water entering the treatment unit and the treated water, to verify that the treatment unit is effective.After installation of a residential drinking water treatment unithigh
#Q009operationaloperationalrecommendedResidential Unit Maintenance Verificationdrinking waterConsumers should verify the expected longevity of the components in the treatment unit according to the manufacturer's recommendations and service it when required.For operation of residential drinking water treatment unitshigh
#Q010designhealthrecommendedCertified Treatment Unit Usedrinking waterHealth Canada does not recommend specific brands of drinking water treatment units, but it strongly recommends that consumers use units that have been certified by an accredited certification body as meeting the appropriate NSF International Standard/American National Standards Institute (NSF/ANSI) for drinking water treatment units.When selecting residential drinking water treatment unitshigh
#Q011designtreatmentmandatoryRO System Selection for Antimonydrinking waterTherefore, an RO system will need to be carefully selected in order to achieve treated water concentrations below the proposed MAC.When using RO residential treatment units for antimony removalhigh
#Q012designoperationalrecommendedPoint-of-Use Installation for RO and Distillationdrinking waterTherefore, these devices should be installed only at the point-of-use.Installation of residential RO and distillation unitshigh
#Q013prohibitionoperationalguidanceAvoidance of Uncontrolled Water Blendingdrinking waterIt is also important to avoid the uncontrolled blending of surface water with groundwater and of chlorinated water with chloraminated water.To maintain water stability for deposited trace inorganic contaminants within the distribution systemhigh
#Q014administrativereportingrecommendedConsultation on Residuals Managementdrinking waterThe appropriate authorities should be consulted to ensure that the disposal of liquid and solid waste residuals from the treatment of drinking water meet applicable regulations.When disposing of liquid and solid waste residuals from water treatmenthigh

P Quantitative Requirements (43)

Req ID Category Intent Legal Status Name Subdomain(s) Limit Type Limit Value Context Conditions Confidence
#P001chemicalhealthmandatoryAntimonydrinking waterrequirement<= 0.0006 mg/LNSF/ANSI Standards 61 and 60 require that the concentration of antimony not exceed the single product allowable concentration of 0.0006 mg/L in components and treatment chemicals, respectively.Applicable to materials (components and treatment chemicals) in contact with drinking water.high
#P002chemicalhealthmandatoryAntimonydrinking waterMAC0.006 mg/LU.S. EPA drinking water standard for antimony of 0.006 mg/L.high
#P003physicaloperationalrecommendedpHdrinking waterrequirement< 2 pHIn order to determine dissolved antimony concentrations, samples should be filtered at the time of collection (not at the laboratory) and the filtrate should be acidified to pH < 2 with concentrated nitric acid.For determination of dissolved antimony concentrations.high
#P004physicaloperationalguidanceTurbiditydrinking waterrequirement> 1 NTUEPA methods 200.5, 200.8, 200.9 and SM 3113B do not require hot acid digestion for total recoverable metals, unless turbidity of the sample is greater than 1 nephelometric turbidity unit (NTU).Condition triggering the requirement for hot acid digestion for total recoverable metals.high
#P005chemicalreportingguidelineAntimony Method Reporting Limit (ICP-MS)drinking waterrequirement0.5 to 1 μg/LA number of accredited laboratories in Canada reported MRLs for total antimony analysis using methods based on ICP-MS.Applicable to total antimony analysis using ICP-MS methods.high
#P006chemicaltreatmentguidanceAntimony Adsorption Breakthrough Thresholddrinking watertreatment_goal6 μg/LAdsorption using titanium-based adsorbents reached breakthrough of 6 μg/L at specified bed volumes and pH.Applied in pilot-scale testing for groundwater treatment.high
#P007chemicaltreatmentguidanceAntimony Pilot Breakthrough Thresholddrinking watertreatment_goal5 μg/LPilot-scale tests evaluated the number of bed volumes to reach a specific breakthrough concentration.Applicable to spring water treatment using iron-based and CeO2·nH2O adsorbents.high
#P008designoperationalguidelineAntimony content in lead-free brassdrinking waterrequirement<= 0.25 %Non-leaded brass and lead-free brass generally contain a specific maximum percentage of antimony.Material composition of plumbing devices and brass materials.high
#P009chemicalhealthguidelineAntimonydrinking waterrequirement<= 0.0006 mg/LNSF/ANSI Standards 61 and 60 require that the concentration of antimony not exceed the single product allowable concentration of 0.0006 mg/L in components and treatment chemicals, respectively.Applicable to materials (components and treatment chemicals) in contact with drinking water.high
#P010designoperationalguidelineAntimony content in brass (high range)drinking waterrequirement0.5 %Non-leaded brass and lead-free brass generally contain a maximum of 0.25% antimony and in some cases as high as 0.5%.Upper range for specific brass material compositions used in plumbing devices.high
#P011chemicalreportingguidelineAntimony Method Detection Limit (EPA 200.5)drinking waterrequirement0.9 μg/LStandardized analytical methods available for the analysis of total antimony in drinking water.Method: Axially viewed inductively coupled plasma-atomic emission spectrometry (wavelength 249.68 nm).high
#P012chemicalreportingguidelineAntimony Method Detection Limit (EPA 200.8 Scanning)drinking waterrequirement0.4 μg/LStandardized analytical methods available for the analysis of total antimony in drinking water.Method: ICP-MS in scanning mode.high
#P013chemicalreportingguidelineAntimony Method Detection Limit (EPA 200.8 SIM)drinking waterrequirement0.04 μg/LStandardized analytical methods available for the analysis of total antimony in drinking water.Method: ICP-MS in selective ion monitoring mode.high
#P014chemicalreportingguidelineAntimony Method Detection Limit (EPA 200.9)drinking waterrequirement0.8 μg/LStandardized analytical methods available for the analysis of total antimony in drinking water.Method: Stabilized temperature graphite furnace atomic absorption.high
#P015chemicalreportingguidelineAntimony Instrument Detection Level (EPA 6020B)drinking waterrequirement0.1 μg/LStandardized analytical methods available for the analysis of total antimony in drinking water.Method: ICP-MS.high
#P016chemicalreportingguidelineAntimony Estimated Detection Level (SM 3113B)drinking waterrequirement0.8 μg/LStandardized analytical methods available for the analysis of total antimony in drinking water.Method: Electrothermal atomic absorption spectrometry.high
#P017chemicalreportingguidelineAntimony Instrument Detection Level (SM 3125)drinking waterrequirement0.07 μg/LStandardized analytical methods available for the analysis of total antimony in drinking water.Method: ICP-MS.high
#P018chemicalreportingguidelineAntimony Instrument Detection Level (ASTM D5673-16)drinking waterrequirement0.08 μg/LStandardized analytical methods available for the analysis of total antimony in drinking water.Method: ICP-MS.high
#P019chemicalreportingguidanceAntimony Detection Limits (Provincial)drinking waterrequirement0.001 to 2 μg/LThe MDLs or MRLs from provincial data are in the range of 0.001 to 2 μg/L.Based on Canadian provincial water exposure data.high
#P020chemicaloperationalmandatoryNSF/ANSI 61 Test Water Free Chlorinedrinking waterrequirement2.0 (± 0.05) mg/LSynthetic test water specifications for leaching tests.NSF/ANSI 61 Section 9 synthetic test water.high
#P021physicaloperationalmandatoryNSF/ANSI 61 Test Water Alkalinitydrinking waterrequirement500 (± 25) mg/L as CaCO3Synthetic test water specifications for leaching tests.NSF/ANSI 61 Section 9 synthetic test water.high
#P022physicaloperationalguidanceCalcium/Magnesium Matrix Interference Thresholddrinking waterrequirement> 125 mg/LMatrix interferences for EPA Method 200.5Applicable when using Axially viewed ICP-AEShigh
#P023physicaloperationalguidanceSilicon Matrix Interference Thresholddrinking waterrequirement> 250 mg/LMatrix interferences for EPA Method 200.5Applicable when using Axially viewed ICP-AEShigh
#P024physicaloperationalguidanceTDS Matrix Interference Thresholddrinking waterrequirement> 0.2 % (w/v)Matrix interferences for EPA Method 200.8 and 6020BApplicable when using ICP-MShigh
#P025chemicaloperationalguidanceHydrochloric Acid Stabilization Concentrationdrinking waterrequirement1 % (v/v)Sb concentrations of 50–500μg/L require 1% (v/v) HCl for stabilityEPA Method 6020B (ICP-MS)high
#P026designtreatmentguidanceEmpty Bed Contact Time (Adsorption)drinking watertreatment_goal2.5 minAntimony was removed by all media at an empty bed contact time of 2.5 minutesPilot-scale study using TiO2, ferric oxide and ferric hydroxidehigh
#P027physicaloperationalguidelineAggressive Leaching Solution Alkalinitydrinking waterrequirement10 mg/L as CaCO3Specifications for aggressive leaching solution used in brass leaching testsSynthetic water used for experimental protocolhigh
#P028physicaloperationalguidelineAggressive Leaching Solution pHdrinking waterrequirement7.4 pHSpecifications for aggressive leaching solution used in brass leaching testsSynthetic water used for experimental protocolhigh
#P029chemicaloperationalguidelineAggressive Leaching Solution Chloraminesdrinking waterrequirement4.0 mg/L Cl2Specifications for aggressive leaching solution used in brass leaching testsSynthetic water used for experimental protocolhigh
#P030physicaloperationalmandatoryNSF/ANSI 61 Section 9 Synthetic Test Water pHdrinking waterrequirement8.0 (± 0.5) pHSynthetic test water specification for leaching tests from end point devicesNSF/ANSI 61 Section 9high
#P031designtreatmentguidanceHydraulic Retention Time (Combined Technology)drinking watertreatment_goal2.2 hourProcess description for coagulation and flocculation followed by ultrafiltrationBench-scale study for Sb(V) removalhigh
#P032designtreatmentguidanceMembrane Flux (Combined Technology)drinking watertreatment_goal30 L/m2·hProcess description for coagulation and flocculation followed by ultrafiltrationBench-scale study for Sb(III) removalhigh
#P033physicaloperationalguidanceSodium Matrix Interference Thresholddrinking waterrequirement> 125 mg/LMatrix interference for standardized analytical methods.Applicable to EPA Method 200.5 using axially viewed ICP-AES.high
#P034designtreatmentguidanceAntimony Removal (Ferric-based Coagulation)drinking watertreatment_goal95 %Bench-scale performance of conventional coagulation for antimony removal.Achieved at low pH (pH 5.1) using ferric-based coagulants.high
#P035designtreatmentguidanceMedia Life (Titanium-based Adsorbent - Alta Pilot)drinking watertreatment_goal100,000 bed volumesTreatment capacity of titanium-based media in pilot testing.To reach breakthrough concentration of 6 μg/L at pH 6.5.high
#P036designtreatmentguidanceMedia Life (TiO2 Adsorbent - Park City Pilot)drinking watertreatment_goal170,000 bed volumesExpected media change interval for titanium dioxide media.Operated at pH 6.5 for removal of antimony and co-occurring contaminants.high
#P037designtreatmentguidanceMedia Life (Ferric Oxide Adsorbent)drinking watertreatment_goal12,000 to 18,000 bed volumesEstimated change frequency for ferric oxide media at Park City pilot site.Required change frequency based on pH 6.5 operating conditions.high
#P038designtreatmentguidanceMedia Life (Ferric Hydroxide Adsorbent)drinking watertreatment_goal29,000 to 50,000 bed volumesEstimated change frequency for ferric hydroxide media at Park City pilot site.Required change frequency based on pH 6.5 operating conditions.high
#P039chemicalhealthmandatoryAntimony Single Product Allowable Concentrationdrinking waterrequirement<= 0.0006 mg/LNSF/ANSI Standards 61 and 60 require that the concentration of antimony not exceed the single product allowable concentration of 0.0006 mg/L in components and treatment chemicals, respectively.Applicable to materials (components and treatment chemicals) in contact with drinking water.high
#P040chemicalhealthmandatoryAntimony (US EPA Standard)drinking waterMAC0.006 mg/LTheoretically, 60% to 85% of the scale deposit would need to be released to exceed the U.S. EPA drinking water standard for antimony of 0.006 mg/L.Benchmark used for calculating potential distribution system release risk.high
#P041physicaloperationalguidelineDissolved Solids Limit (SM 3125)drinking waterrequirement<= 0.5 %Analytical method SM 3125 (ICP-MS) specifies a concentration limit for dissolved solids to ensure measurement accuracy.Applicable during the analysis of total antimony using Standard Method 3125.high
#P042chemicaltreatmentguidanceAntimony Removal (Reverse Osmosis)drinking watertreatment_goal46 to 99 %Anticipated removals of antimony using reverse osmosis based on municipal-scale data.Efficiency is dependent on membrane type and water pH.high
#P043chemicalreportingguidelineAntimony Solder Leaching Detection Limitdrinking waterrequirement1.2 μg/LStudies evaluating the leaching of metals from copper pipes with non-lead-based solders used this detection limit.Referenced in Subramanian et al. (1991, 1994) long-term leaching studies.high

D Definitions (42)

Req ID Category Name Context Confidence
#D001MDLsmethod detection limitshigh
#D002MRLsmethod reporting limitshigh
#D003ICP-MSinductively coupled plasma – Mass Spectrometryhigh
#D004NTUnephelometric turbidity unithigh
#D005ROreverse osmosishigh
#D006Sb(III)antimonitehigh
#D007Sb(V)antimonatehigh
#D008FCferric chloridehigh
#D009HCO3-bicarbonatehigh
#D010SO42-sulfatehigh
#D011PO43-phosphatehigh
#D012HAhumic acidhigh
#D013NOMnatural organic matterhigh
#D014BVsbed volumeshigh
#D015TiO2titanium dioxidehigh
#D016U.S. EPAUnited States Environmental Protection Agencyhigh
#D017TMPtransmembrane pressurehigh
#D018NSF/ANSINSF International Standard/American National Standards Institutehigh
#D019SCCStandards Council of Canadahigh
#D020Total antimonyincludes both the dissolved and particulate (suspended) fractions of antimony in a water samplehigh
#D021FeCl3H2Ohydrated ferric chloridehigh
#D022Sb(III)antimonite in the form of Sb(OH)3high
#D023Sb(V)antimonate an anion in the form of Sb(OH)6-high
#D024Section 8 devicesin-line devices (for example, water meters, building valves)high
#D025Section 9 devicesend point devices (for example, drinking water fountains, faucets)high
#D026opportunity samplessamples that became available including those from water meters, pipes and filtershigh
#D027IDLinstrument detection levelhigh
#D028TDStotal dissolved solidshigh
#D029DOCdissolved organic carbonhigh
#D030In-situ FeOxHyfreshly prepared ferric hydroxidehigh
#D031EBCTempty bed contact timehigh
#D032HRThydraulic retention timehigh
#D033injinjectionhigh
#D034TOCtotal organic carbonhigh
#D035DLdetection limithigh
#D036Nsample sizehigh
#D037SMAPHA standard methodshigh
#D038N/Anot availablehigh
#D039BVbed volumeshigh
#D040ANSIAmerican National Standards Institutehigh
#D041NSFNSF Internationalhigh
#D042MDLmethod detection limithigh