| #P001 | chemical | health | mandatory | Antimony | drinking water | requirement | <= 0.0006 mg/L | NSF/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 |
| #P002 | chemical | health | mandatory | Antimony | drinking water | MAC | 0.006 mg/L | U.S. EPA drinking water standard for antimony of 0.006 mg/L. | | high |
| #P003 | physical | operational | recommended | pH | drinking water | requirement | < 2 pH | In 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 |
| #P004 | physical | operational | guidance | Turbidity | drinking water | requirement | > 1 NTU | EPA 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 |
| #P005 | chemical | reporting | guideline | Antimony Method Reporting Limit (ICP-MS) | drinking water | requirement | 0.5 to 1 μg/L | A 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 |
| #P006 | chemical | treatment | guidance | Antimony Adsorption Breakthrough Threshold | drinking water | treatment_goal | 6 μg/L | Adsorption 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 |
| #P007 | chemical | treatment | guidance | Antimony Pilot Breakthrough Threshold | drinking water | treatment_goal | 5 μg/L | Pilot-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 |
| #P008 | design | operational | guideline | Antimony content in lead-free brass | drinking water | requirement | <= 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 |
| #P009 | chemical | health | guideline | Antimony | drinking water | requirement | <= 0.0006 mg/L | NSF/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 |
| #P010 | design | operational | guideline | Antimony content in brass (high range) | drinking water | requirement | 0.5 % | 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 |
| #P011 | chemical | reporting | guideline | Antimony Method Detection Limit (EPA 200.5) | drinking water | requirement | 0.9 μg/L | Standardized 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 |
| #P012 | chemical | reporting | guideline | Antimony Method Detection Limit (EPA 200.8 Scanning) | drinking water | requirement | 0.4 μg/L | Standardized analytical methods available for the analysis of total antimony in drinking water. | Method: ICP-MS in scanning mode. | high |
| #P013 | chemical | reporting | guideline | Antimony Method Detection Limit (EPA 200.8 SIM) | drinking water | requirement | 0.04 μg/L | Standardized analytical methods available for the analysis of total antimony in drinking water. | Method: ICP-MS in selective ion monitoring mode. | high |
| #P014 | chemical | reporting | guideline | Antimony Method Detection Limit (EPA 200.9) | drinking water | requirement | 0.8 μg/L | Standardized analytical methods available for the analysis of total antimony in drinking water. | Method: Stabilized temperature graphite furnace atomic absorption. | high |
| #P015 | chemical | reporting | guideline | Antimony Instrument Detection Level (EPA 6020B) | drinking water | requirement | 0.1 μg/L | Standardized analytical methods available for the analysis of total antimony in drinking water. | Method: ICP-MS. | high |
| #P016 | chemical | reporting | guideline | Antimony Estimated Detection Level (SM 3113B) | drinking water | requirement | 0.8 μg/L | Standardized analytical methods available for the analysis of total antimony in drinking water. | Method: Electrothermal atomic absorption spectrometry. | high |
| #P017 | chemical | reporting | guideline | Antimony Instrument Detection Level (SM 3125) | drinking water | requirement | 0.07 μg/L | Standardized analytical methods available for the analysis of total antimony in drinking water. | Method: ICP-MS. | high |
| #P018 | chemical | reporting | guideline | Antimony Instrument Detection Level (ASTM D5673-16) | drinking water | requirement | 0.08 μg/L | Standardized analytical methods available for the analysis of total antimony in drinking water. | Method: ICP-MS. | high |
| #P019 | chemical | reporting | guidance | Antimony Detection Limits (Provincial) | drinking water | requirement | 0.001 to 2 μg/L | The 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 |
| #P020 | chemical | operational | mandatory | NSF/ANSI 61 Test Water Free Chlorine | drinking water | requirement | 2.0 (± 0.05) mg/L | Synthetic test water specifications for leaching tests. | NSF/ANSI 61 Section 9 synthetic test water. | high |
| #P021 | physical | operational | mandatory | NSF/ANSI 61 Test Water Alkalinity | drinking water | requirement | 500 (± 25) mg/L as CaCO3 | Synthetic test water specifications for leaching tests. | NSF/ANSI 61 Section 9 synthetic test water. | high |
| #P022 | physical | operational | guidance | Calcium/Magnesium Matrix Interference Threshold | drinking water | requirement | > 125 mg/L | Matrix interferences for EPA Method 200.5 | Applicable when using Axially viewed ICP-AES | high |
| #P023 | physical | operational | guidance | Silicon Matrix Interference Threshold | drinking water | requirement | > 250 mg/L | Matrix interferences for EPA Method 200.5 | Applicable when using Axially viewed ICP-AES | high |
| #P024 | physical | operational | guidance | TDS Matrix Interference Threshold | drinking water | requirement | > 0.2 % (w/v) | Matrix interferences for EPA Method 200.8 and 6020B | Applicable when using ICP-MS | high |
| #P025 | chemical | operational | guidance | Hydrochloric Acid Stabilization Concentration | drinking water | requirement | 1 % (v/v) | Sb concentrations of 50–500μg/L require 1% (v/v) HCl for stability | EPA Method 6020B (ICP-MS) | high |
| #P026 | design | treatment | guidance | Empty Bed Contact Time (Adsorption) | drinking water | treatment_goal | 2.5 min | Antimony was removed by all media at an empty bed contact time of 2.5 minutes | Pilot-scale study using TiO2, ferric oxide and ferric hydroxide | high |
| #P027 | physical | operational | guideline | Aggressive Leaching Solution Alkalinity | drinking water | requirement | 10 mg/L as CaCO3 | Specifications for aggressive leaching solution used in brass leaching tests | Synthetic water used for experimental protocol | high |
| #P028 | physical | operational | guideline | Aggressive Leaching Solution pH | drinking water | requirement | 7.4 pH | Specifications for aggressive leaching solution used in brass leaching tests | Synthetic water used for experimental protocol | high |
| #P029 | chemical | operational | guideline | Aggressive Leaching Solution Chloramines | drinking water | requirement | 4.0 mg/L Cl2 | Specifications for aggressive leaching solution used in brass leaching tests | Synthetic water used for experimental protocol | high |
| #P030 | physical | operational | mandatory | NSF/ANSI 61 Section 9 Synthetic Test Water pH | drinking water | requirement | 8.0 (± 0.5) pH | Synthetic test water specification for leaching tests from end point devices | NSF/ANSI 61 Section 9 | high |
| #P031 | design | treatment | guidance | Hydraulic Retention Time (Combined Technology) | drinking water | treatment_goal | 2.2 hour | Process description for coagulation and flocculation followed by ultrafiltration | Bench-scale study for Sb(V) removal | high |
| #P032 | design | treatment | guidance | Membrane Flux (Combined Technology) | drinking water | treatment_goal | 30 L/m2·h | Process description for coagulation and flocculation followed by ultrafiltration | Bench-scale study for Sb(III) removal | high |
| #P033 | physical | operational | guidance | Sodium Matrix Interference Threshold | drinking water | requirement | > 125 mg/L | Matrix interference for standardized analytical methods. | Applicable to EPA Method 200.5 using axially viewed ICP-AES. | high |
| #P034 | design | treatment | guidance | Antimony Removal (Ferric-based Coagulation) | drinking water | treatment_goal | 95 % | Bench-scale performance of conventional coagulation for antimony removal. | Achieved at low pH (pH 5.1) using ferric-based coagulants. | high |
| #P035 | design | treatment | guidance | Media Life (Titanium-based Adsorbent - Alta Pilot) | drinking water | treatment_goal | 100,000 bed volumes | Treatment capacity of titanium-based media in pilot testing. | To reach breakthrough concentration of 6 μg/L at pH 6.5. | high |
| #P036 | design | treatment | guidance | Media Life (TiO2 Adsorbent - Park City Pilot) | drinking water | treatment_goal | 170,000 bed volumes | Expected media change interval for titanium dioxide media. | Operated at pH 6.5 for removal of antimony and co-occurring contaminants. | high |
| #P037 | design | treatment | guidance | Media Life (Ferric Oxide Adsorbent) | drinking water | treatment_goal | 12,000 to 18,000 bed volumes | Estimated change frequency for ferric oxide media at Park City pilot site. | Required change frequency based on pH 6.5 operating conditions. | high |
| #P038 | design | treatment | guidance | Media Life (Ferric Hydroxide Adsorbent) | drinking water | treatment_goal | 29,000 to 50,000 bed volumes | Estimated change frequency for ferric hydroxide media at Park City pilot site. | Required change frequency based on pH 6.5 operating conditions. | high |
| #P039 | chemical | health | mandatory | Antimony Single Product Allowable Concentration | drinking water | requirement | <= 0.0006 mg/L | NSF/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 |
| #P040 | chemical | health | mandatory | Antimony (US EPA Standard) | drinking water | MAC | 0.006 mg/L | Theoretically, 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 |
| #P041 | physical | operational | guideline | Dissolved Solids Limit (SM 3125) | drinking water | requirement | <= 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 |
| #P042 | chemical | treatment | guidance | Antimony Removal (Reverse Osmosis) | drinking water | treatment_goal | 46 to 99 % | Anticipated removals of antimony using reverse osmosis based on municipal-scale data. | Efficiency is dependent on membrane type and water pH. | high |
| #P043 | chemical | reporting | guideline | Antimony Solder Leaching Detection Limit | drinking water | requirement | 1.2 μg/L | Studies 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 |