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Document ID ca-gcdwqgtd-2020-06-19-2 Title Guidelines for Canadian drinking water quality: Guideline technical document – Total coliforms URL http://www.canada.ca/en/health-canada/services/publications/healthy-living/guidelines-canadian-drinking-water-quality-guideline-technical-document-total-coliforms.html Jurisdiction /ca Subdomain(s) Drinking water, Water treatment, Monitoring and analysis Language en Status completed Analyzed at 2026-03-19 08:01:36.003092+00:00 Relevance National technical guideline for drinking water quality and treatment.

Q Qualitative Requirements (62)

Req ID Category Intent Legal Status Name Subdomain(s) Context Conditions Confidence
#Q001monitoringoperationalrecommendedDistribution system monitoringdrinking waterTotal coliforms should be monitored in the distribution system because they are used to indicate changes in water quality.Applies to the distribution systemhigh
#Q002corrective_actionoperationalrecommendedInvestigation of total coliform detectiondrinking waterDetection 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.Consecutive samples from same site or >10% positive in a given sampling periodhigh
#Q003monitoringoperationalrecommendedTreatment plant water monitoringdrinking waterTotal coliforms should be monitored at least weekly in water leaving a treatment plant.Municipal-scale systems, water leaving a treatment planthigh
#Q004corrective_actionhealthrecommendedNotification and resampling for positive coliformdrinking waterThe presence of any total coliform bacteria in water leaving a treatment plant indicates a serious breach in treatment and is therefore unacceptable. This situation should be corrected immediately. The system owner should notify all responsible authorities and immediately reanalyze the coliform-positive sample(s) for Escherichia coli (E. coli), resample, and test the positive site(s) to confirm the presence or absence of both E. coli and total coliformsWhen any total coliform bacteria are detected in water leaving a treatment planthigh
#Q005corrective_actionhealthrecommendedCarrying out corrective actionsdrinking waterIf corrective actions are deemed necessary, the owner of the drinking water treatment system, in consultation with the responsible authorities, should carry out appropriate corrective actionsWhen deemed necessary based on assessment of problem significance and extenthigh
#Q006corrective_actionhealthrecommendedConditions to rescind boil water advisorydrinking waterA boil water advisory should be rescinded only after a minimum of two consecutive sets of samples, collected 24 hours apart, show negative results that demonstrate full system-wide integrity (including acceptable bacteriological quality, disinfection residuals, and/or turbidity).Prior to rescinding an active boil water advisoryhigh
#Q007treatmenttreatmentrecommendedMinimum treatment for surface water/GUDIdrinking waterMinimum treatment of supplies derived from surface water or GUDI sources should include adequate filtration (or technologies providing an equivalent log removal/inactivation) and disinfection to ensure the removal/inactivation of enteric protozoa and enteric viruses.Supplies derived from surface water or GUDI sourceshigh
#Q008operationaltreatmentrecommendedMaintenance of disinfectant residualdrinking waterIn all systems with a distribution system, a disinfectant residual should be maintained at all times.Systems with a distribution systemhigh
#Q009monitoringhealthrecommendedTesting of new or rehabilitated wellsdrinking waterNew or rehabilitated wells should also be tested before use to confirm the microbiological quality.Before use of new or rehabilitated wellshigh
#Q010monitoringhealthrecommendedResampling of residential-scale suppliesdrinking waterIf a sample contains total coliform bacteria, it should be immediately reanalyzed and the positive site resampled and tested to confirm the presence or absence of both E. coli and total coliforms.When a residential-scale sample is positive for total coliformshigh
#Q011operationaloperationalrecommendedDechlorination of discharged waterdrinking waterWater should be dechlorinated before being discharged into the environment. The responsible authority should be consulted regarding the methods available, as well as the correct procedure, for carrying out dechlorinationWhen discharging flushed or shock-chlorinated water into the environmenthigh
#Q012administrativereportingrecommendedCompliance with directed analytical methodsdrinking waterAll analyses for total coliforms should be carried out as directed by the responsible authority.high
#Q013operationalreportingrecommendedQuality assurance programdrinking waterTo ensure reliable results, a quality assurance (QA) program, which incorporates quality control (QC) practices, should be in place.When performing analytical testinghigh
#Q014monitoringoperationalmandatorySample collection proceduresdrinking waterProper procedures for collecting samples must be observed to ensure that the samples are representative of the water being examined.high
#Q015monitoringoperationalrecommendedSample transportation temperaturedrinking waterThe sample should be transported to the laboratory in a cooler containing ice or cooling packs (at 5 ± 3°C), to minimize changes in populations and concentrationsDuring sample transporthigh
#Q016monitoringoperationalrecommendedProtection from freezing during transportdrinking waterSamples should be protected from direct contact with the ice or cooling packs to prevent freezing during transport.During sample transporthigh
#Q017reportingreportingrecommendedReporting collection or storage issuesdrinking waterWater utilities should record any collection or storage related issues and report them to the laboratory, so that results can be properly interpreted.If issues arise during sample collection or storagehigh
#Q018monitoringreportingrecommendedMinimum sample examination volumedrinking waterA minimum volume of 100 mL of water should be examined to obtain a reliable estimate of the number of organisms (using MTF or MF) or to obtain an accurate presence-absence result at the expected low levels in treated drinking water.high
#Q019monitoringhealthrecommendedMinimum testing frequency for treated waterdrinking waterAs a minimum, water leaving a treatment plant should be tested daily for disinfectant residual and turbidity and at least weekly for total coliforms as part of the verification process in a source-to-tap approach.For water leaving a treatment planthigh
#Q020monitoringoperationalrecommendedDisinfectant residual and turbidity concurrent testingdrinking waterDisinfectant residual and turbidity analyses tests should be conducted when bacteriological samples are taken in the distribution system.When taking bacteriological samples in the distribution systemhigh
#Q021administrativeoperationalmandatoryApproval of sampling point locationsdrinking waterIn municipal-scale systems, the location of sampling points must be selected or approved by the responsible authority.Municipal-scale systemshigh
#Q022operationaltreatmentrecommendedDisinfection and residual maintenancedrinking waterIn general, all drinking water supplies should be disinfected, and a disinfectant residual should be maintained throughout the distribution system at all times.All drinking water supplieshigh
#Q023monitoringhealthrecommendedPeriodic testing of treatment devicesdrinking waterPeriodic testing for E. coli and total coliforms by an accredited laboratory should be conducted on both the water entering the treatment device and the treated water to verify that the treatment device is effective.For residential/small scale treatment deviceshigh
#Q024operationaloperationalrecommendedServicing of treatment devicesdrinking waterTreatment devices should be inspected and serviced in accordance with the maintenance schedule and manufacturer's recommendations.high
#Q025monitoringoperationalrecommendedRegular monitoring of distribution systemsdrinking waterDistribution system water quality should be regularly monitored.high
#Q026operationaloperationalrecommendedImplementation of protection and optimization measuresdrinking waterIn addition to regularly monitoring distribution system water quality, source water protection measures should be implemented, along with treatment optimization, maintenance of physical/hydraulic integrity of the distribution system, and minimization of negative- or low-pressure eventshigh
#Q027administrativehealthrecommendedConsumer notification of contamination incidentdrinking waterIn the event that an incident that may have contaminated the distribution system or interfered with treatment is known to the owner, consumers should be notified immediately to boil the drinking water.When a contamination incident or treatment interference is known to the ownerhigh
#Q028monitoringhealthrecommendedMunicipal distribution sampling frequencydrinking waterIn municipal-scale distribution and storage systems, the number of samples collected for total coliform testing should reflect the size of the population being served, with a minimum of four samples per month.Municipal-scale distribution and storage systemshigh
#Q029operationalhealthrecommendedPhysical condition verification for residential-scale systemsdrinking waterThe first step is to verify the physical condition of the drinking water system, as applicable, including water intake, well, well head, pump, treatment system (including chemical feed equipment, if present), plumbing, and surrounding area. Any identified faults should be corrected before proceeding.Corrective action step for residential-scale disinfected supplieshigh
#Q030monitoringoperationalrecommendedSample labeling requirementsdrinking waterSamples should be labelled with the time, date, location, type of sample (e.g., raw water, distribution system), sampler's name, and identification number (if used), along with the disinfectant residual measurements and any special conditions.high
#Q031monitoringoperationalrecommendedMaximum sample holding timedrinking waterIdeally, for total coliform analysis of drinking water samples, the holding time between the collection of the sample and the beginning of its examination should not exceed 30 hours.high
#Q032operationaloperationalrecommendedO&M programs and hygiene during repairsdrinking waterOperations and maintenance programs should be in place (e.g., watermain cleaning, cross-connection control, asset management) and strict hygiene should be practiced during watermain repairs to ensure drinking water is transported to the consumer with minimum loss of quality.high
#Q033monitoringoperationalrecommendedMinimum Corrective Action Samplingdrinking waterAt a minimum, one sample upstream and one sample downstream from the original sample site(s) plus the finished water from the treatment plant as it enters the distribution system should be tested.When sampling and testing sites adjacent to positive sample sites during corrective actionshigh
#Q034corrective_actiontreatmentrecommendedNon-Disinfected Well Shock Chlorinationdrinking waterShock-chlorinate the well and plumbing system.Corrective action for non-disinfected wells with acceptable physical conditionshigh
#Q035monitoringoperationalrecommendedResidential Well Confirmatory Test Timingdrinking waterConfirmatory tests should be done no sooner than either 48 hours after tests indicate the absence of a chlorine residual or five days after the well has been treated.After shock-chlorination and flushing of non-disinfected wellshigh
#Q036monitoringhealthrecommendedLong-Term Follow-Up Testingdrinking waterAn additional test should be taken after three to four months to ensure that the contamination has not reoccurred.Long-term follow-up for residential well contaminationhigh
#Q037monitoringoperationalrecommendedRepresentative Sampling Locationsdrinking waterIn general, samples should be taken at the point where the water enters the system and from representative points throughout the distribution system.Selection of distribution system sampling pointshigh
#Q038monitoringoperationalrecommendedTargeted Area Samplingdrinking waterThe majority of samples should be taken from potential problem areas: low-pressure zones, reservoirs, dead ends, areas at the periphery of the system farthest from the treatment plant, and areas with a poor previous record.Distribution system monitoringhigh
#Q039operationaltreatmentrecommendedHypochlorite Certification Requirementdrinking waterPrivate and semi-public supplies that use liquid chlorine should use hypochlorite solutions that are certified as meeting NSF/ANSI/CAN Standard 60 (NSF/ANSI/CAN, 2018)When using liquid chlorine for disinfectionhigh
#Q040administrativehealthrecommendedOutbreak Advisory Consultationdrinking waterIf enhanced health surveillance indicates that a waterborne outbreak may be occurring or if conditions exist that could result in a waterborne outbreak, then the necessity of issuing a boil water advisory should be discussed immediately with qualified operations personnel at the water utility and with the responsible authority.During potential waterborne outbreaks or high-risk conditionshigh
#Q041operationalreportingrecommendedTest Kit Performance Requirementsdrinking waterIn addition to the QA/QC program, any test kits used should meet minimum requirements for accuracy, detection (sensitivity), and reproducibility, and be used according the manufacturer's instructions.When using commercial test kits for analysishigh
#Q042administrativeoperationalrecommendedSampling Problem Consultationdrinking waterAny on-going problems with sampling and/or transportation should be discussed with the responsible authority.Presence of persistent sampling or transport issueshigh
#Q043monitoringoperationalrecommendedTimely Examination Commencementdrinking waterTo avoid unpredictable changes in the bacterial flora of the sample, examination should be started as soon as possible after collection.high
#Q044operationaltreatmentrecommendedOperator CT/IT Value Maintenancedrinking waterThus operators should understand and maintain the required CT/IT values (where CT = concentration of disinfectant x contact time, and IT = intensity of UV light x contact time, see sections 7.1.3.1 and 7.3.1.2 for descriptions of the CT and IT concepts, respectively) for primary disinfection, in addition to disinfectant residual requirements for secondary disinfection.Primary disinfection operationshigh
#Q045treatmenthealthrecommendedPoint-of-Use Device Equippingdrinking waterTo minimize the potential health risks from the use of microbiologically-contaminated drinking water, it is important to note that in the absence of a point-of-entry system, all points of water used for drinking, food and beverage preparation, hygiene or washing dishes should be equipped with a point-of-use treatment device.Residential-scale systems without point-of-entry treatmenthigh
#Q046operationaloperationalrecommendedConsumer Maintenance and Verificationdrinking waterConsumers should verify the expected longevity of the components in their treatment device according to the manufacturer's recommendations and establish a clearly defined maintenance schedule.Ownership of residential-scale treatment deviceshigh
#Q047monitoringhealthrecommendedRisk-Based Residential Sampling Frequencydrinking waterSampling frequencies for residential-scale systems will be determined by the authority having jurisdiction for the system and should include times when the risk of contamination is greatest, for example, early spring after the thaw, after an extended dry spell, or following heavy rains.Residential-scale system monitoring programshigh
#Q048monitoringhealthrecommendedInvestigative Phase Samplingdrinking waterContinue selected sampling and testing (e.g., bacteriology, disinfectant residual, turbidity) of all identified sites during the investigative phase to confirm the extent of the problem and to verify the success of the corrective actionsDuring the investigative phase following the detection of total coliforms in municipal systemshigh
#Q049corrective_actionhealthrecommendedRetesting After Flushingdrinking waterFlush the system thoroughly and retest to confirm that the water is free of total coliform contamination.Following shock-chlorination of non-disinfected wellshigh
#Q050monitoringhealthrecommendedConfirmatory Negative Samplesdrinking waterA minimum of two consecutive total coliform-negative samples should be obtained.To confirm a problem has been corrected in residential-scale non-disinfected wellshigh
#Q051administrativereportingrecommendedAnalytical Method Performance Measuresdrinking waterWater utilities should establish performance measures regarding method sensitivity and specificity when selecting analytical methods for internal analysis or when purchasing laboratory services.high
#Q052monitoringoperationalrecommendedDelayed Examination Proceduredrinking waterWhen delays are anticipated, a delayed incubation procedure should be employed or consideration given to on-site testing.When holding time between collection and examination will exceed recommendations (30 hours)high
#Q053operationaltreatmentmandatoryOperator Training and Process Controldrinking waterAdequate process control measures and operator training are also required to ensure the effective operation of treatment barriers at all timeshigh
#Q054monitoringoperationalrecommendedMulti-source samplingdrinking waterIf the water supply is obtained from more than one source, the location of sampling points in the system should ensure that water from each source is periodically sampled.Applies when water supply is obtained from more than one sourcehigh
#Q055treatmenttreatmentmandatoryTreatment target achievement pointdrinking waterIt is essential that the removal and disinfection targets are achieved before drinking water reaches the first consumer in the distribution system.high
#Q056monitoringoperationalrecommendedRemote area repeat sampling proceduredrinking waterif normal transportation time exceeds the above recommendations, the sample should be processed and arrangements made to have another sample collected as soon as the first sample is received.When normal transportation time exceeds recommended holding times (remote areas)high
#Q057administrativeoperationalmandatoryAuthority oversight of distribution monitoringdrinking waterThe sampling points and testing frequencies for total coliforms, residual disinfectant, and turbidity in treated water within distribution and storage systems will be specified and/or approved by the responsible authority.high
#Q058corrective_actionhealthmandatoryResidential Coliform Source Investigationdrinking waterRegardless of whether a boil water advisory is issued, the source of the coliforms needs to be investigated, and appropriate actions need to be taken (see Appendix B).When total coliforms are detected in residential-scale supplieshigh
#Q059monitoringoperationalrecommendedSite-Specific Sampling Frequency Assessmentdrinking watersystems should conduct a site-specific assessment to ensure that their sampling frequency meets the requirements of the responsible authority.Municipal-scale distribution system monitoringhigh
#Q060monitoringoperationalrecommendedStorage Data Recording for Delayed Samplesdrinking waterWhen examination will be delayed, it is particularly important to record the duration and temperature of storage, as this information should be taken into consideration when interpreting the results.When sample examination is delayedhigh
#Q061administrativeoperationalrecommendedRemote Area Holding Time Consultationdrinking waterIn remote areas, up to 48 hours may be an acceptable time interval; however, the implications of the extended holding time should be discussed with the responsible authorities.When sample holding time in remote areas extends up to 48 hourshigh
#Q062prohibitionhealthrecommendedSurface Water Supply Restrictiondrinking waterIn general, surface water is not recommended as a private or semi-public water supply unless it is properly filtered, disinfected and monitored for water quality.Private or semi-public water supplieshigh

P Quantitative Requirements (50)

Req ID Category Intent Legal Status Name Subdomain(s) Limit Type Limit Value Context Conditions Confidence
#P001microbiologicalhealthmandatorytotal coliformsdrinking waterMACnone detectable per 100 mLin water leaving a treatment plant and in non-disinfected groundwater leaving the wellApplies to water leaving a treatment plant and non-disinfected groundwater leaving the wellhigh
#P002microbiologicaloperationalrecommendedtotal coliformsdrinking watertreatment_goal> 10 %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.Applies to distribution systemshigh
#P003microbiologicaltreatmentmandatoryenteric protozoadrinking watertreatment_goal>= 3 logminimum 3 log or 99.99% removal and/or inactivationSurface water or GUDI systemshigh
#P004microbiologicaltreatmentmandatoryenteric virusesdrinking watertreatment_goal>= 4 logminimum 4 log or 99.99% removal and/or inactivationSurface water, GUDI systems, and groundwater systemshigh
#P005physicaloperationalrecommendedStorage temperaturedrinking waterrequirement5 ± 3 °CThe sample should be transported to the laboratory in a cooler containing ice or cooling packs (at 5 ± 3°C)Sample transportationhigh
#P006operationaloperationalrecommendedholding timedrinking waterrequirement<= 30 hoursthe holding time between the collection of the sample and the beginning of its examination should not exceed 30 hours.Ideally, for total coliform analysis of drinking water sampleshigh
#P007physicaloperationalrecommendedMinimum volumedrinking waterrequirement>= 100 mLA minimum volume of 100 mL of water should be examined to obtain a reliable estimate of the number of organismsWater sample collectionhigh
#P008designtreatmentmandatoryUV dosedrinking waterrequirement>= 40 mJ/cm2UV systems certified to NSF/ANSI Standard 55 Class A are designed to deliver a UV dose at least equivalent to 40 mJ/cm2Class A UV systemshigh
#P009microbiologicaltreatmentmandatorybacteria and bacterial sporesdrinking waterrequirement>= 6 logTo meet this standard, a distillation system must provide a minimum 6 log reduction of bacteria and bacterial spores.NSF/ANSI Standard 62 for Drinking Water Distillation Systemshigh
#P010operationaloperationalrecommendedtotal coliforms monitoring frequency (treatment plant)drinking waterrequirement>= 1 per weekTotal coliforms should be monitored at least weekly in water leaving a treatment plant.Water leaving a treatment planthigh
#P011operationaloperationalrecommendedtotal coliforms monitoring frequency (distribution system)drinking waterrequirement>= 4 samples per monthIn municipal-scale distribution and storage systems, the number of samples collected for total coliform testing should reflect the size of the population being served, with a minimum of four samples per month.Municipal-scale distribution and storage systemshigh
#P012operationalreportingmandatoryboil water advisory rescinding criteria (sample sets)drinking waterrequirement>= 2 consecutive sets of samplesA boil water advisory should be rescinded only after a minimum of two consecutive sets of samples... show negative results.Rescinding a boil water advisoryhigh
#P013operationalreportingmandatoryboil water advisory rescinding criteria (sampling interval)drinking waterrequirement>= 24 hoursA boil water advisory should be rescinded only after a minimum of two consecutive sets of samples, collected 24 hours apart...Rescinding a boil water advisoryhigh
#P014operationaloperationalrecommendedwell confirmatory testing (no chlorine residual)drinking waterrequirement>= 48 hoursConfirmatory tests should be done no sooner than either 48 hours after tests indicate the absence of a chlorine residual...Retesting after shock-chlorination of non-disinfected wellshigh
#P015operationaloperationalrecommendedwell confirmatory testing (post-treatment)drinking waterrequirement>= 5 daysConfirmatory tests should be done no sooner than ... five days after the well has been treated.Retesting after shock-chlorination of non-disinfected wellshigh
#P016operationaloperationalrecommendedrecommended sampling frequency (pop up to 5000)drinking waterrequirement4 samples per monthMinimum number of samples per month for population served up to 5000.Distribution system monitoringhigh
#P017operationaloperationalrecommendedrecommended sampling frequency (pop 5000-90,000)drinking waterrequirement1 per 1000 persons (samples per month)Minimum number of samples per month for population served between 5000 and 90,000.Distribution system monitoringhigh
#P018operationaloperationalrecommendedrecommended sampling frequency (pop 90,000+)drinking waterrequirement90 + (1 per 10,000) persons (samples per month)Minimum number of samples per month for population served over 90,000.Distribution system monitoringhigh
#P019chemicaltreatmentguidancefree chlorine CT for E. coli inactivationdrinking watertreatment_goal0.034-0.05 mg·min/LCT values for 99% inactivation at 5°C using Free chlorine.pH 6-7high
#P020physicaltreatmentguidanceUV dose for E. coli inactivationdrinking watertreatment_goal4.1-14 mJ/cm2UV light dose required for inactivation of E. coli.3-log (99.9%) inactivationhigh
#P021operationaloperationalrecommendedWell retest (long term)drinking waterrequirement3-4 monthsAn additional test should be taken after three to four months to ensure that the contamination has not reoccurred.Post-corrective actions for residential-scale wellshigh
#P022operationaloperationalrecommendedSample holding time (remote)drinking waterrequirement<= 48 hoursIn remote areas, up to 48 hours may be an acceptable time interval; however, the implications of the extended holding time should be discussed with the responsible authorities.When travel to lab exceeds standard limitshigh
#P023operationaloperationalrecommendedTreatment plant monitoring frequencydrinking waterrequirement>= 1 per dayAs a minimum, water leaving a treatment plant should be tested daily for disinfectant residual and turbidityWater leaving treatment planthigh
#P024chemicaltreatmentguidanceChloramines CT for E. coli inactivationdrinking watertreatment_goal95-180 mg·min/LCT values for 99% inactivation at 5°C using chloraminespH 8-9high
#P025chemicaltreatmentguidanceChlorine dioxide CT for E. coli inactivationdrinking watertreatment_goal0.4-0.75 mg·min/LCT values for 99% inactivation at 5°C using chlorine dioxidepH 6-7high
#P026chemicaltreatmentguidanceOzone CT for E. coli inactivationdrinking watertreatment_goal0.02 mg·min/LCT values for 99% inactivation at 5°C using ozonepH 6-7high
#P027physicaltreatmentguidanceUV dose for Cryptosporidium inactivationdrinking watertreatment_goal12 mJ/cm2UV light dose required for inactivation of Cryptosporidium3-log inactivationhigh
#P028physicaltreatmentguidanceUV dose for Adenovirus inactivationdrinking watertreatment_goal129-167 mJ/cm2UV light dose required for inactivation of Adenovirus3-log inactivationhigh
#P029physicaltreatmentguidanceUV dose for Rotavirus inactivationdrinking watertreatment_goal23-29 mJ/cm2UV light dose required for inactivation of Rotavirus3-log inactivationhigh
#P030physicaltreatmentguidanceUV dose for Giardia inactivationdrinking watertreatment_goal11 mJ/cm2UV light dose required for inactivation of Giardia3-log inactivationhigh
#P031designtreatmentmandatoryStandard Jurisdictional UV Dosedrinking waterrequirement>= 40 mJ/cm2Many jurisdictions require a minimum UV dose of 40 mJ/cm2 on the basis that 4 log inactivation can be achieved for most pathogensGeneral requirement across multiple Canadian jurisdictionshigh
#P032designtreatmentguidanceUltrafiltration membrane pore sizedrinking waterrequirement< 0.1 µmFor semi-public systems requiring higher capacity, membranes with this pore size should be effective for bacterial reduction.Semi-public systems not certified for bacterial reductionhigh
#P033operationaloperationalrecommendedOptimal sample analysis windowdrinking waterrequirement6-8 hoursWhere on-site facilities are available or when an accredited laboratory is within an acceptable travel distance, analysis within this time is suggested.Proximity to accredited lab or on-site facilityhigh
#P034chemicaltreatmentguidanceFree chlorine CT for Giardia lamblia inactivationdrinking watertreatment_goal65-93 mg·min/LCT values required for 99% (2-log) inactivation at 5°CpH 6-7high
#P035chemicaltreatmentguidanceFree chlorine CT for Viruses inactivationdrinking watertreatment_goal4.0 mg·min/LCT values required for 99% (2-log) inactivation at 5°CpH 6.0-9.0high
#P036physicaltreatmentguidanceUV dose for 4-log E. coli inactivationdrinking watertreatment_goal5.0-18 mJ/cm2UV light dose required for 99.99% inactivationBased on U.S. EPA (2003) datahigh
#P037physicaltreatmentguidanceUV dose for 4-log Protozoa inactivationdrinking watertreatment_goal22 mJ/cm2UV light dose required for 4-log inactivation of Cryptosporidium and GiardiaStandard treatment targets for protozoahigh
#P038operationaloperationalrecommendedgroundwater repeat sampling countdrinking waterrequirement>= 10 samplesgroundwater sources should be sampled multiple times (i.e., 10 or more) to determine their sanitary statusdetermination of sanitary statushigh
#P039operationaloperationalrecommendedMTF test series primary volumedrinking waterrequirement50 mLFor the MTF method, a test series consisting of one 50-mL volume and five 10-mL volumes is suggested by the WHOMTF method testinghigh
#P040designtreatmentguidanceconventional filtration bacterial removaldrinking watertreatment_goal2.1 log (mean)Range of log removals from filtration studieshigh
#P041designtreatmentguidanceslow sand filtration bacterial removaldrinking watertreatment_goal2.7 log (mean)Range of log removals from filtration studieshigh
#P042designtreatmentguidanceultrafiltration bacterial removaldrinking watertreatment_goal> 7 log (mean)Range of log removals from filtration studiespore size 0.01-0.1 µmhigh
#P043operationaloperationalrecommendedadjacent site sampling countdrinking waterrequirement>= 1 sample(s)At a minimum, one sample upstream and one sample downstream from the original sample site(s) plus the finished water from the treatment plant should be tested.Response to positive sample at original sitehigh
#P044operationaloperationalrecommendedMTF test series secondary volumesdrinking waterrequirement5 10-mL volumesFor the MTF method, a test series consisting of one 50-mL volume and five 10-mL volumes is suggested by the World Health OrganizationWater expected to be of good qualityhigh
#P045designtreatmentguidancedirect filtration bacterial removaldrinking watertreatment_goal1.4 log (mean)Range of log removals from filtration studieshigh
#P046designtreatmentguidancemicrofiltration pore sizedrinking waterrequirement0.1-1 µmPhysical removal characteristics of filtration technologiesStandard microfiltration definitionhigh
#P047microbiologicaloperationalguidelinetotal coliform incubation temperaturedrinking waterrequirement35 °CStandard Methods characterization of coliform bacteriaDuring 24-48 hour fermentation or colony developmenthigh
#P048microbiologicaloperationalguidelinethermotolerant coliform incubation temperaturedrinking waterrequirement44.5 °CPortion of the total coliform group capable of forming gas within 24 hours at this temperaturePreviously referred to as fecal coliformshigh
#P049physicaltreatmentguidanceUV dose for 1-log E. coli inactivationdrinking watertreatment_goal1.5-5 mJ/cm2UV light dose required for specific log inactivation90% (1-log) inactivationhigh
#P050physicaltreatmentguidanceUV dose for 2-log E. coli inactivationdrinking watertreatment_goal2.8-9 mJ/cm2UV light dose required for specific log inactivation99% (2-log) inactivationhigh

D Definitions (49)

Req ID Category Name Context Confidence
#D001thermotolerant coliformsthe portion of the total coliform group capable of forming gas within 24 hours at 44.5°C or that produce a blue colony on m-FC broth within 24 hours at 44.5°Chigh
#D002microbiomethe combined genetic material of these microorganismshigh
#D003inactivationthe pathogen is no longer able to multiply within its host and is therefore non-infectious, although it may still be present.high
#D004AGIacute gastrointestinal illnesshigh
#D005ANSIAmerican National Standards Institutehigh
#D006AOCassimilable organic carbonhigh
#D007ATPadenosine triphosphatehigh
#D008BDOCbiodegradable organic carbonhigh
#D009BGLBbrilliant green lactose bile brothhigh
#D010BOMbiodegradable organic matterhigh
#D011CTconcentration of disinfectant × contact timehigh
#D012DBPdisinfection by-producthigh
#D013E. coliEscherichia colihigh
#D014EUEuropean Unionhigh
#D015GUDIgroundwater under the direct influence of surface waterhigh
#D016HCGIhighly credible gastrointestinal illnesshigh
#D017ISOInternational Organization for Standardizationhigh
#D018ITintensity of UV light × contact timehigh
#D019MACmaximum acceptable concentrationhigh
#D020MFmembranefiltrationhigh
#D021MTFmultiple tubefiltrationhigh
#D022NSFNSFInternationalhigh
#D023OPPPopportunistic premise plumbing pathogenhigh
#D024P-Apresence-absencehigh
#D025PCRpolymerase chain reactionhigh
#D026PEPolyethylenehigh
#D027PVCPolyvinyl chloridehigh
#D028QAquality assurancehigh
#D029QCquality controlhigh
#D030ROreverse osmosishigh
#D031RT-PCRreverse transcription polymerase chain reactionhigh
#D032SCCStandards Council of Canadahigh
#D033U.S.United Stateshigh
#D034U.S. EPAUnited States Environmental Protection Agencyhigh
#D035UVultraviolethigh
#D036WHOWorld Health Organizationhigh
#D037Total coliformsAll facultative anaerobic, Gram-negative, non-spore-forming, rod-shaped bacteria that ferment lactose with gas and acid formation within 48 hours at 35°C; or many facultative anaerobic, Gram-negative, non-spore-forming, rod-shaped bacteria that develop red colonies with a metallic (golden) sheen within 24 hours at 35°C on an Endo- type medium containing lactose; or all bacteria possessing the enzyme β-galactosidasehigh
#D038anaerogenicproducing little or no gashigh
#D039ONPGortho-Nitrophenyl-ß-d-galactopyranosidehigh
#D040T10 valuethe time such that 90% of the water meets or exceeds the required contact timehigh
#D041fluencecomputed dose in mJ/cm2 for a specific microorganismhigh
#D042photoreactivationphoto repairhigh
#D043point-of-entry devicestreat all water entering the systemhigh
#D044point-of-use devicestreat water at only a single location-for example, at the kitchen taphigh
#D045CT conceptwhere CT is the product of 'C' (the residual concentration of disinfectant, measured in mg/L) and 'T' (the disinfectant contact time, measured in minutes)high
#D046IT conceptthe product of light intensity 'I' (measured in mW/cm2 or W/m2) and time 'T' (measured in seconds) results in a computed dose (fluence) in mJ/cm2 for a specific microorganismhigh
#D047Total coliformsTraditionally defined based on phenotypic characteristics, such as the ability to ferment lactose, producing gas and acid; specifically characterized as: all facultative anaerobic, Gram-negative, non-spore-forming, rod-shaped bacteria that ferment lactose with gas and acid formation within 48 hours at 35°C; many facultative anaerobic, Gram-negative, non-spore-forming, rod-shaped bacteria that develop red colonies with a metallic (golden) sheen within 24 hours at 35°C on an Endo-type medium containing lactose; or all bacteria possessing the enzyme β-galactosidase, which cleaves a chromogenic substrate resulting in the release of a chromogen.high
#D048fecal coliformsColiforms that have the ability to ferment lactose at 44 to 45ºC; now more commonly referred to as thermotolerant coliforms.high
#D049BOMBiodegradable organic matter; nutrients that contribute to bacterial regrowth and biofilm development, including assimilable and biodegradable organic carbon.high