Parameter Viewer

Q Qualitative Requirements (4)

Req ID Category Intent Legal Status Name Subdomain(s) Context Conditions Confidence
#Q001operationaloperationalmandatoryUse of Alternate Aquatic Life Benchmarksaquatic lifeIf PMRA does not have an ALRV, the USEPA ALB is used.If PMRA does not have an ALRVhigh
#Q002corrective_actionoperationalguidancePMRA Actions on ALRV Exceedanceaquatic lifeAdditional actions that PMRA may take when ALRVs are exceeded could include: examining information about the use of the pesticide and the current risk management measures in place; collecting additional site-specific data to further identify the risk; conducting a re-evaluation or special review that could result in new risk mitigation measuresWhen ALRVs are exceededhigh
#Q003operationaltreatmentmandatoryCompliance with National Effluent Quality StandardswastewaterThey also set achievable national effluent quality standards for owners and operators of wastewater systems that collect and discharge up to 100 cubic metres or more of effluent per day.wastewater systems that collect and discharge up to 100 cubic metres or more of effluent per dayhigh
#Q004prohibitionunknownmandatoryProhibition of deposit of deleterious substancesaquatic lifeThe Fisheries Act prohibits the deposit of deleterious substances in water bodies containing fish or in any place where the deleterious substances may enter any such water, unless authorized by a federal regulation.unless authorized by a federal regulationhigh

P Quantitative Requirements (13)

Req ID Category Intent Legal Status Name Subdomain(s) Limit Type Limit Value Context Conditions Confidence
#P001chemicalhealthguidance1-bromo-3-chloro-5,5-dimethylhydantoin and related hydantoins - Acute Fish ALRVaquatic lifeunknown200 µg/LAquatic Life Reference Valuehigh
#P002chemicalhealthguidance1-bromo-3-chloro-5,5-dimethylhydantoin and related hydantoins - Acute invertebrate ALRVaquatic lifeunknown235 µg/LAquatic Life Reference Valuehigh
#P003chemicalhealthguidance2,4-D - Acute Fish ALRVaquatic lifeunknown47 µg/LAquatic Life Reference Valuehigh
#P004chemicalhealthguidance2,4-D - Chronic Fish ALRVaquatic lifeunknown120 µg/LAquatic Life Reference Valuehigh
#P005chemicalhealthguidance2,4-D - Acute invertebrate ALRVaquatic lifeunknown> 100 µg/LAquatic Life Reference Valuehigh
#P006chemicalhealthguidance2,4-D - Chronic invertebrate ALRVaquatic lifeunknown15 µg/LAquatic Life Reference Valuehigh
#P007chemicalhealthguidance2,4-D - Non-vascular plants ALRVaquatic lifeunknown94 µg/LAquatic Life Reference Valuehigh
#P008chemicalhealthguidance2,4-D - Vascular plants ALRVaquatic lifeunknown70 µg/LAquatic Life Reference Valuehigh
#P009chemicalhealthguidance2,4-DB - Acute Fish ALRVaquatic lifeunknown3240 µg/LAquatic Life Reference Valuehigh
#P010chemicalhealthguidance2,4-DB - Chronic Fish ALRVaquatic lifeunknown1660 µg/LAquatic Life Reference Valuehigh
#P011chemicalhealthguidance2-methyl-4-isothiazolin-3-one - Acute Fish ALRVaquatic lifeunknown35 µg/LAquatic Life Reference Valuehigh
#P012chemicalhealthguidance4,5-dichloro-2-N-octyl-3(2H)-isothiazolone - Acute Fish ALRVaquatic lifeunknown0.7 µg/LAquatic Life Reference Valuehigh
#P013operationaloperationalmandatoryMinimum wastewater system discharge capacitywastewaterrequirement>= 100 m3/dayOwners and operators of wastewater systems that collect and discharge effluent.Applies to systems collecting and discharging this volume or more per day.high

D Definitions (37)

Req ID Category Name Context Confidence
#D001ECCCEnvironment and Climate Change Canadahigh
#D002AOSRAthabasca Oil Sands Regionhigh
#D003Oil sands tailingsOil sands tailings are a mixture of sand, silt, clay, residual bitumen, and contaminated process-affected water.medium
#D004PAHsPolycyclic aromatic hydrocarbonshigh
#D005UNDRIPUnited Nations Declaration on the Rights of Indigenous Peopleshigh
#D006CIWGCrown-Indigenous Working Grouphigh
#D007ALRVspesticide concentrations in surface water below which risks to aquatic life are not expected.high
#D008Short-term (acute) ALRVsThese are indicative of the possible impacts to the aquatic environment that can come from short-term exposure to high concentrations of a pesticide.high
#D009Long-term (chronic) ALRVsThese are indicative of the possible impacts to the aquatic environment that can come from long-term exposure to pesticide concentrations.high
#D010LC5050 percent lethal concentrationhigh
#D011LD5050 percent lethal dosehigh
#D012EC5050 percent effect concentrationhigh
#D013IC5050 percent inhibition concentrationhigh
#D014NOAECno observed adverse effects concentrationhigh
#D015NOELno observed effect levelhigh
#D016NOECno observed effect concentrationhigh
#D017HC55 percent hazard concentrationhigh
#D018UFuncertainty factorhigh
#D019µg/Lmicrogram per literhigh
#D020PMRAHealth Canada's Pest Management Regulatory Agencyhigh
#D021USEPAUnited States Environmental Protection Agencyhigh
#D022USEPA ALBsUSEPA Aquatic Life Benchmarkshigh
#D023ALRV Year Updatedrefers to the year of publication of the final decision for the assessment upon which the latest ALRV was based.high
#D024ALRV Referencerefers to the published document that contains the toxicity values used to derive the ALRV. Where the ALRV reference indicates "EPA Benchmark", no ALRV was available and the EPA Aquatic Life Benchmark was used.high
#D025Representative CAS numberis a single CAS number associated with the active that has been selected to represent the active for the purposes of data analysis (for example, comparison against water monitoring data available on the Open Government Portal).high
#D026Registered CAS number(s)includes CAS numbers of chemical forms associated with the active as it is currently registered; may include multiple CAS numbers.high
#D027Acute Fish ALRV= Toxicity value x UF. UF = 0.1 for LC50 and EC50 values; no UF is applied to NOEC and HC5 values. The selected toxicity value is usually the lowest acute endpoint in a standardized test; examples of test species are Rainbow Trout (Oncorhynchus mykiss), Fathead Minnow (Pimephales promelas), and Bluegill Sunfish (Lepomis macrochirus). NOECs for acute fish endpoints are based on old methods and are updated as actives go through assessments using new methodology.high
#D028Chronic Fish ALRV= Toxicity value. UFs are not applied to chronic toxicity values. The selected toxicity value is usually the lowest NOEC or NOEL from a life-cycle or early life stage test; examples of test species are Rainbow Trout (Oncorhynchus mykiss), Fathead Minnow (Pimephales promelas), and Bluegill Sunfish (Lepomis macrochirus).high
#D029Acute Invertebrate ALRV= Toxicity value x UF. UF = 0.5 for LC50 and EC50 values; no UF is applied to HC5 values. The selected toxicity value is usually the lowest acute endpoint in a standardized test; test species are generally Chironomus or Daphnia species.high
#D030Chronic Invertebrate ALRV= Toxicity value. UFs are not applied to chronic toxicity values. The selected toxicity value is usually the lowest EC50, NOEC or NOEL from a life-cycle test; test species are generally Chironomus or Daphnia species.high
#D031Non-vascular Plant ALRV= Toxicity value x UF. UF = 0.5 for LC50, EC50 and IC50 values; no UF is applied to NOEC and HC5 values. The selected toxicity value is generally the lowest endpoint in a standardized algae toxicity test.high
#D032Vascular Plant ALRV= Toxicity value x UF. UF = 0.5 for EC50 and IC50 values; no UF is applied to NOEC and HC5 values. The selected toxicity value is generally the lowest endpoint in a standardized plant toxicity test; the test species is usually Lemna gibba.high
#D033n/aindicates that acceptable aquatic toxicity values are not available.high
#D034>derived from a "greater-than" value and may overestimate toxicity.high
#D035<derived from a "less-than" value and may underestimate toxicity.high
#D036algaeaquatic non-vascular plantshigh
#D037decision documentsregulatory decision documents published by PMRA for every pesticide evaluation or re-evaluationhigh