| #D001 | | ECCC | Environment and Climate Change Canada | high |
| #D002 | | AOSR | Athabasca Oil Sands Region | high |
| #D003 | | Oil sands tailings | Oil sands tailings are a mixture of sand, silt, clay, residual bitumen, and contaminated process-affected water. | medium |
| #D004 | | PAHs | Polycyclic aromatic hydrocarbons | high |
| #D005 | | UNDRIP | United Nations Declaration on the Rights of Indigenous Peoples | high |
| #D006 | | CIWG | Crown-Indigenous Working Group | high |
| #D007 | | ALRVs | pesticide concentrations in surface water below which risks to aquatic life are not expected. | high |
| #D008 | | Short-term (acute) ALRVs | These are indicative of the possible impacts to the aquatic environment that can come from short-term exposure to high concentrations of a pesticide. | high |
| #D009 | | Long-term (chronic) ALRVs | These are indicative of the possible impacts to the aquatic environment that can come from long-term exposure to pesticide concentrations. | high |
| #D010 | | LC50 | 50 percent lethal concentration | high |
| #D011 | | LD50 | 50 percent lethal dose | high |
| #D012 | | EC50 | 50 percent effect concentration | high |
| #D013 | | IC50 | 50 percent inhibition concentration | high |
| #D014 | | NOAEC | no observed adverse effects concentration | high |
| #D015 | | NOEL | no observed effect level | high |
| #D016 | | NOEC | no observed effect concentration | high |
| #D017 | | HC5 | 5 percent hazard concentration | high |
| #D018 | | UF | uncertainty factor | high |
| #D019 | | µg/L | microgram per liter | high |
| #D020 | | PMRA | Health Canada's Pest Management Regulatory Agency | high |
| #D021 | | USEPA | United States Environmental Protection Agency | high |
| #D022 | | USEPA ALBs | USEPA Aquatic Life Benchmarks | high |
| #D023 | | ALRV Year Updated | refers to the year of publication of the final decision for the assessment upon which the latest ALRV was based. | high |
| #D024 | | ALRV Reference | refers 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 |
| #D025 | | Representative CAS number | is 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 |
| #D026 | | Registered CAS number(s) | includes CAS numbers of chemical forms associated with the active as it is currently registered; may include multiple CAS numbers. | high |
| #D027 | | Acute 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 |
| #D028 | | Chronic 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 |
| #D029 | | Acute 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 |
| #D030 | | Chronic 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 |
| #D031 | | Non-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 |
| #D032 | | Vascular 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 |
| #D033 | | n/a | indicates 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 |
| #D036 | | algae | aquatic non-vascular plants | high |
| #D037 | | decision documents | regulatory decision documents published by PMRA for every pesticide evaluation or re-evaluation | high |