| Req ID | Category | Intent | Legal Status | Name | Subdomain(s) | Context | Conditions | Confidence |
|---|---|---|---|---|---|---|---|---|
| #Q001 | corrective_action | unknown | guidance | Additional Investigation for Exceedances | other | An exceedance of the WQGs presented in this document, however, does not imply that unacceptable risks are present, but that the potential for adverse effects is increased and additional investigation and monitoring may be warranted. | When there is an exceedance of the Water Quality Guidelines (WQGs). | high |
| #Q002 | monitoring | operational | recommended | Ongoing Ecological Monitoring | other | To that end, ongoing ecological monitoring is encouraged to ensure the WQG is indeed protective under field conditions. | high | |
| #Q003 | operational | health | recommended | Lead Reduction in Oyster Growing Areas | aquatic life | Special efforts should be made to reduce lead levels even further in oyster growing areas | Applicable in oyster growing areas (as cited from U.S. EPA 1972 criteria) | medium |
| #Q004 | monitoring | reporting | recommended | 30-Day Average Sampling Frequency | aquatic life | (a) The average concentration of total lead in water over a 30-day period (based on a minimum of 5 weekly samples) should not exceed 2 µg/L at any time. | When calculating the 30-day average concentration of total lead. | high |
| #Q005 | administrative | operational | recommended | Site-Specific Allowance for High Natural Lead | aquatic life | (c) If natural levels exceed (a) or (b) above, then the increase in total lead to be allowed, if any, should be based on site-specific conditions. | If natural levels exceed the recommended 30-day average or maximum criteria for total lead. | high |
| #Q006 | monitoring | operational | recommended | 30-Day Average Sampling Frequency | aquatic life | The average concentration of total lead in water over a 30-day period (based on a minimum of 5 weekly samples) should not exceed 2 µg/L at any time. | When assessing compliance with the 30-day average guideline for marine aquatic life. | high |
| #Q007 | monitoring | operational | recommended | Marine Aquatic Life 30-Day Average and Sample Distribution | aquatic life | The average concentration of total lead in water over a 30-day period (based on a minimum of 5 weekly samples) should not exceed 2 µg/L at any time. Not more than 20% (e.g., 1 in 5) of the values in a 30-day period should exceed 3 µg/L. | Applicable when assessing compliance with marine aquatic life guidelines. | high |
| Req ID | Category | Intent | Legal Status | Name | Subdomain(s) | Limit Type | Limit Value | Context | Conditions | Confidence |
|---|---|---|---|---|---|---|---|---|---|---|
| #P001 | chemical | health | recommended | Lead | aquatic life | MAC | <= 2 µg/L | Marine Aquatic Life | Average concentration over a 30-day period | high |
| #P002 | chemical | health | recommended | Lead | aquatic life | MAC | <= 3 µg/L | Marine Aquatic Life | Not more than 20% (e.g., 1 in 5) of the values in a 30-day period should exceed this concentration | high |
| #P003 | chemical | health | recommended | Lead | aquatic life | MAC | <= 140 µg/L | Marine Aquatic Life | Maximum concentration at any time | high |
| #P004 | chemical | health | recommended | Lead | other | MAC | <= 100 µg/L | Wildlife Water Supply | Maximum concentration at any time | high |
| #P005 | chemical | health | recommended | Lead | agricultural water | MAC | <= 100 µg/L | Livestock Water Supply | Maximum concentration at any time | high |
| #P006 | chemical | health | recommended | Lead | agricultural water | MAC | <= 400 µg/L | Irrigation Water Supply | Neutral and alkaline fine textured soils; maximum concentration at any time | high |
| #P007 | chemical | health | recommended | Lead | agricultural water | MAC | <= 200 µg/L | Irrigation Water Supply | Continuous use on all other soils; maximum concentration at any time | high |
| Req ID | Category | Name | Context | Confidence |
|---|---|---|---|---|
| #D001 | WQG | a scientifically derived numerical concentration or narrative statement considered to be protective of designated values in ambient conditions | high | |
| #D002 | Pb | lead | high | |
| #D003 | Eh | oxidationreduction potential | high | |
| #D004 | ALA-D | δ-aminolevulinic acid dehydratase | high | |
| #D005 | b.w. | body weight | high | |
| #D006 | d.m. | dry matter | high | |
| #D007 | CEC | cation exchange capacity | high | |
| #D008 | WLRS | British Columbia Ministry of Water, Land, and Resource Stewardship | high | |
| #D009 | EC50 | 50% reduction in growth rate and maximum yield of the organisms | high | |
| #D010 | δ-ALA | δ-aminolevulinic acid | high | |
| #D011 | IWD | Inland Waters Directorate | high | |
| #D012 | criteria | ambient water quality guidelines | high | |
| #D013 | B.C. | British Columbia | high | |
| #D014 | chronic value | the geometric mean of the lower and upper limits | high | |
| #D015 | PbS | Galena or lead glance | high | |
| #D016 | mysid | Mysidopsis bahia | high | |
| #D017 | coontail | Ceratophyllum demersum | high | |
| #D018 | Interim WQGs | WQGs developed when the available toxicological data are insufficient | high | |
| #D019 | no-effect concentration | an estimate where no effects are expected if exposure concentrations are below the WQG | high | |
| #D020 | CCME | Canadian Council of Ministers of the Environment | high | |
| #D021 | sheepshead minnow | Cyprinodon variegatus | high | |
| #D022 | mummichog | Fundulus heteroclitus | high | |
| #D023 | inland silverside | Menidia beryllina | high | |
| #D024 | Atlantic silverside | Menidia menidia | high | |
| #D025 | soft-shell clam | Mya arenaria | high | |
| #D026 | blue mussel | Mytilus edulis | high | |
| #D027 | pacific oyster | Crassostrea gigas | high | |
| #D028 | eastern oyster | Crassostrea virginica | high | |
| #D029 | quahog clam | Mercenaria mercenaria | high | |
| #D030 | Dungeness crab | Cancer magister | high | |
| #D031 | gadwall | Anas strepera | high | |
| #D032 | redhead | Aythya americana | high | |
| #D033 | canvas back | Aythya valisneria | high | |
| #D034 | ringnecked ducks | Aythya collaris | high | |
| #D035 | suckers | Catostomidae | high | |
| #D036 | teal | Amus sp. | high | |
| #D037 | shoveler | Spatula clypeata | high | |
| #D038 | Copepod | Acartia clausti | high | |
| #D039 | lesser scaup | a species of duck | high | |
| #D040 | saltwater alga | Champia parvula | high | |
| #D041 | saltwater alga | Dunaliella tertiolecta | high | |
| #D042 | saltwater diatom | Ditylurn brightwelli | high | |
| #D043 | saltwater diatom | Astrionella japonica | high | |
| #D044 | ENV | British Columbia Ministry of Environment and Climate Change Strategy | high | |
| #D045 | U.S. EPA | U.S. Environmental Protection Agency | high | |
| #D046 | CCREM | Canadian Council of Resource and Environment Ministers | high | |
| #D047 | mallards | Anarsplaty hyrchas | high |