Cadmium
Chemical Groups: Inorganic, Metals
Also Known As:
CASRN: 7440-43-9
Water Quality Guidelines for the Protection of Aquatic Life
Freshwater
Short Term Concentration (µg/L) Equation
The short-term benchmark concentration of 1.0 µg·L-1 is for waters of 50 mg CaCO3·L-1 hardness.
The short-term benchmark for cadmium is related to water hardness (as CaCO3):
When the water hardness is 0 to < 5.3 mg/L, the short-term benchmark is 0.11 μg/L
At hardness ≥ 5.3 to ≤ 360 mg/L, the short-term benchmark is calculated using this equation (see calculator below)
Short-term benchmark (μg/L) = 10{1.016(log[hardness]) – 1.71 }
At hardness > 360 mg/L, the short-term benchmark is 7.7 μg/L
Enter water hardness here:
mg/L CaCO3
Calculated cadmium short-term benchmark:
μg/L
Long Term Concentration (µg/L) Equation
The CWQG for cadmium (i.e. long-term guideline) of 0.09 µg·L-1 is for waters of 50 mg CaCO3·L-1 hardness.
The CWQG for cadmium is related to water hardness (as CaCO3):
When the water hardness is > 0 to < 17 mg/L, the CWQG is 0.04 μg/L
At hardness ≥ 17 to ≤ 280 mg/L, the CWQG is calculated using this equation (see calculator below)
CWQG (μg/L) = 10{0.83(log[hardness]) – 2.46 }
At hardness > 280 mg/L, the CWQG is 0.37 μg/L
Enter water hardness here:
mg/L CaCO3
Calculated cadmium guideline:
μg/L
Date 2014
Marine
Short Term Concentration (µg/L) NRG
Long Term Concentration (µg/L) 0.12
This value was not assessed as part of the present update; value is from CCME (1996).
Date 2014
Water Quality Guidelines for the Protection of Agriculture
Irrigation
Concentration (µg/L) 5.1
Guideline values slightly modified from CCREM 1987 + Appendixes due to re-evaluation of the significant figures.
Guideline is crop specific (see fact sheet)
Date 1996
Livestock
Concentration (µg/L) 80
Date 1996
Sediment Quality Guidelines for the Protection of Aquatic Life
Freshwater
Concentration (µg/kg dry weight) ISQG 600
Guideline | % ≤ ISQG | ISQG < % < PEL | % ≥ PEL |
---|---|---|---|
Cadmium | 11 | 12 | 47 |
Concentration (µg/kg dry weight) PEL 3500
Guideline | % ≤ ISQG | ISQG < % < PEL | % ≥ PEL |
---|---|---|---|
Cadmium | 11 | 12 | 47 |
Date 1997
Marine
Concentration (µg/kg dry weight) ISQG 700
Guideline | % ≤ ISQG | ISQG < % < PEL | % ≥ PEL |
---|---|---|---|
Cadmium | 6 | 20 | 71 |
Concentration (µg/kg dry weight) PEL 4200
Guideline | % ≤ ISQG | ISQG < % < PEL | % ≥ PEL |
---|---|---|---|
Cadmium | 6 | 20 | 71 |
Date 1997
Soil Quality Guidelines for the Protection of Environmental and Human Health
Concentration (mg/kg dry weight) Agricultural 1.4
Data are sufficient and adequate to calculate a Soil Quality Guideline for Human Health (SQGHH) and a Soil Quality Guideline for Environmental Health (SQGE). Therefore the soil quality guideline is the lower of the two and represents a fully integrated de novo guideline for this land use, derived in accordance with the soil protocol (CCME 1996;2006). The corresponding interim soil quality criterion (CCME 1991) is superseded by the soil quality guideline.
For guidelines derived prior to 2004, differentiation between soil texture (coarse/fine) is not applicable.
Concentration (mg/kg dry weight) Residential/ parkland 10
The soil-plant-human pathway was not considered in the guideline derivation. If produce gardens are present or planned, a site-specific objective must be derived to take into account the bioaccumulation potential (e.g., adopt the agricultural guideline as objective). The off-site migration check should be recalculated accordingly.
For guidelines derived prior to 2004, differentiation between soil texture (coarse/fine) is not applicable.
Concentration (mg/kg dry weight) Commercial 22
Data are sufficient and adequate to calculate a Soil Quality Guideline for Human Health (SQGHH) and a Soil Quality Guideline for Environmental Health (SQGE). Therefore the soil quality guideline is the lower of the two and represents a fully integrated de novo guideline for this land use, derived in accordance with the soil protocol (CCME 1996;2006). The corresponding interim soil quality criterion (CCME 1991) is superseded by the soil quality guideline.
For guidelines derived prior to 2004, differentiation between soil texture (coarse/fine) is not applicable.
Concentration (mg/kg dry weight) Industrial 22
Data are sufficient and adequate to calculate a Soil Quality Guideline for Human Health (SQGHH) and a Soil Quality Guideline for Environmental Health (SQGE). Therefore the soil quality guideline is the lower of the two and represents a fully integrated de novo guideline for this land use, derived in accordance with the soil protocol (CCME 1996;2006). The corresponding interim soil quality criterion (CCME 1991) is superseded by the soil quality guideline.
For guidelines derived prior to 2004, differentiation between soil texture (coarse/fine) is not applicable.
Date 1999
Tissue Residue Quality Guidelines for the Protection of Widlife Consumer of Aquatic Biota
Concentration (µg/L) No data
Date No data
Groundwater Quality Guidelines for the Protection of Environmental and Human Health
(Coarse Soil) Concentration (mg/L) - Agricultural/Residential No data
(Coarse Soil) Concentration (mg/L) - Commercial/Industrial No data
(Fine Soil) Concentration (mg/L) - Agricultural/Residential No data
(Fine Soil) Concentration (mg/L) - Commercial/Industrial No data
Date No data
Resources
- Cadmium - Scientific Criteria Document for the Development of the Canadian Water Quality Guidelines for the Protection of Aquatic Life (2014)
- Cadmium - Canadian Water Quality Guidelines for the Protection of Aquatic Life (2014)
- Cadmium - Canadian Water Quality Guidelines for the Protection of Agricultural Water Uses (1999)
- Cadmium - Canadian Sediment Quality Guidelines for the Protection of Aquatic Life (1999)
- Cadmium - Canadian Soil Quality Guidelines for the Protection of Environmental and Human Health (1999)