Polychlorinated dibenzo-p-dioxins/dibenzo furans
Chemical Groups: Organic, Polyaromatic compounds, Polychlorinated dioxins and furans
Also Known As: PCDDs, PCDFs
CASRN:
Water Quality Guidelines for the Protection of Aquatic Life
Freshwater
Short Term Concentration (µg/L) No data
Long Term Concentration (µg/L) No data
Date No data
Marine
Short Term Concentration (µg/L) No data
Long Term Concentration (µg/L) No data
Date No data
Water Quality Guidelines for the Protection of Agriculture
Irrigation
Concentration (µg/L) No data
Date No data
Livestock
Concentration (µg/L) No data
Date No data
Sediment Quality Guidelines for the Protection of Aquatic Life
Freshwater
Concentration (µg/kg dry weight) ISQG 0.85 ng TEQ/kg dry weight
Guideline | % ≤ ISQG | ISQG < % < PEL | % ≥ PEL |
---|---|---|---|
Polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans | 0 | 24 | 46 |
Note:
ISQG and PEL are expressed as toxic equivalency (TEQ) units, based on WHO 1998 TEF values for fish. A safety factor of 10 was applied. See factsheet for details.
Note that the incidence of adverse biological effects below the TEL, between the TEL and PEL, and above the PEL were 22%, 24% and 65%, respectively, prior to the application of a safety factor.
Concentration (µg/kg dry weight) PEL 21.5 ng TEQ/kg dry weight
Guideline | % ≤ ISQG | ISQG < % < PEL | % ≥ PEL |
---|---|---|---|
Polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans | 0 | 24 | 46 |
Note:
ISQG and PEL are expressed as toxic equivalency (TEQ) units, based on WHO 1998 TEF values for fish. A safety factor of 10 was applied. See factsheet for details.
Note that the incidence of adverse biological effects below the TEL, between the TEL and PEL, and above the PEL were 22%, 24% and 65%, respectively, prior to the application of a safety factor.
Date 2001
Marine
Concentration (µg/kg dry weight) ISQG 0.85 ng TEQ/kg dry weight
Values are expressed as toxic equivalency (TEQ) units, based on WHO 1998 TEF values for fish. A safety fator of 10 was applied. See factsheet for details.
Provisional; adoption of freshwater ISQG
Concentration (µg/kg dry weight) PEL 21.5 ng TEQ/kg dry weight
Values are expressed as toxic equivalency (TEQ) units, based on WHO 1998 TEF values for fish. A safety fator of 10 was applied. See factsheet for details.
Provisional; adoption of freshwater PEL
Date 2001
Soil Quality Guidelines for the Protection of Environmental and Human Health
Concentration (mg/kg dry weight) Agricultural 4 ng TEQ.kg-1
Data are sufficient and adequate to calculate only a provisional Soil Quality Guideline for Human Health (SQGHH), which is less than the existing interim soil quality criterion (CCME, 1991). Thus the provisional SQGHH becomes the soil quality guideline, which supersedes the interim soil quality criterion for this land use.
For guidelines derived prior to 2004, differentiation between soil texture (coarse/fine) is not applicable.
Concentration (mg/kg dry weight) Residential/ parkland 4 ng TEQ.kg-1
Data are sufficient and adequate to calculate only a provisional Soil Quality Guideline for Human Health (SQGHH), which is less than the existing interim soil quality criterion (CCME, 1991). Thus the provisional SQGHH becomes the soil quality guideline, which supersedes the interim soil quality criterion for this land use.
For guidelines derived prior to 2004, differentiation between soil texture (coarse/fine) is not applicable.
Concentration (mg/kg dry weight) Commercial 4 ng TEQ.kg-1
Data are sufficient and adequate to calculate only a provisional Soil Quality Guideline for Human Health (SQGHH). An interim soil quality criterion (CCME, 1991) was not established for this land use, therefore the provisional SQGHH becomes 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 4 ng TEQ.kg-1
Data are sufficient and adequate to calculate only a Soil Quality Guideline for Human Health (SQGHH). An interim soil quality criterion (CCME, 1991) was not established for this land use, therefore the SQGHH becomes the soil quality guideline.
For guidelines derived prior to 2004, differentiation between soil texture (coarse/fine) is not applicable.
Date 2002
Tissue Residue Quality Guidelines for the Protection of Widlife Consumer of Aquatic Biota
Concentration (µg/L) Variable
Mammalian: 0.71 ng TEQ/kg diet wet weight
Note: TEQ refers to dioxin toxic equivalents using toxic equivalency factors (TEFs) for PCBs for mammals developed by the World Health Organization in 1998. See fact sheet for supporting document for more details.
Avian: 4.75 ng TEQ/kg diet wet weight
Note: TEQ refers to dioxin toxic equivalents using toxic equivalency factors (TEFs) for PCBs for birds developed by the World Health Organization in 1998. See fact sheet for supporting document for more details.
Interim guideline: see factsheet for details.
Date 2001
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
- Polychlorinated Dioxins and Furans (PCDD/Fs) - Canadian Sediment Quality Guidelines for the Protection of Aquatic Life (2001)
- Polychlorinated Dioxins and Furans (PCDD/Fs) - Canadian Soil Quality Guidelines for the Protection of Environmental and Human Health (2002)
- Polychlorinated Dioxins and Furans (PCDD/Fs) - Canadian Tissue Residue Guidelines for the Protection of Wildlife Consumers of Aquatic Biota (2001)