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DCC Equations
DCCs for
Radionuclides
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Resident
Resident Soil DCCs
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
consumption of fruits and vegetables combined with soil
consumption of fruits and vegetables. Both exposed vegetable and root vegetable consumption rates were combined to represent total vegetable consumption.
total
Resident Soil CDIs
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
consumption of fruits and vegetables combined with soil
consumption of fruits and vegetables. Both exposed vegetable and root vegetable consumption rates were combined to represent total vegetable consumption.
Resident Soil 2-D External Exposure DCCs
Direct External Exposure to contamination at infinite depth
Direct External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Resident Soil 2-D External Exposure CDIs
Direct External Exposure to contamination at infinite depth
Direct External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Resident Air DCCs
inhalationexternal exposure to ionizing radiation
total
Resident Air CDIs
inhalationexternal exposure to ionizing radiation
Resident Tap Water DCCs
ingestion of tap waterinhalation (The inhalation exposure route is only calculated for C-14 and H-3 as well as Rn-222, Rn-220, and Rn-219, including their short-lived progeny. Also, volatilization in the equation comes from household uses of water (e.g., showering, laundering, dish washing). To account for disequilibrium between radon and its progeny, an Activty Equlibrium Factor (Aeq) based on household air exchange rates is also applied. See section 4.10.8 of the users guide for additional information.)
submersion (The submersion exposure route is only calculated for C-14 and H-3 as well as Rn-222, Rn-220, and Rn-219, including their short-lived progeny. Also, volatilization in the equation comes from household uses of water (e.g., showering, laundering, dish washing). To account for disequilibrium between radon and its progeny, an Activty Equlibrium Factor (Aeq) based on household air exchange rates is also applied. See section 4.10.8 of the users guide for additional information.)
immersion (The immersion route represents a bath/shower event.)
consumption of fruits and vegetables combined with water
consumption of fruits and vegetables
total
Resident Tap Water CDIs
ingestion of tap waterinhalation (The inhalation exposure route is only calculated for C-14 and H-3 as well as Rn-222, Rn-220, and Rn-219, including their short-lived progeny. Also, volatilization in the equation comes from household uses of water (e.g., showering, laundering, dish washing). To account for disequilibrium between radon and its progeny, an Activty Equlibrium Factor (Aeq) based on household air exchange rates is also applied. See section 4.10.8 of the users guide for additional information.)
submersion (The submersion exposure route is only calculated for C-14 and H-3 as well as Rn-222, Rn-220, and Rn-219, including their short-lived progeny. Also, volatilization in the equation comes from household uses of water (e.g., showering, laundering, dish washing). To account for disequilibrium between radon and its progeny, an Activty Equlibrium Factor (Aeq) based on household air exchange rates is also applied. See section 4.10.8 of the users guide for additional information.)
immersion (The immersion route represents a bath/shower event.)
consumption of fruits and vegetables combined with water
Resident Consumption of Fish DCCs
The consumption of fish equation, presented here, contains the following exposure route:
consumption of fish
Resident Consumption of Fish CDIs
The consumption of fish equation, presented here, contains the following exposure route:
consumption of fish
Composite Worker
Composite Worker Soil DCCs
The composite worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
total
Composite Worker Soil CDIs
The composite worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
Composite Worker Soil 2-D External Exposure DCCs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Composite Worker Soil 2-D External Exposure CDIs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Composite Worker Air DCCs
The composite worker ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalationexternal exposure to ionizing radiation
total
Composite Worker Air CDIs
The composite worker ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalationexternal exposure to ionizing radiation
Outdoor Worker
Outdoor Worker Soil DCCs
The outdoor worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
total
Outdoor Worker Soil CDIs
The outdoor worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
Outdoor Worker Soil 2-D External Exposure DCCs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Outdoor Worker Soil 2-D External Exposure CDIs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Outdoor Worker Air DCCs
The outdoor worker ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalationexternal exposure to ionizing radiation
total
Outdoor Worker Air CDIs
The outdoor worker ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalationexternal exposure to ionizing radiation
Indoor Worker
Indoor Worker Soil DCCs
The indoor worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
total
Indoor Worker Soil CDIs
The indoor worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
Indoor Worker Soil 2-D External Exposure DCCs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Indoor Worker Soil 2-D External Exposure CDIs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Indoor Worker Air DCCs
The indoor worker ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalation (without half-life decay)external exposure to ionizing radiation (without half-life decay)
total (without half-life decay)
Indoor Worker Air CDIs
The indoor worker ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalation (without half-life decay)external exposure to ionizing radiation (without half-life decay)
Construction Worker
Construction Worker Soil - Exposure to Unpaved Roads DCCs
The construction worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
total
Construction Worker Soil - Exposure to Unpaved Roads CDIs
The construction worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
Construction Worker Soil - Exposure to Other Than Unpaved Roads DCCs
The construction worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
total
Construction Worker Soil - Exposure to Other Than Unpaved Roads CDIs
The construction worker soil land use equation, presented here, contains the following exposure routes:
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
Construction Worker Soil 2-D External Exposure DCCs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Construction Worker Soil 2-D External Exposure CDIs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Construction Worker Air DCCs
The composite worker ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalationexternal exposure to ionizing radiation
total
Construction Worker Air CDIs
The composite worker ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalationexternal exposure to ionizing radiation
Recreator
Recreator Soil DCCs
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
consumption of land game - combined with soil
consumption of fowl - combined with soil
total
Recreator Soil CDIs
incidental ingestion of soilinhalation of particulates emitted from soil
external exposure to ionizing radiation
consumption of land game - combined with soil
consumption of fowl - combined with soil
Recreator Soil 2-D External Exposure DCCs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Recreator Soil 2-D External Exposure CDIs
Direct External Exposure to contamination at infinite depthDirect External Exposure to contamination at 1 cm
Direct External Exposure to contamination at 5 cm
Direct External Exposure to contamination at 15 cm
Direct External Exposure to contamination dust
Recreator Air DCCs
The recreator ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalationexternal exposure to ionizing radiation
total
Recreator Air CDIs
The recreator ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalationexternal exposure to ionizing radiation
Recreator Surface Water DCCs
ingestion of surface waterimmersion (The immersion route represents a swimming/wading event.)
consumption of land game - combined with water.
consumption of fowl - combined with water
total
Recreator Surface Water CDIs
ingestion of surface waterimmersion (The immersion route represents a swimming/wading event.)
consumption of land game - combined with water.
consumption of fowl - combined with water
Recreator Consumption of Fowl and Game DCCs
The consumption of game and fowl equations, presented here, contain the following exposure routes:
consumption of fowl - directconsumption of land game - direct
Recreator Consumption of Fowl and Game CDIs
The consumption of game and fowl equations, presented here, contain the following exposure routes:
consumption of fowl - directconsumption of land game - direct
Farmer
Farmer Direct Consumption of Agricultural Products DCCs
consumption of fruits and vegetables. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 9 update of the Exposure Factors Handbook were used to derive the intakes for home-grown produce
consumption of poultry. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced poultry.
consumption of eggs. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced eggs.
consumption of beef. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced beef.
consumption of dairy. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced dairy.
consumption of swine. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced swine.
consumption of fin fish. Chapters 10 and 13 of the 2011 Exposure Factors Handbook were used to derive the intakes for home-caught fin fish.
consumption of shellfish. Table 10-9 of the 2011 Exposure Factors Handbook was used to derive the intakes for home-caught shellfish.
consumption of goat.
consumption of goat milk.
consumption of sheep.
consumption of sheep milk.
Farmer Direct Consumption of Agricultural Products CDIs
consumption of fruits and vegetables. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 9 update of the Exposure Factors Handbook were used to derive the intakes for home-grown produce
consumption of poultry. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced poultry.
consumption of eggs. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced eggs.
consumption of beef. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced beef.
consumption of dairy. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced dairy.
consumption of swine. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced swine.
consumption of fin fish. Chapters 10 and 13 of the 2011 Exposure Factors Handbook were used to derive the intakes for home-caught fin fish.
consumption of shellfish. Table 10-9 of the 2011 Exposure Factors Handbook was used to derive the intakes for home-caught shellfish.
consumption of goat.
consumption of goat milk.
consumption of sheep.
consumption of sheep milk. Farmer Direct Exposure and Consumption of Agricultural Products DCCs - Combined Soil and Biota
incidental ingestion of soil
inhalation of particulates emitted from soil
external exposure to ionizing radiation
consumption of fruits and vegetables. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 9 update of the Exposure Factors Handbook were used to derive the intakes for home-grown produce
where:
consumption of poultry. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced poultry.
consumption of eggs. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced eggs.
consumption of beef. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced beef.
consumption of dairy. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced dairy.
consumption of swine. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced swine.
consumption of fin fish. Chapters 10 and 13 of the 2011 Exposure Factors Handbook were used to derive the intakes for home-caught fin fish.
consumption of shellfish. Table 10-9 of the 2011 Exposure Factors Handbook was used to derive the intakes for home-caught shellfish.
total.
The following consumption routes are provided in site-specific mode only and requires the user to enter their own data, as the tool only provides a transfer factor.
consumption of goat.
consumption of goat milk.
consumption of sheep.
consumption of sheep milk.
Farmer Direct Exposure and Consumption of Agricultural Products CDIs - Combined Soil and Biota
incidental ingestion of soil
inhalation of particulates emitted from soil
external exposure to ionizing radiation
consumption of fruits and vegetables. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 9 update of the Exposure Factors Handbook were used to derive the intakes for home-grown produce
where:
consumption of poultry. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced poultry.
consumption of eggs. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced eggs.
consumption of beef. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced beef.
consumption of dairy. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced dairy.
consumption of swine. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced swine.
consumption of fin fish. Chapters 10 and 13 of the 2011 Exposure Factors Handbook were used to derive the intakes for home-caught fin fish.
consumption of shellfish. Table 10-9 of the 2011 Exposure Factors Handbook was used to derive the intakes for home-caught shellfish.
consumption of goat.
consumption of goat milk.
consumption of sheep.
consumption of sheep milk.
Farmer Direct Exposure and Consumption of Agricultural Products DCCs- Combined Water and Biota
ingestion of tap water
immersion (The immersion route represents a bath/shower event.)
inhalation (The inhalation exposure route is only calculated for C-14 and H-3 as well as Rn-222, Rn-220, and Rn-219, including their short-lived progeny. Also, volatilization in the equation comes from household uses of water (e.g., showering, laundering, dish washing). To account for disequilibrium between radon and its progeny, an Activty Equlibrium Factor (Aeq) based on household air exchange rates is also applied. See section 4.10.8 of the users guide for additional information.)
submersion (The submersion exposure route is only calculated for C-14 and H-3 as well as Rn-222, Rn-220, and Rn-219, including their short-lived progeny. Also, volatilization in the equation comes from household uses of water (e.g., showering, laundering, dish washing). To account for disequilibrium between radon and its progeny, an Activty Equlibrium Factor (Aeq) based on household air exchange rates is also applied. See section 4.10.8 of the users guide for additional information.)
consumption of fruits and vegetables. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 9 update of the Exposure Factors Handbook were used to derive the intakes for home-grown produce
where:
consumption of poultry. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced poultry.
consumption of eggs. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced eggs.
consumption of beef. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced beef.
consumption of dairy. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced dairy.
consumption of swine. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced swine.
consumption of fin fish. Chapters 10 and 13 of the 2011 Exposure Factors Handbook were used to derive the intakes for home-caught fin fish.
consumption of shellfish. Table 10-9 of the 2011 Exposure Factors Handbook was used to derive the intakes for home-caught shellfish.
total
The following consumption routes are provided in site-specific mode only and requires the user to enter their own data, as the tool only provides a transfer factor.
consumption of goat.
consumption of goat milk.
consumption of sheep.
consumption of sheep milk.
Farmer Direct Exposure and Consumption of Agricultural Products CDIs- Combined Water and Biota
ingestion of tap water
immersion (The immersion route represents a bath/shower event.)
inhalation (The inhalation exposure route is only calculated for C-14 and H-3 as well as Rn-222, Rn-220, and Rn-219, including their short-lived progeny. Also, volatilization in the equation comes from household uses of water (e.g., showering, laundering, dish washing). To account for disequilibrium between radon and its progeny, an Activty Equlibrium Factor (Aeq) based on household air exchange rates is also applied. See section 4.10.8 of the users guide for additional information.)
submersion (The submersion exposure route is only calculated for C-14 and H-3 as well as Rn-222, Rn-220, and Rn-219, including their short-lived progeny. Also, volatilization in the equation comes from household uses of water (e.g., showering, laundering, dish washing). To account for disequilibrium between radon and its progeny, an Activty Equlibrium Factor (Aeq) based on household air exchange rates is also applied. See section 4.10.8 of the users guide for additional information.)
consumption of fruits and vegetables. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 9 update of the Exposure Factors Handbook were used to derive the intakes for home-grown produce
where:
consumption of poultry. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced poultry.
consumption of eggs. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced eggs.
consumption of beef. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced beef.
consumption of dairy. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced dairy.
consumption of swine. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced swine.
consumption of fin fish. Chapters 10 and 13 of the 2011 Exposure Factors Handbook were used to derive the intakes for home-caught fin fish.
consumption of shellfish. Table 10-9 of the 2011 Exposure Factors Handbook was used to derive the intakes for home-caught shellfish.
consumption of goat.
consumption of goat milk.
consumption of sheep.
consumption of sheep milk.
Definitions of the input variables are in Table 1.
Farmer Consumption of Agricultural Products DCCs - Combined Soil, Water, and Biota
Results of combined soil, water, and biota exposure are presented in an interactive graph. See Section 4.10.7 for details.
consumption of fruits and vegetables. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 9 update of the Exposure Factors Handbook were used to derive the intakes for home-grown produce.
consumption of poultry. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced poultry.
consumption of eggs. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced eggs.
consumption of beef. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced beef.
consumption of dairy. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced dairy.
consumption of swine. Chapter 13 of the 2011 Exposure Factors Handbook and the 2018 chapter 11 update of the Exposure Factors Handbook were used to derive the intakes for home-produced swine.
consumption of fin fish. Chapters 10 and 13 of the 2011 Exposure Factors Handbook were used to derive the intakes for home-caught fin fish.
consumption of shellfish. Table 10-9 of the 2011 Exposure Factors Handbook was used to derive the intakes for home-caught shellfish.
The following consumption routes are provided in site-specific mode only and require the user to enter their own data, as the tool only provides a transfer factor.
consumption of goat
consumption of goat milk
consumption of sheep
consumption of sheep milk
Results of combined soil, water, and biota exposure are presented in an interactive graph. See Section 4.10.6 for details.
Definitions of the input variables are in Table 1.
Farmer Air DCCs
The resident ambient air land use equation, presented here, contains the following exposure routes without half-life decay:
inhalation
external exposure to ionizing radiation
total
In situations where the contaminant in the air is not being replenished (e.g., an accidental one-time air release from a factory), decay should be used. In situations where the contaminant in the air has a continual source (e.g., indoor radon from radium in the soil, or an operating factory or landfill cap), the equations without decay should be used. The decay function, found in section 4.10.7, can be multiplied by the ambient air equations above to acquire ambient air DCCs with decay. Farmer Air CDIs
inhalation
external exposure to ionizing radiation
Definitions of the input variables are in Table 1.
Soil to Groundwater
PartitioningMass Loading
Dilution Attenuation Factor
Supporting Equations
Particulate Emission Factor-WindParticulate Emission Factor- Unpaved Roads
Particulate Emission Factor-Other Than Unpaved Roads
The following decay function should be multiplied by CDI equations when applicable:
The following decay function should be multiplied by DCC equations when applicable:
