soluble uranium definition for regulatory compliance. · 100 % class y 100 % class w 100 % class d...
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SOLUBLE URANIUM DEFINITION FOR REGULATORY COMPLIANCE
2014 Health Physics Society’s Radiation Safety Conference (July 13–17, 2014)
Roland Benke, Ph.D., CHP (Center for Nuclear Waste Regulatory Analyses)Tanya Oxenberg, Ph.D. (U.S. Nuclear Regulatory Commission)
James Webb (U.S. Nuclear Regulatory Commission)
Background
2
Uranium extraction practices have evolved over decades Existing regulatory guidance is being expanded to address
in-situ recovery processes and operations CNWRA and U.S. Nuclear Regulatory Commission (USNRC) are
updating Regulatory Guide 8.30, Health Physics Surveys in Uranium Recovery Facilities
Regulatory Limits
3
Radiological and chemical toxicity considerations apply to occupational uranium intakes
o Annual radiation dose limits in 10 CFR 20.1201o Weekly intake limit of 10 mg of soluble uranium per 10 CFR 20.1201(e)
Occupational limits for soluble uranium exist to prevent chemical toxicity effects on kidney function due to uranium accumulation in the kidney and its persistence with time
Regulatory Definition Gap
4
In operational settings at uranium recovery facilities, uranium tends to be a mixture of chemical compounds and multiple inhalation classes.
Uranium ore is an exception; singular inhalation class W applies
No soluble uranium definition in 10 CFR Part 20
Guidance needed on which inhalation classes relate to soluble uranium so that weekly occupational intakes can be compared to the 10-mg limit specified in 10 CFR 20.1201(e)
Recommended Definition
5
Recommended definition for soluble uranium
Technical basis addressed by remainder of presentation
INHALATION CLASS BLOOD UPTAKE FRACTION, f1 REGULATORY POSITION
D 0.05 Soluble
W 0.05 Soluble
Y 0.002 Insoluble
Biokinetic Modeling
6
Biokinetic models represent the human body by a group of interconnected compartments.
o Regions of the human respiratory system o Organs (e.g., kidney)
Transfer rates specified between compartments
Compute transfer to, accumulation in, and removal or excretion from compartments
Uranium Concentration in the Kidney
7
Biokinetic modeling for uranium has been described.o NUREG–0874, Internal Dosimetry Model for Applications to Bioassay
at Uranium Mills, U.S. Nuclear Regulatory Commission, Washington, DC, July 1986.
Calculated kidney concentrationso Various uranium compound mixtureso Inhalation and ingestion o Single and continuous intakes
Internal Dosimetry Calculation
8
Influenced by aerosol particle size and chemical form
Aerosol deposition fractions influenced by particle size
Transfer rates among compartments influenced by chemical form (Inhalation classes)
Internal Dosimetry Calculation
9
o NP,Bo TB,Bo P,B
Calculated time dependent solution for each pathway
TB,B P,BNP,B
3 pathways via lung compartments through blood
Many distinct pathways to kidney
Internal Dosimetry Calculation
10
o NP,GIo TB,GI o P,GI(fast)o P,GI(slow)
Calculated time dependent solution for each pathway
TB,GI P,GINP,GI
3 pathways via lung compartments through gastrointestinal tract
(4 solutions)
Many distinct pathways to kidney
o NP,Bo TB,Bo P,B
Internal Dosimetry Calculation
11
o P,L,B
Calculated time dependent solution for each pathway
P,L,B
1 pathway via pulmonary lung through lymph node and blood
Many distinct pathways to kidney
o NP,Bo TB,Bo P,Bo NP,GIo TB,GI o P,GI(fast)o P,GI(slow)
Internal Dosimetry Calculation
12
o NP,B,So TB,B,So P,B,S
Calculated time dependent solution for each pathway
3 additional systemic pathways via blood and other organs
TB,B,S P,B,SNP,B,S
Many distinct pathways to kidney
o NP,Bo TB,Bo P,Bo NP,GIo TB,GI o P,GI(fast)o P,GI(slow)o P,L,B
Internal Dosimetry Calculation
13
o NP,GI,So TB,GI,So P,GI(fast),So P,GI(slow),S
Calculated time dependent solution for each pathway
NP,GI,S TB,GI,S P,GI,S
3 additional systemic pathways via gastrointestinal
tract and other organs(4 solutions)
o NP,B,So TB,B,So P,B,S
Many distinct pathways to kidney
o NP,Bo TB,Bo P,Bo NP,GIo TB,GI o P,GI(fast)o P,GI(slow)o P,L,B
Internal Dosimetry Calculation
14
o P,L,B,S
Calculated time dependent solution for each pathway
1 additional systemic pathway via lymph node, blood, and other organs
o NP,GI,So TB,GI,So P,GI(fast),So P,GI(slow),S
o NP,B,So TB,B,So P,B,S
Many distinct pathways to kidney
o NP,Bo TB,Bo P,Bo NP,GIo TB,GI o P,GI(fast)o P,GI(slow)o P,L,B
P,L,B,S
Continuous Inhalation: 2-Compartment Solution
15
Presenting examples for continuous inhalation intake In-vivo pathways dictate number of compartments and solutions Fractional transfer through blood and gastrointestinal tract (GI)
does not require separate compartment modeling
Lung compartment
Kidney
C1 × Intake rate
C2 × λ1
λ2
via blood
via GI and blood
or
KidneyIntake rate 1 1
16
Continuous Inhalation: 3-Compartment Solution
via blood
via blood
via GI and blood
or
Lung compartment
Kidney
C1 × Intake rate
C2 × λ1
λ3
Lymph node
C3 × λ2
Kidney Intake rate1
Lung compartment
Kidney
C1 × Intake rate
C2 × λ1
λ3
Systemic, organs other than kidney
C3 × λ2
17
Continuous Inhalation: 4-Compartment Solution
Intakerate 1
via blood
via blood
via GI and blood
or
Lung compartment
Kidney
C1 × Intake rate
C2 × λ1
λ4
Lymph node
C3 × λ2
Systemic, organs other than kidney
C4 × λ3 via blood
Kidney
Continuous inhalation intake Applied 2-, 3-, and 4-
compartment solutions for fractional contributions of each inhalation class in the uranium mixture
o Class D (no pathway contributions from pulmonary lung to gastrointestinal tract)
o Class Wo Class Y
Selected Results for Inhalation Intakes
18
Class D — Readily transferred to kidney
Class W — Lesser effectiveness for elevating uranium concentrations in the kidney
Class Y — Least effectivenesso Lower by more than an order of
magnitude at shorter timeso Increased contribution at longer
timeso For single intake, long-term kidney
burden is significantly lower than short-term values
o For continuous intake, long-term burden is significantly lower compared to burden from more soluble compounds
0.000001
0.00001
0.0001
0.001
0.01
0.1
1
1 10 100 1,000Kid
ney
Bur
den
(Ura
nium
Mas
s in
Kid
ney
per U
nit
Inta
ke M
ass)
Time (days)
100 % Class Y
100 % Class W
100 % Class D
0.000001
0.00001
0.0001
0.001
0.01
0.1
1
10
1 10 100 1,000 10,000Kid
ney
Bur
den
(Ura
nium
Mas
s in
Kid
ney
per U
nit
Dai
ly In
take
Mas
s)
Time (days)
100 % Class Y
100 % Class W
100 % Class D
Single Inhalation Intake
Continuous Inhalation Intake
1E-06
1E-05
0.0001
0.001
0.01
0.1
1
1 10 100 1,000Kid
ney
Bur
den
(Ura
nium
Mas
s in
Kid
ney
per U
nit
Dai
ly In
take
Mas
s)
Time (days)
100 % Class Y
100 % Class W100 % Class D
0.000001
0.00001
0.0001
0.001
0.01
0.1
1
1 10 100 1,000Kid
ney
Bur
den
(Ura
nium
Mas
s in
Kid
ney
per U
nit
Inta
ke M
ass)
Time (days)
100 % Class Y
100 % Class W
100 % Class D
Selected Results for Ingestion Intakes
19
Ingestion less effective compared to inhalation
Classes D and W more readily transferred to kidney
Same behavior for Classes D and W following ingestion
Substantially smaller contributions from Class Y
Single Ingestion Intake
Continuous Ingestion Intake
0.0001
0.001
0.01
0.1
1
1 10 100 1,000 10,000
Kid
ney
Bur
den
(Ura
nium
Mas
s in
Kid
ney
per
Dai
ly M
ass
Inta
ke)
Time (days)
Total (All Classes)
Class Y Contribution
Class W Contribution
0.000001
0.00001
0.0001
0.001
0.01
0.1
1 10 100 1,000Kid
ney
Bur
den
(Ura
nium
Mas
s in
Kid
ney
per U
nit
Inta
ke M
ass)
Time (days)
Total (All Classes)
Class Y Contribution
Class W Contribution
Selected Inhalation Results for Uranium Mixture
20
Uranium compound mixtureo Class D
o Class W
o Class Y
Class D—Dominant contribution to maximum kidney burden
Class W—Small contribution
Class Y—Negligible contribution
Single Inhalation Intake
Continuous Inhalation Intake
0.000001
0.00001
0.0001
0.001
0.01
0.1
1
1 10 100 1,000 10,000
Kid
ney
Bur
den
(Ura
nium
Mas
s in
Kid
ney
per
Dai
ly M
ass
Inta
ke)
Time (days)
Total (All Classes)
Class Y Contribution
Class W Contribution
0.000001
0.00001
0.0001
0.001
0.01
0.1
1 10 100 1,000Kid
ney
Bur
den
(Ura
nium
Mas
s in
Kid
ney
per U
nit
Inta
ke M
ass)
Time (days)
Total (All Classes)
Class Y Contribution
Class W Contribution
Selected Ingestion Results for Uranium Mixture
21
Uranium compound mixtureo Class D
o Class W
o Class Y
Classes D & W — Significant (equal) contributions to maximum kidney burden
Class Y — Negligible contribution
Single Ingestion Intake
Continuous Ingestion Intake
Radiotoxicity vs. Chemotoxicity
22
Biokinetic modeling of maximum kidney burden provides technical basis from chemotoxic perspective
Radiological limits also apply to uranium intakes
Most restrictive limit (radiological or chemical) depends on relative abundances of the different uranium compounds
Applying the recommended soluble uranium definition for the inhalation of soluble and insoluble mixtures
o Radiotoxicity is limiting when Class Y abundance > ~9 percento Chemotoxicity is limiting when Class Y abundance < ~9 percent
Conclusions
23
Calculation results support defining soluble uranium as those chemical compounds associated with Inhalation Classes D and W and blood uptake fractions of 0.05.
Class Y compounds with a blood uptake fraction of 0.002 are insoluble and provide small contributions to the maximum uranium concentration in the kidney.
Neglecting the insoluble contribution to the uranium concentration in the kidney is acceptable because radiotoxicity is more limiting than chemical toxicity for inhaled mixtures of soluble and insoluble uranium with significant Class Y contributions.
Acknowledgement
24
This presentation is an independent product of the Center for Nuclear Waste Regulatory Analyses and does not necessarily reflect the view or regulatory position of USNRC. The USNRC staff views expressed herein are preliminary and do not constitute a final judgment or determination of the matters addressed or of the acceptability of any licensing action that may be under consideration at USNRC.