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Ken Sejkora

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Implications of Tritium Dose Conversion Factors in Deriving Regulatory Limits for Drinking Water and Effluent Compliance Ken Sejkora Entergy Nuclear Northeast ... – PowerPoint PPT presentation

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Title: Ken Sejkora


1
  • Ken Sejkora
  • Entergy Nuclear Northeast Pilgrim Station
  • Presented at the 16th Annual RETS-REMP Workshop
  • Mashantucket, CT / 26-28 June 2006

2
Reason for Concern
  • Issue of tritium in groundwater has crossed
    jurisdictional boundaries NRC, EPA, state
    radiation control programs are involved
  • Various limits exist governing effluent
    compliance, safe drinking water standards, and
    dose/risk assessment
  • Recognize the different limits, reasons for
    differences, and implications/applicability

3
EPA Drinking Water Standard from the beginning
  • Specified in 40 CFR 141.25
  • Refer to www.epa.gov/safewater/rads/radfr.pdf
  • 20,000 pCi/Liter, assumed to yield committed dose
    of 4 mrem/yr
  • Based on drinking water consumption of 2
    liters/day 730 liters/yr
  • 20,000 pCi/L 730 L/yr 1.46E7 pCi/yr
  • 4 mrem / 1.46E7 pCi 2.74E-7 mrem/pCi

4
EPA Drinking Water Standard why its important
  • Standard limit adopted by state regulatory
    agencies often takes precedence over ODCM limits
    if groundwater is involved
  • Used as basis for tables in standard ODCM
    guidance NUREG-1301/1302
  • Table 3.12-2, Reporting Levels 20,000 pCi/L
    for drinking water 30,000 pCi/L for non-DW
  • Table 4.12-1, Lower Limit of Detection set at
    1/10 of Reporting Level 2,000 pCi/L for DW
    3,000 pCi/L for non-DW.

5
EPA Drinking Water Standard where did it
come from?
  • Roots in ICRP-2, circa late 1950s
  • Second generation derivative of NRC maximum
    permissible concentration (MPC) value
  • 1 MPC 500 mrem/yr total body
  • Early MPC for tritium 3E-3 uCi/mL
  • (4 mrem / 500 mrem) 3E-3 uCi/mL 2.4E-5
    uCi/mL 24,000 pCi/L
  • Rounded to 20,000 pCi/L one significant figure
  • Gray-hair phenomenon derivation not
    documented, exists only in recollection of
    experts involved

6
Other ICRP-2 based Factors
  • Direct activity-to-dose factors
  • not back-calculated from concentration limit
  • Age-specific dose factors
  • Regulatory Guide 1.109, Ingestion dose factors,
    Tables E-11 through E-14
  • Adult 1.05E-7 mrem/pCi Child 2.03E-7 mrem/pCi
  • Teen 1.06E-7 mrem/pCi Infant 3.08E-7 mrem/pCi

7
Other ICRP-2 based Factors continued
  • LADTAP Factors refinement of RG-1.109 factors
  • Adult 5.99E-8 mrem/pCi Child 1.16E-7 mrem/pCi
  • Teen 6.04E-8 mrem/pCi Infant 1.76E-7 mrem/pCi
  • RG-1.109 and LADTAP dose conversion factors are
    the de facto values used in most plants ODCMs,
    effluent control programs, and effluent dose
    calculation software

8
ICRP-30 based Factors
  • Based on ICRP-26 standard man approach,
    occupational exposure circa early 1970s
  • Single age class adult male
  • Basis for current values in 10CFR20 Appendix B,
    and EPA Federal Guidance Report 11
  • Ingestion DCF 6.40E-8 mrem/pCi
  • Table 2, Column 2 Concentration Limit - Public
    1E-3 uCi/mL, or 1,000,000 pCi/L assumed to
    yield committed dose of 50 mrem/yr

9
ICRP-60/72 Factors
  • Based on ICRP-60 metabolic models most modern,
    circa late 1990s
  • Non-occupational exposure, latest risk quality
    factors, multiple age classes,
  • Adult 7.09E-8 mrem/pCi 5-yr 1.25E-7
    mrem/pCi
  • 15-yr 7.07E-8 mrem/pCi 1-yr 2.04E-7
    mrem/pCi
  • 10-yr 9.06E-8 mrem/pCi Infant  2.79E-7
    mrem/pCi
  • Standard among international community, but not
    widely adopted in USA, nor endorsed by NRC
    however, adopted in EPA FGR-13

10
Side-by-side Comparison
  • EPA DW Standard 2.74E-7 mrem/pCi
  • Reg Guide 1.109
  • Adult 1.05E-7 mrem/pCi Child 2.03E-7 mrem/pCi
  • Teen 1.06E-7 mrem/pCi Infant 3.08E-7 mrem/pCi
  • LADTAP
  • Adult 5.99E-8 mrem/pCi Child 1.16E-7
    mrem/pCi
  • Teen 6.04E-8 mrem/pCi Infant 1.76E-7 mrem/pCi
  • ICRP-30 6.40E-8 mrem/pCi
  • ICRP-72
  • Adult 7.09E-8 mrem/pCi 5-yr 1.25E-7
    mrem/pCi
  • 15-yr 7.07E-8 mrem/pCi 1-yr 2.04E-7
    mrem/pCi
  • 10-yr 9.06E-8 mrem/pCi Infant 2.79E-7
    mrem/pCi

11
Which Limit to Use?
  • RG-1.109/LADTAP for ODCM effluent release
    compliance, possible extension to REMP samples
  • EPA Safe Drinking Water Standard adopted by most
    state programs comes into play if offsite
    groundwater is involved
  • ICRP-72 is not used (except for EPA FGR-13),
    despite being most modern and based on best
    available technology
  • When dealing with the recent groundwater issue,
    one could argue we should use the most up-to-date
    methodology and science available.

12
Beware
  • Organically-bound tritium
  • Strontium-90

13
Organically-bound tritium
  • Existing limits (EPA, NRC) are based on tritium
    in the form of tritiated water
  • High metabolism, rapid turnover/clearance from
    body
  • Relatively low dose impact
  • Organically-bound tritium, once incorporated into
    tissue, has much longer residence time in body
  • More time Higher dose impact
  • Could result in lower limits than those based on
    conventional tritiated water metabolism
  • Organically bound tritium is not of concern in
    drinking water, but could result in modifying
    concentration limits to account for higher
    dose/risk once in the body

14
Strontium-90
  • Exists at low levels in environment from weapons
    testing in 1950s through 1970s often seen in
    REMP samples
  • Has been detected at low levels in groundwater by
    some licensees
  • There is a separate EPA drinking water standard
    for Sr-90 listed in 40CFR141
  • According to Federal Register, based on
    assumption that 8 pCi/L Sr-90 will yield 4
    mrem/yr to bone marrow.
  • Similar rationale to that used for H-3 at 20,000
    pCi/L

15
Strontium-90 -- error in drinking water
standard?
  • 1 MPC 1500 mrem/yr critical organ (bone)
  • MPC for Sr-90 3E-7 uCi/mL
  • (4 mrem / 1500 mrem) 3E-7 uCi/mL 8E-10
    uCi/mL 0.8 pCi/L, NOT 8 pCi/L
  • 8 pCi/L 730 L/yr 5840 pCi/yr intake
  • 5840 pCi/yr 7.58E-3 mrem/pCi 44 mrem/yr, NOT
    4 mrem/yr
  • EPA standard for Sr-90 appears to be 10X too
    high!
  • Compliance with the EPA standard of 8 pCi/L would
    exceed the 10CFR50 Appendix I organ dose limit of
    15 mrem/yr by about 3X

16
Summary
  • Several limits exist for tritium in water
  • EPA drinking water limit 20,000 pCi/L
  • NRC effluent limit 1,000,000 pCi/L (1E-3
    uCi/mL)
  • Fractional limits imposed by states?
  • Various limits are based on different
    assumptions, different bases
  • EPA 20,000 pCi/L 4 mrem/yr, based on ICRP-2
  • NRC 1,000,000 pCi/L 50 mrem/yr, based on
    ICRP-30

17
Summary (continued)
  • Other nuclides, forms may come into play
  • Organically-bound tritium, Sr-90
  • Concern about non-conservative Sr-90 drinking
    water standard
  • If one has to deal with multiple nuclides, it
    makes sense to use a single standard, and
    presumably the most modern one ICRP-72

18
Conclusion
  • This IS a dose issue
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