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Quality Assurance (QA) of OBT Quality Assurance (QA) of OBT Measurement in Environmental Samples Measurement in Environmental Samples September 12, 2011 Sang Bog Kim, Ph.D. Research Scientist Environmental Technologies Branch Chalk River


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Quality Assurance (QA) of OBT Measurement in Environmental Samples Quality Assurance (QA) of OBT Measurement in Environmental Samples

September 12, 2011 UNRESTRICTED / ILLIMITÉ

Sang Bog Kim, Ph.D. Research Scientist Environmental Technologies Branch Chalk River Laboratories Chalk River, Ontario Canada

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Outline

  • 1. Background
  • 2. Analytical Procedure
  • 3. Previous OBT Inter-Laboratory Comparisons
  • 4. CRL’s Experiments
  • 5. Discussions

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  • 1. Background
  • Environmental tritium pathways
  • Release and measurement
  • Recent tritium conferences
  • Lessons learned from Fukushima in Japan
  • Difference between HTO and OBT
  • HTO measurement
  • OBT history and definition
  • OBT classification
  • OBT measurement

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Environmental Tritium Pathw ays

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CNSC (2010)

Tritium in the biological cycle of water

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Release ≠ Measurement

  • Environmental release forms are HT and HTO
  • Environmental measureable forms are HTO and OBT
  • HT → HTO → OBT
  • HTO measurement is relatively simple and

straightforward

  • OBT behaviour in the environment is relatively

complicated and has a higher uncertainty than HTO behaviour

  • OBT measurement is useful for normal operations
  • OBT prediction is useful for accidental situations

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Lessons Learned from Fukushima

  • Earthquake: Natural disaster
  • Tsunami: Natural disaster
  • Radiation: Man-made disaster
  • Are public very conservative or generous?
  • It is a time to reinforce environmental safety!

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Recent Tritium Conferences

  • EMRAS II in Vienna (2009 and 2010)
  • “Tritium 2010” in Japan (2010)
  • ICRER in Hamilton (2011)
  • OBT is a rising topic!

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Differences betw een HTO and OBT

  • Dose conversion factors (DCF) from ICRP

HTO = 1.4 x 10-11 Sv/Bq OBT = 4.2 x 10-11 Sv/Bq

  • Retention time in biota
  • Half-life in humans
  • OBT/HTO ratios in environmental samples
  • Chemical forms
  • Dose contribution
  • Regulation guideline

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HTO Measurement

  • HTO and TFWT or THO (H2O form)
  • IAEA’s Inter-Laboratory Comparison (TRIC2008)
  • Certified Standard Material (Multi-Media RadCheMTM

Assessment Program (MRaD) by Environmental Resource Associates (ERA))

  • Drinking Water Guideline (7,000 Bq/L for Canada)

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OBT History and Definition

  • 70’s and 80’s : Tissue Bound Tritium (TBT)
  • Health Physics (1993) Special Issue :
  • Organically Bound Tritium (OBT)
  • Exchangeable Tritium
  • Non-exchangeable Tritium
  • EMRAS I and II : On-going topic
  • Carbon bound tritium (CBT)
  • XBT (X=N,O,S)
  • Buried Tritium
  • USA : Soluble and non-soluble OBT

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OBT Classification

  • Total OBT = Non-exchangeable OBT + Exchangeable OBT

(Diabate and Strack, 1993)

  • OBT
  • Soluble OBT: Dissolved organic tritium (DOT)

Tritiated organic (TO) Non-exchangeable OBT Exchangeable OBT

  • Insoluble OBT: Non-exchangeable OBT

Exchangeable OBT

  • Buried tritium: Exchangeable OBT

Non-exchangeable OBT

  • Biogenic (early metabolism) and abiogenic (late metabolism)

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Exchangeable and Non-exchangeable OBT

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OBT Measurement

  • Total tritium = Tissue free water tritium (TFWT) + OBT

(Canada, France) OBT

  • OBT = Total Tritium – TFWT (UK)
  • Wet combustion (?)

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TFWT OBT TFWT

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  • 2. Analytical Issues
  • OBT measurement scheme
  • HTO extraction
  • OBT measurement methods
  • Critical steps
  • Where we are!

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OBT Measurement Scheme

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TFWT Extraction

  • Freeze-drying system (Lyophilization)

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Laboratory design Commercial brand

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OBT Measurement Methods

  • Parr Combustion (U.S.A.) : Only available for plant and

animal samples

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Detection limit is approximately 7-10 Bq/L

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OBT Measurement Methods

  • Tube furnace system: Soil samples for CRL

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OBT Measurement Methods

  • Plasma combustion: Germany

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OBT Measurement Methods

  • 3He Mass Spectrometer: University of Ottawa

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OBT Measurement Methods

  • Oxidizer: Packard brand

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Critical Steps

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Critical Step Process Step 1

  • Freeze-dry (water residue)
  • Oven-dry (temperature, duration)
  • Azo-distillation (old fashioned)

Step 2

  • Rinse (volume, duration) or no rinse
  • Combustion (Parr bomb, tube furnace)
  • Distillation (remove impurities)

Step 3

  • Liquid scintillation counter (Quantulus, Packard,

Aloka)

  • Cocktail (Ultima Gold series)
  • Counting condition (background, time)
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Where w e are!

  • No Certified Reference Materials (CRMs)
  • No Standard OBT Procedures
  • IAEA and National Institute of Standard and Technology

(NIST)

  • Quality Assurance (QA)
  • Quality Control (QC)

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  • 3. Previous OBT Inter-Comparisons
  • Canada (CRL)
  • Canada (CRL, OPG, UO)
  • France
  • Japan
  • UK

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Canada (CRL)

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  • Fusion Science and Technology 48, 762-766 (2005) :1998-1999
  • Sample : Lettuce (approximately 990 Bq/L) and Crabapple (approximately 37 Bq/L)
  • Blank sample: Polyethylene beads (Alathon 1145, DuPont, USA)
  • Seven labs (Canada, England, France, Romania, Russia)
  • Parr combustion system (3 labs) and Quartz combustion tube system (5 labs)
  • Better agreement at higher OBT concentrations than lower OBT concentrations
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Canada (CRL, OPG, UO)

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  • COG-09-3015 (2009)
  • CRL and OPG; CRL and UO
  • CRL ‘s measurement was lower than OPG and UO
  • Rinsing process and 3He-ingrowth mass spectrometry
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France (CEA)

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Grass sample (2009) Grass sample (2010)

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Japan

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Swain liver sample Polished rice sample

  • Radioisotopes, 39 (1990)
  • 6 laboratories (5 use Quartz combustion and 1 uses plasma reactor)
  • Aloka LSC-LB (Teflon 100 ml vial and quartz vial)
  • Variation coefficients were 68% for the polished rice and 35% for the Swine liver
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UK (NCAS)

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  • National Compliance and Assessment Service, NCAS/TR/99/003 (1999)
  • 7 Laboratories (Total tritium, tritiated water and OBT)
  • Aliquot sample (added tritium labelled sucrose)
  • This was not an environmental sample!
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  • 4. CRL’s Experiments
  • Water residue
  • Furnace temperature
  • OBT in plants
  • OBT in animals
  • OBT in fish
  • OBT in soil
  • OBT/HTO ratio

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Water Residue (1)

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  • From a commercial brand (Labconco)
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Water Residue (2)

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Sample Fresh weight (g) % after Freeze- dry (3 days) % after Oven- dry (1 day) Tomato 212 198 98.3 98.8 99.8 100 Lettuce 205 210 99.8 100 99.9 100 Beet 209 203 98.2 95.6 99.9 99.9 Average 206±5.2 98.5±1.6 99.9±0.1 CRL’s procedure = Freeze-dry + Oven-dry (at 55ºC)

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Furnace Temperature

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  • Pickering soil (P-2)
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OBT in Plants

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  • Environmental Monitoring Results in 2009
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HTO and OBT in Animals

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  • CRL site and sites greater than 50 km from CRL
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OBT in Fish

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  • Yearly sampling
  • In order to develop “Eco-metabolic tritium model”, MOU is being prepared

between CRL and Romania.

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Sampling Locations – Fish Study

                                                                          

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C C C

                        

  • B02

B09 B08 B04 B03 B01 B10 B07 B06 To (Mackey) Petawawa Allumette Island Sheenboro Chichester To Waltham Demers Centre Pembroke T

  • K

i l l a l

  • e

Rapides des Joachims ORR BMC KMC PET ORF ORH ORD ORP BDO BHC CRH SHC LTH BTH SCB S-7 S-6 SOB OR5 DBC HIL Fort William

Chapeau

Balmer Bay Deep River Chalk River

CRL                                                   

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C

  • Critical Group Location

CRL Environmental Monitoring Locations Outside CRL Boundary

Beach Sediment Fish Surface Water Farm Animals Produce River / Lake Highway 17 Road

Environmental Technologies Branch, CRL February 2008 Map-08-006

Map A-1b: CRL Liquid and Biological Environmental Monitoring Locations - Outside CRL Boundary

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Working on the Ottaw a River

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Mackey 35 Rolphton 26 Sand Spit 36 Cotnam 26 TOTAL # of fish: 123

Todd Chaput

Total Fish Sampled (2010)

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OBT in Soils

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  • Northern Ontario was higher than Ottawa and Saskatchewan
  • What is OBT background in Canada?
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OBT in Soil (HT release site)

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CRL Boundary Decontamination Loop Old Port Hope Road Plant Road

1986/7 Experiment 1994 Experiment C B A 1986/7 Experiment 1994 Experiment C B A

CRL

Sample Locations Cranberry Lake Sample Locations Cranberry Lake

100 200 metres

Map-11-10

LEGEND LEGEND

Sample Location Historic Experiment Road CRL Property Boundary

Soil depth HTO concentration (kBq/L) Percent 0 - 2 cm 2 - 4 cm 2,000 1,500 50.0 % 4 - 6 cm 6 - 8 cm 8 - 10 cm 1,200 1,000 700 41.5% 10 - 12 cm 12 - 14 cm 14 -16 cm 16 -18 cm 18 -20 cm 350 110 80 30 17 8.5 % Total 6,987 100 % Davis et al., (1995)

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OBT in Soil (15 years later)

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OBT is still there, but HTO is not!

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OBT in Soil (Darlington)

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                                                                           Lake O n tario

D arlington P rov incial P ark

Darlington N uclear

H igh w ay 401 Martin Rd. Holt Rd. Rundle Rd. Maple Grove Rd. Green Rd. C

  • u

r t i c e R d . B ase line R d. O s b

  • u

r n e B l

  • r

S t . Solina Rd.

D -1 D -2 D -3

Martin Rd. H

  • l

t R d . Rundle Rd. Maple Grove Rd. Green Rd. Courtice Rd. B ase line R d. O s b

  • u

r n e B l

  • r

S t . Solina Rd. Solina Rd

D AR LIN G T O N                          S a m plin g S ite S a m plin g S ite W o o dla n d W e tla nd R o a d

D-1: Approximately 5 km from the reactors D-2: Approximately 2.1 km from the reactors D-3: Approximately 5 km from the reactors

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OBT in Soil (Darlington)

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OBT/HTO Ratios

  • Rvalue = OBTconcentration / HTOconcentration
  • Interpretation the exposure conditions (dynamic or

equilibrium)

  • If Rvalue is consistent, we can estimate the OBT

concentration by the HTO concentration

  • CRL has analyzed more than 2,000 non-human biota

samples in Canada

  • No single value and only a range
  • OBT activity concentration unit (Bq/L combustion water,

Bq/kg-fresh)

  • CRL uses “Bq/L” for the specific activity model

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OBT/HTO ratio example

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Sample HTO (Bq/kg-f) OBT (Bq/kg-f) Ratio HTO (Bq/L) OBT (Bq/L) Ratio

Leaves 1 2.9 2.6 0.897 3.6 26 7.172 Leaves 2 7.4 7.4 1.000 9.3 74 8.000 Leaves 3 55.2 2.3 0.042 69.0 23 0.333 Leaves 4 105.3 1.3 0.012 131.6 13 0.099 Assumptions: water content is 80% and water equivalent factor (WEF) is 0.5

8 times

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Discussions

  • CRL has analysed OBT in more than 2,000

environmental samples since the 1980’s.

  • CRL is very confident in the analysis of any

environmental samples

  • The OBT/HTO ratio around the CRL site is not

consistent

  • Requires a site-specific environmental tritium study
  • OBT activity unit (Bq/L or Bq/kg-fresh)
  • CRL has many tritium measurement sites
  • Aquatic ecosystem: Perch Lake, Ottawa River
  • Wetland ecosystem: Duke Swamp
  • Terrestrial ecosystem: Acid Rain Site, HT release site

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Aquatic and w etland ecosystems

Perch Lake Duke Swamp

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Terrestrial ecosystem

Perch Lake garden Acid Rain Site garden

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International OBT inter-comparison

  • In May (3 days), 2012 France will be hosted the first

OBT workshop

  • Organized by CEA (France) and AECL (Canada)
  • Candidate : France, Canada, Romania, Germany,

Japan, Korea, India, US, Belgium, UK, Swiss, Russia etc.

  • Three inter-comparison exercise (2012-2015)
  • Dry sample, exchangeable and non-exchangeable OBT
  • Three-days workshop
  • Tritium environmental monitoring
  • OBT in environmental samples
  • Inter comparison exercise

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Thanks!