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OEH&S Radiation Safety Manual Appendix D
BIOASSAYS
A. BIOASSAYS
Bioassays are performed on persons who use unsealed quantities of radioactive
materials to determine whether any activity has entered the body.
The results are used to:
1. Estimate internal organ doses.
2. Determine the presence of airborne radioactive materials.
3. Evaluate work habits, experimental and facility design.
Bioassays are performed either by:
a. Analyzing samples of blood, urine, or tissue. OR
b. Monitoring the organ of interest to determine the presence and quantity
of radioisotopes.
The method chosen depends upon the type of radioisotope involved (e.g.
urine analysis for 3H or thyroid scanning for 125I).
B. BIOASSAY PROGRAM FOR 3H, 14C, 32P AND 35S, and other radioactive
materials except radio-iodine.
1. CRITERIA
Bioassays should ideally be performed:
a. After each procedure where there is a potential for airborne activity,
or personnel exposure.
b. When there is a suspicion that internal contamination might
have occurred.
The University of California, San Francisco (UCSF) bioassay policy requires
that each individual handling greater than 100 millicuries
of potentially volatile 3H, or greater than 50 millicuries of
potentially volatile 14C, 35S, 32P
MUST perform a bioassay after such uses and document
the results
in a logbook. However, it is strongly recommended that
all individuals using millicurie
quantities of any volatile radioisotope per experiment
perform a urine assay after such uses.
Notes:
- The quantity HANDLING refers to the activity of the stock solution from which it is drawn. This will be obtained from the Single Purchase Amount listed on the Radiation Use Authorization (RUA).
- The Radiation Safety Program (RSP) will determine the need for bioassays; this will be indicated in the RUA approval.
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2. PROCEDURE
Urine is analyzed to estimate any uptake of radioactive materials other
than radioiodine.
a. Place 1.0 cc of urine in a scintillation counting vial.
b. Add 9 cc of liquid scintillation cocktail.
c. Set the counter for the appropriate radioisotope.
d. Count the sample for 1 minute.
e. Count a 10 cc LS cocktail for 1 minute as a background
count (Cb).
3. ANALYSIS
a. Obtain net count (Cn).
Cn = Cs - Cb
b. Divide the net count by counter efficiency to obtain dpm.
dpm = Cn / efficiency
c. Convert dpm to activity (uCi).
d. Log the results in the appropriate radioisotope bioassay record sheet.
The results of the calculations on the record sheet should
be compared with those given below.
4. MAXIMUM VALUES
Reference Annual Limit of Intake (ALI) 10 CFR 20 Appendix B.
The activity should not exceed the following values:
| Isotope | ALI (µCi) |
| 3H | 8 x 104 |
| 14C | 2 x 103 |
| 32P | 6 x 102 |
| 35S | 1 x 104 |
5. ACTION LEVELS
If the calculated body burdens exceed 10% of ALI values, inform the Radiation
Safety Officer (RSO) so that an investigation can be conducted
to determine the causes of the uptake and recommendations for remedial can
action be
made. Top of Page C. BIOASSAY PROGRAM FOR 123I, 125I, AND 131I
1. BIOASSAY CRITERIA
The bioassay program is developed for persons working with radioiodine
to aid in determining the extent, if any, of an individual's exposure
to concentrations of airborne radioiodine. Bioassays are performed
by measuring the emissions
from radioiodine within the thyroid. Routine bioassays are performed
for those quantities listed below:
FOR 125I:
| (A=) Single Purchase Authorization (mCi) | FREQUENCY |
| 1.0 < A < 15.0 | (Volatile) | Quarterly |
| 15.0 < A < 20.0 | (Volatile) | Monthly |
| 20.0 < A | (Volatile) | Within 14 days |
| 5.0 < A | (Non-volatile) | Quarterly |
Notes:
- The bioassay frequency is based on the activity in the vial of the 125I stock handled to perform the iodination.
- Single Purchase Authorization is the maximum activity the laboratory can receive in each vial. This determines the frequency.
- The bioassay frequency will be communicated to the Principal
Investigator (PI) in the RUA conditions. The
usage quantity is not the determinant factor
but "A" quantity is!
- Bioassays must be performed by those individuals who have used radioiodine in the laboratory during the period (e.g. month, quarter etc.).
FOR 123I AND 131I:
123I users must obtain a bioassay within 24 hours if the iodination
utilizes more than 5.0 mCi.
131I users must obtain a bioassay within 2 weeks of any iodination
utilizing more than 1.0 mCi.
Individuals administering volatile quantities of 131I for therapeutic
purposes, in excess of five (5) millicurie must obtain a bioassay
within
two weeks of administration. This does not include other personnel
in the room at the time of the administration or subsequent
patient care. However, it is strongly recommended that all persons
in
the room during such an administration should obtain a bioassay
within
two weeks. If capsules are used no bioassays are required,
unless an unusual event takes place.
2. LOCATION OF BIOASSAYS
Thyroid monitoring will be performed at the locations listed below:
All 125I users
Radiation Safety Office at L-235 Parnassus Campus or Building 1, Room
3 (floor below Gallo Foundation) at San Francisco General Hospital (SFGH).
All persons using 123I and 131I will have their bioassays
performed in the Nuclear Medicine Department at SFGH or University of
California Medical
Center (Long
Hospital Third Floor) or Mt. Zion Nuclear Medicine Section.
3. OCCUPATIONAL ALI
The annual limits on intakes are as follows:
Isotope to be Monitored ALI
123I 3000 µCi
125I 40 µCi
131I 30 µCi Top of Page
4. ACTION LEVEL
The action levels set are 10% of the ALIs. When action levels are exceeded
the following steps should be taken:
a. An investigation of the operation
involved, including air sampling, will be carried out to determine
the causes of exposure and to evaluate the potential
for further exposures.
b. If the investigation indicates
that further work in the area might result in exposure of a worker
to concentrations exceeding the Derived Air Concentrations
(DAC) the worker will be restricted
from further exposure until the cause of exposure is discovered
and corrected.
c. Corrective actions that will
eliminate or lower the potential for further
exposures will be implemented.
d. A repeat bioassay will be taken
within 2 weeks of the previous measurement and should be evaluated
within 24 hours after measurement in order to confirm
the presence of internal radioiodine,
and to obtain an estimate of its effective half-life for use in
estimating dose commitment.
e. If the thyroid burden exceeds
50% of ALI, refer the case to appropriate medical consultation
as soon as possible for recommendations regarding therapeutic procedures
that may be carried out to accelerate
removal of radioactive iodine from the body. This should be done
within
2-3 hours after exposure when the time of exposure
is known so that any prescribed thyroid
blocking agent would be effective.
NOTE: All exposures exceeding
the ALI will be reported to the State of California
immediately by telephone and followed
by additional reports and actions prescribed by the State of
California.
5. INCIDENTS OR UNUSUAL EVENTS
Contact the RSO if an incident or unusual event occurs involving any radioisotope
other than radioiodine. The RSO
will request that a urine sample be submitted
for examination to determine if
an exposure occurred.
UCSF TRITIUM BIOASSAY RECORD SHEET
 |
NAME:________________________ | PI:______________________________ |
| |
DATE OF EXPOSURE:____________ | DATE OF SAMPLE:________________ |
| |
DATE OF ANALYSIS:____________ | 3H CHEMICAL FORM: |
| | LIQUID SCINTILLATION ANALYSIS OF URINE SAMPLES (1 ml) |
| | SAMPLE NUMBER cpm/ml BACKGROUND DATA _____________
cpm |
| | 1 _______ TRITIUM EFFICIENCY (EFF.) OF LSC ________ |
| | 2 _______ |
| | 3 _______ |
| |
AVG. OF SAMPLES _______ - (BKG.) _______ cpm = _______ net cpm/ml |
| |
(net cpm/ml)/(EFF.) = ________ dpm/ml |
| |
MDA OF SYSTEM (3 x (BKG cpm)1/2 + BKG cpm / EFF.) = ____________dpm |
| |
IS MDA > SAMPLE dpm --- YES - NO IF NO, DO NOT COMPLETE
SHEET
_________ (dpm/ml)/2.22 x 106 dpm/uCi = __________ uCi/ml
|
| |
BODY WEIGHT IN KILOGRAMS (2.2 lbs/kg) = __________ |
| |
__________ kg x 600 ml WATER/kg = __________ ml OF WATER IN BODY |
| |
__________ ml x ________ uCi/ml = __________ (TOTAL) uCi IN BODY |
| |
ABSORBED DOSE TO TISSUE (WHOLE BODY) BY MIRD TECHNIQUE |
| |
D = A x S x Q WHERE: A = 1.44 x T(eff) x 24 hr/day x uCi |
| |
S = 1.7 x 10-7 Rad/uCi-hr Q = 1 Rad/Rem |
| |
T(eff) = 10 day effective half-life
A = 1.44 x 10 day x 24 hr/day x _________ uCi (IN BODY) |
| |
A = _________ uCi-hr |
| |
D = _________ uCi-hr x 1.7 x 10-7 Rad/uCi-hr x 1 Rad/Rem |
| |
D = _________ Rem _______ Rem/1000 mrem/Rem = ________ mrem |
| |
NOTE: IF THYMIDINE (CHEMICAL FORM) TAKE mrem x 5 TO OBTAIN ABSORBED DOSE
WHOLE BODY ABSORBED DOSE = _________________ mrem |
| | ANALYSIS PERFORMED BY:____________________________________________ |
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UCSF 14C BIOASSAY RECORD SHEET
 |
NAME:________________________ | PI:______________________________ |
| |
DATE OF EXPOSURE:____________ | DATE OF SAMPLE:________________ |
| |
DATE OF ANALYSIS:____________ |
14C CHEMICAL FORM: |
| | LIQUID SCINTILLATION ANALYSIS OF URINE SAMPLES (1 ml) |
| | SAMPLE NUMBER cpm/ml BACKGROUND DATA _____________
cpm |
| |
1 _______ 14C EFFICIENCY
(EFF.) OF LSC ________ |
| | 2 _______ |
| | 3 _______ |
| |
AVG. OF SAMPLES _______ - (BKG.) _______ cpm = _______ net cpm/ml |
| |
(net cpm/ml)/(EFF.) = ________ dpm/ml |
| |
MDA OF SYSTEM (3 x (BKG cpm)1/2 + BKG cpm / EFF.) = ____________dpm |
| |
IS MDA > SAMPLE dpm --- YES - NO IF NO, DO NOT COMPLETE
SHEET
_________ (dpm/ml)/2.22 x 106 dpm/uCi = __________ uCi/ml
|
| |
BODY WEIGHT IN KILOGRAMS (2.2 lbs/kg) = __________ |
| |
__________ kg x 600 ml WATER/kg = __________ ml OF WATER IN BODY |
| |
__________ ml x ________ uCi/ml = __________ (TOTAL) uCi IN BODY |
| | ANALYSIS PERFORMED BY:____________________________________________ |
UCSF 32P BIOASSAY RECORD SHEET
 |
NAME:________________________ | PI:______________________________ |
| |
DATE OF EXPOSURE:____________ | DATE OF SAMPLE:________________ |
| |
DATE OF ANALYSIS:____________ |
32P CHEMICAL FORM: |
| | LIQUID SCINTILLATION ANALYSIS OF URINE SAMPLES (1 ml) |
| | SAMPLE NUMBER cpm/ml BACKGROUND DATA _____________
cpm |
| |
1 _______ 32P EFFICIENCY
(EFF.) OF LSC ________ |
| | 2 _______ |
| | 3 _______ |
| |
AVG. OF SAMPLES _______ - (BKG.) _______ cpm = _______ net cpm/ml |
| |
(net cpm/ml)/(EFF.) = ________ dpm/ml |
| |
MDA OF SYSTEM (3 x (BKG cpm)1/2 + BKG cpm / EFF.) = ____________dpm |
| |
IS MDA > SAMPLE dpm --- YES - NO IF NO, DO NOT COMPLETE
SHEET
_________ (dpm/ml)/2.22 x 106 dpm/uCi = __________ uCi/ml
|
| |
BODY WEIGHT IN KILOGRAMS (2.2 lbs/kg) = __________ |
| |
__________ kg x 600 ml WATER/kg = __________ ml OF WATER IN BODY |
| |
__________ ml x ________ uCi/ml = __________ (TOTAL) uCi IN BODY |
| | ANALYSIS PERFORMED BY:____________________________________________ |
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UCSF 35S BIOASSAY RECORD SHEET
 |
NAME:________________________ | PI:______________________________ |
| |
DATE OF EXPOSURE:____________ | DATE OF SAMPLE:________________ |
| |
DATE OF ANALYSIS:____________ |
35S CHEMICAL FORM: |
| | LIQUID SCINTILLATION ANALYSIS OF URINE SAMPLES (1 ml) |
| | SAMPLE NUMBER cpm/ml BACKGROUND DATA _____________
cpm |
| |
1 _______ 35S EFFICIENCY
(EFF.) OF LSC ________ |
| | 2 _______ |
| | 3 _______ |
| |
AVG. OF SAMPLES _______ - (BKG.) _______ cpm = _______ net cpm/ml |
| |
(net cpm/ml)/(EFF.) = ________ dpm/ml |
| |
MDA OF SYSTEM (3 x (BKG cpm)1/2 + BKG cpm / EFF.) = ____________dpm |
| |
IS MDA > SAMPLE dpm --- YES - NO IF NO, DO NOT COMPLETE
SHEET
_________ (dpm/ml)/2.22 x 106 dpm/uCi = __________ uCi/ml
|
| |
BODY WEIGHT IN KILOGRAMS (2.2 lbs/kg) = __________ |
| |
__________ kg x 600 ml WATER/kg = __________ ml OF WATER IN BODY |
| |
__________ ml x ________ uCi/ml = __________ (TOTAL) uCi IN BODY |
| | ANALYSIS PERFORMED BY:____________________________________________ |
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