DOE-HDBK-1122-99 Module 2.04, Fundamental Academic Training Instructor's Guide Phase I; Module 2.04, Dosimetry
Functional areas: Radiological Training, Instructor's Guide, Technician Training, Dosimetry
This lesson will introduce the types of instruments used to measure external and internal radiation to people. Dosimetry
is the quantitative assessment of radiation received by the human body. There are several types of dosimeters in use
worldwide. This material is valuable to all radiological control personnel since dosimeters are the only direct method to measure and document personnel radiation exposure and ensure regulatory compliance with applicable limits.
Document text
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Section 1
DOE-HDBK-1122-99
Module 2.04 Dosimetry Instructor’s Guide
2.04-1
Course Title: Radiological Control Technician
Module Title: Dosimetry
Module Number: 2.04
Objectives:
2.04.01 Identify the DOE external exposure limits for general employees.
2.04.02 Identify the DOE limits established for the embryo/fetus of a declared
pregnant female general employee.
� 2.04.03 Identify the administrative exposure control guidelines at your site,
including those for the:
a. General Employee
b. Member of the Public/Minor
c. Incidents and emergencies
d. Embryo/Fetus
� 2.04.04 Identify the requirements for a female general employee who has notified
her employer in writing that she is pregnant.
2.04.05 Determine the theory of operation of a thermoluminescent dosimeter
(TLD).
2.04.06 Determine how a TLD reader measures the radiation dose from a TLD.
2.04.07 Identify the advantages and disadvantages of a TLD compared to a film
badge.
� 2.04.08 Identify the types of beta-gamma TLDs used at your site.
� 2.04.09 Identify the types of neutron TLDs used at your site.
� 2.04.10 Determine the requirements for use of TLDs used at your site.
� 2.04.11 Determine the principle of operation, and the types used, for the personnel
neutron dosimeters used at your site.
� 2.04.12 Determine the principle of operation of self-reading dosimetry (SRD) used
at your site.
� 2.04.13 Determine the principle of operation, and guidelines for use, for the
alarming dosimeters used at your site.
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� 2.04.14 List the types of bioassay monitoring methods at your site.
2.04.15 List different uses of area monitoring dosimeters.
References:
1. "Basic Radiation Protection Technology"; Gollnick, Daniel; Pacific Radiation
Press; 1994.
2. ANL-88-26 (1988) "Operational Health Physics Training"; Moe, Harold; Argonne
National Laboratory, Chicago.
3. "DOE Radiological Control Standard" (reference TSP project number SAFT-
0039).
4. 10 CFR Part 835 (1998) "Occupational Radiation Protection"
Instructional Aids:
1. Overheads
2. Overhead projector/screen
3. Chalkboard/whiteboard
4. Lessons learned
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Module 2.04 Dosimetry Instructor’s Guide
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I. MODULE INTRODUCTION
A. Self Introduction
1. Name
2. Phone number
3. Background
4. Emergency procedure review
B. Motivation
This lesson will introduce the types of instruments used to
measure external and internal radiation to people. Dosimetry
is the quantitative assessment of radiation received by the
human body. There are several types of dosimeters in use
worldwide. This material is valuable to all radiological
control personnel since dosimeters are the only direct method
to measure and document personnel radiation exposure and
ensure regulatory compliance with applicable limits.
C. Overview of Lesson
1. Dosimetry terms
2. DOE limits
3. Site administrative guidelines
4. TLDs
5. Site dosimetry
6. Bioassay assessment methods
D. Introduce Objectives O.H.: Objectives
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II. LESSON OUTLINE
A. DOSIMETRY TERMS Majority from 835.2
Understanding the terminology used in discussing dosimetry
and exposure to ionizing radiation is essential for RCTs to do
their job.
Refer to the definitions
provided in the Study
Guide and review terms
with class.
1. Absorbed Dose (D)
2. Dose Equivalent (H)
3. Deep Dose Equivalent (DDE)
4. Shallow Dose Equivalent (SDE)
5. Whole Body
Section 2
6. Extremity
7. Committed Dose Equivalent (CDE)
8. Weighting Factor (Wt)
9. Committed Effective Dose Equivalent (CEDE)
10. Total Effective Dose Equivalent (TEDE)
11. Annual Limit on Intake (ALI)
12. Derived Air Concentration (DAC)
13. Bioassay
14. In Vivo
15. In Vitro
16. Background
17. Declared Pregnant Worker
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B. DOE LIMITS Objective 2.04.01
1. Limits are the legal maximum values stated in 10 CFR
835. To exceed these values is to violate the law.
Programs must be in place to ensure that exposures to
ionizing radiation are kept below these levels. To
accomplish this Administrative Control Levels are
selected well below the regulatory limits. These control
levels are usually multi-tiered with increasing levels of
authority required to approve higher Administrative
Control Levels.
2. Annual dose equivalent limits are based on a calendar
year (January 1st through December 31st). For assigning
internal dose equivalent received from intakes (CDE and
CEDE), the total 50-year committed dose received is
assigned to the time of the intake even though the actual
dose is proportionally received over the 50-year period.
See Table 2
a. General Employees 10 CFR 835.202
1) Whole body (internal + external) - 5 rems (0.05
sievert)
2) Lens of the eye - 15 rems (0.15 sievert)
3) Extremities - 50 rems (0.5 sievert)
4) Organ or tissue and skin - 50 rems (0.5 sievert)
b. Minors/Public - 0.1 rem (0.001 sievert) 10 CFR 835.207 & .208
c. Embryo/Fetus of Declared Pregnant Workers - 0.5
rems (0.005 sievert) per gestation period
10 CFR 835.206
Objective 2.04.02
d. Emergency Exposures 10 CFR 835.1302
e. Planned Special Exposures 10 CFR 835.204
C. SITE ADMINISTRATIVE GUIDELINES
1. Radiological Workers Objective 2.04.03.a
(Insert site specific information here)
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2. Non-Radiation Worker Objective 2.04.03.b
(Insert site specific information here)
3. Exposure from Incidents or Emergencies Objective 2.04.03.c
(Insert site specific information here)
4. Embryo/fetus Objective 2.04.03.d
(Insert site specific information here)
D. TYPES OF DOSIMETRY
1. As a result of irradiation, some solid substances undergo
changes in some of their physical properties.
2. These changes amount to storage of the energy from the
radiation.
3. Since the energy is stored, these materials can be used for
dosimeters. The features that have been studied include:
a. Optical density changes
1) Optical density changes involve a change in the
color of some types of plastics and glass.
2) In glass, the dose range is 103 to 106 rads (10 to
104 gray). The range for plastics is 106 to 109 rads
(104 to 107 gray).
3) An example, film badges, provides low range, 10
mR to 10 R, for personnel and high range, 1 R to
1,000 R for accident readings.
b. Thermoluminescence
1) Thermoluminescence (TL) is the ability of some
materials to convert the energy from radiation to a
radiation of a different wavelength, normally in
the visible light range.
2) There are two categories of thermoluminescence.
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a) Fluorescence - This is emission of light during
or immediately after irradiation (within
fractions of a second) of the phosphor. This is
not a particularly useful reaction for TLD use.
Example - TV or
computer monitor screen
Section 3
b) Phosphorescence - This is the emission of light
after the irradiation period. The delay time can
be from a few seconds to weeks or months.
This is the principle of operation used for
thermoluminescent dosimeters.
3) The property of thermoluminescence of some
materials is the main method used for personnel
dosimeters at DOE facilities and will be discussed
in further detail.
E. TLD OPERATION
1. TLD's use phosphorescence as their means of detection of
radiation.
Objective 2.04.05
2. Electrons in some solids can exist in two energy states,
called the valence band and the conduction band. The
difference between the two bands is called the band gap.
3. Electrons in the conduction band or in the band gap have
more energy than the valence band electrons.
4. Normally in a solid, no electrons exist in energy states
contained in the band gap. This is a "forbidden region."
5. In some materials, or if impurities are added, defects in
the material exist or are made that can trap electrons in the
band gap and hold them there. These trapped electrons
represent stored energy for the time that the electrons are
held. This energy is given up if the electron returns to the
valence band.
See figure 1 - "Electron
Entrapment"
6. In most materials, this energy is given up as heat in the
surrounding material, however, in some materials a
portion of energy is emitted as light photons. This
property is called luminescence.
See figure 2 -
"Thermoluminescence"
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F. TLD Reader Objective 2.04.06
1. Basic principle of operation
a. Heating of the TL material causes the trapped
electrons to return to the valence band. When this
happens, energy is emitted in the form of visible light.
b. The light output is detected and measured by a
photomultiplier tube and a dose equivalent is then
calculated.
c. A typical basic TLD reader contains the following
components:
See figure 3 - "TLD
Reader"
1) Heater
2) Photomultiplier tube
3) Meter/recorder
2. Glow curve See figure 4 - "Glow
curve"
a. Obtained from heating process.
b. The light output from TL material is not easily
interpreted. Multiple peaks result.
1) As the material is heated, electrons trapped in
"shallow" traps are released. This results in a peak
as these traps are emptied. The light output drops
off as these traps are depleted.
2) As heating continues, the electrons in deeper traps
are released. This results in additional peaks.
Usually the highest peak is used for calculations.
The area under the curve represents the radiation
energy deposited.
c. After the readout is complete, the TLD is annealed at
a high temperature. This process essentially zeroes
the TL material by releasing all trapped electrons. The
TLD is then ready for reuse.
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G. ADVANTAGES AND DISADVANTAGES OF TLDs Objective 2.04.07
1. Advantages (primarily as compared to film badges)
a. Able to measure a greater range of doses.
b. Doses may be easily obtained.
c. They can be read on site instead of being sent away
for developing.
d. Quicker turnaround time for readout.
e. Reusable.
2. Disadvantages
a. Each dose cannot be read out more than once.
b. The readout process effectively "zeroes" the TLD.
H. SITE BETA/GAMMA TLDs Objective 2.04.08
(Insert site specific information here)
I. SITE NEUTRON TLDs Objective 2.04.09
(Insert site specific information here)
Section 4
J. DOE EXTERNAL DOSIMETRY GENERAL PROVISIONS 10 CFR 835
1. Dosimetry shall be provided to and used by:
a. General employee expected deep dose equivalent >
0.1 rem (0.001 sieverts); or > 10% of limits for
extremities, organs, and other tissues.
b. Declared pregnant worker expected to receive 0.05
rem (0.0005 sievert) or more during the gestation
period.
c. Minors likely to receive 50% of Occupational Dose
Limits or more in a year.
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d. Public entering controlled areas likely to receive
external deep dose equivalent of 0.05 rem (0.0005
sievert) or more in one year.
e. Individuals entering a high or very high radiation area.
2. Neutron dosimetry provided when applicable threshold is
likely to exceeded due to neutron radiation.
3. Issued to individuals knowledgeable of proper use and
worn only by assignee.
4. Issuance of dosimeters should be discouraged for
individuals other than those where there is a likelihood of
being occupationally exposed to levels above monitoring
thresholds.
5. Dosimeters should be returned at required intervals.
Individuals not returning dosimeters should be restricted.
6. Primary dosimeters should be worn on the chest area or
between the waist and the neck.
7. Individuals should not be assigned multiple primary
dosimeters during different periods of the dosimeter
process year (exchange of primary dosimeter for multi-
badging is acceptable); and avoid exposure of dosimeter
to non-occupational sources.
8. When dosimeters are lost, damaged, or contaminated, the
individual should place work in a safe condition, exit and
notify the RCO. Reenter only after review and approval.
K. SITE REQUIREMENTS FOR USE OF TLDs Objective 2.04.10
(Insert site specific information here)
L. SITE PERSONNEL NEUTRON DOSIMETERS Objective 2.04.11
(Insert site specific information here)
M. POCKET AND ELECTRONIC DOSIMETERS
1. Provide real time dose indication.
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2. Shall be issued for entry into High or Very High
Radiation Area.
3. Should be issue when planned activity levels exceed 0.05
rem (0.0005 sievert) or 10% of control levels.
4. Should be issued when required by RWP.
5. Worn with primary dosimetry and located on chest area,
on or between the waist and the neck.
6. Should be read periodically and should not exceed 75% of
full scale.
7. Authorized work should cease when supplemental
dosimeter indicates total dose or dose rate is > than
expected.
8. When supplemental dosimeters differ by more than 50%
from primary dosimeters and the primary result is >0.1
rem (0.001 sievert), an investigation should be initiated.
N. SITE SELF-READING DOSIMETERS
(Insert site specific information here) Objective 2.04.12
1. Self Reading Pocket Dosimeters (SRPD) See figure 5 - "SRPD"
a. Direct reading ion chamber. Note: SRPDs with steel
walls are usually
insensitive to beta and
low energy gamma
b. Utilizes two electrodes:
1) Fiber electrometer (fixed and moveable
components)
2) Metal frame
c. As chamber is ionized the charge is decreased on the
movable and fixed fiber.
d. The movement of the fiber is proportional to the dose
received.
See figure 6 -"SRPD
Reading"
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O. SITE ALARMING DOSIMETRY
(Insert site specific information here) Objective 2.04.13
P. INTERNAL DOSIMETRY REQUIREMENTS Re-enforce difference
between "internal" and
"external" dose
Section 5
1. Internal dose evaluation programs shall be conducted for: 10 CFR 835.402
a. General employees - likely to receive 0.1 rem (0.001
sievert) or more CEDE.
b. Declared pregnant workers - likely to receive an intake
resulting in dose equivalent of 10% of the limit (or
0.05 rem [0.0005 sievert]).
c. Minors - likely to receive a CEDE in excess of 50% of
limit (or 0.05 rem [0.0005 sievert]).
d. Public - likely to receive a CEDE in excess of 50% of
limit (or 0.05 rem [0.0005 sievert]).
2. Estimation shall be based on bioassay results rather than
air concentration values unless air concentration values
are more reliable or bioassay results are unavailable.
3. Follow-up bioassay monitoring is typically required when
results indicate a committed effective dose equivalent of
0.1 rem (0.001 sievert) or more.
4. A bioassay program should be considered for personnel
routinely exposed to surface or airborne contamination or
to radionuclides readily absorbed through the skin.
5. Personnel are required to submit bioassay samples.
6. Personnel shall be notified of positive bioassay results.
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Q. BIOASSAY ASSESSMENT METHODS
1. General
a. Today's technology has not produced a device that
allows accurate determination of internal exposure
following the entry of radioactive materials into the
body.
b. The method that is used to determine internal dose
contributions relies on calculation of dose to affected
portions of the body based on the quantities of
radioactive materials in the body. Thus, the real
problem becomes one of quantifying the amount of
material present.
c. Bioassay is the term that is used to describe the
assessment of the quantity of radioactive material
present in the body. There are currently two types of
bioassay measurements employed in nuclear
industries:
1) In vivo - analysis of living tissue.
2) In vitro - analysis of excreted samples.
d. Bioassay programs are designed to fulfill two needs:
1) Evaluate effectiveness of contamination control
practices.
a) Routine bioassay programs utilize submission
and analysis of samples from workers in
facilities where the likelihood of intake exists.
b) Primarily limited to urinalysis due to ease of
sample collection.
c) Also includes initial, routine, and termination
whole body counts.
2) Evaluate potential consequences of accidental
inhalation or ingestion of large quantities of
radioactive materials.
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a) Can involve all types of bioassay
measurements with collection and analysis of
nasal, urine, and fecal samples.
b) Whole body counts provide immediate
indications for given radionuclides if
individual(s) involved are free of external
contamination.
2. In vivo measurements
a. The amount of materials is estimated by counting
radiation emitted by radioactive materials in the body.
b. Only good for radioactive materials which emit
gamma radiation of sufficient abundance and energy
to be detected and statistically measured.
c. With use of expensive, sophisticated spectroscopy,
most contributors (radionuclides present) can be
identified.
d. Site In vivo methods
(Insert site specific information here) Objective 2.04.14
e. Advantages
1) No sample required.
2) Results obtained quickly.
3) Some equipment design allows field use.
4) Time and manpower requirements minimized.
f. Disadvantages
1) Limited to detection and measurement of gamma
emitters.
Section 6
2) Individual must be free of external contamination.
3) Long count times for identification.
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4) Effects of background.
5) Complex calibration procedure and calibration
equipment.
6) Expense.
7) Quantification error due to differences in tissue
structure from one person to another as compared
to calibration phantom.
3. In Vitro Measurements
a. The amount of material present in the body is
estimated using the amount of materials present in
excretions or secretions from the body.
b. Samples include urine, feces, blood, sputum, saliva,
hair and nasal discharges.
c. Calculation requires knowledge of and use of
metabolic models which allow use of activity in
samples to be related to activity present in the body.
d. Resulting dose calculations to quantify committed and
effective dose equivalents are estimates.
1) This is due partly to use of default values for
measurements that cannot be readily made such as
mass of particular organs, volumes of particular
fluids, etc., in lieu of actual values for individual
involved. Remember that reference man is an
average.
2) Another contributing factor is different
metabolism from one individual to another.
e. Types of analysis
1) Urinalysis - indicates intake of primarily soluble
material.
2) Fecal analysis - primarily indicates intake of
insoluble material. Provides relatively rapid
indication.
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3) Sputum - may contain insoluble material initially
deposited in the lung and later eliminated by
ciliary action.
4) Saliva - may be use to estimate uptake of tritium
oxide.
5) Nasal discharge - indication of the deposition of
the coarsest inhaled particles in the nose.
f. Site in vitro methods
(Insert site specific information here) Objective 2.04.14
g. Advantages of in vitro measurements
1) Can be used for estimation of neutron doses using
activation product concentration in hair and blood
(32P and 24Na).
2) Can be used to quantify presence of materials
which decay by alpha and beta emission to allow
detection and measurement with external detector
systems.
h. Disadvantages
1) Requires sample submission and analysis.
2) Time and manpower requirements.
3. Bioassay Scheduling Program
a. Contamination found at a given site will depend on
the materials that are used and produced at the site.
Thus, the materials that internal dosimetrists are
primarily concerned with will change from one site to
another as well.
b. Baseline/Routine/Exit Evaluations
(Insert site specific information here)
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c. Special Evaluations
(Insert site specific information here)
d. Investigation Levels
(Insert site specific information here)
e. Medical Uses
(Insert site specific information here)
R. AREA MONITORING DOSIMETERS Objective 2.04.15
1. Area monitoring dosimeters are often used to record and
document radiation levels in routinely occupied areas adjacent
to areas where radiation or radiological operations exist.
Note: This type of monitoring does not apply when the
radiation hazard of concern arises from low-energy beta
sources (e.g., 14C, 3H).
2. Establishment and maintenance of a comprehensive area
monitoring program can demonstrate that doses outside
Radiological Buffer Areas are negligible, and help to
minimize the number of areas requiring the issuance/use of
personnel dosimeters.
Section 7
Minimizing the number of personnel dosimeters issued saves
in the costs of operating the dosimetry program and reduces
costs associated with maintaining personnel with enhanced
training and qualifications.
3. Area monitoring dosimeters are also used to help characterize
workplace conditions to verify the effectiveness of physical
design features, engineering controls, and administrative
controls. In addition, area monitoring dosimeter results can
be used to support dosimetry investigations where personnel
express concerns about their work environments and exposure
to ionizing radiation.
4. Finally, area (and equipment) monitoring dosimeters are
useful for the determination of dose rates and/or integrated
doses for:
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a. equipment and/or areas with suspected high dose rates;
b. devices emitting pulsed radiation not accurately measured
with portable survey instruments;
c. highly collimated beams of radiation; and
d. radiological incidents.
III. SUMMARY
A. Review major topics
1. Dosimetry terms
2. DOE limits
3. Site administrative guidelines
4. TLDs
5. Site dosimetry
6. Bioassay assessment methods
B. Review learning objectives
IV. EVALUATION
Evaluation shall consist of a written examination comprised of
multiple choice, fill-in the blank, matching and/or short answer
questions. 80% shall be the minimum passing criteria for
examinations.
Module Number: 2.04