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DOE-STD-1128-98
Guide of Good Practices for Occupational Radiological Protection in Plutonium Facilities
This document concerns release to controlled areas only. The detailed
requirements for unrestricted release of materials and equipment are found in DOE
Order 5400.5 (DOE, 1993b).  Refer to that document for guidance regarding
unrestricted releases.
4.2.4.3 External Exposure Surveys
To delineate the levels involved, measurements of external exposure should be
made at the time a program is established at all locations where personnel exposure
occurs. Additional photon and neutron measurements should be made at the same
frequency as the contamination surveys. The buildup of plutonium contamination
in glove boxes and on gloves and equipment may contribute substantially to the
external dose rates.
4.2.4.4 Measurement and Survey Techniques
This section discusses four types of contamination surveys that are typically used
in DOE facilities. Surveys for removable contamination include a large-area wipe
survey and a technical swipe or smear survey. Surveys for total/fixed
contamination include a scan survey and a statistically based survey. These
surveys, or a combination of them, are used to survey material for release from
radiological control. The appropriate use of each type of survey is discussed.
Surveys for Removable Contamination
Two types of surveys are used for removable contamination: a large-area wipe
survey and a technical swipe or smear survey.
A large-area wipe survey is used to detect gross removable contamination. A
large-area wipe survey is typically performed using a large floor cloth and a dust
mop type handle to wipe large areas. This technique tends to concentrate any low
levels of removable contamination that may be present. The surface to be wiped
and the wiping material should be industrially clean (i.e., free of debris, grease,
etc.) to reduce self-absorption of alpha contamination. The survey is performed by
wiping the surface of the area being surveyed and conducting frequent checks of
the cloth using a portable instrument. For detection of alpha-emitting isotopes, a
nonabsorbent material should be used. Removable contamination will be
accumulated and concentrated on the wipe, increasing the probability of its
detection. Checking for contamination is conducted by placing an alpha-
measurement instrument approximately 0.25 in. (0.6 cm) from the surface of the
wipe for 5 seconds, and the count rate observed. If there is no increase above
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