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| DOE-STD-1136-2004
Guide of Good Practices for Occupational Radiological Protection in Uranium Facilities
Table 4 -1. Surface Contamination Values,(a) dpm/100 cm2
Total
(b, d)
Nuclide
Removable
(b, c)
(Fixed+Removable)
(g)
(g)
U-nat, 235U, 238U, and associated decay products
1000
5000
Transuranics, 226Ra, 228Ra, 230Th, 228Th, 231Pa, 227Ac, 125I,
20
500
129
I
Th-nat, 232Th, 90Sr, 223Ra, 224Ra, 232U, 126I, 131I, 133I
200
1000
Beta-gamma- emitters (nuclides with decay modes other
1000
5000
than alpha emission or spontaneous fission) except 90Sr
(e)
and others noted above
(f)
10,000
N/A
Tritium and tritiated compounds
(a) The values in this table, with the exception noted in footnote (e), apply to radioactive contamination deposited on, but not incorporated
into the interior or matrix of, the contaminated item. Where surface contamination by both alpha- and beta-gamma emitting nuclides
exists, the limits established for alpha- and beta-gamma-emitting nuclides apply independently.
(b) As used in this table, dpm (disintegrations per minute) means the rate of emission by radioactive material as determined by correcting
the counts per minute observed by an appropriate detector for background, efficiency, and geometric factors associated with the
(c) The levels may be averaged over one square meter provided the maximum surface activity in any area of 100 cm2 is less than three
times the value specified. For purposes of averaging, any square meter of surface shall be considered to be above the surface
contamination value if: 1) From measurements of a rep resentative number of sections it is determined that the average contamination
level exceeds the applicable value; or 2) it is determined that the sum of the activity of all isolated spots or particles in any 100 cm 2 area
exceeds three times the applicable value.
(d) The amount of removable radioactive material per 100 cm2 of surface area should be determined by swiping the area with a dry filter or
soft absorbent paper, applying moderate pressure, and then assessing the amount of radioactive material on the swipe with an
appropriate instrument of known efficiency. (Note--The use of dry material may not be appropriate for tritium.) When removable
contamination on objects of surface area less than 100 cm 2 is determined, the activity per unit area shall be based on the actual area and
the entire surface should be wiped. It is not necessary to use swiping techniques to measure removable contamination levels if direct
scan surveys indicate that the total residual surface contamination levels are within the lim its for removable contamination.
(e) This category of radionuclides includes mixed fission products, including the 90Sr which is present in them. It does not apply to
90
90Sr which has been separated from the other fission products or mixtures where the
Sr has been enriched.
(f) Tritium contamination may diffuse into the volume or matrix of materials. Evaluation of surface contamination shall consider the extent
to which such contamination may migrate to the surface in order to ensure the surface contamination value provided in this appendix is
not exceeded. Once this contamination migrates to the surface, it may be removable, not fixed; therefore, a "Total" value does not
apply.
(g) (alpha)
Scan Survey for Fixed Contamination
A scan survey for fixed contamination requires passing a detector attached to a portable instrument
over the surface of the area being surveyed at a fixed, known scan speed and at a specified distance from
the surface. Typically, the scan speed is 2 in./s (5 cm/s) and the maximum distance is 0.25 in. (0.6 cm) for
alpha-contamination instruments. A scan survey should be used to survey material that resides in an area
controlled for contamination purposes, an area where unsealed radioactive sources are used, or an area
surrounding an area controlled for contamination purposes. A scan survey in conjunction with a swipe
survey should be used to release from radiological control material with a total surface area less than 5 ft2
(0.46 m2). A statistically-based survey, which will be discussed later, should be used to release from
During the performance of scan surveys, the audible response of the instrument is faster than the
needle deflection. Therefore, audible response should be used in conjunction with meter readings. For
alpha surveys, the surveyor should pause for 3 to 5 seconds each time an individual pulse is detected in
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