ML092720438
| ML092720438 | |
| Person / Time | |
|---|---|
| Site: | 07000925 |
| Issue date: | 11/02/1989 |
| From: | Rogers W Cimarron Corp |
| To: | Region 3 Administrator |
| Shared Package | |
| ML092720355 | List:
|
| References | |
| Download: ML092720438 (17) | |
Text
ROOM 127 Room 127 contained both wet and dry gloveboxes used for scrap recovery.
After glovebox removalithe floor coating was removed and the entire room was vacu-blasted.
Initial survey results after 2
blasting indicated one spot on the floor of 2500 dpm/100 cm direct and approximately 20% of the floor between 200 dpm/100 cm2 2
and 500 dpm/100 cm2.
The entire floor and a few spots on the walls were reblasted before the final release survey was started.
A number of pipe sleeves that were installed in room 127 floor had to be removed because of high gamma readings.
We used a Ludlum 2220 with a Ludlum 43-17 low energy gamma probe to identify all cracks and seams that might need decontami-nation.
A Ludlum 2220 with a Ludlum 43-68, 43-4, or 43-27 was used with P-10 gas for all alpha release surveys.
All smears were taken on Whatman smear paper and counted in a Hewlett-Packard 5560 A (low background) automatic sample counter.
W.A.
Rogers
Pu PLANT RELEASE SURVEY PLAN
- 1. For initial decontamination all surfaces will be scanned with an Eberline PRM-6 with a Radeco alpha scintillation probe.
Back-ground will be maintained at less than 100 CPM(200 dpm).
All areas greater than twice background will be marked and reading will be taken with a release survey instrument to document cont-amination levels and random large area smears will be taken.
- 2.
After these initial areas are decontaminated, all floor surfaces and the base of each wall will be completely surveyed with a digital readout release instrument and a Ludlum large area gas proportional alpha detector and random smear samples will be taken.
Release instrumentation shall have a minimum detectable level of at least 50 dpm/100 cm2.
- 3.
All hot spots greater than or equal to 100 dpm/100 cm2 ident-ified will be decontaminated.
- 4.
A random survey with a release instrument will be taken on the walls and ceiling to try to identify any other problem areas.
- 5.
If no problems are identified, each room will be gridded off into approximately 2 meter on a side square on the walls and floor and five readings will be taken in each grid.
Readings shall be taken in the center and at the midpoint from the center to each corner.
- 6.
Each ceiling has closely spaced rafters that will not be easily divided into 2 meter squares.
Because of this, we will take readings on the bottom of each rafter at 2 meter inter-.
vals and one reading centered on the ceiling between rafters.
Readings on each rafter will be staggered one meter.
- 7.
These release readings will be documented on a map that is drawn to approximately scale measurements in meters.
- 8.
Data provided on each map:
- 1. Survey block numbers, identifiable on a scale drawings.
- a. room or area name or number.
- b. surface surveyed.
- c. type of measurement and units.
- 2.
Name of surveyor taking measurements, date of survey, and location.
- 3.
- Type, model number, calibration
- data, sensitivity
- limit, background, and source response of instruments used in survey.
- 4.
When a block surveyed is below the sensitivity of the instru-ment, the fact that such a measurement was made should be included as significant data.
- 9.
All release survey smears will be taken on Whatman smear paper and counted in the automatic sample counters.
Each smear will cover approximately 100 cm 2.
- 10. There will be at least 30 survey blocks in each area to be released.
- 11. Piping and ductwork will be surveyed on all accessable sides at 2 meter intervals.
If more than one line is running parallel in a pipe rack, readings shall be staggered at one meter intervals.
- 12. All readings taken that only cover part of a probe area will be corrected to dpm/100 cm 2.
- 13.
No survey block will measure less than one meter on a side.
- 14.
No survey block will measure more than 3 meters on a side.
- 15.
All portable release survey instruments will be calibrated quarterly and all instruments in use will be source checked daily.
0 Table I-1.
Acceptable surface contamination levels I)
Nuclidesa Ave rageb
,c J Max i mumb "1, U-nat, U-235, U-238, and associated decay products Transuranics, Ra-226, Ra-228, Th-230, Th-228, Pa-231, Ac-227, 1-125, 1-129 Th-nat, Th-232, Sr-90 Ra-223, Ra-224, U-232, 1-126, 1-131, 1-133 Beta-gamma emitters (nuclides with decay modes other than alpha emission or spontaneous fission) except Sr-90 and other noted above.
5,000 dpm a/100 cm2 100 dpm/l00 cm2 1,000 dpm/100 cm2 5,000 dpm By/l00 cm 2 15,000 dpm ci/100 cm2 300 dlpm/lI1)0 cmi 3,000 dpm/l00 cm 2
15,000 dpm Fiy/100 cm' Remnoval I e,,
I, 000 dpm il 100 cm 2
20 dpwi/ 110l cm2 200 dpmn/lO0 cm2 1,000 dpm R'y/I00 cm2 1...a alWhere surface contamination by both alpha-and beta-gamma-emitting nuclides exis-ts, the limits estahlishrd for alpha-and beta-gamma-emitting nuclides should apply independently.
bAs used in this table, dpm (disintegrations per minute) mecans the rate of emi'eion by r'ioi,:nctive material as determined by correcting the counts per minute observed by an appropriate detector for background, efficiency, and geometric factors associated with the instrumentation.
C Measurements of average contaminant should not be averaged over more than 1 square meter.
For objects of less surface area, the average should be derived for each such object.
dThe maximum contamination level applies to an area of not more than 100 cm.
e The amount of removable radioactive material per 100 cm2 of surface area should be determined by wiping that area with dry filter or soft absorbent paper, applying moderate pressure, and assessing the amount of radioactive material on the wipe with an appropriate instrument of known efficiency.
When removable contamination on objects of less surface area is determined, the pertinent levels should he reduced proportionally and the entire surface should be wiped.
fThe" average and maximum radiation levels associated with surface contamination resulting from beta-gamma emitters should not exceed 0.2 mrad/hr at 1 cm and 1.0 mrad/hr at 1 cm, respectively, measured through not more than 7 milligrams per square centimeter of total absorber.
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