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22 Cards in this Set

  • Front
  • Back

Explain why audible response is used.

The audible output response is always faster than the meter response because the instrument responds instantly to each individual ionizing event

List when an audible response is recommended and required during radiological surveys

-Surveying areas or equipment where small intense beams of radiation can be present


-Surveying personnel


-Searching for fixed contamination


-Trying to find he most highly contaminated portion of contaminated materials or areas


-Performing low radiation level evaluations


-Using the AN/PDR-70 on the lowest scale

State the methods for performing a contamination survey

-Swipe


-Frisk


-Large Area Wipe


-As directed per TWD

State the units used to document measurements of surface contamination and describe the manner in which these measurements are obtained.

100 cm^2- firmly swipe a 100 cm^2 area. Unit to document is uuCi/100cm^2


SWIPE- Firmly swipe a 100cm^2 area the units to document are uuCi/100cm^2. If area is less than 100cm^2, the entire are should be swiped, and documented using uuCi/SWIPE


LAW- Damp absorbent wiped over an area covering 1m by 1m


Units used are uuCi/LAW


FRISK- a frisk is a direct reading on the surveyed item or surface within 1/2 inch using a DT-304 probe or equivalent. Units are uuCi/PROBE


Per TWD- the TWD will direct you if any methods are to be used. The units used will be documented in TWD

State why dry swipes are used

-Dry swipes are used because they are more representative of how contamination is spread by personnel brushing past these surfaces, than other methods


-Swipe surveys should be used when background is too high to permit direct frisking or when the area to be surveyed is wet

State the basis for performing swipes of 100 cm^2

-Swipes tend to disintegrate when wiped over a larger area


-Area gives nearly optimum efficiency for collecting and measuring contamination


-Area is convenient

State when wet swipes are allowed

Taking swipes on wet surfaces


When surface contamination is suspected that is not detectable using dry swipes

Explain how to take and count wet swipes

-Counted and taken in the same method as dry swipes


-Shall be counted again when dry, because moisture in the swipes will shield beta activity

State when and why LAW can be used

LAWs may be used to survey potentially contaminated areas to determine that an area is fee of loose surface contamination.

Discuss how LAWs are not used for quantitative measurement, but can be used to document that an area is free of contamination.

-LAWs cannot be used as quantitative measures of surface contamination greater than 450 uuCi/100cm^2


-LAWs can be used to determine that an area is free of loose surface contamination.

Explain how to perform s survey using a large area wipe

-Label LAW with numbers or a short description


-LAW is dampened with water or other liquid not containing hazardous constituents and folded into a 6 in square


-Wipe 1m^2 area, making six passes over the area. If area is less than 1m^2 wipe entire area


-Count LAWs in a location where background is <100. Increase count time if background is 100-300 CPM. LAWs need not be dried before counting


-Frisk LAW within 1/2 inch of all wiped surfaces. If an audible increase, count LAW for at least 15 seconds


-LAWS used to monitor Zn are to be submitted for gamma analysis


-Control LAWs as RAM until released as bulk waste


Document the survey results on the survey record as "per LAW"


State the time required to count swipes when using a DT-304 or HP-260 probe

5 seconds


If clicks or background increase, count swipe for at least 15 seconds and until the counts/meter stabilizes

State the minimum time required to count an air sample filter using a DT-304

At least 15 seconds or until the meter stabilizes

State background limitations for a DT-304 probe in a non casualty situation

-Use the DT-304/PDR probe where the background count rate is <100 CPM


-Permissible to use the DT-304/PDR probe where background is 100-300 CPM


-Do not use the probe where the background is >300 CPM

State the background count rate limitations for a HP-260 probe

-Use the HP-260/PDR probe where the background count rate is <100 CPM


-Do not use the probe where the background count rate exceeds 100 CPM

Discuss the use of the DT-304 probe in casualty situations where the background count rate is >300 cpm

There is no background limit when using the DT-304 probe in casualty situations. However the following restrictions apply


-The frisk results can only be used to estimate the magnitude of surface contamination present


-The frisk results cannot be used to declare the area is free of surface contamination

State why direct frisking is preferred over swiping for contamination surveys

-Direct frisking requires less time than taking and counting swipes


-Direct frisking can measure either fixed or loose surface contamination

State the sample volumes for normal and casualty situation portable air samples

Co-60


-Normal: 1m^3


-Casualty: 0.3m^3



Zn-65


-Normal: 3m^3


-Casualty: 1.5m^3

State the approximate times required to draw a normal and casualty situation portable air sample for Co-60

Normal: 5-6 min


Casualty: 2-3 min

State the approximate times required to draw normal and casualty situation portable air samples for Zn-65

Normal: 8-9 min


Casualty: 4-5 min

Explain how to use a friskier to measure airborne activity

-Determine background count rate


-Hold air filter paper within 1/2 in of DT-304 probe


-Count sample for at least 15 seconds, and until the meter stabilizes


-Subtract background fm to get CCPM


-Calculate air concentration using applicable thumb rule

Discuss how to use an alpha survey meter to measure airborne radioactivity

Hold air filter paper within 1/8 of inch of probe


Count sample for at least 30 seconds


Verify meter is not responding to beta-gamma


-insert a sheet of paper between air filter and probe


-if alpha, the reading will return to background, and alpha is the difference between the readings


Calculate air concentration using applicable thumb rule


-50 CPM = 1x10^-9 uCi/ml for 0.3m^3 air sample


-50 CPM = 3x10^-10 uCi/ml for 1m^3 air sample