
appropriate safety and health practices and determine the
applicability of regulatory limitations prior to use.
2. Referenced Documents
2.1 ASTM Standards:
3
C 859 Terminology Relating to Nuclear Materials
C 993 Guide for In-Plant Performance Evaluation of Auto-
matic Pedestrian SNM Monitors
C 1189 Guide to Procedures for Calibrating Automatic
Pedestrian SNM Monitors
C 1236 Guide for In-Plant Performance Evaluation of Au-
tomatic Vehicle SNM Monitors
C 1237 Guide for In-Plant Performance Evaluation of
Hand-Held SNM Monitors
2.2 Code of Federal Regulations:
Title 10, Part 73, Physical Protection of Plants and Materi-
als
4
2.3 AEC/NRC Regulatory Guides:
5.27 Special Nuclear Material Monitors, June 1974
5
5.7 Control of Personnel Access to Protected Areas, Vital
Areas, and Material Access Areas, May 1980
5
2.4 AEC/ERDA/DOE SNM Monitor Standards:
Personnel Doorway Monitor Standards, January 1974
6
Standards for Hand-Held SNM Detection Instruments for
Personnel, Package, and Vehicle Search, April 1974
6
2.5 NRC NUREG and NUREG/CR Reports:
NUREG 1321, Testing Standards for Physical Security
Systems at Category I Fuel Cycle Facilities, October
1991
5
NUREG 1329, Entry/Exit Control at Fuel Fabrication Fa-
cilities Using or Possessing Formula Quantities of Strate-
gic Special Nuclear Material, November 1985
5
NUREG/CR 5899 (SAND 92-1339), Entry/Exit Control
Components for Physical Protection Systems, 1992
5
3. Terminology
3.1 Definitions of Terms Specific to This Standard:
3.1.1 alternative test sources—there are no other radioac-
tive isotopes that individually or together can duplicate the
radioactive emissions of SNM. Hence, performance testing in
a laboratory environment will use only SNM test sources.
Operational testing at the recommended three-month interval
can most often use SNM test sources, although sometimes a
more readily available equivalent-intensity highly enriched
uranium (HEU) source may be used in place of a very
expensive and hard to obtain plutonium source. The more
frequent daily or weekly operational testing will often substi-
tute alternative isotopic sources. Often these are continuity
tests that can use the cesium-137 (
137
Cs) sources that are on
hand for pulse height calibration. Also barium-133 (
133
Ba) may
be used when a gamma-ray spectrum similar to plutonium is
needed to make a daily or weekly test that must roughly
approximate testing with a particular plutonium test source.
Gas lantern mantles containing thorium are radioactive and
sometimes are used to test continuity in hand-held monitors.
3.1.2 detection sensitivity—specified in terms of the mass of
SNM that will be detected 50 % or more of the time when
carried through the monitor in a specified fashion. This
convenient definition greatly simplifies SNM monitor perfor-
mance testing and makes it possible to readily verify sensitivity
by performing an experiment that mimics the monitor’s normal
use. The related masses that would be detected 95 % or 99 %
of the time can be estimated from the 50 % mass but would be
impractical to determine with high confidence by themselves.
Experiments conducted to determine or verify sensitivity must
be thorough enough to have an upper 95 % confidence coeffi-
cient so that repeating the experiment will probably give the
same result.
3.1.3 monitoring—the process of detecting increased radia-
tion intensity by making one or more measurements of the
intensity in the vicinity of a pedestrian or motor vehicle for
comparison with an alarm threshold derived from the expected
background radiation intensity.
3.1.4 NaI(Tl) detector—an inorganic sodium iodide (thal-
lium activated) (NaI(Tl)) scintillation detector that has inher-
ently good gamma-ray sensitivity but poor neutron response.
3.1.5 nuisance alarms—an alarm not caused by SNM but
by one of a number of other causes. For example, the statistical
variation in the measurement process, natural or process-
induced background intensity increases, or the presence of
non-SNM radiation emitters, among other things, may increase
a monitor’s measurement result by enough to cause an alarm.
Nuisance alarms from statistical variation, by design, are the
only ones present during testing and are the ones of concern in
designing and evaluating SNM monitors. These statistical
alarms are expressed in terms of alarms per comparison (test)
or, more importantly, alarms per passage, which may include a
number of comparisons. A monitor’s susceptibility to statistical
alarms and its detection sensitivity are directly related.
3.1.6 passthrough monitor—a radiation monitor that allows
free passage as it makes monitoring measurements and does
not require the person or vehicle being monitored to stop unless
it alarms.
3.1.7 plastic scintillation detector—a solid organic scintil-
lator that responds to both gamma rays and energetic neutrons
through scattering interactions between the incident radiation
and electrons or protons in the scintillator.
3.1.8 radiation detector—( 1) a detector consisting of a
scintillating material and attached photomultiplier tube that
produces light from neutron or gamma-ray interactions and
converts the light to electrical signals. (2) a neutron propor-
tional counter containing a converter gas to produce electrical
signals from neutron interactions.
3.1.9 standard SNM performance test source—a metallic
sphere or cube of SNM having maximum self-attenuation of its
emitted radiation and an isotopic composition to minimize that
emission. Such minimum radioactive emission sources as
described in 3.1.9.1 and 3.1.9.2 allow testing with the worst-
case forms of SNM. As a result of worst-case testing, routine
3
Annual Book of ASTM Standards, Vol 12.01.
4
Available from the Superintendent of Documents, U.S. Government Printing
Office, Washington, DC 20402.
5
Available from the U.S. Nuclear Regulatory Commission, Washington,
DC 20555.
6
Chapter 4, Entry-Control Systems Handbook, SAND77-1033, Sandia National
Laboratories, Albuquerque, NM 87185.
C 1112 – 99 (2005)
2
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