ITR-16
     SOUTHWESTERN RADIOLOGICAL HEALTH LABORATORY
            INTRALABORATORY  TECHNICAL REPORT
                           July 24,  1967
IODINE-131 ON VEGETATION: CANNED VERSUS BULK COUNTING
                          Wayne A.  Bliss

 Chinese nuclear detonations in late 1966 led to a small amount of radio -
 iodine fallout in southern Nevada which was easily detected on vegeta-
 tion samples.  The Environmental Surveillance Program of the Southwestern
 Radiological Health Laboratory was  at that time pondering the feasi-
 bility of compressing vegetation samples to a standard volume to en-
 hance counting  sensitivity and facilitate reproducible counting geome-
 tries.  The Chinese fallout had.deposited roughly 103 pCi/Kg of 131I
 on vegetation as determined from  sampling in support of the Nash
 Event,  January 19, 1967.   It was concluded that no fresh fission
 products  in the off-site area  at the time were a result of the Nash
 Event.  On January 26,  1967 three vegetation samples were collected
 from each of three locations:  3, 9,  and  25 miles southeast of Lathrop
 Wells,  Nevada along Highway 95.  The monitor making the  collections
 was instructed to choose three or four hundred grams of leafy material
 for each sample.  These samples were loosely packaged in 14 by 24
 inch plastic bags and gamma counted on a 3 x 3 inch Nal(Tl) crystal.
 The samples were then compressed  into  a plastic container 2 inches
 in height  and 4 inches in diameter  and  recounted.  The samples were
 analyzed for iodine-131 and the results,  expressed as pCi/Kg at
 time of collection, are shown in the  attached table.

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Various correlations among the data are shown.  It is readily appar-



ent without statistical proof that compressing the samples increased



the count  results by only a factor of about two.





Compressing these samples required the efforts of two persons.



With the necessary precautions to prevent cross-contamination,



cost of containers, etc. , the process is expensive.  In the bulk pro-



cess, the samples are placed in an additional bag and moved direct-



ly to the counting facility with little time and effort -when compared



to compacting.




Since vegetation sampling is used only for delineating cloud passage



and a rough estimator of milk contamination in routine surveillance,



compaction of samples appears to be unwarranted by these results



for SWRHL off-site surveillance.

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Location
3 miles SE
of Lathrop
Wells, Nevada



9 miles SE
of Lathrop
Wells, Nevada



25 miles SE
of Lathrop
Wells, Nevada



For all
Samples Average
Sample
Number
020317

020318

020319

020320

020321

020322

020323

020324

020325


d
Counting
Geometry
Bulk
Canned
Bulk
Canned
Bulk
Canned
Bulk
Canned
Bulk
Canned
Bulk
Canned
Bulk
Canned
Bulk
Canned
Bulk
Canned
Bulk
Canned
Deviation Ratio Of Ratio Of
Factor Of Of Average Highest Lowest
Greatest Sample Per Canned To Canned To
131 1 Deviation Location Lowest Highest
pCi/Kg Per Location (Canned/Bulk) Bulk Bulk
570 Bulk: 2.00 1.39 2.35 0.89
1010
1140
1190 Canned: 1.33
830
1340
1590 Bulk; 1.42 1.68 3.01 0.82
3370
1360
1310 Canned: 2.57
1120
2160
1410 Bulk: 1.33 1.44 2.42 0.89
2570
1060
1560 Canned: 2.06
1260
1250
1149 1.52 Average=2.59 Average= 0. 87
1751

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