ML112710119
| ML112710119 | |
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| Site: | Duane Arnold |
| Issue date: | 12/31/1989 |
| From: | Huebner L Teledyne Isotopes Midwest Lab |
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Text
'WTELEDYNE ISOTOPES MIDWEST LABORATORY 700 LANDWEHR ROAD NORTHBROOK, ILLINOIS 60062-2310 (708) 564-0700 FAX (708) 564-4517 REPORT TO IOWA ELECTRIC LIGHT AND POWER COMPANY CEDAR RAPIDS, IOWA ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM FOR THE DUANE ARNOLD ENERGY CENTER CEDAR RAPIDS, IOWA Docket No. 50-331 ANNUAL REPORT - PART I
SUMMARY
AND INTERPRETATION JANUARY - DECEMBER 1989 FOR SUBMITTAL TO THE NUCLEAR REGULATORY COMMISSION PREPARED AND SUBMITTED BY TELEDYNE ISOTOPES MIDWEST LABORATORY PROJECT NO. 8001 Approved by:
z (L. G. Huebner General Manager 23 February 1990
?o)420 960421,(:)21.
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9 1 ad-'mj'
PREFACE The staff members of the Teledyne Isotopes Midwest Laboratory were responsible for the acquisition of data presented in this rkport with the exception of Appendices D and E which were completed by Iowa Electric personnel.
All environmental samples, with the exception of aquatic, were collected by personnel of DAEC.
Aquatic samples were collected by University of Iowa Hygenic Laboratory personnel.
The report was prepared by L. G. Huebner, General Manager of the TIML, with the exception of Appendices D and E, which were prepared by Iowa Electric personnel. He was assisted in the report preparation by other staff members of the laboratory.
ii
No.
APPENDICES A
Interlaboratory Comparison Program Results......
B Data Reporting Conventions.........
C Maximum Permissible Concentrations of Radioactivity in Air and Water Above Natural Background in Unrestricted Areas...........
D Summary of the Land Use Census.....
E Annual Radiation Dose Assessment.....
PART II Data Tabulations and Analyses 11i TABLE OF CONTENTS PREFACE List of Tables.
List of Figures INTRODUCTION.
SUMMARY
ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM 3.1 Program Design and Data Interpretation 3.2 Program Description..........
3.3 Program Execution...........
3.4 Laboratory Procedures.........
3.5 Program Modifications.........
RESULTS AND DISCUSSION.
4.1 Atmospheric Nuclear Detonations and Nuclear Accidents..
4.2 Program Findings TABLES AND FIGURES.........
REFERENCES.......
1.0 2.0 3.0 4.0 Page i i iv v
1 2
3 3
4 6
6 7
8 5.0 6.0 8
8 12 32 A-1 B-1 C-1 D-1 E-1 i
LIST OF TABLES No.
5.1 Characteristic Properties of Isotopes Quantified in Gamma-spectroscopic Analyses.
5.2 Sample Collection and Analysis Program, 1989.....
5.3 Sampling Locations, DAEC....
5.4 Type and Frequency of Collections 5.5 Sample Codes Used in Table 5.4.
5.6 Missed Collections and Analyses, 1989 5.7 Environmental Radiological Monitoring Program Summary, 1988 In addition, the following tables are in the Appendices:
Appendix A A-1 Interlaboratory Comparison Program Results, 1986-1989 A-2 Interlaboratory Comparison Program Results, Thermoluminescent Dosimeters (TLDs)
A-3 In-house Spiked Samples..............
A-4 In-house "Blank" Samples.
Attachment B:
Acceptance Criteria for Spiked Samples.
Addendum to Appendix A:
Explanation of the Results Outside of Control Limits Page 13 14 18 20 22 23 24 A-3 A-16 A-20 A-26 A-31 A-32 Appendix C C-1 Maximum Permissible Concentrations of Radioactivity in Air and Water Above Natural Background in Unrestricted Areas.
C-2 iv
LIST OF FIGURES Radiological Environmental Monitoring Program Sampling Stations near the Duane Arnold Energy Center.....
Radiological Environmental Monitoring Program Sampling Stations Outside 0.5 Miles.............
v No.
5-1 5-2 30 31
1.0 INTRODUCTION
This report summarizes and interprets results of the Environmental Radiological Monitoring Program conducted by Teledyne Isotopes Midwest Laboratory at the Duane Arnold Energy Center, Cedar Rapids,
- Iowa, during the period January December, 1989.
This Program monitors the levels of radioactivity in the air, terrestrial, and aquatic environments in order to assess the impact of the Plant on its surroundings.
Tabulation of the individual analyses made during the year are included in Part II of this report.
Duane Arnold Energy Center (DAEC) is located in Linn County on the Cedar River, Iowa, and is operated by Iowa Electric Light and Power Company.
Duane Arnold Nuclear Station is a 565.7 MW(e) boiling water reactor.
Initial criticality was attained on 23 March 1974.
The reactor reached 100% power on 12 August 1974. Commercial operation began on 1 February 1975.
1
2.0
SUMMARY
The Environmental Radiological Monitoring Program required by the U.S. Nuclear Regulatory Commission (NRC) Technical Specifications for the Duane Arnold Nuclear Generating Plant is described.
Results for 1989 are summarized and discussed.
Program findings show background levels of radioactivity in the environmental samples collected in the vicinity of the Duane Arnold Energy Center. No effect on the environment due to the operation of the Duane Arnold Nuclear Plant is indicated.
2
3.0 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM 3.1 Program Design and Data Interpretation The purpose of the Environmental Radiological Monitoring Program at the Duane Arnold Energy Center (DAEC) is to assess the impact of the plant on its environment.
For this purpose, samples are collected from the air, terrestrial, and aquatic environments and analyzed for radioactive content.
In addition, ambient gamma radiation levels are monitored by thermoluminescent dosimeters (TLD's).
Sources of environmental radiation include the following:
(1) Natural background radiation arising from cosmic rays and primordial radionuclides; (2) Fallout from atmospheric nuclear detonations; (3) Releases from nuclear power plants; and (4) Industrial and medical radioactive waste.
In interpreting the data, effects due to the DAEC operation must be distinguished from those due to other sources.
A major interpretive aid in assessment of these effects is the design of the monitoring program at the DAEC which is based on the indicator control concept.
Most types of samples are collected both at indicator locations (nearby,
- downwind, or downstream) and at control locations (distant, upwind, or upstream).
A station effect would be indicated if the radiation level at an indicator location was significantly larger than that at the control location. The difference would have to be greater than could be accounted for by typical fluctuations in radiation levels arising from other sources.
An additional interpretive technique involves analyses for specific radio nuclides present in the environmental samples collected from the DAEC site.
The DAEC's monitoring program includes analyses for strontium-90 and iodine-131, which are fission products, and tritium, which is pro duced by cosmic rays, atmospheric nuclear detonations, and also by nuclear power plants.
Most samples are also analyzed for gamma-emitting isotopes with results for the following groups quantified:
zirconium-95, cesium-137, and cerium-144.
These three gamma-emitting isotopes were 3
selected as radiological impact indicators because of the different characteristic proportions in which they appear in the fission product mix produced by a nuclear reactor and that produced by a nuclear detona tion.
Each of the three isotopes is produced in roughly equivalent amounts by a reactor:
each constitutes about 10% of the total activity of fission products ten (10) days after reactor shutdown.
On the other hand, ten (10) days after a nuclear explosion, the contributions of zirconium-95, cerium-144, and cesium-137 to the activity of the resulting debris are in the approximate ratio 4:1:0.03 (Eisenbud, 1963).
The other group quantified consists of niobium-95, ruthenium-103 and
-106, cesium-134, barium-lanthanum-140, and cerium-141.
These isotopes are released in small quantities by nuclear power plants, but to date their major source of injection into the general environment has been atmospheric nuclear testing.
Nuclides of the next group, manganese-54, cobalt-58 and -60, and zinc-65, are activation products and arise from activation of corrosion products.
They are typical components of nuclear power plant effluents, but are not produced in significant quantities by nuclear detonations.
Nuclides of the final group, beryllium-7, which is of cosmogenic origin, and potassium-40, a naturally-occuring isotope, were chosen as calibration monitors and should not be considered radio logical impact indicators.
Characteristic properties of isotopes quantified in gamma-spectroscopic analyses are presented in Table 5.1.
Other means of distinguishing sources of environmental radiation can be employed in interpreting the data.
Current radiation levels can be compared with previous levels, including those measured before the Plant became operational.
Results of the DAEC's Monitoring Program can be related to those obtained in other parts of the world.
Finally, results can be related to events known to cause elevated levels of radiation in the environment, e.g., atmospheric nuclear detonations.
3.2 Program Description The sampling and analysis schedule for the environmental radiological monitoring program at the DAEC is summarized in Table 5.2 and is briefly reviewed below.
Table 5.3 defines the sampling location codes used in Table 5.2 and specifies for each location its type (indicator or control) and its distance, direction, and sector relative to the reactor site.
The types of samples collected at each location and the frequency of collections are presented in Table 5.4 using codes defined in Table 5.5.
To monitor the air environment, airborne particulates are collected on membrane filters by continuous pumping at twelve (12) locations.
- Also, airborne iodine is collected by continuous pumping through charcoal filters at six (6) of these locations.
Nine (9) of the twelve (12) locations are indicators and three (3) are controls (D-1, D-2, and 4
0-13).
Filters are changed and counted weekly.
Particulate filters are analyzed for gross beta activity.
If gross beta activity exceeds 10 times the yearly mean of the control samples gamma isotopic analysis is performed.
Quarterly composites of airborne particulates from each location are gamma scanned on a germanium detector.
All charcoal filters are analyzed weekly for 1-131 on all samples.
Ambient gamma radiation is monitored at twelve (12) air sampling loca tions.
In addition, gamma radiation is monitored at thirty-two (32) special locations:
seventeen (17) in a circle within 0.5 mi radius of the DAEC stack; six (6) in 22.50 sectors within 1 mi of the DAEC stack; and nine (9) in 22.50 sectors between 1 and 3 miles of the DAEC stack. The sensors are placed in quadruplicate at each location and are exchanged and analyzed quarterly.
Precipitation samples are collected monthly from one location and ana lyzed for gamma-emitting isotopes.
Quarterly composites are analyzed for tritium.
Milk samples are collected monthly from seven (7) locations during the non-grazing season, October through April, and biweekly during the grazing season, May 1 through September 30.
One of the locations is a control (D-105) and the rest are indicators.
All samples are analyzed for 1-131 and gamma-emitting isotopes.
For additional monitoring of the terrestrial environment, grain, hay, and broad leaf natural vegetation samples are collected annually from nine (9) locations:
one control (0-105) and eight (8) indicators (D-57, D-58, D-63, D-72, D-93, D-94, D-106 and D-16).
- Grain, hay, and broad leaf (green leafy) vegetation samples are analyzed for gamma-emitting isotopes and at least one broad leaf vegetation is analyzed for iodine-131.
When meat is slaughtered for home
- use, it is collected annually during or immediately following a grazing period from animals grazing on site.
The sample is analyzed for gamma-emitting isotopes.
Also, potable ground water is collected quarterly from a treated municipal water system (D-53),
the inlet to the municipal water treatment system (D-54),
and four (4) additional ground water locations (D-55, D-57, D-58, and D-72).
The samples are analyzed for gross beta and tritium. If gross beta activity exceeds 10 times yearly mean of the control samples, gamma isotopic, strontium-89, and strontium-90 analyses are performed.
Soil samples are collected once per year at two indicator locations (D-15 and D-16).
The samples are analyzed for strontium-90 and gamma-emitting isotopes.
Surface water is collected monthly from five (5) river, pond, and sewage effluent locations, one (1) control (D-49) and four (4) indicator (D-50, D-51, 0-99, and D-107).
All monthly samples are analyzed for gamma emitting isotopes.
Tritium analyses are performed on quarterly compo sites from each location.
In addition, all samples from Location D-107 (plant sewage discharge) are analyzed for K-40 by flame photometry.
5
The aquatic environment is also monitored by upstream and downstream (D-49 and D-61) semiannual collections of fish.
River bottom sediment is also collected semiannually at the plant's intake and discharge (D-50 and D-51) and downstream of the sewage plant (D-107).
The samples are analyzed for gamma-emitting isotopes.
3.3 Program Execution The program was executed as described in the preceding section with the following exceptions:
(1) No TLD data were available for Locations D-44 and D-39 for the second quarter of 1989 because the TLDs were lost in the field.
(2) No TLD data were available for Location D-10 for the third quarter of 1989 because the TLD was lost in the field.
(3) No TLD data were available for Location D-36 for the fourth quarter of 1989 because the TLD was lost in the field.
(4) No milk samples were collected from Locations D-93 and D-101 on 01-04-89 because samples were not available.
(5) No milk samples were collected from Locations D-93 and D-101 on 02-08-89 because samples were not available.
(6) No milk sample was collected from Location D-101 on 03-07-89 because the sample was not available.
(7) No milk sample was collected from Location D-93 on 05-31-89 because the sample was not available.
(8) Meat samples were not available in 1989 because no meat animals were slaughtered for home use.
3.4 Laboratory Procedures All iodine-131 analyses in milk were made by using a sensitive radio chemical procedure which involves separation of the element of interest by use of an ion-exchange resin and subsequent beta counting.
All gamma-spectroscopic analyses were performed with high resolution germanium detectors.
Levels of iodine-131 in natural vegetation were determined by germanium spectrometry.
Levels of airborne iodine-131 in charcoal samples were measured by germanium spectrometry.
Tritium levels were determined by the liquid scintillation technique.
6
Analytical Procedures used by TIML are specified in detail elsewhere (Teledyne Isotopes Midwest Laboratory, 1985).
Procedures are based on those prescribed by the National Center for Radiological Health of the U. S. Public Health Service (U. S. Public Health Service, 1967) and by the Health and Safety Laboratory of the U. S. Atomic Energy Commission (U. S. Atomic Energy Commission, 1972).
Details of TIML's QA Program are presented elsewhere (Teledyne Isotopes Midwest Laboratory, 1989).
The TIML QA Program includes participation in the Interlaboratory Comparison (Crosscheck)
Program.
Results obtained in the crosscheck program are presented in Appendix A.
3.5 Program Modifications There were no program modifications in 1989.
7
4.0 RESULTS AND DISCUSSION All of the scheduled collections and analyses were made on schedule except those listed in Table 5.6.
All results are summarized in Table 5.7 in a format recommended by the Nuclear Regulatory Commission in Regulatory Guide 4.8.
For each type of analysis of each sample medium, this table lists the mean and range of all indicator and control locations.
The locations with the highest mean and range are also shown.
The tabulated results of all measurements made in 1989 are not included in this section, although references to these results will be made in the discus sion.
The complete tabulation of the 1989 results is contained in Part II of the.1989 Annual Report on the Environmental Radiological Monitoring Program for the Duane Arnold Energy Center.
4.1 Atmospheric Nuclear Detonations and Nuclear Accidents There were no reported atmospheric nuclear tests in 1989.
The last reported test was conducted by the People's Republic of China on October 16, 1980.
The reported yield was in the 200 kiloton to 1 megaton range.
There were no reported accidents at nuclear reactor facilities in 1989.
4.2 Program Findings Results obtained show background levels of radioactivity in the environ mental samples collected in 1989.
Airborne Particulates The average annual gross beta concentration in airborne particulates was similar at indicator and control locations (0.026 and 0.029 pCi/m 3,
respectively) and was similar to levels in 1982 (0.026 pCi/m3, at both indicator and control locations),
1983 (0.022 and 0.024 pCi/m 3, respec tively),
1984 (0.025 and 0.026 pCi/m 3, respectively),
1985 (0.024 pCi/
m3 at both locations), in 1986 (0.024 pCi/im3, at both indicator and control locations),
in 1987 (0.024 and 0.026 pCi/m 3, respectively) and in 1988 (0.026 and 0.028 pCi/m 3, respectively).
The average of 0.024 pCi/m 3 for 1986 does not include the results from May 15 to June 12, 1986, which were influenced by the accident at Chernobyl.
8
A spring peak in beta activity had been observed almost annually for many years (Wilson et al., 1969).
It had been attributed to fallout of nuclides from the stratosphere (Gold et al., 1964).
It was pronounced in
- 1981, occurred to a lesser degree in 1982, and did not occur in 1983,
- 1984, 1985,
- 1987, 1988 or 1989.
In 1986, the spring peak could not be identified because it was overshadowed by the releases of radioactivity from Chernobyl.
Gamma spectroscopic analysis of quarterly composites of air particulate filters yielded similar results for indicator and control locations.
Beryllium-7, which is produced continuously in the upper atmosphere by cosmic radiation (Arnold and Al-Salih, 1955), was detected in all samples.
All other gamma-emitting isotopes were below their respective LLD limits.
No plant effect was indicated.
Airborne Iodine Weekly levels of airborne iodine-131 were below the lower limit of de tection (LLD) of 0.07 pCi/m 3 in all samples.
Ambient Radiation (TLDs)
At twelve (12) air sampling locations, the TLD readings averaged 15.4 mR/quarter at indicator locations and 13.6 mR/quarter at control loca tions.
At locations within 0.5 mile, 1.0 mile, and 3.0 mile radius of the stack, the measurements averaged 18.0 mR/quarter, 19.9 mR/quarter, and 16.5 mR/quarter, respectively.
The 'average for all locations was 17.1 mR/quarter.
This is slightly lower than the estimated average natural background radiation for Middle America, 19.5 mR/quarter, which is based on data on Pages 71 and 108 of the report, "Natural Background Radiation in the United States" (National Council on Radiation Protection and Measurements, 1975).
The terrestrial absorbed dose (uncorrected for structural and body shielding) ranges from 8.8 to 18.8 mrad/quarter and averages 11.5 mrad/quarter for Middle America. Cosmic radiation and cosmogenic radionuclides contribute 8.0 mrad/
quarter for a total average of 19.5 mrad/quarter. No plant effect was indicated.
Precipitation In precipitation, the tritium concentration was below the LLD of 330 pCi/1 in all samples.
All gamma-emitting isotopes were below their respective LLDs. No plant effect was indicated.
Milk Iodine-131 results were below the detection limit of 1.0 pCi/l in all samples.
9
No gamma-emitting isotopes, except naturally occurring potassium-40, were detected in any milk samples.
This is consistent with the finding of the National Center for Radiological Health that most radiocontami nants in feed do not find their way into milk due to the selective metabolism of the cow.
The common exceptions are radioisotopes of po tassium, cesium, strontium, barium, and iodine (National Center for Radiological Health,1968).
In summary, the milk data for 1989 show no radiological effects of the plant operation.
Ground Water The annual mean for gross beta activity measured 3.2 pCi/l and was similar to the levels observed in 1980 through 1988.
The location with the highest mean, 6.8 pCi/l, was D-58, a farm 1.0 miles distant from the plant.
Tritium was below the LLD of 330 pCi/l in all samples.
No plant effect was indicated.
Vegetation Iodine-131 results in broad leaf vegetation were below the LLD level of 0.051 pCi/g wet weight in all samples.
Except for potassium-40, which was observed in all samples (broadleaf vegetation,
- corn, hay, and green beans),
all other gamma-emitting iso topes were below detection limits in all samples.
No plant effect was indicated.
Soil Strontium-90 was detected in both samples and averaged 0.046 pCi/g dry weight.
Cesium-137 was detected in both samples and averaged 0.18 pCi/g dry weight.
Both strontium-90 and cesium-137 concentrations were similar to levels observed in 1987 (0.08 and 0.30 pCi/g dry weight, respectively) and in 1988 (0.064 and 0.33 pCi/g dry weight, respectively).
The only other gamma-emitting isotope detected was potassium-40 and averaged 13.1 pCi/g dry weight.
No plant effect on soil was indicated.
Surface Water Tritium was below the LLD level of 330 pCi/l in all samples.
All gamma-emitting isotopes were below their respective LLDs.
10
K-40 was measured at one location, D-107 (plant sewage discharge onsite).
The concentration ranged from 15.6 to 24.0 pCi/1 and averaged 19.3 pCi/l.
No plant effect on the radioactivity of surface water was indicated.
Fish All gamma-emitting isotopes, except naturally-occurring potassium-40, in edible portions were below detection limits.
The potassium-40 level was similar at both indicator and control locations (3.16 and 3.09 pCi/g wet weight, respectively).
No plant effect on fish was indicated.
River Sediments River sediments were collected in May and November,
- 1989, and analyzed for gamma-emitting isotopes.
Cesium-137 was detected in one sample and measured 0.13 pCi/g dry weight.
Potassium-40 ranged from 6.79 to 11.34 pCi/g dry weight and averaged 8.91 pCi/g dry weight.
All other gamma-emitting isotopes were below detection limits.
There was no indication of plant effect on the environment.
11
5.0 TABLES AND FIGURES 12
Table 5.1 Characteristic properties of isotopes quantified in gamma-spectroscopic analyses.
Designation Comments Isotope Half-lifea I. Naturally-occurring A. Cosmogenic B. Terrestrial Produced by interaction of cosmic rays with atmosphere Primordial Be-7 K-40 53.2 d II. Fission Productsb Nuclear detonations constitute the major environmental source A. Short-lived 1-131 Ba-140 B. Other than short-lived Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 III.
Activation Products Typically found in nuclear power plant effluents Mn-54 Co-58 Co-60 Zn-65 a Half-lives are taken from Appendix E of Environmental Quarterly, Department of Energy, 1978).
b Includes fission-product daughters.
1 January 1978, EML-334 (U. S.
1.26 x 109 y 8.04 d 12.8 d 35.15 d 65 d 39.35 d 368.2 d 2.061 y 30.174 y 32.5 d 284.31 d 312.5 d 70.78 d 5.26 y 245 d
Table 5.2.
Sample collection and analysis program, 1989.
Exposure Pathway Sampling Location and/or Sample Sampling and Type and Frequency Sample Point Description Collection Frequency of Analysis Airborne 1
Cedar Rapids (C)
Continuous operation of Analyze for gross beta activity Particulates 2
Marion (C) sampler with sample more than 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> after filter 3
Hiawatha collection at least once change. Perform gamma isotopic 5
Palo per week or as required analysisa on each sample having 6
Center Point by dust loading, gross beta activity greater than 7
Shellsburg ten times the yearly mean of the 8
Urbana control samples.
10 Atkins 11 Toddville Composite weekly samples to 13 Alburnett (C) form a quarterly composite (by 15 On-site North location).
Analyze quarterly 16 On-site South composite for gamma isotopic.
Airborne 2
Marion (C)
Continuous operation of Analyze each cartridge indivi Iodine 5
Palo sampler with sample dually for iodine-131.
7 Shellsburg collection at least 8
Urbana once per week.
11 Toddville 15 On-site North Ambient 1-3, Air Particulate Two dosimeters contin-Read gamma radiation dose Radiation 5-8, Locations uously at each location, quarterly on one dosimeter.
10,11, Both dosimeters are Anneal and repackage the second 13 changed at least dosimeter.
15,16 quarterly.
18-23, Within 0.5 mile 28-32, of stack 82-86 91 I-.
Table 5.2.
Sample collection and analysis program, 1989 (continued)
Exposure Pathway Sampling Location and/or Sample Sampling and Type and Frequency Sample Point Description Collection Frequency of Analysis Ambient 33-41 Within 3.0 miles Two dosimeters contin-Read gamma radiation dose Radiation of stack uously at each location.
quarterly on one dosimeter.
(continued)
Both dosimeters are Anneal and repackage the second 43-48 Within 1.0 mile changed at least dosimeter.
of stack quarterly.
Surface Water 49 Lewis Access (C)
Once per month.
Gamma isotopic analyses of each 50 Plant Intake (C) sample (by location).
51 Plant Discharge 99 Pleasant Creek Composite monthly samples to form 107 Plant Sewage quarterly composite (by location).
Discharge Analyze quarterly composite for tritium.
Ground Water 53 Treated Municipal Grab sample at least Gross beta and tritium activity (Potable)
Water once per quarter.
analysis on quarterly sample.
If 54 Inlet to Municipal gross beta is greater than ten Water Treatment times the yearly mean of control System samples, perform gamma isotopic 55 On-site well and Sr-89 and Sr-90 analyses.
57,58 Wells off-site 72 and within 4 km of DAEC
Table 5.2.
Sample collection and analysis program, 1989 (continued)
Exposure Pathway Sampling Location and/or Sample Sampling and Type and Frequency Sample Point Description Collection Frequency of Analysis River 50 Plant Intake (C)
At least once every Gamma isotopic analysis of each Sediment 51 Plant Discharge six months sample.
107 Sewage Effluent Canal Vegetation 16, 57, Farms that raise Annually at harvest Gamma isotopic analysis of 58, 63, food crops time.
One sample of edible portions.
72, 93, each:
grain, green 94, 106, leafy, and forage. At 1-131 analysis on broadleaf 105 (C) least one sample should vegetation.
be broadleaf vegetation.
Fish 49 Cedar River One sample per 6 months Gamma isotopic analysis on edible upstream of (once during January portions.
DAEC not through July and once influenced during August through by effluent (C)
December).
61 Downstream of DAEC in influence of effluent
Table 5.2.
Sample collection and analysis program, 1989 (continued)
Exposure Pathway Sampling Location and/or Sample Sampling and Type and Frequency Sample Point Description Collection Frequency of Analysis Milkb 105 Control farm near At least once per two During the grazing season:
Gamma Amana, Iowa weeks during the grazing isotopic and iodine-131 analyses season.
of each sample.
63, 93 Dairy farms At least once per month During the non-grazing season:
94, 96, within 10 during non-grazing gamma isotopic and iodine-131 101, 106 miles of site season.
analyses of each sample Precipitation On-site Monthly Gamma isotopic on all samples.
On-site Tritium on quarterly composites.
Meatc On-site Annually Gamma isotopic.
Soil 15, 16 On-site Annually Gamma isotopic and Sr-90.
a Gamm2 4
n+^4 1
A 1
b c
p c,
ana s
an ania ys) s or gammia-em i ti Lng nucl I i des re er LO h i UCso I U L i
gamma ray spectrum analysis. Any radionuclide detected at a concentration greater than the lower limit of detection (LLD) should be reported quantitatively. Conversely, any radionuclide concentration less than the LLD should not be reported.
The grazing season is considered to be May 1 through September 30.
Meat was not collected in 1989, no animals slaughtered for home use.
Sampling locations, Duane Arnold Energy Center.
Sampling Location Distance and Sampling Location Direction from Code Typea Point Description Site Stack D-1 D-2 D-3 D-5 D-6 D-7 D-8 D-10 D-11 D-13 D-15 D-16 D-18 D-19 D-20 D-21 D-22 D-23 D-28 D-29 D-30 D-31 D-32 D-33 D-34 D-35 D-36 D-37 D-38 D-39 D-40 0-41 D-43 D-44 0-45 D-46 D-47 D-48 D-49 C
1 C
2 3
5 6
7 8
10 11 C
13 15 16 18 19 20 21 22 23 28 29 30 31 32 33 34 35 36 37 38 39 40 41 43 44 45 46 47 48 C
49 Cedar Rapids Marion Hiawatha Palo Center Point Shellsburg Urbana Atkins Toddville Alburnett On-site, Northwest On-site, South Lewis Access, upstream of DAEC SE ESE SE SSW N
W NW SSW E
ENE NW SSE 18 11 11 7
3 7
6 10 9
4 9
0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 3.0 3.0 3.0 3.0 3.0 3.0 3.0 3.0 3.0 1.0 1.0 1.0 1.0 1.0 1.0 4.0
@ 1350
@ 1250
@ 1300
@ 2000
@ 00
@ 2550
@ 3450
@ 2100
@ 900
@ 700
@ 3050
@ 1900 NNE NE ENE ENE E
ESE WSW W
WNW NW NNW N
NNE NE ENE E
SSW WSW W
WNW WNW NW NNW Tabl e 5.3
Sampling locations, Duane Arnold Energy Center (continued)
Sampling Location Distance and Sampling Location Direction from Code Typea Point Description Site Stack D-50 C
50 Plant Intake D-51 51 Plant Discharge D-53 53 Treated Municipal Water D-54 54 Inlet to Municipal Water Treatment System D-55 55 On-site Well D-57 57 Farm (Off-site well) 1.0 mi WSW D-58 58 Farm (Off-site well) 0.5 mi WSW-SW D-61 61 0.5 mi downstream of plant discharge D-63 63 Farm 1.5 mi WNW D-72 72 Farm 2.0 mi SSW D-82 82 0.5 mi SE D-83 83 0.5 mi SSE D-84 84 0.5 mi S D-85 85 0.5 mi SSW D-86 86 0.5 mi SW D-91 91 0.5 mi N D-93 93 Farm 2.8 mi NNE D-94 94 Farm 2.7 mi N D-96 96 Farm 8.0 mi SSW D-99 99 Pleasant Creek Lake 2.5 mi WNW D-101 101 Farm 4.0 mi E D-105 C
105 Farm 21.3 mi SSW D-106 106 Farm 4.5 mi SE D-107 107 Sewage Effluent Canal Onsite a nC" denotes control location.
All other locations are indicators.
19 Table 5.3
Type and frequency of collection.
Location Semi Location Typea Weekly Monthly Quarterly Annually Annually D-1 C
AP,AI TLD 0-3 AP TLD D-5 AP,AI TLD 0-6 AP TLD D-7 AP,AI TLD 0-8 AP,AI TLD D-10 AP TLD D-11 AP,AI TLD D-13 C
AP TLD D-15 AP,AI TLD SO D-16 AP TLD so, Gb D-18 TLD through D-23 D-28 TLD through D-41 D-43 TLD through D-48 0-49 C
SW F
0-50 C
SW RS 0-51 SW RS D-53 WW D-54 WW D-55 WW D-57 WW Gb D-58 WW Gb 0-61 F
D-63 Mc Gb D-72 WW Gb D-82 TLD through D-86 D-91 TLO D-93 Mc Gb D-94 Mc Gb D-96 Mc D-99 SW 20 Tabl e 5.4
Table 5.4 Type and frequency of collection (continued)
Location Semi Location Typea Weekly Monthly Quarterly Annually Annually D-101 Mc D-105 C
Mc Gb D-106 Mc Gb D-107 SW RS On-site P
ME a Control locations are indicated by a "C" in this column.
All other locations b are indicators.
c Vegetation (G) includes broad leaf vegetation and grain.
Monthly from October through April; weekly from May through September.
21
Table 5.5. Sample codes used in Table 5.4.
Code Description AP Airborne Particulates AI Airborne Iodine TLD Thermoluminescent Dosimeter P
Precipitation M
Milk WW Well Water G
Vegetation (broad leaf and grain)
ME Meat SO Soil SW Surface Water F
Fish RS River Sediment 22
Missed collections and analyses, Duane Arnold Energy Center, 1989.
Collection Date Sample Analysis Location or Period Comments Milk 1-131, Gamma D-93 01-04-89 Sample unavailable.
Milk 1-131, Gamma D-101 01-04-89 Sample unavailable.
Milk 1-131, Gamma D-93 02-08-89 Sample unavailable.
Milk 1-131, Gamma D-101 02-08-89 Sample unavailable.
Milk 1-131, Gamma D-101 03-07-89 Sample unavailable.
Milk 1-131, Gamma D-93 05-31-89 Sample unavailable.
TLD Gamma D-44 06-29-89 Lost in the field.
TLD Gamma D-39 06-29-89 Lost in the field.
TLD Gamma D-10 09-21-89 Lost in the field.
TLD Gamma D-36 12-28-89 Lost in the field.
23 Table 5.6.
Table 5.7.
Environmental Radiological Monitoring Program Summary.
Name of Facility Location of Facility Duane Arnold Energy Center Linn, Iowa (County, State)
Docket No.
Reporting Period 50-331 January -
December, 1989 Indicator Location with Highest Control Sample Type and Locations Annual Mean Locations Number of Type Number of Mean (F)c Mean (F)
Mean (F)
Non-routine (Units)
Analysesa LLDb Rangec Locationd Range Range Resultse Airborne GB 624 0.005f 0.026 (465/468)
D-13, Alburnett 0.031 (52/52) 0.029 (155/156) 0 Particylates (0.006-0.128) 9 mi ENE (0.013-0.071)
(0.008-0.073)
(p-/
GS 48 Be-7 0.012 0.058 (36/36)
D-2, Marion 0.071 (4/4) 0.067 (12/12) 0 (0.035-0.10) 11 mi ESE (0.051-0.10)
(0.051-0.10)
Nb-95 0.0029
<LLD
<LLD 0
Zr-95 0.0042
<LLD
<LLD 0
Ru-103 0.0023
<LLD
<LLD 0
Ru-106 0.015
<LLD
<LLD 0
Cs-134 0.0016
<LLD
<LLD 0
Cs-137 0.0019
<LLD
<LLD 0
Ce-141 0.0036
<LLD
<LLD 0
Ce-144 0.011
<LLD
<LLD 0
Airborne Iodine 1-131 312 0.079
<LLD
<LLD 0
15.4 (35/35)
D-8, Urbana 17.2 (4/4) 13.6 (12/12) 0 (mR/Qtr.)
(11.5-18.2) 10 mi NW (16.7-17.8)
(12.0-15.7)
TLD, Within 0.5 Gamma 68 1
18.0 (68/68)
D-31, On-site 22.8 (4/4)
None 0
mi radius of (12.4-23.3) 0.5 mi NW (22.2-23.3) stack (mR/Qtr.)
TLD, Within 1.0 Gamma 23 1
19.9 (23/23)
D-47, 1.0 mi WNW 23.3 (4/4)
None 0
mi radius of (15.1-25.9)
(22.1-25.9) stack (mR/Qtr.)
- TLD, Within 3.0 Gamma 34 1
16.5 (34/34)
D-37, 3.0 mi E 21.6 (4/4)
None 0
mi radius of (12.7-22.9)
(19.6-22.9) stack (mR/Qtr.)
Precipitation H-3 4
330
<LLD None 0
(pCi/1)
GS 12 Mn-54 22
<LLD None 0
Fe-59 43
<LLD None 0
Co-58 19
<LLD None 0
Table 5.7.
Environmental Radiological Monitoring Program Summary Name of Facility Location of Facility Duane Arnold Energy Center Linn, Iowa (continued)
Docket No.
50-331 Reporting Period January - December, 1989 (County, State)
Indicator Location with Highest Control Sample Type and Locations Annual Mean Locations Number of Type Number of Mean (F)c Mean (F)
Mean (F)
Non-routine (Units)
Analysesa LLDb Rangec Locationd Range Range Resultse Precipitation (pCi/1)
(continued)
Milk (pCi/1)
Ground Water (pCi/1)
Broad Leaf Vegetation (pCi/g wet)
Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 1-131 GS K-40 Cs-134 Cs-137 Ba-140 La-140 Gross Beta H-3 1-131 GS K-40 120 120 24 1 24 8
8 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 20 38 23 36 39 17 20 98 21 1.0 100 15 18 60 15 0.8 330 0.051 0.5 0.057 0.059 0.052 0.052 0.096 0.048 0.50
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD 1450 (102/102)
(1000-2040)
<LLD
<LLD
<LLD
<LLD 3.3 (20/24)
(0.9-7.5)
<LLD
<LLD 3.46 (7/7)
(1.54-5.65)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD 0-101, Farm 4.0 mi E D-58, Farm 1.0 mi WSW-SW 0-94, Farm 2.7 mi N 1750 (15/15 (1070-2040) 6.8 (4/4)
(6.3-7.5) 5.65 (1/1)
None None None None None None None None None
<LLD 1250 (18/18)
(1130-1400)
<LLD
<LLD
<LLD
<LLD None None
<LLD 2.91 (1/1)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 o
Table 5.7.
Environmental Radiological Monitoring Program Summary Name of Facility Location of Facility Duane Arnold Energy Center Linn, Iowa (County, State)
(continued)
Docket No.
50-331 Reporting Period January - December, 1989 Indicator Location with Highest Control Sample Type and Locations Annual Mean Locations Number of Type Number of Mean (F)c Mean (F)
Mean (F)
Non-routine (Units)
Analysesa LLDb Rangec Locationd Range Range Resultse Broad Leaf Ru-103 0.048
<LLD
<LLD 0
Vegetation Ru-106 0.50
<LLD
<LLD 0
(pCi/g wet)
Cs-134 0.050
<LLD
<LLD 0
(continued)
Cs-137 0.056
<LLD
<LLD 0
Ce-141 0.073
<LLD
<LLD 0
Ce-144 0.031
<LLD
<LLD 0
Vegetation -
Corn GS 8
(pCi/g wet)
K-40 0.5 2.79 (7/7)
D-72, Farm 3.32 (1/1) 2.76 (1/1) 0 (1.90-3.32) 2.0 mi SW Mn-54 0.025
<LLD
<LLD 0
Co-58 0.024
<LLD
<LLD 0
Co-60 0.029
<LLD
<LLD 0
Nb-95 0.029
<LLD
<LLD 0
Zr-95 0.051
<LLD
<LLD 0
Ru-103 0.024
<LLD
<LLD 0
Ru-106 0.26
<LLD
<LLD 0
Cs-134 0.024
<LLD
<LLD 0
Cs-137 0.029
<LLD
<LLD 0
Ce-141 0.029
<LLD
<LLD 0
Ce-144 0.12
<LLD
<LLD 0
Vegetation Soy Beans (pCi/g wet)
GS K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 1
0.5 0.034 0.031 0.045 0.033 0.055 0.031 0.27 0.031 0.041 0.038 0.17 10.41 (1/1)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD 0-16, Onsite 0.5 mi SSE 10.41 (1/1)
None None None None None None None.
0 0
0 0
0 0
0 0
0 0
0
Table 5.7.
Environmental Radiological Monitoring Program Summary (continued)
Name of Facility Location of Facility Duane Arnold Energy Center Linn, Iowa (County, State)
Docket No.
50-331 Reporting Period January - December, 1989 Sample Type (Units)
Vegetation -
Hay (pCi/g wet)
Soil (pCi/g dry)
Type and Number of Analysesa I
I i
GS K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 Sr-90 6
2 2
GS K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 LLDb 0.5 0.035 0.036 0.034 0.041 0.067 0.039 0.30 0.032 0.035 0.064 0.24 0.01 0.5 0.043 0.080 0.045 0.20 0.17 0.15 0.41 0.045 0.060 0.31 0.25 Indicator Locations Mean (F)c Rangec 13.45 (5/5)
(6.71-17.30)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD 0.046 (2/2)
(0.017-0.076) 11.09 (2/2)
(8.28-13.90)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD 0.18 (2/2)
(0.076-0.28)
<LLD
<LLD Location with Highest Annual Mean Locationd 0-93, Farm 2.8 mi NNE D-15, On-site
- 0.
5 mi NW D-15, On-site 0.5 mi NW D-15, On-site 0.5 mi NW Mean (F)
Range r")
17.30 (1/1) 0.076 (1/1) 13.90 (1/1) 0.28 (1/1)
Control Locations Mean (F)
Range 11.50 (1/1)
<LD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD None None None None None None None None None None None None None Number of Non-routine Resultse 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 i
iIII
Table 5.7.
Environmental Radiological Monitoring Program Summary (continued)
Name of Facility Location of Facility Duane Arnold Energy Center Linn, Iowa (County, State)
Docket No.
Reporting Period 50-331 January - December. 1989 Sample Type (Units)
Surface Water (pCi/1)
River Sediments (pCi/g dry)
Type and Number of Analysesa H-3 K-40 GS Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 GS K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 20 12 60 6
4 LLDb 330 0.5 15 30 15 15 30 15 30 500 15 18 60 15 Indicator Locations Mean (F)c Rangec
<LLD 19.3 (12/12)
(15.6-24.0)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD Location with Highest Annual Mean Locationd D-107, On-site Sewage Effluent
+
+
4 4
1.0 0.056 0.052 0.091 0.011 0.10 0.079 0.40 0.045 0.058 0.14 0.27 8.72 (4/4)
(6.79-10.30)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD D-50, Plant Intake 0-50, Plant Intake 4-
-~ __________________
Mean (F)
Range Control Locations Mean (F)
Range
<LLD None N) 19.3 (12/12)
(15.6-24.0)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD 9.30 (2/2)
(7.27-11.34)
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD
<LLD 0.13 (1/2)
<LLD
<LLD 9.30 (2/2)
(7.27-11.34) 0.13 (1/2)
Number of Non-routine Resultse 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0
Table 5.7.
Environmental Radiological Monitoring Program Summary (continued)
Name of Facility Location of Facility Duane Arnold Energy Center
- Linn, lowa (County, State)
Docket No.
50-331 Reporting Period January - December, 1989 Indicator Location with Highest Control Sample Type and Locations Annual Mean Locations Number of Type Number of Mean (F)c Mean (F)
Mean (F)
Non-routine (Units)
Analysesa LLDb Rangec Locationd Range Range Resultse Fish GS 12 (Edible portion)
(pCi/g wet)
K-40 0.5 3.16 (6/6)
D-61, Cedar River 3.16 (6/6) 3.09 (6/6) 0 (2.07-4.82) 0.5 mi downstream (2.07-4.82)
(2.51-3.77) of discharge Mn-54 0.12
<LLD
<LLD 0
Co-58 0.14
<LLD
<LLD 0
Co-60 0.11
<LLD
<LLD 0
Nb-95 0.18
<LLD
<LLD 0
Zr-95 0.26
<LLD
<LLD 0
Ru-103 0.13
<LLD
<LLD 0
Ru-106 1.09
<LLD
<LLD 0
Cs-134 0.11
<LLD
<LLD 0
Cs-137 0.12
<LLD
<LLD 0
Ce-141 0.23
<LLD
<LLD 0
Ce-144 0.66
<LLD
<LLD 0
a GB = Gross beta; GS = Gamma scan.
b LLD = Nominal lower limit of detection based on 4.66 sigma error for background sample.
c Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (F).
d Locations are specified by: (1) name and code (Table 5.3); and (2) distance, direction, and sector relative to reactor site.
e Nonroutine results are those which exceed ten times the control station value.
If a control station value is unavailable, the result is considered nonroutine if it exceeds ten times the preoperational value for the location.
f One (1) result has been excluded in the determination of LLD for gross beta.
Higher than normal LLD (<0.01 pCi/m 3) resulted from low volume due to pump malfunction.
9 LLD for airborne iodine could not be reached at two locations during 1989.
Values of <0.289 and <0.279 resulted from extremely low volumes due to air sampler pump malfunctions.
N) t.0
e 5-1 Radiological Envirorwental Monitoring Program Sampling Stations near the Duane Arnold Energy Center.
'ma I
0 LUj
~RD 4t--.a-I
+
I I
DAEC a
U I
I U
S I
g~j 1~
CO -' P 30
Rev. 7, 12-18-87
.Figure 5-2.
Radiological Environmental Monitoring Program Sampling Stations outside 0.5 miles.
all r4 31
6.0 REFERENCES
- Arnold, J. R. and H. A. Al-Salih.
1955.
Beryllium-7 Produced by Cosmic Rays Science 121:
451-453.
Eisenbud, M.
1963.
Environmental Radioactivity, McGraw-Hill, New York, New York, pp. 213, 275, and 276.
Gold, S. H. W. Barkhau, B. Shlein, and B. Kahn, 1964. Measurement of Naturally Occurring Radionuclides in Air, in the Natural Radiation Environment, University of Chicago Press, Chicago, Illinois, 369-382.
Hazleton Environmental Sciences.
1981.
Environmental Radiological Monitoring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1980.
Hazleton Environmental Sciences.
1982.
Environmental Radiological Monitoring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1981.
Hazleton Environmental Sciences.
1983.
Environmental Radiological Monitoring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1982.
Hohenemser, C. M. Deicher, A. Ernst, H. Hofsass, G. Lindner, E. Racknagel.
1986.
Chernobyl, in Chemtech, October 1986, pp. 596-605.
National Center for Radiological Health, 1968.
Radiological Health and Data Reports, Vol. 9, Number 12, 730-746.
Teledyne Isotopes Midwest Laboratory.
1985.
Analytical Procedures Manual, Revision 5, 29 July 1985.
Teledyne Isotopes Midwest Laboratory.
1989.
Quality Control
- Program, Revi sion 11, 05 April 1989.
Teledyne Isotopes Midwest Laboratory. 1989. Quality Control Procedures Manual, Revision 10, 30 November 1989.
Teledyne Isotopes Midwest Laboratory.
1990.
Quality Assurance Program Manual, Revision 2, 08 January 1990.
Teledyne Isotopes Midwest Laboratory.
1984.
Environmental Radiological Monit oring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1983.
Teledyne Isotopes Midwest Laboratory.
1985.
Environmental Radiological Monit oring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1984.
32
Teledyne Isotopes Midwest Laboratory.
1986.
Environmental Radiological Moni toring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1985.
Teledyne Isotopes Midwest Laboratory.
1987.
Environmental Radiological Moni toring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1986.
Teledyne Isotopes Midwest Laboratory.
1988.
Environmental Radiological Moni toring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1987.
Teledyne Isotopes Midwest Laboratory.
1989.
Environmental Radiological Moni toring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1988.
Teledyne Isotopes Midwest Laboratory.
1990.
Environmental Radiological Moni toring Program for the Duane Arnold Energy Center, Annual Report - Part II, Data Tabulations and Analyses, January - December 1989.
Wilson, D. W.,
G. M. Ward and J. E. Johnson, 1969.
In Environmental Contami nation of Radioactive Materials, International Atomic Energy Agency,
- p. 125.
33
'WTELEDYNE ISOTOPES MIDWEST LABORATORY 700 LANOWEHR ROAD NORTHBROOK, ILLINOIS 60062-2310 (708) 584-0700 FAX (708) 564-4517 Appendix A Interlaboratory Comparison Program Results NOTE:
TIML participates in intercomparison studies administered by U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada. The results are reported in Appendix A. Also reported are results of in house spikes and blanks. Appendix A is updated twice a year and the complete Appendix is included in January and July monthly reports only.
Please refer to January and July Reports for information.
January 1990.
A-1
Appendix A Interlaboratory Comparison Program Results Teledyne Isotopes Midwest Laboratory (formerly Hazleton Environmental Sciences) has participated in interlaboratory comparison (crosscheck) programs since the formulation of its quality control program in December 1971.
These programs are operated by agencies which supply environmental-type samples (e.g., milk or water) containing concentrations of radionuclides known to the issuing agency but not to participant laboratories.
The purpose of such a program is to provide an independent check on the laboratory's analytical procedures and to alert it to any possible problems.
Participant laboratories measure the concentrations of specified radionuclides and report them to the issuing agency.
Several months later, the agency reports the known values to the participant laboratories and specifies control limits.
Results consistently higher or lower than the known values or outside the control limits indicate a need to check the instruments or procedures used.
The results in Table A-1 were obtained through participation in the environmental sample crosscheck program for milk, water, air filters, and food samples during the period January 1986 through November, 1989.
This program has been conducted by the U.S.
Environmental Protection Agency Intercomparison and Calibration Section, Quality Assurance Branch, Environmental Monitoring and Support Labora tory, Las Vegas, Nevada.
The results in Table A-2 were obtained for thermoluminescent dosimeters (TLD's) during the period 1976,
- 1977, 1979,
- 1980, 1984, and 1985-1986 through partici pation in the Second,
- Third, Fourth,
- Fifth, Seventh, and Eighth International Intercomparison of Environmental Dosimeters under the sponsorships listed in Table A-2. Also Teledyne testing results are listed.
Table A-3 lists results of the analyses on in-house spiked samples.
Table A-4 lists results of the analyses on in-house "blank" samples.
Attachment B lists acceptance criteria for "spiked" samples.
Addendum to Appendix A provides explanation for out of limit results.
A-2
Table A-1.
U.S. Environmental Protection Agency's crosscheck program, com parison of EPA and Teledyne Isotopes Midwest Laboratory results for milk, water, air filters, and food samples, 1986 through 1989.a Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-2ac 1s, N=1 Control Limits STF-447 Food Jan 1986 STW-448 Water Feb 1986 STW-449 Water Feb 1986 STW-450 Water Feb 1986 STM-451 Milk Feb 1986 STW-452 Water Mar 1986 STW-453 Water Mar 1986 STW-454 Water Apr 1986 Sr-89 Sr-90 1-131 Cs-137 K
Cr-51 Co-60 Zn-65 Ru-106 Cs-134 Cs-137 H-3 U total 1-131 Ra-226 Ra-228 Gr. alpha Gr. beta 1-131 24.3+/-2.5 17.3+/-0.6 22.7+/-2.3 16.3+/-0.6 927+/-46 45.0+/-3.6 19.7+/-1.5 44.0+/-3.5
<9.0 28.3+/-2.3 23.7+/-0.6 5176+/-48 8.0+/-0.0 7.0+/-0.0 25.0+/-5.0 10.0+/-1.5 20.0+/-0.6 15.0+/-5.0 950+/-144 38.0+/-5.0 18.0+/-5.0 40.0+/-5.0
- 0.
0+/-5.0 30.0+/-5.0 22.0+/-5.0 5227+/-525 4317<6137
- 9.
0+/-6.0 9.0+/-6.0 3.8+/-0.1 4.1+/-0.6 11.0+/-0.5 12.4+/-1.8 6.7+/-0.6 7.3+/-0.6 7.0+/-0.0 15.0+/-5.0 8.0+/-5.0 9.0+/-6.0 STW-455 Water 456 (Blind)
Sample A Sample B 16.3-33.7 7.4-12.6 9.6-30.4 6.3-23.7 701-1199 29.3-46.7 9.3-26.7 31.3-48.7 0.0-8.7 21.3-38.7 13.3-30.7 0.0-19.4 0.0-19.4 3.0-5.2 9.2-15.5 6.3-23.7 0.0-16.7 0.0-19.4 Apr 1986 Gr. alpha Ra-226 Ra-228 Uranium Gr. beta Sr-89 Sr-90 Co-60 Cs-134 Cs-137 15.0+/-1.0 3.1+/-0.1 1.5+/-0.2 4.7+/-0.6 28.7+/-1.2 5.7+/-0.6 7.0+/-0.0 10.7+/-1.5 4.0+/-1.7 5.3+/-0.6 17.0+/-5.0 2.9+/-0.4 2.0+/-0.3 5.0+/-6.0 35.0+/-5.0
- 7.
0+/-5.0 7.0+/-1.5 10.0+/-5.0 5.0+/-5.0
- 5.
0+/-5.0 8.3-25.7 2.1-3.7 1.5-2.5 0.0-15.4 26.3-43.7 0.0-15.7 4.4-9.6 1.3-18.7 0.0-13.7 0.0-13.7 A-3
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-2oc is, N=i Control Limits STAF-457 Air Filter April 1986 STU-458 Urine April 1986 STW-459 Water May 1986 STW-460 Water May 1986 STW-461 Water June 1986 STW-462 Water June 1986 STM-464 Milk June 1986 STW-465 Water July 1986 STW-467 Water August 1986 STW-468 Water August 1986 STW-469 Water August 1986 STAF-470 471 472 Air Filter Sept 1986 STW-473 Water Sept 1986 Gr. alpha Gr. beta Sr-90 Cs-137 Tritium Sr-89 Sr-90 Gr. alpha Gr. beta Cr-51 Co-60 Zn-65 Ru-106 Cs-134 Cs-137 Tritium Sr-89 Sr-90 1-131 Cs-137 K
Gr. alpha Gr. beta 1-131 Pu-239 Uranium Gr. alpha Gr. beta Sr-90 Cs-137-Ra-226 Ra-228 13.7+/-0.6 46.3+/-0.6 14.7+/-0.6 10.7+/-0.6 4313+/-70 4.3+/-0.6 5.0+/-0.0 5.3+/-0.6 11.3+/-1.2
<9.0 66.0+/-1.0 87.3+/-1.5
- 39. 7+/-2. 5 49.3+/-2.5 10.3+/-1.5 3427+/-25
<1.0 15.3+/-0.6 48.3+/-2.3 43.7+/-1.5 1567+/-114
- 4.
7+/-0. 6 18.7+/-1.2
- 30. 3+/-0. 6 11.3+/-0.6 4.0+/-0.0
- 19. 3+/-1. 5 64.0+/-2.6 22.0+/-1.0
- 25. 7+/-1.5 6.0+/-0.1
- 8. 7+/-1. 1 15.0+/-5.0 6.3-23.7 47.0+/-5.0 38.3-55.7 18.0+/-1.5 15.4-20.6 10.0+/-5.0 1.3-18.7 4423+/-189 4096-4750 5.0+/-5.0 0.0-13.7 5.0+/-1.5 2.4-7.6 8.0+/-5.0 0.0-16.7 15.0+/-5.0 6.3-23.7 0.0+/-5.0 66.0+/-5.0 86.0+/-5.0 50.0+/-5.0 49.0+/-5.0 10.0+/-5.0 0.0-8.7 57.3-74.7 77.3-94.7 41.3-58.7 40.3-57.7 1.3-18.7 3125+/-361 2499-3751 0.0+/-5.0 16.0+/-1.5 41.0+/-6.0 31.0+/-5.0 1600+/-80 0.0-8.7 13.4-18.6 30.6-51.4 22.3-39.7 1461-1739 6.0+/-5.0 0.0-14.7 18.0+/-5.0 9.3-26.7 45.0+/-6.0 34.4-55.4 10.1+/-1.0 8.3-11.9 4.0+/-6.0 0.0-14.4 22.0+/-5.0 66.0+/-5.0 22.0+/-5.0 22.0+/-5.0 13.3-30.7 57.3-74.7 19.4-24.6 13.3-30.7 6.1+/-0.9 4.5-7.7 9.1+/-1.4 6.7-11.5 A-4
Table A-1.
(continued).
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-2oc is, N=1 Control Limits STW-474 Water Sept 1986 STW-475 Water Oct 1986 STW-476 Water Oct 1986 SPW-477 Water Oct 1986 478 (Blind)
Gr. alpha Gr. beta Cr-51 Co-60 Zn-65 Ru-106 Cs-134 Cs-137 H-3 16.3+/-3.2 9.0+/-1.0 63.3+/-5.5 31.0+/-2.0 87.3+/-5.9 74.7+/-7.4
- 25. 7+/-0. 6 46.3+/-1.5 5918+/-60 15.0+/-5.0 6.3-23.7 8.0+/-5.0 0.0-16.7 59.0+/-5.0 31.0+/-5.0 85.0+/-5.0 74.0+/-5.0 28.0+/-5.0 44.0+/-5.0 50.3-67.7 22.3-39.7 76.3-93.7 65.3-82.7 19.3-36.7 35.3-52.7 5973+/-597 4938-7008 Sample A Sample B STM-479 Milk Gr. alpha Ra-226 Ra-228 Uranium Gr. beta Sr-89 Sr-90 Co-60 Cs-134 Cs-137 Nov 1986 STU-480 Urine Nov 1986 STW-481 Water Nov 1986 STW-482 Water Dec 1986 STW-483 Water Jan 1987 Sr-89 Sr-90 1-131 Cs-137 K
H-3 Gr. alpha Gr. beta Ra-226 Ra-228 Sr-89 Sr-90 34.0+/-6.0 5.8+/-0.2
- 2.
7+/-1.0 11.0+/-0.0 38.7+/-1.2 5.0+/-0.0 3.0+/-0.0 24.7+/-1.2 11.0+/-2.0 9.3+/-1.2
- 7.
7+/-1.2 1.0+/-0.0 52.3+/-3.1 45.7+/-3.1 1489+/-104 5540+/-26 12.0+/-4.0 20.0+/-3.5
- 6.
7+/-0. 2 5.2+/-0. 2
- 19. 7+/-5.0 21.0+/-2.0 40.0+/-5.0 6.0+/-0.9 5.0+/-0.8 10.0+/-6.0 51.0+/-5.0 10.0+/-5.0 4.0+/-1. 5 24.0+/-5.0 12.0+/-5.0 8.0+/-5.0 9.0+/-5.0 0.0+/-1.5 49.0+/-6.0 39.0+/-5.0 1565+/-78 31.3-48.7 4.4-7.6 3.7-6.3 0.0-20.4 42.3-59.7 1.3-18.7 1.4-6.6 15.3-32.7 3.3-20.7 0.0-16.7 0.3-17.7 0.0-2.6 38.6-59.4 30.3-47.7 1430-1700 5257+/-912 4345-6169 20.0+/-5.0 11.3-28.7 20.0+/-5.0 11.3-28.7 6.8+/-1.0 5.0-8.6 11.1+/-1.7 8.2-14.0 25.0+/-5.0 16.3-33.7 25.0+/-1.5 22.4-27.6
Table A-1.
(continued).
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-20c is, N=1 Control Limits STW-484 Water Jan 1987 STF-486 Food STF-487 Food (Blank)
Jan 1987 Jan 1987 STW-488 Water Feb 1987 STW-489 Water Feb 1987 STW-490 Water Feb 1987 STM-491 Milk Feb 1987 STW-492 Water Mar 1987 STW-493 Water Mar 1987 STW-494 Water Apr 1987 STAF-495 Air Filter Apr 1987 Pu-239 Sr-90 I-131 Cs-137 K
Co-60 Zn-65 Ru-106 Cs-134 Cs-137 H-3 Uranium 1-131 Gr. alpha Gr. beta Ra-226 Ra-228 1-131 Gr. alpha Gr. beta Sr-90 Cs-137 17.0+/-2.3 36.0+/-4.0 78.0+/-3.4 89.7+/-3.0 942+/-56 2.0+/-0.0
<3
<2 993+/-102 49.0+/-0.0 96.0+/-7.2 92.0+/-20.2 53.0+/-3.4 89.3+/-4.6 4130+/-140 8.3+/-1.2 10.0+/-0.0
- 3. 7+/-1. 2 11.3+/-1.2 7.0+/-0. 1 7.1+/-2.3 8.0+/-0.0 15.0+/-0. 0 41.0+/-2.0 16.3+/-1. 2 7.0+/-0.0 16.7+/-1.7 13.8-19.6 49.0+/-10.0 78.0+/-8.0 84.0+5.0 980+/-49
- 50. 0+/-5.0 91.0+/-5.0 100.0+/-5.0 59.0+/-5.0 87.0+/-5.0 4209+/-420 31.-7-66.3 64.1-91.9 75.3-92.7 895-1065 41.3-58.7 82.3-99.7 91.3-108.7 50.3-67.7 78.3-95.7 3479-4939 8.0+/-6.0 0.0-18.4 9.0+0.9 7.4-10.6 3..0+/-5.0 0.0-11.7 13.0+/-5.0 4.3-21.7 7.3+/-1.1 5.4-9.2 7.5+/-1.1 5.5-9.5 7.0+/-0.7 5.8-8.2 14.0+5.0 43.0+/-5.0 17.0+/-1.5 8.0+/-5.0 5.3-22.7 34.3-51.7 14.4-19.6 0.0-16.7 STW-496 Water 497 (Blind)
Sample A Apr 1987 Gr. alpha Ra-226 Ra-228 Uranium
- 30. 7+/-1. 2 3.9+/-0. 2 4.9+/-0. 9 5.0+/-0.0 30.0+/-8.0
- 3.
9+/-0. 6 4.0+/-0.6 5.0+/-6.0 16.1-43.9 2.9-4.9 3.0-5.0 0.0-15.4 A-6
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-20 c Is, N=1 Control Limits STW-496 Water Apr 1987 497 (Blind)
Sample B STU-498 Urine Apr 1987 STW-499 Water May 1987 STW-500 Water May 1987 STW-501 Water June 1987 STW-502 Water June 1987 STW-503 Water June 1987 STM-504 Milk June 1987 STW-505 Water July 1987 STF-506 Food July 1987 STW-507 Water Aug 1987 STW-508 Water Aug 1987 Gr. Beta Sr-89 Sr-90 Co-60 Cs-134 Cs-137 H-3 Sr-89 Sr-90 Gr. alpha Gr. beta Cr-51 Co-60 Zn-65 Ru-106 Cs-134 Cs-137 H-3 Ra-226 Ra-228 Sr-89 Sr-90 1-131 Cs-137 K
Gr. alpha Gr. beta 1-131 Cs-137 K
1-131 Pu-239 69.3+/-9.4 16.3+/-3.0 10.0+/-0.0 8.3+/-3.0 19.0+/-2.0
- 14. 7+/-1. 2 6017+/-494 38.0+/-6.0 21.0+/-2.0 9.0+/-3.4
- 10. 3+/-1.2 40.0+/-8.0 60.3+/-3.0 11.3+/-5.0
- 78. 3+/-6.4
- 36. 7+/-3.0 80.3+/-4.2 2906+/-86 6.9+/-0.1
- 13. 3+/-1.0 57.0+/-4.3 32.0+/-1.0 64.0+/-2.0
- 77. 7+/-0. 6 1383+/- 17
- 2.
3+/-0. 7 4.0+/-1.0 82.7+/-4.6
- 53. 7+/-3.0 1548+/-57 45.7+/-4.2 5.8+/-0.2 66.0+/-5.0 19.0+/-5.0 10.0+/-1.5 8.0+/-5.0 20.0+/-5.0 15.0+/-5.0 57.3-74.7 10.3-27.7 7.4-12.6 0.0-16.7 11.3-28.7 6.3-23.7 5620+/-795 4647-6593 41.0+/-5.0 32.3-49.7 20.0+/-1.5 17.4-22.6 11.0+/-5.0 2.3-19.7 7.0+/-5.0 0.0-15.7 41.0+/-5.0 64.0+/-5.0 10.0+/-5.0 75.0+/-5.0 40.0+/-5.0 80.0+/-5.0 32.3-49.7 55.3-72.7 1.3-18.7 66.3-83.7 31.3-48.7 71.3-88.7 2895+/-357 2277-3513 7.3+/-1.1 5.4-9.2 15.2+/-2.3 11.2-19.2 69.0+/-5.0 35.0+/-1.5 59.0+/-6.0 74.0+/-5.0 1525+/-76 60.3,77.7 32.4-37.6 48.6-69.4 65.3-82.7 1393-1657 5.0+/-5.0 0.0-13.7 5.0+/-5.0 0.0-13.7 80.0+/-8.0 50.0+/-5.0 1680+/-84 66.1-93.9 41.3-58.7 1534-1826 48.0+/-6.0 37.6-58.4 5.3+/-0.5 4.4-6.2 A-7 a
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis i2oc 1s, N=1 Control Limits STW-509 Water Aug 1987 STAF-510 Air Filter Aug 1987 STW-511 Water Sept 1987 STW-512 Water Sept 1987 STW-513 Water Oct 1987 Uranium Gr. alpha Gr. beta S r-90 C s-137 R a-2 26 Ra-228 Gr. alpha Gr. beta H-3 13.3+/-0.3 9.7+/-0.4 28.3+/-0.6 10.0-0.9 10.0+/-1.0 9.9+/-0.1 8.1+/-1.4 2.0+/-0.6 11.3+/-1.3 4473 +/-100 13.0t6.0 2.6-23.4 10.0+/-5.0 30.0
+/-5.0 10.0+/-1.5 10.0+/-5.0 1.3-18.7 21.3-38.7 7.4-12.6 1.3-18.7 9.7+/-1.5 7.2-12.2 6.3+/-1.0 4.6-8.0 4.0+/-5.0 0.0-12.7 12.0 +/-5.0 3.3-20.7 4492+/-449 3714-5270 STW-514 Water (Blind)
Gr. alpha Ra-226 Ra-228 Uranium Sr-89 S r-90 Co-60 Cs-134 C s-137 STW-516 Water Oct 1987 STU-517 Urine Nov 1987 STW-518 Water Nov 1987 STW-519 Water Dec 1987 Cr-51 C o-60 Zn-65 Ru-106 C s-1 34 C s-i 37 H-3 Gr. alpha Gr. beta 1-131 29.3+/-2.6 4.9+/-0.1 4.2+/-1.0 3.0+/-0.1 14.3+/-1.3 9.7+/-0.4 16.7+/-3.0 16.7+/-2.3 24.3+/-3.3 80.3+/-17.5 16.0+/-2.3 46.3+/-5.6 57.3 +/-15.4 23.7+/-2.5 51.7+/-3.2 7267 +/-100 3.0+/-2.0 15.7+/-2.3 26.0+/-3.0 28.0+/-7.0 4.8 +/-0.7 3.6+/-0.5 3.0 +/-6.0 16.0+/-5.0 10.0 +/-1.5 16.0+/-5.0 16.0+/-5.0 24.0+/-5.0 70.0+/-5.0 15.0+/-5.0 46.0+/-5.0 61.0+/-5.0 25.0+/-5.0 51.0+/-5.0 15.9-40.1 3.6-6.1 2.7-4.5 0.0-13.4 7.3-24.7 7.4-12.6 7.3-24.7 7.3-24.7 15.3-32.7 61.3-78.7 6.3-23.7 37.3-54.7 52.3-69.7 16.3-33.7 42.3-59.7 7432+/-743 6145-8719 7.0+/-5.0 19.0+/-5.0 0.0-15.7 10.3-27.7 26.0+/-6.0 15.6-36.4 A-8 Oct 1987 Sample A Sample B
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-2ciC is, N=1 Control Limits STW-520 Water STW-521 Water STW-523 Water STF-524 Food STW-525 Water STW-526 Water STW-527 Water STM-528 Milk STW-529 Water STW-530 Water STAF-531 Air Filter STW-532 Water Dec 1987 Jan 1988 Jan 1988 Jan 1988 Feb 1988 Feb 1988 Feb 1988 Feb 1988 Mar 1988 Mar 1988 Mar 1988 Apr 1988 Ra-226 Ra-228 Sr-89 Sr-90 Gr. alpha Gr. beta Sr-89 Sr-90 1-131 Cs-137 K
Co-60 Zn-65 Ru-106 Cs-134 Cs-137 H-3 Uranium 1-131 Ra-226 Ra-228 Gr. alpha Gr. beta Gr. alpha Gr. beta Sr-90 Cs-137 1-131 5.1+/-0.8 3.4+/-0.1 27.3+/-5.0 15.3+/-1.2 2.3+/-1.2 7.7+/-1.2 44.0+/-4.0 53.0+/-2.0 102.3t4.2 95.7t6.4 1011+/-158 69.3+/-2.3 99.0+/-3.4 92.7+/-14.4
- 61. 7+/-8. 0 99.7t3.0 3453t103 3.0+/-0.0
- 4. 71.2
- 7. 1+/-0.6 NAe 4.3+/-1.2 13.3+/-1.3 21.0+/-2.0 48.0t0.0 16.7+/-1.2 18.711.3 9.0t2.0 4.8+/-0.7 5.3+/-0.8 3.6-6.0 3.9-6.7 30.0+/-5.0 21.3-38.7 15.0+/-1.5 12.4-17.6 4.0+/-5.0 8.0+/-5.0 46.0+/-5.0 55.0+/-2.8 102.0t10.2 91.0+/-5.0 1230t62 69.0+/-5.0 94.0+/-9.4 105.0+/-10.5 0.0-12.7 0.0-16.7 37.3-54.7 50.2-59.8 84.3-119.7 82.3-99.7 1124-1336 60.3-77.7 77.7-110.3 86.8-123.2 64.0+/-5.0 55.3-72.7 94.0+/-5.0 85.3-102.7 3327+/-362 2700-3954 3.0+/-6.0
- 4. 0+/-0. 4 7.6+/-1. 1
- 7. 71.2 6.0+/-5.0 13.0+/-5.0 20.0+/-5.0 50.0t5.0
- 17. 0+/-1. 5
- 16. 0+/-5.0 7.5+/-0.8 0.0-13.4 3.3-4.7 5.6-9.6 5.7-9.7 0.0-14.7 4.3-21.7 11.3-28.7 41.3-58.7 14.4-19.6 7.3-24.7 6.2-8.8 A-9 I
Tabl e A-1.
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-2uc 1s, N=1 Control Limits STW-533 Water 534 (Blind)
Apr 1988 Gr. alpha Ra-226 Ra-228 Uranium Gr. beta Sr-89 Sr-90 Co-60 Cs-134 Cs-137 STU-535 Urine Apr 1988 STW-536 Water Apr 1988 STW-538 Water June 1988 H-3 Sr-89 Sr-90 Cr-51 Co-60 Zn-65 Ru-106 Cs-134 Cs-137 NDf ND ND 6.0+/-0.0 ND 3.3+/-1.2 5.3+/-1.2 63.31.3 7.7+/-1.2 8.3+/-1.2 6483+/-155 14.7+/-1.3 20.0+/-2.0 331.7+/-13.0 16.0+/-2.0 107.7+/-11.4 191.3+/-11.0 18.3+/-4.6 26.3t1.2 46.0+/-11.0 6.4+/-1. 0 5.6+/-0.8 6.0+/-6.0 57.0+/-5.0 5.0+/-5.0 5.0+/-1.5 50.0+/-5.0
- 7.
05.0 7.0+/-5.0 27.0-65.0 4.7-8.1 4.2-7.0 0.0-16.4 48.3-65.7 0.0-13.7 2.4-7.6 41.3-58.7 0.0-15.7 0.0-15.7 6202+/-620 5128-7276 20.0+/-5.0 11.3-28.7 20.0+/-1.5 17.4-22.6 302.0+/-30.0 15.0+/-5.0 101.0+/-10.0 195.0+/-20.0 20.0+/-5.0 25.0+/-5.0 250.0-354.0 6.3-23.7 83.7-118.3 160.4-229.6 11.3-28.7 16.3-33.7 STW-539 Water June 1988 H-3 5586t92 5565+/-557 4600-6530 STM-541 Milk June 1988 STW-542 Water July 1988 STF-543 Food July 1988 Sr-89 Sr-90 1-131 Cs-137 K
Gr. alpha Gr. beta Sr-89 Sr-90 1-131 Cs-137 K
33.7+/-11.4 55.3+/-5.8 103.7+/-3.1 52.7+/-3.1 1587t23 8.7+/-4.2 5.3+/-1.2 ND ND 115.0+/-5.3 52.7t6.4 1190t66 40.0+/-5.0 60.0+/-3.0 94.0+/-9.0 51.0+/-5.0 1600+/-80 15.0+/-5.0 4.0+/-5.0 33.0+/-5.0 34.0+/-2.0 107.0+/-11. 0 49.0+/-5.0 1240t62 31.3-48.7 54.8-65.2 78.4-109.6 42.3-59.7 1461-1739 6.3-23.7 0.0-12.7 24.3-41.7 30.5-37.5 88.0-126.0 40.3-57.7 1133-1347 A-10 Sample A Sample B
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-2,c 1s, N=i Control Limits STW-544 Water Aug 1988 STW-545 Water Aug 1988 STW-546 Water Aug 1988 STAF-547 Air Filter Aug 1988 STW-548 Water Sep 1988 STW-549 Water Sep 1988 STW-550 Water Oct 1988 STW-551 Water Oct 1988 1-131 Pu-239 Uranium Gr. alpha Gr. beta Sr-90 Cs-137 Ra-226 Ra-228 Gr. alpha Gr. beta Cr-51 CO-60 Zn-65 Ru-106 Cs-134 Cs-137 H-3 80.0+/-0.0 11.0+/-0.2
- 6. 0+/-0.0 8.0+/-0.0 26.3+/-1.2
- 8. 0+/-2.0
- 13. 0+/-2.0 9.3+/-0. 5 5.8+/-0.4
- 7. 0+/-2.0 11.3+/-1.2 252.0+/-14.0 26.0+/-2.0 158.3+/-10.2 153.0+/-9.2 28.7+/-5.0 16.31.2 2333+/-127 76.0+/-8.0 10.2+/-1.0
- 6. 0+/-6. 0 8.0+/-5.0 29.0+/-5.0 8.0+/-1.5 12.0+/-5.0 8.4+/-2.6 5.4+/-1.6 8.0+/-5.0 10.0+/-5.0 251.0+/-25.0 25.0+/-5.0 151.0+/-15.0 152.0+/-15.0 25.0+/-5.0 15.0+/-5.0 2316t350 62.1-89.9 8.5-11.9 0.0-16.4 0.0-16.7 20.3-37.7 5.4-10.6 3.3-20.7 6.2-10.6 4.0-6.8 0.0-16.7 1.3-18.7 207.7-294.3 16.3-33.7 125.0-177.0 126.0-178.0 16.3-33.7 6.3-23.7 1710-2927 STW-552 Water 553 (Blind)
Sample A Sample B Oct 1988 Gr. alpha Ra-226 Ra-228 Uranium Gr. beta Sr-89 Sr-90 Cs-134 Cs-137 38.3+/-8.0 4.5+/-0.5 4.4+/-0.6
- 4.
7+/-1.2 51.3+/-3.0 3.7+/-1.2 10.7+/-1.2 15.3+/-2.3 16.7+/-1.2 41.0+/-10.0 5.0+/-0.8 5.2+/-0.8 5.0+/-6.0 54.0+/-5.0 11.0+/-5.0 10.0+/-1.5 15.0+/-5.0 15.0+/-5.0 23.7-58.3 3.6-6.4 3.6-6.4 0.0-15.4 45.3-62.7 2.3-19.7 7.4-12.6 6.3-23.7 6.3-23.7 A-11
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-2ac 1s, N=1 Control Limits STM-554 Milk Oct 1988 STU-555 Urine Nov 1988 STW-556 Water Nov 1988 STW-557 Water Dec 1988 STW-559 Water Jan 1989 STW-560 Water Jan 1989 STW-561 Water Jan 1989 STW-562 Water Feb 1989 Sr-89 Sr-90 1-131 Cs-137 K
H-3 Gr. alpha Gr. beta 1-131 Sr-89 Sr-90 Pu-239 Gr. alpha Gr. beta Cr-51 Co-60 Zn-65 Ru-106 Cs-134 Cs-137 40.3t7.0 51.0t2.0 94.0+/-3.4 45.0t4.0 1500+/-45 3030t209 9.0+/-3.5 9.7+/-1.2 108.7t3.0 40.0t8.7 24.3t3.1 5.8t1.1 7.3t1.2 5.3+/-1.2 245+/-46 10.0+/-2.0 170+/-10 181t7.6 9.7+/-3.0 11.7+/-1.2 40.0+/-5.0 60.0t3.0 91.0+/-9.0 50.0t5.0 1600+/-80 3025t359 9.0+/-5.0 9.0+/-5.0 115.0+/-12.0 40.0+/-5.0 25.011.5 4.2+/-0.4 8.0+/-5.0 4.0+/-5.0 235+/-24 10.0+/-5.0 159t16 178t18 10.0+/-5.0 10.0+/-5.0 31.3-48.7 54.8-65.2 75.4-106.6 41.3-58.7 1461-1739 2403-3647 0.3-17.7 0.3-17.7 94.2-135.8 31.3-48.7 22.4-27.6 3.5-4.9 0.0-16.7 0.0-12.7 193.4-276.6 1.3-18.7 139.2-186.7 146.8-209.2 1.3-18.7 1.3-18.7 A-12
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+/-2uc 1s, N=1 Control Limits STW-563 Water STW-564 Water STW-565 Water STW-566 Water STW-567 AirFilter STW-568 Water 569 (Blind)
Feb 1989 Feb 1989 Mar 1989 Mar 1989 Mar 1989 I-131 H-3 Ra-226 Ra-228 U
Gr. alpha Gr. beta Sr-90 Cs-137 109.0+/-4.0 2820+/-20 4.2+/-0.3 1.9+/-1.0 5.0+/-0.0 21.7+/-1.2 68.3+/-4.2 20.0+/-2.0 21.3+/-1.2 106.0+/-11.0 86.9-125.1 2754+/-356 2137-3371 4.9+/-0.7 1.7+/-0.3 5.0+/-6.0 21.0+/-5.0 62.0+/-5.0 20.0+/-1.5 20.0+/-5.0 3.7-6.1 1.2-2.2 0.0-15.4 12.3-29.7 53.3-70.7 17.4-22.6 11.3-28.7 Apr 1989 Sample A Sample B STM-570 Milk Apr 1989 Gr. alpha Ra-226 Ra-228 U
Gr. beta Sr-89 Sr-90 Cs-134 Cs-137 Sr-89 Sr-90 Cs-137 K-40 22.7+/-2.3 3.6+/-0.6 2.6+/-1.0 3.0+/-0.0 52.3+/-6.1 9.3+/-5.4 7.0+/-0.0 21.0+/-5.2 23.0+/-2.0 26.0+/-10.0 45.7+/-4.2 54.0+/-6.9 1521+/-208 29.0+/-7.0
- 3.
5+/-0.5 3.6+/-0.5 3.0+/-6.0 57.0+/-5.0 8.0+/-5.0 8.0+/-1.5 20.0+/-5.0 20.0+/-5.0 39.0+/-5.0 55.0+/-3.0 50.0+/-5.0 1600+/-80 16.9-41.2 2.6-4.4 2.7-4.5 0.0-13.4 43.3-65.7 0.0-16.7 5.4-10.6 11.3-28.7 11.3-28.7 30.3-47.7 49.8-60.2 41.3-58.7 1461-1739 A-13
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
+2c 1s, N=1 Control Limits STW-5 7 1g Water May 1989 STW-572 Water May 1989 STW-573 Water Jun 1989 STW-574 STW-575 Water Water STW-576 Water STW-577 Water STW-579 Air Filter STW-580 Water Jun 1989 Jul 1989 Jul 1989 Aug 1989 Aug 1989 Sep 1989 STW-581 Water Sep 1989 Sr-89 Sr-90 Gr. alpha Gr. beta Ba-133 Co-60 Zn-65 Ru-106 Cs-134 Cs-137 H-3 Ra-226 Ra-228 U
1-131 Gr. alpha Cs-137 Sr-89 Sr-90 Gr. alpha Gr. Beta 40.7 5.0+/-1.0 24.0+/-2.0 49.3t15.6 50.7+/-1.2 31.3t2.3 167+/-10 123+/-9.2 40.3+/-1.2 22.3+/-1.2 4513+/-136 16.8+/-3.1 13.8+/-3.7 40.3+/-1.2 84.7+/-5.8 6.0+/-0.0 10.3t2.3 14.7+/-1.2
- 9. 71.2
- 5.
00.0
- 8.
7t2.3 6.0+/-5.0
- 6. 0+/-1. 5 30.0+/-8.0 50.0+/-5.0 49.0+/-5.0 31.0t5.0 165t17 128+/-13 39t5 20+/-5 4503t450 17.7+/-2.7 18.3t2.7 41.0t6.0 83.0+/-8.0 6.0+/-5.0 10.0t5.0 14.0+/-5.0 10.0+/-1.5 4.0+/-5.0
- 6. 05.0 0.0-14.7 3.4-8.6 16.1-43.9 41.3-58.7 40.3-57.7 22.3-39.7 135.6-194.4 105.5-150.5 30.3-47.7 11.3-28.7 3724-5282 13.0-22.4 13.6-23.0 30.6-51.4 69.1-96.9 0.0-14.7 1.3-18.7 5.3-22.7 7.4-12.6 0.0-12.7 0.0-14.7 A-14
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultu Code Type Collected Analysis
+2ac i 1s, N=1 Control Limits STW-583 Water Oct 1989 Ba-133 60.3+10.0 59.0+/-6.0 48.6-69.4 Co-60 29.0+4.0 30.0+/-5.0 21.3-38.7 Zn-65 132.3+6.0 129.0+/-13.0 106.5-151.5 Ru-106 155.3+6.1 161.0+/-16.0 133.3-188.7 Cs-134 30.7+6.1 29.0+/-5.0 20.3-37.7 Cs-137 66.3+4.6 59.0+/-5.0 50.3-67.7 STW-584 Water Oct 1989 H-3 3407+/-150 3496+/-364 2866-4126 STW-585 Water Oct 1989 586 (Blind)
Sample A Gr. Alpha 41.7+/-9.4 49.0+/-12.0 28.2-69.8 Ra-226 7.9+/-0.4 8.4+/-1.3 6.2-10.6 Ra-228 4.4+/-0.8 4.1+/-0.6 3.1-5.1 U
12.0+/-0.0 12.0+/-6.0 1.6-22.4 Sample B Gr. Beta 31.7+/-2.3 32.0+/-5.0 23.3-40.7 Sr-89 13.3+/-4.2 15.0+/-5.0 6.3-23.7 Sr-90 7.0+/-2.0 7.0+/-3.0 4.4-9.6 Cs-134 5.0+/-0.0 5.0+/-5.0 0.0-13.7 Cs-137 7.0+/-0.0 5.0+/-5.0 0.0-13.7 STW-587 Water Nov 1989 Ra-226 7.9+/-0.4 8.7+/-1.3 6.4-11.0 Ra-228 8.9+/-1.2 9.3+/-1.2 6.9-11.7 STW-588 Water Nov 1989 U
15.0+/-0.09 15.0+/-6.0 4.6-25.4 a Results obtained by Teledyne Isotopes Midwest Laboratory as a participant in the environmental sample crosscheck program operated by the Intercomparison and Cali bration Section, Quality Assurance Branch, Environmental Monitoring and Support Laboratory, U.S.
Environmental Protection Agency (EPA),
Las Vegas, Nevada.
b All results are in the pCi/l, except for elemental potassium (K) data in milk, which are in mg/l; air filter samples, which are in pCi/filter; and food, which is in mg/kg.
c Unless otherwise indicated, the TIML results are given as the mean +/- 2 standard deviations for three determinations.
d USEPA results are presented as the known values and expected laboratory precision (1s, 1 determination) and control limits as defined by EPA.
e NA = Not analyzed.
f ND = No data. Not analyzed due to relocation of the lab.
9 Sample was analyzed but the results not submitted to EPA because deadline was missed.
A-15
Table A-2.
Crosscheck program results, thermoluminescent dosimeters (TLDs).
mR Teledyne Average +/-2 ad Lab TLD Result Known (all Code Type Measurement
+/-2aa Valuec participants) 2nd International Intercomparisonb 115-2 CaF 2 :Mn Field Bulb Lab 3rd International Intercomparisone 115-3 CaF 2 :Mn Field Bulb Lab 4th International Intercomparisonf 115-4 CaF 2 :Mn Field Bulb Lab (Low)
Lab (High) 5th International Intercomparisong 115-5A CaF 2 :Mn Field Bulb Lab at beginning Lab at end 17.0+/-1. 9 20.8+/-4.1
- 30. 7+/-3. 2 89.6+/-6.4
- 14. 1+/-1. 1
- 9.
3+/-1. 3 40.4+/-1.4 31.4+/-1.8
- 77. 4+/-5.8
- 96. 6+/-5.8 17.1 21.3
- 16. 4+/-7. 7
- 18. 8+/-7. 6 34.9+/-4.8
- 91. 7+/-14.6
- 14. 1+/-1.4 12.2+/-2.4 45.8+/-9. 2 30.0+/-6.0
- 75. 2+/-7. 6 88.4+/-8.8 31.5+/-3.0 86.2+/-24.0
- 16. 0+/-9. 0
- 12. 0+/-7. 6
- 43. 9+/-13. 2 30.2+/-14.6
- 75. 8+/-40.4
- 90. 7+/-31.2 o'
Table A-2.
(Continued) mR Teledyne Average +/-20 d Lab TLD Result Known (all Code Type Measurement
+/-20 a Valuec participants) 115-5B LiF-100 Field Chips Lab at beginning Lab at the end 7th International Intercomparisonh 115-7A LiF-100 Field Chips Lab (Co-60)
Lab (Cs-137)
CaF 2 :Mn Bulbs Field Lab (Co-60)
Lab (Cs-137)
- 30. 3+/-4.8
- 81. 1+/-7.4 85.4+/-11. 7 75.4+/-2.6 80.0+/-3.5
- 66. 6+/-2. 5 71.5+/-2.6 84.8+/-6.4 78.8+/-1.6
- 30. 0+/-6.0
- 75. 2+/-7. 6 88.4+/-8.8 75.8+/-6.0 79.9+/-4.0
- 75. 0+/-3.8 75.8+/-6.0 79.9+/-4.0 75.0+/-3.8 30.2+/-14.6
- 75. 8+/-40. 4
- 90. 7+/-31.2
- 75. 1+/-29.8
- 77. 9+/-27.6
- 73. 0+/-22. 2
- 75. 1+/-29.8
- 77. 9+/-27.6
- 73. 0+/-22. 2 115-7C CaSO 4 :Dy Field 76.8+/-2.7 75.8+/-6.0 75.1+/-29.8 Cards Lab (Co-60) 82.5+/-3.7 79.9+/-4.0 77.9+/-27.6 Lab (Cs-137 79.0+/-3.2 75.0+/-3.8 73.0+/-22.2 115-7B
TaW A-2.
(Continued)
MW mR Teledyne Average +/-2a d Lab TLD Result Known (all Code Type Measurement
+/-20a Valuec participants) 8th International Intercomparisoni 115-8A LiF-100 Field Site 1 29.5+/-1.4 29.71.5 28.9+/-12.4 Chips Field Site 2 11.3+/-0.8 10.4+/-0.5 10.1+/-9.06 Lab (Cs-137) 13.7+/-0.9 17.2+/-0.9 16.2+/-6.8 115-8B CaF 2 :Mn Field Site 1 32.3+/-1.2 29.71.5 28.9+/-12.4 Bulbs Field Site 2 9.0+/-1.0 10.4+/-0.5 10.1+/-9.0 Lab (Cs-137) 15.8+/-0.9 17.2+/-0.9 16.2+/-6.8 115-8C CaSO4:Dy Field Site 1 32.3+/-0.7 29.71.5 28.9+/-12.4 Cards Field Site 2 10.6+/-0.6 10.4+/-0.5 10.1+/-9.0 Lab (Cs-137 18.1+/-0.8 17.2+/-0.9 16.2t6.8 Teledyne Testing9 89-1 LiF-100 Lab 21.0+/-0.4 22.4 Chips 89-2 Teledyne Lab 20.9+/-1.0 20.3 CaSO 4 :Dy Cards a
b c
d Lab result given is the mean +/-2 standard deviations of three determinations.
Second International Intercomparison of Environmental Dosimeters conducted in April of 1976 by the Health and Safety Laboratory (GASL),
New York, New York, and the School of Public Health of the Uni versity of Texas, Houston, Texas.
Value determined by sponsor of the intercomparison using continously operated pressurized ion chamber.
Mean +/-2 standard deviations of results obtained by all laboratories participating in the program.
00
TM A-2.
(continued) mR Teledyne Average +/-2ad Lab TLD Result Known (all Code Type Measurement
+2Cya Valuec participants)
Footnotes continued e Third International Intercomparison of Environmental Dosimeters conducted in summer of 1977 by Oak Ridge National Laboratory and the School of Public Health of the University of Texas, Houston, Texas.
f Fourth International Intercomparison of Environmental Dosimeters conducted in summer of 1979 by the School of Public Health of the University of Texas, Houston, Texas.
9 Fifth International Intercomparison of Environmental Dosimeter conducted in fall of 1980 at Idaho Falls, Idaho and sponsored by the School of Public Health of the University of Texas, Houston, Texas and h Environmental Measurements Laboratory, New York, New York, U.S. Department of Energy.
Seventh International Intercomparison of Environmental Dosimeters conducted in the spring and summer of 1984 at Las Vegas, Nevada, and sponsored by the U.S. Department of Energy, the U.S. Nuclear Regulatory i Commission, and the U.S. Environmental Protection Agency.
Eighth International Intercomparison of Environmental Dosimeters conducted in the fall and winter of 1985-1986 at New York, New York, and sponsored by the U.S. Department of Energy.
3 Chips were submitted in September, 1989 and cards were submitted in November, 1989 to Teledyne Isotopes, Inc., Westwood, NJ for irradiation.
In-house spiked samples.
Concentration in pCi/1 Lab Sample Date TIML Result Known Expected Code Type Collected Analysis n=3 Activity Precision 1s, n=3a Feb.
1986 Mar.
1986 Apr. 1986 Apr.
1986 Sr-89 Sr-90 1-131 Cs-134 Cs-137 Sr-89 Sr-90 1-131 Co-60 Cs-134 Cs-137 1-131 Cs-134 Cs-137 QC-MI-6 QC-W-14 QC-W-15 QC-MI-7 Milk Water Water Milk Water Water Milk Water Water Water Water Gross alpha Gross beta Sr-89 Sr-90 1-131 Cs-134 Cs-137 Gross alpha Gross alpha Cs-134 Cs-137 Sr-89 Sr-90 6.0+/-1. 9
- 14. 2+/-1. 7 34.2+/-3.8 32.0+/-1.8 35.8+/-2. 1
- 1.
6+/-0.4 2.4+/-0.2 44.9+/-2.4
- 10. 6+/-1. 7 30.2+/-2.4
- 21. 9+/-1. 9
- 39. 7+/-3. 3 28.7+/-2.8 21.2+/-2.8 15.8+/-1.8 16.2+/-0.7 38.4+/-3.5
<1.0
- 12. 6+/-1.8 38.9+/-7.0 33.0+/-3.4 38.5+/-2.8 16.8+/-1.8
- 17. 7+/-0.8 34.7+/-5.6 51.1+/-7.0 13.6+/-4.1 6.4+/-1.6 6.4+/-3.0 12.9+/-2.0 35.2+/-3.5 27.3+/-5.0 35.0+/-5.0
- 1.
6+/-1.0 2.4+/-2.0
- 41. 5+/-7.0
- 12. 1+/-5.0 25.8+/-8.0 19.9+/-5.0 41.5+/-7.0 25.8+/-8.0 19.9+/-5.0 18.0+/-5.0 16.9+/-2.5 30.2+/-5.0 0.0
- 13. 3+/-3.0 34.8+/-7.0 36.1+/-5.0 39.0+/-5.0 18.0+/-5.0 18.0+/-5.0
- 31. 3+/-5. 0 43.3+/-8.0 15.6+/-3.5 6.2+/-2.0 8.7 5.2 10.4 8.7 8.7 7.1 4.2 10.6 7.1lb 7.1lb 7.1lb 10.4 8.7 8.7 Sc 8.7 8.7 7.1lb
- 4. 2b 10.4 8.7 8.7 Sc 8c 8.7 8.7 7.1lb
- 4. 2b A-20 June 1986 June 1986 June 1986 June 1986 Sep. 1986 Sep.
1986 SPW-1 QC-W-16 QC-MI-9 SPW-2 SPW-3 QC-W-18 QC-W-19 May 1986 Gross alpha Table A-3.
In-house spiked samples (continued)
Concentration in pCi/1 Date Collected Analysis TIML Result Known Expected n=3 Activity Precision 1s, n=3a QC-W-21 Water QC-MI-11 Milk QC-W-20 QC-W-22 QC-W-23 QC-MI-12' Water Water Water Milk QC-MI-13 Milk QC-W-24 QC-W-25 Water Water QC-MI-14 Milk QC-W-26 QC-W-27 QC-W-28 Water Water Water Oct.
1986 Oct 1986 Nov. 1986 Dec.
1986 Jan. 1987 Jan. 1987 Jan 1987 Mar 1987 Apr 1987 Apr 1987 Jun 1987 Jun 1987 Jun 1987 C -60 Cs-134 Cs-137 Sr-89 H-3 Gross alpha Gross beta 1-131 1-131 Cs-137 Sr-89 Sr-90 1-131 Cs-134 Cs-137 Sr-89 Sr-90 1-131 1-131 Cs-134 Cs-137 H-3 Co-60 Cs-134 Cs-137 Gr. alpha Gr. beta Gr. alpha Gr. beta 19.2+/-2.2 31.7+/-5.2 23.8+/-1.0 12.31.8 3855+/-180 9.8+/-1.4 21.7+/-2.0 29.8+/-2.5 36.5+/-1.3 32.6t4.2 10.4+/-2.1 14.61.6 49.5+/-1.2 41.6 33.3+/-0.6 24.7+/-3.6 23.9+/-3.8 28.0+/-1.9 25.0+/-2.2 42.1 34.2+/-2.0 3422+/-100 24.8+/-1.4 42.0 21.2+/-0.5
- 8. 51.9 22.6+/-1.9 8.7+/-1.3 12.2t5.2 18.5+/-3.0 25.6t8.0 21.6t5.0 14.3+/-3.0 8.7 8.7 8.7 8.7 3960t350 520b 11.2t4. 0 23.8t5.0 8.7 8.7 27.9+/-3.0 10.4 32.6t5.0 27.4t8.0 12.2t4.0 12.6+/-3.0 54.9+/-8.0 0.0 27.4+/-8.0 25.9+/-5.0 22.8t8.0 10.4 8.7 8.7 5.2 10.4 8.7 8.7 8.7 5.2 29.3t5.0 10.6 23.9t5.0 0.0 27.2t7.0 3362t300 26.5+/-7.0 0.0 21.6+/-7.0 10.1+/-4.0 21.2+/-5.0 10.1+/-4.0 9.4t3.0 10.4 8.7 8.7 520 8.7 8.7 8.7 8.7 8.7 8.7 8.7 A-21 Lab Code Sample Type Tabl e A-3.
In-house spiked samples (continued)
Concentration in pCi/1 Sample Type Date Collected Analysis TIML Result n=3 Known Activity Expected Preci sion 1s, n=3a QC-W-29 Water QC-MI-15 Milk QC-W-30 QC-W-31 QC-W-32 QC-W-33 QC-W-34 Water Water Water Water Water QC-MI-16 Milk QC-MI-17 Milk QC-W-35 QC-W-36 QC-W-37 Water Water Water QC-MI-18 Milk Jun 1987 Jul 1987 Sep 1987 Oct 1987 Dec 1987 Dec 1987 Dec 1987 Feb 1988 Feb 1988 Feb 1988 Feb 1988 Mar 1988 Mar 1988 Gr. alpha Gr. beta Sr-90 1-131 Cs-134 Cs-137 Sr-89 Sr-90 H-3 Gr. alpha Gr. beta Gr. alpha Gr. beta Gr. alpha Gr. beta Sr-89 Sr-90 1-131 Cs-134 Cs-137 1-131 1-131 1-131 Sr-89 Sr-90 1-131 Cs-134 Cs-137 16.4+/-1.3 15.9+/-4.0 19.4+/-1.6 43.5+/-0.7 17.9+/-2.2 25.4+/-1.8 17.5+/-3.0 18.4+/-2.2 2053+/-939 8.6+/-1.0 15.2+/-0.1 7.7+/-1.4 10.9+/-1.0 4.0+/-0.9 9.4+/-0.9 31.8+/-4.7 25.5+/-2.7 26.4+/-0.5 23.8+/-2.3 26.5+/-0.8 10.6+/-1.2 9.7+/-1.1 10.5+/-1.3 17.1+/-2.0 18.7+/-0.9 33.2+/-2.3 31.3+/-2.1 29.9+/-1.4 18.9+/-5.0 11.8+/-4.0 18.8+/-3.5 45.3+/-7.0 16.0+/-5.3 22.7+/-5.0 14.3+/-5.0 17.5+/-2.2 2059+/-306 10.1+/-5.0 13.1+/-3.0 10.1+/-5.0 7.9+/-3.0 5.1+/-3.0 7.9+/-3.0 31.7+/-6.0 27.8+/-3.5 23.2+/-5.0 24.2+/-6.0 25.1+/-6.0 8.7 8.7 5.2 10.4 8.7 8.7 8.7 5.2 520 8.7 8.7 8.7 8.7 8.7 8.7 8.7 5.2 10.4 8.7 8.7 14.3+/-1.6 10.4 11.6+/-1.1 10.4 11.6+/-1.0 10.4 19.8+/-8.0 17.3+/-5.0 26.7+/-5.0 30.2+/-5.0 26.2+/-5.0 8.7 5.2 10.4 8.7 8.7 A-22 Lab Code Tabl e A-3.
In-house spiked samples (continued)
Concentration in pCi/1 Lab Sample Date TIML Result Known Expected Code Type Collected Analysis n=3 Activity Precision is, n=3a QC-W-38 QC-W-39 QC-W-40 QC-W-41 Water Water Water Water QC-MI-19 Milk QC-W-42 QC-W-43 QC-W-44 QC-W-45 Water Water Water Water QC-MI-20 Milk QC-W-46 Water QC-MI-21 Milk Apr 1988 Apr 1988 Apr 1988 Jun 1988 Jul 1988 Sep 1988 Oct 1988 Oct 1988 Oct 1988 Oct 1988 Dec 1988 Jan 1989 1-131 H-3 Co-60 Cs-134 Cs-137 Gr. alpha Gr. beta Sr-89 Sr-90 1-131 Cs-137 Sr-89 Sr-90 Co-60 Cs-134 Cs-137 1-131 H-3 1-131 Cs-134 Cs-137 Gr. alpha Gr. beta Sr-89 Sr-90 1-131 Cs-134 Cs-137 17.1t1.1 4439+/-31 23.7+/-0.5 25.4t2.6 26.6+/-2.3 12.3+/-0.4 22.6+/-1.0
- 15. 1+/-1.6 18.0+/-0.6 88.4+/-4.9 22.7+/-0.8 48.5+/-3.3
- 10. 9+/-1.0 20.9t3.2 38.71.6
- 19. 0+/-2.4 22.2+/-0.6 4109+/-43 59.8+/-0.9 49.6+/-1.8 25.8+/-4.6 11.5+/-2.3 26.5+/-2.0 25.5+/-10.3 28.3+/-3.2 540+/-13 24.5+/-2.6 24.0+/-0.6 14.2+/-5.0 10.4 4176+/-500 26.1+/-4.0 29.2+/-4.5 26.2+/-4.0 13.1+/-5.0 20.1+/-5.0 724 8.7 8.7 8.7 8.7 8.7 16.4+/-5.0 8.7 18.3+/-5.0, 5.2' 86.6+/-8.0 10.4 20.8+/-6.0 8.7 50.8+/-8.0 8.7 11.4+/-3.5 5.2 21.4+/-3.5 8.7 38.0+/-6.0 8.7 21.0+/-3.5 8.7 23.3+/-3.5 10.4 4153+/-500 724 60.6+/-9.0 48.6+/-7.5 24.7+/-4.0 15.2+/-5.0
- 25. 7+/-5.0 34.0+/-10.0 27.1+/-3.0 550+/-20 22.6+/-5.5 20.5+/-5.0 10.4 8.7 8.7 8.7 8.7 8.7 5.2 10.4 8.7 8.7 A-23 Table A-3.
Table A-3.
In-house spiked samples (continued)
Concentration in pCi/1 TIML Result n=3 Known Expected Activity Precision 1s, n=3a QC-W-47 Water QC-MI-22 Milk QC-W-48 QC-W-49 QC-W-50 QC-W-51 Water Water Water Water QC-MI-23 Milk QC-MI-24 Milk QC-W-52 QC-W-53 QC-W-54 Water Water Water a n=3 unless noted otherwise.
b n=2.
C n=1.
A-24 Lab Code Sample Type Date Collected Analysis Mar 1989 Apr 1989 Apr 1989 Apr Apr Jun 1989 1989 1989 Sr-89 Sr-90 1-131 Cs-134 Cs-137 Co-60 Cs-134 Cs-137 1-131 H-3 Gr. alpha Gr. beta Sr-89 Sr-90 1-131 Cs-134 Cs-137 Sr-89 Sr-90 1-131 1-131 Sr-89 Sr-90 15.2+/-3.8 16.4+/-1.7 36.3+/-1.1 20.8t2.8 22.2+/-2.4
- 23. 5t2.0 24.2+/-1.1 23.61.2 37.2+/-3.7 3011+/-59 13.01.8 26.01.2 19.4t6.5 27.6+/-3.5 46.8+/-3.2 27.4+/-1.8 24.1+/-1.8 25.4+/-2.7 46.0+/-1.1 9.6+/-0.3 19.0+/-0.2 25.8+/-4.6 26.5+/-5.3 Jul 1989 Aug 1989 16.1t5.0 16.9+/-3.0 37.2t5.0 20.7+/-8.0 20.4+/-8.0 25.1+/-8.0 25.9+/-8.0 23.0+/-8.0 37.2+/-5.0 3089+/-500 15.0+/-5.0 25.5+/-8.0 22.0+/-10.0 28.6+/-3.0 43.4+/-5.0 28.3+/-6.0 20.8+/-6.0 27.2+/-10.0 47.8+/-9.6 9.7+/-1.9 20.9+/-4.2 24.7+/-4.0
- 29. 7+/-5.0 8.7 5.2 10.4 8.7 8.7 8.7 8.7 8.7 10.4 724 8.7 8.7 8.7 5.2 10.4 8.7 8.7 8.7 8.3 10.4 10.4 8.7 5.2 Sep Sep Sep 1989 1989 1989
In-house spiked samples (continued)
Concentration in pCi/1 Lab Sample Date TIML Result Known Expected Code Type Collected Analysis n=3 Activity Precision Is, n=3a QC-MI-25 Milk Oct 1989 1-131 70.0+/-3.3 73.5+/-20.0 10.4 Cs-134 22.1+/-2.6 22.6+/-8.0 8.7 Cs-137 29.4+/-1.5 27.5+/-8.0 8.7 QC-W-55 Water Oct 1989 1-131 33.3+/-1.3 35.3+/-10.0 10.4 QC-W-56 Water Oct 1989 Co-60 15.2+/-0.9 17.4+/-5.0 8.7 Cs-134 22.1+/-4.4 18.9+/-8.0 8.7 Cs-137 27.2+/-1.2 22.9+/-8.0 8.7 QC-W-57 Water Oct 1989 H-3 3334+/-22 3379+/-500 724 QC-W-58 Water Nov 1989 Sr-89 10.9+/-1.4d 1 1.1+/-1. 0d 8.7 Sr-90 10.4+/-l.0d 10.3+/-1. 0d 5.2 QC-W-59 Water Nov 1989 Sr-89 10 1.0+/-6.0d 104.1+/-10.5d 17.5 Sr-90 98.0+/-3.0d 9 5.0+/-10.0d 17.0 QC-W-60 Water Dec 1989 Gr. alpha 10.8+/-1.1 10.6+/-4.0 8.7 Gr. beta 11.6+/-0.5 11.4+/-4.0 8.7 n=3 unless noted n=2.
otherwise.
n=1.
Concentration in pCi/m1 a
b c
d A-25 Table A-3.
Table A-4.
In-house "blank" samples.
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66a )
(4.66a )
D.I. Water D.I.
D.I.
Water Water BL-5 D.I. Water SPW-2265 D.I. Water D.I.
D.I.
D.I.
D.I.
D.I.
Water Water Water Water Water Milk D.I. Water Milk Milk Nov. 1985 Nov.
Nov.
1985 1985 Nov.
1985 Apr. 1985 Apr. 1986 Apr. 1986 June 1986 June 1986 Jan 1987 Jan 1987 Feb 1987 Feb 1987 Mar 1987 BL-1 BL-2 BL-3 a Low level A-26 Gross alpha Gross beta Cs-137 (gamma)
Sr-89 Sr-90 Ra-226 Ra-228 Gross alpha Gross beta Sr-89 Sr-90 1-131 Cs-137 (gamma)
Gross alpha Gross alpha Gross alpha Gross alpha Ra-226 Ra-228 1-131 Cs-134 Cs-137 H-3 Gross beta Sr-89 Sr-90 Cs-134 Cs-137
<0. 1
<0.4
,<1.9
<0. 5
<0.6
<0.4
<0.4
<0. 6
<2.2
<0.2
<0.4
<0.2
<7.4
<0.4
<0.4
<0.4
<0.3
<0. 1
<0.9
<0. 1
<6. 2
<6.4
<180
<2.6
<0.6 1.9+/-0.4a
<2. 2
<2.5
<1
<4
<10
<5
<1
<1
<1
<1
<4
<5
<1
<1
<10
<1
<1
<1
<1
<1
<1
<1
<10
<10
<300
<4
<5
<1
<10
<10 BL-6 BL-7 BL-8 BL-9 SPW-3185 SPS-3292 SPW-3554 SPS-3555 SPS-3731 (1 - 5 pCi/1) of Sr-90 concentration in milk is not unusual.
In-house "blank" samples (continued).
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66a )
(4.66a )
SPS-3732 D.I. Water SPS-4023 Milk SPS-4203 D.I. Water SPS-4204 SPS-4390 Mil k Mil k SPS-4391 D.I. Water SPW-4627 D.I. Water SPS-4628 SPS-4847 Milk Milk Mar 1987 May 1987 May 1987 May 1987 Jun 1987 Jun 1987 Aug 1987 Aug 1987 Sep 1987 Sr-89 Sr-90 1-131 Co-60 Cs-134 Cs-137 Ra-226 Ra-228 Np-237 Th-230 Th-232 U-234 U-235 U-238 1-131 Gross alpha Gross beta Sr-89 Sr-90 Cs-134 Cs-137 Sr-89 Sr-90 1-121 Co-60 Cs-137 Ra-226 Ra-228 Gross alpha Gross beta Tritium Sr-89 Sr-90 Cs-134 Cs-137 A-2 7
<0.9
<0.8
<0.3
<2.3
<2. 2
<2.4
<0. 1
<1.0
<0.04
<0.05
<0.02
<0.05 (0.03
<0.03
<0. 1
<0.7
<1.7
<0. 5 2.4+/-0.6a
<4.7
<5. 2
<0.4
<0.4
<0.1
<3.8
<5. 7
<0. 1
<0.9
<0.6
<1.4
<150
<0.6
<4.4
<5.3
<5
<1
<1
<10
<10
<10
<1
<1
<1
<0. 1
<0. 1
<0. 1
<0. 1
<0. 1
<1
<1
<4
<5
<1
<10
<10
<5
<1
<1
<10
<10
<1
<1
<1
<4
<5
<1
<10
<10 a Low level (1 - 5 pCi/1) of Sr-90 concentration in milk is not unusual.
Tabl e A-4.
In-house "blank" samples (continued).
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66a )
(4.66a )
SPS-4848 D.I. Water SPW-4849 D.I. Water SPW-4850 D.I. Water SPW-4859 D.I. Water SPS-5348 Milk SPW-5384 D.I. Water SPW-5385 D.I. Water SPS-5386 Mil k SPW-5448 "Dead" Water Nov 1987 Jan 1988 Jan 1988 Gr. alpha Gr. beta Fe-55 1-131 H-3 A-28 1-131
<1 Sep 1987 Sep 1987 Sep 1987 Oct 1987 Dec 1987 Dec 1987 Co-60 Cs-134 Cs-137 Sr-89 Sr-90 Th-228 Th-232 U-234 U-235 U-238 Am-241 Cm-242 Ra-226 Ra-228 Fe-55 Cs-134 Cs-137 Co-60 Cs-134 Cs-137 1-131 Ra-226 Ra-228 Sr-89 Sr-90
<4. 1
<4.8
<4.0
<0.7
<0.7
<0.04
<0.8
<0.03
<0.03
<0.02
<0.06
<0.04
<0. 1
<1.0
<0.5
<2.3
<2. 5
<2.8
<2.6
<2.8
<0.2
<0. 1
<1. 2
<0.5
<0.4
<10
<10
<10
<5
<1
<1
<1
<1
<1
<1
<1
<1
<1
<2
<1
<10
<10
<10
<10
<10
<1
<1
<2
<1
<1
<0.4
<2. 2
<0.3
<0. 1
<177
<1
<4
<1
<1
<300 Tabl e A-4.
In-house "blank" samples (continued).
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.660 )
(4.660 )
SPS-5615 Mil k SPS-5650 D.I. Water SPS-6090 SPW-6209 SPW-6292 SPS-6477 SPW-6478 SPW-6479 SPW-6480 SPW-6625 Milk Water Water Milk Water Water Water Water Mar 1988 Mar 1988 Jul 1988 Jul 1988 Sep 1988 Oct 1988 Oct 1988 Oct 1988 Oct 1988 Dec 1988 Cs-134 Cs-137 1-131 Sr-89 Sr-90 Th-228 Th-230 Th-232 U-234 U-235 U-238 Am-241 Cm-242 Pu-238 Pu-240 Sr-89 Sr-90 1-131 Cs-137 Fe-55 Sr-89 Sr-90 1-131 Cs-134 Cs-137 1-131 Co-60 Cs-134 Cs-137 H-3 Gr. alpha Gr. beta
<2.4
<2. 5
<0. 3
<0.4 2.4+/-0.5a
<0.3
<0.04
<0.05
<0.03
<0.03
<0.03
<0.06
<0.01
<0.08
<0.02
<0.5 1.8+0.5a
<0.4
<0.4
<0.8
<0.7
<0. 7
<0.2
<6. 1
<5.9
<0.2
<5.7
<3.7
<4. 3
<170
<10
<10
<1
<5
<1
<1
<1
<1
<1
<1
<1
<1
<1
<1
<1
<1
<1
<1
<10
<1
<1
<1
<1
<10
<10
<1
<10
<10
<10
<300
<0.7
<1.9
<1
<4 A-29 a Low level (1 - 5 pCi/1) of Sr-90 concentration in milk is not unusual.
Tabl e A-4.
In-house "blank" samples (continued).
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66a )
(4.66(y SPS-6723 SPW-6877 SPS-6963 SPW-7561 SPW-7207 SPS-7208 SPW-7558 SPS-7322 SPW-7559 SPW-7560 SPW-7562 SPS-7605 SPW-7971 Milk Water Milk Water Water Milk Water Milk Water Water Water Milk Water Jan 1989 Mar 1989 Apr 1989 Apr 1989 Jun 1989 Jun 1989 Jun 1989 Aug 1989 Sep 1989 Oct 1989 Oct 1989 Nov 1989 Dec 1989 Sr-89 Sr-90 1-131 Cs-134 Cs-137 Sr-89 Sr-90 1-131 Cs-134 Cs-137 H-3 Ra-226 Ra-228 Sr-89 Sr-90 1-131 Cs-134.
Cs-137 Gr. alpha Gr. beta Sr-89 Sr-90 1-131 Cs-134 Cs-137 Sr-89 Sr-90 1-131 H-3 1-131 Cs-134 Cs-137 Gr. alpha Gr. beta A-30
'0.6 1.9+/-0.5a
<0.2
<4.3
'4.4 (0.4
<0.6
<0. 3
<5.9
<6.2
<150
'0.
2
<0.6
<0.6 2.1+/-0.5a
<0.3
<6.4
<7. 2
'0.2
<1.0
<1.4 4.8+/-1. Oa
<0.2
<6.9
<8.2
<2.0
<0.7
'0.
1
<140
<0.2
<8.6
<10
<0.4
<0.8
<5
<1
<1
<10
<10
<5
<1
<1
<10
<10
<300
<1
<1
<5
<1
<1
<10
<10
<1
<4
<5
<1
<1
<10
<10
<5
<1
<1.0
<300
<1
<10
<10
<1
<4 a Low level (1-5 pCi/1) of Sr-90 concentration in milk is not unusual.
Tabl e A-4.
TIML-8LIND-01 ATTACHMENT B ACCEPTANCE CRITERIA FOR "SPIKED" SAMPLES LABORATORY PRECISION:
ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSESa One Standard Deviation Analysis Level for Single Determination Gamma Emitters Strontium-89b Strontium-90b Potassium Gross Alpha Gross Beta Tritium Radium-226, Radium-228 Plutonium Iodine-131, lodine-129b Uranium-238, Nickel-6 3b, Technetium-99b Iron-55b 5 to 100 pCi/liter or kg
>100 pCi/liter or kg 5 to 50 pCi/liter or k§
>50 pCi/liter or kg 2 to 30 pCi/liter or kg
>30 pCi/liter of kg
>0.1 g/liter or kg
<20 pCi/liter
>20 pCi/liter
<100 pCi/liter
>100 pCi/liter
<4,000 pCi/liter
>4,000 pCi/liter
<0.1 pCi/liter 0.1 pCi/liter, gram, or sample
<55 pCi/liter
>55 pCi/liter
<35 pCi/liter
>35 pCi/liter 50 to 100 pCi/liter 5 pCi/liter 5% of known value 5 pCi/liter 10% of known value 3.0 pCi/liter 10% of known value 5% of known value 5 pCi/liter 25% of known value 5 pCi/liter 5% of known value 1s = (pCi/liter) =
169.85 x (known).0 93 3 10% of known value 15% of known value 10% of known value 6 pCi/liter 10% of known value 6 pCi/liter 15% of known value 10 pCi/liter 10% of known value A-31 a From EPA publication, "Environmental Radioactivity Laboratory Intercompari b son Studies Program, Fiscal Year 1981-1982, EPA-600/4-81-004.
TIML limit.
Revision 0, 12-29-86
ADDENDUM TO APPENDIX A The following is an explanation of the reasons why certain samples were outside the control limit specified by the Environmental Protection Agency for the Interlabora tory Comparison Program starting January 1987.
Lab Code Analysis TIML Result EPA Control Limit Explanation STM-504 Sr-89 Sr-90 STW-511 Ra-228 STW-516 Cr-51 STF-524 K
STW-532 1-131 STW-534 Co-60 5 7.
0+/-4. 3 32.0+/-1.0
- 8.
1+/-1.4
- 80. 3+/- 17.5 1010.7+/-158.5 9.0+/-2.0
- 63. 3+/-1.3 60.3-77.7 32.4-37.6 4.6-8.0 61.3-78.7 1123.5-1336.5 6.2-8.8 41.3-58.7 Milk had high fat content which made analyses difficult.
Ad dition of errors to TIML result would put values within EPA control limits.
EPA also had the same problem in analyzing its own sample.
TINL results are usually within EPA control limits.
Analysis of the next sample was within EPA control limits.
No further action is planned.
Results in the past have been within EPA control limits and TIML will monitor the situation in the future.
Error in transferrance of data.
Correct data was 1105+/-33.
Results in the past have been within the limits and TIML will monitor the situation in the future.
Sample recounted after 12 days.
The average result was 8.8+/-1.7 (within EPA control limits).
The sample was recounted in order to check the decay.
Results in the past have been within the limits and TIML will continue to monitor the situ ation in the future.
High level of Co-60 was due to contamination of beaker.
Beaker was discarded upon dis covery of contamination and sample was recounted.
Recount results were 53.2+/-3.6 and 50.9+/-2.4.
- 50. 9+/-2.4.
A-32
ADDENDUM TO APPENDIX A (continued)
EPA Lab Code Analysis TIML Result Control Limit Explanation STM-554 Sr-90 STW-560 Pu-239 STW-568 Ra-228 STM-570 Sr-89 Sr-90 51.0+/-2.0 5.8+/-1.1 2.6+/-1.0 26.0+/-10.0
- 45. 7+/-4.2 54.8-65.2 3.5-4.9 2.7-4.5 39.0+/-5.0 55.0+/-3.0 The cause of low result is not known and is under investi gation. It should be noted that 63% of all participants failed this test.
Also, the average for all participants was 54.0 pCi/l before the Grubb and 55.8 pCi/l after the Grubb.
The cause of high results is not known (suspected contami nated standard) and is under investigation. New Pu-236 standard was obtained and will be used for the next test.
The cause of low results is under investigation. New dilution was prepared and sample is being reanalyzed.
Sample was used up during testing. Next EPA crosschecks with the control limits.
The cause of low results is under -investigation. New "spike" milk sample was pre pared and being analyzed.
Results of analysis:
See Table A-3, sample QC-Mi-24.
A-33
Appendix B Data Reporting Conventions B-1
Data Reporting Conventions 1.0.
All activitiesexcept gross alpha and gross beta, are decay corrected to collection time or the end of the collection period.
2.0. Single Measurements Each single measurement is reported as follows:
x+/- S where x = value of the measurement; s = 2a counting uncertainty (corresponding to the 95% confidence level).
In cases where the activity is found to be below the lower limit of detection L it is reported as where L = is the lower limit of detection for a background sample.
3.0. Duplicate Analyses 3.1.
Individual results:
Reported result:
based on 4.66a uncertainty xl +/-s X2 S2 x
s where x = (1/2) (x1 + x2) s=(1/2) S2 + 2 3.2.
Individual results:
<L1
<L2 Reported result:
<L where L = lower of L1 and L2 3.3.
Individual results:
x+/- s
<L Reported result:
x +/- s if x > L;
<L otherwise B-2
4.0. Computation of Averages and Standard Deviations 4.1 Averages and standard deviations listed in the tables are computed from all of the individual measurements over the period averaged; for example, an annual standard deviation would not be the average of quarterly standard deviations. The average i and standard deviation(s) of a set of n numbers xl, x2,.
xn are defined as follows:
1 x
x n
5 (x-x) 2 n-1 4.2 Values below the highest lower limit of detection are not included in the average.
4.3 If all of the values in the averaging group are less than the highest LLD, the highest LLD is reported.
4.4 If all but one of the values are less than the highest LLD, the single value x and associated two sigma error is reported.
4.5. In rounding off, the following rules are followed:
4.5.1. If the figure following those to be retained is less than 5, the figure is dropped, and the retained figures are kept unchanged.
As an example, 11.443 is rounded off to 11.44.
4.5.2 If the figure following those to be retained is greater than 5, the figure is dropped, and the last retained figure is raised by 1. As an example, 11.446 is rounded off to 11.45.
4.5.3. If the figure following those to be retained is 5, and if there are no figures other than zeros beyond the five, the figure 5 is dropped, and the last-place figure retained is increased by one if it is an odd number or it is kept unchanged if an even number.
As an example, 11.435 is rounded off to 11.44, while 11.425 is rounded off to 11.42.
8-3
Appendix C Maximum Permissible Concentrations of Radioactivity in Air and Water Above Background in Unrestricted Areas C-1
Table C-1. Maximum permissible concentrations of radioactivity in air and water above natural background in unrestricted areas.a Air Water Gross alpha Gross beta Iodine-131b 3
100 0.14 pCi /m3 pCi/m 3 pCi /m3 Strontium-89 Strontium-90 Cesium-137 Barium-140 Iodine-131 Potassium-40c Gross alpha Gross beta Tritium 3,000 pCi/l 300 pCi/l 20,000 pCi/l 20,000 pCi/l 300 pCi/l 3,000 pCi/l 30 pCi/l 100 pCi/l 3 x 106 pCi/l a Taken from Code of Federal Regulations Title 10, Part 20, Table II and appro priate footnotes. Concentrations may be averaged over a period not greater b than one year.
From 10 CFR 20 but adjusted by a factor of 700 to reduce the dose resulting c from the air-grass-cow-milk-child pathway.
A natural radionuclide.
C-2
APPENDIX D
SUMMARY
OF THE LAND USE CENSUS D-1
SUMMARY
OF THE 1989 LAND USE CENSUS The 1989 land use census was completed in September. It consisted of a house-by-house inspection out to three (3) miles from DAEC for all sectors except the NW and WNW sectors that were surveyed to five (5) miles from DAEC. The Cedar River water usage was surveyed by contacting the Iowa Department of Natural Resources. No direct observation by boat was performed for the second consecutive year due to extremely low river stages.
The Iowa DNR reported no new water use permits issued for 1989.
The main usage of the Cedar River within three (3) miles downstream of DAEC continues to be recreation and fishing.
The census results indicated less changes in land use due to the drought in 1989, than were observed in 1988.
More gardens were observed, as soil moisture improved slightly. A continuation of the home building trend in the SE sector was observed.
No changes in the environmental sampling locations were recommended, as changes in land use did not present any new station-receptor relationships that are not already monitored.
Additionally, a review of the dose calculations included in Appendix E of this report shows that the maximally exposed receptors are in sectors with appropriate sampling.
In all cases, the calculated doses were insignificant.
D-2
APPENDIX E ANNUAL RADIATION DOSE ASSESSMENT E-1
ANNUAL RADIATION DOSE ASSESSMENT The annual offsite radiation dose to a member of the public was determined using environmental dosimeters and by calculations based on monitored effluent releases.
Section A.
Dose Contribution from Direct Radiation Direct radiation dose from the operation of DAEC was recorded by TLDs placed at locations in the surrounding environment as described in the Offsite Dose Assessment Manual (ODAM).
Observations from the collected data follow:
- 1.
Pre-operational and 1989 TLD results were compared using a paired difference test. No difference in the populations were observed at 0.5 and 1 mile using a confidence level of 99%.
- 2.
As stated earlier in this report (part 1, page 9) no plant effect was indicated by the TLDs, as dose results were less than the estimated average natural background for Middle America.
Section B.
Calculated Dose from Effluent Releases The contribution of dose to a member of the public most likely to be exposed from effluent releases was calculated by the Meteorological Information and Dose Assessment System (MIDAS) computer program in accordance with the ODAM. The calculation methods follow those prescribed by Reg Guide 1.109.
Results of these calculations are discussed below:
- 1.
There were no liquid releases in 1989.
- 2.
The doses to air from noble gas released were 1.09E-2 mrad from gamma radiation and 1.25E-2 mrad from beta radiation, both at the south site boundary.
- 3.
The total body dose equivalent to the maximally exposed individual from noble gases was 7.71E-4 mrem, at 1561 meters NNW.
- 4.
The skin dose equivalent to the maximally exposed individual from noble gases was 2.02E-3 mrem, at 1561 meters NNW.
- 5.
The dose equivalent to the maximally exposed individual from iodines and particulates with half-lives greater than eight days was 1.31E-2 mrem to the thyroid of a child at 1561 meters NNW.
E-2
Conclusion No measurable dose was detected by environmental TLDs in 1989.
The calculated dose to the maximally exposed individual for 1989 was 1.39E-2 mrem, and represents the contributions to the total body from noble gases and to a child's thyroid from particulates and iodines. The calculated doses are well below the regulatory limits stated in Appendix I to 10CFR50 and in 40CFR190.
E-3
)IVIDUAL DOSES FOR 1989 AGE GROUP TYPE DISTANCE (meters)
DIRECTION DOSE OR DOSE EQUIVALENT Direct Radiation (as measured by TLDs)
Liquids Releases Noble Gas Gamma air dose Beta air dose Total Body Skin ALL ALL Particulates and lodines Child Thyroid 455 455 1561 1561 1561 S
S NNW NNW NNW 1.09E-2 mrad 1.25E-2 mrad 7.71E-4 mrem 2.02E-3 mrem 1.31E-2 mrem TOTAL (total body plus particulates & iodines) 1.39E-2 mrem E-4 none none
SUMMARY
TABLE OF MAXI
'WTELEDYNE ISOTOPES MIDWEST LABORATORY 700 LANDWEHR ROAD NORTHBROOK, ILLINOIS 60062-2310 (708) 564-0700 FAX (708) 564-4517 REPORT TO IOWA ELECTRIC LIGHT AND POWER CEDAR RAPIDS, IOWA ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM FOR THE DUANE ARNOLD ENERGY CENTER CEDAR RAPIDS, IOWA Docket No. 50-331 ANNUAL REPORT -
PART II DATA TABULATIONS AND ANALYSES JANUARY -
DECEMBER 1989 PREPARED AND SUBMITTED BY TELEDYNE ISOTOPES MIDWEST LABORATORY PROJECT NO. 8001 Approved by:
L.
Huebner General Manager 23 February 1990
TABLE OF CONTENTS List of Tables......
INTRODUCTION.......
LISTING OF MISSED SAMPLES DATA TABLES ii Section 1.0 2.0 3.0 Page 111 1
2 3
LIST OF TABLES No.
Title Pag 1
Airborne particulates collected at Location D-1 (Cedar Rapids), analysis for gross beta........
4 2
Airborne particulates collected at Location D-2 (Marion),
analysis for gross beta and iodine-131.......
5 3
Airborne particulates collected at Location D-3 (Hiawatha),
analysis for gross beta............
6
'4 Airborne particulates collected at Location 0-5 (Palo),
analysis for gross beta......
7 5
Airborne particulates collected at Location D-6 (Center Point), analysis for gross beta and iodine-131 8
6 Airborne particulates collected at Location D-7 (Shellsburg),
analysis for gross beta and iodine-131.........
9 7
Airborne particulates collected at Location D-8 (Urbana),
analysis for gross beta and iodine-131......
10 8
Airborne particulates collected at Location D-10 (Atkins),
analysis for gross beta.........
11 9
Airborne particulates collected at Location D-11 (Toddville),
analysis for gross beta and iodine-131.........
12 10 Airborne particulates collected at Location D-13 (Alburnett),
analysis for gross beta..........
........13 11 Airborne particulates collected at Location 0-15 (on-site, north), analysis for gross beta and iodine-131 14 12 Airborne particulates collected at Location D-16 (on-site, south), analysis for gross beta.....
15 13 Airborne particulate samples, quarterly composites of weekly samples, analysis for gamma-emitting isotopes 16 14 Ambient gamma radiation (TLD), quarterly exposure...
22 iii
LIST OF TABLES (continued)
No.
Title Page 15 Milk samples, analysis for iodine-131 and gamma emitting isotopes.
24 16 Ground water samples, analysis for gross beta and tritium.......................
28 17 Vegetation samples (broad leaf) analysis for iodine-131 and gamma-emitting isotopes............
....30 18 Vegetation samples (hay and grain), analysis for gamma-emitting isotopes..........
31 19 Surface water samples, analysis for gamma-emitting isotopes.........................
33 20 Surface water samples, quarterly composites of monthly samples, analysis for tritium.........
39 21 Fish samples, analysis for gamma-emitting isotopes......
40 22 River sediment samples, analysis for gamma-emitting isotopes.
42 23 Precipitation samples, analysis for gamma-emitting isotopes.................
43 24 Precipitation samples, quarterly composites of monthly samples, analysis for tritium.........
44 25 Meat samples, analysis for gamma-emitting isotopes......
45 26 Soil samples, analysis for strontium-90. and gamma-emitting isotopes...........
46 iv
1.0 INTRODUCTION
The following constitutes a Supplement to the Annual Report for the Radio logical Environmental Monitoring Program conducted at the Duane Arnold Energy
- Center, Cedar Rapids, Iowa in 1989.
Results of completed analyses are pre sented in the attached tables.
For information regarding sampling locations, type and frequency of col lection, and sample codes, please see Tables 5.3 -
5.5 and Figures 5-1 and 5-2 of Part I.
1
OF MISSED SAMPLES Expected Collection Sample Type Location Date Reason Milk D-93 01-04-89 Sample unavailable.
Milk D-101 01-04-89 Sample unavailable.
Milk D-93 02-08-89 Sample unavailable.
Milk D-101 02-08-89 Sample unavailable.
Milk D-101 03-07-89 Sample unavailable.
Milk D-93 05-31-89 Sample unavailable.
TLD D-44 06-29-89 Lost in the field.
TLD D-39 06-29-89 Lost in the field.
TLD D-10 09-21-89 Lost in the field.
TLD D-36 12-28-89 Lost in the field.
2 2.0 LISTING
3.0 DATA TABLES 3
Table 1.
Airborne particulates collected at Location D-1, analysis for gross beta. Collection:
Weekly.
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
(Cedar Rapids),
Date Volume Gross Beta Collected (m3)
(pCi/m 3) 01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 239a 280 279 297 296 297 296 297 297 297 297 299 295 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 295 297 285 287 285 285 286 286 285 285 283 287 286 2nd Qtr mean+/-s.d.
0.073+/-0.006 0.039+/-0.005 0.029+/-0.004 0.021+/-0.004 0.028+/-0.004 0.028+/-0.004 0.020+/-0.004 0.035+/-0.005 0.021+/-0.004 0.023+/-0.004 0.029+/-0.004 0.028+/-0.004 0.030+/-0.004 0.031+/-0.014 0.022+/-0.004 0.017+/-0.004 0.031+/-0.004 0.032+/-0.004 0.017+/-0.004 0.021+/-0.003 0.019+/-0.003 0.018+/-0.003 0.023+/-0.004 0.025+/-0.004 0.013+/-0.003 0.030+/-0.003 0.023+/-0.003 0.022+/-0.006 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 285 286 274 274 234 a 312b 277 273 275 275 235a 313b 285 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 235a 313b 235a 300 344b 300 299 258a 343b 301 299 299 300 4th Qtr mean+/-s.d.
0.022+/-0.004 0.032+/-0.003 0.021+/-0.004 0.023+/-0.004 0.019+/-0.005 0.022+/-0.003 0.026+/-0.004 0.022+/-0.004 0.022+/-0.004 0.018+/-0.003 0.016+/-0.004 0.026+/-0.003 0.016+/-0.004 0.022+/-0.004 0.019+/-0.004 0.028+/-0.004 0.031+/-0.004 0.037+/-0.004 0.029+/-0.003 0.025+/-0.003 0.034+/-0.003 0.028+/-0.005 0.038+/-0.004 0.029+/-0.003 0.054+/-0.004 0.059+/-0.005 0.047+/-0.004 0.035+/-0.012 a 6 day collection period.
b 8 day collection period.
4
Table 2. Airborne particulates collected at Location D-2, (Marion),
analysis for gross beta and iodine-131a. Collection:
Weekly.
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 244b 298 297 297 296 298 296 297 297 297 296 297 295 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 296 299 295 295 300 294 297 300 297 295 296 300 294 2nd Qtr mean+/-s.d.
0.060+/-0.006 0.052+/-0.005 0.033+/-0.004 0.028+/-0.004 0.036+/-0.004 0.034+/-0.004 0.022+/-0.004 0.035+/-0.005 0.026+/-0.004 0.023+/-0.004 0.026+/-0.004 0.028+/-0.004 0.032+/-0.004 0.034+/-0.011 0.023+/-0.004 0.017+/-0.004 0.023+/-0.004 0.028+/-0.004 0.016+/-0.004 0.022+/-0.003 0.016+/-0.003 0.020+/-0.003 0.029+/-0.004 0.030+/-0.004 0.016+/-0.004 0.037+/-0.003 0.029+/-0.004 0.024+/-0.007 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 296 297 298 303 260b 345c 301 302 302 302 261b 345c 305 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89d 12-28-89 259b 343c 259b 302 348c 284 286 244b 326c 287 286 285 284 4th Qtr mean+/-s.d.
0.032+/-0.004 0.042+/-0.004 0.032+/-0.004 0.028+/-0.004 0.021+/-0.005 0.012+/-0.003 0.021+/-0.003 0.014+/-0.003 0.014+/-0.003 0.014+/-0.003 0.008+/-0.003 0.016+/-0.002 0.016+/-0.004 0.021+/-0.010 0.015+/-0.003 0.021+/-0.004 0.021+/-0.003 0.024+/-0.003 0.015+/-0.003 0.028+/-0.004 0.031+/-0.003 0.036+/-0.005 0.040+/-0.004 0.028+/-0.004 0.052+/-0.004 0.004+/-0.003 0.034+/-0.004 0.027+/-0.012 Iodine-131 concentrations are <0.07 6 day collection period.
8 day collection period.
Sample light.
pCi/m 3 unless noted otherwise.
5 a
b c
d
Table 3.
Airborne analysis particulates col for gross beta.
lected at Location D-3, (Hiawatha),
Collection:
Weekly.
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
Date Volume Gross Beta Collected (m3)
(pCi/m 3) 01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 246a 309 307 309 308 309 308 308 308 308 308 132b 249 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 290 293 290 292 293 289 291 292 291 292 291 293 290 2nd Qtr mean+/-s.d.
0.074+/-0.006 0.046+/-0.005 0.034+/-0.004 0.035+/-0.004 0.038+/-0.004 0.041+/-0.004 0.026+/-0.004 0.039+/-0.005 0.027+/-0.004 0.027+/-0.004 0.030+/-0.004 0.020+/-0.007 0.027+/-0.005 0.036+/-0.014 0.021+/-0.004 0.020+/-0.004 0.024+/-0.004 0.032+/-0.004, 0.012+/-0.004 0.013+/-0.003 0.012+/-0.003 0.015+/-0.003 0.023+/-0.004 0.020+/-0.003 0.012+/-0.003 0.024+/-0.003 0.015+/-0.003 0.019+/-0.006 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 290 292 288 289 247a 328c 289 287 288 288 248a 329c 288 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 248a 328c 250a 292 335c 286 292 66b 333c 292 276 291 291 4th Qtr mean+/-s.d.
0.027+/-0.004 0.037+/-0.003 0.021+/-0.004 0.028+/-0.004 0.020+/-0.005 0.020+/-0.003 0.028+/-0.004 0.019+/-0.003 0.022+/-0.003 0.020+/-0.003 0.014+/-0.003 0.025+/-0.003 0.017+/-0.004 0.023+/-0.006 0.024+/-0.004 0.028+/-0.004 0.026+/-0.004 0.031+/-0.004 0.028+/-0.003 0.022+/-0.003 0.030+/-0.003 0.040+/-0.015 0.037+/-0.004 0.030+/-0.004 0.051+/-0.004 0.050+/-0.004 0.034+/-0.004 0.033+/-0.009 a 6 day collection period.
b Low volume; pump out of order.
c 8 day collection period.
6
Table 4. Airborne particulates collected at Location D-5, (Palo), analysis for gross beta and'iodine-131a.
Collection: Weekly.
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
Date Volume Gross Beta Collected (m3)
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 253b 289 287 288 288 289 288 290 288 289 287 288 287 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 288 289 287 287 290 287 288 288 262 288 289 290 287 2nd Qtr mean+/-s.d.
0.078+/-0.006 0.047+/-0.005 0.033+/-0.004 0.028+/-0.004 0.037+/-0.005 0.029+/-0.004 0.023+/-0.004 0.038+/-0.005 0.016+/-0.004 0.021+/-0.004 0.029+/-0.004 0.028+/-0.004 0.036+/-0.004 0.034+/-0.016 0.024+/-0.004 0.019+/-0.004 0.022+/-0.004 0.029+/-0.004 0.016+/-0.004 0.016+/-0.003 0.016+/-0.003 0.017+/-0.003 0.006+/-0.003 0.020+/-0.003 0.015+/-0.004 0.026+/-0.003 0.017+/-0.003 0.019+/-0.006 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 288 287 289 55c 248b 313d 272 276 274 274 235b 314d 274 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 235b 313d 235b 274 316d 273 285 244b 326d 286 286 285 285 4th Qtr mean+/-s.d.
0.022+/-0.004 0.023+/-0.003 0.022+/-0.004 0.092+/-0.018 0.018+/-0.005 0.017+/-0.003 0.032+/-0.004 0.023+/-0.004 0.022+/-0.004 0.021+/-0.003 0.013+/-0.004 0.024+/-0.003 0.018+/-0.004 0.021+/-0.005 0.029+/-0.004 0.030+/-0.004 0.029+/-0.004 0.030+/-0.004 0.022+/-0.003 0.019+/-0.003 0.028+/-0.003 0.033+/-0.005 0.018+/-0.003 0.028+/-0.004 0.044+/-0.004 0.044+/-0.004 0.014+/-0.003 0.028+/-0.009 a Iodine-131 concentrations are <0.07 pCi/m 3 unless noted otherwise.
b 6 day collection period.
c Low volume due to air sampler pump failure, 1-131 concentration <0.279 pCi/m 3 Result not included in mean and standard deviation calculation d 8 day collection period.
7
Table 5.
Airborne analysis particulates collected at Location D-6, (Center Point),
for gross beta.
Collection: Weekly.
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 242a 283 287 288 289 286 288 288 288 289 287 288 287 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 288 289 282 283 284 281 283 283 282 282 283 284 282 2nd Qtr mean+/-s.d.
0.073+/-0.006 0.046+/-0.005 0.028+/-0.004 0.032+/-0.004 0.030+/-0.004 0.033+/-0.004 0.023+/-0.004 0.037+/-0.005 0.029+/-0.004 0.024+/-0.004 0.028+/-0.004 0.032+/-0.004 0.032+/-0.004 0.034+/-0.013 0.023+/-0.004 0.021+/-0.004 0.033+/-0.004 0.044+/-0.005 0.019+/-0.004 0.022+/-0.003 0.022+/-0.003 0.022+/-0.004 0.029+/-0.004 0.032+/-0.004 0.016+/-0.004 0.036+/-0.003 0.027+/-0.004 0.027+/-0.008 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 282 282 283 283 243a 319b 283 282 280 279 240a 320b 280 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 240a 319b 240a 280 323b 273 274 234a 313 b 275 274 274 274 4th Qtr mean+/-s.d.
0.032+/-0.004 0.037+/-0.004 0.024+/-0.004 0.025+/-0.014 0.027+/-0.005 0.016+/-0.003 0.028+/-0.004 0.018+/-0.003 0.020+/-0.003 0.021+/-0.003 0.012+/-0.003 0.025+/-0.003 0.020+/-0.004 0.024+/-0.007 0.018+/-0.003 0.027+/-0.004 0.029+/-0.004 0.029+/-0.004 0.022+/-0.003 0.024+/-0.004 0.031+/-0.003 0.040+/-0.006 0.036+/-0.004 0.030+/-0.004 0.050+/-0.004 0.059+/-0.005 0.043+/-0.004 0.034+/-0.012 a 6 day collection b 8 day collection period.
period.
8
Table 6.
Airborne analysis particulates collected at Location D-7, (Shellsburg),
for gross beta and iodine-131a. Collection:
Weekly.
Date Volume Gross Beta Collected (m3)
(pCi/m 3)
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 223b 260 284 285 285 286 285 285 285 286 284 286 285 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 285 286 285 284 287 284 285 286 285 285 286 287 285 2nd Qtr mean+/-s.d.
0.065+/-0.006 0.054+/-0.006 0.032+/-0.004 0.024+/-0.004 0.032+/-0.004 0.033+/-0.004 0.017+/-0.004 0.038+/-0.005 0.023+/-0.004 0.024+/-0.004 0.025+/-0.004 0.023+/-0.004 0.028+/-0.004 0.032+/-0.014 0.022+/-0.004 0.019+/-0.004 0.023+/-0.004 0.029+/-0.004 0.017+/-0.004 0.016+/-0.003 0.015+/-0.003 0.018+/-0.003 0.020+/-0.004 0.030+/-0.004 0.011+/-0.003 0.027+/-0.003 0.025+/-0.004 0.021+/-0.006 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 284 284 286 291 251b 319c 289 293 291 291 250b 333C 291 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 249 b 333c 250 b 291 323c 279 280 239b 320c 280 280 280 280 4th Qtr mean+/-s.d.
0.023+/-0.004 0.029+/-0.003 0.022+/-0.004 0.027+/-0.004 0.027+/-0.005 0.019+/-0.003 0.029+/-0.004 0.025+/-0.004 0.022+/-0.003 0.023+/-0.003 0.016+/-0.004 0.035+/-0.003 0.021+/-0.004 0.024+/-0.005 0.025+/-0.004 0.032+/-0.004 0.034+/-0.004 0.025+/-0.003 0.028+/-0.003 0.023+/-0.003 0.029+/-0.003 0.030+/-0.005 0.034+/-0.004 0.025+/-0.003 0.046+/-0.004 0.044+/-0.003 0.017+/-0.003 0.030+/-0.008 a Iodine-131 concentrations are <0.07 b 6 day collection period.
c 8 day collection period.
pCi/m 3 unless noted otherwise.
9
Table 7.
Airborne analysis particulates collected at Location D-8, (Urbana),
for gross beta and iodine-131a. Collection:
Weekly.
Date Volume Gross Beta Collected (m3)
(pCi/m 3)
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 231b 272 270 271 271 272 44c 271 271 272 270 223 250 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 293 295 293 294 296 292 294 295 293 293 295 295 292 2nd Qtr mean+/-s.d.
0.052+/-0.006 0.045+/-0.005 0.036+/-0.005 0.032+/-0.004 0.042+/-0.005 0.042+/-0.005
<0.01 0.039+/-0.005 0.015+/-0.004 0.025+/-0.004 0.029+/-0.004 0.025+/-0.005 0.033+/-0.005 0.035+/-0.010 0.020+/-0.004 0.022+/-0.004 0.028+/-0.004 0.022+/-0.004 0.013+/-0.004 0.016+/-0.003 0.014+/-0.003 0.011+/-0.003 0.021+/-0.004 0.020+/-0.003 0.013+/-0.003 0.026+/-0.003 0.018+/-0.003 0.019+/-0.005 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 294 293 280 280 241b 315d 278 282 280 280 237b 320d 279 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 240b 319d 240b 285 329d 284 286 244b 326d 286 286 285 285 4th Qtr mean+/-s.d.
0.021+/-0.003 0.028+/-0.003 0.026+/-0.004 0.025+/-0.004 0.028+/-0.005 0.020+/-0.003 0.031+/-0.004 0.021+/-0.003 0.021+/-0.003 0.010+/-0.003 0.014+/-0.004 0.024+/-0.003 0.018+/-0.004 0.022+/-0.006 0.021+/-0.004 0.025+/-0.004 0.028+/-0.004 0.034+/-0.004 0.025+/-0.003 0.021+/-0.003 0.026+/-0.003 0.026+/-0.005 0.027+/-0.003 0.027+/-0.003 0.041+/-0.004 0.017+/-0.003 0.013+/-0.003 0.026+/-0.007 Iodine-131 concentrations are <0.07 6 day collection period.
Low volume due to power shut-off at 8 day collection period.
pCi/m 3 unless noted otherwise.
pump. 1-131 value less than 0.289.
10 a
b c
d
Table 8.
Airborne analysis particulates collected at Location D-10, for gross beta. Collection:
Weekly.
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
(Atkins),
Date Volume Gross Bta Collected (m3)
(pCi/m )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 239a 280 280 294 290 292 291 291 292 290 291 291 292 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 289 292 288 289 288 287 289 289 288 288 287 290 289 2nd Qtr means+/-s.d.
0.075+/-0.006 0.056+/-0.005 0.029+/-0.004 0.030+/-0.004 0.035+/-0.005 0.032+/-0.004 0.017+/-0.004 0.034+/-0.005 0.023+/-0.004 0.022+/-0.004 0.027+/-0.004 0.027+/-0.004 0.032+/-0.004 0.034+/-0.016 0.018+/-0.004 0.021+/-0.004 0.023+/-0.004 0.028+/-0.004 0.014+/-0.004 0.018+/-0.003.
0.016+/-0.003 0.017+/-0.003 0.019+/-0.004 0.020+/-0.003 0.010+/-0.003 0.025+/-0.003 0.019+/-0.003 0.019+/-0.005 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 288 289 288 271 233a 308b 272 270 273 270 233a 309b 272 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 232a 310b 233a 271 311-b 291 292 247a 332b 292 290 291 291 4th Qtr mean+/-s.d.
0.024+/-0.004 0.027+/-0.003 0.021+/-0.004 0.025+/-0.004 0.021+/-0.005 0.016+/-0.003 0.022+/-0.003 0.020+/-0.004 0.016+/-0.003 0.016+/-0.003 0.011+/-0.003 0.021+/-0.003 0.013+/-0.004 0.020+/-0.005 0.022+/-0.004 0.023+/-0.004 0.026+/-0.004 0.029+/-0.004 0.019+/-0.003 0.021+/-0.003 0.030+/-0.003 0.033+/-0.005 0.034+/-0.004 0.030+/-0.004 0.045+/-0.004 0.049+/-0.004 0.030+/-0.004 0.030+/-0.009 a 6 day collection period.
b 8 day collection period.
11
particulates collected at Location D-11, (Toddville),
for gross beta and iodine-131.a Collection:
Weekly.
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 253b 295 287 288 289 289 288 288 288 289 288 288 287 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 288 289 287 288 287 287 285 286 285 285 286 287 285 2nd.Qtr mean+/-s.d.
-0.067+/-0.006 0.042+/-0.005 0.034+/-0.004 0.033+/-0.004 0.030+/-0.004 0.034+/-0.004 0.020+/-0.004 0.010+/-0.004 0.025+/-0.004 0.020+/-0.004 0.028+/-0.004 0.024+/-0.004 0.029+/-0.004 0.030+/-0.014 0.015+/-0.004 0.016+/-0.004 0.013+/-0.004 0.027+/-0.004 0.014+/-0.004 0.015+/-0.003 0.014+/-0.003 0.018+/-0.003 0.024+/-0.004 0.025+/-0.004 0.013+/-0.003 0.026+/-0.003 0.022+/-0.003 0.019+/-0.005 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 284 285 286 286 250b 332c 292 290 291 291 250b 333c 291 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 250b 332c 250b 292 334c 292 288 247b 329c 289 288 288 288 4th Qtr mean+/-s.d.
0.023+/-0.004 0.029+/-0.003 0.015+/-0.004 0.025+/-0.004 0.021+/-0.005 0.017+/-0.003 0.028+/-0.004 0.025+/-0.004 0.020+/-0.003 0.019+/-0.003 0.016+/-0.004 0.027+/-0.003 0.018+/-0.004 0.022+/-0.005 0.024+/-0.004 0.026+/-0.004 0.029+/-0.004 0.034+/-0.004 0.026+/-0.003 0.024+/-0.003 0.031+/-0.003 0.037+/-0.005 0.034+/-0.004 0.026+/-0.003 0.042+/-0.004 0.022+/-0.003 0.017+/-0.003 0.029+/-0.007 a Iodine-131 concentrations are <0.07 b 6 day collection period.
c 8 day collection period.
pCi/m 3 unless noted otherwise.
12 Table 9.
Airborne analysis
Table 10.
Airborne particulates collected at Location D-13, analysis for gross beta.
Collection:
Weekly.
Date Volume Gross Beta Collected (m3)
(pCi/m 3 )
(Al burnett),
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 253a 295 282 283 283 283 282 282 283 283 282 283 282 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 282 285 287 287 287 287 288 289 288 288 289 290 288 2nd Qtr mean+/-s.d.
0.071+/-0.006 0.050+/-0.006 0.035+/-0.004 0.041+/-0.004 0.048+/-0.005 0.045+/-0.005 0.027+/-0.004 0.047+/-0.005 0.034+/-0.004 0.028+/-0.004 0.029+/-0.004 0.038+/-0.005 0.041+/-0.005 0.041+/-0.012 0.024+/-0.004 0.024+/-0.004 0.027+/-0.004 0.031+/-0.004 0.016+/-0.004 0.021+/-0.003 0.014+/-0.003 0.019+/-0.003 0.025+/-0.004 0.024+/-0.004 0.013+/-0.003 0.029+/-0.003 0.025+/-0.003 0.022+/-0.006 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 287 288 289 286 246a 323b 286 285 285 285 245a 327b 285 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 245a 325b 245a 283 326b 281 283 242a 323b 283 283 282 283 4th Qtr mean+/-s.d.
0.024+/-0.004 0.031+/-0.003 0.023+/-0.004 0.029+/-0.004 0.028+/-0.005 0.019+/-0.003 0.031+/-0.004 0.025+/-0.004 0.024+/-0.004 0.024+/-0.003 0.017+/-0.004 0.030+/-0.003 0.022+/-0.004 0.025+/-0.004 0.026+/-0.004 0.031+/-0.004 0.032+/-0.004 0.037+/-0.004 0.028+/-0.003 0.023+/-0.003 0.034+/-0.003 0.041+/-0.006 0.039+/-0.004 0.033+/-0.004 0.048+/-0.004 0.051+/-0.005 0.033+/-0.004 0.035+/-0.008 a 6 day collection period.
b 8 day collection period.
13
particulates collected at Location D-15, (Onsite North),
for gross beta and iodine-131.a Collection:
Weekly.
Date Volume Gross Beta Collected (m3)
(pCi/m 3)
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 246b 298 296 297 295 299 297 296 297 297 296 296 297 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 296 297 296 118C 283 285 294 290 293 295 295 295 293 2nd Qtr mean+/-s.d.
0.128+/-0.008 0.046+/-0.005 0.031+/-0.004 0.029+/-0.004 0.034+/-0.004 0.038+/-0.004 0.019+/-0.004 0.039+/-0.005 0.025+/-0.004 0.024+/-0.004 0.024+/-0.004 0.025+/-0.004 0.031+/-0.004 0.038+/-0.028 0.021+/-0.004 0.019+/-0.004 0.022+/-0.004 0.035+/-0.009
<0.005 0.006+/-0.002 0.010+/-0.003 0.014+/-0.003 0.021+/-0.004 0.014+/-0.003 0.011+/-0.003 0.018+/-0.002 0.019+/-0.003 0.018+/-0.008 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 294 293 295 294 257b 343d 298 301 300 300 257b 343d 299 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 257b 342d 257b 300 346d 298 285 244b 327d 286 285 285 285 4th Qtr mean+/-s.d.
0.018+/-0.003 0.026+/-0.003 0.019+/-0.004 0.016+/-0.003 0.016+/-0.004 0.013+/-0.003 0.026+/-0.003 0.019+/-0.003 0.019+/-0.003 0.018+/-0.003 0.013+/-0.003 0.022+/-0.003 0.018+/-0.004 0.019+/-0.004 0.023+/-0.004 0.022+/-0.004 0.028+/-0.004 0.030+/-0.003 0.019+/-0.003 0.019+/-0.003 0.028+/-0.003 0.036+/-0.005 0.031+/-0.004 0.026+/-0.003 0.017+/-0.003 0.011+/-0.003 0.012+/-0.003 0.023+/-0.008 a Iodine-131 concentrations are <0.07 pCi/m 3 unless noted otherwise.
b 6 day collection period.
c Low volume due to power failure at pump.
d 8 day collection period.
14 Table 11.
Airborne analysis
Airborne particulates collected at Location D-16, analysis for gross beta. Collection:
Weekly.
Date Volume Gross Beta Collected (m3 )
(pCi/m 3 )
Date Volume Gross Beta Collected (m3)
(pCi/m 3 )
01-05-89 01-12-89 01-19-89 01-26-89 02-02-89 02-09-89 02-16-89 02-23-89 03-02-89 03-09-89 03-16-89 03-23-89 03-30-89 246a 286 287 288 288 289 288 288 288 288 288 288 288 1st Qtr mean+/-s.d.
04-06-89 04-13-89 04-20-89 04-27-89 05-04-89 05-11-89 05-18-89 05-25-89 06-01-89 06-08-89 06-15-89 06-22-89 06-29-89 288 289 287 288 290 288 288 288 288 288 289 281 287 2nd Qtr mean+/-s.d.
0.084+/-0.006 0.052+/-0.005 0.029+/-0.004 0.032+/-0.004 0.038+/-0.005 0.037+/-0.005 0.022+/-0.004 0.040+/-0.005 0.027+/-0.004 0.026+/-0.004 0.029+/-0.004 0.030+/-0.004 0.034+/-0.004 0.037+/-0.016 0.023+/-0.004 0.022+/-0.004 0.028+/-0.004 0.034+/-0.005 0.014+/-0.004 0.020+/-0.003 0.015+/-0.003 0.016+/-0.003 0.022+/-0.004 0.024+/-0.004 0.013+/-0.003 0.027+/-0.003 0.023+/-0.003 0.022+/-0.006 07-06-89 07-13-89 07-20-89 07-27-89 08-02-89 08-10-89 08-17-89 08-24-89 08-31-89 09-07-89 09-13-89 09-21-89 09-28-89 288 287 264 274 235a 313b 283 287 285 285 245a 326b 285 3rd Qtr mean+/-s.d.
10-04-89 10-12-89 10-18-89 10-25-89 11-02-89 11-09-89 11-16-89 11-22-89 11-30-89 12-07-89 12-14-89 12-21-89 12-28-89 245a 326b 245a 285 330b 285 290 246a 330b 289 288 288 287 4th Qtr mean+/-s.d.
0.023+/-0.004 0.027+/-0.003 0.032+/-0.005 0.027+/-0.004 0.024+/-0.005 0.018+/-0.003 0.027+/-0.004 0.022+/-0.003 0.023+/-0.003 0.022+/-0.003 0.018+/-0.004 0.029+/-0.003 0.023+/-0.004 0.024+/-0.004 0.020+/-0.004 0.029+/-0.004 0.031+/-0.004 0.035+/-0.004 0.025+/-0.003 0.021+/-0.003 0.025+/-0.003 0.031+/-0.005 0.031+/-0.004 0.028+/-0.004 0.044+/-0.004 0.042+/-0.004 0.030+/-0.004 0.030+/-0.007 a 6 day collection period.
b 8 day collection period.
15 (Onsite South),
Tabl e 12.
le 13.
Airborne particulate samples, quarterly composites of gamma emitting isotopes.
weekly samples, analysis for Sample Description and Activity (pCi/m 3 )
Location Isotope 1st Qtr.
2nd Qtr.
3rd Qtr.
4th Qtr.
Lab Code Volume (m3)
DAP-1406 3766 DAP-1517 3732 DAP-1637 3598 DAP-1750 3826 0.052+/-0.008
<0.0026
<0.0016
<0.0008
<0.0051
<0.0007
<0.0007
<0.0011
<0.0033 0.064+/-0.013
<0.0015
<0.0019
<0.0011
<0.0059
<0.0008
<0.0009
<0.0010
<0.0029 0.056+/-0.013
<0.0016
<0.0022
<0.0013
<0.0075
<0.0009
<0.0009
<0.0014
<0.0025 0.071+/-0.012
<0.0014
<0.0019
<0.0010
<0.0080
<0.0010
<0.0008
<0.0017
<0.0052 D-2 0~~
Lab Code Volume (m3 )
0.060+/-0.016
<0.0017
<0.0023
<0.0012
<0.010
<0.0012
<0.0014
<0.0021
<0.0059 0.100+/-0.014
<0.0014
<0.0023
<0.0012
<0.009
<0.0009
<0.0010
<0.0017
<0.0057 0.074+/-0.014
<0.0018
<0.0029
<0.0014
<0.010
<0.0012
<0.0012
<0. 0022
<0.0063 0.051+/-0.011
<0.0019
<0.0032
<0.0011
<0.0094
<0. 0007
<0.0013
<0.0027
<0. 0068 D-1 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1407 3805 DAP-1518 3858 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1638 3612 DAP-1751 3793
Airborne particulate samples, quarterly composites of weekly samples (continued)
Isotope 1st Qtr.
Lab Code Volume (m3)
DAP-1408 3709 Sample Description 2nd Qtr.
DAP-1519 3787 and Activity (pCi/m 3 )
3rd Qtr.
4th Qtr.
DAP-1639 3463 DAP-1752 3580 0.052+/-0.010
<0.0014
<0.0019
<0.0009
<0.0060
<0.0006
<0.0007
<0.0009
<0.0023 0.060+/-0.012
<0.0022
<0.0034
<0.0016
<0.014
<0.0015
<0.0015
<0.0025
<0.0073 0.064+/-0.017
<0.0014
<0.0040
<0.0019
<0.013
<0.0010
<0.0017
<0.0027
<0.0079 0.048+/-0.011
<0.0018
<0.0024
<0.0011
<0.0081
<0.0006
<0.0007
<0 0014
<0.0041 I-.
D-5 Lab Code Volume (m3) 0.061+/-0.009
<0.0013
<0.0019
<0.0010
<0.0075
<0.0009
<0.0009
<0.0017
<0.0050 0.066+/-0.015
<0.0023
<0.0032
<0.0015
<0.011
<0.0012
<0:0013
<0.0032
<0.0088 0.058+/-0.011
<0.0016
<0.0026
<0.0016
<0.0096
<0.0011
<0.0013
<0.0025
<0.0071 0.037+/-0.013
<0.0012
<0.0017
<0.0010
<0.0075
<0.0008
<0.0008
<0.0017
<0.0040 Location D-3 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1409 3711 DAP-1520 3720 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1640 3399 DAP-1753 3643 Tabl e 13.
- 3. Airborne particulate samples, quarterly Isotope Lab Code Volume (m3)
Sample Description 1st Qtr.
2nd Qtr.
DAP-1410 3690 DAP-1521 3686 and Activity (pCi/m 3 )
3rd Qtr.
4th Qtr.
DAP-1641 3656 DAP-1754 3593 0.065+0.011
<0.0014
<0.0021
<0.0011
<0.0089
<0.0009
<0.0009
<0.0013
<0.0038 0.092+/-0.016
<0.0016
<0.0025
<0.0015
<0.012
<0.0012
<0.0015
<0.0021
<0.0068 0.062+/-0.016
<0.0021
<0.0024
<0.0013
<0.0085
<0.0009
<0.0011
<0.0028
<0.0077 0.058+/-0.015
<0.0019
<0.0027
<0.0015
<0.0090
<0.0010
<0.0012
<0.0031
<0.0078 D-7 I-Lab Code Volume (m3) 0.058+/-0.013
<0.0016
<0.0020
<0.0012
<0.0076
<0.0008
<0.0011
<0.0024
<0.0065 0.081+/-0.024
<0.0022
<0.0024
<0.0017
<0.013
<0.0014
<0.0019
<0.0033
<0.0096 0.065+/-0.011
<0.0014
<0.0020
<0.0012
<0.0082
<0.0008
<0.0010
<0.0016
<0.0047 0.040+/-0.011
<0.0013
<0.0022
<0.0009
<0.0073
<0.0008
<0.0008
<0.0017
<0.0043 Location D-6 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1411 3619 DAP-1522 3710 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1642 3753 DAP-1755 3684 ites of weekly samples (continued)
Ta 0
- 13.
Airborne particulate samples, quarterly co sites of Sample Description Isotope Lab Code Volume (m3 )
1st Qtr.
DAP-1412 3188 2nd Qtr.
DAP-1523 3820 and Activity (pCi//m3 )
3rd Qtr.
DAP-1643 3659 0.086+/-0.016
<0.0017
<0.0030
<0.0017
<0.013
<0.0011
<0.0014
<0.0032
<0.0098 0.058+/-0.013
<0.0022
<0.0032
<0.0018
<0.012
<0.0013
<0.0015
<0.0025
<0.0077 0.052+/-0.011
<0.0019
<0.0019
<0.0011
<0.0060
<0.0005
<0.0009
<0.0011
<0.0025 0.039+/-0.010
<0.0014
<0.0017
<0.0007
<0.0051
<0.0005
.<0.0008
<0.0013
<0.0035 D-10 I.-
Lab Code Volume (m3 )
0.062+0.010
<0.0014
<0.0020
<0.0011
<0.0066
<0.0010
<0.0009
<0.0013
<0.0041 0.065+/-0.018
<0.0019
<0.0042
<0.0023
<0.014
<0.0013
<0.0018
<0.0036
<0.011 0.060+/-0.015.
<0.0022
<0.0028
<0.0019
<0.012
<0.0012
<0.0016
<0.0031
<0.0078 0.060+/-0.013
<0.0018
<0.0029
<0.0014
<0.0097
<0.0009
<0.0013
<0.0029
<0.0075 Location D-8 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 4th Qtr.
DAP-1756 3695 DAP-1413 3713 DAP-1524 3753 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1644 3576 DAP-1757 3683 weekly samples (continued)
Ta*13.
Airborne particulate samples, quarterly co sites of Isotope 1st Qtr Lab Code Volume (m3 )
DAP-1414 3717 Sample Description 2nd Qtr.
DAP-1525 3725 and Activity (pCi/m 3 )
3rd Qtr.
4th Qtr.
DAP-1645 3761 DAP-1758 3767 0.045+/-0.010
<0.0018
<0.0026
<0.0014
<0.012
<0.0012
<0.0013
<0.0025
<0.0075 0.067+/-0.013
<0.0017
<0.0022
<0.0014
<0.011
<0.0011
<0.0014
<0.0018
<0.0056 0.056+/-0.011
<0.0021
<0.0033
<0.0018
<0.013
<0.0013
<0.0013
<0.0026
<0.0066 0.047+/-0.012
<0.0012
<0.0016
<0.0011
<0.0066
<0.0006
<0.0010
<0.0019
<0.0052 D-13 N)
Lab Code Volume (m3 )
0.080+/-0.012
<0.0018
<0.0029
<0.0016
<0.013
<0.0014
<0.0014
<0.0028
<0.0084 0.074+/-0.016
<0.0029
<0.0035
<0.0011
<0.012
<0.0011
<0.0012
<0.0013
<0.0037 0.072+/-0.012
<0.0017
<0.0020
<0.0012
<0.0084
<0.0010
<0.0008
<0.0018
<0.0052 0.055+/-0.012
<0.0018
<0.0015
<0.0011
<0.0078
<0.0007
<0.0008
<0.0019
<0.0054 Location D-11 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144
'II DAP-1415 3656 DAP-1526 3735 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1646 3717 DAP-1759 3684 weekly samples (continued)
Ta
- 13.
Airborne particulate samples, quarterly c osites of Isotope Lab Code Volume (m3 )
Sample Description and Activity (pCi/m 3 )
1st Qtr.
2nd Qtr.
3rd Qtr.
4th Qtr.
DAP-1416 3807 DAP-1527 3630 DAP-1647 3874 DAP-1760 3797 0.046+/-0.011
<0.0012
<0.0020
<0.0010
<0.0088
<0.0008
<0.0007
<0.0008
<0.0028 0.050+/-0.013
<0.0024
<0.0041
<0.0022
<0.015
<0.0016
<0.0019
<0.0030
<0.0087 0.049+/-0.013
<0.0014
<0.0016
<0.0010
<0.0098
<0.0008
<0.0008
<0.0012
<0.0026 0.035+/-0.012
<0.0019
<0.0026
<0.0012
<0.0071
<0.0008
<0.0009
<0.0029
<0.0066 D-16 I-Lab Code Volume (m3 )
0.068+/-0.011
<0.0017
<0.0023
<0.0013
<0.0086
<0.0010
<0.0011
<0.0019
<0.0058 0.093+/-0.018
<0.0022
<0.0030
<0.0014
<0.012
<0.0012
<0.0014
<0.0036
<0.0095 0.047+0.010
<0.0025
<0.0034
<0.0016
<0.012
<0.0012
<0.0015
<0.0027
<0.0067 0.051+/-0.012
<0.0014
<0.0017
<0.0010
<0.0056
<0.0007
<0.0010
<0.0015
<0.0037 Location D-15 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1417 3700 DAP-1528 3739 Be-7 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 DAP-1648 3657 DAP-1761 3734 weekly samples (continued)
Table 14.
Ambient gamma radiation (TLD), quarterly exposure.
Location mR/91 days No.
1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Air Particulate D-1 D-2 D-3 D-5 D-6 D-7 D-8 D-10 0-11 D-13 D-15 D-16 Mean +/- s.d.
Lpcations 15.2+/-1.1 13.3+/-0.5 15.4+/-0.6 16.2+/-1.0 15.0+/-1.3 18.2+/-1.2 16.7+/-0.4 16.1+/-0.3 11.5+/-0.4 13.3+/-1.2 14.6+/-0.6 13.1+/-0.4 14.9+/-1.8 Within 0.5 mile of stack D-18 D-19 D-20 D-21 D-22 D-23 0-28 D-29 D-30 D-31 D-32 D-82 0-83 D-84 D-85 D-86 D-91 Mean +/- s.d.
14.5+/-0.4 12.2+/-0.4 13.9+/-0.4
- 16. 2+/-0.5 16.0+/-0.4 16.2+/-0.4 17.0+/-0.5 17.6+/-0.6 13.6+/-0.4
- 15. 7+/-0.4 14.0+/-0.6 14.2+/-0.7 15.1+/-1.6 13.7+/-1.2 12.0+/-0.5 14.1+/-0.6 16.0+/-0.8 13.3+/-0.9 17.3+/-1.5 17.5+/-1.2 Missing 15.8+/-0.6 12.9+/-0.8 13.2+/-0.6 13.4+/-1.0 14.5+/-1.9 15.0+/-0.4 12.2+/-0.4 13.9+/-0.7 17.7+/-1.4 17.0+/-1.1 16.2+/-0.8 17.8+/-0.6 17.7+/-0.5 14.2+/-1.2 13.0+/-0.5 15.0+/-0.7 14.0+/-0.8 15.3+/-1.9 16.0+/-0.7 15.4+/-0.7 17.6+/-0.8 15.5+/-0.5 16.1+/-0.9 15.9+/-0.6 16.0+/-1.4 21.0+/-0.8 22.1+/-0.3 22.2+/-0.8 19.5+/-0.8 15.8+/-1.2 17.2+/-0.5 15.3+/-0.5 13.4+/-0.5 17.9+/-0.7 14.0+/-0.7 17.1+/-2.6 16.7+/-0.7
- 17. 1+/-0.6 17.4+/-0.7 13.5+/-0.3
- 15. 2+/-1.1
- 16. 1+/-0.4
- 19. 2+/-1.2 23.0+/-0.9 21.5+/-0.4 23.3+/-1.4 20.6+/-0.4 16.2+/-0.4
- 18. 3+/-1.1 18.0+/-0.5 15.8+/-0.6 20.4+/-0.9 13.7+/-0.5 18.0+/-3.0 20.3+/-2.1 15.5+/-0.6 17.8+/-0.7 16.4+/-0.4 16.3+/-0.7 16.0+/-1.0 21.0+/-1.8 21.9+/-1.0 23.3+/-0.5 22.9+/-0.6 19.8+/-0.5 19.2+/-1.6 17.4+/-0.9 17.0+/-1.6 14.9+/-1.2 18.3+/-0.6 12.4+/-1.1 18.2+/-3.0 16.7+/-0.6 16.9+/-1.3 17.0+/-0.5 16.8+/-1.3 15.8+/-0.6 15.9+/-0.7 20.7+/-0.7 23.1+/-0.5 22.4+/-0.8 22.8+/-0.6 21.4+/-1.0 18.3+/-1.3 18.3+/-1.0 18.3+/-0.8 15.5+/-0.4 20.2+/-1.2 14.1+/-0.4 18.5+/-2.8 22
Table 14.
Ambient gamma radiation (TLD),
quarterly exposure (continued).
Location mR/91 days No.
1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Within 1.0 mile of stack D-43 0-44 D -45 D-46 0-47 D-48 Mean +/- s.d.
- 15. 1+/-1.5 22.1+/-1.3 15.1+/-1.3 20.4+/-0.5 25.9+/-1.6 20.7+/-0.6 19.9+/-4.2 18.0+/-0.5 Missing 17.9+/-0.9 22.6+/-0.8 23.1+/-0.8 19.2+/-1.5 20.2+/-2.5 16.0+/-0.6 21.9+/-1.2 15.8+/-0.6
- 22. 1+/-1.8
- 22. 1+/-0.9 21.3+/-0.7 19.9+/-3.1
- 17. 5+/-0.6 19.3+/-0.7 17.9+/-0.7 21.5+/-0.9 22.2+/-0.6 19.6+/-0.9 19.7+/-1.9 Within 3.0 miles of stack D-33 D-34 D-35 D-36 D-37 D-38 0-39 0-40 D-41 Mean +/- s.d.
12.7+/-0.4 13.3+/-0.5 13.6+/-0.3 15.6+/-0.4 19.6+/-0.4 17.6+/-0.8 17.8+/-0.9 14.6+/-0.4 15.5+/-0.7 15.6+/-2.3 13.3+/-0.4 15.6+/-0.6 14.9+/-0.6 16.0+/-0.5 22.9+/-2.0 17.5+/-0.8 Missing 16.5+/-0.4 18.2+/-1.3 16.9+/-2.9 12.7+/-0.6 13.4+/-0.8 13.1+/-0.4 17.3+/-1.7 21.2+/-1.7 18.0+/-1.1 17.6+/-0.7 16.8+/-1.5 15.0+/-0.6 16.1+/-2.8 13.7+/-0.4 15.3+/-0.5 15.1+/-0.4 Missing 22.8+/-0.6 17.6+/-0.5 18.4+/-0.8 17.9+/-0.9 17.6+/-1.2 17.3+/-2.8 23
'I
/ ~.1 I
Vt,
/
Table 15.
Milk samples, analyses for 1-131 and gamma-emitting isotopes.
Collection:
Monthly during non-grazing season (October 1 through April 30); biweekly during grazing season (May 1 through September 30)
Location and Concentration (pCi/1)
Date Collected Lab Code 1-131 Cs-134 Cs-137 Ba-140 La-140 K-40 Indicator D-63 01-04-89 DMI-2981
<1.0
<15
<18
<60
<15 1320t140 02-08-89 3089
<1.0
<15
<18
<60
<15 1190+/-110 03-07-89 3145
<1.0
<15
<18
<60
<15 1340150 04-04-89 3223
<1.0
<15
<18
<60
<15 1330+/-130 05-02-89 3300,1
<1.0
<15
<18
<60
<15 1380+/-100 05-16-89 3377
<1.0
<15
<18
<60
<15 1470+/-120 05-31-89 3436
<1.0
<15
<18
<60
<15 1360+/-140 06-13-89 3499
<1.0
<15
<18
<60
<15 1180+/-140 06-27-89 3576
<1.0
<15
<18
<60
<15 1220+/-140 07-11-89 3644
<1.0
<15
<18
<60
<15 1290+/-100 07-25-89 3740
<1.0
<15
<18
<60
<15 1300+/-150 08-08-89 3803
<1.0
<15
<18
<60
<15 1400+/-110 08-22-89 3882
<1.0
<15
<18
<60
<15 1400+/-160 09-06-89 3957
<1.0
<15
<18
<60
<15 1380+/-150 09-19-89 4030
<1.0
<15
<18
<60
<15 1000+/-120 10-10-89 4105
<1.0
<15
<18
<60
<15 1240+/-150 11-07-89 4248
<1.0
<15
<18
<60
<15 1250+/-140 12-05-89 4314
<1.0
<15
<18
<60
<15 1070+/-100 24
Milk samples, analysis for (continued) iodine-131 and gamma-emitting isotopes Location and Concentration (pCi/1)
Date.Collected Lab Code 1-131 Cs-134 Cs-137 Ba-140 La-140 K-40 Indicator 0-93 NSa NS DMI-3146 3224 3302 3378 NS 3500 3577 3645 3741 3804,5 3884,5 3958 4031 4106,7 4249 4315 DMI-2982 3090 3147 3225 3303 3379 3437 3501,2 3578 3646 3742 3806 3883 3959 4032 4108 4250 4316,7
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15 1420+/-140 1640+/-150 1800+/-190 1620+/-140 1910+/-150 1920+/-150 1690+/-150 1630+/-150 1920+/-90 1840+/-110 1750+/-140 1760+/-140 1900+/-120 1740+/-120 1340+/-140 1430+/-110 1400+/-90 1340+/-100 1160+/-100 1350+/-150 1230+/-150 1110+/-130 1220+/-130 1360+/-170 1360+/-150 1280+/-110 1070+/-110 1380+/-150 1480+/-170 1380+/-150 1400+/-130 1300+/-100 1520+/-90 a NS = No sample; sample unavailable.
25 Table 15.
01-04-89 02-08-89 03-07-89 04-04-89 05-02-89 05-16-89 05-31-89 06-13-89 06-27-89 07-11-89 07-25-89 08-08-89 08-22-89 09-06-89 09-19-89 10-10-89 11-07-89 12-05-89 D-94 01-04-89 02-08-89 03-07-89 04-04-89 05-02-89 05-16-89 05-31-89 06-13-89 06-27-89 07-11-89 07-25-89 08-08-89 08-22-89 09-06-89 09-19-89 10-10-89 11-07-89 12-05-89
Table 15.
Milk samples, analysis for iodine-131 and gamma-emitting isotopes (continued)
Location and Lab Concentration (pCi/1)
Date Collected Code 1-131 Cs-134 Cs-137 Ba-140 La-140 K-40 Indicator D-96 01-04-89 02-08-89 03-07-89 04-04-89 05-02-89 05-16-89 05-31-89 06-13-89 06-27-89 07-11-89 07-25-89 08-08-89 08-22-89 09-06-89 09-19-89 10-10-89 11-07-89 12-05-89 DMI-2983,8 3091 3148 3226 3304 3380 3438 3503 3579 3647 3743 3807 3886 3960 4033 4109 4251 4318 NSa NS NS DMI-3227 3305 3381,2 3439 3504 3580 3648 3744,5 3808 3887 3961 4034,5 4110 4252 4319
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0 41.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<1.0
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<18
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<60
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15
<15 a NS = No sample; sample unavailable.
26 1420+/-140 1440+/-100 1400+/-120 1400+/-130 1660+/-180 1390+/-100 1320+/-160 1170+/-120 1280+/-140 1370+/-110 1420+/-110 1490+/-160 1350+/-140 1330+/-140 1170+/-130 1270+/-140 1380+/-160 1290+/-60 1780+/-110 1310+/-120 1800+/-150 1740+/-130 1870+/-130 1930+/-160 1700+/-120 1890+/-130 2040+/-190 1850+/-120 1770+/-1 50 1960+/-130 1750+/-160 1720+/-150 1070+/-110 D-101 01-04-89 02-08-89 03-07-89 04-04-89 05-02-89 05-16-89 05-31-89 06-13-89 06-27-89 07-11-89 07-25-89 08-08-89 08-22-89 09-06-89 09-19-89 10-10-89 11-07-89 12-05-89
Table 15.
Milk samples, analysis for iodine-131 and gamma-emitting isotopes (continued)
Location and Concentration (pCi/1)
Date Collected Lab Code 1-131 Cs-134 Cs-137 Ba-140 La-140 K-40 Indicator D-106 01-04-89 DMI-2985
<1.0
<15
<18
<60
<15 1190+/-100 02-08-89 3093
<1.0
<15
<18
<60
<15 1280+/-130 03-07-89 3151
<1.0
<15
<18
<60
<15 1210+/-100 04-04-89 3229,30
<1.0
<15
<18
<60
<15 1220+/-100 05-02-89 3307
<1.0
<15
<18
<60
<15 1080+/-130 05-16-89 3384
<1.0
<15
<18
<60
<15 1280+/-130 05-31-89 3441,2
<1.0
<15
<18
<60
<15 1220+/-90 06-13-89 3506
<1.0
<15
<18
<60
<15 1310+/-140 06-27-89 3582,3
<1.0
<15
<18
<60
<15 1180+/-120 07-11-89 3650
<1.0
<15
<18
<60
<15 1120+/-130 07-25-89 3747
<1.0
<15
<18
<60
<15 1180+/-140 08-08-89 3810
<1.0
<15
<18
<60
<15 1210+/-100 08-22-89 3889
<1.0
<15
<18
<60
<15 1290+/-150 09-06-89 3963
<1.0
<15
<18
<60
<15 1340+/-120 09-19-89 4037
<1.0
<15
<18
<60
<15 1230+/-120 10-10-89 4112
<1.0
<15
<18
<60
<15 1200+/-140 11-07-89 4254
<1.0
<15
<18
<60
<15 1120+/-100 12-05-89 4321
<1.0
<15
<18
<60
<15 1280+/-110 Control D-105 01-04-89 DMI-2984
<1.0
<15
<18
<60
<15 1180+/-140 02-08-89 3092
<1.0
<15
<18
<60
<15 1330+/-130 03-07-89 3149,50
<1.0
<15
<18
<60
<15 1130+70 04-04-89 3228
<1.0
<15
<18
<60
<15 1250+150 05-02-89 3306
<1.0
<15
<18
<60
<15 1330+/-140 05-16-89 3383
<1.0
<15
<18
<60
<15 1260+/-110 05-31-89 3440
<1.0
<15
<18
<60
<15 1350+/-140 06-13-89 3505
<1.0
<15
<18
<60
<15 1230+/-120 06-27-89 3581
<1.0
<15
<18
<60
<15 1210+90, 07-11-89 3649
<1.0
<15
<18
<60
<15 1240+/-150 07-25-89 3746
<1.0
<15
<18
<60
<15 1160+/-120 08-08-89 3809
<1.0
<15
<18
<60
<15 1400+/-140 08-22-89 3888
<1.0
<15
<18
<60
<15 1230+130 09-06-89 3962
<1.0
<15
<18
<60
<15 1170+/-130 09-19-89 4036
<1.0
<15
<18
<60
<15 1360+140 10-10-89 4111
<1.0
<15
<18
<60
<15 1270+/-140 11-07-89 4253
<1.0
<15
<18
<60
<15 1230+110 12-05-89 4320
<1.0
<15
<18
<60
<15 1160+/-140
.27
Table 16.
Ground water samples, analysis for gross beta and tritium.
Collection:
Quarterly.
Location and Lab Concentrati n (pCi/1)
Period Collected Code Gross Beta H-3 D-53 Treated Municipal Water 1st 2nd 3rd 4th Qtr.,
Qtr.,
Qtr.,
Qtr.,
1989 1989 1989 1989 DWW-1176 2280 3396 4614 Annual Mean +/- s.d.
D-54 Inlet to Municipal Water Treatment 1st 2nd 3rd 4th Qtr.,
Qtr.,
Qtr.,
Qtr.,
1989 1989 1989 1989 DWW-1177 2281 3397 4615 Annual Mean +/- s.d.
D-55 On-site Well 2.8+/-0.5 3.3+/-0.3 3.8+/-0.4 3.4+/-0.3 3.3+/-0.4 3.2+/-0.6 4.0+/-0.4 4.8+/-0.4
- 4.
1+/-0.3 4.0+/-0.7
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330 Qtr.,
1989 Qtr., 1989 Qtr., 1989 Qtr.,
1989 DWW-1178 2282 3398,9 4616 Annual Mean +/- s.d.
D-57 Bull Farm Qtr.,
Qtr.,
Qtr.,
Qtr.,
1989 1989 1989 1989 DWW-1179 2283,4 3400 4617 Annual Mean +/- s.d.
1st 2nd 3rd 4th 40.8
<0.7 0.6+/-0.2
<0.4 0.6+/-0.2
<330
<330
<330
<330
<330 1st 2nd 3rd 4th 1.6+/-0.4 1.4+/-0.3
- 1.
3+/-0.3 0.9+/-0.3 1.3+/-0.3
<330
<330
<330
<330
<330 28
Table 16.
Ground water samples, analysis for gross beta and tritium (continued).
Location and Lab Concentration (pCi/1)
Period Collected Code Gross Beta H-3 D-58 Franz Farm 1st Qtr., 1989 DWW-1180 7.5+/-0.7
<330 2nd Qtr., 1989 2285 6.4+/-0.6
<330 3rd Qtr., 1989 3401 6.3+/-0.4
<330 4th Qtr., 1989 4618 7.1+/-0.4
<330 Annual Mean +/- s.d.
6.8+/-0.6
<330 D-72 Van Note Farm 1st Qtr., 1989 DWW-1181 1.1+/-0.4
<330 2nd Qtr., 1989 2286 1.5+/-0.4
<330 3rd Qtr., 1989 3402 1.4+/-0.3
<330 4th Qtr., 1989 4619 1.1+/-0.3
<330 Annual Mean +/- s.d.
1.3+/-0.2
<330 29
Table 17.
Vegetation samples (broad leaf), analysis for 1-131 and gamma emitting isotopes.
Collection:
Annually.
Sample Description and Activity (pCi/g wet)
Indicator Location Date Collected Type Lab Code 1-131 K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 Location Date Collected Type Lab Code 1-131 K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 D-57 07-12-89 Cabbage DVE-648
<0.051 3.30+/-0.54
<0.057
<0.059
<0.052
<0.052
<0.096
<0.048
<0.50
<0.050
<0.056
<0.073
<0.31 D-93 07-11-89 Lettuce DVE-642
<0.024 4.69+/-0.61
<0.029
<0.028
<0.030
<0.029
<0.051
<0.020
<0.21
<0.022
<0.027
<0.018
<0.078 D-58 07-12-89 Cabbage DVE-649,50
<0.041 2.88+/-0. 32
<0. 038
<0.034
<0.030
<0.038
<0.074
<0.033
<0. 32
<0.034
<0. 039
<0.052
<0.22 Indicator D -94 07-11-89 Lettuce DVE-643
<0.040 5.65+/-0.74
<0.037
<0.036
<0. 040
<0.033
<0.061
<0.032
<0.32
<0. 032
<0.036
<0.045
<0.22 D-63 07-11-89 Cabbage DVE-641
<0.023 1.54+/-0.21
<0.023
<0.020
<0.019
<0.022
<0.038
<0.019
<0.18
<0.019
<0.024
<0.030
<0.12 D -106 07-11-89 Cabbage DVE-647
<0.033 3.00+/-0.51
<0.026
<0.026
<0.036
<0.025
<0.047
<0.025
<0.20
<0.027
<0.027
<0.037
<0.17 D -72 07-12-89 Cabbage DVE-651
<0.022 3.16+/-0.41
<0.018
<0.015
<0.015
<0.016
<0.028
<0.014
<0.12
<0.013
<0.016
<0.026
<0.10 Control D-105 07-11-89 Cabbage DVE-646
<0.017.
2.91+/-0.44
<0.020
<0.017
<0.021
<0.021
<0.030
<0.017
<0.13
<0.014
<0.019
<0.014
<0.061 30
Vegetation samples,analysis for gamma-emitting isotopes, (continued).
Sample Description and Activity (pCi/g wet)
Indicator Location Date Collected Type Lab Code K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 Location Date Collected Type Lab Code K-40 Mn-54 Co-58 CO-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 D-63 09-20-89 Hay DVE-783 14.66+/-0.66
<0.027
<0.025
<0.025
<0.029
<0.052
<0.029
<0.23
<0.022
<0.029
<0.059
<0.22 D-106 09-20-89 Hay DVE-788 13.90+/-0.67
<0.026
<0.024
<0.026
<0.027
<0.046
<0.027
<0.22
<0.027
<0.025
<0.046
<0. 19 D-72 09-20-89 Hay DVE-784 6.71+/-0.35
<0.012
<0.013
<0.014
<0.014
<0.023
<0.013
<0.10
<0.013
<0.012
<0.023
<0.092 Indicator D-93 09-20-89 Hay DVE-785 17.30+/-0.85
<0.029
<0.033
<0.034
<0.032
<0.055
<0.029
<0.26
<0.029
<0.031
<0.046
<0.20 DAEC Pasturea 09-20-89 Hay DVE-789,90 7.34+/-0.58
<0.043
<0.043
<0.049
<0.045
<0.075
<0.039
<0.35
<0.040
<0.042
<0.033
<0.12 D-94 09-20-89 Hay DVE-786 14.66+/-0.69
<0.035
<0.036
<0.031
<0.041
<0.067
<0.039
<0.30
<0.032
<0.035
<0.064
<0.24 Control D-105 09-20-89 Hay DVE-787 11.50+/-0.62
<0.026
<0.025
<0.026
<0.029
<0.046
<0.026
<0.21
<0.026
<0.024
<0.047
<0.18 a Special collection.
31 Table 18.
Vegetation samples analysis for gamma-emitting isotopes.
Sample Description and Activity (pCi/g wet)
Indicator Location Date Collected Type Lab Code K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 Location Date Collected Type Lab Code K-40 Mn-54 Co-58 CO-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 D-16 11-08-89 Soy Beans DVE-839,40 10.41+/-0.51
<0.034
<0.031
<0.045
<0.033
<0.055
<0.031
<0.27
<0.031
<0.041
<0.038
<0.17 D-72 11-08-89 Corn DVE -844 3.32+/-0.56
<0.025
<0.023
<0.026
<0.029
<0.040
<0.022
<0.18
<0.017
<0.029
<0.020
<0.086 D-93 11-08-89 Corn DVE-845 3.29+/-0.55
<0.019
<0.024
<0.027
<0.028
<0.046
<0.019
<0.22
<0.018
<0.024
<0.022
<0.077 D-57 11-08-89 Corn DVE-841 2.68+/-0.41
<0.024
<0.023
<0.019
<0.025
<0.043
<0.023
<0.26
<0.020
<0.027
<0.029
<0.12 D-58 11-08-89 Corn DVE-842 1.90+/-0.46
<0.023
<0.021
<0.029
<0.022
<0.051
<0.024
<0.23
<0.023
<0.027
<0.022
<0.079 Indicator D-63 11-08-89 Corn DVE-843 3.01+/-0.39
<0.014
<0.018
<0.022
<0.024
<0.027
<0.019
<0.16
<0.016
<0.027
<0.015
<0.054 Control D-105 11-08-89 Corn DVE-847 2.76+/-0.42
<0.021
<0.020
<0.021
<0.021
<0.032
<0.021
<0.17
<0.017
<0.022
<0.028
<0.10 D-94 11-08-89 Corn DVE-846 2.76+/-0.51
<0.023
<0.024
<0.027
<0.029
<0.030
<0.024
<0.22
<0.024
<0.023
<0.019
<0.069 D-106 11-08-89 Corn DVE-848 2.56+/-0.31
<0.016
<0.017
<0.021
<0.017
<0.028
<0.016
<0.14
<0.015
<0.016
<0.022
<0.094 32 Tabl e 18.
Table 19.
Surface water samples, analysis for gamma-emitting isotopes.
Collection:
Monthly.
Location Sample Description and Activity (pCi/1)
Indicator -
Plant Intake D-50 01-23-89 02-28-89 03-29-89 04-25-89 DSW-244 DSW-708 DSW-1171 DSW-1494
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 09-22-89 10-30-89 DSW-3404 DSW-3999,4000
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30 500
<15
<18
<60
<15 11-30-89 DSW-4256
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 12-26-89 DSW-4609
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 33 05-24-89 06-30-89 07-26-89 08-30-89 DSW-1821 DSW-2270 DSW-2682 DSW-3155
Table 19.
Surface water samples, analysis for gamma-emitting isotopes (continued)
Location Sample Description and Activity (pCi/1)
Indicator -
Plant Discharge D-51 01-23-89 DSW-245
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 02-28-89 DSW-709
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 03-29-89 DSW-1172,3
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 04-25-89 DSW-1495
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 09-22-89 10-30-89 11-30-89 12-26-89 DSW-3405 DSW-4001 DSW-4257 DSW-4610
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 34 05-24-89 06-30-89 07-26-89
. 08-30-89 DSW-1822 DSW-2271 DSW-2683 DSW-3156
Table 19.
Surface water samples, analysis for gamma-emitting isotopes (continued)
Location Sample Description and Activity (pCi/1)
Indicator -
Pleasant Creek D-99 01-23-89 DSW-246,7
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 02-28-89 DSW-710
<15
<30
<15
<15
<30
<15
.<30
<500
<15
<18
<60
<15 03-29-89 DSW-1174
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 04-25-89 DSW-1496
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 09-22-89 10-30-89 11-27-89 12-26-89 DSW-3406 DSW-4002 DSW-4258 DSW-4611
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
. <30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 35 05-24-89 06-30-89 07-26-89 08-30-89 DSW-1823 DSW-2272 DSW-2684 DSW-3157
Table 19.
Surface water samples, analysis for gamma-emitting isotopes (continued)
Location Sample Description and Activity (pCi/1)
Indicator -
Plant Sewage Dischar D-107 Date Collected Lab Code K-40a Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code K-40a Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 ge 01-23-89 02-28-89 03-29-89 04-25-89 DSW-248 DSW-711 DSW-1175 DSW-1497,8 17.38
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 19.20
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 05-24-89 06-30-89 DSW-1824 DSW-2273,4 20.50
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 19.4
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 15.6
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 07-26-89 DSW-2685 16.8
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 20.6
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 08-30-89 DSW-3158 16.3
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 a Analyzed by flame photometry.
36
Surface water samples, analysis (continued) for gamma-emitting isotopes (continued)
Location Sample Description and Activity (pCi/1)
Indicator -
Plant Sewage Discharge D-107 Date Collected 09-22-89 10-30-89 11-27-89 12-26-89 Lab Code DSW-3407 DSW-4003 DSW-4259 DSW-4612,3 K-40a 20.3 Mn-54
<15
<15
<15
<15 Fe-59
<30
<30
<30
<30 Co-58
<15
<15
<15
<15 Co-60
<15
<15
<15
<15 Zn-65
<30
<30
<30
<30 Nb-95
<15
<15
<15
<15 Zr-95
<30
<30
<30
<30 1-131
<500
<500
<500
<500 Cs-134
<15
<15
<15
<15 Cs-137
<18
<18
<18
<18 Ba-140
<60
<60
<60
<60 La-140
<15
<15
<15
<15 a Analyzed by flame photometry.
37 Table 19.
Surface water samples, analysis for gamma-emitting isotopes (continued)
Location Sample Description and Activity (pCi/1)
Control -
Lewis Access D-49 01-23-89 02-28-89 03-29-89 04-25-89 DSW-243 DSW-707 DSW-1170 DSW-1493
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Date Collected Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 09-22-89 10-30-89 11-27-89 12-26-89 DSW-3403 DSW-3998 DSW-4255 DSW-4608
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15
<15
<30
<15
<15
<30
<15
<30
<500
<15
<18
<60
<15 38 05-24-89 06-30-89 07-26-89 08-30-89 DSW-1820 DSW-2269 DSW-2680,1 DSW-3153,4 Tabl e 19.
Table 20.
Surface water samples, quarterly composites of monthly samples, analysis for tritium.
Location and Concentration (pCi/1)
Period Collected Lab Code H-3 Indicator D-50 1st 2nd 3rd 4th Qtr.,
Qtr.,
Qtr.,
Qtr.,
1989 1989 1989 1989 DSW-1101 2392 3587 4719 Annual Mean +/- s.d.
<330
<330
<330
<330
<330 D-51 DSW-1102,3 2393 3588 4720 Annual Mean +/- s.d.
1st 2nd 3rd 4th Qtr.,
Qtr.,
Qtr.,
Qtr.,
1989 1989 1989 1989 Annual Mean +/- s.d.
D-107 1st Qtr., 1989 2nd Qtr., 1989 3rd Qtr., 1989 4th Qtr., 1989 Annual Mean +/- s.d.
Control D-49 1 st, 2nd 3rd 4th Qtr.,
Qtr.,
Qtr.,
Qtr.,
1989 1989 1989 1989 DSW-1104 2394 3589,90 4721 DSW-1105 2395 3591 4722 DSW-1100 2391 3586 4718 Annual Mean +/- s.d.
1st 2nd 3rd 4th Qtr.,
Qtr.,
Qtr.,
Qtr.,
1989 1989 1989 1989 D-99
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330
<330 39
Fish samples, analysis of edible portion for gamma-emitting isotopes.
Collection:
Semiannually.
Sample Description and Activity (pCi/g wet)
Indicator Downstream D-61 Date Collected Type Lab Code K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 04-20-89 Carp DF-656 2.07+/-0.56
<0.026
<0.033
<0.027
<0.044
<0.059
<0.033
<0.26
<0.026
<0.029
<0.054
<0.15 04-20-89 Carpsucker DF-657 2.17+/-0.53
<0.027
<0.027
<0.026
<0.038
<0.052
<0.028
<0.21
<0.022
<0.025
<0.046
<0.13 04-20-89 Black Bullhead DF-658a 3.26+/-2.29
<0.12
<0.14
<0.11
<0.18
<0.26
<0.13
<1.09
<0.11
<0.12
<0.23
<0.66 Date Collected Type Lab Code K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 11-10-89 Carp DF-919,20 2.61+/-0.24
<0.019
<0.021
<0.023
<0.020
<0.031
<0.017
<0.16
<0.018
<0.019
<0.023
<0.10 11-10-89 Shorthead Redhorse DF-921 4.82+/-0.31
<0.024
<0.021
<0.020
<0.024
<0.039
<0.021
<0.18
<0.018
<0.023
<0.039
<0.15 11-10-89 Carpsucker DF-922 4.04+/-0.33
<0.022
<0.023
<0.023
<0.022
<0.040
<0.022
<0.20
<0.022
<0.023
<0.028
<0.12 a Elevated LLD due to small sample size.
40 Table 21.
Fish samples, analysis of edible portion for gamma-emitting isotopes.
(continued)
Sample Description and Activity (pCi/g wet)
Control Upstream D-49 Date Collected Type Lab Code K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 04-20-89 Carp DF-653 3.56+/-0.44
<0.016
<0.016
<0.023
<0.025
<0.035
<0.020
<0.15
<0.016
<0.022
<0.022
<0.061 04-20-89 Shorthead Redhorse DF-654 3.77+/-1.21
<0.055
<0.064
<0.063
<0.089
<0.13
<0.065
<0.49
<0.054
<0.065
<0.10
<0.29 04-20-89 Carpsucker DF-655 2.51+/-0.54
<0.023
<0.025
<0.024
<0.032
<0.046
<0.026
<0.20
<0.021
<0.024
<0.041
<0.12 Date Collected Type Lab Code K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 11-10-89 Carpsucker DF-916 2.81+/-0.29
<0.016
<0.020
<0.017
<0.019
<0.032
<0.018
<0.14
<0.015
<0.019
<0.033
<0.13 11-10-89 Quill Back DF-917 2.51+/-0.53
<0.028
<0.027
<0.031
<0.031
<0.048
<0.028
<0.22
<0.025
<0.030
<0.035
<0.14 11-10-89 Shorthead Redhorse DF-918 3.36+/-0.42
<0.032
<0.030
<0.027
<0.031
<0.051
<0.034
<0.28
<0.031
<0.034
<0.047
<0.18 41 Table 21.
River sediment samples, analysis for gamma-emitting isotopes.
Collection:
Semiannually.
Sample Description and Activity (pCi/g dry)
Control Location Date Collected Lab Code K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 Location Date Collected Lab Code K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 D-51 05-10-89 DBS-520,1 10.30+/-0.32
<0.013
<0.022
<0.015
<0.046
<0.042
<0.038
<0.10
<0.016
<0.011
<0.089
<0.089 D-50 05-10-89 DBS-519 11.34+/-0.59
<0.031
<0.044
<0.034
<0.11
<0.10
<0.079
<0.28
<0.027 0.13+/-0.04
<0.12
<0.11 D-51 11-15-89 DBS-679 6.79+/-0.55
<0.033
<0.030
<0.039
<0.032
<0.054
<0.035
<0.27
<0.033
<0.036
<0.049
<0.18 Table 22.
D-50 11-15-89 DBS-677 7.27+/-0.99
<0.056
<0.052
<0.091
<0.065
<0.092
<0.050
<0.40
<0.045
<0.058
<0.071
<0.27 Indicator D-107 05-09-89 DBS-518 8.70+/-0.44
<0.020
<0.034
<0.030
<0.091
<0.071
<0.064
<0.18
<0.018
<0.025
<0.14
<0.12 D-107 11-15-89 DBS-678 9.08+/-0.77
<0.030
<0.030
<0.041
<0.033
<0.046
<0.030
<0.28
<0.025
<0.028
<0.054
<0.017 42
Table 23.
Precipitation samples, analysis for gamma-emitting isotopes.
Collection:
Monthly, 1989.
Sample Description and Concentration (pCi/1)
Collection Period Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Collection Period Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Collection Period Lab Code Mn-54 Fe-59 Co-58 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 January DP-773,4
<4
<8
<4
<3
<8
<4
<7
<8
<3
<4
<20
<3 May DP-821
<3
<7
<3
<2
<5
<3
<6
<8
<3
<3
<18
<4 September DP-858
<6
<11
<5
<5
<10
<6
<9
<10
<4
<5
<24
<5 February DP-785
<4
<8
<5
<4
<10
<5
<8
<7
<5
<4
<21
<5 June DP-831
<4
<8
<4
<3
<7
<4
<7
<8
<3
<4
<18
<4 October DP-868
<6
<11
<5
<6
<10
<6
<9
<10
<4
<5
<26
<5 Ma rch DP -800
<7
<18
<7
<8
<16
<8
<13
<14
<6
<8
<41
<12 July DP-840
<5
<12
<5
<5
<9
<6
<9
<10
<5
<6
<26
<6 November DP-877a
<22
<43
<19
<20
<38
<23
<36
<39
<17
<20
<98,
<21 a Elevated LLD's due to small sample size (150ml).
43 April DP-810
<5
<14
<5
<5
<11
<6
<10
<9
<5
<5
<31
<9 August DP-848
<6
<12
<6
<6
<11
<7
<12
<12
<5
<6
<30
<7 December DP-886
<3
<7
<3
<3
<7
<3
<5
<7
<3
<3
<17
<6
Table 24. Precipitation samples, quarterly composites of monthly samples, analysis for tritium.
Location and Concentration (pCi/1)
Period Collected Lab Code H-3 1st Qtr. 1989 DP-799
<330 2nd Qtr. 1989 836
<330 3rd Qtr. 1989 859
<330 4th Qtr. 1989 887
<330 44
Table 25.
Meat samples, analysis of edible portion for ganma-emitting isotopes.
Collection:
Annually.
Sample Description and Activity (pCi/g wet)
Location Date Collected Type Lab Code ND K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 a ND = No data.
Meat not available.
45
Soil samples, analysis for strontium-90 and gamma-emitting isotopes.
Collection: Annually.
Sample Description and Activity (pCi/g dry)
Location Date Collected Lab Code Sr-90 K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144 D-15 07-12-89 DSO-319,20 0.076+/-0.011 13.90+/-0.46
<0.043
<0.080
<0.045
<0.20
<0.17
<0.15
<0.41
<0.045 0.28+/-0.02
<0.31
<0.25 D-105a 11-15-89 DSO-384 0.067+/-0.010 13.51+/-0.61
<0.029
<0.028
<0.036
<0.041
<0.052
<0.031
<0.24
<0.027 0.36+/-0.04
<0.049
<0.17 Location Date Collected Lab Code D-16 07-12-89 DSO-321 0.017+/-0.007 8.28+/-0.44
<0.022
<0.044
<0.028
<0.10
<0.075
<0.086
<0.18
<0.018 0.076+/-0.020
<0.16
<0.13 a Special collection.
46 Table 26.
Sr-90 K-40 Mn-54 Co-58 Co-60 Nb-95 Zr-95 Ru-103 Ru-106 Cs-134 Cs-137 Ce-141 Ce-144