United States Eastern Environmental EPA 520/5-85-009
Environmental Protection Radiation Facility December 1984
Agency 1890 Federal Drive
Montgomery, AL 36109
Radiation
&EPA
Environmental Radiation
Data
Report 39
July - September 1984
-------
ENVIRONMENTAL
RADIATION
DATA
REPORT 39
July » September 1984
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Office of Radiation Programs
-------
Preface
Environmental Radiation Data (ERD) is compiled and distributed
quarterly by the Office of Radiation Programs' Eastern Environmental
Radiation Facility (EERF), Montgomery, Alabama, and contains data
from the Environmental Radiation Ambient Monitoring System (ERAMS).
Data from similar networks operated by contributing States, Canada,
Mexico, and the Pan American Health Organization are reported in the
ERD when available.
ERAMS was established in 1973 by the U. S. Environmental
Protection Agency's Office of Radiation Programs (ORP). The ERAMS is
comprised of nationwide sampling stations that provide air, surface
and drinking water, and milk samples from which environmental
radiation levels are derived. The major emphasis for ERAMS is toward
identifying trends in the accumulation of long-lived radionuclides in
the environment.
Sampling locations are selected to provide optimal population
coverage while functioning to monitor fallout from nuclear devices
and other forms of radioactive contamination of the enviromnent. The
radiation analyses performed on these samples include gross alpha and
gross beta levels, gamma analyses for fission products, and specific
analyses for uranium, plutonium, strontium, iodine, radium, krypton,
and tritium. This monitoring effort also provides ancillary
information on natural background levels and on releases into the
environment from stationary sources such as nuclear power reactors,
fuel fabrication facilities, and reprocessing plants.
in
-------
ENVIRONMENTAL RADIATION
DATA
CONTENTS
Page
DATA - Reporting Rationale and Procedures vii
- Table of Reporting Increments and Minimum
Detectable Levels
DATA - ERAMS
SECTION I. Air Program 1
1. Airborne Particulates 1
and Precipitation
2. Plutonium and Uranium in 14
Airborne Particulates
3. Krypton-85 15
SECTION II. Water Program 16
1. Surface Water 16
2. Drinking Water 21
SECTION III. External Gamma Ambient Monitoring Program 31
-------
SECTION IV- Milk Program 34
1. Pasteurized Milk 34
2. Strontiuro-39 and -90 in Jlilk 41
3. Carbon-14 in Milk 43
VI
-------
DATA + Reporting Rationale and Procedures
The U.S. Environmental Protection Agency's Office of Radiation
Programs, in 1973, established the Environmental Radiation Monitoring
System(ERAMS) to provide continuous, accurate, and usable
environmental radiation data to the public. Thus, ERAMS data for all
specific radionuclide analyses are reported as the counting results
indicate, whether the numbers are negative, zero, or positive.
Reporting Rationale
Frequently, concentrations of a radionuclide in environmental
media are close to zero. When the actual concentration of a nuclide
is zero, the net counting results should statistically show a
distribution of negative and positive numbers about zero. This
occurs when the background count is subtracted from a sample which
has only background activity. Prior to July 1975, ERAMS data were
not reported numerically when the results were less than a specified
reporting level or minimum detectable level. The present reporting
procedure allows all the data to be reported and evaluated
statistically without an arbitrary cutoff of small or negative
numbers. This approach will facilitate estimates of bias in the
nuclide analyses and will allow better evaluation of distributions
and trends in environmental data.
When reviewing the data in this report, caution should be
exercised in the interpretation of individual negative values.
Obviously, a negative activity value does not have physical
significance. Such numbers, however, are significant when taken
together with other observations which indicate that the true value
of a distribution is near zero. When an average of several
measurements produces a result less than zero, this indicates a
negative bias in the measurement procedure.
(1) Reported Values
Specific Analyses + All specific radionuclide analyses will
be reported as the counting results indicate, whether the number
is negative, zero, or positive. All reported values are
corrected for decay to the collection date.
vn
-------
Gross Analyses - The actual value of gross radioactivity
measurements will be reported, unless the value is below the
minimum detectable level (MDL) at the 2 sigraa confidence level,
then < minimum detectable level will be reported.
MDL is defined as the 3 sigma error of the background. A
tabulation of fIDL's is given in the following table.
(2) Reported Error Terms
Each reported value for specific analyses will be
accompanied by a counting error term at the 2 sigma (95%)
confidence interval. Potassium concentrations are determined by
specific activity analyses. Error terms are therefore reported
as counting errors. At the very low levels characteristic of
most ERAMS measurements, counting error is the greatest
contributor to overall error.
(3) Significant Figures
All reported values will be rounded to no more than three
significant figures. The last significant figure will be
increased by one if the figure following is five or greater,
otherwise it is left unchanged.
(4) Reporting Levels
The reporting units, smallest increments for reporting, and
minimum detectable levels for each isotope are shown in table 1.
Smallest increments are sometimes considerably smaller than
minimum detectable amounts to avoid truncation errors in
averaging.
(5) Averages
Averages will be calculated along with appropriate error
terms in an annual summary and analysis of ERAMS data. In
calculating these averages, all values of individual data
including negative numbers will be utilized. Averages will not
be included in ERD quarterly reports.
-------
TABLE 1
ERAMS Reporting Increments and Minimum Detectable Levels
for Radionuclide Analyses
Radionuclide
Gross alpha
Gross beta
Tritium
CarboniU
Krypton*85
Plutonium*238,
239
Uranium*234 ,
235,238
Radium*226
Reporting
Media Units
Water
Air
Water
Precipitation
Water
Milk
Milk
Ambient Air
Air
Milk
Water
Air
Milk
Water
Water
pCi/1
pCi/m3
pCi/1
nCi/m2
nCi/1
nCi/1
pCi/1
pCi/m3
aCi/m3
pCi/1
pCi/1
aCi/m3
pCi/1
pCi/1
pCi/1
Reporting
Increments
1 pCi/1
.01 pCi/m3
1 pCi/1
.01 nCi/jn2
.1 nCi/1
.1 nCi/1
1 pCi/1
.1 pCi/m3
.1 aCi/m3
.001 pCi/1
.001 pCi/1
.1 aCi/m3
.001 pCi/1
.001 pCi/1
.1 pCi/1
Minimum
Detectable
Levels
2 pCi/1
.01 pCi/m3
1 pCi/1
.01 nCi/m2(a)
.2 nCi/1
.2 nCi/1
15 pCi/1
2 pCi/m3
.015 pCi(b)
per sample
.015 pCi
per sample
.015 pCi
per sample
.015 pCi(b)
per sample
.015 pCi
per sample
.015 pCi
per sample
.1 pCi/1
IX
-------
Radionuclide
Strontium*90
Strontium*89
Iodine*131
Iodine»129
Cesium*137
Barium*140
Potassium
Potassium*40
Media
Milk
Water
Milk
Milk
Water
Water
(specific
Milk
Milk
Water
Milk
Water
Milk
Water
Water
Reporting
Units
pCi/1
pCi/1
pCi/1
pCi/1
pCi/1
pCi/1
radiochemical
fCi/1
pCi/1
pCi/1
pCi/1
pCi/1
8/1
g/1
pCi/1
Reporting
Increments
.1 pCi/1
.1 pCi/1
1 pCi/1
1 pCi/1
1 pCi/1
.1 pCi/1
analysis)
.1 fCi/1
1 pCi/1
1 pCi/1
1 pCi/1
1 pCi/1
.1 g/1
.1 g/1
1 pCi/1
Minimum
Detectable
Levels
1 pCi/1
1 pCi/1
5 pCi/l(c>
10 pCi/l(c>
10 pCi/l(c>
.4 pCi/1
.4 fCi/1
10 pCi/1
10 pCi/1
10 pCi/l
10 pCi/l(c)
.12 g/1
.12 g/1
100 pCi/1
(a) The value in terms of nCi/m2 would be dependent on precipitation (mm),
(b) This value in terms of pCi/nr* would be dependent on the air volume.
(c) Activity as of the day of counting.
-------
DATA + EPA
ENVIRONMENTAL RADIATION
AMBIENT MONITORING SYSTEM (ERAMS)
SECTION I. Air Program
Airborne Participates and Precipitation
Gross beta radioactivity measurements and certain specific
analyses are performed on air particulates and precipitation samples
as indicator measurements in assessing the general (national) impact
of all contributing sources on environmental levels of radiation.
Airborne particulates are collected continuously at field
stations representing wide geographic coverage, including present and
potential sources of environmental radioactivity. Sampling sites are
located throughout the United States, Virgin Islands, and the Panama
Canal.
Filters ( 10+cm diameter synthetic fiber ) from air samplers are
changed twice weekly and field measurements are made with a G»M
survey meter at 5 hours and 29 hours after collection to allow for
radon and thoron daughter product decay. Field estimates are
reported to appropriate EPA officials by telephone or mail depending
on the activity levels found.
The filters are sent to EERF for more sensitive analyses in a
low background beta counter. Gamma scans are performed on all
filters showing laboratory gross beta counts greater than 1
pCi/m3. The lower gross beta values reported for laboratory
measurements are largely due to the decay of radionuclides which
occurred between the times of the field estimates and laboratory
measurements.
Precipitation samples are collected at the field stations where
air filters are collected. These samples are also sent to EERF where
they are composited monthly for tritium, gross beta activity
measurements and gamma scans. Plutonium*238, +239, and uraniura*234,
+235, and +238 analyses are performed on samples which exceed 2
pCi/liter gross alpha.
-------
Tables 2*4 present the monthly average gross beta
concentrations in airborne particulates for July * September 1984.
Tables 5*7 present the monthly average gross beta
concentration in precipitation July * September 1984.
The tritium in precipitation samples for July * September 1984
at the selected stations are shown in Table 8.
A compilation of individual measurements is available from the
EPA, EERF, Montgomery, AL 36109.
-------
TABLE 2
AIRBORNE PARTICULATES
GROSS BETA CONCENTRATION
JULY 1984
LOCATION
# SAM
5+HR FIELD
ESTIMATE
MAX MIN AVG
(pCi/m3)
EERF LAB
MEASUREMENT
MAX MIN AVG
(pCi/m3)
AL: MONTGOMERY
CA: BERKELEY
CA:LOS ANGELES
CO: DENVER
CT: HARTFORD
DE: WILMINGTON
FL:
FL:
GA:
HI:
JACKSONVILLE
MIAMI
ATLANTA
HONOLULU
IA:IOWA CITY
ID:
ID:
IL:
IN:
KS:
ME:
MI:
MN:
MO:
MS:
NC:
NC:
ND:
NH:
NJ:
NM:
NV:
NY:
NY:
NY:
NY:
NY:
OH:
OH:
OH:
OK:
OR:
BOISE
IDAHO FALLS
CHICAGO
INDIANAPOLIS
TOPEKA
AUGUSTA
LANSING
MINNEAPOLIS
JEFFERSON CITY
JACKSON
CHARLOTTE
WILMINGTON
BISMARCK
CONCORD
TRENTON
SANTA FE
LAS VEGAS
ALBANY
NEW YORK CITY
NIAGARA FALLS
SYRACUSE
YAPHANK
COLUMBUS
PAINESVILLE
TOLEDO
OKLAHOMA CITY
PORTLAND
9
8
9
9
9
9
1
9
3
9
9
9
9
9
2
8
9
9
9
7
7
6
9
9
9
9
7
9
4
9
9
5
5
9
3
9
4
9
0.9
0.0
0.4
0.0
0.2
0.5
0
0
0
0
0
1
0
0
0
1
0
0
0
1
0
0
0
1
0
0
0
0
0
0
0
0
0
0
0
1
1
0
.0
.0
.1
.1
.6
.0
.0
.4
.5
.4
.2
.6
.6
.9
.7
.1
.0
.0
.3
.4
.6
.2
.2
.2
.5
.1
.1
.8
.2
.2
.3
.0
0.1
0.0
0.0
0.0
0.1
0.1
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
0
0
0
0
0
0
0
.0
.0
.0
.2
.3
.0
.1
.1
.2
.1
.1
.1
.2
.2
.0
.0
.0
.0
.1
.2
.0
.1
.1
.2
.1
.0
.2
.1
.2
.5
.0
0.5
0.0
0.2
0.0
0.2
0.2
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
0
0
0
0
0
0
.0
.0
.1
.3
.4
.0
.2
.3
.7
.2
.4
.3
.9
.4
.1
.0
.3
.1
.2
.3
.1
.1
.1
.3
.1
.0
.5
.2
.5
.9
0.0
0.01
0.01
0.01
0.02
0.01
0.01
0.01
0.01
0.01
0.01
0.02
0.02
0.01
0.03
0.01
0.01
0.01
0.03
0.03
0.14
0.04
0.01
0.01
0.02
0.01
0.01
0.01
0.03
0.01
0.02
0.02
0.02
0.01
0.03
0.01
0.04
0.02
0.01
0.01
0.00
0.00
0.01
0.00
0.00
0.01
0.00
0.01
0.00
0.01
0.01
0.01
0.00
0.01
0.00
0.01
0.00
0.01
0.01
0.01
0.01
0.00
0.01
0.00
0.00
0.01
0.01
0.01
0.00
0.01
0.00
0.00
0.01
0.01
0.01
0.01
0.00
0.01
0.00
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.00
0.01
0.01
0.01
0.04
0.02
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.02
0.02
0.00
-------
TABLE 2 (CONTINUED)
LOCATION
AIRBORNE PARTICULATES
GROSS BETA CONCENTRATION
JULY 1984
# SAM
PArHARRISBURG
RI:PROVIDENCE
SC:BARNWELL
SC:COLUMBIA
SD:PIERRE
TN:KNOXVILLE
TN:NASHVILLE
TX:AUSTIN
TX:EL PASO
VAiLYNCHBURG
VA:VIRGINIA BEACH
WA:SEATTLE
WA:SPOKANE
WI:MADISON
WV:CHARLESTON
5*HR FIELD
ESTIMATE
MAX MIN AVG
(pCi/m3)
EERF LAB
MEASUREMENT
MAX MIN AVG
(pCi/m3)
9
4
2
8
8
7
4
9
9
10
4
8
9
8
5
0.5
0.1
0.0
0.1
0.4
0.4
1.0
1.2
0.6
1.1
0.1
0.0
0.3
0.5
0.6
0.0
0.1
0.0
0.1
0.1
0.1
0.5
0.4
0.2
0.3
0.1
0.0
0.2
0.1
0.1
0.2
0.1
0.0
0.1
0.3
0.3
0.7
0.7
0.4
0.6
0.1
0.0
0.3
0.3
0.3
0.01
0.01
0.01
0.01
0.02
0.02
0.01
0.05
0.02
0.01
0.01
0.00
0.01
0.01
0.02
0.01
0.01
0.00
0.01
0.01
0.01
0.01
0.01
0.01
0.00
0.00
0.00
0.01
0.00
0.01
0.01
0.01
0.00
0.01
0.01
0.01
0.01
0.02
0.01
0.01
0.01
0.00
0.01
0.01
0.01
MINIMUM DETECTABLE LIMIT FOR FIELD ESTIMATES * .1 pCi/m3
MINIMUM DETECTABLE LIMIT FOR LAB MEASUREMENT * .01 pCi/m3
-------
TABLE 3
AIRBORNE PARTICULATES
GROSS BETA CONCENTRATION
AUGUST 1984
LOCATION
// SAM
AL:MONTGOMERY
CA: BERKELEY
CArLOS ANGELES
CO:DENVER
CT:HARTFORD
DE:WILMINGTON
FL:JACKSONVILLE
FL:MIAMI
HI:HONOLULU
LA:IOWA CITY
ID:BOISE
ID:IDAHO FALLS
IL:CHICAGO
IN:INDIANAPOLIS
KS:TOPEKA
ME:AUGUSTA
MI:LANSING
MN:MINNEAPOLIS
MO:JEFFERSON CITY
MS:JACKSON
NC:CHARLOTTE
NC:WILMINGTON
ND:BISMARCK
NH:CONCORD
NJ:TRENTON
NM:SANTA FE
NV:LAS VEGAS
NY:ALBANY
NY:NEW YORK CITY
NY:NIAGARA FALLS
NY:SYRACUSE
NY:YAPHANK
OH:COLUMBUS
OH:PAINESVILLE
OH:TOLEDO
OK:OKLAHOMA CITY
OR:PORTLAND
5-HR FIELD
ESTIMATE
MAX MIN AVG
(pCi/m3)
EERF LAB
MEASUREMENT
MAX MIN AVG
(pCi/ra3)
9
9
9
7
9
5
2
9
9
9
9
8
6
7
9
9
9
8
9
8
6
9
6
9
9
5
9
4
9
9
4
7
9
9
9
8
7
2.1
0.1
0.4
0.0
0.4
0.5
0.2
0.0
0.3
0.7
0.7
0.0
0.7
1.1
1.9
0.6
1.0
0.5
2.1
0.9
0.4
0.1
0.8
0.4
0.6
0.6
0.3
0.1
0.2
0.7
0.2
0.1
1.1
0.9
1.5
1.1
0.0
0.1
0.0
0.1
0.0
0.1
0.1
0.1
0.0
0.0
0.0
0.2
0.0
0.0
0.4
0.3
0.1
0.2
0.3
0.4
0.1
0.0
0.0
0.1
0.1
0.1
0.2
0.1
0.0
0.1
0.1
0.0
0.0
0.2
0.1
0.1
0.3
0.0
0.7
0.0
0.3
0.0
0.3
0.2
0.2
0.0
0.1
0.3
0.4
0.0
0.3
0.7
0.8
0.3
0.5
0.4
1.2
0.4
0.2
0.1
0.4
0.3
0.4
0.3
0.2
0.1
0.1
0.3
0.1
0.0
0.6
0.3
0.6
0.6
0.0
0.02
0.00
0.01
0.02
0.01
0.02
0.02
0.02
0.01
0.02
0.02
0.02
0.02
0.03
0.01
0.03
0.02
0.03
0.04
0.08
0.06
0.02
0.03
0.01
0.01
0.01
0.01
0.02
0.02
0.02
0.01
0.01
0.03
0.02
0.02
0.04
0.01
0.00
0.00
0.01
0.01
0.00
0.01
0.01
0.00
0.00
0.01
0.01
0.01
0.01
0.01
0.00
0.00
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.00
0.01
0.01
0.01
0.01
0.01
0.01
0.00
0.01
0.01
0.01
0.01
0.00
0.01
0.00
0.01
0.02
0.01
0.01
0.01
0.01
0.01
0.02
0.02
0.01
0.02
0.02
0.00
0.01
0.01
0.02
0.02
0.02
0.02
0.01
0.02
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.02
0.01
0.01
0.01
0.00
-------
TABLE 3 (CONTINUED)
AIRBORNE PARTICIPATES
GROSS BETA CONCENTRATION
AUGUST 1984
LOCATION
5-HR FIELD
ESTIMATE
# SAM MAX MIN AVG
(pCi/m3)
EERF LAB
MEASUREMENT
MAX MIN AVG
(pCi/m3)
5
4
2
9
3
8
1
9
9
6
2
6
9
9
9
0.6
0.3
0.2
0.5
1.1
1.0
0.0
1.7
0.5
1.3
0.1
0.1
0.4
1.9
0.8
0.2
0.0
0.0
0.1
0.4
0.1
0.0
0.6
0.1
0.2
0.1
0.0
0.2
0.2
0.0
0.4
0.1
0.1
0.3
0.7
0.4
0.0
1.0
0.3
0.7
0.1
0.0
0.3
0.7
0.3
0.01
0.01
0.01
0.03
0.02
0.02
0.00
0.05
0.02
0.01
0.01
0.01
0.01
0.02
0.02
0.01
0.01
0.00
0.01
0.01
0.01
0.00
0.00
0.01
0.01
0.00
0.00
0.01
0.00
0.01
0.01
0.01
0,00
0.02
0.02
0.01
0.00
0.02
0.01
0.01
0.00
0.00
0.01
0.01
0.01
PA:HARRISBURG
RI:PROVIDENCE
SC:BARNWELL
SC:COLUMBIA
SD:PIERRE
TN:KNOXVILLE
TN:NASHVILLE
TX:AUSTIN
TX:EL PASO
VA:LYNCHBURG
VA:VIRGINIA BEACH
WA:SEATTLE
WA:SPOKANE
WI:MADISON
WV:CHARLESTON
MINIMUM DETECTABLE LIMIT FOR FIELD ESTIMATES
MINIMUM DETECTABLE LIMIT FOR LAB MEASUREMENT
.1 pCI/m3
.01 pCi/m3
-------
TABLE 4
AIRBORNE PARTICULATES
GROSS BETA CONCENTRATION
SEPTEMBER 1984
LOCATION
# SAM
5--HR FIELD
ESTIMATE
MAX MIN AVG
(pCi/m3)
EERF LAB
MEASUREMENT
MAX MIN AVG
(pCi/m3)
AL:
AR:
MONTGOMERY
LITTLE ROCK
CA: BERKELEY
CA:
CO:
CT:
DE:
FL:
FL:
HI:
IA:
ID:
ID:
IL:
IN:
KS:
ME:
MI:
MN:
MO:
MS:
NC:
NC:
ND:
NH:
NJ:
NM:
NV:
NY:
NY:
NY:
NY:
NY:
OH:
OH:
OH:
OK:
OR:
LOS ANGELES
DENVER
HARTFORD
WILMINGTON
JACKSONVILLE
MIAMI
HONOLULU
IOWA CITY
BOISE
IDAHO FALLS
CHICAGO
INDIANAPOLIS
TOPEKA
AUGUSTA
LANSING
MINNEAPOLIS
JEFFERSON CITY
JACKSON
CHARLOTTE
WILMINGTON
BISMARCK
CONCORD
TRENTON
SANTA FE
LAS VEGAS
ALBANY
NEW YORK CITY
NIAGARA FALLS
SYRACUSE
YAPHANK
COLUMBUS
PAINESVILLE
TOLEDO
OKLAHOMA CITY
PORTLAND
8
4
8
8
7
8
7
8
8
8
8
8
8
8
7
8
8
8
8
8
8
8
6
6
8
7
4
8
4
8
8
6
8
8
8
7
3
8
2
0
0
0
0
0
0
0
0
0
0
0
0
0
1
0
0
0
0
1
1
0
0
0
0
1
0
0
0
0
0
0
0
1
0
0
0
0
.3
.2
.1
.8
.0
.6
.4
.1
.0
.3
.5
.7
.0
.4
.4
.9
.6
.4
.6
.6
.0
.3
.1
.6
.4
.0
.6
.4
.1
.3
.2
.1
.1
.0
.4
.5
.8
.0
0.4
0.1
0.0
0.2
0.0
0.2
0.1
0.0
0.0
0.1
0*i 0
0.1
0.0
0.1
0.0
0.1
0.1
0.1
0.1
0.2
0.2
0.0
0.0
0.1
0.1
0.3
0.2
0.2
0.0
0.0
0.0
0.0
0.0
0.1
0.1
0.1
0.6
0.0
1.1
0.2
0.1
0.4
0.0
0.3
0.2
0.0
0.0
0.2
0.2
0.4
0.0
0.2
0.4
0.4
0.3
0.3
0.3
0.7
0.6
0.1
0.1
0.3
0.2
0.6
0.4
0.3
0.1
0.2
0.1
0.1
0.0
0.4
0.2
0.3
0.7
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
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.02
.01
.02
.02
.04
.01
.01
.02
.01
.01
.01
.03
.02
.02
.02
.00
.01
.01
.01
.02
.03
.05
.02
.02
.01
.01
.01
.02
.01
.02
.02
.01
.01
.03
.02
.03
.04
.01
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,
0,
0,
0,
0
0,
0
0
0
0
0
0
0
,01
.01
.00
.01
.01
.00
.01
.01
.00
.00
.00
.01
.00
.01
.01
.00
.01
.01
.01
.01
.01
.01
.01
.00
.00
.01
.01
.01
.01
.01
.01
.01
.00
.01
.01
.01
.01
.00
0.01
0.01
0.01
0.01
0.02
0.01
0.01
0.01
0.00
0.01
0.01
0.02
0.01
0.01
0.01
0.00
0.01
0.01
0.01
0.02
0.02
0.02
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.01
0.02
0.01
0.02
0.02
0.00
-------
LOCATION
TABLE 4 (CONTINUED)
AIRBORNE PARTICIPATES
GROSS BETA CONCENTRATION
SEPTEMBER 1984
# SAM
PA:HARRISBURG
RI:PROVIDENCE
SC:BARNWELL
SC:COLUMBIA
TN:KNOXVILLE
TN:NASHVILLE
TX:AUSTIN
TX:EL PASO
VA:LYNCHBURG
VA:VIRGINIA BEACH
WA:SEATTLE
WA:SPOKANE
WI:MADISON
WV:CHARLESTON
5*HR FIELD
ESTIMATE
MAX MIN AVG
(PCi/m3)
EERF LAB
MEASUREMENT
MAX MIN AVG
(pCl/m3)
8
5
2
8
8
4
8
8
8
2
8
8
8
6
0.8
0.8
0.1
1.0
1.5
0.3
2.0
0.7
1.6
0.1
0.1
0.8
0.7
0.6
0.2
0.1
0.0
0.1
0.1
0.3
0.1
0.2
0.0
0.1
0.0
0.2
0.2
0.1
0.4
0.3
0.1
0.3
0.7
0.3
1.1
0.5
0.6
0.1
0.0
0.4
0.5
0.4
0.02
0.01
0.05
0.03
0.02
0.02
0.04
0.02
0.03
0.01
0.01
0.02
0.01
0.03
0.01
0.01
0.00
0.01
0.01
0.01
0.01
0.01
0.01
0.00
0.00
0.01
0.00
0.01
0.01
0.01
0.03
0.02
0.01
0.01
0.01
0.02
0.01
0.00
0.00
0.01
0.01
0.02
MINIMUM DETECTABLE LIMIT FOR FIELD ESTIMATES * .1 pCi/m3
MINIMUM DETECTABLE LIMIT FOR LAB MEASUREMENT * .01 pCi/m3
8
-------
TABLE 5
GROSS BETA CONCENTRATION IN PRECIPITATION
JULY 1984
LOCATION
DEPTH
ACT. + 2s
(mm) (nCi/ra2)
AL: MONTGOMERY
CO: DENVER
CT: HARTFORD
DC: WASHINGTON
DE: WILMINGTON
FL: JACKSONVILLE
FL:MIAMI
GA: ATLANTA
ID: BOISE
ID: IDAHO FALLS
IL: CHICAGO
IN: INDIANAPOLIS
MI: LANSING
MN MINNEAPOLIS
MS: JACKSON
ND: BISMARCK
NH: CONCORD
NJ: TRENTON
NV:LAS VEGAS
NY: ALBANY
NY: NEW YORK CITY
NY: NIAGARA FALLS
NY:YAPHANK
OH: COLUMBUS
OH:PAINESVILLE
OR: PORTLAND
PA:HARRISBURG
SC:BARNWELL
SC: COLUMBIA
SD: PIERRE
TN:KNOXVILLE
TN: NASHVILLE
TX: AUSTIN
TX:EL PASO
VA:LYNCHBURG
VA: VIRGINIA BEACH
WA: SEATTLE
WI: MADISON
140.0
47.4
102.5
90.0
155.0
11.1
93.1
85.0
26.3
47.5
56.3
18.2
12.0
81.7
28.0
7.5
167.8
83.3
107.5
56.6
55.0
32.6
136.3
48.3
74.4
32.5
140.8
60.0
354.5
30.0
50.0
12.8
10.0
5.0
51.5
197.5
13.8
121.3
0.13
0.06
0.12
0.16
0.32
0.01
0.11
0.16
0.07
0.06
0.12
0.06
0.03
0.13
0.03
0.03
0.33
0.24
0.25
0.19
0.07
0.02
0.17
0.05
0.08
0.01
0.31
0.03
0.88
0.02
0.06
0.02
0.04
0.01
0.43
0.48
0.01
0.11
0.06
0.02
0.05
0.05
0.09
0.00
0.05
0.04
0.02
0.02
0.04
0.01
0.01
0.04
0.01
0.01
0.09
0.05
0.06
0.04
0.03
0.01
0.07
0.02
0.04
0.01
0.08
0.02
0.21
0.01
0.03
0.01
0.01
0.00
0.05
0.11
0.01
0.06
ND NO GAMMA ACTIVITY DETECTABLE
s SIGMA COUNTING
ERROR
SPECIFIC
GAMMA ACT,
(pCi/1)
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE 6
GROSS BETA CONCENTRATION IN PRECIPITATION
AUGUST 1984
LOCATION
AL:MONTGOMERY
CO:DENVER
CT:HARTFORD
DE:WILMINGTON
FL:MIAMI
ID:BOISE
ID:IDAHO FALLS
IL:CHICAGO
IN:INDIANAPOLIS
MI:LANSING
MN:MINNEAPOLIS
MS:JACKSON
NH:CONCORD
NJ:TRENTON
NV:LAS VEGAS
NY:ALBANY
NY:NEW YORK CITY
NY:NIAGARA FALLS
NY:YAPHANK
OH:COLUMBUS
OH:PAINESVILLE
OH:TOLEDO
PA:HARRISBURG
RI:PROVIDENCE
SC:BARNWELL
SC:COLUMBIA
SD:PIERRE
TN:KNOXVILLE
TN:NASHVILLE
TX:AUSTIN
TX:EL PASO
VA:LYNCHBURG
WA:SEATTLE
WI:MADISON
DEPTH
(mm)
155.0
41.8
15.6
113.3
106.3
16.3
44.5
17.7
23.1
126.0
58.7
148.1
27.0
31.4
25.0
40.0
43.0
101.7
16.3
79.3
105.6
70.0
82.0
60.0
90.0
87.5
32.5
43.7
8.0
10.0
72.8
135.3
15.0
67.5
ACT.
+ 2s
(nCi/m2)
0.11
0.05
0.06
0.51
0.12
0.06
0.03
0.08
0.03
0.36
0.07
0.04
0.09
0.16
0.02
0.06
0.05
0.06
0.04
0.09
0.15
0.11
0.34
0.69
0.16
0.30
0.01
0.06
0.01
0.02
0.03
0.33
0.02
0.08
0.08
0.02
0.01
0.08
0.06
0.01
0.02
0.01
0.01
0.08
0.03
0.05
0.02
0.02
0.01
0.02
0.02
0.05
0.01
0.04
0.05
0.04
0.06
0.07
0.05
0.06
0.01
0.02
0.00
0.01
0.03
0.07
0.01
0.03
SPECIFIC
GAMMA ACT.
(pCi/1)
ND
ND
ND
ND
ND
ND
214Bi 118 + 80%
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2UBi 64 + 66%
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND NO GAMMA ACTIVITY DETECTABLE
s SIGMA COUNTING ERROR
10
-------
TABLE 7
GROSS BETA CONCENTRATION IN PRECIPITATION
SEPTEMBER 1984
LOCATION
AL: MONTGOMERY
AR: LITTLE ROCK
CT : HARTFORD
DC: WASHINGTON
DE: WILMINGTON
FL: JACKSONVILLE
FL: MIAMI
ID: BOISE
ID: IDAHO FALLS
IL: CHICAGO
IN: INDIANAPOLIS
MI: LANSING
MN MINNEAPOLIS
ND: BISMARCK
NH: CONCORD
NJ: TRENTON
NV:LAS VEGAS
NY: ALBANY
NY: NEW YORK CITY
NY: NIAGARA FALLS
NY:YAPHANK
OH: COLUMBUS
OH:PAINESVILLE
OH: TOLEDO
OR: PORTLAND
PA:HARRISBURG
SC : BARNWELL
TN:KNOXVILLE
TX: AUSTIN
VA:LYNCHBURG
VA: VIRGINIA BEACH
WA: SEATTLE
WI:MADISON
DEPTH
(mm)
18.7
18.9
15.0
15.6
85.0
73.3
132.5
44.8
32.3
7.3
46.3
67.0
115.3
24.1
24.0
69.3
25.0
63.9
33.6
156.1
82.5
46.8
198.1
65.0
40.0
32.5
8.7
10.0
10.0
119.0
25.0
32.5
85.2
ACT.
± 2s
(nCi/m2)
0.02
0.02
0.04
0.00
0.22
0.06
0.09
0.03
0.03
0.01
0.00
0.15
0.10
0.07
0.07
0.30
0.02
0.16
0.10
0.31
0.14
0.03
0.22
0.08
0.04
0.14
0.02
0.02
0.01
0.37
0.09
0.04
0.08
0.01
0.01
0.01
0.01
0.05
0.03
0.06
0.02
0.01
0.00
0.02
0.04
0.05
0.01
0.02
0.05
0.01
0.04
0.02
0.10
0.05
0.02
0.09
0.03
0.02
0.02
0.01
0.00
0.01
0.08
0.02
0.02
0.04
ND NO GAMMA ACTIVITY DETECTABLE
s SIGMA COUNTING
ERROR
SPECIFIC
GAMMA ACT.
(pCi/1)
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
214Bi 114 + 82%
ND
ND
ND
ND
ND
ND
ND
11
-------
TABLE 8
PRECIPITATION
TRITIUM CONCENTRATION
JULY*- SEPTEMBER 1984
LOCATION
AL:MONTGOMERY
AR:LITTLE ROCK
CO:DENVER
CT:HARTFORD
DC:WASHINGTON
DE:WILMINGTON
FL:JACKSONVILLE
FL:MIAMI
GA:ATLANTA
ID .-BOISE
ID:IDAHO FALLS
IL:CHICAGO
IN:INDIANAPOLIS
MI:LANSING
MN:MINNEAPOLIS
MS:JACKSON
ND:BISMARCK
NH:CONCORD
NJ:TRENTON
NV:LAS VEGAS
NY:ALBANY
NY:NEW YORK CITY
NY:NIAGARA FALLS
NY:YAPHANK
OH:COLUMBUS
OH:PAINESVILLE
OH:TOLEDO
OR:PORTLAND
PA:HARRISBURG
RI:PROVIDENCE
SC:BARNWELL
SC:COLUMBIA
SD:PIERRE
TN:KNOXVILLE
JULY
nCi/1 + 2s
.2
.2
0.2 0.2
NS
0.2 0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.
0.2
0.2
0.
0.
0,
0.
0.2
0.3
0,
0.
0,
0,
0,
0.2
0.2
0.2
0.2
0.2
0,
0,
0.2
3 0,
3 0,
0.2
0.2
0.4 0.2
.2
.2
0.
0.
0.2
0.2
0.2
0.2
0.2
0.2
2
2
0.2 0.2
NS
0.2 0.2
0.2 0.2
NS
1.6 0.2
1.3 0.2
0.2 0.2
0.2 0.2
AUGUST
nCl/1
0.2
NS
0.3
0.2
NS
0.2
NS
0.1
NS
0.3
0.2
0.2
0.2
0.2
0.3
0.1
NS
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.4
0.3
0.4
NS
0.2
0.1
4.8
0.8
0.3
0.2
± 2s
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
SEPTEMBER
nCi/1
0.2
0.3
NS
0.3
0.5
0.2
0.3
0.2
NS
0.3
0.4
0.2
0.4
0.3
0.1
NS
0.2
0.2
0.2
0.2
0.2
0.3
0.2
0.2
0.3
0.3
0.2
0.3
0.2
NS
2.1
NS
NS
0.3
± 2s
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.3
0.2
-------
TABLE 8 (CONTINUED)
PRECIPITATION
TRITIUM CONCENTRATION
JULY* SEPTEMBER 1984
LOCATION
TN:NASHVILLE
TX:AUSTIN
TX:EL PASO
VA:LYNCHBURG
VA:VIRGINIA BEACH
WA:SEATTLE
WI:MADISON
JULY
nCi/1 + 2s
0.
0.
0.3 0.2
0.4 0.2
0.2 0.2
0.2 0.2
0.2 0.2
AUGUST
nCi/1 + 2s
0.2
0.2
0.4 0.2
0.1 0.2
NS
0.2 0.2
0.0 0.2
SEPTEMBER
nCi/1 + 2s
NS
0.2 0.2
NS
0.4 0.2
0.4 0.2
0.3 0.2
0.2 0.2
NS NO SAMPLE
s SIGMA COUNTING ERROR
13
-------
Plutonium and Uranium in Airborne Particulates
Environmental radiation levels of plutonium and uranium are
determined by the analyses of quarterly composite samples (air
filters) collected from the 67 continuously operating airborne
particulate samplers.
Analyses of the composited filters consist of ashing, separating
by liquid ion exchange, and coprecipitation of the plutonium or
uranium.
Concentration of the specific isotopes of plutonium*-238, *239,
and uranium-234, -235, and *238 are determined by alpha spectroscopy.
The volume of air passing through the filters normally ranges from
25,000 to 40,000 m3 for each quarterly composite.
Plutonium and uranium in airborne particulates data will be
published when available.
14
-------
Krypton-85
Krypton-85 is a long-lived noble gas with a half life of 10.8
years. It is released into the atmosphere by nuclear reactor
operations, fuel fabrication, fuel reprocessing, and nuclear
detonations. Krypton-85 also occurs naturally in minor quantities
primarily from the neutron capture of stable krypton-84 as well as
spontaneous fission and neutron-induced fission of uranium.
Monitoring of krypton-85 in the atmosphere has been conducted to
identify and establish baseline levels and long-term trends.
Krypton-85 analysis began in January 1973 with sample
collections and analyses being performed for 12 sampling locations.
These locations were selected to provide atmospheric coverage of the
United States with considerations being given to the proximity to
fuel reprocessing plants, nuclear reactors, and wide geographic
coverage.
Dry compressed air samples, collected at each location, are
purchased from commercial air suppliers annually and shipped to the
EERF where the krypton-85 is cryogenically separated and counted in a
liquid scintillation system.
The Kr-85 results will be published when they are available.
15
-------
DATA * EPA
ERAMS
SECTION II. Water Program
The ERAMS water program provides ambient radiation data to
assess the effects of nuclear fallout, the natural radiation
environment, and other nuclear sources on the nation's rivers,
streams and drinking water supplies.
Surface Water
Grab samples are taken quarterly at 58 stations located
downstream from operating or future nuclear facilities.
Surface water monitoring consists of tritium analyses quarterly
and gamma scans annually. Tritium is the primary radioactive
pollutant from nuclear power plants.
Tritium concentrations are determined by liquid scintillation
counting of distilled samples. Gamma scans are performed annually to
determine if there is a buildup of other contaminants.
Tritium concentrations for surface water samples for July *
September 1984 are given in Table 9.
Results from the 1984 annual gamma analyses of surface water are
shown in Table 9.1.
16
-------
TABLE 9
SURFACE WATER
TRITIUM CONCENTRATION
JULY * SEPTEMBER 1984
LOCATION
AL:DECATUR
AL:DOTHAN
AL:SCOTTSBORO
AR:LITTLE ROCK
CA:DIABLO CANYON
CA:EUREKA
CA:SAN ONOFRE
COrGREELEY
CT:EAST HADDAM
FL:CRYSTAL RIVER
FL:FT. PIERCE
FL:HOMESTEAD
IA:CEDAR RAPIDS
ID:BUHL
IL:EAST MOLINE
IL:MORRIS
IL:OREGON
IL:ZION
LA:NEW ORLEANS
MA:PLYMOUTH
MA:ROWE
MD:CONOWINGO
MD:LUSBY
ME:WISCASSET
MI:BRIDGMAN
MIrCHARLEVOIX
MI:MONROE
MI:SOUTH HAVEN
MN:MONTICELLO
MN:RED WING
MS:PORT GIBSON
NC:CHARLOTTE
NC:SOUTHPORT
NE:RULO
NJrBAYSIDE
NJ:OYSTER CREEK
SOURCE
TENNESSEE RIVER
CHATTAHOOCHEE R.
TENNESSEE RIVER
ARKANSAS RIVER
PACIFIC OCEAN
HUMBOLDT BAY
PACIFIC OCEAN
SOUTH PLATTE RIVER
CONNECTICUT RIVER
GULF OF MEXICO
ATLANTIC OCEAN
BISCAYNE BAY
CEDAR RIVER
SNAKE RIVER
MISSISSIPPI RIVER
ILLINOIS RIVER
ROCK RIVER
LAKE MICHIGAN
MISSISSIPPI RIVER
CAPE CODE BAY
DEERFIELD RIVER
SUSQUEHANNA RIVER
CHESAPEAKE BAY
MONTSEWAY BAY
LAKE MICHIGAN
LAKE MICHIGAN
LAKE ERIE
LAKE MICHIGAN
MISSISSIPPI RIVER
MISSISSIPPI RIVER
MISSISSIPPI RIVER
CATAWBA RIVER
ATLANTIC OCEAN
MISSOURI RIVER
DELAWARE RIVER
OYSTER CREEK
DATE
COLLECTED
7/12/84
7/24/84
7/10/84
7/14/84
7/23/84
7/12/84
7/30/84
7/10/84
9/19/84
11 2/84
11 3/84
7/18/84
7/24/84
11 4/84
8/15/84
7/17/84
7/31/84
7/16/84
11 9/84
11 3/84
8/30/84
7/10/84
7/10/84
11 3/84
11 2/84
11 6/84
11 9/84
11 2/84
11 8/84
7/11/84
7/17/84
11 9/84
7/11/84
11 3/84
7/26/84
11 1/84
nCi/1
0.2
0.2
0.2
0.2
0.2
0.1
0.2
0.2
0.4
0.3
0.1
0.3
0.3
0.1
0.2
0.4
0.3
0.3
0.2
0.1
0.4
0.1
0.2
0.1
0.2
0.3
0.2
0.2
0.1
0.2
0.3
0.3
0.1
0.2
0.2
0.2
± 2s
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
17
-------
LOCATION
NV:BOULDER CITY
NY:OSSINING
NY:OSWEGO
NY:POUGHKEEPSIE
OH:TOLEDO
OR:BRADWOOD
PA:DANVILLE
SC:ALLENDALE
SC:BROAD RIVER
SCrHARTSVILLE
TN:DAISY
TN:KINGSTON
TX:EL PASO
TX:MATAGORDA
VA:DOSWELL
WA:NORTHPORT
WA:RICHLAND
WI:TWO CREEKS
WI:VICTORY
WV:WHEELING
TABLE 9 (CONTINUED)
SURFACE WATER
TRITIUM CONCENTRATION
JULY * SEPTEMBER 1984
SOURCE
COLORADO RIVER
HUDSON RIVER
LAKE ONTARIO
HUDSON RIVER
LAKE ERIE
COLUMBIA RIVER
SUSQUEHANNA RIVER
SAVANNAH RIVER
BROAD RIVER
LAKE ROBINSON
TENNESSEE RIVER
CLINCH RIVER
RIO GRANDE
COLORADO RIVER
NORTH ANNA RIVER
COLUMBIA RIVER
COLUMBIA RIVER
LAKE MICHIGAN
MISSISSIPPI RIVER
OHIO RIVER
DATE
COLLECTED
7/10/84
7/17/84
7/15/84
11 5/84
11 3/84
7/ 5/84
7/11/84
7/30/84
7/23/84
7/ 9/84
8/21/84
7/10/84
7/19/84
8/16/84
7/ 5/84
7/10/84
7/10/84
7/23/84
7/ 9/84
7/18/84
nCi/1
0.3
0.2
0.3
0.3
0.2
0.2
0.2
0.3
0.6
0.2
0.4
1.2
0.2
0.2
1.7
0.2
0.2
0.2
0.2
0.4
± 2s
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
s SIGMA COUNTING ERROR
18
-------
TABLE 9.1
LOCATION
ALrDOTHAN
AL:SCOTTSBORO
CA:DIABLO CANYON
CA:EUREKA
CA:SAN ONOFRE
CO:GREELEY
CT:EAST HADDAM
CTrWATERFORD
FL:CRYSTAL RIVER
FL;FT. PIERCE
FL:HOMESTEAD
IA:CEDAR RAPIDS
ID:BUHL
IL:EAST MOLINE
IL:MORRIS
IL:OREGON
IL:ZION
LA:NEW ORLEANS
MA:PLYMOUTH
MA:ROWE
MD:CONOWINGO
MD:LUSBY
ME:WISCASSET
MI:BRIDGMAN
MIrCHARLEVOIX
MI:MONROE
MI:SOUTH HAVEN
MN:MONTICELLO
MN:RED WING
MS:PORT GIBSON
NC:CHARLOTTE
NC:SOUTHPORT
NE:RULO
NJ:OYSTER CREEK
NV:BOULDER CITY
NY:OSSINING
NY:OSWEGO
SURFACE WATER
ANNUAL GAMMA ANALYSIS
1984
DATE
SOURCE COLLECTED
CHATTAHOOCHEE R. 4/20/84
TENNESSEE RIVER 4/ 3/84
PACIFIC OCEAN 4/27/84
HUMBOLDT BAY 4/19/84
PACIFIC OCEAN 4/26/84
SOUTH PLATTE RIVER 4/16/84
CONNECTICUT RIVER 5/ 2/84
CONNECTICUT RIVER 5/ 3/84
GULF OF MEXICO 4/ 9/84
ATLANTIC OCEAN 4/10/84
BISCAYNE BAY 4/20/84
CEDAR RIVER 4/17/84
SNAKE RIVER 4/20/84
MISSISSIPPI RIVER 5/29/84
ILLINOIS RIVER 4/ 7/84
ROCK RIVER 4/15/84
LAKE MICHIGAN 4/ 3/84
MISSISSIPPI RIVER 4/16/84
CAPE CODE BAY 4/ 3/84
DEERFIELD RIVER 4/24/84
SUSQUEHANNA RIVER 4/11/84
CHESAPEAKE BAY 4/10/84
MONTSEWAY BAY 4/10/84
LAKE MICHIGAN 4/ 3/84
LAKE MICHIGAN 4/14/84
LAKE ERIE 4/16/84
LAKE MICHIGAN 4/ 2/84
MISSISSIPPI RIVER 4/ 3/84
MISSISSIPPI RIVER 4/10/84
MISSISSIPPI RIVER 5/17/84
CATAWBA RIVER 4/ 9/84
ATLANTIC OCEAN 4/ 3/84
MISSOURI RIVER 4/11/84
OYSTER CREEK 7/ 1/84
COLORADO RIVER 4/ 9/84
HUDSON RIVER 4/12/84
LAKE ONTARIO 4/15/84
GAMMA
pCi/1 + 2s
ND
ND
ND
282 + 30%
254 + 69%
ND
ND
40K 233 + 36%
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
40K 120 + 68%
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
19
-------
LOCATION
NYrPOUGHKEEPSIE
OH:TOLEDO
OR:BRADWOOD
PA:DANVILLE
SC:ALLENDALE
SC:BROAD RIVER
SC:HARTSVILLE
TN:DAISY
TN:KINGSTON
TX:EL PASO
TX:MATAGORDA
VAiDOSWELL
WA:NORTHPORT
WA:RICHLAND
WI:TWO CREEKS
WI:VICTORY
W: WHEEL ING
TABLE 9.1 (CONTINUED)
SURFACE WATER
ANNUAL GAMMA ANALYSIS
1984
DATE
SOURCE COLLECTED
HUDSON RIVER 4/ 4/84
LAKE ERIE 4/ 3/84
COLUMBIA RIVER 4/12/84
SUSQUEHANNA RIVER 4/11/84
SAVANNAH RIVER 3/30/84
BROAD RIVER 4/23/84
LAKE ROBINSON 4/ 9/84
TENNESSEE RIVER 5/30/84
CLINCH RIVER 4/ 3/84
RIO GRANDE 4/23/84
COLORADO RIVER 3/28/84
NORTH ANNA RIVER 4/ 5/84
COLUMBIA RIVER 5/ 8/84
COLUMBIA RIVER 4/13/84
LAKE MICHIGAN 4/13/84
MISSISSIPPI RIVER 4/ 9/84
OHIO RIVER 4/11/84
GAMMA
pCi/1 + 2s
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND NO GAMMA ACTIVITY DETECTABLE
s SIGMA COUNTING ERROR
20
-------
Drinking Water
The drinking water program provides ambient radiation monitoring
relevant to the effects of the nuclear power industry, natural
environmental levels, and other pertinent sources. These data serve
to assess trends and anomalies in concentrations, and to compare with
standards set forth in the EPA "National Interim Primary Drinking
Water Regulations." These regulations provide for approval of
supplies when the combined radium»226 and radium^228 levels do not
exceed 5 pCi/1, when the gross alpha (excluding radon and uranium)
levels do not exceed 15 pCi/1, when tritium levels do not exceed
20,000 pCi/1, when the strontium*90 levels do not exceed 8 pCi/1, and
when the gross beta levels do not exceed 50 pCi/1.
Grab samples are taken at 78 sites which are either major
population centers or selected nuclear facility environs.
The analyses include (a) tritium on a quarterly basis; (b)
gross alpha, gross beta, strontium*90, and gamma on annual
composites; (c) radium*226 if the gross alpha exceeds 2 pCi/1 and
radium+228 if the radium*226 falls between 3 and 5 pCi/1; (d)
specific iodine*131 on one quarterly sample per year for each
station; and (e) an annual composite for plutonium+238 and +239 and
uranium*234, +235, and 4238 for stations that demonstrate gross alpha
levels greater than 2 pCi/1.
Tritium analyses are performed by scintillation counting of the
distilled samples, gross beta, and gross alpha by evaporating an
aliquot on stainless steel planchets for counting, and radium*226 by
the standard emanation technique. Strontium*90 is determined by beta
counting a strontium carbonate precipitate isolated by ion exchange.
The results of tritium in drinking water analyses for July *
September 1984 are shown in Table 10.
The annual alpha, beta, gamma, radium, and strontium analyses
for 1983 annual drinking water samples are shown in Table 11.
All samples were taken as either a single grab sample or
composite samples taken over 12 to 14 days.
21
-------
TABLE 10
DRINKING WATER
TRITIUM CONCENTRATION
JULY * SEPTEMBER 1984
LOCATION
AK:FAIRBANKS
AL:DOTHAN
AL:MONTGOMERY
AL:MUSCLE SHOALS
AL:SCOTTSBORO
AR:LITTLE ROCK
CA:BERKELEY
CA:LOS ANGELES
CO:DENVER
COrPLATTEVILLE
CT:HARTFORD
DE:DOVER
FL:MIAMI
FL:TAMPA
GA: SAVANNAH
HI .-HONOLULU
IA:CEDAR RAPIDS
ID:IDAHO FALLS
IL:MORRIS
IL:W. CHICAGO
KS:TOPEKA
LA:NEW ORLEANS
MA:LAWRENCE
MD:BALTIMORE
MD:CONOWINGO
ME:AUGUSTA
MI:DETROIT
MI:GRAND RAPIDS
MN:MINNEAPOLIS
MNrRED WING
MS:JACKSON
MS:PORT GIBSON
MT:HELENA
NC:CHARLOTTE
NC:WILMINGTON
ND:BISMARCK
NE:LINCOLN
NH:CONCORD
DATE
COLLECTED
7/12/84
7/24/84
7/13/84
7/11/84
7/10/84
7/ 3/84
7/10/84
11 5/84
8/20/84
8/20/84
11 5/84
11 3/84
11 3/84
7/16/84
11 2/84
7/24/84
7/24/84
7/13/84
11 3/84
11 2/84
11 2/84
7/23/84
8/ 1/84
11 3/84
7/10/84
11 3/84
11 9/84
7/17/84
7/16/84
7/11/84
11 5/84
7/10/84
7/17/84
7/ 9/84
7/12/84
7/ 3/84
7/10/84
7/ 2/84
nCi/1
0.1
0.2
0.1
0.1
0.1
0.3
0.3
0.2
0.4
0.2
0.3
0.1
0.2
0.2
2.3
0.2
0.2
0.5
0.3
0.1
0.3
0.2
0.2
0.2
0.2
0.2
0.3
0.2
0.2
0.2
0.1
0.1
0.3
0.3
0.3
0.3
0.2
0.1
± 2s
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
22
-------
TABLE 10 (CONTINUED)
DRINKING WATER
TRITIUM CONCENTRATION
JULY * SEPTEMBER 1984
LOCATION
NM:SANTA FE
NVrLAS VEGAS
NY:ALBANY
NY:NEW YORK CITY
NY:NIAGARA FALLS
NY:SYRACUSE
OH CINCINNATI
OH:COLUMBUS
OH:EAST LIVERPOOL
OH:PAINESVILLE
OH .-TOLEDO
OK:OKLAHOMA CITY
OR:PORTLAND
PA:COLUMBIA
PA:HARRISBURG
PA:PITTSBURGH
PCrANCON
RI:PROVIDENCE
SC:BARNWELL
SC:COLUMBIA
SC:HARTSVILLE
SC:JENKINSVILLE
SC:SENECA
TN:CHATTANOOGA
TNrKNOXVILLE
TX:AUSTIN
VA:DOSWELL
VA:LYNCHBURG
VA:VIRGINIA BEACH
VI:ST. THOMAS
WA:RICHLAND
WA:SEATTLE
WI:GENOA CITY
WI:MADISON
DATE
COLLECTED
11 2/84
11 3/84
11 3/84
7/11/84
11 2/84
7/17/84
7/ 2/84
7/11/84
7/11/84
7/ 6/84
11 3/84
11 9/84
11 2/84
11 5/84
7/11/84
11 3/84
7/24/84
11 2/84
7/23/84
11 3/84
7/23/84
7/23/84
7/11/84
11 3/84
11 2/84
11 5/84
8/ 1/84
11 3/84
7/10/84
7/18/84
7/10/84
7/ 3/84
7/ 9/84
7/11/84
nCi/1
0.2
0.3
0.3
0.4
0.3
0.2
0.1
0.2
0.2
0.1
0.4
0.1
0.2
0.2
0.2
0.2
0.2
0.1
0.3
0.6
0.2
0.3
0.4
0.4
0.2
0.1
0.2
0.3
0.1
0.1
0.2
0.1
0.2
0.4
± 2s
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
SIGMA COUNTING ERROR
23
-------
TABLE 11
LOCATION
AK:FAIRBANKS
AL.-DOTHAN
AL:MONTGOMERY
AL:MUSCLE SHOALS
AL:SCOTTSBORO
CA:BERKELEY
CA:LOS ANGELES
CO:DENVER
COrPLATTEVILLE
CT:HARTFORD
DC:WASHINGTON
DE:DOVER
DRINKING WATER
ALPHA, BETA AND GAMMA CONCENTRATION
1983
ANNUAL ANALYSES
TOTAL GROSS BETA GROSS ALPHA SPECIFIC
SOLIDS DATE CTD. DATE CTD. 90Sr 226Ra GAMMA
mg/1 pCi/1 + 2s pCi/1 + 2s pCl/1 + 2s pCi/1 + 2s ACTIVITY
205.0
131.2
98.2
124.6
119.6
102.4
374.0
101.8
907.1
36.8
202.3
2.2
1.1
1.0
1.8
1.3
1.1
7.0
2.1
7.6
0.7
2.1
1.3
0.9
0.8
0.9
1.0
0.9
2.4
0.8
4.7
0.7
1.4
0.1 0.9
1/30/84
0.1 0.5
1/30/84
0.3 0.4
1/30/84
0.4 0.5
1/30/84
0.2 0.4
1/30/84
0.3 0.5
1/30/84
15.3 3.3
1/30/84
2.0 0.7
1/30/84
12.0 5.2
1/30/84
0.0 0.3
1/30/84
0.4 0.9
2/29/84
0.0 0.3
1/30/84
0.1 0.3
1/30/84
0.3 0.2
1/30/84
0.3 0.2
1/30/84
0.3 0.3
1/30/84
0.2 0.1
1/30/84
0.1 0.1
1/30/84
0.2 0.2
1/30/84
0.1 0.1
1/30/84
0.3 0.2
1/30/84
0.1 0.1
2/29/84
219.3 2.9 1.8 0.0 0.0 0.0 0.1
1/30/84 1/30/84
NA
NA
NA
NA
NA
NA
0.1 0.1
0.1 0.1
0.2 0.1
NA
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
24
-------
TABLE 11 (CONTINUED)
LOCATION
FL:MIAMI
FL:TAMPA
GA:SAVANNAH
HI:HONOLULU
IA:CEDAR RAPIDS
ID:BOISE
ID:IDAHO FALLS
IL:MORRIS
IL:W. CHICAGO
KS:TOPEKA
LA:NEW ORLEANS
MA:LAWRENCE
DRINKING WATER
ALPHA, BETA AND GAMMA CONCENTRATION
1983
ANNUAL ANALYSES
TOTAL GROSS BETA GROSS ALPHA SPECIFIC
SOLIDS DATE CTD. DATE CTD. 90Sr 226Ra GAMMA
mg/1 pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s ACTIVITY
200.8 1.9 1.0
0.9 0.9
1/30/84
183.5 2.0 1.0
69.4 1.0 0.8
349.0 17.1 3.7
358.0 20.8 4.5
341.0 6.0 3.6
173.3 2.9 1.4
108.6 2.2 0.9
26.5 4.5
21 7/84
18.2 3.8
21 7/84
0.1 0.2
1/30/84
187.3 2.2 1.1 0.4 0.8 0.2 0.5
21 7/84 21 7/84
75.4 2.3 0.9 0.4 0.3 0.2 0.2
21 7/84 21 7/84
191.0 1.3 1.0 0.5 0.7 0.2 0.1
21 7/84 21 7/84
1.2 0.8 *0.3 0.1
21 7/84 21 7/84
0.3 0.3 -0.1 0.1
21 7/84 21 7/84
290.0 22.4 3.3 41.7 4.7 +0.1 0.3
21 7/84 2/17/84
0.1 0.0
21 7/84
0.0 0.1
21 7/84
2.0 1.6 0.3 0.1
21 7/84 21 7/84
1.0 0.9 0.0 0.1
21 7/84 21 7/84
0.4 0.5 0.4 0.1
21 7/84 21 7/84
NA
NA
NA
NA
NA
NA
0.0 0.1
6.3 0.1
4.2 0.1
0.1 0.1
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
25
-------
TABLE 11 (CONTINUED)
LOCATION
MA:ROWE
MD:BALTIMORE
MD:CONOWINGO
ME:AUGUSTA
MI:DETROIT
MI:GRAND RAPIDS
MN:MINNEAPOLIS
MN:RED WING
MS:JACKSON
MS:PORT GIBSON
MT:HELENA
NC:CHARLOTTE
DRINKING WATER
ALPHA, BETA AND GAMMA CONCENTRATION
1983
ANNUAL ANALYSES
TOTAL GROSS BETA GROSS ALPHA
SOLIDS DATE CTD. DATE CTD.
90
Sr
SPECIFIC
GAMMA
mg/1 pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s ACTIVITY
50.2 1.6 0.8 0.2 0.3 -0.4 0.2
21 7/84 21 7/84
111.2 2.6 1.0
212.3 3.7 1.7
0.1 0.4 »0.2 0.1
21 7/84 21 7/84
1.2 0.9 0.0 0.1
21 7/84 21 7/84
59.2 1.5 0.8 0.3 0.3 0.0 0.2
21 7/84 21 7/84
120.0 2.1 0.9 0.4 0.5 0.7 0.2
21 7/84 21 7/84
157.3 2.1 1.2 0.7 0.6 0.5 0.3
21 7/84 21 7/84
109.2 2.8 0.9
203.5 4.7 1.7
0.3 0.4 -0.7 1.3
21 7/84 21 7/84
5.8 1.8 *0.1 0.2
2/ 9/84 21 9/84
88.6 1.9 0.9 0.2 0.3 0.2 0.2
21 9/84 21 9/84
341.0 2.8 1.5 5.4 2.1 -0.2 0.3
21 9/84 21 9/84
154.4 3.6 1.1 1.6 0.8 0.1 0.2
21 9/84 21 9/84
54.6 1.3 1.0 0.1 0.2 0.5 0.2
21 9/84 21 9/84
NA
NA
NA
NA
NA
NA
NA
2.0 0.1
NA
0.1 0.1
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
26
-------
TABLE 11 (CONTINUED)
LOCATION
NC:WILMINGTON
ND:BISMARCK
NE:LINCOLN
NH:CONCORD
NJ:TRENTON
NJ:WARETOWN
NM:SANTA FE
NVrLAS VEGAS
NY:ALBANY
NY:NEW YORK CITY
NY:NIAGARA FALLS
NY:SYRACUSE
DRINKING WATER
ALPHA, BETA AND GAMMA CONCENTRATION
1983
ANNUAL ANALYSES
TOTAL GROSS BETA GROSS ALPHA SPECIFIC
SOLIDS DATE CTD. DATE CTD. 90Sr 226Ra GAMMA
mg/1 pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s pCl/1 + 2s ACTIVITY
151.5 2.7 1.1. 1.2 0.9 0.0 0.5
2/ 9/84 21 9/84
337.0 5.6 2.1
364.0 8.5 2.4
70.0 1.2 0.7
123.0 1.9 0.9
48.0 2.3 0.8
148.4 1.6 0.8
697.0 8.5 3.8
92.8 1.9 1.0
43.2 1.1 0.7
5.1 2.0 *0.3 0.9
21 9/84 21 9/84
6.3 2.3
21 9/84
11.3 4.2
21 9/84
0.1 0.2
21 9/84
3.2 0.3 *0.2 0.1
21 9/84 21 9/84
0.3 0.6 0.3 0.2
21 9/84 21 9/84
0.9 0.4 0.2 0.1
21 9/84 21 9/84
0.9 0.7 *0.7 0.7
21 9/84 21 9/84
0.3 0.4
21 9/84
0.2 0.3 0.3 0.5
21 9/84 21 9/84
0.3 0.4 -0.2 0.5
21 9/84 21 9/84
175.0 2.7 1.2 0.4 0.6 0.5 0.4
21 9/84 21 9/84
136.4 2.5 0.9 0.5 0.6 0.4 0.5
21 9/84 21 9/84
NA
0.1 0.1
0.3 0.1
NA
NA
NA
NA
0.1 0.1
NA
NA
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND-
ND
ND
27
-------
TABLE 11 (CONTINUED)
LOCATION
OH:CINCINNATI
OH:COLUMBUS
OH:EAST LIVERPOOL
OH:PAINESVILLE
OH:TOLEDO
OK:OKLAHOMA CITY
OR:PORTLAND
PA:COLUMBIA
PA:HARRISBURG
PA .-PITTSBURGH
PC:ANCON
RI:PROVIDENCE
DRINKING WATER
ALPHA, BETA AND GAMMA CONCENTRATION
1983
ANNUAL ANALYSES
TOTAL GROSS BETA GROSS ALPHA
SOLIDS DATE CTD. DATE CTD.
90,
Sr
226
Ra
SPECIFIC
GAMMA
mg/1 pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s ACTIVITY
216.3 1.8 1.3 0.9 0.9 0.0 0.4
21 9/84 21 9/84
284.5 6.2 2.1
252.7 3.0 1.4
200.3 2.9 1.2
120.2 1.7 0.9
86.4 2.7 1.0
0.8 0.9 0.0 0.5
21 9/84 21 9/84
-0.2 0.8 0.1 0.6
2/13/84 2/13/84
0.1 0.4
2/13/84
221.3 2.7 1.5
0.2 0.7
2/13/84
0.2 0.3
2/13/84
0.1 0.4 0.3 0.4
2/13/84 2/13/84
22.6 0.9 0.8 0.0 0.2 +0.3 0.2
2/13/84 2/13/84
200.8 2.0 1.3 0.2 0.6 0.4 0.2
2/13/84 2/13/84
38.2 0.7 0.8 0.1 0.3 0.1 0.1
2/13/84 2/13/84
0.3 0.2
2/13/84
100.8 1.0 0.8 0.2 0.4 *0.1 0.1
2/13/84 2/13/84
68.6 1.3 0.9 0.2 0.3 »0.4 1.2
2/13/84 2/13/84
NA
8.7 2.3 0.2 0.2 0.1 0.1
21 9/84 21 9/84
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
28
-------
TABLE 11 (CONTINUED)
SC:COLUMBIA
SC:HARTSVILLE
SC:JENKINSVILLE
SC:SENECA
TN:CHATTANOOGA
TN:KNOXVILLE
TX:AUSTIN
VA:DOSWELL
VA:LYNCHBURG
VA:VIRGINIA BEACH
VI:ST. THOMAS
DRINKING WATER
ALPHA, BETA AND GAMMA CONCENTRATION
1983
ANNUAL ANALYSES
LOCATION
SC:BARNWELL
TOTAL GROSS BETA GROSS ALPHA
SOLIDS DATE CTD. DATE CTD. 90Sr 226Ra
mg/1 pCl/1 + 2s pCi/1 + 2s pCl/1 + 2s pCi/1 + 2s
25.6 1.1 0.7 0.3 0.3 0.1 0.1 NA
2/13/84 2/13/84
SPECIFIC
GAMMA
ACTIVITY
ND
65.8 1.9 0.9
36.2 0.6 0.6
0.2 0.3 0.2 0.2
2/13/84 2/13/84
0.3 0.3 *0.3 0.1
2/13/84 2/13/84
186.2 4.4 0.5 44.4 3.5 -0.2 0.4
2/13/84 2/13/84
32.0 0.4 0.8
114.6 3.0 1.0
0.1 0.2
2/13/84
0.1 0.2
2/13/84
0.2 0.4 0.1 0.1
2/29/84 2/29/84
140.0 1.3 0.6 2.1 0.8 *0.1 0.5
2/13/84 2/13/84
227.0 3.4 1.6 0.5 1.1 *0.7 0.8
2/14/84 2/14/84
174.6 5.6 1.3 0.4 0.6 »0.5 0.6
2/14/84 2/14/84
71.2 1.6 0.9 0.2 0.3 0.3 0.1
2/14/84 2/14/84
113.2 2.5 0.9 0.1 0.4 0.5 0.2
2/14/84 2/14/84
56.4 1.6 0.8 0.2 0.3 *0.6 1.1
2/29/84 2/29/84
NA
NA
1.5 0.1
NA
NA
0.0 0.1
NA
NA
NA
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
29
-------
LOCATION
WA:RICHLAND
WA:SEATTLE
WI:GENOA CITY
WI:MADISON
TABLE 11 (CONTINUED)
DRINKING WATER
ALPHA, BETA AND GAMMA CONCENTRATION
1983
ANNUAL ANALYSES
TOTAL GROSS BETA GROSS ALPHA
SOLIDS DATE CTD. DATE CTD. 90Sr
226
Ra
mg/1 pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s pCi/1 + 2s
80.2
ND NO ACTIVITY DETECTABLE
NA NO ANALYSIS
S SIGMA COUNTING ERROR
1.5 0.8
40.0 0.6 0.8
186.7 1.6 1.2
215.7 1.0 1.0
0.4 0.5
2/14/84
0.1 0.2
2/14/84
0.8 0.8
2/14/84
1.6 1.0
2/14/84
0.2 0.1
2/14/84
0.0 0.1
2/14/84
0.0 0.3
2/14/84
,0.4 0.2
2/14/84
NA
NA
NA
SPECIFIC
GAMMA
ACTIVITY
ND
ND
ND
0.4 0.1
ND
30
-------
SECTION III. External Gamma Ambient Monitoring Program
The external gamma monitoring program, which began in October
1978, provides a continuous measurement of ambient gamma exposure
rates, including cosmic, at selected sites throughout the continental
United States. Data from this program are used to evaluate
fluctuations in natural background due to variations in environmental
conditions and to provide a means of monitoring any significant
increases in ambient gamma levels due to weapons fallout, reactor
operations, etc. The program consists of approximately 22 sites
representing a wide geographic coverage throughout the country.*
Although exposure measurements at these few sites are not totally
representative of nationwide exposures, they will be indicative of
national trends.
The monitoring program utilizes CaF2:Mn thermoluminescent
dosimeters(TLD's). These dosimeters are commercially available
glass*bulb type dosimeters with energy compensating shields. A group
of three TLD's is located at each station or site. Dosimeters are
annealed by the station operator prior to positioning in the field.
The dosimeters are returned to EERF for readout on an approximate
one*month cycle.** Several dosimeters are annealed by the station
operator as controls and returned with the exposed field dosimeters
to correct for any exposures accumulated during shipment.
Results from the period July » September 1984 are shown in Table
12.
* Some of these sites may not return dosimeters each period and
consequently the number of sites listed may vary slightly.
** Starting October, 1984, this program will change to a
quarterly cycle.
31
-------
TABLE 12
ENVIRONMENTAL GAMMA AMBIENT MONITORING PROGRAM
INTEGRATED EXPOSURE
LOCATION DATE RANGE EXPOSURE RATE
AL:MONTGOMERY
AL:MONTGOMERY
AL:MONTGOMERY
CA:BERKELEY
CA:BERKELEY
CA:BERKELEY
CO:DENVER
CO:DENVER
CO:DENVER
FL:ORLANDO
FL:ORLANDO
ID:BOISE
ID:BOISE
IL:CHICAGO
IL:CHICAGO
ND:BISMARCK
ND:BISMARCK
ND:BISMARCK
NJ:TRENTON
NJ:TRENTON
NM:SANTA FE
NM:SANTA FE
NM:SANTA FE
NV:LAS VEGAS
NV:LAS VEGAS
NV:LAS VEGAS
NY:NEW YORK
NY:NEW YORK
OH:COLUMBUS
OH: COLUMBUS
OH:COLUMBUS
OK:OKLAHOMA CITY
OK:OKLAHOMA CITY
OR:PORTLAND
OR:PORTLAND
PA:HARRISBURG
PA:HARRISBURG
PA:HARRISBURG
RI:PROVIDENCE
RI:PROVIDENCE
SC:BARNWELL
70284* 80284
80284* 90484
90484*100184
70584* 80184
80184* 90584
90584-100384
62984* 80784
80784* 90584
90584*100284
70384* 90484
90484*100184
70984* 80984
80984* 90684
70684* 81484
81484* 90784
70584* 80184
80184- 90784
90784*100384
100383* 80184
80184* 90784
70984- 80284
80284* 91084
91084*100484
70284* 73184
73184* 90484
90484*100384
71684- 81584
81584* 91284
70384* 80284
80284* 90484
90484*100184
71384- 82284
82284* 91084
70984* 80384
80384*100284
70284- 73184
73184* 90584
90584-100184
70584* 82084
82084* 90684
71984* 80984
MR
5.7
6.1
5.9
4.5
5.7
4.7
13.3
9.8
10.4
10.3
5.2
9.1
8.0
7.9
5.0
8.1
9.1
6.7
81.4
10.6
9.0
13.8
9.0
5.7
6.0
5.3
6.3
6.3
6.2
6.3
5.7
8.6
3.9
5.4
13.5
4.9
6.6
4.9
12.9
4.8
4.3
MICRO R/HR + 2 s *
7.6
7.7
9.1
6.9
6.8
7.0
14.2
14.1
16.1
6.8
8.0
12.2
11.9
8.4
8.6
12.5
10.2
10.8
11.2
11.9
15.6
14.7
15.6
8.3
7.1
7.6
8.7
9.4
8.7
8.0
8.8
8.9
8.5
9.1
9.4
7.0
7.6
7.9
11.7
11.8
8.6
6.2
7.1
6.0
5.3
4.4
6.3
4.4
6.5
6.9
4.0
5.6
25.2
7.9
10.1
5.4
6.5
6.8
7.7
2.5
12.0
9.2
7.4
3.8
9.8
6.5
6.6
7.8
7.4
3.5
9.0
4.0
4.0
10.0
8.0
7.7
8.4
7.6
5.5
7.5
6.9
5.6
32
-------
TABLE 12 (CONTINUED)
ENVIRONMENTAL GAMMA AMBIENT MONITORING PROGRAM
INTEGRATED EXPOSURE
LOCATION DATE RANGE EXPOSURE RATE
SC:BARNWELL
SC:COLUMBIA
SC:COLUMBIA
SC:COLUMBIA
TN:KNOXVILLE
TNrKNOXVILLE
TN:KNOXVILLE
VA:RICHMOND
VA:RICHMOND
VA:RICHMOND
VT:MONTPELIER
VT:MONTPELIER
VT:MONTPELIER
MR
80984* 91384
62984* 73084
73084* 90484
90484-100284
70284* 80284
80284* 90784
90784-100484
70584* 80184
80184- 90584
90584-100484
53184* 73184
73184* 81084
81084* 91784
8.4
7.3
7.3
6.8
7.6
9.0
7.1
5.9
7.9
6.5
12.0
2.1
8.8
MICRO R/HR + 2 s *
10.0
9.9
8.
10.
10.
10.
10.
9.2
9.4
9.4
8.2
8.9
9.7
.4
.1
.2
.4
.9
3.7
5.5
4.1
16.2
5.7
4.9
4.4
4.8
7.6
8.5
5.8
5.9
6.7
* s = SIGMA ERROR (IN PERCENT)
33
-------
SECTION IV. Milk Program
Pasteurized Milk
This is a cooperative program of the EPA, ORP and the Dairy and
Lipid Products Branch, Milk Sanitation Section, Food and Drug
Administration. Milk is a reliable indicator of the general
population's intake of radionuclides since it is consumed by a large
segment of the population and contains several of the biologically
important contaminants resulting from environmental releases from
nuclear activities. A primary function of this program is to obtain
reliable monitoring data relative to current radionuclide
concentrations and determine any long*term trends.
Monthly samples are collected at 65 sampling sites with one or
more located in each state, Puerto Rico, and the Panama Canal. These
are composite samples representing more than 80 percent of the milk
consumed in a given population center^.
These samples are analyzed for iodine*131, barium*140,
cesium-i-137, and potassium. All 65 samples are analyzed annually in
July for strontium*-89, and strontium*-90. Also, for the first month
of the three quarters beginning January, April and October, 10
regional composite samples of milk made up from the states within
each of EPA's 10 regions are analyzed for strontium*89 and
strontiumA90.
Iodine*131, barium*140, cesium*137 and potassium are determined
by gamma spectral analysis. Strontium*89 and strontium*90 are
determined by beta counting a total strontium precipitate which has
been chemically separated by ion*exchange.
The values from the pasteurized milk samples for July *
September 1984 are shown in Tables 13 * 15.
Strontium values from regional composite samples collected July
* September 1984 are shown in Table 16.
34
-------
TABLE 13
CONCENTRATIONS OF RADIONUCLIDES IN PASTEURIZED MILK
JULY 1984
LOCATION
AL:MONTGOMERY
AR:LITTLE ROCK
AZ:PHOENIX
CA:LOS ANGELES
CA:SACRAMENTO
CA:SAN FRANCISCO
CO .'DENVER
CO:DENVER
CT:HARTFORD
DC:WASHINGTON
FL:TAMPA
GA:ATLANTA
HI:HONOLULU
HI:HONOLULU
IA:DES MOINES
ID:IDAHO FALLS
IL:CHICAGO
IN:INDIANAPOLIS
KS:WICHITA
KY:LOUISVILLE
MA:BOSTON
MD:BALTIMORE
ME:PORTLAND
MI:DETROIT
MI:GRAND RAPIDS
MN:MINNEAPOLIS
MN:ST PAUL
MO:KANSAS CITY
MO:ST LOUIS
MS:JACKSON
MT:HELENA
NC:CHARLOTTE
ND:MINOT
NE:OMAHA
NH:MANCHESTER
NJ:TRENTON
NV:LAS VEGAS
NY:BUFFALO
DATE
COLLECTED
11 6/84
11 2/84
11 5/84
7/12/84
11 2/84
11 3/84
11 2/84
7/30/84
7/16/84
7/ 6/84
7/ 3/84
7/ 2/84
7/30/84
7/ 1/84
7/ 9/84
7/19/84
7/10/84
7/ 2/84
7/ 2/84
7/ 3/84
7/10/84
7/ 6/84
7/ 3/84
7/ 5/84
11 2/84
7/ 9/84
11 3/84
7/ 5/84
7/13/84
11 9/84
7/10/84
7/ 2/84
7/27/84
7/ 6/84
7/ 2/84
7/ 5/84
7/23/84
7/10/84
K
g/l+2s
1.
1,
1,
1.
1.
1,
1,
1.
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1
1,
1
1
1
1
1
1
1
1
1
1
1
1
1
.50
.43
.53
.69
.63
.62
.66
.40
.58
.55
.52
.55
.57
.63
.50
.78
.42
.52
.48
.55
.50
.62
.54
.54
.49
.57
.79
.60
.58
.42
.62
.71
.61
.35
.63
.72
.53
.64
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
0
0
0
0
0
0
0
0
0
0
0
0
.
*
m
.
9
0
09
12
13
13
09
13
13
12
13
13
13
13
09
13
09
25
12
13
12
13
13
13
13
09
12
13
25
13
13
12
13
24
13
12
13
13
13
13
u/(
Cs
pCi/l+2s
3
9
9
4
-2
1
2
1
3
*1
11
4
41
-1
2
8
*3
1
2
5
5
2
9
0
7
*1
4
*2
*2
6
*2
8
2
4
0
*4
1
*4
5
7
7
7
5
7
7
7
7
7
7
7
5
7
5
18
7
7
7
7
7
7
7
5
7
7
18
7
7
7
7
18
7
7
7
7
7
7
i«*U
Ba
pCi/l+2s
*!
2
-7
»1
*4
-6
-2
3
0
1
*4
*5
»4
0
0
*4
A3
1
0
*2
4
*1
*3
1
-5
-2
5
-4
0
0
»1
2
+7
+4
-1
*4
»2
2
6
9
9
9
6
9
9
9
9
9
9
9
6
9
6
18
9
9
9
9
9
9
9
6
9
9
19
9
9
9
9
19
9
9
9
9
9
9
J.J1
I
pCi/l+2s
2
*4
0
-2
2
I
6
1
*4
1
1
*1
1
2
0
*2
0
2
1
+3
5
2
1
0
5
0
1
2
*2
+6
0
»1
2
-2
0
6
6
2
5
7
7
7
5
7
7
7
7
7
7
7
5
7
5
14
7
7
7
7
7
7
7
5
7
7
14
7
7
7
7
14
7
7
7
7
7
7
35
-------
TABLE 13 (CONTINUED)
CONCENTRATIONS OF RADIONUCLIDES IN PASTEURIZED MILK
JULY 1984
LOCATION
NY:NEW YORK CITY
NY:SYRACUSE
OH: CINCINNATI
OH:CLEVELAND
OK:OKLAHOMA CITY
OR:PORTLAND
PA:PHILADELPHIA
PA:PITTSBURGH
PC:CRISTOBAL
PR:SAN JUAN
SC:CHARLESTON
SD:RAPID CITY
TN:CHATTANOOGA
TN:MEMPHIS
TX:AUSTIN
UT:SALT LAKE CITY
VA:NORFOLK
VT:BURLINGTON
WA:SEATTLE
WA:SPOKANE
WV:CHARLESTON
WY:LARAMIE
DATE
COLLECTED
11 2/84
11 2/84
7/ 9/84
11 9/84
7/23/84
7/ 2/84
7/ 2/84
7/ 3/84
7/26/84
7/16/84
7/12/84
7/ 5/84
7/ 2/84
7/25/84
7/ 2/84
7/ 2/84
7/19/84
7/ 5/84
7/ 2/84
7/ 2/84
7/18/84
7/ 3/84
K
8/1+2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
.54
.48
.45
.48
.52
.58
.63
.51
.57
.53
.82
.57
.52
.44
.48
.47
.50
.61
.60
.58
.51
.55
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
s
.13
.12
.12
.12
.09
.09
.13
.13
.13
.09
.25
.13
.13
.12
.12
.12
.08
.09
.13
.13
.13
.09
j. j /
Cs
pCi/l+2s
*1
7
2
5
-1
0
5
6
13
5
6
2
1
*3
1
0
5
*3
2
3
0
*1
7
7
7
7
5
5
7
7
7
5
18
7
7
7
7
7
5
5
7
7
7
5
x'+u
Ba
pCi/l+2s
6
4
1
2
1
1
-5
A4
-6
-4
*7
"1
-1
+2
*5
3
*3
-7
2
*4
*(>
*1
9
9
9
9
6
6
9
9
9
6
18
9
9
9
9
9
6
6
9
9
9
6
131Z
pCi/l+2s
*2
1
1
-3
0
1
0
1
-2 14
»1 7
0 7
43 7
6
0
3
3
SIGMA COUNTING ERROR
36
-------
TABLE 14
CONCENTRATIONS OF RADIONUCLIDES IN PASTEURIZED MILK
AUGUST 1984
LOCATION
AL:MONTGOMERY
AR:LITTLE ROCK
AZ:PHOENIX
CA:LOS ANGELES
CA:SACRAMENTO
CA:SAN FRANCISCO
CO: DENVER
CT:HARTFORD
FL:TAMPA
GA:ATLANTA
GA:ATLANTA
IA:DES MOINES
ID:IDAHO FALLS
IL:CHICAGO
IN:INDIANAPOLIS
KS:WICHITA
KY:LOUISVILLE
LA:NEW ORLEANS
MA:BOSTON
MD:BALTIMORE
ME:PORTLAND
MI:DETROIT
MI:GRAND RAPIDS
MN:MINNEAPOLIS
MN:ST PAUL
MO:KANSAS CITY
MO:ST LOUIS
MS:JACKSON
MT:HELENA
NC:CHARLOTTE
ND:MINOT
ME:OMAHA
NH:MANCHESTER
NJ:TRENTON
NM:ALBUQUERQUE
NY:BUFFALO
NY:NEW YORK CITY
NY:SYRACUSE
DATE
COLLECTED
8/13/84
8/ 8/84
8/ 9/84
8/21/84
8/ 1/84
8/ 8/84
8/31/84
8/ 8/84
8/ 8/84
8/ 6/84
8/30/84
8/ 7/84
8/ 6/84
8/ 6/84
8/ 6/84
8/ 7/84
8/ 7/84
8/10/84
8/ 7/84
8/ 3/84
8/ 8/84
8/ 9/84
8/ 6/84
8/ 6/84
8/ 6/84
8/ 9/84
8/ 8/84
8/13/84
8/10/84
8/ 6/84
8/22/84
8/10/84
8/ 6/84
8/ 9/84
8/ 6/84
8/14/84
8/ 6/84
8/ 6/84
K
iJ/P0 iHUn., i-"-!
l»S Del J.
g/l+2s
1.
1.
1.
1.
1.
1.
1.
1,
1,
1,
1,
1,
1,
1,
1.
1.
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1,
1
1
1,
1
1
1
1
1
1
1
,53
,69
,38
,61
,63
,56
,50
.57
.56
.60
.59
.54
.61
.70
.54
.55
.59
.50
.56
.50
.53
.55
.54
.51
.67
.65
.57
.50
.49
.54
.68
.44
.43
.53
.58
.49
.55
.55
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
0
0
0
0
0
0
0
0
0
0
0
.
.
13
13
12
13
13
13
12
09
13
13
13
13
13
13
13
09
13
09
13
12
13
13
13
13
24
13
13
09
12
24
13
12
12
13
13
12
.09
0.13
pCi/l+2s
4
0
4
0
0
0
*3
2
13
5
6
1
3
2
3
*2
0
3
4
*!
8
3
1
1
10
"2
1
4
A2
8
1
5
4
2
-3
4
+2
0
7
7
7
7
7
7
7
5
7
7
7
7
7
7
7
5
7
5
7
7
7
7
7
7
18
7
7
5
7
18
7
7
7
7
7
7
5
7
pCi/l+2s
-4
*!
4
*1
2
0
-5
*1
3
-7
-1
1
»3
*3
*2
0
-2
-2
*2
6
7
*3
*2
»1
A8
*6
2
»5
*3
-4
4
-3
*6
6
*8
0
4
*2
9
9
9
9
9
9
9
6
9
9
9
9
9
9
9
6
9
6
9
9
9
9
9
9
18
9
9
6
9
18
9
9
9
9
9
9
6
9
pCi/l+2s
-1
2
1
3
0
4
-2
-2
*!
2
*1
"2
4
1
*1
*2
2
0
5
*1
2
3
-4
*1
8
5
4
2
1
11
0
2
*4
1
4
1
0
3
7
7
7
7
7
7
7
5
7
7
7
7
7
7
7
5
7
5
7
7
7
7
7
7
14
7
7
5
7
14
7
7
7
7
7
7
5
7
37
-------
TABLE 14 (CONTINUED)
CONCENTRATIONS OF RADIONUCLIDES IN PASTEURIZED MILK
AUGUST 1984
LOCATION
OH:CINCINNATI
OH: CLEVELAND
OK:OKLAHOMA CITY
OR: PORTLAND
PA PHILADELPHIA
PA PITTSBURGH
PC:CRISTOBAL
PR:SAN JUAN
SC:CHARLESTON
SD:RAPID CITY
TN:CHATTANOOGA
TN:KNOXVILLE
TN:MEMPHIS
UT:SALT LAKE CITY
VA:NORFOLK
VT:BURLINGTON
WA:SEATTLE
WI:MILWAUKEE
WI:MILWAUKEE
WV:CHARLESTON
WY:LARAMIE
DATE
COLLECTED
8/ 6/84
8/ 7/84
8/ 6/84
8/ 7/84
8/ 6/84
8/ 8/84
8/30/84
8/23/84
8/22/84
8/ 9/84
8/ 6/84
8/ 6/84
8/29/84
8/ 5/84
8/10/84
8/ 8/84
8/ 1/84
8/31/84
8/ 1/84
8/22/84
8/ 7/84
K
g/l+2s
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
.54
.65
.57
.54
.50
.51
.49
.49
.55
.76
.52
.63
.63
.57
.65
.64
.56
.72
.59
.47
.58
0,
0.
0.
0,
0.
0.
0.
0,
0,
0.
0.
0.
0,
0.
0.
0.
0.
0,
0,
0.
0.
.13
.09
.13
.13
.09
.12
.12
.12
.13
.17
.13
.13
.13
.13
.13
.13
.09
.13
.13
.12
.13
LJI
Cs
pCi/l+2s
2
2
0
4
2
1
13
^3
3
9
3
3
*3
1
4
0
3
3
-I
2
3
7
5
7
7
5
7
7
7
7
13
7
7
7
7
7
7
5
7
7
7
7
1HU
Ba
pCi/l+2s
0
-2
0
4-1
0
*5
*4
5
3
0
4
*-2
*3
*10
*3
*i
*2
-11
*3
»2
*4
9
6
9
9
6
9
9
9
9
13
9
9
9
9
9
9
6
9
9
9
9
i j j.
I
pCi/l+2s
-3
0
»2
1
-2
5
2
A3
3
1
-4
3
4
2
7
A3
1
-3
*3
5
+1
7
5
7
7
5
7
7
7
7
10
7
7
7
7
7
7
5
7
7
7
7
SIGMA COUNTING ERROR
38
-------
TABLE 15
CONCENTRATIONS OF RADIONUCLIDES IN PASTEURIZED MILK
SEPTEMBER 1984
LOCATION
AK:PALMER
AL:MONTGOMERY
AR:LITTLE ROCK
AZ:PHOENIX
CA:LOS ANGELES
CA:SACRAMENTO
CA:SAN FRANCISCO
CO:DENVER
CT:HARTFORD
FL:TAMPA
HI:HONOLULU
IA:DES MOINES
ID:IDAHO FALLS
IL:CHICAGO
IN:INDIANAPOLIS
KS:WICHITA
KY:LOUISVILLE
LA:NEW ORLEANS
MA:BOSTON
MD:BALTIMORE
ME:PORTLAND
MI:GRAND RAPIDS
MNMINNEAPOLIS
MN:ST PAUL
MO:KANSAS CITY
MO:ST LOUIS
MS:JACKSON
MT:HELENA
NC:CHARLOTTE
ND:MINOT
NE:OMAHA
NH:MANCHESTER
NJ:TRENTON
NM:ALBUQUERQUE
NV:LAS VEGAS
NY:BUFFALO
NY:NEW YORK CITY
NY:SYRACUSE
DATE
COLLECTED
9/18/84
9/ 7/84
9/10/84
9/ 6/84
9/24/84
9/ 4/84
9/11/84
9/27/84
9/17/84
9/11/84
9/ 4/84
9/10/84
9/11/84
9/10/84
9/ 6/84
9/10/84
9/ 5/84
9/12/84
9/11/84
9/ 7/84
9/ 4/84
9/ 4/84
9/10/84
9/ 4/84
9/ 6/84
9/ 5/84
9/ 5/84
9/10/84
9/ 4/84
9/20/84
9/ 7/84
9/10/84
9/ 6/84
9/ 4/84
9/10/84
9/10/84
9/10/84
9/ 4/84
K
J-J'Tc i'*'-'Tla iJJ-T
US Da L
g/l+2s
1,
1
1,
1,
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
.60
.64
.57
.55
.68
.56
.58
.42
.51
.53
.60
.56
.57
.54
.54
.58
.59
.50
.46
.54
.59
.53
.57
.54
.57
.55
.54
.52
.75
.56
.44
.52
.56
.51
.57
.69
.54
.58
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
0
0
0
0
0
0
0
0
0
0
0
0
13
13
13
13
13
13
09
12
12
13
13
13
13
13
13
13
09
13
12
13
13
13
09
13
13
09
13
13
24
09
12
09
13
09
13
13
.13
09
pCi/l+2s
1
4
4
1
0
3
3
1
-2
11
5
*2
6
1
2
*2
41
5
5
4
9
3
4
2
2
4
4
2
10
1
1
2
2
*2
1
2
3
3
7
7
7
7
7
7
5
7
7
7
7
7
7
7
7
7
5
7
7
7
7
7
5
7
7
5
7
7
18
5
7
5
7
5
7
7
7
5
pCi/l+2s
-5
*3
3
1
3
*3
-7
*1
-7
*5
0
*1
-4
1
0
1
0
9
3
+2
*5
*5
+1
-1
*1
*1
»3
*4
0
0
*3
*2
*2
0
1
1
-1
0
9
9
9
9
9
9
6
9
9
9
9
9
9
9
9
9
6
9
9
9
9
9
6
9
9
6
9
9
19
6
9
6
9
6
9
9
9
6
pCi/l+2s
6
0
2
0
0
1
-2
3
2
4
-1
0
0
7
*2
0
1
0
4
3
-I
0
0
*3
6
*2
*1
3
4.3
1
2
4
0
2
2
0
2
0
7
7
7
7
7
7
5
7
7
7
7
7
7
7
7
7
5
7
7
7
7
7
5
7
7
5
7
7
14
5
7
5
7
5
7
7
7
5
39
-------
TABLE 15 (CONTINUED)
CONCENTRATIONS OF RADIONUCLIDES IN PASTEURIZED MILK
SEPTEMBER 1984
LOCATION
OH:CINCINNATI
OH:CLEVELAND
OK:OKLAHOMA CITY
OR:PORTLAND
PA PITTSBURGH
PC:CRISTOBAL
PR:SAN JUAN
SD:RAPID CITY
TN:CHATTANOOGA
TNrKNOXVILLE
TN:MEMPHIS
TX:AUSTIN
UT:SALT LAKE CITY
VA:NORFOLK
VT:BURLINGTON
WA:SEATTLE
WI:MILWAUKEE
WV:CHARLESTON
WY:LARAMIE
DATE
COLLECTED
9/10/84
9/10/84
9/ 4/84
9/ 4/84
9/ 5/84
9/27/84
9/28/84
9/ 6/84
9/ 4/84
9./10/84
9/26/84
9/18/84
9/ 9/84
9/ 4/84
9/ 7/84
9/ 4/84
9/28/84
9/25/84
9/ 5/84
K
g/1+2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
.45
.60
.57
.44
.50
.48
.71
.60
.43
.57
.66
.51
.54
.64
.93
.45
.51
.46
.59
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
s
.12
.13
.13
.08
.09
.12
.24
.13
.12
.13
.13
.12
.13
.13
.25
.12
.12
.12
.13
i j/
Cs
pCi/l+2s
2
-4
10
0
0
16
16
1
6
0
2
*2
2
4
4
4
2
4
3
7
7
10
5
5
7
18
7
7
7
7
7
7
7
18
7
7
7
7
itu
Ba
pCi/l+2s
-4
6
-2
-2
0
1
-4
5
0
"3
»7
*1
+5
*3
3
1
*2
-3
+4
9
9
11
6
6
9
18
9
9
9
9
9
9
9
19
9
9
9
9
i_> j.
I
pCi/l+2s
2
5
2
2
3
0
5
-5
-3
2
5
4
1
2
9
5
1
3
1
7
7
8
5
5
7
14
7
7
7
7
7
7
7
14
7
7
7
7
NS NO SAMPLE
s SIGMA COUNTING ERROR
40
-------
TABLE 16
STRONTIUM--90 AND STRONTIUM*89 IN PASTEURIZED MILK
ANNUAL REPORT
JULY * SEPTEMBER 1984
EPA
REGION
AK: PALMER
AL: MONTGOMERY
AR: LITTLE ROCK
AZ: PHOENIX
CA:LOS ANGELES
CA: SACRAMENTO
CA:SAN FRANCISCO
CO: DENVER
CT: HARTFORD
DC: WASHINGTON
FL: TAMPA
GA: ATLANTA
HI: HONOLULU
IA:DES MOINES
IL: CHICAGO
IN: INDIANAPOLIS
KS: WICHITA
KY: LOUISVILLE
MA: BOSTON
MD: BALTIMORE
ME: PORTLAND
MI: DETROIT
MI: GRAND RAPIDS
MN: MINNEAPOLIS
MN:ST. PAUL
MO: KANSAS CITY
MO: ST. LOUIS
MS: JACKSON
MT: HELENA
NC: CHARLOTTE
ND:MINOT
NE: OMAHA
NH: MANCHESTER
NJ: TRENTON
90g]
pCi/1
9/18/84
11 6/84
11 2/84
11 5/84
7/12/84
11 2/84
11 3/84
7/ 2/84
7/16/84
7/ 6/84
7/ 3/84
11 2/84
7/ 1/84
11 9/84
7/10/84
7/ 2/84
11 2/84
7/ 3/84
7/10/84
7/ 6/84
7/ 3/84
7/ 5/84
11 2/84
7/ 9/84
11 3/84
7/ 5/84
7/13/84
7/ 9/84
7/10/84
7/ 2/84
7/27/84
7/ 6/84
7/ 2/84
7/ 5/84
r
± 2s
1.1
3.1
4.1
0.1
-0.3
0.1
-0.1
1.6
2.4
2.0
1.6
2.0
1.3
2.0
2.5
2.6
2.9
2.8
2.9
2.5
3.0
2.7
3.6
3.4
4.1
2.7
2.1
2.6
1.4
2.6
2.5
2.3
2.3
2.3
0.7
0.8
0.7
0.9
0.4
0.5
1.2
0.6
1.0
0.8
1.0
0.4
0.6
0.6
0.2
0.4
0.3
0.3
1.1
0.8
0.7
0.6
0.9
0.8
0.7
0.5
0.6
0.6
0.8
1.0
0.8
0.5
1.0
1.3
89Sr
pCi/1 + 2s*
0
0
1
1
1
1
1
0
0
0
0
0
0
1
0
0
0
»1
0
0
0
0
1
0
*1
0
1
0
0
0
0
0
1
0
1
1
1
1
1
1
2
1
1
1
1
0
1
1
0
1
0
0
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
2
41
-------
TABLE 16 (CONTINUED)
STRONTIUM*90 AND STRONTIUM*89 IN PASTEURIZED MILK
ANNUAL REPORT
JULY * SEPTEMBER 1984
EPA
REGION
90Sr
pCI/1 + 2s
NM:ALBUQUERQUE 8/ 6/84 1.2
NV:LAS VEGAS 7/23/84 -0.2
NY:BUFFALO 7/10/84 2.4
NY:NEW YORK CITY 7/ 2/84 3.8
NY:SYRACUSE 7/ 2/84 2.8
OH CINCINNATI 7/ 9/84 1.7
OHCLEVELAND 7/ 9/84 3.4
OK:OKLAHOMA CITY 7/23/84 4.7
OR:PORTLAND 7/ 2/84 1.3
PAPHILADELPHIA 7/ 2/84 2.8
PA:PITTSBURGH 7/ 3/84 3.7
PC:CRISTOBAL 7/26/84 1.2
PR:SAN JUAN 7/16/84 0.0
SC:CHARLESTON 7/12/84 2.6
SD:RAPID CITY 7/ 5/84 2.4
TN:CHATTANOOGA 7/ 2/84 2.0
TNrKNOXVILLE 8/ 6/84 3.2
TN:MEMPHIS 7/25/84 2.7
TX:AUSTIN II 2/84 -0.2
UT:SALT LAKE CITY 8/ 5/84 0.7
VA:NORFOLK 7/19/84 2.2
VT:BURLINGTON 7/ 5/84 2.4
WA:SEATTLE 7/ 2/84 0.8
WA:SPOKANE 7/ 2/84 2.1
WIMILWAUKEE 8/31/84 1.7
WV:CHARLESTON 7/18/84 2.5
WY:LARAMIE 7/13/84 1.7
.5
.5
0.3
0.2
0.7
0.9
0.8
0.5
1.0
0.3
0.9
0.
0.
0.6
0.4
0.4
0.4
0.9
1.0
0.5
1.4
0.6
0.7
0.6
1.6
0.9
1.2
0.6
0.5
°'Sr
pCi/1 + 2s*
0
1
0
-1
0
0
-1
*1
0
*1
-1
0
1
-1
0
1
-1
0
2
1
0
-1
2
0
1
0
0
0
0
1
1
1
1
1
0
1
1
1
1
0
0
0
1
1
1
2
1
1
1
2
1
2
1
1
SIGMA COUNTING ERROR
ANALYTICAL ERROR TERM WHICH CLOSELY APPROXIMATES
THE COUNTING ERROR
42
-------
Carbon*14 _ln Milk
Nine stations, chosen for wide geographical distribution,
contribute milk samples for annual analysis for carbon*14. These
samples have monitored the carbon*14 levels in the food chain
resulting from nuclear testing.
Analysis consists of combusting the samples and measuring
released carbon dioxide through liquid scintillation.
Data will be published as it becomes available.
43
-------
ENVIRONMENTAL RADIATION DATA (ERD) is published quarterly
(January, April, July, October) by the U. S. Environmental
Protection Agency's Office of Radiation Programs.
Requests for information concerning publication and distribution
of ERD should be directed to:
Charles M. Petko
Technical Support Branch
Eastern Environmental Radiation Facility
1890 Federal Drive
Montgomery, Alabama 36109
Requests for information concerning the operation of ERAMS
should be directed to:
Geraldine A. Luster, Acting Chief
Monitoring and Analytical Services Branch
Eas-tern Environmental Radiation Facility'
1890 Federal Drive
Montgomery, Alabama 36109
or to:
James W. Gunter, Chief
Environmental Studies and Statistics
Analysis and Support Division (ANR*461)
U. S. Environmental Protection Agency
Waterside Mall East
401 M Street, SW
Washington, DC 20460
***
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