ML20102A597
| ML20102A597 | |
| Person / Time | |
|---|---|
| Site: | Quad Cities  |
| Issue date: | 07/02/1992 |
| From: | COMMONWEALTH EDISON CO. |
| To: | |
| References | |
| PROC-920702, NUDOCS 9207270137 | |
| Download: ML20102A597 (20) | |
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Attached is a reproduction of the'recent revistoit previouslyj dtstrjbuted.
The Offsite Dose Calculation Manual'(OOCH), Quad Cltles Station Annex,'. Chapter
- 11, is being re-issued in entirety for a'page correction.-lThe page change is considered to be an administrative change.,
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-i MAY:1992:.
QUAD CITIES: ANNEX-INDEK-PAGE REVISION CHAPTER 11-l-
11-1 0.G' 11-il 0.C l
11-111 0.C ll-vi
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11-2
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O 11-1
QUAD CITIES' REVISION:O.C-
-FEBRUARY--1991
- c J.
CHAPTER 11 ENVIRONMENTAL RADIOLOGICAL MONITORING TABLE OF CONTENTS PAGE 11 ENVIRONMENTAL RADIOLOGICAL MONITORING 11-l' O
p O
11-11
QUAD CITIES.
REVISION 0.C-FEBRUARY 1991
-('N L)
CIIAPTER 11 LIST OF TABLES NUMBER TITLE EAGE 11-1 Environmental Radiological Monitoring Program 11-2 11-2 Reporting Levels for Radioactivity-Concentrations in Environmental Samples 11-8 11-3 Maximum Values for the Lower Limits of Detection (LLD) 11,9 fh V
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c 11-111 1
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QUAD CITIES REVISIO!J 0.C FEl3RUARY 1991 i
O CitAPTER 11 LIST OY FIGURES liUM. DIE TITLE FAGE 11-1 Fixed Air Sampling Sites and Outer Ring TLD Locations 11-12 11-2 Inner Ring TLD Locations 11-13 11-3 Milk, Fish, Wator, and Sediment Sample Locations 11-14 O
O 11-iv
QUAD CITIES REVISION O MARCH 1989 t
CilAPTER 11 ENVIRONMENTAL RADIOLOGICAL MONITORING The parameters of the environmental radiological monitoring program to be performed in the environs around Quad-Cities Station are presented in Table 11-1.
Figure 11-1 shows the 16 fixed air sampling sites and TLD locations; a)so shown nra the outor ring (approximately 5 miles distant) TLD locations.
Figure 11-2 shows the innor ring TLD locations.
The TLDs are codu numbered as follows:
XYY-N X=1 means inner ring, X=2 means outer eing, and YY-N is an identification code.
Figure 11-3 shows the milk, fish, water, and sediment sample locatior L The reporting levels for radioactivity concentrations in environmental samples are given in Table 11-2.
The practical lower limits of detection for this program are given in Table 11-3.
0 11-1
s
(""g REVISL,,,J.C FEBRUARY 1991 QUAD CITIES Table 11-1 Environmental Radiological Monitoring Program Exposure Pathway Sampling or Type and Frequency
_and/or Samole Samo11no or Monitorin1 Locationsa Collection Frecuency of Analysis 1.
Airborne a.
Onsite and Near Fieldb Ceatinaous sampler operation Particulate Samalgt:
with particulate filter Q-01 Onsite No. 1 0.5 mi N (0.8 km A) collection weekly ar.d Gross beta analysis Q-02 Onsito No. 2 0.5 mi ENE (0.8 km D) radiciodine canister following filter Q-03 Onsite No. 3 0.6 mi S (1.0 km J) collection biweeklyC changed Q-04 Nitrin 1.5 mi NE (2.4 km C) 0-05 Saddle lub Dairy Farm 1.8 mi SSE (2.9 km H)
Q-06 Hanson's Boat Landing 1.8 mi NNH (2.9 km R) 4 Radiciodine Canister:
I-131 analysis biweekly inmolino Train:
4 i
Test and maintenance i
weekly b.
Far Fieldb Continuous sampler operation Particulate Samoler:
with particulate filter 0-07 Clinton 9.0 mi NE (14.5 km C) exchange weekly and Gross beta when d
Q-08 Sikkema Farm 7.0 mi ENE (11.3 km D) radiolodine canister exchange analyses are made e 0-09 Erie 13.0 mi ESE (20.9 km F) biweeklyC 11-2
I AD CITIES REL 0.C FEBRUARY 1991 i
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Table 11-1'(Cont'd)
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F Exposure Pathway Sampling or Type and Frequency j~
and/or Sample Samplina or Monitor!rnocationsa Collection freauency of Analysis
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l 0-10 Hillsdale 10.0 mi SE iib 1 km G)-
Radioiodine Canister:
Q-11 Port Byron'8.0 mi S (12.9 Km J) i 0-12 Bettendorf 13.0 mi SM (20.9 km L)
I-131 when analyses l
Q-13 Princeton 4.8 mi.S'4 (7.7 km L)
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Q-14 Utica Ridge Roat' 1.0 mi M (17.7 km N).
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Q-15 DeWitt 13.0 mi MNN (20.9 km P)
Sasolina Train:
1 Q-16 Low Moor 6.0 mi NMW (9.7 km R) l Testandmaintenarce'}
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weekly s'
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Direct Radiation a.
At Air Sampler Sitesb Quarterly Gaara dose quarterly I
Same location'as fixed al'r sampling locations j
in Ites 1.
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Inner Rinaf Quarterly Gamma dose quarterly I
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G-101-1, 0.7 mi N 1.1 km A l
0-101-2, 0.7 al N
. 1.1 km A i-Q-102-1, 1.7 mi NNE 2.7 km B
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Q-102-2, _
1.2 al ENE 1.9 km D 1.7 mi NME 2.7 km B' l
Q-103-1,.
Q-103-2, 1.2 al'ENE 1.9 km D l
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Q-104-1, l1.1 mi ENE 1.8 km D
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Q-104-2, 1.0 ri ENE 1.6.km D Q-104-3, 0.6 al ENE 1.0 km D l
-Q-105-1, 0.8 mi E 1.3 km E Q-105-2, 0.8 mi E-1.3 km E-c r
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h ITIES 15103 0.C i
FEBRUARY.1991 L
Table 11-1 (Cont'd) l l
- Exposure Pathway-Sampling or Type and Frequency i
and/or Samole Samlina or Monitorina Locationsa Collection Freauency of Analysis p
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2.
Direct Radiation - Q-106-1, 0.7 mi ESE 1.1 km F j
(Cont'd).
Q-107-1,
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l 0-106-2, 0.7 al ESE 1.1'km F Q-107-2, 0.7 mi SE 1.2 km G i
4
. 0-107-3,,
0.8 mi SE-1.3 km G' Q-108-1, 0.9 mi SSE 1.4 km H 0-108-2,.
0.9 mi SSE '1.4 km H
,i 0-109-1, 0.9 mi S 1.4 km J
' Q-109-2,-
0.9 mi S 1.4 km J
- Q-111-1,.
2.6 mi SW 4.2 km L i
- Q-111-2, 2.6 mi SN. 4.2 km L L
Q-112-1,.
2.4 mi NSW 3.9 km M Q-112-2,-
2.4 mi.MSN.3.9 km M
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Q-113-1, 2.5 mi-h-4.0 km N Q-113-2, 2.5 mi N. 4.0 km W I-Q-114-1,
.2.6 mi NNN 4.2 km P l
Q-114-2,
' 2.5 mi leN 4.2 km P
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Q-115-1, 2.3 al NN-
't.7 km Q
- Q-115-2,
.2.3 al NN. 3.7 km Q t
. Q-116-1, 2.2.mi NNW 3.5 km R i
Q-116-2, 2.2 mi NNN 3.5'km R c.
Outer Rinab-Quarterly Gamma dose quarterly i
Q-201-1, 4.0 mi N-
~ 6.4 km A' Q-201-2,-
4.0 mi N -
6.4 km A t
. Q-202-1,.
4.4 mi NNE 7.1 km B Q-202-2, 4.4 mi NNE 7.1 km B l
Q-203-1,-
5.5 mi NE 8.8 km C' Q-203-2, 5.5'mi NE' 8.8 km C i
i 11-4 i
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AD CITIES RE ON O.C TEBRUARY 1991 Table 11-1 (Cont *d)
Exposure Pathway Sampling or Type and Frequency and/or Samole Samolino or Honitorino Locationsa Collection Frecuency of Analysis 2.
Direct Radiation Q-204-1, 4.5 mi ENE 7.2 km D (Cont'd) 0-204-2, 4.5 mi ENE 7.2 km D Q-205-1, 4.5 mi E 7.2 km E Q-205-2, 4.5 al E 7.2 km E Q-206-1, 4.8 mi ESE 7.7 km F Q-206-2, 4.8 mi ESE 7.7 km F Q-207-1, 4.8 mi SE 7.7 km G Q-207-2, 4.8 mi SE 7.7 km G Q-208-1, 4.4 mi SSE 7.1 km H Q-208-2, 4.4 mi SSE 7.1 km H Q-209-1, 4.8 r.1 5 7.7 km J Q-209-2, 4.8 mi S 7.7 km J Q-210-1, 4.4 mi SSH 7.1 km K Q-210-2, 4.4 mi SSH 7.1 km K Q-211-1, 5.0 mi SH 8.0 km L Q-211-2, 5.0 mi SH 8.0 km L Q-212-1, 4.8 al HSH 7.7 km H 0-212-2, 4.8 mi HSH 7.7 km H Q-213-1, 4.7 al N 7.6 km N 0-213-2, 4.7 mi H 7.6 km N 0-214-1, 4.8 al NH 7.7 km Q 0-214-2, 4.8 mi NH 7.7 km Q 0-215-1, 4.8 mi NH 7.7 km Q Q-215-2, 4.8 mi NH 7.7 km Q Q-216-1, 4.5 mi NNH 7.2 km R Q-216-2, 4.5 mi NNH 7.2 km R I
11-5
REVIST O.G
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MAY 16 _ /
QUAD CITIES 3.
Waterborne 9 a.
Public Water Q-19 East Moline Hater Horks, 16.0 ml SSH Heekly collection cospostted Gamma isotopic (25.8 km K) monthly analysis monthly Q-20 Davenport Hater Works, 18.0 ml SSH (29.0 km L) b.
Cooling Hater Q-21 Intake Canal. 0.1 m1 H (0.2 km N)
Neekly Gross beta analysis Q-22 Discharge Canal. 0.1 mi SH (0.2 km L) weekly c.
Shoreline Q-27 Albany, Upstream on Mississippi River, Annually Gamma isotopic Sediments 9 5.5 m1 NE (8.8 km C) analysis annually Q-28 Cordova Downstream on Mississippi River, 3.3 mi SSH (5.3 km K) h 4.
Inaestion l
a.
M11kl Q-18 Musal Dalry, 5.5 mi SH (8.9 km L)
Heekly: May to October I-131 analysis on each Q-25 Donald Halte Da?ry, 13.0 mi E Monthly: November to April sample 1
(20.9 km E)
'Q-26 Bill Stanley Dalry, 3.0 mi ENE (4.8 km D) b.
Fish 3 Q-24 Pool #14 of Miss. River Semlannually Gamma isotopic on edible portions of each sample.
5.
Land Use Census a.
Hilch Animals 1 Site boundary to 2 m11es Annually during grazing season Enumeration by a door-to-door or equivalent counting technique.
11-6 2
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QUAD CITIES REVISIC3 0.C FEBRUARY 1991 Table 11-1 (Cont'd)
Exposure Pathway Sampling or Type and Frequency ard/or Samole Samalina or Monitorina locationsa Collection Frecuency of Analysis i
5.
Land Use Census 2.
2 to 5 miles Annually during grazing season Enumeration by using (Cont'd) referenced information from county agricultural agencies or other reliable sources.
t, 3.
At dairies listed in Item 4.a.
Annually during grazing seascn Inquire as to feeding practices:
a.
Pasture only.
b.
Feed and chop l
only.
i c.
Pasture and feed; If both, ask farmer to estimate' l-fraction of food from pasture:
<251,25-501, 50-751, or >751.
11-7
p f) x (Xis_,lITIES CORRECTL AGE s
REVISIG;l 0.G MAY 1992 Table 11-1 (Cont'd)
Exposure Pathway Sampling or Type and Frequency and/or Samole Samo11no or Monitorina locationsa Collection Frecuency of Analysis b.
Nearest Resident In all 16 sectors up to 5 miles.
Annually I
,See Table D-16 of Appendix 0 for definitions of sector codes used with kilometer distances.
e b
See Figure 11-1.
c Biweekly means every two weeks.
d A gamma isotopic analysis shall be performed herever the gross beta concentration in a sample exceeds by five times (5x) the average concentration of the precedir.g endar quarter for the sample location.
e Far field samples are analyzed when near ft 4a results are inconsistent with previous measurements and radioactivity is i
confirmed as having its origin in etrborne offluents released from the station or at the discretion of the Emergency Preparedness Director.
I See Figure 11-2.
9 Upstream shoreline sediment monitoring location is not required, serves as control oily.
h Sea Figure 11-3.
)
I Hilk samples are required from two monitoring locations only. Three dairies are listed to ensure the minimum criteria.
3 The fish monitoring location is not identified exactly on the er.p. the point, Q-24, represents the area of the station discharge. Pool #14.
11-8
1 I
QUAD CITIES REVISION 0.C MAY 1992
<iO
'as't "-r fLEPORTING LEVELS FOR. RAD 10 ACTIVITY CONCENTRATIONS IN ENVIRONMENTAL SAMPLES 6
Reporting Levels i
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f; 1
Fish Milk Food Products I
AirbornePartleg)iate-(pC1/Kg, wet)
(pC1/1)
(pci/Kg. wet) l Analysis Hater or Gases (pCl/m (pCill) i t-i 4
l H-3 2 x 10 (a) i Mn-54 1 x 103 3 x 104 i
4 Fe-59 4 x 102 1 x 10 -
s s
-4 Co-58 1 x 103 3 x 10 4
Co-60 3 x 102
- 1 x 10 -
Zn-65 3 x 102 2 x-104 4
Zr-Nb-95 4 x 10 (b) 2 t
1-131 2
0.9 3
l' x 102 Cs-134 30 10 1 x 103 50-
.1 x 103 4
Cs-137 50 20 1 x 10 -
70 2 x 103 3
Ba-la-140-2 x 10 (b) 3 x 102
,i 2
a)
For drinking water samples.
This is 40 CFR Part 141 value.
- b) Total for perent and daughter.
11-9 b
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QUA3 CITIES REVISION 0.G MAY 1992 O
TABLE 11-3 PRACTICAL LOWER LIMITS OF DETECTION (LLD).
FOR STANDARD ENVIRONMENTAL RADIOLOGICAL HONITORING PROGRAM Sample Media Analysis LLD *8 Units A
(4.66 t_1 Airborne " Particulate" Gross Beta +
0.01 pCi/m3 3
Gamma Isotopic 0.01 pC1/m Airborne I-131 lodine 131 0.10 pCi/m3 Hi 4/Public Water 1-131 50 pCi/1 Cs-134 10 pC1/1 Cs-137 10 A pC1/1
~
Tritium 200 pCill Gross Beta +
5 pC1/1 Camma Isotopic 20 pCi/1/nuclide Sediment Gross Beta +
2 pC1/g dry Gamma Isotopic 0.2 pC1/g dry Fish Tissue I-131 Thyroid 0.1 pC1/g wet Cs-134. 137 0.1 pC1/g wet 1.0 pC1/g wet Gross Beta +.
O.2 pC1/g wet Gamma Isotopic' 0
0.5 pCill-on milk samples collected during the. pasture season.
+
Referenced to Cs-137 6
5.0 pCill on milk samples 11-10 0
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i.
QUAD CITIES REVISION 0.C FEBRUARY 1991 l
j Table ll-b (Cont'd) j General Notes:
4 1.
Other radionuclidos which are measurable and iden*_ifiable by gamma ray spectrometry, together with the nuclides indicated in Table 11-3, shall also be identified and reported when an actual analysis is performed on a sample.
Nuclides which are below the LLD for the analyseu s;1811 not be reported as being present at the LLD level for that nuclide.
2.
The LLD in the smallest concentration of radioactive j
material in a sample that will be detected with 95%
l probability with only 5% probability of falsely concluding i
that a blank observation represents a real signal.
For a particular measurement system (which may include i
radiochemical separation).
i i
4.66 (Sb)
LLD =
(A)
(E)
(V)
(2.25)
(Y)
(exp (-AAt))
(t) i LLD The a priori lower limit of detection for a blank j
sample or background analysis as defined above (as l
pCi per unit muss or volume).
d i
Sb The square root of the backgroundLcount or of a blank sample count; i t is the estimated standard error of a background count or a blank ssmple count as appro-priate (in units of counts).
E The counting efficiency (as counts per disintegra-i tion).
A The number of gamma-rays emitted per distintegration for gamma-ray radionuclide analysis (A = 1.0 for gross alpha and tritium measurements).
V The sample size (in units of mass or volume).
2.22 The number of disintegrations per minute per picocurie.
Y The fractional radiochemical yield when applicable (otherwise Y = 1.0).
O 11-11
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QUAD CITIES REVISION 0.C FEDRUARY 1991 O
Table 11-3 (Cont'd)
A The radioactive decay constant for the particular radionuclide (in units of reciprocal minutes).
4 at The elapsed time between the midpoint of sample collection and the start time of counting (at = 0.0 for environmental samples and for gross alpha measurements),
t The duration of the count (in units of minutes).
The value of Sb used in the calculation of the LLD for a detection system shall be based on an actual observed background count or a blank sample count (as appropriate) rather than on an unverified theoretically predicted value.
. Typical values of E, V, Y, t,
and at shall be used in the calculation.
For gamma-ray radionuclide analyses the background counts are determined from the total counts in the channels which l
are within plus or minus one FWHM (Full Width at Half l
Maximum) of the gamma-ray photopeak energy normally used O
for the quantitative analysis for that radionuclide.
Typical values of the FWHM shall be used in the calculatior.
l The LLD for all measureta.is is defined as an a priori (before the fact) limit tepresenting the capability of a measurement system and not as an a posteriori (after the fact) limit for a particular measurement.
Footnotes:
a Referenced to Cs-137.
b For thyroid.
c l
0.5 pCi/L on samples collected during the pasture season.
i
+
11-12
QUAD CITIES REVISION 0.C FEBRUARY 1991
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