ML20097G078
| ML20097G078 | |
| Person / Time | |
|---|---|
| Site: | Quad Cities  |
| Issue date: | 05/31/1992 |
| From: | COMMONWEALTH EDISON CO. |
| To: | |
| References | |
| PROC-920531-01, NUDOCS 9206160277 | |
| Download: ML20097G078 (7) | |
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QUAD CITIES REVISION 0.0 MAY 1992 4
OUAD CITIES ANNEX INDEX O
PAGE RE3flE10H CHAPTER 11 l
11-1 0.0 11-11 0.C 11-111 0.C 11-vi 0.C 11-1 0
11-2 0.C 11-3 0.C 11-4 0.C 11-5 0.C 11-6 0.0 11-7 0.C 11-8 0.0 11-9 0.G l
11-10 0.0 11-11 0.C 11-12 0.C 11-13 0.C 11-14 0.C 11-15 0.G O
11-1 L
O O
W QUAD CITIES
-3.
Waterborne 9
~I a.
Public' Hater 0-19 East Noline Water Works 16.0 mi SSN Neekly collection composited Gamma isotopic (25.8 km K) monthly analysis monthly l
Q-20 Davenport Water Works, 18.0 mi SSN (29.0 km L) b.
Coolina Mater 0 21 Intake Canal. 0.1 al N (0.2 km N)
Neekly Gros-s beta analysis Q-22_ Discharge Canal. 0.1 al SW (0.2 km L) weekly j
c.
Shoreline Q-27 Albany Upstream on Mississippi River.
Annually Gamma Isotopic Sediments 9 5.5 mi NE (8.8 km C) analysis annually Q-28 Cordova, Downstream on Mississippi River, 3.3 al SSN (5.3 km K) h
- 4..Incestion i
0-18 Musal Dairy, 5.5 at SN (8.9 km L)
Neekly: May to October I-131 analysts on each a.
M11k Q-25 Donald Malte Dalry, 13.0 ml E Nonthly: November to Apr11 sample (20.9 km E) 0-26 8111' Stanley Dairy, 3.0 mi EME
'(4.8 km D)
- b., f11t13 Q-24 Pool'#14 cf Miss. River Semiannually Gasma isotopic on 1
edible portions of each sample.
5.
Land Use Census a.
Milch Animals 1.
Site boundary to 2 miles Annually during grazing season Enumeration by a door-to-door or equivalent counting technique.
l.
11-6
QUAD CITIES REVISION 0.G MAY 1992
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TABLE 11-2 REPORTIN'; L(yELS FOR RADI0 ACTIVITY CQNC[NTRATIONS IN ENVIRONMENTAL SAMPLES Reporting Levels 1
Analysis Heter Airborne Partic late Fish Hilk Food Products (pCill) or Gaser (pC1/m )
(pC1/Kg, wet)
(pC1/1)
(pC1/Kg, wet) 4 H-3 2 x 10 (a)
Hn-54 1 x 103 3 x 104 Fe-59 4 x 102 1 x 104 Co-58 1 x 103 3 x 104 Co-60 3 x 102 1 x 104 2n-65 3 x 102 2 x 104 Zr-Nb-95 4 x 10 (b) 2 I-131 2
0.9 3
-1 x 102 Cs-134 30 10 1 x 103 60 1 x 103 Cs-137 50 20 1 x 103 70 2 x 103 Ba-La-140 2 x 10 (b)
- 3 x 102-2 a). For drt_nking water samples.
This is 40 CFR Part 141 value, b) Total for parent and daughter.
11-9 1
QUAD CITIES REVISION 0.G W.Y 1992 TABLE 11-3 PRACTICAL LOWER LIMITS OF DETECTION (LLD)
TOR STANDARD ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM Sample Media Analysis LLD *8 Units A
(4.66 E ).
Airborne "Patticulate" Gross Beta +
0.01 pC1/m3 Gamma Isotopic 0.01 pC1/m3 Airborne I-131 lodine 131 0.10 pC1/m3 Hilk/Dublic Water I-131 50 pC1/1 Cs-134 10 pC1/1-Cs-137 10 a pC1/1 Trittum 200 pCl/1 Gross Beta +
5 pC1/1_
Gama Isotopic 20 pCi/1/nuclide ediment Gross Beta +
2 pC1/g dry Gama Isotopic 0.2
-pC1/g dry Fish Tissue I-131 Thyroid 0.1 pC1/g wet j
Cs-134. 137 0.1 pCi/g wet Gross Beta +
1.0 pC1/g wet Gama Isotopic 0.2 pC1/g wet 0
0.5 pC1/1 on milk samples collected during the pasture season.
+
Referenced to Cs-137 6
5.0 pC1/1 on slik samples 11-10 0
v 0.G J
QUA TIES Table 11-1 (Cont'd)
Sampling or Type and Frequency Exposure Pathway and/or Samole Samo11no 9r Monitorino Locations Collection Frecuency of Analysts a
b.
Nearest Resident In all 16 sectors up to 5 miles.
Annually See Table D-16 of Appendix 0 for definitions of sector codes used with kilometer distances.
a b S:e Figure 11-1.
c Biweekly means every two weeks.
A gamma isotopic analysis shall be performed wherever the gross beta concentration in a sample exceeds by five times (5x) d the average concentration of the preceding calendar quarter for the sample location.
Far field samples are analyzed when near field results are inconsistent with previous measurements and radioactivity is e
confirmed as having its origin in airborne effluents released from the station or at the discretton of the Emergency Preparedness Director.
I -See Figure 11-2.
Upstream shoreline sediment monitoring location is not required, serves as control only.
9 h See Figure 11-3.
I Milk samples are required from two monitoring location", only.
Three dairles are listed to ensure the minimum criteria.
3 The fish monitoring location is not identified exactly on the map, the point, Q-24, represents the area of the station discharge.-Pool #14.
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11-12 l
.e QUAD CITIES REVISION 0.0 MAY 1992
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? *'a 0FFSITE DOSE CALCULATION MANUAL QUAD CITIES STATION IlGURE 114 g
MILK. FISH, WATER. AND SEDIMENT SAMPLE LOCATONS l
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11-15
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