ML20205F558
| ML20205F558 | |
| Person / Time | |
|---|---|
| Site: | Quad Cities  |
| Issue date: | 12/31/1985 |
| From: | COMMONWEALTH EDISON CO. |
| To: | |
| References | |
| PROC-851231-02, NUDOCS 8608190243 | |
| Download: ML20205F558 (76) | |
Text
QUAD-CITIES REVISION 11 DECEMBER 1985 ODCM LIST OF TABLES FOR QUAD-CITIES SECTION 7.2 NUMBER TITLE PAGE 7.2-1 Aquatic Environment Doce Parameters 7.2-1 7.2-2 Annual Design Objectives Set by 10 CFR 50, Appendix I for Each Reactor 7.2-2 7.2-3 Station Characteristics 7.2-3 7.2-4 Critical Ranges 7.2-4 7.2-5 Terrain Correction Factors (h )
~
t 7.2-6 X/Q and D/C Maxima At or Beyond the Unrestricted Area Boundary 7.2-6 7.2-7 D/C at the Nearest Milk Cow and Meat Animal Locations Within 5 Miles 7.2-8 7.2-8 Maximum Offsite Finite Plume Gamma Dose Factors for Selected Nuclides 7.2-9 l
0()
8608190243 851231 7.2-i PDR ADOCK 05000254 P
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QUAD-CITIES REVISION 11 i
DECEMBER 1985 1
l ODCM LIST OF FIGURES FOR QUAD-CITIES SECTION 7.2 NUMBER TITLE t'
7.2-1 Unrestricted Area Boundary i
l P
b
- O
(
I i
)
7.2-i1 t
QUAD-CITIES REVISION 11 DECEMBER 1985 TABLE 7.2-1 AQUATIC ENVIRONMENT DOSE PARAMETERS PARAMETER CUAD CITIES U",
water usage, liters /hr 0.083 f
-3 U
fish consumption, kg/hr 2.4 x 10 1/M" l
I 1/M 1
4 F",
ft /sec 4.7 x 10 3
F ft /sec 4.7 x 10 f
t hr*
24 t",
hr**
7.5 B
- Regulatory Guide 1.109, Revision 1, October 1977, Table A-1, g
Column 2 for freshwater fish.
See Table 7.1-12.
F ft /sec F",
ft /sec 1/M" Not applicable.
No outdoor tanks without overflow pipes connected T",
hr to other storage pipes.
t V, gal to, hr J
l f
- t (hr) = 24 hr (all stations) for the fish ingestion pathway l
- t" (hr) = 7. 5 hr (Distance to Davenport is 15 miles; flow rate s
of 2 m.p.h.)
1 7.2-1 l
QUAD-CITIES REVISION 11 DECEMBER 1985 O
TABLE 7.2-2 ANNUAL DESIGN OBJECTIVES SET _BY 10 CFR 50, APPENDIX I FOR EACH REACTOR TYPE OF DOSE ANNUAL DESIGN OBJECTIVES Airborne Releases Gamma Air Dose 10 mrad Beta Air Dose 20 mrad 5 mrem Whole Body Dose l
Skin Dose 15 mrem Infant Thyroid Dose 15 mrem Liquid Releases l
3 mrem l
Whole Body Dose j
10 mrem Thyroid Dose 10 mrem i
Bone Dose 10 mrem Skin Dose l
7.2-2
,, - ~. - - - - -, -___,-,,,n_,,,_,n__.
,.,,,,,_,_,,,,_,n,,--,+,,_--
-n
QUAD-CITIES REVISION 11 DECEMBER 1985 TABLE 7.2-3 STATION:
Quad-Cities Nuclear Power Station LOCATION:
Cordova, Illinois CHARACTERISTICS OF ELEVATED RELEASE POINT 3.35 m
- 1) Release Height =
95 m
- 2) Diameter
=
~1
-1 20.3 ms
- 4) Heat Content =
4.lE3 KCal s
- 3) Exit Speed
=
CHARACTERISTICS OF VENT STACK RELEASE POINT
- 1) Release Height =
48 m
- 2) Diameter =
2.74 m
-1 15.3 ms f
- 3) Exit Speed
=
CHARACTERISTICS OF GROUND LEVEL RELEASE
- 1) Release Height = 0m 36 m
- 2) Building Factor (D)
=
i METEOROLOGICAL DATA A
296 ft.
Tower is Located 1623 m SSE of Elevated Release Point Tower Data Used in Calculations Release Point Wind Speed Differential And Direction Temperature Elevated 296 ft.
296-33 ft.
Vent 196 ft.
196-33 ft.
Ground 33 ft.
196-33 ft.
(:)
i
- 7. 2-3
REVISION 11 QUAD-CITIES DECEMBER 1985 O
TABLE 7.2-4 CRITICAL RANGES PRACTICAL SITE NEAREST NEAREST DAIRY TARM BOUNDARY
- RESIDENT **
RANGE ***
DIRECTION (m)
(m)
(m)
N 864 966 NNE 1029 1600 NE 1212 2100 ENE 1367 4600 E
1170 3700 ESE 1170 3219 SE 1189 1600 SSE 1422 1800 I
S 1198 1300 SSW 2140 4800 l
SW 1372 4600 WSW 823 3219 O%
W 713 4000 WNW 713 4000 NW 823 3219 NNW 1481 3200 4
- Nearest land in unrestricted area
- Estimate range
- Within 5 miles O
7.2-4 j
d i
l O
O O
TABLE 7.2-5 i
1 TERRAIN CORRECTION FACTORS (h.) - QUAD-CITIES bTAT1UN m
3 1
1 1s
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,- a i
e r
i.
i.
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i Ou 3:::.:8aa:.as::::s :83i::i:i:;:ei3;8asi
- -:-::::::::::::::::::::i.D :::::: ::::::::j:::::::
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)6 g
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w t
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s:::::-::::::::: :::- :
shaded area has h =0.
e m
jA.
t d s v.',g aga V. i:i:i.:.!8..i.3!:i:iS.. i.S.::.:::s::8.. 3. :.:i.8...i.:.i.: 8. i.:D.s:S.:i.::!
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- . ss::s;.::isi.-s:8:::..:s::s:s::s:s;::..:s:ii:.:
Point 145 is the site.
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TABLE 7.2-6
)
X/Q AND D/O MAXIMA AT OR SEYDND THE UNRESTRICTED AREA BOUNDARY j
DOWNWIND ELEVATED (STACK) RELEASE MIXED _MODElyENT) RELEASE.
_GR_OUND_ (EV EL_RELE A SE, DIRECTION RADIUS X/Q +
RADIUS D/QA RADIUS X/Q +
D/Q A RADIUS X/Q +
D/0 A (METERSJ (SEC_/Me*3) (METERS)
(1/Me*2)
(METERS) (SEC/Me*3) (1/M**2)
(METERS) (SEC/Me*3) (1/Mo*2) i (h
N 864.
3.359-08 664 1.627-09 864.
1.569-06 1.050-08 864.
3.785-06 2.085-08 NNE to29.
4.304-08
- 1029, 1.869-09 1029.
5.723-07 4.333-09 1029.
1.151-06 6.452-09 NE 2000 3.649-08 1212.
1.419-09 1212.
7.858-07 3.502-09 1212.
1.299-06 4.967-09 O
ENE 2000.
2.203-08 1367.
6.363-10 1367.
5.866-07 2.572-09 1367.
1.003-06 4.418-09
[
-J E
3219.
2.288-08 1170.
8.769-10 1170.
4.843-07 3.558-09 1170.
1.010-06 6.056-09 y
i ESE 2000.
3.026-08 1170.
1.317-09 1170.
7.185-07 4.754-09 1170.
1.228-06 7.493-09 r3 SE 28vo.
3.906-08 1189.
1.428-09 1189.
9.715-07 5.298-09 1189.
1.681-06 9.041-09 H
cs SSE 2000.
3.067-08 1422.
8.104-10 1422.
5.276-07 2.488-09 1422.
1.108-06 4.828-09
]
I#
S 3020.
2.526-08 1198.
7.757-10 1190.
3.412-07 2.253-09 1990.
1.261-06 5.022-09 SSW 3219.
2.194-08 1024.
7.054-10 1024.
2.913-07 2.639-09 1024.
1.002-06 5.535-09 SW 654 3.439-08 654.
9.739-10 654.
6.155-07 4.495-09 654.
2.794-06 1.168-08 WSW 494.
7.298-08 500.
1.672-09 494.
1.039-06 6.518-09 494.
3.338-06 1.697-08 W
451.
6.637-08 500.
1.729-09 451.
2.657-06 1.238-08 451.
5.717-06 2.636-08 WNW 451.
7.002-08 500.
1.800-09 451.
5.104-06 1.824-08 451.
9.660-06 3.163-08 NW 485.
7.614-08 500.
1.698-09 485.
5.043-06 1.490-08 485.
1.218-05 2.980-08 NNW 640.
3.829-08 640.
1.335-09 640.
2.773-06 1.048-08 640.
5.197-06 1.810-08 1
I l
QUAD-CITIES 182 SITE METEOROLOGICAL DATA 1/74 - 12/75 00 n<
t1 H
- c us WH
$0
+
Beta air, beta skin, and inhalation dose pathways.
A Produce and leafy vegetable pathways.
Z oo UI l
i l
1 1
QUAD-CITIES REVISION ~11 DECEMBER 1985 O
TABLE 7.2-6 (Cont'd) i QUAD-CITIES 1&2 i
AVERAGE WIND SPEEDS FOR EACH RELEASE MODE DOWNWIND AVERAGE WIND SPEED (m/sec)
DIRECTION ELEVATED MIXED MODE GROUND LEVEL N
6.5 4.4 4.0 NNE 5.7 3.9 3.4 NE 5.8 3.7 2.9 ENE 5.8 3.9 3.5 E
6.4 4.6 4.4 ESE 6.7 4.7 4.4 O
SE 6.2 4.1 3.8 i
SSE 5.2 3.7 3.2 S
5.2 3.7 3.3 SSW 5.3 4.2 4.1 SW 5.4 4.0 3.7 WSW 4.5 3.5 3.3 5.7 4.0 3.7 WNW 6.1 3.7 3.4 NW 5.9 3.4 2.8 l:
NNW 6.2 3.8 3.5 O
7.2-7
QUAD-CITIES REVISION 11 DECEMBER 1985 I
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l TABLE 7.2-8 QUAD-CITIES 1&2 MAXIMUM OFFSITE FINITE PLUME GAMMA DOSE FACTORS FOR KR 83M DOWNWIND RESTRICTED _EAILV ATED( ST ACK ) RELEASE,
_M1X_ED_MODElyENT ) RELEASE,
_ GROUND _LEYEL RELJASE I
DIRECTION AREA BOUND RADIUS S
50AR RADIUS V
VBAR RADIUS G
GBAR (METERS) (METERS _) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /VR)/(UCI/SEC) (METERS) (MRADfYR)/(UCI/SEC),
OC h
N 864 864.
4.43G-06 4.006-07 864.
1.726-04 1.559-05 864.
1.081-04 3.685-05
-J NNE 1029.
1029.
5.563-06 5.024-07 1029.
6.291-05 5.681-06 1029.
1.210-04 1.092-05 g
NE 1212.
1212.
4.239-06 3.028-07 1212.
8.139-05 7.350-06 1212.
1.336-04 1.206-05 o
Y ENE 1367.
1367.
2.259-06 2.040-07 1367.
5.986-05 5.406-06 1367.
1.019-04 9.203-06 H
j c
E 1170.
1170.
2.396-06 2.164-07 1170.
5.173-05 4.671-06 1170.
1.048-04 9.461-06 ESE 1170.
1170.
3.347-06 3.022-07 1170.
7.541-05 6.810-06 1170.
1.272-04 1.149-05 m
l SE 1189.
1189.
4.093-06 3.696-07 1189.
1.019-04 9.200-06 1189.
1.737-04 1.568-05 U1 3
SSE 1422.
1422.
3.156-06 2.850-07 1422.
5.367-05 4.847-06 1422.
1.114-04 1.006-05 5
1198.
1198.
2.567-06 2.318-07 1198.
3.656-05 3.301-06 1198.
1.298-04 1.172-05 SSw 1024 1024.
2.294-06 2.071-07 1024.
3.283-05 2.965-06 1024.
1.050-04 9.481-06 i
Sw 654 654.
4.231-0G 3.820-07 654.
7.185-05 6.488-06 654.
2.932-04 2.648-05 l
WSW 494.
494.
8.240-06 7.441-07 494.
1.164-04 1.051-05 494.
3.653-04 3.298-05 W
- 451, 451.
7.616-06 6.877-07 451.
2.770-04 2.501-05 451.
5.883-04 5.313-05 WNw 451.
451.
7.837-06 7.077-07 451.
5.155-04 4.655-05 451.
9.168-04 8.279-05 NW 485.
485.
8.367-06 7.556-07 485.
4.985-04 4.501-05 485.
1.109-03 1.002-04 NNW 640.
640.
4.750-06 4.289-07 640.
2 900-04 2.619-05 640.
5.238-04 4.730-05 QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75 yg o<
MH i
U1 H
MO l
- D Z HH
@H CO U1 s
a
O O
o a
i TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1&2 l
MAXIMUM OFFSITE FINITE PLUME GAMMA DOSE FACTORS FOR KR 85M DOWNWIND RESTRICTED ELEVATED (STACK) RELEASE MIXED MODE (VENT) RELEASE GROUND LEVEL fifLE251 DIRECTION AREA BOUND RADIUS S
SBAR RADIUS V
V8AR RADIUS G
G8AR (METERS), (METERS) (MRAD /YR)/(UCI/SEC) (METERS) HRAD/YR)/(UCl/SEC).iME T E 815 ) (MR20 /YR)/ (UCy%CJ_
o C
N 864 864.
2.003-04 1.066-04 864.
1.192-03 6.175-04 RS4.
2.252-13 1.15a-03 4
N NNE 1029.
1029.
2.401-04 1.278-04 1029.
6.266-04 3.278-04 1029.
7.455-24 3 847-04 f
e NE 1282.
1212.
1.692-04 9.001-05 1212.
6.397-04 3.325-04 1212 6.024-34 4.134-04 o
3 h
ENE 1367.
1367.
9.329-05 4.965-05 1367.
4.656-04 2.419-04 13ti7.
6.447-34 3.327-04 H
E 1170.
1870.
1.134-04 6.037-05 1170.
4.396-04 2.291-04 1170.
6.585-34 3.400-04 d
o i
ESE 1170.
1170.
1.416-04 7.539-05 1170.
5.858-04 3.045-04 1170.
7.905-34 4.000-04 l
SE 1889.
1189.
1.772-04 9.431-05 1189.
7.843-04 4.o75-08 1189.
1.097-33 5.6G2-04 y)
SSE 1422.
1422.
1.212-04 6.446-05
- 1422, 4.612-04 2 403-04 1422 7.236-04 3.738-04 S
5198.
1198.
1.232-04 6.559-05 1198.
3.642-04 1.905-04 1198.
7.618-04 3.922-04 i
SSw 1024
- 1024, 1.326-04 7.066-05 1024.
3 430-04 1.797-08 1024 6.186-04 3.187-04 i
j SW 654.
654.
1.973-04 1.051-04 654.
6.135-04 3.199-04 654.
1.439-03 7.360-04 WSW 494 494.
3.307-04 1.760-04
- 494, 9.683-04 5.c47-04 494.
1.800-03 9.210-04 W
451.
451.
3.395-04 1.808-04 451.
1.668-03 8.605-04 451.
2.739-03 1.398-03 WNw 451.
451.
3.176-04 1.690-04 45%.
2.666-03 1.367-03 451.
3.988-03 2.028-03 Nw 485.
485.
3.193-04 1.699-04 493.
2.597-03 1.332-03 485.
4.722-03 2.399-03
)
NNw 640.
640.
2.252-04 1.199-04 640.
1.659-03 8.538-04 640.
2 466-03 1.259-03 l
I QUAD. CITIES 182 SITE METEOROLOGICAL DATA 1/74 - 12/75 cM l
MM O<
1 MH 4
3 U1 (D H MO MZ I.
@t8 00 LA
p
{'
V V
s TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1&2 MAXIMUM *0FFSITE FINITE PLUME GAMMA DOSE FACTORS FOR KR 85 GROUND LEVEL REf. EASE RADIUS- ~ (yENT) RELEASE MIXED MODE ~-
V8AR RADIUS G
G8AR DIRECTICN AREA BOUND ITADIU$' ~
S
-RELEASE DOWNWIND RESTRICTED ELEVATED (STACK)
SBAR V
(METERS) (METERS) (MRAD /VR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCI/SECJ (METERS) (MR AD/YR)fjuCIfSEC)
OC J
N 864.
864 2.596-06 1.607-06 864.
1.350-05 8.354-06
- 864, 2.484-05 1.538-05 NNE 1029.
1029.
3.135-06 1.941-06 1029.
7.378-06 4.567-06 1029.
8.309-06 5.143-06 NE 1212.
1212.
2.208-06 1.367-06 1212.
7.455-06 4.614-06 1212.
9.040-06 5.596-06 O
H ENE
- 1367, 1367.
1.224-06 7.576-07 1367.
5.424-06 3.357-06 1367.
7.3i3-06 4.526-06 H
H E
1 1 "' 2.
1170.
1.475-06 9.133-07 1170.
5.086-06 3.148-06 1170.
7.362-06 4.557-06 dg ESE 1170 1170.
1.034-06 1.138-06 1170.
6.750-06 4.178-06 1170.
8.840-06 5.472-06 m
SE 1189.
1989.
2.309-06 1.429-06 1189.
9.048-06 5.601-06 1189.
1.229-05 7.606-06 u)
SSE 1422.
1422.
1.595-06 9.874-07 1422.
5.427-06 3.360-06 1422.
8.222-06 5.090-06 S
1198.
1198.
n.616-06 1.000-06 1190.
4.296-06 2.660-06 1190.
8.551-06 5.293-06 SSW 1024.
1024.
1.740-06 1.077-06 1024 4.033-06 2.497-06 1024.
6.861-06 4.247-06 SW 654 654 2.564-06 1.587-06 654.
7.098-06 4.394-06 654 1.575-05 9.750-06 WSW A94.
494.
4.303-06 2.664-06 494.
1.124-05 6.955-06 494.
1.960-05 1.213-05 W
451.
451.
4.446-06 2.752-06 451.
1.800-05 1.164-05 451.
2.973-05 1.841-05 WNW 451.
451.
4.163-06 2.577-06 451.
2.961-05 1.833-05 451.
4.328-05 2.679-05 NW 4ES.
485.
4.160-06 2.575-06 485.
2.891-05 1.790-05 485.
5.130-05 3.175-05 NNW 640.
640.
2.919-06 1.807-06 640.
1.860-05 1.151-05 640.
2.697-05 1.669-05 l
QUAD-CIllES 182 SITE METEOROLOGICAL DATA 1/74 - 12/75 ny al mm O <.
mH 3: (n.
I (D H mO
- c Z HH
@H CD U1
~
O O
i r
i TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1&2 i
MAXIMUM OFFSITE FANITE PLUME _GAE A_ DOSE FACTORS FOR MR 87 00WNWIND RESTRICTED ELEVATED (STACK) RELEASE MIXED MODE (VENT) RELEASE G%OUND LEVEL RE:LE ASE
-' DIRECTION AREA BOUND RADIUS S
58AR RADIUS V
VSAR RADIUS G
GBAR (METERS) (METERS) (MRAD /VR)/(UCl/SEC) (METERS) (MR A0f Y R )/ (UCl/$f C_),
( ME T E_R3 ),(MRAD /YR)/(UCI/SEC)
()C
-J N
064 864.
8.531-04 6.236-04 864.
3.740-03 2.710-03 8G4.
6.768-03 4.887-03 NNE 1029.
1029.
9.989-04 7.301-04 1029.
2.030-03 1.494-03 1029.
2.224-03 1.606-03 C3 I#
NE 1212.
1212.
6.913-04 5.051-04 1212.
f.967-03 1.424-03
- 1212, 2.324-03 1.676-03 b
Ed ENE 1367.
1367.
3.785-04 2.765-04 1367.
1.397-03 1.011-C3 1367.
1.863-03 1.346-03 H
i hJ E
1170.
1170.
4.711-04 3.443-04 1170.
1.388-03 1.005-03 1170.
1.957-03 1.413-03 63 ESE 1170.
1170.
5.879-04 4.096-04 1170.
1.623-03 1.320-03 1170.
2.349-03 1.696-03 y
I SE 1 89.
1189.
7.291-04 5.328-04 1189.
2.418-03 1.750-03 s189.
3.246-03 2.344-03 m
l SSE 1422.
1422.
4.858-04 3.549-04 1422.
1.408-03 1.020-03 1422.
2.089-03 1.509-03 l
5 1193.
1198.
5.031:04 3.677-04 1198.
1.172-03 8.500-04 1198.
2.214-03 1.598-03 i
SSW 1024.
1024.
5.527-04 4.037-04 1024.
1.138-03 8.257-04 1024.
1,842-03 1.330-03 SW 654.
654.
8.411-04 6.148-04 654.
2.054-03 1.488-03 654.
4.334-03 3 129-03 WSW 494.
494.
1.428-03 1.044-03 494.
3.322-03 2.409-03 494 5.520-03 3.985-03 W
451.
451.
1.487-03 1.087-03 451.
5.442-03 3.938-03 451.
8.387-0) 6.054-03 WNW 451.
451.
1.390-03 1.016-03 451.
S.411-03 6.000-03 451.
1.212-02 8.749-03 NW 485.
485.
1.389-03 1.015-03 485.
8.166-01 5.903-03 485.
1.423-02 1.027-02 j
NNW 640.
640.
9.672-04 7.071-04 640.
5.160-03 3.746-03 640.
7.397-03 5.339-03 QUAD-CITIES 182 SITE METEOROLOGICAL DATA 1/74 - 12/75 ty m MM l
i n4 MH T 01 WH MO i
- D :25 HH
@H C0 U1 4
I J
l
O b
m N)
TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1 & 2 MARIMUM OF F SI T E F INI T E P LtJME_GA,MMA_ DOSE _F_ACTORU0R_KR _88_.
DOWNWIND RESTRICTED ELEVATED l STACK) RELEASE MizfD MODE (VENT) RELEASE GROUND LEVEL RELEASE DIRECTION AREA BOUND RE6TuS S
s8AR RabluS
-v
- V8Ai' RADIUS
~~G c84R (METER 3) (METERS) (MRAD /YR)/(UCI/SEC)_ (METERS) (MRAD /VR)/(UCI/SEC) (METERS) (MR ADf YR )/ (UCl / SEC )
()C N
864.
864.
2.135-03 1.647-03 864.
9.137-03 6.971-03 864.
1.636-02 1.244-02
%J h3 NNE 1029 1029.
2.535-03 1.956-03 1029.
5.143-03 3.938-03 1029.
5.449-03 4.149-03 f
I, NE 1212.
1212.
1.764-03 1.361-03 1212.
4.977-03 3.002-03 1212.
5.803-03 4.416-03 O
ENE 1367.
1367 9.697-04 7.478-04 1367.
3.550-03 2.710-03 1367.
4.669-03 3.555-03 Hd E
1170.
1170.
1.193-03 9.200-04 1170.
3.454-03 2.640-03 1170.
4.797-03 3.652-03 v2 ESE 1170.
1170.
1.484-03 1.145-03 1170.
4.541-03 3.468-03 1170.
5.762-03 4.387-03 SE 1109.
1189.
1.052-03 1.428-03 1189.
6.050-03 4.619-03 1189.
7.984-03 6.079-03 u)
SSE 1422.
1422.
1.252-03 9.654-04 1422.
3.598-03 2.750-03 1422.
5.247-03
- 3.996-03 S
1198.
1198.
1.290-03 9.947-04 1198.
2.952-03 2.260-03 1198.
5.496-03 4.182-03 SSW 1024.
1024.
1.407-03 1.086-03 1024.
2.825-03 2.163-03 1024.
4.488-03 3.415-03 SW 654.
654.
2.103-03 1.622-03 654.
4.995-03 3.821-03 654.
1.040-02 7.900-03 WSW 494.
494.
3.549-03 2.738-03 494.
8.043-03 6.154-03 494 1.311-02 9.965-03 i
W 451.
451.
3.672-03 2.833-03 451.
1.304-02 9.942-03 451.
1.986-02 1.508-02 i
WNW 451.
451.
3.433-03 2.648-03 451.
2.012-02 1.531-02 451.
2.878-02 2.184-02 NW 485.
485.
3.442-03 2.656-03 435.
1.963-02 1.494-02 485.
3.396-02 2.576-02 NNW 640.
640.
2.407-03 1.857-03 640.
1.256-02 9.568-03 640.
1.777-02 1.349-02 QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75 t) N MM O<
MH 3: U) to m MO NZ HH
@H 00 U1
TABLE 7.2-8 (Cont'd)
QUAD -CITIES 1&2 max! mum OFrSITE FINITE PLUME GAMMA DOSE FACTORS FOR KR 89 DOWNWIND RESTRICTED
.E LEV. ATED(ST ACK) RELEASE MIXED MODE (VENT) RELEASE GRDUND LEVEL RELQSE, DIRECTION AREA ROUND RADIUS S
58AR RADIUS V
VSAR RADIUS G
GBAR O
(METERS) (METERS) (MRAD /vR)/(UCI/SEC) (METERS) (MRAD /YR)/(UC1/SEC) (METERS) (MRAD /YR)/(UCl/SEg)
C N
864 864.
8.05G-04 5.943-04 864.
2.160-03 1.576-03 864.
3.780-03 2.753-03 h
PJ NNE 1029.
1029.
6.806-04 5.020-04 1029.
8.818-04 6.449-04 1029.
8.991-04 6.552-04 L
1 NE 1212.
1212.
4.23G-04 3.124-04 1212.
5.550-04 4.057-04 1212.
5.668-04 4.130-04 0
ENE 1367.
1367.
2.140-04 1.578-04 1367.
3.773-04 2.755-04 1367.
4.751-04 3.462-04 y
E 1870.
1170.
3.486-04 2.571-04 1970.
6.405-04 4.677-04 1170.
8.439-04 6 148-04 s
ESE 1170.
1870.
4.631-04 3.415-04 1170.
8.0*.5-04 5.882-04 1170.
1.025-03 7.469-04 M
SE 1189.
1189.
5.015-04.3.698-04 1189.
9.158-04 6.687-04 1189.
1.259-03 9.173-04 M
SSE 1422.
1422.
2.346-04 1.729-04 1422.
3.697-04 2.702-04 1422.
5.091-04 3.705-04 S
1898.
1198.
2.758-04 2.034-04 1198.
4.251-04 3.107-04 1998.
6.592-04 4.802-04 SSW 1024 1024.
3.404-04 2.511-04 1024.
5.820-04 4.253-04 1024 8.797-04 6.408-04 SW 654.
- 654, 7.494-04 5.528-04 654.
1.365-03 9.976-04 654.
2.595-03 f.890-03 WSW 494 494.
1.414-03 1.043-03 494.
2.503-03 1.830-03 494 4.276-03 3.114-03 W
451.
451.
1.745-03 1.287-03 451.
4.334-03 3.164-03 451.
6.959-03 5.067-03 WNW 451.
451.
1.630-03 1.202-03 451.
5.883-03 4.291-03 451.
8.959-03 6.523-03 NW 485.
485.
1.535-03 1.132-03 485.
4.917-03 3.588-03 485.
8.718-03 6.347-03 NNW 640.
640.
9.993-04 7.372-04 640.
2.760-03 2.014-03 640.
4.153-03 3.024-03 QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75 gg MM O<H M
l H
i MO l
- U Z I
HH DH 00 1
TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1&2 MAXIMUM OFFSITE FINITE PLUME CAMMA DOSE FACTORS FOR KR 90 DOWNWINO RESTRICTED ELEVATED (STACK) RELEASE MIXED MODE (VENT) RELEASE GROUND LEVEL RELEASE DIRECTION AREA 80UND RADIUS S
58AR RADIUS V
V8AR RADIUS G
G84R (METERS) (METERS) (MRAD /VR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /YR)/(LCl/SEC) oC q
N 864 864.
1.015-04 7.277-05 864.
1.480-04 1.047-04 864.
1.835-04 1.295-04 a
U N
NNE 1029.
1029.
5.079-05 3.641-05 1029.
3.336-05 2.365-05 1029.
2.365-05 1.669-05 NE 1212.
1212.
2.263-05 1.622-05 1212.
1.122-05 7.957-06 1212.
5.414-06 3.023-06 b
l h
ENE 13G7.
1367.
0.713-06 6.242-06 1367.
7.049-06 4.989-06 1367.
6.174-06 4.360-06 H
E 1170.
1170.
2.397-05 1.718-05 1170.
2.571-05 1.819-05 1170.
2.491-05 1.759-05 63 i
on ESE 1170.
1170.
3.671-05 2.630-05 1170.
3.368-05 2.383-05 1170.
3.320-05 2 343-05 y
SE 1189.
1189.
3.286-05 2.354-05 1189.
2.564-05 1.815-05 1189.
2.389-05 1.687-05 uj i
SSE 1422.
1422.
6.624-06 4.744-06 1422.
4.173-06 2.957-06 1422.
3.379-06 2 387-06 S
1198.
1198.
1.289-05 9.233-06 1198.
9.167-06 6.494-06 1198.
8.062-06 5.692-06 i
SSw 1024.
1024.
2.230-05 1.598-05 1024.
2.678-05 1.895-05 1024.
3.068-05 2.166-05 SW 654.
654.
1.085-04 7.776-05 654.
1.430-04 1.012-04 654.
1.925-04 1.358-04 I
WSW 494 494.
2.325-04 1.666-04 494.
3.155-04 2.237-04 494.
4.241-04 2.992-04 w
451.
451.
4.430-04 3.175-04 451.
7.115-04 5.036-04 451.
8.888-04 6.270-04
)l WNw 451.
451.
4.456-04 3.194-04 451.
7.985-04 5.648-04 451.
9.518-04 6 715-04 Nw 485.
485.
3.687-04 2.644-04 485.
5.259-04 3.722-04 485.
6.338-04 4.470-04 NNW 640.
640.
1.869-04 1.340-04 640.
2.602-04 1.841-04 640.
2.887-04 2.036-04 QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75 0h n <:
MH 1
3 ut j
tD H MO
- D Z i
HH
@H CD U1 I
l I
i i
W TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1&2 MAXIMUM OFFSITE FINITE PLUME GAMMA DOSE FACTORS FOR XE131M DOWNWIND RESTRICTED ELEVATED (STACK) RELEASE MIXED MODE (VENT) RELEASE _
CROUND LEVEL RELEASE DIRECTION AREA BOUND RADIUS S
SBAR RADIUS V
VSAR RADIUS G
GBAR (METERS) (METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCI/SEC)
()C 4
N 864.
864.
7.85G-06 2.614-06 864 1.679-04 2.624-05 864.
3.832-04 5.531-05 h
NNE 1029.
1029.
9.733-06 3.179-06 1029.
6.641-05 1.193-05 1029.
1.168-04 1.748-05 y
l NE 1212.
1212.
7.163-06 2.273-06 1212.
8.439-05 1.369-05 1212.
1.318-04 1.943-05 o
Fd ENE 1367.
1367.
3.903-06 1.252-06 1367.
6.241-05 1.007-05 1367.
1.018-04 1.527-05 H
E 1170.
1170.
4.399-06 1.483-06 1170.
5.307-05 8.942-06 1170.
1.018-04 1 533-05 8
ESE 1170.
1170.
5.762-06 1.874-06 1170.
7.659-05 1.244 05 1170.
1.236-04 1.852-05 SE 1189.
1189.
7.180-06 2.348-06 1189.
1.039-04 1.b79-05 1189.
1.695-04 2.554-05 m
SSE 1422.
1422.
5.280-06 1.649-06 1422.
5.711*05 9.571-06 1422.
1.120-04 1.695-05 S
1998.
1198.
4.792-06 1.620-06 1198.
3.897-05 6.984-06 1198.
1.270-04 1 859-05 i
SSW 1024.
1024.
4.744-06 1.703-06 1024.
3.457-05 6.363-06 1024.
1.004-04 1.480-05 SW 654 654.
7.621-06 2.564-06 654.
7.147-05 1.217-05 654.
2.691-04 3.740-05 WSW 494.
494.
1.360-05 4.359-06 494.
1.144-04 1.930-05 494 3.309-04 4.619-05 W
451.
451.
1.325-05 4.404-06 451.
2.578-04 3.854-05 451.
5.281-04 7.239-05 WNW 451.
451.
1.295-05 4.169-06 451.
4.716-04 6.683-05 451.
8.198-04 1.099-04 NW 485.
485.
1.344-05 4.232-06 485.
4.588-04 6.511-05 485.
9.954-04 1.324-04 NNW 640.
640.
8.598-06 2.912-06 64G.
2.731-04 3.992-05 640.
4.793-04 6.570-05 0%
QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75 mm o<
MH 3: U1 i
CD H MO I
- D Z HH
@H 00 U1
m j
%/
TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1&2 MAXIMUM OFFSITE FINITE PLUME GAMMA DOSE FACTORS FOR XE133M DOWNWIND RESTRICTED ELEVATED (STACK) RELEASE MIXED MODE (VENT) RELEASE GROUND LEVEL RELEASE DIRECTION AREA BOUND RADIUS S
S8AR RADIUS V
VBAR RADIUS G
GEIII (METERS) (METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /YR)/(UC1/SEC) (METERS) (MRAD /YR)/(UCI/SEC)
O h
-4 N
864.
864.
3.220-05 1.557-05 864.
3.141-04 1.020-04 864.
6.591-04 1.972-04 NNE 1029.
1029.
3.913-05 1.883-05 1029.
1.437-04 5.239-05 1029.
2.087-04 6.491-05 ty f
NE 1212.
1212.
2.794-05 1.333-05 1212.
1.640-04 5.514-05 1212.
2.315-04 7.088-05 I
H ENE 1367.
1367.
1.539-05 7.367-06 1367.
1.206-04 4.034-05 1367.
1.021-04 5.677-05 O
'4 E
1170.
1170.
1.82G-05 8.866-06 1170.
1.074-04 3.726-05 1170.
1.831-04 5.730-05 y'
ESE 1170.
1170.
2.307-05 1.109-05 1170.
1.490-04 5.013-05 1170.
2.211-04 6.889-05 s
SE 1889.
1189.
2.889-05 1.390-05 1189.
2.011-04 6.735-05 1189.
3.049-04 9.554-05 M
SSE 1422.
1422.
2.025-05 9.614-06 1422.
1.148-04 3.966-05 1422.
2.022-04 6.362-05 W
S 1198.
1198.
1.995-05 9.692-06 1998.
8.410-05 3.061-05 1198.
2.214-04 6.729-05 SSW IC24.
- 1024, 2.100-05 1.037-05 1024.
7.677-05 2.847-05 1024.
1.765-04 5.402-05 i
SW 654.
654.
3.160-05 1.533-05 654.
1.463-04 5.121-05 654.
4.449-04 1.273-04 l
WSW 494.
494.
5.367-05 2.568-05 494.
2.321-04 8.067-05 494.
5.497-04 1.581-04 i
W 451.
451.
5.428-05 2.625-05 451.
4.605-04 1.431-04 451.
8.607-04 2.421-04 I
WNW 451.
451.
5.134-05 2.460-05 451.
7.960-04 2.332-04 451.
1.305-03 3.564-04 NW 485.
485.
5.208-05 2.479-05 485.
7.754-04 2.275-04 485.
1.571-03 4.246-04 NNW 640.
640.
3.590-05 1.745-05 640.
4.761-04 1.444-04 640.
7.807-04 2.196-04 I
QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75 h$
n<
MH 3: (n tn H MO 22 HH
@H CO U1
f
{}
U b
TABLE 7.2-8 (Cont'd) 1 I
f QUAD-CITIES 1&2 l
1 1
MAXIMUM OFFSITE FINITE PLUME GAMMA DOSE FACTORS FOR XE133 DOWNW1hD RESTRICTED ELEVATED (STACK) RELEASE MIXED MODE (VENT) RELEASE GROUND LEVEL RELEASE DIRECTION AREA BOUND RADIUS S
S8AR RADIUS V
VBAR RADIUS G
CEIAR (METERS) (MEiERS) (MRAD /VR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCl/SEC)
N 864 664.
3.323-05 1.268-05 864.
3.515-04 1.056-04 864.
7.318-04 2.092-04 C
,-J 1
PJ NNE 1029.
1029.
4.043-05 1.538-05 1029.
1.619-04 5.209-05
- 1029, 2.347-04 6.892-05 y
f I
NE 1282.
1212.
2.900-05 1.100-05 1212.
1.840-04 5.641-05 1212.
2.597-04 7.550-05
[
ENE 1367.
1367.
- 1. 60'J-05 6.101-06 1367.
1.361-04 4.167-05 1367.
2.053-04 6.041-05 b
E 1170.
1170.
1.882-05 7.204-06 1170.
1.214-04 3.800-05 1170.
2.069-04 6.110-05 H
ESE f170.
1170.
2.390-05 9.085-06 1170.
1.677-04 5.149-05 1170.
2.494-04 7.343-05 d
SE 1189.
1189.
2.995-05 1.140-05 1189.
2.263-04 6.928-05 1189.
3.447-04 1.018-04 m
SSE 1422.
1422.
2.128-05 8.026-06 1422.
1.294-04 4.035-03 1422.
2.285-04 6.766-05 u)
S 1998.
1198.
2.059-05 7.887-06 1198.
9.490-05 3.053-05 1190.
2.481-04 7.179-05 i
SSw 1024 1024.
2.148-05 8.319-06 1024.
8.670-05 2.821-05 1024.
1.977-04 5.746-05 i
SW 654.
654.
- 3. 23 ts-0 5 1.230-05 654.
1.635-04 5.127-05 654.
4.873-04 1.351-04 1
WSw 494 494.
5.596-05 2.121-05 494.
2.566-04 7.985-05 494.
6.018-04 1.673-04 w
451.
451.
5.613-05 2.143-05 451.
5.031-04 1.460-04 451.
9.354-04 2.559-04 j
WNW 451.
- 451, 5.329-05 2.022-05 451.
8.636-04 2.415-04 451.
1.403-03 s.755-04 i
NW 485.
485.
5.444-05 2.056-05 485.
8.414-04 2.355-04 485.
1.683-03 4.469-04 l
i NNw 640.
640.
3.675-05 1.407-05 640.
5.222-04 1.497-04 640.
8.494-04 2.325-04 k
QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75 o<
MH l
3: u) to H MO
- D Z WH b
i I
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0
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&l TABLE 7.2-8 (Cont'd) l QUAD-CITIES 1&2 l
hAXIMUM OFFSITE FINITE PLUME CAMMA DOSE FACTORS FOR XE135M i
DOWNWIND RESTRICTED ELEVATED (STACK) RELEASE MINED MODE (VENT) RELEASE GROUND 6EVEL RELEASE DIRECTION AREA BOUND RADIUS S
SBAR RADIUS V
V8AR RADIUS G
G84R
=-(METERS)
(METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /VR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCI/SEC)
K)
C N
864.
864.
3.872-04 2.393-04 864.
1.720-03 1.052-03 864.
3.220-03 1.964-03 h
h3 NNE 8029 1029.
4.150-04 2.564-04 1029.
8.409-04 5.166-04 1029.
9.696-04 5.923-04 i
NE 1212.
1212.
2.783-04 1.720-04 1212.
7.184-04 4.404-04 1212.
8.897-04 5.432-04 O
F" ENE 1367.
13G7.
1.488-04 9.193-05 1367.
4.963-04 3.041-04 1367.
7.041-04 4.302-04 H
E 1170.
1170.
2.000-04 1.236-04 1170.
5.748-04 3.525-04 1170.
8.513-04 5.202-04 d
ESE 1170.
1810.
2.540-04 1.570-04 1170.
7.447-04 4.564-04 1870.
1.021-03 6.237-04 m
SE 1189.
1189.
3.027-04 1.871-04 1189.
9.546-04 5.850-04 1189.
1.382-03 8.442-04 U1 l
SSE 1422.
1422.
1.838-04 1.136-04 1422.
4.911-04 3.013-04 1422.
7.799-04 4.767-04 S
1198.
1198.
1.966-04 1.215-04 1198.
4.539-04 2.788-04 1190.
8.818-04 5.383-04 SSW 1024 1024.
2.234-04 1.381-04 1024.
4.870-04 2.992-04 1024.
8.318-04 S.078-04
)
SW 654.
654.
3.810-04 2.355-04 654.
9.794-04 6.000-04 654.
2.151-03 1.310-03 WSW 494 494.
6.701-04 4.141-04 494.
1.647-03 1.010-03 494.
2.933-03 1.786-03 W
451.
- 451, 7.248-04 4.480-04 451.
2.815-03 1.721-03 451.
4.546-03 2.766-03 4
WNW 451.
451.
6.778-04 4.188-04 451.
4.326-03 2.638-03 451.
6.456-03 3.923-03 NW 485.
485.
6.649-04 4.109-04 485.
4.068-03 2.481-03 485.
7.321-03 4.446-03 l
NNW 640.
640.
4.526-04 2.797-04 640.
2.440-03 1.490-03 640.
3.637-03 2 213-03 i
a j
QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75
%y O<
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TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1&2 MAXIMUM OFFSITE FINITE PLUME GAMMA DOSE FACTORS FOR XE135 4
DOWNWIND RESTRICTED ELEVATED (STACK) RELEASE mixed MODE (VENT) RELEASE GROUND LEVEL RELE A?iE DIRECTION AREA EQUND RADIUS S
58AR RADIUS V
VBAR RADIUS G
GBAR (r.1E T E RS ) (METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCl/SEC) oC f
N 864.
864.
2.814-04 1.522-04 864.
1.627-03 8.738-04 864 3.046-03 1.633-03 N
NNE 1029.
1029.
3.387-04 1.831-04 1029.
8.676-04 4.670-04 1029.
1.015-03 5.448-04 f
1 NE 1212.
1212.
2.389-04 1.291-04 1212.
8.843-04 4.753-04 1212.
1.097-03 5.886-04 n
N ENE 1367 1367 1.320-04 7.135-05 1367.
6.446-04 3.464-04 1367.
8.844-04 4.746-04 H
E 1170.
1170.
1.598-04 8.643-05 1170.
6.063-04 3.260-04 1170.
8.982-04 4.820-04 8
H ESE 1170.
1170.
1.995-04 1.078-04 1170.
8.064-04 4.334-04 1170.
1.078-03 5.784-04 g
SE 1189.
1189.
2.499-04 1.351-04 1189.
1.081-03 5.807-04 1189.
1.497-03 8.034-04 y3 SSE 1422.
1422.
1.717-04 9.281-05 1422.
6.407-04 3.445-04 1422.
9.941-04 5.335-04 5
1190.
1198.
1.743-04 9.424-05 1198.
5.054-04 2.720-04 1198.
1.040-03 5.576-04 SSW 1024.
1024.
1.874-04 1.014-04 1024.
4.747-04 2.556-04 1024 8.404-04 4.507-04 Sw C54.
654.
2.773-04 1.499-04 654.
8.413-04 4.525-04 654 1.934-03 1.036-03 WSW 494.
494.
4.638-04 2.508-04 494.
1.325-03 7.127-04 494.
2.413-03 1.292-03 W
451.
451.
4.760-04 2.575-04 451.
2.257-03 1.211-03 451.
3.660-03 1.959-03 WNW 451.
451.
4.452-04 2.408-04 451.
3.587-03 1.922-03 451 5.316-03 2.844-03 NW 485.
485.
4.475-04 2.420-04 485.
3.499-03 1.875-03 485.
6.296-03 3.367-03 l
NNW 640.
640.
3.161-04 1.709-04 640.
2.247-03 1.205-03 640.
3.309-03 1.771-03 QUAD-C1 TIES 142 SITE METEORDLOGICAL DATA 1/74 - 12/75
$(
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v TABLE 7.2-8 (Cont'd)
QUAD-CITIES 1&2 MAXIMUM OFFSITE FINITE PLUME GAMMA DOSE FACTORS FOR XE137 DOWNWIND RESTRIC7ED ELEVATED (STACK) RELEASE MIXED MODE (VENT) RELEASE GROUND LEVEL RELEAtE DIRECTION AREA SOUND HADIUS S
SBAR RADIUS V
VSAR RADIUS G
CNR (METEkSi (METERS) (MRAD /VR)/(UCI/SEC) (METERS) (MRAD /YR)/(UCI/SEC) (METERS) (MRAD /YR)/(UC1/SEC)
K)
C h
Q N
864.
864.
1.103-04 7.148-05 864.
3.458-04 2.226-04 864.
6.269-04 4 031-04 NNE 1029.
1029.
9.70G-05 6.286-05 1029.
1.429-04 9.211-05 1029.
1.551-94 9.976-05 i
N NE 1212.
1212.
6.142-05 3.977-05 1212.
9.384-05 6.046-05 1212.
1.041-04 6 693-05 O
ENE 1367.
1367.
3.14G-05 2.037-05 1367.
6.455-05 4.156-05 13G7.
8.642-05 5.557-05 y
b E
1170.
1170.
4.952-05 3.206-05 1170.
1.038-04 6.686-05 1170.
1.438-04 9.247-05 g
ESE 1170.
1170.
6.538-05 4.233-05 1170.
1.306-04 8.411-05 1170.
1.739-04 1.113-04 m
e SE 1189.
1189.
7.175-05 4.646-05 1189.
1.515-04 9.758-05 1189.
2.184-04 1.404-04 U1 SSE 1422.
1422.
3.533-05 2.287-05 1422.
6.340-05 4.084-05 1422.
9.355-05 6.016-05 5
1198.
1198.
4.051-05 2.623-05 1198.
7.053-05 4.545-05 1198.
1.176-04 7.561-05 SSW 1024.
1024.
4.912-05 3.181-05 1024.
9.325-05 6.007-05 1024.
1.463-04 9.534-05 j
SW 654.
654.
1.038-04 6.723-05 654.
2.145-04 1.382-04 654 4.306-04 2.768-04 i
i WSw 494.
494.
1.944-04 1.259-04 494.
3.884-04 2.503-04 494 6.907-04 4.441-04 W
451.
- 451, 2.344-04 1.518-04 451.
6.798-04 4.377-04 451.
1.116-03 7.175-04 j
WNW 451.
451.
2.191-04 1.419-04 451.
9.533-04 6.133-04 451.
1.467-03 9.426-04 NW 485.
485.
2.071-04 1.341-04 485.
8.128-04 5.230-04 485.
1.471-03 9.457-04 NNW 640.
640.
1.355-04 8.779-05 640.
4.535-04 2.918-04 640.
6.963-04 4.476-04 1
I QUAD-CITIES 1A2 SITE METEOROLOGICAL DATA 1/74 - 12/75 oz MM i
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QUAD-CITIER 1&2 MAXIMUM OFFSITE FINITE PLUME GAMMA DOSE FACTORS FOR AR 41 DOWNWIND REJTRICTED ELEVATED (STACK) RELEASE MIXED MODE (VENT) RELEASE GROUND LEVEL RELEASE DIRECTION AREA BOUND AADIUS S
SBAR RADIUS V
V8AR RADIUS G
GBAR (METERS) (METERS) (MRAD /YR)/(UC1/SEC) (METERS) (MRAD /YR)/(UCl/SEC) (METERS) (MRAD /YR)/(UCI/SEC)
OC N
864.
864.
1.279-03 9.016-04 G64.
5.818-03 4.102-03 864.
1.057-02 7.449-03 U
NNE 1029.
1029.
1.507-03 1.062-03 1029.
3.201-03 2.256-03 1029.
3.492-03 2.462-03 q
t0 NE 1212.
1212.
1.044-03 7.361-04 1212.
3.109-03 2.192-03 1212.
3.698-03 2.607-03 b
8 ENE 1367.
1367.
5.741-04 4.048-04 1367.
2.218-03 1.564-03 1367.
2.965-03 2.090-03 H
E 1170.
1170.
7.079-04 4.991-04 1970.
2.172-03 1.531-03 1170.
3.084-03 2.175-03
- 3 N
ESE 1170 1170.
8.827-04 6.223-04 1170.
2.862-03 2.018-03 1170.
3.703-03 2.611-03 y
I SE 1989.
1189.
1.098-03 7.742-04 1189.
3.808-03 2.685-03 1189.
5.128-03 3.615-03 g3 i
SSE 1422.
1422.
7.391-04 5.211-04 1422.
2.233-03 1.574-03 1422.
3.329-03 2.347-03 5
1198.
1198.
7.619-04 5.371-04 1198.
1.836-03 1.294-03 1198.
3.517-03 2.480-03 SSW 1024 1024.
8.349-04 5 886-04 1024.
1.764-03 1.244-03 1024 2.891-03 2.038-03 SW 654.
654.
1.258-03 8.872-04 654.
3.150-03 2.221-03 654.
6.756-03 4.763-03 i
WSW 494.
494.
2.140-03 1.509-03 494.
5.085-03 3.585-03 494 8.554-03 6.031-03 W
451.
451.
2.219-03 1.564-03 451.
8.373-03 5.903-03 451.
1.300-02 9.168-03 WNW 451.
451.
2.074-03 1.462-03 451.
1.302-02 9.179-03 451.
1.885-02 1.329-02 i
NW 485.
485.
2.076-03 1.463-03 485.
1.266-02 8.926-03 465.
2 219-02 1.565-02 NNW 640.
640.
1.443-03 1.017-03 640.
8.046-03 5.673-03 640.
1.155-02 8.142-03 QUAD-CITIES 142 SITE METEOROLOGICAL DATA 1/74 - 12/75 g
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..i-a QUAD-CITIES REVISION 11 DECEMBER 1985 8.0 RADIOACTIVE EFFLUENT TREATMENT SYSTEMS, MODELS FOR SETTING GASEOUS AND LIQUID EFFLUENT MONITOR ALARM AND TRIP SETPOINTS, AND ENVIRONMENTAL RADIOLOGICAL MONITORING TABLE OF CONTENTS PAGE 8.1 GASEOUS RELEASES 8.1-1 8.1.1
System Design
8.1-1 8.1.1.1 Gaseous Radwaste Treatment System 8.1-1 l
8.1.2 Alarm and Trip Setpoints 8.1-1 8.1.3 Main Chimney Releases 8.1-3 8.1.3.1 Chimney Noble Gas Monitors 8.1-3 8.1.3.2 SJAE Off-Gas Monitors 8.1-5 l
8.1.3.3 Allocation of Effluents from Common Release Points 8.1-6 l
=
8.1.4 Reactor Building Ventilation Stack Releases 8.1-7 8.1.4.1 Ventilation Stack Monitors 8.1-7 8.1.4.2 Allocation of Effluents from Common Release Points 8.1-8 8.1.5 Symbols Used in Section 8.1 8.1-9 8.1.6 Constants Used in Section 8.1 8.1-11 8.2 LIQUID RELEASES 8.2.1 8.2.1
System Design
8.2-1 8.2.2 Alarm ~Setpoints 8.2-1 8.2.3 Radwaste Discharge Line Releases 8.2-2 8.2.3.1 Radwaste Discharge Monitor 8.2-2 8.2.3.2 Allocation of Effluents from Common i
Release Points 8.2-3 8'.2.3.3 Administrative and Procedural Controls for Radwaste Discharges 8.2-4 8.2.4 Service Water Header Releases 8.2-5 8.2.4.1 Service Water Effluent Monitors 8.2-5 8.2.5 Determination of Initial Dilution Stream Flow Rates 8.2-6 8.2.6 Symbols Used in Section 8.2 8.2-7 8.3, SOLIDIFICATION OF WASTE / PROCESS
'O CONTROL PROGRAM 8.3-1 S.4 ENVIRONMENTAL RADIOLOGICAL MONITORING 8.4-1 1
8-i L
QUAD-CITIES REVISION 11 DECEMBER 1985 ODCM LIST OF TABLES FOR QUAD-CITIES SECTION 8.0 l
NUMBER TITLE PAGE 8.4-1 Radiological Monitoring Program 8.4-2 8.4-2 Reporting Levels For Radioactivity Concentrations In Environmental Samples 8.4-6 8.4-3 Maximum values For The Lower Limits of Detection (LLD) 8.4-7 f
5 O
l i O 8-ii i
l
QUAD-CITIES REVISION 11 DECEMBER 1985 O
l ODCM LIST OF FIGURES FOR QUAD-CITIES SECTION 8.0 NUMBER TITLE 8.1-1 Simplified Gaseous Radwaste and Gaseous Effluent Flow Diagram 8.2-1 Simplified Liquid Radwaste Processing Diagram 8.2-2 Simplified Liquid Effluent Flow Diagram 8.3-1 Simplified Solid Radwaste Processing Diagram 8.4-1 Fixed Air Sampling Sites and Outer Ring TLD Locations 8.4-2 Inner Ring TLD Locations l
8.4-3 Milk, Fish, Water and Sediment Sample Locations l
l f
L O
O 8-iii
CUAD-CITIES REVISION 11 DECEMBER 1985 7-i
/
\\/
8.0 RADIOACTIVE EFFLUENT TREATMENT SYSTEMS, MODELS FOR SETTING GASEOUS AND LIQUID EFFLUENT MONITOR ALARM AND TRIP SETPOINTS, i
AND ENVIRONMENTAL RADIOLOGICAL MONITORING 8.1 GASEOUS RELEASES 8.1.1
System Design
A simplified gaseous radwaste and gaseous effluent flow diagram is provided in Figure 8.1-1.
8.1.1.1 Gaseous Radwaste Treatment System A gaseous radwaste treatment system shall be any system designed and installed to reduce radioactive gaseous effluents by collecting
()
primary coolant system off-gases from the primary system and pro-viding for delay or holdup for the purpose of reducing the total radioactivity prior to release to the environment.
8.1.2 Alarm and Trip Setpoints Alarm and trip setpoints of gaseous effluent monitors at the principal points of release of ventilation exhaust air containing radioactivity are established to ensure that the release limits of 10 CFR 20 are not exceeded.
The setpoints are found by solving Equations 2.6 and 2.7 for each class of release.
l For this evaluation the radioactivity mixture in the exhaust air is assumed to have the composition of gases listed in Table 3-3 from " Technical Derivation of BWR 1971 Design Basis Radioactive Material Source Terms", NEDO-10871, March 1973, General Electric Company.
This mixture of radioactive gases O
(_)
is representative of the activity found at the point of release from the fuel with no radioactive decay accounted for.
8.1-1 t
i
QUAD-CITIES REVISION 11 DECEMBER 1985 t
Equation 2.6 is rewritten using the fractional composition of l
each nuclide, f, and a total release rate, O ' f r each class:
i t
1.11 Q
I8i*f) +Q lVi* f)
<500 " **
ts i
tv i
(8.1) f Fractional Radionuclide Composition i
The release rate of radionuclide i divided by the total release of all radionuclides.
O Total Release Rate, Stack Release (pCi/sec) ts The release rate for all radionuclides due to a stack release.
O Total Release Rate, Vent Release (pCi/sec) tv The release rate for all radionuclides
{\\m-due to a vent release.
for each class of release Equation 8.1 can be solved for Qt for releace limit determinations.
Similarly, Equation 2.7 can be rewritten:
l
~
{t_i "(X/Q)s Q f
tv i eXP(- A R/3600u )
f
+ IX/0)v O i **PI-A R/3600u )
i y
i s
ts 1
f f
<3000 * **
(8.2)
~
si+v0tv i
+ 1.11 SQ i
g
.)
Equation 8.2 can be solved for Q f r each class of release and t
a corresponding release limit be determined.
The most conservative release limit determined from Equations 8.1 and 8.2 will be used in selecting the appropriate alarm and trip setpoints for each class of release.
The exact settings will be selected to ensure that 10 CFR 20 l
limits are not exceeded.
l l
8.1-2 l
QUAD-CITIES REVISION 11 DECEMBER 1985
(~)
V Surveillance. frequencies for gaseous effluent monitors will be as stated in Table 4.2-4 of the Technical Specifications.
Calibration methods will be consistent with the definitions found in Section 1.0 of the Technical Specifications.
8.1.3 Main chimney Releases 8.1.3.1 Chimney Noble Gas Monitors Releases of radioactive noble gases from the main chimney release point are continuously monitored by a General Electric (GE) off-line monitoring system consisting of two instrument channels, each of which uses a scintillation detector as its sensing element.
Samples of the effluent stream are taken high in the chimney, where good mixing is ensured, and drawn through a constant flow-and-pump network, past the detectors.
)
The detector equipment part numbers are RE 1/2-1731A and RE l
1/2-1731B.
Each monitoring channel consists of a 2-inch by 2-inch sodium iodide thallium activated scintillation detector, shielded l
i f'
sample chamber, pulse preamplifier, and process radiation (log count) monitor with integral power supply for providing l
high voltage to the detector.
The channels share a common l
recorder and common trip auxiliaries unit whose output initiate l
high radiation alarm annunciations.
The recorder, alarms, l
and remote control switches for the chimney gas monitoring I
system are located in the main control room.
l f
The monitor display has a logarithmic scale with a range of
~1 6
10 to 10 counts per second.
l 8.1-3 l
l l
1
QUAD-CITIES REVISION 11 DECEMBER 1985 O
In addition to the GE noble gas monitors, the gas sample is routed through a filter paper on which particulates are deposited, through a charcoal cartridge which traps the iodines, and through Eberline low and medium range noble gas detectors.
Under accident conditions, the above pathway can be bypassed l
and the sample routed through an Eberline/Victorcen system l
which has an Eberline high range noble gas monitor and a Victoreen postaccident particulate and iodine sampler.
The Eberline low and medium range noble gas detectors view the same volume, while the Eberline high range noble gas i.
detector views externally a section of one inch stainless steel tubing as its sample volume.
The low range is monitored by a beta scintillation detector (Eberline Model RDA-3A),
()
while both the medium and high range measurements are performed by an energy-compensated GM detector.
Sample flow is provided by a stainless steel diaphragm vacuum pump and an air flow regulator.
Sample flow is set to insure isokinetic sampling monitored by a solid-state flow sensor.
The three Eberline noble gas detectors are part of a microprocessor-controlled gaseous effluent monitoring system (Eberline SPING-4).
The monitoring system's control terminal, strip chart recorder panel 912-1 and annunciating panel 912-4 are located in the control room on Panel 912-1.
The control terminal provides immediate access to current detector activity, operating parameters, and history files for any detector.
Changes in detector operational status are automatically printed and audibly acknowledged.
The SPING-4 microprocessor's memory has battery backup to maintain all operating parameters and history files for any detector in the event of a system power
()
loss.
8.1-4
QUAD-CITIES REVISION 11 DECEMBER 1985 For all of the above monitors, the sample pumps and detectors, l
with local controls, are located in the chimney sample house at the base of the chimney.
Power is supplied to the process radiation monitors from the station 48/24-Vdc battery systems.
The main chimney noble gas monitor alarm setpoints will be selected to ensure that the combined release rate of the main chimney and the reactor building vent stack does not exceed the most conservative release limit determined from Equations 8.1 and 8.2.
8.1.3.2 SJAE Off-Gas Monitors The major source of radioactive noble gases is from each unit's off-gas system.
Each unit's off-gas system has its own radia-I) tion detection instrumentation capable of isolating the off-U gas release pathway.
Off-gas from the main condenser is monitored for gross gamma activity downstream of the steam jet air ejectors (SJAE) and' prior to release to the main chimney.
Continuous radiation monitoring is maintained on the off gas hold-up pipe.
The off-gas mon-itoring system for each unit is performed in two channels, eachofwhichincludesagammasensitiveion-chamberdetecIor, and a logarithmic radiation monitor with integral power supply.
The two channels share a common two pen recorder and a trip auxiliaries unit whose output feeds an interval timer.
System controls, alarm annunciators, recorder, and displays are located on panels in the main control room.
The ion-chamber detectors are mounted adjacent to and at the beginning of the off-gas hold-up pipe, a 36-inch diameter header whose function is to contain the off-gas for a period of time dependent on off-()
gas flow and allow for radioactive decay prior to release to the chimney.
8.1-5
QUAD-CITIES REVISION 11 DECEMBER 1985 A high radiation condition in the hold-up pipe will initiate an interval timer with a variable setting of 0 to 15 minutes.
When the preselected time interval has elapsed, an isolation valve at the inlet to the chimney from the off-gas system will automatically close, preventing release of radioactive gases from the affected off-gas system.
Power is supplied to the off-gas process radiation monitors from the station's 48/24-Vdc battery systems.
Power to the interval timer is from the 120-Vac essential service bus.
The timer provides the signal to the solenoid-operated valves 4
which control the air supply to the air-operated isolation valve (equipment.part number A0 1(2)-5406).
The monitor display 6
is a logarithmic scale and has a range of 1 to 10 units (mR/hr).
The detectors equipment part numbers are RE 1(2)-1733A and RE 1(2)-1733B.
The SJAE monitor alarm setpoints will be selected to ensure that the combined release rate of the main chimney and station vent stack does not exceed the most conservative release limit determined from Equations 8.1 and 8.2.
l 8.1.3.3 Allocation of Effluents from Common Release Points l
Radioactive gaseous effluents released from the main chimney are comprised of contributions from both units.
Under normal operating conditions, it is difficult to allocate the radio-activity between units due to fuel performance, in-plant leakage, power history, and other variables.
Consequently, allocation will normally be made evenly between the units.
During extended unit shutdowns or periods of known differences, the apportionment will be adjusted accordingly.
The allocation of the effluents will be made on a monthly basis.
8.1-6 i
l
QUAD-CITIES REVISION 11 DECEMBER 1985 f
(g.
8.1.4 Reactor Building Ventilation Stack Releases 8.1.4.1 Ventilation Stack Monitors Releases of radioactive noble gases from each reactor building's ventilation system are monitored prior to introduction to the ventilation stack.
Two sensor and converter (detector) units are located in each unit's reactor building exhaust duct, and provide continuous gamma radiation monitoring.
The sensor is a Geiger-Mueller tube, polarized by high voltage from the power supply.
The output signal from each sensor converter is applied to an indicator and trip unit, where it is amplified and used to drive a meter.
This unit also provides trip functions for upscale and downscale alarms through auxiliary units.
A downscale trip in either channel annunciates
()
a low radiation (malfunction) alarm.
An upscale trip in either channel initiates a reactor building ventilation system high-high radiation alarm.
Control logic is such that one channel high level trip or two channel low level trips will shut down and isolate the reactor building ventilation system for both units and initiate the standby gas treatment system.
The exhaust duct monitors provide a signal to a two-pen recorder which will annunciate a high radiation condition in the exhaust duct.
This is an alarm only, and does not initiate corrective action.
The recorder, controls, indicator and trip units, alarms, and annunciators are located on panels in the main control room.
The power supply to each sensor channel is supplied from a different power source.
The A channel is fed from the 120-Vac.
)
A reactor protection system and the B channel are fed from the 120-Vac B reactor protection system.
l l
8.1-7
QUAD-CITIES REVISION 11 DECEMBER 1985 I'd The indicating meters have a logarithmic scale with a range NJ of 0.01 to 100 mR/hr.
The sensor and converter units have equipment part numbers RE 1(2)-1735A and RE 1(2)-1735B.
Each reactor building's ventilation system is isolated by closure of two air-operated butterfly valves (A0 1(2)A-5741 and A0 1(2) B-5741) located in series downstream of the reactor building ventilation supply fans, and by closure of two air-operated butterfly valves (A0 1(2) A-5742 and A0 1(2)B-5742) located in series downstream of the radiation sensors and up-stream of the exhaust fans.
Air supplies to these valves are controlled by solenoid valves powered from the 125-Vdc station battery systems.
The control logic relays which operate these solenoids are powered by the 120-Vac essential service bus.
The reactor building ventilation stack monitor alarm setpoint
! / }
will be 2 mR/hr above background.
Using an empirical relationship l
of mR/hr and u/Ci/sec at design flowrates, the calculated reactor building ventilation stack release rate will be employed in Equation 8.1 and 8.2 to select the most conservative main chimney monitor alarm setpoints.
8.1.4.2 Allocation of Effluents from Common Release Points Radioactive gaseous effluents released from the reactor building vent stack are comprised of contributions from both units.
Estimates of noble gas contributions from each unit will be made by analyzing grab samples from the individual units.
Allocations of radiciodine and radioactive particulate releases will be made by analyzing samples taken from continuous samples on each unit.
The allocation of the effluents will be made on a monthly basis.
lO 8.1-8
QUAD-CITIES REVISION 11 DECEMBER 1985 O
\\
8.1.5 Symbols Used in Section 8.1 SYMBOL NAME UNIT Q
Total Release Rate, Stack Release (pCi/sec) ts 5
Gamma Whole Body Dose Constant, Stack (mrad /yr per g
Release pCi/sec) f Fractional Radionuclide Composition g
Q Total Release Rate, Vent Release (pCi/sec) tv V
Gamma Whole Body Dose Constant, (mrad /yr per Vent Release Ci/sec) )
Release Rate of Nuclide i, Stack Release (pCi/sec)
Qig l
Q Release Rate of Nuclide i, Vent Release (pCi/sec) gy E
Beta Skin Dose Constant (mrem /yr per g
3 UCi/m )
3 (x/Q) s Relative Effluent Concentration, (sec/m )
l Vent Stack Release A
Radiological Decay Constant (hr~1) g R
Downwind Range (m) u Average Wind Speed, Stack Release (m/sec) g
\\
l O
8.1-9
QUAD-CITIES REVISION 11 DECEMBER 1985 SYMBOL NAME UNIT 3
(X/Q) y Relative Effluent Concentration, Vent ec/m )
Release Average Wind Speed, Vent Release (m/sec) uy S
Gamma Dose Constant, Stack Release (mrad /yr per i
pCi/sec)
V Gamma Dose Constant, Stack Release (mrad /yr per i
pCi/sec)
O I
t c
O l
8l.1-10
QUAD-CITIES REVISION 11 DECEMBER 1985 0
.6 8.1 Constants Used In Section 8.1 NUMERICAL VALUE NAME UNIT 1.11 Conversion Constant (mrem / mrad) 3600 Conversion Constant (sec/hr) i i
e O
1 l
I i
i I
I k
ll l
lO l
8.1-11 i
.. _. ~ _ -,, -.
l RES!N 4000 CFM SOLIDIFICATION 0FF GAS 52000 CFM
- BLDG, RECOMBINER BLDC.
UNIT I TURBINE BLDG, IT2200 CFM MAXIMUM RECYCLE 6000 CFM UNIT I
=
RADWASTE BLDG.
0FF GAS 152000 CFM RECOMBINER BLDC.
UNIT 2 OFF-GAS 5000 CFM BLDG.
TURBINE BLDG.
IT2200 CFM UNIT 2 RA0 WASTE 40000 CFM BLDG.
y a
HRSS 7
y1000 CFM UNIT I
~
LOG u
LIN AA =
hhh HRSS M
U1000 CFM UNIT 2
~
- ~ {:
77 --
-~~
-~~
O!
HOLO UP (4 HRS.WHEN RECOMBINER IN)
UNIT I RECOMBINER
~
~-
MAIN l
DRYER A
I
'l*-
'WJ CONDENSER AIR EJELTOR l
l e____.
AMBIENT AIR RBINE BLDG.
l UNIT I REACTOR B'jlLDING y..--H______________l l
,___-w.___
>________N______,
l l
T l_ _
AMBIENT
[* -- H ---
---_--..._J A
TURBINE RE-l-2418A { ]
[ @ RE-I-2418B UNIT 2 l
REACTOR BUILDING b
g DRYWELL
'~
- - - - - - - - *j
}
RE-l-2418C RE-l-24180 r
'DRYWELL PURGE 8-l l
i__.
O
>H I
. l.
LEGEN
%g es
- HEPA FILTER PARI!CULATE $
- h IODINE SAMPL CHARCCAL FLOW-THROUGF 8 @ b P PARTICUL:
!=100!NE LN.MN & HN R'
/
11' DI AlETER 310' ABOYE GRADE REVISION 11 DECEMEER 1985 III l-IT31A 2
1/2-IT898 r,
l-IT318 LM_Nf - ---+
/2-y l P l I lL N, y
n
__ g
__f
+
1/2
+
U 431800 CFM
=@LNI*[HNW VENTILATION 4E-T839 7
7 9' DIAMETER g
159' ABOVE GRADE C
C i
i h LJ LJ E 9
n i II lRYER
=
CHARC0AL ADSORBER r
4 e
UNIT 2 q
0FF GAS l
SGTS r-------------------------------
RX BLDG.
e l
VENTILATION n*f.
~
EXHAUST 2J STACK l AIR BLDG.
T PLANT GRADE l*lI93 M
4 104500 CFM ELEVATI,0N l
=
I I
g APERTURE CARD
}ANDNOTES Also Avalle61e On h RADI AtiON cETECTm A erturei.hrd P
QUAD-CITIES STATION wtE NCRMALLY CCNTINUCUS Units 1 & 2 FLOW PATH DURING
- ~
RADI ATION MONITOR:
VE
OCCASIONAL FLCW PATH FL W ELEMENT GASEOUS EFFLUENT FLOW DIAGRAM
.74. G DIU2 & HIGH ! NOBLE GAS NOTE: ALL FLOW RATES ARE DESIGN J FLOW RATES. NOT ACTUAL % 0 $ M o 2 % 3 - O 2- ~
QUAD-CITIES REVISION 11 DECEMBER 1985 8.2 LIQUID RELEASES 8.2.1
System Design
Simplified liquid radwaste and liquid effluent flow diagrams are provided in Figures 8.2-1 and 8.2-2. A liquid radwaste treatment system shall be a system designed and installed to treat radioactive liquid effluents by collecting the liquids, providing for retention or holdup, and providing for treatment by demineralization to reduce the total radioactivity prior to the release of liquids to the environment. 8.2.2 Alarm Setpoints Alarm setpoints of liquid effluent monitors at the principal release points are established to ensure that the limits of O 10 CFR 20 are not exceeded in the unrestricted area. The U concentration limit (Cyg,) in the discharge line prior to I dilution in the initial dilution scream is: - dp"#' p"r + Clim = MPC r (8.3) p max C Limiting Concentration (u Ci/ml) yg, in Discharge Line The maximum concentration in the dis-charge line permitted to be discharged to the initial dilution stream. MPC Weighted Maximum Permissible (uCi/ml) Concentration n n g [Ag hC MPC = U# 9 C A (8.4) g g MPC MPC i=1 g g,y g l 8.2-1
QUAD-CITIES REVISION 11 DECEMBER IS85 (h L.) where: C = pCi/ml of nuclide i; g MPC i = maximum permissible concentration pCi/ml of nuclide i; and A = p Ci of nuclide i released in time t. i E F,,, Maximum Flow Rate, Radwaste Discharge (ft /sec) The maximum flow rate of radwaste from the discharge tank to the initial dilution stream. 0F,y, Average Flow Rate, (ft /sec) Initial Dilution Stream The average flow rate of the initial ( dilution stream which carries the radionuclides to the unrestricted area boundary. Surveillance frequencies for liquid effluent monitors will be as stated in Table 4.2-3 of the Technical Specifications. Calibration methods will be consistent with the definitions found in Section 1.0 of the Technical Specifications. 8.2.3 Radwaste Discharge Line Releases 8.2.3.1 Radwaste Discharge Monitor The radwaste releases are currently monitored for radioactivity using two grab samples and a composite sample. These samples are analyzed for alpha, beta, and gamma radiation. MPC calculations are done to determine discharge rate and dilution ) volume. 8.2-2 i
QUAD-CITIES REVISION 11 DECEMBER 1985 b G Installation of a new continuous monitor for the radwaste I discharge line is in progress. It is an offline monitoring system which uses a 2-inch by 2-inch sodium iodine thallium actuated scintillation detector in a lead-shielded housing. The sample container is bowl shaped to minimize crud buildup. A GM tube is used to determine the background radiation level. The radwaste discharge monitor provides a signal to a recorder and an Eberline CT-2 control terminal. A high radiation alarm will be activated by the control terminal. The process radiation monitor, control terminal, alarm, and annunciator are located on panels in the main control room. The process liquid monitor has a logarithmic scale with -1 6 a range of 10 to 10 counts /sec. The monitor is powered by 120-Vac. J The radwaste discharge line detector (RE 1/2-1799-01) is mounted adjacent to the radwaste control room. The flow is routed there after the flow control valves and prior to the selection of several alternate discharge routes. The alarm setpoint for the radwaste discharge monitor is established at or below the maximum concentration determined by Equation 8.3. The concentration is converted to an alarm setpoint using an efficiency curve developed for the monitor through use of a Cs-137/Ba-137m liquid calibration sources. 8.2.3.2 Allocation of Effluents From Common Release Points i Radioactive liquid effluents released from the radwaste j treatment system are comprised of contributions from both units. Determination of the allocation of waste is achieved by comparing l 8.2-3 l
QUAD-CITIES REVISION 11 DECEMBER 1985 the pump timer totals for each unit's floor drain and equipment drain pumps to the amount of waste sent to the river discharge tank from the floor drain and waste collector storage tanks. I Liquid effluents from laundry and chemical waste are allocated evenly between units. During extended unit shutdown or periods of significant plant input differences, the apportionment will be adjusted accordingly. The allocation of the effluents will be made on a monthly basis. 8.2.3.3 Administrative and Procedural Controls for Radwaste Discharges Administrative and procedural controls have been implemented to ensure proper control of radioactive liquid radwaste discharges, to preclude a release in excess of 10 CFR 20 limits. The dis-charge rate for each batch is calculated by a technician and ,() then independently verified by two operating staff personnel. A single river discharge tank has been designated and modified from which all radwaste discharges will normally be released. This tank has manual inlet and discharge valves which can be locked. The inlet valve is locked closed during recirculation of the tank prior to sampling and during the discharge to preclude an accidental addition to the tank which could change its activity. j The discharge valve is locked closed at all times except during l the discharge. All other lines, which tie-in with the discharge line, are locked closed. The high and low flow control valves are selected by a key-lock switch which allows the use of only one of the two flow control valves at any one time. The key to this switch and the locked valves is under the administrative control of the radwaste foreman. O 8.2-4
QUAD-CITIES REVISION 11 DECEMBER 1985 's) RJ A documented valve checklist is prepared for each batch discharge. The proper valve lineup is checked by the operator and the radwaste foreman, prior to release. If any sudden significant increase of the radiation monitor occurs during the discharge, the release is terminated. These controls are documented in Station Operating and Administrative Procedures. 8.2.4 Service Water Header Releases 8.2.4.1 Service Water Effluent Monitors Each unit's main service water effluent header is monitored for radioactivity by taking grab samples every twelve hours and analyzing for gross beta activity. Installation of a new continuous monitor for both service f-water headers is in progress. It is an offline continuous monitoring system. The process liquid monitor uses a 2-inch l by 2-inch sodium iodine thallium-activated scintillation j detector in a lead shielded housing. The sample container is bowl shaped to minimize crud buildup. A GM tube is used to determine background radiation levels. i The service water effluent monitor on each unit provides a signal to a recorder and to an Eberline CT-2 control terminal, I which initiates a high radiation alarm. The process radiation i monitor, recorder, alarm and annuciator are located on the panels in the main control room. l i The process liquid monitors have logarithmic scales with a ~1 6 range of 10 to 10 counts per second. The monitors are I powered from 120 Vac. O 8.2-5
QUAD-CITIE REVISION 11 DECEMBER 1985 O("~i The service water system detectors (RE 1(2)-1799-01) are located adjacent to the main service water effluent header on each unit prior to release to the discharge bay. The alarm setpoints for the service water effluent monitors are established at or below the maximum concentration determined by Equation 8.3. 8.2.5 Determination of Initial Dilution Stream Flow Rates For those release paths which have installed flow monitoring instrumentation, that instrumentation will be used to determine the flow rate of the initial dilution stream. This instrumenta-tion will be operated and maintained as prescribed by the Tech-nical Specifications. For those release paths which do not have installed flow monitoring instrumentation, flow rates will be \\- determined by use of appropriate engineering data such as pump curves, differential pressures, or valve position indication. O 8.2-6
QUAD-CITIES REVISION 11 DECEMBER 1985 0 8.2.6 Symbols Used In Section 8.2 SYMBOL NAME UNIT C lim Liquid Release Limit (pCi/ml) MPC Weighted Maximum Permissible (pCi/ml) Concentration C Nuclide Concentration (pCi/ml) g MPC Maximum Permissible g Concentration (pCi/ml) A Nuclide Quantity Released (pCi) g F,x Maximum Flow Rate, Radwaste (f t /sec) E Discharge d F Average Flow Rate, Initial (ft /sec) ave Dilution Stream
- O 8.2-7 4
f
Ow w ~:: REVISION 11 DECEMBER 1985 l t =~ a i i o e$2 i
- a i
sM ,s I -on l so w B i$ ~- ~ s y i REI 8!: i
==s l I
- =
a 1 1 i = l ~ l E ,5 55 B" 5l l ,1-l -=-
s-a
wu s y~8 g w s: c.g B" R _a 3 SI as a r 'o 7 I 7 a i ^ =;^ --en i i 1 = b .I I as ses is 18 es 'Ii2 5EE g-q 1E s i E-g3 3 i i l i mT' o a e o i t,1 lL-i l l I i l l ~ l ^ j i i r i .E.gtl l l " 's i s = u .les-t=s3 8Es = s53 g i ag-l gs-g 7 g- =i l l l QU AD-CITIES STATION t Units 1 & 2 i FIGURE 8.2-1 e SIMPLIFIED LIQUID RADWASTE PROCESSING DIAGRAM i
f t REVISION 11 C j DECEMBER 1985 i 2 ( y 3 g g g z E E. r ]i: ? ( I l ))i i t i !E-I i ~iii;; lit j = E } l l l l !: EH E i , 4,0 l i s g e I lg 5 i,, ~~ l 'NT !!h! 9 3 Is a os : = a rg_w:ra e gi a ? a
- s :
\\ s=! ~ = 8 ffj =!!!Ejyj p ' ) gg 5 i r 9.i I ~l f f f' I i r = j t I 1 = / /
- f I
f 6 7. -l "HIH a e EE f l J. / w {: 90 si s'; Et l t i QUAD-CITIES STATION Units 1 4. 2 i FIGURE 8.2-2 i SIMPLIFIED LIQUID EFFLUENT FLOW DIAGRAM
.=_. 't QUAD-CITIES REVISION 11 DECEMBER 1985 O 8.3 SOLIDIFICATION OF WASTE / PROCESS CONTROL PROGRAM The process control program (PCP) shall contain the sampling, i analysis, and formulation determination by which solidification of radioactive wastes from liquid systems is ensured. Figure 8.3-1 is a simplified diagram of solid radwaste processing. i i O i i E 1 l i i i i ' O 8.3-1 i
E# REVISION 11 O I!~ l DECEMBER 1985
- a J
L m E a g / / .1 \\\\ m I a n 9 0 oo .1-M lE a a i II n n n E a ii 1 O e\\ u u w a n o I I si s khI h !a gag
- w t
3 d r- ; e,) Bis !!!a l l l QUAD-CITIES STATION Units 1 4. 2 FIGURE 8.3-1 SIMPLIFIED SOLID RADWASTE PROCESSING DIAGRAM
1 QUAD-CITIES REVISION 11 DECEMBER 1985 8.4 ENVIRONMENTAL RADIOLOGICAL MONITORING The environmental radiological monitoring program to be performed in the environs around Quad-Cities Station is given in Table 8.4-1. i l Figure 8.4-1 shows the 16 fixed air sampling sites and TLD locations; also shown are the " outer ring" (approximately 5 miles distant) TLD locations. Figure 8.4-2 shows the " inner ring" TLD locations. The TLD's are code numbered as follows: l XYY-N, where: X= 1 means inner ring, X= 2 means outer ring, and YY-N is an identification code. Figure 8.4-3 shows the milk, fish, water, and sediment sample locations. The reporting levels for radioactivity concentrations in envi-ronmental samples are given in Table 8.4-2. The practical l lower limits of detection for this program are given in Table 8.4-3. l l O l 8.4-1
O O ) TABLE 8.4-1 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM EXPOSURE PATHWAY SAMPLING OR TYPE AND FREQUENCY AND/OR SAMPLE SAMPLING OR MONITORING LOCATIONS COLLECTION FREQUENCY OF ANALYSIS Onsite or Hear Field" Particulate Sampler 1. Airborne a. Q-01 Onsite Station 1 0.5 mi N Continuous sampfer Gross beta analysis b Q-02 Onsite Station 2 0.5 mi. ENE operation with partic-following filter change Q-03 Onsite Station 3 0.6 mi S ulate filter collec-Q-04 Nitrin 1.5 mi NE tion weekly and Radiciodine Canister Q-05 Saddle Club Dairy 1.8 mi SSE radiolodine canister Farm collection bi-weekly I-131 analysis bi-weekly Q-06 Hanson's Boat 1.8 mi NNW Landing Sampling Train: Test and maintenance weekly b. Far Field" Q-07 Clinton 9.0 mi NE Continuous sampler Particulate Sampler Q-08 Sikkeaa Fara 7.0 mi ENE oper,ation with partic-Q-09 Erie 13.0 mi ESE ulate filter exchange Gross beta when o b c Q-10 Hillsdale 10.0 al. SE weekly and radiolodine analyses are made,c P Q-ll Port Byron 8.0 mi S canister exchange 5 y Q-12 Bettendorf 13.0 mi SW bi-weekly Radiolodine Canister: E Q-13 Princeton 4.8 mi SW y w Q-14 Utica Ridge Road 11.0 mi ESE I-131 whgn analyses y Q-15 DeWitt 13.0 mi WNW are made m Q-16 Low Moor 6.0 mi NNW . Sampling Train Test and maintenance weekly l 93 5" e 3
O O TABLE B.4-1 (Cont'd) EXPOSURE PATHWAY SAMPLING OR TYPE AND FREQUENCY AND/OR SAMPLE SAMPLING OR MONITORING LOCATIONS COLLECTION FREQUENCY OF ANALYSIS At Air Sampling Sites
- Quarterly Camma dose quarterly 2.
Direct Radiation a. Same locations as fixed air sampling locations in Item 1. b. Inner Ring Quarterly Gamma dose quarterly 101-1 0.7 mi N 101-2 0.8 mi N 102-1 1.7 mi NME 102-2 1.7 mi NNE 103-1 1.2 al NE 104-1 1.1 al ENE 104-2 0.95 mi ENE 104-3 0.63 mi ENE 105-1 0.75 mi E 106-1 0.71 mi ESE o 106-2 0.71 mi ESE c ? 107-1 0.73 mi SE 7 107-2 0.78 al SE f w 107-3 0.86 mi SE M ~ 108-1 0.96 mi SSE d i 108-2 0.89 mi SSE Q j i 109-1 0.87 mi S i 109-2 0.98 mi S I 111-1 2.6 mi SW 111-2 2.6 mi SW i 112-1 2.5 mi WSW 112-2 2.2 mi WSW 113-1 2.6 mi W 113-2 2.5 mi W 114-1 2.6 mi WNW 114-2 2.5 mi WNW 115-1 2.6 mi NW 115-2 2.0 mi NW 116-1 2.2 mi NNW 1 116-2 2.4 mi NNW EE i nS !!2
== ~;: 3 w + r
O TABLE II.4-1 (Cont'd) i SAMPLING OR TYPE AND FREQUENCY EXPOSURE PATHWAY e l AhD/OH SAMPLE SAMPLING ON NONITORING LOCATIONS COLLECTION FREQUENCY OF ANALYSIS m 2. Darect Hadiation Outer Ringg* Quarterly Gamma dose quarterly (Cont'd) c. 201-1 4.6 mi N 201-2 4.0 mi N 202-1 4.4 mi NNE 202-2 5.0 mi NME 203-1 5.0 mi NE 203-2 4.5 mi NE 264-1 4.5 mi ENE 204-2 3.9 mi ENE I 205-1 5.6 mi E 205-2 4.7 mi E 206-1 5.0 mi ESE 206-2 4.8 mi ESE 207-1 4.3 mi SE 207-2 4.6 mi SE Q 208-1 4.4 mi SSE p. ? i m j 208-2 4.7 mi SSE O 209-1 4.4 mi S U s e* 209-2 4.5 mi S E" 210-1 4.4 mi SSW ) 210-2 4.4 mi SSW 211-1 3.5 mi SW i 212-1 5.4 mi WSW 212-2 4.7 mi WSW 213-1 4.7 mi W 213-2 5.5 mi W 214-1 4.4 mi WNW 214-2 4.4 mi WNW 215-1 4.8 mi NW 215-2 4.5 mi NW 216-1 4.5 mi NNW j 216-2 4.2 mi NNW i 4 M 1 I"a n
- s 4
F ed @ >e } } 9 i 5 i I 1
O 1 TABLE 8.4-1 (Cont'd) i 1 q EXPOSURE PATHWAY SAMPLING OR TYPE AND FREQUENCY AND/OR SAMPLE SAMPLING OR MONITORING LOCATIONS COLLECTION TREQUENCY OF ANALYSIS 3. Waterbornee a. Public Water Q-19 East Moline Water 16.0 mi SSW Weekly collection Gamma isotopic analysis l Supply Works composited monthly monthly Q-20 Davenport Water 18.0 mi SSW f Works b. Cooling Water Q-21 Inlet at station Weekly Cross beta analysis weekly Sample Q-22 Discharge at station c. Sediment Q-23 Lock and Dam 15.0 mi SSW Annually Gamma isotopic analysis No. 14 annually 4. Ingestione a. Milk Q-17 Hansen Dairy Farn 6.0 mi ENE Weekly collection when I-131 analysis on each Q-18 Musal Fara 5.5 mi SW animals in pasture sample (May to Oct.); monthly, t Nov. to March c b. Fish Q-24 Davenport Fars 15.0 mi SSW Semi-annually Gamma isotopic on Market (Pool edible portions of each O 414 of Miss. River) sample d E
- Ste Figure 8.4-1.
A gamma isotopic analysis shall be performed wherever the gross beta concentration in a sample exceeds by five b times (5X) 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 I and radioactivity is confirmed as having its origin in airborne effluents released from the station, or at the discretion of the Emergency Planning Supervisor. t 2 d l Sse Figure 8.4-2.
- Sie Figure 8.4-3.
g f, ogh n 3 I
1 L 4 TABLE 8.4-2 REPORTING LEVELS FOR RADIOACTIVITY CONCENTRATIONS IN ENVIRONMENTAL SAMPLES i I I REPORTING LEVELS AIRBORNE PARTICULATE WATER OR GASFS FISH MILK FOOD PRODUCTS j y ANALYSIS (pC i/g. ) (pCi/m ) (pCi/Kg, wet) (pCi/g) (pCi/Kg, wet) H-3 20,000* Mn-54 1,000 30,000 Fe-59 400 10,000 Co-58 1,000 30,000 -a o I C Co-60 300 10,000 g Zn-65 300 20,000 h I; N Zr-Nb-95 400** mm 1-131 2 0.9 3 100 I l Cs-134 30 10 1,000 60 1,000 Cs-137 50 20 1,000 70 2,000 Ba-La-140 200** 300** n R5 i
- r m
- For drinking water samples.
This is 40 CFR Part 141 value. gg
- Total for parent and daughter.
"Z
O O O TABLE 8.4-3 l MAXIMUM VALUES FOR Tile LOWER LIMITS i OF DETECTION (LLD) a, b l AIRBORNE PARTICULATE WATER OR GASgS FISH MILK SEDIMENT ANALYSIS (pCi/E) (pCi/m ) (pCi/Kg, wet) (pCi/t) (pCi/Kg, dry) j c Gross Beta 5 0.01 1,000 5 2,000 i Gamma Isotopic 20 0.01 200 20 200 I-131 5 0.1 100 5(0.5)* d o m Cs-134 10 100 10 g
- u o
4 Cs-137 10 100 5 5 3 11 - 3 200 H l EE 95 55 MO lc Z I
QUAD-CITIES REVISION 11 (-w DECEMBER 1985 TABLE 8.4-3 (Cont'd) NOTES: a. Other radionuclides which are measurable and identifiable by gamma-ray spectrometry, together with the nuclides indicated in Table 8.4-3, shall also be identified and reported when an actual analysis is performed on a sample. Nuclides which are below the LLD for the analyses shall not be reported as being present at the LLD level for that nuclide. b. The LLD is the smallest concentration of radioactive material in a sample that will be detected with 95 percent probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal. For a particular measurement system (which may include redio-chemical separation) 4.66- (Sb) (A)- (E). (V)- (2.22). (Y). (exp (- A A t) ). (t) O) (- Where: LLD is the "a priori" lower limit of detection for a blank sample or background analysis as defined above (as pCi per unit mass or volume). S is the square root of the background count or of a blank g sXmple count; it is the estimated standard error of a background count or a blank sample count as appropriate (in units of counts). E is the counting efficiency (as counts per disintegration). A is the number of gamma-rays emitted per disintegration for gamma-ray radionuclide analysis (A = 1.0 for gross alpha and tritium measurements). V is the sample size (in units of mass or volume). 2.22 is the number of disintegrations per minute per picocurie. Y is the fractional radio-chemical yield when applicable (otherwise Y = 1.0). O 8.4-8
QUAD-CITIES REVISION 11 DECEMBER 1985 O TABLE 8.4-3 (Cont'd) Lambda is the radioactive decay constant for the particular radionuclide (in units of reciprocal minutes). Delta t is the elapsed time between the midpoint of sample collection and the start time of counting. (At = 0.0 for enviromental samples and for gross alpha measurements.) t is the duration of the count (in units of minutes). The value of "S " used in the calculation of the LLD for a detection syskem 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 " delta t" shall be used in the calculation. For gamma-ray radionuclide analyses the background counts are determined from the total counts in the channels which are within plus or minus one FWHM (Full Width at Half Maximum) /" of the gamma-ray photopeak energy normally used for the ( quantitative analysis for that radionuclide. Typical values of the FWHM shall be used in the calculation. The LLD for all measurements is defined as an "a priori" (before the f act) limit representing the capability of a measurement system and not as an "a posteriori" (after the f act) limit for a particular measurement. c. Referenced to Cs-137. d. For thyroid. e. 0.5 pCi/t on samples collected during the pasture season. O 8.4-9
REVISION 11 DECEMBER 1985 L3 o R. f Fulton Clinton v y 7 US 30 15 8 # 16e 201-i 202 2 256-iae h a,eL 216-2 20'1 2 I 215-1 5 203 2 Iowa 2i5 2g Ill.inois 8 2 *- ai4 e o8 e US 67 { E 204 2 I 4 23-l e2 g 3 p205 2 21223 Eg206-1 212-1s e5 m206 2 US 61 g 52071 20 @ 210-209-1 , 20s 1 I 20s 2 ILL-2 'd / 1 ~118 . so Davenport uS 67 R ch Rant att.s4 gjjy y
- n ILL 2; 3
at'aes /,h, e Air Sampling Site E Outer Ring TLD Location
- -74 l-s0 l
0 5 1,0 1,5 2,0 Miles 0 5 10 15 20 25 30 km QUAD-CITIES STATION Units 1 4, 2 l FIGURE 8.4-1 FIXED AIR SAMPLING SITES AND OUTER RING TLD LOCATIONS ISa's'-372
REVISIO'4 11 DECEMBER 1985 r'./- its.2 / 6 l f l / 4 6 ' q/ u s., / senricker[# /gsk }l f ) p g _,.,i,. ! !/ i " 5-2 r u n s.1 . /./w - ^o.r..,o,., j / /, y/ r ) j/g ,/ ,6 Camanche a us.2
- l
{ f //h* k lj */s // s ennien county & hf -y E M*' ) 2 I * ) f" \\. j j., j e 1015 h'! IN.T. gy \\. ?!j- [ s.) / / io4 3 404 2 I m u s.2 = Quad-io i [ va' ma.;eCities 3 Station s. ./ g g / m i13-1 g ios.2 O a 7. . _.y 3, j N, / ,1 s, 107 i l/ I./ )* -/ \\ u22m / i ma.\\ / ior., Ih ./ io,.i s g ,a y, e., f /g., 3 105-2 n a-i n ios. \\\\\\ \\-, ) {< [:j N f r
- \\ \\
cordova [' ) .j l u s.: e i 31: '/ .s.g\\.s i j j l i I / l Mb.-- htl) - - l \\ Y i } L f Princeton / j f j ht ,Y bl. '.! gi towa/ ] h Jf kJ /iilinois/ e i S** QUAD-ClTIES STATlON i 1 l ""' Units 1 4. 2 5 b~ O INNER RING TLD LOCATIONS o, 0,. 5 1, k m IIs's'-an /
REVIS10f1 11 DECEriBER 1985 4 i, 4 ose Lak, US67 y,,,,,,, O River t 1LL g4 Clinton Y US 61 q IOWA 136 FultOn us s7 ii.t 7e gg C&NW DeWitt ]
- }
7 US 30 BN C&NW = MOrriSOn amanche Albany Wapsipinicon River t t 17 j itt re a 3 lilinois towa 3' Whiteside 1 CMSTP&P l 318 COrdOVag Princeton 4 f 4 ILL 2 US 61 Ene Scott 1 A 130 Hillsdale. BN l [ " Port Byron / ,,gn i J lsland Davenport 2 24 ) y f "7"f'ff 2o ,,,,,j,, g 1 is,'" [ Oline Colons CRi&P r Rock '3 ~\\ { .80 N B Samphng Station Scale 9,,,,s is i,s 2p unes ?,,..? p ip 2p 2p 3,0 k m QU AD-CITIES STATION Units 1 & 2 FIGURE 8.4-3 f1 ILK, FISH, WATER, AND SEDIf1EllT SAMPLE LCCATIONS ISa's# v2 A}}