ML20102A597

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Corrected Chapter 11 to, Environ Radiological Monitoring Table of Contents, Odcm,Revs 0.C & G
ML20102A597
Person / Time
Site: Quad Cities  Constellation icon.png
Issue date: 07/02/1992
From:
COMMONWEALTH EDISON CO.
To:
References
PROC-920702, NUDOCS 9207270137
Download: ML20102A597 (20)
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- 11, is being re-issued in entirety for a'page correction.-lThe page change is * <

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-QUAD: CITIES REVISION-0.G~ -i

, MAY:1992:.

QUAD CITIES: ANNEX-INDEK-PAGE REVISION .

CHAPTER 11- l-11-1 0.G' 11-il 0.C 11-111 0.C l ll-vi -0.C 11-1 0 11-2 .0.C 11 0.C 11-4 0.C u-5 .0.C 11-6. 0 ~. G 11-7 0.C 11-8 0.G s 11-9 0.G L 11-10 0.G 11-11' O.C.

11-12 0.C 11-13 0.C 11-14 0.C-11-15 0.G O

O 11-1

REVISION:O.C-QUAD CITIES'

-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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11-111 1

l

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.

1 0

11-1

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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 4

inmolino Train:

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 Q-08 Sikkema Farm 7.0 mi ENE (11.3 km D) radiolodine canister exchange analyses are maded e 0-09 Erie 13.0 mi ESE (20.9 km F) biweeklyC 11-2

I AD CITIES REL 0.C

!: FEBRUARY 1991 -

.. i

[ 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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, 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) - are madee

p. Q-14 Utica Ridge Roat' 1.0 mi M (17.7 km N) .

^

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) j.

Testandmaintenarce'}

weekly s'

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'2. Direct Radiation a. At Air Sampler Sitesb Quarterly Gaara dose quarterly Same location'as fixed al'r sampling locations j in Ites 1.  ;

l b. Inner Rinaf Quarterly Gamma dose quarterly i

t G-101-1, 0.7 mi N 1.1 km A

0-101-2, 0.7 al N . 1.1 km A i- Q-102-1, 1.7 mi NNE 2.7 km B

}' Q-102-2, _ 1.7 mi NME 2.7 km B' l Q-103-1, . 1.2 al ENE 1.9 km D

! Q-103-2, 1.2 al'ENE 1.9 km D

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Q-104-1, l1.1 mi ENE 1.8 km D 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 t

l 11-3 g

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h ITIES 15103 0.C i FEBRUARY.1991 Table 11-1 (Cont'd)

- Exposure Pathway- Sampling or Type and Frequency and/or Samole Samlina or Monitorina Locationsa Collection Freauency of Analysis p .

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l 2. Direct Radiation - Q-106-1, 0.7 mi ESE 1.1 km F (Cont'd). 0-106-2, 0.7 al ESE 1.1'km F Q-107-1, - 0.7 mi SE 1.1 km G -

Q-107-2, 0.7 mi SE 1.2 km G i

. 0-107-3,, 0.8 mi SE- 1.3 km G' 4

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

!- - Q-111-2, 2.6 mi SN . 4.2 km L L Q-112-1,. 2.4 mi NSW 3.9 km M

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Q-112-2,- 2.4 mi.MSN .3.9 km M 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 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 Q-203-1,- 5.5 mi NE 8.8 km C' ,

Q-203-2, 5.5'mi NE' 8.8 km C -

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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

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REVIST O .G 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) ,
4. Inaestion h 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

O

~

O QUAD CITIES OREVISIC3 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

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x (Xis_,lITIES CORRECTL 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

e

,See Table D-16 of Appendix 0 for definitions of sector codes used with kilometer distances.

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

! . l iO fLEPORTING LEVELS FOR. RAD 10 ACTIVITY

'as't "-r CONCENTRATIONS IN ENVIRONMENTAL SAMPLES 6

Reporting Levels i

i i

f; 1 Analysis Hater Fish Milk Food Products I (pCill) AirbornePartleg)iate-or Gases (pCl/m (pC1/Kg, wet) (pC1/1) (pci/Kg. wet) l i i t-l H-3 2 x 104 (a) i Mn-54 1 x 103 3 x 104 i

1 x 104-Fe-59 4 x 102 s s

-4 3 x 10 Co-58 1 x 103 Co-60 3 x 102 - 1 x 104-Zn-65 3 x 102 2 x-104 ,

4

!- Zr-Nb-95 4 x 102 (b) 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 103- 70 2 x 103 Ba-la-140- 2 x 102 (b) 3 x 102 ,i a) For drinking water samples. This is 40 CFR Part 141 value.

- b) Total for perent and daughter.

11-9  ;

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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 LLDA *8 Units (4.66 t_1 Airborne " Particulate" Gross Beta + 0.01 pCi/m3 Gamma Isotopic 0.01 pC1/m 3 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 Gross Beta + . 1.0 pC1/g wet Gamma Isotopic' O.2 pC1/g wet 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 .

- - - . . . - - . _ _ - - - - - __- - _~._ . - , . - ._ . .-

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 i particular measurement system (which may include i radiochemical separation).

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 0.5 pCi/L on samples collected during the pasture season.

l i

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11-12

QUAD CITIES REVISION 0.C FEBRUARY 1991

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0FFSITE DOSE CALCULATION MANUAL QUAD CITIES SVATION

j. O MLK. FISH. WATER, AND SEDtMENT l EAMPLE LOCATONS i

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