ML051360174

From kanterella
Jump to navigation Jump to search
ODCM-07.01, Rev 7, Radiological Environmental Monitoring Program
ML051360174
Person / Time
Site: Monticello Xcel Energy icon.png
Issue date: 05/09/2005
From: Thomas J. Palmisano
Nuclear Management Co
To:
Document Control Desk, Office of Nuclear Reactor Regulation
References
FOIA/PA-2010-0209, L-MT-05-042 ODCM-07.01, Rev 7
Download: ML051360174 (24)


Text

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 1 of 24 I/plr OFFSITE DOSE CALCULATION MANUAL - TABLE OF CONTENTS SECTION PAGE 1.0 RECORD OF REVISION 2

2.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 3

2.1 Monitoring Program 3

2.2 Land Use Census 5

2.3 Sampling 6

2.4 Interlaboratory Comparison Program 7

2.5 Bases 8

Figure 1 Radiation Environmental Monitoring Program Sampling Locations 9

Figure 2 4 - 5 Mile Ring, Control and Special Interest TLD Locations 10 Figure 3 Site Boundary TLD Locations 11 Table 1 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sample Collection and Analysis 12 Table 2 Reporting Levels for Radioactivity Concentrations in Environmental Samples (Reporting Levels) 17 Table 3 Maximum Values for the Lower Limits of Detection (LLD)a,e 18 Table 4 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sampling Locations 20 OC Final Review Meeting:

Prepared By:

Approved By Plant Manager:

Reviewed By:

Date:

Date:

Resp Supv:

CHEM Assoc Ref:

SR:

2 yrs N

Freq:

CHEM-I ARMS:

ODCM-07.01 Doc Type:

Admin Initials:

Date:

7030 FOR ADMINISTRATIVE USE ONLY 3087 (DOCUMENT CHANGE, HOLD, AND COMMENT FORM) incorporated:

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 2 of 24 I/plr 1.0 RECORD OF REVISION Revision No.

Date Reason for Revision 1

October - 2000 Moved previous ODCM-05.01 (RADIATION ENVIRONMENTAL MONITORING PROGRAM) into this document, changed the title to RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM and incorporated Tech Spec section 4.16 Radiation Environmental Monitoring Program into this document.

2 November - 2001 Deleted incorrect reference in section 2.1.3.C.

3 November - 2002 Table 4, page 22, TLD M02S from Edgar Klucas Res., 1.1, 148, SE to Krone Residence, 0.5, 223, SW.

4 April - 2003 Table 4, page 20, TLD M-10c from Goenner Farm, 12.4, 322, NW to Campbell Farm, 10.6, 357, N.

5 October - 2003 Change in the Critical Garden location.

6 November - 2003 Updated sampling locations on Figures 1, 2 and 3.

7 September - 2004 Change in the Critical Garden location.

Change 2.4.1.A. to require cross check program to be NIST traceable. NRC no longer approves cross check programs.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 3 of 24 I/plr 2.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 2.1 Monitoring Program 2.1.1 Controls A.

In accordance with T.S.6.8.A, the Radiological Environmental Monitoring Program (REMP) SHALL be conducted as specified in Table 1.

B.

Radioanalysis SHALL be conducted meeting the requirements of Table 3.

2.1.2 Applicability At all times.

2.1.3 Action A.

Whenever the Radiological Environmental Monitoring Program is not being conducted as specified in Table 1 the Annual Radiological Environmental Operating Report SHALL include a description of the reasons for not conducting the program as required and plans for preventing a recurrence.

B.

Deviations are permitted from the required sampling schedule if samples are unobtainable due to hazardous conditions, seasonable unavailability, or to malfunctions of automatic sampling equipment. If the latter occurs, every effort SHALL be made to complete corrective action prior to the end of the next sampling period.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 4 of 24 I/plr C.

With the level of radioactivity in an environmental sampling medium exceeding the reporting levels of Table 2 when averaged over any calendar quarter, submit a special report to the Commission within 30 days from the end of the affected calendar quarter. When more than one of the radionuclides in Table 2 are detected in the sampling medium, this report SHALL be submitted if:

concentration (1) concentration (2)

+

+... >1.0 limit level (1) limit level (2)

When radionuclides other than those in Table 2 are detected and are the result of plant effluents, this report SHALL be submitted if the potential annual dose to an individual is equal to or greater than the calendar year limits of ODCM-02.01 (LIQUID EFFLUENTS) Control 1.2.1.A, ODC-M-03.01 (GASEOUS EFFLUENTS) Control 1.2.1.A, or ODCM-03.01 Control 1.3.1.A.

This report is not required if the measured level of radioactivity was not the result of plant effluents; however, in such an event, the condition SHALL be reported and described in the Annual Radiological Environmental Operating Report.

D.

Although deviations from the sampling schedule are permitted under Paragraph B. above, whenever milk or leafy green vegetation samples can no longer be obtained from the designated sample locations required by Table 1, the Annual Radiological Environmental Operating Report SHALL explain why the samples can no longer be obtained and identify the new locations which have been or will be added to and deleted from the monitoring program.

2.1.4 Surveillance Requirements The radiological environmental monitoring samples SHALL be collected pursuant to Table 1 from the specific locations in Table 4 and SHALL be analyzed pursuant to the requirements of Table 1 and the detection capabilities required by Table 3.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 5 of 24 I/plr 2.2 Land Use Census 2.2.1 Controls A Land Use Census SHALL be conducted and SHALL identify:

A.

The location of the nearest milk animal, the nearest residence, and the nearest garden of greater than 500 ft2 producing fresh leafy vegetables in each of the 16 meteorological sectors within a distance of 5 miles.

B.

The location of ALL milk animals and ALL 500 ft2 or greater gardens producing broad leaf vegetation in each of the meteorological sectors within a distance of 3 miles.

2.2.2 Applicability At all times.

2.2.3 Action A.

With a Land Use Census identifying a location which yields a calculated dose or dose commitment (via the same exposure pathway) 20 percent greater than at a location from which samples are currently being obtained in accordance with Controls 2.1.1.A., the Annual Radioactive Effluent Release Report for this period SHALL identify the new location. The new location SHALL be added to the Radiological Environmental Monitoring Program within 30 days. The sampling location, excluding the control station location, having the lowest calculated dose or dose commitment (via the same exposure pathway) may be deleted from this monitoring program after October 31 of the year in which this Land Use Census was conducted.

2.2.4 Surveillance Requirements A.

The Land Use Census SHALL be conducted at least once per year between the dates of May 1 and October 31 by door to door survey, aerial survey, or by consulting local agricultural authorities associations.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 6 of 24 I/plr 2.3 Sampling Table 1 and Figure 1 specify the current sampling locations for the radiation environmental monitoring program. These sampling locations are based on the latest land use census.

If it is learned from an annual census that milk animals or gardens are present at the location which yields a calculated thyroid dose greater than those locations previously sampled, the new milk animal or garden locations resulting in the higher calculated doses SHALL be added to the surveillance program as soon as practicable. Sample locations (except the control) having lower calculated doses may be dropped from the program at the end of the grazing or growing season (October 31) to keep the total number of sample locations constant.

If the plant begins routine discharges of liquid radioactive effluent into the Mississippi River, a land use survey will be conducted to determine whether any crops are irrigated with water taken from the Mississippi River between the plant discharge canal and a point 5 miles downstream. If edible crops are being irrigated from Mississippi River water, appropriate samples will be collected and analyzed per Table 1.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 7 of 24 I/plr 2.4 Interlaboratory Comparison Program 2.4.1 Controls A.

Analyses SHALL be performed on radioactive materials supplied as part of an NIST traceable cross--check program. This program involves the analyses of samples provided by a control laboratory and comparison of results with those of the control laboratory as well as with other laboratories which receive portions of the same samples. Media used in this program (air, milk, water, etc.) SHALL be limited to those found in the Radiological Environmental Monitoring Program.

2.4.2 Applicability At all times.

2.4.3 Action A.

When required analyses are not performed, corrective action SHALL be reported in the Annual Radiological Environmental Operating Report.

2.4.4 Surveillance Requirements A.

The summary results of analyses performed as part of the above required program SHALL be included in the Annual Radiological Environmental Operating Report.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 8 of 24 I/plr 2.5 Bases 2.5.1 Monitoring Program Control 2.1.1 provides measurements of radiation and radioactive materials in those exposure pathways and for those radionuclides which lead to the highest potential radiation exposures of individuals resulting from the plant operation. This program thereby supplements the radiological effluent monitoring by verifying that the measurable concentrations of radioactive materials and levels of radiation are not higher than expected on the basis of the effluent measurements and modeling of the environmental exposure pathways. After a specific program has been in effect for at least 3 years of operation, program changes may be initiated based on this experience.

The detection capabilities required by Table 1 are state-of-the art for routine environmental measurements in industrial laboratories. The LLDs for drinking water meet the requirement of 40CFR Part 141.

2.5.2 Land Use Census Control 2.2.1 is provided to ensure that changes in the use of off-site areas are identified and that modifications to the monitoring program are made if required by the results of this census. The best survey information from door-to-door, aerial or consulting with local agricultural authorities SHALL be used. This census satisfies the requirements of Section IV.B.3 of Appendix I to 10CFR Part 50. Restricting the census to gardens of greater than 500 square feet provides assurance that significant exposure pathways via leafy vegetables will be identified and monitored since a garden of this size is the minimum required to produce the quantity (26 kg/year) of leafy vegetables assumed in Regulatory Guide 1.109 for consumption by a child. To determine this minimum garden size, the following assumptions were used: 1) that 20% of the garden was used for growing broad leaf vegetation (i.e.,

similar to lettuce and cabbage), and 2) a vegetation yield of 2 kg/square meter.

2.5.3 Sampling Section 2.3, paragraph 3, is worded to conform to LAR-39 and its associated NRC Safety Evaluation (SER).

2.5.4 Interlaboratory Comparison Program The requirement for participation in an interlaboratory comparison program is provided to ensure that independent checks on the precision and accuracy of the measurements of radioactive material in environmental sample matrices are performed as part of a quality assurance program for environmental monitoring in order to demonstrate that the results are reasonably valid.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 9 of 24 I/plr Figure 1 Radiation Environmental Monitoring Program Sampling Locations

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 10 of 24 I/plr Figure 2 4 - 5 Mile Ring, Control and Special Interest TLD Locations

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 11 of 24 I/plr Figure 3 Site Boundary TLD Locations

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 12 of 24 I/plr Table 1 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sample Collection and Analysis Exposure Pathway Number of Samples Sampling and Type and Frequency and/or Sample and Sample Locations**

Collection Frequency of Analysis 1.

Airborne Radioiodine &

Samples from 5 locations:

Continuous Sampler Radioiodine analysis Particulates 3 samples from offsite locations operation with sample Weekly for I-131 (in different sectors) of the collection weekly.

highest calculated annual Particulate:

average ground level D/Q, 1 Gross beta activity sample from the vicinity of a on each filter community having the highest weekly*. Analysis calculated annual average SHALL be per-ground-level D/Q, and 1 sample formed more than from a control location specified 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> following in Table 4.

filter change.

Perform gamma isotopic analysis on composite (by location) sample quarterly.

2.

Direct 40 TLD stations established with Quarterly Gamma Dose Radiation duplicate dosimeters placed at quarterly the following locations:****

If gross beta activity in any indication sample exceeds 10 times the yearly average of the control sample, a gamma isotopic analysis is required.

Sample locations are further described in Table 4.

        • Three control TLD locations have only one dosimeter.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 13 of 24 I/plr Table 1 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sample Collection and Analysis (contd)

Exposure Pathway Number of Samples Sampling and Type and Frequency and/or Sample and Sample Locations**

Collection Frequency of Analysis 2.

Direct Radiation (contd)

1. Using the 16 meterological wind sectors as guidelines, an inner ring of stations in the general area of the site boundary is established and an outer ring of stations at 4 to 5 mile distance from the plant site is established. Because of inaccessibility, two sectors in the inner ring are not covered.
2. Ten dosimeters are established at special interest areas and four control stations.

3.

Waterborne

a. Surface Upstream & downstream Monthly composite of Gamma Isotopic locations.

weekly samples (water analysis of each

& ice conditions monthly composite permitting)

Tritium analysis of quarterly composites of monthly composites Sample locations are further described in Table 4.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 14 of 24 I/plr Table 1 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sample Collection and Analysis (contd)

Exposure Pathway Number of Samples Sampling and Type and Frequency and/or Sample and Sample Locations**

Collection Frequency of Analysis 3.

Waterborne (contd)

b. Ground Three samples from wells within Quarterly Gamma Isotopic 5 miles of the plant site and one and tritium analyses sample from a well greater than of each sample 10 miles from the plant site.
c. Drinking One sample from the City of Monthly composite of I-131 Analysis and Minneapolis water supply.

weekly samples Gross beta and Gamma isotopic analysis of each monthly composite Tritium analysis of quarterly composites of monthly composites

d. Sediment from One sample upstream of plant, Semiannually Gamma isotopic Shoreline one sample downstream of analysis of each plant, and one sample from sample shoreline of recreational area.

Sample locations are further described in Table 4.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 15 of 24 I/plr Table 1 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sample Collection and Analysis (contd)

Exposure Pathway Number of Samples Sampling and Type and Frequency and/or Sample and Sample Locations**

Collection Frequency of Analysis 4.

Ingestion

a. Milk One sample from dairy farm Monthly or biweekly if Gamma isotopic and having highest D/Q, one sample animals are on I-131 analysis of from each of three dairy farms pasture each sample (if available) calculated to have doses from I-131 >1 mrem/yr,and one sample from 10-20 miles.
b. Fish and One sample of one game specie Samples collected Gamma isotopic Invertebrates of fish located upstream and semi-annually analysis on each downstream of the plant site.

sample (edible portion only on One sample of Invertebrates fish).

upstream and downstream of the plant site.

Sample locations are further described in Table 4.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 16 of 24 I/plr Table 1 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sample Collection and Analysis (contd)

Exposure Pathway Number of Samples Sampling and Type and Frequency and/or Sample and Sample Locations**

Collection Frequency of Analysis 4.

Ingestion (contd)

c. Food Products One sample of corn and At time of harvest Gamma isotopic potatoes from any area that analysis of edible is irrigated by water in which portion of each liquid radioactive effluent has sample been discharged.***

One sample of broad leaf At time of harvest I-131 analysis vegetation from highest D/Q of edible portion garden and one sample from of each sample 10-20 miles.

Sample locations are further described by in Table 4.

As determined by methods outlined in section 2.3.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 17 of 24 I/plr Table 2 Reporting Levels for Radioactivity Concentrations in Environmental Samples (Reporting Levels)

Water Airborne Particulate Fish Milk Vegetables Analyis (pCi/l) or Gas (pCi/m3)

(pCi/kg, wet)

(pCi/l)

(pCi/kg, wet)

H-3 2 x 104(a)

Mn-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 Zn-65 3 x 102 2 x 104 Zr-Nb-95 4 x 102(b)

I-131 2(c) 0.9 3

1 x 102 Cs-134 30 10 1 x 103 60 1 x 103 Cs-137 50 20 2 x 103 70 2 x 103 Ba-La-140 2 x 102(b) 3 x 102(b) a - For drinking water samples b - Total for parent and daughter c - If no drinking water pathways exist, a value of 20 pCi/l may be used.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 18 of 24 I/plr Table 3 Maximum Values for the Lower Limits of Detection (LLD)a,e gross beta 4b 1 x 10-2 3H 2000(1000b) 54Mn 15 130 59Fe 30 260 58, 60Co 15 130 65Zn 30 260 95Zr-Nb 15c 131Id 1b 7 x 10-2 1

60 134, 137Cs 15(10b), 18 1 x 10-2 130 15 60 150 140Ba-La 15c 15c Water Airborne Particulate Fish Milk Food Products Sediment Analysis (pCi/l) or Gas (pCi/m3)

(pCi/kg, wet)

(pCi/l)

(pCi/kg, wet)

(pCi/kg, dry)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 19 of 24 I/plr Table 3 Maximum Values for the Lower Limits of Detection (LLD)a,e (contd)

TABLE NOTATION a -

The LLD is the smallest concentration of radioactive material in a sample that will be detected with 95%

probability with 5% probability of falsely concluding that a blank observation represents a real signal.

For a particular measurement system (which may include radiochemical separation):

LLD =

4.66 sb E. V. 2.22. Y. exp(- t) where:

LLD is the apriori lower limit of detection as defined above (as picocurie per unit mass or volume),

sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate (as counts per minute). Typical values of E, V, Y and t SHALL be used in the calculations.

E is the counting efficiency (as counts per transformation)

V is the sample size (in units of mass or volume) 2.22 is the number of transformations per minute per picocurie Y is the fraction radiochemical yield (when applicable) is the radioactive decay constant for the particular radionuclide t is the elapsed time between sample collection (or end the sample collection period) and time of counting b -

LLD for drinking water.

c -

Total for parent and daughter d -

These LLDs apply only where I-131 analysis is specified.

e -

Where Gamma Isotopic Analysis is specified, the LLD specifications applies to the following radionuclides: H-3, Mn-54, Fe-59, Co-58, Co-60, Zn-65, Zr-Nb-95, Cs-134, Cs-137 and Ba-La-140.

Other peaks which are measurable and identifiable, together with the above nuclides SHALL be identified and reported.REV 89 3/13/86

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 20 of 24 I/plr Table 4 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sampling Locations Location Type of Sample Code Collection Site Distance Miles Compass Heading Sector River water M-8c Upstream of plant w/in 1000 ft upstream of plant intake River water M-9 Downstream of plant w/in 1000 ft downstream of plant discharge Drinking water M-14 City of Minneapolis 37.0 132 SE Well water M-10c Campbell Farm 10.6 357 N

Well water M-11 City of Monticello 3.4 126 SE Well water M-12 Plant Well No. 11 0.2 232 SW Well water M-27 Wise Residence 0.6 198 SSW Sediment-River M-8c Upstream of plant w/in 1000 ft upstream of plant intake Sediment-River M-9 Downstream of plant w/in 1000 ft downstream of plant discharge Sediment-Shoreline M-15 Montissippi Park 1.4 114 ESE Periphyton or M-8c Upstream of plant w/in 1000 ft upstream of plant intake p y Macroinver-tebrates M-9 Downstream of plant w/in 1000 ft downstream of plant discharge Fish M-8c Upstream of plant w/in 1000 ft upstream of plant intake Fish M-9 Downstream of plant w/in 1000 ft downstream of plant discharge Milk M-10c Campbell Farm 10.6 357 N

Milk M-24 Weinand Farm 4.8 178 S

Milk M-28 Hoglund Farm 3.6 300 WNW

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 21 of 24 I/plr Table 4 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sampling Locations (contd)

Location Type of Sample Code Collection Site Distance Miles Compass Heading Sector Cultivated crops (leafy green vegetables)

M-27 Available Producer Highest D/Q Garden**

>10.0 0.64 207 SSW (corn)*

(potatoes)*

Particulates and Radio-iodine (air)

M-1c Air Station M-1 11.0 307 NW (air)

M-2 Air Station M-2 0.9 137 SE (air)

M-3 Air Station M-3 0.7 104 ESE (air)

M-4 Air Station M-4 0.9 146 SSE (air)

M-5 Air Station M-5 2.7 134 SE Direct Radiation - (general area of the site boundary)

(TLD)

M01A Sherburne Ave. So.

0.7 1

N (TLD)

M02A Sherburne Ave. So.

0.8 31 NNE (TLD)

M03A Sherburne Ave. So.

1.3 55 NE (TLD)

M04A Biology Station Rd.

0.6 91 E

(TLD)

M05A Biology Station Rd.

0.6 118 ESE (TLD)

M06A Biology Station Rd.

0.7 130 SE (TLD)

M07A County Road 75 0.6 148 SSE (TLD)

M08A County Road 75 0.6 170 S

(TLD)

M09A County Road 75 0.6 192 SSW (TLD)

M10A County Road 75 0.5 218 SW (TLD)

M11A County Road 75 0.4 240 WSW (TLD)

M12A County Road 75 0.4 260 W

(TLD)

M13A North Boundary Rd.

0.8 324 NW Collected only if plant discharges radioactive effluent into the river, then only from river irrigated fields. (See Section 2.1)

As determined by Annual Land Use Census.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 22 of 24 I/plr Table 4 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sampling Locations (contd)

Location Type of Sample Code Collection Site Distance Miles Compass Heading Sector (TLD)

M14A North Boundary Rd.

0.7 340 NNW Direct Radiation - (about 4 to 5 miles distant from the plant)

(TLD)

M01B Sherco No. 1 Air Sta.

4.6 3

N (TLD)

M02B County Road 11 4.4 20 NNE (TLD)

M03B County Rd. 73 & 81 4.3 53 NE (TLD)

M04B County Rd. 73 (196n Street) 4.3 68 ENE (TLD)

M05B City of Big Lake 4.4 90 E

(TLD)

M06B County Rd 14 &

196th Street 4.4 117 ESE (TLD)

M07B Monte Industrial Dr.

4.4 136 SE (TLD)

M08B Residence Hwy 25 &

Davidson Ave 4.7 161 SSE (TLD)

M09B Weinand Farm 4.8 178 S

(TLD)

M10B Reisewitz Farm -

Acacia Ave 4.2 204 SSW (TLD)

M11B Vanlith Farm - 97th Ave 4.0 226 SW (TLD)

M12B Lake Maria St. Park 4.2 254 WSW (TLD)

M13B Bridgewater Sta.

4.0 270 W

(TLD)

M14B Anderson Res. - Cty Rd 111 4.3 289 WNW (TLD)

M15B Red Oak Wild Bird Farm 4.3 309 NW (TLD)

M16B Sand Plain Research Farm 4.3 341 NNW Direct Radiation - (special interest locations)

(TLD)

M01S Osowski Fun Market 0.6 234 SW (TLD)

M02S Krone Residence 0.5 223 SW (TLD)

M03S Big Oaks Park 1.6 102 ESE (TLD)

M04S Pinewood School 2.4 129 SE

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 23 of 24 I/plr Location Type of Sample Sector Compass Heading Distance Miles Collection Site Code (TLD)

M05S Rivercrest Christian Academy 3.1 118 ESE (TLD)

M06S Monte Public Works 2.7 134 SE (TLD)

M01C Kirchenbauer Farm 11.5 323 NW (TLD)

M02C Cty Rd 4 & 15 11.2 47 NE (TLD)

M03C Cty Rd 19 & Jason Ave 13.0 100 E

(TLD)

M04C Maple Lake Water Tower 10.3 226 SW

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Revision 7 ODCM-07.01 MONTICELLO NUCLEAR GENERATING PLANT TITLE:

Page 24 of 24 I/plr Table 4 Monticello Nuclear Generating Plant Radiological Environmental Monitoring Program Sampling Locations (contd)

Notes on Table 4:

c denotes control locations. All other locations are indicator locations.

a. Control leafy green vegetable will be taken in locations as available outside 10 mi.

EPZ.

The letters after TLD code numbers have the following meanings:

A Locations in the general area of the site boundary; B Locations about 4 to 5 miles distant from the plant; S Special interest locations.