ML20217K438
| ML20217K438 | |
| Person / Time | |
|---|---|
| Site: | Wolf Creek  |
| Issue date: | 12/31/1997 |
| From: | Warren C WOLF CREEK NUCLEAR OPERATING CORP. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| WO-98-0032, WO-98-32, NUDOCS 9805010217 | |
| Download: ML20217K438 (183) | |
Text
W$LF CREEK NUCLEAR OPERATING CORPORATION Clay C. Warren Chief Operating Officer April 28, 1998 WO 98-0032 U. S. Nuclear Regulatory Commission ATTN:
Document Control Desk Mail Station F1-137 Washington, D. C.
20555
Subject:
Docket No. 50-482: Annual : adiological Environmental Operating Peport Gentlemen:
Enclosed is the Annual Radiological Environmental Operating Report, which is being submitted pursuant to Wolf Creek Generating Station (WCGS) Facility Technical Specification 6.9.1.6.
This report covers the operation of WCGS for the period of January 1, 1997 to December 31, 1997.
If you should have any questions regarding this submittal, please contact me at (316) 364-8831, extension 4485, or Michael J. Angus at extension 4077.
Very truly yours, Cla C. Warren CCW/rir Enclosure cc:
W.
D.
Johnson (NRC), w/e E. W.
Merschoff (NRC), w/e J.
F. Ringwald (NRC), w/e K.
M.
Thomas (NRC), w/e
\\\\
by I
9805010217 971231 PDR ADOCK 05000482 R
pyg i t, Jl y P.O. Box 411/ Burlington, KS 66839 / Phone: (316) 364-8831 An Equal Opportunity Employer M/F/HCNET
WOLF CREEK NUCLEAR OPERATING CORPORATION WOLF CREEK GENERATING STATION 1997 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT M
APRIL 14,1998
TABLE OF CONTENTS List of Tables ii List of Figures lii Introduction 1
I.
Program Description 2
II.
Discussion of Results 5
III.
Annual Land Use Census Results and Program Revisions 10 IV.
Program Deviations 11 V.
Interlaboratory Comparison Program Results 12 VI.
Comparison to Radioactive Effluents Release Program 13 Tables 14 Figures 36 4
Appendix A A-1 Appendix B B-1 i
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LIST OF TABLES i
l 1 1997 Radiological Environmental Monitoring Program 14 l
l 2 Sample Location Numbers, Distances, and Directions 19 1
3 Airborne Particulate Gross Beta Analyses 20 4 Airborne Particulate Ouarterly Composite Gamma Isotopic Analyses 21 5 First and Second Quarter TLD Results 22 1
6 Third and Fourth Quarter TLD Results 23 1
7 Drinking Water Radiological Analyses 24 l
8 Surface Water Radiological Analyses 25 I
9 Shoreline Sediment Radiological Analyses 26 10 Milk Radiological Analyses 26 l
11 Broadleaf Vegetation Radiological Analyses 26 12 Crop Radiological Analyses 27 l
13 Fish Radiological Analyses 27 l
14 Bottom Sediment Radiological Analyses 27 l
15 Aquatic Vegetation Radiological Analyses 28 16 Terrestrial Vegetation Radiological Analyses 28 17 Soil Radiological Analyses 28 1
18 1997 Land Use Census Data 29 l
19 1997 Land Use Census Milk and Garden Data 30 20 EPA Interlaboratory Comparison Program 1997 31 12 1 Analytics Cross Check Comparison Program 1997 33 l
22 Dosimetry Performance Testing Results 35 I
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LIST OF FIGURES 1 Airborne Pathway Sampling Locations 36 2 Direct Radiation Pathway Sampling Locations 37 3 Waterborne Pathway Sampling Locations 38 I
4 Ingestion Pathway Sampling Locations 39 5 Distant Sampling Locations 40 6 1997 Airborne Gross Beta Weekly Results 41 1
7 Historical Airborne Smoothed Indicator and Control Gross Beta 42
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i 8 TLD Nearsite Locations and Control Locations 43 9 Variation of Nearsite TLD Averages Expressed as a Ratio to Control 44 Values 10 Drinking Water Gross Beta, Historical 45 11 Wolf Creek Lake Surface Water Smoothed Tritium a
46 12 Cumulative Liquid Effluent Tritium Data 47
- 13. Cs-137 in Shoreline Sediment (Location Discharge Cove) 48 14 Tritium in Wolf Creek Lake Fish 49 15 Tritium Dose in WCL Surface Water and Released Liquid Tritium 50 Maximum Organ Dose lii i
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l INTRODUCTION l
The 1997 Annual Radiological Environmental Operating Report for Wolf Creek l
Generating Station (WCGS) covers the period from January 1,
through l
December 31, 1997.
WCGS is located in Coffey County, Kansas, approximately five miles northeast of Burlington, Kansas.
Fuel loading commenced at WCGS on March 12, 1985.
The operational phase of the Radiological Environmental Monitoring Program (REMP) began with initial 4
criticality on May 22,
- 1985, and the first detectable quantities of l
radioactivity were reported in plant effluents in June 1985.
This report contains a description of the REMP conducted by Wolf Creek Nuclear Operating Corporation (WCNOC), results of sample analyses, a discussion of l
monitoring program results, a description of revisions to and deviations from the program, and the results of Interlaboratory Comparison Programs.
Individual sample results and a summary of results in the Nuclear Regulatory Commission (NRC) Branch Technical Position specified format are included as appendices.
l During 1997, activation products were not detected in airborne particulate and radiciodine filters, broadleaf vegetation, crops, milk, ground water, soil, terrestrial vegetation or drinking water.
During 1997, activation products attributable to plant operation were detected in aquatic vegetation, shoreline sediment, bottom sediment, surface water and fish samples.
All nuclides detected in the REMP samples were below applicable NRC reporting levels and all required lower limits of detection were obtained, i
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l 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 1 of 50
l I.
PRCiGRAM DESCRIPTION Radiological environmental samples were collected according to the schedule in Attachment A,
Table 5-1 of the WCGS Offsite Dose Calculation Manual (ODCM).
Samples were collected by the WCGS Environmental Management group and were analyzed by Teledyne Brown Engineering Environmental Services of Westwood, New Jersey.
Environmental TLDs were processed by Enrico Fermi 2.
Table 1 lists j
sampling pathways and frequencies of sampling and analysis.
Table 2 lists each sample location's distance and direction from the plant.
Samples in addition *:.:...e required by the WCGS ODCM were also obtained.
The following is a description of the sampling and analysis program by individual pathways.
A.
Airborne Low volume air sampling pumps continually collected particulate and l
radioiodine samples on 47 mm glass fiber filters and charcoal canisters, respectively.
Weekly, the filters and charcoal canisters were changed out, labeled, and shipped to Teledyne Brown Engineering Environmental Services for analysis.
The volume of air sampled was calculated from the average of initial and final flow rates and the total time of collection.
Each pump was equipped with a time totalizer that was checked weekly against the elapsed time.
Gross beta analysis of - the air particulate samples was performed after 72 hours8.333333e-4 days <br />0.02 hours <br />1.190476e-4 weeks <br />2.7396e-5 months <br /> post collection to allow the radon and thoron daughter products to l
decay.
Weekly air particulate filters were combined into quarterly composites for each location and analyzed for gamma emitting isotopes.
Charcoal canisters were routinely counted in groups of five to determine the presence or absence of I-131.
Positive indication of I-131 would have resulted in analysis of each individual charcoal canister.
Air samples were collected from the three sectors with the highest ground level deposition constants (D/Q) (locations 2, 3 and 37), the community of New Strawn (location 32), and a control location (location 40).
Distances and directions to. sampling locations from the plant are listed in Table 2,
locations are shown in Figure 1 (nearby locations) and Figure 5 (distant locations).
B.
Direct Radiation Panasonic UD-814-AQ TLDs were used during the 1997 sample year.
The TLDs consist of one lithium-borate element and three calcium sulfate elements in a plastic case.
TLDs were typically positioned roughly 3 to 4 feet above the ground. The TLDs were contained in plastic thermostat boxes.
The thermostat boxes protect the TLDs from the elements and tampering.
Two TLDs were placed at each designated location.
TLD sample locations are illustrated in Figure 2 (nearby locations) and Figure 5 (distant locations).
Table 2 provides the distance and direction of each location from the plant.
i 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 2 of 50
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C.
Waterborne All water samples were analyzed to determine if gamma emitters were present.
In addition to gamma analysis, radiochemical analysis for I-131 was performed i
on drinking water and ground water samples.
Gross beta analysis was also l
performed on drinking water samples.
Tritium analysis was performed monthly by liquid scintillation for surface water and quarterly for drinking water.
Tritium analysis for ground water was performed quarterly by gas counting.
Water sampling locations are listed in Table 2 and shown in Figures 3 and 5.
Drinking water was sampled at the water treatment facilities for the towns of Burlington (control location) and LeRoy (indicator location).
The Burlington l
facility is located upstream and the LeRoy facility is located downstream of the confluence of the discharge from Wolf Creek Lake (WCL) and the Neosho River.
Monthly, composite samples were obtained from automatic composite samplers at each location that pulled approximately 10 ml samples hourly.
Grab samples were obtained fro: surface water locations monthly.
Surface water was sampled from the outfall of John Redmond Reservoir (JRR) as a control location and from the discharge cove and spillway of WCL for indicator I
locations.
Ground water samples were collected quarterly from four locations. One ground water well is hydrologically upgradient from the site (location B-12) and is used as a control location.
Three additional samples (C-10, C-49, and D-65) were obtained from wells hydrologically downgradient from the site as indicator samples.
Duplicate samples were obtained from location C-49 and were labeled L-4 9.
These duplicate samples served as a laboratory quality check.
Shoreline sediments were sampled semiannually for gamma analysis at the discharge cove (indicator, Figure 3), Make-up Water Discharge Structure (MUDS)
[ indicator, Figure 3] and at JRR (control, Figure 3).
Shoreline sediment samples were also obtained from the Environmental Education Area (EEA)
[ indicator, Figure 3].
Bottom sediments were collected semiannually for gamma analysis at the
)
discharge cove (indicator, Figure 3) and JRR (control, Figure 3).
Aquatic vegetation was collected semiannually for gamma analysis from the discharge cove (indicator, Figure 3),
MUDS (indicator, Figure 3) and EEA (indicator, Figure 3).
D.
Ingestion Milk samples were collected monthly from January through March and semimonthly during the month of April from the control location.
During 1997, the dairy that supplied control milk samples went out of business.
No sampling locations that produce milk for human consumption were identified within five miles of the plant during 1997.
The REMP was revised to require control samples be collected if indicator milk locations were sampled, thus, a control location was not established since milk indicator sampling locations are not available.
Radiochemical I-131 and gamma isotopic analyses were performed on l
each sample.
The control location (S-3) is illustrated on Figure 5.
j Broadleaf vegetation samples were collected monthly during the growing season from three gardens.
Two indicator gardens (Figure 4) and a control garden (Figure 5) were sampled.
Gamma isotopic analyses were performed on all j
samples.
j 1997 Annual Radiological Environmental Operating Report i
Wolf Creek Generating Station Page 3 of 50 l
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Three crop samples, one of which was irrigated with water from the Neosho River, were obtained from two locations downstream of the confluence of Wolf Creek and the Neosho River (indicator, Figure 5) and two samples were obtained upstream (control, Figure 4).
Gamma isotopic analysis was performed on each sample.
Fish were sampled semiannually from the tail waters of JRR (control, Figure 4) and from WCL (indicator, Figure 4) for gamma isotopic analysis.
Several species of gamefish and roughfish were sampled.
Gamma isotopic analysis was performed on boneless meat portions of the fish.
Fish were also analyzed for l
Soil was sampled semiannually from two locations, the MUDS and EEA, for gamma isotopic analyses.
These samples were a cooperative sgmpling effort with the Kansas Department of Health and Environment (KDHE).
i Terrestrial vegetation was also sampled semiannually from locations MUDS and EEA for gamma isotopic analyses.
These samples were a cooperative sampling effort with the KDHE.
l Sampling, locations listed in this section are outlined in Table 2.
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1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 4 of 50
II.
DISCUSSION OF RESULTS Analysis results for all pathways are summarized in Appendix A using the format described in Radiological Assessment Branch Technical
- Position, Revision 1, November 1979 (NRC Generic Letter 79-065).
Results for individual samples are listed in Appendix B.
In this section, results are discussed by pathway and analysis type.
Operational results are related to controls, preoperational values, sources of radioactivity, and effluent releases when applicable.
Trends or seasonal effects are discussed. Associated counting uncertainties for positive results on data contained in Tables 3 through 17 may be obtained in Appendix B.
A.
Airborne Results of the weekly gross beta analysis are summarized in Table 3.
In addition, Figure 6 illustrates a graph of weekly gross beta results for 1997.
Figure 7 represents the historical smoothed averages of indicator and control gross beta.
Figures 6 and 7 demonstrate how closely the indicator and control locations tracked together.
Figure 7 reveals a seasonal cyclic trend in which gross beta values peak in the winter months (December or January) and decrease to a low point in the spring months (May or June).
During the collection period starting November 18, 1997, and ending November 25, 1997, all locations had elevated gross beta activity detected.
Since the control location results were elevated as well as the indicator location results, the elevated results were not attributed to plant operation.
The KDHE gross beta analysis results on air particulates for the same time frame were also higher than normal at all sample locations by approximately 40 to 50 percent.
I-131 activity was not detected in the weekly analysis of charcoal filters.
Results of the quarterly gamma analysis of air particulate filter composites are summarized in Table 4.
Naturally occurring Be-7 and K-40 were the on' y nuclides detected.
Effects of plant operation were not seen via the airborne pathway for the year and no unusual trends were noted.
B.
Direct Radiation Quarterly gamma exposures measured at each location for 1997 are shown in Tables 5 and 6.
Values are normalized to a standard 90-day quarter.
Location 47 is located 0.16 miles south of the reactor and was added to the sampling program in the third quarter of 1997 due to an item identified during l
the annual Self-Assessment conducted by Quality Evaluations (Performance Improvement Request 97-1709).
The highest TLD results of the year were from location 47 (21.0 and 44.0 mR/90 day quarter for the third and fourth l
quarters, respectively).
The close proximity of location 47 to the Radwaste Building likely is the reason this location experiences the elevated results.
Waste generated from the outage which occurred during the fourth quarter is j
being stored in the Radwaste Building and activity from this stored waste likely was measured.
Performance Improvement Request 96-1898 was initiated July 25, 1996, regarding consistent TLD housings.
(Six locations had TLDs housed in air sampler boxes, while the rema.ning TLDs were housed in thermostat boxes.)
During the fourth l
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 5 of 50
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i quarter of 1996, two sets of TLDs were placed in the field at locations 2, 3, 31, 32, 37 and 40.
At each location, one set of TLDs were placed in the air sampler boxes and one set of TLDs were placed in newly installed thermostat boxes.
An evaluation was conducted that compared the results of the TLDs housed in air sampler boxes to the results of the TLDs that were housed in thermostat boxes.
The conclusion from that evaluation was that moving the TLDs from air sampler boxes to thermostat boxes did not significantly impact the TLD results.
The environmental TLDs in the field are now housed in thermostat boxes at all of the sample locations.
Results from TLDs located near the plant (less than approximately three miles), which would be most sensitive to changes due to plant operation, were combined into quarterly averages.
These nearsite averages, using locations 1, 2,
7-14, 18, 26-30, 37 and 38, are compared to control location results (locations 39 and 40) in Figure 8.
In addition, variation of the nearsite averages from the control location results is displayed graphically in Figure 9.
These figures also include preoperational data for comparison.
The nearsite TLD locations have historically trended higher than the control locations both prior to and after WCGS became operational.
No unusual trends were noted.
C.
Waterborne (1) Drinking Water Results of drinking water gamma isotopic analyses are summarized in Table 7.
Figure 10 illustrates the historical drinking water gross beta data through 1997.
Only gross beta activity was detected in drinking water and it was detected in all of the drinking water samples.
The annual mean of the control location gross beta activity (5.7 pCi/ liter) was higher than the annual mean of the indicator location (5.0 pCi/ liter).
Figure 10 illustrates how closely the gross beta results were for the indicator and control locations.
Activity due to plant operation was not evident in drinking water samples during 1997 and no unusual trends were noted.
(2)
Surface Water Tritium, attributable to WCGS operation, was detected in all surface water samples collected from WCL in 1997 According to the Radioactive Effluents Release Program, a total of 1,351 curies of liquid tritium was released during the year.
Measured concentrations are shown in Table 8.
An adult drinking 1.5 liters per day of surface water collected from the discharge cove, using the highest detected tritium activity (15,000 pCi/ liter), would receive a i
calculated committed dose of 0.51 mrem per year.
(According to the National Council on Radiation Protection and Measurements (NCRP Report No.
94), the j
estimated total effective dose equivalent rate for a member of the population in the United States from various sources of natural background radiation is 300 mrem per year.)
Figure 11 illustrates smoothed tritium data for locations DC and SP from startup in May 1985 through 1997.
The cumulative curies of liquid tritium released to WCL is illustrated on Figure 12.
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During 1997, the annual mean for detected tritium at the WCL spillway was 12,145 pCi/ liter.
It can be seen in Figure 11 that monthly surface water tritium concentrations have increased since plant startup.
This is expected until the tritium concentration of the lake reaches equilibrium, which has been estimated at 13,074 pCi/ liter.
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 6 of 50 i
i Tritium was the only activity detected in surface water samples and no unusual trends were noted.
(3)
Ground Water During 1997, radioactivity was not detected in ground water samples.
(4)
Shoreline Sediment Naturally occurring nuclides (K-40, Ra-226 and Th-228) were detected in all shoreline sediment samples.
Another naturally occurring nuclide (Be-7) was detected in four indicator location samples.
Co-60 was detected (133 pCi/kg) in a sample obtained from the WCL discharge cove.
This activity is attributable to plant operation.
Cs-137 was detected (156 pCi/kg) in a sample obtained from the EEA indicator location.
Since Cs-134 was not detected, this activity may indicate fallout as opposed to newly produced fission products.
The presence of Cs-134 is expected if the occurrence of Cs-137 is related to plant operation.
Since Cs-134 has a shorter half-life than Cs-137 (2 years versus 30 years), it is not expected to be found when the presence of Cs-137 is due to fallout.
Cs-137 was also detected (103 pCi/kg) in a sample obtained from the JRR control location.
Figure 13 illustrates that Cs-137 activity was detected preoperationally and is routinely detected at the discharge cove.
In 1997, Cs-137 activity was not detected in discharge cove samples.
A linear trendline indicates that the Cs-137 activity detected in the discharge cove is showing a downward trend.
Analysis results are summarized in Table 9.
D.
Ingestion (1) Milk No indicator locations for milk existed during 1997 (see Program Deviation section for explanation).
Control samples were obtained January through April.
The dairy supplying samples went out of business during the sample year.
All milk samples analyzed contained K-40.
The yearly average K-40 concentration was 1,360 pCi/ liter.
Table 10 summarizes milk analysis results for 1997.
No other gamma emitters were detected.
(2)
Food and Garden Crops Gamma analyses of broadleaf vegetation samples during 1997 detected naturally occurring gamma emitters Be-7 and K-40.
Additional gamma emitters were not detected in broadleaf vegetation samples. Activity due to plant operation was not detected.
Table 11 shows the results of 1997 analysis, in addition to broadleaf vegetation, crop samples were collected.
Two control samples were obtained from cropland upstream of the confluence of Wolf Creek and the Neosho River, and three indicator samples were obtained downstream.
One indicator sample location was irrigated with Neosho River water.
Due to the wet summer, the other sample locations were not irrigated with Neosho River water.
Gamma analysis detected naturally occurring K-40 to be present in all of the samples, with no nuclides detected due to plant operation.
Results of crop analyses are summarized in Table 12.
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1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 7 of 50
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(3)
Fish Analysis results are illustrated in Table 13.
Naturally occurring K-40 activity was detected in all fish samples.
Cs-137 activity (20.7 pCi/kg) was detected in an WCL indicator sample.
Although fallout Cs-137 is regularly measured in other environmental media and is probably reflected, it is assumed that the Cs-137 concentration is attributable to WCGS operational releases since Cs-137 activity was not detected in the four control samples. An adult consuming 21 kilograms of fish with a Cs-137 concentration of 20.7 pCi/kg would receive a calculated committed dose of 0.020 mrem.
(According to the National Council on Radiation Protection and Measurements
[NCRP Report No.
94),
the estimated total effective dose equivalent rate for a member of the population in the United States from various sources of natural background radiation is 300 mrem per year.)
During 1997, fish were also analyzed for tritium. All fish samples taken from WCL had tritium activity detected (7,108 pCi/kg annual mean).
The detected tritium activity is attributable to plant operation.
An adult consuming 21 kilograms of fish, at the maximum measured tritium concentration for 1997 (14,000 pCi/kg) would receive a calculated committed dose of 0.018 mrem.
(According to the National Council on Radiation Protection and Measurements (NCRP Report No. 94], the estimated total effective dose equivalent rate for a member of the population in the United States from various sources of natural background radiation is 300 mrem per year.)
Figure 14 illustrates the tritium concentrations detected in fish from WCL.
Tritium activity was also detected in one sample obtained from the JRR control location (270 pCi/kg), which may be attributed to residual left from weapons testing.
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E.
Special Samples (not required by the WCGS ODCM)
(1)
Bottom Sediment Table 14 shows gamma emitters detected during 1997 in bottom sediment samples.
Naturally occurring nuclides detected include K-40, Ra-226, and Th-228.
Mn-54 was detected (94.3 pCi/kg) in a WCL discharge cove sample.
This activity is attributable to plant operation and is regularly identified in plant effluents.
Co-60 was detected in both samples obtained from the WCL discharge cove.
Co-60 activity is attributable to plant operation and is commonly identified in plant effluents.
Cs-137 activity was detected in samples taken from indicator locations and in samples taken from the control location.
Since Cs-134 was not present and Cs-137 activity was also detected from the control location samples, this activity is primarily due to fallout, and not to a newly produced fission product of plant origin.
No other radionuclides were detected.
l (2) Aquatic Vegetation l
Table 15 lists gamma emitters detected in aquatic vegetation samples.
Naturally occurring Be-7, K-40, Ra-226 and Th-228 were detected.
Other activity detected included Mn-54, Co-58, Co-60, Sb-125, Cs-134 and Cs-137.
This activity is attributed to plant operation and is regularly identified in plant effluents.
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Terrestrial Vegetation Pasturage samples were obtained from two locations:
EEA and MUDS.
All i
samples had naturally occurring Be-7 and K-40 activity detected.
No other l
nuclides were detected.
Table 16 reflects gamma emitters detected in l
terrestrial vegetation samples.
(4)
Soil Soil samples were obtained from two locations:
EEA and MUDS.
Naturally occurring Be-7, K-40, Ra-226 and Th-228, activity was detected.
Cs-137 activity was detected in three of the four soil samples.
The Cs-137 activity is attributable to fallout since Cs-134 activity was not detected and the activity levels for Cs-137 are well within the preoperational range (255 to 2,160 pC1/kg).
Table 17 lists the activity detected in soil samples.
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1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 9 of 50
I III.
ANNUAL LAND USE CENSUS RESULTS AND PROGRAM REVISIONS i
l Summary The annual Land Use Census of rural residents within five miles of WCGS was completed in 1997.
Changes were required in the REMP regarding broadleaf i
vegetation sample locations and their D/Q rankings for the 1998 sampling l
period.
The two locations with the highest calculated annual average D/0 rankings are G1.6-QURD1384 and F1.8-14RD1730.
The ODCM specifies that an
" alternate location may be used to provide continued monitoring".
The garden at E1.8-QULA1485 is third by the D/O ranking, and was a likely candidate for the alternate garden location.
The residents at G1.6-QURD1384 and F1.8-14RD1730 have agreed in the past to allow sampling from their respective gardens.
The residents at G1.6-QURD1384, F1.8-14RD1730 and E1.8-QULA1485 have been contacted and the REMP has been revised accordingly.
The results and
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notable changes are summarized and illustrated in Tables 18 and 19.
B-tground Section 5.2, Attachment A, of the ODCM procedure (AP 07B-003), directs that "a l
Land Use Census shall be conducted annually during the growing season to identify the nearest (1) milk animal, (2) residence, and (3) garden of greater i
l that 500 square feet producing broadleaf vegetation in each of the 16 meteorological sections within five miles of the WCGS site" and "the results of the Land Use Census shall be included in the Annual Radiological Environmental Operating Report."
Table 5-1, Attachment A,
of the ODCM requires that broadleaf vegetation samples be collected from "two indicator locations with the highest calculated annual average D/Q."
Table 5-1, Attachment A,
of the ODCM also requires that milk samples be collected from "three indicator locations within 5 miles of the site having the highest dose potential."
l Methodology Surveys were mailed to the rural residents within five miles of WCGS during the third week of June 1997.
A follow-up mailing was sent to residents who did not respond.
The survey excluded the residents of New Strawn, Burlington, and a trailer park just north of Burlington.
These locations are excluded due i
to the large number of households and the low likelihood that information l
gained from these residences would affect the locations chosen for REMP sampling.
Of the 165 surveys mailed to the rural residents, 131 were returned by mail and 34 surveys were partially completed with information obtained by driving by the locations.
I Results l
l Table 18 reflects the nearest residences, milk animals and broadleaf gardens.
l Table 19 lists the changes as compared to the 1996 Land Use Census results for l
milk animals and gardens producing broadleaf vegetation.
l Changes in the nearest residence occurred in three sectors (J, M and P) and no milk locations were identified.
Numerous location changes were noted for the nearest garden producing broadleaf vegetation.
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 10 of 50
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i IV.
PROGRAM DEVIATIONS Drinking Water Location BW-15 (Burlington):
On November 18, the drinking water sampler was found with a disconnected hose.
Drinking water wLs not sampled from November 4 through November 18.
A grab sample was obtained and the drinking water sampler was re-started with the hose connected.
A follow-up check made on November 19 found the drinking water sampler operable.
(Performance Improvement Request 97-3828) i TLDs j
Location 13:
During changeout of the second quarter environmental TLDs, it was discovered that the TLDs in the field were missing.
A new utility pole apparently had been recently installed.
"Do Not Disturb" stickers were generated which adhere to the outside of the TLD boxes.
The stickers identify the boxes as property of WCNOC and list tr.3 company address and telephone number.
(Performance Improvement Request 97-2944)
Milk 1
Indicator sample locations are still unavailable within five miles of the plant.
Refer to Section III, Annual Land Use Census Results and Program i
Revisions.
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1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 11 of 50
V.
INTERLABORATORY COMPARISON PROGRAM RESULTS Teledyne Brown Engineering Environmental Services is contracted to perform radiological analysis of environmental samples for the WCGS.
Teledyne participated in the Environmental Protection Agency (EPA) Interlaboratory Comparison Program during 1997 Table 20 shows interlaboratory comparison test results received during the year.
The table lists the collection date, the sample medium, the nuclide or analysis tvpe, the known value reported by the EPA, the measured value reported by Teledyne Brown Engineering Environmental Services (based upon triplicate analysis), and the normalized deviation from the known.
Beginning with 1996, the EPA discontinued providing milk and air particulate filter samples.
For replacements, *eledyne Brown Engineering Environmental Services purchased comparable spiked samples from Analytics, Incorporated (see Table 21).
Table 22 is a summary of statistical results of performance testing of TLDs processed at Enrico Fermi 2 (Detroit Edison) in participation with the National Voluntary Laboratory Accreditation Program.
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1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 12 of 50
I VI. COMPARISON TO THE RADIOACTIVE EFFLUENTS RELEASE PROGRAM As described in the sections discussing radioisotopes found in the surface l
water from WCL, dose that may be received as a result of tritium released from l
WCGS is consistent with the theoretical doses as calculated by the Radioactive Effluent Release Program.
Figure 15 indicates that the dose to a man resulting from drinking surface water from WCL lake is within a reasonable expected value.
Dose for the surface water was determined using the December tritium activity detected for each calendar year at the discharge cove.
Released tritium maximum organ dose (mnem) values were obtained from Annual Radioactive Effluent Release Reports and are not cumulative (the values reflected are the totals for the respective year).
The tritium dose values are being compared on a qualitative basis.
It 1.=
not expected that the annual doses, as calculated in the Radioactive Effluent Release Report, would compare directly to those calculated from the REMP.
The Radioactive Effluent Release Report provides a ' snap shot' of potential dose resulting from the years release.
The REMP indicates the accumulated result of releasing tritium into the cooling lake since the start of plant operation.
Additional comparisons showed that all plant-related nuclides detected in REMP samples are identified as being released by the Radioactive Effluent Release Program.
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TABLE 1 1997 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (SAMPLE COLLECTION REQUIRED BY ODCM)
EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY /
AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS AIRBORNE Figures 1 & 5 Radiciodine Samples from five Continuous sampler Analyze and locations operation with sample radiciodine Particulates collection weekly, or canister weekly more frequently if for I-131 required by dust l
loading.
l Samples from Analyze locations near the particulate site boundary in filter weekly three sectors for gross beta having the highest activity; calculated annual perform average D/O quarterly gamma (Locations 2, 3,
isotopic and 37 on Figure 1) analysis composite (by location)
Sample from the vicinity of a I
community having the highest calculated annual average D/O l
(Location 32 on l
Figure 1, New Strawn) l Sample from a control location 10-20 miles distant l
in a low D/O sector l
(Location 40 on l
Figure 5) i i
i 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 14 of 50
TABLE 1 (Cont)
EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND FREQUENCY "ATHWAY/
AND SAMPLE LOCATIONS COLLECTION FREQUENCY OF ANALYSIS SAMPLE DIRECT RADIATION Figures 2 & 5 40 routine Quarterly Gamma dose monitoring stations quarterly with two or more dosimeters measuring dose continuously, placed as follows:
An inner ring of stations, one in each meteorological sector 0-3 mile range from the site (Locations 1, 7-9, 11-13, 18, 26, 27, 29-31, 37, 38 and 47 on Figure 2)
An outer ring of stations, one in each meteorological sector in the 3-5 mile range from the site (Locations 4-6, 15-17, 19-25, and 33-36 on Figure 2).
Five sectors (A, B, D, G, and L]
contain an additional station (Locations 2, 3, 10, 14 and 28)
The balance of the stations to be placed in special interest areas such i
as population centers (Locations 23 and 32), nearby I
residences l
l l
l l'
l 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 15 of 50
TABLE 1 (Cont)
EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE.WD PATHWAY /
AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE IDCATIONS ANALYSIS DIRECT RADIATION (cont)
(many locations are near a residence),
schools (Location 23), and in one or l
two areas to serve as control stations 10-20 miles distant from the site (Locations 39 and 40 on Figure 5)
NATERBORNE Figure 3 Surface One sample upstream Monthly grab sample Monthly gamma (Location MUSH on isotopic Figure 3) and one analysis and sample downstream composite for (Location DC on tritium analysis Figure 3).
quarterly i
Ground Samples from one or Quarterly grab sample Quarterly gamma two sources only if isotopic and I
l likely to be tritium analysis affected.
i l
l Indicator samples at locations hydrologically downgradient of the site (Locations C-10, C-49, and D-65 on Figure 3);
Control sample at a location hydrologically upgradient of the site (Location B-12 on Figure 3)
I l
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 16 of 50
TABLE 1 (Cont)
EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY /
AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS WATERBORNE (cont)
Drinking Sample of municipal Monthly Composite Monthly gamma water supply at an isotopic indicator location analysis and downstream of the gross beta site (Location analysis of LW-40 on Figure 5);
composite control sample from
- sample, location upstream Quarterly of the site tritium analysis (Location BW-15 on of composites.
Figure 3)
Shoreline One sample from the Semiannually Semiannual gamma sediment vicinity of Wolf isotopic Creek Lake analysis discharge cove; control sample from John Redmond Reservoir (Locations DC and JRR respectively on Figure 3)
INGESTION Figures 4 & 5 Milk Samples from Semimonthly April to Gamma isotopic milking animals at November; monthly analysis and three indicator December-March I-131 analysis locations within of each sample five miles of the site having the highest dose potential (currently there are no locations producing milk for human consumption within five miles of the site); one sample from a control location greater than 10 miles from the site if indicator locations are sampled.
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 17 of 50
TABLE 1 (Cont)
EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY /
AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF
. SAMPLE LOCATIONS ANALYSIS INGESTION (cont)
Fish Indicator samples Semiannually Gamma isotopic of 1-3 analysia on recreationally edible portions important spe,ies from Wolf Creek i
l Lake; control i
samples of similar l
species from John l
Redmond Reservoir spillway (Figure 4)
Broadleaf Samples of Monthly when Gamma isotopic
. Vegetation available broadleaf available analysis on vegetation fAom two edible portions indicator locations with highest i
calculated annual l
average D/O (Locations R-1 and G-1 and alternate location F-1);
sample of similar broadleaf vegetation from a control location greater than 10 miles from the site in a low D/O sector (Location S-4 on Figure 5)
Irrigated Sample of crops At time of harvest Gamma isotopic Crops irrigated with analysis on water from the edible portions Neosho River downstream of the Neosho River - Wolf l
Creek confluence i
(Location NR-D1 and j
NR-D2 on Figure 5) l i
i 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 18 of 50
i i
TABLE 2-l SAMPLE LOCATION NUMBERS, DISTANCES (Miles), AND DIRECTIONS l
Location Distance /
Location Distance /
Location Number Distance /
Number Direction Number Direction Direction Air Particulates and Radioiodines 2
2.7/N l
3 3.0/NNE 32 3.2/WNW 37 2.1/NNW 40
>15.0/WNW l
TLDs 1
1.4/N 17 3.6/SE 33 3.7/WNW 2
2.7/N 18 3.0/SSE 34 4.0/NW 3
3.0/NNE 19 4.0/SSE 35 4.6/NNW 4
4.0/NNE 20 3.3/S 36 4.2/N 5
4.0/NE 21 3.8/S 37 2.1/NNW 6
4.4/ENE 22 4.1/SSW 38 1.2/NW 7
1.9/NE 23 4.5/SW 39 13.0/N 8
1.6/NNE 24 4.1/WSW 40
>15.0/WNW l
9 2.0/ENE 25 3.6/W 41 0.8/NNW 10 2.4/ENE 26 2.6/WSW 42 0.8/SSE 11 1.6/E 27 2.1/SW 43 0.8/WNW 12 1.8/ESE 28 2.8/SW 44 3.0/NNW 13 1.5/SE 29 2.6/SSW 45 1.6/WNW 14 2.6/SE 30 2.2/W 46 1.5/WNW j
15 4.5/ESE 31 3.0/WNW 47
.16/S 16 4.2/E 32 3.2/WNW l
l Ground water Drinking water Surface water j
l B-12 2.2/NNE BW-15 3.9/SW MUSH 3.6/W j
C-10 2.8/W LW-40
>10.0/SSE DC 0.6/WNW C-49/L-49 2.9/SW SP 2.9/S D-65 3.9/S Milk Broadleaf vegetation Irrigated Crops l
S-3
>15.0/WNW F-1 1.8/ESE NR-U1 4.2/SW G-1 1.6/SE NR-D1 9.2/S l
S-4
>15.0/WNW NR-D2
>10.0/S Fish Shoreline Soil Aquatic Vegetation / Algae WCL 0.6/WNW DC 0.6/WNW DC 0.6/WNW JRR 4.0/W JRR 4.0/W EEA 3.0/NNW EEA 3.0/NNW MUDS 1.5/WNW MUDS 1.5/WNW Terrestrial Vegetation & Soil Botton Sediment EEA 3.0/NNW DC 0.6/WNW MUDS 1.5/WNW JRR 4.0/W l
l 1997 Annual Radiological Environmental Operating Report l
Wolf Creek Generating Station Page 19 of 50
TABLE 3 Airborne Particulate Gross Beta Analyses (pCi/ cubic noter, analysis counting uncertainties reported in Appendix B)
Date Location Beginning Ending 2
3 32 37 40 (Control) 12/31/96 01/06/97 0.032 0.035 0.028 0.033 0.035 01/06/97 01/14/97 0.025 0.026 0.027 0.025 0.029 01/14/97 01/21/97 0.026 0.027 0.027 0.025 0.028 01/21/97 01/30/97 0.030 0.032 0.034 0.034 0.035 01/30/97 02/04/97 0.023 0.025 0.019 0.024 0.023 02/04/97 02/11/97 0.021 0.028 0.024 0.021 0.028 02/11/97 02/18/97 0.020 0.024 0.024 0.025 0.027 02/18/97 02/26/97 0.017 0.016 0.018 0.021 0.017 02/26/97 03/04/97 0.018 0.019 0.016 0.022 0.020 03/04/97 03/12/97 0.018 0.020 0.017 0.020 0.010 03/12/97 03/18/97 0.020 0.020 0.020 0.024 0.022 03/18/97 03/25/97 0.019 0.021 0.019 0.021 0.020 03/25/97 04/01/97 0.014 0.016 0.014 0.016 0.019 04/01/97 04/08/97 0.019 0.019 0.019 0.020 0.016 04/08/97 04/16/97 0.020 0.021 0.020 0.020 0.023 04/16/97 04/22/97 0.023 0.026 0.025 0.028 0.027 04/22/97 04/30/97 0.017 0.017 0.015 0.020 0.018 04/30/97 05/06/97 0.015 0.017 0.013 0.019 0.017 05/06/97 05/13/97 0.017 0.018 0.016 0.017 0.016 05/13/97 05/20/97 0.017 0.016 0.017 0.017 0.016 05/20/97 05/27/97 0.014 0.015 0.016 0.016 0.014 05/27/97 06/04/97 0.013 0.014 0.014 0.018 0.016 06/04/97 06/10/97 0.022 0.018 0.021 0.023 0.018 06/10/97 06/17/97 0.020 0.018 0.018 0.022 0.021 06/17/97 06/24/97 0.020 0.021 0.020 0.021 0.022 06/24/97 07/01/97 0.016 0.013 0.018 0.018 0.017 07/01/97 07/09/97 0.015 0.016 0.016 0.017 0.017 07/09/97 07/15/97 0.016 0.019 0.019 0.018 0.020 07/15/97 07/22/97 0.022 0.023 0.024 0.026 0.027 07/22/97 07/29/97 0.032 0.027 0.033 0.028 0.032 07/29/97 08/06/97 0.032 0.027 0.032 0.029 0.030 08/06/97 08/13/97 0.028 0.027 0.025 0.027 0.029 08/13/97 08/19/97 0.020 0.021 0.021 0.021 0.024 08/19/97 08/27/97 0.033 0.035 0.036 0.033 0.031 08/27/97 09/03/97 0.040 0.038 0.043 0.042 0.038 09/03/97 09/09/97 0.035 0.034 0.035 0.038 0.033 09/09/97 09/16/97 0.036 0.032 0.033 0.034 0.033 09/16/97 09/23/97 0.023 0.022 0.025 0.029 0.024 09/23/97 09/30/97 0.020 0.019 0.022 0.022 0.021 09/30/97 10/07/97 0.038 0.035 0.035 0.035 0.034 10/07/97 10/14/97 0.019 0.022 0.021 0.022 0.020 i
10/14/97 10/21/97 0.024 0.025 0.026 0.028 0.027 l
10/21/97 10/28/97 0.022 0.020 0.023 0.022 0.021 10/28/97 11/04/97 0.021 0.023 0.023 0.026 0.024 l
11/04/97 11/11/97 0.021-0.019 0.024 0.022 0.020 11/11/97 11/18/97 0.027 0.030 0.031 0.031 0.032 11/18/97 11/25/97 0.057 0.055 0.061 0.062 0.062 11/25/97 12/02/97 0.025 0.028 0.027 0.027 0.025 12/02/97 12/10/97 0.018 0.017 0.018 0.019 0.018 12/10/97 12/17/97 0.038 0.037 0.039 0.039 0.035 12/17/97 12/24/97 0.026 0.027 0.025 0.024 0.024 12/24/97 12/31/97 0.018 0.017 0.020 0.021 0.018 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 20 of 50
TABLE 4 Airborne Particulate Quarterly Composite C====
Isotopic Analyses (pCi/ cubic meter, analysis counting uncertainties reported in Appendix B)
Location Quarter Be-7 K-40 2
1 0.0644 3
1 0.0683 32 1
0.0616 37 1
0.0660 40 1
0.0685 2
2 0.0979 3
2 0.0804 32 2
0.0860 37 2
0.10S 40 2
0.109 2
3 0.0887 3
3 0.0820 1
32 3
0.0965 37 3
0.0970 40 3
0.0905 2
4 0.0612 3
4 0.0503 32 4
0.0717 0.00805 37 4
0.0526 0.0227 40 4
0.0545 l
l i
l i
l l
l l
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 21 of 50
i i
TABLE 5 First and Second Quarter TLD Results (ar/90 day qtr)
First Quarter Second Quarter Location Days 90 Day 2 std dev Location Days 90 Day 2 std dev Average Average l
1 79.0 17.3 0.4 1
83.9 17.9 0.8 l
2 79.2 15.8 0.8 2
83.8 16.5 1.0 l
3 79.2 16.1 0.9 3
83.8 16.8 1.1 4
79.2 16.8 0.6 4
83.8 17.6 1.3 5
79.2 15.3 0.8 5
83.8 16.4 0.5 6
79.1 15.5 0.7 6
83.8 16.1 0.6 7
79.0 15.3 1.0 7
83.9 16.3 0.8 8
79.0 16.7 1.0 8
83.9 17.9 1.0 9
79.1 14.9 0.6 9
83.8 15.6 1.3 10 79.1 16.8 1.2 10 83.9 17.7 0.6 11 79.1 17.5 0.2 11 83.8 18.9 1.4 12 79.1 16.3 0.9 12 83.8 17.1 0.8 13 79.1 17.0 1.6 13***
14 79.1 16.8 0.7 14 83.8 18.0 0.6 15 79.2 16.7 1.1 15 83.7 17.4 0.6 16 79.2 16.6 0.9 16 83.7 17.0 0.8 17 79.1 15.9 0.6 17 83.7 16.8 0.7 ~~
j 18 79.1 17.3 0.8 18 83.7 18.3 0.7 19 79.1 17.7 1.1 19 83.9 18.0 0.6 20 79.1 16.7 0.8 20 83.9 17.9 0.9 21 79.1 14.1 0.8 21 83.9 14.9 0.9 22 79.1 16.9 1.7 22 83.9 17.6 1.0 23 79.1 16.3 1.1 23 83.9 17.4 1.2 24 79.1 16.3 0.8 24 83.9 17.5 1.1 l
25 79.1 13.3 1.0 25 83.8 14.3 0.7 26 79.1 14.7 0.4 26 83.8 15.9 0.5 27 79.0 16.5 0.9 27 83.8 17.4 1.3 28 79.0 14 4 O.7 28 83.8 15.3 0.9 29 79.0 13.7 0.8 29 83.8 14.9 0.9 j
30 80.0 16.0 1.5 30 82.9 13.1 0.6 31 79.1 15.5 0.8 31 83.8 16.8 1.1 32 79.3 15.0 0.9 32 83.8 16.4 0.9 33 79.1 16.7 1.0 33 83.8 18.0 0.7 34 79.2 16.6 1.0 34 84.8 17.8 1.1 l
35 79.1 16.0 0.9 35 83.8 16.9 0.8 j
36 79.2 15.7 1.3 36 83.8 17.0 0.8 l
37 79.0 15.4 1.4 37 84.0 16.7 0.7 l
38 79.0 17.3 1.0 38 84.0 19.1 1.3 39 79.1 15.8 0.9 39 84.9 17.4 0.9 40 79.1 13.9 1.1 40 84.9 14.6 0.7 41 79.0 16.0 0.8 41 83.9 16.0 0.7 42 79.1 11.2 0.7 42 83.9 12.0 0.6 43 79.2 10.7 0.7 43 83.8 11.4 0.9 44 78.8 16.3 0.9 44 84.0 17.1 1.4 45 79.1 17.2 0.8 45 83.9 18.4 0.9 46 79.1 16.0 0.9 46 83.8 17.1 0.5 TLDs disappeared while in the field 1997 Annual Radiological Environmental Operating Report I
Wolf Creek Generating Station Page 22 of 50 1
a TABLE 6 Third and Fourth Quarter TLD Results (ar/90 day qtr)
Third Orarter Fourth Quarter Location Days 90 Day 2 std dev Location Days 90 Day 2 std dev Average Average 1
97.1 19.0 1.5 1
98.0 15.5 1.6 2
97.1 16.9 1.4 2
98.1 13.5 1.1 3
97.1 17.4 0.4 3
98.1 13.5 1.4 4
97.1 18.3 1.1 4
98.1 14.4 0.6 5
97.1 17.2 1.1 5
98.1 13.1 0.9 6
97.1 17.2 1.3 6
98.1 13.0 1.0 7
97.1 16.5 0.9 7
98.0 13.0 0.7 8
97.1 18.7 1.6 8
98.0 15.1 1.2 9
97.1 16.0 0.6 9
98.0 12.9 0.9 10 97.1 18.5 0.8 10 98.0 14.6 0.2 11 97.1 19.1 0.6 11 98.0 16.5 0.7 12 97.2 18.4 1.0 12 98.0 14.5 1.1 13 97.2 18.4 0.9 13 98.0 14.9 0.5 14 97.2 18.3 1.1 14 98.0 14.2 1.5 15 97.1 17.6 0.9 15 98.1 14.7 1.1 16 97.1 17.7 0.8 16 98.2 14.5 1.0 17 97.2 17.4 1.3 17 98.0 14.1 0.6 18 97.2 18.7 0.5 18 98.0 15 3 1.2 19 97.1 18.2 1.2 19 98.0 14.9 1.4 20 97.1 17.9 1.0 20 98.0 14.2 1.1 21 97.1 15.3 0.7 21 98.0 11.8 0.8 22 97.1 18.0 0.8 22 98.0 14.8 1.0 1
23 97.1 17.4 0.6 23 98.0 14.1 0.7 24 97.1 17.8 1.2 24 98.0 14.1 1.0 25 97.2 14.2 1.4 25 98.0 10.9 1.0 26 97.2 16.3 2.4 26 98.0 13.0 0.6 27 97.2 18.1 0.9 27 98.0 14.5 1.1 28 97.2 15.8 1.0 28 98.0 11.7 0.6 29 97.1 14.7 0.9 29 98.0 11.3 1.6 30 97.1 18.1 1.3 30 98.0 15.1 1.4 31 97.2 16.4 0.8 31 98.0 13.0 0.9 l
32 97.2 16.7 0.7 32 98.0 12.8 1.7 33 97.2 19.1 0.8 33 98.0 15.0 1.4 34 96.3 18.7 0.2 34 97.8 14.9 1.6 35 97.1 17.7 0.8 35 98.1 14.5 1.2 36 97.1 17.5 0.7 36 98.1 14.6 0.7 37 97.0 16.8 1.4 37 98.1 13.0 1.3 38 97.0 19.1 1.0 38 98.1 16.0 1.1 39 96.3 17.7 0.9 39 97.8 14.5 0.7 40 96.4 14.9 0.3 40 97.8 11.8 1.1 41 97.1 18.1 1.0 41 98.0 13.3 1.9 42 97.1 11.7 0.6 42 98.0 8.6 1.3 43 97.1 11.1 1.1 43 98.1 7.9 0.9 44 96.9 17.7 0.8 44 98.1 14.0 0.8 45 97.1 19.1 0.9 45 98.0 16.4 1.1 46 97.2 17.1 0.8 46 98.0 14.0 0.7 47 96.9 21.0 1.5 47 98.0 44.0 4.3 1997 Annual Radiological Environmental Operating Report l
Wolf Creek Generating Station Page 23 of 50
I l
TABLE 7 Drinking Water Radiological Analyses
. (pci/ liter, analysis counting uncertainties reported in Appendix B))
'Locat..;n Start Date Gr-B LW40 1/6/97 5.4 BW15 1/6/97 5.6 LW40 2/4/97 3.9 BW15 2/4/97 4.2 LW40 3/4/97 3.5 BW15 3/4/97 5.4 LW40 4/1/97 4.6 i
BW15 4/1/97 5.5 l
LW40 5/6/97 4.1 l
BW15 5/6/97 4.6 l
LW40 6/5/97 5.8 l
BW15 6/5/97 6.0
)
l LW40 7/2/97 4.4 J
l BW15 7/2/97 5.2 l
LW40 8/6/97 5.8
{
l BW15 8/6/97 5.9 j
LW40 9/5/97 5.1 BW15 9/5/97 6.0 l
LW40 10/7/97 6.0 BW15 10/7/97 6.5 l
BW15 11/18/97 (grab) 7.3
~
LW40 11/4/97 4.8 BW15 11/18/97 6.1 LW40 12/3/97 6.1 l
BW15 12/3/97 6.1 l
l l
I l
f I
l 1997 Annual Radiological Environmental Operating Report Wolf Creek Ge.r.erating Station Page 24 of 50
l TABLE B l
Surface Water Radiological Analyses (pCi/ liter, analysis counting uncertainties reported in Appendix B)
Location Date H-3 DC 1/21/97 8600 DC 2/18/97 8400 SP 2/18/97 8500 DC 3/25/97 7800 SP 3/25/97 7100 DC 4/22/97 11000 SP 4/22/97 11000 DC 5/21/97 14000 SP 5/21/97 13000 l
DC 6/17/97 15000 l
SP 6/17/97 15000 DC 7/22/97 14000 l
SP 7/22/97 14000 DC 8/19/97 13000 SP 8/19/97 13000 DC 9/16/97 14000 SP 9/16/97 14000 DC 10/21/97 15000 SP 10/21/97 14000 DC 11/21/97 13000 SP 11/21/97 12000 DC 12/23/97 11000 SP 12/23/97 12000 l
l l
l r
l.
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 25 of 50 l
i l
l l
TME 9 Shoreline Sediment Radiological Analyses (pCi/kg, dry, analysis counting uncertainties reported in Appendix B)
Location Date Be-7 K-40 Co-60 Cs-137 Ra-226 Th-228 l
DC 5/22/97 7780 1270 905 l
JRR 5/22/97 8420 103 1830 1010 MUDS 6/19/97 7690 3410 1630 EEA 6/19/97 895 15200 2450 1300 EEA 9/10/97 982 11300 156 1270 1240 MUDS 9/10/97 810 12600 2530 1520 DC 9/15/97 778 7890 133 2520 947 JRR 9/15/97 5620 3330 1650 TABLE 10 Milk Radiological Analyses (pCi/litar, analysis counting uncertainties reported in Appendix B)
Location Type Date K-40 S-3 cow 1/14/97 1500 S-3 cow 2/11/97 1380 S-3 cow 3/11/97 1360 S-3 cow 4/8/97 1290 S-3 cow 4/22/97 1270 TABLE 11 Broadleaf Vegetation Radiological Analyses (pCi/kg, wet, analysis counting uncertainties reported in Appendix B)
Type Location Date Be-7 K-40 HORSERADISH LEAVES F-1 5/27/97 434 3760 CABBAGE G-1 5/27/97 6800 CABBAGE S-4 5/27/97 164 5320 HORSERADISH LEAVES F-1 6/24/97 328 5870 CABBAGE G-1 6/24/97 233 4050 CABBAGE S-4 6/24/97 320 3720 CABBAGE S-4 7/29/97 960 5700 CABBAGE G-1 7/29/97 809 4490 HORSERADISH LEAVES F-1 7/29/97 590 4100 CABBAGE S-4 8/27/97 994 3950 HORSERADISH LEAVES F-1 8/27/97 399 4400 HORSERADISH LEAVES F-1 9/30/97 738 5350 TURNIP LEAVES G-1 9/30/97 478 7560 RHUBARB LEAVES S-4 9/30/97 885 4010 HORSERADISH LEAVES F-1 10/28/97 701 6050 TURNIP LEAVES G-1 10/28/97 411 5910 l
l 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 26 of 50
l TABLE 12 Crops Radiological Analyses (pCi/kg, wet, analysis counting uncertainties reported in Appendix B) l l
Type Location Date K-40 CORN (IRRIGATED)
NR-D1 10/8/97 3030 CORN (NOT IRRIGATED)
NR-D2 10/17/97 3050 SOYBEANS (NOT IFRIGATED)
NR-D2 10/17/97 17300 CORN (NOT IRRIGATED)
NR-U1 10/17/97 2900 SOYBEANS (NOT IRRIGATED)
NR-U1 10/17/97 16500 l
TABLE 13 Fish Radiological Analyses (pci/kg, wet, analysis counting uncertainties reported in Appendix B)
Species Location Date K-40 H-3 Cs-137 COMMON CARP WCL (Causeway) 4/16/97 3120 5900 WALLEYE WCL (Causeway) 4/16/97 3950 6500 l
WIPER WCL (Causeway) 4/16/97 3310 6100 l
WHITE CRAPPIE WCL (Causeway) 4/16/97 3520 6900 WHITE BASS WCL (Causeway) 4/16/97 3190 4500 COMMON CARP JRR 4/30/97 3430 WHITE CRAPPIE JRR 4/30/97 3720 WIPER / WHITE BASS WCL (DC) 5/23/97 3240 14000 t
BM BUFFALO JRR 9/15/97 3140 W CRAPPIE /
JRR 9/15/97 3280 270 CHANNEL CAT WALLEYE WCL (MUDS) 9/17/97 5520 790 20.7
~
COMMON CARP WCL (MUDS) 9/17/97 4600 6200 l
SM BUFFALO WCL (MUDS) 9/17/97 3470 3200 FRESHWATER DRUM WCL (Main Body /
9/17/97 3130 11000 l
Causeway)
WHITE BASS WCL (DC) 10/15/97 2980 7000 l
SM BUFFALO WCL (DC) 10/15/97 2460 7200 l
l TABLE 14
)
Bottom Sediment Radiological Analyses (pCi/kg, dry, analysis counting uncertainties reported in Appendix B)
Location Date K-40 Mn-54 Co-60 Cs-137 Ra-226 Th-228 i
DC 5/22/97 10800 94.3 1130 344 1490 1080 JRR 5/22/97 16300 189 2270 1430 j
DC 9/15/97 12500 1290 470 2450 1260 JRR 9/15/97 16900 234 1920 1680 l
l l
1997 Annual Radiological Environmental Operating Report j
Wolf Creek Generating Station Page 27 of 50 i
TABLE 15 Aquatic Vegetation Radiological Analyses (pCi/kg, wet, analysis counting uncertainties reported in Appendix B)
Location Type Date Be-7 K-40 Mn-Co-Co-Sb-Cs-Cs-Ra-Th-l 54 58 60 125 134 137 226 228 DC ALGAE 5/22/97 770 2050 11.2 11.2 149 53.3 20.4 40.4 222 157 l
MUDS PONDWEED 6/19/97 152 3540 EEA PONDWEED /
6/19/97 337 3800 27.2 486 226 BULRUSH MUDS AM PONDWEED 9/10/97 164 1560 192 EEA ALGAE /WTR 9/10/97 151 2250 19.4 354 162 EVNG PRMRSE DC AM LOTUS 9/15/97 1400 2920 1
TABLE 16 Terrestrial Vegetation Radiological Analyses (pCi/kg, wet, analysis counting uncertainties reported in Appendix B) l l
Type Location Date Be-7 K-40 GRASS MUDS 6/19/97 979 4130 GRASS EEA 6/19/97 1680 5980 GRASS MUDS 9/10/97 659 5780 GRASS EEA 9/10/97 1810 3820 TABLE 17 Soil Radiological Analyses (pCi/kg, dry, analysis counting uncertainties reported in Appendix B)
Location Date Be-7 K-40 Cs-137 Ra-226 Th-228 EEA 6/19/97 11000 197 2200 1190 MUDS 6/19/97 4240 12400 330 2010 1130 EEA 9/10/97 463 11100 166 2060 1130 MUDS 9/10/97 11700 1980 1400 1
1 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 28 of 50 l
l l
l
i l
}
TABLE 18 l
1997 Land Use Census Data i
Location of Nearest:
Sector Residence Milk Animal Broadleaf Garden j
A A2.6-17TE1520 None None B
B3.1-QURD1712 None B3.6-QURD1755 C
C1.9-16RD1655 None C2.2-16RD1670 I
D D2.1-QULA1571 None D2.1-QULA1571 l
E El.8-QULA1485 None El.8-QULA1485 F
F1.6-14RD1711 None F1.8-14RD1730 G
G1.6-QURD1384 None G1.6-QURD1384 H
H3.1-12RD1711 None H4.85-10RD1698 J
J2.0-11RD1549 None J3.8-11RD1535 K
K2.6-12LA1439 None K3.8-11RD1499 L
L2.4-NARD 1339 None L2.6-NARD 1309 M
M2.3-14RD1322 None M2.4-14RD1321 N
N2.5-HW751439 None N2.8-HW751480 P
P2.0-16RD1150 None P4.5-KARD1630 Q
Q1.4-NALA1574 None Q3.2-17RD1310 R
R2.1-NALA1650 None None Locations are identified based upon the following protocol:
EXAMPLE:
A1.4-16RD1525 First letter is based upon sector, thus "A" designates this residence is in sector A.
The number immediately following the first letter designates the distance (in miles) from the powerblock.
The characters following the dash represent a unique identifier based upon location address.
The example is in sector A, 1.4 miles from the plant, at 1525 16th Road.
l 1997 Annual Radiological Environmental Operating Report l
Wolf Creek Generating Station Page 29 of 50
TABLE 19 1997 Land Use Census Milk and Garden Data SECTOR 1996 1997 1996 CLOSEST 1997 CLOSEST D/Q MILK MILK GARDEN GARDEN PRODUCING RANKING ANIMAL ANIMAL PRODUCING BROADLEAF BROADLEAF VEGETATION VEGETATION A
none none none none B,
none none B3.1-QURD1712 B3.6-QURD1755 4
C none none C2.2-16RD1670 C2.2-16RD1670 5,
D none none D2.1-QULA1571 D2.1-QULA1571 11_
E none none El.8-0ULA1485 E1.8-QULA1485
_3_
F none none F1.8-14RD1730 F1.8-14RD1730 2
G none none G1.6-QURD1384 G1.6-QURD1384 1
H none none H4.9-10RD1698 H4.85-10RD1698 13 J
none none J3.8-11RD1535 J3.8-11RD1535 1_0 K
none none K4.1-NARD 1120 K3.8-11RD1499 12_
l L
none none L2.6-NARD 1309 L2.6-NARD 1309 8_
M none none M2.4-14RD1321 M2.4-14RD1321 6
l N
none none N2.8-HW751480 N2.8-HW751480 9
l P
none none P4.3-16RD1112 P4.5-KARD1630 M
Q none none 02.3-MILA1619 03.2-17RD1310 7
R none none R2.1-NALA1650 none l
NOTE:
Underlined entries indicate changes from the 1996 Land Use Census.
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 30 of 50
i TABI2 20 EPA Interlaboratory Comparison Program 1997 Environmental Collection Medium Nuclide EPA Result (a)
Telodyne Brown Deviation Date Engineering (c)
Result (b) 01/17/97 Water Sr-89 12.0+
5.0 10.00+~
1.00
-0.69 l
Sr-90 25.01 5.0 25.001 1.00 0.00 01/31/97 Water Gross Alpha 5.21 5.0 8.101 0.89 1.00 Gross Beta 14.71 5.0 15.00+
1.00-0.10 02/07/97 Water I-131 86.01 9.0 106.001 4.36 3.85 (d) 02/14/97 Water Ra-226 5.9+
0.9 5.27+~
0.23
-1.22 Ra-228 8.25 2.1 8.401 0.30 0.16 03/07/97 Water H-3 7900.01 790.0 7366.671 378.59
-1.17 04/15/97 W&ter
~ Gr-Beta 102.1+
15.3 103.33+
5.77 0.14 Sr-89 24.07 5.0 23.007 1.00
-0.35 Sr-90 13.07 5.0 12.677 1.15
-0.12 Co-60 21.07 5.0 22.677 0.58 0.58 Cs-134 31.07 5.0 28.677 0.58
-0.81 Cs-137 22.07 5.0 24.677 1,53 0.92 Gr-Alpha 4 8. 0T_
12.0 54.675 1.53 0.96 Ra-226 13.01 2.0 13.00+
1.00 0.00 Ra-228 3.1+~
0.8 4.87+
0.12 3.82 l
(e)
J
~
l l
06/06/97 Water Co-60 18.0+
5.0 19.00+
0.00 0.35 Zn-65 100.07 10.0 99.337 1.15
-0.12 Cs-134 22.07 5.0 18.677 1.15
-1.15 Cs-137 49.07 5.0 48.677 0.58
-0.12 Ba-133 25.0[
5.0 22.333 2.52
-0.92 06/13/97 Water Ra-226 3.0+
0.5 3.43+
0.49 1.50 Ra-228 3.15 0.8 3.431 0.23 0.72 06/18/97 Water Gr-Alpha 3.11 5.0 2.931 0.25
-0.06 Gr-Beta 15.11 5.0 14.001 1.00 0.38 07/11/97 Water Sr-89 44.0+
5.0 38.33+
1.53
-1.96 Sr-90 16.01 5.0 25.001 0.00 3.12 (f) 08/08/97 Water H-3 110101 1101.0 12000.001 0.00 1.56 09/12/97 Water Ra-226 20.0+
3.0 20.00+
1.73 0.00 Ra-228 8.05 2.0 7.401 0.17
-0.52 i
09/19/97 Water I-131 10.01 6.0 11.001 0.00 0.29 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 31 of 50
TABLE 20 (Cont)
EPA Interlaboratory Comparison Program 1997 Environmental Collection Medium Nuclide EPA Result (a)
Teledyne Brown Deviation I
j Date Engineering (c)
Result (b) l 10/21/97 Water Gr-Beta 143.4+
21.5 136.67+
5.77
-0.54 Sr-89 36.07 5.0 36.007 1.00 0.00 Sr-90 22.07 5.0 21.677 2.08
-0.12 Co-60 10.07 5.0 10.677 0.58 0.23 Cs-134 41.07 5.0 41.337 0.58 0.12 l
Cs-137 34.07 5.0 36.007 1.00 0.69 Gr-Alpha 49.9[
12.5 45.671 1.15
-0.59 Ra-226 5.0+
0.8 5.90+
0.10 1.95 Ra-228 5.05 1.3 4.275 0.12
-0.98 10/31/97 Water Gr-Alpha 14.7+
5.0 19.671 1.53 1.72 i
Gr-Beta 48.9+
5.0 50.671 3.51 0.61 11/07/97 Water Co-60 27.0+
5.0 25.0G+
1.00
-0.69 Zn-65 75.07 8.0 71.007 3.61
-0.87 Cs-134 10.07 5.0 10.677 0.58 0.23 Cs-137 74.07 5.0 76.007 1.00 0.69 l
Ba-133 99.01 10.0 78.675 0.58
-3.52 (g)
Footnotes:
l a) EPA Results-Expected laboratory precision (1 sigma).
Units are pCi/ liter for water, j
b) Teledyne Results - Average one sigma.
Units are pCi/ liter for water.
I c) Normalized deviation from the known, d) Erroneously high reading of the stable iodine content by ion specific j
electrode occurred, causing an erroneously low chemical yield.
If the
~
electrode reading is ignored, the average I-131 result becomes 90 pCi/1, in I
good agreement with the given value. An erroneous electrode reading can be caused by certain chemical species in the sample, such as sulfide. We will investigate suspiciously high electrode readings by performing a
gravimetric yield on the sample without the addition of iodine carrier or I
the I-131 content of active samples can also be verified by performing a gamma spectral analysis, e) An investigation discovered a low chemical yield on one sample and the loss of another during analysis.
In the future we will repeat analyses of samples with yields less than 85%.
f) Error apparently caused by insufficient training.
The strontium separation chemistry was performed on 7/22/97 by a summer employee.
Initial results for the three samples did not agree well, so all were remilked by a senior analyst.
This was insufficient to correct the problem.
In-house QC samples showed satisfactory results at this time.
Additional in-house analyses performed after retraining have been acceptable, g) No apparent cause for the discrepancy could be identified.
No corrective action has been taken.
The investigation is continuing.
l I
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 32 of 50 i
1 TABLE 21 Analytics Cross Check Comparison Program 1997 Sample Medium Nuclide Teledyne Analytics Ratio ID/ Date Brown Result (b)
Engineering Result (a)
E0975-396 Milk I-131 18+
1 20+
1 0.90 TI#41238 Ce-141 L.T.17 2327 12 03/20/97 Cr-51 381+
38 3877 19 0.98 Cs-134 1327 13 1437 7
0.92 Cs-137 1287 13 1147 6
1.12 Co-58 897 9
797 4
1.13 Mn-54 1957 20 1767 9
1.11 Fe-59 1617 16 1447 7
1.12 Zn-65 1717 17 1657 8
1.04 Co-60 1793 18 1763 9
1.02 E0976-396 Milk Sr-89 13+
3 25+
1
- 0. 52 (c)
TI#41239 Sr-90 167 1
197 1
0.84 03/20/97
~
~
E1092-396 Air Filter Ce-141 143+
8 132+
7 1.08 TI#49899-Cr-51 2297 17 1987 10 1.16 901 Cs-134 747 4
817 4
0.91 06/19/97 Cs-137 1437 8
115I 6
1.24 Co-58 897 5
777 4
1.16 Mn-54 1027 6
847 4
1.21 Fe-59 987 6
757 4
1.31 Zn-65 1887
~
5 1.09 Co-60 113~
11 1397 7
1.35 1
7 104 E1093-396 Cartridge I-131 1061 6
881 4
1.20 TI#49902-04 06/19/97 E1094-396 Air Filter Sr-90 881 5
961 5
0.92 TI#49893-95 06/19/97 E1095-396 Air Filter Gross 1031 6
931 5
1.11 TI#49996-Alpha 98 Gross 210+
06/19/97 Beta
~
6 193+~
10 1.09 E1204-396 Milk I-131 97+
10 87+
4 1.11 TI#57520 Ce-141 837 8
777 4
1.08 09/18/97 Cr-51 3237 40 3047 15 1.06 Cs-134 987 10 1027 5
0.96 Cs-137 1177 12 1077 5
1.09 Cc-58 647 6
607 3
1.07 Mn-54 993 10 88~
4 1.13 i
Fe-59 132+
13 119+
6 1.11 Zn-65 2187 22 1967 10 1.11 Co-60 2091 21 1973 10 1.06
[
1997 Annual Radiological Environmental Operating Report I
Wolf Creek Generating Station Page 33 of 50
l TABLE 21 (Cont)
Analytics Cross Check Comparison Program 1997 Sample ID/
Medium Nuclide Teledyne Analytics Ratio Date Brown Result (b)
Engineering Result (a)
E1203-396 Milk Sr-89 14+
1 15+
1 0.93 TI#57517 Sr-90 187 1
147 1
1.29 09/18/97 l
Footnotes:
a) Teledyne Results - counting uncertainty is two standard deviations.
Units i
are pCi/ liter for water and milk.
For gamma results, if two standard deviations are less than 10%, then a 10% counting uncertainty is reported.
Units are total pCi for air particulate filters, b) Ratio of Teledyne Brown Engineering to Analytics results.
c) Caused by incorrect rinsing of the strontium extraction column.
Additional training was conducted on 9/5/97 and was documented in the analyst's training file.
Subsequent tests on two milk samples spiked with Sr-89 produced good results.
l l
I l
l I
1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 34 of 50
TABLE 22 Dosimetry Performance Testing Results NATIONAL VOLUNTARY LABORATORY ACCREDITATION PROGRAM PERSONNEL DOSIMETRY PERFORMANCE TESTING
SUMMARY
OF STATISTICAL RESULTS PROCESSOR NAME: DETROIT EDISON COMPANY PROCESSOR CODE NO.:
100529B TYPE OF DOSIMETER: PANASONIC UD-802AS/ISA 820 TEST RESULTS FOR QUARTER: 1996-4 TESTING STATUS: INITIAL REPORT PRINTED: Jan 16, 1997 SHALLOW DEEP DEPTH DEPTH CATEGORY B
S lBl+ S L
B S
lBl + S L
I NO TEST
.010
.045
.055
.300 II NO TEST
.033
.115
.148
.300 IIIA
.073
.086
.160
.500
.027
.187
.214
.500 IIIB IV NO TEST
.035
.068
.103
.019
.085
.103
.500 NO TEST VC NO TEST l
i VI
.031
.081
.111
.500
.038
.087
.125
.500 VII
.010
.051
.060
.500
.008
.044
.051
.500 j
VIII-TOTAL NO TEST
.003
.045
.043
.500 VIII-NEUTRON NO TEST
.063
.075
.138
.500 IX
.011
.049
.061
.500
.057
.068
.125
.500
- PROCESSOR DID NOT PARTICIPATE IN THIS CATEGORY B = Bias S = Standard Deviation L = Limit 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 35 of 50
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l 1997 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 37 of 50
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AQUATIC VEGETATION / ALGAE l l l l 1997 Annual Radiological Environmental Operating Report Wolf creek Generating Station Page 30 of 50 i FIGURE 4 l l l 1 fA .IN' _P i j 3Rh \\Ji B 4 j i i \\ MM -N b n. C[ i I j - Dj I / I d/Ql \\ / li LJ' <4 '\\m,6:' M A M l ,\\ l 7x
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2 2 / / o a / / 2 8 /2 21 25 i e / n M Nd Me a ( ( 24 22 ( 1 I f 0 (0 ic MR (4 (2 5 8 5 3 e A o 4 4 0 5 4 6 4 6 5 p l t R ei a 1 u 0 0 2 3 9 71 9 4 s n" r k e 1 G cP 2 4 4( 1 ( 1 ( 4( t O o n a R Dg A s n n t P i t t s io n r e e G o h c m t N p ig e e e l ir r I i R n R o D W W W W W W us O i h N N N N N N a t T a i d e t t n W W N N N W m S w a IN r n e s s s s s s e O g s o M i s ai e n le le le l i e o c i i le le l n a t Si b t t im im Am Am Am Dm a a t a n cacmt c L r a id oai C6 C6 E0 E0 E0 U e s e K n 5 A n t LND D0 D0 E3 E3 E3 M1 e I T e ,y d N G f tn o E k u e o n M e o r C N C i t y c O lo r f e ) a R T o O ) ) 0 r t ) )4 ) ) ) 0 )8 F f V W o as( I e )6 )6 41 4 9 icnng 6 6 0 6 8 6 2 48 4 5 ly N :C / / / / dioa n 1 3 4 / / e 44 32 (1 (0 n nt a ( a (4 (2 (7 2 9 8 2 o E y:y cMR 4 09 I t 4 9 2 5 8 5 2 8 L i it lAL" o 0 9 1 8 2 6 9 3 t A l l l s i ic 2 2( 3( 1 1 1 c 1 ( 1 ( 4( n C a a e F F m IG f f n e O o o f o r oi u L e n r t ) s O mo wieD et c a ai e mt L 0 0 0 I t D Na oie L 0 0 0 0 0 0 m c LLD( 2 A o 2 2 5 1 1 R L le ba f t o ce r t d e e nb d ) am d 4 7 6 8 4 n s us e 3 3 2 2 ( o 2 2 a 7 0 p iNim 1 1 s s 4 u lyr s s a h m e lyl o a aaf C C R m B K d I e t r non e a s ATAP G a b e g na ) r t n ) ) d f e t t n n e nl e o m i c g ioaiw a o w m yd f i wlpt s ea/ e e/ e n r t r t a e o u g a ai at u t t k t sk eM dh mnia gui gri et e eqC eC r aaU e MPS(M V A (p V T (p m$o i c 1\\ l1 1l s tn f e e on m r i d e t euter f) b or u ( r os mnpa s u oe e es NNRM 0 0 0 0 0 0 0 0 0 he tne ra s p no n i i ta d c) e of ) t L (n g 3 a e c 1 ) i /3 l a n 5) 3 ) ) d H) 2 n o e 7 3 ) ) ) ) r a 1 3 1 2 nMR S - 1 1 4 24 4 4 t 1 i W0 (2 1 / / / / 1 / / / U/ s 74. 0 0 - 0 0 0 0 0 o Y 7 i C"" B (- 5( M (- ( ( ( B (- ( ( s R 9 n 9 A 2 o 1 i 8 M 4 l ) a t a ) c M 0 u 0 o I ) U 5 n f ) 0 I l / n n( 2 0 d e I S
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l 5 e e a n 2 /1 (1 i o M Nd Me a 1 f 6 5 0 i MR c A R ei a A (5 A A A A A A 4 0 e t o l 03 1 / / / / / / 1 p / n" " N 5( N N N N N N u r 2 7 s k e G cP 1 ( t O o n a R Dg A s n n t P it t e io n s e G o h c m r t N p I e ig e e r f i E r l R n R u o D S s O i h S a t d e T a it n s N li S m E w t I a e r n e s e O g s o o c 0 m i s ai e n ile l n a t b M a 40 a t t icamt A W10 A A A A A A c m a n t c s L r a d e oai / / / / / / / P9 e K n A n LND N L> N N N N N N S2 e t I T e ,y d N G t f n o E k u e o M e n r C o N C ) i t y 3) c O f e o ) r 0 a R l ff f ) 2/ 0 r o tas( 2 30 F IV W o e cnng 1 ) 25 C /1 id ioa n ) 2 ) ) ) ) ) l N ( 1 y e nt a 2 6 2 ) 6 6 6 3 4 0 n E y: : I 1 cMR a 1 ( 1 4 y 2 0 0 o 1 I 1 t 5 L l i l i t / / / / / / 1 l l o 0 03 0 0 0 0 0 0 2 7 t 1 A ic i AL" " s ( ( ( ( ( ( ( c 5( 1 ( n C a a e F F I m G f f n e O o o f o r oi u L e n r t ) O mo et c s eD 0 0 0 a ai w imt L 0 0 0 e I t D Na oie L 5 0 5 0 0 m c LLD( 0 2 0 A o 1 1 1 R L le ba f t o ) c 5 e r t d e 2 e ( ) ) ) ) ) d nb 5 0 0 5 5 a ) am d ) 2 8 ) 2 2 3 3 n t s us e 5 e ( ( 0 ( ( ( ( o isNim 2 B a 2 a p a lyl yr s m m m m m m u s ( ( o 1 u u u t r i I i m i d a alaf 3 o m it 3 m i a it e s t non e 1 r a r 1 a r r s ATAP G G T G T G T a I 1 b eg g na ) n d e r t i n c d n k f e n u a f n o m i r u o r a r m yd f e D G S r n a e o u rl rI rl ea ) ) ) iuwlpt s e/i t i i e/ el dh M mia aC aC aC t n e t et a aU MPS(M W (p W (p W (p 2b
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Appendix B 1997 :ndividual Sample Results l l 1' l l 1 l l-l l l 1 J l i i I 1 i Page B-1 a ) te yM 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 0 40 0 0 0 0 0 0 0 0 0 0 0 0 0 40 0 O0 0 0 0 0 Biu t v EEE E E E E EEE EEEEEEEEEEEEEEE sic sci t 4 3 3 3 4 3 3 3 2 3 2 3 3 2 3 3 3 2 3 3 3 3 2 3 3 / oAC - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O - - - - - - - - - - - - - - - - - - - - - - - - r + + + + + + + + + + + + + + + + + + + + + + + + + G p ( 2 5 6 0 3 1 4 0 7 8 8 0 9 4 9 0 3 7 5 7 7 4 3 2 0 3 2 2 3 2 2 2 2 1 1 1 2 1 1 1 2 2 1 1 1 1 1 1 2 2 tn 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 ue 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 / / / / / / / / / / / / / / / / / / / / / / / / / ot 4 3 9 6 9 6 8 7 4 0 7 7 2 7 5 5 4 9 7 1 8 3 1 5 5 Ca 1 2 2 0 O 1 1 2 0 1 1 2 0 0 1 2 0 0 1 2 2 0 1 2 2 / / / / / / / / / / / / / / / / / / / / / / / / D 1 1 1 2 2 2 2 2 3 3 3 3 4 4 4 4 5 5 5 5 5 6 6 6 6 d 0 0 0 0 G 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 i M no i ta ropro 2 C s 0 r g t R e n l t E i il' I e 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 a 8 r e M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 e m p ta O l U uC EE E E EE E E E E EE E E EE E EE E EEE E E 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0 0 0 0 O 0 0 0 u N loc 6 3 0 9 2 0 0 1 4 7 4 6 0 1 9 S 6 5 5 0 1 B 3 5 0 lc P I c r it a N V 2 3 3 3 2 3 3 3 3 2 3 2 3 3 2 3 2 3 2 3 3 2 3 2 3 e r O a u T r A N iA T ke S erC f l oW po tSn e 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 t 9 9 7 7 9 9 9 7 9 9 9 7 9 9 oa 7 9 9 9 7 9 9 9 9 7 9 / 5 1 8 1 2 3 6 1 2 2 / 1 1 / / / / / / 9 / 7 0 7 9 / 9 9 / / 9 / / / / 9 / 8 / / 9 i 2 6 2 0 3 0 cD / 4 1 0 / 1 1 8 6 t / / 4 6 1 2 3 4 1 1 1 2 4 1 1 2 / / / / / / / / / / / / / / / / / / / / / / / / le / 1 1 1 2 2 2 2 2 3 3 3 3 4 4 4 4 4 5 5 5 5 6 6 6 1 lo C tra t S e 6 nt 9 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 e oa 7 9 9 9 7 7 9 9 9 7 9 9 9 7 7 9 9 9 7 9 9 9 7 9 t / a / 9 9 / / / 9 / / / 9 1 / / / 4 1 0 / 9 //9 / / 5 / / 6 2 0 / 3 0 7 / 1 ic 9 / / / 9 it 0 D 3 1 8 6 / 2 8 / 6 1 2 3 4 4 1 1 2 4 1 1 2 1 8 1 2 3 6 1 2 2 4 c / e 2 lo D l 1 1 1 1 1 2 2 2 2 2 3 3 3 3 4 4 4 4 4 5 5 5 5 66 lp / / / / / / / ///////////////// u C tN0 U(b ) a te y M. 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 Biu - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 t v EE EE EEEE EE E EEE EE EEE EEEEEE sic t 3 3 3 2 3 3 3 3 3 3 3 4 4 4 3 3 4 3 3 3 3 3 3 3 4 sci / oAC - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 r + + + + + + + + + + + + + + + + + + + + + + + + + G p 0 6 7 5 6 2 2 2 8 0 3 0 5 6 3 0 8 9 4 2 1 1 7 0 7 ( 2 1 1 1 1 2 3 3 2 2 3 4 3 3 2 2 3 1 2 2 2 2 2 3 5 tn 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 ue 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 / / / / / / / / / / / / / / / / / / / / / / / / / ot 0 8 8 4 0 8 4 2 0 6 4 3 0 5 1 9 4 2 1 3 7 1 3 3 1 / / / / / / / / / 2 2 0 0 1 2 3 0 0 2 0 0 Ca 2 2 0 1 1 / / / 1 2 2 0 3 0 0 1 / / / / / / / / / / / / / D 6 7 7 7 7 7 8 8 8 8 9 9 9 9 0 0 0 0 0 1 1 1 2 2 2 d 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 i M no i taropro 2 C s 0 r g te R n l E i i B F t e te M e 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 ar 8 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 m 0 p a U uC E E E E E E EEEEE EEE E E EEE EEE EEE 0 0 0 0 0 0 0 0 0 O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O l N u 0 1 0 0 0 1 loc 9 0 0 4 6 1 0 5 1 1 1 9 0 6 S 0 6 9 1 c r N V 2 3 3 3 2 3 3 3 3 2 3 3 2 2 3 3 2 3 3 3 3 3 3 3 3 a it r e a O l P I c u T N i A r A T ke S erC f loW p o t S 7 7 7 7 7 7 7 e nt 7 7 7 7 7 7 7 7 7 7 7 9 9 9 7 9 9 9 9 / / / / / / / 9 9 7 7 7 9 9 9 7 9 9 9 7 7 9 9 9 9 oa /4 / / / / / / / 4 1 8 / 1 B 8 5 / / / 9 9 / / / 9 3 9 7 / / 6 3 0 7 1 2 2 4 1 1 1 2 9 9 9 it D 5 2 9 / / / / / / / / / / c 2 1 1 9 1 2 2 6 1 1 2 3 9 1 2 3 0 0 0 0 1 1 1 1 1 / / / / / / / / / / / / / / / / le 6 7 7 7 7 7 7 8 8 8 8 9 9 9 9 9 1 1 1 1 1 1 1 1 1 loC tra tS 7 7 7 7 7 7 e nt 7 7 7 7 7 7 7 7 7 7 7 7 7 9 9 9 7 9 9 9 e / / / t / / / 9 oa 9 9 9 7 7 9 9 9 7 9 9 9 7 7 9 9 9 9 / / / 9 / / / 9 9 / / / / 4 1 8 1 1 8 a / / / / 9 9 5 2 9 3 9 7 / / / 6 3 0 7 1 2 2 4 1 1 1 it c D 7 4 4 / / 1 2 2 6 1 1 2 3 9 1 2 3 / / / / / / 1 / c 1 2 2 1 / / / / / / / / / / / / / 0 0 0 0 1 1 1 1 il 9 / / / / le 6 6 6 7 7 7 7 7 8 8 8 8 9 9 9 9 9 1 1 1 1 1 1 1 1 p u lo D C J [g f C ) a te y M. 2 2 2 2 2 Biu - 0 0 0 0 0 t - E E E v EE sic sci 3 3 4 3 3 t / o 0 0 0 0 0 rAC + + + + + G p 5 8, 8 6 8 ( 2 1 3 2 1 tn 7 7 7 8 8 ue 9 9 9 9 9 / / / / / ot 2 8 1 7 )6 Ca 1 1 3 0 4 D 2 2 2 1 1 / / / / d 1 1 1 0 0 i M n io t a r o p ro 2 C s 0 r g te R n l it i E F B ar e M e 8 8 8 8 8 0 0 0 0 0 e m p ta U uC EEE EE O lu N 0 0 0 0 0 loc 0 4 9 0 0 c r N V 3 3 2 3 3 a it r e a O l P I cu T r N i A A k T e S e rC lfoW po tS e 7 7 7 7 nt 7 9 9 9 9 oa 9 / / / / 0 7 4 1 / icd t 2 1 1 2 3 / / / / / le 2 2 2 2 2 1 1 1 1 1 lo C tra tS e 7 7 7 7 nt 9 7 9 9 9 e / 9 / / / t oa 5 0 7 4 a / it D 2 2 1 1 2 ic c / / / / / lp 1 2 2 2 2 le 1 1 1 1 1 u lo D C 'W4Q D L. O 0 C a ) 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 0 - - - E E E E E E E EEEEE E E E EE EEEE e y M. - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 t EE EE - - - - - - - - - - - - - - - - - Biu t v 4 3 3 3 4 3 3 2 3 3 3 3 3 3 3 3 4 2 3 3 3 2 2 3 3 stiC O - + + + + + + + + + + + + + + + + + + + + + + + sci - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 / o + + - - - - - - - - - - - - - - - - - - - - - - - rAC 5 6 7 2 5 8 4 6 9 0 1 0 6 9 1 6 7 7 8 6 5 4 8 8 1 G p ( 3 2 2 3 2 2 2 1 1 2 2 2 2 1 1 2 2 1 1 1 1 1 1 1 1 tn 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 ue 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 / 3 1 5 5 9 9 9 9 9 / / / / / / / / / / / / / / / / / / / / / / / / ot 1 2 2 0 0 1 2 0 1 7 7 7 2 7 5 5 4 9 7 1 2 0 4 3 9 6 9 6 7 4 0 8 Ca 1 1 1 2 2 2 2 3 3 3 3 3 4 4 4 4 5 5 5 5 5 6 6 6 6 1 1 2 0 1 2 0 / / / / / / / / / / / / / / / / / / / / / 0 0 1 2 1 2 2 D / / / d 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 i M n io t aropro 3 C s 0 r g e tt n ll i t l i il' i e 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 l a p te M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 r 8 e J m a uC EE E EEEE E E EEEE E EE E E E E EE E E E t O l N 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0 u oC l 0 5 1 8 2 0 9 4 6 3 3 5 9 9 8 4 5 4 4 9 0 9 3 S 0 a ic r e t N V 2 3 3 3 2 3 2 3 2 3 3 2 2 2 2 3 2 3 2 2 3 2 3 2 3 ra O l P IT cu r N iA TA ke S erC f l oW po t S nte 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 oa 7 9 9 9 7 9 9 9 7 9 9 9 9 7 7 9 9 9 7 9 9 9 7 9 9 / / / 9 / / / / / / / / 9 9 / / / 9 9 9 / / / 9 icD le / 1 2 3 4 1 1 2 4 1 1 1 2 1 / 1 2 3 6 1 2 2 4 10 7 3 0 7 / t 6 2 0 / / 4 1 0 / 1 8 6 / 2 2 8 5 / / 8 1 6 / / / / / / / / / / / / / / / / / / / / / / / 1 1 1 1 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 6 6 6 loC tra t S e 6 nt 9 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 lc / 7 9 9 9 7 9 9 9 7 7 9 9 9 7 7 9 9 9 7 9 9 9 7 9 ioa / a 1 / / / 9 9 / / / 9 / / / 9 / / / 9 9 2 / / / / / / 1 2 / 9 / / / 9 3 0 7 / 0 D 3 6 2 0 / 1 8 6 / 2 8 5 / / 1 2 3 6 1 2 2 4 1 ic / 4 1 0 / tc / 6 8 1 2 3 4 1 4 4 1 1 2 1 1 1 1 1 1 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 6 6 lp / / / / / / / / / / / / / / / / 1 / le lo uD C [M f0 5 a 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 ) t E - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 00 - - - - - - - - - - - - - - - - - - - - - - - te y M. - EEEE EEEEE EEEE EEE EE EEEEEE Biu v 3 2 2 3 3 3 3 3 3 3 3 4 4 4 3 3 3 3 3 3 3 3 3 4 3 sic 0 - + + + + + + + + + + + + + + + + + + + + + oAC - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O t sci / + + + + G p 1 3 6 9 3 7 67 7 1 5 8 4 2 2 9 5 2 5 0 3 9 0 5 8 r ( 2 1 1 1 2 2 2 2 2 2 3 3 3 3 2 1 3 2 2 2 2 1 3 5 2 tn 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 ue 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 / / / / / / / / / / / / / / / / / / / / / / / / / 2' 0 3 1 2 ot 0 8 4 0 8 4 4 2 0 6 4 3 0 5 1 9 4 2 1 3 7 1 2 2 0 1 2 2 0 0 1 2 3 0 0 1 1 Ca 3 0 1 2 2 0 0 i / / / / / / / / / / / / / / / / / / / / / / / / / D 6 7 7 7 7 8 8 8 8 8 9 9 3 9 0 0 0 0 0 1 1 1 2 2 2 -d 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 M no itaro p r o 3 C s 0 r g t R e n l E i F t i l r e M e 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 i a e 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 p t m O l U uC E EE E E EEEEE E EEEE E EE E E E E EEE a 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 u N 1 2 1 1 1 0 9 0 0 loc 9 0 4 6 0 0 0 5 0 6 4 0 5 9 1 1 a ic e t N V 2 3 3 2 3 3 3 3 3 2 3 3 2 2 3 3 2 3 3 3 3 3 3 3 3 r l P I ra O cu T r A N iA T ke S erC f loW po tS 7 7 7 7 7 7 e nt 7 7 7 7 7 7 7 7 7 7 7 7 7, 9 9 7 9 9 9 7 / / 9 / / / 9 9 9 oa 9 7 7 9 0 9 9 7 9 9 9 7 7 G9 /") 7 1 2 2 4 1 1 2 2 / / 6 2'3 / 4 1 8 / 1 8 5 / / / / / 9 9 / / / / 9 3 9 7 / 9 9 5 2 9 9 / icD t 4 / / / / / / / / / / 2 1 / 1 2 2 2 6 3 / / / / / / / / 1 1 2 3 9 1 9 / / / / / / / / 0 0 0 0 1 1 1 1 2 le 6 7 7 7 7 7 7 8 8 8 8 9 9 9 9 9 1 1 1 1 1 1 1 1 1 lo C tr a t S 7 7 7 7 7 7 e nt 7 7 7 7 7 7 7 7 7 7 7 7 7 9 9 9 7 9 9 9 e oa 9 9 7 7 9 9 9 9 7 9 9 9 7 7 9 9 9 9 / / 9 / / / t 1 8 5 a 4 1 8 / / / / 9 9 / 3 0 7 1 2 2 4 1 1 2 c 9 / / / / / / / / / 9 9 5 2 2 9 6 it / 3 9 7 D 7 4 / / 1 2 2 2 6 / / / / / / / / / / / / / / / / / / /// / / / / / / 0 0 0 0 1 1 1 1 i 1 1 2 3 9 1 2 3 c 9 1 2 1 lle 6 6 7 7 7 7 7 7 8 8 8 8 9 9 9 9 9 1 1 1 1 1 1 1 1 lp u o D C O D ' $* th ) 2 2 2 2 2 a 0 e y M. - 0 40 0 t EEE E E Biu t v 2 4 4 3 3 sic 0 - + + sci - 0 0 0 0 t / o + + + rAC G p 7 7 9 7 7 ( 1 3 3 2 1 tn 7 7 7 8 8 ue 9 9 9 9 9 / / / / / ot 8 1 1 7 6 Ca 1 3 3 0 0 / / / / / D 2 2 2 1 1 d 1 1 1 0 0 i M no itaropro 3 C s 0 r n t R g e i l E t i B F a e 8 8 8 8 8 r e M 0 0 0 0 0 m e t U uC EEE EE p a O lu N O 0 0 0 0 loc S 9 9 1 0 c r N V 3 2 2 3 3 a it O r e a lc P I u T r A N iA T ke S e rC f lo W po tSn e 7 7 7 7 7 oa / 9 9 9 9 t 9 / / / / 0 7 7 4 1 icD 1 1 1 2 3 t / / / / / 2 2 2 2 2 le 1 1 1 1 1 loC tra tS e 7 7 7 7 e nt 7 9 9 9 9 t oa 9 / / / / / 0 0 7 4 a / / / / / ic icD 2 1 1 1 2 lp t 2 2 2 2 2 le 1 1 1 1 1 u lo D C MP w14 ) a 0 0 0 0 0 0 0 40 0 0 0 0 0 0 0 40 0 0 40 0 0 0 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 te y M. - E EEEE EE EEEEEE EEEEE E E E E EE E - - - - - - Biu t v 4 3 3 3 3 3 3 3 3 2 3 3 2 3 3 3 3 2 3 3 3 3 2 3 3 sc/ sic rAC - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 40 O 0 O 0 0 o i 0 - + + + + + + + + + + + + + + + + + + + + + + + t + + 8 7 7 4 9 4 4 8 6 7 0 9 4 9 9 0 5 5 3 6 7 6 4 1 8 G p ( 2 2 2 3 1 2 2 1 1 1 2 1 1 1 1 2 2 1 1 1 1 1 1 2 1 tn 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 ue 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 / / / / / / / / / / / / / / / / / / / / / / / / / ot 4 3 9 6 9 6 7 4 0 7 7 2 7 5 5 5 4 9 7 1 8 3 1 5 5 Ca 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 2 / 1 2 0 1 1 2 0 0 1 1 2 0 0 1 2 2 0 1 2 2 1 2 2 0 0 / / / / / / / / / / / / / / / / / / / / / / / / 2 2 2 3 3 3 3 4 4 4 4 4 5 5 5 5 5 6 6 6 6 D id 0 M no ita ropro 2 C s 3 r g t R e n l E i i B t F a 8 8 8 8 8 e 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 e t M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 r e 0 0 0 0 0 m O l U uC E E EE E E E EE EE E EE EEE EE E E E EEE p a 0 0 0 0 0 0 0 0 0 0 O 0 0 0 0 O 0 O 0 0 0 0 O 0 u N loc 6 6 9 8 2 9 9 4 7 4 f 0 9 7 7 S 6 S 5 0 0 8 4 S 9 i c ra i N V 2 3 2 3 2 2 2 3 2 3 2 3 2 2 2 3 2 3 2 3 3 2 3 2 2 e t O ra lc P I u T r A N iA T ke S erC f lo W po tS nte 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 9 7 9 9 9 7 7 7 9 9 9 7 9 9 9 7 9 9 oa 7 9 9 9 7 9 9 / 9 / / / / / 9 / / / 9 / / / / / 9 9 9 / / / 9 9 icd 3 0 7 / 0 7 / 4 1 3 4 1 1 2 4 1 1 2 1 8 8 16 2 0 / 1 8 6 / 2 8 5 0 / t / / / 2 3 6 1 2 2 4 1 1 6//////////////////////// 1 2 le 1 1 1 1 2 2 2 2 3 3 3 3 4 4 4 4 4 4 5 5 5 5 6 6 6 loC tra tS nte 69 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 e / 7 9 9 9 7 9 9 9 7 9 9 9 7 7 7 9 9 9 7 9 9 9 7 9 t oa 9 / a / / / 9 / / / 1 / / / 9 / / / 9 / / / 9 9 9 2 8 5 / / / 6 2 0 / 3 0 7 / 0 c 9 it D 3 4 1 0 1 8 6 / 2 21 2 3 1 1 2 4 1 1 2 1 1 8 / 1 2 2 4 1 1 2 3 6 c 1 1 1 1 1 2 2 2 2 3 3 3 3 4 4 4 4 4 4 5 5 5 5 6 6 li / 4 / / / / / / / / / / / / / / / / / / / / / / / le pu lo D C [W [0 0 ) a 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 e y M. - 0 0 0 40 0 0 40 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 - - - t EEEEEEEEEEEEEE E E EEE E EE E EE Biu t v 3 3 2 3 3 3 3 3 3 3 3 4 4 4 3 3 3 3 3 3 3 3 3 4 3 sic 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 t sci / o + rAC - + + + + + + + + + + + + + + + + + + + + + + + + 0 8 6 9 4 3 2 5 1 6 3 3 5 3 5 2 5 1 6 3 3 4 7 1 1 G p ( 2 1 1 1 2 3 3 2 2 3 3 4 33 2 2 3 2 2 2 2 2 3 6 2 tn 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 ue 9 9 9 9 9 / 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 / / / / / / / / / / / / / / / / / / / / / / / / ot 0 8 4 0 8 4 2 0 6 4 4 3 0 5 1 9 4 2 1 3 7 1 3 1 2 Ca 1 2 2 0 0 1 2 3 0 0 2 0 1 1 3 0 1 2 2 0 / / / / / / 1 2 2 0 0////////////// / / / / D 6 7 7 7 7 8 8 8 8 9 9 9 9 9 0 0 0 0 0 1 1 1 2 2 2 -d 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 i M no i ta ropro 2 C s 3 r g te lt n l E i i B t F a p te M e 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 S 8 8 8 8 8 8 8 8 8 r 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0 0 0 0 0 0 0 0 0 e m a U uC EEE E EEEEEE EEEEEEE EEE EE EE E O lu N 0 0 0 0 0 0 0 0 0 O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 loc 9 0 3 6 0 0 5 0 6 S 5 0 6 0 1 1 9 0 0 0 1 0 0 1 0 a ic r N V 2 3 3 2 3 3 3 3 2 3 3 3 2 3 3 3 2 3 3 3 3 3 3 3 3 tr e a O lc P I u T r N iA A k T e S erC f l oW p o t S n e 7 7 7 7 7 7 t 7 7 7 7 7 7 7 7 7 7 7 7 9 9 9 7 9 9 9 7 oa 9 7 7 9 9 9 7 9 9 9 9 7 7 9 9 9 9 / / / 9 / / / 9 i / / / / 4 1 8 / 1 8 5 / 3 9 7 7 / 9 / / / / 9 6 3 0 7 1 2 2 4 1 1 2 2 / 9 9 / / / 9 cD t 4 / / 5 2 9 / / / / / / / / / / / 2 1 9 1 2 2 6 1 1 2 2 3 9 1 2 3 0 0 0 0 1 1 1 1 2 le / / / / / / / / / / / / / / / / 6 7 7 7 7 7 8 8 8 8 8 9 9 9 9 9 1 1 1 1 1 1 1 1 1 lo C tra tS 7 7 7 7 7 7 nte 7 7 7 7 7 7 7 7 7 7 7 7 7 9 9 9 7 9 9 9 e / / / t oa 9 9 7 7 9 9 9 7 9 9 9 9 7 7 9 9 9 9 / / 8 / 1 8 5 a / 9 9 3 9 9 7 / 9 / / / / 4 1 / / / / 9 / / / / / 9 85 2 9 it / 6 3 0 7 1 2 2 4 1 1 2 D 7 4 1 2 1 9 1 2 2 6 1 1 1 2 3 9 1 2 3 / / / / / / / / ic / / c / / / / / / / / / / / / / / / / / 0 0 0 0 1 1 1 1 6 6 7 7 7 7 7 8 8 8 8 8 9 9 9 9 9 1 1 1 1 1 1 1 1 lp le u lo D C e0 fO q ) a 2 2 2 2 0 0 0 0 te y M. t EEEE Biu v 2 4 3 3 sic 0 0O 0 t sci / oAC - + + + + r G p 8 9 5 0 ( 1 3 2 2 tn 7 7 8 8 ue 9 9 9 9 / / / / ot 8 1 7 6 Ca 1 3 0 0 / / / / D 2 2 1 1 d 1 1 0 0 i M no i taropro 2 C s 3 r n te R g E i li B F tar e M e 8 8 8 8 0 0 0 0 e m p ta U uC EEEE O l N 0 0 0 0 u loc 5 9 1 0 c r it a N V 3 2 3 3 r e a O l P c I u T r N i A A k T e S erC f loW po tSn e 7 7 7 7 t 9 9 9 9 oa / / / / 0 7 4 1 icD t 1 1 2 3 / / / / le 2 2 2 2 1 1 1 1 loC tra tS e 7 7 7 nt 7 9 9 9 e t oa 9 / / / 0 7 4 a / icD 2 1 1 2 c t / / / / i 2 2 2 2 l le 1 1 1 1 pu lo D C otbo tnD a C i ) 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 a e y M. - 0 0 c0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 t 0 - - - - - EE E EEEEE E E EE EE EEE EE t E EEEEE Biu v 4 3 3 3 4 3 3 3 3 3 3 3 2 3 3 4 3 3 3 3 3 3 2 3 3 sic 0 - + + + + + + + + + + + + + + + + + + + + + + + sci - 0 00 0 40 0 0 0 0 0 0 0 0 0 0 0 0 40 0 0 0 0 t / o + + - - - rAC 3 5 5 4 4 1 5 1 2 0 4 1 6 0 0 8 0 9 8 7 7 6 8 3 2 G p ( 3 2 2 3 2 2 2 2 2 2 2 2 1 2 2 2 2 1 1 1 1 1 1 2 2 tn 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 ue 9 3 9 9 9 9 9 9 9 9 9 9 9 9 9 9 / 9 9 3 9 9 9 9 9 9 / 8 / / / / / / / / / / / / / / / / / / / / / / ot 4 3 9 6 9 6 7 4 0 7 7 2 7 5 5 4 9 7 7 1 8 3 1 5 5 Ca 1 1 2 2 0 1 2 2 / / / / / / / / / / / / / 1 2 0 0 1 2 0 1 1 2 0 0 1 2 2 0 0 / / / / / / / / / / / / - 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- ) 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 a 0 0 0 40 40 40 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 te y M. - EE E EEEEE E EE EEEE EE E EEE EEE Biu v 3 3 2 3 3 3 3 3 3 3 4 4 4 3 3 3 4 3 3 3 3 3 3 4 3 sic 00 0 0 0 40 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 t o + - - - - sci - + + + + + + + + + + + + + + + + + + + + + + + + / rAC G p 1 8 7 8 6 8 9 7 1 3 2 8 4 9 5 2 5 2 8 2 6 2 1 2 7 ( 2 1 1 1 2 2 2 2 2 3 4 3 3 2 2 2 3 2 2 2 2 2 3 6 2 tn 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 ue 9 9 9 9 9 9 9 9 9 9 9 9 / 9 9 9 9 9 9 99 9 9 9 9 / / / / / / / / / / / 9 / / / / / / / / / / / ot 0 8 4 0 8 4 2 0 6 4 3 0 5 1 3 9 4 2 1 3 7 1 3 1 2 3 0 1 2 2 0 !1 2 2 0 1 2 2 0 0 0 / 2 3 0 0 2 0 / / / / / / 1 1 Ca / / / / / / / / / / / / / / / 1 / / - D 6 7 7 7 7 8 8 8 8 9 9 9 9 0 0 0 0 0 0 1 1 1 2 2 2 i 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 d M no itaropro 7 C s 3 r g te R n l ta E i i B e 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 l 8 0 0 0 0 0 0 0 0 0 0 e te M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 r m E E EE EEEEEE EE EE EEEEEE EE EE E O l U uC p a 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 loc 9 0 4 6 1 0 5 0 6 3 0 5 9 0 0 1 9 0 0 0 1 0 0 0 9 u N a ic 2 3 3 2 3 3 3 3 2 3 3 2 2 3 3 3 2 3 3 3 3 3 3 3 2 r N V ic t O r a c P I u T r A N iA T k S ee rC f loW po tS 7 7 7 7 7 7 n e t 7 7 7 7 7 7 7 7 7 7 7 7 9 9 9 7 9 9 9 7 / / / 9 oa 9 7 7 9 9 9 7 9 9 9 7 7 9 9 9 9 9 / / 9 1 8 5 / / / / 9 9 / / / / / 4 1 8 / 6 3 3 0 7 1 2 2 4 1 1 2 2 / 9 cD / 9 9 / / 9 / i 5 2 3 9 7 / / 4 t 1 2 3 9 1 2 2 3 / / / / / / / / / 2 1 /9 1 2 2 6 / ////////0 0 0 0 1 1 1 1 2 / / / / / / 1 / le 6 7 7 7 7 7 8 8 8 8 9 9 9 9 9 9 1 1 1 1 1 1 1 1 1 loC tr a tS 7 7 7 7 7 7 nt 7 7 7 7 7 7 7 7 7 7 7 7 7 9 9 9 7 9 9 9 e e / / / t / / / 9 oa 9 9 7 7 9 9 9 7 9 9 9 7 7 9 9 9 9 9 / / / / / 4 1 8 / 1 8 5 a / / / 9 9 6 6 3 0 7 1 2 2 4 1 1 2 ic / / / 9 3 9 7 9 9 5 2 9 / / / it D 7 4 / / / / / / / / / / / / 0 0 0 0 1 1 1 1 c 1 2 1 9 1 2 2 6 1 1 2 3 9 1 1 2 3 le 6 6 7 7 7 7 7 8 8 8 8 9 9 9 9 9 9 1 1 1 1 1 1 1 1 lp / / / / / / / / / / / / / / / / u lo D C 0* fP 4 ) 2 2 2 2 a 0 0 0 0 te y M. t EEE E Biu v 3 4 3 3 sic 00 0 0 t sci / + + + + oAC r G p 9, 9 4 1 ( 1 3 2 2 tn 7 7 8 8 ue 9 9 9 9 1 / / / ot 8 1 7 6 Ca 1 3 0 0 / / / / D 2 2 1 1 d 1 1 0 0 i M no itar o p r o 7 C s 3 r g t R e n l t i E i F B a r e M e 8 8 8 8 0 0 0 0 m e t p a l uC EEE E t O lu N 0 0 0 0 loc 4 9 1 0 a ic r N V 3 2 3 3 t r e a O lc P I u T r A N iA T k e S e rC f lo W po tS e 7 7 7 7 nt 9 9 9 9 oa 0 7 4 1 / / / / icD 1 1 2 3 t / / / / 2 2 2 2 le 1 1 1 1 lo C tra tS e 7 7 7 e nt 7 9 9 9 t / / / oa 9 a / 0 7 4 D 2 1 1 2 ic itc / / / / l 2 2 2 2 p le 1 1 1 1 u lo D C d % wIH( 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 a ) . 0 - 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T. 1 I' l T 1 I' I' 1 l l tw l' 4 1 1 I 1 I 1 1 1 1 1 l 1 1 1 1 1 1 4 l. 1 o W R I 8 t A 3 6 4 7 0 1 4 6 8 4 0 5 5 1 0 3 4 4 2 2 9 0 7 5 5 1 1 3 1 1 1 41 2 2 M 7 0 5 5 6 6 9 l l 1 5 S l I' A 1 3 1 1 i 4 N 0 0 N R i A I l l 4 I K k 0 0 / / R iR 1 C C l C C R 1 / l l l' l 3 l l' A-2 t 0 1) 4 4 4 4 3 4 4 3 3 4 i C 8 0 0 0 0 0 0 0 0 t 0 0 ) 4 u 4 3 3 0 I 6 I ~- 0 ? M i i 0 0 l 1 M I 1 I l 1 I l I I I l 1 I I I l 9 0 4 7 5 4 1 5 5 7 8 I A T 6 5 1 6 2 2 9 R ~. R 6 I T l. l. T I I' T T_ T_ 1 T_ T. + P 8 l T_ T1 1 f 1 L 1 1 1 l i 1 1T 1T l I 3 I A 6 5 9 0 5 5 0 0 1 3 4 1 4 6 8 3 6 4 7 0 9 4 8 4 4 2 2 2 1 K h I 0 N 1 8 3 1 3 1 1 1 2 2 / 7 0 5 5 6 6 9 1 1 i i 3 4 l 0 l 0 / i li i 1 0 C I C C R 1 N 0 t l 5 S A l l A 1 / 1 I 1 1 1 1 Z R R us0D WswW o 8 ( ~ SE I X 2 3 I 0 0 4 l 0 l O 8 1 4 H 0 1 4 4 O u u 3 M 1 l' 8 6 M M M ~- 0 0 0 0 0 M I M 4 4 t t 0 C 2 1 l' I I I I I' I l I I' I I l I I 1 t 7 3 i 1 4 1 5 1 5 5 4 3 5 1 8 8 R 4 1 6 ~. 1 2 i 3 T. 1_ 3 T. T T 1 + A i T 1 I 1 l 1 T 1 t 7 5 1 0 J. I' R 7 8 I 1 1 I 1 l l 1 1 l 1 1 l 1 1 1 I A 3 6 4 7 0 1 4 2 2 1 6 8 7 4 8 0 0 1 1 9 5 9 0 5 5 1 1 3 13 3 I 1 1 2 2 4 4 / 7 n 5 6 6 9 l li 1 5 s A l A 1 5 0 i 1 N R i 1 1 N b h 3 l a l O 1 O 7 / R R 1 0 U 1 C IC R 1 / i 9 t K k N l l A. 2 1 1 3 4 4 i 0 1 M 0 0 0 0 0 1 t 1 0 0 0 4 l 4 4 t 3 3 4 1 3 4 O 3 4 M M M C 7 i 0 i 0 0 i M M t 9 1 l 1 I I 4 I I I I I I 1 l I ik I t 8 4. 3 1 4 4 i A 9 5 5 2 4 6 I 7 \\- 7 0 T_ 1 T, T t' T l 8 l 5' 1 T I' 1 s I 9 1 1 1 T.I 1 l 1 I 1 1 I 1 1 l lT_ T T. l 6 1 1 R 1 1 1 no te e A i is t ta o a ro p D p m s o o 2 i tr r s a 3 yt C sC laS R g laly E n n 3 6 4 7 0 1 4 6 8 Ao 4 8 0 0 1 1 1 i A 1 n i e 1 i 7 5 9 0 5 5 1 1 3 1 3 41 1 1 2 2 l r ) 4 4 2 2 1 it t 7 i N 5 6 6 9 1 7 0 5 M. M m t M 4 l 0 1 0 N R t 1 1 S 5 A 1 l I l i 1 l r a c r e au uU ule / t K k 0 1 0 / / R 1 1 C 0 I ( C R 1 1 I e taQCNt o rl p l eC c O u / c n i Np oC r e a it pOS r c r s a ai ( ITa S i P s c y md E u rl A e I Tmt N iAna X s 2 ai S ( 6 0 l l 3 O O 3 4 0 H 2 k A GI l' 1 0 0 D O 0 0 1 4 l 2 4 4 3 4 3 4 i i 0 0 ) 0 e i ? M M M M i M M r e l 8 I l I I I' I I I I 1 I I l MI I 1 I s e c C ip t 6 2 9 a i o 0 2 7 6 l 7 5 1 5 6 4 1 3 8 8 f D M s l l to A T. T. T 1 T l t' 1 I. l. 1 T T T W Is 6 1 I 8 1 1 1 8 I 1 1. 1T 1 1 1 l 1 I I o 0 l R 8 I A 3 6 4 7 0 1 4 6 8 4 7 0 5 6 6 9 1 3 3 4 4 4 2 2 7 5 9 0 5 5 8 1 3 1 1 1 1 1 2 2 8 0 0 M 5 l A i A i I l 4 N b 0 N R lt i S S I 1 l 4 t K M 0 1 C / / I R 1 C 0 I C C R T t / i 1 t l SE I X 2 I 0 2 4 4 3 4 3 4 l 4 4 3 4 O 3 4 t 1 0 0 0 0 0 0 0 i 3 O i 0 0 0 0 0 0 0 C 2 I ? i M M i i M i l 6 I I I I l I I 1 I l 1 1 l I l I 0 l 5 2 7 6 i A 6 T 4 1 5 1 5 5 4 1 5 5 I 6 T. T. R 1 R 6 1 1 1 T T. T. T. T 1 T T T. T. T + T T. 1 1 L 1 1 l. 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T T T 9 7 3 U 1 3 2 4 0 1 1 1 1 1 3 6 4 7 0 1 4 6 8 4 8 9 0 5 5 1 1 1 3 3 4 4 4 2 2 0 0 7 5 2 1 i 3 1 1 1 1 1 2 2 6 6 9 I A I 5 5 M 7 0 i I R I 2 1 4 N O l O N R 1 1 S S A 4 t 1 l 5 1 K M C 1 C Z Z 1 I 1 C C C C T I / 1 1 t I - C o'gD no i taropc ri s ot Ci a s Cu Dy c gqi la R inA t ) i A a n u il t q sl i i 3 3 yA WMm l 0 0 0 0 0 o 0 P 0 a 0 O o r 0 0 ea u Oh n G t lS 1 1 1 l o 1 1 1 1 2 l i I 1 l 1 2 l pw U r 1 4 9 0 o N c t i i i i i I I t I i i o K e 1 2 I l l I l I I I l l I l l r ta i l iN p U / 0 0 l 3 2 3 2 2 1. 2 2 2 2 2 9 3 3 aP ta 6 + 1 e te COS lc e I 0 2 T. T t' T T. T. T.. pI a l L 1 1 f. T. r ( h 4 9 T T t l. I 1 1T. 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T T T 1 1 l 1 3 f at le C 5 I I l I I a o pIOa H T 6 t l lcP r I' T ~ 3 6 l 2 J. L u eh Tm M l l 1 1 L ( 1 1 1 NuS Am 5 1 r 8 l k s Ta e o ep SG r x CE f lo 6 8 3 6 4 7 0 1 I 2 2 1 i W 1 7 8 9 0 5 5 0 0 3 3 1 5 6 6 9 l 3 l 1 2 2 1 1 I 1 1 9 7 0 5 5 A i / 4 N 0 E 0 N R L li 1 I S S A 1 5 l l i 9 K I C C Z 7 R R 1 C C I C 0 M l l 1 l / i L I t i NEM ep 2 3 3 s 1 U 0 0 Es 0 l l 2 l l O u 6 O I 2 E E i 2 2 2 l t O U 4 0 1 1 o i i 2 E 0 0 o O u o O !I E 3 E U 4 E 5 1 li i i N E I i I. E 8 E l l l l l 0 0 4 2 0 7 2 I I 0 3 8 3 I 4 3 4 i 1 9 + E 3 4 T. 8 0 0 T. 3 l 4 T T T T. T. T T T T T. 3 T.1 1 t 2 s T. a L L L 1 1 N 1 1 L 8 1 l 1 1 1 1 1 ts 4 6 8 3 6 4 7 0 1 4 2 2 0 3 3 4 4 0 5 5 0 1 3 4 8 9 2 2 7 1 1 1 1 1 1 1 5 5 6 6 9 9 7 0 1 A / 5 l 2 4 N 0 E O N R 1 i 1 S S A i l l 1 i S B K M C C Z Z R M 1 C C I C 0 R T L 2 E I / 1 n nj 7c" o 3 3 30 O 0 2 1 l I 2 1 2 1 1 2 2 1 l 2 2 2 i 3 1 l 1 4 i i E E E i I i i 0 0 U 0 0 o 4 4 0 o D 0 0 0 0 0 O l l 1 E l 7 1 i i 7 i l l l l l 0 0 7 0 5 T. 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I 3 6 4 7 o 6 8 W E 4 8 9 0 5 5 0 0 3 3 l l 4 5 l 4 2 2 t 5 5 6 6 9 8 1 1 1 1 I i 1 2 2 H 7 0 l S S A i l N i l l 3 A i I l 4 N 0 E 0 N H l l 1 C C I C C R T l i t l l S i K h 0 1 C Z 7 R I 1 t 3 3 3 0 0 0 1 2 2 1 1 2 2 2 E E 0 7 0 1 1 1 2 I 0 0 0 0 0 0 0 0 6 6 2 E 1 0 0 0 O D 7 E E E E E E E E E E 7 1 1 i 1 i i 1 l 1 l 0 0 l 7 0 4 9 4. I 6 3 5 5 2 1 3 + + 7 4 t 3 4 T. 9 5 + 7 I 1 1 1 l 1 l T. T. T T T. 4 6 / T 6 T T.. T T. T T. T 1 I 1 I 1 1 1 3 1 9 9 t 1 /6 I T f DM I D. tS EN I. 1 4 6 8 l 3 6 4 7 0 4 4 4 2 2 E 4 8 2 2 t 5 9 0 5 5 0 0 3 3 1 1 1 H 7 0 5 6 6 9 1 1 1 1 1 1 5 3 4 N O E O N R li t 1 S S A E A i i M E l 1 S B K M C l' C Z Z R R 1 C C C C R T l I l n n) ete co 7 M I H M i I t 0 I ) i m i i i l 8M s I n u ( o o t M M M M i M M I l l M ( I t t ( O ( M I ( ( / i i i i u. l i i i i 4 B B l I 1 I 1 l 1 i l 1 I l 1 l 1 l I 3 4 1 9 6 l. 7 I 6 l. l. 5 1 1 1 H I 8 l ~ 1 1 I I l 1 7 l. T. 1_ l 1 I 1 I 1 1 I I 5 1 1 i 1 I 1 1 1 l 1 1 I I 1 1 i 1 1 4/ 3 M l l A W UN o I l o 8 I 1 6 1 l t I l 2 2 0 i i 2 1 E M 9 u 5 5 0 1 1 l 1 I m N 7 o 5 h e 9 1 l 1 't U i 0 1 A 1 5 5 I. I. i 3 i t l l 4 8 1 l s S l 1 r i 1 i l i l N I 4 / / \\ i l N R 1 I 1 t 1 1 t p I K h C I 4 ( t a r e en 5 g r s r l i o o b Ws Cr ly e O a gt n n a r R A e iaWt ) i t a r l 7 t 0 0 i o 1 l O eB m M i M M H l i I O 0 0 n 1 M W i. M u r - M l 4 o l M ( E. i 1: 1 l 1 1 l l l i 1 B l ( ( it 0 o o t O 0 0 o 0 0 0 epy / l I l l 1 l i 1 i i i l i i r 3 gl i s i i Oa Utc l wiCNp 3 2 2 i 2 5 2 2 3 2 2 3. 3 l 4 4 n i e / k 2 2 l' l'. ~. rh at p e a n NS T. l' 1 I 1 l 1 1 1 T 1 1 1 1 I 1 l l. 1 I l 1 lc l' i ( h Oa 7 m 5 l 1 I 1 1 1 1 1 1 I f I u e t I Nr Tm 4 / u 2 Aa k s e o T G ep S r x Cl i tl lf t i o N W W UN 1 0 h 8 I M. 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T iP i ( D IOa r 4 c m u e Nr T m u Aa k s eo T G e p S r x CE M f E l I o X W W G N K 8 9 0 5 5 0 0 3 3 4 1 8 6 8 I 3 0 4 7 0 I 5 6 6 9 1 1 1 1 1 1 1 4 2 2 4 5 2 2 NI 7 0 5 1 i D i l 1 l s 3 M li 4 N O 1 0 N R i t 1 S S A E l A l i I t K h C 1 C Z Z R R 1 U C I C C R T I 7 9 4 E I U 0 0 0 0 0 o 1 0 0 0 0 0 l l 0 0 i 0 0 0 0 n 0 I M U 0 0 0 0 3 0 o o / i l 1 l II l 'l. l 1 E E E E B l ( l l i 1 i i i i i E i 8 9 3 7 3 7 4. 3 4 4 4 4. 5 2 7 6 3 3 3 7 T. T. T.. T. T.. T T T._ T. T. 1 f. T. T.. . T 9 1 1 I 1 1 1 1 1 I 1 1 1 f 1 1 T. T T_ l - 1 l l R E IN W GN 4 6 8 l 3 6 4 7 0 1 41 2 2 k 4 8 9 0 5 5 1 1 1 0 0 3 3 4 2 2 5 6 6 9 1 1 1 41 5 N 7 0 5 t i l 3 i A i l 4 N 0 l O N R 1 i 1 S S A 1 l l i l !1 K M C I' C Z Z l R 1 C C C l R T C i 1 t l l l 1 y yN* ~ 7 X ) M Z M I 0 0 0 1 0 0 0 M l I 0 / I 0 i ) 0 0 0 7 I O 0 ( M IN o o 0 0 0 0 0 I ( / D l 'I 'I E E i E l B i l ( 1 l i i I i 1 E l I l I i i i i 7 3 5 3 3 3 6 3 3 6 3 3 5 7 3 8. 7 T. 6 I' 4 ~. F l'. T. 3 T_ T. 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T e t I 1 1 1 1 1 l 1 1 l 1 I 1 1 1 l 1 I M !TA w GN 1 4 6 8 I 3 6 4 7 0 4 4 4 2 2 K 4 8 9 0 5 5 1 1 1 1 1 1 1 1 0 0 3 3 2 2 5 5 6 6 9 N 7 0 5 3 J 1 S S A E A i l 4 N O E O N R U I M, E t i K M C 1' C Z Z 1 R C C C l R T C I 1 l l I I l uuoD obro - c t c t n o i ~ t tr o e mr 0 n s o o 4i Cr Ws b ly e La gt n na r R e A aWt it ) E a rBn r e e~y-Wt n p i Ma Or gL n i Ut / c wiCNe rh k p at n p NS eai ( l cP Oa rD m u e I Nu T r m Aa k s eo T G ep S r x CE f loW 7 9 / l / 0 0 0 0 0 0 0 I 0 1 1 0 ) / o 1 0 0 0 M 4 i 0 0 0 0 ( 0 0 0 1 0 0 0 t s I I M 0 0 0 0 1 i i i 1 1 l 1 l E E E E E E E E E l 1 I 3 3 7 3 7 3 3 3 4. 3 4 4 5 2 7. 6, 3 9 T T. 1 1 1 1 1 1 T. T. 1 1 1 l 1 7 / T T T. T. T. T. T.. T T T T T 1 T. 9 4 L 1 1 1 / 3 1 1 1 I'U D R E T A W GN 4 6 8 I 3 6 4 7 0 1 4 2 2 K 4 8 9 0 5 5 0 0 13 1 1 1 1 2 2 3 3 4 4 5 1 1 1 6 6 9 N 7 0 5 5 K M C C Z Z R R 1 C C l C l A l i i l I 4 N O 5 O N R U U S S A s t 1 i 1 C 1 T H 1 1 1 I 1 yoj
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T T T. 4 9 3 3 3 7 4 8 3 4. 3 4 4 4 5 5 2 7 6 7 1 1 T + /2 T. l 1 1 1 1 l l 1 1 1 I. 1 1 L 1 1 1 T. 2 / R F I A W EC 1 4 6 8 3 6 4 7 0 A 4 8 0 5 5 1 0 3 1 l 3 0 4 4 4 2 2 R 1 1 1 3 1 1 2 2 F 5 9 5 6 6 9 7 0 5 3 l 4 N O E O N t i 0 1 S S A E E A i l - t i 1 K M C C Z iZ R 11 1 C C I C C R T l I 1 S 1 I o* m a: oe 2 4 I 2 O 0 0 0 O 0 O 0 O U O O 0 1 0 1 0 0 i 0 O 0 O 0 l l 0 i 0 0 0 0 n o o 0 i i i l C i i i l i i l 7 l I I l I? I'. li 1 l i I I I l l i l l 1 9 1 0 / 4. 4 4 I 4 1 5 5 4 8 5 5 6 8 3 9. 7 3 T. 1 I l I 1 I' I' I I'. T. T. i 2 T. T T. T. I' I / 8 1 1 1 1 1 1 1 1 1 1 1 1 1 I 1 1 1. 1 2 1 R L I N W EC 3 6 4 7 0 I 4 6 8 A 4 5 9 0 5 5 1 1 1 3 1 ? 1 1 2 2 8 0 0 3 1 4 4 2 2 5 6 6 9 1 l 7 0 5 H l 4 N O ? 0 N R l i 1 S S A I i A 1 3 i l t 3 t i K A C 0 7 7 R R 1 C C I C l R 1 11 I l' I C T S t l no s i is tar ly o e a n pr n ro o CA I 0 0 0 0 0 n 0 0 0 0 O 0 0 O 4 b Cr D 1 O 0 0 0 0 0 o 0 1 0 0 0 O 0 1 1 0 ? m 0 0 0 0 e gt R u i 1 i i 1 i i i E
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n a E i iWt it 7 l l 1 1 l l 1 l l 1 il CI I l l I I l 1 r t e ) 3 r 1 3 5 3 3 6 3. 6 3 4. 2 8 3 3 5 7. 2 7. 7. 0 9 / a r I T T. T T T. T. 1 T., T I T T l T. T. 3 2 I' T I' 4 a eM r - T p y W i. U e t / d I l n wc iNa I I 1 l 1 1 1 1 1 1 1 1 l 1 1 l I 1 I 1 Oa e l CpN m rh a t f u ea r Or ( u lcP I t S u e Tc e Nr Ap u k s TS e o S a R E e p m r x I CE m N f a W l G o E W C 3 6 4 7 0 I 4 6 8 A 4 5 9 0 5 5 1 0 3 3 4 I 4 2 2 8 0 1' 7 0 5 N R i i 1 H 1 4 N O l 0 l 3 1 1 1 1 1 2 2 5 6 6 9 t 1 K h C l' C Z Z R R 1 C C I C C R l 1 i 1 1 l t S S A i i S 1 I l l A 1 3 1 1 ~ 4 0 0 O 0 l O 0 0 0 0 0 O l l 0 0 1 0 1 t 0 1 o O 0 0 0 0 0 O o O 0 0 0 0 o i i i l l i i i ? i I l i i I 7 I l l l l i i l l l I I I I I i l l 1 1 4. 9 3 4. 8 3 8 4 5 3 2 4 4. l 7. 2 7. 7. 0 9 / + 2 T T. T.. T. T 1 T T. T. I T. 1 T.. T. 5 1 1 1 I 1 1 1 1 1 I 1 1 L 1T. T l 1 l 1 1 T. l /0 I R E I A W E C 3 6 4 7 0 I 4 6 8 A 4 8 0 0 3 3 4 4 4 2 2 / 5 9 0 5 5 1 1 1 1 1 1 1 1 2 2 6 6 9 5 5 I 7 0 I i 3 R i 4 N O i O N R i it 1 S S A I l A l 3-t' l K h C l C Z Z R R 1 C C I C C R i l l t l S I I T l l o s$ t I l i i i { ? 0 l 0 2 I 0 0 i 0 o 0 0 t 0 0 0 1 0 t 0 0 t 0 t 0 1 0 ( 0 0 0 1 o 0 0 1 R M M 0 0 ? l 4 I I i l l 1 li I l l I 1 1 I I I 9 2 7 4 3 3 5 3 6 3 3 3 4 3 3 4 6 3 7. 6 2 / T. I. T. 1 T. l 5 T. T. I I' I' I' T. I I' I' I T. T. 2 /3 1 I 1 1 1 1 I 1 1 1 1 1 1 1 I 1 1 1 1 R E TA W E C 3 6 4 7 0 i I. 2 2 6 8 0 0 1 l l A 4 8 9 0 5 5 1 1 1 3 3 i l t t 1 l 3 1 1 1 l l 2 2 5 F 7 0 6 6 9 5 5 i i 1 3 k i h I K h C l 0 Z / f I 1 C C I C l A 1 1 t l 4 N 0 0 N I 1 l 1 S S A l C I T 1 l ( t I t n io is s ta y ro e la n l n r r iSA ro o 0 2 b 0 0 0 0 0 n 0 0 0 O 0 O l l 0 0 Cr U 1 1 0 0 0 0 0 o 0 1 0 0 i I l l i 1 0 0 0 O 0 O o o Mm i i i i i i I e gt i l 1 l l 1 l l l I 1 I l i i l I 1 u n a t t 7 5 2 5 5 2 r l ir iaWt rE 3 7 3 3 6. 3 7. 3 3 3 5 3 3 l. T. t e ) a T 5 ~. T T l'. I' T 8 I' r - teB 1 I' 1 I I t' I' I' 1 I' T T T. 1 L 1 1 1 1 l p y W i. M n e d a l 2 1 1 1 1 1 1 1 1 1 1 L / 1 Owc iCNm e l Ua rh a at f p u e a r Nr ( u lcP u e IOtc S e Nr Tp u AS k s R e o Ta E e p S m r x I CE m N f a W G lo I W C 3 6 4 7 1 4 1 2 2 0 1 4 6 8 F 7 0 5 5 6 9 1 1 1 1 I I 1 4 2 2 A 4 8 9 0 5 5 0 0 3 3 5 6 S I ( 1 l 1 i A l 3 1 1 1 3 H 1 N O T. 0 N 11 1 1 1 S S A i l K h C I C Z / l 1 l C C l C l t T l C i I 1 1 0 0 0 0 0 0 O 1 O 0 0 0 0 1 l 0 2 O 0 0 0 0 0 0 0 0 0 0 0 0 O 0 0 o 0 0 1 f I 1 1 F. l I I l l l l I 1 1 i 1 I 1 E i i i i i l 1 3 7 7 3 3 6 3 6 3 3 3 4. 3 3 3 5 2 6 5 1 5 ~. T. I I T, T T. I. T. I 1 T T.. T. I l 1 T. I T 1 1 1 I 1 1 1 1 1 T.1 1 1 1 2 I 1 l 1 L / I 1 RT IN W F. 4 6 8 C 3 6 4 7 0 1 4 2 2 A 4 8 9 0 5 5 1 1 1 3 1 1 1 1 2 2 0 0 3 4 4 5 F 7 0 6 6 9 5 5 1 H i 4 N O i O N i l 1 1 S S A i i A 1 3 3 i 1 t S I l 1 l l l I 1 1 t' l K M C l C Z Z I 1 1 C C l C C I 1 1 l' l ouoo o - c t t t 1 f 0 ( 0 0 0 0 O 1 ) O 1K 0 D 0 0 0 0 O 0 0 0 2 0 o 0 t O ( 0 0 1 l 0 0 H N 0 o i l l i i i i i i ? 1 l I l i l I l l I I'. l I l I 1 l I I 7 6 3 3 4 7 3 4. 3 5 4. 4. 4. 7. 3 8. 7. 2 3 6 M T 1 1 I. 1 1 T_ T.. I' l. T. I T. T. l I 1 71 I' I' T I T. I 1 1 1 1 1 1 1 1 1 1 1 T. I / 6 l f t tE I A W E t 3 6 4 7 0 1 4 6 8 A 4 5 9 0 5 5 0 0 1 3 4 1 l 2 2 8 5 6 r 7 0 5 6 9 1 1 1 1 1 1 I i 2 2 u ? 4 M 0 I O N 1 t t 3 t 1 K M C I C / 7 I I l C C I C l A i 3 r 1 i J 1 S S A I i l l I C I l' l t S 1 t t 1 no s it i s ao e ly r a n l pr i n ro o SA 1 O 0 0 0 0 0 0 1 O O 0 0 0 1 1 U 0 O 0 0 0 0 0 0 O O 0 0 0 U 2 b U 1 Cr m 0 0 0 0 0 gt Mu I i 1 i i i I i 1 i s e na i I: I l l I 1 l l l l I
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6 4 7 0 I 4 2 2 4 6 8 A 4 8 9 0 5 5 1 1 1 3 3 1 1 1 2 2 0 0 4 4 5 F 7 0 5 6 6 9 I. 1 I A I 3 5 t l 1 3 t I i 4 N O O N i l 1 1 C C I C C I T 1 S S A 1' l K M C I C 7 Z I i 1 I I I t I 1 5 I l' t t l moot o s o oi$r t I o 0 0 u 0 n 1 0 2 O 0 ( n 0 0 o 0 o I 0 I M o 0 f 1 0 0 f 1 N N O 0 ( ( t 0 o 0 1 sI l l l l l l l l I I I 1 l I 1 1 1: i i i i i i i i i I 7 / 2 5 2 2 5 3 5 3 3 2 3 3 1 3. 5 2 6. 5 3 9 1 1 I' l'. T 1 1 1 1 1 1 1 1 1 1 1 l 1 1 1 6 I' I' I 1 T T.. T. T. 11 T T.. T T I l / 9 1 1 1 1 R E I X W E C 3 6 4 7 0 6 8 4 0 U 3 3 1 i 1 2 2 A 3 5 9 0 5 5 1 I 1 l 1 I I l 2 2 5 6 6 9 l 1 F 7 0 5 t i i A l I i 4 N 0 l C Z / R i I l l i O N R lt l 3 A l C T l S t K M C l R 1 C C l C l R i 3 S S i ~ l l no s i i t s ar y o e la pn in l r r o o SA 1 l 0 0 0 i 0 l I I 1 I l l I 1 l l I Cr U 0 0 0 I 0 0 0 1 0 0 0 0 0 I l n 2 b 0 0 0 0 0 W Mm i 0 o 0 0 0 0 o o 0 e gt u i i i n a i l l l 1 1 I 21 i I i i ? i i r Ri t 7 4 3 1. 5 3 6. 3 3 3 4. 3 3 4 5 2 6 5 2 iaWt t e ) 9 2 E r a T 1 l' I' l' T. r / e teB 1 I' T_ I 1 1 1 1 1 1 l 1 1 1 1 1 T l r - 9 T. i l T. T. T, T.. T. T T T. wc iUa 1 T_ pyWiMn / ~ I d L 8 1 1 Oa e / CNm r i a alt f p u Nr e a r ( u lcP S Ot u e I c e Nr Tp u AS k s eo Ta R E e p S m r x I CE m N f a W l G o E W C 6 8 3 6 4 7 0 1 8 A 4 5 9 0 5 5 1 1 1 3 3 4 4 4 2 2 8 0 0 l' 7 0 5 5 6 6 9 i I O N t l i 3 I 1 1 l 2 2 1 l 5 4 N O I C Z Z R R 1 C C l C C R l' 1 r i l 1 t 1 K M C l' i i t 1 S S A l l A i 3-1 l S 1 1 l 0 0 0 0 0 0 0 l 0 0 ( 0 0 1 1 u 2 0 0 ) 0 0 H 0 o 0 0 0 0 0 0 0 O 0 0 o O 5 i i i I i i i I i I s i 1 l l I l i l l I I I l I I l I 1 I l 9 3 7 6 3 3 7 3 7. 3 3 3 4 3 4. 4. 6 2 7 7 2 / T. I T.. T. T T. T_ 7 I 1 1 T.. T. T. T T. T. T. T. 1 I' 2 T T. 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 / R E I A W EC 3 6 4 7 0 1 4 6 8 A 4 8 9 0 5 5 1 O 1 3 3 1 l l 2 2 0 4 4 4 2 2 5 F 7 0 6 5 5 6 9 I 1 1 i l t l 3 i i 1 3 fR i 4 N O i O N R l t 1 S S A l l A 1 l t l K M C I C Z Z R R l C C I C C i ~ l S l I t l t aa [w 3 o 1 2 0 0 i 0 0 0 0 1 m 0 0 I l l N ) ) 2 H M N 0 0 0 0 0 t 0 0 l o o O 0 0 0 0 i i i 1 1 l i l l l ( 2I. i l i i i ( E 1 l I I li li l E l l E i i 7 1 I 4. 8 4. 8 4 4. 3 7 4 4 6 6. 2 T T. 5 4 7. 6. 2 3 T I' T. T l T T. T. T 2 T. T.. T. l I 1 1 1 l I. 1 1 f l 1 1 T l. 1 T. l /2 1 1 1 f 1 f 1 R E I A W EC 3 6 4 7 0 1 4 6 8 A 4 8 9 0 5 5 1 1 1 3 3 1 1 1 2 2 0 0 4 4 4 2 2 5 F 7 0 5 5 6 6 9 1 l 3 R l 0 N i U U 1 S S A l i A l 3 4 N 0 E l i i i t t' l K h C l C Z Z R R 1 C C I C C R T 31 1 I S I no s il i s oe ly r a pn in l r r o o SA Cr U f 1 0 0 0 0 0 0 I 0 0 ( 0 O l l 0 2 b 0 0 0 0 ) 0 0 0 0 t 0 O M M m o 0 U o o 0 0 gt Mu i i i i 1 1 i i i i i s ( e na i 7 I E E l E l l l 1 I 1 l l E l l l I I r Ri t M 9 T. T. l. 1 T T T. a eB T 1 3 5 3 4. 7. 3 7. 4. 4. 3 3. 4 7 8 3 7. 3 Wt i e 2 T. T T T. T T. T. T. 9 ) t r rE t r - L l T. 1 T. 1 1 1 1 1 1 1 1 1 f I 1 1 L L pyWiMn 1 e t / d 1 1 l 1 I Oac e iUa / v c C N m. rh a it f p u ea r Nr ( u lcP S Ot u e c I e Nu Tp r AS k s R e o Ta E e p S m r
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