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EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT RADIOLOGICAL IMPACT ON MAN FOR THIRD AND FOURTH QUARTERS, 1979 4 | |||
e VERMONT YANKEE NUCLEAR POWER STATION S | |||
EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT RADIOLOGICAL IMPACT ON MAN FOR | |||
THIRD AND FOURTH QUARTERS, 1979 | |||
VERMONT YANKEE NUCLEAR POWER STATION | |||
S | |||
TABLE OF CONTENTS Page | TABLE OF CONTENTS Page | ||
==1.0 INTRODUCTION== | ==1.0 INTRODUCTION== | ||
.................................................. I 2.0 METEOROLOGICAL DATA........................................... 2 3.0 RADIOACTIVITY RELEASES........................................ 3 3.1 Liquid Releases.......................................... 3 3.2 Caseous Releases......................................... 3 | .................................................. I 2.0 METEOROLOGICAL DATA........................................... 2 3.0 RADIOACTIVITY RELEASES........................................ 3 3.1 Liquid Releases.......................................... 3 3.2 Caseous Releases......................................... 3 | ||
; 4.0 DOSE | ; 4.0 DOSE ASSESSMENT............................................... 4 4.1 Organ Doses to Individuals from Receivin Exposure Pathways.......................g-Water ................. 4 4.2 Individual Whole-Body and Skin Doses from Noble Caseous Effluents........................................ 6 4.3 Organ Doses to Individuals from Radioactive Iodine . | ||
and Particulates in Caseous Effluents.................... 8 4.4 Whole-Body Doses in Unrestricted Areas from Direct Radiation......................................... 10 4.5 Whole-Body Doses to the General Population from all Receiving Water Related Pathways......................... 11 4.6 Doses to the General Population and Average Individual within Fifty Miles from Caseous Effluents................ 13 REFERENCES......................................................... 15 TABLES.................e........................................... 16-45 APPENDIX A - SUPPLEMENTAL INFORMATION.............................. Al e | |||
ASSESSMENT............................................... 4 4.1 Organ Doses to Individuals from Receivin Exposure Pathways.......................g-Water ................. 4 4.2 Individual Whole-Body and Skin Doses from Noble Caseous Effluents........................................ 6 4.3 Organ Doses to Individuals from Radioactive Iodine . | |||
and Particulates in Caseous Effluents.................... 8 4.4 Whole-Body Doses in Unrestricted Areas from Direct Radiation......................................... 10 4.5 Whole-Body Doses to the General Population from all Receiving Water Related Pathways......................... 11 4.6 Doses to the General Population and Average Individual within Fifty Miles from Caseous Effluents................ 13 REFERENCES......................................................... 15 | |||
TABLES.................e........................................... 16-45 APPENDIX A - SUPPLEMENTAL INFORMATION.............................. Al | |||
e | |||
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LIST OF TABLES Table No. Title 1A Caseous Effluents - Summation of all Releases 1B Caseous Effluents - Elevated Releases IC Caseous Effluents - Routine Ground Level Releases ID Caseous Effluents - Non-Routine Releases 1A Liquid Effluents - Summation of all Releases 3 | |||
LIST OF TABLES Table No. Title 1A Caseous Effluents - Summation of all Releases 1B Caseous Effluents - Elevated Releases IC Caseous Effluents - Routine Ground Level Releases ID | |||
Caseous Effluents - Non-Routine Releases 1A Liquid Effluents - Summation of all Releases 3 | |||
Solid Waste and Irradiated Fuel Shipments 4-A to 4-H Vermont Yankee Joint Frequency Distribution July - September, 1979 5-A to 5-H Vermont Yankee Joint Frequency Distribution October - December, 1979 . | Solid Waste and Irradiated Fuel Shipments 4-A to 4-H Vermont Yankee Joint Frequency Distribution July - September, 1979 5-A to 5-H Vermont Yankee Joint Frequency Distribution October - December, 1979 . | ||
6 Quarterly Average X/Q and D/Q Values for - | 6 Quarterly Average X/Q and D/Q Values for - | ||
Selected Receptors 7 | Selected Receptors 7 | ||
Summary of Radiological Impact on Man | Summary of Radiological Impact on Man | ||
-iii- | -iii- | ||
VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT RADIOLOGICAL IMPACT ON MAN JULY - DECEMBER 1979 1.0 INfRODUCTION Using actual measured effluent and meteorological data for the second six months of 1979, this report estimates potential doses from radioactive effluents that could affect individuals and the general population near | VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT RADIOLOGICAL IMPACT ON MAN JULY - DECEMBER 1979 1.0 INfRODUCTION Using actual measured effluent and meteorological data for the second six months of 1979, this report estimates potential doses from radioactive effluents that could affect individuals and the general population near | ||
~ | ~ | ||
the Vermont Tankee Nuclear Power Station. Tables 1 through 3 list the recorded radioactive effluents and solid waste for this semi-annual period. | |||
Tables 4 and 5 report the cumulative joint frequency distribution of wind speed, wind direction, and atmospheric stability observed during the second | Tables 4 and 5 report the cumulative joint frequency distribution of wind speed, wind direction, and atmospheric stability observed during the second half of 1979, while Table 6 lists the calculated I/Q and D/Q values at different points of interest based on the meteorological record presented in Tables 4 and 5 for both quarters. Table 7 summarizes the potential radiological dose commitments to individuals and the general population surrounding the plant. Supplemental information concerning the plant's regulatory release limits and the methods used in measuring released radioactivity is given in Appendix A. | ||
half of 1979, while Table 6 lists the calculated I/Q and D/Q values at different points of interest based on the meteorological record presented in Tables 4 and 5 for both quarters. Table 7 summarizes the potential radiological dose commitments to individuals and the general population surrounding the plant. Supplemental information concerning the plant's regulatory release limits and the methods used in measuring released radioactivity is given in Appendix A. | |||
All estimates of potential dose for the second six months of 1979 t | All estimates of potential dose for the second six months of 1979 t | ||
were within the dose objectives set forth in Appendix I to 10CFR50. This | were within the dose objectives set forth in Appendix I to 10CFR50. This was accomplished while the plant realized net capacity factors (design MWe) of 72.5 percent and 60.1 percent for the third and fourth quarters, respectively. | ||
e 2.0 METEOROLOGICAL DATA Meteorological data was collected during this reporting period from the site's 300 foot met tower located approximately 2200 feet northwest of the reactor building, and about 1,400 feet from the plant stack. The 300 foot tower is approximately the same height as the primary plant stack (94 meters) and is designed to meet the requirements of Regu? r ; iry Guide 1.23 for meteorological sonitoring. | |||
was accomplished while the plant realized net capacity factors (design MWe) | |||
of 72.5 percent and 60.1 percent for the third and fourth quarters, respectively | |||
e | |||
2.0 METEOROLOGICAL DATA Meteorological data was collected during this reporting period from the site's 300 foot met tower located approximately 2200 feet northwest of the reactor building, and about 1,400 feet from the plant stack. The 300 foot tower is approximately the same height as the primary plant stack (94 meters) and is designed to meet the requirements of Regu? r ; iry Guide 1.23 for meteorological sonitoring | |||
Implementation of the Central Meteorological System (CMS) was completed during the month of May, 1978. Combined data recoverability for the third and feurth quarters was 88.4 percent and 99.8 percent respect 1vely. , | Implementation of the Central Meteorological System (CMS) was completed during the month of May, 1978. Combined data recoverability for the third and feurth quarters was 88.4 percent and 99.8 percent respect 1vely. , | ||
X/Q and D/Q values were derived for all receptor points from the site meteorological record for each quarter using a straight-line airflow model. All dispersion and air concentration factors have been calculated employing appropriate source configuration considerations, as described in Regulatory Guide 1.111(1), plus a source depletion model as described in Meteorology and Atomic Energy (1968),(2) and deposition velocities as given by Pelletier and Zimbrick(3). Changes in terrain elevations in the site environment were also factored into meteorological models. A full description of the methods used to evaluate air dispersion phenomenon at the plant site is given in Vermont Yankee's 10CFR Part 50, Appendix I I evaluation (4). | |||
X/Q and D/Q values were derived for all receptor points from the site meteorological record for each quarter using a straight-line airflow model. All dispersion and air concentration factors have been calculated employing appropriate source configuration considerations, as described in Regulatory Guide 1.111(1), plus a source depletion model as described | |||
in Meteorology and Atomic Energy (1968),(2) and deposition velocities as given by Pelletier and Zimbrick(3). Changes in terrain elevations in the site environment were also factored into meteorological models. A full description of the methods used to evaluate air dispersion phenomenon at | |||
the plant site is given in Vermont Yankee's 10CFR Part 50, Appendix I I evaluation (4) | |||
t | t | ||
...~..-. ...... . . . . . . . . . . . . . . . . | ...~..-. ...... . . . . . . . . . . . . . . . . | ||
3.0 RADIOACTIVITY RE1. EASES 3.1 Liquid Releases During the semi-annual period, a total of 16 planned and controlled batch releases of liquid radioactivity (totalling less than 2.90 x 10-4 C1) were discharged f rom Vermont Yankee in accordance with the plant's operating Technical Specifications. All liquid effluent recorded for the second half of the year are listed in Tables 2A and 2B. Approximately 484,000 litets | 3.0 RADIOACTIVITY RE1. EASES 3.1 Liquid Releases During the semi-annual period, a total of 16 planned and controlled batch releases of liquid radioactivity (totalling less than 2.90 x 10-4 C1) were discharged f rom Vermont Yankee in accordance with the plant's operating Technical Specifications. All liquid effluent recorded for the second half of the year are listed in Tables 2A and 2B. Approximately 484,000 litets of waste liquid was released to the Connecticut River through the plant's | ||
of waste liquid was released to the Connecticut River through the plant's | |||
: liquid radvaste system. Average river flow for the release periods was approximately 4063 cfs. During the same time period, there were no unplanned or non-routine releases of radioactivity in any liquid effluents. | : liquid radvaste system. Average river flow for the release periods was approximately 4063 cfs. During the same time period, there were no unplanned or non-routine releases of radioactivity in any liquid effluents. | ||
3.2 Caseous Releases | 3.2 Caseous Releases | ||
* All gaseous effluent recorded for the second half of the year are listed in Tables LA through ID. All gaseous effluents were recorded as continuous in nature, and were released to the environment via the 94 meter stack located approximately 875 feet north of the Reactor Building. As indicated in Table 1A, all gaseous effluents were well within the plants | |||
All gaseous effluent recorded for the second half of the year are listed in Tables LA through ID. All gaseous effluents were recorded as continuous in nature, and were released to the environment via the 94 meter stack located approximately 875 feet north of the Reactor Building. As | |||
indicated in Table 1A, all gaseous effluents were well within the plants | |||
~ | ~ | ||
operating Technical Specification for gaseous re1 eases of radioactivity. | operating Technical Specification for gaseous re1 eases of radioactivity. | ||
In addition, there were no unplanned or non-routine releases of radioactivity in gaseous effluents during this reporting period. | |||
M 4.0 DOSE ASSESSMENT Following the guidance of NUREG-0473(7), nuclides in particulate form which were not detected above the lower limit of detection, (LLD) have | |||
4.0 DOSE ASSESSMENT | |||
Following the guidance of NUREG-0473(7), nuclides in particulate form which were not detected above the lower limit of detection, (LLD) have | |||
, been reported as "less than' the LLD and have not been included in the dose calculations. However, the release rate of noble gases from the plant stack, af ter treatment of the gas stream from the air ejector through the augmented off-gas system, is so low that no noble gases are detectable above the LLD. | , been reported as "less than' the LLD and have not been included in the dose calculations. However, the release rate of noble gases from the plant stack, af ter treatment of the gas stream from the air ejector through the augmented off-gas system, is so low that no noble gases are detectable above the LLD. | ||
Therefore, as a conservative approach for the noble gas releaser, it has | Therefore, as a conservative approach for the noble gas releaser, it has | ||
- been assumed for dose calculational purposes that the principal noble gases | - been assumed for dose calculational purposes that the principal noble gases measured in the off-gas mix at the air ejector are present at the LLD level determined for the plant stack. | ||
measured in the off-gas mix at the air ejector are present at the LLD level determined for the plant stack. | |||
4.1 Organ Doses to Individuals from Receiving-Water Exposure Pathways '. | 4.1 Organ Doses to Individuals from Receiving-Water Exposure Pathways '. | ||
During the third quarter 16 separate batches of liquid waste totalling 484,000 liters, were released. The radiological health significance of these releases were evaluated using the liquid pathway model described in NRC Regulatory Guide 1.109(5). Site specific parameters used in applying this dosimetric model to the Vermont Yankee environment have been described and documented in the report (4) submitted to the NRC Office of Nuclear Reactor Regulation in connection with 10CFR50, Appendix I. | During the third quarter 16 separate batches of liquid waste totalling 484,000 liters, were released. The radiological health significance of these releases were evaluated using the liquid pathway model described in NRC Regulatory Guide 1.109(5). Site specific parameters used in applying this dosimetric model to the Vermont Yankee environment have been described and documented in the report (4) submitted to the NRC Office of Nuclear Reactor Regulation in connection with 10CFR50, Appendix I. | ||
The liquid pathway dose analysis for the third quarter was per. formed | The liquid pathway dose analysis for the third quarter was per. formed | ||
. at a point in the Connecticut River just below Vernon Dam 0.5 mile downstream of the plant. Fishing from the shoreline was assumed to be the sole contribution to dose. The ingestion of river water and aquatic invertebrates was not considered since these pathways do not exist along this portion of the Connecticut River or any known downstream location. | . at a point in the Connecticut River just below Vernon Dam 0.5 mile downstream of the plant. Fishing from the shoreline was assumed to be the sole contribution to dose. The ingestion of river water and aquatic invertebrates was not considered since these pathways do not exist along this portion of the Connecticut River or any known downstream location. | ||
E The irrigation of farm land by river water was not taken into account because it has not been observed below the plant. Fishing in Vernon Pond was not considered due to the relatively small fish population and because the shoreline access is largely restricted. | |||
E | All liquid effluent from the plant was assumed to be homogeneously mixed in the volume' of water which passed over the dam during the period of release. | ||
The irrigation of farm land by river water was not taken into account because it has not been observed below the plant. Fishing in Vernon Pond was not considered due to the relatively small fish population and because the shoreline access is largely restricted. | |||
All liquid effluent from the plant was assumed to be homogeneously | |||
mixed in the volume' of water which passed over the dam during the period of release. | |||
This leads to a conservative estimate of the radionuclide concentrations below the dam since no credit is taken for dilution or deposition in Vernon Pond. | This leads to a conservative estimate of the radionuclide concentrations below the dam since no credit is taken for dilution or deposition in Vernon Pond. | ||
The average river flow over the das during the time of release in the third quarter was 4063 cfs. | The average river flow over the das during the time of release in the third quarter was 4063 cfs. | ||
Usage factors for adults, teenagers and children were obtained from Regulatory Guide 1.109, and doses were calculated for whole-body, bone,'. | Usage factors for adults, teenagers and children were obtained from Regulatory Guide 1.109, and doses were calculated for whole-body, bone,'. | ||
kidney, GI-LLI, liver, thyroid and lung. The GI-LLI (gastro-intestinal and lower-large-intestine) was the critical organ for the adult age group with Tritium and Manganese-54 being the principle nuclides contributing to dose. | kidney, GI-LLI, liver, thyroid and lung. The GI-LLI (gastro-intestinal and lower-large-intestine) was the critical organ for the adult age group with Tritium and Manganese-54 being the principle nuclides contributing to dose. | ||
. As indicated in Table 7, the resulting individual CI-LLI dose commitments due to liquid releases during the third quarter are 4.2 x 10-6 | . As indicated in Table 7, the resulting individual CI-LLI dose commitments due to liquid releases during the third quarter are 4.2 x 10-6 mrem, 3.0 x 10-6 and 1.8 x 10-6 to the adult, teen and child age groups respectively. | ||
mrem, 3.0 x 10-6 and 1.8 x 10-6 to the adult, teen and child age groups respectively. | |||
It should also be noted that these doses assume that each individual ingests, in the third quarter, one half of the total annual' intake | It should also be noted that these doses assume that each individual ingests, in the third quarter, one half of the total annual' intake | ||
. of fish recommended for a maximum individual in Regulatory Guide 1.109. | . of fish recommended for a maximum individual in Regulatory Guide 1.109. | ||
All calculated doses due to radioactivity in liquid effluent are well below the dose criteria of 10CFR50, Appendix I. | All calculated doses due to radioactivity in liquid effluent are well below the dose criteria of 10CFR50, Appendix I. | ||
There were no non-routine liquid releases from Vermont Yankee during | There were no non-routine liquid releases from Vermont Yankee during | ||
~5- | ~5- | ||
the reporting period. As a result, no accidental or unplanned liquid effluents in receiving water pathways could contribute to any whole body or organ doses to individuals in unrestricted areas. | the reporting period. As a result, no accidental or unplanned liquid effluents in receiving water pathways could contribute to any whole body or organ doses to individuals in unrestricted areas. | ||
4.2 Individual Whole-Body and Skin Doses from Noble Caseous Effluents Based on the method of sector averaging discussed in " Meteorology and Atomic Energy - 1968", and utilizing the site meteorological data recorded for this reporting period, the point of maximum off-site ground level air concentration of radioactive materials in gaseous effluents was | 4.2 Individual Whole-Body and Skin Doses from Noble Caseous Effluents Based on the method of sector averaging discussed in " Meteorology and Atomic Energy - 1968", and utilizing the site meteorological data recorded for this reporting period, the point of maximum off-site ground level air concentration of radioactive materials in gaseous effluents was | ||
-determined for each quarter. ' Terrain height in the vicinity of the effluent stack was taken into account in calculating these effluent ground level concentrations. For the third and fourth quarters of 1979, the points of maximum ground level air concentration were determined to be approximately WNW at 2400m and NW at 4000m of the plant stack. The undepleted I/Q's at these locations were calculated to be 4.9 x 10-7 sec/m3 and 4.8 x 10-7 sec/m3 for third and fourth quarters of the year, respectively. | |||
-determined for each quarter. ' Terrain height in the vicinity of the effluent stack was taken into account in calculating these effluent ground level concentrations. For the third and fourth quarters of 1979, the points of maximum ground level air concentration were determined to be approximately | Whole-body and skin doses were calculated at these off-site points as a result of noble gas releases occurring in both quarters. The methodology applied to the dose calculations is consistent with that of Regulatory Guide 1.109(5) for an elevated release point. Dose conversion factors for noble gases and daughters were taken from Table B-1 of this Regulatory Guide. For the beta contribution to the skin dose, a semi-infinite cloud model was used. The whole-body gamma dose was evaluated using a finite cloud sector average model with Gaussian activityd 'istribution in the vertical plane. The gamma radiation received at a point of interest from a differential volume of the cloud is calculated. The radiation is then integrated over the entire cloud, taking into account of the geometry of the cloud, variation in concentration, attenuation by the interaction of photons with matter in the path between source and the receptor point, and scattering of radiation from material outside the direct path to the point of interest. An attenuation factor of 0.7 is also applied to the dose calculations to account for the dose reduction due to shielding which would be provided by a residential structure. No additional credit is taken for decay of radionuclides in transit to the receptor point. | ||
-- ,For the third quarter, the skin and whole-body doses from exposure to noble gases at the point of maximum ground level air concentration were calculated to be 0.069 mrem and 0.03 mrem, respectively. For the noble gaseous effluent during the fourth quarter, the skin and whole-body doqes at the point of maximum ground level air concentration were calculated to be 0.049 mrem and 0.022 mram, respectively. | |||
WNW at 2400m and NW at 4000m of the plant stack. The undepleted I/Q's at these locations were calculated to be 4.9 x 10-7 sec/m3 and 4.8 x 10-7 sec/m3 for third and fourth quarters of the year, respectively. | |||
Whole-body and skin doses were calculated at these off-site points as a result of noble gas releases occurring in both quarters. The methodology applied to the dose calculations is consistent with that of Regulatory Guide 1.109(5) for an elevated release point. Dose conversion factors for noble gases and daughters were taken from Table B-1 of this | |||
Regulatory Guide. For the beta contribution to the skin dose, a semi- | |||
infinite cloud model was used. The whole-body gamma dose was evaluated using | |||
a finite cloud sector average model with Gaussian activityd 'istribution in the vertical plane. The gamma radiation received at a point of interest from a differential volume of the cloud is calculated. The radiation is | |||
then integrated over the entire cloud, taking into account of the geometry of the cloud, variation in concentration, attenuation by the interaction of photons with matter in the path between source and the receptor point, and scattering of radiation from material outside the direct path to the point of interest. An attenuation factor of 0.7 is also applied to the dose calculations to account for the dose reduction due to shielding which would be provided by a residential structure. No additional credit is taken for decay of radionuclides in transit to the receptor point. | |||
-- ,For the third quarter, the skin and whole-body doses from exposure | |||
to noble gases at the point of maximum ground level air concentration were calculated to be 0.069 mrem and 0.03 mrem, respectively. For the noble gaseous effluent during the fourth quarter, the skin and whole-body doqes at the point of maximum ground level air concentration were calculated to be 0.049 mrem and 0.022 mram, respectively. | |||
In addition, the maximum nearest resident and site boundary whole-body and skin doses have been calculated due to noble gaseous effluents from the plant stack during the reporting period. The maximum whole-body and skin site boundary doses (both approximately 0.1 mrem) for the third quarter of 1979 occurred in the S sector. 0.24 miles from the stack. The | In addition, the maximum nearest resident and site boundary whole-body and skin doses have been calculated due to noble gaseous effluents from the plant stack during the reporting period. The maximum whole-body and skin site boundary doses (both approximately 0.1 mrem) for the third quarter of 1979 occurred in the S sector. 0.24 miles from the stack. The | ||
, fourth quarter maximum whole-body and skin site boundary doses (both 0.05 arem) occurred in the N sector 0.25 miles from the stack. | , fourth quarter maximum whole-body and skin site boundary doses (both 0.05 arem) occurred in the N sector 0.25 miles from the stack. | ||
In the third quarter, the maximum skin and whole-body dose to the nearest resident (both approximately 0.07 mrem) in any direction was determined to be in the S sector, 0.33 mils. xrom the plant stack. As a result of the fourth quarter meteorology and noble gas effluents, the maximum whole-body and skin dose to the nearest resident (both 0.03 mrem) in any sector occurred to the resident 0.33 miles south of the plant stack. | |||
In the third quarter, the maximum skin and whole-body dose to the nearest resident (both approximately 0.07 mrem) in any direction was determined to be in the S sector, 0.33 mils. xrom the plant stack. As a result of the fourth quarter meteorology and noble gas effluents, the maximum | |||
whole-body and skin dose to the nearest resident (both 0.03 mrem) in any sector occurred to the resident 0.33 miles south of the plant stack. | |||
The resultant doses due to noble gas effluents for the maximum site boundary location, maximum nearest resident, and point of maximum ground level air concentration are tabulated in Table 7. All doses are conservative in that they assume 100 percent occupancy at each point. Whole-body doses consider the gamma radiation received from the effluent plume overhead. | The resultant doses due to noble gas effluents for the maximum site boundary location, maximum nearest resident, and point of maximum ground level air concentration are tabulated in Table 7. All doses are conservative in that they assume 100 percent occupancy at each point. Whole-body doses consider the gamma radiation received from the effluent plume overhead. | ||
The skin doses considers both the beta and gamma contributions at the L | The skin doses considers both the beta and gamma contributions at the L | ||
receptor point. All doses from noble gaseous effluents are well below the | receptor point. All doses from noble gaseous effluents are well below the dose criteria of 10CFR50, Appendix I. | ||
4.3 Organ Doses to Individuals from Radioactive Iodine and Particulates in Caseous Effluents The critical pathway of internal exposure to radioactive iodine and particulates, including tritium, resulting from gaseous effluents for the third quarter is through the grass-milk pathway. It is assumed that milk animals are free to graze on open pasture during the third quarter with no supplemental feeding. This assumption is conservative since most of the milk animals inventoried in the site vicinity are fed stored feed throughout the entire year with only limited grazing allowed during the growing season. | |||
dose criteria of 10CFR50, Appendix I. | |||
4.3 Organ Doses to Individuals from Radioactive Iodine and Particulates in Caseous Effluents | |||
The critical pathway of internal exposure to radioactive iodine and particulates, including tritium, resulting from gaseous effluents for the third quarter is through the grass-milk pathway. It is assumed that milk animals are free to graze on open pasture during the third quarter with no supplemental feeding. This assumption is conservative since most of the milk animals inventoried in the site vicinity are fed stored feed throughout the entire year with only limited grazing allowed during the growing season. | |||
. During the vinter months of the year, the dose commitment through the milk pathway and fresh vegetable ingestion is insignificant. The maximum length of annual growing season is approximately six months long in this part of New England. Therefore, the milk pathway and vegetable ingestion doses for the fourth quarter are the result of activity deposited on feed u | . During the vinter months of the year, the dose commitment through the milk pathway and fresh vegetable ingestion is insignificant. The maximum length of annual growing season is approximately six months long in this part of New England. Therefore, the milk pathway and vegetable ingestion doses for the fourth quarter are the result of activity deposited on feed u | ||
~ "' | ~ "' | ||
. -- ; .. . .~~~~2 . r ......_ T : ~~. *' | . -- ; .. . .~~~~2 . r ......_ T : ~~. *' | ||
~ ~ ~ ' ' | ~ ~ ~ ' ' | ||
and vegetables grown during the growing season and allowed to decay while held in storage. As a result, the critical pathway of exposure for radioactive iodine and particulates during the fourth quarter is through inhalation. | and vegetables grown during the growing season and allowed to decay while held in storage. As a result, the critical pathway of exposure for radioactive iodine and particulates during the fourth quarter is through inhalation. | ||
As a result of the milk and fresh vegetable pathways, the maximum dose for the third quarter from gaseous releases of radioactive iodine and particulates was determined to occur at a farm 3.5 miles south-southeast of the plant. The critical organ was an tufant thyroid with a calculated | As a result of the milk and fresh vegetable pathways, the maximum dose for the third quarter from gaseous releases of radioactive iodine and particulates was determined to occur at a farm 3.5 miles south-southeast of the plant. The critical organ was an tufant thyroid with a calculated | ||
---dose of 0.049 mrem. For the fourth quarter, with inhalation being the principle pathway of exposure, the maximum organ dose was projected to also be at the same farm. The critical organ was a child's thyroid with a calculated dose of 0.0081 mrem. The pathways of exposure which were assuned to exist during the third quat ter at this farm include ground plane exposure, inhalation, fresh home grown vegetables and cow's milk. The pathways of exposure considered at the farm during the fourth quarter include continuous ground plane exposure, inhalation and contributions from stored vegetables and milk. | |||
---dose of 0.049 mrem. For the fourth quarter, with inhalation being the | e Table 7 shows the maximum calculated quarterly organ dose due to the combination of exposures from all pathways which have been identified at the farm. Table 7 also shows the calculated organ doses to the highest exposed nearby res'. dent, and potential organ doses to individuals if a.ssumed | ||
, standing at the highest ground level air concentration point on the site l boundary for the entire six-month reporting period. The site boundary doses include only exposure from inhalation, and direct radiation from the ground plane. The nearest resident is assumed to have a vegetable garden during the growing season which contributes to his or her ingestion dose. For all ground plane exposures, the activity is assumed to accumulate on the ground for 15 years at the rate equivalent to that observed during each quarter. | |||
principle pathway of exposure, the maximum organ dose was projected to also be at the same farm. The critical organ was a child's thyroid with a calculated dose of 0.0081 mrem. The pathways of exposure which were assuned to exist during the third quat ter at this farm include ground plane exposure, inhalation, fresh home grown vegetables and cow's milk. The pathways of exposure considered at the farm during the fourth quarter include continuous ground plane exposure, inhalation and contributions from stored vegetables and milk. | |||
e Table 7 shows the maximum calculated quarterly organ dose due to the combination of exposures from all pathways which have been identified | |||
at the farm. Table 7 also shows the calculated organ doses to the highest exposed nearby res'. dent, and potential organ doses to individuals if a.ssumed | |||
, standing at the highest ground level air concentration point on the site l boundary for the entire six-month reporting period. The site boundary doses | |||
include only exposure from inhalation, and direct radiation from the ground plane. The nearest resident is assumed to have a vegetable garden during the growing season which contributes to his or her ingestion dose. For | |||
all ground plane exposures, the activity is assumed to accumulate on the ground for 15 years at the rate equivalent to that observed during each quarter. | |||
This is a simplified method of approximating the average deposition over the life of the plant. The calculated dose from direct exposure to activity on the ground thus represents the dose an individual would see in each quarter if ,the plant had been operating 15 years. This approach is very conservative, but shows the relative impact the plant would have on the dose consitment over its operating life if the releases were to continue at the levels recorded during this reporting period. | This is a simplified method of approximating the average deposition over the life of the plant. The calculated dose from direct exposure to activity on the ground thus represents the dose an individual would see in each quarter if ,the plant had been operating 15 years. This approach is very conservative, but shows the relative impact the plant would have on the dose consitment over its operating life if the releases were to continue at the levels recorded during this reporting period. | ||
The critical organs for the third and fourth quarters for the nearest resident with the most exposure were the thyroid and bone respectively, | The critical organs for the third and fourth quarters for the nearest resident with the most exposure were the thyroid and bone respectively, and for the maximum site boundary location, was calculated in both cases to be a child's thyroid. The respective doses at these locations for the-third quarter were 1.7 x 10-3 mrem (SSE 1.3 miles) and 2.1 x 10-4 mrem (SSE 0.53 miles). For the fourth quarter both doses were 4.4 x 10-4 mrem. | ||
4.4 Whole-Body Doses in Unrestricted Areas from Direct Radiation The major source of direct radiation (including sky shine) from the station is due to N-16 decay in the turbine building. Because of the orientation of the turbine building on the site, and the shielding effects of the adjacent reactor building, only the seven westerly sectors (SSW - | |||
and for the maximum site boundary location, was calculated in both cases | |||
to be a child's thyroid. The respective doses at these locations for the-third quarter were 1.7 x 10-3 mrem (SSE 1.3 miles) and 2.1 x 10-4 mrem (SSE 0.53 miles). For the fourth quarter both doses were 4.4 x 10-4 mrem. | |||
4.4 Whole-Body Doses in Unrestricted Areas from Direct Radiation | |||
The major source of direct radiation (including sky shine) from the station is due to N-16 decay in the turbine building. Because of the orientation of the turbine building on the site, and the shielding effects of the adjacent reactor building, only the seven westerly sectors (SSW - | |||
NNW) see any significant direct radiation. | NNW) see any significant direct radiation. | ||
High pressure ionization chamber (HPIC) measurements have been made in the plant area in order to estimate the direct radiation from the station. | |||
High pressure ionization chamber (HPIC) measurements have been made | |||
in the plant area in order to estimate the direct radiation from the station. | |||
The chamber was located at a point along the west site boundary which has been determined to receive the maximum direct radiation from the plant. | The chamber was located at a point along the west site boundary which has been determined to receive the maximum direct radiation from the plant. | ||
E | E | ||
~" ~ | ~" ~ | ||
..............-a........ | ..............-a........ | ||
Using measurements of dose rate made while the plant operated at different power levels, from shutdown to 100 percent, the total integrated dose from direct radiation over each three month period was determined by considering the quarterly gross megawatts generated. Field measurements of exposure, in units of Roentgen, where modified by multiplying by 0.6 to obtain whole body dose equivalents, in units of rem, in accordance with recommendations of RASL report 305(6) for radiation fields resulting from N-16 photons. | Using measurements of dose rate made while the plant operated at different power levels, from shutdown to 100 percent, the total integrated dose from direct radiation over each three month period was determined by considering the quarterly gross megawatts generated. Field measurements of exposure, in units of Roentgen, where modified by multiplying by 0.6 to obtain whole body dose equivalents, in units of rem, in accordance with recommendations of RASL report 305(6) for radiation fields resulting from N-16 photons. | ||
Estimates of the population exposure from direct radiation during | Estimates of the population exposure from direct radiation during | ||
. . . the third and fourth quarters have been made out to two miles. Beyond two miles, the dose from the turbine building is negligiole. As a result, the estimated population dose for each of the two quarters respectively was approximately 1.6 x 10-2 and 1.3 x 10-2 person-rem, for a total population of about 351 persons. The estimated direct radiation dose at the maximum, site boundary location was approximately 2.8 mrem for the third quarter of 1979, and 2.3 mrem for the fourth. These hypothetical individual doses assume a 100 percent occupancy factor, taking no credit for the shielding effect of any residential structure. Table 7 summarizes these results. | . . . the third and fourth quarters have been made out to two miles. Beyond two miles, the dose from the turbine building is negligiole. As a result, the estimated population dose for each of the two quarters respectively was approximately 1.6 x 10-2 and 1.3 x 10-2 person-rem, for a total population of about 351 persons. The estimated direct radiation dose at the maximum, site boundary location was approximately 2.8 mrem for the third quarter of 1979, and 2.3 mrem for the fourth. These hypothetical individual doses assume a 100 percent occupancy factor, taking no credit for the shielding effect of any residential structure. Table 7 summarizes these results. | ||
4.5 Whole-Body Doses to the General Population from all Receiving Water Related Pathways Using the liquid pathway whole-body dose model discussed in Section 4.1, an estimate of the population dose due to the third quarter liquid t | |||
4.5 Whole-Body Doses to the General Population from all Receiving Water Related Pathways Using the liquid pathway whole-body dose model discussed in Section 4.1, an estimate of the population dose due to the third quarter liquid | . batch release has been calculated. The dose per kilogram of fish ingested at the site of the maximum individual (see Section 4.1) was assumed to apply to the entire yield of fish within fifty air miles of the plant. No credit was taken for radionuclide loss by sedimentation or further dilution by | ||
t | |||
. batch release has been calculated. The dose per kilogram of fish ingested | |||
at the site of the maximum individual (see Section 4.1) was assumed to apply to the entire yield of fish within fifty air miles of the plant. No credit was taken for radionuclide loss by sedimentation or further dilution by | |||
- - - - -- _ . . . . . . . . - ~ . . . . - . .. . _ . . . . . ._ | - - - - -- _ . . . . . . . . - ~ . . . . - . .. . _ . . . . . ._ | ||
4 tributaries below Vernon Dam nor for the biological removal and decay of activity in the fish during the time periods when no radioactivity was being discharged from the plant. | 4 tributaries below Vernon Dam nor for the biological removal and decay of activity in the fish during the time periods when no radioactivity was being discharged from the plant. | ||
A 1975 creel census of the Deerfield River, which is a stocked tributary of the Connecticut River downstream of the plant, reported an annual average catch of 431 fish per river mile in a 28 week season. The average weight of these fish was conservatively estimated to be equivalent to one pound of edible flesh. Assuming that there are 100 downstream river | A 1975 creel census of the Deerfield River, which is a stocked tributary of the Connecticut River downstream of the plant, reported an annual average catch of 431 fish per river mile in a 28 week season. The average weight of these fish was conservatively estimated to be equivalent to one pound of edible flesh. Assuming that there are 100 downstream river | ||
~ ~~ | ~ ~~ | ||
miles within 50 miles of the plant, the yearly yield of edible fish mass in the Connecticut River may be estimated as: | |||
miles within 50 miles of the plant, the yearly yield of edible fish mass | |||
in the Connecticut River may be estimated as: | |||
431 fish / mile x 52 weeks x 1 lb. x 0.453 Kg x 100 miles 28 weeks year fish lb. | 431 fish / mile x 52 weeks x 1 lb. x 0.453 Kg x 100 miles 28 weeks year fish lb. | ||
- 3.6 x 104 Kg/ year ' | - 3.6 x 104 Kg/ year ' | ||
Fishing activity is greater on the Deerfield River than on the Connecticut River because the stocked fish attract more sport fishing activity. If it is assumed that one-half of the annual fish catch is caught and con need in the quarter, the resulting calculation yields a quarterly population dose commitment of 3.5 x 10-3 person-rem for a population made up of adults (62.6 percent), teenagers (11.9 percent) and children (23.7 percent). | |||
Fishing activity is greater on the Deerfield River than on the Connecticut River because the stocked fish attract more sport fishing activity. If it is assumed that one-half of the annual fish catch is caught and con need in the quarter, the resulting calculation yields a quarterly population dose commitment of 3.5 x 10-3 person-rem for a population made | |||
. | |||
m | m | ||
- - . . ~ . . | - - . . ~ . . | ||
4.6 | 4.6 | ||
_ Doses to the General Population and Average Individual Within Fif ty Miles from Caseous Effluents Using site meteorological data in Tables 4 and 5, quarterly average I/Q values were determined for each sector formed by placing radial rings from the plant at distances of one, two, three, four, five, ten, twenty, thirty, forty and fifty miles, and their intersection with radial lines drawn to form each of the sixteen principal compass directions. For noble gases, whole-body and skin doses were calculated for each sector and | _ Doses to the General Population and Average Individual Within Fif ty Miles from Caseous Effluents Using site meteorological data in Tables 4 and 5, quarterly average I/Q values were determined for each sector formed by placing radial rings from the plant at distances of one, two, three, four, five, ten, twenty, thirty, forty and fifty miles, and their intersection with radial lines drawn to form each of the sixteen principal compass directions. For noble gases, whole-body and skin doses were calculated for each sector and | ||
.. multiplied by the estimated population within each sector to determine the | .. multiplied by the estimated population within each sector to determine the sector person-rem. | ||
sector person-rem. | |||
No credit for decay in transit of activity was assumed. | No credit for decay in transit of activity was assumed. | ||
For the approximately 1.1 x 106 people within fifty miles of the plant, the third and fourth quarter whole-body doses from noble gas cloud ~ | For the approximately 1.1 x 106 people within fifty miles of the plant, the third and fourth quarter whole-body doses from noble gas cloud ~ | ||
exposure were estimated to be 1.3 person-rem and 0.5 person-rem, respectively. | exposure were estimated to be 1.3 person-rem and 0.5 person-rem, respectively. | ||
For the same two quarters, the average individual whole-body doses were 1.1 x 10-3 mrem and 4.5 x 10-4 mrem, respectively. The skin doses for the two quarters were 2.1 person-rem and 0.95 person-rem, respectively. | For the same two quarters, the average individual whole-body doses were 1.1 x 10-3 mrem and 4.5 x 10-4 mrem, respectively. The skin doses for the two quarters were 2.1 person-rem and 0.95 person-rem, respectively. | ||
The average individual skin dose was 1.8 x 10-3 and 8.2 x 10-4 mrem for the third and fourth quarters. | The average individual skin dose was 1.8 x 10-3 and 8.2 x 10-4 mrem for the third and fourth quarters. | ||
Table 7 also indicates the population whole-body and thyroid dose connitments from radioactive iodine and particulates (including tritium) released from the plant in gaseous vaste. The pathways of exposure which | Table 7 also indicates the population whole-body and thyroid dose connitments from radioactive iodine and particulates (including tritium) released from the plant in gaseous vaste. The pathways of exposure which | ||
, have been considered for the 50 mile population include inhalation, ingestion of vegetables, milk and meat produced within 50 miles, and the direct exposure to activity deposited on the ground plane. The total whole-body andthyroiddosecommitmentsforthethirdquarterverecalcukatedtobe | , have been considered for the 50 mile population include inhalation, ingestion of vegetables, milk and meat produced within 50 miles, and the direct exposure to activity deposited on the ground plane. The total whole-body andthyroiddosecommitmentsforthethirdquarterverecalcukatedtobe 9 | ||
9 | |||
+ . .- . .. ..... | + . .- . .. ..... | ||
l.1 x 10-2 person-rem and 6.3 x 10-2 person-rem respectively. For the fourth quarter, these doses were 9.4 x 10-2 person-rem and 0.11 person-rem respectively. | l.1 x 10-2 person-rem and 6.3 x 10-2 person-rem respectively. For the fourth quarter, these doses were 9.4 x 10-2 person-rem and 0.11 person-rem respectively. | ||
e e | e e | ||
g e | g e | ||
4 | 4 9 | ||
e f | |||
f | |||
^~ ~ | ^~ ~ | ||
-- ~ . ~ . ~ . ' . - --. . '.: ~.~.:. ~... ... ...... .. - . . . | -- ~ . ~ . ~ . ' . - --. . '.: ~.~.:. ~... ... ...... .. - . . . | ||
REFERENCES | REFERENCES | ||
: 1. Regulatory Guide 1.111. "Hethods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light- | : 1. Regulatory Guide 1.111. "Hethods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light- | ||
~ | ~ | ||
Line 400: | Line 156: | ||
NUREG-0473, " Radiological Effluent Technical Specifications for Ei'9.'s", | NUREG-0473, " Radiological Effluent Technical Specifications for Ei'9.'s", | ||
Revision 2, July 1979; Table 4.11-1, notation f. | Revision 2, July 1979; Table 4.11-1, notation f. | ||
B e | |||
B | 1 TABLE lA VERMONT YANKEE EFFLQENT AND WASTE DISPOSAL SEMI ANNUAL REPORT JULY - DECEMBER 1979 CASE 0US EFFULENTS - SUMMATION OF ALL RELEASES Unit Quarter Quarter Est. Total 3 4 Error, % | ||
TABLE lA VERMONT YANKEE EFFLQENT AND WASTE DISPOSAL SEMI ANNUAL REPORT | |||
JULY - DECEMBER 1979 CASE 0US EFFULENTS - SUMMATION OF ALL RELEASES | |||
Unit Quarter Quarter Est. Total 3 4 Error, % | |||
A. Fission & activation gases k- | A. Fission & activation gases k- | ||
'~~ | '~~ | ||
1.''Totai Eelease" Ci | |||
1.''Totai Eelease" | |||
Ci | |||
: 2. Average release rate for period <7.91E2 <7.78E2 1.0 E2 3. | : 2. Average release rate for period <7.91E2 <7.78E2 1.0 E2 3. | ||
uCi/sec <1.01E2 <9.89El Percent of technical specification limil % <1.24E-1 <8.47E-2 | uCi/sec <1.01E2 <9.89El Percent of technical specification limil % <1.24E-1 <8.47E-2 B. Iodines | ||
B. Iodines | |||
%n | %n | ||
~ | ~ | ||
: 1. Total iodine - 131 Ci 3.16E-3 | : 1. Total iodine - 131 Ci 3.16E-3 | ||
Line 442: | Line 171: | ||
: 2. 1.52E-2 5.0 El i Averaee release rate for oeriod uCi/sec 1. 76E-4 5.25E-4 j 3. Percent of technical specification limit | : 2. 1.52E-2 5.0 El i Averaee release rate for oeriod uCi/sec 1. 76E-4 5.25E-4 j 3. Percent of technical specification limit | ||
, 4 Cross alpha radioactivity | , 4 Cross alpha radioactivity | ||
% 1.29E-2 8.54E-2 C1 1.71E-7 1.87E-7 D. Tritium | % 1.29E-2 8.54E-2 C1 1.71E-7 1.87E-7 D. Tritium f | ||
f | |||
: 1. Total release Ci 7.60E0 2.56E0 I 5.0 | : 1. Total release Ci 7.60E0 2.56E0 I 5.0 | ||
. 2. Average release rate for period E1 I uCi/sec 9.66E-1 3.25E-1 | . 2. Average release rate for period E1 I uCi/sec 9.66E-1 3.25E-1 | ||
: 3. Percent of technical specification limit % N.A. | : 3. Percent of technical specification limit % N.A. | ||
N.A. | N.A. | ||
) | ) | ||
e 8 | |||
e | 8 | ||
8 | |||
- - - ' ~ | - - - ' ~ | ||
TABLE IB EFFLUENT AND WASTE DISPOSAL SEMIANNUAL JULY - DECDiBER 1979 GASEOUS EFFLUENTS - ELEVATED RELEASE E CONTINUOUS MODE BATCH MODE *(2) | |||
TABLE IB | |||
E CONTINUOUS MODE BATCH MODE *(2) | |||
Nuclides Released t u Unit Quarter 3 | Nuclides Released t u Unit Quarter 3 | ||
Quarter Quarter 3 | Quarter Quarter 3 | ||
Line 485: | Line 189: | ||
krypton-85 - ~~ | krypton-85 - ~~ | ||
) | ) | ||
l krypton-85m Ci - * (l) | l krypton-85m Ci - * (l) | ||
I I | I I | ||
Line 492: | Line 195: | ||
xenon-133 <1.03El E Ci <8.29E0 E xenon-135 <7.78E1 E _ | xenon-133 <1.03El E Ci <8.29E0 E xenon-135 <7.78E1 E _ | ||
Ci <2.85E2 E xenon-135m <2.21El <1.60El E E | Ci <2.85E2 E xenon-135m <2.21El <1.60El E E | ||
xenon-138 Ci <l.30E2 <9.67El E_ _ E | xenon-138 Ci <l.30E2 <9.67El E_ _ E | ||
_Ci <5.33E2 Others (specify) ~ Ci- <3.58E2 E _ | _Ci <5.33E2 Others (specify) ~ Ci- <3.58E2 E _ | ||
E | E E E Ci E E l E E Ci E E unidentified Ci E E E | ||
E i | |||
E E Ci E E l E E Ci E E unidentified Ci E E E | Tota {for period E E E | ||
E | |||
l Ci E E ] | l Ci E E ] | ||
i | i | ||
<7.91 E2 { <7.78E2 | <7.91 E2 { <7.78E2 E | ||
E | |||
: 2. Iodines l E < | : 2. Iodines l E < | ||
E t | E t | ||
Line 514: | Line 211: | ||
E 3 Ci i 1.09E-2 E l | E 3 Ci i 1.09E-2 E l | ||
1.33E-2 E | 1.33E-2 E | ||
: 3. Part.'culates | : 3. Part.'culates E 1 E 1 3 | ||
st ron tiem-89 ; | |||
E 1 E 1 | |||
i Ci 5.01E-5 | i Ci 5.01E-5 | ||
\ | \ | ||
Line 525: | Line 218: | ||
\ | \ | ||
1 cesium-li4 2.18E-6 1.32E-6 E | 1 cesium-li4 2.18E-6 1.32E-6 E | ||
E | E cesium-137- Ci 2.54E-4 E Ci 3.91E-4 E | ||
cesium-137- Ci 2.54E-4 E Ci 3.91E-4 E | |||
- barium-lanthanum-140 2.15E-4 6.65E-4 E | - barium-lanthanum-140 2.15E-4 6.65E-4 E | ||
E cobalt-58 Ci 3.46E-4 E 1.29E-4 _ _ E | E cobalt-58 Ci 3.46E-4 E 1.29E-4 _ _ E cobalt-60 _ | ||
cobalt-60 _ | |||
Ci 2.23E-3 8.39E-4 E | Ci 2.23E-3 8.39E-4 E | ||
E ' | E ' | ||
Line 541: | Line 230: | ||
releasnot detected in offgas y = 6.79E-7 mix-limit uCi/cc of detecta | releasnot detected in offgas y = 6.79E-7 mix-limit uCi/cc of detecta | ||
,.-7-----, ,__ ,__;___,_,_, | ,.-7-----, ,__ ,__;___,_,_, | ||
TABLE IC VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT - 197 JULY - DECEMBER CASEOUS EFFLUENTS - ROUTINE CROUND LEVEL RELEASES | |||
* There were no routine measured ground level continous, or batch mode gaseous effluent releases during the reporting period. - | |||
TABLE IC VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT - 197 JULY - DECEMBER CASEOUS EFFLUENTS - ROUTINE CROUND LEVEL RELEASES | |||
* There were no routine measured ground level continous, or batch mode | |||
gaseous effluent releases during the reporting period. - | |||
J e | J e | ||
O e | O e | ||
t | t | ||
TABLE ID | TABLE ID | ||
* VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT - 1979 JULY - DECEBER GASEOUS EFFLUENTS - NON-ROUTINE RELEASES | * VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT - 1979 JULY - DECEBER GASEOUS EFFLUENTS - NON-ROUTINE RELEASES | ||
* There were no non-routine or accidental gaseous effluents releases. | * There were no non-routine or accidental gaseous effluents releases. | ||
during the reporting period. | during the reporting period. | ||
t 8 | |||
I t | |||
t | |||
t | |||
t o | t o | ||
TABLE 2A EFFLUEhT AND WASTE DISPOSAL SEMIANNUAL REPORT JULY - DECEMBER 1979 | |||
. LIQUID EFFLUENTS - SU5MATION OF ALL RELEASES Unit Quarter Quarter 3 | |||
TABLE 2A | |||
EFFLUEhT AND WASTE DISPOSAL SEMIANNUAL REPORT | |||
JULY - DECEMBER 1979 | |||
. LIQUID EFFLUENTS - SU5MATION OF ALL RELEASES | |||
Unit Quarter Quarter 3 | |||
Est. Total 4 *1 Error, 't. | Est. Total 4 *1 Error, 't. | ||
A. Fission and activation products | A. Fission and activation products | ||
: 1. Total relecse (not including tritium, gases, alpha) | : 1. Total relecse (not including tritium, gases, alpha) | ||
Ci 2.40E-4 | Ci 2.40E-4 | ||
Line 618: | Line 254: | ||
: 1. Total release | : 1. Total release | ||
._ Ci 4.04E0 | ._ Ci 4.04E0 | ||
: 2. Average diluted concentration during 5.0El | : 2. Average diluted concentration during 5.0El period | ||
period | |||
: 3. Percent of applicable limit VCi/mi 4.16E-6 | : 3. Percent of applicable limit VCi/mi 4.16E-6 | ||
% 1.38E-1 C. Dissolved and entrained gases | % 1.38E-1 C. Dissolved and entrained gases | ||
: 1. Total release C1 1.06E-1 | : 1. Total release C1 1.06E-1 | ||
: 2. Average period diluted concentration during i5.0El | : 2. Average period diluted concentration during i5.0El | ||
: 3. Percent of applicable limit UCi/ml 1.62E-7 | : 3. Percent of applicable limit UCi/ml 1.62E-7 4.05E-1 D. Gross alpha radioactivity | ||
4.05E-1 D. Gross alpha radioactivity | |||
: 1. Total relt ase ' | : 1. Total relt ase ' | ||
Ci *2 t5.0El | Ci *2 t5.0El E. Volume of waste released (prior to dilution) liters I A1.0 El F. Volume of dilution water used during period liters | ||
E. Volume of waste released (prior to dilution) liters | |||
I A1.0 El | |||
F. Volume of dilution water used during period liters | |||
*1 . | *1 . | ||
No Liquid Effluents for 4th Quarter 1979 - | No Liquid Effluents for 4th Quarter 1979 - | ||
*2 No alpha detected, Minimum sensitivity - <9.00x10~II uci/ml o | *2 No alpha detected, Minimum sensitivity - <9.00x10~II uci/ml o | ||
TABLE 2B EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT JULY - DECDGER 1979 LIQUID EFFLUENTS - | TABLE 2B EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT JULY - DECDGER 1979 LIQUID EFFLUENTS - | ||
5 CONTINUOUS MODE *1 BATCH MODE *2 Nuclide., Released Unit Quarter Quarter Quarter Quarter 3rd 4th 3rd. 4th strontium-89 Ci <4.84E-6 strontium-90 Ci 2.71E-6 | 5 CONTINUOUS MODE *1 BATCH MODE *2 Nuclide., Released Unit Quarter Quarter Quarter Quarter 3rd 4th 3rd. 4th strontium-89 Ci <4.84E-6 strontium-90 Ci 2.71E-6 | ||
, cesium-134 Ci <8.62E-6 cesium-137 C1 <1.08E-5 iodine-131 Ci <6.68E-6 cobalt-58 Ci <1.10E-5 cobalt-60 Ci <1.54E-5 iron-59 Ci <2.58E-5 zine-65 Ci <2.89E-5 | , cesium-134 Ci <8.62E-6 cesium-137 C1 <1.08E-5 iodine-131 Ci <6.68E-6 cobalt-58 Ci <1.10E-5 cobalt-60 Ci <1.54E-5 iron-59 Ci <2.58E-5 zine-65 Ci <2.89E-5 manganese-54 Ci 5.85E-5 chromium-51 Ci <5.03E-5 zirconium-niobium-95 Ci <2.27E-5 molyb<lenum-99 Ci <2.90E-6 technetium-99m Ci <3.09E-6 barium-Janthanum-140 Ci <3.21E-5 cerium-141 Ci <5.66E-6 9 | ||
manganese-54 Ci 5.85E-5 chromium-51 Ci <5.03E-5 zirconium-niobium-95 Ci <2.27E-5 molyb<lenum-99 Ci <2.90E-6 technetium-99m Ci <3.09E-6 barium-Janthanum-140 Ci <3.21E-5 cerium-141 Ci <5.66E-6 9 | |||
Other (specify) Ci Ci Ci Ci Ci unidentified Ci i | Other (specify) Ci Ci Ci Ci Ci unidentified Ci i | ||
Total for period (above) Ci e | |||
<2.90E-4 | <2.90E-4 xenon-133 Ci 2.92E-2 xenon-135 ' | ||
xenon-133 Ci 2.92E-2 | |||
xenon-135 ' | |||
Ci 7.64E-2 | Ci 7.64E-2 | ||
*1 No continuous mode releases. | *1 No continuous mode releases. | ||
*2 No 4th Quarter batch releases. | *2 No 4th Quarter batch releases. | ||
.-.------..~.--..--.-. -. | .-.------..~.--..--.-. -. | ||
TABLE 3 EFFLUENT AND WASTE DISPOSAL SE!!IANNUAL REPORT JULY - DECEMBER 1979 SOLID WASTE AND IRRADIATED FUEL SHIPMENTS A. bOLID h'ASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSA | |||
: 1. Type of waste Unit 6-month Est. Total Period Error, % , | |||
TABLE 3 EFFLUENT AND WASTE DISPOSAL SE!!IANNUAL REPORT | |||
: 1. Type of waste Unit 6-month Est. Total | |||
Period Error, % , | |||
: a. Spent resins, filter sludges, evaporator m3 3.59El bottoms, etc. Ci + 7.5El 7.01E2 - | : a. Spent resins, filter sludges, evaporator m3 3.59El bottoms, etc. Ci + 7.5El 7.01E2 - | ||
: b. Dry compressible waste, contaminated m3 1. 72El | : b. Dry compressible waste, contaminated m3 1. 72El | ||
, equip, etc. Ci | , equip, etc. Ci | ||
+ 7.5El | + 7.5El 1.87E0 - | ||
1.87E0 - | |||
: c. Irradiated components, control m3 0 rods, etc. | : c. Irradiated components, control m3 0 rods, etc. | ||
Ci 0 mb 0 | Ci 0 mb 0 | ||
: d. Other (describe) Ci 0 | : d. Other (describe) Ci 0 | ||
: 2. Estimate of major nuclide composition (by type of waste) | : 2. Estimate of major nuclide composition (by type of waste) | ||
: a. Ce-141 % 4.69E-2 I.131 % 1.04E-1 Cs-134 % 2.90E+1 Ba-140 % 5.18E-1 | : a. Ce-141 % 4.69E-2 I.131 % 1.04E-1 Cs-134 % 2.90E+1 Ba-140 % 5.18E-1 Cs-137 % 5.llE+1 .Cr-51 % 4.51E-2 Co-58 % 7.31E-1 Zr-95 % 1.27E-2 Mn-54 % 2.67E-1 ' I-134 Zn-65 | ||
Cs-137 % 5.llE+1 .Cr-51 % 4.51E-2 Co-58 % 7.31E-1 Zr-95 % 1.27E-2 Mn-54 % 2.67E-1 ' I-134 Zn-65 | |||
% 5.71E-3 | % 5.71E-3 | ||
% 1.21E-1 Mn-56 % 5.50E-3 Co-60 % 1.71E+1 i r,-110 % 1.54E-3 | % 1.21E-1 Mn-56 % 5.50E-3 Co-60 % 1.71E+1 i r,-110 % 1.54E-3 | ||
: b. Cs-134 % 2.31E+1 ' | : b. Cs-134 % 2.31E+1 ' | ||
Mn-54 % | Mn-54 % | ||
Line 703: | Line 294: | ||
% 4.08E+1 Zn-65 % 8.38E0 Co-58 9.80E-1 | % 4.08E+1 Zn-65 % 8.38E0 Co-58 9.80E-1 | ||
' % Co-60 % 2.43E+1 | ' % Co-60 % 2.43E+1 | ||
: c. % % | : c. % % | ||
: d. g g | : d. g g | ||
: 3. Solid Waste Dispo'ition s | : 3. Solid Waste Dispo'ition s | ||
, Number of Shipments Mode of Transportation Destination - | , Number of Shipments Mode of Transportation Destination - | ||
9 Truck Chem-Nuclear | 9 Truck Chem-Nuclear | ||
, Barnwell, South Carolina B. IRRADIATED FUEL SHIPMENTS (Disposition) | |||
, Barnwell, South Carolina | |||
B. IRRADIATED FUEL SHIPMENTS (Disposition) | |||
Number of Shipments Mode of Transportation | Number of Shipments Mode of Transportation | ||
* Destination None | * Destination None a | ||
a | |||
_ _ _ . , . . _ . . . _ . . - . - - - - ~ - - - - - - - - - | _ _ _ . , . . _ . . . _ . . - . - - - - ~ - - - - - - - - - | ||
o, _ _ ,,. . _ _. .. . -. ..s - - - - - - - | o, _ _ ,,. . _ _. .. . -. ..s - - - - - - - | ||
. - .= a- . . . . .. . . . - - . - . - + + - - - - - - - - - ~ ~ * | . - .= a- . . . . .. . . . - - . - . - + + - - - - - - - - - ~ ~ | ||
* l \ . I yg%]r g wu nll t I C_I J 000 NOO NOO N>m @# 4 e OO NGO OOO MOO | |||
l \ . I | |||
yg%]r g wu nll t I C_I J 000 NOO NOO N>m @# 4 e OO NGO OOO MOO | |||
= e e | = e e | ||
>= km ame MN km OO NQw e o ee e e e e e o u OO O O N = O e e o e | >= km ame MN km OO NQw e o ee e e e e e o u OO O O N = O e e o e | ||
Line 743: | Line 317: | ||
2 OOO DOD 000 OOO OOO a a 90 OO OOO OOO OOD w 90 90 OO DO | 2 OOO DOD 000 OOO OOO a a 90 OO OOO OOO OOD w 90 90 OO DO | ||
-- --' ~* e e e e o e -e DO OO J | -- --' ~* e e e e o e -e DO OO J | ||
*= e 4 e e o e e e e OO OO 90 OO w 99 90 OO DO O 4 w w a OuO OOO 900 ooc W e Oh OOO OOO 900 000 & | |||
*= e 4 e e o e e e e OO OO 90 OO | |||
w 99 90 OO DO O | |||
90 OO 90 OO DO 3 3 e e o e o e OO DO e w e e e e e o e o e a OO CD OO DO DO DO 90 OO O | 90 OO 90 OO DO 3 3 e e o e o e OO DO e w e e e e e o e o e a OO CD OO DO DO DO 90 OO O | ||
" d m A OOO m e > 900 OOD 000 000 ODO OOO m OO 90 OO OO 900 A h u e e OO DO OO 90 w o e e e e e e e e e E # DO 09 e o e e W w OO DO DO SO 90 | " d m A OOO m e > 900 OOD 000 000 ODO OOO m OO 90 OO OO 900 A h u e e OO DO OO 90 w o e e e e e e e e e E # DO 09 e o e e W w OO DO DO SO 90 | ||
* OO & | * OO & | ||
a 3 x 'd O o a 900 000 000 000 OOO n 8 w R e OO OO DO DO OOO 900 000 u E m e e e OO OO OO DO e e e o e e o e o e e | a 3 x 'd O o a 900 000 000 000 OOO n 8 w R e OO OO DO DO OOO 900 000 u E m e e e OO OO OO DO e e e o e e o e o e e 4 s De OO e e e e 5 | ||
> 2 9e OO DO 90 OO 0 | > 2 9e OO DO 90 OO 0 | ||
J G 99 u 4 D 3 e m e OOO 900 OOD 7 4 > OO Mem OOO OOO 000 Mee M w 99 OO C= OO OO J u e e e e e e OO Om a u w OO DO OO M e e e o e e e e e e m e a = | J G 99 u 4 D 3 e m e OOO 900 OOD 7 4 > OO Mem OOO OOO 000 Mee M w 99 OO C= OO OO J u e e e e e e OO Om a u w OO DO OO M e e e o e e e e e e m e a = | ||
90 OO GO M 4 " = | 90 OO GO M 4 " = | ||
g J W | g J W | ||
O w ece OOO COO eeOM = mem | O w ece OOO COO eeOM = mem e CO CO OO MO OOO OO OOO mna - | ||
e CO CO OO MO OOO OO OOO mna - | |||
Q e o e ee e e e e CO WM w 2 OO OO 90 o e e e e e o e J = 4 O 90 OO O 3 M M a w 000 mem OOO 900 e e 99 Me 99 000 OOO OOO -me s OO DO me 90 | Q e o e ee e e e e CO WM w 2 OO OO 90 o e e e e e o e J = 4 O 90 OO O 3 M M a w 000 mem OOO 900 e e 99 Me 99 000 OOO OOO -me s OO DO me 90 | ||
^ | ^ | ||
Line 765: | Line 332: | ||
De e OO Oc 99 OO e e e e o Oc O wm O 4 UE 2 m OOO OOO NGO m@M OOO ew Q O O DO OO >= MG 900 000 MW@ && | De e OO Oc 99 OO e e e e o Oc O wm O 4 UE 2 m OOO OOO NGO m@M OOO ew Q O O DO OO >= MG 900 000 MW@ && | ||
m a w e e DO CO OO em | m a w e e DO CO OO em | ||
> e e e e e o e o e e e e 4 GD OO O W e e De | > e e e e e o e o e e e e 4 GD OO O W e e De | ||
* 3 J OO 00 CO M mm m 21 m W O > | * 3 J OO 00 CO M mm m 21 m W O > | ||
909 mmm OOO OOO 900 OOO OOO mMr | 909 mmm OOO OOO 900 OOO OOO mMr | ||
*E G or 7 CC &C -EE | *E G or 7 CC &C -EE | ||
> e e e e o e +G C *C*C pac 3S e > e e o e e e e e e e yo so O Oc OO EC OC Oc d e am u" | > e e e e o e +G C *C*C pac 3S e > e e o e e e e e e e yo so O Oc OO EC OC Oc d e am u" | ||
w | w | ||
, O OOO OOO DO 900 me | , O OOO OOO DO 900 me | ||
> e 4 OO 000 000 000 -9 9 9 dd u > 99 OO 99 OO w e e e e e * * * | > e 4 OO 000 000 000 -9 9 9 dd u > 99 OO 99 OO w e e e e e * * * | ||
Line 780: | Line 344: | ||
* SO OO 90 OO 09 OO ** | * SO OO 90 OO 09 OO ** | ||
3 == | 3 == | ||
* O w OOO OO e OOO OOO OOO mm | * O w OOO OO e OOO OOO OOO mm w & OO OO DOS 300 OOO Em E 99 OO OO DO | ||
w & OO OO DOS 300 OOO Em E 99 OO OO DO | |||
. o * | . o * | ||
* e e e e e o e 90 OO ww m OO OO DO DO e e o e e | * e e e e e o e 90 OO ww m OO OO DO DO e e o e e | ||
* e9 DO 09 OO Oe OO | * e9 DO 09 OO Oe OO | ||
. , > QQ | . , > QQ | ||
} d m | } d m | ||
w OOO OsO 900 000 OOO OOO | w OOO OsO 900 000 OOO OOO 4 99 OO DO DO DOS 900 00 O e 2 * * * | ||
4 99 OO DO DO DOS 900 00 O e 2 * * * | |||
* 90 99 OO DO uu | * 90 99 OO DO uu | ||
* * * * | * * * * | ||
Line 797: | Line 356: | ||
. | . | ||
* OO OO 09 OO uw e w O | * OO OO 09 OO uw e w O | ||
** w 2 OOO OOO DOS =FF JJ a O DO DO OOO OOO 900 | ** w 2 OOO OOO DOS =FF JJ a O DO DO OOO OOO 900 mee JJ g 90 MO 99 @@ | ||
mee JJ g 90 MO 99 @@ | |||
g e e e e e e e | g e e e e e e e | ||
* DO Me == | * DO Me == | ||
Line 808: | Line 365: | ||
* m W F G & WW N w e EE w e5 a J mm O J m et g ww | * m W F G & WW N w e EE w e5 a J mm O J m et g ww | ||
. g | . g g~++---.----._.. ._ _ . . , , ,__ | ||
g~++---.----._.. ._ _ . . , , ,__ | |||
*========*-e. .= =. . . . . . . . ~~ ~~ ~ ~ ~-~. . ._..._.m. . . . . . _ | *========*-e. .= =. . . . . . . . ~~ ~~ ~ ~ ~-~. . ._..._.m. . . . . . _ | ||
r 3 | r 3 | ||
-m'N i I'l | -m'N i I'l | ||
* vgo 1 | * vgo 1 | ||
Gy/r] ,t-y n'et O.,_ O__ e,_ O 4t. . O s. DOO 50 J 9.O oM OO 54m cO | Gy/r] ,t-y n'et O.,_ O__ e,_ O 4t. . O s. DOO 50 J 9.O oM OO 54m cO 88 GG ** m art fis e O f%d e a m | ||
88 GG ** m art fis e O f%d e a m | |||
* m as e e o e e e a= o e e e e e o e e e s'm M e se O == em O OO O s=t eJ OO O E e= == 840 m ft$ | * m as e e o e e e a= o e e e e e o e e e s'm M e se O == em O OO O s=t eJ OO O E e= == 840 m ft$ | ||
se 13. | se 13. | ||
E OOO OSo OOO O Ooo OOO 3aO onO DoO co e m | E OOO OSo OOO O Ooo OOO 3aO onO DoO co e m | ||
e OO 09 oO oO Oo 99 oo e e e e e e e e e o e *e e e e 3 e e Oo OO co DO DO DO Oo DO | e OO 09 oO oO Oo 99 oo e e e e e e e e e o e *e e e e 3 e e Oo OO co DO DO DO Oo DO O | ||
4 o =e OOo == c a == | |||
s oat O fts > O emO 4 S == m o art 2 th O e* m #%s om O == OM OO fts O O e e J r e e e e e e e s e o e o E O Er' e O OO O == as | s oat O fts > O emO 4 S == m o art 2 th O e* m #%s om O == OM OO fts O O e e J r e e e e e e e s e o e o E O Er' e O OO O == as | ||
&O sts We f%8 3 O | &O sts We f%8 3 O | ||
Line 829: | Line 381: | ||
ooo OOO Omo OOo as er a OOO Ooo OOo OOO OO OO OO OO OO Z O A OO OO OO o e o e == | ooo OOO Omo OOo as er a OOO Ooo OOo OOO OO OO OO OO OO Z O A OO OO OO o e o e == | ||
e e e e e e o e o e e e e A OO DO DO Oo GF't OO DO OO OO e9 | e e e e e e o e o e e e e A OO DO DO Oo GF't OO DO OO OO e9 | ||
* em OOO OOO OOD OOO OoO 90O OOO tad E OOO OO OO .,6 OO OO OO Oo OO DO E o e e e e o e o e e e e e e e e | * em OOO OOO OOD OOO OoO 90O OOO tad E OOO OO OO .,6 OO OO OO Oo OO DO E o e e e e o e o e e e e e e e e OO OO en De -OO 90 Oo O aam De ** | ||
OO OO en De -OO 90 Oo O aam De ** | |||
* - -- - . . . . . . . . .. .y ** | * - -- - . . . . . . . . .. .y ** | ||
d OOO OOo OOO OOo eOO OOO EL taa A .O O O OOO DO 99 Oo es es Oo Do OO DO 'OO U e e e o e o e o e e e e e e a 2 e o OO OO DO OO 90 GC OO L3 ma OO # | d OOO OOo OOO OOo eOO OOO EL taa A .O O O OOO DO 99 Oo es es Oo Do OO DO 'OO U e e e o e o e o e e e e e e a 2 e o OO OO DO OO 90 GC OO L3 ma OO # | ||
Line 844: | Line 394: | ||
> 2 op O g | > 2 op O g | ||
E 3 | E 3 | ||
=s as | =s as an e= | ||
* *** OO | * *** OO | ||
*** DO | *** DO | ||
Line 868: | Line 416: | ||
*= es eO ens e OO OO OO OO ses en KL 3 J oe= e= | *= es eO ens e OO OO OO OO ses en KL 3 J oe= e= | ||
O U Oeo eOO Oco OOO en est es ee ena eOO == sst are OOO a > es s ya e ee c.c s=c es c es s se c ea e o e o e e e e o e e o e e e e UQ o= >= Oc eO *eO e= a, en O en sO == 0C sO o* J en en G ** | O U Oeo eOO Oco OOO en est es ee ena eOO == sst are OOO a > es s ya e ee c.c s=c es c es s se c ea e o e o e e e e o e e o e e e e UQ o= >= Oc eO *eO e= a, en O en sO == 0C sO o* J en en G ** | ||
e9o OOe OOO O O se sua o et 44 | e9o OOe OOO O O se sua o et 44 se sa OOO ae sse et fis r= O oO eO eO O en uu | ||
se sa OOO ae sse et fis r= O oO eO eO O en uu | |||
> as 4 OO set O e == OO e e e e e e * * * * * * | > as 4 OO set O e == OO e e e e e e * * * * * * | ||
* e e e == o o u e= ans | * e e e == o o u e= ans | ||
== su 9O OO OO OO e o= == | == su 9O OO OO OO e o= == | ||
a en O sa ** | a en O sa ** | ||
w >b 3 OOO OOO OoO OOO sts em o sz a E.D ena OOO == m afs == m art e == | w >b 3 OOO OOO OoO OOO sts em o sz a E.D ena OOO == m afs == m art e == | ||
o aan & OO me mo aO o e OO o e 90 o e Oe e e e e tan ame ee ns a e e o e e e pu | o aan & OO me mo aO o e OO o e 90 o e Oe e e e e tan ame ee ns a e e o e e e pu | ||
== == OO OO OO OO er a an. OO QQ | == == OO OO OO OO er a an. OO QQ p= O3 | ||
* d aa# #OO so m ett ** m art OOO OOO OOO OOo ses e o ee 4 oO mO s't O OO Oo OO OO e ** OO | |||
p= O3 | |||
* d aa# #OO so m ett ** m art OOO OOO OOO OOo ses e o | |||
* e * * * * * * | * e * * * * * * | ||
* e * | * e * | ||
Line 888: | Line 430: | ||
* OO | * OO | ||
. O E Oe OO en O OO et ta u ep ,at= ep O se == | . O E Oe OO en O OO et ta u ep ,at= ep O se == | ||
an ma esf and Q OOO M Eft OOO OOO OOO fie Pm ed J OOO em m art | |||
?. taa a o E | ?. taa a o E | ||
DO no Go ""m O De OO oO ee o.e | DO no Go ""m O De OO oO ee o.e | ||
Line 905: | Line 447: | ||
j e6 | j e6 | ||
' a == fis ese op aE 33-E | ' a == fis ese op aE 33-E | ||
.+-~- -~~~-. .n....__, _ __ , _ _ _ _ | .+-~- -~~~-. .n....__, _ __ , _ _ _ _ | ||
" ~~~~~~ *- - - - - - -. | " ~~~~~~ *- - - - - - -. | ||
r3 Q /, { | r3 Q /, { | ||
O O ' f UR') i L].,1 f' , i F g mej dN MN:h bdbi]b b'' | O O ' f UR') i L].,1 f' , i F g mej dN MN:h bdbi]b b'' | ||
Line 920: | Line 458: | ||
E 000 mee em em no mNe a ao ao mee e e o e e o e e e e J a e o e e e e em e oo De o > N e N J U | E 000 mee em em no mNe a ao ao mee e e o e e o e e e e J a e o e e e e em e oo De o > N e N J U | ||
mop opm mom 04o Mem W a coo o00 Mem no oo mme ao mm so No d oo s e o e e e e e e e e o a e e e e ao o y ao ao m e ~ | mop opm mom 04o Mem W a coo o00 Mem no oo mme ao mm so No d oo s e o e e e e e e e e o a e e e e ao o y ao ao m e ~ | ||
. E poo ooo He@ e e e poo mee noeaooco wo Neo em Do ao mm ,L e A oo e A e e ne o. e e | . E poo ooo He@ e e e poo mee noeaooco wo Neo em Do ao mm ,L e A oo e A e e ne o. e e ao e e a | ||
ao e e a | |||
o e ao e e no e o N | o e ao e e no e o N | ||
e e = | e e = | ||
Line 937: | Line 473: | ||
w | w | ||
*1 -- - | *1 -- - | ||
ooo o00 oco Neo a W | ooo o00 oco Neo a W | ||
3 ooo ooo Weo Goo oo oo Do Fm a U e so ao em oc e e e e l a a e e e e e e o e e e e o o | 3 ooo ooo Weo Goo oo oo Do Fm a U e so ao em oc e e e e l a a e e e e e e o e e e e o o | ||
g on no = co ao ao ao a w 2 m m oso ooo ooo Mee a | g on no = co ao ao ao a w 2 m m oso ooo ooo Mee a | ||
' M a com ooo ooo 00nem mm ao ao oc mm w o > e ao oo e e e o e e e e n u o e s e o e e e on oo ao w oo no ao N L 6 A J w = e m 3 1 000 000 med o00 000 ooo @me u o O 3 000 oc e m. | ' M a com ooo ooo 00nem mm ao ao oc mm w o > e ao oo e e e o e e e e n u o e s e o e e e on oo ao w oo no ao N L 6 A J w = e m 3 1 000 000 med o00 000 ooo @me u o O 3 000 oc e m. | ||
e w a e ao ao no em Oo | e w a e ao ao no em Oo 90 | ||
*e e e e o e i m e o e ** e e * | *e e e e o e i m e o e ** e e * | ||
* a n no no on n u e m ao oo go - | * a n no no on n u e m ao oo go - | ||
= | = | ||
* e 2 U J e D *** *** ao*** | * e 2 U J e D *** *** ao*** | ||
T 3 * " *** *** *** *-=be mom ' "o s* no meo | T 3 * " *** *** *** *-=be mom ' "o s* no meo f M e" > oo oo o e e e e e e e e o e e e e 4 w J u e e | ||
> en on mm U w on oo > = | |||
f M e" > oo oo o e e e e e e e e o e e e e 4 w J u e e | |||
> en on mm | |||
U w on oo > = | |||
M e . a M = | M e . a M = | ||
u oco ooo neo neo ooo ooo oco emo m J o | u oco ooo neo neo ooo ooo oco emo m J o | ||
< w a a. o. o. c. e. m. | < w a a. o. o. c. e. m. | ||
g a o e teo. ce c. eem. e. me s. o. | g a o e teo. ce c. eem. e. me s. o. | ||
oo so ao n | oo so ao n w a == == = = | ||
w a == == = = | |||
J m. | J m. | ||
l 3 emo >>e a w ooo mee Neo o00 ao 000 ao 000 oo em u | l 3 emo >>e a w ooo mee Neo o00 ao 000 ao 000 oo em u w a we no em mm e o e e u e o e o e e e e e e e o m m OO oc oc e wm | ||
w a we no em mm e o e e u e o e o e e e e e e e o m m OO oc oc e wm | |||
* a on a um 3 ew I e u con ooo Wem && | * a on a um 3 ew I e u con ooo Wem && | ||
* a w oooocemo ere mm em Neo em oo Doo oc ce mee g | * a w oooocemo ere mm em Neo em oo Doo oc ce mee g | ||
O e e e o e e e e e o e e ep m e W e e e e e o mm | O e e e o e e e e e o e e ep m e W e e e e e o mm | ||
#. ao M e e ao ao en e | #. ao M e e ao ao en e | ||
> e KE 3 J ww e u m w con mer meo poo ooo pop 000 mem | > e KE 3 J ww e u m w con mer meo poo ooo pop 000 mem p as c eC y s == cs *CC .s s es F - ee a e e e e e o e o e e e e e o e e ou | ||
= w *oo to N Em m M .o S | = w *oo to N Em m M .o S | ||
* eo So m J em o m ooo ooo ooo poo wao se | * eo So m J em o m ooo ooo ooo poo wao se | ||
^ | ^ | ||
w w eco mer m ee r oo ao em uG | w w eco mer m ee r oo ao em uG | ||
> e a ao Po no on oo e e mm e e e e e e e e e o i | > e a ao Po no on oo e e mm e e e e e e e e e o i | ||
u > w e e e o no no go ao a we a e ao ne w Pp 2 | u > w e e e o no no go ao a we a e ao ne w Pp 2 | ||
Line 994: | Line 515: | ||
* e * * | * e * * | ||
* e e e o e a g, O e 2 on = m op on wo a ww g-w | * e e e o e a g, O e 2 on = m op on wo a ww g-w | ||
. 4 JJ | . 4 JJ I w O ooo Neo Phe eMo eme ooo con koM JJ | ||
I w O ooo Neo Phe eMo eme ooo con koM JJ | |||
* s W d em mN mm no oo *No en s u oo ** o e e e e e e e o e e s e e o e d | * s W d em mN mm no oo *No en s u oo ** o e e e e e e e o e e s e e o e d | ||
e g | e g | ||
Line 1,006: | Line 524: | ||
> w ad a e & u o m e m wa j w m m w w n ^ | > w ad a e & u o m e m wa j w m m w w n ^ | ||
e mE | e mE | ||
* p o Q EE N W J mm W* J mm | * p o Q EE N W J mm W* J mm m e ww o | ||
m e ww o | |||
4 . | 4 . | ||
..e .. . . . . - . . . . . . . . . . . - | ..e .. . . . . - . . . . . . . . . . . - | ||
~ . s -o - . . . . . . ..u_ | ~ . s -o - . . . . . . ..u_ | ||
f | f O -l 1 gW< t)(I | ||
O -l 1 gW< t)(I | |||
; \__ % J 'I t | ; \__ % J 'I t | ||
-'' h d- $ b a OOO enO eee OOm eeN eOm noe e 'O m e OO wmm men mme mee Nmm em noe | -'' h d- $ b a OOO enO eee OOm eeN eOm noe e 'O m e OO wmm men mme mee Nmm em noe | ||
Line 1,027: | Line 537: | ||
E J 000 OOO 030 OOO 030 000 eOO 000 O e OO 90 cc 90 00 OO OC 00 e 2 e e e e e e e o e e e e e e e e e | E J 000 OOO 030 OOO 030 000 eOO 000 O e OO 90 cc 90 00 OO OC 00 e 2 e e e e e e e o e e e e e e e e e | ||
> OO DO 90 OO DO DO OO DO N | > OO DO 90 OO DO DO OO DO N | ||
Nem m>m Q 2 | Nem m>m Q 2 | ||
000 eme emm mm> 000 e>> m 00 med WOW myy Nmm mee OO Mer 2 * | 000 eme emm mm> 000 e>> m 00 med WOW myy Nmm mee OO Mer 2 * | ||
Line 1,036: | Line 545: | ||
= = eN y e E | = = eN y e E | ||
& OOO mee eom men emm OOO OOD Ohm e e 2 00 em mm =ph me> OO 00 emO I e a e e o e e o e e e e o e e e e e > | & OOO mee eom men emm OOO OOD Ohm e e 2 00 em mm =ph me> OO 00 emO I e a e e o e e o e e e e o e e e e e > | ||
y eO | y eO m = OO 99 mm M | ||
m = OO 99 mm M | |||
2 M e | 2 M e | ||
000 eNO mer mNe ese OOO 900 WOm W | 000 eNO mer mNe ese OOO 900 WOm W | ||
Line 1,052: | Line 559: | ||
, 000 000 m.m eem amm mom OOO =Ne OO DO mm om =O me OO mem w h u o e e e e e e e e e e o e e e e E 4 99 90 = | , 000 000 m.m eem amm mom OOO =Ne OO DO mm om =O me OO mem w h u o e e e e e e e e e e o e e e e E 4 99 90 = | ||
W W 00 A e J M J o O E OOO e M40 0&m MOS -FM OOO OOO Nem* u 9 W m e OO Nm =Nm em om OO 90 Nem a a e e e e e e e o e o e e e o e e e . 5 e m 90 = MO DO | W W 00 A e J M J o O E OOO e M40 0&m MOS -FM OOO OOO Nem* u 9 W m e OO Nm =Nm em om OO 90 Nem a a e e e e e e e o e o e e e o e e e . 5 e m 90 = MO DO | ||
% E Nm u O J e om | % E Nm u O J e om e a e a OOO mee W Om mem >>m eme mee me e Q 9 4 > OO ON N=N WeM SOW em eN hoh w J u e e o e e e e o e e e o e e m e e u W 99 mm Os eN 4 a - | ||
e a e a OOO mee W Om mem >>m eme mee me e Q 9 4 > OO ON N=N WeM SOW em eN hoh w J u e e o e e e e o e e e o e e m e e u W 99 mm Os eN 4 a - | |||
= | = | ||
Ne m N J O W 000 =Ne met mee MPm OOO OOO Own W e CC mer MR4 mme om emm b > C e e e e e e e e o e e CO e e 90 e o e e W 2 OO m em em OO DO J m Os m | Ne m N J O W 000 =Ne met mee MPm OOO OOO Own W e CC mer MR4 mme om emm b > C e e e e e e e e o e e CO e e 90 e o e e W 2 OO m em em OO DO J m Os m | ||
Line 1,064: | Line 569: | ||
909 OOO OOO 900 a > .OC Ce * *= h W" CC GC eG E's e.m o Pe m ae | 909 OOO OOO 900 a > .OC Ce * *= h W" CC GC eG E's e.m o Pe m ae | ||
= w e e e e e e e e e e * | = w e e e e e e e e e e * | ||
* e m e e o e vu Se = = MS Sc OC se N hm a J u m we e W won mem | * e m e e o e vu Se = = MS Sc OC se N hm a J u m we e W won mem OOO 909 eOO OOO OOO ee= | ||
OOO 909 eOO OOO OOO ee= | |||
> m 4 90 pm M= OO 09 OO DO de u > W e e e o e o e e e e o e | > m 4 90 pm M= OO 09 OO DO de u > W e e e o e o e e e e o e | ||
=Ne uu a e e e e o mm se OO es OO e9 m >= | =Ne uu a e e e e o mm se OO es OO e9 m >= | ||
W | W | ||
& ne D W mem DD | & ne D W mem DD W | ||
e00 eNO wmm eOS OOO eOO >Om a2 z OO mee FN =O oO 90 OO =NS ww a e e e e e * * * | |||
* e e * * * * | * e e * * * * | ||
* We | * We | ||
. N e0 = e9 eo OO N mm | . N e0 = e9 eo OO N mm | ||
. e > QQ | . e > QQ a | ||
2 W OOO pee MOe emm eOO eoO eOS Nem On w a OO me FM MM 99 eo me New uu 3 e g e e o e oe e e e e g e Os = em e e e e e e Q3 a * | |||
w a OO me FM MM 99 eo me New uu 3 e g e e o e oe e e e e | |||
g e Os = em e e e e e e Q3 a * | |||
* se se N= uu | * se se N= uu | ||
} W D dd | } W D dd | ||
Line 1,087: | Line 585: | ||
> 3 * = Ub | > 3 * = Ub | ||
> > e == | > > e == | ||
3 g m Emm amm Mmm Nmm Emm eme emm emm 22 g X JaN Gem G =N *=N ==N a O g gww uww eww Sww N=N N=N D=N We | 3 g m Emm amm Mmm Nmm Emm eme emm emm 22 g X JaN Gem G =N *=N ==N a O g gww uww eww Sww N=N N=N D=N We a e a u e tww eww ww Www uw | ||
a e a u e tww eww ww Www uw | |||
- y > W 22 W > w = m W E WW e O u | - y > W 22 W > w = m W E WW e O u | ||
* LL M W # # | * LL M W # # | ||
W J MM | W J MM g J =% | ||
g J =% | |||
e mm er | e mm er | ||
...-..3---..-...-.... | ...-..3---..-...-.... | ||
@ n (=' b 9 hJ jd[diNNi, iP M!% | @ n (=' b 9 hJ jd[diNNi, iP M!% | ||
(A J J 000 o.. ame o ..m mee .== ~o= | (A J J 000 o.. ame o ..m mee .== ~o= | ||
= oc o p m. e .m>m .pm em | = oc o p m. e .m>m .pm em | ||
Line 1,126: | Line 614: | ||
= - ee m = ce m= u | = - ee m = ce m= u | ||
.s -. | .s -. | ||
en 2 w w E -o o o who ene who m m we 000 ooo oem L u e no mm en N= me ao oo =mm m a a e e e e e e e e e e e e o e e e w on oo ao e o E 4 w w | |||
en 2 w | |||
w E -o o o who ene who m m we 000 ooo oem L u e no mm en N= me ao oo =mm m a a e e e e e e e e e e e e o e e e w on oo ao e o E 4 w w | |||
= e 000 een e== e== poo ooo oso eem & | = e 000 een e== e== poo ooo oso eem & | ||
e > e om em em em oo ao oo ==e = | e > e om em em em oo ao oo ==e = | ||
Line 1,137: | Line 622: | ||
8 % | 8 % | ||
w e | w e | ||
J | J u | ||
00 o e eme e mmm som =em m= em opp o e e e e e e e e e e e u w 00 mm em m me W e .a = | |||
& "o w een men m J me= =>m oco =mc =>o eee 4 w a to =>e ecm m>e to =c m= see b > c e . e e o e o e e e e e o e e e o e w a oo - em m= oo =e J m = | & "o w een men m J me= =>m oco =mc =>o eee 4 w a to =>e ecm m>e to =c m= see b > c e . e e o e o e e e e e o e e e o e w a oo - em m= oo =e J m = | ||
3 m w eco pee enn m>o =mc =mc 000 c== | 3 m w eco pee enn m>o =mc =mc 000 c== | ||
Line 1,150: | Line 634: | ||
m o. =ec ec s cc c r. =ce me | m o. =ec ec s cc c r. =ce me | ||
> > e e e e e o e e e e e e e e e e yo e m oo = eo ao .e s ce m mm | > > e e e e e o e e e e e e e e e e yo e m oo = eo ao .e s ce m mm | ||
= J u m en e w em> mme | = J u m en e w em> mme een o00 ooo ooo con eam 44 | ||
een o00 ooo ooo con eam 44 | |||
> g a ao mow =o ao ao ao oo ==s uu u > w e e e e o e o e e e e e e e o e mm a e ao m eo so. en oc m >= | > g a ao mow =o ao ao ao oo ==s uu u > w e e e e o e o e e e e e e e o e mm a e ao m eo so. en oc m >= | ||
w n= | w n= | ||
Line 1,159: | Line 640: | ||
a w soo e=e Mme ece aos med soo me e- ma | a w soo e=e Mme ece aos med soo me e- ma | ||
. w z 00 me m= co no ao ao mee ww a e e o e o e o e e e e e o e e e en h so = om en so oo = mm | . w z 00 me m= co no ao ao mee ww a e e o e o e o e e e e e o e e e en h so = om en so oo = mm | ||
> GQ | > GQ | ||
' e E w eco =mc mee poo 300 een eco emm no M z eo moo em op om ao em mee vu o e E e e o e e e o e e e e e e o e e 33 | ' e E w eco =mc mee poo 300 een eco emm no M z eo moo em op om ao em mee vu o e E e e o e e e o e e e e e e o e e 33 | ||
Line 1,174: | Line 654: | ||
m w me w J mm m a == | m w me w J mm m a == | ||
e' q ww | e' q ww | ||
_ _- . _..e_.._.. . | _ _- . _..e_.._.. . | ||
D Td ~D "D@@ilj\.L. UIMit 6 s a - | D Td ~D "D@@ilj\.L. UIMit 6 s a - | ||
J OOO .. ~N, ..O OOO 909 O. | J OOO .. ~N, ..O OOO 909 O. | ||
- DO -- .. N. ON | - DO -- .. N. ON w OO e e | ||
w OO e e | |||
. ~~m. e e e O. O. O. Oo m 00 | . ~~m. e e e O. O. O. Oo m 00 | ||
- - _.. .e mm m | - - _.. .e mm m | ||
N OO DO m | N OO DO m | ||
DO Om m, | DO Om m, E | ||
E | |||
. 0O ., .OO 90 | . 0O ., .OO 90 | ||
.O . | .O . | ||
Line 1,202: | Line 672: | ||
O .e O .e O. O. O. 90 90 e | O .e O .e O. O. O. 90 90 e | ||
.. DO OO .e | .. DO OO .e | ||
, Op. .. .._ mm. D | , Op. .. .._ mm. D 2 | ||
OO e e OO e | |||
e | |||
m.. | m.. | ||
e e | e e | ||
..O ON e e O | ..O ON e e O | ||
e e 600 OO e e 000 O | e e 600 OO e e 000 O | ||
e e | e e e e J | ||
e N OO OO em e m 3 R DOD OOm mem NNO U OOO DOD OOO OnN d 4 OO Og Os Om OO 90 OO m e e e e e e e e e e e mer e o e e z OO e e m 90 OO DO y W w & OOO mme nm@ OOO DOO 2 | |||
e e | |||
: 90. SOm e O | : 90. SOm e O | ||
e E | e E | ||
DO e e MO e e m.am M '@m OO OO 90 mmm E e e e e e e %e o e o e W 9 OO M m DO m 99 @@ @ | DO e e MO e e m.am M '@m OO OO 90 mmm E e e e e e e %e o e o e W 9 OO M m DO m 99 @@ @ | ||
W R 900 NNO Wee MMM W o - - OOO SOO SOO 99# W OS em ON Fw OO DO 90 Fw g* e e s e s e o e e e s e J | W R 900 NNO Wee MMM W o - - OOO SOO SOO 99# W OS em ON Fw OO DO 90 Fw g* e e s e s e o e e e s e J | ||
= | = | ||
* 90 m e e e e | * 90 m e e e e | ||
Line 1,252: | Line 711: | ||
> g d OO Om WOO 99@ MM S dd WG 99 WO DO mm u > W e e oe e e e e e e e e 90 UU d W 99 R e e e e mm GO GO DO @@ | > g d OO Om WOO 99@ MM S dd WG 99 WO DO mm u > W e e oe e e e e e e e e 90 UU d W 99 R e e e e mm GO GO DO @@ | ||
w M | w M | ||
M | M O W SOO WWS 900 OOO GOS | ||
, ,m & me DOS OOO MMd E2 ON OO 90 99 On en 2 e e o e e e e e FN ww m e o e e o e e e en OO N SO @@ SO SO Os N 09 | |||
O W SOO WWS 900 OOO GOS | |||
, ,m & me DOS OOO MMd E2 ON OO 90 99 On en 2 e e o e e e e e FN ww | |||
. . > Q3 | . . > Q3 | ||
* 2 m SOS P&S NNO SOS GOO m OOO SOO ==S D3 E eO WW Om OW 99 es mee Q q 3 e e w e e e e * * | * 2 m SOS P&S NNO SOS GOO m OOO SOO ==S D3 E eO WW Om OW 99 es mee Q q 3 e e w e e e e * * | ||
* e e De JD 7 m we e m SO WW o e e e CD | * e e De JD 7 m we e m SO WW o e e e CD 4 em se c ww | ||
. W Q | . W Q | ||
. W 3 OOO ewN 998 000 900 JJ g OOO mme d | . W 3 OOO ewN 998 000 900 JJ g OOO mme d | ||
Line 1,269: | Line 721: | ||
99 e e men e e me G | 99 e e men e e me G | ||
* 90 e | * 90 e | ||
* 00 | * 00 39 99 y ,0 m>m JJ gg 4 m e e *e e o e SO M S OO OO | ||
> d 99 pg == | > d 99 pg == | ||
hh ub | |||
> > e 2 e pm h Emm Mem ham Nam Sam emm Wmm maa O Z Jam Sam 0=N mmN ==N N=N 22 | > > e 2 e pm h Emm Mem ham Nam Sam emm Wmm maa O Z Jam Sam 0=N mmN ==N N=N 22 | ||
& O, & eww uww eww 8*w Sww N=N OmN WW M e tww ww www gg | & O, & eww uww eww 8*w Sww N=N OmN WW M e tww ww www gg | ||
Line 1,279: | Line 729: | ||
s as 8 N W g mg 8 | s as 8 N W g mg 8 | ||
W mE a y J mm E s m ew 4 ww | W mE a y J mm E s m ew 4 ww | ||
. .., , . . . .-e%. . - - - - . . . - = . - - - ~ = - - - ~ | |||
* e e oon o ne * * & 6 e e ew e O&RMR J o.. | |||
. .., , . . . .-e%. . - - - - . . . - = . - - - ~ = - - - ~ * | |||
e e oon o ne * * & 6 e e ew e O&RMR | |||
J o.. | |||
oo | oo | ||
.>. WN | .>. WN | ||
Line 1,305: | Line 749: | ||
oo ao me o ao oo no oo ee n J e o e e e o e e e e e e e e e o m" ~- | oo ao me o ao oo no oo ee n J e o e e e o e e e e e e e e e o m" ~- | ||
oo ao > Oo ao en ou > c | oo ao > Oo ao en ou > c | ||
& w w w u | & w w w u | ||
E 000 000 mem Doo com ooo oDo me@ K e ao oo me ao ao no ao no e a e e o e e o e e o e o e o e e o e M on eo > oo ao no L no % D w 4 | E 000 000 mem Doo com ooo oDo me@ K e ao oo me ao ao no ao no e a e e o e e o e e o e o e o e e o e M on eo > oo ao no L no % D w 4 | ||
Line 1,313: | Line 756: | ||
a e m ao OO on De ao De | a e m ao OO on De ao De | ||
> 2 on oo u J e D 4 : S m e ooo ooo me e ooo ooo ooo ooo M e > oc oo me@ | > 2 on oo u J e D 4 : S m e ooo ooo me e ooo ooo ooo ooo M e > oc oo me@ | ||
w ao ao Oo ao 00 me W J u o e e e o e e e e o e o e o e o u- w oo oo > oo oo ao ao A e a e A | w ao ao Oo ao 00 me W J u o e e e o e e e e o e o e o e o u- w oo oo > oo oo ao ao A e a e A | ||
* p J | |||
p J | |||
w o w e | w o w e | ||
o00 oc 000 we e ooo ooo ooo ooo mem oo ao on es ce CC =c | o00 oc 000 we e ooo ooo ooo ooo mem oo ao on es ce CC =c | ||
Line 1,336: | Line 778: | ||
* e e e e e o e me e s no ao on De eo e | * e e e e e o e me e s no ao on De eo e | ||
ao em on om | ao em on om | ||
, , G0 m | , , G0 m | ||
2 w eco mer ese 900 000 ooo eco mer OO | 2 w eco mer ese 900 000 ooo eco mer OO | ||
Line 1,344: | Line 785: | ||
% > on p up oo os * | % > on p up oo os * | ||
* 33 4 om se p ww w | * 33 4 om se p ww w | ||
D w 2 000 mem ooo mem ooo JJ m O oo me so no one one Ne o JJ 4 & e e De so no Nm ** | D w 2 000 mem ooo mem ooo JJ m O oo me so no one one Ne o JJ 4 & e e De so no Nm ** | ||
e e e e e e e e s e o e e e e m oo > oo 7 4 M oo go es e km o | e e e e e e e e s e o e e e e m oo > oo 7 4 M oo go es e km o | ||
Line 1,350: | Line 790: | ||
= > pm J A m Ema Mmm ham Nam emm nam D E JmN emm Sam 22 e=N emN mmN mmN Nom NmN Omm WM | = > pm J A m Ema Mmm ham Nam emm nam D E JmN emm Sam 22 e=N emN mmN mmN Nom NmN Omm WM | ||
& a a oww www sww oww sww aww ww www 2 e k u e y uu w h w M > w ma F F o a m W & we e | & a a oww www sww oww sww aww ww www 2 e k u e y uu w h w M > w ma F F o a m W & we e | ||
N E& | N E& | ||
w me | w me | ||
: w. J mm a J mm o 6 ww em | : w. J mm a J mm o 6 ww em | ||
s . . . - . . . . | s . . . - . . . . | ||
. . . - - - . . . . . . . . . - . . .....m___._.. | . . . - - - . . . . . . . . . - . . .....m___._.. | ||
e | e J .00 ___ .mm O.. m. e ... wNN NGO e 99 Nee Wh> ese emE SMM mWh MOO m o e e o e eo e ee e N e a e e e e y e e u OO mm ee >> NN NN MOO m | ||
J .00 ___ .mm O.. m. e ... wNN NGO e 99 Nee Wh> ese emE SMM mWh MOO m o e e o e eo e ee e N e a e e e e y e e u OO mm ee >> NN NN MOO m | |||
* NN Mm NN mm 90 *E em & | * NN Mm NN mm 90 *E em & | ||
E J 900 000 OOO 900 000 000 OOO OOO O e 90 OO 90 op OO 90 OO 00 e 3 e e e o e e e e e e e e e o e e e D OO OO DO oO DO OO DO OO O | E J 900 000 OOO 900 000 000 OOO OOO O e 90 OO 90 op OO 90 OO 00 e 3 e e e o e e e e e e e e e o e e e D OO OO DO oO DO OO DO OO O | ||
Line 1,370: | Line 806: | ||
* e o e e e e e o e e o e m o e Z 00 mm NN == == ee y 2 | * e o e e e e e o e e o e m o e Z 00 mm NN == == ee y 2 | ||
o A 000 pee phh ese mee ace mem mee e O E OO We meD m>> NNN 90 00 ese K e B e e e e o e e e e e o e e e e o w e ao == == | o A 000 pee phh ese mee ace mem mee e O E OO We meD m>> NNN 90 00 ese K e B e e e e o e e e e e o e e e e o w e ao == == | ||
* ee D O m e | * ee D O m e 3 OOO 944 wee enM hhh mF@ OOO Nem W | ||
. -- e OO we mmm NNN mee ce OO dem J s _ _ . , _ . _ .. _ | . -- e OO we mmm NNN mee ce OO dem J s _ _ . , _ . _ .. _ | ||
e e e e e e e e e e o e e e e e a 'ee om eo MM U p w d w | e e e e e e e e e e o e e e e e a 'ee om eo MM U p w d w | ||
Line 1,383: | Line 818: | ||
0 3 m m e OOO m>> eNN Ere mee kee emm Ore M e > OO med FOO erm mee mm ee msg w J u e e e e e e e e e e e e e o e me o M u w OO RM kW mm er 4 9 m - - | 0 3 m m e OOO m>> eNN Ere mee kee emm Ore M e > OO med FOO erm mee mm ee msg w J u e e e e e e e e e e e e e o e me o M u w OO RM kW mm er 4 9 m - - | ||
== | == | ||
m m Q J O w one emm >>> mem mee mer No0 ede p w . e OC NmM 999 em* mM CC m= mFF s O e e e e e e e e o e e e e e e N e e w 2 60 mm es es oO J m um | m m Q J O w one emm >>> mem mee mer No0 ede p w . e OC NmM 999 em* mM CC m= mFF s O e e e e e e e e o e e e e e e N e e w 2 60 mm es es oO J m um E w OOO mee som mMk NOO mee mee ene w e se see eNN mee == og so Nee u a e e e e e e o e o e o e e e m e e o a J e0 NN mm de wm J J U2 8 e ww 2 W OOO rpm MOO Mee OOO 000 000 mee && | ||
E w OOO mee som mMk NOO mee mee ene | |||
L e e Se emm e== mm OO ec OO pep | L e e Se emm e== mm OO ec OO pep | ||
= e w e e e e e e o e o e e e e e o e em | = e w e e e e e e o e o e e e e e o e em | ||
Line 1,398: | Line 830: | ||
a w eOO mee Nee m** OOO een ene Few am w a ao Nmm mm SO OO em so m>> ww | a w eOO mee Nee m** OOO een ene Few am w a ao Nmm mm SO OO em so m>> ww | ||
* a ee o e e e o e | * a ee o e e e o e | ||
* e e o e e e o me m ao == 90 0e eo == em | * e e o e e e o me m ao == 90 0e eo == em oo a w moo MOO oNN ped mm | ||
oo a w moo MOO oNN ped mm | |||
=OO De som een see Os m d NGO se oO mee uu | =OO De som een see Os m d NGO se oO mee uu | ||
'N o e z O. Oo a N. Ne e e ** | 'N o e z O. Oo a N. Ne e e ** | ||
Line 1,413: | Line 841: | ||
* e >> | * e >> | ||
I m m Emm mam Mmm Nam emm Emm eme emm gg i O E e E | I m m Emm mam Mmm Nam emm Emm eme emm gg i O E e E | ||
JmN | JmN | ||
<g w w gmN uww tmN gww mmN emm ="m m | <g w w gmN uww tmN gww mmN emm ="m m | ||
te N NmN Smw NmN | te N NmN Smw NmN ww Omm Wm" ww uu E e a u e F w gg d N m * | ||
ww Omm Wm" ww uu | |||
E e a u e F w gg d N m * | |||
* 4 m my i | * 4 m my i | ||
# F G e h& | # F G e h& | ||
g' N W em l 6 J mm a d mN e e ww | g' N W em l 6 J mm a d mN e e ww | ||
, g e | , g e | ||
-- .- - . ' - ' - .' 1. . ' . ' . _ . _ _* . | -- .- - . ' - ' - .' 1. . ' . ' . _ . _ _* . | ||
e f f i i' | |||
. 9 i | |||
. .. i I | |||
1 ! | |||
e f | |||
f i i' | |||
. 9 | |||
i | |||
. .. i | |||
! i | ! i | ||
' ) | ' ) | ||
TABLE 5-A i f | TABLE 5-A i f | ||
.I | .I k1 i t | ||
%ER> UNI YA&MEE JulN1 FREQUEACT -C1sta18UTION= UPPER LEVEL * (OCf f 9 = OEC79) ' i M 7.0 71 albD CA14 ! ' | %ER> UNI YA&MEE JulN1 FREQUEACT -C1sta18UTION= UPPER LEVEL * (OCf f 9 = OEC79) ' i M 7.0 71 albD CA14 ! ' | ||
STABILITY CLASS A CLASS FPEebEncy (PERCEAT.1 a l 0.00 ' | STABILITY CLASS A CLASS FPEebEncy (PERCEAT.1 a l 0.00 ' | ||
NC C68EnvAllChs Mp Tk!S GRfluP ' | NC C68EnvAllChs Mp Tk!S GRfluP ' | ||
9 4 | 9 4 | ||
,c,, | ,c,, | ||
'W? ' | 'W? ' | ||
2 N | 2 N | ||
L=Es 50) r~ | L=Es 50) r~ | ||
C | C | ||
== | == | ||
WD 622 gD | WD 622 gD | ||
[P O | [P O | ||
h, n n g-n.,wim,n.u mp_ g 4 \3 y nm | |||
h, n n | |||
g-n.,wim,n.u | |||
mp_ g 4 \3 y nm | |||
\ | \ | ||
m~ | m~ | ||
Line 1,499: | Line 876: | ||
ps ss o s ... .. | ps ss o s ... .. | ||
-.. ... ... _., N. ... ... | -.. ... ... _., N. ... ... | ||
e .. | e .. | ||
N | N N | ||
N | |||
E a ... | E a ... | ||
= . . | = . . | ||
3 | 3 | ||
. . . . s N N > | |||
. . . . s | |||
N N > | |||
d ... .. | d ... .. | ||
.u N N | |||
. 2 g | |||
w | |||
.u | |||
N N | |||
. 2 | |||
. . . . o | . . . . o | ||
- 4 | - 4 | ||
: m. . ... .. ... .. ... .. ... .. ... .. | : m. . ... .. ... .. ... .. ... .. ... .. | ||
.... . ..... ..... w | .... . ..... ..... w | ||
_ o . | _ o . | ||
M . | M . | ||
. M. . | . M. . | ||
. .o W | . .o W | ||
m, w o . | m, w o . | ||
o a O_ | o a O_ | ||
w . ... .. ... .. ... .. ... .. ..... ..... | w . ... .. ... .. ... .. ... .. ..... ..... | ||
. .a .o w - | |||
A o | |||
. .a .o | m o . ... .. ... .. ... .. ... c. | ||
w - | |||
A | |||
o . ... .. ... .. ... .. ... c. | |||
... o. | ... o. | ||
... No. | ... No. | ||
Q . a. .e | Q . a. .e | ||
. . . e. . . | . . . e. . . | ||
s s - | s s - | ||
E N | E N | ||
N E W ... ..& ... ........ ... ... | |||
N | |||
E W ... ..& ... ........ ... ... | |||
w m | w m | ||
. ^ | . ^ | ||
Line 1,605: | Line 914: | ||
W 4 ... .. ... . . ... .. ... ... .. | W 4 ... .. ... . . ... .. ... ... .. | ||
.... . ...e O.. | .... . ...e O.. | ||
ed m | |||
ed | |||
m | |||
> 4 W S. . c. .. | > 4 W S. . c. .. | ||
C S MM J | C S MM J | ||
D. o EL | D. o EL M | ||
W . | |||
W | W | ||
...*S.. | ...*S.. | ||
Line 1,619: | Line 924: | ||
S* | S* | ||
C | C | ||
. > ..C. C. . e s. C. | . > ..C. C. . e s. C. | ||
* C. C. C. *C.. BB UQ J | * C. C. C. *C.. BB UQ J | ||
Line 1,625: | Line 929: | ||
.M' -. W ... ........ ... ... ..w ... | .M' -. W ... ........ ... ... ..w ... | ||
U 4 | U 4 | ||
b 4 | b 4 4 | ||
b Wo dd mm w . >> | |||
Wo dd mm w . >> | |||
3 49 W . | 3 49 W . | ||
W E | W E | ||
d ... .. ... .. ........ .. ... ... .. .... . ...' .g 43 .. WW h . | d ... .. ... .. ........ .. ... ... .. .... . ...' .g 43 .. WW h . | ||
. > QQ | . > QQ | ||
.* 2 m | .* 2 m | ||
3 4 W | 3 4 W | ||
J ... .. ... .. ... .. ..... ... .. ... .. | J ... .. ... .. ... .. ..... ... .. ... .. | ||
OO yo 2 * * * * * * | |||
* 7 > .. .. .. 33 4 | |||
OO yo 2 * * * * * * | |||
7 > .. .. .. 33 4 | |||
. 4 . .w . | . 4 . .w . | ||
w a | |||
w | d O | ||
d d | |||
d | |||
JJ as eg 4 M . | JJ as eg 4 M . | ||
.. . .e .e S .e | .. . .e .e S .e | ||
& a bE | & a bE WW E & m pm Emm Mmm ham NMM .mm eem .mm O 1 Jam Sam 8*N **N .mm 22 | ||
. ==N N=N N-N Q-N E eww uww ww tww ww aww ed uu w | |||
WW E & m pm Emm Mmm ham NMM .mm eem .mm O 1 Jam Sam 8*N **N .mm 22 | W .S w w M .a w w > w 2 3 | ||
. ==N N=N N-N Q-N | |||
E eww uww ww tww ww aww ed uu | |||
* w w | * w w | ||
: d. N. U ' | : d. N. U ' | ||
L da N W g | L da N W g | ||
+4 W W W | +4 W W W | ||
" J | " J | ||
" a "me"w g ww | " a "me"w g ww | ||
Line 1,679: | Line 958: | ||
ee.-,..e=*- ee-- -.. . =e . -. ~ - - * - ~ ~ = = + ~ - - - | ee.-,..e=*- ee-- -.. . =e . -. ~ - - * - ~ ~ = = + ~ - - - | ||
.--e- .. , - ._ - .. .- | .--e- .. , - ._ - .. .- | ||
vyp 10$$E | vyp 10$$E | ||
... ........ . ..- ..- ~~ ..- | ... ........ . ..- ..- ~~ ..- | ||
J e .. -- ~ ~~ ..~ | |||
J | |||
e .. -- ~ ~~ ..~ | |||
. ~_ | . ~_ | ||
. ~ | . ~ | ||
. ~ ~ - | . ~ ~ - | ||
- . _. _ O m | - . _. _ O m | ||
J emp DOS OOO 900 000 com 000 O O O. 99 99 99 99 O. | J emp DOS OOO 900 000 com 000 O O O. 99 99 99 99 O. | ||
O O. O. O. O. O. . | O O. O. O. O. O. . | ||
Line 1,703: | Line 972: | ||
... ... ..- ..G ... ... >. - | ... ... ..- ..G ... ... >. - | ||
O O... O. .. ~~ -- .. .. | O O... O. .. ~~ -- .. .. | ||
e e | e e e e OO e e e e 90 OO o e O | ||
e e | |||
OO e e e e 90 OO o e O | |||
ee' O e e m | ee' O e e m | ||
o e e G J | o e e G J | ||
Line 1,715: | Line 980: | ||
2 M E OOO 900 000 mem New mem 900 see e N A DO 90 OO #9 OO DO 90 mm & | 2 M E OOO 900 000 mem New mem 900 see e N A DO 90 OO #9 OO DO 90 mm & | ||
* 5 e e e e e e o e e e e e e e o e e N 99 O@ OO N e N OO e e M M | * 5 e e e e e e o e e e e e e e o e e N 99 O@ OO N e N OO e e M M | ||
E DOO 900 OOO 000 000 wwe 900 mo@ M e 90 GO 90 OO 99 90 no CO J e e e o e o e o e o e e e e e e | E DOO 900 OOO 000 000 wwe 900 mo@ M e 90 GO 90 OO 99 90 no CO J e e e o e o e o e o e e e e e e og Op DO @@ m DO m u a | ||
p eO w | |||
og Op DO @@ m DO m u | |||
eO w | |||
d w a OOO 900 & | d w a OOO 900 & | ||
w 3 -OOO GOO 900 OOO OOO OOO DO DO DO 90 M U e DO OO DO 90 e e E A e e e e o e e e e e e e e e w GO GO OO OO DO SO DO DO O | w 3 -OOO GOO 900 OOO OOO OOO DO DO DO 90 M U e DO OO DO 90 e e E A e e e e o e e e e e e e e e w GO GO OO OO DO SO DO DO O | ||
& 4 w w a A OSO SOO GOD SOO DOS SOO OOO OOO A e OO DO OO 90 w F > GO 90 OO DO o e e e e e e e M u e e e o e o e e u a OO 09 90 90 OO 09 OO OO & | & 4 w w a A OSO SOO GOD SOO DOS SOO OOO OOO A e OO DO OO 90 w F > GO 90 OO DO o e e e e e e e M u e e e o e o e e u a OO 09 90 90 OO 09 OO OO & | ||
Line 1,731: | Line 991: | ||
W | W | ||
> 2 Q > e Q g U e m o OOO OCO 900 NOT mWF wem WOO W49 SO OO OO DO 00 == | > 2 Q > e Q g U e m o OOO OCO 900 NOT mWF wem WOO W49 SO OO OO DO 00 == | ||
m Q e w J | m Q e w J W | ||
90 e e e e 90 e e e e e e e e o e e e w w OO 09 OO e =- = OO e g e a m J O W OOO OOO ==c 003 900 men w e 90 e s e. O O. O O ~~ | |||
m J O W OOO OOO ==c 003 900 men w e 90 e s e. O O. O O ~~ | |||
<p > O e o e S. O. O. Ce m. e S. o e e C. .. e e w a = O 90 = e OO GO Go o w m J | <p > O e o e S. O. O. Ce m. e S. o e e C. .. e e w a = O 90 = e OO GO Go o w m J | ||
E E w OOO 900 mer Nee OOO 900 000 H%m w e 99 OO OO DO 90 09 OO wm U a e e e o e e e e e o e e o e e e O a OO 90 m e 09 OO 00 4 wm 3 W4 e U *w 2 m OOO 990 000 OOO WOO OOO SOO 900 && | E E w OOO 900 mer Nee OOO 900 000 H%m w e 99 OO OO DO 90 09 OO wm U a e e e o e e e e e o e e o e e e O a OO 90 m e 09 OO 00 4 wm 3 W4 e U *w 2 m OOO 990 000 OOO WOO OOO SOO 900 && | ||
C e e DC OO 90 SO Oe DC 09 60 | C e e DC OO 90 SO Oe DC 09 60 m e w e e e o e e e o e o e e e * | ||
m e w e e e o e e e o e o e e e * | |||
* e me I > e OO @@ &O 90 eO DO OO 90 MM 3 J KL | * e me I > e OO @@ &O 90 eO DO OO 90 MM 3 J KL | ||
* O u >> | * O u >> | ||
> w OOO 980 900 eOO OOO DOS SOO OSO e > e6 G eC C eCC CC .CC *CE .CC CO 9S | > w OOO 980 900 eOO OOO DOS SOO OSO e > e6 G eC C eCC CC .CC *CE .CC CO 9S | ||
> > e o e o e e e e e e e o e e e e ou | > > e o e o e e e e e e e o e e e e ou a w .s e es OS es eO eO st 60 mm M J me u m WOO OOO a w OOO OOO SOS OOO GOD 900 dd | ||
a w .s e es OS es eO eO st 60 mm M J me u m WOO OOO a w OOO OOO SOS OOO GOD 900 dd | |||
> e d 99 OO DO 90 99 OO 99 99 WW u > w e e e e o e o e e e .e e o e e e mm 3 | > e d 99 OO DO 90 99 OO 99 99 WW u > w e e e e o e o e e e .e e o e e e mm 3 | ||
4 e GO 90 90 se eO 99 OO OO >> | 4 e GO 90 90 se eO 99 OO OO >> | ||
Line 1,753: | Line 1,006: | ||
* h ee OO DO 9e OO OO SO 99 OS 1 | * h ee OO DO 9e OO OO SO 99 OS 1 | ||
* GO | * GO | ||
.* A m eOS eOS onO DOS SOS One OOO *EO DO e w a 90 SG WO 99 OO OO DO OO D'J g e a e e e e o e o e o e e e e e e e 33 | .* A m eOS eOS onO DOS SOS One OOO *EO DO e w a 90 SG WO 99 OO OO DO OO D'J g e a e e e e o e o e o e e e e e e e 33 | ||
. g , eO e9 m es me me em m ww | . g , eO e9 m es me me em m ww | ||
Line 1,760: | Line 1,012: | ||
> d * | > d * | ||
* WV | * WV | ||
> e we | > e we | ||
& K n &Am MMM >** NAA eMa enn *A n n WMH && | & K n &Am MMM >** NAA eMa enn *A n n WMH && | ||
Q E Jam 0=4 SmN ==N ==m mmm mm 3=4 ww I & W & eww Www Sww Sww sww gww ww www WW E e & W e R p > W 22 w % w m m m m ad g ' JP F G - | Q E Jam 0=4 SmN ==N ==m mmm mm 3=4 ww I & W & eww Www Sww Sww sww gww ww www WW E e & W e R p > W 22 w % w m m m m ad g ' JP F G - | ||
e && | e && | ||
N w BW w_ J mm s J em W8 e We f | N w BW w_ J mm s J em W8 e We f | ||
---.a. . . . . . . . . . . . . . _ , . _ . | ---.a. . . . . . . . . . . . . . _ , . _ . | ||
- - - - ~ ~ . - . - - - ~ . . . . . . - . | - - - - ~ ~ . - . - - - ~ . . . . . . - . | ||
._~..;.e- _ _ . . | ._~..;.e- _ _ . . | ||
,,{V T {k :'y-.i | ,,{V T {k :'y-.i | ||
. s I r ., i * *h d j [ | . s I r ., i * *h d j [ | ||
6%' | 6%' | ||
b J 000 hee cem NNe mne emm eme moq | b J 000 hee cem NNe mne emm eme moq | ||
Line 1,795: | Line 1,036: | ||
m e | m e | ||
. e 3 000 mee ene one eNe one mee ese w | . e 3 000 mee ene one eNe one mee ese w | ||
. e no Nm me Nmo Nem moe mo emm J e e e e e e e e e e o e e e e e | . e no Nm me Nmo Nem moe mo emm J e e e e e e e e e e o e e e e e a no Nm Nm o mm o o = w 2 w w a moo Net mee one mee eco coo sem a u e on ms> N= moe me ao ao =>e e a a e e e a e e e e e o e o e e e e w so e ao ao = c a a w = | ||
a no Nm Nm o mm o o = w | |||
2 w w a moo Net mee one mee eco coo sem a u e on ms> N= moe me ao ao =>e e a a e e e a e e e e e o e o e e e e w so e ao ao = c a a w = | |||
m a moo Nee emm mme wee New ooe ems a e > e ao me FN moe mm me no Nw= w e u o e e o e e e * * * * | m a moo Nee emm mme wee New ooe ems a e > e ao me FN moe mm me no Nw= w e u o e e o e e e * * * * | ||
* e e e e u e ao = eo N= n t w w J O n n e | * e e e e u e ao = eo N= n t w w J O n n e | ||
Line 1,811: | Line 1,048: | ||
> 2 m e D . | > 2 m e D . | ||
Qp u e = m ooo see ese e== och use oco mac Q e > 00 mm =mc eme cem km Do moe p w J u e o e e e e e e o e e e e e o s e u w on m em wN en ne M 9 . E = | Qp u e = m ooo see ese e== och use oco mac Q e > 00 mm =mc eme cem km Do moe p w J u e o e e e e e e o e e e e e o s e u w on m em wN en ne M 9 . E = | ||
m 4 J o w ooo ese eme N>m see ooo een McN M w e oc ph mem see me co co sem | m 4 J o w ooo ese eme N>m see ooo een McN M w e oc ph mem see me co co sem w | ||
c e e e e e e e e e e e e o e e e e b a m | |||
. on N= e= op oc km J | . on N= e= op oc km J | ||
B 8 | B 8 | ||
Line 1,821: | Line 1,057: | ||
= w mee new eco woo eco eco ece a > o.nsce ne n. cc cc ac ac c en su | = w mee new eco woo eco eco ece a > o.nsce ne n. cc cc ac ac c en su | ||
> > e e e e e e e o e e o e e e e e uu e = se oc en en to mm m J u m me I' | > > e e e e e e e o e e o e e e e e uu e = se oc en en to mm m J u m me I' | ||
a w eco see eco eco woo moo moo ese ed | a w eco see eco eco woo moo moo ese ed | ||
> e e oo em oc oo ao ao oo em uw | > e e oo em oc oo ao ao oo em uw | ||
Line 1,830: | Line 1,065: | ||
w =e a as a w een och emo ese mom con som hen az w a eo em oc oo -o ao ao em ww | w =e a as a w een och emo ese mom con som hen az w a eo em oc oo -o ao ao em ww | ||
*# a e e * * * * | *# a e e * * * * | ||
* e e e a e *e o e me | * e e e a e *e o e me m ao ao ao so ao me s Q3 a w ese mee een een moc ese one eem ao m a en N= FN eN me es om men oo 3 e a e o e o e e e e o e e e o e o e 33 g > ee me se = ww w o JJ w 2 ene New emm Noe p>m ese eos mee sa a u oo ==e NNN n=e se om eo ese se d a e e e e e e e o e e e e e e e e e = es e No em os ao em um | ||
m ao ao ao so ao me | |||
s Q3 | |||
w o JJ w 2 ene New emm Noe p>m ese eos mee sa a u oo ==e NNN n=e se om eo ese se d a e e e e e e e o e e e e e e e e e = es e No em os ao em um | |||
, > d Wu | , > d Wu | ||
> = >> | > = >> | ||
3 g m Emm mmm >mm NmM emm emme emm emm d2 3 g Jam S-N S*N mmN mmN N=N D=N de j a e a eww uww oww Sww Sww Sww =NmN ww dww wu 4 | 3 g m Emm mmm >mm NmM emm emme emm emm d2 3 g Jam S-N S*N mmN mmN N=N D=N de j a e a eww uww oww Sww Sww Sww =NmN ww dww wu 4 | ||
3 e a u o m e = w a2 w M w m m W m de 9 e D e KL N w me w d mm m a um e y e wm e | 3 e a u o m e = w a2 w M w m m W m de 9 e D e KL N w me w d mm m a um e y e wm e | ||
... ...... ._. ... .. _ . ._ m . _.. _ . . . . | ... ...... ._. ... .. _ . ._ m . _.. _ . . . . | ||
g\ ;i h)N'(. . _Nh T | g\ ;i h)N'(. . _Nh T | ||
r0 1 b; .{M O | r0 1 b; .{M O | ||
* i sW ;;\\ Ollju\b, . | * i sW ;;\\ Ollju\b, . | ||
_ Qg \ | _ Qg \ | ||
s | |||
* e J OsO mem OmM N.. mee ese men ~Oe e aO mee Nae M-e eOW was nM SON | |||
e J OsO mem OmM N.. mee ese men ~Oe e aO mee Nae M-e eOW was nM SON | |||
= e e N e e M e e N o e e o e e o e a e e J DO MD eW 40 mW N OG m m N Mm Nm m as 1 m & | = e e N e e M e e N o e e o e e o e a e e J DO MD eW 40 mW N OG m m N Mm Nm m as 1 m & | ||
E J OOO OSM OOO OOO OSS 900 090 000 9 3 OO 99 OO OO De 99 OU OO e 3 e e o e o e e e e e e e e e e e e P OO DO OD OO DO DO 90 OO Q | E J OOO OSM OOO OOO OSS 900 090 000 9 3 OO 99 OO OO De 99 OU OO e 3 e e o e o e e e e e e e e e e e e P OO DO OD OO DO DO 90 OO Q | ||
Line 1,872: | Line 1,087: | ||
* wo 90 eN l @ | * wo 90 eN l @ | ||
* W M | * W M | ||
3 SOS eWh SO4 med NMF mme 999 WNW W 3 cm em 9M eM NO me SO New J | 3 SOS eWh SO4 med NMF mme 999 WNW W 3 cm em 9M eM NO me SO New J e e e e o e s e e e e e e e o e m 99 OO N* U e - | ||
e e e e o e s e e e e e e e o e m 99 OO N* U e - | |||
M w g 2 W w a eOO cem cem Sam amp OOO OOO SOM & | M w g 2 W w a eOO cem cem Sam amp OOO OOO SOM & | ||
l U n OO FN mN FN mO 99 OO mwW n e 2 3 e e e e e e o e e e o e e e e e w OO DO OO .* O | l U n OO FN mN FN mO 99 OO mwW n e 2 3 e e e e e e o e e e o e e e e e w OO DO OO .* O | ||
Line 1,883: | Line 1,095: | ||
* e e e e e e 8 e e e e e * | * e e e e e e 8 e e e e e * | ||
* W W & OO m a OO DO Mm o U W 2 N > m O u e = e OOO Wee m>m eeM ree Wes DOO ANe i O e e Oc mee NMe mN> mee em oc eeM | * W W & OO m a OO DO Mm o U W 2 N > m O u e = e OOO Wee m>m eeM ree Wes DOO ANe i O e e Oc mee NMe mN> mee em oc eeM | ||
@ w J U e e e e e e e e e e e e e e o e u w OO e N em N ee De M G E m | @ w J U e e e e e e e e e e e e e e o e u w OO e N em N ee De M G E m m J O w eOO Mme e-W Mem aoM eme era eMe g W W OO mem WMc eE9 -Eh W= We MM* | ||
I b > O e e o e e e e e e o e o e e e m e e w 2 40 m eN em m me a m m 3 | I b > O e e o e e e e e e o e o e e e m e e w 2 40 m eN em m me a m m 3 | ||
m w 300 MNO MON hWM de h NMP ==M OCe w W WO Mhm PON NON eN NO m e e>M u s e o e e e o e o e o e e o e m e o O a eO M= eM Mm me wm 3 m U2 e W ew e 2 W OOO NWO e@W mew OOO GOS GOO DOM && | m w 300 MNO MON hWM de h NMP ==M OCe w W WO Mhm PON NON eN NO m e e>M u s e o e e e o e o e o e e o e m e o O a eO M= eM Mm me wm 3 m U2 e W ew e 2 W OOO NWO e@W mew OOO GOS GOO DOM && | ||
Q W W GC. NWO wee Me 99 CO 99 MWh t m a W e e e e e e e e o e e e e e o e SW | Q W W GC. NWO wee Me 99 CO 99 MWh t m a W e e e e e e e e o e e e e e o e SW M e WO Nm m 90 OO DO W = mm 3 J l Ez a u ** | ||
M e WO Nm m 90 OO DO W = mm 3 J l Ez a u ** | |||
= w weO SOM emp OOO OOO 900 SOO WNW g a > C G *EM wO OC EC CC SE *W P SS | = w weO SOM emp OOO OOO 900 SOO WNW g a > C G *EM wO OC EC CC SE *W P SS | ||
> > e e e e e e o e o e e o e e e e uw 4 m @@ m OS SO SE SO e hh m J u m am | > > e e e e e e o e o e e o e e e e uw 4 m @@ m OS SO SE SO e hh m J u m am W w WOO NmW NMP 999 OOO 990 969 WeW dd | ||
W w WOO NmW NMP 999 OOO 990 969 WeW dd | |||
> g d OO eMm NO 99 OO 90 60 mee wy U w w e e e e e e e e e e e e e e e e mm d W 99 m 99 WO SO 90 m wp W em J PP G W GOS OMM m=p OOO SOS DOS 300 mgG 22 | > g d OO eMm NO 99 OO 90 60 mee wy U w w e e e e e e e e e e e e e e e e mm d W 99 m 99 WO SO 90 m wp W em J PP G W GOS OMM m=p OOO SOS DOS 300 mgG 22 | ||
,. w E 9 0 mmW mW OO 90 39 30 mNm ww g e e e e e e e o e e e e e o e e me b 90 m 99 90 SO 90 m 33 | ,. w E 9 0 mmW mW OO 90 39 30 mNm ww g e e e e e e e o e e e e e o e e me b 90 m 99 90 SO 90 m 33 | ||
> 33 | > 33 | ||
* e e d W OOO NmW Wee mmm WOO Sep OOO MNM DO | * e e d W OOO NmW Wee mmm WOO Sep OOO MNM DO | ||
= d eO mmc W= m 3 SO me mW my> GU | = d eO mmc W= m 3 SO me mW my> GU O e 2 * * | ||
O e 2 * * | |||
* e e e e e e e e e o e o e 33 e | * e e e e e e e e e o e o e 33 e | ||
m p om m em eO se = ww g ' ' | m p om m em eO se = ww g ' ' | ||
Line 1,918: | Line 1,120: | ||
e . . . . . .. . . | e . . . . . .. . . | ||
%@, g g$ N'p %>[ N D ROU e. | |||
%@, g | |||
g$ N'p %>[ N D ROU e. | |||
UM ~ | UM ~ | ||
~m. .so s ooo ~~e -.., So, o.O | ~m. .so s ooo ~~e -.., So, o.O | ||
Line 1,937: | Line 1,130: | ||
e ee o. | e ee o. | ||
a o. | a o. | ||
a o.e o. | |||
a o.e | e u | ||
o. | |||
e | |||
u | |||
ao s,.. | ao s,.. | ||
.e e - o eue m | .e e - o eue m | ||
E. | E. | ||
aoo Deo goo 33. One og3 o J emo e se o oo eo eo me no e es eo oo oo e e e e e e e e e g e e e e e e e e ee oo no eo 00 00 oo a eo u | aoo Deo goo 33. One og3 o J emo e se o oo eo eo me no e es eo oo oo e e e e e e e e e g e e e e e e e e ee oo no eo 00 00 oo a eo u | ||
Line 1,962: | Line 1,146: | ||
se A oeo en e art eo We se m est me ya eo eo eo em & | se A oeo en e art eo We se m est me ya eo eo eo em & | ||
so a oo e e ee e e e e e e e e om e 3 e e e o eo set y eo - eo eo - | so a oo e e ee e e e e e e e e om e 3 e e e o eo set y eo - eo eo - | ||
et e se S eoo Rs m e ooo sts M 9 eoo eoo eoo e are e ens ao ec no eo eo ao oo em .a | et e se S eoo Rs m e ooo sts M 9 eoo eoo eoo e are e ens ao ec no eo eo ao oo em .a e e e e e e e e e e e e o e e e e eo eo ee o en e= 4.s | ||
e e e e e e e e e e e e o e e e e eo eo ee o en e= 4.s | |||
- - - - -. . - _ . . . . . " . . . -.e=- .. | - - - - -. . - _ . . . . . " . . . -.e=- .. | ||
eo M | eo M | ||
4 oeo oeo art = m as ens E ooo se e art om e e se e art eoe oo o en m as er u as oo eo m es eo eo e e o e e e e e e e e e e e a a e o eo su o eo e= ee oo # | |||
4 oeo oeo art = m as | |||
ens E ooo se e art om e e se e art eoe oo o en m as er u as oo eo m es eo eo e e o e e e e e e e e e e e a a e o eo su o eo e= ee oo # | |||
ans em ** | ans em ** | ||
w oeo a o se as o o eoo e est e a a== m oeo eoo e art e oo eo eo e == w s= es oo oo e == oo e e e e e e e e e e o e er. | w oeo a o se as o o eoo e est e a a== m oeo eoo e art e oo eo eo e == w s= es oo oo e == oo e e e e e e e e e e o e er. | ||
r u e e e e en o eo eo eo =* K u d eo eo == =* | r u e e e e en o eo eo eo =* K u d eo eo == =* | ||
ens ans *e | ens ans *e O 3 x, eoo eoo e e em u u O a eoo eW #9 F sts m en su m e oeo oo e ne | ||
*== a es eo ya yo yo eo en e e e e e a e e ens e e o e ee e e ** e o a es. se e up eo eo ns u en en, eo | *== a es eo ya yo yo eo en e e e e e a e e ens e e o e ee e e ** e o a es. se e up eo eo ns u en en, eo | ||
* e= 2 | * e= 2 | ||
Line 2,012: | Line 1,190: | ||
* e e em ot a e * * | * e e em ot a e * * | ||
* eo eo == me oe == eo eo ee | * eo eo == me oe == eo eo ee | ||
. m 43 3 | . m 43 3 o= eoo == p e es e ers e as o ee soo eoe eoo se e e oo ens eo eo eo eo =* ere et oa | ||
o= eoo == p e es e ers e as o ee soo eoe eoo se e e oo ens eo eo eo eo =* ere et oa | |||
.a 4 g | .a 4 g | ||
oo e e | oo e e | ||
Line 2,021: | Line 1,197: | ||
g m Q eoo eeo eoo e == s ans d eooeses m ye e ====e9 oet m e> n ==e ee ee ee en e e't m en e | g m Q eoo eeo eoo e == s ans d eooeses m ye e ====e9 oet m e> n ==e ee ee ee en e e't m en e | ||
# .s g g oe e e e e e e e e e e g gg e e ee oe eo & && | # .s g g oe e e e e e e e e e e g gg e e ee oe eo & && | ||
oe F == Oe ao e.m | oe F == Oe ao e.m e-- e-- o-n o,= | ||
. - - .-- ~-- e-- - | . - - .-- ~-- e-- - | ||
, ., .a m. . . e= W=ed~ - SWW - as . - - ~ .e .e ~ .~e. o-~ e ,ns o & 4***** W *"r w G w 98 9 w 8'8 | , ., .a m. . . e= W=ed~ - SWW - as . - - ~ .e .e ~ .~e. o-~ e ,ns o & 4***** W *"r w G w 98 9 w 8'8 | ||
Line 2,039: | Line 1,212: | ||
* e | * e | ||
.. , . . . . . .. .. . ......m.~. . .- | .. , . . . . . .. .. . ......m.~. . .- | ||
e e- . . m e.= ... -. ... ~ , , , , . | e e- . . m e.= ... -. ... ~ , , , , . | ||
3 | 3 | ||
. ... m.. ..m N-. --. ... 99... ... | . ... m.. ..m N-. --. ... 99... ... | ||
Line 2,059: | Line 1,229: | ||
W OOO 900 909 OOO OOO OOO SOS DOS d e-OO DO 90 OO DO DO DO DO J e e e o e e e o e's e o e e e e | W OOO 900 909 OOO OOO OOO SOS DOS d e-OO DO 90 OO DO DO DO DO J e e e o e e e o e's e o e e e e | ||
,' m SO 90 90 DO 90 SO DO DO | ,' m SO 90 90 DO 90 SO DO DO | ||
. y O E W W E OOO DOS OOO COO SOO GOO COO OOO & | |||
. y O | |||
W E OOO DOS OOO COO SOO GOO COO OOO & | |||
W W OO DO 90 CO DO 90 OO DO M S B e o e e e e e e o e e e e e e e d De 9e OO 90 DO Oe 99 OO O 6 2 w | W W OO DO 90 CO DO 90 OO DO M S B e o e e e e e e o e e e e e e e d De 9e OO 90 DO Oe 99 OO O 6 2 w | ||
M m B OOO OOO mme OOO e > 900 946 OOO mhp B W OC 00 4O OO OO DO OO SO w | M m B OOO OOO mme OOO e > 900 946 OOO mhp B W OC 00 4O OO OO DO OO SO w | ||
Line 2,071: | Line 1,237: | ||
> 2 | > 2 | ||
> W D u m m e 900 mne OOO 999 OOO OOO OOO m>m Q e > OO 40 OO OO OO 09 OO eO O w J u e o e e e e o e e e e e e e e e u w OO e 99 9e OO 90 OO e ga e -a J | > W D u m m e 900 mne OOO 999 OOO OOO OOO m>m Q e > OO 40 OO OO OO 09 OO eO O w J u e o e e e e o e e e e e e e e e u w OO e 99 9e OO 90 OO e ga e -a J | ||
* g J O w OOO OOO enz =>e OOO 900 OOe cam W e em | * g J O w OOO OOO enz =>e OOO 900 OOe cam W e em H | ||
> O e CO CO e e e e ec e e Oc e e OC Oc mm w a 90 Oc e e OO On OO m J m N B | |||
H | |||
> O e CO | |||
m O M OOO =>p NMO 900 OOO OOO OOO meg | m O M OOO =>p NMO 900 OOO OOO OOO meg | ||
' W e 99 30 me OO 99 OO 9e em u s e e e e o e e e o e e e e o e e O a De e m OO 3 m DO OO - 90 O wm e u N DE e 2 W OOO whW OOO ew SOO GOO OOO OOO mh@ && | ' W e 99 30 me OO 99 OO 9e em u s e e e e o e e e o e e e e o e e O a De e m OO 3 m DO OO - 90 O wm e u N DE e 2 W OOO whW OOO ew SOO GOO OOO OOO mh@ && | ||
* O e e DC ec OO 90 OO CO DO ee m O W e e o e o e e o e o e e e e e e em l > e OS e OO DO se OO DO e mm D J KR O u ww m W OOO OOO OOO 996 000 990 OOO SOO t a > sc e > se e. O. O e Os e e e o | * O e e DC ec OO 90 OO CO DO ee m O W e e o e o e e o e o e e e e e e em l > e OS e OO DO se OO DO e mm D J KR O u ww m W OOO OOO OOO 996 000 990 OOO SOO t a > sc e > se e. O. O e Os e e e o | ||
*O n se e e se se ma e e e e e e bu e m OO DO De Os SO DO OO 90 M J sh 8 | *O n se e e se se ma e e e e e e bu e m OO DO De Os SO DO OO 90 M J sh 8 | ||
u m me 9 W OOO OOO OOO 990 OOO OOO 999 990 dd | u m me 9 W OOO OOO OOO 990 OOO OOO 999 990 dd | ||
> M d OO GO 99 OO 99 99 99 OO uu u > W e e e e e e e e e e e e e e e e mm o O 99 OO 99 OO DO 99 99 OO >> | > M d OO GO 99 OO 99 99 99 OO uu u > W e e e e e e e e e e e e e e e e mm o O 99 OO 99 OO DO 99 99 OO >> | ||
w me e J Ob O W OOO 999 969 999 OOO 909 OOO 900 | w me e J Ob O W OOO 999 969 999 OOO 909 OOO 900 42 e' M R 99 90 99 90 OO DO DO De ww | ||
42 e' M R 99 90 99 90 OO DO DO De ww | |||
'' 3 e o e e e e e e e e e e e e e e 69 E 99 99 @@ 99 OO 99 OO DO DO e 3D e | '' 3 e o e e e e e e e e e e e e e e 69 E 99 99 @@ 99 OO 99 OO DO DO e 3D e | ||
d W OOO OOO 900 OOO 900 000 SOO 900 00 i m 4 OO DO DO DO p | d W OOO OOO 900 OOO 900 000 SOO 900 00 i m 4 OO DO DO DO p | ||
Q q E e e e e o e e e 99 e e 99 e e 99 o e OO ou e e 33 7 p @@ 99 OO 99 OO uu h'' | Q q E e e e e o e e e 99 e e 99 e e 99 o e OO ou e e 33 7 p @@ 99 OO 99 OO uu h'' | ||
4 99 99 99 ' | 4 99 99 99 ' | ||
* - O JJ w 4 OOO SOS mhm OOO OOO SOO SOO m>p JJ K U 99 99 O@ OO 90 99 99 e9 g 4 4 4 e e O e e o e e o e e e e e o e e m DO @@ e 09 | * - O JJ w 4 OOO SOS mhm OOO OOO SOO SOO m>p JJ K U 99 99 O@ OO 90 99 99 e9 g 4 4 4 e e O e e o e e o e e e e e o e e m DO @@ e 09 | ||
Line 2,102: | Line 1,254: | ||
, W6 m > == | , W6 m > == | ||
E h m Emm men hme %mm Omm Omm Omm Omm II Q E Jem Omm Sam amm =mN Nmm Nmm Omm wd | E h m Emm men hme %mm Omm Omm Omm Omm II Q E Jem Omm Sam amm =mN Nmm Nmm Omm wd | ||
: i. O & eww uww Www tww sww eww e e & M ww www Wu d h w S a O > e AE D F G m m w n aM N w W EM | : i. O & eww uww Www tww sww eww e e & M ww www Wu d h w S a O > e AE D F G m m w n aM N w W EM M me 8 | ||
m J mm O J m ew 4 mw | m J mm O J m ew 4 mw | ||
: 7. .. < - . . . . . . _ . - . - - . | : 7. .. < - . . . . . . _ . - . - - . | ||
4....-.-====- - - - - - . - . - . - | 4....-.-====- - - - - - . - . - . - | ||
* '. as. | * '. as. | ||
e w ... | e w ... | ||
%!y}{ D h_ 3 h@ f$a | %!y}{ D h_ 3 h@ f$a | ||
.o. ... .NN hmm N.. .-- N.. | .o. ... .NN hmm N.. .-- N.. | ||
4 OO MSG hew Nem FNN mer mee | 4 OO MSG hew Nem FNN mer mee | ||
- e e M e e e** ee e 600 u m o e m o e o e N e e | - e e M e e e** ee e 600 u m o e m o e o e N e e DO em op we 9e er mm NGO m mm MM NN mm OO ,E mm & | ||
DO em op we 9e er mm NGO m mm MM NN mm OO ,E mm & | |||
E J 300 300 000 coo m #G Om OO 333 000 eso esO 3 90 00 OO OL OO e 3 e e e e e e e e e e e e e e | E J 300 300 000 coo m #G Om OO 333 000 eso esO 3 90 00 OO OL OO e 3 e e e e e e e e e e e e e e | ||
> Oo OO OC e o e OO OO OO DO em E OOS ONN emm O 044 mNN Nmm woo One > | > Oo OO OC e o e OO OO OO DO em E OOS ONN emm O 044 mNN Nmm woo One > | ||
Line 2,133: | Line 1,279: | ||
e o e e e e e e e e e e e | e o e e e e e e e e e e e | ||
. . . . . . _ , . mm y y .De -. um ee O | . . . . . . _ , . mm y y .De -. um ee O | ||
._ 4 W W X eOS ese mOC W u e GO mm =pp hhh Mew MOO DOO ekh & | |||
._ 4 W W X eOS ese mOC W | |||
u e GO mm =pp hhh Mew MOO DOO ekh & | |||
-h> mm OO DO e e & * | -h> mm OO DO e e & * | ||
* e e o e e e o e e e e e MMM e e w OO OO E OO == O w & | * e e o e e e o e e e e e MMM e e w OO OO E OO == O w & | ||
Line 2,151: | Line 1,294: | ||
== ee m. m | == ee m. m | ||
.Oe | .Oe | ||
- .. . . e m. N w 4 oO em se J = NN 3 == | - .. . . e m. N w 4 oO em se J = NN 3 == | ||
3 w S00 emm e@ e Mmm w e e@ mee RO O ewe med mm Nee mem Nee a - | 3 w S00 emm e@ e Mmm w e e@ mee RO O ewe med mm Nee mem Nee a - | ||
Line 2,179: | Line 1,321: | ||
e e mer e e mm e e ao e e em om ean ouo 00 m e e o e e 33 7 se == | e e mer e e mm e e ao e e em om ean ouo 00 m e e o e e 33 7 se == | ||
We me e NN w u. | We me e NN w u. | ||
W D | W D w a goo see NNN JJ a O em mem ese See em" mFP | ||
w a goo see NNN JJ a O em mem ese See em" mFP | |||
-em eenOO eso kmm sa a g e e e e e e ** e e e o Se mme eg | -em eenOO eso kmm sa a g e e e e e e ** e e e o Se mme eg | ||
% m e e e o e eO ** NN NN OO ce | % m e e e o e eO ** NN NN OO ce | ||
> & MM k% | > & MM k% | ||
m | m | ||
, uu | , uu d b m gmm mmm ham Nam ema emm MM Q E JmN 3-N tmN saa emm ZZ | ||
d b m gmm mmm ham Nam ema emm MM Q E JmN 3-N tmN saa emm ZZ | |||
& O | & O | ||
**N ==N N=N N=N OmN we g a a gww uww aww Swa tw= tww ww www wu w | **N ==N N=N N=N OmN we g a a gww uww aww Swa tw= tww ww www wu w | ||
Line 2,196: | Line 1,334: | ||
= w& | = w& | ||
-I TABLE 6 VERMONT YANKEE l! | |||
-I | QUARTERLY AVERACE X/Q, D/Q AND CAMMA I/Q VALUES FOR SELECTED RECEPTORS POINT OF INTEREST t THIRD QUARTER FOURTH QUARTER Maximum offsite ground Location: ; | ||
TABLE 6 | |||
VERMONT YANKEE l! | |||
QUARTERLY AVERACE X/Q, D/Q AND CAMMA I/Q | |||
VALUES FOR SELECTED RECEPTORS | |||
POINT OF INTEREST t THIRD QUARTER FOURTH QUARTER | |||
Maximum offsite ground Location: ; | |||
1evel air concentration WNW 1.5 mi Location: i location X/Q (undepleted)*: 4.904x10-}es NW 2.5 mi1 | 1evel air concentration WNW 1.5 mi Location: i location X/Q (undepleted)*: 4.904x10-}es NW 2.5 mi1 | ||
* X/Q (depleted)*: X/Q (undepleted): 4.811x10''9s 4.882 x 10-7 X/Q (depleted): | * X/Q (depleted)*: X/Q (undepleted): 4.811x10''9s 4.882 x 10-7 X/Q (depleted): | ||
D/Q**: 9.418 x 10-10 4.588 x 10-7 | D/Q**: 9.418 x 10-10 4.588 x 10-7 | ||
* i Camma X/Q:* D/Q: 1.290 x 10-10 . | * i Camma X/Q:* D/Q: 1.290 x 10-10 . | ||
2.211 x 10-7 , | 2.211 x 10-7 , | ||
Camma X/Q: 2.347 x 10-7 | Camma X/Q: 2.347 x 10-7 | ||
* For whole body and skin , | * For whole body and skin , | ||
doses from noble gases | doses from noble gases | ||
: 1) Maximum site boundary t | : 1) Maximum site boundary t | ||
Location: S 0.24 mi location | Location: S 0.24 mi location X/Q (undepleted): 2.10x10-ges Location: N 0.25 mi X/Q (depleted): 2.10 x 10-9 X/Q (undepleted): 3.04x10-gs i D/Q: X/Q (depleted): 3.04 x 10-II t | ||
X/Q (undepleted): 2.10x10-ges Location: N 0.25 mi | |||
X/Q (depleted): 2.10 x 10-9 X/Q (undepleted): 3.04x10-gs i D/Q: X/Q (depleted): 3.04 x 10-II t | |||
1.03 x 10-II D/Q: , | 1.03 x 10-II D/Q: , | ||
Camma X/Q: 7.38 x 10-7 2.90 x 10-13 , | Camma X/Q: 7.38 x 10-7 2.90 x 10-13 , | ||
Line 2,236: | Line 1,353: | ||
X/Q (undepleted): 3.65x10ges S 0.33 miles ' | X/Q (undepleted): 3.65x10ges S 0.33 miles ' | ||
X/Q (depleted): X/Q (undepleted): 5.58 x 10-10 3.65 x 10-9 X/Q (depleted): | X/Q (depleted): X/Q (undepleted): 5.58 x 10-10 3.65 x 10-9 X/Q (depleted): | ||
D/Q: 2.00 x 10-II 5.58 x 10-10 D/Q: 4.17 x 10-12 Camma X/Q: 5.41 x 10-7 For organ doses from Camma X/Q: 3.21 x 10-7 iodine and particulates in gaseous effluents - | |||
D/Q: 2.00 x 10-II 5.58 x 10-10 D/Q: 4.17 x 10-12 Camma X/Q: 5.41 x 10-7 For organ doses from Camma X/Q: 3.21 x 10-7 | : 1) Maximum farm location Location: 1 SSE 3.5 m Location: | ||
iodine and particulates in gaseous effluents - | |||
: 1) Maximum farm location Location: 1 | |||
SSE 3.5 m Location: | |||
X/Q (undepleted): 2.84x10-}1es SSE 3.5 mi - | X/Q (undepleted): 2.84x10-}1es SSE 3.5 mi - | ||
e X/Q (depleted): X/Q (undepleted): 2.42x10-}1es 2.80 x 10-7 X/Q (depleted): | e X/Q (depleted): X/Q (undepleted): 2.42x10-}1es 2.80 x 10-7 X/Q (depleted): | ||
D/Q: 9.71 x 10-II 2.37 x 10-7 D/Q 1.02 x 10-9 Camma X/Q: 1.82 x 10-7 Camma X/Q: 1.58 x 10-7 | D/Q: 9.71 x 10-II 2.37 x 10-7 D/Q 1.02 x 10-9 Camma X/Q: 1.82 x 10-7 Camma X/Q: 1.58 x 10-7 G | ||
G | |||
,i | ,i | ||
. v - . ... g | . v - . ... g | ||
. t i | . t i | ||
TABLE 6 (continued) \ | TABLE 6 (continued) \ | ||
POINT OF INTEREST i s | POINT OF INTEREST i s | ||
TillRD QUARTER . \ | TillRD QUARTER . \ | ||
FOURTil QUARTER a ! | FOURTil QUARTER a ! | ||
: 2) Maximum nearest residence Location: SSE 1.3 a . | : 2) Maximum nearest residence Location: SSE 1.3 a . | ||
X/Q (undepleted): 8.27x10gles Location: SSE 1.3 m X/Q (depleted): X/Q (undepleted): 8.35x10gles ., | |||
8.25 x 10-8 X/Q (depleted): ,' : | 8.25 x 10-8 X/Q (depleted): ,' : | ||
D/Q: 4.63 x 10-10 8.33 x 10-8 , i D/Q: 5.74 x 10-10 i | D/Q: 4.63 x 10-10 8.33 x 10-8 , i D/Q: 5.74 x 10-10 i Camma X/Q: 2.82 x 10-7 , | ||
Camma X/Q: 2.82 x 10-7 , | |||
Camma X/Q: 2.44 x 10-7 l I | Camma X/Q: 2.44 x 10-7 l I | ||
: 3) Maximum site boundary Location: | : 3) Maximum site boundary Location: | ||
location SSE 0.53 Location: | location SSE 0.53 Location: | ||
i X/Q (undepleted): 4.33x10-giles SSE 0.53 X/Q (depleted): X/Q (undepleted): 6.67x10-giles | |||
i X/Q (undepleted): 4.33x10-giles SSE 0.53 | |||
* 4.32 x 10-8 X/Q (depleted): | * 4.32 x 10-8 X/Q (depleted): | ||
D/Q: 2.82 x 10-10 6.66 x 10-9 - | D/Q: 2.82 x 10-10 6.66 x 10-9 - | ||
l Camma X/Q: 5.47 x 10-7 D/Q 6.90 x 10-II i Camma X/Q: 4.49 x 10-7 l Depleted and undepletedX/Qs and Gamma X/Q are in units of sec./m 3 Delta (D/Q) in units of 1/m2 | l Camma X/Q: 5.47 x 10-7 D/Q 6.90 x 10-II i Camma X/Q: 4.49 x 10-7 l Depleted and undepletedX/Qs and Gamma X/Q are in units of sec./m 3 Delta (D/Q) in units of 1/m2 | ||
~ | ~ | ||
TABLE 7 | TABLE 7 | ||
==SUMMARY== | ==SUMMARY== | ||
OF RADIOLOGICAL IMPACT ON MAN | OF RADIOLOGICAL IMPACT ON MAN | ||
' Vermont Yankee Nuclear Power Station : | ' Vermont Yankee Nuclear Power Station : | ||
Third and Fourth Quarters, 1979 t | |||
EST1 HATED THIRD ESTIMATED FOURTH 1 | |||
TENTIAL PATHWAY OR TYPE OF EXPOSURE ' | TENTIAL PATHWAY OR TYPE OF EXPOSURE ' | ||
QUARTER DOSE ! | QUARTER DOSE ! | ||
QUARTER DOSE . ' | QUARTER DOSE . ' | ||
COMMITNENT COMMITMENT l { | COMMITNENT COMMITMENT l { | ||
Maximum individual whole body and Whole Body | Maximum individual whole body and Whole Body critical organ doses from receiving- 3.2 x 10-6 ! I water exposure pathways from 2.6 x 10-6 (adult) liquid releases (arem). teen) No liquid releases , | ||
critical organ doses from receiving- 3.2 x 10-6 ! I water exposure pathways from 2.6 x 10-6 (adult) | |||
liquid releases (arem). teen) No liquid releases , | |||
2.2 x 10-6 ((child) | 2.2 x 10-6 ((child) | ||
Castro-Intestinal- l i | Castro-Intestinal- l i | ||
Lower-Largg 4.2 x 10- (Intestine ' | Lower-Largg 4.2 x 10- (Intestine ' | ||
3.0 x 10-6 teen) | 3.0 x 10-6 teen) | ||
(adult) , | (adult) , | ||
1.8 x 10-6 (child) | 1.8 x 10-6 (child) | ||
A. Whole body and skin doses to individuals exposed at point ' | A. Whole body and skin doses to individuals exposed at point ' | ||
of maximum offsite ground I 1evel air concentration of radioactive noble gaseous l effluents i (at WNW, 2400m) (at NW, 4000m) | of maximum offsite ground I 1evel air concentration of radioactive noble gaseous l effluents i (at WNW, 2400m) (at NW, 4000m) | ||
Line 2,334: | Line 1,409: | ||
: 11. Whole body dose (arem) 7.3 x 10-2 3.0 x 10-2 7.2 x 10-2 1.0 , in-2 | : 11. Whole body dose (arem) 7.3 x 10-2 3.0 x 10-2 7.2 x 10-2 1.0 , in-2 | ||
.- i' | .- i' | ||
;\ | ;\ | ||
8 TABLE 7 (continued) ii | 8 TABLE 7 (continued) ii 50TENTIAL PATifWAY OR TYPE OF EXPOSURE ESTIMATED TIIIRD F .TIMATED FOURTil ' | ||
50TENTIAL PATifWAY OR TYPE OF EXPOSURE ESTIMATED TIIIRD F .TIMATED FOURTil ' | |||
QUARTER DOSE QUARTER DOSE ' | QUARTER DOSE QUARTER DOSE ' | ||
COMMITMENT COMMITMENT | COMMITMENT COMMITMENT | ||
Line 2,351: | Line 1,417: | ||
radioactive lodine and particulates . | radioactive lodine and particulates . | ||
in gaseous effluents (including tritium). , | in gaseous effluents (including tritium). , | ||
A. Maximum farm location e | A. Maximum farm location e | ||
' i | ' i Maximum individual whole body ! | ||
Maximum individual whole body ! | |||
and organ doses from all pathways (at SSE, 3.5 miles) (at SSE, 3.5 miles) i i. | and organ doses from all pathways (at SSE, 3.5 miles) (at SSE, 3.5 miles) i i. | ||
Bone (mrem) { | Bone (mrem) { | ||
Line 2,371: | Line 1,432: | ||
(mrem) 3.2 x 10-4child) | (mrem) 3.2 x 10-4child) | ||
((child) 4.0 x 10~3 teen) 3.9 x 10-3 ((child) | ((child) 4.0 x 10~3 teen) 3.9 x 10-3 ((child) | ||
TABLE 7 (continued) ' | TABLE 7 (continued) ' | ||
*l POTENTIAL PATifWAY OR TYPE OF EXPOSURE ESTIMATED TIIIRD ! | *l POTENTIAL PATifWAY OR TYPE OF EXPOSURE ESTIMATED TIIIRD ! | ||
ESTIMATED FOUR1H QUARTER DOSE ! | ESTIMATED FOUR1H QUARTER DOSE ! | ||
Line 2,392: | Line 1,439: | ||
COMMITHENT COMMITMENT ' | COMMITHENT COMMITMENT ' | ||
,I C. | ,I C. | ||
Organ doses to individuals at point of maximum ground level air l- | Organ doses to individuals at point of maximum ground level air l-concentration of gaseous effluents , | ||
from inhalation and ground exposure . | |||
concentration of gaseous effluents , | |||
of iodine and particulates e . | of iodine and particulates e . | ||
(at VNW, 2400m) - | (at VNW, 2400m) - | ||
i. | i. | ||
(at NW, 4000m) | (at NW, 4000m) | ||
Line 2,408: | Line 1,452: | ||
j | j | ||
' D. Organ doses to individuals at or teen) j point cf maximum site boundary air concentration of gaseous ! | ' D. Organ doses to individuals at or teen) j point cf maximum site boundary air concentration of gaseous ! | ||
effluents from Inhalation and ground exposure of iodine ' } | effluents from Inhalation and ground exposure of iodine ' } | ||
and particulates . | and particulates . | ||
Line 2,417: | Line 1,460: | ||
4.2 x 10~4 111. GI(LLI) (arem) 2.1 x 10'' (child) 4.4 x 10-4 (all) iv. Whole body as 1.1 x 10'4 (all) 4.2 x 10~4 (child) critical organ 1.1 x 10-4 (all) 4.2 x 10-4 all) | 4.2 x 10~4 111. GI(LLI) (arem) 2.1 x 10'' (child) 4.4 x 10-4 (all) iv. Whole body as 1.1 x 10'4 (all) 4.2 x 10~4 (child) critical organ 1.1 x 10-4 (all) 4.2 x 10-4 all) | ||
((all) t | ((all) t | ||
; -i 1 | |||
1 TABLE 7 (continued) l | |||
; -i | |||
1 | |||
1 | |||
TABLE 7 (continued) l | |||
, I i i i | , I i i i | ||
ESTIMATED TIIIRD ESTIMATED FOURTH | ESTIMATED TIIIRD ESTIMATED FOURTH | ||
'OTENTIAL PATilVAY OR TYPE OF EXPOSURE k QUARTER DOSE QUARTER DOSE COMMITMENT ! | 'OTENTIAL PATilVAY OR TYPE OF EXPOSURE k QUARTER DOSE QUARTER DOSE COMMITMENT ! | ||
COMMITHENT l | COMMITHENT l | ||
V. ! | V. ! | ||
Line 2,444: | Line 1,472: | ||
g facility. | g facility. | ||
i e A. Maximum site boundary (mrem) | i e A. Maximum site boundary (mrem) | ||
(west of turbine - | (west of turbine - | ||
building) 2.8 2.3 ! > | building) 2.8 2.3 ! > | ||
B. Population dose (person-rem) 1.5 x 10-2 1.3 x 10-2 | B. Population dose (person-rem) 1.5 x 10-2 1.3 x 10-2 Whole body dose to the population from all receiving-water related pathways from liquid releases. | ||
Whole body dose to the population from all receiving-water related pathways from liquid releases. | |||
(person-rem). , | (person-rem). , | ||
3.5 x 10-3 No liquid releases t | 3.5 x 10-3 No liquid releases t | ||
- . . ~ . - . . . . . . , | - . . ~ . - . . . . . . , | ||
. ;1 9 . hh | |||
. ;1 | |||
9 . hh | |||
( | ( | ||
il | il | ||
, i, TABLE 7 (continued) l l | , i, TABLE 7 (continued) l l | ||
f' | f' i | ||
POTENTIAL PATHWAY OR TYPE OF EXPOSURE ESTIMATED THIRD ESTIMATED FO!!RTH i li i QUARTER DOSE l '; | |||
QUARTER DOSE COMMITMENT [ | QUARTER DOSE COMMITMENT [ | ||
COMMITNENT e .l VI. | COMMITNENT e .l VI. | ||
I! | |||
A. ~ ! ,! | A. ~ ! ,! | ||
Whole body doses to the population '' | Whole body doses to the population '' | ||
and average individual out to 50 l' | and average individual out to 50 l' | ||
'I alles from noble gaseous ! i I,' | 'I alles from noble gaseous ! i I,' | ||
effluents i | effluents i t * | ||
t | |||
: 1. Whole body dose to population 1 l (person-rem) l | : 1. Whole body dose to population 1 l (person-rem) l | ||
: 11. 1.3 ! | : 11. 1.3 ! | ||
Line 2,496: | Line 1,499: | ||
111. Skin dose to population 1.11 x 10-3 4.5 x 10-4 i (person-rem) iv. Average individual skin dose 2.1 9.5 x 10-I (arem) , | 111. Skin dose to population 1.11 x 10-3 4.5 x 10-4 i (person-rem) iv. Average individual skin dose 2.1 9.5 x 10-I (arem) , | ||
1.8 x 10-3 8.2 x 10-4 B. Organ doses to 50 mile popula- ; | 1.8 x 10-3 8.2 x 10-4 B. Organ doses to 50 mile popula- ; | ||
tion, and average individual, ' | tion, and average individual, ' | ||
from inhalation, inge,' tion of milk, meat, and vegetables, and ground exposure to iodine and parti-culates in gaseous effluents * | from inhalation, inge,' tion of milk, meat, and vegetables, and ground exposure to iodine and parti-culates in gaseous effluents * | ||
: 1. Thyroid population dose (person-rem) | : 1. Thyroid population dose (person-rem) | ||
Line 2,505: | Line 1,506: | ||
Average individual whole body 1.1 x 10-2 9.4 x 10-2 dose (mrem) 9.5 x 10-6 . | Average individual whole body 1.1 x 10-2 9.4 x 10-2 dose (mrem) 9.5 x 10-6 . | ||
8.2 x 10-5 | 8.2 x 10-5 | ||
APPENDIX A EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT Supplemental Information July - December 1979 Facility: Vermont Yankee Nuclear Power Station Licensee: Vermont Yankee Nuclear Power Corporation | |||
APPENDIX A EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT | |||
Supplemental Information July - December 1979 | |||
Facility: Vermont Yankee Nuclear Power Station | |||
Licensee: Vermont Yankee Nuclear Power Corporation | |||
_ 1. Regulatory Limits | _ 1. Regulatory Limits | ||
: a. Fission and activation gases: 0.08/E7 Ci/sec. | : a. Fission and activation gases: 0.08/E7 Ci/sec. | ||
: b. Iodines: 0.48 pC/sec. | : b. Iodines: 0.48 pC/sec. | ||
: c. Particulates, half-lives >8 days: | : c. Particulates, half-lives >8 days: | ||
Line 2,532: | Line 1,515: | ||
: d. Liquid effluents: | : d. Liquid effluents: | ||
1.03-7 uC/ml (HTO: 3.0E-3 pC/ml, dissolved Noble gases: | 1.03-7 uC/ml (HTO: 3.0E-3 pC/ml, dissolved Noble gases: | ||
4.0E-5 uC/ml). isotopic limits are found in 10CFR20 App. B, Table II, Column 2. | 4.0E-5 uC/ml). isotopic limits are found in 10CFR20 App. B, Table II, Column 2. | ||
: 2. Mar.imum Permissible Concentrations | : 2. Mar.imum Permissible Concentrations | ||
. Provided below are the MPC's used in determining allowable release rates or concentrations. | . Provided below are the MPC's used in determining allowable release rates or concentrations. | ||
: a. Fission and activation gases: No MPC limits | : a. Fission and activation gases: No MPC limits | ||
: b. Iodines: No MPC limits t | |||
: b. Iodines: No MPC limits | i N | ||
N | |||
, 2.'-...,........-.................-.. | , 2.'-...,........-.................-.. | ||
c. | c. | ||
Particulates, half-lives >8 days: See 100FR20, App. B, Table II, Column | Particulates, half-lives >8 days: See 100FR20, App. B, Table II, Column | ||
Line 2,558: | Line 1,528: | ||
. 3. Average Energy Provided below are the average energy (I) of the radionuclide mixture in releases of fission and activation gasses, if applicable. | . 3. Average Energy Provided below are the average energy (I) of the radionuclide mixture in releases of fission and activation gasses, if applicable. | ||
: a. Average gamma energy: 3rd Quarter 0.987 MeV/ Dis. | : a. Average gamma energy: 3rd Quarter 0.987 MeV/ Dis. | ||
4th Quarter 0.685 MeV/ Dis. | 4th Quarter 0.685 MeV/ Dis. | ||
: b. Average beta energy: Not Applicable 4. | : b. Average beta energy: Not Applicable 4. | ||
Measurements and Approximations of Total Radioactivity , | Measurements and Approximations of Total Radioactivity , | ||
Provided below are the methods used to measur, or approximate the total radioactivity in effluents and the methods used to determine radionuclide composition. | Provided below are the methods used to measur, or approximate the total radioactivity in effluents and the methods used to determine radionuclide composition. | ||
a. | a. | ||
Fission and Activation Cases | Fission and Activation Cases Daily samples are drawn at the discharge of the Air Ejector. | ||
Daily samples are drawn at the discharge of the Air Ejector. | |||
Isotopic breakdown of the releases are determined from these samples. A logarithmic chart of the stack gas monitor is read daily to determine the gross release rate. At the very low release | Isotopic breakdown of the releases are determined from these samples. A logarithmic chart of the stack gas monitor is read daily to determine the gross release rate. At the very low release | ||
. rates normally encountered during operation with the Augmented Off Cas system the error of release rates may be approximately 2' | |||
. rates normally encountered during operation with the Augmented | |||
Off Cas system the error of release rates may be approximately 2' | |||
+ 100%. - | + 100%. - | ||
: b. Iodines Continuous isokinetic samples are drawn from the plant stack through a particulate filter and charcoal cartridge. The filters and cartridge are removed weekly (if releases are less than 4% | |||
: b. Iodines Continuous isokinetic samples are drawn from the plant stack | |||
through a particulate filter and charcoal cartridge. The filters and cartridge are removed weekly (if releases are less than 4% | |||
of the Tech Spec limit), or daily (if they are greater than 4% | of the Tech Spec limit), or daily (if they are greater than 4% | ||
of the limit), and are analyzed for radioicdine 131, 132, 133, 134, and 135. | of the limit), and are analyzed for radioicdine 131, 132, 133, 134, and 135. | ||
5 | 5 The iodines found on the filter are added to those on the charcoal cartridge. The error involved in these steps may be approximately 150%. | ||
: c. Particulates The particulate filters described in b. above are also counted - | |||
The iodines found on the filter are added to those | |||
on the charcoal cartridge. The error involved in these steps | |||
may be approximately 150%. | |||
: c. Particulates | |||
The particulate filters described in b. above are also counted - | |||
for particulate radioactivity. The error involved in this sample is also approximately 150%. | for particulate radioactivity. The error involved in this sample is also approximately 150%. | ||
: d. Liquid Effluenta | : d. Liquid Effluenta Radioactive liquid effluents released from the facility are continuously rionitored. | ||
Radioactive liquid effluents released from the facility are continuously rionitored. | |||
Measurements are also made on a representative sample of each batch of radioactive liquid effluents released. | Measurements are also made on a representative sample of each batch of radioactive liquid effluents released. | ||
For each batch, station records are retained of the total activity (mci) released, concentration (pCi/ml) of gross | For each batch, station records are retained of the total activity (mci) released, concentration (pCi/ml) of gross radioactivity, volume (liters), and approximate total quantity | ||
. . of water (liters) used to dilute the liquid effluent prior to release to the Connecticut River. r M | |||
. . of water (liters) used to dilute the liquid effluent prior to release to the Connecticut River. r | |||
M | |||
. -p - _ . - - - . . . . . - . . . . | . -p - _ . - - - . . . . . - . . . . | ||
- -- - - . - - - - - ~ . . . ~ . .. . . . . . | - -- - - . - - - - - ~ . . . ~ . .. . . . . . | ||
Each batch of radioactive liquid effluent released is analyzed for gross gamma and gan=a isotopic radioactivity. .A monthly proportional composite sample, comprising an aliquot of each batch I | Each batch of radioactive liquid effluent released is analyzed for gross gamma and gan=a isotopic radioactivity. .A monthly proportional composite sample, comprising an aliquot of each batch I | ||
released during a month, is also analyzed for tritium, SR-89, SR-90, gross beta and gross alpha radioactivity, in addition to gamma spectroscopy. | released during a month, is also analyzed for tritium, SR-89, SR-90, gross beta and gross alpha radioactivity, in addition to gamma spectroscopy. | ||
There were no liquid releases during the reporting period. | There were no liquid releases during the reporting period. | ||
t ~ | t ~ | ||
Line 2,631: | Line 1,557: | ||
: a. Liquid | : a. Liquid | ||
: 1. Number of batch releases: 16 ". | : 1. Number of batch releases: 16 ". | ||
: 2. Total time period for batch releases: 14,490 min. | : 2. Total time period for batch releases: 14,490 min. | ||
: 3. Maximum time period for a batch release: 1,539 min. | : 3. Maximum time period for a batch release: 1,539 min. | ||
: 4. Average time period for batch releases: 905 min. | : 4. Average time period for batch releases: 905 min. | ||
: 5. Minimum time period for a batch release: 331 min. | : 5. Minimum time period for a batch release: 331 min. | ||
: 6. Average stream flow during periods of release 4,063 cfs | : 6. Average stream flow during periods of release 4,063 cfs i | ||
of effluent into a flowing stream: | |||
: b. Caseous There were no routine gaseous batch releases during the repo,rting | |||
: b. Caseous | |||
There were no routine gaseous batch releases during the repo,rting | |||
' t | ' t | ||
, period. | , period. | ||
{ | { | ||
) | ) | ||
A4 | A4 | ||
~ | ~ | ||
: 6. Abnormal Releases | : 6. Abnormal Releases | ||
: a. Liquid There were no non-routine liquid releases during the reporting period. | |||
: a. Liquid | |||
There were no non-routine liquid releases during the reporting period. | |||
: b. Gaseous There were no non-routine gaseous releases during the reporting period. | : b. Gaseous There were no non-routine gaseous releases during the reporting period. | ||
e 6 | e 6 | ||
9 | 9 O | ||
9 RE}} | |||
RE}} |
Latest revision as of 02:25, 22 February 2020
ML19290E948 | |
Person / Time | |
---|---|
Site: | Vermont Yankee ![]() |
Issue date: | 12/31/1979 |
From: | VERMONT YANKEE NUCLEAR POWER CORP. |
To: | |
Shared Package | |
ML19290E946 | List: |
References | |
NUDOCS 8003170367 | |
Download: ML19290E948 (53) | |
Text
..,
EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT RADIOLOGICAL IMPACT ON MAN FOR THIRD AND FOURTH QUARTERS, 1979 4
e VERMONT YANKEE NUCLEAR POWER STATION S
TABLE OF CONTENTS Page
1.0 INTRODUCTION
.................................................. I 2.0 METEOROLOGICAL DATA........................................... 2 3.0 RADIOACTIVITY RELEASES........................................ 3 3.1 Liquid Releases.......................................... 3 3.2 Caseous Releases......................................... 3
- 4.0 DOSE ASSESSMENT............................................... 4 4.1 Organ Doses to Individuals from Receivin Exposure Pathways.......................g-Water ................. 4 4.2 Individual Whole-Body and Skin Doses from Noble Caseous Effluents........................................ 6 4.3 Organ Doses to Individuals from Radioactive Iodine .
and Particulates in Caseous Effluents.................... 8 4.4 Whole-Body Doses in Unrestricted Areas from Direct Radiation......................................... 10 4.5 Whole-Body Doses to the General Population from all Receiving Water Related Pathways......................... 11 4.6 Doses to the General Population and Average Individual within Fifty Miles from Caseous Effluents................ 13 REFERENCES......................................................... 15 TABLES.................e........................................... 16-45 APPENDIX A - SUPPLEMENTAL INFORMATION.............................. Al e
~:::L:-~. . . . . . . . . . .
LIST OF TABLES Table No. Title 1A Caseous Effluents - Summation of all Releases 1B Caseous Effluents - Elevated Releases IC Caseous Effluents - Routine Ground Level Releases ID Caseous Effluents - Non-Routine Releases 1A Liquid Effluents - Summation of all Releases 3
Solid Waste and Irradiated Fuel Shipments 4-A to 4-H Vermont Yankee Joint Frequency Distribution July - September, 1979 5-A to 5-H Vermont Yankee Joint Frequency Distribution October - December, 1979 .
6 Quarterly Average X/Q and D/Q Values for -
Selected Receptors 7
Summary of Radiological Impact on Man
-iii-
VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT RADIOLOGICAL IMPACT ON MAN JULY - DECEMBER 1979 1.0 INfRODUCTION Using actual measured effluent and meteorological data for the second six months of 1979, this report estimates potential doses from radioactive effluents that could affect individuals and the general population near
~
the Vermont Tankee Nuclear Power Station. Tables 1 through 3 list the recorded radioactive effluents and solid waste for this semi-annual period.
Tables 4 and 5 report the cumulative joint frequency distribution of wind speed, wind direction, and atmospheric stability observed during the second half of 1979, while Table 6 lists the calculated I/Q and D/Q values at different points of interest based on the meteorological record presented in Tables 4 and 5 for both quarters. Table 7 summarizes the potential radiological dose commitments to individuals and the general population surrounding the plant. Supplemental information concerning the plant's regulatory release limits and the methods used in measuring released radioactivity is given in Appendix A.
All estimates of potential dose for the second six months of 1979 t
were within the dose objectives set forth in Appendix I to 10CFR50. This was accomplished while the plant realized net capacity factors (design MWe) of 72.5 percent and 60.1 percent for the third and fourth quarters, respectively.
e 2.0 METEOROLOGICAL DATA Meteorological data was collected during this reporting period from the site's 300 foot met tower located approximately 2200 feet northwest of the reactor building, and about 1,400 feet from the plant stack. The 300 foot tower is approximately the same height as the primary plant stack (94 meters) and is designed to meet the requirements of Regu? r ; iry Guide 1.23 for meteorological sonitoring.
Implementation of the Central Meteorological System (CMS) was completed during the month of May, 1978. Combined data recoverability for the third and feurth quarters was 88.4 percent and 99.8 percent respect 1vely. ,
X/Q and D/Q values were derived for all receptor points from the site meteorological record for each quarter using a straight-line airflow model. All dispersion and air concentration factors have been calculated employing appropriate source configuration considerations, as described in Regulatory Guide 1.111(1), plus a source depletion model as described in Meteorology and Atomic Energy (1968),(2) and deposition velocities as given by Pelletier and Zimbrick(3). Changes in terrain elevations in the site environment were also factored into meteorological models. A full description of the methods used to evaluate air dispersion phenomenon at the plant site is given in Vermont Yankee's 10CFR Part 50, Appendix I I evaluation (4).
t
...~..-. ...... . . . . . . . . . . . . . . . .
3.0 RADIOACTIVITY RE1. EASES 3.1 Liquid Releases During the semi-annual period, a total of 16 planned and controlled batch releases of liquid radioactivity (totalling less than 2.90 x 10-4 C1) were discharged f rom Vermont Yankee in accordance with the plant's operating Technical Specifications. All liquid effluent recorded for the second half of the year are listed in Tables 2A and 2B. Approximately 484,000 litets of waste liquid was released to the Connecticut River through the plant's
- liquid radvaste system. Average river flow for the release periods was approximately 4063 cfs. During the same time period, there were no unplanned or non-routine releases of radioactivity in any liquid effluents.
3.2 Caseous Releases
- All gaseous effluent recorded for the second half of the year are listed in Tables LA through ID. All gaseous effluents were recorded as continuous in nature, and were released to the environment via the 94 meter stack located approximately 875 feet north of the Reactor Building. As indicated in Table 1A, all gaseous effluents were well within the plants
~
operating Technical Specification for gaseous re1 eases of radioactivity.
In addition, there were no unplanned or non-routine releases of radioactivity in gaseous effluents during this reporting period.
M 4.0 DOSE ASSESSMENT Following the guidance of NUREG-0473(7), nuclides in particulate form which were not detected above the lower limit of detection, (LLD) have
, been reported as "less than' the LLD and have not been included in the dose calculations. However, the release rate of noble gases from the plant stack, af ter treatment of the gas stream from the air ejector through the augmented off-gas system, is so low that no noble gases are detectable above the LLD.
Therefore, as a conservative approach for the noble gas releaser, it has
- been assumed for dose calculational purposes that the principal noble gases measured in the off-gas mix at the air ejector are present at the LLD level determined for the plant stack.
4.1 Organ Doses to Individuals from Receiving-Water Exposure Pathways '.
During the third quarter 16 separate batches of liquid waste totalling 484,000 liters, were released. The radiological health significance of these releases were evaluated using the liquid pathway model described in NRC Regulatory Guide 1.109(5). Site specific parameters used in applying this dosimetric model to the Vermont Yankee environment have been described and documented in the report (4) submitted to the NRC Office of Nuclear Reactor Regulation in connection with 10CFR50, Appendix I.
The liquid pathway dose analysis for the third quarter was per. formed
. at a point in the Connecticut River just below Vernon Dam 0.5 mile downstream of the plant. Fishing from the shoreline was assumed to be the sole contribution to dose. The ingestion of river water and aquatic invertebrates was not considered since these pathways do not exist along this portion of the Connecticut River or any known downstream location.
E The irrigation of farm land by river water was not taken into account because it has not been observed below the plant. Fishing in Vernon Pond was not considered due to the relatively small fish population and because the shoreline access is largely restricted.
All liquid effluent from the plant was assumed to be homogeneously mixed in the volume' of water which passed over the dam during the period of release.
This leads to a conservative estimate of the radionuclide concentrations below the dam since no credit is taken for dilution or deposition in Vernon Pond.
The average river flow over the das during the time of release in the third quarter was 4063 cfs.
Usage factors for adults, teenagers and children were obtained from Regulatory Guide 1.109, and doses were calculated for whole-body, bone,'.
kidney, GI-LLI, liver, thyroid and lung. The GI-LLI (gastro-intestinal and lower-large-intestine) was the critical organ for the adult age group with Tritium and Manganese-54 being the principle nuclides contributing to dose.
. As indicated in Table 7, the resulting individual CI-LLI dose commitments due to liquid releases during the third quarter are 4.2 x 10-6 mrem, 3.0 x 10-6 and 1.8 x 10-6 to the adult, teen and child age groups respectively.
It should also be noted that these doses assume that each individual ingests, in the third quarter, one half of the total annual' intake
. of fish recommended for a maximum individual in Regulatory Guide 1.109.
All calculated doses due to radioactivity in liquid effluent are well below the dose criteria of 10CFR50, Appendix I.
There were no non-routine liquid releases from Vermont Yankee during
~5-
the reporting period. As a result, no accidental or unplanned liquid effluents in receiving water pathways could contribute to any whole body or organ doses to individuals in unrestricted areas.
4.2 Individual Whole-Body and Skin Doses from Noble Caseous Effluents Based on the method of sector averaging discussed in " Meteorology and Atomic Energy - 1968", and utilizing the site meteorological data recorded for this reporting period, the point of maximum off-site ground level air concentration of radioactive materials in gaseous effluents was
-determined for each quarter. ' Terrain height in the vicinity of the effluent stack was taken into account in calculating these effluent ground level concentrations. For the third and fourth quarters of 1979, the points of maximum ground level air concentration were determined to be approximately WNW at 2400m and NW at 4000m of the plant stack. The undepleted I/Q's at these locations were calculated to be 4.9 x 10-7 sec/m3 and 4.8 x 10-7 sec/m3 for third and fourth quarters of the year, respectively.
Whole-body and skin doses were calculated at these off-site points as a result of noble gas releases occurring in both quarters. The methodology applied to the dose calculations is consistent with that of Regulatory Guide 1.109(5) for an elevated release point. Dose conversion factors for noble gases and daughters were taken from Table B-1 of this Regulatory Guide. For the beta contribution to the skin dose, a semi-infinite cloud model was used. The whole-body gamma dose was evaluated using a finite cloud sector average model with Gaussian activityd 'istribution in the vertical plane. The gamma radiation received at a point of interest from a differential volume of the cloud is calculated. The radiation is then integrated over the entire cloud, taking into account of the geometry of the cloud, variation in concentration, attenuation by the interaction of photons with matter in the path between source and the receptor point, and scattering of radiation from material outside the direct path to the point of interest. An attenuation factor of 0.7 is also applied to the dose calculations to account for the dose reduction due to shielding which would be provided by a residential structure. No additional credit is taken for decay of radionuclides in transit to the receptor point.
-- ,For the third quarter, the skin and whole-body doses from exposure to noble gases at the point of maximum ground level air concentration were calculated to be 0.069 mrem and 0.03 mrem, respectively. For the noble gaseous effluent during the fourth quarter, the skin and whole-body doqes at the point of maximum ground level air concentration were calculated to be 0.049 mrem and 0.022 mram, respectively.
In addition, the maximum nearest resident and site boundary whole-body and skin doses have been calculated due to noble gaseous effluents from the plant stack during the reporting period. The maximum whole-body and skin site boundary doses (both approximately 0.1 mrem) for the third quarter of 1979 occurred in the S sector. 0.24 miles from the stack. The
, fourth quarter maximum whole-body and skin site boundary doses (both 0.05 arem) occurred in the N sector 0.25 miles from the stack.
In the third quarter, the maximum skin and whole-body dose to the nearest resident (both approximately 0.07 mrem) in any direction was determined to be in the S sector, 0.33 mils. xrom the plant stack. As a result of the fourth quarter meteorology and noble gas effluents, the maximum whole-body and skin dose to the nearest resident (both 0.03 mrem) in any sector occurred to the resident 0.33 miles south of the plant stack.
The resultant doses due to noble gas effluents for the maximum site boundary location, maximum nearest resident, and point of maximum ground level air concentration are tabulated in Table 7. All doses are conservative in that they assume 100 percent occupancy at each point. Whole-body doses consider the gamma radiation received from the effluent plume overhead.
The skin doses considers both the beta and gamma contributions at the L
receptor point. All doses from noble gaseous effluents are well below the dose criteria of 10CFR50, Appendix I.
4.3 Organ Doses to Individuals from Radioactive Iodine and Particulates in Caseous Effluents The critical pathway of internal exposure to radioactive iodine and particulates, including tritium, resulting from gaseous effluents for the third quarter is through the grass-milk pathway. It is assumed that milk animals are free to graze on open pasture during the third quarter with no supplemental feeding. This assumption is conservative since most of the milk animals inventoried in the site vicinity are fed stored feed throughout the entire year with only limited grazing allowed during the growing season.
. During the vinter months of the year, the dose commitment through the milk pathway and fresh vegetable ingestion is insignificant. The maximum length of annual growing season is approximately six months long in this part of New England. Therefore, the milk pathway and vegetable ingestion doses for the fourth quarter are the result of activity deposited on feed u
~ "'
. -- ; .. . .~~~~2 . r ......_ T : ~~. *'
~ ~ ~ ' '
and vegetables grown during the growing season and allowed to decay while held in storage. As a result, the critical pathway of exposure for radioactive iodine and particulates during the fourth quarter is through inhalation.
As a result of the milk and fresh vegetable pathways, the maximum dose for the third quarter from gaseous releases of radioactive iodine and particulates was determined to occur at a farm 3.5 miles south-southeast of the plant. The critical organ was an tufant thyroid with a calculated
---dose of 0.049 mrem. For the fourth quarter, with inhalation being the principle pathway of exposure, the maximum organ dose was projected to also be at the same farm. The critical organ was a child's thyroid with a calculated dose of 0.0081 mrem. The pathways of exposure which were assuned to exist during the third quat ter at this farm include ground plane exposure, inhalation, fresh home grown vegetables and cow's milk. The pathways of exposure considered at the farm during the fourth quarter include continuous ground plane exposure, inhalation and contributions from stored vegetables and milk.
e Table 7 shows the maximum calculated quarterly organ dose due to the combination of exposures from all pathways which have been identified at the farm. Table 7 also shows the calculated organ doses to the highest exposed nearby res'. dent, and potential organ doses to individuals if a.ssumed
, standing at the highest ground level air concentration point on the site l boundary for the entire six-month reporting period. The site boundary doses include only exposure from inhalation, and direct radiation from the ground plane. The nearest resident is assumed to have a vegetable garden during the growing season which contributes to his or her ingestion dose. For all ground plane exposures, the activity is assumed to accumulate on the ground for 15 years at the rate equivalent to that observed during each quarter.
This is a simplified method of approximating the average deposition over the life of the plant. The calculated dose from direct exposure to activity on the ground thus represents the dose an individual would see in each quarter if ,the plant had been operating 15 years. This approach is very conservative, but shows the relative impact the plant would have on the dose consitment over its operating life if the releases were to continue at the levels recorded during this reporting period.
The critical organs for the third and fourth quarters for the nearest resident with the most exposure were the thyroid and bone respectively, and for the maximum site boundary location, was calculated in both cases to be a child's thyroid. The respective doses at these locations for the-third quarter were 1.7 x 10-3 mrem (SSE 1.3 miles) and 2.1 x 10-4 mrem (SSE 0.53 miles). For the fourth quarter both doses were 4.4 x 10-4 mrem.
4.4 Whole-Body Doses in Unrestricted Areas from Direct Radiation The major source of direct radiation (including sky shine) from the station is due to N-16 decay in the turbine building. Because of the orientation of the turbine building on the site, and the shielding effects of the adjacent reactor building, only the seven westerly sectors (SSW -
NNW) see any significant direct radiation.
High pressure ionization chamber (HPIC) measurements have been made in the plant area in order to estimate the direct radiation from the station.
The chamber was located at a point along the west site boundary which has been determined to receive the maximum direct radiation from the plant.
E
~" ~
..............-a........
Using measurements of dose rate made while the plant operated at different power levels, from shutdown to 100 percent, the total integrated dose from direct radiation over each three month period was determined by considering the quarterly gross megawatts generated. Field measurements of exposure, in units of Roentgen, where modified by multiplying by 0.6 to obtain whole body dose equivalents, in units of rem, in accordance with recommendations of RASL report 305(6) for radiation fields resulting from N-16 photons.
Estimates of the population exposure from direct radiation during
. . . the third and fourth quarters have been made out to two miles. Beyond two miles, the dose from the turbine building is negligiole. As a result, the estimated population dose for each of the two quarters respectively was approximately 1.6 x 10-2 and 1.3 x 10-2 person-rem, for a total population of about 351 persons. The estimated direct radiation dose at the maximum, site boundary location was approximately 2.8 mrem for the third quarter of 1979, and 2.3 mrem for the fourth. These hypothetical individual doses assume a 100 percent occupancy factor, taking no credit for the shielding effect of any residential structure. Table 7 summarizes these results.
4.5 Whole-Body Doses to the General Population from all Receiving Water Related Pathways Using the liquid pathway whole-body dose model discussed in Section 4.1, an estimate of the population dose due to the third quarter liquid t
. batch release has been calculated. The dose per kilogram of fish ingested at the site of the maximum individual (see Section 4.1) was assumed to apply to the entire yield of fish within fifty air miles of the plant. No credit was taken for radionuclide loss by sedimentation or further dilution by
- - - - -- _ . . . . . . . . - ~ . . . . - . .. . _ . . . . . ._
4 tributaries below Vernon Dam nor for the biological removal and decay of activity in the fish during the time periods when no radioactivity was being discharged from the plant.
A 1975 creel census of the Deerfield River, which is a stocked tributary of the Connecticut River downstream of the plant, reported an annual average catch of 431 fish per river mile in a 28 week season. The average weight of these fish was conservatively estimated to be equivalent to one pound of edible flesh. Assuming that there are 100 downstream river
~ ~~
miles within 50 miles of the plant, the yearly yield of edible fish mass in the Connecticut River may be estimated as:
431 fish / mile x 52 weeks x 1 lb. x 0.453 Kg x 100 miles 28 weeks year fish lb.
- 3.6 x 104 Kg/ year '
Fishing activity is greater on the Deerfield River than on the Connecticut River because the stocked fish attract more sport fishing activity. If it is assumed that one-half of the annual fish catch is caught and con need in the quarter, the resulting calculation yields a quarterly population dose commitment of 3.5 x 10-3 person-rem for a population made up of adults (62.6 percent), teenagers (11.9 percent) and children (23.7 percent).
m
- - . . ~ . .
4.6
_ Doses to the General Population and Average Individual Within Fif ty Miles from Caseous Effluents Using site meteorological data in Tables 4 and 5, quarterly average I/Q values were determined for each sector formed by placing radial rings from the plant at distances of one, two, three, four, five, ten, twenty, thirty, forty and fifty miles, and their intersection with radial lines drawn to form each of the sixteen principal compass directions. For noble gases, whole-body and skin doses were calculated for each sector and
.. multiplied by the estimated population within each sector to determine the sector person-rem.
No credit for decay in transit of activity was assumed.
For the approximately 1.1 x 106 people within fifty miles of the plant, the third and fourth quarter whole-body doses from noble gas cloud ~
exposure were estimated to be 1.3 person-rem and 0.5 person-rem, respectively.
For the same two quarters, the average individual whole-body doses were 1.1 x 10-3 mrem and 4.5 x 10-4 mrem, respectively. The skin doses for the two quarters were 2.1 person-rem and 0.95 person-rem, respectively.
The average individual skin dose was 1.8 x 10-3 and 8.2 x 10-4 mrem for the third and fourth quarters.
Table 7 also indicates the population whole-body and thyroid dose connitments from radioactive iodine and particulates (including tritium) released from the plant in gaseous vaste. The pathways of exposure which
, have been considered for the 50 mile population include inhalation, ingestion of vegetables, milk and meat produced within 50 miles, and the direct exposure to activity deposited on the ground plane. The total whole-body andthyroiddosecommitmentsforthethirdquarterverecalcukatedtobe 9
+ . .- . .. .....
l.1 x 10-2 person-rem and 6.3 x 10-2 person-rem respectively. For the fourth quarter, these doses were 9.4 x 10-2 person-rem and 0.11 person-rem respectively.
e e
g e
4 9
e f
^~ ~
-- ~ . ~ . ~ . ' . - --. . '.: ~.~.:. ~... ... ...... .. - . . .
REFERENCES
- 1. Regulatory Guide 1.111. "Hethods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-
~
Water-Cooled Reactors", U.S. Nuclear Regulatory Commission, Office of Standards Development, March 1976.
- 2. Meteorology and Atomic Energy, 1968, Section 5-3.2.2, " Cloud Depletion",
pg. 204. U. S. Atomic Energy Commission, July 1968.
- 3. C. A. Pelletier, .and J. D. Zimbrick, " Kinetics of Environmental Radiciodine Transport Through the Milk-Food Chain". Environmental Surveillance in the Vicinity of Nuclear Facilities, Charles D. Thomas Publishers, Springfield, Illinois, 1970.
- 4. " Supplemental Information for the Purposes of Evaluation of 10CFR Part
.: 50, Appendix I", Vermont Yankee Nuclear Power Corporation, June 2, i
~~
1976. .
- 5. Regulatory Guide 1.109, " Calculation of Annual Deses to Man From Routine Release of Reactor Effluents for the Purpose of Evaluating Compliance with 10CFR Part 50, Appendix I", U. S. Nuclear Regulatory Commission, Office of Standards Development, Revision 1, Octobtr 1977. ,
- 6. W. M. Lowder, P. D. Raf t, and G. dePlanque Burke, " Determination of.
N-16 Camma Radiation Fields at BWR Nuclear Power Stations", Health and Safety Laboratory, Energy Research & Development Administration, Report No. 305, May 1976.
7.
NUREG-0473, " Radiological Effluent Technical Specifications for Ei'9.'s",
Revision 2, July 1979; Table 4.11-1, notation f.
B e
1 TABLE lA VERMONT YANKEE EFFLQENT AND WASTE DISPOSAL SEMI ANNUAL REPORT JULY - DECEMBER 1979 CASE 0US EFFULENTS - SUMMATION OF ALL RELEASES Unit Quarter Quarter Est. Total 3 4 Error, %
A. Fission & activation gases k-
'~~
1.Totai Eelease" Ci
- 2. Average release rate for period <7.91E2 <7.78E2 1.0 E2 3.
uCi/sec <1.01E2 <9.89El Percent of technical specification limil % <1.24E-1 <8.47E-2 B. Iodines
%n
~
- 1. Total iodine - 131 Ci 3.16E-3
- 2. Average release rate for period 6.56E-3 5.0 El uCi/sec 4.02E-4 8.34E-3
- 3. Parcent of technical specification limit % 8.37E-2 1.74E-1 C. Particulates
- 1. Particulates with half-lives Ci 1.39E-3
- 2. 1.52E-2 5.0 El i Averaee release rate for oeriod uCi/sec 1. 76E-4 5.25E-4 j 3. Percent of technical specification limit
, 4 Cross alpha radioactivity
% 1.29E-2 8.54E-2 C1 1.71E-7 1.87E-7 D. Tritium f
- 1. Total release Ci 7.60E0 2.56E0 I 5.0
. 2. Average release rate for period E1 I uCi/sec 9.66E-1 3.25E-1
- 3. Percent of technical specification limit % N.A.
N.A.
)
e 8
8
- - - ' ~
TABLE IB EFFLUENT AND WASTE DISPOSAL SEMIANNUAL JULY - DECDiBER 1979 GASEOUS EFFLUENTS - ELEVATED RELEASE E CONTINUOUS MODE BATCH MODE *(2)
Nuclides Released t u Unit Quarter 3
Quarter Quarter 3
s 4 Quarter
- 1. Fission gases 3 f
~
krypton-85 - ~~
)
l krypton-85m Ci - * (l)
I I
krypton-87 Ci *(1) E
<2.99EO <3.43E0 E kryp ton-88 Ci <1.49El- E Ci <1.05El E [
xenon-133 <1.03El E Ci <8.29E0 E xenon-135 <7.78E1 E _
Ci <2.85E2 E xenon-135m <2.21El <1.60El E E
xenon-138 Ci <l.30E2 <9.67El E_ _ E
_Ci <5.33E2 Others (specify) ~ Ci- <3.58E2 E _
E E E Ci E E l E E Ci E E unidentified Ci E E E
E i
Tota {for period E E E
l Ci E E ]
i
<7.91 E2 { <7.78E2 E
- 2. Iodines l E <
E t
iodine-131 iodine-133 1
Ci t 3.16E-3 I Ci 6.56E-3 I iodine-135 5.14E-3 E '
E '
u Total for period Ci 2.00E-3 2.62E-3 4.72E-3 E
E 3 Ci i 1.09E-2 E l
1.33E-2 E
- 3. Part.'culates E 1 E 1 3
st ron tiem-89 ;
i Ci 5.01E-5
\
strontiun30 Ci 5.1BE-4
\
1 cesium-li4 2.18E-6 1.32E-6 E
E cesium-137- Ci 2.54E-4 E Ci 3.91E-4 E
- barium-lanthanum-140 2.15E-4 6.65E-4 E
E cobalt-58 Ci 3.46E-4 E 1.29E-4 _ _ E cobalt-60 _
Ci 2.23E-3 8.39E-4 E
E '
zinc-65 Ci 3.15E-4 E ,' '
E manganese-54 Ci _2.03E-4 8. 32 E--] E L C1 3.04E-3 E cerium-139 2.47E-5 1.71E-4 E E L cerium-134 Ci E j_ 7.60E-6 < 2.83E-5 E Ci i<4.07E-5 i 1.61E-5 t E E
(
- (1) Kr00 j
- (2) No Batch mode es for *** -
releasnot detected in offgas y = 6.79E-7 mix-limit uCi/cc of detecta
,.-7-----, ,__ ,__;___,_,_,
TABLE IC VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT - 197 JULY - DECEMBER CASEOUS EFFLUENTS - ROUTINE CROUND LEVEL RELEASES
- There were no routine measured ground level continous, or batch mode gaseous effluent releases during the reporting period. -
J e
O e
t
TABLE ID
- VERMONT YANKEE EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT - 1979 JULY - DECEBER GASEOUS EFFLUENTS - NON-ROUTINE RELEASES
- There were no non-routine or accidental gaseous effluents releases.
during the reporting period.
t 8
I t
t o
TABLE 2A EFFLUEhT AND WASTE DISPOSAL SEMIANNUAL REPORT JULY - DECEMBER 1979
. LIQUID EFFLUENTS - SU5MATION OF ALL RELEASES Unit Quarter Quarter 3
Est. Total 4 *1 Error, 't.
A. Fission and activation products
- 1. Total relecse (not including tritium, gases, alpha)
Ci 2.40E-4
- 2. Average period diluted concentration during 15.0E1 I pCi/ml 7.16E-10
- 3. Percent of applicable limit % s 7.I6E-1 B. Tritium
- 1. Total release
._ Ci 4.04E0
- 2. Average diluted concentration during 5.0El period
- 3. Percent of applicable limit VCi/mi 4.16E-6
% 1.38E-1 C. Dissolved and entrained gases
- 1. Total release C1 1.06E-1
- 2. Average period diluted concentration during i5.0El
- 3. Percent of applicable limit UCi/ml 1.62E-7 4.05E-1 D. Gross alpha radioactivity
- 1. Total relt ase '
Ci *2 t5.0El E. Volume of waste released (prior to dilution) liters I A1.0 El F. Volume of dilution water used during period liters
- 1 .
No Liquid Effluents for 4th Quarter 1979 -
- 2 No alpha detected, Minimum sensitivity - <9.00x10~II uci/ml o
TABLE 2B EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT JULY - DECDGER 1979 LIQUID EFFLUENTS -
5 CONTINUOUS MODE *1 BATCH MODE *2 Nuclide., Released Unit Quarter Quarter Quarter Quarter 3rd 4th 3rd. 4th strontium-89 Ci <4.84E-6 strontium-90 Ci 2.71E-6
, cesium-134 Ci <8.62E-6 cesium-137 C1 <1.08E-5 iodine-131 Ci <6.68E-6 cobalt-58 Ci <1.10E-5 cobalt-60 Ci <1.54E-5 iron-59 Ci <2.58E-5 zine-65 Ci <2.89E-5 manganese-54 Ci 5.85E-5 chromium-51 Ci <5.03E-5 zirconium-niobium-95 Ci <2.27E-5 molyb<lenum-99 Ci <2.90E-6 technetium-99m Ci <3.09E-6 barium-Janthanum-140 Ci <3.21E-5 cerium-141 Ci <5.66E-6 9
Other (specify) Ci Ci Ci Ci Ci unidentified Ci i
Total for period (above) Ci e
<2.90E-4 xenon-133 Ci 2.92E-2 xenon-135 '
Ci 7.64E-2
- 1 No continuous mode releases.
- 2 No 4th Quarter batch releases.
.-.------..~.--..--.-. -.
TABLE 3 EFFLUENT AND WASTE DISPOSAL SE!!IANNUAL REPORT JULY - DECEMBER 1979 SOLID WASTE AND IRRADIATED FUEL SHIPMENTS A. bOLID h'ASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSA
- 1. Type of waste Unit 6-month Est. Total Period Error, % ,
- a. Spent resins, filter sludges, evaporator m3 3.59El bottoms, etc. Ci + 7.5El 7.01E2 -
- b. Dry compressible waste, contaminated m3 1. 72El
, equip, etc. Ci
+ 7.5El 1.87E0 -
- c. Irradiated components, control m3 0 rods, etc.
Ci 0 mb 0
- d. Other (describe) Ci 0
- 2. Estimate of major nuclide composition (by type of waste)
- a. Ce-141 % 4.69E-2 I.131 % 1.04E-1 Cs-134 % 2.90E+1 Ba-140 % 5.18E-1 Cs-137 % 5.llE+1 .Cr-51 % 4.51E-2 Co-58 % 7.31E-1 Zr-95 % 1.27E-2 Mn-54 % 2.67E-1 ' I-134 Zn-65
% 5.71E-3
% 1.21E-1 Mn-56 % 5.50E-3 Co-60 % 1.71E+1 i r,-110 % 1.54E-3
- b. Cs-134 % 2.31E+1 '
Mn-54 %
Cs-137 '
2.45E0
% 4.08E+1 Zn-65 % 8.38E0 Co-58 9.80E-1
' % Co-60 % 2.43E+1
- c. % %
- d. g g
- 3. Solid Waste Dispo'ition s
, Number of Shipments Mode of Transportation Destination -
9 Truck Chem-Nuclear
, Barnwell, South Carolina B. IRRADIATED FUEL SHIPMENTS (Disposition)
Number of Shipments Mode of Transportation
- Destination None a
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- - O JJ w 4 OOO SOS mhm OOO OOO SOO SOO m>p JJ K U 99 99 O@ OO 90 99 99 e9 g 4 4 4 e e O e e o e e o e e e e e o e e m DO @@ e 09
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- i. O & eww uww Www tww sww eww e e & M ww www Wu d h w S a O > e AE D F G m m w n aM N w W EM M me 8
m J mm O J m ew 4 mw
- 7. .. < - . . . . . . _ . - . - - .
4....-.-====- - - - - - . - . - . -
- '. as.
e w ... %!y}{ D h_ 3 h@ f$a .o. ... .NN hmm N.. .-- N.. 4 OO MSG hew Nem FNN mer mee - e e M e e e** ee e 600 u m o e m o e o e N e e DO em op we 9e er mm NGO m mm MM NN mm OO ,E mm & E J 300 300 000 coo m #G Om OO 333 000 eso esO 3 90 00 OO OL OO e 3 e e e e e e e e e e e e e e > Oo OO OC e o e OO OO OO DO em E OOS ONN emm O 044 mNN Nmm woo One > K E 00 e e ese Wee emm WNN eFF mmm mee e e o e e m o e e e e o e e e o e 00 == ee ee mm mm J OO e NN 3 a DoD emm D e*, mee eSe eGe Dee Omm Wee do OO Mpp err Wem emm mmm mee FOO e e e e e e e e o e o e o e m o e OO mm 3 NN NN wm FF u O a pmm 2 9 2 300 eee epp moe Wee ede wh> 4 e OO ee Nam =OO hem New mM 944 & a e o e e e o e e e e o e e e - e e > O Oe == O NN MM - ==
- WW a e 2 000 moo >>> ese e e se -me m>>
ehh MDP mem eNN w e e e e mer NNN mem OO chh J m e o e e e e e e e e e e e . . . . . . _ , . mm y y .De -. um ee O ._ 4 W W X eOS ese mOC W u e GO mm =pp hhh Mew MOO DOO ekh & -h> mm OO DO e e & *
- e e o e e e o e e e e e MMM e e w OO OO E OO == O w &
= 3 000 e>> M y > e eNN mee ese mye con mee d > u 90 NN mee mee mm 90 OO S00 w e e e e e e e e e e e e u 4 De e e e e w w DO NN L O. 3 E J ep O g E too mee ese Neo won wem mem NNN p 3 m a e OO mer med NOO wer E L e e e e e e e s e 99 OO een e m e e e e o e e e e DO == E > 2 NN u' h a Q s u e = m ooO mee ehh === @ D 4 h OO NOC FNN -NN mee ooo mmm w J u e e e e o e OPP - e e DNN mem GO eOO W W w OO == o e o e e e N e o y NN es MM OO 3 e W N se N. e < J G w Oee b w - c o. o m e. e. m. m= = m e n, see se.e , o e .. .m m.--m. . m. N. W. . == ee m. m .Oe - .. . . e m. N w 4 oO em se J = NN 3 == 3 w S00 emm e@ e Mmm w e e@ mee RO O ewe med mm Nee mem Nee a - e e e e WO 90 err u a e e e e b o e e e e e J em NN ee w- N e e OO u 3 J Me a g wm um E w OOO Nem gw c e m e oO mee meen== mem oneNN eso on op Geo om ees NNN && a w e o e e e e e e o e e o W e oc == -m em og e e e o em 3 J eO NN == e u KK = m emo mee e>> 9c0 000 000 ph e > .t e nt e hn ec 000 eNN = > #E *s c *ts nP P es e e e e e e e e e e o e a = .e e == e o e e og
J eo se se me == mm u
n, w een mem mee noe woo poo me
> = 4 Om Ne* -- en ooo eve se u > OO oO oO uu w * * * *
- e * * * *
- e e e Noe 4 w eO e9 * * ==
w OO en so == ww a em
- a w een om- men eso -em >>
w ee eeO one Neo *za 4 New OO SO en oO eo 2 * * * * * * * * *
- Neo ww m so
- e
- e * * ##
. se ao ao == az
.
- QQ a w 000 ese New WNN mem som one are j m 3 e .
d 2
eO e e N==
e e mer e e mm e e ao e e em om ean ouo 00 m e e o e e 33 7 se ==
We me e NN w u.
W D w a goo see NNN JJ a O em mem ese See em" mFP
-em eenOO eso kmm sa a g e e e e e e ** e e e o Se mme eg
% m e e e o e eO ** NN NN OO ce
> & MM k%
m
, uu d b m gmm mmm ham Nam ema emm MM Q E JmN 3-N tmN saa emm ZZ
& O
- N ==N N=N N=N OmN we g a a gww uww aww Swa tw= tww ww www wu w
a u e M e - w me w
- F G a - e a we N w e h%
w W e s J mm e a -N
= w&
-I TABLE 6 VERMONT YANKEE l!
QUARTERLY AVERACE X/Q, D/Q AND CAMMA I/Q VALUES FOR SELECTED RECEPTORS POINT OF INTEREST t THIRD QUARTER FOURTH QUARTER Maximum offsite ground Location: ;
1evel air concentration WNW 1.5 mi Location: i location X/Q (undepleted)*: 4.904x10-}es NW 2.5 mi1
- X/Q (depleted)*: X/Q (undepleted): 4.811x109s 4.882 x 10-7 X/Q (depleted):
D/Q**: 9.418 x 10-10 4.588 x 10-7
- i Camma X/Q:* D/Q: 1.290 x 10-10 .
2.211 x 10-7 ,
Camma X/Q: 2.347 x 10-7
- For whole body and skin ,
doses from noble gases
- 1) Maximum site boundary t
Location: S 0.24 mi location X/Q (undepleted): 2.10x10-ges Location: N 0.25 mi X/Q (depleted): 2.10 x 10-9 X/Q (undepleted): 3.04x10-gs i D/Q: X/Q (depleted): 3.04 x 10-II t
1.03 x 10-II D/Q: ,
Camma X/Q: 7.38 x 10-7 2.90 x 10-13 ,
Camma X/Q: 5.38 x 10-7 ',
- 2) Maximum nearest Location:
residence S 0.33 mi Location:
X/Q (undepleted): 3.65x10ges S 0.33 miles '
X/Q (depleted): X/Q (undepleted): 5.58 x 10-10 3.65 x 10-9 X/Q (depleted):
D/Q: 2.00 x 10-II 5.58 x 10-10 D/Q: 4.17 x 10-12 Camma X/Q: 5.41 x 10-7 For organ doses from Camma X/Q: 3.21 x 10-7 iodine and particulates in gaseous effluents -
- 1) Maximum farm location Location: 1 SSE 3.5 m Location:
X/Q (undepleted): 2.84x10-}1es SSE 3.5 mi -
e X/Q (depleted): X/Q (undepleted): 2.42x10-}1es 2.80 x 10-7 X/Q (depleted):
D/Q: 9.71 x 10-II 2.37 x 10-7 D/Q 1.02 x 10-9 Camma X/Q: 1.82 x 10-7 Camma X/Q: 1.58 x 10-7 G
,i
. v - . ... g
. t i
TABLE 6 (continued) \
POINT OF INTEREST i s
TillRD QUARTER . \
FOURTil QUARTER a !
- 2) Maximum nearest residence Location: SSE 1.3 a .
X/Q (undepleted): 8.27x10gles Location: SSE 1.3 m X/Q (depleted): X/Q (undepleted): 8.35x10gles .,
8.25 x 10-8 X/Q (depleted): ,' :
D/Q: 4.63 x 10-10 8.33 x 10-8 , i D/Q: 5.74 x 10-10 i Camma X/Q: 2.82 x 10-7 ,
Camma X/Q: 2.44 x 10-7 l I
- 3) Maximum site boundary Location:
location SSE 0.53 Location:
i X/Q (undepleted): 4.33x10-giles SSE 0.53 X/Q (depleted): X/Q (undepleted): 6.67x10-giles
- 4.32 x 10-8 X/Q (depleted):
D/Q: 2.82 x 10-10 6.66 x 10-9 -
l Camma X/Q: 5.47 x 10-7 D/Q 6.90 x 10-II i Camma X/Q: 4.49 x 10-7 l Depleted and undepletedX/Qs and Gamma X/Q are in units of sec./m 3 Delta (D/Q) in units of 1/m2
~
TABLE 7
SUMMARY
OF RADIOLOGICAL IMPACT ON MAN
' Vermont Yankee Nuclear Power Station :
Third and Fourth Quarters, 1979 t
EST1 HATED THIRD ESTIMATED FOURTH 1
TENTIAL PATHWAY OR TYPE OF EXPOSURE '
QUARTER DOSE !
QUARTER DOSE . '
COMMITNENT COMMITMENT l {
Maximum individual whole body and Whole Body critical organ doses from receiving- 3.2 x 10-6 ! I water exposure pathways from 2.6 x 10-6 (adult) liquid releases (arem). teen) No liquid releases ,
2.2 x 10-6 ((child)
Castro-Intestinal- l i
Lower-Largg 4.2 x 10- (Intestine '
3.0 x 10-6 teen)
(adult) ,
1.8 x 10-6 (child)
A. Whole body and skin doses to individuals exposed at point '
of maximum offsite ground I 1evel air concentration of radioactive noble gaseous l effluents i (at WNW, 2400m) (at NW, 4000m)
- 1. Skin dose (arem)
- 11. 6.9 x 10- 4.9 x 10-2 Whole body dose (ares) 3.0 x 10-2 2.2 x 10-2 B. Whole body and skin doses at maximum site boundary location from radioactive noble gaseous ef,fluents (at S, 0.24 miles) (at N, 0.25 miles)
- 1. Skin dose (area)
- 11. Whole body dose (area) 9.9 x 10-2 5.0 x 10-2 9.9 x 10-2 5.0 x 10-2 C. Whole body and skin doses at maximum nearest residence ,-
from radioactive noble gaseous ,
effluents.
(at S, 0.33 miles) (at S, 0.33 miles)
- 1. Skin dose (mrem)
- 11. Whole body dose (arem) 7.3 x 10-2 3.0 x 10-2 7.2 x 10-2 1.0 , in-2
.- i'
- \
8 TABLE 7 (continued) ii 50TENTIAL PATifWAY OR TYPE OF EXPOSURE ESTIMATED TIIIRD F .TIMATED FOURTil '
QUARTER DOSE QUARTER DOSE '
COMMITMENT COMMITMENT
- 11. Organ doses to individuals from .
radioactive lodine and particulates .
in gaseous effluents (including tritium). ,
A. Maximum farm location e
' i Maximum individual whole body !
and organ doses from all pathways (at SSE, 3.5 miles) (at SSE, 3.5 miles) i i.
Bone (mrem) {
, 11. Thyroid (arem) 1.1 x 10-3 .
4.9 x 10-2infant)
((child) 8.2 x 10~3 child) !
111. CI(LLI) (arem) 8.1 x 10-3 ((child) iv. Whole body (arem) 8.6 x 10~4 (child) 7.4 x 10~3 teen) !
1.0 x 10-3 (child) 7.3 x 10-3 ((child) !
B. Critical organ doses to maximum nearest resident from the inhalation, lngestion and ground plane exposure of iodine and particulates (at SSE, 1.3 miles) (at SSE, 1.3 miles)
- 1. Bone dose (mrem)
- 11. Thyroid dose (mrem) 3.7 x 10~4 (child) 111. CI(LLI) (arem) 1.7 x 10-3 4.4 x 10-3 child) iv.
Whole body as critical organ 2.8 x 10-4 (child) 4.3 x 10~3 ((child)
(mrem) 3.2 x 10-4child)
((child) 4.0 x 10~3 teen) 3.9 x 10-3 ((child)
TABLE 7 (continued) '
- l POTENTIAL PATifWAY OR TYPE OF EXPOSURE ESTIMATED TIIIRD !
ESTIMATED FOUR1H QUARTER DOSE !
QUARTER DOSE '
COMMITHENT COMMITMENT '
,I C.
Organ doses to individuals at point of maximum ground level air l-concentration of gaseous effluents ,
from inhalation and ground exposure .
of iodine and particulates e .
(at VNW, 2400m) -
i.
(at NW, 4000m)
Bone dose (arem) ,'
- 11. Thyroid dose (arem) 3.4 x 10-4 (teen) 1.6 x 10'3 8.2 x 10-4 111. GI(LLI) (arem) 2.5 x 10-3 (child) iv.
Whole body as critical organ (mrem) 4.8 x 10 (child) teen) 8.8 x 10~4 (child)
I S 4.8 x 10-4 ((teen) 8.5 x 10-4 adult
((adult) -
j
' D. Organ doses to individuals at or teen) j point cf maximum site boundary air concentration of gaseous !
effluents from Inhalation and ground exposure of iodine ' }
and particulates .
(at SSE, 0.35 miles)
- 1. (at SSE, 0.53 miles) ,
Bone dose (arem)
- 11. Thyroid dose (mrem) 9.9 x 10-5 (all) .
4.2 x 10~4 111. GI(LLI) (arem) 2.1 x 10 (child) 4.4 x 10-4 (all) iv. Whole body as 1.1 x 10'4 (all) 4.2 x 10~4 (child) critical organ 1.1 x 10-4 (all) 4.2 x 10-4 all)
((all) t
- -i 1
1 TABLE 7 (continued) l
, I i i i
ESTIMATED TIIIRD ESTIMATED FOURTH
'OTENTIAL PATilVAY OR TYPE OF EXPOSURE k QUARTER DOSE QUARTER DOSE COMMITMENT !
COMMITHENT l
V. !
Whole body doses to individuals and I populations in unrestricted areas i i
from direct radiation from the :
g facility.
i e A. Maximum site boundary (mrem)
(west of turbine -
building) 2.8 2.3 ! >
B. Population dose (person-rem) 1.5 x 10-2 1.3 x 10-2 Whole body dose to the population from all receiving-water related pathways from liquid releases.
(person-rem). ,
3.5 x 10-3 No liquid releases t
- . . ~ . - . . . . . . ,
. ;1 9 . hh
(
il
, i, TABLE 7 (continued) l l
f' i
POTENTIAL PATHWAY OR TYPE OF EXPOSURE ESTIMATED THIRD ESTIMATED FO!!RTH i li i QUARTER DOSE l ';
QUARTER DOSE COMMITMENT [
COMMITNENT e .l VI.
I!
A. ~ ! ,!
Whole body doses to the population
and average individual out to 50 l'
'I alles from noble gaseous ! i I,'
effluents i t *
- 1. Whole body dose to population 1 l (person-rem) l
- 11. 1.3 !
Average individual whole body , 5.1 x 10-I '
dose (mrem) ,
111. Skin dose to population 1.11 x 10-3 4.5 x 10-4 i (person-rem) iv. Average individual skin dose 2.1 9.5 x 10-I (arem) ,
1.8 x 10-3 8.2 x 10-4 B. Organ doses to 50 mile popula- ;
tion, and average individual, '
from inhalation, inge,' tion of milk, meat, and vegetables, and ground exposure to iodine and parti-culates in gaseous effluents *
- 1. Thyroid population dose (person-rem)
- 11. Ayerage individual thyroid 6.3 x 10-2 1.1 x 10-I dose (mrem) iii. Whole body population dose 5.5 x 10-5 9.2 x 10-5 (person-rem) .
iv.
Average individual whole body 1.1 x 10-2 9.4 x 10-2 dose (mrem) 9.5 x 10-6 .
8.2 x 10-5
APPENDIX A EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT Supplemental Information July - December 1979 Facility: Vermont Yankee Nuclear Power Station Licensee: Vermont Yankee Nuclear Power Corporation
_ 1. Regulatory Limits
- a. Fission and activation gases: 0.08/E7 Ci/sec.
- b. Iodines: 0.48 pC/sec.
- c. Particulates, half-lives >8 days:
1.6E+3 MPCa Ci/sec.
- d. Liquid effluents:
1.03-7 uC/ml (HTO: 3.0E-3 pC/ml, dissolved Noble gases:
4.0E-5 uC/ml). isotopic limits are found in 10CFR20 App. B, Table II, Column 2.
- 2. Mar.imum Permissible Concentrations
. Provided below are the MPC's used in determining allowable release rates or concentrations.
- a. Fission and activation gases: No MPC limits
i N
, 2.'-...,........-.................-..
c.
Particulates, half-lives >8 days: See 100FR20, App. B, Table II, Column
- d. Liquid effluents: See 10CFR20, App. B, Table II, Colucm 2.
. 3. Average Energy Provided below are the average energy (I) of the radionuclide mixture in releases of fission and activation gasses, if applicable.
- a. Average gamma energy: 3rd Quarter 0.987 MeV/ Dis.
4th Quarter 0.685 MeV/ Dis.
- b. Average beta energy: Not Applicable 4.
Measurements and Approximations of Total Radioactivity ,
Provided below are the methods used to measur, or approximate the total radioactivity in effluents and the methods used to determine radionuclide composition.
a.
Fission and Activation Cases Daily samples are drawn at the discharge of the Air Ejector.
Isotopic breakdown of the releases are determined from these samples. A logarithmic chart of the stack gas monitor is read daily to determine the gross release rate. At the very low release
. rates normally encountered during operation with the Augmented Off Cas system the error of release rates may be approximately 2'
+ 100%. -
- b. Iodines Continuous isokinetic samples are drawn from the plant stack through a particulate filter and charcoal cartridge. The filters and cartridge are removed weekly (if releases are less than 4%
of the Tech Spec limit), or daily (if they are greater than 4%
of the limit), and are analyzed for radioicdine 131, 132, 133, 134, and 135.
5 The iodines found on the filter are added to those on the charcoal cartridge. The error involved in these steps may be approximately 150%.
- c. Particulates The particulate filters described in b. above are also counted -
for particulate radioactivity. The error involved in this sample is also approximately 150%.
- d. Liquid Effluenta Radioactive liquid effluents released from the facility are continuously rionitored.
Measurements are also made on a representative sample of each batch of radioactive liquid effluents released.
For each batch, station records are retained of the total activity (mci) released, concentration (pCi/ml) of gross radioactivity, volume (liters), and approximate total quantity
. . of water (liters) used to dilute the liquid effluent prior to release to the Connecticut River. r M
. -p - _ . - - - . . . . . - . . . .
- -- - - . - - - - - ~ . . . ~ . .. . . . . .
Each batch of radioactive liquid effluent released is analyzed for gross gamma and gan=a isotopic radioactivity. .A monthly proportional composite sample, comprising an aliquot of each batch I
released during a month, is also analyzed for tritium, SR-89, SR-90, gross beta and gross alpha radioactivity, in addition to gamma spectroscopy.
There were no liquid releases during the reporting period.
t ~
. . . . . ~ 5..' Batch Releases~
- a. Liquid
- 1. Number of batch releases: 16 ".
- 2. Total time period for batch releases: 14,490 min.
- 3. Maximum time period for a batch release: 1,539 min.
- 4. Average time period for batch releases: 905 min.
- 5. Minimum time period for a batch release: 331 min.
- 6. Average stream flow during periods of release 4,063 cfs i
of effluent into a flowing stream:
- b. Caseous There were no routine gaseous batch releases during the repo,rting
' t
, period.
{
)
A4
~
- 6. Abnormal Releases
- a. Liquid There were no non-routine liquid releases during the reporting period.
- b. Gaseous There were no non-routine gaseous releases during the reporting period.
e 6
9 O
9 RE