ML18052B475: Difference between revisions
StriderTol (talk | contribs) (Created page by program invented by StriderTol) |
StriderTol (talk | contribs) (Created page by program invented by StriderTol) |
||
(2 intermediate revisions by the same user not shown) | |||
Line 3: | Line 3: | ||
| issue date = 01/25/1988 | | issue date = 01/25/1988 | ||
| title = Discusses Results of Evaluation & Survey of 871113 Flooding Incident at Plant,Per Util 871112 Request to Dispose of Soil Inplace,Per 10CFR20.302.Relocation of Activities to New Radwaste Facility Scheduled for Completion in 1988 | | title = Discusses Results of Evaluation & Survey of 871113 Flooding Incident at Plant,Per Util 871112 Request to Dispose of Soil Inplace,Per 10CFR20.302.Relocation of Activities to New Radwaste Facility Scheduled for Completion in 1988 | ||
| author name = | | author name = Bordine T | ||
| author affiliation = CONSUMERS ENERGY CO. (FORMERLY CONSUMERS POWER CO.), | | author affiliation = CONSUMERS ENERGY CO. (FORMERLY CONSUMERS POWER CO.), | ||
| addressee name = | | addressee name = | ||
Line 17: | Line 17: | ||
=Text= | =Text= | ||
{{#Wiki_filter:,.._, | {{#Wiki_filter:,.._, | ||
~*-* | |||
consumers Power l'OWERIN& | consumers Power l'OWERIN& | ||
lllllCHl&AN'S l'RO&RESS General Offices: 1945 West Parnell Road, Jackson, Ml 49201 * (517) 788-0550 January 25, 1988 Nuclear Regulatory Commission Document Control Desk Washington, DC 20555 DOCKET 50-255 -LICENSE DPR | lllllCHl&AN'S l'RO&RESS General Offices: 1945 West Parnell Road, Jackson, Ml 49201 * (517) 788-0550 January 25, 1988 Nuclear Regulatory Commission Document Control Desk Washington, DC 20555 DOCKET 50-255 - LICENSE DPR PALISADES PLANT - | ||
-REQUEST TO RETAIN SOIL IN ACCORDANCE WITH 10CFR20.302 Consumers Power Company letter dated November 12, 1987, requested zation to dispose of soil in place as specified by The letter included the results of a survey and evaluation performed in August, 1987. Following submittal of that letter, a cooling tower overflow on November 13, 1987 again flooded the South Radwaste Building. | SUPPLEMENT - REQUEST TO RETAIN SOIL IN ACCORDANCE WITH 10CFR20.302 Consumers Power Company letter dated November 12, 1987, requested authori-zation to dispose of soil in place as specified by 10CFR20~302. The letter included the results of a survey and evaluation performed in August, 1987. | ||
The flooding caused additional activity that necessitated Consumers Power Company to request placing our November 12, 1987 request on hold until further evaluation and surveys could be completed. | Following submittal of that letter, a cooling tower overflow on November 13, 1987 again flooded the South Radwaste Building. The flooding caused additional activity that necessitated Consumers Power Company to request placing our November 12, 1987 request on hold until further evaluation and surveys could be completed. This .letter includes the results of our evaluation and survey of the November 13, 1987 flooding incident and is intended to supplement our original November 12, 1987 request. | ||
This .letter includes the results of our evaluation and survey of the November 13, 1987 flooding incident and is intended to supplement our original November 12, 1987 request. Following the cooling tower overflow, a survey indicated additional activity had been released from the building. | Following the cooling tower overflow, a survey indicated additional activity had been released from the building. The building was being maintained in a non-contaminated condition to prevent this type of occurrence; however, during this period a destructive testing program on waste packages was being con-ducted in a small area of the building. The survey clearly showed the release of activity from the building adjoining the testing area. The top six inches of soil from the sectors adjoining the building were removed and packaged (588 cubic feet) to prevent additional dispersion of radioactivity. The area was then completely resurveyed. | ||
The building was being maintained in a non-contaminated condition to prevent this type of occurrence; however, during this period a destructive testing program on waste packages was being ducted in a small area of the building. | An evaluation of the August 1987 and November 1987 (post packaging) activities is attached. The survey indicates a drop of 49% in activities between the August and November surveys. We propose the activities specified in the November 12, 1987 submittal be used as justification for the request because they are conservative. In addition since the November 13, 1987 flooding and following the most recent survey the area was subject to heavy rains which could have diluted some activities to below minimum detectable activity (MDA is nominally lE-06 µC~/g). | ||
The survey clearly showed the release of activity from the building adjoining the testing area. The top six inches of soil from the sectors adjoining the building were removed and packaged (588 cubic feet) to prevent additional dispersion of radioactivity. | ~--"-1_ ..JL____. --r2s~~~~~1 r eeo201015s -s~g 00 _ 2 55 .( \ . J | ||
The area was then completely resurveyed. | \_:_**~DR_ ~~P~_K._0, -PDR "*LJ / *. | ||
An evaluation of the August 1987 and November 1987 (post packaging) activities is attached. | -. ', - Ji (\ .. *- - ' L OC0188-0018-NL02 | ||
The survey indicates a drop of 49% in activities between the August and November surveys. We propose the activities specified in the November 12, 1987 submittal be used as justification for the request because they are conservative. | |||
In addition since the November 13, 1987 flooding and following the most recent survey the area was subject to heavy rains which could have diluted some activities to below minimum detectable activity (MDA is nominally lE-06 | e Nuclear Regulatory Commission 2 Palisades Nuclear Plant Retain Soil in Accord. with 10CFR20.302 January 25, 1988 The one non-conservative value from our August survey and evaluation is the maximum dose rate at 18 inches' above the surface. The November survey value from MICROSHIELD is 1.17 mR/hr as opposed to 1.02 mR/hr. This small increase only slightly changes the radiation workers' conservative dose estimate from 4.08 mR/year to 4.7 mR/year. | ||
..JL____. | Following approval of this application, it is proposed to account for the most conservative values of activity, which was stated in the November 12, 1987 submittal, as an abnormal release in the semi-annual report. In order to prevent recurrence of these releases to the environment, Consumers Power Company is also committing to transfer radwaste activities from this area, except for high level vault use which is not a potential flooding release problem. | ||
r eeo201015s 2 | Relocation of these activities to a new radwaste facility is currently scheduled to be completed in 1988. | ||
Thomas C Bordine Administrator, Nuclear Licensing CC Administrator, Region III, NRC NRC Resident Inspector | A check in the amount of $150.00 was attached to our November 12, 1987 submittal pursuant to 10CFR170.12(c). | ||
-Palisades Attachment OC0188-0018-NL02 | Thomas C Bordine Administrator, Nuclear Licensing CC Administrator, Region III, NRC NRC Resident Inspector - Palisades Attachment OC0188-0018-NL02 | ||
Attachment A Consumers Power Company Palisades Nuclear Plant Docket 50-255 Evaluation and Survey Results Comparison Post November Flood and Packaging*Versus the November 12, 1987 Submittal MI0188-0001A-HP01 | |||
The most heavily affected sectors were I-10, I-11, J | |||
Core samples were-taken as far down as in.the 1986 and August 1987 surveys, and in some instances even further in this survey. Results showed that no activity was detected below 6 inches as shown in Figure 2. Table 1 and Table 2 show comparisons between the August and November 1987 soil surveys. Table 1 compares the depths, the. activities, the total cu.ft. and total µCi per sector. After the removal of soil, the November 1987 soil survey results showed approximately a 49.3% drop in total contaminated soil (cu.ft.) and a 51.1% drop in total µCi in comparison to the August 1987 survey results. In Table 2 the comparison is between sectors affected in each survey and the depth at which each of these sectors were sampled. No activity was detected past 6 inches in the November 1987 soil survey, in comparison to that of 18 inches detected in August Direct dose to an individual working in the affected areas was calculated using the MICROSHIELD code. The activities from sectors H-9 and J-9 were used for a dose at 18" inches above the surface. The dose rates from H-9 and-J-9 are 9.97E-6 R/hr and 1.17E-5 R/hr, respectively. | 'A' Cooling Tower - South Radwaste Flood In August of 1987, a resurvey was co.nducted of the soil at the South Radwaste Building and its adjacent areas. The resurvey was conducted to verify the l~cation of ground contamination and if any contamination migrated further into the ground since the 1986 survey. | ||
Therefore, a SO-hour occupancy in one week could result in a maximum exposure of .59 millirem. | After submittal of the 198) soil results and request to retain, in accordance with 10CFR20.302, 'A' Cooling Tower Basin overflowed again flooding the South Radwaste Building and outlying areas. Immediately following the occurrence, one liter sample was taken with no activity detected on the Multi-Channel Analyzer (MCA). Then, another complete survey was conducted which included at least two surface samples and core samples in every sector (Figures 1 and 2). | ||
Normal -occupancy of *this area is on an "as needed basis" and averages less than 8 hours/week per individual in contact with the contaminated soil. In reviewing the soil results between August and November 1987, the August 1987 soil survey remains more conservative based on the information shown on Tables 1 and 2. Therefore, the August 1987 soil survey still valid in support of our request to retain the soil in accordance with 10CFR20.302. | Surface sample results showed that activities have increased as well as new sectors contaminated. The most heavily affected sectors were I-10, I-11, J and K-9 (Figure lA).. To keep these areas from spreading, the t0-p 6" of each of these sectors was removed and placed in 6 LSA boxes (approx. 588 cu.ft) and stored for disposition at a later date. | ||
MI0188-0001A-HP01 | After removal of soil, the sectors were resurveyed (Figure lB) and core samples were taken in each sector in 6-inch increments. Core samples were-taken as far down as in.the 1986 and August 1987 surveys, and in some instances even further in this survey. Results showed that no activity was detected below 6 inches as shown in Figure 2. | ||
Table 1 and Table 2 show comparisons between the August and November 1987 soil surveys. Table 1 compares the depths, the. activities, the total cu.ft. and total µCi per sector. After the removal of soil, the November 1987 soil survey results showed approximately a 49.3% drop in total contaminated soil (cu.ft.) | |||
and a 51.1% drop in total µCi in comparison to the August 1987 survey results. | |||
In Table 2 the comparison is between sectors affected in each survey and the depth at which each of these sectors were sampled. No activity was detected past 6 inches in the November 1987 soil survey, in comparison to that of 18 inches detected in August 1987~ | |||
<HDA H-10 2.60E-6 <MDA <MDA 3.20E-6 <MDA <HDA H-11 3.75E-5 <HDA <HDA 8.45E-6 <HDA <HDA <HDA 3.22E-5 <HDA <HDA <HDA <HDA <MDA <HDA H-12 <HDA N/A 2.20E-6 N/A I-9 l.24E-5 <HDA <MDA 6.79E-6 <MDA <HDA I-10 <HDA <HDA 5.39E-6 <MDA <HDA <HDA <HDA <HDA <HDA <MDA <HDA <MDA <HDA <HDA | Direct dose to an individual working in the affected areas was calculated using the MICROSHIELD code. The activities from sectors H-9 and J-9 were used for a dose at 18" inches above the surface. The dose rates from H-9 and-J-9 are 9.97E-6 R/hr and 1.17E-5 R/hr, respectively. Therefore, a SO-hour occupancy in one week could result in a maximum exposure of .59 millirem. Normal -occupancy of *this area is on an "as needed basis" and averages less than 8 hours/week per individual in contact with the contaminated soil. | ||
<HDA <HDA I-11 <MDA' N/A <HDA <HDA <HDA | In reviewing the soil results between August and November 1987, the August 1987 soil survey remains more conservative based on the information shown on Tables 1 and 2. Therefore, the August 1987 soil survey ~s still valid in support of our request to retain the soil in accordance with 10CFR20.302. | ||
<HDA I-12 <MDA N/A 3.00E-6 N/A J-9 5.39E-6 <HDA <HDA 2.0SE-5 <HDA <MDA J-12 6.39E-6 <HDA <HDA 2.60E-6 N/A <HDA K-9 <MDA N/A 3.39E-6 <HD.A <HDA <MDA <HDA <MDA <HDA L-9 <MDA 6.77E-6 .<HOA <HOA <HDA N/A <HDA <HDA MI0188-0001A-HP01 Microshield | MI0188-0001A-HP01 | ||
================= | |||
CConsuMer's Power CoMpany -#0371 Page I File SOIL1 .MSH Run date: January 18, 1988 Run tiMe: | *.Table 1 Comparison Table Between Total Cu. Ft. and Total µCi August 1987 | ||
p.M. CASE: CONTAMINATED SOIL@ H-9 LOCATION <6 INCHES DEEP) GEOMETRY 11: Rectangular solid source -slab shields Distance to detector ....*.....**.....*....... | .Sector ff Sg,.ft. x DeEth ft 3 x g/ft 3 x µCi/g, = Total µCi E-11 375 0.5 187.5 48144 2.07E-6 18.7 E-13 . 375 0.5 187.5 48144 4.39E-6 39.6 H-9 625 1.5 937 *. 5 48144 4.79E-6 216.2 H-10 625 0.5 312.5 48144 2 .60E-6 . 39.l H-11 625 2.0 1250* 48144 3.75E-5 2256.8 I-9 527 0.5 263,5* 48144 l.24E"'."'5 157.3. | ||
X Source. width ............................. | I-10 . 275 1.5 412.5 48144 5.39E-6 107.0 J-9 . 450 0.5 225 . 48144 5.39E-6 58.4 J-12 200 0.5 100 48144 6.39E-6 30.8 L-9 . 150 1.0 150 48144 6. 77E-6 48 .9*. | ||
; .... W Source length ..*............................. | I-9 East 98 1.5 147 48144 l.40E-5 *99.1 4325 4173 3071.9 | ||
*1250 .*2256.8 = | |||
T2 | 73.57. of total activity November 1987 | ||
Urania UraniuM Water I .0 | *E-11 375 0.5 187.5 48144 l.80E-6 16.25 H-9 625 0.5 312.5 48144 . 4.35E-5 654.46 H-10 . 625 0.5 312.5 48144 3.20E-6 48.14 H-.11. 625. 0.5 . 312.5 48144 3.22E-5 . 484 .45. | ||
* Zirconiul'i | H-12 250 0.5 125 48144 2.20E-6 13.24 I-9 527 0.5 263.5 48144 6.79E-6 86.14 I-12 220. 0.5 110 48144 3.0E-6 15. 89 . | ||
J-9 450 0.5 225 48144 2.05E-5 222.06 J-12 200 0.5 100 48144 2.60E-6 12.52 K-9 216 0.5 108 48144 3 .39E-6 . 17.63 4113 . 2056.5 1570.78 | |||
= | |||
MI0188-0001A-HP01 | |||
Ta.ble 2 Survey Comparison Between August and. November 1987 Soil Surveys August 1987 November 1987 Sector Surface 6" 12" 18" 24" 30" 36 11 42 11 E-11 E-13 2.07E-6 l *.80E-6 | |||
.4.39E-6 | |||
<MDA | |||
<MDA | |||
<MDA | |||
<MDA | |||
<MDA | |||
<MDA | |||
<MI>A | |||
<MDA | |||
<MDA e | |||
<MDA N/A <MDA <MDA H-9 4 .19E-6 . <MDA .4. 79E-6 <HDA <HDA <HDA 4.35E-5 <HDA <HDA <HDA <HDA <HDA H-10 2.60E-6 <MDA <MDA 3.20E-6 <MDA <HDA H-11 3.75E-5 <HDA <HDA 8.45E-6 <HDA <HDA <HDA 3.22E-5 <HDA <HDA <HDA <HDA <MDA <HDA H-12 <HDA N/A 2.20E-6 N/A I-9 l.24E-5 <HDA <MDA 6.79E-6 <MDA <HDA I-10 <HDA <HDA 5.39E-6 <MDA <HDA <HDA <HDA <HDA | |||
<HDA <MDA <HDA <MDA <HDA <HDA <HDA <HDA I-11 <MDA' N/A | |||
<HDA <HDA <HDA <HDA I-12 <MDA N/A 3.00E-6 N/A J-9 5.39E-6 <HDA <HDA 2.0SE-5 <HDA <MDA J-12 6.39E-6 <HDA <HDA 2.60E-6 N/A <HDA K-9 <MDA N/A 3.39E-6 <HD.A <HDA <MDA <HDA <MDA <HDA L-9 <MDA 6.77E-6 .<HOA <HOA | |||
<HDA N/A <HDA <HDA MI0188-0001A-HP01 | |||
Microshield 3~02 | |||
================= | |||
CConsuMer's Power CoMpany - #0371 Page I File SOIL1 .MSH Run date: January 18, 1988 Run tiMe: ~:17 p.M. | |||
CASE: CONTAMINATED SOIL@ H-9 LOCATION <6 INCHES DEEP) | |||
GEOMETRY 11: Rectangular solid source - slab shields Distance to detector ....*.....**.....*....... X 60.960 CM, Source. width ............................. ; .... W 762. | |||
Source length ..*............................. L 762. | |||
Rectangular solid, thickness toward dose pt .. Tl 15. 240 . | |||
Thickness 6f second shield ......... ~ ......... T2 45. 720 | |||
*Source VoluMe: 8.84901e+6 cubic centiMeters MATERIAL DENSITIES Cg/cc): | |||
Material Source Shield 2 Air .001220 .001~20 AluMinuM Carbon 1 .70 Concrete Hydrogen Iron Lead LithiUM Nickel Tin TitaniuM Tungsten* | |||
Urania UraniuM Water I .0 | |||
* Zirconiul'i r | |||
. Page 2 e eiie: | |||
CASE: CONTAMINATED SOIL @ H-9 LOCATION (6 INCHES DEEP> | |||
SOfLi .MSH BUILDUP FACTOR: based o~ TAYLOR Method.* | |||
Using the. characteristics of the Materials in shield 1 | |||
* INTEGRATION PARAMETERS: | * INTEGRATION PARAMETERS: | ||
NuMber of lateral angle segMents (Ntheta).; | NuMber of lateral angle segMents (Ntheta).; .. . *5 NuMber of aziMuthal angle segMents CNpsi)... .. 5 NuMber of radial segMents (Nradius).... ....... 5 SOURCE NUCL IDES: | ||
.. . *5 NuMber of aziMuthal angle segMents CNpsi)... | Ba-i37M: 3.8493e-04 curies RESULTS: | ||
.. 5 NuMber of radial segMents (Nradius).... | Group Energy Activity Dose point .flux Dose rate | ||
....... 5 SOURCE NUCL IDES: Ba-i37M: 3.8493e-04 curies RESULTS: Group # | # CMeV) (photons/sec) MeV/(sq cM)/sec (Mr/hr) 1 .664 1 . 282e+07 4.808e+00 9.969e-03 2 | ||
3 4 | |||
* 4*. 808e+00 9.969e-03 | 5 6 | ||
7 8 | |||
solid source slab shields Distanc.e to detector ......................... . x 60.960 Source width ............................. , ... : w 762. Source length .. , ..*..*.. , ............ , .. *,.; .. L 548.640 Rectangular solid, thickness toward dose pt .. Tl 15.240 Thickness of second shield .............. ... . T2 45. 720 Source VoluMe: 6.37129e+6 cubic centiMeters Mat er"! al | 9 10 11 . | ||
*source Shield 2 . .001220 .001220 Carbon l.70 Con-crete Hydrogen * *Iron Lead LithiuM Nickel Tin Titaniul'l .Tungsten Urania UraniuM Water I .0 ZirconiuM | 12 13 14 15. | ||
.. Page 2 Ai* i* "' * "'1* T; ., M. <; H | 16 17 18 19 20 TOTALS: 1 . 282e+07 | ||
* 4*. 808e+00 9.969e-03 | |||
the characteristics of the Materials in shield 1. INTEGRATION PARAMETERS: | |||
NuMber of lateral angle segMents (Ntheta>..... | Microshield 3.02 (ConsuMer's Power CoMpany #037) | ||
5 NuMber of aziMuthal angle .segMents (Npsi ).. . . . 5 NuMber of radial segMents (Nradius) | Page File SOIL2~MSH Run date: January 18, 1988 Run tiMe: 4:26 p.M. | ||
... ... , . 5 SOURCE NUCLIDES: | CASE: CONTAMINATED ~OIL@ J-9 LOCATION ~6 INCHES DEEP> | ||
Co-S0: 8.9198e-05 curies RESULTS: .Group # | GEOMETRY 1 I: RectanQul~r solid source slab shields Distanc.e to detector ......................... . x 60.960 CM, Source width ............................. , ... : w 762. | ||
Source length .. , ..*..*.. , ............ , .. *,.; .. L 548.640 Rectangular solid, thickness toward dose pt .. Tl 15.240 Thickness of second shield .............. ~ ... . T2 45. 720 Source VoluMe: 6.37129e+6 cubic centiMeters MATERIAL DENSITIES (glee):~ | |||
Mat er"! al *source Shield 2 . | |||
Air .001220 .001220 AluMinuM Carbon l.70 Con-crete Hydrogen * | |||
FIGURE 18 I..., ' *"" I | *Iron Lead LithiuM Nickel Tin Titaniul'l | ||
.Tungsten Urania UraniuM Water I .0 ZirconiuM | |||
fOl . 1U11MCe AllEA IHIER ASl' | |||
.. Page 2 Ai* i* "' * "'1* T; | |||
~ _, * | |||
., M. <;'- H | |||
...J..l-l-'-* | |||
*CASE: CONTAMINATED SOIL@ J-9 LOCATION (6 INCHES OEEPI BUILDUP FACTOR: based on TAYLOR Method. | |||
U~ing the characteristics of the Materials in shield 1. | |||
INTEGRATION PARAMETERS: | |||
NuMber of lateral angle segMents (Ntheta>..... 5 NuMber of aziMuthal angle .segMents (Npsi ).. . . . 5 NuMber of radial segMents (Nradius) ... *~* ... , . 5 SOURCE NUCLIDES: | |||
Co-S0: 8.9198e-05 curies RESULTS: | |||
.Group Energy Activity Dose point flux Dose rate | |||
# (MeV) (photons/sec) MeV/(sq cril)/sec (Mr/hr) 1 1 .336 3.300e+06 3A 11 e+00 6.155e-03 2 1. 180 3.300e+06 2.958e+00 5.497e;_03 3 .695 5.383e+02 2.889e-04 5.950e-07 4 | |||
5 s | |||
*7 8 | |||
9 10 11 .. | |||
12 13 14 15 16 17 18 19 20 TOTALS: 6.601e+06 6.370e+00 1 .1S5e-02 | |||
FIGURE 1A SURFACE | |||
FIGURE 18 . | |||
I..., ' *"" I SURFACE . | |||
. / ;/~ ./** | |||
I . q.lft.'A LEGEND .*. . . .. | |||
fOl .1U11MCe AllEA IHIER~-~~n | |||
~ 0 ASl'HALT | |||
*. l .. .. | |||
~ *L~~~~~-~4~~~~~-~N~~ | |||
L.Q_J CORE SAMPLE UNDER FOUNDATION_ * | |||
,.....~*] SURFACE ACTIVITY OF SECTOR | |||
/~ | |||
ASPHALT AREAS* | |||
-EXAMPLE: ONLY | |||
... *}} | ... *}} |
Latest revision as of 13:08, 3 February 2020
ML18052B475 | |
Person / Time | |
---|---|
Site: | Palisades ![]() |
Issue date: | 01/25/1988 |
From: | Bordine T CONSUMERS ENERGY CO. (FORMERLY CONSUMERS POWER CO.) |
To: | NRC OFFICE OF ADMINISTRATION & RESOURCES MANAGEMENT (ARM) |
References | |
NUDOCS 8802010155 | |
Download: ML18052B475 (13) | |
Text
,.._,
~*-*
consumers Power l'OWERIN&
lllllCHl&AN'S l'RO&RESS General Offices: 1945 West Parnell Road, Jackson, Ml 49201 * (517) 788-0550 January 25, 1988 Nuclear Regulatory Commission Document Control Desk Washington, DC 20555 DOCKET 50-255 - LICENSE DPR PALISADES PLANT -
SUPPLEMENT - REQUEST TO RETAIN SOIL IN ACCORDANCE WITH 10CFR20.302 Consumers Power Company letter dated November 12, 1987, requested authori-zation to dispose of soil in place as specified by 10CFR20~302. The letter included the results of a survey and evaluation performed in August, 1987.
Following submittal of that letter, a cooling tower overflow on November 13, 1987 again flooded the South Radwaste Building. The flooding caused additional activity that necessitated Consumers Power Company to request placing our November 12, 1987 request on hold until further evaluation and surveys could be completed. This .letter includes the results of our evaluation and survey of the November 13, 1987 flooding incident and is intended to supplement our original November 12, 1987 request.
Following the cooling tower overflow, a survey indicated additional activity had been released from the building. The building was being maintained in a non-contaminated condition to prevent this type of occurrence; however, during this period a destructive testing program on waste packages was being con-ducted in a small area of the building. The survey clearly showed the release of activity from the building adjoining the testing area. The top six inches of soil from the sectors adjoining the building were removed and packaged (588 cubic feet) to prevent additional dispersion of radioactivity. The area was then completely resurveyed.
An evaluation of the August 1987 and November 1987 (post packaging) activities is attached. The survey indicates a drop of 49% in activities between the August and November surveys. We propose the activities specified in the November 12, 1987 submittal be used as justification for the request because they are conservative. In addition since the November 13, 1987 flooding and following the most recent survey the area was subject to heavy rains which could have diluted some activities to below minimum detectable activity (MDA is nominally lE-06 µC~/g).
~--"-1_ ..JL____. --r2s~~~~~1 r eeo201015s -s~g 00 _ 2 55 .( \ . J
\_:_**~DR_ ~~P~_K._0, -PDR "*LJ / *.
-. ', - Ji (\ .. *- - ' L OC0188-0018-NL02
e Nuclear Regulatory Commission 2 Palisades Nuclear Plant Retain Soil in Accord. with 10CFR20.302 January 25, 1988 The one non-conservative value from our August survey and evaluation is the maximum dose rate at 18 inches' above the surface. The November survey value from MICROSHIELD is 1.17 mR/hr as opposed to 1.02 mR/hr. This small increase only slightly changes the radiation workers' conservative dose estimate from 4.08 mR/year to 4.7 mR/year.
Following approval of this application, it is proposed to account for the most conservative values of activity, which was stated in the November 12, 1987 submittal, as an abnormal release in the semi-annual report. In order to prevent recurrence of these releases to the environment, Consumers Power Company is also committing to transfer radwaste activities from this area, except for high level vault use which is not a potential flooding release problem.
Relocation of these activities to a new radwaste facility is currently scheduled to be completed in 1988.
A check in the amount of $150.00 was attached to our November 12, 1987 submittal pursuant to 10CFR170.12(c).
Thomas C Bordine Administrator, Nuclear Licensing CC Administrator, Region III, NRC NRC Resident Inspector - Palisades Attachment OC0188-0018-NL02
Attachment A Consumers Power Company Palisades Nuclear Plant Docket 50-255 Evaluation and Survey Results Comparison Post November Flood and Packaging*Versus the November 12, 1987 Submittal MI0188-0001A-HP01
'A' Cooling Tower - South Radwaste Flood In August of 1987, a resurvey was co.nducted of the soil at the South Radwaste Building and its adjacent areas. The resurvey was conducted to verify the l~cation of ground contamination and if any contamination migrated further into the ground since the 1986 survey.
After submittal of the 198) soil results and request to retain, in accordance with 10CFR20.302, 'A' Cooling Tower Basin overflowed again flooding the South Radwaste Building and outlying areas. Immediately following the occurrence, one liter sample was taken with no activity detected on the Multi-Channel Analyzer (MCA). Then, another complete survey was conducted which included at least two surface samples and core samples in every sector (Figures 1 and 2).
Surface sample results showed that activities have increased as well as new sectors contaminated. The most heavily affected sectors were I-10, I-11, J and K-9 (Figure lA).. To keep these areas from spreading, the t0-p 6" of each of these sectors was removed and placed in 6 LSA boxes (approx. 588 cu.ft) and stored for disposition at a later date.
After removal of soil, the sectors were resurveyed (Figure lB) and core samples were taken in each sector in 6-inch increments. Core samples were-taken as far down as in.the 1986 and August 1987 surveys, and in some instances even further in this survey. Results showed that no activity was detected below 6 inches as shown in Figure 2.
Table 1 and Table 2 show comparisons between the August and November 1987 soil surveys. Table 1 compares the depths, the. activities, the total cu.ft. and total µCi per sector. After the removal of soil, the November 1987 soil survey results showed approximately a 49.3% drop in total contaminated soil (cu.ft.)
and a 51.1% drop in total µCi in comparison to the August 1987 survey results.
In Table 2 the comparison is between sectors affected in each survey and the depth at which each of these sectors were sampled. No activity was detected past 6 inches in the November 1987 soil survey, in comparison to that of 18 inches detected in August 1987~
Direct dose to an individual working in the affected areas was calculated using the MICROSHIELD code. The activities from sectors H-9 and J-9 were used for a dose at 18" inches above the surface. The dose rates from H-9 and-J-9 are 9.97E-6 R/hr and 1.17E-5 R/hr, respectively. Therefore, a SO-hour occupancy in one week could result in a maximum exposure of .59 millirem. Normal -occupancy of *this area is on an "as needed basis" and averages less than 8 hour9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br />s/week per individual in contact with the contaminated soil.
In reviewing the soil results between August and November 1987, the August 1987 soil survey remains more conservative based on the information shown on Tables 1 and 2. Therefore, the August 1987 soil survey ~s still valid in support of our request to retain the soil in accordance with 10CFR20.302.
MI0188-0001A-HP01
- .Table 1 Comparison Table Between Total Cu. Ft. and Total µCi August 1987
.Sector ff Sg,.ft. x DeEth ft 3 x g/ft 3 x µCi/g, = Total µCi E-11 375 0.5 187.5 48144 2.07E-6 18.7 E-13 . 375 0.5 187.5 48144 4.39E-6 39.6 H-9 625 1.5 937 *. 5 48144 4.79E-6 216.2 H-10 625 0.5 312.5 48144 2 .60E-6 . 39.l H-11 625 2.0 1250* 48144 3.75E-5 2256.8 I-9 527 0.5 263,5* 48144 l.24E"'."'5 157.3.
I-10 . 275 1.5 412.5 48144 5.39E-6 107.0 J-9 . 450 0.5 225 . 48144 5.39E-6 58.4 J-12 200 0.5 100 48144 6.39E-6 30.8 L-9 . 150 1.0 150 48144 6. 77E-6 48 .9*.
I-9 East 98 1.5 147 48144 l.40E-5 *99.1 4325 4173 3071.9
- 1250 .*2256.8 =
73.57. of total activity November 1987
- E-11 375 0.5 187.5 48144 l.80E-6 16.25 H-9 625 0.5 312.5 48144 . 4.35E-5 654.46 H-10 . 625 0.5 312.5 48144 3.20E-6 48.14 H-.11. 625. 0.5 . 312.5 48144 3.22E-5 . 484 .45.
H-12 250 0.5 125 48144 2.20E-6 13.24 I-9 527 0.5 263.5 48144 6.79E-6 86.14 I-12 220. 0.5 110 48144 3.0E-6 15. 89 .
J-9 450 0.5 225 48144 2.05E-5 222.06 J-12 200 0.5 100 48144 2.60E-6 12.52 K-9 216 0.5 108 48144 3 .39E-6 . 17.63 4113 . 2056.5 1570.78
=
MI0188-0001A-HP01
Ta.ble 2 Survey Comparison Between August and. November 1987 Soil Surveys August 1987 November 1987 Sector Surface 6" 12" 18" 24" 30" 36 11 42 11 E-11 E-13 2.07E-6 l *.80E-6
.4.39E-6
<MDA
<MDA
<MDA
<MDA
<MDA
<MDA
<MI>A
<MDA
<MDA e
<MDA N/A <MDA <MDA H-9 4 .19E-6 . <MDA .4. 79E-6 <HDA <HDA <HDA 4.35E-5 <HDA <HDA <HDA <HDA <HDA H-10 2.60E-6 <MDA <MDA 3.20E-6 <MDA <HDA H-11 3.75E-5 <HDA <HDA 8.45E-6 <HDA <HDA <HDA 3.22E-5 <HDA <HDA <HDA <HDA <MDA <HDA H-12 <HDA N/A 2.20E-6 N/A I-9 l.24E-5 <HDA <MDA 6.79E-6 <MDA <HDA I-10 <HDA <HDA 5.39E-6 <MDA <HDA <HDA <HDA <HDA
<HDA <MDA <HDA <MDA <HDA <HDA <HDA <HDA I-11 <MDA' N/A
<HDA <HDA <HDA <HDA I-12 <MDA N/A 3.00E-6 N/A J-9 5.39E-6 <HDA <HDA 2.0SE-5 <HDA <MDA J-12 6.39E-6 <HDA <HDA 2.60E-6 N/A <HDA K-9 <MDA N/A 3.39E-6 <HD.A <HDA <MDA <HDA <MDA <HDA L-9 <MDA 6.77E-6 .<HOA <HOA
<HDA N/A <HDA <HDA MI0188-0001A-HP01
Microshield 3~02
=====
CConsuMer's Power CoMpany - #0371 Page I File SOIL1 .MSH Run date: January 18, 1988 Run tiMe: ~:17 p.M.
CASE: CONTAMINATED SOIL@ H-9 LOCATION <6 INCHES DEEP)
GEOMETRY 11: Rectangular solid source - slab shields Distance to detector ....*.....**.....*....... X 60.960 CM, Source. width ............................. ; .... W 762.
Source length ..*............................. L 762.
Rectangular solid, thickness toward dose pt .. Tl 15. 240 .
Thickness 6f second shield ......... ~ ......... T2 45. 720
- Source VoluMe: 8.84901e+6 cubic centiMeters MATERIAL DENSITIES Cg/cc):
Material Source Shield 2 Air .001220 .001~20 AluMinuM Carbon 1 .70 Concrete Hydrogen Iron Lead LithiUM Nickel Tin TitaniuM Tungsten*
Urania UraniuM Water I .0
- Zirconiul'i r
. Page 2 e eiie:
CASE: CONTAMINATED SOIL @ H-9 LOCATION (6 INCHES DEEP>
SOfLi .MSH BUILDUP FACTOR: based o~ TAYLOR Method.*
Using the. characteristics of the Materials in shield 1
- INTEGRATION PARAMETERS:
NuMber of lateral angle segMents (Ntheta).; .. . *5 NuMber of aziMuthal angle segMents CNpsi)... .. 5 NuMber of radial segMents (Nradius).... ....... 5 SOURCE NUCL IDES:
Ba-i37M: 3.8493e-04 curies RESULTS:
Group Energy Activity Dose point .flux Dose rate
- CMeV) (photons/sec) MeV/(sq cM)/sec (Mr/hr) 1 .664 1 . 282e+07 4.808e+00 9.969e-03 2
3 4
5 6
7 8
9 10 11 .
12 13 14 15.
16 17 18 19 20 TOTALS: 1 . 282e+07
- 4*. 808e+00 9.969e-03
Microshield 3.02 (ConsuMer's Power CoMpany #037)
Page File SOIL2~MSH Run date: January 18, 1988 Run tiMe: 4:26 p.M.
CASE: CONTAMINATED ~OIL@ J-9 LOCATION ~6 INCHES DEEP>
GEOMETRY 1 I: RectanQul~r solid source slab shields Distanc.e to detector ......................... . x 60.960 CM, Source width ............................. , ... : w 762.
Source length .. , ..*..*.. , ............ , .. *,.; .. L 548.640 Rectangular solid, thickness toward dose pt .. Tl 15.240 Thickness of second shield .............. ~ ... . T2 45. 720 Source VoluMe: 6.37129e+6 cubic centiMeters MATERIAL DENSITIES (glee):~
Mat er"! al *source Shield 2 .
Air .001220 .001220 AluMinuM Carbon l.70 Con-crete Hydrogen *
- Iron Lead LithiuM Nickel Tin Titaniul'l
.Tungsten Urania UraniuM Water I .0 ZirconiuM
.. Page 2 Ai* i* "' * "'1* T;
~ _, *
., M. <;'- H
...J..l-l-'-*
- CASE: CONTAMINATED SOIL@ J-9 LOCATION (6 INCHES OEEPI BUILDUP FACTOR: based on TAYLOR Method.
U~ing the characteristics of the Materials in shield 1.
INTEGRATION PARAMETERS:
NuMber of lateral angle segMents (Ntheta>..... 5 NuMber of aziMuthal angle .segMents (Npsi ).. . . . 5 NuMber of radial segMents (Nradius) ... *~* ... , . 5 SOURCE NUCLIDES:
Co-S0: 8.9198e-05 curies RESULTS:
.Group Energy Activity Dose point flux Dose rate
- (MeV) (photons/sec) MeV/(sq cril)/sec (Mr/hr) 1 1 .336 3.300e+06 3A 11 e+00 6.155e-03 2 1. 180 3.300e+06 2.958e+00 5.497e;_03 3 .695 5.383e+02 2.889e-04 5.950e-07 4
5 s
- 7 8
9 10 11 ..
12 13 14 15 16 17 18 19 20 TOTALS: 6.601e+06 6.370e+00 1 .1S5e-02
FIGURE 1A SURFACE
FIGURE 18 .
I..., ' *"" I SURFACE .
. / ;/~ ./**
I . q.lft.'A LEGEND .*. . . ..
fOl .1U11MCe AllEA IHIER~-~~n
~ 0 ASl'HALT
- . l .. ..
~ *L~~~~~-~4~~~~~-~N~~
L.Q_J CORE SAMPLE UNDER FOUNDATION_ *
,.....~*] SURFACE ACTIVITY OF SECTOR
/~
ASPHALT AREAS*
-EXAMPLE: ONLY
... *