Essential Raw Cooling Water Conduit Settlement Monitoring Data.Oversize Tables Q2.86-1 & Q2.84-1 EnclML19347C730 |
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Site: |
Sequoyah |
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Issue date: |
12/31/1980 |
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From: |
TENNESSEE VALLEY AUTHORITY |
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To: |
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Shared Package |
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ML19347C729 |
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References |
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NUDOCS 8101050250 |
Download: ML19347C730 (5) |
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Category:ENVIRONMENTAL MONITORING REPORTS(&RADIOLOGICAL)-PERIODIC
MONTHYEARML20217J7831999-09-30030 September 1999 Discharge Monitoring Rept for Sequoyah Nuclear Plant for Third Quarter of 1999. with ML20209H1951999-06-30030 June 1999 Discharge Monitoring Rept for 990401-990630. with ML20205R1881999-03-31031 March 1999 NPDES Discharge Monitoring Rept,Jan-Mar 1999. with ML20203C4051998-12-31031 December 1998 1998 Annual Reports for Sequoyah Nuclear Plant. with ML20209J1431998-12-31031 December 1998 Radiological Impact Assessment Rept, for Jan-Dec 1998 ML20209J1221998-12-31031 December 1998 Annual Radioactive Effluent Release Rept, for 1998 ML20205H8931998-12-31031 December 1998 1998 Tennessee Multi-Sector General Permit Storm Water Monitoring Rept for Sqn ML20205T0231998-12-31031 December 1998 Annual Radiological Environ Operating Rept for Sequoyah Nuclear Plant 1998. with ML20199G3751998-12-31031 December 1998 Discharge Monitoring Rept for Sequoyah Nuclear Plant for Period of 981001-1231. with ML20155J3881998-09-30030 September 1998 Annual Non-Radiological Environ Operating Rept for Period Oct 1997-Sept 1998. with ML20154P5511998-09-30030 September 1998 NPDES Discharge Monitoring Rept for Period 980701-0930 ML20236Q9231998-06-30030 June 1998 Discharge Monitoring Rept for Sequoyah Nuclear Plant from 980401-980630 ML20217N4621997-12-31031 December 1997 1997 Annual Repts for Sequoyah Nuclear Plant ML20217F0891997-12-31031 December 1997 Annual Radioactive Effluent Release Rept for Period of Jan-Dec 1997 ML20217A6541997-12-31031 December 1997 Annual Radiological Environ Operating Rept,Sequoyah Nuclear Plant for 1997 ML20198N7211997-10-0101 October 1997 Annual Non-Radiological Environ Operating Rept for Period from 960915-1001 ML20138F2381996-12-31031 December 1996 Annual Radioactive Effluent Release Rept for Jan-Dec 1996 ML20138B3591996-12-31031 December 1996 1996 Annual Radiological Environ Operating Rept for Sequoyah Nuclear Plant ML20138F2431996-12-31031 December 1996 Radiological Impact Assessment Rept ML20132D3641996-09-14014 September 1996 Annual Non-Radiological Environ Operating Rept 950915- 960914 ML20108A0981995-12-31031 December 1995 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant 1995 ML20108B3991995-12-31031 December 1995 Radiological Impact Assessment Sequoyah Nuclear Plant Jan- Dec 1995 ML20108B3931995-12-31031 December 1995 Annual Radioactive Effluent Release Rept for Period of Jan- Dec 1995 ML20094G7761995-09-14014 September 1995 Annual Nonradiological Environ Operating Rept for 940915- 950914 ML20080L6361994-12-31031 December 1994 Annual Rept for 1994, Consisting of Occupational Exposure Data,Rcs Specific Activity Analysis & Diesel Generator Reliability Data ML20082P9881994-12-31031 December 1994 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant 1994 ML20087H4951994-12-31031 December 1994 Annual Radioactive Effluent Release Rept for Jan-Dec 1994 ML20080B7381994-09-14014 September 1994 Annual Non-Radiological Environ Operating Rept 930915- 940914 ML20065Q6221993-12-31031 December 1993 Radiological Impact Assessment Rept Sequoyah Nuclear Plant Jan-Dec 1993 ML20029C7391993-12-31031 December 1993 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant. W/940419 Ltr ML20064C3661993-12-31031 December 1993 Annual Repts to NRC Jan- Dec 1993, Containing Summary of Occupational Exposure Data, RCS Specific Activity Analysis & DG Reliability Data.W/ ML20065Q6181993-12-31031 December 1993 Annual Radioactive Effluent Release Rept for Period Jan-Dec 1993 ML20058L1111993-09-14014 September 1993 Annual Environ Operating Rept. W/ ML20126B2261992-12-15015 December 1992 Annual Environ Operating Rept for 910915-920914 ML20114C8051992-06-30030 June 1992 Semiannual Radioactive Effluent Release Rept for Jan-June 1992 ML20090D2041991-12-31031 December 1991 Semiannual Effluent Release Rept for Jul-Dec 1991 ML20095K0121991-12-31031 December 1991 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant 1991 ML20090D2101991-12-31031 December 1991 Radiological Impact Assessment Rept, Jan-Dec 1991 ML20082L3601991-06-30030 June 1991 Effluent & Waste Disposal Semiannual Rept Jan-June 1991 ML20073G4761990-12-31031 December 1990 Annual Radiological Environ Operating Rept,Sequoyah Nuclear Plant,1990 ML20029B2481990-12-31031 December 1990 Semiannual Radioactive Effluent Release & Radiological Impact Assessment Rept for Jul-Dec 1990. W/910225 Ltr ML20065R7241990-09-14014 September 1990 Annual Environ Operating Rept 890915-900914 ML20012A0751989-12-31031 December 1989 Radiological Impact Assessment Rept,Sequoyah Nuclear Plant, 1989. ML20012A0731989-12-31031 December 1989 Supplemental Effluent & Waste Disposal Semiannual Rept for Second Half 1989. ML19332G0881989-09-14014 September 1989 Annual Environ Operating Rept 880915-890914. W/891215 Ltr ML20247J7611989-06-30030 June 1989 Chicamauga Reservoir 1988 Fisheries Monitoring Cove Rotenone Results ML20246H3761989-06-30030 June 1989 Effluent & Waste Disposal Semiannual Rept Supplemental Info Jan-June 1989 ML20246M8871988-12-31031 December 1988 Annual Radiological Environ Operating Rept - Sequoyah Nuclear Plant 1988 ML20246B3931988-12-31031 December 1988 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant 1988 ML20196D0891988-09-14014 September 1988 Annual Environ Operating Rept for 870915-880914 1999-09-30
[Table view] Category:TEXT-ENVIRONMENTAL REPORTS
MONTHYEARML20217J7831999-09-30030 September 1999 Discharge Monitoring Rept for Sequoyah Nuclear Plant for Third Quarter of 1999. with ML20209H1951999-06-30030 June 1999 Discharge Monitoring Rept for 990401-990630. with ML20205R1881999-03-31031 March 1999 NPDES Discharge Monitoring Rept,Jan-Mar 1999. with ML20205T0231998-12-31031 December 1998 Annual Radiological Environ Operating Rept for Sequoyah Nuclear Plant 1998. with ML20209J1431998-12-31031 December 1998 Radiological Impact Assessment Rept, for Jan-Dec 1998 ML20203C4051998-12-31031 December 1998 1998 Annual Reports for Sequoyah Nuclear Plant. with ML20205H8931998-12-31031 December 1998 1998 Tennessee Multi-Sector General Permit Storm Water Monitoring Rept for Sqn ML20209J1221998-12-31031 December 1998 Annual Radioactive Effluent Release Rept, for 1998 ML20199G3751998-12-31031 December 1998 Discharge Monitoring Rept for Sequoyah Nuclear Plant for Period of 981001-1231. with ML20155J3881998-09-30030 September 1998 Annual Non-Radiological Environ Operating Rept for Period Oct 1997-Sept 1998. with ML20154P5511998-09-30030 September 1998 NPDES Discharge Monitoring Rept for Period 980701-0930 ML20236Q9231998-06-30030 June 1998 Discharge Monitoring Rept for Sequoyah Nuclear Plant from 980401-980630 ML20248M1031998-05-26026 May 1998 NPDES Noncompliance Notification:On 980518,spill of Sodium Hypochlorite Occurred.Sys Was Shut Down & Monitoring Was Conducted to Verify That No Detectable Total Residual Chlorine Discharged from Outfall 101 to Tn River ML20217A6541997-12-31031 December 1997 Annual Radiological Environ Operating Rept,Sequoyah Nuclear Plant for 1997 ML20217F0891997-12-31031 December 1997 Annual Radioactive Effluent Release Rept for Period of Jan-Dec 1997 ML20217N4621997-12-31031 December 1997 1997 Annual Repts for Sequoyah Nuclear Plant ML20198N7211997-10-0101 October 1997 Annual Non-Radiological Environ Operating Rept for Period from 960915-1001 ML20138F2381996-12-31031 December 1996 Annual Radioactive Effluent Release Rept for Jan-Dec 1996 ML20138F2431996-12-31031 December 1996 Radiological Impact Assessment Rept ML20138B3591996-12-31031 December 1996 1996 Annual Radiological Environ Operating Rept for Sequoyah Nuclear Plant ML20132D3641996-09-14014 September 1996 Annual Non-Radiological Environ Operating Rept 950915- 960914 ML20108B3931995-12-31031 December 1995 Annual Radioactive Effluent Release Rept for Period of Jan- Dec 1995 ML20108A0981995-12-31031 December 1995 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant 1995 ML20108B3991995-12-31031 December 1995 Radiological Impact Assessment Sequoyah Nuclear Plant Jan- Dec 1995 ML20094G7761995-09-14014 September 1995 Annual Nonradiological Environ Operating Rept for 940915- 950914 ML20087H4951994-12-31031 December 1994 Annual Radioactive Effluent Release Rept for Jan-Dec 1994 ML20082P9881994-12-31031 December 1994 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant 1994 ML20080L6361994-12-31031 December 1994 Annual Rept for 1994, Consisting of Occupational Exposure Data,Rcs Specific Activity Analysis & Diesel Generator Reliability Data ML20080B7381994-09-14014 September 1994 Annual Non-Radiological Environ Operating Rept 930915- 940914 ML20065Q6221993-12-31031 December 1993 Radiological Impact Assessment Rept Sequoyah Nuclear Plant Jan-Dec 1993 ML20065Q6181993-12-31031 December 1993 Annual Radioactive Effluent Release Rept for Period Jan-Dec 1993 ML20064C3661993-12-31031 December 1993 Annual Repts to NRC Jan- Dec 1993, Containing Summary of Occupational Exposure Data, RCS Specific Activity Analysis & DG Reliability Data.W/ ML20029C7391993-12-31031 December 1993 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant. W/940419 Ltr ML20058L1111993-09-14014 September 1993 Annual Environ Operating Rept. W/ ML20126B2261992-12-15015 December 1992 Annual Environ Operating Rept for 910915-920914 ML20114C8051992-06-30030 June 1992 Semiannual Radioactive Effluent Release Rept for Jan-June 1992 ML20095K0121991-12-31031 December 1991 Annual Radiological Environ Operating Rept Sequoyah Nuclear Plant 1991 ML20090D2041991-12-31031 December 1991 Semiannual Effluent Release Rept for Jul-Dec 1991 ML20090D2101991-12-31031 December 1991 Radiological Impact Assessment Rept, Jan-Dec 1991 ML20082L3601991-06-30030 June 1991 Effluent & Waste Disposal Semiannual Rept Jan-June 1991 ML20073G4761990-12-31031 December 1990 Annual Radiological Environ Operating Rept,Sequoyah Nuclear Plant,1990 ML20029B2481990-12-31031 December 1990 Semiannual Radioactive Effluent Release & Radiological Impact Assessment Rept for Jul-Dec 1990. W/910225 Ltr ML20065R7241990-09-14014 September 1990 Annual Environ Operating Rept 890915-900914 ML20012A0751989-12-31031 December 1989 Radiological Impact Assessment Rept,Sequoyah Nuclear Plant, 1989. ML20012A0731989-12-31031 December 1989 Supplemental Effluent & Waste Disposal Semiannual Rept for Second Half 1989. ML19332G0881989-09-14014 September 1989 Annual Environ Operating Rept 880915-890914. W/891215 Ltr ML20246L8801989-08-31031 August 1989 Predictive Section 316(a) Demonstration for Alternative Winter Thermal Discharge Limit for Sequoyah Nuclear Plant, Chickamauga Reservoir,Tn ML20247J7611989-06-30030 June 1989 Chicamauga Reservoir 1988 Fisheries Monitoring Cove Rotenone Results ML20246H3761989-06-30030 June 1989 Effluent & Waste Disposal Semiannual Rept Supplemental Info Jan-June 1989 ML20245G8971989-04-26026 April 1989 NPDES Noncompliance Notification:On 880801,dead Fish Discovered in Intake Forebay & Sample of Intake Water Analyzed for Total Residual Chlorine.Caused by Release of Sodium Hypochlorite to Water.Levels within NPDES Limits 1999-09-30
[Table view] |
Text
ESCLOSURr.
. SEOUOYAll NUCLEAR PLANT
, ERCW CONDUIT SETTLEMENT MONITORING Updated Results - December 1980 The results of the settlement monitoring program to date (December 1980) are given below.
Diesel Generator Building The previous settlement data are given in Table Q2.70-1 and Figure Q2.70-1.
These data and the additional data are presented in Table Q2.86-2.
ERCV Pumping Station, Access Cells, and Dike The settlement monitoring program for the ERCW system is discussed in our response to Question 2.78. Settlement data, current to March 1980, were presented in our original response to Question 2.86. The results of a h3C site visit (of October 27, 1980), additional data, requested additional diseassion, and a summary oi previous responses are presented here.
The ERCW system consists of a pumping station, access cells,faccess dike, electrical conduits, and pipelines. Settlemen.t markers are locatcd on all of these except the pipelines as follows:
Pumping Station - two survey markers are located on the pumping station, one each on the NE and NW corners.
Access Cells - one survey marker is located at the centerline of each cell and arch cell (#1CL to F13).
Access Dike - two survey markers (one on each side of the road) are located on each side of the ERCW electrical conduit bank supports. These are located at 30-foot intervals along the access dike (#14 N/S to 20 N/S). These were extended (#21N, 21S, 22N, 22S) to include 4 survey markers (two on each side) at the end of the support slab. These markers are located in the rockfill approximately 5 (#21 N/S) and 40 (#22 N/S) feet from ,
the end of the slab on the shore side.
Electrical Conduit Bank - five survey markers (#23 to 27) are located along the ERCW electrical conduit route between the end of the slab and soil boring ss-69.
These markers are located on manhole groups 54, 55, and 56 and midway between them.
Settlement data for these features, current. t > March 1980, were given in our original response to Question 2.86. The (ata were tabulated in Table Q2.86-1 and presented graphically in Figures Q2.86-1 to -5.
These data indicated movements of up to 0.1 inches. Table Q2.30-1 has been updated to include the latert readings.
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'As discussed in our response to Q2.86, several settlement markers were hit '
during construction. This is documented in the survey notes.
The surveyers reported markers as either " monument hit" or " monument possibly hit." These data are included in Table Q2.86-1. During the site visit October 27, 1980, the NRC representative, Raman Pichumani, viewed these markers. The distress to the markers, which are just rebars in a pipe s leeve, was visually very apparent. The procedure used to correct the actual survey data to account for marker disturbance is thus justified.
The apparent movement of the disturbed markers is not logically explained as just consolidation settlement. For example, the markers were reported as hit on the December 19, 1979, survey. No settlement trend existed based on the previous data. Variations are only a few thousandths of a foot. on monthly reading for four months. In fact some of the readings show an upward not downward movement (19N & 20N). The markers were reported hit with the December 19, 1979, reading. " Movements" of up to - 0.079 feet (down)-
are reported. However, movement from December 19, 1979,- to present ::how no settlement trend. Variations are again a few thousandths on monthly readings for four months. Such a sudden jump in settlement with no pre- or post-activity is not logically explained by any consolidation theory.
Also, the reported " movements" are not logical'when viewed in plan. Markers are present on each side of the road (road width is 20 feet, approximate marker separation is 25 feet) and at 30-feet intervals along the road. Figure Q2.84-6 shows an enlargement of the area between markers 17 and 22, the area of interest. The data shown are for the December 19, 1979, the reported hit date. The largest " movement" is reported for #19N (-0.079 ft.). However,
- 18N (30 feet east) reports 0.0 ft., #19S (25 feet south) reports -0.004 feet,
- 20N (30 feet west) reports -0.034 (also reported as hit), and #21N (10 feet west) reports -0.033 (also reported as hit). The second largest " movement" is reported for #18S (-0.048 feet). Adjacent markers #17S (30 feet east) reports -0.009 feet, #19S (30 feet west) reports -0.004 feet, #18N (25 feet north) reports 0.0 feet. In addition, the road and curbing show no signs of distress in the vicinity of these markers. Such local pockets of settle-ment might be explained by consolidation. However, consolidation cannot explain that they appear in one month with no pre- or post- activity and cannot explain the lack of impact on the road.
Nevertheless, even if the 0.079 feet of settlement is valid and should' be considered, it has no adverse effect on the pipes. The 36-inch diameter ERCW pipes are protected by a 60-foot long steel 42-inch diameter steel pipe sleeve as it crosses from the pile supported slab to insitu soil. The pipe sleeve extends from 20 feet back along the slab to 40 feet beyond the end of the slab. Details of the pipe sleeve are shown in figure Q2.71-5.
The ERCW pipes as sleeved will withstand settlements of six inches and be within allowable limits. This is as discussed in our response to Question 2.72.
The latest readings (September 19, 1980) show some erratic data points. Of
) notable interest are 17S, 18S, 19N, and 20N where results of -0.161, -0.081,
-0.047, and -0.007 feet are reported. Number 18S appears to have moved 4
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'down from -0.048 to -0.081 while 19N appears to have moved up from -0.081 '
to -0.047. Likewise, 17S moved down frca -0.010 to -0.161 while 20N moved up from -0.047 to -0.007. In these data, no consistent pattern of movement is evident. The road and curbing show no signs of distress. The magnitude of the remaining data generally fall within the range of the previously reported data.
Based on our evaluation, the total and differential settlements are not significant; there are no trends being exhibited; and there has been no adverse structural performance.
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