ML20034B970

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Forwards Results of post-lower Head Sampling Program Cleanup on 900302,including Results of Mar 1990 Video Insp, Updated Criticality Analyses & Clarification of Several Defueling Completion Rept Items Discussed W/Nrc
ML20034B970
Person / Time
Site: Crane 
Issue date: 04/12/1990
From: Roche M
GENERAL PUBLIC UTILITIES CORP.
To:
NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM)
References
4410-90-L-0026, 4410-90-L-26, NUDOCS 9005010248
Download: ML20034B970 (17)


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' a OPU Nuclear Corporation l N

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' outa 1 So n Middletown, Pennsylvania 17057 0191' 717 944 7621

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TELEX 84 2386.

Writer's Direct Dial Number::

f(717) 948-8400 April 12,1990 4410-90-L-0026/0531P US Nuclear Regulatory Commission Washington,-DC 20555 j

i Attention: Document Control Desk Three File Island Nuclear Station, Unit 2 (TMI-2)

Operating License No._DPR-73 Docket No. 50-320 Results of Post-Lower Head Sampling Piogram Cleanup

Dear Sirs:

The NRC-sponsored Lower Head Sampling Program was successfully completed on i

March 2, 1990.

Some residual fuel was removed by the sampling program and data gathered during the sampling' enabled us to improve our. knowledge of-i residual fuel in the incore nozzles. As discussed in'the TMI-2 Defueling Completion Report (DCR), a final cleanup was to be conducted immediately following the sampling program. A video inspection of the Lower Core Support Assembly (LCSA) and bottom head regions followed.the final cleanup to reassess-l the amount of core debris remaining. As part of this video-inspection, an attempt was made to examine areas of the LCSA that were previously inaccessible.

The re.tult of this work was that the residual fuel estimates have been revised. The total quantity of residual fuel-(i.e..UO ) in the'TMI-2 2

facility is now estimated to be less than 850 kg (i.e.,-le'ss than-1% of the original core inventory).

In addition, analyses have'been performed based on-1 as-defueled Reactor Vessel conditions which indicate an increased margin of subcriticality in the TMI-2 Reactor Vessel.

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/:j APll Nuclear Corporation is a subsidiary of the General Public Utilities Corporation -

l ' b-9005010248 900412 n-pDR ADOCK 05000320 l

P D C..

' Document Control Desk

. April 12,1990

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Page 2 4410-90-L-0026 The attached report provides the results of the March 1990 video inspection',

the updated criticality analyses, and clarification of several DCR items discussed with the NRC during the recent review of the'DCR. As these changes increase the margin of safety for the TMI-2 facility beyond that described in the DCR, GPU Nuclear intends to transition TMI-2 to facility Mode 2 on April 27,1990,. as planned.

Sincerely,

%(h kW J-.-

M. B. Roche Director, THI-2 EDS/mkk Attachment cc:

T. T. Martin - Depuh' Regional Administrator, Region I' J. F. Stolz - Director, Plant Directorate I-4 3

L. H. Thonus - Project Manager, THI Site

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F. I. Young - Senior Resident Inspector, TMI l

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L 4410-90-L-0026 Results of Post-Lower Head Sampling Program Cleanup Following the NRC-sponsored Lower Head Sampling Program, a final cleanup was conducted, as discussed in the TMI-2 Defueling Completion Report (DCR). A video inspection of the Lower Core Support Assembly (LCSA) and bottom head regions was also performed in March 1990 to determine the amount of core debris remaining. 'This inspection included an examination of areas of the LCSA that were previously inaccessible due to equipment. design. As h result, residue.1-fuel estimates have been revised.

In addition, the criticality analyses presented in the DCR were based on the September 1989 estimates of residual fuel quantities'and locations.

Revised analyses have been performed based on the January 1990 "as-defueled" Reactor Vessel (RV) inspection.

The following presents.the results of the March 1990 video-inspection, the criticality analyses, and clarification of several DCR items-previously discussed with the NRC Results of March 1990 Video Inspection i

Based on the March 1990 video inspection, the total quantity of residual fuel I

(i.e., UO ) in the LCSA and bottom head regions was reduced to 272.7 and 2

23.3 kg, respectively (See Table 1).

Thus, the total quantity of residual fuel in the RV and the THI-2 facility is now estimated to be 608.8 and 833.8 kg, respectively.

The location and mass of the residual fuel deposits are J

detailed on a sub-region basis as follows:

-f 1

Lower Core Support Assembly Region i

Between Lower Grid Rib Section (LGRS) and Lower Grid Distributor Plate (LGDP)

The March 1990 video inspection verified that two small masses seen in f

the January 1990 video inspection, amounting to 1.7 kg of resolidified

_j core debris (Type 3), remain in this area.

In addition, there is a thin layer of fine debris (Type 1) uniformly distributed on~the surface of the LGDP amounting to 0.9 kg.

Therefore, the total-quantity of core debris estimated to be in this area is 2.6 kg (2.0 kg 00 )-

2 LGDP Peripheral Flow Holes In the January 1990 video inspection of this area, all but two holes were inspected and seen to contain no debris.

To be conservative, these holes

'i were assumed to be full of debris.

However, the remaining two holes were examined.during the March 1990 video inspection and were verified to be empty.

, 0531P I

4 4

7 4410-90-L-0026 Between LGDP and Forging During the March 1990 video inspection, it.was observed lthat only one mass of core debris.(Type 3) remains in the southeast quadrant'rather than the three masses seen during the January 1990 inspection.

Based on the estimated volume, a. total of 0.3 kg of residual core debris remains.

In addition, there is a thin layer of fine debris (Type 1)-on the surface of the forging amounting to 1.2 kg.. Therefore, the total.quanity of core i

debris in this area is estimated to be 1.5 kg (1.1 kg 00 }-

2 Forging Peripheral Flow Holes l

During the March 1990 video inspection, an attempt'was made to insert a l

camera into each of the six remaining small diameter holes in the forging l

that were not examined during the January 1990 video inspection.

Three.

)

of these holes were observed to be void of fuel, one hole was

-approximately 'l/3 full of resolidified debris (Type 3). and one_ hole was-i approximately 2/3 full of resolidified debris (Type 3)..

The remaining hole was verified to be full of small stones, i.e., resolidified~ debris (Type 3).

Of the large diameter flow holes, 21 were observed to contain-1; varying amounts of resolidified debris (Type 3).

Based on the estimated i

volume, there is 123.8 kg of residual core debris *(89.9 kg UO )

2 remaining in these holes.

Inside Support Post Stubs The inside support posts were cut off 5.1 to 10.2 cm (2 to 4 inches) above the top of the forging.

It was relatively easy to vacuum loose i

debris (Type 1) out of the stubs.

During the. cleanup following the Lower j

Head Sampling Program, the small rocks that were previously seen in the stubs were also vacuumed out.

Therefore, no residual core debris remains

{

in these stubs.

i Between Forging and Incore Guide Support; Plate-(IGSP) l The space between the forging and the IGSP.is 1,3-cm (1/2-inch) wide-where the forging is the thickest.

Because of the-taper on the forging, the space increases to 20.3 cm (8 inches) at the periphery.. This region was cleaned with a flushing tool inserted through a number of the holes' in the forging and operated to flush both the hole and the space.below the hole.

Based on the March 1990 video inspection, it is estimated that there is 180.1 kg of core debris (Type 3) in this region.

The' bulk of-t that core debris is in the form of a single solidified mass _of-approximately 150 kg (110 kg 00 ) in the southeast quadrant of this-2 region. This mass is inaccessible to defueling because of the pattern of cutting of the forging.

In any event, the configuration and condition of this mass is such that criticality is not a concern (i.e., mass is less j

than the Safe Fuel Mass Limit (SFML)).

i 2 0531P

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i 4410-90-L-0026 In addition, there is a thin layer of fine debris (Type 1) uniformly-distributed on the surface of the IGSP. Also' observed.was a piece of.

fuel rod approximately 30.5-cm (12-inches) in length that was assumed to be filled with fuel pellets and which was located such that it could not be removed.

The total amount of Type 1 material is 1.9 kg.

Therefore, the total quantity of. core debris estimated to be in this area is 182.0 kg of core debris (132.9 kg UO ).

This estimate includes ~ debris 2

observed in the. flow holes in the IGSP.

Between IGSP and Flow Olstributor Based.on the March 1990 video inspection, it is estimated that there is' 6.5 kg of resolidified core debris (Type 3) in this' area and 1.1 kg of loose, fine debris (Type 1) distributed on the surfaces of this area.

Therefore, the total quantity of core debris estimated to be in this area 1s 7.6 kg (5.5 kg UO )-

2 Bottom Head Realon.

1 Head Surface The bottom head region was examined in the. March 1990 video inspection.

L There appears to be a fine dusting of material (Type 1)' distributed over l

the entire bottom head surface except for two patches where!the granular a

material was somewhat deeper [an average of 0.3-cm (0.1-inch)]. Based on l

the estim3ted volume, 11.2 kg~of core debris (8.1 kg UO ) remains in 2

j this area.

Incore Instrument Nozzles Nineteen incore instrument nozzles have partial guide tubes standing t

above them which could have prevented materlal from collecting in:the nozzles if the instrument strings were still intact (including the spiral seal).

Guide tubes around the remaining 33 nozzles have been removed and the instrument strings severed.

'A number of the nozzles were melted off,

~1 some to within 2.5 cm (1 inch) of-the head surface.

During the Lower Head Sampling Program, 14 of the incore nozzles were cut and removed.

These nozzles w1re videotaped during and following removal.

The results of that video examination provide the basis for estimating the remaining l

l residual fuel. As a conservative upper limit, it is assumed that ten of the 33 incore nozzles have the annular space between the instrument-i l

string and the inside of the nozzle / guide pipe filled with loose debris (Type 1) to a depth of 2.4 meters (8 feet), ten contain no debris, and 13 L

contain a 2.5-cm (1-inch) long plug of resolidified fuel material in the annular space.

Based on the estimated volumes, 12.5 kg of loose core debris (Type-1) and 0.3 kg of resolidified debris (Type 3) are estimated to reside in these locations.

Therefore, the total quantity of core debris estimated to be in this area is 12.8 kg (9.2 kg UO )-

2 Standing Incore Guide Tubes The quantity of core debris reported in the DCR was in error.

The correct value is 8.2 kg of core debris (6.0 kg UO ) remaining in this 2

area.

.j 0531 P

4410-90-L-0026 Reactor Vessel Residual Fuel Criticality Assesiment Criticality Safety Analysis An updated criticality safety analysis was performed based on the January 1990 video inspection results.

That analysis incorporated a more conservative approach than that reported in the DCR in that the fuel debris was modelled entirely as burned batch 3 fuel (i.e., 2.67.wt %

U-235 enrichment).

The analysis discussed here was developed for actual plant conditions (i.e., as existed in January 1990).

The criticality calculations presented were performed by Oak Ridge National Laboratory (ORNL) and were reported in* Reference 1.

The model, shown in figure 1, represents the end state RV condition following the completion of in-vessel defueling (i.e., January 1990).

The three major areas where core debris resides are the RV bottom head, the LCSA, and the core former area (i.e., between the core former baffle plates and the core barrel) in the/ Upper Core Support Assembly (UCSA).

Fuel accumulations in other locations within the vessel were considered to be too small (i.e., much less than the SFML) and/or separated from these three areas by a far enough distance (i.e., the equivalent of approximately 30.5 cm (12 inches) of water, Reference 2) so as not to cause a reactivity increase due to neutronic interaction between these areas. Additionally, the conservative debris quantities that were modelled will more than compensate for the small quantity.of debris not specifically modelled.

Details of the modelling of each of the regions follow:

Core Former Region To conservatively model remaining <1ebris in the core former area, it was assumed that a 0.3-cm (0.1-inch) thick, 3-meter (10-foot) high surface debris layer remained attached to the core barrel.

This conservative representation of the core former region also bounds the limited amount of core debris that remains in the regions above/outside the UCSA.

Lcwer Core Support Assembly The major focus and detail of the geometrical model occurred in the modelling of this region.

The LGRS and LGDP were assumed to be of the same radial thickness (i.e., 12.7 cm (5 inches), AR of Figure 13 and the lower grid forging and the IGSP were assumed to.0 of the same radial thickness (i.e., 50.8 cm (20 inches), _ AR of Figure 1J The flow holes in both the LGR$ and the LGDP are volu of fuel.

There is some debris on these plates but much less than is modelled (Figure 1).

The flow holes in the forging were assumed to be filled such that 50% of the forging volume in the model is comprised of a debris / water mixture and 50% is stainless steel. To account for the small amount of core debris remaining in the IGSP flow holes, this plate was modelled as two regions.

The inner region contained only water and steel (i.e,. the plate holes are empty).

The outer region (i.e., closer to the vessel 0531P

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4410-90-L-0026 wall) was modelled with the holes completely filled with an optimally moderated core debris / water mixture.

The inner and outer regions of the IGSP were 35.6 cm (14 inches) and 15.0 cm (6 inches), respectively, in radial thickness. An additional conservative assumption included in the model was that the flow holes in the forging were filled with fuel and unborated water in an optimal mixture, even though, many of the holes were free of debris.

Although significant portions of the LC'SA plates were free of debris, a debris layer was applied to each of the modelled LCSA plates to account for any debris that could not be removed from the plate surfaces.

These debris layers were conservatively assumed to extend the entire 360*

around the RV.

The thickness of the debris layer on top of the LGRS was assumed to be 0.3 cm (0.1 inch).

Between the LGRS and the LGDP, two debris accumulatiens were modelled.

The first was a 0.3-cm (0.1-inch) radial thickness accumulation located on the outer periphery of this region which extended axially the entire distance between the two plates.

The second debris layer modelled in this region was a 0.3-cm (0.1-inch) thickness placed on top of the LGDP.

The region between the LGDP and the lower grid forging was similarly modelled with these two debris layers.

Due to the small separation distance between the lower grict forging and the IGSP (i.e., 1.3-cm (1/2-inch)], there has been limited access to the area underneath the lower grid forging.

However, to support the conservative approach, the amount of core debris modelled in this region was assumed to be much larger than that assumed for other areas of the l

LCSA.

Based on the January 1990 video inspection, the-core debris was assumed to fill the outer 20.3 cm (8 inches) from the vessel wall inward over the entire distance separating the lower grid forging from the IGSP.

The remaining radial 17.8 cm (7 inches) of this region were free of debris accumulations and were modelled as unborated water only.

Underneath the IGSP, a 3.8-tm (1.5-inch) layer of debris with a 5.1-tm (2-inch) radial thickness was modelled representing debris left in the

" knuckle" of the flow distributor plate.

The actual vertical offsetting of the plates was conservatively neglected.

Instead, the LCSA plates were assumed to have a constant outer radius corresponding to the lower grid forging.

Similarly, the core former and the bottom head regions were conservatively assumed to connect directly to the LCSA.

No consideration was given for the effect of offsetting of these regions.

This approach modelled the various regions as being closer to each other than actual, implying neutron interaction between the modelled debris accumulations.

A 20.3-cm (8-inch) carbon steel region was placed on the outside of the annular ring to represent the RV wall.

This approach essentially moved the water region between the core barrel and the vessel wall to outside the vessel.

This was considered appropriate and conservative since only small accumulations of debris fines were found in this region and because analyses have shown steel to be a better neutron reflector than unborated-water.

Finally, an unborated water reflector of effectively infinite thickness was placed outside the carbon stsel region. 0531P

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4410-90-L-0026 Reactor Vessel Bottom Head Using a conservative approach, a 0.4-cm (0.15-inch) layer of core debris covering the entire inside surface of the bottom head was assumed to.

exist in the model for this criticality assessment; this amount of material is greater than that observed in the bottom head region.

Conservative Approach Summary As discussed above, significant conservative assumptions were built into the geometrical model for this analysis.

These ;onservative assumptions are summarized below:

Conservative values for thr modelled layers of ces debris on the LCSA plates.

~

The entire inside surface of tne RV bottom head was assumed to be covered with a 0.4-cm (0.15-int h) thick layer of core debris.

A 0.3-cm (0.1-inch) thick layer of core debris, with a hi ght of 3 i

meters (10 feet), was assumed to be attached to the core barrel in the core former region of the model.

1 No credit was taken for the vertical offsetting of the LCSA plates or the other regions of the model, and the regions between the plates were conservatively modelled.

Each of the LCSA plates was modelled with a radial thickness that bounded the presence of core debris on tha plate.

The tardelled debris and vessel internals were assumed to extend 360' around the periphery of the RV.

The flow holes, as modelled for the forging, were assu'ned to be filled with core debris and unborated water in an optimal dxture.

Unborated water was assumed to fill all portions of the RV, excluding the modelled debris accumulations and vessel internals.

No credit was taken for the plans to eventually drain the RCS, essentially leaving the RV without a moderating medium.

Considerably more core debris was included in the analytical model than remains in the RV (see Table 2).

Considering the above approach and the conditiot of the RV following defueling, it was concluded that the geometrica1'model described above, including the postulated core debris locations, wa3 conservative and appropriately bounds the RV configuration that, exists. 0531P

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' Attachment 1 4410-90-1.-0026 1

Fuel Modelling The original loading of the core included 56 assemblies of 1.98 wt1 (batch 1), 61 assemblies of 2.64 wt1 (batch 2), and 60 assemblies of 2.96 wt% (batch 3) 0-235 enrichment.

The enrichment of the fuel used in this evaluation was that corresponding to burned batch 3 fuel (i.e., 2.67 wt%

U-235 enrichment).

Thit extremely conservative assumption bounds the enrichment of fuel remaining in the RV.

The fuel was represented as a homogeneous medium for which the neutronic data correspeded to a dodecahedral lattice of spherically shaped fuel pellets.

The size of the.

spherical pellets was the equivalent of sf.andard cylindrical fuel pellets. Another maximum reactivity assumption was the preservation of the pellet surface to mass ratio in the fuel pellet volume.

This assumption enhanced the resonance shielding effect on the U-238 cross-sections. Conservatively, it'was also assumed that there was nothing present in the fissile media except fuel pellets and unborated water.

Thus, the negative reactiviity effects due to the presence of cladding absorber material and structural materials were ignored.

Unborated water was used for the moderating wadium.

The presence of residual boron which would remain in the RV following the draining process has been it)nored.

Furthermore, an optimum fuel volume fraction (i.e resulting in a maximum k ) for fuel and unborated water (VF -

0.28) was determined and used in this evaluation.

The optimal fuel particle size for UO2 particles moderated with unborated water was shown in previous analyses to be greater than a l

standard-size fuel pellet.

However, any core debris particles larger than standard-size pellvts were considered to contain impurities, as melting and subsequent resolidification was the only credible means by l

which the larger particles could have been forn.ed.

In such a proces's the

(

other materials within the vessel (e.g., cladding, structural materials, and poisons) would have intermixed with the fuel, thus reducing the reactivity of the debris, Furthermore, particle sizes less than a standard-size pellet have been shown to be significantly less reactive than full pellets.

Defueling experience has indicated that particle sizes much smaller then standard pellets are representative of the remaining core debris.

Co~nsequently, in accordance with the conservative method used, the spherical equivalent of standard full-size pellets was assumed for this evaluation.

As discussed above, a significantly conservative approach was included in the development of the analytical fuel model.

This conservative approach is summarized below:

No credit was taken for the structural or solid materials existing in the debris, though sample data has shown the presence of impurities in all samples evaluated to date.

Unborated water, optimally mixed with the core debris, was assumed e

for the moderating material in all fuel bearing regions of the model.

, OS31P

4410-90-L-0026 The fuel particle size was assumed to be the equivalent of standard full-size pellets.

Actual fission product retention was considerably greater than that which was assumed in the analysis.

The fuel enrichment was represented as 100% TMI-2 batch 3 burned fuel.

Batch 3 fuel is the most highly enriched of the THI-2 fuel.

Results To evaluate the criticality safety consequences of the residual core debris in the RV, ORNL performed an analysis using the Monte Carlo computer program KENO V a (Reference 3) and the model described'above.

The result of this analysis, provided in Reference 1, is a calculated neutron multiplication factor (keff) for this case of 0.945 which includes the addition of 0.025 ok for computer code bias.

?

It is therefore concluded that the residual core debris in the RV will remain subtritical.

Furthermore, because the core debris in the vessel i

is well separated from ex-vessel debris locations, the effect of neutronic coupling between in-and ex-vessel debris accumulations will be negitgible during post-defueling plant conditions.

The analyses were performed assuming that the debris was optimally moderated with unborated water; therefore, the above conclusions would be applicable whether or not the RV is drained. A significant reactivity reduction would be expected with reduced moderation, which would be representative of the draining of the vessel.

Criticality Event Analysis The analysis discussed above applies to the currently estimated residual core debris quantity, its configuration, and its distribution within the RV.

The analysis denenstrated that there is no potential for a criticality event.

This section evaluates the criticality safety of a potential relocation and accumulation of substantial residual core debris to the bottom head.

e With approximately 609 kg of residual fuel (UO ) in the RV, it can be 2

postulated that the drying and spalling of surface films, a seismic event, aging and corrosion, or other unidentified events could cause the residual core debris to accumulate in one area resulting in a potentially critical mass.

However, as evidenced by the extensive defueling effort, the residual core debris and contained fuel has consistently resisted multiple removal attempts by aggressive mechanical means.

Nonetheless, because the total amount of residual fuel in the RV exceeds the SFML, it is necessary to evaluate the significance of a relocation and accumulation of a larger quantity of residual fuel.

Therefore, the following evaluation bounds any credible fuel relocation.

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4410-90-L-0026 The worst-case accumulation of core debris would occur if a substantial quantity of debris relocated to the bottom head.

If this occurred,-it is considered incredible for the debris to collect in an ideal spherical geometry. The vessel geometry would not facilitate collection in such a small and confined arrangement.

Most likely, debris would coilect on the bottom head in a pile or layer.

The relatively large surface area of such a geometry would significantly onchance neutron leakage and, thus, reduce kerf.

This effect was seen in the results of an analysis performed by ORNL.

The analysis assumed more than half of the remaining core debris in the RV (i.e., 350 kg) would collect in the bottom head.

The 350 kg value conservatively bounds the total quantity of Type 1 debris (i.e., loose, fine, granular debris) and Type 2 debris (i.e.,

l surface films) that could accumulate in the bottom head.

The Type 3 debris (i.e., resolidified material) most likely will remain in place and accounts for approximately 339 kg of the 609 kg total in the RV. As a modelling conservative assumption, the relocation included the Type 1 material in the annular gap between the thermal shield and the core barrel, a quantity of approximately 119 kg, that most likely would not

+

relocate due to the geometric configuration and confinement of that

volume, i

The assumed configuration of the debris is shown in Figure 2.

Region Lj contains an optimal mixture of 350 kg of core debris and unborated water.

Region L2 contains approximately 500 gallons of unborated water.

The height of L2 is large enough to consider it an effectively infinite water reflector.

This 500 gallons is significantly more water than is expected to accumulate in the RV throughout PDMS.

The core debris was assumed to be 2.67 wt% U-235 (i.e., burned batch 3 fuel),

standard fuel pellets, and contained no impurities.

The resultant neutron multiplication for this configuration was k rr = 0,913 e

(Reference 1), including a 0.025 ok computer code bias.

Thus, there is no criticality safety concern associated with this unlikely occurrence L

and resultant configuration.

References:

1.

Letter, C. V. Parks, Oak Ridge National Laboratory, to D. S. Williams, GPU Nuclear Corporation, April 9, 1990.

2.

Nuclear Safety Guide, TID-7016 Thomas, J. T., Revision 2, June 1978.

3.

NUREG/CR-0200, Petrie, L. H., et. al., KENO V.a: An Improved Monte Carlo Criticality Program with Super-Grouping, included as Section Fil in SCALE: A Modular Code System for Performing Standardized Computer l

Analyses for Licensing Evaluations, Vols. 1-3, U.S. Nuclear Regulatory l

Commission, Revision 3, December 1984.

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Attachment i 4410-90-L-0026 i

Clarification of DCR Items AFHB Cubicle FH304 AFHB cubicle FH304 was inadvertently omitted from the DCR Table 5-1, i.e., AFHB Cubicles which Contains No Residual Fuel.

FH304 is the annular area on the 347'-6" elevation between the Reactor Building and the Auxiliary Building.

All pathways have been isolated since the accident; thus, this area is void of fuel.

Results of SRG Reviews The TMI-2 Safety Review Group (SRG) performed a detailed review of the preparations and conduct of the residual fuel measurements and the derivation of the residual fuel values reported in-the DCR.

The elements of the fuel measurements program evaluated by the SRG included the video inspection plan, the sample data supporting DCR fuel mass assumptions, an independent review of the videotapes, a verification of the computer program, observations of videotape data collection, a review of post-inspection in-vessel work activities and the subsequent March 1990 video inspection.

During the review of the computer program methodology for determining the volume of fuel in specific locations, a conservative worst case approach was used to ensure that there was no potential for j

the residual fuel quantities reported in the DCR to exceed those used in the criticality safety model.

The SRG concluded that the residual fuel measurements were adequately performed, provided a bounding estimate of the residual fuel mass and were sufficiently accurate to ensure that the residual fuel was properly identified by location and quantity. A comparison of the residual fuel l

measurement results to the DCR criticality safety analysis for the RV 1

l found that the analysis bounded the final residual fuel configuration.

Therefore, the S'lG concluded that the measurements were adequate and agreed with the DCR conclusion that criticality safety was assured.

l DCR Table 5-10 Reference Errors The correct references for the sample analyses detailed on the DCR Table 5-10 are as follows:

Sample Reference 1

OTSG 'B' 5.15 Core Debris 5.34 Bottom Head 5.37 Pressurizer 5.52 MUF-5B (B&W) 5.51 1

MUF-50 (0104) 5.51 MUF-5B (0105) 5.51 MUF-58 (0111) 5.51 0531P

t 4410-90-L-0026 TABLE 1 RESIDUAL FUEL QUANTIFICATION IN THE REACTOR VESSEL DEBRIS CORE RESIDUAL FUEL LOCATION TYPE

  • DEBRIS (ka)

(ko UO2)

Work Platform Recien and Suspended Equipment Westinghouse Vacuum Pump Module 1

1.3 0.9 In-Vessel Filtration System 1

22.7 16.3 Canister Positioning System 1

19.0 13.7 DHCS Inlet / Outlet Piping N/A

__ 0 0

Subtotal 43.0 30.9 Downcomer Reaton Cold leg Flow ueflectors 1

16.5 11.9 Hot Leg Bosses in CSS 1

37.0 26.6 Outer Surface of CSS N/A 0

0 Surface Deposits on RV Cylindrical Shell N/A 0

0 Thermal Shield Outer Surface N/A O_

0 Surveillance Specimen Capsule Holders 1

4.9 3.5 l

Thermal Shield Support Blocks 1

21.2 15.2 (Top Surface)

Thermal Shield Inner Surface 1

164.9 118.6 and Annular Gap Drain Holes at Bottom of 3

0.3 0.2 Thermal Shield Core Catchers / Seismic Restraint Blocks 1

4.0 2.9 Subtotal 248.8 178.9 l

Internals Indexing Fixture Region RV Flange, IIF Flange, and CSS Flange 1

6.8 4.9 Internals Indexing Fixture Inside Surface N/A 0

0 Subtotal 6.8 4.9

  • Debris Type:

1 - Loose / Fine Debris 2 - Surface Film Material 3 - Resolidified Material

    • Includes fuel rod piece assumed full of fuel pellets; the weight per length of rod segment is 1 kg/m and contains 80.3 % UO2 (Reference 5.70). 0531P

4410-90-L-0026 TABLE 1 (Cont'd)

RESIDUAL FUEL QUANTIFICATION IN THE REACTOR VESSEL DEBRIS CORE RESIDUAL FUEL LOCATI,0N TYPE DEBRIS (ka)

(ko 002)

CSS Region Vent Valve Seats (Inner Surfaces) 1 12.2 8.7 Hot Leg Openings 1

0.3 0.2 LOCA Bosses 1

1.1 0.8 Inner Surface of SS N/A 0

0 Top of Lower CSS Flanae 1

1.4 1.0 Subtotal 15.0 10.7 UCSA Reaion Baffle Plate Inside Surface 3

23.3 17.0 Baffle Plate Outside Surface 3

23.3 17.0 Baffle Plate Flow Holes and Bolt Holes 1

14.6 10.5 Former Plates Top and Bcttom Surfaces 1,3 54.8 39.9 Former Plates Edge Holes N/A 0

0 Core Barrel Inner Surface N/A 0

0 Orifice Holes to Thermal Shield Gap 3

1.3 0.9-Subtotal 117.3 85.3 i

LCSA Renion LGRS Top Surface and Peripheral Flow Holes 1,3 56.6 41.3 Between LGRS and LGDP 1,3 2.6 2.0 LGDP Peripheral Flow Holes N/A 0

0 Between LGDP and Forging 1,3 1.5 1.1 Forging Peripheral Flow Holes 3

123.8 89.9 Inside Support Post Stubs N/A 0

0 Between Forging and IGSP (includes IGSP 1,3 182.0**

132.9**

Flow Holes)

Between IGSP and Flow Distributor 1,3 7.6 5.5 Flow Distributor Flow Holes N/A 0

0 Subtotal 374.1 272.7 Bottom Head Region Head Surface i

11.2 8.1 Incore Instrument Nozzles 1,3 12.8 9.2 Standing Incore Guide Tubes 3

8.2

__6.0 Subtotal 32.2 23.3 Surface Film Deposits (See Table 5-6) 2 N/A 2.1 TOTAL = 608.8 kg Ob31P

.4410-90-L-0026.

]

TABLE 2 COMPARISON OF MODEL TO ESTIMATED REMAINING FUEL MASSES

.)

=f MASS OF 00 (kg) 1 2

LOCATION ESTIMATED MODEL Bottom Head.

23.3-200'

?

UCSA' 85.3 240 l

LCSA 272.7-2,470

.i m

NOTES:

1.

Estimated quantities were taken from Table 1 of-this document.-

2.

The other regions of the RV that contain debris werefconsidered to be separated from the areas.of interest by.large distances.-(>30.5 i

cm (12 inches)) and/or.to have smaller-than-SFML quantities.'

1 3.

The neutron multiplication of-a fuel mass is,not onip influenced by mass; the configuration of.the mass is also an important 1

consideration, j

i

)

9 1

i 1

I j

.i

?

i.,

-}

t

[

Ji l

~.

] 0531P J

u

t

.i m

y q

R) o, 67.5 inches (171.E cm)

.l VESSEL i-Ct.

Unborated Weter

-0.10"-

f (Infinite Thickness)

Debris l10'*0" i

Debris:

0.1" Grid Rib 50% Weter 50% ss 5.25" 5.0" Infinite Thickness

.DobrIe Unborsted

--0.1 "

5.0" Water Reflector-0.1"-

Externet To Vesset-Distributor Plate 1.0" AR e 5.0" 45% Water 55% st i

Debris 7

5, 0" Note Drawing is

.-- C.1" not to scale 0.1" Lower Grid Forging l

50% Debris 50% ss 6.0"

- -4. 0"---

/

6.1" Doorts

-2.0"-

Unborated Water 7"

3" -

1,9a AR " 20" Incore %lde T@e -

Suppr: Plate 14" 6" -

2.0" 40% Water 40% Debris Unborated Water 60% SS^

60% 88 (Infinite Thickness)

AR" 2" 06bris 1.5" D

B" Steet 2

0.15" thickness e

Reactor Vessel l

b Watt J

s

/

Hem sphere VESSEL CL

.I I

COMPUTER MODEL FIGURE 1 Void Rec'.on Above Water s

h i

j 1

2 L

1 4

4" of steel j

l i

unborated water i

infinite thickness l

4 rg = 217.7 cm r2 = 234.0 cm Lg = region containing 350 kg of core debris and unborated water L = region containing -500 gallons of unborated water 2

BOTTOM HEAD FUEL MODEL Figure 2 ;

i em