Text

Responses to NUMARC Aquatic Resources Survey
	ML20085M494
Person / Time
Site:	Robinson
Issue date:	11/11/1991
From:	; CONSUMERS ENERGY CO. (FORMERLY CONSUMERS POWER CO.)
To:	;
References
	RTR-NUREG-1437 S, WM, NUDOCS 9111110059
	Download: ML20085M494 (57)
	v • d • e

_......,

NLS-90-159 ATTACHMENT A Carolina rawer & Light Company H. B. Robinson Steam Electric Plant, Unit No. 2 NUMARC Aquatic Resources Survey Responses i

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i 9111110059 9111.11 PDR NUREO 1437 C PDR

y CAROLINA POWER & IJGHT COMPANY H. B. ROBINSON STEAM ELECTIUC PLANT, UNIT 2 NUMARC AQUATIC RESOURCES SURVEY

Background

On July 31,1970 the Atomic Energy Commission (AEC) issued Carolina Power &

Light Company (CP&L) a facility operating license DPR-23 for the H. B. Rchinson Steam Electric Plant (SEP), Unit 2 (hereafter referred to as Unit 2). The low power level restriction was removed on September 23,1970, and the plant was dec!ared commercial on March 7,197L In April 1975, the Nuclear Regulatory Commission (formerly the AEC) issued a Final Environmental Statement (FES) recommending " continuation of Facility Operating License DPR-23 to Carolina Power and Light Company for H. B. Robinson Unit 2, Docket No. 50-261" (copy provided).

The 2,250-acre Robinson Impoundment supplies cooling water for Unit 2 and an associated coal-fired-unit (Unit 1). No other facilities operate on or discharge to the impoundment. The impoundment waters are darkly stained (blackwater), acidic, and relatively low in primary productivity. The aquatic biota consists of organisms typical of blackwater systems with bluegill, largemouth bass, and warmouth as the dominant fish species. A canal (4.2 miles long) discharges heated water approximately mid-impoundment.

A 316 Demonstration [P.L 92-500; Sections 316 (a) and (b)] submitted in 1976 provided the basis for operation of the unit at maximum heat rejection with once-through cooling and an exemption from intake modifications to minimize impingement /entrainment. After the 316 Demonstration was completed, environmental monitoring studies continued to be conducted each year through the present to confirm the results of the 316 Demonstration and to identify any additional measurable impacts to the aquatic resources.

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RESPONSES TO NUMARC AQUATIC RESOURCE SURVEY OUESTIONS H.B. ROBINSON SEP, UNIT 2 (ROBINSON IMPOUNDMENT)

Several em*ironmental reports including a 316 Demonstration document, the NRC FES, and a series of CP&L environmental monitoring reports serve as the basis for CP&L's response to the NUMARC survey for the H. B. Robinson SEP, Unit 2. These reports are referenced in responding to the following questions.

1.

Post-licensing modifications and/or changes in operations of intake and/or discharge systerns may have altered the effects of the power plant on aquatic resources, or may have been made specifically to mitigate impacts that were not anticipated in the design of the plant. Describe any such modifications and/or operational changes to the condenser cooling water intake and discharge systems since the issuance of the Operating License.

Response

No intake / discharge modifications have been made since the issue of the operating license to mitigate environmental impacts. Minor changes (e.g.

j replacing a pump, etc.) have been made but none that have measurably altered the effects of Unit 2 on the aquatic resources.

2.

Summanze and describe (or provide documentation of) any known impacts on aquatic resources (e.g., fish kills, violations of discharge permit conditions) or National Pollutant Discharge Flimination System (NPDES) enforcement actions that have occurred since issuance of the Operating Lc' nse. How have e

these been resolved or changed over time? (The response to this question should indicate whether impacts are ongoing or were the result of start-up problems that were subsequently resolved.)

Response

Localized impacts to fish, benthos, zooplankton, and aquatic vegetation from the heated discharge are known to occur in the impoundment. The 316 Demonstration originally described the effects of the discharge on aquatic organisms (CP&L 1976b). The extent of the thermal impact was considered limited by state (South Carolina Department of Health and Em'ironmental Control) and federal (U. S. Environmemal Protection Agency) regulatory agencies and no action was required.

Skeletal deformities in fish, particularly bluegill, were detected during fisheries monitoring programs in the mid to late 1970's.

The deformitics were described in detail in CP&L (1979a). In 1979, fish population declines were noted downstream of the discharge concomitant with a increase in deformity

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incidence rates in bluegills (CP&L 1980). Intensive bioassay studies were begun to determine the cause of both problems and ultimately copper loading in the impoundment was found to be responsible (CP&L and LMS 1981).

The copper source was determined to be corrosion / erosion of the Admiralty 2

Brass

condenser tubes within the power plant. The tubing was replaced in 1981 eliminating the copper loading in the impoundment. Fish populations recovered after the tubing change and the skeletal deformities disappeared.

The fishery has maintained a higher standing crop than the period when Admiralty Brass' tubing was in use.

No fish kills have been detected or reported in the impoundment since the issue of the operating licerse.

' DES permit violations directly related to the operation of Unit 2 have been wermal in nature (exceedances of daily and monthly average temperature limits). These occurrences were reviewed with the appropriate regulatory agencies at the time, and it was understood that enforcement actions would not be taken, pending continued biological monitoring by the Company to verify that no adverse consequences occurred. Most of these exceedances occurred in 1986, during a recorded-breaking drought. The only other permit violations were indirectly associated sewage treatment plant exceedances related to difficulties in start-up of that facility in 1986.

3.

Changes to the NPDES permit during ooeration of the plant cotdd indicate whether water quality parameters were determined to have no significant impact: (and were dropped from monitoring requirements) or were subsequently raised as a water quality issue. Provide a brief summary of changes (and when they occurred) to the NPDES permit for the plant since issuance of the Operating Ucense.

Response

Unit 2 has had no water quality-related changes to the permit except for the addition of thermal limits fobowing the 316 Demonstration in the mid-70's (see question 9). The original post-operating license NPDES permit required that biological studies be conducted to determine the effects cf cooung water on the lake, and after thore studies made the successful demonstration, the permit was modified in 1978 to incorporate thermal limits. The last permit was issued in 1983 and continued to incorporate thermal limits on the once-through cooling water at the end of the discharge canal. In the current

4 NPDES permit renewal application, the Company has requested modification of the thermal limits to lessen the possibility of thermal permit violations (see response to question 2 for explanation). This effort is expected to have a favorable resolution because the new requested... nits allow for a more natur i and even rise in lake the temperatures.

4.

An examination of trends in the effects on aquatic resources monitoring can indicate whether impacts have increased, decreased, or remained relatively stable during operation. Describe and summarize (or provide documentation of) results of monitoring of water quality and aquatic biota (e.g., related to NPDES ' permits, Environmental Technical Specifications, site-specific monitoring required by federal or state agencies). What trends are apparent over time?

Response

A document that best describes long-term trends of water quality variables and aquatic organisms is the Interpretive Report (CP&L 1988).

One documented trend was the response of the fish population to the increase and subsequent decline of copper input into the impoundment (described in responso 2 above). Another trend described in the report is a decline in zoopir ikton populations beginning in the early 1980's and continuing to the present. This trend was attributed to a significant increase in predation from fish populations which were increasing during that period.

5.

Summarize types and numbers (or provide documentation) of organisms entrained and impinged by the condenser cooling water system since issuance of the Operating Ucense. Descrik any seasonal patterns associated with entrainment and impingement.

How has entrainment and impingement changed over time?

Response

The 316 Demonstration document (CP&L 1976a) contains information on the types and numbers of fish entrained (1975 1976) and impinged (1973-1975) by the unit intake structure (Tables 4.8.1 and 4.9.2). Entrainment samples were dominated by percid larval fish (Etheostoma m.). The only other larvae collected in the entrainment samples were small numbers of centrarchids 3

(Lecomis m.) and catastomids. Density was reported in number /100 m in the 316 Demonstration but in subsequent years densities were reported in 3

number /1000 m. Comparing densities from 1976-1980, entrainment remained relatively constant with respect to species and numbeis (CP&L 1979b,1980, and 1982).

These same documents describing entrainment contain the impingement data collected from 1973-1980. Bluegill was the major species collected (> 90%) in impingement samples from 1973-1975 [316 (b) demonstration, CP&L 1976b]. Similar rates were found in 1980 (CP&L 1982).

Based on a determination in 1977 by the EPA and agreed upon by regulatory ag ncies that entrainment and impingement was not significantlyimpacting the fimery, this sampling was deleted from the monitoring program in 1980.

6.

Aquatic habitat enhancement or testoration efforts (e.p, anadromous fish runs) during operation may have enhanced the biological communities in the vicinity of the plant. Alternatively, degradation of habitat or water quality may have resulted in loss of biological resources near the site. Describe any changes to aquatic habitats (both enhancement and degradation) in the vicinity of the power plant since the hsuance of the Operating License including those that may have resulted in different plant impacts than those initially predicted.

Response

No aquatic habitat improvement has been required for mitigation in Robinson Impoundment; however, a few artificial reefs were installed in an attempt to increase fishing success for anglers by concentrating fish in an accessible location.

Degradation of habitat from heeted water in vicinity of the discharge (described in the 316 (a) Demonstration) and by the effects from copper loading in the impoundment in the late 1970's and early 1980's were both detailed in the response to Question 2.

7.

Plant operations may have had positive, negative, or no impact on the use of aquatic resources by othen. Harvest by conunercial or recreational fishermen may be constrained by plant operation. Alternatively commercial harvesting may be relatively large compared with fish losses caused by the plant.

Descrilx: (or provide documentation for) other nearby uses of waten affected by cooling water systems (e.g., swimmmg, boating, nanual harvest by commercial and recreational fisheries) and how these impacts have changed since issuance of the Operating Ucense.

Response

Robinson Impoundment is open to the public for recreational purposes. One public access ramp and two privateh owned access ramps exist on the lae.

Uses include swimming, boating, water skiing, fishing and 'aunting. Privately owned property with houses and boat docks exist along the eastern shore of the lake. No restrictions on the recreational uses have been documented for Robinson Impoundment, but it is likely that some limit on swimming and skiing in the area of the discharge exists during the hottest months of the year (usually July and August) because of the warm water temperatures. However, the warm water likely extends the swimming and skiing season in spring and fall. Winter fishing in the vicinity of the discharge canal also occurs. No commercial fishing occurs at the Robinson Impoundment.

4 8.

Describe other sources of !mpacts on aquatic resources (e.g., industrial discharges, other power plants, agriculturr,1 runoff) that could centribute to cumulativ' 7 pacts. What are the relative contributions by percent of these sources, inJuding the contributions due to the power plant, to overall water quality degradation and losses of aquatic biota?

Response

The Company is not aware of any other significant industrial or agricultural input into the lake that could potentially impact aquatic resources. Monitoring Black Creek upstream of the lake has not revealed any unusually elevated water quality variables. The Sandhills National Wi!J!ife Refuge, peach orchards, and a small winery are located within twenty miles upstream of the Robinson Impoundment but are thought to have no significant influence on the impoundment.

9.

Provide a copy of your Section 316 (a) and (b) Demonstration Report required by the Clean Waste (sic) Act.

What Section 316(a) and (b) determinations have been made by the regidatory authorities?

Response

The 316 Demonstration (CP&L 1976b) performed in the early 1970's provided the basis for regulatory exemption (EPA 1977) from the construction and use of cooling towers [316 (a)] and intake structure modifications to limit entrainment/ impingement impacts [316 (b)]. Regulatory authorities have determined that the demonstration showed that a balanced and indigenous population of fish and shellfish could be maintained in the, absence, of such plant modifications. A copy of the demonstration document and the EPA's Findings of Fact is provided. Entrainment and impingement sampling was deleted from the monitoring program after 1980.

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l' DOCUMENE CirED CP&L 1976a.

H. B. Robinson Steam Electric Plant 316 Demonstration. Summary.

Carolina Power & Ught Company, Raleigh, NC.

1976b. H. B. Robinson Steam Electric Plant 316 Demonstration. Volume 11.

Carolina Pawer & Light Company, Raleigh, NC.

1979a.

H. B. Robinson Steam Electric Plant 1976-78 environmental monitoring program results. Volume I. Summary. Carolina Power & Light Company, Raleigh, NC.

1979b.

H. B. Robinson Steam Electric Plant 1976 78 emironmental monitoring program results. Volume II. Carolina Power & Light Company, Raleigh, NC.

1980. H. B. Robinson Steam Electric Plant environmental monitoring program.

1979 annual report. Carolina Powe.r & Light Company, Raleigh, NC.

1982. H. B. Robinson Steam Electric Plant environmental monitoring program.

1980 annual report. Carolina Power & Light Company, Raleigh, NC.

1988.

H. B. Robinson Steam Electric Plant environmental monitoring program.

Interpretive report June 1988. Carolina Power & Light Company, Raleigh, NC.

CP&L and LMS.1981. Investigations of deformities and lowered recruitment of bluegill (Lenomis macrochirus) in Robinson Impoundment.

Carolina Power & Light Company, New Hill, NC and Lawler, Matusky, and Skelly Engineers, Pearl River, NY.

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ATTACHMENT 1 l

RESPONSES TO NUMARC QUESTIONNAIRE TO SUPPORT PART 51 RULE CHANGE SOCIOECONOMIC QUESTIONS Carolina Power & Light Company H.

B.

ROBINSON STEAM ELECTRIC PLANT, UNIT NO. 2 DOCKET NO. 50-261/ LICENSE NO. DPR-23 Responses Apply to Entire Site

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SOCIOECONOMIC IMPACT OF H.

B.

ROBINSON, NO. 2 1.

Estimate the number of permanent workers on-site for the most recent year for which data are available.

The number of permanent workers on-site for 1990 is 650 utility and contractors for HBR2.

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Estimate the average number of permanent workers on-site, in 5 year increments, starting with the issuance of the plant's operating license.

1970 Estimates Not Available 1975 Estimates Not Available 1980 356 Permanent Workers 1985 709 Permanent Workers 1990 650 Permanent Workers 3.

Provide for the following three cases:

A.

a typical planned outage B.

an ISI outage C.

the largest single outage (in terms of # of workers involved) to date.

(1) estimate of additional workers involved (2) length of outage (3) months and year in which work occurred, and cost (4) exposure.

Response for 3h - Typical Planned Outage Length:

8 Weeks Cost:

8 Million Dollars Dose:

350 man rem Manpower: 1200 to 1500 temporary and permanent plant workers.

Response for 3B - ISI Outage:

Length:

170 days (February 26, 1932 through August 19, 1982.)

Cost:

15.844 Million Dollars Dose:

1242.956 man rem Manpower: 1195 temporary and permanent plant workers (breakdown by task is not available.)

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SOCIOECONOMIC IMFACT OF HDR2 (CONT'D)

Response for 30 - Largout Single Outage - Steam Generator Replacement p

by Length:

349 Days (January 26, 1984 to J nesry 9, 1985) b'<

Cost:

144 Million Doll. ara Dose:

3355.954 canrer..

HanpoWor 12';s Temporary and Permanont Plant Workers (breakdown by ptincipal tanks not available)

Attached is a done breakdown by major ta '.

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IIBR2 Exposure Dreakdown

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1984 Steam Ganorator Replacement Outage Actual Man-Rem 1.

Mod 713 - Steam Generator Replacement 1206.820 2.

Steam Generator Inspections a.

Eddy current inspection prior to 35.650 steam ganerator replacement b.

Eddy current inspection after steam 8.470 generator replacement 3.

IIcalth physics coverage a.

total exposure for tage 389.888 b.

Exposure for steam 9enerator (119.100) soplacement 4.

Valve operation, inspections and 149.707 surveillance 5.

Decon and rndwasto 156.036 6.

ISI inspection and 79-14 hanger 137.253 inspection wal.;down 7.

Refueling work includes all head work 136.691 except initial defueling a.

Initial defueling (included in (34.275)

Steam Generator Replacement 8.

Valve Work, (removal, repair, replace 41.350 and repack) 9.

I&C Work 17.490 l

a.

Calibratir i 10.830 l

b.

Misc. equ.oment replacement 2.315 l

c.

NIS detectsr repla.coment 0.450 d.

RTD repair 0.150 e.

Heat tracing 0.600 f.

Penetration wou'-

0.425 g.

ILRT setup 0.900 h.

Pull cables 0.150 1.

Repair pas 0.400 j.

Repair elevator 0.875 k.

Repair emergency lighting 0.395 10.

Insulation - (Pressurizer' and Mod 806 27.110

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JIDR2 Exposure Dreakdo!fn 1984 Cteam Generator Replacement Oqiang Continued 11.

Bellows repair (SP-587) 16.390 12.

Misc. grouting and painting 15.750 13.

Fire watch in containment and auxiliary 74.767 building 14.

Service water piping repair 97.004 15.

Seismic support repairs (Mod 492) 240.765 16.

Replace Icvol transmitters in CV sump 6.965 (Mod 525) 17.

Reactor vossol lovel indication system 94.310 (Mod 526) 18.

Rolocatien of pressurizer spray valves 111.305 (Mod 612) 19.

Service water pipe relocation (Mod 686) 3.370 20.

Pressurizer safety and relico valvo 18.940 system (Mod 729) 21.

Steam generator blowdown and wet layup 164.298 system (Mod 747) 22.

Hydrogen recombiner (Mod 750) 6.720 23.

Dedicated alternate shutdown system 28.200 (Mods 755 and 795) 24.

Charging system improvements (Mod 7660 21.533 2f LOOSE PARTS MONITOR (MOD 783) 23.745 26.

"C" accumulator support (Mod 816) 0.735 27.

"A" RTD bypass loop valves (Mod 827) 8.650 28.

Misc. Work 44.784 a.

Filter 1.

waste holdup tank 2.37'i 2.

Seal water injection 0.660 3.

Reactor coolant 1.760 4.

Spent fuel pit 0.210

IIDR2 Exposure Dreakdown 1984 Steam Generator Replacement Outage b.

Numbers 1 and 2 sumps 2.105

.i' c.

Boric acid evaporctor 5.695 i

d.

Waste evaporator 2.480 c.

Boric acid storage tank area 1.025 f.

IIVE and !!VH 1.315 g.

Spent fuel pit (sip fuel) 1.940 h.

Repair debris screens 1.774 i

1.

Reactor coolant pumps 1.015 j.

Misc. pumps 1.665 k.

Pour concreto 1.825 1.

Snubber 0.770 m.

Waste gas compressor 0.670 n.

Charging pump room 0.185 o.

Painting 0.990 p.

Fire barriers 0.670 q,

RHR pit 0.345 r.

Repair grating 0.025 s.

Repair doors 0.370 t.

Rotate pump shafts 0.035 i

u.

Misc. insulation work 14.380 j

29.

Ilands on inspection 35.434 30.

General maintenance 36.323 4

TOTAL 3355.954 l

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TLD D arsure (REM)
~
Com7any-lat Quarter 2nd Qua r *.er 3r d Oua rt e r Tota 1 3.
CI'AL Plant
~
a.
Opera tions 19.708-48.366 10.808 78.882 b.
Herhanics 24.424 69.307 14.188 107.919 7.156 19.206
_12.113 38.475 c.
16C
~
10.382 31.48?
4.711 46.580 d,
FARC e.
Engineers 5.728 18.766 2.925 27.419 f.
QA 7.040 8.109 1.350 11.499 g.
Others 0.560-5.6 81__
0.421 6.662 r
PLANT TOTAL 69.998 200.922 46.516 317.436 2.
CP&L Corporate i
s.
Engineers 2.J30 8.576 4.085 14.791 b.
Mechanics 1.090 19.859 12.631 33.580 c.
I&C 1.768 2.955 0.014 4.737
- CORPORATE TOTAL-4.988 31.390 16.730 33.108-g 3.
IRM a.
H.P.'s 23.147 58.188 8.W29 90.164 b.
- De con
. '17.248 56.621
'24.365 98.234 1RM TOTAL-40.395 114.809 33.194 188.398 4
Daniels '
36.823 199.400-32.079 268.302 5.
- Westinghouse 33.389 145:170 1.414 187.973 6.
Power Plant Maintenance 21.796 37.583 6.979 66.358 7.
. Yearsin 15.766 62.009
.5.910 83.685 8.
Dudley 14.546 13.901 2.0 59 30.506 2.261 4.9 90 0.726 7.977 9.
Barna
~
~~10. Gilbert 1.545 1.542 0.881, 3.968 11; Southern Space 0.408 -~~
~~1.747 0.470 2.625 2.783~~
~~12. General Electric 0.476 2.307 1.060 2.060~~
~~13. Exxon:~~
7.915 7.915 14.-Clean Co.
15.
KRC -
0.183 0.464 0.053 0.700 8.094
,'16.
-SWE1 0.027 8.067 1.085 17.. J. A. Jones 0.012 1.073 0.370
~~18. -NNI 0.297 0.023~~
- 19. NCS
'0,101 0.111 0.020 0.:32
~~20. Misc.~~
'1.223 7.493 1.715 10.431-
.T0TAL
'244.234 841.976 156.746 1.242.956:
RWP Dame - official Dose ID tm -
, g Official Dose t
42M56
- - - 1,442
+16.08%
x 100
=
=
x 100
=
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Scheduled Outage Days t
+)51 x 100
(
=
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y i
1-ATTACHMENT 5 RESPOPSES TO NUMARC QUEcTIONNAIRE TO SUPPORT PART 51 RULE CHANGE SOCIOECONOMIC QUESTION # 4 Carolina Power & Light Company H.
B. ROBINSON. STEAM ELECTRIC PLANT, UNIT.NO. 2 BRUSWICK STEAM ELECTRIC PLANT, UNIT NOS. 1&2 SHEARON HARRIS NUCLEAP POWER PLANT Response Applies to Entire Site at All Three Plants i
1 1
i
~-
w 1
QUESTIDs: 10 understand the plants fiscal lepcrttace to specific jurisdict a.5, e
for 1983, 1955, 1:d the latest year for which data are availabse; estisate the entire plan;'s taxable assessed value ar.d the ascent of tave; pale to the state and to each local taxing Jurisdict A.
FESNNSE RFUNSWICK HARRIS M!lN3DN 1920 1985 1939 1980 1935 liS?
1960 1935 1989 TAXA 8t! ASSEESED VALUE 525,335,352 659,471,367 649,537,154 4t0,383,107 1,353.582,34! 1.385,433,199 10.237.259 18,210,6 "
27.767.309 1 AXES FAID 2,839,511 4,187,643 4,124,561 3 c41,lE0 7,?S6,13o 10.944,S22 I,372,267 2.194.422 4 62,575 l
l l
l i
e
ATTACHMENT 4 RESPONSES TO NUMARC QUESTIONNAIRE TO SUPPORT PART 51 RULE CHANGE WASTE MANAGEMENT QUESTIONS Carolina Power & Light Company H..
B.
ROBINSON STEAM ELECTRIC PLANT, UNIT NO. 2 BRUNSWICK STEAM ELECTRIC PLANT, UNIT NOS. 1 & 2 SHEARON HARRIS NUCLEAR POWER PLANT Responses Apply to Entire Site at All Three Plants f
RESPONSE TO NUMARC SURVEY IN SUPPORT OF 10CFR51 ANFR A.
SPENT FUEL QUESTIONS EliE ME litiE l.
A.
Reracking of spent fuel Completed Completed N/A B.
Control rod repositioning No No No C.
Above ground dry storage Yes No No D.
' anger fuel burnup 6 0,000 90,000
.560,000 FND/MTU FND/MTU MWD /MIU E.
Transshipment Late 1990 Yes Peceipt Plant 2.
A.
Continue technique No Yes Yes B.
Change or modify Yes No No 3.
A.
Reracking of spent tuel B.
Control rod repositioning No No No C.
Above ground dry storage Maybe Maybe No
_6v,000 D.
Longer fue1 burnup 3f 0, r)00
<60,000 MVD/MTU MVD/MTU MWDAtIU E.
Transshipment Yes Yes Yes 4.
Techniques Adequate 1.
Operating license Yes Yes Yes i
2.
20-year extension No No No 3.
Other plans No No No 5.
Acquire additional land 1.
Operating license No No No 2.
20-year extension No No No
6.
Additional construct activity 1.
Operating license No No No 2
20 year extension Yes Yes Yes 7.
Amplification on Questior. 6 Should additional at-reactor spent fuel storage be required beyond the operating liceise, it will most likely be provided through above 6round dry storage facilities or such cther ieans as may be technologically and economically acceptizble.
4
-___________-____________._._.-._._____-_.._______________-_-_._.____---.-.________--______-_-__-_._-____--_-__._--J
. :/
l
+.
B.
LOW-LEVEL RADIOACTIVE WASTE MANAGEMENT QUESTIONS YES ASSUMING THE COMPLETION OF A SOUTl! EAST COMPACT SITE FOR LOW 3.
LEVEL WASTE. BURIAL.
(Ti!IS APPLIES TO ALL THREE PLANTS) 2.
COMPACTION, THEN STORAGE IN AIR ABOVE GROUND STORAGE BUILDING / FACILITY.
POSSIBLE INCINERATION, Ti!EN STORAGE IN BUILDING.
(Tl!IS APPLIES TO ALL THREE PINITS) 3.
SEE ATTACHMENT
~~4. SEE ATTACHMENT 5.~~
NO 6.
NA 7.
YES 8.
NO CONSTRUCTION ACTIVITY TO DATE.
IN PRE-PLANNING STAGE.
NO MAJOR PLANT MODIFICATIONS OR REFURBISHMENTS THAT ARE LIKELY TO 9,.
OR GENERATE UNUSUSAL VOLUMES OF LOW-LEVEL RADIOACTIVE WASTE PRIOR TO, DUhING, THE RELICENSING PERIOD FOR ALL THREE PLANTS.
PROBABLY JUST RECIRCULATION SYSTEM MODIFICATIONS, BUT NONE YET ANTICIPATED.
h se l
l NUMARC QUESTIONNAIRE SPECIFIC METHODS OF RW MANAGEMENT &
% CURRENT LLRW BY VOLUME IS MANAGED BY:
B.N.P.
[ Brunswick Nuclear Project)
< 10%
A. COMPACTION:
50-60%
B.
WASTE SEGREGATION:
0 C.
DECONTAMINATION OF WASTES:
3-4% current 25-30% prior D.
WASTE SORTING: (CLEAN VS, CONTAMINATED.)
61%
E. OTHER MANAGEMENT PRACTICES:
SPECIFIC METHODS A. Compacts higher activity D. A.W / filters and non incinerable low activity _radwaste to conserve space & reduce number of packages stored onsite.
B.
Radwaste is segregated at the point of generation where practical. Clean or unnecessary packaging, bracing or cor. tainers
.are removed prior to entry into the power block area. Radwaste is also further segregated at the point of packaging for shipment.
C. Have onsite decon capability. Do not usually decontaminate waste products. unless it is cost justifiabls. Decon priurities are on job / mod relatedlcoroponents and tools / equipment.
D. Radwaste is sorted based on dose rates of the wasta. If a waste is.<= 5 Mr/hr it is sorted to remove the itons that cause the waste to be >'lmR/hr. Waste that is <= 1 Mr/hr is frisked to remove any clean. waste from the contaminated wastes. Radwaste from known high contamination areas are not usually frisked.
E. Strive-to keep the contaminated square feet of plant space-to a minimum to prevent the generation of radioactive waste / material.
Have aggressive rad. taste volume reduction program that attempts to eliminate generation of unnecessary radwaste and reduce the amount of radioactive material (tools & equipment) that become contam-inated. All ~10w activity dry active waste is sorted / segregated and shipped to S. E.G.,- Inc.
for further volume reduction prior to burial.
e
,e-r
~
ANTICIPATED PLANS FOR LLRW MANAGEMENT &
% OF ANTICIPATED LLRN VOLUME MANAGED BY:
B.N.P.
< 10%
A.
COM9 ACTION:
> 70%
B.
WASTE SEGREGATION:
0 C.
DECONTAMINATION OF WASTES:
< 10%
D.
WASTE SORTING: (CLEAN VS. CONTAMINATED.)
>61%
E.-OTHER MANAGEMENT PRACTICES:
SPECIFIC PLANS A.
Do not foresee.any change in current methods.
B.
Do not foresee any change to current methods.
C.
De not foresee any change tc current methods. Will keep up with changes in technology and change practices as necessary.
D. Do not foresee any change to current methods. Will keep un with-changes in technology and change practices as necessary. Also hava to factor 'in - the coct benefit of waste sorting / frisking.
If technology changes so it is cost prohibitive to sort and frisk you may see - a reduction in this area. Also, as control methods get better we should see less clean waste in the contaminated waste stream-therefore eliminating the need to remove clean material.
E..Do not foresee any change to current methods. Will strive to keep plant. contaminated square footage-to a minimum. ~ Also plan to keep an. aggressive volume raduction program for further up front elimination of radioar:tive waste. Plans are to-keep sending low activity radwaste to S.E.G.
for. reprocessinq & volume reduction until current technology offers improved processing.
i:
I i
NUMARC QUESTIONNAIRE SPECIFIC METHODS OF RW MANAGEMENT &
% CURRENT LLRW BY VOLUME IS MANAGEO BY:
R.N.P.
[H.B. Robinson Nuclear Project) 0 A.
COMPACTION:
60-75%
B.
WASTE SEGREGATION:
1-5%
C.
DECONTAMINATION OF WASTES:
70%
D.
WASTE SvRTING: ( CLEAN '.'S. CONTAMINATED.)
75%
E.
OTHER MANAGEMENT PRACTICES:
SPECIFIC METHODS A.
No onsite compaction is done to reduce radwaste volume.
B.
Radwaste is segregated at the point of generation where practical. Clean or unnecessary packaging, bracing or containers are removed prior to entry into the power block area. Radwaste is also further segreJated at the point of packaging for shipment.
C. Onsite decon is job specific. Do not usually decontaminate waste products, unless it is cost justifiable. Decon priorities are on iob/ mod related componer.ts and tools / equipment.
D. Radwaste is sorted based on dose rates of the waste. If a waste is <= 5 Mr/hr it is sorted to remove the items that cause the waste to re > 1mR/hr. Waste that is <= 1 Mr/hr is frisked to remove any cle an waste frr the contaminated wantes. Radwaste from kr.own high contamination areas are not usually frisked.
E. Strive to keep the contaminated square feet of plant space to a minimum to prevent the generation of radioactive waste / material.
All low activity Dry at.tive waste is sortec/ segregated and shipped to S.E.G.,
Inc. for further volume reduction prior to burial.
t ANTICIPATED-PLANS-FOR LLRW MANAGEMENT &
.% OF ANTICIPATED LLRW VOLUME MANAGED BY:
R.N.P.
O A.
COMPACTION:
> 75%
B. WASTE SEGREGATION:
1-5%
C.
DECONTAMINATION OF WASTES:
< 70%
D. WASTE SORTING: (CLEAN VS. CONTAMINATED.)
75%
E.
OTHER MANAGEMENT PRACTICES:
SPECIFIC PLANS A.
Do not - foresee any onsite radvaste compaction for volume o
reduction.
B.
Do not foresee-any change'to current methods.
C. Do not foresee any change tc, current methods. Will keep up with changes in technology and change practices as necessary.
D. Do not foresee any change to current methods. Will keep up with changes in technology and change practices as necessary. Also have to factor. in the cost benefit of wasta sorting / frisking.
If technology changes so it io cost-prohibitive to sort and frisk you may see a reduction in this area. Also, as control _ methods get better we-should see less clean waste in the. contaminated waste stream therefore eliminating the need to remove clean material.
E.
Do not_ foresee any cnanga to current' methods. Will strive to keep plant contaminated square f.cotage to-a minimum. Plans are to keep sending low activity radwaste to S.E.G.
for reprocessing &
volume reduction until current technology offers improved procecsing.
(
i 1-NUMARC QUESTIONNAIRE FPECIFIC METHODS OF RW MANAGEMENT a
% CURRENT LLRW BY VOLUME IS MANAGED BY:
(Marris Nuclear Project)
H.N.P.
0
-A.
COMPACTION:
60-70%
B.
WASTE SEGREGATION:
1-5%
C.
DECONTAMINATION OF WASTES:
50-75%
D.
WASTE SORTING: (CLEAN VS. CONTAMINATED.)
80-85%
E.
OTHER MANAGEMENT PRACTICES:
SPECIFIC METHODS A '. No ensite compaction done currently done to reduce radwaste volumes.
B. Radwaste is segregated at the point of gsneration as practical.
Clean or unnecessary packaging, bracing or other material removed prior to entering the power block area.
Radwaste is further segregated at the packaging statica prior to shipment.
C.
Onsite decon is job cpecific. Waste products are not routinely decontaminated. Decon priorities are on job / mod related equipment and tools / equipment.
r D.
Radwaste is sorted based on dose rates of the waste. All waste that is <.5 1*'-/hr is sorted and frisked to remove clean items.
Approximately 50 % or better of this level waste is finally removed as clean material. Wastes up to 2 mR/hr are sorted to remove all 7
items >
.5 mR/hr. Then the waste is frisked to recover clean material.
E.
Keep contaminated square feet of plant space to a minimum to prevent generation of radioactive waste / material. All ow activity dry active waste is sorted / segregated and shipped to S.E.G.,
Inc.
for further volume reduction prior to burial.
l
4.-
~
4 o
ANTICIPATED PLANS FOR LLRW MANAGEMENT &
% OF ANTICIPATED LLRW VOLUME MANAGED BY:
H.N.P.
O A. COMPACTION:
>70%
B. WASTE SEGREGATION:
1-S%
C.
DECONTAMINATION OF WASTES:
<75%
D. WASTE SORTING: (CLEAN VS. CONTAMINATED.)
75%
E. OTHER M7J'AGEMENT PRACTICES:
SPECIFIC PLANS A.
Do not -forosee any onsite radwaste compaction for volume reduction.
B.
Do not forcsee any change to current methods.
C.
Do r at foresee any change to current methods. Will keep up with changes in technology and change practices as necessary.
D. Do not foresee any change to current methods. Will keep up with changes in technology and change practices as necessary. Also he.ve lo f actor in -- the _ cost benefit of waste sorting / frisking.
If tochnology changes'so it is cost prohibitive to sort and frisk, you may se4 a, reduction in this area, also, as control methods get
- bother we should'see less clean waste-in the contaminated waste
~~stream, therefore eliminating the need-to remove the clean inaterial, u~~
n____________________________________________________-____--__
E.
Do not foresee-any change to current methods. Will strive to keep plant contaminated square footaae to a minimum. Plant are to ktep sending low activity radwaste o S.E.G.
for reprocessing &
volume reduction until current-technology offers improved.
processing.
>

ML20085M494

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