ML20151N756

1987 Annual Environ Operating Rept & Aerial Photographs

ML20151N756
Person / Time
Site:	Byron
Issue date:	12/31/1987
From:	Pleniewicz R COMMONWEALTH EDISON CO.
To:	Davis A NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III)
References
BYRON-88-0350, BYRON-88-350, NUDOCS 8804260009
Download: ML20151N756 (51)

Text

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d ATTACIEENT A Byron Station Environmental protection plan 1987 Annual Environmental Operating Report Section 4.2 Environmental Monitoring Section 4.2.1 Aerial Remote Sensing The aerial photographic monitoring program was done in 1987, as scheduled in the Environmental protection plan for Byron Station. The aerial photographs and the field survey covered an area of approximately one mile radius centered at the Byron Station cooling towers. The photographs were taken at a scale of one inch to five hundred feet using false color infrared film. The photography was done on August 17, 1987 and the field survey was done on Septeaber 12, 1987.

The examination and analysis of the photographs and the field su:vey was performed by a consulting plant pathologist. Dead, dying and stressed foliage signatures and different plant types were identified and marked on the photographs and then inspected during the field survey to determine the cause of the sigratures on the photographs.

The plant pathologist prepared a report covering the results of the analysis of the aerial photographs and the ground truthing field survey of the suspect areas. The conclusion being that a wide-rango of plant species were observed in the survey area but no saline aerosol or salt injury was identified.

Abnormal foliage signatures seen on the photographs or in the field survey were feind to be the result of herbicide applications, plant diseases and water damage or from planting and cultivating problems. A copy of the consultant's report is submitted herewith together with a set of positive color transparencies encompassing the survey area.

The 1987 aerial photographic monitoring represents the second operational survey, the third operational survey is scheduled to be done during the sunser*

of 1989.

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t ATTACHMENT A Byron Station Environmental Protection Plan 1987 Annual Environmental Operating Report Section 4.2 Environmental Monitoring Section 4.2.2 Confirmatory Sound Level Survey A. During 1987, sound level surveys were performed at various points around the perimeter of Byron Station as well as noise sensitive locations within a five mile radius of the plant. All measurements were performed with Unit 1 and Unit 2 under normal operation and the cooling tower operating with a water flow rate near design capacity. Surveys were performed during the sununer snonths with the foliage at near peak presence.

Real time octave and one-third octava band data was acquired at each tricrophone location. In addition, a twenty minute recorded sample was taken at each site location which was later analyzed in the Commonwealth Odison System Operational Analysis Department laboratory to determine the statistical variation of the sound levels. Efforts were made during field acquisition to eliminate extraneous noise events fitos the recorded samples. This was ocne so as not to bias the tape recordings with data that would not allow a true assessment of the amount of noise generated from the facility. However, in certain situations, the tape recorded data is simply an indication of the ambient noise as opposed to the stacion's contribution to it. This was the case either in high background noise areas or in areas distant enough fr.xa the Generating Station so that plant activity was r.ot apparent. At some locations the traffic noise was the dominant noise. Since traffic noise was constant, efforts to eliminate it from the recordings were futile. In these cases, this information has been noted on the data sheets and the noise measured cannot be construed to indicate the actual impact of the facility upon that area.

All measurements taken conform with ANSI Standards and Procedures for Type-1 instrumentation setups. The results of the data analysis include the daytime, nighttime, and day / night equivalent sound levels measured. This appears on the data sheets in the form of exceedance levels of L-1 and L-99. The L-1 level is a statistical parameter indicating the noise level which.is exceeded 1% of the time. This could be considered the high range of the noise levels l present. On the other hand, L-99 indicates the noise level exceeded 99% of the time and can be considered to be the lowest levels present at this locale.

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ATTACHMENT A (Continued)

The data sheets, also delineate the overall A-weighted sound level measured as well as the octave band levels between the frequency bands of 31.5 to 8000 Hz center frequencies. Furthermore, the appropriate regulatory criteria or guidelines appear on the forms.

The State of Illinois Regulations were amended on January 22, 1987. The major amendment to the previous regulations consists of the Leg, with a one-hour reference time, as the measurement which shall be utilized to determine compliance with sound emissions standards of Part 901. Analyses of the tape recordings indicate compliance with the State of Illinois regulations. At certain locations, the numerical values would exceed the criteria at various octave band frequencies. In these situations, a notation on the data form explains the reason for the high value. A tonal ccaponent was found at Location-1 as noted on Data Sheet 4.2.2-1. However, this level would not exceed the State of Illinois discrete tone rule, 901.106.

Overall review of the data alvo indicates compliance with Federi.1 EPA and HUD criteria. Noise levels at several locations would exceed Federal EPA and HUD criteria. However, again, explanations are offered by tha notations on the i data forms.

Similar sound level readings will be made at the sams location during the winu e manths and a final assessment of the environmental impact with both units ucder normal operation will be made.

B. Noise Related Complaints - No noise complaints concerning Byron Station were received by Commonwealth Edison in 1987, i

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ATTACHMENT A (Continued)

Results of the 1987 Foliar Survey of the Byron Generating Station and its Environs Prepared by Barry J. Jacobsen, Ph.D.  ;

Plant Pathologist for r - nwealth Edison Company .

Chicago, IL i

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r Introduction.

The 1987 foliar survey done on 9/12/87. Plant foliage within 1-1.5 miles of the cooling towers was inspected for potential injury from saline aerosols.

This and previous surveys detail the plant diseases and other foliar abnormalities present in the survey area. Special attention was given to salt injury type damage, since work by McCune et al. (1) indicates that acute foliar injury from saline aerosols might be anticipated under certain conditions (eg., high temperature, high humidity, still air, prolonged inversion conditions) on sensitive plant species growing downwind from natural draft cooling towers. The most salt sensitive plant species common in the environs of the Byron generating station include American elm, white pine, and alfalfa. This survey documents the condition of foliage 2 years after the plant became operational. .

Methods and Materials. -

Analysis of aerial infrared Cibachrome print photographs, ground truth examination of areas of unusual signature, and random ground surveys were all used in the survey. Infrared photographs, taken by Aerometric Engineering Inc., Sheboygan, WI on 8-17-87, were of high quality. The area photographed covered all or portions of sections 7, 8,17,18,19, and 20 of Marion township and sections 11, 12, 13, 14, 15, 23, and 24 of Rockvale Township.

Ground surveys were generally limited to this area except for examination of similar plant species 10-20 miles away from the survey crea.

Photographs 1-1 through 1-8 dre from the most northerly flight line and show an area from approximately 0.25 mile east of Black Walnut Rd. to approximately 1

McCune. D., D. Silbernam, R. Mandel, L. Weinstein, P. Freudenthal, and P.

Giardina. 1977. Studies on the effects of saline aerosols cooling towers origin on plants. J. Air Poll. Contr. Assoc. 27:319-324.

2 0.6 miles west of Razorville Rd. The northerly limit of this set of photo-graphs is roughly Acorn Rd. and the southerly limit the parking areas on the northside of the generating station.

Photographs 2-1 through 2-8 depicted the approximately the same limits east and west as Photographs 1-1 through 1-8 but had a riortherly limit of the railroad track at the north edge of the station and a southerly limit at the south edge of the generating station.

Photographs 3-1 through 3-7 depict the area with approximately the same east and west boundaries on Photograph sets 1-1 through 1-8 and 2-1 through 2-8.

The northern boundary of this flight line is the south edge of the station and the southern boundary is approximately 0.5 miles south of Deer Path Road.

Photographs 4-1 through 4-3 are high altitude photographs and depict the area within sections 7, 8, 9, 16, 17, 18, 19, 20, 21 and portions of 28, 29, and 30 of Marion township and sections 11, 12, 13, 14, 15, 22, 23, 24, and portions of 25, 26, 27 of Rockvale township.

Results.

No saline aerosol or salt related injuries were identified in the survey area. Abnonnal signatures on infrared phntographs and in ground truth surveys were found to be due to soil erosion, weeds growing in crop fields, herbicide injury, root damage due to construction associated compaction or grade changes, fertility deficiencies, plant diseases, insect damage, soil type differences, and transplant problems. Specific examples are given in analysis of the following photographs.

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Photograph 4-1.

Site 4-1-1. This area is woody ornamental planting. Generally, hawthorn, green ash, viburnum, dogwood, maple, and linden specimens were healthy. Abnormalities found included anthracnose of green ash and early senescence of dogwood associated with stress.

Although not shown on the photograph the large maple (site 4-1-la) showed a significant amount of wind damage at the time of the survey. Limbs up to 6" in diameter were broken primarily on the northwest face of the tree.

Site 4-1-2 is an eroded area where corn growth is poor due to nutrient deficiency. Due to lack of crop competition, grassy weeds were the prevalent growth in this area of the corn field.

Photograph 4-3.

The site marked 4-3-1 is an area of pipeline construction. While foliar signatures are normal in the photo, ground survey identified root damage that will show up as unilateral dieback in future years.

Sites 4-1-3 and 4-1-5. These sites are corn fields showing lodging damage. Lodging was found to be caused by damage from stalkrot diseases and corn borer damage. At site 4-1-3, potash deficiency was evident and this predisposed the corn pl:nts to stalkrot problems.

Site 4-1-4 denotes the unusual signatures on the borders of this corn field. Ground truth identified this as damage from corn crop herbicide taken up through the root system of woody plants such as slippery elm, hackberry and boxelde:.

Photograph 1-1.

Site 1-1-1. This signature was described previously as site 4-1-5,

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Site 1-1-2. This is a large dead oak. The cause of death could not be determined.

Photograph 1-3.

Site 1-3-1 shows oaks with some stagheading. Ground truth indicated that this dieback appeared to be associated with a changed watertable, erosion, and culvert construction.

Photograph 1-4.

Site 1-4-1. These large trees are dying. A specific cause was not identified in the ground survey but both the oak wilt and Dutch Elm diseases are common in this area. Surrounding trees have normal signatures.

Site 1-4-3. This planting of crabapple, maple, redpine, scotch pine, white spruce, honey locust, pin oak, and hawthorn were generally healthy. Some chlorosis was noted on some crabapple and pin oak specimens and appeared to be as sociated with planting depth and/or transplant shnck.

Photograph 1-5.

Sites 1-5-1 and 1-5-2 are dead or dying trees. Site 1-5-2 is the same as 1-4-1. Site 1-5-1 is on private property (motocross course) and tree decline is likely associated with soil compaction or damage caused by motorcycle operations.

Photograph 1-7.

Sites 1-7-1 denotes an oak with significant dieback. Dieback is associated with road construction in previous years.

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Photograph 2-2.

Sites 2-2-1 and 2-2-3 denote elms dying from Dutch Elm Disease.

Site 2-2-3 has been discussed previously as site 4-1-2.

Photograph 2-3.

Site 4-1-4. This area has been discussed previously as site 4-1-4 on Photograph 4-1.

Photograph 2-6.

Site 2-6-1. This was a large boxelder with a heavy seed set. This indicates stress. There were no' obvious signs of pathology evident. However, other boxelder in the area also showed marginal chlorosis and heavy seed set.

This was also true in areas 10-20 miles away from the survey areas.

Site 2-6-2. Ground survey did not reveal any problem at this site.

Photograph 3-1.

Site 3-1-1 were sites where decline most likely associated with decay. Site 3-2-1 were crabapples showing damage from the scab disease. Site 3-1-2 is an area of water damage.

Photograph 3-3.

Site 3-3-1 was an elm dying from Dutch Elm Disease.

Site 3-3-2. This is an area of differing soil types resulting in poorer corn growth.

Site 3-3-3 was a hackberry shewing chlorosis typical of triazine type herbicide injury. Adjacent hackberry trees appeared normal.

6 photograph 3-4.

Site 3-4-1 was an area of erosion damage.

Site 3-4-2 was normal and the abnormal signature appears to be due to sun angle false signature.

General Coments.

The following are host abnormalities noted during the ground survey.

Corn---comon rust, grey leafspot, northern corn leaf blight, stalkrot, anthracnose, corn borer damage, potash and nitrogen deficiency Soybeans---Brown stem rot, Septoria brown spot, bacterial blight, downey mildew Grape (wild)---Isariopsis leaf spot, blackrot, phenoxy herbicide injury Brambles---Orange rust, Septorai leafspot, anthracnose Apple---Apple scab, transplant damage, Sooty blotch, Flyspeck, blackrot Elm (American, Slippery, Siberian)---canker, herbicide injury (photosynthetic inhibitor type), blackspot Dutch Elm disease Maple---Stom damage, decay Hickory---Leafspot, tent caterpiller injury Oak---Stom damage decay, Actinopeltae leafspot, transplant damage Boxelder---Herbicide injury (both phenoxy and photosynthetic inhibitors type), heavy seed set and early senecence from suspected environmental stress.

This was observed in areas 10-20 miles remote from the plant.

Hackberry---Nipple gall mite damage, herbicide injury (photosynthetic inhibitortype)

Green Ash---Anthracnose, dieback associated with transplant stress '

Blackcherry---tent caterpillar damage

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Alfalfa---common leafspot, leafhopper burn Horsenettle---chlorosis of unknown causes Smartweed---Septoria leafspot Golden rod---aster yellows White pine---minor ozone injury Conclusion. .

No saline aerasol or salt related injury was identified in the area surveyed. Abnormalities noted were caused by plant diseases, transplant shock, construction, drainage problems, fertility, soil differences, erosion, herbicide injury, or weeds.

It should be noted that in the area of new pipeline construction west of the generating station dieback of oaks and other hardwoods can be expected where grades were changed or where soil piles sit for more than 30 days. This damage will be most pronounced in 2-3 years.

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ATTACHMENT A (Continued)

Results of the 1987 Confinatory Sound Level Survey of the Byron Generating Station and its Environs Prepared for Byron Station by Terrence J. Whalen System Operational Analytical Department Commonwealth Edison Company Chicago, Illinois t

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BYRON UNIT-1 cnd UNIT-2 SOUND LEVEL SURVEY DATA SHEET 4.2.2-1 NEASURED NOISE LEVELS DUE TO NORMAL CONTINUOUS OPERATION OCTAVE BAND CENTER FREQUENCIES IN HERTZ dBA E il 121 21Q 102 n n n R CQi LOCATION NUMBER ONE (ll) .

l Winter Day Winter Hight Summer Day 37 46 44 39 35 33 30 29 28 26

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• a e Summer Night 64 53 52 47 b2 42 37 40 41 60 (1,2)

LOCATION NUMBER M (92)

Winter Day Winter Night e

Summer Day 37 46 41 37 27 27 25 27 34 27 (1) e e .

Summer Night 42 36 34 29 26 28 26 33 32 41 (1) i ILLINOIS POLLUTICH CONTROL BOARD RULES, SECTION 901.102 (3)

Daytime (Rule a) 75 74 69 64 58 52 47 43 40 Nighttime (Rule b) 69 67 62 54 47 41 36 32 32 COMMENTS:

(1)

• High levels in these octave bands due to the contribution of insect noise.

(2) & Tonal component in the 250 octave band does not exceed the State of ,

Illinois discrete tone rule.

(3) 3 Ammended January 22, 1987. The new cmendment which caly af fects the measurement procedure, has no significance, in this case, since the station noise is continuous and steady-state.

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BYRW UNIT-1 c"d UNIT-2 SOUND LEVEL SURVEY DATA SHEET 4.2.2-2 MEASURED NOISE LEVELS DUE TO NORMAL CONTINUOUS OPERATION l OCTAVE BAND CENTER FREQUENCIES IN HERTZ dBA E 11 ni liq 102 h 21 h n CQi,.

LOCATION NUMBER THREE (03)

Winter Day Winter Night Summer Day 38 57 53 46 33 33 31 29 29 29 Summer Night 59 60 59 51 37 33 32 30 34 54 (1)

LOCATIN NUMBER FOUR (94)

Winter Day Winter Night Summer Day 44 52 54 52 45 40 38 36 31 27 a e Summer Night 55 49 52 47 37 33 29 33 37 48 (1) 0 ILLINOIS POLLUTION CNTROL BOARD RULES, SECTIN 901.102 (2)

Daytime (Rule a) 75 74 69 64 50 52 47 43 40 Nighttime (Rule b) 69 67 62 54 47 41 36 32 32 COMMENTS:

(1)

• High levels in these octave bands due to the contribution of insect noise.

(2) i Ammended January 22, 1987. The new meendment which only affects the measurement procedure, has no significance, in this case, since the station noise is continuous and steady-state.

(2010M/0220M/041388/2)

. BYRON UNIT-1 cid UNIT-2 SOUND LEVEL SURVEY DATA SHEET 4.2.2-3 MEASURED NOISE LEVELS DUE TO NORMAL CONTINUOUS OPERATION OCTAVE BAND CENTER FREQUENCIES IN HERTZ dBA 11 ft1 121 210 102 h 21 h n CA BYRON CITY LIMITS Winter Day Winter Hight Summer Day 35 45 49 44 34 29 27 25 25 26 e a Summer Night 46 35 35 27 26 18 17 32 42 42 (1)

OREGCH CITY LIMITS Winter Day Winter Night Summer Day 41 47 50 52 41 35 32 28 30 27 e a Summer Night 43 44 46 48 35 29 25 30 39 38 (1) 4 -

ILLINOIS POLLUTION CONTROL BOARD RULES, SECTION 901.102 (2)

Daytime (Rule a) 75 74 69 64 58 52 47 43 40 Nighttime (Rule b) 69 67 62 54 47 41 36 32 32 CCM4ENTS :

(1)

• High levels in these octave bands due to the contribution of insect noise.

(2) i Ammended January 22, 1987. The new amendment which only affects the measurement procedure, has no significance, in this case, since the station noise is continuous and steady-state.

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BYRW UNIT-1 Ond UNIT-2 SOUND LEVEL SURVEY 4

DATA SHEET 4.2.2-4 CALCULATED SATATISTICAL NOISE LEVELS DUE TO NORMAL CONTINUOUS OPERATION NOISE LEVELS IN DECIBELS Ld La Idin L:1 le.22 LOCATION NUMBER ONE (ll)

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Summer Day 39 68 46 35 8 i Summer Night 62 68 67 51 LOCATI N NUMBER D O (42)

Winter Day Winter Night Summer Day 45 49 52 36 Summer Night 42 49 45 40 LOCATION NUMBER THREE (83) '

Winter Day Winter Night i

Summer Day 42 65 51 37 4 4 Summe,r Night 59 65 62 50  ;

Ldn TEDERAL GUIDLINE Evnironmental Protection Agency (EPA) <55 FEDERAL CRITERIA Housing & Urban Development (RUD) <65 COMMENTS: (0) High level due to contribution of insect noise.

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BYRN UNIT-1 Ed UNIT-2 SOUND LEVEL SURVEY

, DATA SHEET 4.2.2-5 CALCULATED SATATISTICAL NOISE LEVELS DUE TO NORMAL CONTINUOUS OPERATIN NOISE LEVELS IN DECIBELS Ld La Ldn Icl ical LOCATION NUMBER ONE (84)

Winter Day Winter Night e

Summer Day 48 66 54 44 e e Summer Night 60 66 62 58 BYRON CITY LIMITS Winter Day Winter Night Summer Day 39 53 44 34 Summer Night 47 53 51 45 OREGN CITY LIMITS Winter Day Winter Night e

Summer Day 43 56 48 40 m e -

Summer Night 50 56 60 43 9

Ldn FEDERAL GUIDLINE Evnironmental Protection Agency (EPA) <55 FEDERAL CRITERIA Housing & Urban Development (HUD) (65 COMMENTS: (*) Nigh level due to contribution of insect noise. I i

(2010M/0220M/041388/5)

4 Byron Station Environmental Protection Plant 1987 Annual Environmental Operating Report ATTACHNDIT B 1 l

l List of Environmental Protection Plan non-compliances and corrective actions.

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'4-Byron Station l Environmental Protection Plan l 1987 Annual Environmental Operating Report i ATTACHMENT C Section 3.1 ,Plent Design and Operation t

List of~ changes in station design, operation, tests and ,

experiments which involved a potentially significant unreviewed environmental question.

1. In 1987, the City of Byron sought to lease or buy approximately one '

acre of land on the station site for the purpose of building a water tower. The land parcel is located on the make-up and blowdown j

corridor, west of Rasorville Road, on the south side of Acorn Road.

The action was reviewed for environmental-affects and it was determined that it did not represent an unreviewed environmental question with regard to the design or operation of Byron Station. It was decided that the parcel would be sold to the City of Byron and ,

the NRC was informed of the action. A Copy of the memoranduin confirming the review is attached.

The make-up and blowdown lines between the station and the Rock River

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were replaced during 1987. The plans for the replacement were s reviewed and it was determined that all the construction activity was  !

to be confined to on-site areas previously disturbed ducirq site preparation and plant construction, and was not subject to an '

environmental evaluation requirement. A copy of the memorandum confirming the review is attached.

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March 25, 1987 To: M. A. Onishi

Subject:

Water Tower on Byron Station Froperty Environmental Affairs (EAD) has reviewed the request for location of a water tower on Byron Station property, reference J. J. Bruen's February 24 and March 17 letters. EhD defers to Transmission and Distribution Engineering, concerning clearance from present and future transmission facilities.

In our opinion, building a water tower at this location would not result in any adverse environmental impacts and would not represent an unreviewed environmental question with regard to the desiga or operation of Byron station. However, the selected location is part of the restricted area of the station as specified in section 2.1.1.3 of the Byron Final safety Analysis Report (PSAR). In Section 2.1.1.2 of the FRAR the following statement regarding site land use is made: "There will be no industrial, institutional, commercial, recreational, or residential structures on the site other than those used by Commonwealth Edison company in the normal conduct of 1ta ut111ty business. The development of the site for uses other than power generation and agriculture is not planned". This couaiteent would have to be revised in consultation with the Woclear Regulatory Commission before entering into any agreement for a use such as the proposed water temer.

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n. orivttre J. J. Bruen File: 04-oet-

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. 1 Commonwealth Edison One First Nabonal Plaza CNeago. Infos Address Repy to: Post omce Box 757 Chcego,innois 60600 0767 June 17, 1987 U.S. Nuclear Regulatory Comunission Attn: Document Control Desk i Washington, DC 20555 l

Subject:

Byron Station Units 1 and 2 Site Boundary Revision WRC Dockst Nos. 50-454 and 50-455 Gentlemen:

This is to provide an advance copy of an FSAR change concerning a revision to the Byron site boundary. Ceaumonwealth Edison plans to sell a small portion of our Byron site property to the city of Byron for a water tower. The city of Byron proposes to install a 100-foot water tower on property which has been part of the pipeline corridor from the plant to the Rock River. A 200' by 233' parcel will be sold to them for this purpose.

The location of this parcel is identified by an arrow on the attached revision of PSAR Figure T.1-6.

Building a water tcver at this location does not involve any sdverse environmental impacts, unreviewed environmental question, or unreviewed safety question. The change to Figure 2.1-6 will be included in a future FSAR amendment.

Please direct any questions regarding this matter to this office.

Very truly yours.

K. A. Ainger Nuclear Licensing Administrator Attachment

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To: W. P. Dijstelbergen .1 ,

subject: Environmental Review of Proposed 5 5T.

Replacement of Make-Up and 1 Blowdown Lines at Byron station section 3.1 of the Byron station environmental Protection Plan requires that any additional construction activity which may significantly affect the environment be evaluated for any environmental affects prior to engaging in construction activities.

The Environmental Affairs Department has reviewed the plans for replacing the make-up and blowdown lines at Byron Station and finds that this construction activity can be excluded from the enviroemental evaluation because all the measurable environmental effects are confined to on-site areas previously disturbed during site preparation and plant construction.

The basis for this finding is contained in the following considerations. The new pipelines will be placed within the previously cleared corridor between the station structures and the river screenhouse and blowdown structures. Traffic will be maintained on the two local roads which cross the project route. The corridor and fenced areas have been previously surveyed for archeological sites and none will be affected by construction. The land contours will be restored, topecil replaced and seeded to restore the area disturbed by construction. No additional off-site stors water runoff is expected. Local residents and the Illinois and Federal Environmental Protection Agencies have expressed concerns about contaminated soil and groundwater in the vicinity of the construction area.

They have been informed of the construction project and will be allowed to take soit samples as construction progresses.

C. L. McDonough 1403e BB5: :CtJt:dd '

cc: R. E. Quario

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P. R. Donavin T. E. Hemminger l

s. K. Winship H. F. Bernhard File: 06-GEN-

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Byron Station Environmental Protection Plant 1987 Annual Environmental Operating Report ATTACHMENT D List of non-routine reports submitted in accordance with Subsection 5.4.2.

None 4

(2001M/0217M/040888)

r-- ,

Commonwealth Edison I Byron Nucl:ar Station i

• i 4450 North Gerrnan Church Road Byron, Illinois 61010 l

l April 11, 1988 i LTR: BYRON 88-0350 File: 2.7.300 Mr. A. Bert Davis Ragional Administrator Region III U. S. Nuclear Rogulatory Com;aission 799 Roosevelt Road Glen Ellyn, II. 60137

SUBJECT:

Annual Environmental Operation Report for Facility Licenses NPF-37 and 66 ,

Dear Mr. Davis:

Attached you will find the Annual Environmental Operating Report as required by the Technical Specifications, Appendix B, Section 5.4 for Facility License NPF-37 & 66. The period of the report is from January 1, 1987 to December 31, 1987.

The report was reviewed against the objectives of the Environmental Protection Plan as stated in the Technical Specifications, Appendix B, Section 1.0 Byron Station and it has been determined that these objectives are being met.

The report is contained in Attachments A, B, C, and D as indexed -

Attachment A - Summaries and analysis of the results of environmental protection activities required by Appendix B, Section 4.2, including a set of color transparencies as required by Section 4.2.1.

Attachment'B - A list of non compliances to the Environm1ntal Protection Plan and the corrective actions.

Attachment C - A list of all changes in Station design or operation, tests or experiments as required by Appendix B. section 3.1.

Attachment D - A list of all non-routine reports as required by Appendix B, section 5.4.2.

p s /m A L

BYRON 88-0350 Page 2 In accordance with Regulatory Guide 10.1, one copy of this report is provided for your use and 18 copies are being submitted directly to the Document Control Desk, U. S. Nuclear Regulatory Commission, Washington, D. C. 20555.

l Sincerely, cdf ~

R. Pleniewies i Station Manager I Byron Nuclear Power Station l

RP/da (2001M/0217M) I l

Attachment l cc NRC Resident Inspector

! Document Control Desk (18 copies)

Site Nuclear Licensing Administrator Environmental Affaire 1 - _ ----

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