ML093020116

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Submittal of State Pollutant Discharge Elimination System Discharge Permit NY-000-1015
ML093020116
Person / Time
Site: Nine Mile Point  Constellation icon.png
Issue date: 10/22/2009
From: Syrell T
Constellation Energy Nuclear Group
To:
Document Control Desk, Office of Nuclear Reactor Regulation
References
Download: ML093020116 (39)


Text

Constellation Energy-Nine Mile Point Nuclear Station P.O. Box 63 Lycoming, NY 13093 October 22, 2009 U.S. Nuclear Regulatory Commission Washington, D.C. 20555-0001 ATTENTION:

SUBJECT:

Document Control Desk Nine Mile Point Nuclear Station, LLC Unit Nos. I & 2; Docket Nos. 50-220 & 50-410 Report on the Status of the New York State Pollutant Discharge Elimination System (SPDES) Permit Gentlemen:

Enclosed is a copy of the State Pollutant Discharge Elimination System (SPDES) Discharge Permit #NY-000-1015 for the Nine Mile Point Nuclear Station. The permit was approved on September 29, 2009, and will become effective on December 1, 2009. Notification of issuance of this permit is provided in accordance with the following:

Nine Mile Point Unit I letter dated April 15, 1983, which states that any changes or violations of the SPDES Permit will be provided to the NRC.

Nine Mile Point Unit 2 Environmental Protection Plan (Appendix B to Renewed Facility Operating License No. NPF-69), Section 3.2, which requires that changes or renewals of the SPDES Permit be reported to the NRC within 30 days following the date the change or renewal is approved.

In the event there are any questions concerning the permit renewal, please contact me at (315) 349-5219.

Very truly yours, Terry F. Syrell Director, Licensing TFS/RJC

Enclosure:

State Pollutant Discharge Elimination System (SPDES) Discharge Permit

Document Control Desk October 22, 2009 Page 2 cc:

R. V. Guzman, NRC Project Manager S. J. Collins, NRC Regional Administrator, Region I Senior NRC Resident Inspector

ENCLOSURE STATE POLLUTANT DISCHARGE ELIMINATION SYSTEM (SPDES)

DISCHARGE PERMIT Nine Mile Point Nuclear Station, LLC October 22, 2009

New York State Department of Environmental Conservation Division of Environm ental Permits, 4th Floor 625 Broadway, Alban, y, New York 12233-1750,,

Phone: (518) 402-9167 e FAX:.(518).402-9,68,'

Website: iwwwdec Saite~ny~us Alexanddr P. Grarnis Com'missioner September 29,12009 Kenit St6ffl.e.

Nine: Milel'oint Nuclear Staiion, LLC P.O. Boxx'63; Lycoming, New York, 13093 RE:: SPDES Permit,(DEC#: 7-3556-60.0Oi )0

- Nine Mile PointtNuclearStatioin

Dear Mr. Stof fle:

r n

In coqnfo*rice

'ith* thc e requirh"ments of the Staie'UhiformrPr6edures ACt, Artidle 70 of the.Environmental Conseiati on. Law2and its is.impl ementing: reduii atio ns 6 NY*cR Part 621

,(UnifomiProcedures), enclosed'is the State Pollutant Dischargc Elimination SYstem(SPDES) permit for the above, referenced facility.

P'lease-read all dco n

ditions of thepermit. Feel free to-coiitacdt our bffice if yoU have any questionsor'concems regardingthe terms of the. penrimt or your,obligations under the

.permt..

4Sint..rel

/o(,

  • Prisojec7Manager
i. ;

cc:

Bureau, of Water Peniits. Permit Coordinator Regional Xater'E*igineer Region 7 (via e0nail)

O'0eg County Department of Health USEPARegion 2*- Michelle Jo silo J..FeItm.n - Region 7 RPA (via email)

M.ý. Wang, Dow-- CO0(via.email)

M, Calaban (Via email)

File

NEW YO A

  • State Po Industrial Code:

4911 Discharge Class (CL):

03 Toxic Class (TX):

T Major Drainage Basin: 03 Sub Drainage Basin:

03 Water Index Number:

Lake Ontario Compact Area:

IEC RK STATE DEPARTMENT OF ENVIRONMENTAL CONSERVATION

'Ilutant Discharge Elimination System (SPDES)

DISCHARGE PERMIT First3.99 SPDES Number:

DEC Number:

Effective Date (EDP):

Expiration Date (ExDP):

Modification Dates:(EDPM)

NY-000 1015 7-3556-00013/00001 12/01/09 11/30/14 This SPDES permit is issued in compliance with Title 8 of Article 17 of the Environmental Conservation Law of New York State and in compliance with the Clean Water Act, as amended, (33 U.S.C. §1251 et.seq.)(hereinafter referred to as "the Act").

PERMITTEE NAME AND ADDRESS Name:

Nine Mile Point Nuclear Station, LLC Street:

348 Lake Road City:

Oswego is authorized to discharge from the facility described below:

Attention: Principal Engineer, Environmental State: NY Zip Code: 13093 FACILITY NAME AND ADDRESS Name:

Nine Mile Point Nuclear Station Location (C,T,V):

Scriba (T)

Facility Address:

348 Lake Road County:

Oswego City:

Lycomig State: NY Zip Code: 13093 NYTM -E:

From Outfall No.:

010 at Latitude: 43

  • NYTM - N:

31 '

17 "

& Longitude:

76 0 24 Class: A 39 "

into receiving waters known as:

'Lake Ontario and; (list other Outfalls, Receiving Waters & Water Classifications)

See Next Page in accordance with: effluent limitations; monitoring and reporting requirements; other provisions and conditions set forth in this permit; and 6 NYCRR Part 750-1.2(a) and 750-2.

DISCHARGE MONITORING REPORT (DMR) MAILING ADDRESS Mailing Name:

Nine Mile Point Nuclear Station, LLC Street:

348 Lake Road City:

Lycoming Responsible Official or Agent:

Terry Syrell, Licensing Director State: NY Zip Code: 13093 Phone: (315) 349-1364 This permit and the authorization to discharge shall expire on midnight of the expiration date shown above and the permittee shall not discharge after the expiration date unless this permit has been renewed, or extended pursuant to law. To be authorized to discharge beyond the expiration date, the permittee shall apply for permit renewal not less than 180 days prior to the expiration date shown above.

DISTRIBUTION:

CO BWP - Permit Coordinator RWE, Region 7 RPA EPA Region II - Michelle Josilo Oswego County Department of Health Permit Administrator: William R. Adriance Address:

625 Broadway, 4 th Floor Albany, NY 12233 Signstu

.ý Date:

/97? '0?.

SPDES PERMIT NUMBER NY 000 1015 Page 2 of 35 List of all Outfalls, Receiving Waters and Water Classifications Outfalls

  • Latitude Longitude Receiving Water and Classification Permit Outfall Nine Page #

designation (Note: Direct outfalls are lined up on the left and Mile for internal outfalls are lineup on the right)

Unit #

Effluent Direct Internal in NY2C Limits 010 43-31-17 76-24-39 Lake Ontario (A) 1 4,15 011 43-31-17 76-24-39 Lake Ontario (A) via Outfall 010 5

10A 010A 43-31-17 76-24-39 Lake Ontario (A) via Outfall 010 or 020 5

020 43-31-17 76-24-39 Lake Ontario (A) 6 10A 010A 43-31-17 76-24-39 Lake Ontario (A).via Outfalls 020 or 010 5

07(B) 007(B) 43-31-17 76-24-39 Lake Ontario (A) via Outfall 020 7

024 43-31-17 76-24-39 Lake Ontario (A) via Outfall 020 8

021 43-31-17 76-24-39 Lake Ontario (A) 8 023 43-31-17 76-24-39 Ditch (U ISW), then to Lake Ontario (D/A) 9 025 43-31-17 76-24-39 Ditch (U ISW), then to Lake Ontario (D/A) 2 9

030 43-31-17 76-24-39 Ditch (U1SW), then to Lake Ontario (D/A) 1 & 2 10 026 43-13-17 76-24-39 Lake Ontario (A) via Outfalls 040 or 030 12 040 43-31-17 76-24-39 Lake Ontario (A) 2 11, 15 01A 001A 43-31-17 76-24-39 Lake Ontario (A) via Outfall 040 12 026 43-31-17 76-24-39 Lake Ontario (A) viaOutfalls 040 or 030 12 40A 040A 43-31-17 76-24-39 Lake Ontario (A) via Outfall 040 13 40B 040B 43-31-17 76-24-39 Lake Ontario (A) via Outfalls 040 or 001 5

041 43-31-17 76-24-39 Lake Ontario (A) via Outfall 040 13 001 43-31-25 76-24-20 Lake Ontario (A) 14, 15 07(A, C-G) 007(A, C-G) 43-31-17 76-24-39 Lake Ontario (A) via Outfall 001 7

01A 001A 43-31-17 76-24-39 Lake Ontario (A) via Outfall 001 12 40B 040B 43-31-17 76-24-39 Lake Ontario (A) via Outfalls 001or 040 5

002 43-31-25 76-24-16 Lake Ontario (A) 14 008 43-31-17 76-24-39 Lake Ontario (A) 6 Notes:

  • SPDES outfall numbers are assigned for three spaces in the EPA Permit Compliance System (PCS). Outfallswith four numbers in the NY2C application have been changed to three number in order to be compatible with the EPA PCS program.
    • This column identifies outfall with four spaces as listed in the NY2C application.

SPDES PERMIT NUMBER NY 000 1015 Page3 of 35 PERMIT LIMITS, LEVELS AND MONITORING DEFINITIONS OUTFALL WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING This cell describes the type of wastewater authorized This cell lists classified waters The date this page The date this page is for discharge. Examples include process or sanitary of the state to which the listed starts in effect. (e.g.

no longer in effect.

wastewater, storm water, non-contact cooling water, outfall discharges.

EDP or EDPM)

(e.g. ExDP)

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQ. SAMPLE TYPE e.g. pH, TRC, The minimum level that must be The maximum level that may not SU, °F, Temperature, D.O.

maintained at all instants in time.

be exceeded at any instant in time.

mg/I, etc.

PARA-EFFLUENT LIMIT PRACTICAL QUANTITATION ACTION UNITS SAMPLE SAMPLE METER LIMIT (PQL)

LEVEL FREQUENCY TYPE Limit types are defined below in For the purposes of compliance Type I or This can Examples Examples Note I.

The effluent limit is assessment, the analytical method Type Ii include units include Daily, include developed based on the more specified in the permit shall be used Action Levels of flow, pH, 3/week, grab, 24 stringent of technology-based to monitor the amount of the pollutant are

mass, weekly, hour standards, required under the Clean in the outfall to this level, provided monitoring Temperature, 2/month, coinposite Water Act, or New York State water that the laboratory analyst has requirements, concentration. monthly, and 3 grab quality standards. The limit has been complied with the specified quality as defined Examples quarterly, 2/yr samples derived based on existing assurance/quality control procedures below in Note include pg/I, and yearly.

collected assumptions and rules.

These in the relevant method. Monitoring 2, that trigger lbs/d, etc.

over a 6 assumptions include receiving water, results that are lower than this level ' additional hour hardness, pH and temperature; rates must be reported, but shall not be monitoring period.

of this and other discharges to the used to determine compliance with and permit receiving stream; etc. If assumptions the calculated limnit. This PQL can be review when or rules change the limit may, after neither lowered nor raised without a exceeded.

due process and modification of this modification of this permit.

_ penrit, change.

I I

I I

NoteI: DAILY DISCHARGE: The discharge ofa pollutant measured during a calendar day or any 24-hour period that reasonably represents te caendar day for the purposes of sampling. For pollutants expressed in units of mass, the 'daily discharge' is calculated as the total mass of the pollutant discharged over the day. For pollutants with limitations expressed in other units of measurement, the 'daily discharge' is calculated as the average measurement of the pollutant over the day.

DAILY MAX: The highest allowable daily discharge. DAILY MIN: The lowest allowable daily discharge.

MONTHLY AVG (daily avg): The highest allowable average of daily discharges over a calendar month, calculated as the sum of each of the daily discharges measured during a calendar month divided by the number of daily discharges measured during that month.

RANGE: The minimum and maximum instantaneous measurements for the reporting period must remain between the two values shown.

7 DAY ARITHMETIC MEAN (7 day average): The highest allowable average of daily discharges over a calendar week.

12 MRA (twelvemonth rolling avg): The average of the most recent twelve month's. monthly averages.

30 DAY GEOMETRIC MEAN (30 d geo mean): The highest allowable geometric mean of daily discharges over a calendar month, calculated as the antilog of : the sum of the log of each of the daily discharges measured during a calendar month divided by the number of daily discharges measured during that month.

7 DAY GEOMETRIC MEAN (7 d geo mean): The highest allowable geometric mean of daily discharges over a calendar week.

Note2: ACTION LEVELS: Routine Action Level monitoring results, if not provided for on the Discharge Monitoring Report (DMR) form, appended to the DMR for theperiod during which the sampling was conducted. If the additional monitoring requirement is triggered as noted below,the permittee shall undertake a short-term, high-intensity monitoringprogram for the parameter(s). Samples identical to those required for routine monitoring purposes shall be taken on each of at least three consecutive operating and discharging days and analyzed.

Results shall be expressed in terms ofbothconcentration and mass, and shall be submitted no later than the end of the third month following the month when the additional monitoring requirement was triggered. Results may be appended to the DMR or transmitted under separate cover to the same address. If levels higher than the Action evels are confirmed, the permit may be reopened by the Department for consideration of revised Action Levels or effluent limits. The permittee is notauthorized to discharge any of the listed parameters at levels which may cause or contribute to a violation of water quality standards. TYPE I : The additional monitoring requirement is triggered upon receipt by the permittee of any monitoring results in excess of the stated Action Level. TYPE II: The additional monitoring requirement is triggered upon receipt by the permittee of any monitoring results that show the stated action level exceeded for four of six consecutive samples, or for two of six consecutive samples by 20 % or more, or for any one sample by 50 % or more.

SPDES PERMIT NUMBER NY 000 1015 Page 4 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL WASTEWATER TYPE RECEIVING EFFECTIVE EXPIRING No.

WATER 010 Unit#I - Non-contact cooling water (417.6 MGD), IMP 01OA(forebay cleaning, Lake Ontario EDP 11/30/14 100,000 gpd), Outfall 01 1 (Unit #1 wastewater), seal water system (25 gpm), and stormnVater runoff [FN I, 28]

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE FOOTNOTES (FN)

TYPE pH 6.0 9.0 SU Monthly Grab EFFLUENT LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE.

SAMPLE FN UNITS FREQUENCY TYPE Daily Avg.

Daily Max.

TYPEI TYPE II UNI1 S FREQENCY TYP Flow NA 417.6 MGD Continuous Calculated 2, 3,4 Discharge Temperature NA 115 o F Continuous Recorder 5

Temperature Difference (A T)

NA 35

° F Continuous Recorder 5, 6 (Discharge temp. - Intake temp.)

Net Rate of Addition of Heat NA 4,405 MBTU/hr Hourly Calculated 6

Total Residual Oxidant NA 0.1 mg/I Batch Grab 16, 19 Solids, Total Suspended Monitor Monitor mg/I Daily during Grab forebay cleaning Copper, Total NA 0.053 mg/I Monthly Grab 7

Zinc, Total 0.05 mg/I Quarterly Grab WET - Acute Invertebrate 0.69 TUa Quarterly see footnote 24 WET - Acute Vertebrate 0.69 TUa Quarterly see footnote 24 WET-Chronic Invertebrate 4.6 TUc Quarterly see footnote 24 WET - Chronic Vertebrate 4.6 TUc Quarterly see footnote 24 Footnotes: See Pages 16 - 18 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 5 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING Oil Unit I - Dernineralized water for steam generation. Batch discharge: 0 Lake Ontario via EDP 11/30/1 I batch per year and < I day per batch Outfall 010 PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE FOOTNOTES (FN)

TYPE 6.0 9.0 SU Once per batch Grab 8

ENFORCEABLELIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPE I TYPE II Flow Monitor Monitor MGD Batch Calculated Oil & Grease NA 15 mg/l Quarterly Grab 9

Oil & Grease NA 15 mg/I Batch before Grab 9

discharge Suspcndcd, Total Suspended 30 50 mg/I Quarterly Grab 9

Suspended, Total Suspended 30 50 mg/I Batch before Grab 9

discharge OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING

[ OA Unit #1 Forebay cleaning Lake Ontario via Outfall 020 (primary) or Outfall EDP 11/30/14 010 (alternate) 40B Unit #2 Forebay cleaning Lake Ontario via Outfall 040 (primary) or Outfall EDP 11/30/14

- 1 001 (altemate)

PARAMETER MINIMUM I MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE FOOTNOTES (FN)

I I I

I ~TYPE ISF) pH 6.0 9.0-SU Daily During Discharge Grab ENFORCEABLELIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE

.Monthly,.vg:.,

'DailyMax.- TYPEI TYPEII Flow Monitor Monitor MGD Daily During Calculated I

Discharge Oil & Grease NA i5 mg/I Daily During Grab Discharge Solids, Total Suspended 50 100 mg/I Daily During Grab

_1_

1_

_Discharge Footnote: See.Page 16 of this permit.

SPDES PERMIT NUMBER NY.000 1015 Page 6 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL WASTEWATER TYPE RECEIVING EFFECTIVE EXPIRING NUMBER WATER 020 Outfall 07B (floor & equipment drains, 1,000 gpd - routine), Outfall IOA Lake Ontario EDP 11/30/14 NMP-I forcbay cleaning (100,000 gpd; 14 batch /year; I day/batch), Outfall 024 NMP-I (Diesel offloading pad condensate water NMP-I, stormwater and perimeter water [FN I]

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE TYPE FOOTNOTES (FN) pH 6.0 9.0 SU Monthly Grab EFFLUENT LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPE I TYPE 11 Flow Monitor Monitor GPD Monthly Calculated 9

Oil & Grease NA 15 mg/I Quarterly Grab or calculated from sub-streams Solids, Total Suspended NA 50 mg/I Quarterly Grab or calculated from sub-streams Copper, Total 0.03 mg/I Quarterly Grab or calculated from sub-streams Zinc, Total 0.15 mg/I Quarterly Grab or calculated from sub-streams OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 008 Screen well fish diversion system Lake Ontario EDP 11/30/14 (See Footnote 11)

No monitoring required. The permittee should addressmeans to minimize pollutants discharging to Lake Ontario in the Best Management Plan (BMP).

Footnote:

See Page 16 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 7 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING NUMBER 07A manhole #110 in the Unit 2 Chiller building, Lake Ontario via Outfall 001 EDP 11/30114 1000 gpd 07B Floor and unit I administration building sump I; 1000 gpd Lake Ontario via Outfall 020 EDP 11/30/14 Equipment (See Footnote 12)

Drains from 07C unit 2 service water pump 2DFM - sump 2B; Lake Ontario via Outfall 001 EDP 11/30/14 1600 gpd 07D unit 2 service water pump 2DFM - sump 2A; Lake Ontario via Ouffall 001 EDP.

11/30/14 1600 gpd 07E unit 2 control building 2DFM - sump 4; 460 gpd Lake Ontario via Outfall 001 EDP 11/30/14 07F manhole # 103 screenhouse west, no regular Lake Ontario via Outfall 001 EDP 11/30/14 flow 07G manhole # 207 screenhouse north; no regular Lake Ontario via Outfall 001 EDP 11/30/14

.flow PARAMETER MINIMUM MAXIMUM UNIT SAMPLE SAMPLE FOOTNOTES S

FREQUENCY TYPE I (FN) pH 6.0 9.0 SU Monthly Grab EFFLUENT LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPE I TYPE II Flow NA Monitor GPD Monthly Estimated Oil & Grease NA 15 mg/I Monthly Grab Solids, Total'Suspended 30 50 mg/I Monthly Grab Aluminum, Total NA 4.0 mg/I Monthly Grab Iron, Total NA 4.0 mg/I Monthly Grab Copper, Total 0.1 mg/I Quarterly Grab Nickel, Total 0.1 mg/I Quarterly Grab Zinc, Total 0.8 mg/l Quarterly Grab Footnote: See Page 16 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 8 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL NUMBER WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 024 Stormwater from NMP - I diesel off-loading pad. Batch Lake Ontario via Outfall EDP 11/30/14 discharge with four batches per year 020 PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE TYPE FOOTNOTES (FN)I PH 6.0 9.0 SU Each dischar" e Grab EFFLUENT LIMIT PQL MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

DailyMax.

Daily Max.

TYPE I TYPE I1 Flow NA Monitor GPD Each discharge Estimate Oil & Grease NA 15 mg/I Each discharge Grab Solids, Total Suspended NA 50 mg/-

Each discharge Grab OUTFALL NUMBER WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 021 Filter backwash and demineralizer make-up water; Lake Ontario EDP 11/30/14 Batch discharge - max. one batch per year for one day.

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE TYPE FOOTNOTES (FN) pH 6.0 9.0 SU Batch Each Dischar e Grab EFFLUENT LIMIT PQL MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

Daily Max.

TYPE I TYPE 11 Flow Monitor Monitor GPD Batch Calculated Oil & Grease NA 15 mg/I Batch Each Grab I_

discharge Solids, Total Suspended 30 50 mg/1 Batch-Each Grab 1

1 _

1_

_D ischargUe II

-if

SPDES PERMIT NUMBER NY 000 1015 Page 9 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 023 Unit I - Oil spill retention basin (Basin capacity 0.214 MG); Batch To Ditch (UI SW),

EDP 11/30/14 discharge 6 - 12 times per year; Duration per batch < I day; Each batch then to Lake Ontario discharges 66,000 gpd - 214,000 gpd) [FN I ]

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE FOOTNOTES (FN)

I I

I I

I TYPE II PH 6.0 9.0 SU Each Discharge Grab 13 ENFORCEABLE LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPE I TYPE It Flow NA Monitor GPD Each Discharge Estimate Oil & grease NA 15 mg/I Each Discharge Grab Zinc, Total 0.05 "

mg/I Each Discharge Grab OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 025 Unit #2 Cooliný tower emergency overflow from cooling tower To Ditch (UI SW), then EDP 11/30/14 basin; Batch Discharge; < one discharge per year and < one day to Lake Ontario Xer batch.

ay PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE FOOTNOTES (FN)

TYPE pH 6.0 9.0 SU Each Discharge Grab ENFORCEABLE LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPE I TYPE II Flow NA Monitor GPD Each Discharge Estimate Copper, Total NA 1.0 mg/I Each Discharge Grab 25 Zinc, Total NA 0.163 mg/I Each Discharge Grab 25 Discharge Temperature NA Monitor

  • F ' °C)

Each Discharge Grab 25 Intake - Discharge Temperature NA Monitor F ( 'C)

Each Discharge Grab 25 Difference Free Available Chlorine NA 0.19 mg/I Each Discharge Grab 16,25 Total Residual Oxidant NA 0.19 mg/I Each Discharge Grab 16,25 Footnotes: See Pages 16 - 18 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 10 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL No.

LIMITATIONS APPLY:

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 030 X] All Year Sanitary wastewater and Lake Ontario EDP 11/30/14 Seasonal from to Outfall 026 as alternate route

[FN I1]

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE FOOTNOTES (FN)

TYPE pH 6.0 9.0 SU 2 / month Grab Dissolved Oxygen 4.0 NA mgl 2/ month Grab EFFLUENT LIMIT MONITORING REQUIREMENTS PARAMETER FN Location Sample Sample Type Limit Units

Limit, Units Frequency Type Inf7.

Eft.

Flow Monthly average 120,000 GPD 2/Month Metered X

14 Flow Daily Max.

Monitor GPD 2/Month X

14 BODN Monthly average 25 mg/I NA Ibs/d 2/Month Grab X

BODs Daily Maxr 45 ng/o NA Ibs/d 2!Month Grab X

Solids, Suspended Monthly average 25 00 g/

NA

/bs/d 2/Month Grab X

Solids, Suspended Daily Max, 45 mg/l NA lbs/d 2/Month Grab X

Solids, Settleable Daily Max.

0.1I ml/I 2/Month Grab X

Nitrogen, Ammonia (as N)

Daily Max.

Monitor mng/l NA I bs/d 2/Month Grab X

Nitrogen, Ammonia (as N)

Monthly Average Monitor mg/I NA lbs/d 2/Month Grab X

Effluent Disinfection required: [X ] Ali Year []Seasonal from to Coliform, Fecal 30 day 200 No./

2/Month Grab X

15 geometric mean 100 ml Chlorine, Total Residual Daily Max.

0. I mg/I 2/Month Grab X

I5 Footnotes: See Page 17 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 11 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL WASTEWATER TYPE RECEIVING EFFECTIVE EXPIRING NUMBER WATER 040 Unit 2 - Noncontact cooling water (72 mgd); Outfall 40B (Forebay cleaning; Lake Ontario EDP 11/30/14 100,000 gpd); Outfall 041 (NMP-2 wastcwater from demincralized water, reverse osmosis, electrodeionization filtration and treated radioaciive wastewater; 50,000 gpd); Outfall 01A (Decay heat cooling tower; 120 gpm); Outfall 026 (Unit 2 -

process wastewater from generation of demineralized water, 41,000 gpd) and Outfall 040A( CWS sumps; 21,000 gpd) [FN I]

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE TYPE FOOTNOTES (FN) pH 6.0 9.0 SU 2/Week Grab 26 EFFLUENT LIMIT MONITORING PARAMETER PQL ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPE I TYPE II Flow Monitor 72.0 MGD Continuous Metered 17 Discharge Temperature NA 110 (43.3) 0F ( °C )

Continuous Metered 5

Temperature Difference (AT)

NA 30(16.7)

° F( °C )

Continuous Metered 5

(Discharge temp. - Intake temp.).

Net Rate of Addition of Heat NA 470 MBTU/hr Daily Calculated Solids, Total Suspended Monitor Monitor mg/I Daily during Grab forebay cleaning Free Available Chlorine 0.2 0.27 mg/I Once per each Grab 16, 18 treatment Total Residual Oxidant NA 0.2 mg/I Once per each Grab 16 treatment Copper, Total NA 0.25 mg/I Monthly Grab 22 Phosphorus (as P)

NA 0.5 mg/I Monthly Grab Iron, Total NA 1.0 mg/I Monthly Grab Mercury, Total NA 50 0.5 ng/I Monthly Grab 23 Zinc, Total 0.3 mg/I Quarterly Grab WET - Acute Invertebrate 8.1 TUa Quarterly see footnote 24 WET - Acute Vertebrate 8.1 TUa Quarterly see footnote 24 WET - Chronic Invertebrate 54 TUc Quarterly see footnote "24 WET - Chronic Vertebrate 54 TUc Quarterly see footnote 24 The 126 priority pollutants No detectable mg/I or Annual Grab (Appendix A of 4 CFR 423) amount lg/I as contained in chemicals added appropriate to cooling tower maintenance, except as noted at this Outfall.

Footnotes: See Pages 16 - 18 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 12 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING]

0I A Decay heat cooling water blowdown (120 gpm)

Lake Ontario via Outfall 040 (primary EDP I 1/30/14

__II

_pathway) or Outfall 001 PARAMETER MINIMUM MAXIMUM UNITS SAMPLEFREQUENCY SAMPLE FOOTNOTES (FN)

SM IM U

IT S

TYPE F

H 6.0 9.0 SU Monthly Grab ENFORCEABLE LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPE I TYPE II Flow NA Monilor GDP Monthly Calculated Temperature NA 90 mg/l Monthly Grab 20 Total Residual Chlorine NA 0.2 mg/l Monthly Grab 16 OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 026 Unit 2 Resin regeneration, demineralizcr test water and reverse Lake Ontario via Outfall EDP 11/30/14 osmosis wastewater. Batch discharge: 12 - 24 batch per year.

040 (primary) or Outfall 30 Duration per batch= 1 day [FN I]

(alternate)

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE FOOTNOTES TYPE (FN)

OH 6.0 9.0 SU Once / Batch discharge Grab ENFORCEABLE LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN T UNITS FREQUENCY TYPE Monthly Avg.

Daily Max. TYPEVILTYPE II Flow NA Monitor GPD Batch Calculated Footnote: See Page 17 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 13 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL No.

WASTEWATERITYPE RECEIVING WATER EFFECTIVE EXPIRING 40A Unit 2 - Recirculated cooling tower effluent through area sumps; I 1000 gpd.

Lake Ontario via EDP 11/30/14 Multiple discharged per day; 5-20 rain.. each discharge.

I Outfall 040 PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY SAMPLE FOOTNOTES (FN)

I TYPE Pl-H 6.0 9.0 SU Monthly Grab ENFORCEABLE LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPEI TYPEII Flow NA Monitor GPD Monthly Calculated 21 Oil & Grease NA 15 mg/I Monthly Grab OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 041 Unit 2 wast*cater (dcmineralization water, reverse.osmosis, electrodeionization Lake Ontario via EDP I1/30/14 filtration, and treated radioactive wastewater); Batch discharge: 0 - 30 batch per Outfall 040

[,ear and lcas than one day per btchth'0.046 MGD per batch PARAMETER MINIMUM MAXIMUM UNITS

.SAMPLE FREQUENCY SAMPLE FOOTNOTES (FN)

TYPE pH 6.0 9.0 SU Once per Batch Grab 8

ENFORCEABLE LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Avg.

Daily Max.

TYPEI TYPEII Flow Monitor Monitor MGD Monthly Calculated I

Oil & Grease NA 15 mg/I Quartcrly Grab 9

Oil & Grease NA 15 mg/I Batch Grab 9

Solids, Suspended 30 50 rmg/I Quarterly Grab 9

Solids, Suspended 30 50 mg/I Batch Grab 9

Conductivity Monitor

'Monitor minho/cin Batch Grab 9

Footnotes: See Pages 16 and 17 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 14 of 35 PERMIT LIMITS, LEVELS AND MONITORING OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 001 Contact cooling water (decay heat cooling tower blowdown, 120 gpm= 172,800 gpd, i.e. 01A); Unit 2 - torebay cleaning (40B; Lake Ontario EDP 11/30/14 100,000 gpd); floor & equipment drains [Outfall 07 (A, C-G); 5000 gpd]; alternate forebay cleaning (120,000 gpd,Outfall 01A) [Total flow = - 397,800 gpd] [FN 1]_

PARAMETER MINIMUM MAXIMUM UNITS SAMPLE FREQUENCY I SAMPLE I

FOOTNOTES 11 1

TYPE (FN) pH 6.0 9.0 SU Quarterly Grab 27 j

ENFORCEABLE LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE FN UNITS FREQUENCY TYPE Monthly Daily Max.

TYPE I TYPE II Avg.

Flow NA Monitor GPD Quarterly Estimated or calculated from sub-streams Oil & Grease NA 15 mg/I Quarterly Grab or calculated from sub-streams Solids, Suspended NA 50 mg/I Quarterly Grab or calculated from sub-streams Copper, Total 0.05 mg/I Quarterly Grab or calculated from sub-streams Zinc, Total 0.15 mg/I Quarterly Grab or calculated from sub-streams OUTFALL No.

WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 002 Stormwater runoff only Lake Ontario EDP 11/30/14 No monitoring required Footnote: See Pages 16 and 18 of this permit.

SPDES PERMIT NUMBER NY 000 1015 Page 15 of 35 PERMIT LIMITS, LEVELS AND MONITORING Zebra Mussel Control Program OUTFALL NUMBER WASTEWATER TYPE RECEIVING WATER EFFECTIVE EXPIRING 010 See Page 4 of this permit Lake Ontario EDP 11/30/14 040 See Page 11 of this permit Lake Ontario EDP 11/30/14 001 Equipment Sump Storm Drain Lake Ontario EDP 11/30/14 EFFLUENT LIMIT MONITORING PARAMETER ACTION LEVEL SAMPLE SAMPLE UNITS FREQUENCY TYPE FN Monthly Avg.

Daily Max.

TYPE I TYPE II EVAC at Outfall 010 NA 2.0 **

mg/l Duration of chemical Multiple application and discharge Grab

  • EVAC at Outfall 040 NA 1.0 **

mg/I Duration of chemical Multiple application and discharge Grab

  • EVAC at Outfall 001 NA 0.1
  • mg/l One Treatment Grab Notes:
  • For purpose of this authorization, mnultiple grab. is defined as individual grab samples collected on intervals not to exceed eight hours.

Calculated based on samples obtained before discharge.

Pathway from incidental leakage of lake water (Outfall 040) during EVAC application.

Special Conditions for Zebra Mussel Control Program:

The Nalco EVAC (name change from Calgon) program for zebra mussel control, application submitted by letter application dated May 29, 1998 to Paul Kolakowski and Joanne March is approved with the following conditions:

I. The concentrations at the mixing zone shall not exceed 20 pg/I (ppb) of Alkylamine or 35 g/il (ppb) of whole product for Calgon EVAC, these limitations will be achieved by limiting whole product concentrations.

2.

Each individual zebra mussel control treatment is limited to a maximum of 48 hours5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> duration.

3.

Treatment for Zebra Mussel control treatment is limited to a maximum two treatments annually per plant. Treatment s shall be separated by at least 45 days.

4.

Records of product dosage concentration, effluent flow and effluent concentration of product during addition and discharge must be maintained. The flow shall be measured at the frequency specified for flow elsewhere in this permit or at the frequency of the parameter specified above, whichever is more frequent.

5.

The Regional Water Engineer shall be notified not less than 48 hours5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> before initiation of a zebra mussel control program.

6.

Reports describing the results of the effectiveness of the Zebra Mussel control program and the effluent analyses for Calgon EVAC shall be submitted to the Regional Water Engineer, NYDEC, in an annual report to be submitted by March Ist.

7.

This permit modification is issued based on the best environmental and aquatic toxicity information available at this time.

SPDES PERMIT NUMBER NY 000 1015 Page 16 of 35 FOOTNOTES,

1. Consistent with New York's Multi-Sector General Permit for Industrial Stormwater (GP-0-06-002), the permitted outfalls (00 1, 002,030, 023 and 020) with this footnote may include: Discharges from fire fighting activities; Potable water sources including waterline flushings; Uncontaminated air conditioning or compressor condensate; and other uncontaminated condensate such as condensate from the surface of pressurized gas cylinders stored outfside; and Landscape watering provided that all pesticides (note that the use of pesticide and fungicideproducts should follow GP-0-06-002) and fertilizers have been applied in accordance with manufacturer's instructions. These Outfalls may also include treated potable or lake water (treated through demineralization, reverse osmosis or other similar method.

For Outfalls 040, 010 and 026 with this footnote may include all discharges listed above excluding discharges from landscape watering.

2.

The use of sand separators at the Unit I Seal Water System and associated wastewaters are approved for discharge.

3.

Calculated flows are based on the "Adam Strainer" pressure reading, which is indicative of lake level. Weekend/holiday calculated flows are based on the "Adams Strainer" pressure reading from the previous surveillance. Calculated flows for Monday through Friday are based on the respective lake level for the calculation date.

4.

Changes in Service Water System flowrates should be made in a manner that minimizes the rapid discharge of deposited sediments during periods of normal operation above 5% power load.

5.

Computer data, logged at least hourly, maybe utilized for this parameter in order to verify compliance during normal operation conditions. During unusual operating conditions or in situations where the hourly data is near the outfall limitation, chart recorder data will be reviewed and utilized to demonstrate compliance.

6.

The intake temperature for this designated outfall shall be considered that temperature existing after intake waters have been tempered. The Intake - Discharge Temperature Difference limit may be exceeded during periods when plant safety is at issue, during periods when the circulating water system (CWS) is experiencing an emergency situation that is outside the normal operating envelop or during routine maintenance of the system, such as, but not limited to, the following situations: debris blockage of a CWS component, an emergency steam release, pump breakdown, etc.

In the event of such an emergency/breakdown, the permittee shall take corrective action to bring the temperature parameter within the permit limit as soon as possible. The permittee, whenever possible, should take action to avoid temperature parameter exceedance from June through September.

In the event that the facility is experiencing inlet icing conditions during the winter season, the Intake - Discharge Temperature Difference limit (A T ) may be exceeded by 35%, or 12.25 ° F, for no more than one hour during each reverse flow or return to normal flow operation. The facility may exceed the 35% criteria for a period of fifteen (15) minutes when the facility returns to normal flow configuration. This momentary increase during return to normal flow configuration is acceptable.

The permittee shall indicate in the Discharge Monitoring Report the reason for operating outside of the permit limit, and the dates

'and times of the associated event. In no case-shall the permit limitation be exceed for more than 5% of the operating time during the operating year.

7.

Copper - The permittee shall use Standard Method 313B (Digestion followed by Direct Current Plasma) with 8 ug/l or EPA Method 220.2 (Digestion followed by FGAA) with PQL = 4 ug/l or Method 200.7 (Digestion followed by Inductively Coupled Plasma) with PQL = 20 ug/l. It is recommended that clean technology EPA Method be used.

8.

pH range of 4.0 to 9.0 is allowable for wastewater having a conductivity of less than 10 ptmho/cm.

9.

High purity wastewater discharges that have a conductivity of 10 gtmho/cm or less are permitted for.an oil and grease and total suspended solids measurement frequency of once per calendar quarter.

10. Permit outfalls with this designation include the discharge of uncontaminated precipitation storm water and/or groundwater from.

containment systems and other similar structures to the surrounding grounds including storned areas. Contaminated water from said structures will be managed per NMPNS spill procedures, the.Spill Prevention Report (SPR), the Spill Prevention, Control and Countermeasure (SPCC) plan, and stormwater pollution prevention plans (SWPPPs).

11. During tempering of service waters with cooling water, a portion of the tempering waters will be discharged via this outfall.

Furthermore. During drainage of the cooling tower system, a portion of these drainage waters will also be discharged via this outfall.

12. Discharge from the two switch yard oil separators will be sampled before combination with waste stream 020.

SPDES PERMIT NUMBER NY 000 1015 Page 17 of 35

13. The use of barley straw for pH control in the Unit 1 Oil Retention Basin is acceptable.
14. Emergency discharge of fire foam from Units I and 2 may be routed to this treatment plant for treatment.
15. Monitoring of these parameters is only required during the period whendisinfection is required.
16. Outfall 010 - The current Total Residual Oxidant limit of 0.2 mg/I as daily maximum remains in effect until EPD + 1 year.

Outfall 030 - The current Total Residual Chlorine limit of 0.5 mg/I as daily maximum remains in effect until EDP + 1 year.

Outfall 040 - The current Free Available Chlorine limit of 0.2 mg/I as daily average and 0:5 mg/l as daily maximum and total residual oxidant of 0.2 mg/I as daily maximum remain in effect until EDP + 1 year.

17. There shall be no discharge of heat from the main condensers except heat may be discharged in blowdown from recirculated cooling water systems provided the temperature at which the blowdown is discharged does not exceed at any time the lowest temperature of recirculated cooling water prior to the addition of the markup water. Outfall 040 includes cooling tower blowdown as well as service water flow.
18. The Free Available Chlorine samples shall be obtained prior to combination with Service Water.
19. Total Residual Oxidant applies only to treatments of Service Water System.
20. In no case shall the temperature limit be exceeded more than 5% of the time during the operating year.
21. Outfall 40A has two contributing sources, each originating from an individual sump located in the Circulating Water Pump pits.
22. The total copper samples should be obtained from the Cooling Water System (CWS) blowdown line or the cooling tower basin.

The total copper concentration for Outfall 040 will be based on a calculated value taking into consideration the flow from the service water system. The equation and parameters for performing this calculation are as follows:

Total Copper Concentration at Outfall 040

[CWSlcu X CWS Blowdown Flow + [TF]cu X Tempering Flow Total Flow for Outfall 040

[CWS]cu = Copper concentration of Circulating Water System (CWS) Blowdown, Total Flow for Outfall 040 =CWS Blowdown Flow and Tempering Flow (i.e. Service Water Discharge Flow),

[TF]cu = Copper concentration of Tempering Flow. [TF], and Tempering Flow = The amount of service water (discharge effluent) used to temper the service water influent during winter months.

23. EPA Method 1631 shall be used for analyzing Mercury. From EDP to EDP + I year, the permittee may have an interim mercury limit of 70 ng/l. The permittee shall comply with the final mercury limitation of 50 ng/l starting from "EDP + 1 year" and after.
24. Whole Effluent Toxicity (WET) Testing:

Testing Requirements - WET testing shall consist of/ Chronic only. WET testing.shall be performed in accordance with 40 CFR Part 136 and TOGS 1.3.2 unless prior written approval has been obtained from the Department. The test. species shall be.

Ceriodaphnia dubia (water flea - invertebrate) and Pimephales pronmelas (fathead minnow - vertebrate). Receiving water collected upstream from the discharge should be used for dilution. All tests conducted should be static-renewval (two 24 hr composite samples with one renewal for Acute tests and three 24 hr composite samples with two renewals for Chronic tests). The appropriate dilution series bracketing the IWC and including one exposure group of 100% effluent should be.used to generate a definitive test endpoint, otherwise an immediate rerun of the test is required. WET testing shall be coordinated with the monitoring of chemical and physical parameters limited by this permit so that the resulting analyses are also representative of the

SPDES PERMIT NUMBER NY 000 1015 Page 18 of 35 sample used for WET testing. The ratio of critical receiving water flow to discharge flow (i.e. dilution ratio) is 4.6 :1 for chronic at Outfall 010 and 54:1 For chronic at Outfall 040. Discharges which are disinfected using chlorine should be dechlorinated prior to WET testing or samples shall be taken immediately prior to the chlorination system.

Monitoring Period - WET testing shall be performed at the specified sample frequency for a period of one full year beginning at EDP+ 3 Months.

Reporting - Toxicity Units shall be calculated and reported on the DMR as follows: TUa = (100)/(48 hr LC50) or (100)/(48 hr EC50) (note that Acute data is generated by both Acute and Chronic testing) and TUc = (1 00)/(NOEC) when Chronic testing has been performed or TUc = (TUa) x (10) when only Acute testing has bccn performed and is used to predict Chronic test results, where the 48 hr LC50 or 48 hr EC50 and NOEC are expressed in % effluent. This must be done for both species and using the Most Sensitive Endpoint (MSE) or the lowest NOEC and corresponding highest TUc. Report a TUa of 0.3 if there is no statistically significant toxicity in 100% effluent as compared to control.

The complete test report including all corresponding results, statistical analyses, reference toxicity data, daily average flow at the time of sampling and other appropriate supporting documentation, shall be submitted within 60days following the end of each test period to the Toxicity Testing Unit. A summary page of the test results for the invertebrate and vertebrate species indicating TUa, 48 hr LC50 or 48 hr EC50 for Acute tests and/or TUc, NOEC, IC25, and most sensitive endpoints for Chronic tests, should also be included at the beginning of the test report.

WET Testing Action Level Exceedances - If an action level is exceeded then the Department may require the permittee to conduct additional WET testing including Acute and/or Chronic tests. Additionally, the permittee may be required to perform a Toxicity Reduction Evaluation (TRE) in accordance with Department guidance. If such additional testing or performance of a TRE is necessary, the permittee shall be notified in writing by the Regional Water Engineer. The written notification shall include the reason(s) why such testing or a TRE is required.

25. During periods of discharge from Outfall 025, representative samples can be collected from the cooling tower basin for parameter monitoring within 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> of the initiating discharge.
26. At Outfall 040, the pemittee may take pH samples at thecooling tower basin for~compliance purposes.
27. At Outfall 001, pH sampling and reporting is Waived during November to March due to unsafe sampling conditions. In case, there are unsafe sampling conditions existed outside of November to March, the permittee may adjust the sampling dates and report on the DMR forms.
28. Based on report: Near-Field and Far-Field Modeling Studies For the Nine Mile Point Unit I and 2 (Hydro Qual, Inc. January 2009)

ADDITIONAL REQUIREMENTS

1. The following requirements areapplicable to Units #1 and #2 I.

According to 40CFR423, neither free available chlorine nor total residual chlorine maybe discharge from any unit for more than two hours in any one day and not more than one unit in any plant may discharge free available or total residual chlorine at any one time. The term average concentration as it relates to chlorine discharge meansthe average of analysis made over a single period of chlorine release which does not exceed two hours.

SPDES PERMIT NUMBER NY 000 1015 Page, 19 of 35

8.

The water temperature at the surface of Lake Ontario shall not be raised more than three Fahrenheit degrees over the temperature that existed before the addition of heat of artificial origin except in a mixing zone consisting of an area of 300 acres from the point of discharge, this temperature may be exceed.

I1. The following requirements are applicable to Unit #2 No discharge from this facility shall cause violation of the New York State Department of Health regulations contained in 10 NYCRR Part 170 at the source of intake of any water supply used for drinking, culinary or food processing purposes.

SPDES PERMIT NUMBER NY 000 1015 Page 20 of 35 MONITORING LOCATIONS The permittee shall take samples and measurements, to comply with the monitoring requirements specified in this permit, at the location(s) specified below:

Nine Mile Point Nuclear station (NY 000 1015) -Water Balmlani Dipartia

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SPDES PERMIT NUMBER NY 000 1015 Page 21 of 35 Outfall Location Map Form NY-2C i,/01). Secaon IFtms Attachment In Map of Facility and Discharge Locations

SPDES PERMIT NUMBER NY 000 1015 Page 22 of 35 011 Unit I 010 10A Simplified Flow Path for Nine Mile Point Nuclear Station (NY 000 1015) 07B 024 Legend:

Normal flow direction Alternate flow direction 020 lqw=-

Nsm Cooling water blowdown A t% I'*

I*d A

Unit 2 40A 041 040 026

,ut vuIA J

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U1sw 023 025 07A 07C 07D 07E 07F 07G Ditch 002 -4 008 021 -'

002 008 021

SPDES PERMIT NUMBER NY 000 1015 Page 23 of 35 BIOLOGICAL MONITORING REQUIREMENTS All submissions under this section should provide:

Two (2) copies to the Steam Electric Unit Leader; One (1) copy of the cover letter to the Division of Water State Pollution Discharge Elimination System (SPDES)

Compliance Information Section; and One (1) copy of the cover letter to the Regional Water Engineer; unless otherwise noted.

Impingement and Entrainment Characterization Study I1.

By EDP + 6 Month, a final report for the 2006-2007 Impingement and Entraimnent Study conducted at Nine Mile Point Unit 1 shall be submitted to the offices listed above for Department review and approval. The report shall contain an estimate of the abundance of fish impinged and entrained at current operating conditions, and at full flow calculation baseline conditions over the one year study period. Each flow scenario shall provide an estimate, in tabular form, of the total numbers of organisms impinged and entrained each month. Biota shall be identified to species, or lowest practical taxon, and each taxonomic group entrained shall also be subdivided by lifestage.

Design and Construction Technology Plan

2.

By EDP + 6 months, the permittee must submit an approvable Design and Construction Technology Plan that includes:

a.

Tables showing the average monthly and annual cooling water use and net generation of the facility in MWhr (megawatt hours) measured over the last 5 years.

b.

An estimate of the abundance of fishimpinged and entrained at current operating conditions, and at full flow calculation baseline conditions over the one year study period.

c.

An analysis of all feasible technologies and/or operational measures capable of being installed and implemented at Nine Mile Point Unit 1 to minimize impingement and entrainment of fish, including the use of closed cycle cooling. For each alternative, the following information shall be included:

i.

A detailed description of the alternative (including preliminary drawings'and site maps, if appropriate);

ii.

A discussion of the engineering feasibility of the alternative; iii.

An assessment of the mitigative benefits in reducing entrainment abundance for all life stages of fish through utilization of the alternative; iv.

A breakdown of all applicable costs including costs associated with capital improvements, operation and maintenance, and construction downtime;

v.

An estimate of the time required to implement the alternative; and vi.

An evaluation of any adverse environmental impacts to aquatic biota, habitat, or water quality that may result from construction, installation, and use of the alternative.

Proposed Suite of Technologies or Operational Measures

3.

Within 1 month of the Department's approval of the Design and Construction Technology Plan, the permitted must submit, for Department review and consideration, a Proposed Suite of Technologies or Operational Measures that meets the requirements of 6 NYCRR Part 704.5 and adheres to the following requirements:

a.

The reductions in entrainment resulting from existing and proposed technologies and/or operational measures can be no less stringent, and if possible, should be substantially better than 60 percent from the full-flow calculation baseline;

b.

The reductions in impingement mortality resulting from existing and proposed technologies and/or operational measures can be no less stringent, and if possible, should be substantially better than 80 percent from the full-flow calculation baseline NOTE: Based on this and other relevant information, the Department will select technologies and/or operational measures that meet the requirements of 6 NYCRR Part 704.5 and will modify this SPDES permit to require the use of these selected technologies and/or operational measures.

SPDES PERMIT NUMBER NY 000 1015 Page 24 of 35 Technology Installation and Operation Plan

4.

Within 3 months of the effective date of the permit modification requiring technologies and/or operational measures to meet requirements of 6 NYCRR Part 704.5, the permittee must submit an approvable Technology Installation and Operation Plan.

This plan must include:

a.

a schedule for installing and implementing the technologies and/or operational measures selected to meet requirements of 6 NYCRR Part 704.5; and

b.

the methodology for assessing the efficacy of these technologies and operational measures.

Upon receipt of Department approval, the permittee must implement the Technology Installation and Operation Plan in accordance with the approved schedule. The Technology Installation and Operation Plan and approved schedule will become an enforceable condition of this SPDES permit.

Verification Monitoring Plan

5.

Within 3 months of Department approval of the Technology Installation and Operation Plan, the permittee must submit an approvable Verification Monitoring Plan. This plan must include details of procedures to confirm that the necessary reductions in impingement and entrainment required by this permit are being achieved, including the following:

a.

A five year averaging period which shall include, at a minimum, two years of biological monitoring to verify ihe full-scale performance of selected BTA measures for entrainment reduction.

b.

A description of the frequency and duration ofimonitoring, the parameters to be monitored, and the basis for determining the parameters and the frequency and duration for monitoring.

c.

A schedule of implementation.

d.

A draft proposed Standard Operation Procedure (SOP) that describes the sampling protocols for these monitoring studies.

The plan and SOP must be updated as required by the Department. Upon receipt of Department approval the permittee must complete the Verification Monitoring Plan in accordance with the approved schedule. The Verification Monitoring Plan-and approved schedule will become an enforceable condition of this SPDES permit.

6.

Within 6 months of completion of the studies required in the approved Verification Monitoring Plan, the permittee must submit an approvable report to the Steam Electric Unit Leader that demonstrates compliance with 6 NYCRR Part 704.5.

Additional Reporting Requirements

7.

The permittee must maintain records of all data, reports and analysis pertaining to compliance with 6NYCRR Part 704 and Section 316(b) CWA for.a period no less than 10 years from EDP.

8.

The permittee must submit status reports at EDP + 2.5 years and EDP + 4.5 years. At a minimum, these statusreports must include a description of the.operational status of the facility during the preceding two years and compliance with Biological Requirements I through 5 of this permit.

General Requirement

9.

Modification of the facility cooling water intake must not occur without prior Department approval. The permittee must submit written notification, including detailed descriptions and plans, to the NYS DEC Steam Electric Unit; the Director of the Bureau of Water Compliance Program; and both the Regional Permit Administrator and the Regional Water Engineer, Region 2, at least 60 days prior to any proposed change which would result in the alteration of the permitted operation, location, design, construction or capacity of the cooling water intake structure. The permittee must submit with the written notification a demonstration that the change reflects the best technology available for minimizing adverse environmental impacts pursuant to 6 NYCRR §704.5 and Section 316(b) of the Clean Water Act. As determined by NYS DEC, a permit modification application in accordance with 6 NYCRR Part 621 may be required.

SPDES PERMIT NUMBER NY 000 1015 Page 25 of 35

10.

Thermal Discharge Study The permittee submitted a Thermal Modeling Study work plan dated 4 April 2008 to the Department consistent with the Thermal Discharge Study requirement that the Department handed out during the meeting of September 20, 2007. The Thermal Modeling Study work plan was designed to describe all applicable criteria contained in 6 NYCRR Part 704 and evaluate compliance with those criteria for determining (and verifying) the size of the mixing zone and the mapping of the facility's thermal plume during summer, winter or other critical climatological conditions. The Thermal Modeling Study work plan includes study protocols, a schedule for conducting the studies and the submission ofan approvable Thermal Study Report. The Department approved the Thermal Modeling Study work plan on 22 April 2008. The pennittee is required to submit an approvable final thermal modeling study report to the Department within six months of the Effective Date of this Permit (EDP) [EDP + 6 months].

Potential Increase in Ambient Temperature/Global Warming There is a potential of increasing lake ambient temperatures due to global warming. This could be more visible during warm months (July, August and some part of September). In view of this, the permittee shall expand the thermal study to cover the potential high lake temperatures and present the model findings to address requirements stipulated in 6 NYCRR Part 704 and CWA See. 316(a).

The permittee should analyze the ambient data for trends and to ascertain if the receiving waters are becoming warmer than the preceding years or if global warming is taking place in the ambient waters. The permittee should provide technical information to the maximum extent tojustify warming trends, if any. To account for future increases in ambient temperatures due to global warming, the permittee shall perfornm three (3) additional modeling projection runs in increments of 2 degrees Fahrenheit starting with the baseline worst-case scenario. Results must be included as part of the final Thermal Discharge Study Report required above. The baseline worst-case scenario may include but is not limited to: the criticalambient temperature, climatological, seasonal conditions and etc. All runs shall be made under maximum thermal discharge loading condition. The impact assessment shall be made for change in the spatial extent of the mixing zone, and etc.

SPDES PERMIT NUMBER NY 000 1015 Page 26 of 35 SPECIAL CONDITIONS - INDUSTRY BEST MANAGEMENT PRACTICES 1I General - The permittee shall develop, maintain, and implement a Best Management Practices (BMP) plan to prevent releases of significant amounts of pollutants to the waters of the State through plant site runoff; spillage and leaks; sludge or waste disposal; and stormwater discharges including, but not limited to, drainage from raw material storage.

The BMP plan shall be documented in narrative form and shall include the 13 minimum BMPs and any necessary plot plans, drawings, or maps. Other documents already prepared for the facility such as a Safety Manual or a Spill Prevention, Control land Countermeasure (SPCC) plan may be used as part of the plan and may be incorporated by reference. A copy of.the current BMP plan shall be submitted to the Department as required in item (2.) below and a copy must be maintained at the facility and shall be available to authorized Department representatives upon request.

2.

Compliance Deadlines - If a plan exists, a letter indicating that all requirements addressed in this section have been complied with or an amendment to the approved BMP to comply with all requirements in this Special Conditions must be submitted within 6 months of EDP to the Regional Water Engineer. The BMP plan shall be implemented within 6 months of submission, unless a different time frame is approved by the Department. The BMP plan shall be reviewed annually and shall be modified whenever- (a) changes at the facility materially increase the potential for releases of pollutants, (b) actual releases indicate the plan is inadequate, or (c) a letter from the Department identifies inadequacies in the plan. The permittee shall certify in writing, as an attachment to the December Discharge Monitoring Report (DMR), that the.annual review has been completed. All BMP plan revisions (with the exception of SWPPPs - see item (4.B.) below) must be submitted to the Regional Water Engineer within 30 days. Note that the permittee is not required to obtain Department approval of the BMP plan (or of any SWPPPs) unless notified otherwise. Subsequent modifications to or renewal of this permit does not reset or revise these deadlines unless a new deadline is set explicitly by such permit modification or renewal.

3.

Facility Review - The permittee shall review all facility components or systems (including but not limited to material storage areas; in-plant transfer, process, and material handling areas; loading and unloading operations; storm water, erosion, and sediment control measures; process emergency control systems; and sludge and waste disposal areas) where materials and pollutants are used, manufactured, stored or handled to evaluate the potential for the release of pollutants to the waters of the State. In performing such an evaluation, the permittee shall consider such factors as the probability of equipment failure or improper operation, cross-contamination of storm water by process materials, settlement of facility air emissions, the effects of natural phenomena such as freezing temperatures and precipitation, fires, and the facility's history of spills and leaks. The relative toxicity of the pollutant shall be considered in determining the significance of potential releases.

The review shall address all substances present at the facility that are identified in Tables 6-10 of SPDES application Form NY-2C (available at http:/Avww.dec.state.ny.us/website/dcs/permits/olpermits/form2c.pdJ) and that are required to be monitored for by the SPDES permit.

4.

A. 13 Minimum BMPs -.Whenever the potential for a release of pollutants to State waters is determined to be present, the permittee shall identify BMPs that have been established to prevent or minimize such potential releases. Where BMPs are inadequate or absent, appropriate BMPs shall be established. In selecting appropriate BMPs, the permittee shall consider good industry practices and, where appropriate, structural measures such as secondary containment and erosion/sediment control devices and practices. USEPA guidance for development of stormwater elements of the BMP is available in the September 1992 manual Stormn Water Management for Industrial Activities, EPA 832-R-92-006 (available from NTIS, 703-487-4650, order # PB 92235969)..,As a minimum, the plan shall include the following BMPs:

I. BMP Pollution Prevention Team

6. Security
10. Spill Prevention & Response
2. Reporting of BMP Incidents
7. Preventive Maintenance
11. Erosion & Sediment Control
3. Risk Identification & Assessment
8. Good Housekeeping
12. Management of Runoff
4. Employee Training
9. Materials/Waste Handling,
13. Street Sweeping
5. Inspections and Records Storage,& Compatibility Note that for some facilities, especially those with few employees, some of the above BMPs may not be applicable. It is

SPDES PERMIT NUMBER NY 000 1015 Page 27 of 35 acceptable in these cases to indicate "Not Applicable" for the portion(s) of the BMP Plan that do not apply to your facility, along with an explanation.

B. Stormwater Pollution Prevention Plans (SWPPPs) Required for Discharges of Stormwater From Construction Activity to Surface Waters - As part of BMP #11, a SWPPP shall be developed prior to the initiation of any site disturbance of one acre or more of uncontaminated area. Uncontaminated area means soils or groundwater which are free of contamination by any toxic or non-conventional pollutants identified in Tables 6-10 of SPDES application Form NY-2C.

Disturbance of any size contaminated area(s) and the resulting discharge of contaminated stormwater is not authorized by this permit unless the discharge is under State or Federal oversight as part of a remedial program or after review by the Regional Water Engineer; nor is such discharge authorized by any SPDES general permit for stormwater discharges. SWPPPs are not required for discharges of stormwater from construction activity to groundwaters.

The SWPPP shall conform to the New York Standards and Specifications for Erosion and Sediment Control and New York State Stormwater Management Design Manual, unless a variance has been obtained from the Regional Water Engineer, and to any local requirements. The permittee shall submit a copy of the SWPPPand any amendments thereto to the local governing body and any other authorized agency having jurisdiction or regulatory control over the construction activity at least 30 days prior to soil disturbance. The SWPPP shall also be submitted to the Regional Water Engineer if contamination, as defined above, is involved and the permittee must obtain a determination of any SPDES permit modifications and/or additional treatment which may be required prior to soil disturbance. Otherwise, the SWPPP shall be submitted to the Department only upon request. When a SWPPP is required, a properly completed Notice oflntent (NOI) form shall be submitted (available at wwwidec.state.ny.us/1website/dow/toolbox/swforms.html) prior to soil disturbance. Note that submission of a NOI is required for informational purposes; the permittee is not eligible for and will not'obtain coverage under any SPDES general permit for stormwater discharges; nor are any additional permit fees incurred. SWPPPs must be developed and submitted for subsequent site disturbances in accordance with the above requirements. The permittee is responsible for ensuring that the provisions of each SWPPP is properly implemented.

SPDES PERMIT NUMBER NY 000 1015 Page 28 of 35 MERCURY MINIMIZATION PROGRAM REQUIREMENTS - Outfall 040 INDUSTRIAL FACILITIES I.

General - The permittee shall develop, implement, and maintain a Mercury Minimization Program (MMP) for Outfall 040. The MMP is required because the 50 ng/L permit limit exceeds the, state-wide calculated water quality based effluent limit (WQBEL) of 0.70 nanograms/liter (ng/L) for Total Mercury. The goal of the MMP will be to reduce mercury effluent levels in pursuit of the calculated WQBEL.

2.

MMP Elements - The MMP shall be documented in narrative form and shall include any necessary drawings or maps. Other related documents already prepared for the facility may be used as part of the MMP and may be incorporated by reference. As a minimum, the MMP shall include an on-going program consisting of: periodic monitoring; an acceptable control strategy which will become enforceable under this permit; and, submission of annual status reports.

A. Monitoring - The permittee shall conduct periodic monitoring designed to quantify and, over time, track the reduction of mercury. All permit-related wastewater and stormwater mercury monitoring shall be performed using EPA Method 1631 and shall be coordinated so that the results can be compared. All samples should be grabs and use of EPA Method 1669 during sample collection is recommended.

Monitoring of raw materials, equipment, treatment residuals, and other non-wastewater/non-stormwater substances may'be performed using methods other than EPA Method 1631 if appropriate. Minimum required monitoring shall be in accordance with the minimum frequency specified on the mercury permit limits page at each of the following locations: outfalls, wastewater treatment plant influents and effluents, key locations in the wastewater and/or stormwater collection systems, and known or potential mercury sources, including raw materials. Additional monitoring must be completed as may be required elsewhere in this permit or upon Department request.

B. Control Strategy - An acceptable control strategy is required for reducing mercury discharges via cost-effective, measures, which may include, but is not limited to, more stringent control of tributary waste streams, remediation, and/or installation of new or improved treatment facilities. Required monitoring shall also be used, and supplemented if appropriate, to determine the most effective way to operate the wastewater treatment system(s) to ensure effective removal of mercury while maintaining compliance with other permit requirements.

C. Annual Status Report - An annual status report shall be submitted to the Regional Water Engineer and to the Bureau of Water Permits summarizing: (a)all MMP monitoring results for the previous year; (b) a list of known and potential mercury sources; (c) all action undertaken pursuant to the strategy during the previous year, (d) actions planned for the upcoming year, and (e) progress toward the goal. The first annual report is due EDP + 1 year and follow-up reports are due annually thereafter. Note that the complete MMP documentation need not be submitted to the Department unless otherwise requested.

3.

MMP Modification -The MMP shall be modified whenever: (a)changes at the facility or within the collection system increase the potential for mercury discharges; (b) actualdischarges exceed 50 ng/L;' (c) a letter from the Department identifies inadequacies in the MMP; or (d) pursuant to a permit modification.

SPDES PERMIT NUMBER NY 000 1015 Page 29 of 35 WATER TREATMENT CHEMICAL (WTC) REQUIREMENTS (9199)

H.MI&2SPOESpemt8-6-0.,"d New or increased use of a WTC requires prior DEC review and authorization. At a minimum, the permittee must notify the DEC in writing of its intent to change WTC use by submitting a completed WTCFX Form for each WTC. The DEC will review that submittal and determineif a SPDES permit modification is necessary or whether WTC review and authorization may proceed outside of the formal permit adminisirativeprocess. The majority of WTC authorizations do not require formal SPDES permit modification. WTCs which are uscd in closcd systems and cannot be discharged or those which are discharged to municipal STP do not require DEC review. WTC use and discharge questions or requests for forms should be directed to the DEC staff person who developed your SPDES permit. If you are not sure who that is, contact the DEC staff person who last inspected your facility.

Examples of WTCs include, biocides, coagulants, conditioners, corrosion inhibitors, defoamers, flocculants, scale inhibitors, sequestrants, and settling aids. DEC staff may also direct you to use a WTCFX Form for review and authorization of substances other than WTCs, e.g.

process chemicals.

The permittee must demonstrate that the use and discharge of any WTCs containing phosphorus, tributary to the Great Lakes Basin or other ponded waters, is necessary and that no acceptable alternatives exist. Please note that in some cases your permit may require modification to regulate phosphorus.

Generic WTC Usaae Requirements

1.

WTC use shall not exceed the rate reported by the pprmittee or authorized below, whichever is less.

2.

The discharge shall not cause or contribute to a violation of water quality or an exceedance of ambient water quality criteria.

3.

The permittee must maintain a logbook of all WTC use, noting for each WTC the date, time, exact location, and amount of each dosage, and, the name of the individual applying or measuring the chemical. The logbook must also document that adequate process controls are in place-to ensurethat excessive levels of WTCs are not used and subsequently discharged through outfalls.

The permittee shall retain the logbook data for a period of at least 5 years. This period may be extended by request of the DEC.

4.

The permittee shall provide an annual report, attached to the December DMR, containing the following information for each outfall: the current list of WTCs authorized for use and discharge by the DEC, for each WTC the amount in pounds used during

ýthe year, identification of authorized WTCs the permittee no longer uses, and any other pertinent information.

List of WTCs Authorized for Use and Discharge*

Affected Dosage (lbs/day)

WTC Manufacturer and Product Name WTC Function Outfall(s)

Avg Max 010 636.5 1018 Nalco Company-Nalco 73551 Deposit Penetrant 787 787 Nalco Company - STABREX ST170 Microorganism control chemical at Unit 1 condenser cooling water 2,346 4,083 Nalco Company - EVAC Mollusicide at Unit 1 condenser cooling water 32 64 Slack Company - Sodium Hypochlorite Chlorination 13.1 26.2 Nalco Company - Acti-Broom 1338 Biodispersant-at Unit I condenser 20.2 GE Betz -Sulfuric acid (or reagent pH control at Unit 1 oil spill retention basin 023 grade) 040 2,583 3,363 Nalco Company - EVAC Mollusicide (Zebra Mussel) at Unit 2 cooling tower blowdown and service'water

SPDES PERMIT NUMBER NY 000 1015 Page 30 of 35 Affected Dosage (lbs/day)

WTC Manufacturer and Product Name WTC Function Outfall(s)

Avg Max 557 1,980 GE Infrastructure, Water & Process Water based deposit control agent at Unit 2 Technology - POWERLINE 3450 circulating water service (CWS) 2,000 3,000 Betz Dearborn - Inhibitor AZ8104 Copper inhibitor at Unit 2 CWS (Slug feed)

(Slug feed) 3336 5,004 Nalco Company - CUPROSTAT PF Copper inhibitor at Unit 2 CWS (Slug feed)

(Slug feed) 040 396 1,170 GE Betz - DeposiTrol BL 5323 Water based corrosion inhibitor/deposit control agent at CWS (covered by permit limit of 2 mg/I as P) 10,169 11,379 Slack Chemical - Sulfuric acid pH control at Unit 2 CWS 2,192 3,288 PVS Company - Sodium Hypochlorite Chlorination at Unit 2 CWS 339 630 Slack Chemical Company - Super Chlor (Sodium Hypochlorite Solution)

Biocide (chlorination of service water system to produce hypobromite) - used 2 hour2.314815e-5 days <br />5.555556e-4 hours <br />3.306878e-6 weeks <br />7.61e-7 months <br />s/day, 148 274 Great Lake Chemical Corporation; 7 daus/week per 40CFR423 Distributed by Slack Chemical Company

- SLACKBROM-40 295 566 Sulco Chemicals Ltd.; Distributed by Water treatment (reduce hypobromite and Slack Chemical Company - Sodium hypqchlorite to its salts prior to discharge to Bisulfite Solution outfall)

- Authorized. WTCs must either be listed above or identified in a letter sent to the permittee by the DEC subsequent to issuance of this permit page. In cases where a WTC is listed above and in a letter from the DEC, the more recent document will control.

.SPDES PERMIT NUMBER NY 000 1015 Page 31 of 35 SCHEDULE OF COMPLIANCE a)

The permittee shall comply with the following schedule:

Action Outfall Code Number(s)

Compliance Action Due Date 010, 040 Water treatment chemical (WTC) - EVAC is listed in the existing SPDES EDP + 3 and 001 permit. The permittee shall submit a completed WTC request form for EVAC. Pay Months special attention to the following items.

EVAC (Nalco) for Outfall 010, 040 and 001 - Item 9a to 9d (WTC composition) and item 12 (toxicity information for acceptable aquatic species) of the WTC form.

010, 040 Total Residual Oxidant (Outfalls 010 and 040), and Free Available Chlorine (Outfall EDP + 6 and 025 040): See Page 17 of this permit. The permittee shall submit an engineering plans by Months EDP + 6 months with the compliance date to achieve the final limits at these Outfalls by EDP + I year.

Total Residual chlorine (Outfall 030): See Page 17 of this permit. The permittee shall EDP + 6 030 submit an approvable engineering report by EDP + 6 months for a design to achieve the Months final TRC limit at this Outfall by EDP + 1 year.

Best Management Practices (BMP) Plan - The permittee shall submit an approvable EDP + 6 BMP according to the requirements outlined in Page 25 of this permit.

Months Mercury MinimiZation Program (MMP) - The permittee shall submit annual status report EDP +

with first annual report due by "EDP + I year" Year The above compliance actions are one time requirements. The permittee shall comply withthe above compliance actions to the Department's satisfaction once. When this pernit is adndnistratively renewed by NYSDEC letter entitled "1SPDES NOTICE/RENEWAL APPLICATION/PERMIT," the permittee is. not required to repeat the submission(s) noted above. The above due dates are independent from the effective date of the permit stated in the letter of."SPDES NOTICE/RENEWAL APPLICATION/PERMiT."

b)

The permittee shall submit a written notice of compliance or non-compliance with eachof the above schedule datesno later than 14 days following each elapsed date, unless conditions require more immediatenotice as prescribed in 6' NYCRR Part 750-1.2(a) and 750-2. All such compliance or non-compliance notification shall be sent to the locations listed under the section ofthis permit entitled RECORDING, REPORTING AND ADDITIONAL MONITORING REQUIREMENTS. Each notice of non-compliance shall includethe following information:

1. A short description of the non-compliance;
2. A description of any actions taken or proposed by the permittee to comply with the elapsed schedule requirements without further delay and to limit environmental impact associated with the non-compliance;

.3. A description or any factors which tend to explain or mitigate the non-compliance; and

4. An estimate of the date the permittee will comply with the elapsed schedule requirement and an assessment of the probability that the permittee will meet the next scheduled requirement on time.

c)

The permittee shall submit copies of any document required by the above schedule of compliance to NYSDEC Regional Water Engineer at the location listed under the section of this permit entitled RECORDING, REPORTING AND ADDITIONAL MONITORING REQUIREMENTS and to the Bureau of Water Permits, 625 Broadway, Albany, N.Y. 12233-3505, unless otherwise specified in this permit or in writing by the Department.

SPDES PERMIT NUMBER NY 000 1015 Page 32 of 35 SCHEDULE OF COMPLIANCE a)

The permittee shall comply with the following schedule:

Action Outfall Code Number(s)

Compliance Action Due Date BIOLOGICAL MONITORING REQUIREMENTS (Refer to Pages 23 - 25 of this permit)

B 1. Submit an approvable Impingement and Entrainment Characterization Study EDP + 6 Months B2. Submit an approvable Design and Construction Technology Plan (DCTP)

EDP + 6 Months B3. Submit an approvable proposed suite of Technologies or Operational DEC approval of Measures DCTP + I Months B4. Submit an approvable Technology Installation and Operation Plan (TIOP)

EDP + 3 Months B5. Submit an approvable Verification Monitoring Plan (VMP)

DEC approval of TIOP + 3 Months B6. Submit an approvable report that demonstrates:compliance with 6 NYCRR Completion of VMP Part 704.5

+ 6 Months B8. Submit two Status Reports according to Biological Monitoring Requirement. 8, EDP + 2.5 Years &

Page 23 of this permit.

EDP + 4.5 Years B 10. Submit an approvable final Thermal Modeling Study Report EDP + 6 Months The above compliance actions are one time requirements. The permittee shall comply.with the above compliance actions to the Department's satisfaction once.

When this permit is administratively renewed by NYSDEC letter entitled "SPDES NOTICE/RENEWAL APPLICATION/PERMIT," the permittee is not required to repeat the submission(s) noted above. The above due dates are independent from the effective date of the permit stated in the letter of,SPDES NOTICE/RENEWAL APPLICATION/PERMIT."

b)

The permittee shall-submit a written notice of compliance or non-compliance with each of the above schedule dates no later than 14 days following each elapsed date, unless conditions require more immediate notice as prescribed in 6 NYCRR Part 75041.2(a) and 750-2. All such compliance or non-compliance notification shall be sent to the locations listed under the section of this permit entitled RECORDING, REPORTING AND ADDITIONAL MONITORING REQUIREMENTS. Each notice of non-compliance shall include the following information:

I. A short description of the non-compliance;

SPDES PERMIT NUMBER NY 000 1015 Page 33 of 35

2. A description of any actions taken or proposed by the permittee to comply with the elapsed schedule requirements without further delay and to limit environmental impact associated with the non-compliance;
3. A description or any factors which tend to explain or mitigate the non-compliance; and
4. An estimate of the date the permittee will comply with the elapsed schedule requirement and an assessment of the probability that the permittee will meet the next scheduled requirement on time.

c)

The permittee shall submit copies of any document required by the above schedule of compliance to NYSDEC Regional Water Engineer at the location listed under the section of this permit entitled RECORDING, REPORTING AND ADDITIONAL MONITORING REQUIREMENTS and to the Bureau of Water Permits, 625 Broadway, Albany, N.Y. 12233-3505, unless otherwise specified in this permit or in writing by the Department.

,4!

ok' SPDES PERMIT NUMBER NY 000 1015 Page 34 of 35 DISCHARGE NOTIFICATION REQUIREMENTS (a)

Except as provided in (c) of these Discharge Notification Act requirements, the pcrmittee shall install and maintain identification signs at all outfalls to surface waters listed in this permit. Such signs shall be installed within 90 days of the Effective Date of this Modification.

(b)

Subsequent modifications to or renewal of this permit does not reset or revise the deadline set forth in (a) above, unless a new deadline is set explicitly by such permit modification or renewal.

(c)

The Discharge Notification Requirements described herein do not apply to outfalls from which the discharge is composed exclusively of storm water, or discharges to ground water.

(d)

The sign(s) shall be conspicuous, legible and in as close proximity to the point of discharge as is reasonably possible while ensuring the maximum visibility from the surface water and shore. The signs shall be installed in such a manner to pose minimal hazard to navigation, bathing or other water related activities. If the public has access to the water from the land in the vicinity of the outfall, an identical sign shall be posted to be visible from the direction approaching the surface water.

The signs shall have minimum dimensions of eighteen inches by twenty four inches (18" x 24") and shall have white letters on a green background and'contain the following information:

N.Y.S. PERMITTED DISCHARGE POINT SPDES PERMIT No.: NY OUTFALL No.:

For information about this permitted discharge contact:

Permittee Name:

Permittee

Contact:

Permittee Phone:

(

) -### -

OR:

NYSOEC Division of Water Regional Office Address:

NYSDEC Division of Water Regional Phone: (

) - ### -#: #

(e)

For each discharge required to have a sign in accordance with a), the permittee shall, concurrent with the installation of the sign, provide a repository of copies of the Discharge Monitoring Reports (DMRs), as required by the RECORDING, REPORTING AND ADDITIONAL MONITORING REQUIREMENTS page of this permit. This repository shall be open to the public, at a minimum, during normal daytime business hours. The repository may be at the business office repository of the permittee or at an off-premises location of its choice (such location shall be the village, town, city orcounty clerk's office, the local library or other location as approved by the Department). In accordance with the RECORDING, REPORTING AND ADDITIONAL MONITORING REQUIREMENTS page of your permit, each DMR shall be maintained on record for a period of five years.

(f)

The permittee shall periodically inspect the outfall identification signs in order to ensure that they are maintained, are still visible and contain information that is current and factually correct.

SPDES PERMIT NUMBER NY 000 1015 Page 35 of 35 RECORDING, REPORTING AND ADDITIONAL MONITORING REQUIREMENTS a)

The permittee shall also refer to 6 NYCRR Part 750-1.2(a) and 750-2for additional information concerning monitoring and reporting requirements and conditions.

b)

The monitoring information required by this permit shall be summarized, signed and retained for a period of three years from the date of the sampling for subsequent inspection by the Department or its designated agent. Also, monitoring information required by this permit shall be summarized and reported by submitting; n (if box is checked) completed and signed Discharge Monitoring Report (DMR) forms for each I month reporting

[

period to the locations specified below. Blank forms are available at the Department's Albanyoffice listed below. The first reporting period begins on the effective date of this permit and the reports will be due no later than the 28th day of the month following the end of each reporting period.

F] (if box is checked) an annual report to the Regional Water Engineer at the address specified below. The annual report is due by February 1 and must summarize information for January to December of the previous year in a format acceptable to the Department.

'"](if box is checked) a monthly "Wastewater Facility Operation Report..." (form 92-15-7) to the:

[I" Regional Water Engineer and/or El County Health Department or Environmental Control Agency specified below Send the DMRs with original signatures to:

Send a copy of each DMR page to:

Department of Environmental Conservation Department of Environmental Conservation Regional Water Engineer, Region 7 Division of Water Bureau of Water Compliance Programs 615 Erie Boulevard - West 625 Broadway Syracuse, New York 13204-2400 Albany, New York i2233-3506 Phone: 315-426-7500 Phone: (518) 402-81.77 Send an additional coy of each DMR page to:

Oswego County Department of Health 70 Bunner Street Oswego, New York 13126 c)

Noncompliance with the provisions of this permit shall be reported to the Department as prescribed in 6 NYCRR Part 750-1.2(a) and 750-2.

d)

Monitoring must be conducted according to test procedures approved under 40 CFR Part 136, unless other test procedures have been specified in this permit.

e)

If the permittee monitors any pollutant more frequently than required by the permit, using test procedures approved under 40 CFR Part 136 or as specified in this permit, the results of this monitoring shall be.included in the calculations and recording of the data on the Discharge Monitoring Reports.

)

Calculation for all limitations which require averaging of measurements shall utilize an arithmetic mean unless otherwise specified in this permit.

g)

Unless otherwise specified, all information recorded on the Discharge Monitoring Report shall be based upon measurements and sampling carried out during the most recently completed reporting period.

h)

Any laboratory test or sample analysis required by this permit for which the State Commissioner of Health issues certificates of approval pursuant to section five hundred two of the Public Health Law shall be conducted by a laboratory which has been issued a certificate of approval. Inquiries regarding laboratory certification should be sent to the Environmental Laboratory Accreditation Program, New York State Health Department.Center for Laboratories and Research, Division of Environmental Sciences, The Nelson A. Rockefeller Empire State Plaza, Albany, New York 12201.