permit fact sheet general information · 6/5/1984 · notes prop comp mercury, total recoverable...
TRANSCRIPT
Page 1 of 21
Permit Fact Sheet
General Information
Permit Number: WI-0028541-09-0
Permittee Name: CITY OF WATERTOWN
Address: 800 Hoffman Dr
City/State/Zip: Watertown WI 53094
Discharge Location: West Bank 4,850 feet downstream of Hwy Bus. 26 bridge in the NE ¼ of SE ¼ of
Section 8, T8N, R15E
Receiving Water: Rock River (Middle Rock River Watershed, UR01 – Upper Rock River Basin) in
Jefferson County
StreamFlow (Q7,10): Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
7-Q10
(cfs) 45 56 109 278 109 48 30 22 20 21 45 47
7-Q2
(cfs) 169 184 440 819 365
18
0
10
9 86 77 102 193 184
Stream Classification: Warm Water Sport Fishery (WWSF), non-public water supply
Design Flow(s) Annual
Average
Design Flow(s)
Significant Industrial
Loading?
Yes, Waste Pak (Pepsi Co.), Johnsonville (Butcher Co.), Western Industries, Ad Tech,
Clasen Quality, Diversey
Operator at Proper Grade? Yes, required: Advanced – A1, B, C, D, P & SS. SS is required by the end if this
permit term.
Approved Pretreatment
Program?
June 5, 1984
Facility Description
The City of Watertown operates a recently upgraded (2002-2004) wastewater treatment facility serving a population of
23,655 designed to treat a daily flow of 5.2 MGD of domestic, commercial and industrial wastewater. The plant currently
receives approximately 3.2-3.5 MGD for treatment. The facility consists of parallel bar screens and grit removal, two
primary clarifiers followed by a splitter box to three activated sludge tanks with an anoxic selector in the front of the
basins. At the end of the tanks ferric chloride is added to bind up phosphorus and then the flow goes to two final clarifiers,
UV disinfection and step aeration prior to discharge to the Rock River. Waste sludge is co-settled in the primary clarifiers
and all sludge is pumped into anaerobic digesters. Digesters are heated to 95-98 degrees F and mixed with draft tube
mixers. Once processed, sludge is pumped to centrifuges that thicken the sludge to ~23-28% solids and then to sludge
storage and finally hauled and land applied to DNR-approved farm fields to the agronomic needs of the cover crop. Over
180 days of sludge storage is available. BLENDING: The permittee has requested blending approval as part of their
permit application. Based on an evaluation of their request and associated documentation, blending is approved per s. NR
210.12(2), Wis. Adm. Code.
The permittee has been found to be in substantial compliance with its current permit. Shaded cells below indicate changes.
Page 2 of 21
Sample Point Designation
Sample
Point
Number
Discharge Flow, Units, and
Averaging Period
Sample Point Location, WasteType/sample Contents and
Treatment Description (as applicable)
701 4.25 MGD (2019) Influent: 24-Hr flow proportional sampler located after raw influent
screening. Flow meter located after raw wastewater pumps.
001 4.12 MGD (2019) Effluent: 24-Hr flow proportional sampler located prior to UV
disinfection. Grab samples taken post aeration prior to discharge to
the Rock River.
002 N/A Representative samples of class B, anaerobically digested liquid
sludge shall be collected from the secondary digester, if this sludge
is land applied. If this sample point is activated, the sludge shall be
analyzed for List 2 parameters (Nutrients) just prior to land
application and DNR shall be notified prior to land application.
004 401 MT (2017-2019) Representative samples of class B, anaerobically digested cake
sludge shall be collected from the centrifuge.
102 <0.12 ng/L (2019) Collect the mercury field blank using sample handling procedures
specified in NR 106.145(9), Wisconsin Administrative Code.
103 4.25 MGD (2019) Sample point for reporting diverted flow from the primary clarifiers
during high flow events. Flow bypasses the aeration basins and final
clarifiers but receives disinfection prior to discharge. Department
approval for blending shall be obtained prior to use of this sample
point. Any flow diverted prior to blending approval shall be
considered to be a bypass, is prohibited, and should be reported to
the Department as such. The permittee shall notify the Department
when blending occurs. See Blending requirements in the Standard
Requirements section of the permit.
1 Influent - Proposed Monitoring
Sample Point Number: 701- INFLUENT
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Flow Rate MGD Daily Continuous
BOD5, Total mg/L 5/Week 24-Hr Flow
Prop Comp
Suspended Solids,
Total
mg/L 5/Week 24-Hr Flow
Prop Comp
Cadmium, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Page 3 of 21
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Chromium, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Copper, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Lead, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Nickel, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Zinc, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Mercury, Total
Recoverable
ng/L Quarterly 24-Hr Flow
Prop Comp
Changes from Previous Permit:
Flow frequency changed to ‘daily’ from ‘continuous’ for consistency and eDMR reporting purposes. Metals sampling
frequency changed to quarterly throughout the full permit term. Mercury influent sampling increased to monthly.
Explanation of Limits and Monitoring Requirements
BOD5 and Total Suspended Solids: Tracking of BOD5, and Suspended Solids are required for percent removal
requirements found in s. NR 210.05, Wis. Adm. Code and in the Standard Requirements section of the permit.
Metals: Quarterly metals sampling throughout the permit term is required for permittees with approved pretreatment
programs.
Mercury, Total Recoverable: Mercury monitoring is included in the proposed permit pursuant to s. NR 106.145, Wis.
Adm. Code. Required field blanks for Mercury monitoring per ss. NR 106.145(9) and (10), Wis. Adm. Code,
requirements. The permittee shall collect a mercury field blank for each set of mercury samples (a set of samples may
include a combination of influent, effluent or other samples all collected on the same day). The permittee shall report
results of influent and effluent samples and field blanks to the Department on Discharge Monitoring Reports.
2 Inplant - Proposed Monitoring and Limitations
Sample Point Number: 102- GEN PLANT (Hg blank)
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Mercury, Total
Recoverable
ng/L Quarterly Blank See Mercury Monitoring
section
Changes from Previous Permit:
No changes made.
Explanation of Limits and Monitoring Requirements
Page 4 of 21
Required field blanks for Mercury monitoring per ss. NR 106.145(9) and (10), Wis. Adm. Code, requirements. The
permittee shall collect a mercury field blank for each set of mercury samples (as set of samples may include a
combination of influent, effluent or other samples all collected on the same day). The permittee shall report results of
influent and effluent samples and field blanks to the Department on Discharge Monitoring Reports.
Sample Point Number: 103- BLENDING
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Flow Rate MGD Per
Occurrence
Continuous See Blending Flow permit
section.
Time hours Per
Occurrence
Calculated Report the total duration of
blending within a given day
(12:00 am - 11:59 pm) in
which blending occurs. See
Blending Flow permit
section.
Changes from Previous Permit:
The permittee requested blending as part of the permit application. Blending requirements including reporting
requirements added.
Explanation of Limits and Monitoring Requirements
Blending requires approval by the Department and reporting of flow rate and time per occurrence of blending. The
Approval for blending is required upon each permit reissuance. See Standard Requirements section of the permit for
additional requirements. Department has determined that blending as defined in s. NR 210.03 (2e), Wis. Adm. Code, may
occur at this sewage treatment facility.
3 Surface Water - Proposed Monitoring and Limitations
Sample Point Number: 001- EFFLUENT
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Flow Rate MGD Daily Continuous
BOD5, Total Monthly Avg 30 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective January through
May
BOD5, Total Monthly Avg 16 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective June
BOD5, Total Monthly Avg 12 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective July and October
BOD5, Total Monthly Avg 10 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective August and
September
Page 5 of 21
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
BOD5, Total Monthly Avg 25 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective November
BOD5, Total Monthly Avg 29 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective December
BOD5, Total Weekly Avg 31 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective January
BOD5, Total Weekly Avg 35 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective February
BOD5, Total Weekly Avg 45 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective March through
May
BOD5, Total Weekly Avg 16 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective June
BOD5, Total Weekly Avg 12 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective July and October
BOD5, Total Weekly Avg 10 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective August and
September
BOD5, Total Weekly Avg 25 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective November
BOD5, Total Weekly Avg 29 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective December
BOD5, Total Weekly Avg 1,400 lbs/day 5/Week Calculated Effective January
BOD5, Total Weekly Avg 1,500 lbs/day 5/Week Calculated Effective February
BOD5, Total Weekly Avg 690 lbs/day 5/Week Calculated Effective June
BOD5, Total Weekly Avg 530 lbs/day 5/Week Calculated Effective July and October
BOD5, Total Weekly Avg 450 lbs/day 5/Week Calculated Effective August
BOD5, Total Weekly Avg 440 lbs/day 5/Week Calculated Effective September
BOD5, Total Weekly Avg 1,100 lbs/day 5/Week Calculated Effective November
BOD5, Total Weekly Avg 1,300 lbs/day 5/Week Calculated Effective December
Suspended Solids,
Total
Monthly Avg 30 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective January through
May
Suspended Solids,
Total
Monthly Avg 16 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective June
Suspended Solids,
Total
Monthly Avg 12 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective July and October
Suspended Solids, Monthly Avg 10 mg/L 5/Week 24-Hr Flow Effective August and
Page 6 of 21
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Total Prop Comp September
Suspended Solids,
Total
Monthly Avg 25 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective November
Suspended Solids,
Total
Monthly Avg 29 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective December
Suspended Solids,
Total
Weekly Avg 31 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective January
Suspended Solids,
Total
Weekly Avg 35 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective February
Suspended Solids,
Total
Weekly Avg 45 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective March through
May
Suspended Solids,
Total
Weekly Avg 16 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective June
Suspended Solids,
Total
Weekly Avg 12 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective July and October
Suspended Solids,
Total
Weekly Avg 10 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective August and
September
Suspended Solids,
Total
Weekly Avg 25 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective November
Suspended Solids,
Total
Weekly Avg 29 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective December
Suspended Solids,
Total
Monthly Avg 1,270 lbs/day 5/Week Calculated Effective January, March,
and May
Suspended Solids,
Total
Monthly Avg 1,410 lbs/day 5/Week Calculated Effective February
Suspended Solids,
Total
Monthly Avg 1,310 lbs/day 5/Week Calculated Effective April
Suspended Solids,
Total
Monthly Avg 700 lbs/day 5/Week Calculated Effective June
Suspended Solids,
Total
Monthly Avg 510 lbs/day 5/Week Calculated Effective July and October
Suspended Solids,
Total
Monthly Avg 430 lbs/day 5/Week Calculated Effective August
Suspended Solids,
Total
Monthly Avg 440 lbs/day 5/Week Calculated Effective September
Suspended Solids, Monthly Avg 1,100 lbs/day 5/Week Calculated Effective November
Page 7 of 21
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Total
Suspended Solids,
Total
Monthly Avg 1,230 lbs/day 5/Week Calculated Effective December
Suspended Solids,
Total
Weekly Avg 1,400 lbs/day 5/Week Calculated Effective January
Suspended Solids,
Total
Weekly Avg 1,500 lbs/day 5/Week Calculated Effective February
Suspended Solids,
Total
Weekly Avg 2,270 lbs/day 5/Week Calculated Effective March and May
Suspended Solids,
Total
Weekly Avg 2,340 lbs/day 5/Week Calculated Effective April
Suspended Solids,
Total
Weekly Avg 690 lbs/day 5/Week Calculated Effective June
Suspended Solids,
Total
Weekly Avg 530 lbs/day 5/Week Calculated Effective July and October
Suspended Solids,
Total
Weekly Avg 450 lbs/day 5/Week Calculated Effective August
Suspended Solids,
Total
Weekly Avg 440 lbs/day 5/Week Calculated Effective September
Suspended Solids,
Total
Weekly Avg 1,100 lbs/day 5/Week Calculated Effective November
Suspended Solids,
Total
Weekly Avg 1,300 lbs/day 5/Week Calculated Effective December
Nitrogen, Ammonia
(NH3-N) Total
Daily Max 20 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective November
through March
Nitrogen, Ammonia
(NH3-N) Total
Weekly Avg 20 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective November
through March
Nitrogen, Ammonia
(NH3-N) Total
Weekly Avg 17 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective June
Nitrogen, Ammonia
(NH3-N) Total
Weekly Avg 9.0 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective July
Nitrogen, Ammonia
(NH3-N) Total
Weekly Avg 6.4 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective August
Nitrogen, Ammonia
(NH3-N) Total
Weekly Avg 8.9 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective September
Nitrogen, Ammonia Weekly Avg 13 mg/L 5/Week 24-Hr Flow Effective October
Page 8 of 21
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
(NH3-N) Total Prop Comp
Nitrogen, Ammonia
(NH3-N) Total
Monthly Avg 20 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective November
through March
Nitrogen, Ammonia
(NH3-N) Total
Monthly Avg 17 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective June
Nitrogen, Ammonia
(NH3-N) Total
Monthly Avg 9.0 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective July
Nitrogen, Ammonia
(NH3-N) Total
Monthly Avg 6.4 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective August
Nitrogen, Ammonia
(NH3-N) Total
Monthly Avg 8.9 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective September
Nitrogen, Ammonia
(NH3-N) Total
Monthly Avg 9.3 mg/L 5/Week 24-Hr Flow
Prop Comp
Effective October
Dissolved Oxygen Daily Min 6.0 mg/L Daily Grab
pH Field Daily Max 9.0 su Daily Grab
pH Field Daily Min 6.0 su Daily Grab
Fecal Coliform Geometric
Mean -
Monthly
400 #/100 ml 2/Week Grab Interim limit effective May
– September annually until
the final E. coli limit goes
into effect per the “Effluent
Limitations for E. coli”
Schedule.
E. coli #/100 ml 2/Week Grab Monitoring only May –
September annually until
the final limit goes into
effect per the “Effluent
Limitations for E. coli”
Schedule.
E. coli Geometric
Mean -
Monthly
126 #/100 ml 2/Week Grab Limit Effective May –
September annually per the
“Effluent Limitations for E.
coli” Schedule.
E. coli % Exceedance 10 Percent Monthly Calculated Limit Effective May –
September annually per the
“Effluent Limitations for E.
coli” Schedule. See the “E.
coli Percent Limit” section
below. Enter the result in
the DMR on the last day of
Page 9 of 21
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
the month.
Phosphorus, Total Monthly Avg 0.8 mg/L 5/Week 24-Hr Flow
Prop Comp
This is an interim MDV
limit effective upon
reissuance. See the
MDV/Phosphorus
subsections and phosphorus
schedules.
Phosphorus, Total Monthly Avg 13.7 lbs/day Monthly Calculated Effective January starting
in 2022
Phosphorus, Total Monthly Avg 19.5 lbs/day Monthly Calculated Effective February starting
in 2022
Phosphorus, Total Monthly Avg 18.4 lbs/day Monthly Calculated Effective March starting in
2022
Phosphorus, Total Monthly Avg 16.5 lbs/day Monthly Calculated Effective May starting in
2022
Phosphorus, Total Monthly Avg 17.7 lbs/day Monthly Calculated Effective July starting in
2021
Phosphorus, Total Monthly Avg 16.2 lbs/day Monthly Calculated Effective August starting in
2021
Phosphorus, Total Monthly Avg 14.8 lbs/day Monthly Calculated Effective September
starting in 2021
Phosphorus, Total Monthly Avg 12.3 lbs/day Monthly Calculated Effective October and
November starting in 2021
Phosphorus, Total Monthly Avg 11.9 lbs/day Monthly Calculated Effective December starting
in 2021
Phosphorus, Total lbs/month Monthly Calculated Report the total monthly
phosphorus discharged in
lbs/month on the last day of
the month on the DMR. See
Standard Requirements for
'Appropriate Formulas' to
calculate the Total Monthly
Discharge in lbs/month.
Phosphorus, Total lbs/yr Annual Calculated Report the sum of the total
monthly discharges (for the
months that the MDV is in
effect) for the calendar year
on the Annual report form.
Chloride mg/L 4/Month 24-Hr Flow Monitoring only in 2024
Page 10 of 21
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Prop Comp
Mercury, Total
Recoverable
Daily Max 3.7 ng/L Quarterly Grab This is an Alternative
Mercury Effluent Limit.
See Mercury section and
schedule.
Temperature
Maximum
3/Week Continuous
Acute WET TUa See Listed
Qtr(s)
24-Hr Flow
Prop Comp
See WET section.
Chronic WET Monthly Avg 1.5 TUc See Listed
Qtr(s)
24-Hr Flow
Prop Comp
See WET section.
Cadmium, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Chromium, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Copper, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Lead, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Nickel, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Zinc, Total
Recoverable
ug/L Quarterly 24-Hr Flow
Prop Comp
Nitrogen, Total
Kjeldahl
mg/L Quarterly 24-Hr Flow
Prop Comp
Nitrogen, Nitrite +
Nitrate Total
mg/L Quarterly 24-Hr Flow
Prop Comp
Nitrogen, Total mg/L Quarterly Calculated Total Nitrogen shall be
calculated as the sum of
reported values for Total
Kjeldahl Nitrogen and
Total Nitrite + Nitrate
Nitrogen.
Changes from Previous Permit
Page 11 of 21
Flow sample frequency changed to daily from continuous for eDMR reporting purposes. Weekly and monthly average
ammonia limits updated. Phosphorus limits updated including MDV requirements added. Temperature monitoring year
round upon reissuance per the approved DC study (this change was made and the permit re-public noticed). Nitrogen
series monitoring added. Metals sampling updated to quarterly throughout the full permit term.
The permittee has applied for a multi-discharger variance (MDV) for phosphorus for this permit term only for April and
June and the application has been approved by the Department. An MDV interim limit of 0.8 mg/L has been included.
The permittee is now required to report the total amount of phosphorus discharged in lbs/month and lbs/year. By March 1
of each year the permittee shall make a payment(s) to participating county(s) of $54.23 per pound of phosphorus
discharged during the previous year in excess of the target value of 0.2 mg/L. For all other months, TMDL phosphorus
limits are effective starting July 1, 2021.
Fecal coliform monitoring and limits have been replaced with Escherechia coli (E. coli) monitoring and limits. E. coli
monitoring is required at the permit effective date. An interim fecal coliform limit of 400 #/100 ml as a monthly geometric
mean will apply from the permit effective date through the end of a compliance schedule. At the end of the compliance
schedule, E. coli limits of 126 #/100 ml as a monthly geometric mean that may never be exceeded and 410 #/100 ml as a
daily maximum that may not be exceeded more than 10 percent of the time in any calendar month will apply.
Explanation of Limits and Monitoring Requirements Water Quality Based Limits and WET Requirements and Disinfection (if applicable)
Refer to the WQBEL memo for the detailed calculations, prepared by Sarah Luck dated September 20, 2019, WQBEL
addendum for temperature dated October 23, 2019 and the WQBEL addendum for E. coli limits dated May 1, 2020 used
for this reissuance.
BOD5, pH, DO, Fecal Coliform, and Total Suspended Solids – The categorical limitations for BOD5, TSS, pH and DO
are carried over into this permit. These limitations are not subject to change at this time because the receiving water
characteristics have not changed. On May 1, 2020 revisions to the bacteria surface water criteria became effective.
Therefore, this permit has been updated to include the existing fecal coliform limit as an interim limit along with E-coli
monitoring and a compliance schedule to meet required E. coli limits. The interim fecal coliform limit is effective until the
final E. coli limit becomes effective per the Schedule.
E. Coli & Fecal Coliform - Revisions to bacteria surface water quality criteria to protect recreational uses and
accompanying E. coli WPDES permit implementation procedures became effective May 1, 2020. See changes from
previous permit above and the e-coli WQBEL addendum for more information. The new rule requires that WPDES
permits for facilities with required disinfection include monitoring for E. coli while facilities are disinfecting during the
recreation period, and establish effluent limitations for E. coli established in s. NR 210.06 (2), Wis. Adm Code. The
administrative code rule changes included the following actions: revised the bacteria water quality criteria from fecal
coliform to E. coli to protect recreation in ch. NR 102, Wis. Adm. Code.; removed fecal coliform criteria for certain
individual waters from ch. NR 104, Wis. Adm. Code.; revised permit requirements for publicly and privately owned
sewage treatment works in ch. NR 210, Wis. Adm. Code.; and, updated approved analytical methods for bacteria in ch.
NR 219, Wis. Adm. Code.
Ammonia – Current acute and chronic ammonia toxicity criteria for the protection of aquatic life are included in Table 2C
and Table 4B of ch. NR 105, Wis. Adm. Code (effective March 1, 2004). Subchapter IV of ch. NR 106 establishes
procedures for calculating water quality-based effluent limitations (WQBELs) for ammonia (effective March 1, 2004).
Weekly average and monthly average ammonia limits are required in accordance with the federal regulation 40 CFR
122.45(d), limits in this permit are to be expressed as weekly average and monthly average limits whenever practicable.
See limit memo for month by month explanation of ammonia limits.
Page 12 of 21
Rock River Total Maximum Daily Load - The City of Watertown WWTP is in the Rock River Basin. A total
maximum daily load (TMDL) was developed for the Rock River Basin to determine the maximum amounts of phosphorus
and sediment that can be discharged to protect and improve water quality. The Rock River Basin’s TMDL was approved
by the Environmental Protection Agency (EPA) in September 2011. These final effluent limits were derived from and
comply with the applicable water quality criterion and are consistent with the assumptions and requirements of the EPA-
approved waste load allocation (WLA) for the Rock River. The entire report can be found at:
http://dnr.wi.gov/topic/TMDLs/RockRiver/Final_Rock_River_TMDL_Report_with_Tables.pdf. The proposed permit
includes limitations and requirements necessary to implement the recommendations of the TMDL. For specific limits see
below.
Phosphorus – Phosphorus rules became effective December 1, 2010 per NR 217, Wis. Adm. Code, that required the
permittee to comply with water quality based effluent limits (WQBELs) for total phosphorous. For this permit term, the
permittee has applied for the Multi-Discharger Variance (MDV) for phosphorus as provided for in s. 283.16, Wis. Stats.,
and approved by USEPA on February 6, 2017 until February 5, 2027. The permittee qualifies for the MDV in the months
of April and June for the TMDL derived limit because it is an existing source and a major facility upgrade is needed to
comply with the applicable phosphorus WQBELs, thereby creating a financial burden. The effluent limit for total
phosphorus is 0.8 mg/L as an average monthly limit and is effective upon reissuance. The limit was derived using DMR
data from October 2014 to April 2019. TMDL limits for January through March, May, and July through December are
effective starting June 2021.
Conditions of the MDV require the permittee to optimize phosphorus removal throughout the proposed permit term,
comply with interim limits and make annual payments to participating county(s) by March 1 of each year based on the
pounds of phosphorus discharged during the previous year in excess of the specified target value. The “price per pound”
value is $50.00 adjusted for CPI annually during the first quarter as defined by s. 283.16(8)(a)2, Wis. Stats and takes
effect for reissued permits with effective dates starting April 1. This may differ from the “price per pound” that is public
noticed; however, the “price per pound” is set upon reissuance and is applicable for the entire permit term. The
participating county(s) uses these payments to implement non-point source (agricultural and urban) phosphorus control
strategies at the watershed level.
Rock River TMDL Total Phosphorus - Mass limits were calculated to comply with the Rock River TMDL and were
derived consistent with the assumptions and requirements of the EPA-approved WLA for the Rock River. Limits for the
permit were determined using the code changes and the provisions of the TMDL. The final effluent mass limits for
phosphorus are expressed as monthly averages and is effective for all months starting July 1, 2021 (except April and June,
see MDV). The approved total phosphorus TMDL mass limits for this permittee are included in the following table below:
Month
Monthly Average
Total P Effluent Limit
(lbs/day)
Jan 13.7
Feb 19.5
March 18.4
April 18.3
May 16.5
June 17.6
July 17.7
Aug 16.2
Sept 14.8
Oct 12.3
Nov 12.3
Page 13 of 21
Month
Monthly Average
Total P Effluent Limit
(lbs/day)
Dec 11.9
Total Suspended Solids - Weekly average and monthly average mass limits for total suspended solids were required to
comply with the Rock River TMDL and were derived consistent with the assumptions and requirements of the EPA-
approved WLA for the Rock River. The current permit contains weekly TSS mass limits for the months of June through
February that are more stringent than the TMDL limits for those same months. Due to antidegradation rules (NR 207,
Wis. Adm. Code), these more stringent limits will be retained in the reissued permit in lieu of the weekly average TMDL
limits for the months of June through February. The calculated weekly average TSS TMDL limits for March through
April, and the monthly average TSS TMDL limits for January through December are retained. There are no changes
proposed in current concentration limits. These limits are in addition to the concentration limits for suspended solids in the
current permit, which vary from 10 mg/L to 30 mg/L as a monthly average and from 10 mg/L to 45 mg/L as a weekly
average. The approved total suspended solids TMDL limits for this permittee are included in the following table,
expressed as weekly average and monthly average effluents limits, and remain in effect except as superseded by more
stringent water quality based effluent limits:
Total Suspended Solids Effluent Limitations
Month
Monthly Average
TMDL TSS
Effluent Limit
(lbs/day)
Weekly Average
TMDL TSS
Effluent Limit
(lbs/day)
Weekly Average
TSS Effluent Limit
in Current Permit
(lbs/day)
Effective Weekly
Average TSS
Effluent Limit
(lbs/day)
Jan 1270 2270 1400 1400
Feb 1410 2500 1500 1500
March 1270 2270 -- 2270
April 1310 2340 -- 2340
May 1270 2270 -- 2270
June 700 1250 690 690
July 510 910 530 530
Aug 430 760 450 450
Sept 440 770 440 440
Oct 510 910 530 530
Nov 1100 1950 1100 1100
Dec 1230 2190 1300 1300
Chloride - When the representative data is compared to the calculated limits, the data shows there is no reasonable
potential for the permittee to exceed the calculated limits. Therefore, no chloride limits are included in the proposed
permit. However, the permittee shall monitor effluent chloride concentrations frequently enough to ensure adequate data
for permit reissuance.
Mercury – Watertown applied for and was granted an alternative mercury effluent limit of 3.7 ng/L for the current permit
term. Watertown implemented a mercury pollutant minimization program (PMP) during the current permit term and was
Page 14 of 21
successful at reducing mercury effluent concentrations. An analysis of mercury effluent data generated during the current
permit term (P99s) show that Watertown is still unable to consistently meet the wildlife water quality criterion of 1.3
ng/L. Watertown has applied for another variance from the mercury water quality standards, which requires EPA
approval. If granted, the mercury variance limit will remain as 3.7 ng/L as a daily maximum and continued
implementation of Watertown’s mercury PMP will be required. Mercury influent, effluent and sludge monitoring is
required along with the collection and analysis of at least one field blank shall be collected at each site for each day a
sample is collected. See the schedules section for the mercury schedule. Requirements for mercury are included in s. NR
106.145, Wis. Adm. Code.
Temperature: Requirements for Temperature are included in NR 102 Subchapter II Water Quality Standards for
Temperature and NR 106 Subchapter V Effluent Limitations for Temperature. Thermal discharges must meet the Public
Health criterion of 120 degrees F and the Fish & Aquatic Life criteria which are established to protect aquatic
communities from lethal and sub-lethal thermal effects. Final water quality based effluent limits for the month of October
was required per the WQBEL. The proposed permit was public noticed with a schedule for submittal of a DC study and
this limit to become effective during the permit term. The Department has since approved a DC study and therefore re-
public noticed the permit with removal of the temperature limits and schedule to submit the DC study. Monitoring 3/week
throughout the permit term is required and the DC study will need to be reevaluated at the time of the next permit
reissuance.
Whole Effluent Toxicity: Whole effluent toxicity (WET) testing requirements and limits (if applicable) are determined in
accordance with ss. NR 106.08 and NR 106.09 Wis. Adm. Code, as revised August 2016. (See the current version of the
Whole Effluent Toxicity Program Guidance Document and checklist and WET information, guidance and test methods at
http://dnr.wi.gov/topic/wastewater/wet.html). Annual WET testing in rotating quarters is required as listed in the permit.
Toxics – Metals monitoring throughout the permit term is required for all permittee’s with approved pretreatment
programs. Sampling is required quarterly year-round throughout the permit term.
Total Nitrogen Monitoring (NO2+NO3, TKN and Total N): The Department has included effluent monitoring for
Total Nitrogen in the permit through the authority under §§ 283.55(1)(e), Wis. Stats., which allows the department to
require the permittee to submit information necessary to identify the type and quantity of any pollutants discharged from
the point source, and through s. NR 200.065(1)(h), Wis. Adm. Code, which allows for this monitoring to be collected
during the permit term. Quarterly effluent monitoring for Total Nitrogen is included in the permit because of the potential
for higher nitrogen loading resulting from higher flows (major facilities), higher concentrations, or both. More
information on the justification to include total nitrogen monitoring in wastewater permits can be found in the “Guidance
for Total Nitrogen Monitoring in Wastewater Permits” dated October 1, 2019.
Page 15 of 21
4 Land Application - Proposed Monitoring and Limitations Municipal Sludge Description
Sample
Point
Sludge
Class (A or
B)
Sludge
Type
(Liquid or
Cake)
Pathogen
Reduction
Method
Vector
Attraction
Method
Reuse
Option
Amount
Reused/Dis
posed (Dry
Tons/Year)
002 B Liquid Fecal
Coliform &
Anaerobic
Digestion
Volatile
Solids
Reduction
Land
Application
Inactive
004 B Cake Fecal
Coliform &
Anaerobic
Digestion
Volatile
Solids
Reduction &
Incorporatio
n
Land
Application
401 MT
(2017-2019)
Does sludge management demonstrate compliance? Yes
Is additional sludge storage required? No
Is Radium-226 present in the water supply at a level greater than 2 pCi/liter? Yes
If yes, special monitoring and recycling conditions will be included in the permit to track any potential
problems in landapplying sludge from this facility
Is a priority pollutant scan required? Yes, see permit
Priority pollutant scans are required once every 10 years at facilities with design flows between 5 MGD
and 40 MGD, and once every 5 years if design flow is greater than 40 MGD.
Sample Point Number: 002- LIQUID SLUDGE and 004- CAKE SLUDGE
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Solids, Total Percent Quarterly Composite
Arsenic Dry Wt Ceiling 75 mg/kg Quarterly Composite
Arsenic Dry Wt High Quality 41 mg/kg Quarterly Composite
Cadmium Dry Wt Ceiling 85 mg/kg Quarterly Composite
Cadmium Dry Wt High Quality 39 mg/kg Quarterly Composite
Copper Dry Wt Ceiling 4,300 mg/kg Quarterly Composite
Copper Dry Wt High Quality 1,500 mg/kg Quarterly Composite
Lead Dry Wt Ceiling 840 mg/kg Quarterly Composite
Lead Dry Wt High Quality 300 mg/kg Quarterly Composite
Page 16 of 21
Monitoring Requirements and Limitations
Parameter Limit Type Limit and
Units
Sample
Frequency
Sample
Type
Notes
Mercury Dry Wt Ceiling 57 mg/kg Quarterly Composite
Mercury Dry Wt High Quality 17 mg/kg Quarterly Composite
Molybdenum Dry Wt Ceiling 75 mg/kg Quarterly Composite
Nickel Dry Wt Ceiling 420 mg/kg Quarterly Composite
Nickel Dry Wt High Quality 420 mg/kg Quarterly Composite
Selenium Dry Wt Ceiling 100 mg/kg Quarterly Composite
Selenium Dry Wt High Quality 100 mg/kg Quarterly Composite
Zinc Dry Wt Ceiling 7,500 mg/kg Quarterly Composite
Zinc Dry Wt High Quality 2,800 mg/kg Quarterly Composite
Nitrogen, Total
Kjeldahl
Percent Quarterly Composite
Nitrogen, Ammonium
(NH4-N) Total
Percent Quarterly Composite
Phosphorus, Total Percent Quarterly Composite
Phosphorus, Water
Extractable
% of Tot P Quarterly Composite
Potassium, Total
Recoverable
Percent Quarterly Composite
Radium 226 Dry Wt pCi/g Annual Composite
PCB Total Dry Wt Ceiling 50 mg/kg Once Composite Monitor for PCB's as part
of the priority pollutant
scan in 2022.
PCB Total Dry Wt High Quality 10 mg/kg Once Composite Monitor for PCB's as part
of the priority pollutant
scan in 2022.
Municipal Sludge
Priority Pollutant
Scan
Once Composite As specified in ch. NR
215.03 (1-4), Wis. Adm.
Code.
Changes from Previous Permit:
No changes made.
Explanation of Limits and Monitoring Requirements
Municipal sludge priority pollutant scan shall be completed in 2022 along with PCB testing. Requirements for land
application of municipal sludge are determined in accordance with ch. NR 204 Wis. Adm. Code. Ceiling and high quality
limits for metals in sludge are specified in s. NR 204.07(5), Wis. Adm. Code. Requirements for pathogens are specified
Page 17 of 21
in s. NR 204.07(6) and in s. NR 204.07 (7), Wis. Adm. Code for vector attraction requirements. Limitations for PCBs are
addressed in s. NR 204.07(3)(k), Wis. Adm. Code.
5 Schedules
5.1 Mercury Pollutant Minimization Program As a condition of the variance to the water quality based effluent limitation(s) for mercury granted in accordance with s.
NR 106.145(6), Wis. Adm. Code, the permittee shall perform the following actions.
Required Action Due Date
Annual Mercury Progress Reports: Submit an annual mercury progress report. The annual mercury
progress report shall:
Indicate which mercury pollutant minimization activities or activities outlined in the approved
Pollutant Minimization Plan have been implemented;
Include an analysis of trends in monthly and annual total effluent mercury concentrations based on
mercury sampling; and
Include an analysis of how influent and effluent mercury varies with time and with significant
loading of mercury such as loads from industries into the collection system.
The first annual mercury progress report is to be submitted by the Due Date.
01/31/2021
Annual Mercury Progress Report #2: Submit a mercury progress report as defined above. 01/31/2022
Annual Mercury Progress Report #3: Submit a mercury progress report as defined above. 01/31/2023
Annual Mercury Progress Report #4: Submit a mercury progress report as defined above. 01/31/2024
Final Mercury Report: Submit a final report documenting the success in reducing mercury
concentrations in the effluent, as well as the anticipated future reduction in mercury sources and
mercury effluent concentrations. The report shall summarize mercury pollutant minimization
activities that have been implemented during the current permit term and state which, if any, pollutant
minimization activities from the approved pollutant minimization plan were not pursued and why.
The report shall include an analysis of trends in monthly and annual total effluent mercury
concentrations based on mercury sampling during the current permit term. The report shall also
include an analysis of how influent and effluent mercury varies with time and with significant loading
of mercury such as loads from industries into the collection system.
If the permittee intends to reapply for a mercury variance per s. NR 106.145, Wis. Adm. Code, for the
reissued permit, a detailed pollutant minimization plan outlining the pollutant minimization activities
proposed for the upcoming permit term shall be submitted along with the final report.
01/31/2025
Annual Mercury Reports After Permit Expiration: In the event that this permit is not reissued on time,
the permittee shall continue to submit annual mercury reports each year covering pollutant
minimization activities implemented and mercury concentration trends.
Explanation of Schedule
Watertown has applied for a variance from the mercury water quality criterion for the protection of wildlife (1.3 ng/L). As
a condition of receiving a mercury variance, s. NR 106.145(7), Wis. Adm. Code, requires the permittee to continue to
develop and implement a Mercury Pollutant Minimization Program (PMP). The schedule requires the permittee to
implement the Mercury PMP and submit annual status reports on PMP activities. Annual status reports are required to be
submitted by January 31st of the following year, regardless of whether or not the permit expires without being reissued.
Page 18 of 21
5.2 Phosphorus Schedule - Optimization Plan The permittee is required to optimize performance to control phosphorus discharges per the following schedule.
Required Action Due Date
Optimization Plan: The permittee shall prepare an Optimization Plan and submit it for Department
approval. The plan shall include an evaluation of collected effluent data, possible source reduction
measures and operational improvements to optimize performance to control phosphorus discharges.
The plan shall contain a schedule for implementation of the measures and improvements. Once the
plan is approved by the Department, the permittee shall take the steps called for in the Optimization
Plan and follow the schedule of implementation as approved.
06/30/2021
Progress Report #1: Submit a progress report on optimizing removal of phosphorus. 06/30/2022
Progress Report #2: Submit a progress report on optimizing removal of phosphorus. 06/30/2023
Progress Report #3: Submit a progress report on optimizing removal of phosphorus. 06/30/2024
Progress Report #4: Submit a progress report on optimizing removal of phosphorus. 06/30/2025
Explanation of Schedule
Per s. 283.16(6)(a), Wis. Stats. the Department may include a requirement that the permittee optimize the performance of
a point source in controlling phosphorus discharges, which may be necessary to achieve compliance with multi-discharger
variance interim limits. This compliance schedule requires the permittee to continue to implement the optimization plan
that was approved during the previous permit term.
5.3 Phosphorus Payment per Pound to County The permittee is required to make annual payments for phosphorus reductions to the participating county or counties in
accordance with s. 283.16(8), Wis. Stats, and the following schedule. The price per pound will be set at the time of permit
reissuance and will apply for the duration of the permit.
Required Action Due Date
Annual Verification of Phosphorus Payment to County: The permittee shall make a total payment to
the participating county or counties approved by the Department by March 1 of each calendar year.
The amount due is equal to the following: (lbs of phosphorus discharged minus the permittee’s target
value) times $54.23 or $640,000, whichever is less. See the payment calculation steps in the Surface
Water section.
The permittee shall submit Form 3200-151 to the Department by March 1 of each calendar year
indicating total amount remitted to the participating counties to verify that the correct payment was
made. The first payment verification form is due by the specified Due Date.
Note: The applicable Target Value is the TMDL derived limit value as defined by s. 283.16(1)(h),
Wis. Stats. The "per pound" value is $50.00 adjusted for CPI.
03/01/2021
Annual Verification of Payment #2: Submit Form 3200-151 to the Department indicating total
amount remitted to the participating counties.
03/01/2022
Annual Verification of Payment #3: Submit Form 3200-151 to the Department indicating total
amount remitted to the participating counties.
03/01/2023
Annual Verification of Payment #4: Submit Form 3200-151 to the Department indicating total
amount remitted to the participating counties.
03/01/2024
Page 19 of 21
Annual Verification of Payment #5: Submit Form 3200-151 to the Department indicating total
amount remitted to the participating counties.
03/01/2025
Continued Coverage: If the permittee intends to seek a renewed variance, an application for the MDV
(Multi Discharger Variance) shall be submitted as part of the application for permit reissuance in
accordance with s. 283.16(4)(b), Wis. Stats.
Annual Verification of Payment After Permit Expiration: In the event that this permit is not reissued
prior to the expiration date, the permittee shall continue to submit Form 3200-151 to the Department
indicating total amount remitted to the participating counties by March 1 each year.
Explanation of Schedule
Subsection 283.16(6)(b), Wis. Stats., requires permittees that have received approval for the multi-discharger variance
(MDV) to implement a watershed project that is designed to reduce non-point sources of phosphorus within the HUC 8
watershed in which the permittee is located. The permittee has selected the “Payment to Counties” watershed option
described in s. 283.16(8), Wis. Stats. Under this option the permittee shall make annual payment(s) to participating
county(s) that are calculated based on the amount of phosphorus actually discharged during a calendar year in pounds per
year less the amount of phosphorus that would have been discharged had the permittee discharged phosphorus at a target
value concentration based on TMDL-derived limitations. The pounds of phosphorus discharged in excess of the target
value is multiplied by a per pound phosphorus charge that will equal $54.23 per pound. This schedule requires the
permittee to submit Form 3200-151 to the Department indicating the total amount remitted to the participating county(s).
5.4 Effluent Limitations for E. coli (Outfall 001) The permittee shall comply with surface water limitations for E. coli as specified. No later than 14 days following each
compliance date, the permittee shall notify the Department in writing of its compliance or noncompliance. If a submittal is
required, a timely submittal fulfills the notification requirement.
Required Action Due Date
Status Update: The permittee shall submit information within the discharge monitoring report
(DMR) comment section documenting the steps taken in preparation for properly monitoring and
testing for E. coli including, but not limited to, selected test method and location of sampling.
11/21/2020
Operational Evaluation Report: The permittee shall prepare and submit an Operational Evaluation
Report to the Department for review and approval. The report shall include an evaluation of collected
effluent data and proposed operational improvements that will optimize efficacy of disinfection at the
treatment plant during the period prior to complying with final E. coli limitations and, to the extent
possible, enable compliance with the final E. coli limitations. The report shall include a plan and
schedule for implementation of the operational improvements. These improvements shall occur as
soon as possible, but not later than April 30, 2022. The report shall state whether the operational
improvements are expected to result in compliance with the final E. coli limitations.
The permittee shall implement the operational improvements in accordance with the approved plan
and schedule specified in the Operational Evaluation Report and in no case later than April 30, 2022
If the Operational Evaluation Report concludes that the operational improvements are expected to
result in compliance with the final E. coli limitations, the permittee shall comply with the final E. coli
limitations by April 30, 2022 and the permittee is not required to comply with subsequent milestones
identified below in this compliance schedule (‘Submit Facility Plan’, 'Final Plans and Specifications',
'Treatment Plant Upgrade to Meet Limitations', ‘Construction Upgrade Progress Report’, 'Complete
Construction', 'Achieve Compliance').
FACILITY PLAN - If the Operational Evaluation Report concludes that operational improvements
10/31/2021
Page 20 of 21
alone are not expected to result in compliance with the final E. coli limitations, the permittee shall
initiate development of a facility plan for meeting final E. coli limitations and comply with the
remaining required actions in this schedule of compliance.
If the Department disagrees with the conclusion of the report, and determines that the permittee can
achieve final E. coli limitations using the existing treatment system with only operational
improvements, the Department may reopen and modify the permit to include an implementation
schedule for achieving the final E. coli limitations sooner than April 30, 2025.
Submit Facility Plan: If the Operational Evaluation Report concluded that the permittee cannot
achieve final E. coli limitations with operational improvements alone, the permittee shall submit a
Facility Plan per s. NR 110.09, Wis. Adm. Code. The permittee may submit an abbreviated facility
plan if the Department determines that the modifications are minor.
04/30/2022
Final Plans and Specifications: The permittee shall submit final construction plans to the
Department for approval pursuant to ch. NR 108, Wis. Adm. Code, specifying treatment plant
upgrades that must be constructed to achieve compliance with final E. coli limitations and a schedule
for completing construction of the upgrades by the complete construction date specified below.
03/31/2023
Treatment Plant Upgrade to Meet Limitations: The permittee shall initiate bidding, procurement,
and/or construction of the project. The permittee shall obtain approval of the final construction plans
and schedule from the Department pursuant to s. 281.41. Stats., prior to initiating activities defined as
construction under ch. NR 108, Wis. Adm. Code. Upon approval of the final construction plans and
schedule by the Department pursuant to s. 281.41, Stats., the permittee shall construct the treatment
plant upgrades in accordance with the approved plans and specifications.
09/30/2023
Construction Upgrade Progress Report: The permittee shall submit a progress report on
construction upgrades.
09/30/2024
Complete Construction: The permittee shall complete construction of wastewater treatment system
upgrades.
03/31/2025
Achieve Compliance: The permittee shall achieve compliance with final E. coli limitations. 04/30/2025
Explanation of E. coli Schedule
A compliance schedule is included in the permit to provide time for the permittee to investigate options for meeting new
effluent E. coli water quality-based effluent limits while coming into compliance with the limits as soon as reasonably
possible.
Special Reporting Requirements None
Other Comments: None
Attachments: Substantial Compliance Determination – 5/8/19
Water Quality Based Effluent Limits, with Map(s) – 9/20/19
WQBEL Addendum E. coli – 5/1/2020
Public Notice
MDV Application – 4/2/19
MDV Checklist – 4/29/19
Page 21 of 21
MDV Conditional Approval – 5/8/19
Mercury Variance documents
Additional Attachment at Re-Public Notice:
DC study approval letter – 6/9/2020
Proposed Expiration Date: September 30, 2025
Justification Of Any Waivers From Permit Application Requirements None
Prepared By: Jennifer Jerich, Wastewater Specialist
Date: 1/30/2020
Revision date post fact check: 4/3/2020; revisions to the fecal coliform and E. coli requirements and editorial changes
made.
Revisions at re-public notice: 6/22/2020; Temperature limits and schedules removed.
Revision date post public notice & hearing: