HomeMy WebLinkAboutIndustrial Wastewater Discharge Permit Renewal - Honeywell International, Inc.BOARD OF PUBLIC WORKS
AGENDA ITEM REVIEW REQUEST FORM
Date 8/30/2021
Name Serena Lozano-Shane Department UTILITIES
BPW Date 9/14/2021 Phone Extension 5798
Review and Approval Required Prior to Submittal to Board Diversity Compliance
and Inclusion Officer Officer Name BPW Attorney Attorney Name
Dept. Attorney Attorney Name
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x Other: Honeywell Groundwater Remediation Industrial Discharge Permit Modification
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New Completion Date:
June 18th, 2021
Mr. Marcus Wolfram
Plant Director
Honeywell Aerospace
3520 Westmoor Street
South Bend, IN 46628
Re: Industrial Remediation Discharge Permit
Dear Mr. Wolfram:
Honeywell Remediation Site’s Revised Draft Industrial Wastewater Discharge Permit is enclosed. Please
review and submit any comments before July 19th, 2021. This permit is for the facility located at:
3520 Westmoor Street
South Bend, IN 46628
If you have any questions, please feel free to contact me at 574-235-5798 or via email at sshane@southbendin.gov
Sincerely,
Serena Shane
Pretreatment Manager
City of South Bend
3113 Riverside Drive
South Bend, IN 46628
Please note the following changes to Honeywell’s permit:
• Soil Vapor Extrusion System Spent Scrubber water (outfall 003C00175) has been added as a permitted waste stream.
• The required frequency at Outfall 003C00175 for all analytics except pH and Oil and Grease Total, TPH has been stated as
Once per Permit Cycle (please see Board of Public Works signature page for dates of permit term). Please see Part II of the
permit.
• Required Certified Operator has been upgraded to Class B due to the pH neutralization system for Outfall 003C00175.
Please see permit section Part III (F).
• Mercury shall be collected as a grab sample.
Honeywell’s permit includes the following requirements found within the discharge permit:
• Honeywell’s Authorized Representative shall sign with the certification statement (found in Part III (A) (4)) all reports
including but not limited to Periodic Compliance Reports (PCR), Flow Measurement Plans, corrective actions in response to
permit violations, and any correspondence relating to compliance with this industrial discharge permit.
• Please review Section Part IV (B) (15), which clarifies the requirements concerning the Authorized Representative.
• Please see Part III (I) (3) for more details, which clarifies required documentation necessary to appoint an Authorized
Representative responsible to receive correspondence from the City.
• Honeywell shall, within 90 days of receipt of this discharge permit, submit a Flow Measurement Plan, or report as to whether
the existing plan is still being implemented, with the certification statement signed by an Authorized Representative. Please
see Part III (E) and (H).
• When collecting composite samples, samples must be obtained over a 24 hour period or for the duration of discharge within
the 24 hour sampling period including, if applicable, multiple batches.
• Samples shall be obtained through a flow-proportional sampling technique. If Honeywell can demonstrate that time-
proportional sampling is as representative as flow-proportional sampling, then a time-proportional sample may be collected.
If Honeywell chooses to demonstrate that time-proportional sampling is accurate they must do so within 120 days of the
effective date of this permit or they shall commence flow-proportional sampling at that time. Please see Part II (B) (1) of
your wastewater discharge permit for details.
• Transfer of Ownership: If permittee plans to change ownership or transfer of this wastewater discharge permit, permittee
shall give the Control Authority at least 30 days notice with written certification by the new owner or operator. See Part IV
(B)(11) of permit for more details.
• If sampling performed by Honeywell indicates a violation, Honeywell shall notify the City orally within 24 hours of becoming
aware of the violation, submit a written follow up report within five (5) days, and resample and submit the results of the
analysis to the Control Authority within thirty (30) days after becoming aware of the violation. See Part III (D) of permit for
more details on permit violations.
• The permittee shall notify the Control Authority of any significant changes to the permittee’s operations or system which
might alter the nature, quality, or volume of its wastewater at least thirty (30) days before the change. See Part III (G)
• In the event that an oral notification is required due to a spill or slug to the sewer, or other emergency, the permittee shall
immediately call 574-277-8515 and dial zero (0) to reach an operator followed by a written verification within five (5) days
of the incident. See Part III (I) of your permit for details.
PERMIT BRIEFING MEMO
Honeywell International – Groundwater Remediation
1. Facility Description
Honeywell International, Inc. installed the Naphtha Recovery Well System in 1978 and VOC Recovery Well
system in 1988. The Naphtha Recovery Well system was used to remove free product from the top of the
water table until no further free product was detected in 2003. The well systems currently act as water-table
depression wells to control groundwater from migrating off-site. In 2021 a catalytic-oxidation soil vapor
extraction (SVE) treatment system was installed to remove volatile organic compounds from the soil above
the water table. VOCs are destroyed in the catalytic oxidation process and any remaining VOCS are sent
through an exhaust stack. Water cycles through a scrubber in the exhaust stack to reduce HCL emissions.
2. Discharge description:
Currently, the Naphtha Recovery Well system consists of three (3) recovery wells: E3A, RWB-16, and RWB-
23 with a total average discharge rate of 0.086 mgd.
Maximum allowable discharge of 0.173 mgd.
The VOC Recovery Well system consists of four (4) recovery wells: EW-1R, EW-2, EW-3 and EW-5R
with a total average discharge flow of 0.069 mgd.
Maximum allowable discharge of 0.154 mgd.
Soil Vapor Extraction system
Spent Scrubber water is stored onsite inside two frac tanks, totaling 40,000 gallon capacity, until batch
discharge occurs. Discharge will be on an as needed basis, with a 7,000 -gallon capacity tanker truck.
Estimated Discharge Rate: Average 500 gallons per minute, Maximum 1,000 gallons per minute.
3. Sample Site Description
The Naphtha System and VOC System maps indicating the well locations can be found in the Honeywell
Groundwater Remediation permit application dated January 14, 2020.
Naphtha Recovery Well System:
Monitoring is conducted at each of the three (3) operating Naphtha Recovery Wells. Samples are collected
from spigots at each well. Each discharge point has a totalizer meter to record flows.
VOC Recovery Well System:
Monitoring is conducted at each of the four (4) operating VOC Recovery Wells. Samples are collected from
spigots at each well. Each discharge point has a totalizer meter to record flows.
Soil Vapor Extraction System
Monitoring is done at the sample port installed along the discharge pipe at the base of the frac tank. A Flow
Meter is located in the discharging pipe off the frac tank. The Sampling Port is after the Flow Meter on the
discharge pipe. Wastewater from the frac tanks will be transferred with a dedicated tanker truck to
Discharge Location # 003C00175, near Plant 14.
4. Wastewater Treatment
pH Neutralization is achieved by adding Sodium Hydroxide to the spent scrubber water.
5. Classification
Honeywell International – Groundwater Remediation is classified as an Industrial User (IU) as defined in
the South Bend Municipal Code and is classified as an F category discharger since it is a remediation site.
6. Calculation of Limits
Permit limits for Honeywell International – Groundwater Remediation’s discharge are from the South Bend
Municipal Code.
7. Monitoring Frequency
Monitoring frequencies are based South Bend’s US EPA approved industrial pretreatment program
monitoring plan.
8. Industrial Operator Certification Requirement
Operator Certification Requirement: B
Industrial operator certification requirements are based on the criteria listed in Indiana Administrative Code,
Title 327, 5-22-5.
Permit Drafted by:
City of South Bend
Industrial Pretreatment Group
February 2020
City of South Bend
Department of Public Works
Industrial Pretreatment Program
Remediation Site – Permit No. 004
In accordance with all the terms of Chapter 17 of the City of South Bend’s Municipal Code, and with any applicable
provisions of federal or state law and regulations, permission is hereby granted to:
Honeywell International, Inc.
3502 Westmoor Street
South Bend, IN 46628
for the contribution of wastewater into the City of South Bend Publicly Owned Treatment Works.
This permit is granted in accordance with the application filed on 14 January, 2020.
Effective on: 14 April, 2020
Expires on the: 13 April, 2025
Revised on: August 10, 2021
Any violation of the terms and conditions of this permit shall be deemed a violation of the City of South Bend Municipal
Code and will subject the permittee to the sanctions set out in section 17-11 through 17-13 of the Municipal Code.
The permittee shall file an application for a renewal permit, a minimum of 90 days prior to the expiration date.
CONTENTS
PART I
PART II
PART III
PART IV
ATTACHMENT 1
ATTACHMENT 2
ATTACHMENT 3
ATTACHMENT 4
EFFLUENT LIMITATIONS
MONITORING REQUIREMENTS
REPORTING REQUIREMENTS
STANDARD CONDITIONS
DEFINITIONS
ENFORCEMENT RESPONSE PLAN
APPEALS PROCEDURE
ORGANIC PRIORITY POLLUTANT
LIST
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 1 of 39
Facility Description
Honeywell International, Inc. Naphtha Recovery Well system and VOC Recovery Well system currently act as
water-table depression wells to control groundwater from migrating off-site. Catalytic-oxidation Soil Vapor
Extraction (SVE) treatment system was installed to remove volatile organic compounds from the soil above the water table.
There are four operating VOC Recovery Wells (EW-1-R, EW-2, EW-3, and EW-5-R), three operating Naphtha
Recovery Wells (E3A, RWB16, and RWB23), and one discharge point for spent scrubber water from the Soil
Vapor Extraction System (003C00175).
PART I – EFFLUENT LIMITATION
Sample Port and Collection Location
1.Sample monitoring is located at the Naphtha Recovery Well system and VOC Recovery Well
system. Samples are collected from spigots at each well. For the Soil Vapor Extrusion system
sample monitoring is done at the sampling port after the Flow Meter on the discharge pipe of the
frac tank. Wastewater from the frac tanks will be transferred with a dedicated tanker truck to
Discharge Location # 003C00175, near Plant 14.
2.Sample Sites EW-1-R, EW-2, EW-3, EW-5-R, E3A, RWB16, RWB23, and 003C00175 shall not
exceed the following effluent limitation: Any discharge of water or waste having a pH lower than
6.0 S.U. or a pH higher than 11.0 S.U. is prohibited. In addition, the permittee’s wastewater
discharge shall not exceed the following effluent limitations:
Parameter Daily Maximum Limit (mg/L)
Arsenic (mg/L) Report
B-TEX (ug/L)Report
Cadmium (mg/L) Report
Chromium (mg/L) Report
Copper (mg/L) Report
Cyanide (mg/L) Report
Closed Cup Flashpoint (Degrees F) * <140 Degrees Fahrenheit Prohibited
Lead (mg/L) Report
Mercury (mg/L) Report
Nickel (mg/L) Report
Oil and Grease – Total (mg/l) 300
Oil and Grease TPH (mg/L) 100
Organic Priority Pollutants (ug/L) Report
Silver (mg/L) Report
Zinc (mg/L) Report
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 2 of 39
a.Daily Maximum Limit means the maximum allowable discharge limit of a pollutant during
a calendar day or any 24-hour period that represents a calendar day. Where Daily Maximum
Limits are expressed in units of mass, the daily discharge is the total mass discharged over
the course of the day. Where Daily Maximum Limits are expressed in terms of a
concentration, the daily discharge is the arithmetic average measurement of the pollutant
concentration derived from all measurements taken that day. In the case of samples
collected by the grab method, the daily maximum shall be applied as an Instantaneous
Maximum Allowable Discharge Limit or as an Instantaneous Minimum Allowable
Discharge Limit as follows:
i.Instantaneous Maximum Allowable Discharge Limit – shall mean the
maximum concentration or loading of a pollutant allowed to be
discharged at any time, determined from analysis of any discrete or
composite sample collected, independent of the industrial flow rate and
the duration of the sampling event.
ii.Instantaneous Minimum Allowable Discharge Limit – shall mean the
minimum concentration of a pollutant allowed to be discharged at any
time, determined from analysis of any discrete or composite sample
collected, independent of the industrial flow rate and the duration of the
sampling event. The lower pH limit is applied as an Instantaneous
Minimum Allowable Discharge Limit.
b.Monthly Average Limit means the maximum allowable average of daily discharges over a
calendar month, calculated as the sum of the concentrations of all daily discharges measured
during a calendar month divided by the number of daily discharges measured that month.
c.Prohibited: No permittee shall introduce or cause to be introduced certain pollutants,
substances, or wastewater into any public sewers, directly or indirectly into the POTW
including, but not limited to gasoline, benzene, naphtha, fuel oil or other pollutants which
create a fire or explosive hazard to the City’s sewer system or POTW.
d.* Closed Cup Flashpoint: this parameter must be monitored using the test methods
specified in 40 CFR 261.21
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 3 of 39
PART II - MONITORING REQUIRMENTS
Monitoring Frequency
1.The following parameters shall be monitored at the frequency and with the sampling type stated
below. All measurements, tests, and analyses of the characteristics of water and wastes to which
reference is made in this permit shall be conducted using the methods and procedures approved
in 40 CFR 136 and amendments thereto, unless otherwise specified in an applicable Categorical
Pretreatment Standard.
The following parameters shall be monitored at sample sites EW-1-R, EW-2, EW-3, EW-5-R, E3A, RWB16, and
RWB23 with the methods and at the frequency stated below:
Parameter Sampling Frequency Sampling Type
Flow, Monthly (gal) Monthly Continuously
B-TEX (ug/L)SemiAnnual Grab
Total Oil and Grease (mg/L) SemiAnnual Grab
Oil and Grease TPH (mg/L) SemiAnnual Grab
pH (SU) SemiAnnual Grab
Ammonia, nitrogen (mg/L) Once per First Year of Permit Cycle* Composite
Arsenic (mg/L) Once per First Year of Permit Cycle* Composite
BOD5 (mg/L) Once per First Year of Permit Cycle* Composite
Cadmium (mg/L) Once per First Year of Permit Cycle* Composite
Chromium (mg/L) Once per First Year of Permit Cycle* Composite
Closed Cup Flashpoint (Degrees F) Once per First Year of Permit Cycle* Grab
Copper (mg/L) Once per First Year of Permit Cycle* Composite
Cyanide (mg/L) Once per First Year of Permit Cycle* Grab
Lead (mg/L) Once per First Year of Permit Cycle* Composite
Mercury (mg/L) Once per First Year of Permit Cycle* Grab
Nickel (mg/L) Once per First Year of Permit Cycle* Composite
Organic Priority Pollutants (ug/L) Once per First Year of Permit Cycle* Grab
Phosphorus (mg/L) Once per First Year of Permit Cycle* Composite
Silver (mg/L) Once per First Year of Permit Cycle* Composite
TSS (mg/L) Once per First Year of Permit Cycle* Composite
Zinc (mg/L) Once per First Year of Permit Cycle* Composite
See Flow Measurement Requirements referenced in Part III - Reporting Requirements.
*Once per First Year Permit Cycle: Parameters with this requirement must be monitored within the first year (12
months) of each permit cycle. Please see Board of Public Works signature page for dates of permit term.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 4 of 39
The following parameters shall be monitored at sample site 003C00175 with the methods and at the frequency stated
below:
Parameter Sampling Frequency Sampling Type
Flow, Monthly (gal) Monthly Continuously
Total Oil and Grease (mg/L) SemiAnnual Grab
Oil and Grease TPH (mg/L) SemiAnnual Grab
pH (SU) SemiAnnual Grab
Ammonia, nitrogen (mg/L) Once per Permit Cycle Composite
Arsenic (mg/L) Once per Permit Cycle Composite
BOD5 (mg/L) Once per Permit Cycle Composite
Cadmium (mg/L) Once per Permit Cycle Composite
Chromium (mg/L) Once per Permit Cycle Composite
Closed Cup Flashpoint (Degrees F) Once per Permit Cycle Grab
Copper (mg/L) Once per Permit Cycle Composite
Cyanide (mg/L) Once per Permit Cycle Grab
Lead (mg/L) Once per Permit Cycle Composite
Mercury (mg/L) Once per Permit Cycle Grab
Nickel (mg/L) Once per Permit Cycle Composite
Organic Priority Pollutants (ug/L) Once per Permit Cycle Grab
Phosphorus (mg/L) Once per Permit Cycle Composite
Silver (mg/L) Once per Permit Cycle Composite
TSS (mg/L) Once per Permit Cycle Composite
Zinc (mg/L) Once per Permit Cycle Composite
A. Monitoring Definitions
1. Composite – Samples are obtained through flow-proportional sampling technique over a 24-hour
period or for the duration of discharge within the 24-hour sampling period, including multiple
batches of wastewater. If the permittee demonstrates that time-proportional sampling is accurate
or as representative as flow-proportional sampling, then a time-proportional sample may be
collected.
a. If the permittee chooses to demonstrate that time-proportional sampling is accurate or as
representative as flow-proportional sampling, the permittee must submit a request, which
includes the certification statement found in Part III (A) (4) signed by the Authorized
Representative [see Part IV (B) (15)], within 120 days of the effective date of this permit
or they shall commence flow-proportional sampling at that time. Request to conduct
time-proportional sampling is subject to the Control Authority approval.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 5 of 39
2. Grab Sample – A single sample collected from a wastestream without regard to the flow in the
wastestream and over a period of time not to exceed fifteen (15) minutes and taken at a time
representative of normal discharge.
3. Continuously – The permittee shall monitor the discharge flow continuously and submit totalized
daily flows with the Periodic Compliance Report (PCR). Each PCR shall include all flow
measurements for the entire monitoring period covered in the report. This flow information shall
be in addition to the flow data collected during sampling which shall be measured from the start
of the sampling event to the end of the sampling event.
4. Daily monitoring frequency requires sampling to be conducted one (1) time in each calendar
day. (Report due on the 20th of the following month)
5. Weekly monitoring frequency requires sampling to be conducted one (1) time in each calendar
week (Sunday to Saturday). (Report due on the 20th of the following month)
6. Monthly monitoring frequency requires sampling to be conducted a minimum of one (1) time
per calendar month. (Report due on the 20th of the following month)
7. Semiannual monitoring frequency requires sampling to be conducted a minimum of one (1) time
per semiannual period. (1st Semiannual Period: January to June [Report due on the 20th of July].
2nd Semiannual Period: July to December [Report due on the 20th of January])
8. Quarterly monitoring frequency requires sampling to be conducted a minimum of one (1) time
per calendar quarter. (1st Quarterly Period: January to March [Report due on the 20th of April].
2nd Quarterly Period: April to June [Report due on the 20th of July]. 3rd Quarterly Period: July
to September [Report due on the 20th of October]. 4th Quarterly Period: October to December
[Report due on the 20th of January])
9. The following conventional pollutants shall incur a surcharge in excess of the stated limitations
below, as stated in Section 17-23(b) of the City of South Bend’s Municipal Code.
Surcharge for ammonia (NH3-N) >25 mg/L
Surcharge for BOD5 >250 mg/L
Surcharge for phosphorus >10 mg/L
Surcharge for Total Suspended Solids (TSS) >250 mg/L
B. Representative Sampling
1. Sampling shall be carried out by customarily accepted methods to reflect the effect of
constituents upon the sewage works and to determine the existence of hazards to life, limb and
property.
2. All wastewater samples must be representative of the permittee’s discharge.
3. Wastewater monitoring and flow measurement facilities shall be properly operated, kept clean,
and maintained in good working order at all times.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 6 of 39
a. The failure of a permittee to keep its monitoring facility in good working order shall not
be grounds for the permittee to claim that sample results are unrepresentative of its
discharge.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 7 of 39
PART III- REPORTING REQUIREMENTS
A. Monitoring Reports
1. Monitoring results obtained shall be summarized and reported on an Industrial User Periodic
Compliance Report (PCR). The PCRs are due on the twentieth (20th) day of the month following
the required monitoring time frame.
2.The PCR shall indicate the nature and concentration of all pollutants in the effluent for which
sampling and analysis were performed during the monitoring time frame preceding the
submission of each report, including measured flows. The PCRs shall also include all supporting
documentation necessary to demonstrate compliance.
3.All reports, including but not limited to PCRs, the Flow Measurement Plan, the Slug Control Plan,
and corrective actions in response to permit violations, shall include the following certification
statement signed by an Authorized Representative. See Part IV (B)(15) of this permit for
requirements concerning the Authorized Representative.
“I certify under penalty of law that this document and all attachments were
prepared under my direction or supervision in accordance with a system
designed to assure that qualified personnel properly gather and evaluate the
information submitted. Based on my inquiry of the person or persons who
manage the system, or those persons directly responsible for gathering the
information, the information submitted is to the best of my knowledge and belief,
true, accurate, and complete. I am aware that there are significant penalties for
submitting false information, including the possibility of fine and imprisonment
for knowing violations.”
a. If the designation of an Authorized Representative is no longer accurate because a
different individual or position has responsibility for the overall operation of the facility
or overall responsibility for environmental matters for the company, a new written
authorization must be submitted to the Director prior to or together with any reports to
be signed by the Authorized Representative. Please see Part IV B. 15. of this permit for
more information on designating a new Authorized Representative.
B. Additional Sampling
1. If the permittee monitors their wastewater discharge for any pollutant more frequently than
required by this permit, using test procedures in 40 CFR 136 or amendments thereto or otherwise
approved by U.S EPA or as specified in the permit, the results of such monitoring shall be
included in any calculations of actual daily maximum or monthly average pollutant discharge,
and results shall be reported in the specific time frame report submitted to the Control Authority.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 8 of 39
C. Notification of Batch or Infrequent Discharge
1. Within 30 days of the effective date of this permit, the permittee shall commence to notify the City of
South Bend via e-mail twenty-four (24) hours in advance of all batch or infrequent discharges to the
City’s sewer so that during this time compliance monitoring may be conducted. The subject line shall
include the words “discharge notification” followed by the outfall number, anticipated time of discharge,
and the anticipated volume of discharge. The permittee may request a modification of notification
requirements. All requests for modification of notification requirements are subject to approval by the
City of South Bend. The notification shall be made via e-mail to Pretreatment@SouthBendIN.Gov.
D. Noncompliance Notification and Re-Sampling
1. The permittee shall notify the Control Authority immediately of discharges that may cause
problems to the POTW, including any slugload or accidental discharge.
2. If sampling performed by the permittee indicates a violation, the permittee shall:
a. notify the Control Authority orally within twenty-four (24) hours of becoming aware of
the violation and;
b. submit a written follow up report within five (5) days of becoming aware of the violation,
which shall include a description of the violation, the date and time the violation
occurred, and plan for investigating the violation, and;
c. resample and submit the results of that analysis to the Control Authority within thirty
(30) days after becoming aware of the violation.
3. The permittee shall notify the Control Authority of any other noncompliance with this permit,
not described in D(1) and D(2) above, in writing within five (5) days of becoming aware of the
noncompliance.
E. Accidental Discharge/Slug Discharge Control
An accidental Discharge/Slug Discharge control plan is not required for Honeywell Groundwater
Remediation.
F. Certified Operator Requirement:
1. As required by Section 17-10 (o)(4)(b) of the South Bend Municipal Code:
Honeywell International, Inc.
3502 Westmoor Street
South Bend, IN 46628
(Hereafter “permittee”) shall be required to have a Certified Industrial Wastewater Operator of the
State of Indiana with the minimum classification listed below, sign all periodic compliance reports,
90 day compliance status reports, and all compliance schedule reports, indicating whether
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 9 of 39
Pretreatment Standards are being met on a consistent basis, and if not whether additional operation
and maintenance and/or additional pretreatment is required to meet the Pretreatment Standards and
Requirements.
The Certified Operator shall sign one of the following statements:
“Pretreatment Standards and Requirements are being met on a consistent basis.”
Or
“Pretreatment Standards and Requirements are not being met on a consistent basis.
Additional operation and maintenance and/or additional pretreatment is required to meet
the Pretreatment Standards and Requirements.”
Industrial Certified Operator Classification: B
2.This permit holder shall have a certified operator, with the minimum classification listed above,
sign all periodic compliance reports, 90-day compliance status reports, and all compliance
schedule reports.
3.If a certified operator is not signing permittee’s user reports, a $500.00 fine will be assessed
followed by a $500.00 fine for every user report submitted, until the certified operator
requirement is met.
4.If laboratory analytical data was not reported on the PCR, the requirement for the PCR to be signed
by a Certified Industrial Wastewater Operator is not required, unless otherwise indicated by the
Director.
G. Significant Change in Discharge / or Production
1.The permittee shall notify the Control Authority of any significant changes to the permittee’s
operations or system which might alter the nature, quality, or volume of its wastewater at least
thirty (30) days before the change.
2.For permittees subject to categorical production-based mass standards, average rates of production
shall be reported in the months of July and January. If at any time the permittee becomes aware
that the average production rate has changed or will change by twenty (20) percent or more, the
permittee shall notify the Control Authority regarding the change.
a. Any permittee operating under a permit incorporating equivalent mass or concentration
limits calculated from a Production-Based Standard shall notify the Director within two
(2) business days after the permittee has a reasonable basis to know that the production
level will significantly change within the next calendar month. Any permittee not
notifying the Control Authority of such anticipated change will be required to meet the
mass or concentration limit in its permit that were based on the original estimate of the
long-term average production rate.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 10 of 39
H. Flow Measurement Devices 1.The permittee shall submit a Flow Measurement Plan (FMP) within 90 days of the issuance of this
permit or report as to whether the existing plan is still being implemented. The FMP shall
describe, at a minimum, how the permittee will measure and record water and wastewater flow
in their facility, including how wastewater discharged to the sewer will be measured, and shall
include the certification statement found in Part III (A) (4) signed by the Authorized Representative [see
Part IV (B) (15)].
2.When internal process flow measurement is requested by the Director, the FMP shall also describe how
the flow of any internal processes will be measured. The FMP shall be subject to review by the
Control Authority.
3.The permittee shall measure and report the wastewater discharge flow for the duration of each
sampling event. Totalized daily flows shall also be submitted with the Periodic Compliance
Report (PCR). For batch discharges, the permittee shall report the date and the volume of each
and every batch discharge. Each PCR shall include all flow measurements for the entire
monitoring period covered in the report.
4.The permittee shall calibrate any flow measurement device as needed, but no less than once
annually. The calibration shall be performed by a qualified individual, with the appropriate
equipment, and by a method acceptable to the Control Authority. The permittee shall submit all
records of calibration to the Control Authority.
5.Spare level sensing and totalizing/recording instrumentation, and sampling repair parts shall be
available for immediate installation upon discovery that flow measurement devices are not
operating properly, or as described in the FMP.
6.The permittee shall not, at any time, remove, alter, or change any of the flow measurement devices
described in the FMP. Any proposed change to the FMP shall be submitted to the Control
Authority for approval. If the permittee is unable to measure flow as described in the FMP, the
permittee shall immediately notify the Control Authority.
I. Reporting Information and Correspondence with the Permittee
1.Unless otherwise provided in this permit, all correspondence related to this wastewater discharge
permit shall be sent to the Control Authority at this address:
City of South Bend
Division of Environmental Services
Industrial Pretreatment Group
3113 Riverside Dr.
South Bend IN 46628
2.In the event that an oral notification is required due to a spill or slug to the sewer, or other
emergency, the permittee shall call 574-277-8515 and dial zero (0) to reach an operator.
3.All correspondence from the Control Authority to the permittee regarding compliance with this
permit will be directed to the Authorized Representative identified in the application in Question
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 11 of 39
A.3. The permittee shall be responsible for all requirements and information in correspondence
directed to the attention of this designated individual, including but not limited to due dates.
a. Should the permittee wish to change the Authorized Representative responsible to
receive correspondence from the Control Authority a written designation must be
submitted to the Control Authority indicating the name of the new Authorized
Representative designated to receive compliance correspondence, their position in the
company, a statement that they meet the requirements in Part IV (B) (15) of this permit,
complete contact information, and an effective date of this designation.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 12 of 39
PART IV – STANDARD CONDITIONS
A. Prohibited Discharges
1. General prohibitions. No permittee shall introduce or cause to be introduced into the POTW
any pollutant or wastewater which causes Pass Through or Interference.
2. Specific prohibitions. No permittee shall introduce or cause to be introduced certain
pollutants, substances, or wastewater into any public sewers or directly or indirectly into the
POTW. Those pollutants, substances or wastewater prohibited by this subsection shall not
be processed or stored in such a manner that they could be discharged to the POTW. The
following described pollutants are expressly prohibited:
a. Any gasoline, benzene, naphtha, fuel oil or other pollutants which create a fire or
explosive hazard to the POTW, including, but not limited to, wastestreams with a
closed-cup flashpoint of less than one hundred forty (140) degrees Fahrenheit (sixty
(60) degrees Celsius) using the test methods specified in 40 CFR 261.21.
b. Any wastewater containing toxic pollutants in sufficient quantity, either singly or by
interaction with other pollutants, to injure or interfere with any wastewater treatment
process, constitute a hazard to humans or animals, create a toxic effect in the receiving
waters of the wastewater works, or to exceed the limitations set forth in the applicable
Federal Categorical Pretreatment Standards or other pretreatment standards or
regulation issued by the EPA or the IDEM. Toxic pollutants are identified pursuant
to Section 307(a) of the Federal Water Pollution Control Act, as amended.
c. Solid or viscous substances in quantities or of such size capable of causing obstruction
to the flow in sewers, or other interference with the proper operation of the sewage
works such as, but not limited to ashes, cinders, sand, mud, straw, shavings, metal,
glass, rags, feathers, tar, plastics, wood, unground garbage, whole blood, paunch
manure, hair and fleshings, entrails, paper, dishes, cups, milk containers, etc., either
whole or ground by garbage grinders.
d. Any pollutant, including oxygen-demanding pollutants (BOD, etc.), released in a
discharge at a flow rate and/or pollutant concentration which, either singly or by
interaction with other pollutants, will cause interference with the POTW.
e. Wastewater or any liquid having a temperature greater than one hundred fifty (150)
degrees Fahrenheit (sixty-five (65) degrees Celsius), or which will inhibit biological
activity in the treatment plant resulting in interference, but in no case wastewater or
liquid which causes the temperature at the introduction into the treatment plant to
exceed one hundred four (104) degrees Fahrenheit (forty (40) degrees Celsius).
f. Trucked or hauled pollutants, except at discharge points designated by the Director.
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g. Any pollutant that results in the presence of toxic gases, vapors, or fumes within the
POTW in a quantity that may cause acute worker health and safety problems.
h. Any radioactive wastes or isotopes of such half-life or concentration as may exceed
limits established by the Board in compliance with applicable State or Federal
regulations.
i. Any water or waste containing Total Oil and Grease (biodegradable animal and
vegetable fats, oil, waxes and greases and non-biodegradable hydrocarbon oils and
greases), whether emulsified or not, in excess of three hundred (300) mg/L, Total Oil
and Grease. The hydrocarbon portion of the Total Oil and Grease concentration may
not exceed one hundred (100) mg/L. Proper testing procedures shall be outlined for
each permittee. No permittee shall introduce or cause to be introduced petroleum oil,
non-biodegradable cutting oil, or products of mineral oil origin, in amounts that will
cause Pass Through or Interference.
j. Any garbage that has not been properly shredded. The installation and operation of
any garbage grinder equipped with a motor of three-fourths-horsepower (0.76 hp
metric) or greater shall be subject to the review and approval of the Board.
k. Any waters or wastes containing strong acid iron pickling wastes or concentrated
plating solutions whether neutralized or not.
l. Any waters or wastes containing iron, chromium, copper, zinc and similar
objectionable or toxic substances; or wastes exerting an excessive chlorine
requirement, to such degree that any such material received in the composite sewage
at the sewage treatment works exceeds the limits established by the Director for such
materials.
m. Any waters or wastes containing phenols or other taste- or odor-producing substances,
in such concentrations exceeding limits which may be established by the Board as
necessary, after treatment of the composite sewage, to meet the requirement of the
State, Federal or other public agencies of jurisdiction for such discharge to the
receiving waters.
n. Any waters or wastes having a pH lower than 6.0, any waters or wastes having a pH
in excess of 11.0, or having any corrosive property capable of causing damage or
hazard to structures, equipment, or personnel of the publicly owned treatment works
(POTW), or that interferes with any treatment process.
o. Noxious or malodorous liquids, gases, solids, or other wastewater which, either singly
or by interaction with other wastes, are sufficient to create a public nuisance or a
hazard to life, or to prevent entry into the sewers for maintenance or repair.
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p. Sludges, screenings, or other residues from the pretreatment of industrial wastes.
q. Medical Wastes, except as specifically authorized by the Director.
r. Wastewater causing, alone or in conjunction with other sources, the POTW’s effluent
to fail a toxicity test.
s. Materials which exert or cause:
i. Unusual concentrations of inert suspended solids (S.S.) (such as, but not limited
to, Fullers earth, lime slurries and lime residues) or of dissolved solids (such as,
but not limited to, sodium chloride and sodium sulfate).
ii. Excessive discoloration (such as, but not limited to, dye wastes and vegetable
tanning solutions).
iii. Unusual S.S., CBOD, BOD, ammonia-nitrogen, phosphorus, or chlorine
requirements in such quantities as to constitute a significant load on the sewage
treatment works.
iv. Unusual volume of flow or concentration of wastes constituting "slugs," as
defined herein.
t. Waters or wastes containing substances which are not amenable to treatment or
reduction by the sewage treatment processes employed, or are amenable to treatment
only to such degree that the sewage treatment plant effluent will be compromised.
u. It shall be unlawful for any permittee to place, deposit, permit to be deposited, or
discharged in any manner whatsoever, any substance into a sewer at a point different
than the proposed sewer connection to the sanitary sewer system.
3. Dilution Prohibition. No permittee shall ever increase the use of process water, or in any
way attempt to dilute a discharge as a partial or complete substitute for adequate treatment
to achieve compliance with a discharge limitation unless expressly authorized by an
applicable Pretreatment Standard or Requirement. The Director may impose mass
limitations on permittees who are using dilution to meet applicable Pretreatment Standards
or Requirements or in other cases when the imposition of mass limitations is appropriate.
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4. Right of Revision. The City reserves the right to establish by ordinance or in individual
wastewater discharge permits, more stringent standards or requirements on discharges to the
POTW consistent with the purpose of the Pretreatment Program.
B. General Pretreatment Requirements
1. Power and Authority of Inspectors
a. The Director, Inspector and other duly authorized employees of the City bearing
proper credentials and identification shall be permitted to enter all properties for the
purpose of inspection, observation, measurement, sampling, and testing in accordance
with the provisions of the City of South Bend’s Municipal Code. The Director or his
representative shall have no authority to inquire into any processes including
metallurgical, chemical, oil, refining, ceramic, paper or other industries that do not
have a direct bearing on the kind and source of discharge to the sewers or waterways
of facilities for waste treatment.
b. While performing the necessary work on private properties, the Director or duly
authorized employees of the City shall observe all safety rules applicable to the
premises established by the company and the company shall be held harmless for
injury or death to the City employees and the City shall indemnify the company
against loss or damage to its property by City employees and against liability claims
and demands for personal injury or property damage asserted against the company
and growing out of the gauging and sampling operation, except as such may be caused
by the negligence or failure of the company to maintain safe conditions in their
facility.
c. The Director and other duly authorized employees of the City bearing proper
credential and identification shall be permitted to enter all private properties through
which the City holds a duly negotiated easement for the purpose of, but not limited to,
inspection, observation, measurement, sampling, repair and maintenance of any
portion of the sewage works lying within said easement. All entry and subsequent
work on said easement shall be done in full accordance with the terms of the duly
negotiated easement pertaining to the private property involved.
2. Facilities Operation
a. The permittee shall at all times maintain in good working order and operate as
efficiently as possible, all pretreatment or control facilities or systems installed or used
by the permittee to achieve compliance with the terms and conditions of this permit.
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3. Bypassing
a. The permittee may allow any bypass (i.e., an intentional diversion of any wastestream
from any portion of the permittee’s treatment facility) to occur that does not cause any
Pretreatment Standards or Requirements to be violated, provided that the bypass is for
maintenance essential to assure efficient operation of the facility.
b. Any other bypass is prohibited except:
i. where it would be unavoidable to prevent loss of life, personal injury or severe
property damage. Severe property damage means substantial physical damage
to property, damage to the treatment facilities which causes them to become
inoperable or substantial and permanent loss of natural resources which can
reasonably be expected to occur in the absence of a bypass. Severe property
damage does not mean economic loss caused by delays in production.
ii. where there was no feasible alternative to the bypass, such as the use of auxiliary
treatment facilities, retention of untreated wastes, or maintenance during normal
periods of equipment downtime (this condition is not satisfied if, in the exercise
of reasonable engineering judgment, adequate back-up equipment should have
been installed to prevent a bypass during normal periods of equipment
downtime or preventative maintenance); and
iii. where the permittee has submitted notice to the control authority as required
below.
c. If the permittee knows in advance of the need to bypass, the permittee shall provide
verbal notice to the Control Authority, if possible, at least ten (10) days before the
date of bypass. In the event of an unanticipated bypass, the permittee shall notify the
Control Authority of any bypass that violates any Pretreatment Standard or
Requirement within twenty-four (24) hours of becoming aware of the bypass. Within
five (5) days of becoming aware of the bypass, the permittee must submit a written
report to the Director, unless waived by the Director, containing;
i. a description of the bypass and its cause;
ii. the duration of the bypass, including exact dates and times, and if the bypass
has not been corrected, how long the bypass is expected to continue; and
iii. steps taken or planned to reduce, eliminate, and prevent reoccurrence of the
bypass.
4. Duty to Mitigate
a. The permittee shall take all reasonable steps to minimize any adverse impact to the
POTW resulting from noncompliance with any effluent limitations specified in this
permit, including such accelerated or additional monitoring necessary to determine
the nature and impact of the non-compliant discharge.
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5. Upset Provision
a. Upset means an exceptional incident in which there is unintended and temporary
noncompliance with categorical Pretreatment Standards because of factors beyond the
reasonable control of the permittee. An upset does not include noncompliance to the
extent caused by operational error, improperly designed treatment facilities,
inadequate treatment facilities, lack of preventative maintenance, or careless or
improper operation.
b. An upset shall constitute an affirmative defense to an action brought for
noncompliance with categorical Pretreatment Standards if the requirements below are
met.
c. A permittee who wishes to establish the affirmative defense of upset shall
demonstrate, through properly signed contemporaneous operating log, or other
relevant evidence that:
i. an upset occurred and the permittee can identify the cause(s) of the upset
ii. the facility was at the time being operated in a prudent workman-like manner
and in compliance with applicable operation and maintenance procedures; and
iii. the permittee has submitted the following information to the Director within
twenty-four (24) hours of becoming aware of the upset (if this information is
provided orally, a written submission must be submitted within five (5) days):
a. a description of the discharge and cause of noncompliance;
b. the period of noncompliance, including exact dates and times, or, if
not corrected, the anticipated time the noncompliance is expected to
continue; and
c. the steps being taken and/or planned to reduce, eliminate, and prevent
recurrence of the noncompliance.
d. In any enforcement proceeding, the permittee seeking to establish the occurrence of
an upset shall have the burden of proof.
e. The permittee shall have the opportunity for a judicial determination on any claim of
upset only in an enforcement action brought for noncompliance with categorical
Pretreatment Standards.
f. The permittee shall control production of all discharges to the extent necessary to
maintain compliance with categorical Pretreatment Standards upon reduction, loss, or
failure of its treatment facility until the facility is restored or an alternative method of
treatment is provided. This requirement applies in the situation where, among other
things, the primary source of power of the treatment facility is reduced, lost, or fails.
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6. Administrative Enforcement
a. Any permittee found in violation of any applicable local, state, federal law, City of
South Bend Municipal Code Chapter 17, or any conditions within this permit will be
subject to Administrative Enforcement Action in accordance with the Enforcement
Response Plan (ERP) provided in Attachment 2 to this permit.
7. Penalties for False Reporting
a. Any person who knowingly makes any false statement, representation or certification
in any application, record, report, plan or other document filed or required to be
maintained pursuant to this permit, or who falsifies, tampers with, or knowingly
renders inaccurate any monitoring device or method required under this permit, shall
be subject to administrative fines of not more than $2500 per day per violation and/or
civil litigation and/or fines and imprisonment upon criminal conviction.
8. Penalties for Violation of Pretreatment Standards
a. Any permittee found in violation of Pretreatment Standards and Requirements (40
CFR 403), the City of South Bend Municipal Code, or this industrial wastewater
discharge permit issued by the City of South Bend and any applicable compliance
schedules, shall be subject to administrative fines of not more than $2500 per day per
violation and/or civil litigation and/or fines and imprisonment upon criminal
conviction.
9. Revocation of Permit
a. The Director may revoke an individual wastewater discharge permit for good cause,
which shall be subject to appeal under Article 2, Chapter 17, Subsection 17-11(c) of
the South Bend Municipal Code, but the effectiveness of revocation shall not be stayed
pending administrative appeal. Reasons for permit revocation by the Director include,
but are not limited to the following:
i. Failure to notify the Director of significant changes to the wastewater prior to
the changed discharge;
ii. Failure to provide prior notification to the Director of changed conditions
pursuant to Article 2, Chapter 17, Subsection17-10(o)(5);
iii. Misrepresentation or failure to fully disclose all relevant facts in the wastewater
discharge permit application;
iv. Falsifying periodic compliance reports and certification statements;
v. Tampering with monitoring equipment;
vi. Refusing to allow the Director timely access to the facility premises and records;
vii. Failure to meet effluent limitations;
viii. Failure to pay fines;
ix. Failure to pay sewer charges;
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 19 of 39
x. Failure to meet compliance schedules;
xi. Failure to complete a wastewater discharge survey or the wastewater discharge
permit application;
xii. Failure to provide advance notice of the transfer of business ownership of a
permitted facility; or
xiii. Violation of any Pretreatment Standard or Requirement, or any terms of this
permit or Chapter 17 of the City of South Bend’s Municipal Code.
10. Confidentiality
a. Information and data on a permittee obtained from reports, surveys, wastewater
discharge permit applications, individual wastewater discharge permits and
monitoring programs, and from the Director’s inspection and sampling activities, shall
be available to the public without restriction, unless the permittee specifically
requests, and demonstrates, to the satisfaction of the Director, that the release of such
information would divulge information, processes, or methods of production entitled
to protection as trade secrets under the Indiana Access to Public Records Act (IC 5-
14-3-4(A)(4)). Any such request must be asserted at the time of submission of the
information or data by stamping the words “confidential business information” on
each page containing such information. When requested and demonstrated by the
permittee furnishing a report that such information should be held confidential, the
portions of a report which might disclose trade secrets or secret processes shall not be
made available for inspection by the public, but shall be made available immediately
upon request to governmental agencies for uses related to the NPDES program or
pretreatment program, and in enforcement proceedings involving the person
furnishing the report.
b. Wastewater constituents and characteristics and other effluent data, as defined at 40
CFR 2.302 shall not be recognized as confidential information and shall be available
to the public without restriction.
c. All other information which is submitted to the State or Board of Public Works shall
be available to the public at least to the extent provided by 40 CFR 2.302.
11. Transfer of Ownership or Control
a. This permit may be transferred to a new owner or operator only if the permittee gives
at least thirty (30) days advance notice to the Director and the Director approves the
individual wastewater discharge permit transfer. The notice to the Director must
include a written certification by the new owner or operator which:
i. Identifies the new owner or operator, including address and telephone
number;
ii. Identifies the Authorized Representative for the new owner or operator in
accordance with Part IV (B)(15) of this permit, including telephone number
and email address;
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iii. States that the new owner and/or operator has no immediate intent to change
the facility’s operations and processes;
iv. Identifies the specific date on which the transfer is to occur; and
v. Acknowledges full responsibility for complying with the existing individual
wastewater discharge permit.
b. Failure to provide advance notice of a transfer renders this permit void as of the date
of transfer.
12. Reopening Clause
a. This permit shall be modified, or alternatively, revoked and reissued, to comply with
any applicable effluent limitation or standard issued or approved under section 307(b)
of the Clean Water Act if the effluent limitation or standard so issued or approved:
i. Contains different conditions or is otherwise more stringent than any effluent
limitation in the permit; or
ii. Controls any pollutant not limited in the permit.
b. The permit, as modified or reissued under this paragraph, shall also contain any other
requirements of the Clean Water Act when applicable.
13. Records Retention
a. Permittees shall retain, and make available for inspection and copying, all records of
information obtained pursuant to any monitoring activities required by this permit,
any additional records of information obtained pursuant to monitoring activities
undertaken by the permittee independent of such requirements, and documentation
associated with Best Management Practices established under Section 17-8 of the
South Bend Municipal Code. Records shall include the date, exact place, method, and
time of sampling, and the name of the person(s) taking the samples; the dates analyses
were performed; who performed the analyses; the analytical techniques or methods
used; any information used to demonstrate that the analysis was performed in
accordance with methods approved in 40 CFR Part 136; and the results of such
analyses. These records shall remain available for a period of at least three (3) years.
This period shall be automatically extended for the duration of any litigation
concerning the permittee or the City, or where the permittee has been specifically
notified of a longer retention period by the Director.
14. Federal and State Pretreatment Requirements
a. Compliance with this wastewater discharge permit does not relieve the permittee of
responsibility for compliance with all applicable Federal and State Pretreatment
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Standards, including those which become effective during the term of this wastewater
discharge permit.
15. Authorized Representatives
a. The permittee shall be represented by an Authorized Representative and/or Duly
Authorized Representative.
i. The Authorized Representative or Duly Authorized Representative of the
permittee shall be:
a. If the Permittee is a corporation:
i. The president, secretary, treasurer, or a vice-president of the
corporation in charge of a principal business function, or any
other person who performs similar policy or decision-making
functions for the corporation; or
ii. The manager of one (1) or more manufacturing, production,
or operating facilities, provided the manager is authorized to
make management decisions that govern the operation of the
regulated facility including having the explicit or implicit
duty of making major capital investment recommendations,
and initiate and direct other comprehensive measures to
assure long-term environmental compliance with
environmental laws and regulations; can ensure that the
necessary systems are established or actions taken to gather
complete and accurate information for individual wastewater
discharge permit requirements; and where authority to sign
documents has been assigned or delegated to the manager in
accordance with corporate procedures.
b. If the permittee is a partnership or sole proprietorship: A general
partner or proprietor, respectively.
c. If the permittee is a Federal, State, or local government facility: A
director or highest official appointed or designated to oversee the
operation and performance of the activities of the government
facility, or their designee.
ii. The individuals described in paragraphs (a) through (c) above, may designate
a Duly Authorized Representative if the authorization is made in writing by
the individual described in (a) through (c) above, the authorization specifies
either an individual or a position having responsibility for the overall
operation of the facility from which the Industrial Discharge originates, such
as the position of plant manager, operator of a well, or well field
superintendant, or a position of equivalent responsibility, or having overall
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responsibility for environmental matters for the company, and the written
authorization is submitted to the Director.
iii. Should the permittee wish to change the Authorized Representative
responsible to receive correspondence from the Control Authority a
written designation must be submitted to the Control Authority
indicating the name of the new Authorized Representative designated
to receive compliance correspondence, their position in the company,
a statement that they meet the requirements in Part IV (B) (15) of this
permit, complete contact information, and an effective date of this
designation.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 23 of 39
ATTACHMENT 1:
Definitions
As used in this Industrial Discharge Permit:
Board: shall mean the City of South Bend acting through its Board of Public Works or duly authorized officials
or board acting in its behalf.
Calendar day: shall mean any 24-hour period that represents a calendar day for the purposes of sampling.
Certified Operator: shall mean a person certified by the state of Indiana to sign all user reports indicating
whether pretreatment standards are being met on a consistent basis, and if not whether additional operation
and maintenance and/or additional pretreatment is required to meet the Pretreatment Standards and
Requirements.
Director: Director means the Director of Utilities of the City of South Bend, Indiana, or the Director's
authorized deputy, agent or representative.
Control Authority or Industrial Pretreatment Group: shall mean the Bureau of Wastewater Division of
Environmental Services located at: 3113 Riverside Drive, South Bend, IN 46628.
Industrial wastes: means any solid, liquid or gaseous substances or form of energy discharged, permitted to
flow or escape from an industrial, manufacturing, commercial or business process or from the development,
recovery or processing of any natural resource carried on by a permittee or a person, and shall further mean
any nondomestic waste to a City sewer system.
Slug (or slug load): shall mean any discharge at a flow rate or concentration which could cause a violation of
the prohibited discharge standards set forth in section 17-8 of the City of South Bend Municipal Code, herein,
or any discharge of a non-routine, episodic nature, including, but not limited to, an accidental spill or non-
customary batch discharge.
Batch or Infrequent Discharge: shall refer to the discharge produced from a treatment or manufacturing process
in which a tank or reactor is filled, the wastewater (or solution) is held or a chemical solution is prepared, and
the tank is emptied, resulting in a discrete discharge to the sanitary sewer. Batch or infrequent discharge shall
also mean wastewater produced due to cleaning, stabilizing, or conditioning chemical solutions for use in
industrial manufacturing and treatment processes as well as the discharge from processes that are not in
operation on a regular basis, and from occasional maintenance activities.
Batch Composite Sampling: A batch composite sample shall consist of at least three (3) grab samples that are
collected throughout the duration of the discharge from the batch tank. At a minimum, the samples shall be
collected at the beginning, the middle, and the end of the discharge from each batch tank.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 24 of 39
ATTACHMENT 2:
ENFORCEMENT
RESPONSE
PLAN
CITY OF SOUTH BEND
INDUSTRIAL PRETREATMENT
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 25 of 39
Enforcement Response Plan Outline
I. Management Plan
A. Permit Application and Classification
B. Permitting
C. Monitoring
D. Field Inspection and Analysis
E. Compliance Decisions and Enforcement
II. Enforcement Procedures
III. Significant Non-Compliance
IV. Enforcement Response Examples
A. Sampling, Monitoring, Reporting
B. Compliance Schedules
C. Discharge Limitations
D. Non-Compliance Detected Through Inspections or Field Investigations
E. Other Non-Compliance
V. Timeframes for Responses
This Enforcement Response Plan was written with the guidance of U.S. EPA document PB90-185083,
Guidance for Developing Control Authority Enforcement Response Plans. Office of Water Enforcement and
Permits. U.S. Environmental Protection Agency, Washington, DC 20460 1989.
Revised 4/29/2011
Approved by US EPA in a letter dated July 21, 2011
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 26 of 39
This document will describe the enforcement procedures that are used in controlling industrial discharges to
the South Bend Publicly Owned Treatment Works.
I. Management Plan
The pretreatment program for the City of South Bend is administered by the Division of Environmental
Services. The responsibilities of the pretreatment program are:
1. Collect and verify industrial discharge data through laboratory analyses.
2. Make recommendations to the Board of Public Works concerning the issuance of discharge
permits.
3. Review user discharge monitoring reports.
4. Determine the status of user compliance with federal, state, and local regulations.
5. Write federal, state, and local mandated pretreatment reports.
6. Make recommendations for enforcement actions.
Enforcement procedures such as letters of violation, administrative fines, and administrative orders are issued
by a Pretreatment Coordinator. Pretreatment Coordinators recommend more serious enforcement responses
to the Environmental Compliance Manager and the Director of Environmental Services. Severe violations
are reported to the Board of Public Works with recommendations from the Director of Environmental
Services.
The following information describes in more detail the management procedures which are used in
enforcement of the program.
A. Permit Application and Classification
Lists of Industrial Users (IUs) are evaluated based on operations performed, water usage and discharge, and
chemical inventory, among other factors. Industries identified as belonging to one of the following groups
are issued industrial wastewater discharge permits, and categorized as either an Industrial User, or a
Significant Industrial User.
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1. IUs subject to federal categorical standards – SIU
2. IUs that have process wastewater discharge exceeding 25,000 gallons per day – SIU
3. IUs that contribute process wastewater discharge exceeding 5% of the POTW’s dry weather
hydraulic or organic loading capacity.- SIU
4. IUs that have a reasonable potential to adversely affect POTW workers, the POTW itself, and the
receiving stream. – SIU
5. IUs that have non-significant waste water discharge streams may or may not be issued an industrial
wastewater discharge permit. – IU/SIU
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B. Permitting
The pretreatment staff assesses the information supplied by a user in its permit application. Discharge
parameters to be monitored are set based on application information and local requirements, and limits are
set in accordance with local, state, and federal regulations. The industrial wastewater discharge permit is
issued by the South Bend Board of Public Works.
C. Monitoring
Monitoring consists primarily of the following items:
1. Periodic Compliance Reports submitted to the City of South Bend pretreatment staff as described in
each permitted user’s discharge permit.
2. Control Authority (City of South Bend) monitoring including site inspections, and sample collection
and analysis. Monitoring events will be conducted both with and without announcement.
3. Compliance report submitted to the City of South Bend pretreatment staff as described in each
permitted user’s discharge permit.
4. Other information and reports that convey compliance status which the City of South Bend
pretreatment staff may request.
D. Field Inspection and Analysis
The City of South Bend pretreatment staff collect wastewater discharge samples and inspect industries as
required to determine compliance, and to obtain verification of self monitoring data.
E. Compliance Decisions and Enforcement
Industries found to be out of compliance with federal state, or local requirements are subject to the conditions
found in Chapter 17 of the South Bend Municipal Code, described in this Enforcement Response Plan.
Informal enforcement actions, letters of violation, administrative fines, and administrative orders are
conducted by a Pretreatment Coordinator or by the Director of Environmental Services, depending on the
severity of the noncompliance. Enforcement actions which require legal action, criminal investigation, sewer
ban, or other penalties may be made by the Board of Public Works upon the recommendation of the Director
of Environmental Services.
II. Enforcement Response
Violations and discrepancies that have been identified are evaluated by the City of South Bend pretreatment
staff as to the type of enforcement response necessary. In order to ensure equitable treatment of violators and
provide a stronger basis for selection of appropriate responses to violations, the following Enforcement
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Response Plan should normally be followed. However, certain circumstances or types of violations may
require responses that deviate from this plan.
The Enforcement Response Plan indicates the type of noncompliance, the circumstances which might vary
the type of response and the range of responses for that particular category of noncompliance. The
Enforcement Response Plan has been developed with the intention of serving the following purposes.
1. It recommends enforcement responses that are appropriate in relation to the nature and
severity of the violation and the overall degree of noncompliance.
2. It provides a guide to encourage a uniform application of enforcement responses to
comparable levels in types of violations, and it can be used as a mechanism to review the
appropriateness of the response.
The Enforcement Response Plan groups various types of violations into the following four categories:
1. Violations of sampling, monitoring, and reporting
2. Violations of compliance schedules
3. Violations of discharge limitations
4. Violations detected through inspection or field monitoring
In order to provide a concise document in a usable format, abbreviations have been used for the types of
response. A definition of each abbreviation is listed in increasing order of severity.
1. IA – An Informal Action may be used to respond to minor violations. This is typically
conveyed to the industry contact person, either by phone or with a written notice. This
type of response is used for very minor violations that only require follow up action at the
next compliance event.
2. LOV – A Letter of Violation is the most widely used and is a written notification to the
User indicating the type of apparent violation. The LOV will require a response within 14
days which usually consists of a written letter to the Control Authority (POTW – City of
South Bend) indicating the reason for the noncompliance and a description of measures
that are being taken to eliminate similar future violations.
3. AF – An Administrative Fine is a monetary penalty assessed by the Control Authority for
violations of pretreatment standards and requirements. An administrative fine may not
exceed $2,500 per day per violation and the Control Authority has discretion in setting the
amount of the fine. In the case of long term noncompliance, or noncompliance with a long
term average standard, a fine shall accrue for each day of the period of noncompliance.
4. AO – An Administrative Order is issued to a User by the Control Authority and contains
necessary corrective measures that need to be carried out by a User to achieve compliance.
The four basic types of administrative orders are: Cease and Desist, Consent, Show Cause,
and Compliance. A description of each follows. The order would normally contain a
short time frame.
a. Cease and Desist - When the Director finds that a User has violated, or continues to
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 30 of 39
violate, any provision of this ordinance, an individual wastewater discharge permit,
or order issued hereunder, or any other Pretreatment Standard or Requirement, or that
the User's past violations are likely to recur, the Director may issue an order to the
User directing it to cease and desist all such violations and directing the User to:
(1) Immediately comply with all requirements; and
(2) Take such appropriate remedial or preventive action as may be needed
to properly address a continuing or threatened violation, including halting
operations and/or terminating the discharge. Issuance of a cease and desist order
shall not be a bar against, or a prerequisite for, taking any other action against
the User.
b. Consent - The Director may enter into Consent Orders, assurances of compliance,
or other similar documents establishing an agreement with any User responsible for
noncompliance. Such documents shall include specific action to be taken by the User
to correct the noncompliance within a time period specified by the document.
c. Show Cause - The Director may order a User which has violated, or continues to
violate, any provision of this ordinance, an individual wastewater discharge permit,
or order issued hereunder, or any other Pretreatment Standard or Requirement, to
appear before the Director and show cause why the proposed enforcement action
should not be taken. Notice shall be served on the User specifying the time and place
for the meeting, the proposed enforcement action, the reasons for such action, and a
request that the User show cause why the proposed enforcement action should not be
taken.
d. Compliance - When the Director finds that a User has violated, or continues to
violate, any provision of this ordinance, an individual wastewater discharge permit,
or order issued hereunder, or any other Pretreatment Standard or Requirement, the
Director may issue an order to the User responsible for the discharge directing that the
User come into compliance within a specified time. If the User does not come into
compliance within the time provided, sewer service may be discontinued unless
adequate treatment facilities, devices, or other related appurtenances are installed and
properly operated. Compliance orders also may contain other requirements to address
the noncompliance, including additional self-monitoring and management practices
designed to minimize the amount of pollutants discharged to the sewer. A compliance
order may not extend the deadline for compliance established for a Pretreatment
Standard or Requirement, nor does a compliance order relieve the User of liability for
any violation, including any continuing violation.
5. LIT – Litigation is the most severe enforcement action and is utilized when a User has not
cooperated with the Control Authority or responded to the other enforcement remedies.
Litigation defines several courses of action including civil suits for injunctive relief and/or
civil penalties, criminal suits, termination of service, etc. These types of actions would all
involve the courts and the City Attorney and would follow the procedures necessary for
the due process.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 31 of 39
III. Significant Non-Compliance (SNC)
Utilizing the Enforcement Response Plan, Pretreatment Staff will initiate the appropriate response and see that
the enforcement tracking files have been updated to show the type of action being taken and the response date.
On a quarterly basis the Pretreatment Staff will be responsible for reviewing the compliance file of all Industrial
Users for the previous six (6) months to determine significant non-compliance of any industrial user and on an
annual basis, the names of all Industrial Users found in significant non-compliance will be published in the
South Bend Tribune. A definition of significant non-compliance follows.
Instances of Significant Non-Compliance (SNC) are Industrial User Violations which meet one or more of the
following criteria:
(a) Chronic violations of wastewater Discharge limits, defined here as those in which
sixty-six (66) percent or more of all of the measurements taken for the same pollutant
parameter during a six-month period exceed (by any magnitude) a numeric
Pretreatment Standard or Requirement, including instantaneous limits, as defined by
40 CFR 403.3(l);
(b) Technical Review Criteria (TRC) violations, defined here as those in which thirty-
three (33) percent or more of all of the measurements taken for the same pollutant
parameter during a six-month period equal or exceed the product of the numeric
Pretreatment Standard or Requirement including instantaneous limits, multiplied by
the applicable TRC (TRC = 1.4 for BOD, TSS, fats, oils and grease, and 1.2 for all
other pollutants except pH);
(c) Any other violation of a Pretreatment Standard or Requirement that the Director
determines has caused, alone or in combination with other Discharges, Interference or
Pass Through (including endangering the health of POTW personnel or the general
public);
(d) Any discharge of a pollutant that has caused imminent endangerment to human
health, welfare, or to the environment, or has resulted in the POTW's exercise of its
emergency authority to halt or prevent such a discharge;
(e) Failure to meet, within ninety (90) days after the schedule date, a compliance
schedule milestone contained in local control mechanism or enforcement order for
starting construction, completing construction, or attaining final compliance;
(f) Failure to provide, within thirty (30) days after the due date, required reports, such
as baseline monitoring reports, ninety (90) day compliance reports, periodic
compliance reports, and reports on compliance with compliance schedules;
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 32 of 39
(g) Failure to accurately report noncompliance;
(h) Any other violation or group of violations, which may include a violation of Best
Management Practices, which the Director determines will adversely affect the
operation or implementation of the local Pretreatment program.
Note: A determination of Significant Non-Compliance will not be made if the non-compliance events
triggering SNC occurred only in the first 3 month period of any 6 month period being evaluated, and if the
events caused the user to be in SNC for the previous 6 month period. If a user is found to be in SNC and
continuing violations of the same type occur in the following 6 month period, the events from the previous
quarter may be used in determining SNC in the following period.
IV. Enforcement Response Plan Examples
A. Sampling, Monitoring, and Reporting
Non-Compliance Circumstances Range of Response
Failure to sample, monitor
or report Isolated, or infrequent
LOV requiring correction within 14
days, AF, AO
Failure to sample, monitor,
report, and notify Control
Authority Isolated or infrequent
LOV requiring correction within 14
days, Escalated AF, AO
Failure to sample, monitor,
report, and notify Control
Authority
Frequent, or IU does not respond to
LOV LOV, AF, AO, SNC
Failure to notify of effluent
limit violation, or slug
discharge
Isolated, or infrequent. No known
effects.
LOV, AF, AO if no response within 14
days
Failure to notify of effluent
limit violation Frequent or continued violation LOV, AF, AO, SNC, LIT
Failure to notify of effluent
limit violation, or slug
discharge
Known environmental or POTW
damage LOV, AF, SNC, AO, Lit
Failure to submit renewal
permit application 90 days
prior to permit expiration Number of days will be considered LOV, AF
Reporting false information Any instance LIT, Criminal Investigation
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 33 of 39
B. Discharge Limitations
Non-Compliance Circumstances Range of Response
Exceeding Final Limits
(categorical, local, or
prohibited) Infrequent or isolated minor violation LOV, AF
Exceeding Final Limits
Infrequent or isolated major violations,
exceed TRC limits
LOV & AF, AO, LIT if environmental
harm results
Exceeding Final Limits Violation(s) which are SNC AF, AO, LIT
Exceeding Interim Limits No known damages LOV, AF, AO
Exceeding Interim Limits
Results in known environmental or
POTW damage - SNC LOV, AF, AO, LIT
Reported Slug load Isolated, no known damage LOV, Show cause, AF, AO
Reported Slug load
Isolated with known interference, pass
through or damage LOV, AF, AO, LIT
Reported Slug load Recurring - SNC LOV, AF, AO, LIT
Discharge without permit
or approval One time, no known damage LOV, AO, AF
Discharge without permit
or approval One time, results in damage
LOV,AF, AO, LIT, or request for
criminal investigation
Discharge without permit
or approval
Continuing violation with known
damage
LIT, request for criminal investigation,
sewer disconnect
C. Non-compliance detected through inspections or field investigation
Non-Compliance Circumstances Range of Response
Minor violation of
analytical procedures Any instance LOV, AF with continuing violation
Major violation of
analytical procedures No evidence of intent LOV, AF, AO
Major violation of
analytical procedures Evidence of negligence or intent - SNC
LOV, AF, AO, LIT (possible criminal
action)
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 34 of 39
Minor violation of permit
condition No evidence of negligence or intent
LOV, immediate corrective action
required, AF
Minor violation of permit
condition Evidence of negligence or intent - SNC
AF, AO, SNC, LIT (possible criminal
action)
Major violation of permit
condition Evidence of negligence or intent - SNC
AF, AO, SNC, LIT (possible criminal
action)
D. Compliance schedules
Non-Compliance Circumstances Range of Response
Reporting false information Any instance - SNC LIT, criminal investigation
Missed interim date
Will not cause late final or other
interim date LOV
Missed interim date
Will result in other missed interim
dates, violation for valid cause LOV, AO
Missed interim date
Will result in other missed interim
dates, no valid cause - SNC LOV, AO, LIT
Missed final date
90 days or more, failure or refusal to
comply without a valid cause AO, LIT
V. Time frame for responses
A. Initial enforcement action responses [involving contact with industrial users and requesting
information on corrective or preventative action (s)] will occur within 15 days of becoming aware of
violation.
B. Follow up actions for continuing or recurring violations will be taken within sixty (60) days of the
initial enforcement response. For all continuing violations, the response will include an administrative
order with milestones or deadlines.
C. Violations which threaten health, property, or environmental quality are considered emergencies and
will receive immediate responses such as halting the discharge or terminating service.
D. All violations meeting the criteria for Significant Non-Compliance will be addressed with an
enforceable order within 30 days of the identification of Significant Non-Compliance.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 35 of 39
ATTACHMENT 3:
Appeals Procedure
Any permittee desiring to dispute a fine must file a written request for the Director to reconsider the fine along
with full payment of the fine amount within ten (10) days of being notified of the fine. Where a request has
merit, the Director may convene a hearing on the matter. In the event the permittee’s appeal is successful, the
Director may reconsider to waive or reduce the fine. The Director may add the costs of preparing administrative
enforcement actions, such as notices and orders, to the fine.
Any User aggrieved by a final action of the Director requiring a permittee to restrict the volume or point of
discharge; requiring a permittee to install a storage or flow-control facility; denying a permit transfer; revoking
a permit; or issuing any authorized Administrative Enforcement Remedy, may request reconsideration by the
Director within fifteen (15) days of such Director action, and the Director shall have thirty (30) days from
receipt of request to make a decision related to reconsideration.
An administrative appeal from any terms of an individual wastewater discharge permit shall be made as
described in the paragraph above, but the effectiveness of the individual wastewater discharge permit shall not
be stayed pending the administrative appeal.
Appeals to the Director shall be submitted to:
Director of Public Utilities
3113 Riverside Drive
South Bend, IN 46628
If the ruling made by the Director is unsatisfactory to the person requesting reconsideration, or if the Director
fails to act within thirty (30) days from receipt of the request, the permittee may, within seven (7) days after
notification of action, or if the Director fails to act, within thirty-five (35) days of the date of request for
Director reconsideration, file a written appeal to the Board of Public Works. The written appeal shall be heard
by the Board within thirty (30) days from the date of filing. The Board of Public Works shall make a final
ruling on the appeal within thirty (30) days of the close of the meeting. The Director's decision, action, or
determination shall remain in effect during such period of reconsideration and appeal. Appeals to the Board
of Public Works shall be submitted to:
Board of Public Works
1316 County City Building
227 W. Jefferson Blvd
South Bend, IN 46601
All appeals shall carbon copy (cc) the City of South Bend’s Pretreatment Coordinator(s).
For clarification or additional details about the appeals procedure see the City of South Bend Ordinance
Sections 17-10 & 17-11.
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 36 of 39
ATTACHMENT 4:
ORGANIC PRIORITY POLLUTANT LIST
Acenaphthene 3,3-dichlorobenzidine
Acrolein 1,1-dichloroethylene
Acrylonitrile 1,2-trans-dichloroethylene
Benzene 2,4-dichlorophenol
Benzidine 1,2-dichloropropane
Carbon tetrachloride (tetrachloromethane) 1,3-dichloropropylene (1,3-dichloropropene)
Chlorobenzene 2,4-dimethylphenol
1,2,4-trichlorobenzene 2,4-dinitrotoluene
Hexachlorobenzene 2,6-dinitrotoluene
1,2-dichloroethane 1,2-diphenylhydrazine
1,1,1-trichloroethane Ethylbenzene
Hexachloroethane Fluoranthene
1,1-dichloroethane 4-chlorophenyl phenyl ether
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 37 of 39
1,1,2-trichloroethane 4-bromophenyl phenyl ether
1,1,2,2-tetrachloroethane Bis (2-chloroisopropyl) ether
Chloroethane Bis (2-chloroethoxy) methane
Bis (2-chloroethyl) ether Methylene chloride (dichloromethane)
2-chloroethyl vinyl ether (mixed) Methyl chloride (chloromethane)
2-chloronaphthalene Methyl bromide (bromomethane)
2,4,6-trichlorophenol Bromoform (tribromomethane)
Parachlorometa cresol Dichlorobromomethane
Chloroform (trichloromethane) Chlorodibromomethane
2-chlorophenol Hexachlorobutadiene
1,2-dichlorobenzene Hexachlorocyclopentadiene
1,3-dichlorobenzene Isophorone
1,4-dichlorobenzene Naphthalene
Nitrobenzene 1,12-benzoperylene
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 38 of 39
2-nitrophenol (benzo(ghi)perylene)
4-nitrophenol Fluorene
2,4-dinitrophenol Phenanthrene
4,6-dinitro-o-cresol 1,2,5,6-dibenzanthracene
N-nitrosodimethylamine (dibenzo(a,h)anthracene)
N-nitrosodiphenylamine Indeno (1,2,3-cd) pyrene)
N-nitrosodi-n-propylamine (2,3-o-phenylene pyrene)
Pentachlorophenol Pyrene
Phenol Tetrachloroethylene
Bis (2-ethylhexyl) phthalate Toluene
Butyl benzyl phthalate Trichloroethylene
Di-n-butyl phthalate Vinyl chloride (chloroethylene)
Di-n-octyl phthalate Aldrin
Diethyl phthalate Dieldrin
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 39 of 39
Dimethyl phthalate 4,4-DDT
1,2-benzanthracene 4,4-DDE (p,p-DDX)
(benzo(a)anthracene) 4,4-DDD (p,p-TDE)
Benzo(a)pyrene (3,4-benzopyrene) Alpha-endosulfan
3,4-Benzofluoranthene Beta-endosulfan
(benzo(b)fluoranthene) Endosulfan sulfate
11,12-benzofluoranthene Endrin
(benzo(k)fluoranthene) Endrin aldehyde
Chrysene Heptachlor
Acenaphthylene Heptachlor epoxide
Anthracene 2,3,7,8-tetrachlorodibenzo-
(BHC-hexachlorocyclohexane) p-dioxin (TCDD)
Alpha-BHC Gamma-BHC
Beta-BHC Delta-BHC
Honeywell Groundwater Remediation Industrial Wastewater Discharge Permit page 40 of 39
(PCB-polychlorinated biphenyls) PCB-1016 (Arochlor 1016)
PCB-1221 (Arochlor 1221) PCB-1232 (Arochlor 1232)
PCB-1242 (Arochlor 1242) PCB-1248 (Arochlor 1248)
PCB-1254 (Arochlor 1254) PCB-1260 (Arochlor 1260)
Toxaphene Chlordane (technical mixture and metabolites)