Region 2 NPDES Program and Permit Quality

Review

New Jersey

Review Date: September 2021
Report Date: March 2023

United States Environmental Protection Agency

Region 2
290 Broadway
New York, New York 10007

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Contents

Executive Summary	3

Common Acronyms	5

I.	PQR BACKGROUND	6

A.	2021 NJ PQR	6

B.	2016 NJ PQR	7

II.	STATE PROGRAM BACKGROUND	8

A.	Program Structure	8

B.	Universe and Permit Issuance	9

C.	State-Specific Challenges	9

D.	Current State Initiatives	10

III.	CORE REVIEW FINDINGS	10

A.	Basic Facility Information and Permit Application	10

1.	Facility Information	10

2.	Permit Application Requirements	11

B.	Developing Effluent Limitations	13

1.	Technology-based Effluent Limitations	13

2.	Reasonable Potential and Water Quality-Based Effluent Limitations	15

3.	Final Effluent Limitations and Documentation	19

C.	Monitoring and Reporting Requirements	21

D.	Standard and Special Conditions	22

E.	Administrative Process	24

F.	Administrative Record and Fact Sheet	25

IV.	NATIONAL TOPIC AREA FINDINGS	26

A.	Permit Controls for Nutrients in Non-TMDL Waters	26

B.	Effectiveness of POTW NPDES Permits with Food Processor Contributions	29

C.	Small Municipal Separate Storm Sewer System (MS4) Permit Requirements	42

V.	PERMITS REVIEWED FOR 2021 NJ PQR	45

VI.	2016 NJ PQR ACTION ITEM REVIEW	46

VII.	ACTION ITEMS IDENTIFIED DURING THE 2021 PQR	52

List of Tables

Table 1. Commonly Used Acronyms	5

Table 2. New Jersey Pretreatment Program Numbers	30

Table 3. CCUAand RVRSA Pretreatment Program Overview	31

Table 4. Industrial User Overview	32

Table 5. NJPDES Permits Reviewed for the 2021 NJ PQR	45

Table 6. Essential Action Items Identified During the 2016 PQR	46

Table 7. Recommended Action Items Identified During the 2016 PQR	49

Table 8. Essential Action Items Identified During the 2016 PQR	53

Table 9. Recommended Action Items Identified During the 2016 PQR	55

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Executive Summary

EPA Region 2's National Pollutant Discharge Elimination System (NPDES) Program and Permit
Quality Review (PQR) for New Jersey found that permits issued in the state were generally
sufficiently stringent to protect water quality and adhere to applicable state and federal
regulations. The majority of the areas of improvement identified in the PQR were in regard to
ensuring a complete and robust administrative record and ensuring that permits clearly
describe the conditions permittees must comply with.

The PQR examined 13 individual permits and 1 general permit issued by the New Jersey
Department of Environmental Protection (NJDEP) as well as state permitting policies and
practices. The PQR also focuses on three national topic areas:

•	Permit Controls for Nutrients in Non- Total Maximum Daily Load (TMDL) Waters,

•	Effectiveness of publicly owned treatment works (POTW) NPDES Permits with Food
Processor Contributions, and

•	Small Municipal Separate Storm Sewer System (MS4) Permit Requirements.

The 2021 NJ PQR found that NJDEP administers a robust and thorough State Pollutant
Discharge Elimination System program overall. New Jersey permits are largely comprehensive,
enforceable, and protective of water quality. The New Jersey Environmental Management
System (NJEMS) ensures that permits are complete and that fact sheets are comprehensive and
document the basis of the permitting decisions well. The water quality-based and technology-
based effluent limits established in permits are generally sufficiently stringent and comply with
the applicable federal regulations; secondary treatment standards are consistently applied
correctly. Additionally, NJDEP works to ensure their application forms remain up-to-date and
that meaningful information is collected from the applicants. In early 2021, NJDEP proactively
initiated a per- and polyfluoroalkyl substances (PFAS) Source Evaluation and Reduction Strategy
and has been working with selected categories of New Jersey Pollutant Discharge Elimination
System (NJPDES) permittees on monitoring and data collection.

The PQR recognizes the challenges in staffing and workload faced by New Jersey, including
emerging issues like permitting for applications of biological agents (i.e., the application of
microbes to surface water to control algal blooms) and high-priority contaminants like PFAS,
such as perfluorooctane sulfonic acid (PFOS). NJDEP also continues to improve their program
through initiatives to address contaminants of emerging concern; enhance community
engagement, particularly in the Environmental Justice communities; and update the NJPDES
permit application forms and forms within the NJEMS to create stronger environmental
protection.

Although the permits reviewed commonly conform to national requirements, EPA identified
several concerns, primarily regarding improved documentation of the basis of permitting
decisions or adjustments needed to more clearly document conformance with federal
regulations. Based on this PQR, EPA is recommending improvements to the:

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•	Authorization-to-discharge statement, special and standard conditions, and cooling
water intake provisions in the permits;

•	NJPDES permit applications and public notice language to ensure the appropriate
information is collected from the permittee and shared with the public; and

•	Development of nutrient effluent limitations to ensure permits are protective of
impaired downstream waters and that reasonable potential analysis is performed and
documented in the fact sheet.

NJDEP was provided with a draft of this report on August 4, 2022, and on February 9, 2023 and
provided comments to EPA. NJDEP's comments and the subsequent discussions with EPA
helped clarify details within the report, ensure EPA accurately described NJDEP's program, and
that the report provided a clear basis for report findings and the resulting action items .

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Common Acronyms

Table 1. Commonly Used Acronyms

BAT

Best Available Technology

BCT

Best Conventional Technology

BOD

Biochemical Oxygen Demand

BPJ

Best Professional Judgement

BAT

Best Available Technology

CBOD

Carbonaceous Biochemical Oxygen Demand

CFR

Code of Federal Regulations

CWA

Clean Water Act

DMR

Discharge Monitoring Report

ELG

Effluent Limitations Guideline

EPA

Environmental Protection Agency

MS4

Municipal Separate Storm Sewer System

NJEMS

New Jersey Environmental Management System

NJDEP

New Jersey Department of Environmental Protection

NJPDES

New Jersey Pollutant Discharge Elimination System

NPDES

National Pollutant Discharge Elimination System

POTW

Publicly Owned Treatment Works

PQR

Program and Permit Quality Review

R2

Region 2

TBEL

Technology-based Effluent Limitation

TSD

Technical Support Document for Water Quality-based Toxics Control

TSS

Total Suspended Solids

TMDL

Total Maximum Daily Load

WET

Whole Effluent Toxicity

WLA

Wasteload Allocation

WQS

Water Quality Standard

WQB El-

Water Quality-based Effluent Limitation

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I. PQR BACKGROUND
A. 2021 NJ PQR

National Pollutant Discharge Elimination System (NPDES) Program and Permit Quality Reviews
(PQRs) are an evaluation of a select set of NPDES permits to determine whether permits are
developed in a manner consistent with applicable requirements established in the Clean Water
Act (CWA) and NPDES regulations. Through this review mechanism, the Environmental
Protection Agency (EPA) promotes national consistency and identifies successes in the
implementation of the NPDES program as well as opportunities for improvement in the
development of NPDES permits.

EPA's review team, consisting of five EPA Region 2 (R2) staff members and two EPA contractors,
conducted a review of New Jersey Pollutant Discharge Elimination System (NJPDES) program
which included virtual meetings on September 15, 23, and 30, 2021.

The New Jersey PQR included reviews of core permit components and national and regional
topic areas, as well as discussions between the PQR evaluation team and New Jersey
Department of Environmental Protection (NJDEP) staff regarding program status and the permit
issuance process. The permit reviews focused on core permit quality and included a review of
the permit application, draft permit, fact sheet, final permit, and other requested
documentation which provides the basis for the development of the permit conditions and
related administrative process. The PQR also included conversations between EPA and the state
about program status, the permitting process, responsibilities, organization, staffing, and
program challenges the state is experiencing.

A total of 14 permits were reviewed as part of the 2021 NJ PQR. Of these, 11 were reviewed for
the core review, and 6 were reviewed for national topic areas. Some permits were reviewed for
both the core review and a national topic area review. Permits were selected based on issuance
date and the review categories that they fulfilled. A full list of the permits reviewed, and the
review categories, is in Section V.

Core Review

The core permit review involved the evaluation of selected permits and supporting materials
using basic NPDES program criteria. Reviewers completed the core review by examining
selected permits and supporting documentation, assessing these materials using standard PQR
tools, and talking with NJDEP management and staff regarding the permit development
process. The core review focused on the Central Tenets of the NPDES Permitting Program1 to
evaluate the NJPDES program. Core topic area permit reviews are conducted to evaluate similar
issues or types of permits in all states.

Topic Area Reviews

1 More information can be found at: https://www.epa.gov/npdes/central-tenets-npdes-permitting-program

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The national topics reviewed in the NJPDES program were:

•	Permit controls for nutrients in non-Total Maximum Daily Load (TMDL) waters,

•	Small Municipal Separate Storm Sewer System (MS4) permit requirements, and

•	Effectiveness of publicly owned treatment works (POTW) NPDES permits with food
processor contributions.

EPA did not identify a regional topic area for the 2021 NJ PQR.

Action Items

As part of the PQR, the evaluation team proposed action items to improve the NJPDES permit
program. The proposed action items are identified in Section VI of this report and are divided
into two categories to identify the priority that should be place on each item.

•	Essential Actions - Proposed "essential" action items address noncompliance with
respect to a federal regulation. EPA has provided the citation for each essential action
item. The permitting authority must address these action items in order to comply with
federal regulations.

•	Recommended Actions - Proposed "recommended" action items are recommendations
to increase the effectiveness of the states or Region's NPDES permit program.

The essential actions are used to augment the existing list of follow up actions currently tracked
by EPA Headquarters on an annual basis and are reviewed during subsequent PQRs.

B. 2016 NJ PQR

EPA conducted a PQR of the NJPDES Program on May 31 and June 1, 2016. The PQR summary
report is available at: https://www.epa.gov/npdes/regional-and-state-npdes-program-and-
permit-quality-review-pqr-reports.

The 2016 PQR review included the core permit review component as well as special topic area
reviews. The national topic areas were nutrients, pretreatment program, pesticides general
permit, and stormwater. The regional topic areas were reasonable potential analysis, power
plants, combined sewer overflows, and arsenic.

As part of the 2021 PQR, EPA requested updates from NJDEP on the progress of the action
items identified in the 2016 PQR. The 2016 PQR categorized findings into Critical Findings,
Recommended Actions and Suggested Practices. Generally, NJDEP was able to resolve many of
the action items. Of the 17 essential2 action items identified during the 2016 PQR, 6 have been
resolved, 1 was erroneously identified as an action item, and the remainder represent actions
that are either longer-term or low-priority activities which NJDEP is still addressing. Section V of

2 During the 2012-2017 PQR cycle, these action items were known as "Category 1" and address deficiencies or
noncompliance with respect to federal regulations. EPA is now referring to those action items going forward, as
essential. In addition, previous PQR reports identified recommendations as either "Category 2" or "Category 3"
action items. EPA is now consolidating these categories of action items into a single category: recommended.

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this report contains a detailed review of the progress on action items identified during the 2016
PQR.

II. STATE PROGRAM BACKGROUND

A. Program Structure

The NJ DEP, Division of Water Quality houses the pretreatment and NJPDES surface water
permitting staff under the Assistant Commissioner for Water Resource Management. The
Division of Watershed Protection and Restoration houses the Bureau of NJPDES Stormwater
Permitting and Water Quality Management under the Assistant Commissioner for Watershed
and Land Management Area. The NJDEP permitting offices are located in Trenton, New Jersey;
there are no regional or field offices.

The NJPDES program has approximately 38 permit writers. These positions include permit
writers for pretreatment, stormwater, and surface water permits. Each permit writer can issue
between 5 and 15 individual NJPDES surface water permit actions annually depending on the
complexity of each permit and the number of public comments received. Permit writers are
also responsible for issuing multiple general permit authorizations. Permit writing staff are
regularly enrolled in the EPA NPDES Permit Writers' Course and new staff are paired with a
mentor in their unit to help them learn permit writing. In Summer 2021, the Water Quality
Division introduced a virtual training program for 10 incoming staff members to introduce them
to the Division and NJPDES permitting in which each Bureau in the Division presented an
overview of their function. The presentations were recorded and are available for future
reference.

The NJPDES permit writers are supported by other units in the Bureaus such as the Permit
Administrative staff and Water Quality Analysis Unit in the Division of Water Quality and the
Stormwater Management Unit in the Division of Watershed Protection and Restoration. The
Division of Monitoring and Standards also provides support in standards development, ambient
monitoring, and TMDL development. Compliance and Enforcement staff assist with compliance
inspections, Administrative Consent Orders, and emergency preparedness and reactions. The
Division of Information Technology assists with ongoing maintenance and assistance with
information systems. Finally, the state Deputy Attorneys General from the Division of Law, the
Delaware River Basin Commission, and Soil Conservation Districts also support the NJPDES
program when appropriate.

The Division of Water Quality, and NJDEP as a whole, rely heavily on the New Jersey
Environmental Management System (NJEMS), an environmental information management
system which supports permit development and administration and other NJDEP activities.
NJEMS is used for permit development, administration and tracking, inspection and compliance
action support, and compliance monitoring and storage of associated documents. NJDEP has
developed systems that transfer data to EPA's Integrated Compliance Information System
(ICIS). All of the relevant historical data has been entered into ICIS.

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Many of the tools that the Division of Water Quality relies on to support permit development
are integrated into NJEMS. For example, NJEMS develops and populates templates for permits
and fact sheets based on information entered into the system by permit writers. All significant
permit administration and development documents (e.g., letters of completeness, public
notices) also have templates in NJEMS. Standard operating procedures and policies are also
embedded within NJEMS, including boilerplate language and standard options for permit
writers to select from as they develop permits.

NJEMS includes a library of narrative permit provisions that permit writers can adjust based on
the specific conditions of the permit. The system also includes substantial template information
from NJPDES fact sheets. The templates prompt each permit writer to address all pertinent
regulations and requirements when developing the basis for the permit.

The use of NJEMS promotes uniformity and consistency across the Division of Water Quality.
Even so, all permits undergo a rigorous quality assurance process, which is facilitated through
NJEMS. When the quality assurance process has been completed, permits are electronically
signed by management and locked to prevent further editing. Once locked, a permit can only
be unlocked by select individual users.

NJEMS also assists with maintaining the administrative records. Permit development
documentation and correspondence are maintained within the system, as are draft and final
permits and other pertinent documents. Some large paper files are archived in an off-site
warehouse, in accordance with established procedures, rather than being electronically stored
in NJEMS.

B.	Universe and Permit Issuance

Based on information dated September 15, 2021, the NJPDES permit universe consists of 551
individual permits which includes 190 POTW permits (102 majors, 88 minors), 100 industrial
permits (28 major, 72 minor), 179 individual stormwater permits, 66 individual pretreatment
permits, and 25 combined sewer overflow permits.

The NJPDES program also includes 25 general permits which, as of September 15, 2021,
covered a total of 11,119 permittees. The general permits are available on NJDEP's website at
www.ni.gov/dep/dwq/gps.htm.

As of July 10, 2022, 18.6 percent of major individual permits were backlogged and 27.9 percent
of minor individual permits were backlogged. Overall, 23.7 percent of all individual NPDES
surface water permits were backlogged.

C.	State-Specific Challenges

The challenges facing NJDEP are common to many states. NJDEP is facing an ever-increasing
amount of work in the permitting program without a commensurate increase in staffing.
Management and staff are also pulled away from their day-to-day responsibility to work on
new and high-priority concerns including permitting biological applications, emerging

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contaminants such as PFAS, and stormwater issues, namely unfunded mandates and MS4 size
definitions.

D. Current State Initiatives

NJDEP is working on a variety of initiatives to improve the efficiency and effectiveness of the
NJPDES permitting program and to address emerging environmental issues. The NJPDES
program has taken a number of steps in identifying and addressing potential sources of PFAS.
The NJPDES application forms are currently undergoing review and revision to ensure they
conform with the NPDES Updates Rule and that they collect meaningful and pertinent
information. NJDEP is also consistently updating and improving NJEMS documents to ensure
that permit templates and fact sheet development are robust, defensible, and seamless.

III. CORE REVIEW FINDINGS

A. Basic Facility Information and Permit Application

t. Facility Information

Background

Basic facility information is necessary to properly establish permit conditions. For example,
information regarding facility type, location, processes, and other factors is required by NPDES
permit application regulations (40 CFR 122.21). This information is essential for developing
technically sound, complete, clear, and enforceable permits. Similarly, fact sheets must include
a description of the type of facility or activity subject to a draft permit.

Program Strengths

The fact sheets reviewed for the 2021 NJ PQR were all developed using the NJEMS permit and
fact sheet template language and provided a clear description of the subject facility, the
wastewater streams, and the treatment processes. The permits also included appropriate
issuance, effective, and expiration dates, and receiving water information such as designated
uses and impairments.3

Areas for Improvement

The NPDES program requires permits for all entities discharging pollutants from a point source
into "waters of the United States" (40 CFR 122.1(b)(1)). The permitting authority, in this case is
NJDEP, authorizes a permittee to discharge. Most permitting authorities include very specific
language in the permit (e.g., [Permitting authority] authorizes [facility operator] to discharge at
[facility name] from [outfall number] to [receiving water]) authorizing the discharge. All the
NJPDES permits reviewed as part of the PQR included the information typically found in the
"authorization to discharge" statement but usually did not provide it in a clear, concise

3 A typographical error in the expiration date of the reviewed Bayshore Regional Sewerage Authority Wastewater
Treatment Plant (NJ0024708) was found during the PQR. NJDEP promptly issued a modified permit correcting the
error.

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sentence. Only one permit (NJ0024694 - Monmouth County Bayshore Outfall Authority)
provided a clear authorization-to-discharge sentence.

EPA recommends including a clear authorization-to-discharge statement (from where, to
where, by whom) in all NJPDES permits in a consistent location. Most permitting authorities
include this sentence on the cover or first page of the permit; however, it can be elsewhere in
the permit document.

Action Items

2. Permit Application Requirements

Background and Process

Federal regulations at 40 CFR 122.21 and 122.22 specify application requirements for
permittees seeking NPDES permits. Although federal forms are available, authorized states are
also permitted to use their own forms provided they include all information required by the
federal regulations. This portion of the review assesses whether appropriate, complete, and
timely application information was received by the state and used in permit development.

Permit applications are often received electronically, usually in .pdf format. Upon receipt, they
are logged in and distributed to the Administrative Review Section for an administrative
completeness review. This review includes ensuring that the correct forms were used, all fields
are complete, etc. Depending on the findings of the review, the Administrative Review Section
will issue either a completeness letter or an incompleteness letter requesting the outstanding
information to the applicant. Only after the application is deemed administratively complete is
the application then forwarded to the Permitting Bureau for a technical completeness review.

The technical completeness review conducted by the Permitting Bureau is to ensure that the
correct information, sufficient data, correct flow diagrams, and the like have been submitted. If
the technical review identifies missing information or if the permit writer has questions, they
communicate directly with the permittee to resolve them. Generally, the data submitted as
part of the application is supplemental as NJDEP requires all permittees to conduct priority
pollutant scans and whole effluent toxicity (WET) testing during the previous permit term.

• NJDEP should provide clear authorization-to-discharge language, as
referenced in 40 CFR 122.1(b)(1), in all NJPDES permits.

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Program Strengths

In general, the permit applications for the core review were submitted using the appropriate
NJDEP forms, complete applications were received, and the information included in the
applications was accurate. NJPDES applications were also usually submitted in a timely manner,
180 days prior to the expiration date of the existing permit.

Areas for Improvement

In a few instances, it wasn't immediately clear if the appropriate official had signed the permit
application. Federal regulations at 40 CFR 123.25 require that all state programs must
implement specific federal regulations, or impose more stringent requirements, including the
signatory requirements at 40 CFR 122.22. The signatory requirements state that permit
applications for a corporation must be signed by a responsible corporate officer or manager of
a manufacturing, production, or operating facility and that applications for a municipality or
public agency must be signed by either a principal executive officer or ranking elected official.
EPA recommends that NJDEP revise the permit application so that the applicant can more easily
identify that the signatory requirements are met or, if necessary, provide training or resources
to the necessary staff to assist them in determining whether the application has been signed by
the appropriate individual.

On June 12, 2019, the NPDES Application and Program Updates Rule became effective. The
rule, in part, modernizes the NPDES regulations, promotes submission of complete permit
applications, and clarifies regulatory requirements to allow more timely development of NPDES
permits that protect human health and the environment. States which issue NPDES permits
were required to use EPA's updated application forms or update their forms to reflect the latest
requirements within one year from promulgation of the final rule (June 19, 2020). If a state
needed to amend or enact a statute to accomplish such changes, then the state had to use
EPA's forms or update its own forms within two years (June 19, 2021). NJDEP requires NJPDES
applicants to use NJ-specific forms which are based, in part, on EPA forms. As of December
2021, the NJ application forms do not conform with the NPDES Updates Rule in its entirety.
While some of the changes implemented by the Updates Rule were already reflected in NJ
forms (e.g., North American Industry Classification System codes, applicant's email address),
some changes are still necessary to include items such as an indication of cooling water intake
structures, variance requests, and others. NJDEP believes that NJPDES Form 1 as well as a few
supplemental forms for specific discharger types (e.g., industrial surface water dischargers,
stormwater, etc.) must be edited to ensure compliance with the NPDES Updates Rule. The
process of updating forms is underway and NJDEP plans to have updated forms available in
2023.

Action Items

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• NJDEP must ensure compliance with the NPDES Application and
Program Updates Rule (84 FR 3324) as soon as possible.

• EPA recommends that NJDEP revise the application so that the
applicant can more easily identify that the signatory requirements
are met or, if necessary provide training or resources to the
necessary staff to assist them in determining whether the application
has been signed by the appropriate individual.

B. Developing Effluent Limitations

1. Technology-based Effluent Limitations

NPDES regulations at 40 CFR 125.3(a) require that permits include applicable technology-based
effluent limitations. Permits, fact sheets and other supporting documentation for POTWs and
non-POTWs were reviewed to assess whether technology based effluent limitations (TBELs)
represent the minimum level of control that must be imposed in a permit.

TBELs for POTWs

Background and Process

POTWs must meet secondary or equivalent-to-secondary standards which include limits for
biochemical oxygen demand/carbonaceous biochemical oxygen demand (BOD/CBOD), total
suspended solids (TSS), pH, and percent removal, and must contain numeric limits for all of
these parameters (or authorized alternatives) in accordance with the secondary treatment
regulations at 40 CFR Part 133. A total of five POTW permits were reviewed as part of the PQR.

Program Strengths

EPA found that the appropriate numeric secondary treatment standards for BOD/CBOD, TSS,
pH, and percent removals were all established in POTW permits. The limits were expressed in
an appropriate unit of measure (concentration) and included both short- and long-term (7-day
and 30-day averages) limits. The fact sheets provided a robust description of the treatment
processes, clearly identified which secondary treatment standard were established in the
permit, and identified the basis for the decision.

Areas for Improvement

No areas of improvement were identified during the 2021 PQR.

Action Items

No action items were identified during the 2021 PQR.

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TBELs for Non-POTW Dischargers
Background and Process

Permits issued to non-POTWs must require compliance with a level of treatment performance
equivalent to Best Available Technology Economically Achievable (BAT) or Best Conventional
Pollutant Control Technology (BCT) for existing sources, and consistent with New Source
Performance Standards (NSPS) for new sources. Where federal effluent limitations guidelines
(ELGs) have been developed for a category of dischargers, the TBELs in a permit must be based
on the application of these guidelines. If ELGs are not available, a permit must include
requirements at least as stringent as BAT/BCT developed on a case-by-case using best
professional judgment (BPJ) in accordance with the criteria outlined at 40 CFR 125.3(d).

NJDEP has found that the water quality standards are the prevailing factor for most effluent
limitations. TBELs prevail less frequently, and limits developed based on BPJ are very unusual —
so unusual that there is no written procedure for developing BPJ limits.

The CWA Act section 316(b) Existing Facilities Rule was not a specific focus of this PQR;
however, two permits with section 316(b) provisions were reviewed as part of the core reviews.
NJDEP generally writes consistent and well-documented fact sheets regarding compliance with
CWA section 316(b) regulations. The Wheelabrator Gloucester (NJ0062391) permit is for an
industrial facility with a design intake flow of 17.82 MGD, more than 25% of which is used for
cooling purposes. The fact sheet included a determination of Best Technology Available (BTA)
to minimize adverse impact, as required by CWA section 316(b), where the permittee selected
option (2) of the BAT standards, and NJDEP has the option of including additional protective
measures. However, the final permit did not include those technologies to require compliance
with impingement mortality standards at 40 CFR 125.94(c). NJDEP also provided the Hope
Creek Generating Station (NJ0025411) permit for review as a good example of NJDEP practices
regarding CWA section 316(b) BTA determinations. The fact sheet for Hope Creek Generating
Station is indeed very thorough and well-documented and includes a final determination of BTA
for both the impingement mortality standard and the entrainment standard. In the case of
Hope Creek, neither the BTA nor monitoring requirements were included in the final permit.

Program Strengths

NJPDES fact sheets generally provide a robust discussion of the wastestreams and the
pollutants in the discharge. The description of the treatment process and identification of
applicable standards is also clear and thorough. TBELs are in appropriate units and forms (i.e.,
concentration and mass).

Areas for Improvement

Occasionally, an effluent limitation is based on a rule or policy that originates outside of NJDEP
or EPA. In these instances, EPA recommends providing a specific reference to the rule, policy, or
standard to provide additional clarity in the fact sheet. For example, the fact sheet for the
IMTT-Bayonne (NJ0002089) permit states that the TSS effluent limitation is consistent with the

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Interstate Environmental Commission regulations but no citation to these regulations is
provided.

Regarding permits with CWA section 316(b) provisions, conditions required for compliance with
the impingement mortality standard and, where applicable, the entrainment standard must be
included in the final permit as enforceable requirements, as required by 40 CFR 125.98(c)(2).

Action Items

Essential

• Final permits with CWA section 316(b) provisions must include the
technologies and monitoring specified as BTA for compliance with
the impingement mortality standard (40 CFR 125.98(c)) and the
entrainment standard (40 CFR 125.94(d)), as enforceable
conditions of the final permit, as required by 40 CFR 125.98(b)(2).

• NJDEP should include a specific citation to the regulation, policy, or
standard when an effluent limitation is established based on a rule
or policy from outside NJDEP (i.e., the Interstate Environmental
Commission, Delaware River Basin Commission).

Recommended

2. Reasonable Potential and Water Quality-Based Effluent Limitations

Background

The NPDES regulations at 40 CFR 122.44(d) require permits to include any requirements in
addition to or more stringent than technology-based requirements where necessary to achieve
state water quality standards, including narrative criteria for water quality. To establish such
"water quality-based effluent limits" (WQBELs), the permitting authority must evaluate
whether any pollutants or pollutant parameters could cause, have reasonable potential to
cause, or contribute to an excursion above any applicable water quality standard. EPA's
Technical Support Document for Water Quality-based Toxics Control (TSD)4 provides guidance
to authorized programs regarding calculating reasonable potential and determining appropriate
water quality-based effluent limitations.

The NJ PQR assessed the processes employed to implement these requirements. Specifically,
the PQR reviewed permits, fact sheets, and other documents in the administrative record to
evaluate how permit writers and water quality modelers:

4 Available at https://www3.epa.gov/npdes/pubs/owm0264.pdf.

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•	determined the appropriate water quality standards applicable to receiving waters,

•	evaluated and characterized the effluent and receiving water including identifying
pollutants of concern,

•	determined critical conditions,

•	incorporated information on ambient pollutant concentrations,

•	assessed any dilution considerations,

•	determined whether limits were necessary for pollutants of concern, and,

•	where necessary, calculated such limits or other permit conditions.

For impaired waters, the PQR also assessed whether and how permit writers consulted and
developed limits consistent with the assumptions of applicable EPA-approved TMDLs.

Process for Assessing Reasonable Potential

NJDEP employs a two-step "cause" and
"reasonable potential" decision making
process, which is shown in Figure 1. The
cause analysis is generally conducted
based on 8-12 data points, but can be
assessed using fewer data points, and
evaluates whether the existing effluent
results in an excursion of the applicable
water quality standard by comparing
sampling data to a wasteload allocation
(WLA), If any data points are greater
than the WLA, cause is determined and
a WQBEL is established in the permit.

If the cause analysis does not
demonstrate that a discharge currently
causes or contributes to an exceedance
of water quality standards, NJDEP
conducts a statistical analysis to
determine whether there is reasonable
potential to cause or contribute to an
excursion of the water quality
standard. Reasonable potential to
cause or contribute is determined when the projected effluent (maximum data point times a
multiplying factor) exceeds the WLA. If reasonable potential is shown, a WQBEL is established in
the permit.

NJDEP generally uses one permit cycle of data for cause and reasonable potential analysis
determinations and prefers to use a dataset of at least 10 results for the statistical analyses.
However, if warranted, NJDEP will occasionally use data from an extended timeframe.



Detects?



(using Sufficiently Sensitive Methods)

Yes



No

i



Monitoring only

Cause?



Yes

No



r

WQBEL

¦4

Reasonable Potential?



Yes

y

No



WQBEL

M

Monitoring only

Figure 1: New Jersey Cause and Reasonable Potential Analysis Process

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Monitoring requirements are increased as needed so that the permittee is required to collect
sufficient data for a cause analysis each permit cycle.

NJDEP uses an Excel-based tool to evaluate cause and reasonable potential. Each pollutant is
evaluated on a separate WQBEL Analysis Data Sheet. Receiving water information and site-
specific hardness information, if available, is entered into the data sheet and informs the
identification of the applicable water quality standards (WQS). The existing effluent data for
each parameter is entered by the permit writer manually and the coefficient of variation is
automatically calculated. The manual data entry functions as another quality control/quality
assurance point as permit writers sometimes notice data inconsistencies (e.g., incorrect units)
which can usually be resolved by referring to the original discharge monitoring reports (DMRs).

NJDEP rarely removes a data point when evaluating cause or reasonable potential. When
permit writers notice an unusual data point, the lab sheets are often requested to determine
whether it is a transposition mistake or unit mistake. If the permit writer corrects this type or
error, it is noted in the fact sheet. When necessary, a statistical outlier procedure is conducted
to determine if the unusual data point is a true outlier. If the data point is determined to be an
outlier, it is removed from the cause and reasonable potential analysis and is fully documented
in the fact sheet.

NJDEP evaluates cause and, if no cause is demonstrated, the statistical analysis for reasonable
potential to cause or contribute, for all 126 priority pollutants using data submitted under the
priority pollutant scan requirements in all NJPDES permits. In addition, NJDEP evaluates all data
received through the waste characterization forms, DMRs, and the permit application when
determining whether effluent limitations are appropriate in a permit. Ambient data is not
routinely used when determining effluent limitations for renewal permits, except for ammonia.
Ambient data is typically only used in TMDL-based limitations and for new or expanding
facilities. NJDEP requires permittees to conduct studies rather than use default background
values.

Process for Developing WQBELs

NJDEP permit writers determine the impairment and TMDL status for every new and renewal
permit. Impairments are generally determined by hydrologic unit code (HUC). The most
common impairment across New Jersey is for phosphorus and there are a few large, watershed
TMDLs (Passaic RiverTMDL, Raritan TMDL, etc.). Impairment status is reviewed carefully. If the
facility discharges detectable levels of a pollutant that may be contributing to the impairment,
end-of-pipe or more stringent limits are established in the permit. If the facility does not
discharge the pollutant, monitoring will usually be established in the permit.

NJ's WQS allow for mixing zones. Most mixing zones are in non-tidal waters. Complete mixing is
initially assumed; further analysis for incomplete mixing is guided by EPA's TSD. In tidal waters,
a dilution study and modeling are required to determine if a mixing zone is appropriate. NJDEP
generally gives permittees the option to complete a dilution study in order to get a more

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complex, accurate, and often larger, mixing zone. The calculations to determine the mixing
zone always err on the side of safety. No dilution is permitted for intermittent streams.

Program Strengths

NJDEP's spreadsheet for statistical analysis of reasonable potential to cause or contribute to
excursions of a water quality standard is very thorough. While the spreadsheet itself is
considered deliberative and not included in the permit fact sheet, results of the analysis are
well documented in permit files through the WQBEL Analysis Data Sheet. The outlier test data
sheet results are also reasonably well summarized in the fact sheet. Another strength is that the
coefficient of variation (CV) is calculated individually for each data set and the basis for the CV is
provided in the data sheet. The data quality check conducted by the permit writers when
entering data into the WQBEL Data Analysis Sheet is also a valuable checkpoint for ensuring the
most appropriate limits are established in the permit.

NJDEP establishes appropriate and protective WQBELs in permits. The fact sheets contain a
complete discussion of factors considered in WQBEL development including impairments,
dilution studies, mixing zones, effluent data, outliers, and the like.

Areas for Improvement

NJDEP conducts a cause analysis and a reasonable potential to cause or contribute analysis on
all pollutants of concern. However, the language in the fact sheet does not consistently state
explicitly whether a cause analysis or reasonable potential analysis was completed and the
results of the analysis. EPA recommends including language similar to the following suggestions
for each evaluated parameter:

•	Based on the results of a cause analysis, there is no cause for this pollutant to result in an
excursion of the state's WQS. Based on the results of a reasonable potential analysis,
including for both potential to cause or contribute to a WQS excursion, there is the
reasonable potential for an excursion of the state's WQS. As a result, an effluent limitation
was established.

•	Based on the results of a cause analysis, the effluent shows cause for an excursion of the
state's WQS. As a result, an effluent limitation was established. A reasonable potential
analysis is not necessary.

•	Based on the results of a cause and reasonable potential analysis, the effluent does not
cause, have the reasonable potential to cause, or contribute to an excursion of the state's
WQS. As a result, no effluent limitation was established. However, additional monitoring
that is representative of the permitted activity and reporting the monitoring data (40 CFR
122.48(b)) is required.

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EPA supports NJDEP's two-step process for calculating cause and reasonable potential.
However, as Chapter 3 of the TSD provides guidance for calculating reasonable potential with a
limited sample size, EPA believes that NJDEP must calculate reasonable potential for all
parameters with effluent data regardless of sample size.

Action Items

3. Final Effluent Limitations and Documentation

Background and Process

Permits must reflect all applicable statutory and regulatory requirements, including technology
and water quality standards, and must include effluent limitations that ensure that all
applicable CWA standards are met. The permitting authority must identify the most stringent
effluent limitations and establish them as the final effluent limitations in the permit. In
addition, for reissued permits, if any of the limitations are less stringent than limitations on the
same pollutant in the previous NPDES permit, the permit writer must conduct an anti-
backsliding analysis, and if necessary, revise the limitations accordingly. In addition, for new or
increased discharges, the permitting authority should conduct an antidegradation review, to
ensure the permit is written to maintain existing high quality of surface waters, or if
appropriate, allow for some degradation. The water quality standards regulations at 40 CFR
131.12 outline the common elements of the antidegradation review process.

In addition, permit records for POTWs and industrial facilities should contain comprehensive
documentation of the development of all effluent limitations (40 CFR 124.56). TBELs should
include assessment of applicable standards, data used in developing effluent limitations, and
actual calculations used to develop effluent limitations. The procedures implemented for

• NJDEP must calculate the reasonable potential of all pollutants of concern
to cause or contribute to an exceedance of WQS to be consistent with EPA
regulations at 40 CFR 122.44(d). This also applies to situations with limited
or no data available, such as new facilities.

• EPA recommends explicitly stating in the fact sheet whether a cause, the
reasonable potential to cause or contribute to an excursion of the state's
WQS analysis was completed and the results of the analysis.

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determining the need for WQBELs as well as the procedures explaining the basis for
establishing, or for not establishing, WQBELs should be clear and straightforward. The permit
writer should adequately document changes from the previous permit, ensure draft and final
limitations match (unless the basis for a change is documented), and include all supporting
documentation in the permit file (e.g., permit fact sheet [40 CFR 124.56] and administrative
record). The permit writer should sufficiently document in the permit fact sheet the
determinations regarding anti-backsliding and antidegradation requirements.

Specific types of discharges may require additional effluent limitations and permit provisions as
well. The CWA Section 403 Ocean Discharge Criteria establish guidelines for discharges into the
territorial seas, waters of the contiguous zone, or the oceans. As part of the 2021 PQR, EPA
reviewed the final Monmouth County Bayshore Outfall Authority (NJ0024694) permit.

Regarding the ocean discharge criteria, EPA agrees with NJDEP's conclusion that the discharge
is not causing unreasonable degradation to the marine environment in the vicinity of the
discharge and is, therefore, consistent with federal regulations at 40 CFR 125.123(a).
Additionally, the inclusion of additional permit requirements specifically addressed the ocean
discharge provision at the next permit renewal. NJDEP's ocean discharge criteria assessment is
generally thorough and well-documented in the fact sheet. However, EPA suggests including
additional permit provisions to collect monitoring and technical information in the following
areas of significant importance to more completely meet the requirements of 40 CFR
125.122(a):

•	Shellfish harvesting area, commercial and recreational fishing grounds;

•	Primary and secondary contact recreation, and bathing beach water quality;

•	Maintenance, migration and propagation of the natural and established biota; and

•	Potential impacts on threatened and endangered species.

Program Strengths

Permit fact sheets provide a detailed discussion of the development of effluent limits and the
basis for the final effluent limitation. Permit writers seem to consistently apply the most
stringent applicable effluent limitations.

The fact sheets consistently address federal anti-backsliding requirements and state
antidegradation requirements and seem compliant with both sets of regulatory requirements.

Areas for Improvement

While the information is implied by the referenced regulations, NJDEP does not explicitly state
in fact sheets whether an effluent limit is a TBEL or a WQBEL. EPA recommends clearly stating
in the fact sheet if an effluent limitation is a TBEL or a WQBEL.

NJDEP's assessment of the ocean discharge criteria is generally thorough and well documented
in the fact sheet. To further bolster the ocean discharge criteria assessment, EPA recommends
including specific requirements to collect additional monitoring and technical information
during the permit term on areas of significant importance (commercial and recreational fishing

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grounds, recreational water quality, etc.) This will help ensure that NJDEP has the information
required to continue to confirm that the discharge had no adverse impacts on the receiving
water.

Additionally, for ocean discharge permits, EPA recommends revising the reopener clause in
permits to specifically list the need to incorporate "biological sampling" as a reason to modify
or revoke the permit. The inclusion of biological sampling as a reason to modify or revoke the
permit will ensure that NJDEP can require studies to confirm the biota in the vicinity of the
outfall are balanced and healthy.

Action Items

• NJDEP should explicitly state in fact sheets whether an effluent
limitation is a TBEL or a WQBEL to more clearly comply with 40 CFR
124.56.

Recommended

• In ocean discharge permits, NJDEP should specifically include
requirements to collect additional monitoring and technical
information about areas of significant importance listed at 40 CFR
125.122(a) during the permit term so the determination of no
adverse effects can be completed thoroughly at renewal.

• In ocean discharge permits, NJDEP should include "biological
sampling" in the reopener clause as a reason to modify or revoke a
permit

C. Monitoring and Reporting Requirements

Background and Process

NPDES regulations at 40 CFR 122.41(j) require permittees to evaluate compliance with the
effluent limitations established in their permits and provide the results to the permitting
authority. Monitoring and reporting conditions require the permittee to conduct routine or
episodic self-monitoring of permitted discharges and, where applicable, internal processes, and
report the analytical results to the permitting authority with information necessary to evaluate
discharge characteristics and compliance status.

Specifically, 40 CFR 122.44(i) requires NPDES permits to establish, at minimum, annual
reporting of monitoring for all limited parameters sufficient to assure compliance with permit
limitations, including specific requirements for the types of information to be provided and the
methods for the collection and analysis of such samples. In addition, 40 CFR 122.48(b) requires
that permits specify the type, intervals, and frequency of monitoring sufficient to yield data
which are representative of the monitored activity. The regulations at 40 CFR 122.44(i) also

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require reporting of monitoring results with a frequency dependent on the nature and effect of
the discharge. 40 CFR Part 127 requires NPDES-regulated entities to submit certain data
electronically, including discharge monitoring reports and various program-specific reports, as
applicable.

NPDES permits should specify appropriate monitoring locations to ensure compliance with the
permit limitations and provide the necessary data to determine the effects of the effluent on
the receiving water. A complete fact sheet will include a description and justification for all
monitoring locations required by the permit. States may have policy or guidance documents to
support determination of appropriate monitoring frequencies; documentation should include
an explicit discussion in the fact sheet providing the basis for establishing monitoring
frequencies, including identification of the specific state policy or internal guidance referenced.
Permits are also required to specify the sample collection method for all parameters required
to be monitored in the permit. Additionally, the fact sheet is required to present the rationale
for requiring grab or composite samples and discuss the basis of a permit requirement
mandating use of a sufficiently sensitive 40 CFR Part 136 analytical method.

Program Strengths

NJPDES permits require permittees to collect enough water quality data to support permitting
decisions. NJPDES WET effluent limitations and monitoring requirements were appropriately
established in permits. Permits also consistently included requirements to submit electronic
DMRs.

Standard language in Part 4 of the NJPDES permits requires that sufficiently sensitive methods
used when collecting and analyzing effluent data. There is detailed guidance available on
NJDEP's website at https://www.ni.Qov/dep/dwa/pdf/sstm-fag.pdf.

Overall, monitoring and reporting requirements seem sufficient to assess permit compliance
and inform permitting decisions.

Areas for Improvement

No areas for improvement were identified during the 2021 PQR.

Action Items

No action items were identified during the 2021 PQR.

D. Standard and Special Conditions

Background and Process

Federal regulations at 40 CFR 122.41 require that all NPDES permits, including NPDES general
permits, contain certain "standard" permit conditions. Further, the regulations at 40 CFR 122.42
require that NPDES permits for certain categories of dischargers must contain additional
standard conditions. Permitting authorities must include these conditions in NPDES permits and

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may not alter or omit any standard condition, unless such alteration or omission results in a
requirement more stringent than those in the federal regulations.

Permits may also contain additional requirements that are unique to a particular discharger.
These case-specific requirements are generally referred to as "special conditions." Special
conditions might include requirements such as: additional monitoring or special studies such as
a mercury minimization plan; best management practices [see 40 CFR 122.44(k)], or permit
compliance schedules [see 40 CFR 122.47]. Where a permit contains special conditions, such
conditions must be consistent with applicable regulations.

NJDEP includes boilerplate template language provided in NJEMS in all NPDES permits. Most
special conditions also have boilerplate language provided in NJEMS that the permit writer
selects, customizes, and inserts into the permit. The bases for special conditions, when
established, are discussed in the fact sheet.

NJDEP incorporates federal standard conditions by reference to NJ Administrative Code;
included as Part I of the permit. In addition, NJAC 7:14A-2.3(a) incorporates NPDES regulations
(including standard conditions) by reference, stating:

"The requirements applicable to the NJPDES program of the Federal Clean Water
Act (33 USC 1251 et seq.), the Federal Safe Drinking Water Act (42 USC 300F et
seq.), the State Act, and all Federal regulations cited in this chapter, including but
not limited to, 40 CFR Part 110, 122, 123, 124, 125, 129, 133, 126, 144, 258, 262,

403, and National Pretreatment Standards in 40 CFR chapter I, subchapter N, and
including all amendments and supplements thereto, are incorporated into this
chapter by reference unless the context clearly indicates otherwise."

Program Strengths

NJPDES permits consistently include the boilerplate standard and special conditions language
provided by NJEMS. Appropriate special conditions are established in the permits, when
necessary.

Areas for Improvement

The provisions for bypass (40 CFR 122.41(m)), upset (40 CFR 122.41(n)), and the additional
reporting requirement for non-POTWs (40 CFR 122.42(a)) appear to be absent from direct
inclusion in the permit. A crosswalk between the NJ standard condition regulations and the
federal standard condition regulations would provide clarity and transparency to NJPDES
permits.

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Action Items

• NJPDES permits must include provisions for bypass, upset, and the
additional reporting requirements for non-POTWs as required by
40 CFR 122.41(m), 122.41(n), and 122.42(a), respectively.

E. Administrative Process

Background and Process

The administrative process includes documenting the basis of all permit decisions (40 CFR 124.5
and 40 CFR 124.6); coordinating EPA and state review of the draft (or proposed) permit (40 CFR
123.44); providing public notice (40 CFR 124.10); conducting hearings if appropriate (40 CFR
124.11 and 40 CFR 124.12); responding to public comments (40 CFR 124.17); and modifying a
permit (if necessary) after issuance (40 CFR 124.5). EPA discussed each element of the
administrative process with NJDEP, and reviewed materials from the administrative process as
they related to the core permit review.

NJPDES public notices are managed by NJDEP. Notices for major permits are published in the
newspaper and in the NJDEP Bulletin which is published biweekly online. Notices for minor
permits are only published in the NJDEP Bulletin unless the permit has generated significant
public interest. NJDEP provides the text of the public notice to the newspaper with a time
period for publication. Upon publication, an affidavit or proof of publication is provided by the
newspaper and most newspapers are available for public review under

www.njpublicnotices.com. The affidavit is saved in hard copy and electronically. The hard copy
is warehoused in NJDEP's document repository. Permittees are responsible for coordinating the
public notice when requesting coverage under a general permit.

Comments received during the public comment period are logged through NJDEP's mail
procedures and provided to the permit writer. The response to comments is written by the
permit writer, with assistance from colleagues when necessary, and then is provided with the
final permit, and is documented in the permit files.

Hearings are required when there is significant public interest. Usually, a public hearing is held
when five or more individuals or entities request one. The hearings are transcribed and
documented in the permit record. A more detailed description of the hearing process is
available on NJDEP's website at https://www.nj.gov/dep/legal/adminhear.htm.

Program Strengths

The public notice is consistently and appropriately completed and documented in the permit
files. The response to comments is consistently provided and provides and clear and detailed
discussion of basis for the permitting decision or, if necessary, the basis for the change to the
draft permit.

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Areas for Improvement

Federal regulations at 40 CFR 123.25 establish administrative provisions that each state NPDES
program must implement, or must impose more stringent requirements than, including
provisions regarding public notices at 40 CFR 124.10(d). The public notices provided for NJPDES
permits include all the information required by the federal regulations except for the provision
which requires a general description of the location of each existing or proposed discharge
point. EPA recommends including a plain-language description of the outfall location in the
public notice to comply with this regulation, as required by 40 CFR 124.10(d)(vii).

Action Items

• NJDEP must include a general description of the location of each
existing or proposed discharge point in the public notice, as
required by 40 CFR 124.10(d)(vii).

F. Administrative Record and Fact Sheet

Background and Process

The administrative record is the foundation that supports the NPDES permit. If EPA issues the
permit, 40 CFR 124.9 identifies the required content of the administrative record for a draft
permit and 40 CFR 124.18 identifies the requirements for a final permit. Authorized NPDES
state permit programs should have equivalent documentation. The record should contain the
necessary documentation to justify permit conditions. At a minimum, the administrative record
for a permit should contain the following: the permit application and supporting data; draft
permit; fact sheet or statement of basis;5 all items cited in the statement of basis or fact sheet
including calculations used to derive the permit limitations; meeting reports; correspondence
between the applicant and regulatory personnel; all other items supporting the file; final
response to comments; and, for new sources where EPA issues the permit, any environmental
assessment, environmental impact statement, or finding of no significant impact.

Current regulations (40 CFR 124.56) require that fact sheets include information regarding the
type of facility or activity permitted, the type and quantity of pollutants discharged, the
technical, statutory, and regulatory basis for permit conditions, the basis and calculations for
effluent limits and conditions, the reasons for application of certain specific limits, rationales for
variances or alternatives, contact information, and procedures for issuing the final permit.
Generally, the administrative record includes the permit application, the draft permit, any fact

5 Per 40 CFR 124.8(a), every EPA and state-issued permit must be accompanied by a fact sheet if the permit:
Incorporates a variance or requires an explanation under 124.56(b); is an NPDES general permit; is subject to
widespread public interest; is a Class I sludge management facility; or includes a sewage sludge land application
plan.

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sheet or statement of basis, documents cited in the fact sheet or statement of basis, and other
documents contained in the supporting file for the permit.

As NJDEP uses NJEMS to draft the permits and fact sheets, NJPDES fact sheets are consistent,
robust, and very detailed. As a practice, NJDEP develops fact sheets for both major and minor
permits.

Program Strengths

NJPDES fact sheets are very detailed, thorough, robust, and well organized. Generally, a wealth
of information is included that provides a clear description of the facility, the receiving water,
existing effluent quality, relevant pollutants, and the basis for the permitting decisions.

Areas for Improvement

While NJPDES fact sheets are very thorough, there are a few instances where the language
could more clearly describe the basis for the permitting decision. For example, fact sheets
should clearly distinguish between TBELs and WQBELs (as noted in Section III.B.3) or explicitly
state whether a cause or reasonable potential analysis has been completed and the outcome of
that analysis (as noted in Section III.B.3). These areas for improvement and the associated
action items are discussed elsewhere in this report.

Action Items

No action items were identified during the 2021 PQR.

IV. NATIONAL TOPIC AREA FINDINGS

National topic areas are aspects of the NPDES permit program that warrant review based on
the specific requirements applicable to the selected topic areas. These topic areas have been
determined to be important on a national scale. National topic areas are reviewed for all PQRs.
The national topics areas are Permit Controls for Nutrients in Non-TMDL Waters, Effectiveness
of POTW NPDES Permits with Food Processor Contributions, and Small Municipal Separate
Storm Sewer System (MS4) Permit Requirements.

A. Permit Controls for Nutrients in Non-TMDL Waters

Background

Nutrient pollution is an ongoing environmental challenge, however, nationally permits often
lack nutrient limits. It is vital that permitting authorities actively consider nutrient pollution in
their permitting decisions. Of the permits that do have limits, many are derived from wasteload
allocations in TMDLs, since state criteria are often challenging to interpret. For this section,
waters that are not protected by a TMDL are considered. These waters may already be
impaired by nutrient pollution or may be vulnerable to nutrient pollution due to their hydrology
and environmental conditions. For the purposes of this program area, ammonia is considered
as a toxic pollutant, not a nutrient.

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Federal regulations at 40 CFR 122.44(d)(vii)(A) require permit limits to be developed for any
pollutant that causes, has reasonable potential to cause, or contributes to an impairment of
water quality standards, whether those standards are narrative or numeric.

To assess how nutrients are addressed in the NJPDES program, EPA R2 reviewed four permits as
well as the New Jersey Nutrient Criteria as amended on December 12, 2019. The four permits
reviewed were Town of Phillipsburg (NJ0024716), Bayshore Regional Sewerage Authority
WWTP (NJ0024708), Butterworth Water Pollution Control Facility (NJ0024911), and Monmouth
County Bayshore Outfall Authority (NJ0024694).

NJDEP has a long-standing narrative criterion for nutrients, which states:

"Except as due to natural conditions, nutrients shall not be allowed in concentrations
that render the waters unsuitable for the existing or designated uses due to
objectionable algal densities, nuisance aquatic vegetation, diurnal fluctuations in
dissolved oxygen or pH indicative of excessive photosynthetic activity, detrimental
changes to the composition of aquatic ecosystems, or other indicators of use
impairment caused by nutrients." (N.J.A.C.7:9B-1.14(d)4i)

NJDEP has also established a numeric total phosphorus criterion of 0.1 mg/L in any non-tidal
stream, and 0.05 mg/L for lakes, ponds, reservoirs, or tributaries to such waters, unless
watershed specific translators are established or the NJDEP determines that such levels would
render the waters unsuitable, for example due to algal overgrowth. NJDEP does not have a
numeric criterion for Total Nitrogen currently.

The Delaware River Basin Commission (DRBC) is an Interstate Agency which establishes water
quality requirements and technology-based treatment standards for dischargers to the main
stem of the Delaware River. The discharge of pollutants into surface waters within the
Delaware River Basin require approval by the DRBC, in addition to NJPDES permit coverage. For
nutrients, DRBC sets technology-based treatment levels in its water quality regulations,
including 30-day average effluent limits for Total Nitrogen and Total Phosphorus that represent
"Best Demonstrable Technology (BDT)." DRBC's water quality-based approach to nutrient
control is focused on dissolved oxygen levels in the Delaware River, and what point and
nonpoint sources may be contributing to low levels of dissolved oxygen.

Program Strengths

NJDEP includes detailed fact sheets, which include reasonable potential analyses, calculations,
and discussion of discharge monitoring data. Fact sheets include effluent characteristics for
Total Phosphorus, Total Nitrogen, and Nitrogen compounds such as Nitrate-Nitrite. Permit fact
sheets consistently list whether the receiving waterbody is impaired, and for which pollutants.
Permits tend to have at least monitoring requirements for Total Phosphorus, resulting in
discharge monitoring data for NJDEP to discuss in their permit fact sheets and to perform
reasonable potential analyses.

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Areas for Improvement

For one permit (Town of Phillipsburg) there were nutrient related impairments downstream of
the immediate receiving water. In this example, NJDEP did not include limitations, determining
there was not reasonable potential for the immediate receiving water, and noting that the
downstream impairments involved other standards such as those of the Delaware River Basin
Commission. While this is documented in the calculations and reasonable potential section, the
impairments listing at the beginning of the fact sheet could be clearer regarding which
impairments were downstream and which were in the immediate receiving water. NJDEP must
ensure that permits are protective of downstream uses, both numeric and narrative nutrient
criteria, including water quality criteria of other states and interstate entities such as DRBC, as
required by 40 CFR 122.44(d).

None of the permits included a reasonable potential analysis for total nitrogen. A numeric
criterion for marine waters would make this easier for permit writers to implement.

In all four permits there were detailed calculations provided for a pollutant such as nitrate or
ammonia nitrogen. There was also narrative discussion on whether there is reasonable
potential for an excursion of the applicable phosphorus state water quality standards. None of
the permits included discussion of protection of waterbodies to prevent algal blooms, or
nutrient-related impairments in downstream waterbodies.

In the case of Bayshore, while the immediate receiving water segment does not list dissolved
oxygen impairments, the fact sheet notes that the Atlantic Ocean, which is the downstream
receiving water, is impaired for dissolved oxygen. Reasonable potential analyses for this
discharge should include contributions to downstream dissolved oxygen impairments from the
discharge of total nitrogen.

These findings and the resulting action items are similar to those identified in the 2016 PQR.

Action Items

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• NJDEP must evaluate whether a discharge causes or contributes, or
has the reasonable potential to cause or contribute to an
exceedance of narrative or numeric WQS, and include numeric
limits where necessary as required by 40 CFR 122.44(d).

Essential

• NJDEP must ensure that permits are protective of downstream
uses, for both numeric and narrative nutrient criteria, including
water quality criteria of other states and interstate entities such as
DRBC, as required by 40 CFR 122.44(d).

•	NJDEP should clarify in the impairments section whether the
direct receiving water is impaired, or a downstream segment

•	NJDEP should include monitoring requirements for Total
Nitrogen, particularly for dischargers to marine water or
tributaries to marine waters, such that waste load allocations may
be calculated if there is a TMDL for dissolved oxygen impairment
or algal overgrowth.

B. Effectiveness of POTW NPDES Permits with Food Processor
Contributions

The general pretreatment regulations (40 CFR Part 403) establish responsibilities of federal,
state, local government, and industrial users to implement pretreatment standards to control
pollutants from indirect dischargers which may cause pass through or interfere with POTW
treatment processes or which may contaminate sewage sludge.

Background

Indirect discharges from food processors can be a significant contributor to noncompliance at
recipient POTWs. Food processing discharges contribute to nutrient pollution (e.g., nitrogen,
phosphorus, ammonia) to the nation's waterways. Focusing specifically on the Food Processing
Industrial Sector will synchronize PQRs with the Office of Enforcement and Compliance
Assurance (OECA)'s Significant Non-compliance (SNC)/National Compliance Initiative (NCI).

The goal of the PQR was to identify successful and unique practices with respect to the control
of food processor discharges by evaluating whether appropriate controls are included in the
receiving POTW NPDES Permit and documented in the associated fact sheet or Statement of
Basis; as well as by compiling information to develop or improve permit writers' tools to be
used to improve both POTW and industrial user compliance.

Recommended

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The PQR also assessed the status of the pretreatment program in New Jersey as well as specific
language in POTW NPDES permits. With respect to NPDES permits, focus was placed on the
following regulatory requirements for pretreatment activities and pretreatment programs:

•	40 CFR 122.42(b) (POTW requirements to notify Director of new pollutants or
change in discharge);

•	40 CFR 122.44(j) (Pretreatment Programs for POTWs);

•	40 CFR 403.8 (Pretreatment Program Requirements: Development and
Implementation by POTW), including the requirement to permit all SlUs;

•	40 CFR 403.9 (POTW Pretreatment Program and/or Authorization to revise
Pretreatment Standards: Submission for Approval);

. 40 CFR 403.12(i) (Annual POTW Reports); and

•	40 CFR 403.18 (Modification of POTW Pretreatment Program).

Pretreatment Program Summary and Background Information

New Jersey is authorized as the approval authority by EPA. The NJDEP oversees 17 approved
pretreatment programs. The approved pretreatment programs regulate 409 Significant
Industrial Users (SlUs), of which 167 are Categorical Industrial Users (ClUs). The approved
pretreatment programs have designated 18 Non-Significant Categorical Industrial Users
(NSCIUs) in addition to the 167 ClUs. NJDEP directly implements the pretreatment program
in 35 non-approved areas (areas not serviced by a POTW with an approved program) and
oversees 66 SlUs, of which 25 are ClUs (and there are no NSCIUs). These industries were issued
individual permits; general permits were not issued by NJDEP. Table 1, below, provides a
summary of industrial users by type.

Table 2. New Jersey Pretreatment Program Numbers



Approved Programs
(POTW Control Authority)6

Non-Approved Programs
(NJDEP Control Authority)

Number

17

35

SlUs including ClUs

409

66

ClUs

167

25

NSCIUs7

18

0

NJDEP reviews the POTWs' NPDES applications, writes and issues the NJPDES permits, and
develops and updates the NJPDES permit fact sheets. NJDEP is responsible for determining
which POTWs need to develop a pretreatment program. Pretreatment regulations and
requirements are written out in Section F of the NJPDES permits.

6	Please note that 3 approved programs operate more than one POTW: Bergen County Utilities Authority operates
2 POTWs, Ocean County Utilities Authority operates 3 POTWs, and the Township of Morris operates 2 POTWs

7	NSCIUs are not considered ClUs.

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POTWs without an approved pretreatment program are required to submit an annual report,
which requires submitting a list of all SlUs in accordance with the POTW's NJPDES permit. In
addition, all individual NJPDES SIU permits issued by the NJDEP contain the pretreatment
conditions or requirements as noted in the NJPDES Rules, N.J.A.C. 7:14A-21.10.

The pretreatment program is managed through NJDEP's Division of Water Quality, Bureau of
Surface Water and Pretreatment Permitting. The program conducts pretreatment compliance
audits (PCAs) of the 17 approved programs either every two years if the pretreatment program
is in good standing or the following year if the pretreatment program received a rating of
'Conditionally Acceptable' or 'Unacceptable' during the previous audit. The NJDEP
Pretreatment Program and EPA R2 do not conduct any pretreatment compliance inspections
(PCIs) based upon a memorandum of agreement (MOA) between EPA and NJDEP8; the audit
frequency is sufficient to forgo conducting PCIs between PCAs. NJDEP staff also review annual
pretreatment program reports and local limit sampling and local limit development packages.
Local limits must be evaluated each time the NJPDES permit is renewed and NJDEP has a
protocol for POTWs to follow to conduct the evaluation.

NJPDES Discharge to Surface Water (i.e., non-stormwater, individual) permits are issued by
the Surface Water Section in the Bureau of Surface Water and Pretreatment Permitting. For all
POTW surface water permits being renewed, including non-approved programs, an internal
draft is shared with the Pretreatment Unit. The Pretreatment Unit reviews the pretreatment
language to ensure the correct pretreatment language is included. The Pretreatment Unit is
also copied on the draft and final permits to ensure that the language is correct.

For this PQR, EPA staff reviewed documentation for two pairs of POTW-approved pretreatment
programs and industrial users selected by NJDEP: the Cumberland County Utility
Authority (CCUA) (permit NJ0024651) and Innovation Foods, LLC, and the Rockaway Valley
Regional Sewerage Authority (RVRSA) (permit NJ0022349) and Anthony & Sons Bakery (see
Table 2 and Table 3). The NPDES application, permit and fact sheet, 2021 Pretreatment Annual
Report, the most recent Pretreatment Audit Report (conducted by NJDEP), and the sewer use
ordinances9 were reviewed. For each industrial user, the industrial user permit, industrial user
fact sheet, and most recent pretreatment inspection report were reviewed.

Table 3. CCUA and RVRSA Pretreatment Program Overview

Permittee

Permit No.

Approved

Design Flow

No. of

No. of Food

Controls on





Pretreatment

Average

SlUs1

Processors1

Conventional





Program?

(MGD)





Pollutants or
Nutrients in sewer
use ordinance?

8	New Jersey Department of Environmental Protection Bureau of Pretreatment & Residuals

Pretreatment Program SOP for Approved Industrial Pretreatment Program (IPP) Audit Frequency Determination.

9	For RVRSA, the Sewer Use Ordinance is located at https://rvrsa.org/wp-content/uploads/FINAL-Addendum-to-
Service-Rules-2017-219493x9DC53.pdf and for CCUA the Sewer Use Ordinance is located at https://ccua.info/wp-
content/uploads/2018/08/Sewer-Use-Rules-updated-1.18.18.pdf.

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Cumberland County
Utility

Authority (CCUA)

NJ0024651

Yes

7.0

7

1

Limits for BOD and
TSS. No surcharges.

Rockaway Valley
Region Sewerage
Authority (RVRSA)

NJ0022349

Yes

2.8

15

2 SIU, 1IU

Limits for BOD, TSS,
and

Ammonia. Surcharge
for CBOD, TSS, and
Ammonia.

Table 4. Industrial User Overview

Facility
Name

Permit
Number

Receiving
POTW

Type of Food
Processor

Classification by
POTW

Average Process
Wastewater
Discharge
[gallons per day
[gpd])

Monitored
Pollutants

Anthony &
Sons Bakery

No Permit
Number

RVRSA

Large
Commercial/
Retail Bakery

"Other
Regulated" (non-

categorical)
Industrial Users:

6,000'

Limits: CBOD, TSS,
ammonia, pH, Oil and
Grease, TPHC,
copper, lead,
molybdenum, nickel,
and zinc. Report:
Flow, BOD, TDS, and
total phosphorus.

Innovation
Foods, LLC

#A009

CCUA

Fruit juice and
related
products.

SlU/Minor

8,0002

Flow, COD, TSS, Oil
and Grease, and pH.

1	Based on information included in the industrial user's permit and fact sheet.

2	Based on information included in the industrial user's fact sheet, pretreatment annual report and industrial user's
permit.

NPDES Permit Application

EPA's Application Form 2A Section F requires identification of industrial user discharges per 40
CFR 122.21(j)(6)(i) and (ii); NJDEP has adopted an alternative New Jersey-specific form10 in their
permit application. The "Application Completeness Checklist: NJPDES/Discharge to Surface
Water" at the end of the permit application states:

Form SIU-1: Submit one form for each Significant Indirect User (SIU) not previously
served by the applicant and reported to the Department. If there is no such SIU, or the
treatment system is privately owned and operated, submit one copy of the form
indicating NONE in response to the request for "User Name".

10 Form SIU-112/02: New Jersey Department of Environmental Protection Division of Water Quality Significant
Indirect User Discharges and RCRA/CERCLA Wastes.

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While EPA's Application Form 2A Section F requires information on all industrial users, New
Jersey only requires information on new users, according to the Application Completeness
Checklist. EPA was not provided information on existing users from previous permit application
submissions. Since there were no new industrial users, CCUA did not complete the NJDEP Form
SIU-112/02. Elsewhere in CCUA's 2014 permit application, CCUA did include the number of
industrial users (lUs) in the pretreatment program, which was six. Since then, the number of lUs
had increased to seven in the 2020 pretreatment annual report, along with zero ClUs. But CCUA
did not provide additional information on specific lUs such as SIC codes, classifications,
addresses, etc., nor did the application identify which lUs discharge food wastes.

In the RVRSA's 2012 permit application, Section 19 includes the number of lUs. Form SIU-1
12/02 is included in the application but is not filled out; instead, the applicant entered "See
Attachments" on the first line. The attachment presents information on SlUs but does not
address all the elements included in the form. The attachment's table includes data on the lUs,
including the average daily volume of wastewater discharged (without specifying the amount
contributed by process flow and non-process flow) and the discharge limits for each IU.
However, marginally legible bold type denotes categorical limits and non-bold type denotes
local limits in the table. The table does not identify for categorical industrial users (ClUs), the
category and subcategory. In addition, the table does not provide the principal products and
raw materials of the SIU that affect or contribute to the SlU's discharge.

In lieu of providing information on SlUs in the permit application, the NJDEP Pretreatment
Program includes a pretreatment requirement/condition in all POTWs' NJPDES permits to
prepare and submit an annual pretreatment program report consisting of a listing of all SlUs for
POTWs with non-approved pretreatment programs and a listing of regulated lUs for POTWs
with approved pretreatment programs. Therefore, the NJDEP Pretreatment program does not
rely on the POTW's NJPDES permit application submission which is every 5 years or longer to
obtain the inventory of POTWs' SlUs. This option is allowable according to 40 CFR
122.21(j)(6)(iii) which states that information required in 40 CFR 122.21(j)(6)(i] and (ii] may be
waived by the Director for POTWs with pretreatment programs if the applicant has submitted
either of the following that contain information substantially identical to that required in those
paragraphs: (A) An annual report submitted within one year of the application; or (B) A
pretreatment program submitted within one year of the application.

One option is to include the most recent information on lUs provided in the annual reports as
an attachment to the NPDES permit application so that the permit application includes,
independently of other documents, all the required information. To reiterate, the requirement
is that the POTWs are supposed to provide the following information in the permit application
for each SIU, as defined at 40 CFR 403.3(v), that discharges to the POTW:

•	Name and mailing address,

•	Description of all industrial processes that affect or contribute to the SlU's
discharge,

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•	Principal products and raw materials of the SIU that affect or contribute to the
SlU's discharge,

•	Average daily volume of wastewater discharged, indicating the amount
attributable to process flow and non-process flow,

•	Whether the SIU is subject to local limits,

•	Whether the SIU is subject to categorical standards, and if so, under which
category(ies) and subcategory(ies), and

•	Whether any problems at the POTW (e.g., upsets, pass through, interference)
have been attributed to the SIU in the past four and one-half years.

POTW NPDES Fact Sheet

One of most important components of the administrative record is the permit fact sheet or
statement of basis. The NPDES regulations at 40 CFR 124.8 require both state and EPA
permitting authorities to prepare a fact sheet for draft permits for certain types of regulated
facilities. The fact sheets must be prepared to accompany the draft permits for all major NPDES
facilities and where there is widespread public interest. The requirements for the content of the
fact sheet are established in 40 CFR 124.8 and 124.56. 40 CFR 124.8(b) states that "...The fact
sheet shall include, when applicable: ...(2) The type and quantity of wastes, fluids, or pollutants
which are proposed to be or are being treated, stored, disposed of, injected, emitted, or
discharged."

Federal Regulations are not prescriptive of what needs to be included in a fact sheet with
regard to pretreatment program-related information. That said, current regulations (40 CFR
124.56) require that fact sheets include information regarding the type of facility or activity
permitted, the type and quantity of pollutants discharged, the technical, statutory, and
regulatory basis for permit conditions, the basis and calculations for effluent limits and
conditions, the reasons for application of certain specific limits, rationales for variances or
alternatives, contact information, and procedures for issuing the final permit. EPA suggests that
the following elements be included in the NPDES Fact Sheet in order to make informed
decisions and a sound technical basis during NPDES permit development.

Both POTW NPDES fact sheets reviewed for pretreatment as part of this PQR included the
following:

•	The approval dates of the approved POTW pretreatment program, and

•	Information on their local limits. RVRSA has adopted local limits

for BOD/CBOD, TSS, and ammonia, while CCUA has local limits for CBOD/BOD
and TSS. Neither program has adopted local limits for phosphorus and nitrogen.

Both POTWs' NPDES fact sheets are lacking some information needed to fully describe
circumstances of the facility and/or permit as follows:

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•	POTW pretreatment program modification dates; either there were
no modifications, or the dates were not included.

•	Whether hauled waste is accepted by the POTW.

•	The identity of contributing industrial dischargers and their characteristics. In
addition, the source of the information regarding industrial dischargers should
be identified in the NPDES fact sheet (such as NPDES permit application, annual
report, NPDES inspection, or TRI/DMR11 pollutant loading tool, other...).

It also would be helpful to include the following information in the fact sheet:

•	Whether the POTW has a compliance history of violations attributed to flow or
strength of wastewater from industrial discharge(s), or, otherwise, if this is not
the case. However, this information can be obtained from annual pretreatment
reports and pretreatment audits.

•	CCUA does not have the flow diagram in the NPDES permit application nor is
information provided in the CCUA POTW fact sheet which describes where food
processing waste is introduced into the POTW. On the other hand, the
RVRSA NPDES permit application does have a flow diagram which indicates that
wastewater is sent to the headworks via the collection system, and it is surmised
(but not explicitly stated) that the food processing waste is introduced to the
POTW via the collection system to the plant's headworks. NJDEP could either
request flow diagrams from the POTW or, based on the NPDES permit
application and/or pretreatment annual reports, include in the fact sheet a table
of industrial users and whether their wastewater discharge is sent to the
headworks via the collection system or hauled by truck to the POTW intake, or
hauled by truck to a location other than the headworks (e.g., introduced to
digester).

•	Identification of food processors that are SlUs or lUs based on the annual
pretreatment reports and/or the NJDPES permit applications.

POTW Permit Review

The permits for both pretreatment POTWs contain secondary treatment standards in
accordance with 40 CFR 133.102.

The RVRSA NPDES permit imposes phosphorus and ammonia limitations and reporting only
monitoring requirements for nitrogen-nitrate in the effluent. For BOD and TSS, the influent and
effluent monitoring is conducted twice per week, while the effluent is monitored for ammonia
and nitrogen-nitrate three times per week and phosphorus is monitored four times per
month. The CCUA NPDES permit only imposes ammonia limitations and once-per-week effluent
monitoring. The sampling frequency of influent and effluent for BOD and TSS is twice per week;
limits are established for effluent and percent removal while influent results are reported only
(but are used to calculate percent removal).

11 Toxics Release Inventory (TRI) and Discharge Monitoring Report (DMR)

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The NPDES permits require the POTWs to implement approved Pretreatment Programs per 40
CFR 403.8. The NPDES permits require a written technical evaluation of the need to revise local
limits following permit issuance or reissuance as required under N.J.A.C. 7:14A-19.7(f) (per 40
CFR 122.44(j)(2)(ii)) within 6 months of the permit being issued. According to NJDEP staff, any
timeline for local limit revision would be established based on discussions between NJDEP and
the POTW; henceforth, the timeline would not be included in the permit. Local limits have been
adopted for CBOD, TSS and ammonia by RVRSA, and for BOD and TSS by CCUA.

The NPDES permits also require the submittal of an annual pretreatment report (per 40 CFR
403.12(i)).

Neither POTW was granted an adjustment to the secondary treatment standards per 40 CFR
133.103(b)12 [i.e., limits for BOD and TSS different from 40 CFR 133.102]. However, this is an
option that the POTWs could pursue. If NJDEP opts to grant adjustments, information and
calculations upon which the adjustments were made should be documented in the NPDES
permit fact sheet.

Based on the information available, EPA cannot determine whether NJDEP includes language in
NPDES permits, when warranted, such as a condition to develop and enforce local limits or
require the POTW to evaluate treatment plant operation to ensure no recurrence per 40 CFR
403.5(c)(2). However, per N.J.A.C. 7:14A-19.7(d), any development of local limits is required to
be conducted under an NJDEP approved workplan. In addition, this information would be
included as part of the required annual reporting. Therefore, NJDEP has a mechanism outside of
the NPDES permitting process which requires POTWs with a compliance history of violations
due to industrial dischargers to develop local limits.

Neither of the NPDES permits:

• Requires notification and impact assessment of significant changes in industrial
flow or character in accordance with 40 CFR 122.42(b)13. This could be in the
form of a reporting requirement when POTWs inform NJDEP of changes or new
pollutants being discharged to the system. This could either be included in the

12	Adjustment to secondary treatment standards may be granted if the industrial process flow or loading exceeds
10% of the POTW design flow or loading and not greater than those that the industry would be subject to if a
direct discharger.

13	All POTWs must provide adequate notice to the Director of the following:

•	Any new introduction of pollutants into the POTW from an indirect discharger which would be subject to
section 301 or 306 of CWA if it were directly discharging those pollutants.

•	Any substantial change in the volume or character of pollutants being introduced into that POTW by a
source introducing pollutants into the POTW at the time of issuance of the permit.

•	Adequate notice shall include information on the quality and quantity of effluent introduced into the
POTW.

•	Adequate notice shall include information on any anticipated impact of the change on the quantity or
quality of effluent to be discharged from the POTW.

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Pretreatment Annual Report (requirements are in Section F.10. of the NPDES
permit) or a separate requirement to inform NJDEP of any changes within a
specific predetermined amount of time.

•	Provides the approval and most recent modification date(s) of the approved
pretreatment program.

•	Requires an updated list of pollutants or information on significant changes in
pollutant loadings and flows; however, the permits do require an updated user
inventory to be included in the Pretreatment Annual Report.

If a POTW cannot meet its permit limits or experiences operational issues due to loadings from
food processing industries, NJDEP could opt to add optional clauses in the POTW's NPDES
permit, including:

•	Require reporting of industrial discharge flow volume (and changes) or reporting
of industrial batch discharges (including cleaning processes, boiler blowdown,
seasonal changes, etc.).

•	Special conditions to control or monitor the indirect food processing waste
stream.

•	Internal pollutant quality monitoring locations and internal pollutant limitations.

•	The development and enforcement of any Best Management Practices (BMPs)
specific to the food processing facility or waste stream (e.g., discharge
equalization, slug or spill control plan, monitoring and maintenance of grease
traps).

•	Specific controls on or monitoring of the food processing discharge

(i.e., including sampling at an "internal"/collection system monitoring point).
These could include methods to control the food processing industry via local
limits, surcharges, permits, and/or spill or slug control plans.

Innovative/Voluntary Programs

NJDEP staff stated that the two POTWs do not participate in any voluntary programs to reduce
food waste or reuse food waste for energy generation. NJDEP stated that the two POTWs did
not implement innovative technologies or techniques such as, but not limited to, (1) struvite
nitrogen or phosphorus removal technology and (2) energy co-generation technology in
conjunction with either restaurant grease collection or hauled food processing collection.

Industrial User Control Mechanism (Permit) and Fact Sheet

NJDEP did not provide the industrial permit application forms for Anthony and Sons Bakery
(RVRSA) or Innovation Foods (CCUA). For both lUs, an individual control mechanism (aka
industrial user permit) was used. CCUA's IU fact sheet for Innovation Foods did not contain
much information and could be significantly improved. The Anthony and Sons Bakery fact sheet
was acceptable, and included information on a recent approved variance accorded to the
bakery:

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"Since Anthony and Sons Bakery desires to discharge a CBOD5 concentration in excess of
500 mg/L, Anthony & Sons Bakery has submitted a variance application on June 30,
2020, requesting an increase in CBOD5 concentration to a daily maximum limit of 3,000
mg/L. This variance request was approved by the RVRSA Board by Resolution #20-069
on August 13, 2020."

The Innovation Foods permit does not impose nutrient effluent limitations but does have limits
and requires monthly flow-proportional composite samples for COD and TSS. CCUA does not
impose surcharge values. Meanwhile, the Anthony and Sons Bakery permit imposes
ammonia and TSS limitations and a requirement to report only for phosphorus and BOD; all
of these parameters require a time-proportional composite sample monthly. For RVRSA,
surcharge values are implemented for BOD, TSS and Ammonia.

The following items were included in both industrial user permits:

•	Statement of duration (< 5 years)

•	Self-monitoring requirements, including an identification of pollutants to be
monitored, sampling locations and/or discharge points.

•	Sampling requirements

•	Reporting requirements (including all monitoring results)

•	Recordkeeping requirements

•	Indication of parameters for which there are surcharge values (for RVRSA; CCUA
does not assess surcharges)

•	Notification of spills, bypasses, upsets, etc.

•	The basis for the limitation and/or monitoring requirement in RVRSA's Anthony
and Sons Bakery permit; there are no such requirements applied to Innovation
Foods by CCUA.

Neither the CCUA nor the RVRSA permit included the requirement for the IU to notify the
POTW of a change affecting the potential for a slug discharge per 40 CFR 403.8(f)(2)(vi).

The following items were missing from CCUA's Innovation Foods permit:

•	A permit issuance date: the letter at the beginning of the permit is not dated. As
a result, we cannot determine if the Innovation Foods permit was issued before
or after its start date. The requirement is that the issuance date, the permit
effective date, and the permit expiration date be clearly stated in the permit.

•	Statement of non-transferability without prior notification/approval (40
CFR 403.8(f)(l)(iii)(B)(2)).

•	A map or schematic of the facility which includes the sampling and effluent
discharge points; however, the narrative in the permit adequately identifies the
location of the sampling point.

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The compliance schedule language in the Innovation Foods permit issued by CCUA is confusing.
In Section C.2. of the permit, the compliance schedule language seems to apply to only
ClUs but the permittee is not a major SIU nor a CIU and is identified as a SlU/minor. It is unclear
if the language is included because it pertains to Innovation Foods, or if it is boilerplate
language that is included in all permits even if the language does not apply to the permittee. In
contrast, RVRSA has the appropriate language regarding compliance schedules in its permit.

CCUA's permit does not included a 24-hour notification of violation/resample requirement per
40 CFR 403.12(g)(2) nor slug discharge control plan conditions, if determined by the POTW to
be required. The CCUA permit has a requirement for a slug discharge control plan, but no
instructions of what should be included in the plan per 40 CFR 403.8(f)(l)(iii)(B)(6) and
403.8(f)(2)(vi). Meanwhile, RVRSA's permit includes both requirements.

CCUA's Innovation Foods permit included a notice of slug loadings in the IU permit, but RVRSA's
Anthony and Sons Bakery permit does not properly include a "Notice of Slug Discharges" per 40
CFR 403.12(f). Section 9.E. of Anthony and Sons Bakery permit (Notification of Non-Compliance
or Accidental Discharge: Protection from Accidental Discharge) has detailed information of
what should be in a slug discharge control plan (i.e., procedures for notification of slug loading)
for significant industrial users. But the slug discharge control plan requirement in 40 CFR
403.12(f)14 applies to all users, and the language in RVRSA's IU permit does not contain
adequate language. In addition, Section 9.A. of the permit has notification of non-compliance or
accidental discharge, but the permit does not contain a definition of what is accidental
discharge. While the permit includes information regarding notice of slug discharge, the
applicability of the slug discharge control plan and the notice could be presented more clearly.

RVRSA's Anthony and Sons Bakery fact sheet does not offer a rationale as to why time-
proportional rather than a flow-proportional monthly sampling is accepted. Per 40 CFR
403.12(g)(3):

"...Grab samples must be used for pH, cyanide, total phenols, oil and grease, sulfide, and
volatile organic compounds. For all other pollutants, 24-hour composite samples must
be obtained through flow-proportional composite sampling techniques, unless time-
proportional composite sampling or grab sampling is authorized by the Control
Authority. Where time-proportional composite sampling or grab sampling is authorized
by the Control Authority, the samples must be representative of the Discharge and the
decision to allow the alternative sampling must be documented the Industrial User file
for that or facilities..."

14 403.23(f): All categorical and non-categorical Industrial Users shall notify the POTW immediately of all discharges
that could cause problems to the POTW, including any slug loadings, as defined by § 403.5(b), by the Industrial
User.

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RVRSA's Anthony and Sons Permit Section 15 includes most applicable civil penalties and
Section 16 applicable criminal penalties; however, Section 15 does not state what the minimum
daily penalty should be per 403.8(f)(l)(iii)(B)(5) and 403.8(f)(l)(vi)(A).15

RVRSA's Anthony and Sons Bakery permit does not have language regarding notification of
significant change in discharge (per 40 CFR 403.12(j)) while CCUA's IU permit includes this
language.

Action Items

15 40 CFR 403.8(f)(l)(iii)(B)(5) states:

"Statement of applicable civil and criminal penalties for violation of Pretreatment Standards and requirements,
and any applicable compliance schedule. Such schedules may not extend the compliance date beyond applicable
federal deadlines;"

And 403.8(f)(l)(vi)(A) states:

"Obtain remedies for noncompliance by any Industrial User with any Pretreatment Standard and Requirement. All
POTW's shall be able to seek injunctive relief for noncompliance by Industrial Users with Pretreatment Standards
and Requirements. All POTWs shall also have authority to seek or assess civil or criminal penalties in at least the
amount of $1,000 a day for each violation by Industrial Users of Pretreatment Standards and Requirements."

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• NJDEP must ensure that permits require notification and an impact
assessment of significant change in industrial flow or character in
accordance with 40 CFR 122.42(b) along with an updated list of
pollutants or information on significant changes in pollutant loading
and flows. In addition, the NPDES permit should include the approval
and most recent modification date(s) of the approved pretreatment
program.

Essential

• NJDEP must ensure that all IU permits include:
o The requirement of the IU to notify the POTW of a change affecting
the potential for a slug discharge per 40 CFR 403.8(f)(2)(vi),
o A permit issuance date along with the permit start and end date,
o A statement of non-transferability without prior
notification/approval per 40 CFR 403.8(f)(l)(iii)(B)(2),
o A 24-hour notification of violation/resample requirement per 40
CFR 403.21(f),

o Details on what minimum elements should be included in a slug
discharge control plan per 40 CFR 403.8(f)(2)(vi),
o Minimum daily civil penalties per 40 CFR 403.8(f)(l)(vi)(A), and
o Requirement for notification of significant change in discharge per
40 CFR403.12(g)(3).

• NJDEP must require that the RVRSA requires flow-proportional
monthly sampling in their permits or document within the IU's fact
sheet the basis for accepting time-proportional sampling, as required
by 40 CFR 403.12(g)(3).

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Recommended

•	NJDEP can opt to add an addendum to permit applications that
includes data on IUs from the previous year pretreatment annual
reports so that the NJPDES Permit Application includes,
independent of other documents, the information required by
EPA's Application Form 2A Section F that requires identification
of Industrial User Discharges per 40 CFR 122.21(j)(6)(i) and (ii)
and 40 CFR403.3(v).

•	NJDEP can opt to include additional information in its NPDES
fact sheets. The NPDES fact sheets are missing several
components such as POTW pretreatment modification dates, a
list of the POTW's compliance history of violations, whether the
POTW accepts hauled waste, wastewater flow diagrams, and a
list of contributing industrial dischargers and their
characteristics including whether they are minor-IUs, SIUs, or
CIUs.

•	NJDEP can include language in the NPDES permit requiring the
POTW to provides the approval date and most recent
modification date (s) of the approved pretreatment program.

•	If a POTW cannot meet its permit limits due to loading from
food processing industries, NJDEP can opt to include additional
requirements in the POTWs NPDES permit regarding
monitoring sampling, and reporting of food processing wastes
and implementation of BMPs.

•	NJDEP should encourage POTWs to participate in voluntary
programs to reduce food waste or reuse food waste for energy
generation.

•	POTWs should keep the most recent IU permit on file, and it
should be made available to NJDEP when requested.

•	IU Permits should only include the compliance schedule clause if
it applies to the particular IU as required by 40 CFR
403.8(f)(l)(iv). Clauses which do notpertain to that particular IU
should not be included in the IU permit.

C. Small Municipal Separate Storm Sewer System (MS4) Permit
Requirements

Background

As part of this PQR, EPA reviewed the NJDEP Highway Agency Stormwater General Permit R12
(NJ0141887), issued on November 29, 2019, for consistency with the Phase II stormwater
permit regulations. In 2016 EPA updated the small MS4 permitting regulations to clarify:

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•	The procedures to be used when coverage is by general permits (see 40 CFR 122.28(d));

•	The requirements that the permit establish the terms and conditions necessary to meet
the MS4 permit standard (i.e., "to reduce the discharge of pollutants from the MS4 to
the maximum extent practicable (MEP), to protect water quality, and to satisfy the
appropriate water quality control measures, reporting, and, as appropriate, water
quality requirements" (see 40 CFR 122.34(a) and (b)); and

•	That permit terms must be established in a "clear, specific, and measurable" manner
(see 40 CFR 122.34(a)).

Program Strengths

The permit's stormwater management requirements and the stormwater pollution prevention
plan are prescriptive.

The state's Statewide Basic Requirements (six minimum control measures) are prescriptive,
clear, specific, and measurable.

Attachment A of the permit provides the measurable goals for the six minimum control
measures, and stormwater facility maintenance. These goals are enforceable in the permit,
clear, specific, and measurable.

Attachment B of the permit provides a list of public education and outreach activities with a
point system for each activity. The permittee needs to meet a minimum number of points to
meet the requirement of these two minimum control measures.

Attachment E of the permit provides best management practices for maintenance yards which
are clear, specific, and measurable.

Areas for Improvement

The permits sections forTMDLs and Additional Requirements should be strengthened. EPA R2
believes that these sections that address TMDLs, impaired waters, and pollutants of concern
are the least prescriptive sections of the permit. The State of New Jersey Council on Local
Mandates16 may consider the removal of Additional Measures addressing TMDLs (Part 4 Tier A
Municipal General MS4 Permit, Section D) if the state has not provided funds to the MS4
permittee for the implementation of the additional measures. NJDEP should include a
requirement in MS4 permits to use BMPs that would directly address specific pollutants of
concern and explore options to overcome the unfunded mandate as a barrier to
implementation.

There currently are no standard procedures that involve EPA in the stormwater permit
development process or notify EPA of impending permit actions. This has made it difficult at
times for EPA to participate in permit development and address concerns in a cooperative
manner prior to permit issuance. It would be beneficial to have a standard procedure for

16 More information can be found at https://www.ni.gov/localmandates/general/.

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regular coordination between EPA and NJDEP stormwater staff for the permit development and
issuance process.

Action Items

•	NJDEP should strengthen their program by providing sufficient
detail in the permit to implement BMPs and other strategies
regarding TMDLs, impaired waters, and pollutant of concerns.

•	NJDEP should coordinate earlier, more often and regularly with
EPA throughout the general permit development process.

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V. PERMITS REVIEWED FOR 2021 NJPQR

Table 5. NJPDES Permits Reviewed for the 2021 NJ PQR

NJ0024708 Bayshore Regional Sewerage Authority
Wastewater Treatment Plant

NJ0024694 Monmouth County Bayshore Outfall

Authority
NJ0002089 IMTT- Bayonne
NJ0024716 Town of Phillipsburg

NJ0024911	Butterworth Water Pollution Control
Plant

NJ0062391	Wheelabrator Gloucester Co., LP.

NJ0005240	Bridgeport Disposal, LLC.

NJ0024821	Francis S. Doyle Jr. Treatment Facility

NJ0000809	Hopewell Business Campus

NJ0020923	Trenton Sewer Utility

NJ0024651	Cumberland County Utilities Authority

NJ0022349 Rockaway Valley Regional Sewerage
Authority

NJ0025411 Hopewell Creek Generating Station
NJ0141887 Highway Agency Stormwater General
Permit

Core review,

Nutrients in non-TMDL waters
Core review,

Nutrients in non-TMDL waters
Core review
Core review,

Nutrients in non-TMDL waters
Core review,

Nutrients in non-TMDL waters

Core review

Core review

Core review

Core review

Core review

Core review, POTW permits with
food processor contributions
Core review, POTW permits with
food processor contributions
Core review
Small MS4

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¥1. 2016 NJ PCJR ACTION ITEM REVIEW

This section provides a summary of the main findings from the last PQR and provides a review of the status of the state's efforts in
addressing the action items identified during the last PQR, conducted in 2016. As discussed previously, during the 2012-2017 PQR
cycle, EPA referred to action items that address deficiencies or noncompliance with respect to federal regulations as "Category 1".
EPA is now referring to these action items going forward, as Essential. In addition, previous PQR reports identified recommendations
to strengthen the state's program as either "Category 2" or "Category 3" action items. EPA is consolidating these two categories of
action items into a single category: Recommended.

Table 6. Essential Action Items Identified During the 2016 PQR

Basic Facility
Information and
Permit Application

Technology-based
Effluent Limitations

Technology-based
Effluent Limitations

Nutrients

Nutrients

Nutrients

NJDEP must ensure that a permit is not administratively continued if the permit
application as not submitted 180 days prior to expiration of the existing permit to
be consistent with EPA regulations at 40 CFR 122.22(c) and 122.21(d) or, if applicable,
NJDEP must ensure that a proof of an extension was included in the administrative
record.

NJDEP must include a clear discussion in fact sheets for non-POTWs subject to ELGs
regarding ELG applicability (or why a seemingly-applicable ELG does not apply) in order to
be consistent with EPA regulations at 40 CFR 124.56.

NJDEP must ensure that when effluent limitations are carried forward from the previous
permit, the basis for the effluent limitation is discussed in the fact sheet in order to be
consistent with 40 CFR 124.56.

NJDEP must ensure that fact sheets consistently include a reasonable potential analysis for

all nutrient related parameters to be consistent with EPA regulations at 40 CFR

124.56.

NJDEP must ensure that fact sheets address how downstream impacts, such as algal
blooms and dissolved oxygen impairments, were considered in the reasonable potential
analysis, and if necessary, in limit development to be consistent with federal
regulations at 40 CFR 124.56.

NJDEP must ensure that the monitoring requirements specified in the permit are sufficient
to provide a representative sample for use in future reasonable potential calculations and
limit development to be consistent with federal regulations at 40 CFR 122.44(i).

Resolved. This action item
was erroneously established
in the 2016 PQR.

Resolved.

Resolved.

In progress. This is also
being addressed as a 2021
PQR Action Item.
In progress. This is also
being addressed as a 2021
PQR Action Item.

Resolved.

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Pretreatment	NJDEP must use ICIS to enter pretreatment data to improve consistency and

transparency as soon as possible, but in no case later than the agreed upon action plan
included in the 2017-2019 Performance Partnership Agreement, to be consistent
with EPA regulations at 40 CFR 127.21.

Stormwater

Stormwater

Stormwater
((instruction
Activity

Stormwater - Tier
A MS4

Stormwater - Basic
Industrial

Reasonable
Potential

Reasonable
Potential

Power Plants

NJDEP must ensure that the permit provisions ensure that the WQS will be met in the
receiving water to be consistent with EPA regulations at CWA
Section 301(b)(1)(C).

NJDEP must include specific requirements for sites that will discharge to impaired waters
to be consistent with 40 CFR 122.34(b)(6)(e).

NJDEP must ensure that the fact sheet includes contact information to request additional
information to be consistent with EPA regulations at 40 CFR 124.8(b)(7).

NJDEP must ensure that the permit specifies which SIC codes are applicable and which
regulated industries are required to receive coverage under the permit to be
consistent with EPA regulations at 40 CFR 122.44(d)(l)(vii)(B).

NJDEP must ensure that the permit specifies which SIC codes are applicable and which
regulated industries are required to receive coverage under the permit to be
consistent with EPA regulations at 40 CFR 122.26 and 122.41.

NJDEP must ensure that effluent limitations are established in permits for all parameters
whose discharge causes, has the reasonable potential to cause, or contribute to an
excursion of applicable WQS to be consistent with EPA
regulations at 40 CFR 122.41(d).

NJDEP must, for all pollutants of concern, evaluate whether a discharge causes or
contributes or has the reasonable potential to cause or contribute to an exceedance of
WQS to be consistent with EPA regulations at 40 CFR 122.44(d), including where there is
limited or no data available.

NJDEP must ensure that fact sheets clearly document the basis and schedule for CWA
316(b) requirements for impingement and entrainment to be consistent
with EPA regulations at 40 CFR 125.98.

In progress. The

Pretreatment program has
been entering data but
there is a backlog due to the
lack of trained staff able to
complete an audit.
Additional staff members
are being trained.
In progress.

In progress.

Resolved.

In progress.

In progress.
Resolved.

In progress. This is also
being addressed as a 2021
PQR Action Item.

In progress.

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Power Plants

Power Plants

NJDEP must ensure that the development of CWA 316(b) decisions consider the impacts In progress,
to threatened and endangered species to be consistent with EPA regulations at 40
CFR 125.94.

NJDEP must ensure that the requirements for cooling water intake structures are	In progress,

consistent with the revised Final Regulation to Establish Requirements for Cooling
Water Intake Structure at Existing Facilities at 40 CFR 122 and 125.

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Table 7. Recommended Action Items Identified During the 2016 PQR

Basic Facility
Information and
Permit Application
Basic Facility
Information and
Permit Application
Special and
Standard
Conditions
Special and
Standard
Conditions
Special and
Standard
Conditions
Administrative
Record

Administrative
Record

Administrative
Process

Pretreatment

Stormwater

Stormwater

NJDEP should include standard authorization-to-discharge, as described in 40 CFR
122.1(b)(1), terminology to be included on the first page of the NJPDES permit.

NJDEP should include a zip code in the address provided for the discharging facility in the
permit.

NJDEP should cite the specific NJAC provisions in permits that correspond with the standard
conditions required by 40 CFR 122.41 and 122.42.

NJDEP should cite the specific NJAC provisions in permits that establish notification
requirements for POTWs, to clearly capture these requirements.

NJDEP should cite the specific NJAC provisions in permits that establish the notification
requirements for non-POTWs, to more clearly capture these requirements.

NJDEP should include the WQBEL Analysis Data Sheets or, at minimum, clearly reference
them in the administrative record.

NJDEP should include or reference the calculations used to develop any TBELs established in
the permit in the administrative record.

NJDEP should file the proof of public notice in the permit file with the remainder of the
administrative record.

NJDEP should streamline the pretreatment reporting requirement into a single report that
covers a consistent monitoring period.

NJDEP should establish specific requirements for corrective action, including timeframes for
correcting deficiencies in all general permits.

NJDEP should specify in the permit the required qualifications or training of the individual
conducting inspections.

In progress. This is also
being addressed as a
2021 PQR Action Item.
Resolved.

In progress. This is also
being addressed as a
2021 PQR Action Item.
In progress. This is also
being addressed as a
2021 PQR Action Item.
In progress. This is also
being addressed as a
2021 PQR Action Item.
In progress.

In progress.

Resolved.

Resolved. This action
item was erroneously
included in the 2016 PQR.
Resolved.

Resolved.

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Stormwater -

Construction

Activity

Stormwater -

Construction

Activity

Stormwater
((instruction
Activity
Stormwater
((instruction
Activity

NJDEP must establish a requirement that the permittee must provide a paper submission 30 Resolved,
days prior to the commencement of "construction activities", rather than the
"commencement of land disturbance", to be consistent with the federal
Construction General Permit and 40 CFR 122.28.

NJDEP should specify in the permit basis stormwater and/or NJPDES training requirements In progress,
for permittees or operators to ensure that an individual on site has sufficient
knowledge of stormwater requirements and practices.

NJDEP should define "completed" and "operating entity" in the permit.	In progress.

EPA suggests that NJDEP include related federal endangered species requirements in the In progress,
permit.

Stormwater
((instruction
Activity
Stormwater
((instruction
Activity

Stormwater - Basic
Industrial

Reasonable
Potential

Power Plants

Combined Sewer
Overflows

Combined Sewer
Overflows

NJDEP should establish uniform requirements to terminate coverage and should specify In progress,
what site stabilization criteria are required prior to termination.

NJDEP should require inspection every 7 days in the permit, rather than weekly, to ensure In progress,
adequate implementation and enforcement.

NJDEP should include requirements in the permit for controls to be implemented at all	In progress,

industrial site to manage stormwater runoff, salt storage, and vehicle dust reduction and
should specify a frequency for maintenance of control measure.

In the case of limited data sample size, NJDEP should either use EPA's TSD procedures for Resolved,
limited data or ensure that a representative data set is available to be consistent
with EPA regulations at 40 CFR 122.44(d) and EPA guidance in the Technical Support
Document for Water Quality-based Toxics Control.

NJDEP must ensure that all coal-fired power plant permits reflect the revised ELGs in order Resolved,
to be consistent with EPA regulations at 40 CFR 423, upon reissuance.

NJDEP Should require in the permit that a thorough evaluation of a sufficient range of	Resolved,

control alternatives is conducted in accordance with EPA's CSO Control Policy.

NJDEP should require in the permit that a comprehensive monitoring program be	Resolved,

developed and implemented in accordance with EPA's CSO Control Policy.

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Combined Sewer
Overflows

Combined Sewer
Overflows

NJDEP should adopt a multiple discharger variance for arsenic in the State's WQS that
conforms with federal regulations at 40 CFR 131.14.

The permit should include a requirement to develop and submit a report documenting the
implementation of the nine minimum controls, as per the CSO Control Policy.

NJDEP should consider requiring permittees to submit ambient monitoring data in an
electronic format suitable for inclusion in state water-quality systems.

Arsenic

In progress.
Resolved.

Resolved. Based on
additional research, a
multiple discharger
variance may not be the
best approach for arsenic
at this time. NJDEP
continues to research this
issue.

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2021 New Jersey Program and Permit Quality Review

VII. ACTION ITEMS IDENTIFIED DURING THE 2021 PQR

This section provides a summary of the main findings of the PQR and provides proposed action items to improve New Jersey's
NPDES permit programs, as discussed throughout sections III and IV of this report.

The proposed action items are divided into two categories to identify the priority that should be placed on each Item and facilitate
discussions between EPA Regions and states.

•	Essential Actions - Proposed "Essential" action items address noncompliance with respect to a federal regulation. EPA has
provided the citation for each Essential action item. The permitting authority is expected to address these action items in
order to comply with federal regulations. As discussed earlier in the report, prior PQR reports identified these action items as
Category 1. Essential actions are listed in Table 3 below.

•	Recommended Actions - Proposed "Recommended" action items are recommendations to increase the effectiveness of the
state's or Region's NPDES permit program. Prior reports identified these action items as Category 2 and 3. Recommended
actions are listed in Table 4 below.

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Table 8. Essential Action Items Identified During the 2016 PQR

Permit Application Requirements

TBELs for Non-POTWs

NJDEP must ensure compliance with the NPDES Application and Program Updates Rule (84 FR 3324) as
soon as possible.

Reasonable Potential and WQBELs

Standard and Special Conditions

Administrative Process

Nutrients

Nutrients

Pretreatment

Final permits with CWA section 316(b) provisions must include the technologies and monitoring
specified as BTA for compliance with the impingement mortality standard (40 CFR 125.98(c)) and the
entrainment standard (40 CFR 125.94(d)), as enforceable conditions of the final permit, as required by
40 CFR 125.98(b)(2).

NJDEP must calculate the reasonable potential of all pollutants of concern to cause or contribute to an
exceedance of WQS to be consistent with EPA regulations at 40 CFR 122.44(d). This also applies to
situations with limited or no data available, such as new facilities.

NJPDES permits must include provisions for bypass, upset, and the additional reporting requirements
for non-POTWs as required by 40 CFR 122.41(m), 122.41(n), and 122.42(a), respectively.

NJDEP must include a general description of the location of each existing or proposed discharge point
in the public notice, as required by 40 CFR 124.10(d)(vii).

NJDEP must evaluate whether a discharge causes or contributes, or has the reasonable potential to
cause or contribute to an exceedance of narrative or numeric WQS, and include numeric limits where
necessary, as required by 40 CFR 122.44(d).

NJDEP must ensure that permits are protective of downstream uses, for both numeric and narrative
nutrient criteria, including water quality criteria of other states and interstate entities such as DRBC, as
required by 40 CFR 122.44(d).

NJDEP must ensure that permit require notification and an impact assessment of significant change in
industrial flow or character in accordance with 40 CFR 122.42(b) along with an updated list of
pollutants or information on significant changes in pollutant loading and flows. In addition, the NPDES
permit should include the approval and most recent modification date(s) of the approved
pretreatment program.

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Pretreatment	NJDEP must ensure that all IU permits include:

•	The requirement of the industrial user to notify the POTW of a change affecting the potential
for a slug discharge per 40 CFR 403.8(f)(2)(vi),

•	A permit issuance date along with the permit start and end date,

•	A statement of non-transferability without prior notification/approval per 40 CFR
403.8(f)(l)(iii)(B)(2),

•	A 24-hour notification of violation/resample requirement per 40 CFR 403.21(f),

•	Details on what minimum elements should be included in a slug discharge control plan per 40
CFR 403.8(f)(2)(vi),

•	Minimum daily civil penalties per 40 CFR 403.8(f)(l)(vi)(A), and

•	Requirement for notification of significant change in discharge per 40 CFR 403.12(g)(3).

Pretreatment	NJDEP must require that the RVRSA requires flow-proportional monthly sampling in their permits or

document within the lU's fact sheet the basis for accepting time-proportional sampling, as required by
40 CFR 403.12(g)(3).

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2021 New Jersey Program and Permit Quality Review

Table 9. Recommended Action Items Identified During the 2016 PQR

Facility Information

Permit Application Requirements

TBELs for Non-POTW POTWs

NJDEP should provide clear authorization-to-discharge language, as referenced in 40 CFR 122.1(b)(1),
in all NJPDES permits.

EPA recommends that NJDEP revise the application so that the applicant can more easily identify that
the signatory requirements are met or, if necessary, provide training or resources to the necessary
staff to assist them in determining whether the application has been signed by the appropriate
individual.

NJDEP should include a specific citation to the regulation, policy, or standard when an effluent
limitation is established based on a rule or policy from outside NJDEP (i.e., the Interstate
Environmental Commission, Delaware River Basin Commission).

Reasonable Potential & WQBELs

Final Effluent Limitations

Final Effluent Limitations

EPA recommends explicitly stating in the fact sheet whether a cause, the reasonable potential to cause
or contribute to an excursion of the state's WQS analysis was completed and the results of the analysis.

NJDEP should explicitly state in fact sheets whether an effluent limitation is a TBEL or a WQBEL to more
clearly comply with 40 CFR 124.56.

In ocean discharge permits, NJDEP should specifically include requirements to collect additional
monitoring and technical information about areas of significant importance listed at 40 CFR 125.122(a)
during the permit term so the determination of no adverse effects can be completed thoroughly at
renewal.

Final Effluent Limitations

In ocean discharge permits, NJDEP should include "biological sampling" in the reopener clause as a
reason to modify or revoke a permit.

Nutrients

Nutrients

NJDEP should clarify in the impairments section whether the direct receiving water is impaired, or a
downstream segment.

NJDEP should include monitoring requirements for Total Nitrogen, particularly for dischargers to
marine water or tributaries to marine waters, such that waste load allocations may be calculated if
there is a TMDL for dissolved oxygen impairment or algal overgrowth.

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Pretreatment

Pretreatment

Pretreatment

Pretreatment

Pretreatment

Pretreatment

NJDEP can opt to add an addendum to permit applications that includes data on lUs from the previous
year pretreatment annual reports so that the NJPDES Permit Application includes, independent of
other documents, the information required by EPA's Application Form 2A Section F that requires
identification of Industrial User Discharges per 40 CFR 122.21(j)(6)(i) and (ii) and 40 CFR 403.3(v).

NJDEP can opt to include additional information in its NPDES fact sheets. The NPDES fact sheets are
missing several components such as POTW pretreatment modification dates, a list of the POTW's
compliance history of violations, whether the POTW accepts hauled waste, wastewater flow diagrams,
and a list of contributing industrial dischargers and their characteristics including whether they are
minor-IUs, SlUs, or ClUs.

NJDEP can include language in the NPDES permit requiring the POTW to provide the approval date and
most recent modification(s) date of the approved pretreatment language.

If a POTW cannot meet its permit limits due to loading from food processing industries, NJDEP can opt
to include additional requirements in the POTWs NPDES permit regarding monitoring, sampling, and
reporting of food processing wastes and implementation of BMPs.

NJDEP should encourage POTWs to participate in voluntary programs to reduce food waste or reuse
food waste for energy generation.

POTWs should keep the most recent IU permit on file, and it should be made available to NJDEP when
requested.

Pretreatment

MS4s

MS4s

IU Permits should only include the compliance schedule clause if it applies to the particular IU as
required by 40 CFR 403.8(f)(l)(iv). Clauses which do not pertain to that particular IU should not be
included in the IU permit.

NJDEP should strengthen their program by providing sufficient detail in the permit to implement BMPs
and other strategies regarding TMDLs, impaired waters, and pollutant of concerns.

NJDEP should coordinate with EPA earlier, more often and regularly with EPA throughout the general
permit development process.

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