40 CFR §122.5 Effect of a permit.
(a) Applicable to State programs, see §123.25. (1)
Except for any toxic effluent standards and prohibitions imposed under section 307 of the
CWA and "standards for sewage sludge use or disposal'' under 405(d) of the CWA,
compliance with a permit during its term constitutes compliance, for purposes of
enforcement, with sections 301, 302, 306, 307, 318, 403, and 405 (a)-(b) of CWA.However, a
permit may be modified, revoked and reissued, or terminated during its term for cause as
set forth in §§122.62 and 122.64.
(2) Compliance with a permit condition which implements a particular "standard for
sewage sludge use or disposal'' shall be an affirmative defense in any enforcement action
brought for a violation of that "standard for sewage sludge use or disposal''
pursuant to sections 405(e) and 309 of the CWA.
(b) Applicable to State programs, See §123.25. The issuance of a permit does not convey
any property rights of any sort, or any exclusive privilege.
(c) The issuance of a permit does not authorize any injury to persons or property or
invasion of other private rights, or any infringement of State or local law or
regulations.
(48 FR 14153, Apr. 1, 1983, as amended at 54 FR 18782, May 2, 1989)
§122.6 Continuation of expiring permits.
(a) EPA permits. When EPA is the permit-issuing authority, the conditions of an expired
permit continue in force under 5 U.S.C. 558(c) until the effective date of a new permit
(see §124.15) if:
(1) The permittee has submitted a timely application under §122.21 which is a complete
(under 122.21(e)) application for a new permit; and
(2) The Regional Administrator, through no fault of the permittee does not issue a new
permit with an effective date under §124.15 on or before the expiration date of the
previous permit (for example, when issuance is impracticable due to time or resource
constraints).
(b) Effect. Permits continued under this section remain fully effective and enforceable.
(c) Enforcement. When the permittee is not in compliance with the conditions of the
expiring or expired permit the Regional Administrator may choose to do any or all of the
following:
(1) Initiate enforcement action based upon the permit which has been continued;
(2) Issue a notice of intent to deny the new permit under §124.6. If the permit is
denied, the owner or operator would then be required to cease the activities authorized by
the continued permit or be subject to enforcement action for operating without a permit;
(3) Issue a new permit under Part 124 with appropriate conditions; or
(4) Take other actions authorized by these regulations.
(d) State continuation. (1) An EPA-issued permit does not continue in force beyond its
expiration date under Federal law if at that time a State is the permitting authority.
States authorized to administer the NPDES program may continue either EPA or State-issued
permits until the effective date of the new permits, if State law allows. Otherwise, the
facility or activity is operating without a permit from the time of expiration of the old
permit to the effective date of the State-issued new permit.
(48 FR 14153, Apr. 1, 1983, as amended at 50 FR 6940, Feb. 19, 1985)
§122.7 Confidentiality of information.
(a) In accordance with 40 CFR Part 2, any information submitted to EPA pursuant to these
regulations may be claimed as confidential by the submitter. Any such claim must be
asserted at the time of submission in the manner prescribed on the application form or
instructions or, in the case of other submissions, by stamping the words
"confidential business information'' on each page containing such information. If no
claim is made at the time of submission, EPA may make the information available to the
public without further notice. If a claim is asserted, the information will be treated in
accordance with the procedures in 40 CFR Part 2 (Public Information).
(b) Applicable to State programs, see §123.25. Claims of confidentiality for the
following information will be denied:
(1) The name and address of any permit applicant or permittee;
(2) Permit applications, permits, and effluent data.
(c) Applicable to State programs, see §123.25. Information required by NPDES application
forms provided by the Director under §122.21 may not be claimed confidential. This
includes information submitted on the forms themselves and any attachments used to supply
information required by the forms.
§122.21 Application for a permit (applicable to State programs, see §123.25).
(a) Duty to apply. Any person who discharges or proposes to discharge pollutants or who
owns or operates a "sludge-only facility'' and who does not have an effective permit,
except persons covered by general permits under §122.28, excluded under §122.3, or a
user of a privately owned treatment works unless the Director requires otherwise under
§122.44(m), shall submit a complete application (which shall include a BMP program if
necessary under 40 CFR §125.102) to the Director in accordance with this section and Part
124.
(b) Who applies? When a facility or activity is owned by one person but is operated by
another person, it is the operator's duty to obtain a permit.
(c) Time to apply. (1) Any person proposing a new discharge, shall submit an application
at least 180 days before the date on which the discharge is to commence, unless permission
for a later date has been granted by the Director. Facilities proposing a new discharge of
storm water associated with industrial activity shall submit an application 180 days
before that facility commences industrial activity which may result in a discharge of
storm water associated with that industrial activity. Facilities described under
§122.26(b)(14)(x) shall submit applications at least 90 days before the date on which
construction is to commence. Different submittal dates may be required under the terms of
applicable general permits. Persons proposing a new discharge are encouraged to submit
their applications well in advance of the 90 or 180 day requirements to avoid delay. See
also paragraph (k) of this section and §122.26 (c)(1)(i)(G) and (c)(1)(ii).
(2) Permits under section 405(f) of CWA. (i) POTWs with currently effective NPDES permits
shall submit the application information required by paragraph (d)(3)(ii) of this section
with the next application submitted in accordance with paragraph (d) of this section or
within 120 days after promulgation of a "standard for sewage sludge use or disposal''
applicable to the POTW's sludge use or disposal practice(s), whichever occurs first.
(ii) Any other existing "treatment works treating domestic sewage'' not covered under
paragraph (c)(2)(i) of this section shall submit an application to the Director within 120
days after promulgation of a "standard for sewage sludge use or disposal'' applicable
to its sludge use or disposal practice(s) or upon request of the Director prior to the
promulgation of an applicable "standard for sewage sludge use or disposal'' if the
Director determines that a permit is necessary to protect public health and the
environment from any potential adverse effects that may occur from toxic pollutants in
sewage sludge.
(iii) Any "treatment works treating domestic sewage'' that commences operations after
promulgation of an applicable "standard for sewage sludge use or disposal'' shall
submit an application to the Director at least 180 days prior to the date proposed for
commencing operations.
(d) Duty to reapply. (1) Any POTW with a currently effective permit shall submit a new
application at least 180 days before the expiration date of the existing permit, unless
permission for a later date has been granted by the Director. (The Director shall not
grant permission for applications to be submitted later than the expiration date of the
existing permit.)
(2) All other permittees with currently effective permits shall submit a new application
180 days before the existing permit expires, except that:
(i) The Regional Administrator may grant permission to submit an application later than
the deadline for submission otherwise applicable, but no later than the permit expiration
date; and
(3)(i) All applicants for EPA-issued permits, other than POTWs, new sources, and
"sludge-only facilities,'' must complete Forms 1 and either 2b or 2c of the
consolidated permit application forms to apply under §122.21 and paragraphs (f), (g), and
(h) of this section.
(ii) In addition to any other applicable requirements in this part, all POTWs and other
"treatment works treating domestic sewage,'' including "sludge-only
facilities,'' must submit with their applications the information listed at 40 CFR
§501.15 (a)(2) within the time frames established in paragraph (c)(2) of this section.
(e) Completeness. The Director shall not issue a permit before receiving a complete
application for a permit except for NPDES general permits. An application for a permit is
complete when the Director receives an application form and any supplemental information
which are completed to his or her satisfaction. The completeness of any application for a
permit shall be judged independently of the status of any other permit application or
permit for the same facility or activity. For EPA administered NPDES programs, an
application which is reviewed under §124.3 is complete when the Director receives either
a complete application or the information listed in a notice of deficiency.
(f) Information requirements. All applicants for NPDES permits shall provide the following
information to the Director, using the application form provided by the Director
(additional information required of applicants is set forth in paragraphs (g) through (k)
of this section).
(1) The activities conducted by the applicant which require it to obtain an NPDES permit.
(2) Name, mailing address, and location of the facility for which the application is
submitted.
(3) Up to four SIC codes which best reflect the principal products or services provided by
the facility.
(4) The operator's name, address, telephone number, ownership status, and status as
Federal, State, private, public, or other entity.
(5) Whether the facility is located on Indian lands.
(6) A listing of all permits or construction approvals received or applied for under any
of the following programs:
(i) Hazardous Waste Management program under RCRA.
(ii) UIC program under SDWA.
(iii) NPDES program under CWA.
(iv) Prevention of Significant Deterioration (PSD) program under the Clean Air Act.
(v) Nonattainment program under the Clean Air Act.
(vi) National Emission Standards for Hazardous Pollutants (NESHAPS) preconstruction
approval under the Clean Air Act.
(vii) Ocean dumping permits under the Marine Protection Research and Sanctuaries Act.
(viii) Dredge or fill permits under section 404 of CWA.
(ix) Other relevant environmental permits, including State permits.
(7) A topographic map (or other map if a topographic map is unavailable) extending one
mile beyond the property boundaries of the source, depicting the facility and each of its
intake and discharge structures; each of its hazardous waste treatment, storage, or
disposal facilities; each well where fluids from the facility are injected underground;
and those wells, springs, other surface water bodies, and drinking water wells listed in
public records or otherwise known to the applicant in the map area.
(8) A brief description of the nature of the business.
(g) Application requirements for existing manufacturing, commercial, mining, and
silvicultural dischargers. Existing manufacturing, commercial mining, and silvicultural
dischargers applying for NPDES permits, except for those facilities subject to the
requirements of §122.21(h), shall provide the following information to Director, using
application forms provided by the Director.
(1) Outfall location. The latitude and longitude to the nearest 15 seconds and the name of
the receiving water.
(2) Line drawing. A line drawing of the water flow through the facility with a water
balance, showing operations contributing wastewater to the effluent and treatment units.
Similar processes, operations, or production areas may be indicated as a single unit,
labeled to correspond to the more detailed identification under paragraph (g)(3) of this
section. The water balance must show approximate average flows at intake and discharge
points and between units, including treatment units. If a water balance cannot be
determined (for example, for certain mining activities), the applicant may provide instead
a pictorial description of the nature and amount of any sources of water and any
collection and treatment measures.
(3) Average flows and treatment. A narrative identification of each type of process,
operation, or production area which contributes wastewater to the effluent for each
outfall, including process wastewater, cooling water, and stormwater runoff; the average
flow which each process contributes; and a description of the treatment the wastewater
receives, including the ultimate disposal of any solid or fluid wastes other than by
discharge. Processes, operations, or production areas may be described in general terms
(for example, "dye-making reactor'', "distillation tower''). For a privately
owned treatment works, this information shall include the identity of each user of the
treatment works. The average flow of point sources composed of storm water may be
estimated. The basis for the rainfall event and the method of estimation must be
indicated.
(4) Intermittent flows. If any of the discharges described in paragraph (g)(3) of this
section are intermittent or seasonal, a description of the frequency, duration and flow
rate of each discharge occurrence (except for stormwater runoff, spillage or leaks).
(5) Maximum production. If an effluent guideline promulgated under section 304 of CWA
applies to the applicant and is expressed in terms of production (or other measure of
operation), a reasonable measure of the applicant's actual production reported in the
units used in the applicable effluent guideline. The reported measure must reflect the
actual production of the facility as required by §122.45(b)(2).
(6) Improvements. If the applicant is subject to any present requirements or compliance
schedules for construction, upgrading or operation of waste treatment equipment, an
identification of the abatement requirement, a description of the abatement project, and a
listing of the required and projected final compliance dates.
(7) Effluent characteristics. Information on the discharge of pollutants specified in this
paragraph (except information on storm water discharges which is to be provided as
specified in 122.26). When "quantitative data'' for a pollutant are required, the
applicant must collect a sample of effluent and analyze it for the pollutant in accordance
with analytical methods approved under 40 CFR Part 136. When no analytical method is
approved the applicant may use any suitable method but must provide a description of the
method. When an has two or more outfalls with substantially identical effluents, the
Director may allow the applicant to test only one outfall and report that the quantitative
data also apply to the substantially identical outfalls. The requirements in paragraphs
(g)(7) (iii) and (iv) of this section that an applicant must provide quantitative data for
certain pollutants known or believed to be present do not apply to pollutants present in a
discharge solely as the result of their presence in intake water; however, an applicant
must report such pollutants as present. Grab samples must be used for pH, temperature,
cyanide, total phenols, residual chlorine, oil and grease, fecal coliform and fecal
streptococcus. For all other pollutants, 24-hour composite samples must be used. However,
a minimum of one grab sample may be taken for effluents from holding ponds or other
impoundments with a retention period greater than 24 hours. In addition, for discharges
other than storm water discharges, the Director may waive composite sampling for any
outfall for which the applicant demonstrates that the use of an automatic sampler is
infeasible and that the minimum of four (4) grab samples will be a representative sample
of the effluent being discharged. For storm water discharges, all samples shall be
collected from the discharge resulting from a storm event that is greater than 0.1 inch
and at least 72 hours from the previously measurable (greater than 0.1 inch rainfall)
storm event. Where feasible, the variance in the duration of the event and the total
rainfall of the event should not exceed 50 percent from the average or median rainfall
event in that area. For all applicants, a flow-weighted composite shall be taken for
either the entire discharge or for the first three hours of the discharge. The
flow-weighted composite sample for a storm water discharge may be taken with a continuous
sampler or as a combination of a minimum of three sample aliquots taken in each hour of
discharge for the entire discharge or for the first three hours of the discharge, with
each aliquot being separated by a minimum period of fifteen minutes (applicants submitting
permit applications for storm water discharges under §122.26(d) may collect flow weighted
composite samples using different protocols with respect to the time duration between the
collection of sample aliquots, subject to the approval of the Director). However, a
minimum of one grab sample may be taken for storm water discharges from holding ponds or
other impoundments with a period greater than 24 hours. For a flow-weighted composite
sample, only one analysis of the composite of aliquots is required. For storm water
discharge samples taken from discharges associated with industrial activities,
quantitative data must be reported for the grab sample taken during the first thirty
minutes (or as soon thereafter as practicable) of the discharge for all pollutants
specified in §122.26(c)(1). For all storm water permit applicants taking flow-weighted
composites, quantitative data must be reported for all pollutants specified in §122.26
except pH, temperature, cyanide, total phenols, residual chlorine, oil and grease, fecal
coliform, and fecal streptococcus. The Director may allow or establish appropriate
site-specific sampling procedures or requirements, including sampling locations, the
season in which the sampling takes place, the minimum duration between the previous
measurable storm event and the storm event sampled, the minimum or maximum level of
precipitation required for an appropriate storm event, the form of precipitation sampled
(snow melt or rain fall), protocols for collecting samples under 40 CFR Part 136, and
additional time for submitting data on a case-by-case basis. An applicant is expected to
"know or have reason to believe'' that a pollutant is present in an effluent based on
an evaluation of the expected use, production, or storage of the pollutant, or on any
previous analyses for the pollutant. (For example, any pesticide manufactured by a
facility may be expected to be present in contaminated storm water runoff from the
facility.)
(i)(A) Every applicant must report quantitative data for every outfall for the following
pollutants:
Biochemical Oxygen Demand (BOD5)
Chemical Oxygen Demand
Total Organic Carbon
Total Suspended Solids
Ammonia (as N)
Temperature (both winter and summer)
pH
(B) The Director may waive the reporting requirements for individual point sources or for
a particular industry category for one or more of the pollutants listed in paragraph
(g)(7)(i)(A) of this section if the applicant has demonstrated that such a waiver is
appropriate because information adequate to support issuance of a permit can be obtained
with less stringent requirements.
(ii) Each applicant with processes in one or more primary industry category (see appendix
A to Part 122) contributing to a discharge must report quantitative data for the following
pollutants in each outfall containing process wastewater:
(A) The organic toxic pollutants in the fractions designated in table I of appendix D of
this part for the applicant's industrial category or categories unless the applicant
qualifies as a small business under paragraph (g)(8) of this section. Table II of appendix
D of this part lists the organic toxic pollutants in each fraction. The fractions result
from the sample preparation required by the analytical procedure which uses gas
chromotography/mass spectrometry. A determination that an applicant falls within a
particular industrial category for the purposes of selecting fractions for testing is not
conclusive as to the applicant's inclusion in that category for any other purposes. (See
Notes 2, 3, and 4 of this section.)
(B) The pollutants listed in table III of appendix D of this part (the toxic metals,
cyanide, and total phenols).
(iii)(A) Each applicant must indicate whether it knows or has reason to believe that any
of the pollutants in table IV of appendix D (certain conventional and nonconventional
pollutants) is discharged from each outfall. If an applicable effluent limitations
guideline either directly limits the pollutant or, by its express terms, indirectly limits
the pollutant through limitations on an indicator, the applicant must report quantitative
data. For every pollutant discharged which is not so limited in an effluent limitations
guideline, the applicant must either report quantitative data or briefly describe the
reasons the pollutant is expected to be discharged.
(B) Each applicant must indicate whether it knows or has reason to believe that any of the
pollutants listed in table II or table III of appendix D (the toxic pollutants and total
phenols) for which quantitative data are not otherwise required under paragraph (g)(7)(ii)
of this section, is discharged from each outfall. For every pollutant expected to be
discharged in concentrations of 10 ppb or greater the applicant must report quantitative
data. For acrolein, acrylonitrile, 2,4 dinitrophenol, and 2-methyl-4,6 dinitrophenol,
where any of these four pollutants are expected to be discharged in concentrations of 100
ppb or greater the applicant must report quantitative data. For every pollutant expected
to be discharged in concentrations less than 10 ppb, or in the case of acrolein,
acrylonitrile, 2,4 dinitrophenol, and 2-methyl-4,6 dinitrophenol, in concentrations less
than 100 ppb, the applicant must either submit quantitative data or briefly describe the
reasons the pollutant is expected to be discharged. An applicant qualifying as a small
business under paragraph (g)(8) of this section is not required to analyze for pollutants
listed in table II of appendix D (the organic toxic pollutants).
(iv) Each applicant must indicate whether it knows or has reason to believe that any of
the pollutants in table V of appendix D of this part (certain hazardous substances and
asbestos) are discharged from each outfall. For every pollutant expected to be discharged,
the applicant must briefly describe the reasons the pollutant is expected to be
discharged, and report any quantitative data it has for any pollutant.
(v) Each applicant must report qualitative data, generated using a screening procedure not
calibrated with analytical standards, for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) if
it:
(A) Uses or manufactures 2,4,5-trichlorophenoxy acetic acid (2,4,5,-T);
2-(2,4,5-trichlorophenoxy) propanoic acid (Silvex, 2,4,5,-TP); 2-(2,4,5-trichlorophenoxy)
ethyl, 2,2-dichloropropionate (Erbon); O,O-dimethyl O-(2,4,5-trichlorophenyl)
phosphorothioate (Ronnel); 2,4,5-trichlorophenol (TCP); or hexachlorophene (HCP); or
(B) Knows or has reason to believe that TCDD is or may be present in an effluent.
(8) Small business exemption. An applicant which qualifies as a small business under one
of the following criteria is exempt from the requirements in paragraph (g)(7)(ii)(A) or
(g)(7)(iii)(A) of this section to submit quantitative data for the pollutants listed in
table II of appendix D of this part (the organic toxic pollutants):
(i) For coal mines, a probable total annual production of less than 100,000 tons per year.
(ii) For all other applicants, gross total annual sales averaging less than $100,000 per
year (in second quarter 1980 dollars).
(9) Used or manufactured toxics. A listing of any toxic pollutant which the applicant
currently uses or manufactures as an intermediate or final product or byproduct. The
Director may waive or modify this requirement for any applicant if the applicant
demonstrates that it would be unduly burdensome to identify each toxic pollutant and the
Director has adequate information to issue the permit.
(10) (Reserved)
(11) Biological toxicity tests. An identification of any biological toxicity tests which
the applicant knows or has reason to believe have been made within the last 3 years on any
of the applicant's discharges or on a receiving water in relation to a discharge.
(12) Contract analyses. If a contract laboratory or consulting firm performed any of the
analyses required by paragraph (g)(7) of this section, the identity of each laboratory or
firm and the analyses performed.
(13) Additional information. In addition to the information reported on the application
form, applicants shall provide to the Director, at his or her request, such other
information as the Director may reasonably require to assess the discharges of the
facility and to determine whether to issue an NPDES permit. The additional information may
include additional quantitative data and bioassays to assess the relative toxicity of
discharges to aquatic life and requirements to determine the cause of the toxicity.
(h) Application requirements for manufacturing, commercial, mining and silvicultural
facilities which discharge only non-process wastewater. Except for stormwater discharges,
all manufacturing, commercial, mining and silvicultural dischargers applying for NPDES
permits which discharge only non-process wastewater not regulated by an effluent
limitations guideline or new source performance standard shall provide the following
information to the Director, using application forms provided by the Director:
(1) Outfall location. Outfall number, latitude and longitude to the nearest 15 seconds,
and the name of the receiving water.
(2) Discharge date (for new dischargers). Date of expected commencement of discharge.
(3) Type of waste. An identification of the general type of waste discharged, or expected
to be discharged upon commencement of operations, including sanitary wastes, restaurant or
cafeteria wastes, or noncontact cooling water. An identification of cooling water
additives (if any) that are used or expected to be used upon commencement of operations,
along with their composition if existing composition is available.
(4) Effluent characteristics. (i) Quantitative data for the pollutants or parameters
listed below, unless testing is waived by the Director. The quantitative data may be data
collected over the past 365 days, if they remain representative of current operations, and
must include maximum daily value, average daily value, and number of measurements taken.
The applicant must collect and analyze samples in accordance with 40 CFR Part 136. Grab
samples must be used for pH, temperature, oil and grease, total residual chlorine, and
fecal coliform. For all other pollutants, 24-hour composite samples must be used. New
dischargers must include estimates for the pollutants or parameters listed below instead
of actual sampling data, along with the source of each estimate. All levels must be
reported or estimated as concentration and as total mass, except for flow, pH, and
temperature.
(A) Biochemical Oxygen Demand (BOD5).
(B) Total Suspended Solids (TSS).
(C) Fecal Coliform (if believed present or if sanitary waste is or will be discharged).
(D) Total Residual Chlorine (if chlorine is used).
(E) Oil and Grease.
(F) Chemical Oxygen Demand (COD) (if non-contact cooling water is or will be discharged).
(G) Total Organic Carbon (TOC) (if non-contact cooling water is or will be discharged).
(H) Ammonia (as N).
(I) Discharge Flow.
(J) pH.
(K) Temperature (Winter and Summer).
(ii) The Director may waive the testing and reporting requirements for any of the
pollutants or flow listed in paragraph (h)(4)(i) of this section if the applicant submits
a request for such a waiver before or with his application which demonstrates that
information adequate to support issuance of a permit can be obtained through less
stringent requirements.
(iii) If the applicant is a new discharger, he must complete and submit Item IV of Form 2e
(see §122.21(h)(4)) by providing quantitative data in accordance with that section no
later than two years after commencement of discharge. However, the applicant need not
complete those portions of Item IV requiring tests which he has already performed and
reported under the discharge monitoring requirements of his NPDES permit.
(iv) The requirements of Parts i and iii of this section that an applicant must provide
quantitative data or estimates of certain pollutants do not apply to pollutants present in
a discharge solely as a result of their presence in intake water. However, an applicant
must report such pollutants as present. Net credit may be provided for the presence of
pollutants in intake water if the requirements of 122.45(g) are met.
(5) Flow. A description of the frequency of flow and duration of any seasonal or
intermittent discharge (except for stormwater runoff, leaks, or spills).
(6) Treatment system.
A brief description of any system used or to be used.
(7) Optional information. Any additional information the applicant wishes to be
considered, such as influent data for the purpose of obtaining "net'' credits
pursuant to 122.45(g).
(8) Certification. Signature of certifying official under §122.22.