(1)
Pretreatment standards specifying quantities or concentrations of pollutants or
pollutant properties which have the potential to be discharged in accordance
with 40 C.F.R. Part
403.6, as of July 1, 2009, hereby adopted and incorporated
by reference, to a WWF by existing or new industrial users, in specific
industrial subcategories, are established as separate Federal regulations under
the appropriate subpart of 40 C.F.R. Chapter I, Subchapter
N, parts 405 through
471. These pretreatment standards, unless specifically noted otherwise, shall
be in addition to all applicable pretreatment standards and requirements set
forth in this chapter.
(2) Category
determination request.
(a) Request deadline.
Within 60 days after the effective date of a pretreatment standard for a
subcategory under which an industrial user may be included, the industrial user
or control authority may request that the Department provide written
certification on whether the industrial user falls within that particular
subcategory. If an existing industrial user adds or changes a process or
operation which may be included in a subcategory, the existing industrial user
must request this certification prior to commencing discharge from the added or
changed processes or operation. A new source must request this certification
prior to commencing discharge. Where a request for certification is submitted
by a control authority, the control authority shall, at the same time, send a
copy of the request to any affected industrial user. The industrial user may
provide written comments on the control authority's request to the Department
within 30 days of the date of the request.
(b) Contents of request. Each request shall
contain a statement:
1. Describing which
subcategories might be applicable; and,
2. Citing evidence and reasons why a
particular subcategory is applicable and why others are not applicable. Any
person signing the request shall make the following certification: "I certify
under penalty of law that this document and all attachments were prepared under
my direction or supervision in accordance with a system designed to assure that
qualified personnel properly gather and evaluate the information submitted.
Based on my inquiry of the person or persons who manage the system, or those
persons directly responsible for gathering the information, the information
submitted is to the best of my knowledge and belief, true, accurate, and
complete. I am aware that there are significant penalties for submitting false
information, including the possibility of fine and imprisonment for knowing
violations."
(c)
Deficient requests. The Department shall only act on written requests for
determinations that contain all of the information required. Persons who have
made incomplete submissions will be notified by the Department that their
request is deficient. If the deficiency is not corrected within 30 days of the
date of the notification, the request for a determination shall be
denied.
(d) Final decision.
1. Upon receipt of a complete request, the
Department shall consider the submission, any additional evidence that may have
been requested, and any other available information relevant to the request.
The Department shall then make a written determination of the applicable
subcategory and state the reasons for the determination.
2. The Department shall forward the
determination to the EPA Water Management Division Director. The EPA Water
Management Division Director may waive receipt of these determinations. If the
EPA Water Management Division Director does not modify the Department's
decision within 60 days after receipt thereof, or if the EPA Water Management
Division Director waives receipt of the determination, the Department's
decision is final.
3. Where the EPA
Water Management Division Director elects to modify the Department's decision,
the decision shall be forwarded to the Department. The Department shall adopt
the modified decision as its final determination.
4. The Department shall send a copy of the
final determination to the affected industrial user and the control
authority.
(e) Requests
for administrative hearing. Within 14 days following the date of receipt of the
copy of the final determination as provided for by subparagraph (d)4., above,
the industrial user or control authority may submit a petition for
administrative hearing under Section
120.57, F.S., to reconsider or
contest the decision.
(3)
Deadline for compliance with categorical standards. Compliance by existing
sources with categorical pretreatment standards shall be within 3 years of the
date the standard is effective in the appropriate subpart of 40 C.F.R. Chapter
I, Subchapter
N, parts 405 through 471, unless a shorter compliance time is
specified as part of the categorical standard. Existing sources which become
industrial users subsequent to promulgation of an applicable categorical
pretreatment standard shall be considered existing industrial users except
where such sources meet the definition of a new source as defined in subsection
62-625.200(13),
F.A.C. New sources shall install and have in operating condition, and shall
"start-up, " all pollution control equipment required to meet applicable
pretreatment standards before beginning to discharge. Within 90 days of
initiating discharge, new sources must meet all applicable pretreatment
standards.
(4) Concentration and
mass limits.
(a) Pollutant discharge limits in
categorical pretreatment standards will be expressed either as concentration or
mass limits. Wherever possible, where concentration limits are specified in
pretreatment standards, equivalent mass limits will be provided so that local,
State or Federal authorities responsible for enforcement may use concentration
or mass limits. Limits in categorical pretreatment standards shall apply to the
effluent of the process regulated by the pretreatment standard, or as otherwise
specified by the pretreatment standard.
(b) When the limits in a categorical
pretreatment standard are expressed only in terms of mass of pollutant per unit
of production, the control authority may convert the limits to equivalent
limitations expressed either as mass of pollutant discharged per day or
effluent concentration for purposes of calculating effluent limitations
applicable to individual industrial users.
(c) A control authority calculating
equivalent mass-per-day limitations under paragraph (b), above, shall calculate
such limitations by multiplying the limits in the pretreatment standard by the
industrial user's average rate of production. This average rate of production
shall be based not upon the designed production capacity but rather upon a
reasonable measure of the industrial user's actual long-term daily production,
such as the average daily production during a representative year. For new
sources, actual production shall be estimated using projected
production.
(d) A control authority
calculating equivalent concentration limitations under paragraph (b), above,
shall calculate such limitations by dividing the mass limitations derived under
paragraph (c), above, by the average daily flow rate of the industrial user's
regulated process wastewater. This average daily flow rate shall be based upon
a reasonable measure of the industrial user's actual long-term average flow
rate, such as the average daily flow rate during a representative
year.
(e) When the limits in a
categorical pretreatment standard are expressed only in terms of pollutant
concentrations, an industrial user may request that the control authority
convert the limits to equivalent mass limits. The control authority may convert
to equivalent mass limits only if the industrial user meets all the following
conditions:
1. Employs, or demonstrates that
it will employ, water conservation methods and technologies that substantially
reduce water use during the term of its control mechanism;
2. Currently uses control and treatment
technologies adequate to achieve compliance with the applicable categorical
pretreatment standard, and not have used dilution as a substitute for
treatment;
3. Provides sufficient
information to establish the industrial user's actual average daily flow rate
for all wastestreams, based on data from a continuous effluent flow monitoring
device, and the industrial user's long-term average production rate, if
applicable. Both the actual average daily flow rate and the long-term average
production rate must be representative of current operating
conditions;
4. Does not have daily
flow rates, production rates, or pollutant levels that vary more than 20
percent so that equivalent mass limits are not appropriate to control the
discharge; and,
5. Has consistently
complied with all applicable categorical pretreatment standards during the
period prior to the industrial user's request for equivalent mass
limits.
(f) An industrial
user subject to equivalent mass limits based on paragraph (e), above, must:
1. Maintain and effectively operate control
and treatment technologies adequate to achieve compliance with the equivalent
mass limits;
2. Record the
facility's flow rates through the use of a continuous effluent flow monitoring
device;
3. Record the facility's
production rates and notify the control authority when the production rates are
expected to vary more than 20 percent from its baseline production rates
determined in subparagraph (e)3., above; and,
4. Continue to employ the same or comparable
water conservation methods and technologies as those implemented pursuant to
subparagraph (e)1., above.
(g) A control authority which chooses to
establish equivalent mass limits:
1. Must
calculate the equivalent mass limit by multiplying the actual average daily
flow rate of the regulated process(es) of the industrial user by the
concentration-based daily maximum and monthly average standard for the
applicable categorical pretreatment standard and the appropriate unit
conversion factor;
2. Must reassess
the equivalent mass limit and recalculate the limit, as necessary, to reflect
changed conditions at the facility upon notification from the industrial user
of a revised production rate; and,
3. May retain the same equivalent mass limit
in subsequent control mechanism terms if:
a.
The industrial user's actual average daily flow rate was reduced solely as a
result of the implementation of water conservation methods and
technologies;
b. The actual average
daily flow rates used in the original calculation of the equivalent mass limit
were not based on the use of dilution as a substitute for treatment pursuant to
subsection (5), below; and,
c. The
industrial user is in compliance with Rule
62-625.860,
F.A.C.
(h) The
control authority may not express limits in terms of mass for pollutants such
as pH, temperature, radiation, or other pollutants which cannot appropriately
be expressed as mass.
(i) The
control authority may convert the mass limits of the categorical pretreatment
standards in 40 C.F.R. Parts
414,
419, and
455 to concentration limits for
purposes of calculating limitations applicable to individual industrial users
under the following conditions:
1. When
converting such limits to concentration limits, the control authority must use
the concentrations listed in the applicable subparts of 40 C.F.R. Parts
414,
419, and
455; and,
2. Document that
dilution is not being substituted for treatment as prohibited by subsection
(5), below.
(j)
Equivalent limitations calculated in accordance with paragraphs (c), (d), (e)
and (i), above, are deemed pretreatment standards for the purposes of section
307(d) of CWA and this chapter. The control authority must document how the
equivalent limits were derived and make this information available in the
industrial user's file for public review. Once incorporated into its control
mechanism, the industrial user must comply with the equivalent limitations in
lieu of the categorical pretreatment standards from which the equivalent
limitations were derived.
(k) Many
categorical pretreatment standards specify one limit for calculating maximum
daily discharge limitations and a second limit for calculating maximum monthly
average, or 4-day average limitations. Where such standards are being applied,
the same production or flow figure shall be used in calculating both the
average and the maximum equivalent limitations.
(l) Any industrial user operating under a
control mechanism, as described in subparagraph
62-625.500(2)(a)
2., F.A.C., incorporating equivalent mass or concentration limits calculated
from a production based standard shall notify the control authority within 2
business days after the industrial user has a reasonable basis to know that the
production level will change more than 20 percent within the next calendar
month. Any industrial user not notifying the control authority of such
anticipated change will be required to meet the mass or concentration limits in
its control mechanism that were based on the original estimate of the long-term
average production rate.
(5) Dilution prohibited as substitute for
treatment. Except where expressly authorized to do so by an applicable
pretreatment standard or requirement, no industrial user shall ever increase
the use of process water, or in any other way attempt, to dilute a discharge as
a partial or complete substitute for adequate treatment to achieve compliance
with a pretreatment standard or requirement. The control authority shall impose
mass limitations on industrial users which are using dilution to meet
applicable pretreatment standards or requirements.
(6) Combined waste stream formula. Where
process effluent is mixed prior to treatment with wastewaters other than those
generated by the regulated process, fixed alternative discharge limits may be
derived by the control authority or by the industrial user with the written
concurrence of the control authority. When the Department is acting as the
control authority, the Department shall allow the development of fixed
alternative discharge limits when direct sampling of the regulated waste stream
is not technically feasible. These alternative limits shall be applied to the
mixed effluent. When deriving alternative categorical limits, the control
authority or industrial user shall calculate both an alternative daily maximum
value using the daily maximum values specified in the appropriate categorical
pretreatment standards and an alternative consecutive sampling day average
value using the monthly average values specified in the appropriate categorical
pretreatment standards. The industrial user shall comply with the alternative
daily maximum and monthly average limits fixed by the control authority until
the control authority modifies the limits or approves an industrial user
modification request. Modification is authorized whenever there is a material
or significant change in the values used in the calculation to fix alternative
limits for the regulated pollutant. An industrial user must immediately report
any such material or significant change to the control authority. Where
appropriate, new alternative categorical limits shall be calculated within 30
days.
(a) Alternative limit calculation. For
purposes of these formulas, the "average daily flow" means a reasonable measure
of average daily flow for a 30-day period of production during a representative
year. For new sources, flows shall be estimated using projected values. The
alternative limit for a specified pollutant shall be derived by the use of
either of the following formulas:
1.
Alternative concentration limit.
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2.
Alternative mass limit.
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3. The
terms used in the equations in 1. and 2. above are defined as follows:
CT
|
=
|
The alternative concentration limit for the combined
waste stream.
|
Ci
|
=
|
The categorical pretreatment standard concentration
limit for a pollutant in the regulated stream i.
|
MT
|
=
|
The alternative mass limit for a pollutant in the
combined waste stream.
|
Mi
|
=
|
The categorical pretreatment standard mass limit for
a pollutant in the regulated stream i (the categorical pretreatment mass limit
multiplied by the appropriate measure of production).
|
Fi
|
=
|
The average daily flow (at least a 30-day average) of
stream i to the extent that it is regulated for such pollutant.
|
FD
|
=
|
The average daily flow (at least a 30-day average)
from waste streams identified in subsection (7), below.
|
Ft
|
=
|
The average daily flow (at least a 30-day average)
through the combined treatment facility (includes Fi,
Fd and unregulated streams).
|
N
|
=
|
The total number of regulated streams.
|
(b) Alternative limits below detection limit.
An alternative pretreatment limit shall not be used if the alternative limit is
below the analytical detection limit for any of the regulated
pollutants.
(c) Self-monitoring.
Self-monitoring required to ensure compliance with the alternative categorical
limit shall be conducted in accordance with the requirements of Rule
62-625.600, F.A.C.
(d) Choice of monitoring location. Where a
treated regulated process waste stream is combined prior to treatment with
wastewaters other than those generated by the regulated process, the industrial
user may monitor either the segregated process waste stream or the combined
waste stream for the purpose of determining compliance with applicable
pretreatment standards. If the industrial user chooses to monitor the
segregated process waste stream, it shall apply the applicable categorical
pretreatment standard. If the industrial user chooses to monitor the combined
waste stream, it shall apply an alternative discharge limit calculated using
the combined waste stream formula as provided in paragraph (a), above. The
industrial user may change monitoring points only after receiving approval from
the control authority. The control authority shall ensure that any change in an
industrial user's monitoring points will not allow the industrial user to
substitute dilution for adequate treatment to achieve compliance with
applicable standards.
(7)
For the purposes of the combined waste stream formula, dilute waste streams
include:
(a) Boiler blowdown streams,
noncontact cooling streams, stormwater streams, and demineralizer backwash
streams; unless such streams contain a significant amount of a pollutant and
are combined with the regulated process waste stream prior to treatment, and
the treatment will result in a substantial reduction of that pollutant. The
control authority shall determine whether such streams are classified as
diluted or unregulated. The industrial user shall provide engineering,
production, sampling and analysis, and such other information so that the
control authority can make its determination;
(b) Sanitary waste streams where such streams
are not regulated by a categorical pretreatment standard;
(c) Any process waste streams which were or
could have been entirely exempted from categorical pretreatment standards for
one or more of the following reasons:
1. The
pollutants of concern are not detectable in the effluent from the industrial
user;
2. The pollutants of concern
are present only in trace amounts and are neither causing nor likely to cause
toxic effects;
3. The pollutants of
concern are present in amounts too small to be effectively reduced by known
technologies; or
4. The waste
stream contains only pollutants which are compatible with the
WWF.
(d) Waste streams
from the list of industrial user subcategories identified in subsection
62-625.880(1),
F.A.C.