Current through Register Vol. 41, No. 3, September 23, 2024
A.
General.
1. Definitions for the purpose of
this section:
"Removal" means a reduction in the amount of a pollutant in
the POTW's effluent or alteration of the nature of a pollutant during treatment
at the POTW. The reduction or alteration can be obtained by physical, chemical
or biological means and may be the result of specifically designed POTW
capabilities or may be incidental to the operation of the treatment system.
Removal as used in this subpart shall not mean dilution of a pollutant in the
POTW.
"Sludge requirements" means the following statutory
provisions and regulations or permits issued thereunder (or more stringent
Virginia or local regulations): § 405 of the CWA; the Solid Waste Disposal
Act (SWDA) ( 42 USC § 6901 et seq.) (including Title II more commonly
referred to as the Resource Conservation Recovery Act (RCRA) ( 42 USC §
6901 et seq.) and Virginia regulations contained in any Virginia sludge
management plan prepared pursuant to Subtitle D of SWDA); the Clean Air Act (
42 USC § 4701 et seq.); the Toxic Substances Control Act ( 15 USC §
2601 et seq.); and the Marine Protection, Research and Sanctuaries Act ( 33 USC
§ 1401 et seq.).
2.
General. Any POTW receiving wastes from an industrial user to which a
categorical pretreatment standards applies may, at its discretion and subject
to the conditions of this section, grant removal credits to reflect removal by
the POTW of pollutants specified in the categorical pretreatment standards. The
POTW may grant a removal credit equal to or, at its discretion, less than its
consistent removal rate. Upon being granted a removal credit, each affected
industrial user shall calculate its revised discharge limits in accordance with
subdivision 4 of this subsection. Removal credits may only be given for
indicator or surrogate pollutants regulated in a categorical pretreatment
standard if the categorical pretreatment statement so specifies.
3. Conditions for authorization to give
removal credits. A POTW is authorized to give removal credits only if the
following conditions are met;
a. Application.
The POTW applies for, and receives, authorization from the director to give a
removal credit in accordance with the requirements and procedures specified in
subsection E of this section;
b.
Consistent removal determination. The POTW demonstrates and continues to
achieve consistent removal of the pollutant in accordance with subsection B of
this section;
c. POTW local
pretreatment program. The POTW has an approved pretreatment program in
accordance with and to the extent required by this part; provided, however, a
POTW which does not have an approved pretreatment program may, pending approval
of such a program, conditionally give credits as provided in subsection D of
this section;
d. Sludge
requirements. The granting of removal credits will not cause the POTW to
violate the local, state and federal sludge requirements which apply to the
sludge management method chosen by the POTW. Alternatively, the POTW can
demonstrate to the director that even though it is not presently in compliance
with applicable sludge requirements, it will be in compliance when the
industrial users to whom the removal credit would apply is required to meet its
categorical pretreatment standards as modified by the removal credit. If
granting removal credits forces a POTW to incur greater sludge management costs
than would be incurred in the absence of granting removal costs, the additional
sludge management costs will not be eligible for EPA grant assistance. Removal
credits may be made available for the following pollutants:
(1) For any pollutant listed in Appendix G-I
of the regulation incorporated by reference in
9VAC25-31-750 for the use or
disposal practice employed by the POTW, when the requirements of Part VI of
this chapter for that practice are met;
(2) For any pollutant listed in Appendix G-II
of the regulation incorporated by reference in
9VAC25-31-750 for the use or
disposal practice employed by the POTW when the concentration for a pollutant
listed in Appendix G-II of the regulation incorporated by reference in
9VAC25-31-750 in the sewage sludge
that is used or disposed does not exceed the concentration for the pollutant in
Appendix G-II of the regulation incorporated by reference in
9VAC25-31-750; and
(3) For any pollutant in sewage sludge when
the POTW disposes all of its sewage sludge in a municipal solid waste landfill
that meets the criteria in the Code of Virginia and the Solid Waste Management
Regulations, 9VAC20-81;
e. VPDES permit limitations. The granting of
removal credits will not cause a violation of the POTW's permit limitations or
conditions. Alternatively, the POTW can demonstrate to the director that even
though it is not presently in compliance with applicable limitations and
conditions in its VPDES permit, it will be in compliance when the industrial
user or users to whom the removal credit would apply is required to meet its
categorical pretreatment standard or standards, as modified by the removal
credit provision.
4.
Calculation of revised discharge limits. Revised discharge limits for a
specific pollutant shall be derived by use of the following formula:
where:
x = pollutant discharge limit specified in the applicable
categorical pretreatment standard
r = removal credit for that pollutant as established under
subsection B of this section (percentage removal expressed as a proportion,
i.e., a number between 0 and 1)
y = revised discharge limit for the specified pollutant
(expressed in same units as x)
B. Establishment of removal credits;
demonstration of consistent removal.
1.
Definition of "consistent removal." "Consistent removal" means the average of
the lowest 50% of the removal measured according to subdivision 2 of this
subsection. All sample data obtained for the measured pollutant during the time
period prescribed in subdivision 2 of this subsection must be reported and used
in computing consistent removal. If a substance is measurable in the influent
but not in the effluent, the effluent level may be assumed to be the limit of
measurement, and those data may be used by the POTW at its discretion and
subject to approval by the director. If the substance is not measurable in the
influent, the data may not be used. Where the number of samples with
concentrations equal to or above the limit of measurement is between eight and
12, the average of the lowest six removals shall be used. If there are less
than eight samples with concentrations equal to or above the limit of
measurement, the director may approve alternate means for demonstrating
consistent removal. The term "measurement" refers to the ability of the
analytical method or protocol to quantify as well as identify the presence of
the substance in question.
2.
Consistent removal data. Influent and effluent operational data demonstrating
consistent removal or other information, as provided for in subdivision 1 of
this subsection, which demonstrates consistent removal of the pollutants for
which discharge limit revisions are proposed. This data shall meet the
following requirements:
a. Representative
data; seasonal. The data shall be representative of yearly and seasonal
conditions to which the POTW is subjected for each pollutant for which a
discharge limit revision is proposed;
b. Representative data; quality and quantity.
The data shall be representative of the quality and quantity of normal effluent
and influent flow if such data can be obtained. If such data are unobtainable,
alternate data or information may be presented for approval to demonstrate
consistent removal as provided for in subdivision 1 of this
subsection;
c. Sampling procedures:
composite.
(1) The influent and effluent
operational data shall be obtained through 24-hour flow-proportional composite
samples. Sampling may be done manually or automatically, and discretely or
continuously. For discrete sampling, at least 12 aliquots shall be composited.
Discrete sampling may be flow-proportioned either by varying the time interval
between each aliquot or the volume of each aliquot. All composites must be flow
proportional to each stream flow at time of collection of influent aliquot or
to the total influent flow since the previous influent aliquot. Volatile
pollutant aliquots must be combined in the laboratory immediately before
analysis.
(2)
(a) Twelve samples shall be taken at
approximately equal intervals throughout one full year. Sampling must be evenly
distributed over the days of the week so as to include no-workdays as well as
workdays. If the director determines that this schedule will not be most
representative of the actual operation of the POTW treatment plant, an
alternative sampling schedule will be approved.
(b) In addition, upon the director's
concurrence, a POTW may utilize an historical data base amassed prior to July
24, 1996, provide that such data otherwise meet the requirements of this
paragraph. In order for the historical data base to be approved it must present
a statistically valid description of daily, weekly and seasonal sewage
treatment plant loadings and performance for at least one year.
(3) Effluent sample collection
need not be delayed to compensate for hydraulic detention unless the POTW
elects to include detention time compensation or unless the director requires
detention time compensation. The director may require that each effluent sample
be taken approximately one detention time later than the corresponding influent
sample when failure to do so would result in an unrepresentative portrayal of
actual POTW operation. The detention period is to be based on a 24-hour average
daily flow value. The average daily flow used will be based upon the average of
the daily flows during the same month of the previous year.
d. Sampling procedures: Grab.
Where composite sampling is not an appropriate sampling technique, a grab
sample or samples shall be taken to obtain influent and effluent operational
data. Collection of influent grab samples should precede collection of effluent
samples by approximately one detention period. The detention period is to be
based on a 24-hour average daily flow value. The average daily flow used will
be based upon the average of the daily flows during the same month of the
previous year. Grab samples will be required, for example, where the parameters
being evaluated are those, such as cyanide and phenol, which may not be held
for any extended period because of biological, chemical or physical
interactions which take place after sample collection and affect the results. A
grab sample is an individual sample collected over a period of time not
exceeding 15 minutes;
e. Analytical
methods. The sampling referred to in subdivisions 2 a through d of this
subsection and an analysis of these samples shall be performed in accordance
with the techniques prescribed in 40 CFR Part 136 and amendments thereto. Where
40 CFR Part 136 does not contain sampling or analytical techniques for the
pollutant in question, or where the administrator determines that the Part 136
sampling and analytical techniques are inappropriate for the pollutant in
question, sampling and analysis shall be performed using validated analytical
methods or any other applicable sampling and analytical procedures, including
procedures suggested by the POTW or other parties, approved by the
administrator; and
f. Calculation
of removal. All data acquired under the provisions of this section must be
submitted to the department. Removal for a specific pollutant shall be
determined either, for each sample, by measuring the difference between the
concentrations of the pollutant in the influent and effluent of the POTW and
expressing the difference as a percentage of the influent concentration, or,
where such data cannot be obtained, removal may be demonstrated using other
data or procedures subject to concurrence by the director as provided for in
subdivision 1 of this subsection.
C. Provisional credits. For pollutants which
are not being discharged currently (i.e., new or modified facilities, or
production changes) the POTW may apply for authorization to give removal
credits prior to the initial discharge of the pollutant. Consistent removal
shall be based provisionally on data from treatability studies or demonstrated
removal at other treatment facilities where the quality and quantity of
influent are similar. Within 18 months after the commencement of discharge of
pollutants in question, consistent removal must be demonstrated pursuant to the
requirements of subsection B of this section. If, within 18 months after the
commencement of the discharge of the pollutant in question, the POTW cannot
demonstrate consistent removal pursuant to the requirements of subsection B of
this section, the authority to grant provisional removal credits shall be
terminated by the director and all industrial users to whom the revised
discharge limits had been applied shall achieve compliance with the applicable
categorical pretreatment standards within a reasonable time, not to exceed the
period of time prescribed in the applicable categorical pretreatment standards,
as may be specified by the director.
D. Exception to POTW pretreatment program
requirement. A POTW required to develop a local pretreatment program by
9VAC25-31-800 may conditionally
give removal credits pending approval of such a program in accordance with the
following terms and conditions:
1. All
industrial users who are currently subject to a categorical pretreatment
standard and who wish conditionally to receive a removal credit must submit to
the POTW the information required in
9VAC25-31-840 B 1 through 7 (except
new or modified industrial users must only submit the information required by
9VAC25-31-840 B 1 through 6),
pertaining to the categorical pretreatment standard as modified by the removal
credit. The industrial users shall indicate what additional technology, if any,
will be needed to comply with the categorical pretreatment standard or
standards as modified by the removal credit;
2. The POTW must have submitted to the
department an application for pretreatment program approval meeting the
requirements of
9VAC25-31-800 and
9VAC25-31-810 in a timely manner,
not to exceed the time limitation set forth in a compliance schedule for
development of a pretreatment program included in the POTW's VPDES permit, but
in no case later than July 1, 1983, where no permit deadline exists;
3. The POTW must:
a. Compile and submit data demonstrating its
consistent removal in accordance with subsection B of this section;
b. Comply with the conditions specified in
subdivision A 3 of this section; and
c. Submit a complete application for removal
credit authority in accordance with subsection E of this section;
4. If a POTW receives authority to
grant conditional removal credits and the director subsequently makes a final
determination, after appropriate notice, that the POTW failed to comply with
the conditions in subdivisions 2 and 3 of this subsection, the authority to
grant conditional removal credits shall be terminated by the director and all
industrial users to whom the revised discharge limits had been applied shall
achieve compliance with the applicable categorical pretreatment standards
within a reasonable time, not to exceed the period of time prescribed in the
applicable categorical pretreatment standards, as may be specified by the
director;
5. If a POTW grants
conditional removal credits and the POTW or the director subsequently makes a
final determination, after appropriate notice, that the industrial user or
users failed to comply with the conditions in subdivision 1 of this subsection,
the conditional credit shall be terminated by the POTW or the director for the
noncomplying industrial user or users and the industrial user or users to whom
the revised discharge limits had been applied shall achieve compliance with the
applicable categorical pretreatment standards within a reasonable time, not to
exceed the period of time prescribed in the applicable categorical pretreatment
standards, as may be specified by the director. The conditional credit shall
not be terminated where a violation of the provisions of this paragraph results
from causes entirely outside of the control of the industrial user or users or
the industrial user or users had demonstrated subsequential compliance;
and
6. The director may elect not
to review an application for conditional removal credit authority upon receipt
of such application, in which case the conditionally revised discharge limits
will remain in effect until reviewed by the director. This review may occur at
any time in accordance with the procedures of
9VAC25-31-830, but in no event
later than the time of any pretreatment program approval or any VPDES permit
reissuance thereunder.
E. POTW application for authorization to give
removal credits and director review.
1. Who
must apply. Any POTW that wants to give a removal credit must apply for
authorization from the director.
2.
To whom application is made. An application for authorization to give removal
credits (or modify existing ones) shall be submitted by the POTW to the
department.
3. When to apply. A
POTW may apply for authorization to give or modify removal credits at any
time.
4. Contents of the
application. An application for authorization to give removal credits must be
supported by the following information:
a.
List of pollutants. A list of pollutants for which removal credits are
proposed;
b. Consistent removal
data. The data required pursuant to subsection B of this section;
c. Calculation of revised discharge limits.
Proposed revised discharge limits for each affected subcategory of industrial
users calculated in accordance with subdivision A 4 of this section;
d. Local pretreatment program certification.
A certification that the POTW has an approved local pretreatment program or
qualifies for the exception to this requirement found at subsection D of this
section;
e. Sludge management
certification. A specific description of the POTW's current methods of using or
disposing of its sludge and a certification that the granting of removal
credits will not cause a violation of the sludge requirements identified in
subdivision A 3 d of this section; and
f. VPDES permit limit certification. A
certification that the granting of removal credits will not cause a violation
of the POTW's VPDES permit limits and conditions as required in subdivision A 3
e of this section.
5.
Director review. The director shall review the POTW's application for
authorization to give or modify removal credits in accordance with the
procedures of
9VAC25-31-830 and shall, in no
event, have more than 180 days from public notice of an application to complete
review.
6. Nothing in this part
precludes an industrial user or other interested party from assisting the POTW
in preparing and presenting the information necessary to apply for
authorization.
F.
Continuation and withdrawal of authorization.
1. Effect of authorization. Once a POTW has
received authorization to grant removal credits for a particular pollutant
regulated in a categorical pretreatment standard it may automatically extend
that removal credit to the same pollutant when it is regulated in other
categorical standards, unless granting the removal credit will cause the POTW
to violate the sludge requirements identified in subdivision A 3 d of this
section or its VPDES permit limits and conditions as required by subdivision A
3 e of this section. If a POTW elects at a later time to extend removal credits
to a certain categorical pretreatment standard, industrial subcategory or one
or more industrial users that initially were not granted removal credits, it
must notify the department.
2.
Inclusion in POTW permit. Once authority is granted, the removal credits shall
be included in the POTW's VPDES permit as soon as possible and shall become an
enforceable requirement of the POTW's VPDES permit. The removal credits will
remain in effect for the term of the POTW's VPDES permit, provided the POTW
maintains compliance with the conditions specified in subdivision 4 of this
subsection.
3. Compliance
monitoring. Following authorization to give removal credits, a POTW shall
continue to monitor and report on (at such intervals as may be specified by the
director, but in no case less than once per year) the POTW's removal
capabilities. A minimum of one representative sample per month during the
reporting period is required, and all sampling data must be included in the
POTW's compliance report.
4.
Modification or withdrawal of removal credits.
a. Notice of POTW. The director shall notify
the POTW if, on the basis of pollutant removal capability reports received
pursuant to subdivision 3 of this subsection or other relevant information
available to it, the director determines:
(1)
That one or more of the discharge limit revisions made by the POTW, of the POTW
itself, no longer meets the requirements of this section, or
(2) That such discharge limit revisions are
causing a violation of any conditions or limits contained in the POTW's VPDES
Permit.
b. Corrective
action. If appropriate corrective action is not taken within a reasonable time,
not to exceed 60 days unless the POTW or the affected industrial users
demonstrate that a longer time period is reasonably necessary to undertake the
appropriate corrective action, the director shall either withdraw such
discharge limits or require modifications in the revised discharge
limits.
c. Public notice of
withdrawal or modification. The director shall not withdraw or modify revised
discharge limits unless it shall first have notified the POTW and all
industrial users to whom revised discharge limits have been applied, and made
public, in writing, the reasons for such withdrawal or modification, and an
opportunity is provided for a public hearing. Following such notice and
withdrawal or modification, all industrial users to whom revised discharge
limits had been applied, shall be subject to the modified discharge limits or
the discharge limits prescribed in the applicable categorical pretreatment
standards, as appropriate, and shall achieve compliance with such limits within
a reasonable time (not to exceed the period of time prescribed in the
applicable categorical pretreatment standards) as may be specified by the
director.
G.
Removal credits in state-run pretreatment programs. Where the director elects
to implement a local pretreatment program in lieu of requiring the POTW to
develop such a program the POTW will not be required to develop a pretreatment
program as a precondition to obtaining authorization to give removal credits.
The POTW will, however, be required to comply with the other conditions of
subdivision A 3 of this section.
H.
Compensation for overflow. For the purpose of this section, "overflow" means
the intentional or unintentional diversion of flow from the POTW before the
POTW treatment plant. POTWs which at least once annually overflow untreated
wastewater to receiving waters may claim consistent removal of a pollutant only
by complying with either subdivision 1 or 2 of this subsection. However, this
subsection shall not apply where industrial users can demonstrate that overflow
does not occur between the industrial users and the POTW treatment plant:
1. The industrial user provides containment
or otherwise ceases or reduces discharges from the regulated processes which
contain the pollutant for which an allowance is requested during all
circumstances in which an overflow event can reasonably be expected to occur at
the POTW or at a sewer to which the industrial user is connected. Discharges
must cease or be reduced, or pretreatment must be increased, to the extent
necessary to compensate for the removal not being provided by the POTW.
Allowances under this provision will only be granted where the POTW submits to
the department evidence that:
a. All
industrial users to which the POTW proposes to apply this provision have
demonstrated the ability to contain or otherwise cease or reduce, during
circumstances in which an overflow event can reasonably be expected to occur,
discharges from the regulated processes which contain pollutants for which an
allowance is requested;
b. The POTW
has identified circumstances in which an overflow event can reasonably be
expected to occur, and has a notification or other viable plan to insure that
industrial users will learn of an impending overflow in sufficient time to
contain, cease or reduce discharging to prevent untreated overflows from
occurring. The POTW must also demonstrate that it will monitor and verify the
data required in subdivision 1 c of this subsection, to insure that industrial
users are containing, ceasing or reducing operations during POTW system
overflow; and
c. All industrial
users to which the POTW proposes to apply this provision have demonstrated the
ability and commitment to collect and make available, upon request by the POTW,
the director or EPA Regional Administrator, daily flow reports or other data
sufficient to demonstrate that all discharges from regulated processes
containing the pollutant for which the allowance is requested were contained,
reduced or otherwise ceased, as appropriate, during all circumstances in which
an overflow event was reasonably expected to occur; or
2.
a. The
consistent removal claimed is reduced pursuant to the following equation:
where:
rm = POTW's consistent removal rate
for that pollutant as established under subsections A 1 and B 2 of this
section
rc = removal corrected by the
overflow factor
Z = hours per year that overflow occurred between the
industrial user or users and the POTW treatment plant, the hours either to be
shown in the POTW's current VPDES permit application or the hours, as
demonstrated by verifiable techniques, that a particular industrial user's
discharge overflows between the industrial user and the POTW treatment
plant.
b. The POTW is
complying with all VPDES permit requirements and any additional requirements in
any order or decree, issued pursuant to the Clean Water Act affecting combined
sewer outflows. These requirements include, but are not limited to, any
combined sewer overflow requirements that conform to the Combined Sewer
Overflow Control Policy.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia; § 402 of
the federal Clean Water Act; 40 CFR Parts 122, 123, 124, 403, and 503.