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PIN
13
ILLINOIS POLLUTI
N CONTROL
BOARD
L
STAlE
OF
ILLINOIS
Pollution
Control Board
IN THE MATTER OF:
PROPOSED AMENDMENTS TO:
PART
309 SUBPART A
-
35
Ill.
Adm Code
309.105, 309.7,
309.8,
309.9,
309.10,
309.12,
309.13,
309.14,
309.117, 309.119, 309.143, 309.147; and
PROPOSED
35
Ill.Adm, Code
120
through
122
-
NPDES PERMITS AND
PERMITTING PROCEDURES
NOTICE OF FILING
PLEASE TAKE NOTICE that the Environmental Law
and Policy Center of the Midwest,
Illinois Chapter of the Sierra Club, Prairie Rivers Network and the 225
persons whose signatures
are included
with the petition, hereby petition the Illinois Pollution Control Board
to amend
Illinois Administrative Code Title 35
Environmental Protection Act; Subtitle C: Water Pollution;
Chapter I:
Pollution Control Board; Part
309 subpart A.
Petitioners are today filing:
-
The language ofthe proposed rules and rule amendments;
-
A statement of reasons supporting the proposed rules
and rule changes together
with 4 exhibits (A-D) to the statement;
-
A synopsis ofthe testimony to be presented by the proponents
at the hearing
consisting of the pre-filed testimony of Cynthia Skrukrud Ph.D., Beth Wentzel
and Albert Ettinger;
I
-
A petition signed by at least 200 persons
-
Proofofservice of the original and 9 copies on the Clerk
and one copy
each with
the Attorney General, the Illinois Environmental Protection Agency and the
Illinois Department ofNatural Resources.
The pre-filed testimony ofAlbert Ettinger includes a written statement that the proposal
amends the most recent version ofthe rule as published on the Board’s Web site.
Albert F. Ettinger (ARØ~
# 3125045)
Counselfor EnvironmentalLaw
& Policy
Center,
Prairie Rivers Network and Sierra
Club
Environmental Law& Policy Center
35
E.
WackerDr. Suite
1300
Chicago, Illinois 60601-2110
312 795
3707
January 13, 2003
2
SectIon
309.105
Authority to Deny NPDES Permits
No
NPDES
Permitmaybe
issued
in any case
in
which:
a)
The
permit
would authorize the discharge of a radiological,
chemical or
biological
warfare
agent or high-level radioactive waste;
b)
The
discharge would,
in
thejudgment of the
Secretary
of the
Army
acting
through the Chief of Engineers, result in the substantial
impairment of anchorage
and
navigation;
c)
The proposed
permit
is objected to in
writing
by the Administrator of the
U.S.
Environmental Protection Agency pursuant to
any
right to object
given to the
Administrator
under
Section
402(d) of the CWA;
d)
The
permit
would
authorize a discharge from a point source which is in
conflict with a plan approved under Section 208(b) of the CWA; or
e)
The applicant
has
not provided proof to the Agency
that
he will meet any
schedule of compliance which
may
be established, in
accordance
with the
Act and
regulations,
as a
condition
of
his
permit.
The public has not
had
a
fair opportunity
to comment on
all
substantial
terms of the
permit,
The nermit.
nermit conditions or nr~eduresused to
draft or issue
the
permit
are not
consistent with
any
anvlicable federal
law.
SectIon 309.107
DIstribution
of
Applications
When
the Agency
determines that
an application for an
NPDES
Permit
is
complete,
it
a)
Unless otherwise agreed, send a copy of the application to the District
Engineer of the appropriate district of the U.S.
Corps of Engineers with
a letter requesting
that
the District
Engineer
provide, within 30 days or
as otherwise
stated
in the Agency’s later,
his
evaluation of the impact of
the discharge on anchorage and navigation.
If the District
Engineer
responds that
anchorage
and
navijtionof
any
of the naviEation waters
tWould
be substantially
inj~iairS
by die grintin~
of a
permit,
the
permit
~:J?iuc.
~i!UiiWfflbedenled
and theAgeiic~slia1lnotlf~thè
applicant.
If the District
g)
Engineer informs the Agency that the imposition of specified conditions
upon the NPDES Permit is necessary to avoid any substantial impairment
ofany of the navigable waters,
the Agency shall
include
in
the permit
those conditions
specified by the District Engineer.
b)
Send two
copies of the application
to
the Regional Administrator of the
U.S..
Environmental Protection Agency with a letter stating that the
application is complete.
c)
Subject
o any memorandum of agreement between the Agency
and
the
Illinois Department of Natural Resources (IDNR).
notify the IDNR.
Section 309.108
Tentative Determination and Draft Permit
Following the receipt of a complete
application for an NPDES Permit, the Agency
shall
prepare
a tentative determination.
Such determination shall include at least the
following:
a)
A Statement regarding whether an NPDES Permit is to be issued or
denied;
~jgj
b)
If the determination is to issue the permit, a draft permit containing:
1)
Proposed effluent limitations, consistent with
federal and state
requirements;
2)
A proposed schedule of compliance,
if the applicant
is not in
compliance with applicable requirements,
including
interim dates
and requirements consistent with the CWA
and applicable
regulations,
for meeting the proposed
effluent limitations;
3)
A briefdescription ofanyotherprppQ~çd
special
conditions
which will have a significant impact upon the discharge.
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c)
A siàtement ofthe basis for each of the permit conditions listed in Section
309.108(b), including a description of how the conditions of the draft
pcnnit were derived as well
as the statutory or rcgulatory provisions and
appropriate supporting references.
ci)
.
Upon tentative determination to issue or deny
an NPDES
Permit:
1)
If the determination is to
issue the
permit the Agency
shall notify
II’
thea~phcantlnwrthngofthecontent9ftheteatative
U
~
determsnationanddiaftpermitandpfits mtent1tocirculate public
notice of issuance
in accordance with Sections
309.108 through
309.112;
2)
If the determination is to deny the permit,
the Agency shall notify
the applicant in writing of the tentative determination and of its
intent to circulate public notice of denial,
in accordance with
Sections 309.108 through 309.112.
In the case of denial,
notice
to the applicant
shall
include a statement of the reasons for denial,
as required by
Section 39(a) of the Act.
e)
In support of its tentative decision
to
issue or deny
an
NPDES
permit
the
Agency shall prepare
p
draft administrative record
containing the basis
for the allowances or disallowances of each proposed
discharge and
which:
1)
Shows
that any discharge
to be
permitted
will
not cause or contribute
to
the violation of any applicable numeric or narrative
water quality
standard.
2)
Shows the basis
for each
limit
and special
condition in the permit.
3)
Shows the method(s)
by which each limit or special condition of the
permit will
be
monitored
for
compliance.
Section 309.109
Public Notice
a)
Upon tentative determination to issue
or deny an NPDES Permit,
completion of the draft permit, if any. or re-notice of a substantively
changed draft permit,
and not earlier than 10 days following notice to the
applicant pursuant to Section 309.108(d), the Agency shall circulate
public notice of the completed application for an NPDES Permit in a
maimer designed to
inform interested
and potentially interested persons
of the discharge or proposed discharge and
of
the proposed
determination to issue or deny an NPDES Permit for the discharge or
proposed discharge.
Procedures
for the
circulation
of public
notice shall
include at least the following concurrent actions:
1)
Notice shall be milled to the applicant;
2)
Notice shall be circulated within the geographical area ofthe
proposed discharge;
such circulation may include
any or all of the
following:
A)
Posting
in the post office and public places of the
municipality nearest the premises of the applicant in which
the effluent source is located;
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B)
Posting
near
the entrance to
the applicant’s premises and
in
nearby
places;
C)
Publishing
in
local
newspapers and
periodicals, or, if
appropriate,, in a daily
newspaper of general circulation;
and
D)
Any
other notice
requirements
necessary
to meet the
requirements of the Act
and
the CWA;
3)
Notice shall be
mailed to
any
person or
group
upon request;
4)
The Agency shall add
the
name
of
any person or group
upon
request to a mailing list to receive
copies of notices for all
NPDES
applications
within the State of Illinois or within a certain
geographical area.
b)
The Agency shall provide a period of not less than
30 days
following the
date of first publication of the public
notice during which time interested
persons may
submit their written views on the
tentative determinations
with respect to the
NPDES
application.
All comments shall be submitted
to the Agency
and to the applicant.
All written comments submitted
during the 30 day comment period shall be
retained by the Agency and
considered in the formulation of its final determinations
with
respect to
the NPDES
application.
The
period
for comment
may be extended at
the
discretion of the Agency
by publication as provided
in Section 309.109.
(Source:
Amended
at 2
Ill.
Reg. no.
16, page 20, effective
April 20,
1978.)
Section 309.110
Contents of Public
Notice
of Application
.
.
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The
contents
of public
notice,
of appiicafiops.fçr,~1P
DES
units
~hallin
lude
at least
the
following:
‘
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4~fl~5~ç
a)
Name,
address,
and
telephone number, of the Agency;
b)
Name and address of the applicant;
c)
Brief description of the
applicant’s activities or operations which result
in the discharge described
in the NPDES application (e.g.,
municipal
waste treatment plant,
steel
manufacturing,
drainage from
mine
,.,acti’vi4es);
.
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d)
Name, if any, of the waterway
to which the discharge is made and a
short description of the location of the discharge
indicating
whether it is
a new or an existing
discharge
including
the latitude
and longitude of the
outfalls as well as the river
mile ofthe outfall;
e)
A statement of the tentative
determination to issue ordeny anNPDES
Permit for the discharge described in
the application;
A
bricidcscription
of the
nrocedures
for
the
formulation of final
determinations. including.:
(1)
The bcainniniz and ending dates of the comment
period and
the
address where comments
will
be received;
Procedures
for requesting
a hearing and the nature of that hearing;
(2)
and
(3)
Any other procedures bY which the public may participate in the
fiuial
decision.
g)
Address and telephone number ofAgency premises at which
interested
persons
may obtain further information, request a copy
of the
fact sheet,
and
inspect and copy NPDES forms
and
related documents.
Section 309.112
Agency Action
After Comment Period
Subject to Sections
309.121
and 309.122,
if,
after the comment period provided, no
public hearing is held with respect to the permit,
the Agency
shall,
after evaluation of
any comments which may have
been received,
either issue or deny the
permit.
(Source:
Amended at 2 Ill.
Reg.
no.
16,
page 20,
effective April 20, 1978.)
Section
309.113
Fact Sheets
a)
For every
discharge
which has a
total volume of mote than 500,000
gallons
(1.9
megaliters)
oh any thy of the
year, the Agency shall prepare
and,
following public
notice,
shall send upon
request
to any person
a fact
sheet with
respect
to the
application described in the public notice. The
contents ofsuch fact
sheets
shall
include at
least
the following
information:
1)
A
sketch or dethiled description of the
location
of the
discharge
described in the application;
2)
A
quantitative description ofthe proposed discharge described in
the application which
includes at least the following:
A)
The rate or frequency of the proposed
discharge; ifthe
discharge is continuous, the average daily flow;
B)
For
thermal discharges subject to limitation under the Act,
the average
monthly temperatures
for the discharge;
C)
The
average daily mass discharged
and average
concentration in milligrams
per liter, or other applicable
units of measurement, of any contaminants which are
present
in significant quantities or which are subject to
limitations or prohibitions under applicable provisions of
the CWA or the Act or regulations
adopted thereunder;
3)
The tentative determinations required under
Section 309.108;
4)
A brief citation,
including an identification of the uses for which the
receiving waters have been classified, of the water quality standards
and effluent standards
and limitations
applicable
to the proposed
discharge;
5)
A brief description of
the
significant factual,
legal,
methodological
and policy
Questions considered
in preparing the draft pennit;
6)
Flow of the
receiving waters
in the penflit and
permit
fact
sheet,
including 701010w
flow:
7)
A description of
the
mixing zone, or the dilution
factor
used
to
calculate allowed mixing, pursuant to
~302.l02
8) in
the. case
of. modified and
reissued
ocrmjts.
a summary
of changes
..~,between
the public noticed permit and the previous
m~miit
o~rc5L1
9)
Summary of the Agency’s antidegradation analysis and
characterization of the receiving
waters including
the existing
uses of
the receiving
waters:
10) A more detailed description of the procedures for the formulation of
fmal determinations
than that given in
the public
notice,
including:
A)
The 30
day comment period;
B)
Procedures for requesting a public hearing and the
nature
thereof;
and
C)
Any
other procedures by which the public may participate
in the formulation of the final determination and
11)
Information on
how to obtain
the complete
draft permit
administrative
record
sunpofling the tentative determination.
b)
The Agency
shall add the
name
of any person or group,
upon request,
to
a mailing
list to receive copies of fact sheets.
Section 309.114 Notice to Other Govermnental Agencies
At the time of issuance of public
notice pursuant to
Sections
309.109
through 309.112,
the Agency
shall:
a)
Send a fact sheet,
if
one
has
been
prepared,
to any other States
whose
waters
may be affected by the
issuance ofthe proposed
permit
and,
upon
request,
provide such
States
with a
copy
of the application and a
copy
of
the
draft
permit.
Each
affected
State
shall be
afforded an opportunity
to
submit
written
recommendations within a
stated number
of days
to
the
Agency
and
to the Regional Administrator of the
U.S. Environmental
Protection Agency,
which the Agency may incorporate
into
the
permit if
issued.
Should the Agency decline to incorporate
any written
recommendations thus received,
it shall provide to the
affected
State or
States
(and to the Regional
Administrator) a
written
explanation of
its
reasons
for declining to accept
any
of the
written recommendations.
b)
Following the procedure
setforth in (a) above,
notify and receive
recommendations
from any interstate agency
having
water
quality
control
authority
over waters which
may be
affected
by the
permit.
c)
iJnless otherwise
agreed, in acáordance
with
40CFR
124.34(c),
send a
copy of the fact sheet, if
one
has
been prepared, to
theappropriate
District Engineer of the
Army
Corps of Engineers
for discharges
(other
than minor discharges)
into
navigiable waters.
d)
Upon request,
send a copy
of the public
notice and
a copy of the fact
sheet for
NPDES
Permit applications
to
any
other Federal,
state,
or local
agency,
or any
affrcted
country,
and provide such agencies an
opportunity to respond, comment,
or request a public
hearing
pursuant to
Sections
309.115-309.119.
Such agencies shall
include at least the
following:
1)
The agency responsible for the preparation of an approved
plan
pursuant to
Section 208(b) of the CWA; and
2)
The State or interstate
agency responsible for the preparation of a
plan pursuant to an approved continuous planning process under
Section 303(e) of the CWA.
e)
Send notice to,
and coordinate with,
appropriate public health agencies
for the purpose
of assisting the applicant
in integrating the relevant
provisions of the CWA with any applicable requirements of such public
health agencies.
Section 309.117
Agency Hearing
The applicant or any person shall be permitted to submit oral or written statements and
data concerning the proposed permit or group of permits.
The Chairman shall have
authority
to
fix
reasonable limits upon the time
allowed for oral
statements,
and may
require
statements
in writing.
The
documents or other materials referred to
or relied on
by
the Agency or the applicant
to support the tentative decision
shall
be
identified by
the Agency or Applicant at the hearing.
Section 309.119
Agency Action After Rearing
Subject to Sections 309.121
and 309.122,
following the public hearing,
the Agency
may make such modifications in the terms and conditions of proposed permits as may
be appropriate
and shall transmit to
the Regional Administrator for his
approval a copy
of the permit proposed to be
issued unless the Regional Administrator has waived his
right to receive and review permits of its class.
.me Agency
shall provide a notice of
suck transmission to the applicant,
to any person who participates in the public hearing,
to any person who requested a public hearing,
and to
appropriate persons on the
mailing list established under Sections 309.109 through 309.112.
Such notice shall
briefly, indicate any significant
changes
which were made frqni. terms and conditions set
forth
m the draft permit
All permits become effective when issued
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Section
309.t20
Oblization of Atrnlicant and Commenters to
Place Arguments
in
Record
All persons, including applicants, who believe
any conditioi
of a draft
permit is
inappropriate or
that
the Agency’s tentative decision to deny
an application.
terminate
a
permit.
or prepare
p
draft pennit
is inaPPropriate,
must
raise
all
reasonably ascertainable iss~s
and submit
all reasonably
available arguments
supporting their position
by th&close of the public commeqt period (including
any public hearing and post-hearing comment period),
Ahy
supporting
materials that are submitted shall
be
included
in
full
and may
not be
incorporated
by reference,
unless they are already
part of the administrative
record in
the same
proceeding, or consist of State or Federal statutes and
regulations,
EPA documents of general
applicability,
or other generally
available reference materials.
Commenters
shall
make
supporting materials
not
already
included
in the administrative record
available to EPA
as directed by
the
agency
(A comment
period
longer than
30 days may be
necessary
to
give
commenters
a reasonable opportunity to
comply
with the requirements of this
section.
Additional
time shall
be
granted to
the extent that a commenter
who
requests additional
time
demonstrates the need for such time).
Section
309.121
Reopening the Record to
Receive Additional Written
Comment
I)
The
Agency may order the public comment period
reopened
for
written
comment if the
procedures of this paragraph could expedite
the decision
making process.
When
the public comment
period is reopened
under
this paragraph,
all persons,
including applicants, who
believe any
condition of a draft permit is inappropriate or that the Agency’s tentative
decision to deny
an
application,
terminate
a permit,
or prepare a draft
permit is inappropriate, must submit all
reasonably available factual
grounds supporting their position,
including
all
supporting material,
by
a
date not
less than sixty
days after public
notice under paragraph (2) of
this section.
set
by the Agency.
Thereafter,
any person
may file
a
written response to the material
filed
by any other person, by
a date not
less than
thirty days after the date set for filing of the material,
set by
the
Agency.
2)
Public
notice of any comment period under this paragraph shall
identify
the issues as to
which the public comment period
is reopened.
3)
On its own
motion or
on the request of any person, the Agency
may
direct that
the requirements of paragraph
(1) of this section shall apply
during the initial
comment period where it reasonably
appears that
issuance of the permit will
be
substantially contested and that applyin~
the requirements of paragraph (1) of this section will
substantially
expedite
the decision making
process.
The notice ofthe draft permit
shall state whenever this has
been done.
4)
A comment
period of longer than 60 days will
often be necessary
in
complicated
proceedings to
give commenters p reasonable opportunity to
comply
with the requirements of this
section.
Commenters
may request
longer comment periods and they
shall
be
granted to the extent they
appear
necessary,
Section 309.122
Requirement
to Reopen Record if
Draft Permit is
Substantially Modified or Substantial New Ouestions Are
Raised
During
Comment
Period,
a)
!f~,after giving public notice of its tentative decision,
the Agency
determines to
modify any draft permit significantly,
the Agency shall
prepare a new draft permit,
appropriately modified and give
notice of the
new permit under
Section 309.109.
The Agency
may
restrict comments
on the modified draft permit
to
issues
on which there
has
not
been a
previous opportuiiity to comment.
b)
If any data, information or arguments
submitted during the public
comment period
appear
to
raise
substantial
new questions
concerning a
permit,
the Agency
may take one or more of the following actions:
I)
Prepare a
revised statement of basis under ~ 309.121: or
2)
Reopen or extend the comment period
to
give interested
persons
an opportunity to
comment on the information or arguments
submitted.
Comments
filed during the
reopened comment
period
shall be
limited to the substantial
new questions that caused
its
reopening.
The public
notice under ~i309.109 shall define the
scope of the reopening.
Section
309.123
Definition of the “Record
before the Agency”
The
record “before the Agency”
includes
all
documents or other materials
prepared, properly placed
in the record or identified in
the record pursuant
to
35
Ill.
Adm.
Code
309.108-110.
113,117, or
119-22.
SUBPART A:
NPDES PERMITS
SectIon 309.143 Effluent Limitations
a)
Effluent limitations
must control
all
pollutant or pollutant
parameters
(either conventional,
nonconventional, or toxic
pollutants) which the
Agency
determines are or may
be discharged at
a
level which
will
cause,
have the reasonable
potential
to cause, or contribute to
an
excursion
above any
State
water quality standard,
including State
narrative criteria
for water quality.
b)
In the application of effluent standards and limitations,
water quality
standards
and other applicable requirements,
the Agency shall, for each
permit,
specit5
average and maximum daily
quantitative limitations for
the level of pollutants in the
authorized discharge in terms ofweight
(exceptpH,
temperature,
radiation,
and
any other pollutants
not
appropriately óxpressed by weight,
and except for discharges whose
constituents cannot be appropriately expressed by
weight).
The Agency
may,
in
its discretion,
in addition to specification of daily quantitative
limitations by weight, speci& other limitations, such as average or
maximum concentration limits, for the level of pollutants
in the
authorized discharge.
Effluent
limitations for multiproduct operations
shall provide for appropriate waste variations
from such plants.
Where a
schedule of compliance is included as a condition
in a permit,
effluent
limitations shall be included for the interim period
as well as for the
period following the final compliance date.
Section 309.146
Authority to Establish Recording,
Reporting,
Monitoring and
Sampling Requirements
a)
The Agency
shall require every holder of an NPDES
Permit, as a
condition of the NPDES Permit issued to
the holder,
to:
1)
Establish, maintain and retain records;
2)
Make reports
adeuuate to
determine the compliance or tack
of
compliance by the permit holder with
all
effluent
limits and
special
conditions
in the permit.
3)
Install, calibrate, use and maintain
monitoring equipment or
methods
(including where appropriate biological monitoring
methods);
4)
Take samples of effluents (in accordance with such methods,
at
such locations,
at such intervals,
and in such a manner as may be
prescribed; and
5)
All permits
shall specify
requirements concerning the proper use.
maintenance, and
installation,
when appropriate, of monitoring
equipment or methods (including
biological
monitoring methods
when appropriate): required monitoring including
type.
intervals,
and frequency sufficient to
yield
data which are representative of
the nionitored activity
including, when
appropriate, continuous
monitoring
~
Provide such other
information as may reasonably be required.
b)
The Agency may require every holder of an NPDES Permit for a
publicly owned and publicly regulated treatment
works, as a condition of
the NPDES Permit,
to require industrial
users ofsuch a treatment
works
to:
1)
Establish, maintain and
retain
records;
2)
Make reports;
3)
Install, calibrate,
use and maintain monitoring equipment or
methods (including where appropriate biological monitoring
methods);
4)
Take samples of effluents (in accordance with such methods,
at
such locations, at
such intervals,
and in such a manner as may be
prescribed);
and
5)
Provide such other information as may reasonably be required.
c)
All such
requirements
shall be included as
conditions of the
NPDES
Permit issued to
the discharger,
and shall be at least as stringent as those
required by applicable federal
regulations when these become effective.
cIr~i~
(~r~
JPN
13
~Q03
ILLINOIS POLLUTION CONTROL BOARD
STATE OF ILLINOIS
Pollution
Control Board
IN THE MAFFER OF:
PROPOSED AMENDMENTS TO:
)
PART 309 SUBPART A
-
)
35
III. Adm Code 309.105, 309.7,
309.8,
)
“p,
~i3~
‘7
309.9, 309.10, 309.12, 309.13,
309.14,
309.117,309.119,309.143,309.147;
and
PROPOSED
35
I11.Adm, Code
120
)
through
122
-
NPDES PERMITS AND
)
PERMITTING PROCEDURES
)
STATEMENT OF REASONS
The Environmental
Law and Policy Center ofthe Midwest,
Illinois Chapter of the Sierra
Club, Prairie Rivers Network
and
the 225
persons whose signatures
are
filed with this
petition,
petition the Illinois Pollution Control Board (“IPCB”) to
amend Illinois Administrative Code
Title 35
Environmental
Protection Act;
Subtitle C: Water Pollution; Chapter I:
Pollution Control
Board; Part 309
subpart A. The amendments sought are to improve Illinois’
implementation of
the Clean Water Act, 33 U.S.C.
Section
1251
et seq., and the National Pollutant Discharge
Elimination System (NPDES) by amending the relevant regulations to require that:
•
The public is properly informed ofdraft NPDES permits
and is provided a fair opportunity
to
comment on substantial terms ofpermits before they are issued;
•
hearings are held when necessary to allow the public an opportunity
to comment on draft permits
and important revisions to draft permits;
•
the administrative record regarding eachpermit shows that the permit was properlyissued
and
that the permit does not purport to allow discharges that would
cause or contribute to a violation
ofIllinois water quality standards;
•
necessary monitoring ofNPDES
limits and conditions are include in permits; and,
•
Illinois permit procedures and NPDES
permits cothply with the Clean Water Act.
Adoption ofthe proposed amendments by the IPCB will improve the Illinois NPDES
permitting process, Illinois EPA issued permits, and Illinois water quality.
)
1
I.
The Proposed Amendments, Facts Supporting the Proposal and the Purpose and
Effect of the Proposal
It is proposed to amend Part
309 as discussed below.
Proposed New 309.105(1)
-
The proposed language
increase the situations in which a
NPDES permit may not be issued to include
cases in which “The public has not had a fair
oppbrtunity
to comment on all substantive terms ofthe permit.” It is beyond debate that both the
federal Clean Water Act and the Illinois Environmental
Protection Act mandate that members of
the public be granted broad opportunities to
participate in the permitting process. The proposed
amendment would help assure an opportunity for public participation as to
all NPDES permits.
The opportunity formeaningful public participation is an essential
part
ofthe
NPDES
pennitting process.
Section 101(e),
33 U.S.C.
§
1251(e), of the Clean Water Act provides:
Public participation in thedevelopment,revision,
and enforcement ofany
regulation, standard, effluent limitation, plan, orprogram established by
the Administrator or
any State under this chapter shall be provided for,
encouraged, and assisted by the Administrator and
the States.
Section 402 ofthe Clean Water Act,
33 U.S.C.
§
1342, requires that effective public
participation be allowed
in the
drafting
of
NPDES permits.
In a case involving athird-party
appeal ofaNPDES permit, the United States Court ofAppeals for the First Circuit wrote that
Congress enactedpublicparticipation rules understandingthat
“these
regulations would
do
more
than
pay lip
service
to
public
participation; instead ‘the public must have a genuine opportunity to
speak
on the issue ofprotection ofits
waters’
on
federal,
state and
local levels.” Natural Resources Defense Council v. U.S.E.P.A.. 859
F.2d 156,177 (D.C. Cir.
1988) (citations omitted) (construing public
participation
regulations
in
state
enforcement
process).
The
legislative
history
of the
CWA
also
echoes
the
desire
“that
its
provisions
be
administered
and
enforced
in
a
fishbowl-like
atmosphere.”
2
Adams v.
U.S. Environmental Protection Agency, 38 F.3d 43, 52
(1st Cir.
1994).
See also Webb
v. The Honorable William
L.
Fury,
167 W.Va.
434,
282
S.E.2d 28,
38
n.5
(W. Va. 1981)
(important role ofpublic participation
in permit writing and enforcement discussed in a case
involving
a suit to silence public opposition to certain mining).
Illinois law
also requires that the public be
allowed to participate fully in the NPDES
permitting process. This is true because, as discussed
further below, Illinois law requires that
Clean Water Act requirements be followed in NPDES permitting. Further, the Illinois General
Assembly in passing the Environmental Protection Act acted
inter alia
to
“assure that
all
interests
are
given a full hearing and to
increase public
participation in the task of protecting the
environment
...“
415 ILCS
5/2
(a)(v).
Public participation must be allowed as to all substantive provisions ofthe permit.
For
example, the monitoring conditions ofa permit must be developed in public, notbehind closed
doors.
The Environmental Appeals Board, a specialized federal administrative board which
reviews NPDES permits issued by the U.S. Environmental Protection Agency, rendered a
decision that makes clear that all important terms ofa permit must be subject to public
participation
and opportunity for comment.
In Re: Government ofthe District ofColumbia
Municipal Senarate Storm Sewer Systems,
20
EAD (2002) (hereinafter ~DCStorm Sewer
Systems” attached as Ex. A) held that the U.S. EPA had erred in granting a NPDES permit to the
District ofColumbia that allowed certain monitoring conditions
for a discharge on “Hickey Run”
to be developed after issuance ofthe permit. The Environmental Appeals Board wrote:
While
we recognize that the monitoring requirements
are
expected to
be added
at the time ofthe District’s First Annual Report and thus should be
in place before
the Hickey Run effluent limit becomes effective, we are troubled that this would
3
be accomplished through aminor permit modification without notice and
opportunity for public conmient.
See Permit pts. III.E &
IX.A.5
(as
amended).
Given that the regulations appear to contemplate that monitoring
requirements
ordinarily
be included as up-front permit conditions
—
conditions which would
thus ordinarily be subjected to public notice and comment
and the fact that we
find nothing
in the regulations
allowing for minor permit modifications that
authorizes
use ofa minor permit modification
in
this
setting, we conclude that
this
Permit does not meet minimum regulatory requirements and that remand of these
parts ofthe Permit is necessary. (pp. 32-33)
The Appellate Court in Prairie
Rivers
Network v. Illinois Pollution Control
Board No. 4-
01-0801 (hereinafter “Prairie Rivers”,
Slip Opinion attached as Ex.
B), which considered a
number of objections raised
to public participation procedures used in the consideration of a
particular
NPDES permit, expressed
no opinion on the merits ofappellant’s “policy-related”
arguments relating to
flaws in Illinois’ public participation practices. The Appellate Court
indicated that such issues should be
taken
to
the Board. (Slip op. at 10-11) Fairness, as well as
sound policy, favors allowing citizens to participate in decisions that effect the-health ofIllinois
rivers,
lakes
and streams. Accordingly, we herebypetition the IPCB for changes to
Part 309 that
will prevent permits from being issued if the public
has not been allowed an opportunity to
comment on all substantial terms ofthe permit.
Petitioners do not anticipate that many permits will be overturned on appeal based on the
proposed provision. Illinois EPA currently normally affords the public an opportunity
to
comment on all substantive provisions of NPDES permits and adoption ofthe proposed-rule-will
probably cause Illinois EPA to be even more careful in this regard.
Proposed New 309.105(g)
-
The proposed language
adds
to
the situations in which an
NPDES permit may not be issued the case in which the “permit, permit conditions or procedures
used to
draft or issue the permit are not consistent with any applicable federal law.” The wording
4
of this proposed provision borrows
from 415
ILCS
5/28.l(c)(4), which pertains to adjusted
standards.
Illinois law is clear that Illinois environmental
statutes and regulations should be read to
accord with the Clean Water Act and other federal laws.
Peabody Coal Co. v. Pollution Control
,
36111. App.
5,344 N.E.2d 279, 285
(5th
Dist.
1976);
see
also 415 III.
Comp. Stat.
5/13(b)
(Bo~rdrules shall be consistent with the Clean
Water Act). If the Illinois Environmental
Protection Act is interpreted or implemented by Illinois in
such a manner that
it does not fully
implement the letter and policies ofthe Clean Water Act,
Illinois could
lose the ability
to
administrate NPDES permitting in Illinois.
See 40 C.F.R. §~123.63,123.64(b) (U.S. EPA may
withdraw program approval when a state program no longer complies with federal regulations,
person may petition U.S. EPA for withdrawal ofstate program authority).
It is the express policy
of the General Assembly that the IPCB and the Illinois EPA administer the Clean Water Act in a
maimer consistent with Illinois administering the NPDES permitting system. 415 ILCS
5/1 1(a)(7),
(b). Clearly,
the Illinois legislature intended Illinois permits and procedures to comply
with federal
law.
Nonetheless, the Appellate Court in Prairie Rivers
held that
any conflicts between
Illinois regulations and
federal law can only be corrected by the IPCB by changing the
regulations (slip op.
at 11) or by U.S. EPA disapproving of the Illinois NPDES permit program
(Slip op.
at
9). Accordingly, petitioners ask the IPCB to make clear through this
proposed
regulatory change that
in the future no deviations will be allowed between federal legal
requirements
and Illinois NPDES program and that permits may only be issued if they meet at
least the minimum requirements offederal
law.
5
Proposed New 309,107(c)
-
Giving a copy ofthe application to the Illinois Department
of Natural Resources
(“IDNR”)
is clearly
beneficial.
IDNR
has
much ofthe responsibility for
studying and protecting wildlife in Illinois. Giving notice to
IDNR is already required as to
permits proposing new or increased discharges (see 35
Ill.
Adm. Code
l05(f)(l)(F)) and should
be done as a matter ofcourse.
The proposal allows for a memorandum ofunderstanding to be reached between IEPA
and IDNR that will specif~’
the terms for giving IDNR notice.
It is our understandingthat
such a
memorandum is already under discussion between Illinois EPA and IDNR.
Proposed Additional Clause to 309.108(c) and Proposed New 309.108(e)
-
The
proposed revisions to Section 309.108 elaborate on the matters that Illinois EPA shall discuss
in
its statement of the basis
for the permit and provide that the agency shall create a draft
administrative record in
support of its tentative decision to issue the permit.
Section 3 9(a) of the Environmental Protection Act that states that permits shall only be
issued “upon proof by the applicant” that the permit “will not cause a violation ofthis Act or the
regulations hereunder.”
415
ILCS
5/39(a);
See also Panhandle Eastern Pipe Line Co. v. Illinois
EM,
314
Ill. App. 3d 296,
743 N.E. 2d
18,24
(4th
Dist. 2000); ESG Watts. Inc. v. Pollution
Control Board, 224
III. App.
3d 592, 586
N.E. 2d
1320,
1322 (3d Dist.
1992).
The
Environmental Protection Act also implicitly requires that the Illinois EPA create a reviewable
record.
415 Ill. Comp. Stat.
5/40(d)
and (e), which govern
appeals both refer to the
“administrative record” as the subject of IPCB review and 5/40(e) states that
“the Board shall
hearthe petition
...
exclusively on the basis ofthe record before the Agency.”
Plainly, then, it is
necessary that a clear record supporting the Illinois EPA’s permit decision be created.
6
Although use ofthe U.S. EPA NPDES
Permit Writers’ Manual (December
1996)
(hereinafter“Permit Writers’ Manual”portions of which are attached as Ex. C)
is not strictly
mandatory on state NPDES programs, its discussion ofthe need for creation ofa clear
administrative record is useful here:
The administrative record
is the foundation for issuing permits. IfEPA is the
issuer, the contents ofthe administrative record areprescribed by regulation (see
40CFR §~124.9
and
124.18). All supporting materials must be made available
to
the public, whether a
State, Territory, Tribe or EPA issues the permit. The
importance ofmaintaining the permit records in
a neat, orderly, complete, and
retrievable form cannot
be over
emphasized. The record allows personnel from
the permitting agency to reconstruct thejustification for a given permit.
It also
must be made available to the public at any time and may be examined during the
public comment period and any subsequent public hearing.
(~J
11.1.1, p.193)
Proposed Additional Clause in 309.109(a)
-
This amendment
is proposed to recognize
re-noticed draft permits.
This issue
is discussed further below in connection with proposed new
sections 309.12 1 and 309.122.
Proposed
Deletion From 309.109(b)
and 309.113(a)(10)(A)
-
This
is merely a
clarifying provision which eliminates an inconsistency in the terminology in
the regulations.
Its
is proposed to strike the reference to
a “30 day” comment period because the comment period
may be longer than 30days under the first sentence of309.109(b).
Proposed Additions to 309.110(1)
-
This proposed revision fl.irther specifies the
information that must be contained in the permit notice. The information to be added is useful
and much of it is already given by IllinoisEPA asamatterofcourse.
-
40 CFR §l24.10(d)(v), which is applicable to
all states that wish to administer a NPDES
program, explicitly requires providing all
ofthe information that the proposal would require to be
7
supplied. If Illinois
is to
continue administering
an NPDES program, itmust adopt rules
-
regarding notice that are at least as stringent as the federally required language.
40 CFR
123.25.
Proposed Additions to 309.113(a)
-
This proposed language would
add information to
the fact sheets that
is necessary for documentation of compliance with 35
Ill. Adm. Code
302.102, 302.105 and 304.105. The portion of the proposal that requires a “brief descriptionof
the
isignificant
factual, legal, methodological
and policy questions considered in
preparing the
draft permit” is federally required language taken directly from 40 CFR
§
124.8(a). The portion of
the proposed language that is nottaken directly from 40 CFR
§
124.8
is reasonably necessary to
inform the public of the critical
facts regarding the permit and comply with 40 CFR
§
124.56,
which is also directly applicable to states wishing to
administer a NPDES program.
To the extent that the proposal goes beyond what is explicitly required by applicable
federal regulations,
it requires information that
is necessary to understanding the basis for the
permit. As is explained by the U.S. EPA
Permit Writers Handbook, “a detailed
discussion of
permit limits for each pollutant should be included in the fact sheet” and:
For each pollutant the following information is necessary:
Calculation and assumptions
-
-
Production
-
Flow
Types oflimitations (i.e.
effluent guideline-, water quality-, or BPJ
best
professional judgement-based)
Whether the effluent guidelines used were BPT, BCT or BAT
The water quality standards or criteria used
Whetherany pollutants were indicators for other pollutants
Citations to appropriate wasteload allocation studies, guidance documents,
other references. ¶11.1
(p. 197)
Proposed Change to 309.114(c)
-
Spelling Correction on
“Navigable”.
Proposed Additional Sentence to 309.117
-
This proposal requires that Illinois EPA
identi& the materials it relied on in
making its
tentative decision regarding
thepennit. This
8
information is needed to
allow proper review ofIllinois EPA permit decisions.
Particularly
given
that Illinois law restricts third party review to
documents in the administrative record, 415
ILCS 5/40(e), the rules should leave no room for debate as to
what was properly before the
Agency.
See also,
Permit Writers’ Manual
§
11.1.1.
Proposed Additions to 309.112
and 309.119
-
This language is added simply to
prevent
anj confusion regarding the applicability ofproposed sections 309.121
and
309.122, discussed
below. The change to 309.119 is necessary to eliminate the inference drawn by the IPCB and the
Appellate Court in
Prairie Rivers that the public should never be allowed an opportunity
to
comment on a revised permit even
in circumstances in which the Clean Water Act or proper
concern for public participation requires that opportunity for additional comment be allowed.
Proposed New 309.120
-
This proposed amendment provides that persons wanting to
object to permits or permit conditions
must make their points during the public comment period.
The proposed section is modeled on 40 CFR
§
124.13, which is used by U.S. EPA in states in
which
it administers the NPDES program.
The federal
regulation that was used
as a model for the proposal is not mandatory on the
states
and Illinois
is not legally bound to track exactly
this
federal procedure. However, fairness
and administrative economy call for all persons, including applicants, to
raise all reasonably
ascertainable issues and submit all reasonably available arguments to the Illinois EPA before the
close ofthe public comment period. There is no excuse for failing to present
arguments to
Illinois EPA during the comment period.
Proposed New
309.121
and Proposed New 309.122
-
The proposed language for
309.121
is borrowed from 40 CFR
§
124.14(a) which is npt directly applicable to the states, but
9
which should be
adopted by Illinois.
It sets forth
an orderly procedure for reopening the record
when circumstances make
it fair and necessary to do so.
The proposed language of309.122 is based on 40 CFR
§
124.14(b) and requires that the
record be reopened
to allow further
comment
in
a limited class ofcircumstances.
The proposed
language is less restrictive than 40 CFR
§
124.14(b) which appears to require a new comment
perfod whenever a draft permit
is modified.
The proposed language only would require a new
comment period ifthe changes are
significant. Although the specific language proposed is not
mandatory on the states, making allowance for reopening ofthe hearing record after changes are
made to
a draft permit is required by the Clean Water Act and basic concepts offairness.
Decisions by the JPCB and the Appellate Court in Prairie
Rivers have made it absolutely
imperative that an
amendmentbe made that makes clear that another opportunity for public
comment must be allowed in cases in which substantial changes have been made to
the draft
permit on which the public was allowed to comment. Prairie Rivers held that a second
opportunity for public comment can never be allowed under Illinois law no matter how
significant the changes that are made
to the draft permit by Illinois EPA.
This allows as a
practical matter the complete destruction ofthe public’s ability to participate in the process and is
not tolerable under the Clean Water Act.
That the public must be allowed
in some
circumstances to comment on a revised draft
permit can be seen by considering a simple example.
Let us assume that
in a particular draft
permit all ofthe pollutants that may be
discharged are strictly limited and monitored so as to
prevent any damage to the receiving waters or violation ofwater quality standards. No members
ofthe public would probably even bother to comment after receiving notice of such a draft
permit. Now, what if Illinois EPA, after the close ofthe public comment period, eliminated
10
effluent limits or critical monitoring from the permit and then issued the transmogrified permit as
the final permit ? Certainly, persons
concerned with
the receiving waters would want to
object,
but, if there
can
never be a second round ofopportunity
for public comment, those persons are
precluded from having any sayon the actual terms ofthe permit as issued.
Persons concerned about the receiving water in the example could take a third party
ap$eal to the IPCB, but they would have a very hard time establishing a basis for appeal.
Appeals
to the Board are limited to the record before theAgency (415 ILCS 5/40(e)), but, under the facts
presented by the example, there will be no comments in the record showing that
the permit needs
the effluent limits ormonitoring requirements that were deleted after the close of the comment
period. No one would have had
any chance to put anything into the record showing that the
deletions
were improper because no round ofcomment was allowed after the deletions were
made. Under this example, effective public participation is completely denied but nothing can be
done about it under current Illinois regulations.
It is not suggested that the Illinois EPA currently makes ahabit of deleting substantial
protections from permits after the close ofthe public comment period. Petitioners believe,
however,
that in
a few cases changes have been made to draft permits
in circumstances in which
further comment should have been allowed. The key point is that Illinois procedures allow a
wholesale circumvention ofpublic participation. This loophole must be plugged or Illinois’
NPDES program is very unfair and
violates
the Clean Water Act.
Judicial and administrative decisions show that the Clean Water Act and proper respect
for public participation requires that provision be made for reopening the administrative record to
allow further public comment in cases where the agency has decided to make substantial changes
in the draft permit.
When the revised permit substantially deviates from the draft permit, the
11
public is not given
an opportunity
to comment on the permit that
is actually issued unless the
revised permit is submitted to public comment.
-
In Hi-Line Svortsmen Club
v. Milk River Irrigation Districts, 786
P.2d
13
(Mont.
1990),
persons concerned with potential injury to fisheries objected to certification under
§
401 ofthe
Clean Water Act ofaproposal to allow warm
water from an auxiliary outlet from a reservoir to
flo~’
into an
important fishery.
fiat
14-15.
During proceedings regarding the auxiliary outlet
proposal, the applicant proposed a scheme whereby cooler water would be siphoned from below
the auxiliaryoutlet.
flat
16.
This proposal was approved by the decision maker without giving
the public a chance
to comment.
a
Although this siphon proposal was designed to meet
environmental concerns, the Montana Supreme Court
affirmed
the decision ofthe trial court that
due process would be violated ifthe Clean Water Act
§
401
certification was granted without
giving the third parties the opportunity
in hearings to explore the proposal ofa using a siphon to
prevent thermal pollution.
fiat
17.
Similarly, a very recent decision by U.S. EPA Administrator Christine Todd Whitman
on
a permit granted under the Clean Air Act (“CAA”) provides strong persuasive authority
regarding what was required. In Mailer of Orange Recycling and
Ethanol Production Facility.
Pencor-Masada Oxvnol LLC (Petition
No: 11-2000-07),
Administrator
Whitman
decided that
revisions made by the New York State Department ofConservation (“NYSDEC”) in consultation
with the applicant and U.S. EPA to
adraft permit after the close ofthe public
comment period,
while sound, had to be renoticed to allow
further comment. Administrator
Whitman wrote:
The CAA
and its implementing regulations at
part
70 provide for public comment
on “draft” permits and generally do not require permitting authorities to conduct a
second -round ofcomments when sending the revised “proposed” permit to EPA
for review. It is abasic principle of administrative law that agencies are
encouraged to
learn from public comments
and, where appropriate, make changes
12
that are a “logical outgrowth” of the original proposal.
See, e.g.,
Sierra Club
v.
Costle,
657 F.2d 298,
352
(DC Cir.
1981). However, there are well recognized
limits to the concept of“logical outgrowth”
in the context ofAgency rulemaking
that, by analogy, apply to title V
permits as well. As the US Court ofAppeals for
the DC Circuit
has
explained, “if the final rule deviates too sharply from the
proposal, affected parties will be deprived of notice and an opportunity
to respond
to the proposal.”
Small Refiner Lead Phase-Down TaskForce
v.
EPA,
705
F.2d
506,
547 (DC Cir. 1983) (vacating portion of final
CAA
rule governing leaded
gasoline because agency notice was “too general” and did not apprise interested
parties “with reasonable specificity” of the range of alternatives being
considered). See
also
Shell Oil
Company v.
EPA,
950 F.2d 741
(DC Cir.
1991)
(remanding final
RCRA “mixture and derivedfrom”
rule
because “interested
parties cannot
be expected to
divine the EPA’s unspoken
thoughts”);
Ober v.
EPA,
84 F.3d 304, 312
(9th
Cir.
1996) (requiring an additional round ofpublic
comment on EPA’s approval of Arizona’s PM-b
Implementation Plan because
public never had an opportunity
to comment on state’s post-comment period
justifications which were critical to EPA’s approval decision). Courts have noted
that providing the public meaningful notice improves the quality ofagency
decisionmaking, promotes fairness to
affected parties, and enhances the quality of
judicial
review.
Small Refiner,
705 F.2d at
547. I find that these fundamental
principles apply with equal force in the context of title V permitting.
Otherwise, if
a final permit no longer resembled the permit that the public commented upon,
then the public would be deprived ofthe opportunity
to comment guaranteed by
the
CAA
and
EPA’s rules.
Determining how much notice is sufficient is inherently a matter of
judgment. In this case, however, the operational constraints imposed on the
facility
in the proposed permit were so
significantly different from those in
the
draft permit that I find that additional public notice on this particular aspect ofthe
permit is required.(Slip op.
at 7-8, footnote omitted)’
It must be emphasized here that there are two things that proposed 309.121
and
309.122
do not do. First, these provisions do not require an infinite number of rounds ofpublic comment.
An additional round ofpublic comment must only be allowed in very limited circumstances and
the need for more than one additional round ofpublic comment will probably never arise.
‘This decision is attached as Ex. D.
It is also published on the Internet at
www.epa.gov/rgytgrnj/programs/ortdlair/title5/petitiondb/petitions/masasadecision2000.pdf.
13
Second, even when it is decided that additional public comment should be
allowed, it is
not
necessary
to allow any additional hearing although Illinois EPA may hold additional hearings
after significantly revising apermit if it believes that itwould be useful to allowadditional
comment in that form.
Thus, even in those very few cases in which it is necessary to allow
additional comment, allowing written comment
will normally suffice.
Proposed New 309.123
-
This language simply makes clear what is in the “record before
the Agency” so as to prevent any
confusion as to the matters that areproperly before the Board in
hearing any appeal under 415
ILCS 5/40(d)
or (e).
Proposed New 309.b43 (a)
-
The proposed language requires that effluent limitations in
NPDES permits control all pollutants sufficiently such that the discharge does not cause or
contribute to a violation ofwaterquality standards,
including narrative standards.
This language
is taken verbatim from 40 CFR 122.44(d)(l)(i). Language as stringent, ormore
stringent, must
be
followed by Illinois
EPA if it is to continue to administer the NPDES program. These
requirements have been recognized by the IPCB in the past. In the Mailer of: Petition of
Commonwealth Edison Company for Adjusted Standard from
35111.
Adm.
Code 302.211(dI and
(~),
AS 96-10 (PCB, October 3,
1996)
The Board could incorporate 40 CFR
122.48
by reference. ~
415
ILCS
5/7.2. However,
in view ofthe importance ofthis
issue, it is best to place the federal requirement directly into the
Illinois regulations.
-
309.143(b) in the proposal consists of the current 309.143
Proposed additions to 309.146(a)(2)
-
The proposed language makes clear that effluent
limits and special conditions in the permit shall be
monitored and
enforceable both
through
Agency and citizen actions.
~
Permit Writer’s Handbook Chapter 7; United States v.
14
AlleghenyLudlum
Corp.,
118 F.Supp. 2d
615, 618
(W.D. Pa.
2000) (importance ofself-
monitoring and reporting under Clean Water Act)
Proposed New 309.146(a)(5)
-
This language is
taken verbatim from 40 CFR
§
122.48,
which is applicable to state programs. Language as stringent, ormore stringent, is mandatory for
Illinois
EPA if it is to
continue to administer the NIPDES program in Illinois. 40 CFR §123.25.
A jiermit
that fails to spell out the necessary monitoring violates this regulation and the public’s
right
to participate
in commenting on monitoring provisions.
See also DC Storm Sewer Systems
Again, the Board could incorporate 40 CFR
§
122.48
by reference, $~ç
415 ILCS 5/7.2.
However, because there has been confusion in thepast to the extent that it has sometimes by seen
as acceptable to
issue a permit without
all of the key monitoring terms in the permit,
it is wiser
for the Board to incorporate this provision directly into the Board’s regulations.
It is proposed to renumber what is currently 309.146(a)(5)
as 309.146(a)(6).
H. Affected Sources and the Economic Impact of the Proposal
It
is unclear whether any sources, facilities and dischargers will be affected by the
proposal and
it is also unclear if the proposal
will have any significant economic impact. This is
true because many of the procedures established by the proposal are already being followed to
a
large degree by the Illinois EPA in writing NPDES permits.
This is
true
although, under Prairie
Rivers, it appears Illinois EPA may not currently be required by Illinois law to follow those
procedures or otherwise comply with federal
law.
To the extent that the proposal
will require the Illinois EPA to give notice, allow public
comment or create descriptions or documents that it does not
currently create, the proposal may
have
some effect on the speed in which the agency makes permitting decisions. It is believed by
petitioners,
however, that the proposal will ultimately expedite consideration ofNPDES permit
15
applications by creating clearer and fairer procedures. As more information becomes available
through proper notices, fact sheets and fair hearings, there will be less need for time consuming
Freedom ofInformation Act document requests, hearings on
matters
that could havebeen
avoided had the necessary information been recorded, and permit appeals to the IPCB. Proposed
309.120 will serve directly to expedite proceedings by preventing persons
from attempting to
base appeals on arguments that they did not place in the administrative record. Moreover,
by
assuring fair procedures and that permits are
issued in compliance with the Clean Water Act, the
proposal as a whole will prevent future delays and controversies regarding Illinois NPDES
permits and Illinois EPA’s permit writing authority.
To the extent that improved permitting procedures, permits
and
compliance with federal
laws leads to
the issuance ofpermits
that
require dischargers to reduce the extent or
environmental
impacts of theirdischarges, there may be some new costs imposed on dischargers.
Petitioners believe that some such costs will result
from enactment of
this
proposal but that the
extent ofsuch impacts is impossible to estimate. Moreover,
any such economic impacts will be
necessary to protect the environment and comply with the Clean Water Act.
Finally,
improvements to the Illinois NPDES permitting process will result in better
NPDES permits. This in turn will reduce water pollution and have a positive -economic impact on
all ofthe citizens,businesses and public entities in Illinois that benefit directly or-indirectly from
a healthier Illinois environment. As was specifically found by the Illinois General Assembly,
“pollution of the waters ofthis State
....
impairs domestic, agricultural, industrial, recreational,
and other beneficial uses ofwater and
depresses property values
“415 ILCS
5/1
I(a)(l).
16
CONCLUSION
The Board should adopt the proposed changes to
part
309 to assure that proper public
participation in NPDES permitting
is allowed, that Illinois NPDES permits
are issued
in
compliance with federal
law and
that Illinois NPDES permits properly protect Illinois
rivers,
lakes and streams.
g.EttingerS3l2SO45I~
Counselfor Environmental Law & Policy
Center, Prairie Rivers Network and Sierra Club
Environmental Law& PolicyCenter
35 E. Wacker Dr. Suite 1300
Chicago, Illinois 60601-2110
312 795 3707
January 13, 2003
17
(Slip Opinion)
NOTICE:
This
opinion
is
subject
to
formal
revision
before
publication
in the Environmental Administrative Decisions(E.A.D.).
Readers
are requested to
notitS’ the
Environmental Appeals
Board,
U.S.
Environmental Protection Agency, Washington,
D.C. 20460,
of
any typographical or other format
errors, in order that corrections
may
be made before publication.
BEFORE THE ENVIRONMENTAL APPEALS
BOARD
UNITED STATES ENVIRONMENTAL PROTECTION
AGENCY
WASHINGTON,
D.C.
.
)
Inre:
)
)
Government of the
District of
)
Columbia
Municipal
Separate
)
Stomi Sewer System
)
NPDES Permit No.
DC 0000221
)
)
NPDES Appeal Nos. 00-14
&
01-09
Decided
February 20, 2002
ORDER DEN YING RE
VIEWIN
PART
AND
REMANDING IN PART
Before
Environmental
Appeals
Judges
Scott
C
Edward E. Reich,
and
Kathie A.
Stein.
Fulto,z,
EXHIBIT A
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
NPDES
Appeal Nos. 00-14 &
0 1-09
ORDER
DENYING REVIEW
IN
PART
AND REMANDING IN
PART
Decided February
20, 2002
Syllabus
In April2000,
U.S.
EPA Region Ill (the “Region”) issued
a National
Pollution
Discharge Elimination System (“NPDES”)permit, number DC
0000221
(the “Permit”),
to the Government of the
District of Columbia (the “District”).
The Permit authorizes
storm
water
discharges
from
the
District’s
municipal
separate
storm
sewer
system
(“MS4”).
The Permit
requires
the
District to
use
various
best
management
practices
(“EMPs”) to control pollutant
discharges in furtherance of attaining the District’s water
quality
standards.
The
required
BMPs
are
set
forth
in
the
District’s
storm
water
management
plan (“SWMP”), which
is incorporated into the
Permit by
reference.
On
August II, 2000, Friends of the
Earth and Defenders of Wildlife (“Petitioners”) timely
filed
a petition
requesting that the Environmental Appeals Board review the Permit (the
‘Petition”) (the
Petitioners also
filed
a
second petition
after the Region withdrew
and
reissued
a portion of the Permit).
HELD:
The
Permit
is
remanded
to
the
Region
for
further
analysis
and
explanation
in
a
number
of
areas.
Petitioners
and
the
Region
have
grouped
their
arguments
in
the nine
categories described
below,
and
the Board’s holding
on
each
is
summarized as
follows:
I.
Compliance
with
Water
Quality
Standards.
Petitioners
object
to
the
Permit’s conditions that specify
BMPs, rather than numeric
limits, to control
pollutant
discharges
and
meet
the
District’s water quality
standards.
The
Petitioners’
general
argument that the Region violated
an affirmative duty to
set numeric
limits is rejected,
in
keeping with
the
Board’s decision on similar issues
in
In re Ariz.
Mun.
Star,,,
Water
NPDES Permits,
7
E.A.D.
646
(1998).
The
Petitioners’
more specific
argument
that
numeric limits could
have bcen
set equal to the
numeric water quality
standards
of the
receiving waters is also rejected
on the grounds that Petitioners failed to demonstrate that
they raised this argument
and
the cited authority during the public comment period.
The
Petitioners’ argument that the Region should have included narrative provisions requiring
compliance with water quality
standards is also rejected
on
the grounds that there
is
no
statutory or regulatory provision
that requires
use of narrative limits.
2
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
There is merit, however, to Petitioners’
argument thatthe Region failed to show
that
the
selected
BMPs
will
be
adequate
to
ensure
compliance
with
water
quality
standards.
First,
it is not clear
that the Region’s determination that the specified BMPs
are “reasonably capable” of achieving water quality
standards
fully comports with 40
C.F.R.
§
122.4(d),
which
prohibits
issuing
a permit
“when
imposition of conditions
cannot
ensure
compliance with the applicable water quality requirements ofall affected
states.” (emphasis added). Second, even accepting the Region’s suggestion that ensuring
compliance was what the permit writer has in mind,
there is nothing
in the record, apart
from
the District’ssection 401 certification, that supports the conclusion that the Permit
would, in fact, achieve water quality standards.
Without such record support the Board
cannot
conclude
that the approach
selected by the
Region is rational
in light of all
the
information
in the
record.
The
Region
does not
dispute
that
the Region
cannot
rely
exclusively on the District’s section 401
certification, at least in a circumstance like this
one
in
which there
is
a body
of information
drawing the
certification
into question.
Accordingly, additional
record support for the Region’s determination is
required, and
the Permit is remanded for fUrther analysis in this regard.
2.
Mickey
Run.
Petitioners
argue that
the Permit
is
deficient
in
that
(a) it
contains an aggregate numeric effluent limitfor fouroutfalls into Mickey Run instead of
a
limit for each outfall
and (b)
it contains monitoring requirements that the Petitioners
allege
are inadequate.
The regulation cited by Petitioners contains the disjunctive phrase
“outfall
or
other discharge
point”
and
therefore
must be
read
as
contemplating some
flexibility in appropriate circumstances to frame effluent limitsat
a discharge point other
than the outfall.
There is no clear error in the
Region’s conclusion that,
in the
unique
circumstances of this case,
an aggregate limitfixed
at
a point proximate to four closely
connected outfalls was appropriate.
However, the proposed delayed development ofthe
Mickey Run
monitoring requirements
is
problematic in
two
respects.
First,
both 40
C.F.R.
§
122.48tb) and 40 C.F.R.
§
122.440) require
that certain monitoring conditions
be included in all permits.
The Region has not explained how its issuance of this Permit,
which
does
not
at
its
inception
contain
monitoring
requirements
for
Mickey
Run,
comports with the regulatory directive that all permits include these conditions.
Second,
while the monitoring requirements are expected to be added
at the time ofthe District’s
first
annual
report and
thus should be
in
place
before
the
Mickey Run effluent limit
becomes effective, the Board finds it troubling that this would be accomplished through
minor permit modification without notice
and opportunity for public comment.
Given
that the
regulations
appear to
contemplate that
monitoring requirements ordinarily be
included
as up-front
permit conditions
--
conditions
which
would
thus ordinarily
be
subjected to public notice
and comment--and there does not appearto be anything in the
regulations allowing forminorpermit modifications that authorizes use ofa minor permit
modification in this setting,
the Board concludes that this Permit does not meet minimum
regulatory requirements and that remand of these parts of the Permit is necessary.
3.
Reductions to the
“Maximum Extent
Practicable”.
Petitioners’
argument
that the
Region erred
in detcrminating
that
the
Permit will
reduce storm water pollutant
discharges to the maximum extent practicable (“MEP”) as required by CWA
§
402(p)
is
GOVERNMENT OF THE DISTRICT OF COLUMBIA
3
MUNICIPAL SEPARATE STORM SEWER
SYSTEM
rejected.
The
record demonstrates that
the Region duly considered the issue
raised by
Petitioners
in their comments,
and the record does not
lead to the conclusion that any
additional BMPs beyond those identified in the
Permit are
practicable in
this
case.
4.
Deferral of Complete
l’ro2ram.
Petitioners’
arguments that
the
Permit’s
provision for upgrading the SWMP indicates that the Permit is inadequate at its inception
is
rejected.
The
evaluation
and
upgrade requirement
incorporates
into
the
Permit
a
process
for
adjusting
the
Permit’s
terms
and
conditions
to
take
into
account
new
knowledge and changed circumstances affecting practicality ofBMPs.
This adjustment
process does not imply that the Region has failed
to properly assess MEP at
the time of
the Permit’s issuance; it simply recognizes that what is practicable will change overtime
and
that the Permit should be adaptable to such
changes.
5.
Failure to Reauire Compliance Within
3
Years.
Petitioners’ argument that
the Permit fails to require compliance within the three-year
time period set forth
in CWA
§
402(p)(4)
is rejected.
The Permit does not authorize
a deferred
implementation of the
BMPs
that were determined to be MEP at the time of
issuance
ofthe Permit; instead, the
Permit
simply recognizes that what is practicable will change during
the Permit’s term
and that upgrades of the Permit’s requirements should not be delayed until the Permit
is
renewed.
6 & 7.
Storm Water Implementation Plan and
FundinE.
Petitioners’ argument
that
the
“cost
benefit
and affordability”
analysis
required by
Part
III.E of the
Permit
violates
the CWA is rejected.
Information concerning
a
“cost benefit
analysis” of the
various
BMPs
is
relevant
to
the
upgrading
of the
SWMP
and
BMPs.
Cost
benefit
information, however,
is not relevant for purposes of determining compliance with
the
Permit’s requirement that
the District implement the BMPs
in its current SWMP.
The
Permit
recognizes
this
distinction
and
states
that “a)ffordability
cannot
be
used
as
a
defense for noncompliance.”
8.
Modifications.
The
Board
addresses
Petitioners’
various
arguments
regarding deficiencies
in
the Permit’s modification
provisions
as follows.
The
Board
adopts the Region’s interpretation that the reference in the Permit to 40 C.F.R.
§
122.63
serves to limitthe allowable extensions ofinterim compliance dates undertaken
as minor
modifications to “not more than
120
days after
the date specified in
the existing permit
and
provided
that it)
does
not
interfere with
attainment of the
final
compliance date
requirement.”
40 C.F.R.
§
l22.63(c).
The Region did not err in characterizing
the deadlines set forth in Part
I ll.A and
Part lIl.B.I0 ofthe Permit as “interim compliance dates
in
a schedule of compliance”
that may be modified
by minor modification as
set forth in 40 C.F.R.
§
122.63(c).
On
the
other
hand,
Permit
Parts
IV.A.l, VIllA,
IX.A.5
&
IX,C,
which
together
authorize
changes
in
monitoring location by minor modification, cannot be
squared with 40 CF. R.
§
122.63(c).
That section only authorizes the addition of new monitoring requirements
hy minor modification; it does not authorize
a
change in monitoring location
by
tilimlor
4
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE
STORM SEWER SYSTEM
modification.
Accordingly,
any
such
changes must be made through the formal “notice
and comment”
procedures of section
122.62.
Therefore
Permit
Parts lV.A.l, VIllA,
IX.A.5 & IX.C are remanded for revision.
Petitioners object to thePermit’s conditionsthat allow the Region to “approve”
schedules fordevelopingand implementingan enforcementplan (Petition, Part 111.8.11),
to approve
certain
additional SWMP program
activities (Petition, Part
111.8.12), and
to
approve, disapprove or revise the District’sAnnual Reports and Annual Implementation
Plans (Petition, Part DIE).
It is unclear whether
these provisions are simply intended to
reference
EPA
actions
in
administering
the
Permit
that
do
not
themselves
result
in
changes to the Permit (or the SWMPs
subsumed within the Permit) and thus should not
be
subjected to
formal
notice
and
comment
procedures, or whether
these
provisions,
referenced
as they
are
in the minor modification section of the permit,
are intended to
serve as a
basis for substantive changes to permit conditions.
The Region is directed
on
remand to clari& the extent to which
these provisions in the Permit allow for changes in
permit conditions by minor modification.
9.
Waivers and
Exemmions.
The
Petitioners argue
that
the District’s storm
water
regulations,
incorporated
into
the Permit
by
reference,
require
the
granting of
variouswaivers or exemptions that are in conflict with the CWA and EPA
mles.
Because
the
Region’s
Second
Response
to
Comments
does
not
challenge
the
validity
of
Petitioners’
Comments,
but
rather tends
to treat
them
as meritorious,
and
because
the
Region failed to make changes to the Permit orto otherwise address Petitioners’ concerns
regarding these waivers and exemptions, this portion of the
Permit is
remanded to
the
Region
to
either
make
appropriate
changes
to
the
Permit
or
to
explain
why
the
Petitioners’
comments do not merit such
changes.
Before
Environmental
Appeals
Judges
Scott
C.
Fulton,
Edward E. Rekh, and Kathie A. Stein.
Opinion ofthe Board by Judge
Fulton:
In
Apr11
2000,
U.S.
EPA Region
III (the
“Region”)
issued
a
National Pollution Discharge Elimination
System
(“NPDES”)t
permit,
number DC 0000221
(the “Permit”), tothe Governmentof the District of
Under the Clean Water Act (“CWA”), persons who discharge
pollutants from
point sources (discrete conveyances,
such
as pipes) into waters ofthe United States must
have
a permit
in order for the discharge
to be
lawful.
CWA
§
301,
33
U.S.C.
§
1311.
The National Pollutant Discharge Elimination System is the principal permitting program
under
the CWA.
CWA
§
402,33 U.S.C.
§
1342.
GOVERNMENT OF THE
DISTRICT OFCOLUMBIA
S
MUNICIPAL SEPARATE STORM
SEWER SYSTEM
Columbia.
The
Permit
authorizes
storm
water
discharges
from
the
District ofColumbia’s municipal separate stormsewer system (“MS4”).2
On August
II,
2000,
Friends of the
Earth
and
Defenders of Wildlife
(“Petitioners”) timely filed a petition requesting that the Environmental
Appeals Board review
the Permit (the “Petition”).3
The Petition argues
that
the
Region
clearly
erred
or
abused
its
discretion
in
setting
the
Permit’s conditions.
The Region has
fileda responseto the Petition,
and
both parties have filed supplemental reply briefs.
As discussed below, we have, based on our consideration of the
issues presented,
determined
that
a
number of issues
warrant
further
consideration by
the
Region.
Thus, we remand
the
Permit,
in part,
for
further proceedings consistent with this decision.
I.
BACKGROUND
A.
Factual
and Procedural Background
The MS4 that
is owned and operated by
the Government of the
District
of Columbia (the
“District”)
discharges
storm water
into
the
Potomac
and
Anacostia
Rivers
and
their tributaries.
Pursuant
to
the
requirements
for
system-wide
MS4
permitting
set
forth
in
CWA
§
402(p)(4) and the implementing regulations at 40 C.F.R.
§
122.26(d),
2Under CWA
§
402@)
and 40 C.F.R.
§
122.26,
an NPDES
permit is required
for
M54s serving
populations of 250,000
or more (large
systems),
and
those
serving
populations of
more
than
100,000
but
less
than
250,000
(medium
systems).
It
is
undisputed that the District’s MS4 is
a large
system.
3The Petitioners originally filed
a timely request for an evidentiary hearing with
the
Regional
Hearing
Clerk.
However,
on
May
IS,
2000,
EPA published
a
final rule
modi~ting,
among
other things, the appeal
process for NPDES
permits
set
forth
in
40
C.F.R, part
124.
See
Amendments to
Streamline
the
NPDES
Program
Regulations:
Round
11,65
Fed.
Keg.
30,866
(May
IS,
2000).
This
rule
eliminated
the
previously
existing requirement
that
a party
seek
an
evidentiary hearing before filing
a petition
for
review
with
this
Board.
The
new
rule
granted
certain
petitioners,
including
the
Petitioners
in
this
ease,
until
August
13,
2000,
to
file
a
petition
for
review
with
this
Board.
6
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
MUNICIPALSEPARATE STORM
SEWER SYSTEM
the
District
was
required
to
file a two-part
application
for an NPDES
permit
covering
discharges
from
the
District’s
MS4.4
The
District
submitted Part
1
ofthe required NPDES permit application
in July
1991
and
the
Part
2
application
in
1994.
See
Certified
Index
to
the
Administrative Record (“Index”) pts. 1.1 .n & J.3.a.
On July31,
1998, the
District
submitted
revisions
and
updated
materials
for
the
Part
1
application, and, on
November 4,
1998, the District submitted revisions
and updated materials for the
Part
2
application.
Id.
pts.
1.5
-
.6.
The
revised
Part
2
application
also
included
the
District’s
current
Storm
Water Management Plan (“SWMP”).
Thereafter,
the
Region
prepared
a
draft
permit
and,
on
February
20,
1999,
the
Region
provided
public
notice
and
requested
public
comments
on
its
first
draft
permit
for
the
District’s
MS4
discharges.
Index pts. 1.7 -.8.
As part ofthe first public comment period,
the Region conducted a public
hearing on March
29, 1999.
Id.
pt.
1.10.
Subsequently,
the
Region revised
the terms of the
proposed permit
in
response to comments
received from the public, and it issued
a
second
draft
permit
on
October
1,
1999
(the
“Second
Draft
Permit”)
and
requested further public
comments.
Id.
pts.
1.11
-
.12.
At that time,
the
Regionalso issued its response to comments regarding the February
1999
draftpermit
(“Region’s First Response to Comments”).
Id.
pt.
1.17.
On
January
6, 2000,
the District
of Columbia
Department
of
Health (“DCDH”) issued its certification5 that
the conditions set forth in
‘The
permitting
process is described below in Part l.Rofthis decision.
See also
In re
Cityof Irving,
Tex.. Mien. Separate Storm Sewer Sys.,
NPDES
Appeal No. 00-IS,
slip op. at
13-16 (EAB, July
16, 2001),
10 E.A.D.
—.
5A1l NPDES permit applicants must obtain
a certification from the appropriate
state agency validating the permit’s compliancewith the pertinent federal and state water
pollution control
standards.
CWA
§
401(a)(l),
33 U.S.C.
§
134 I(a)(l).
The regulatory
provisions pertaining to state certification provide that EPA may not issue
a pennit until
a certification
is granted
or waived by
the state
in which
the discharge originates,
40
C.F.R.
§
124.53(a).
The regulations furtheradd that
‘when certification is required
*
*
no
final
permit
shall
be
issued
*
*
unless
the
final
permit
incorporates
the
(continued...)
GOVERNMENT OF THE
DISTRICT OFCOLUMBIA
7
MUNICIPAL SEPARATE STORM SEWER SYSTEM
the second draft
pennit
would
comply
with the District’s water quality
standards,
approved
water
quality
management
plans
and
District
monitoring requirements.
Id.
pt.
I.15.a.
On April
19,
2000,
the Region
issued
the
final
Permit and fact
sheet.
Id.
pt.
1.20.
The
Region
also
issued
its
summary ofthe comments on the second
draft pennit and the
Region’s responses to those comments (“Region’s Second Response to
Comments”).
Id.
pt.
1.18.
On
May
25,
2000,
the
Petitioners
filed
a
request
for
an
evidentiary hearing
pursuant to the regulations governing
the NPDES
programat that time.
On July 14,2000,
the Region returned Petitioner’s
Request for Evidentiary Hearing and notified Petitionersof their rightto
file an appeal
with the Board under changes made to the NPDES permit
appeals process that
became effective
on
June
14,
2000.6
Thereafter,
Petitioners timely filed the
Petition with the Board
on
August Il, 2000.
The Petition
incorporates the
May 25, 2000
request for an evidentiary
hearing
as stating the
basis of the Petitioners’
objections
to the
Permit.
The
Petitioners
have
grouped
their
arguments
in
nine
categories.
(Throughout this decision, we will generally follow the Petitioners’
lead
and considerthe arguments grouped in categories identified by the
issue
number used in the Petition
—
we will summarize these categories below
in Part
I.C.)
The Region filed
a response to
the Petition.
See
Region
Ill’s
Response to Petition for Review (Sept. 28,2000) (“Region’s Response”).
The Region’s
Response generally
argues
that
the Petitioners
have
not
shown that their Petition should be granted.
In one respect,however, the
Region
states
that
it withdraws a portion
of the
Permit in response
to
Petitioners’ issue number eight (thisissue, as described more fully below,
relates to whether the Permit improperly allows amendments or changes
without
requiring
the
formal
procedures
contemplated
by
the
regulations).
‘(continued)
requirements specified
in
the certification.”
40 C.F.R.
§
124.55(a).
siijn’u
note
3.
8
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE
STORM SEWER SYSTEM
Subsequently,
on
January
12,
2001,
the
Region
reissued
the
withdrawn portion of the Permitwith several
amendments.
Thereafter,
the Petitionersfiled a petition requesting review ofthe amendments to the
Permit and they requested that this second petition be consolidated with
their
original
Petition.
See
Petition
for
Review
and
Motion
to
Consolidate
(Feb.
2, 200l).~ The
Petitioners
also
filed supplemental
briefing concerning issue number eight from their original Petition.
See
Supplemental
Reply Based on Intervening Permit Modification (Feb. 2,
2001).
The Region has
responded to the Petitioners’
second petition.
More recently, on December
18, 2001, the Board held
oral argument on
several of the issues raised in this case.
B.
Statutory and
Regulatory Background
The CWA, which was enacted by Congress in 1972, prohibits the
discharge of any
pollutant to waters
of the
United
States from
a point
source
unless the discharge is
authorized by an NPDES permit.
Section
402(a)(l) of the CWA authorizes
the Administrator
to issue permits for
the discharge ofpollutants into navigable waters ofthe United States.
33
U.S.C.
§
l342(a)(l).
Section 402(a)(2) ofthe CWA states that the “Administrator shall
prescribe
conditions
for such
permits
to
assure
compliance
with
the
requirements of’ section 402(a)(l).
A requirement of section 402(a)(1)
is
that
the permitted
discharges must
comply
with
section
301
of
the
CWA, 33
U.S.C.
§
1311.
Section
301
requires,
among other
things,
achievement of”any more stringent limitation, includingthose necessary
to meet water quality standards
*
*
*
established pursuant to any
State
law or regulation
*
*
~“
33
U.S.C.
§
131 1(b)( fl(C).
The
statutory
requirement
of CWA
§
301(b)(l)(C)
to protect
water
quality
standards
has
been
implemented
through
a
variety
of
‘The
Petitioners’ original petition was assigned EAB docket number NPDES
00-14 and their second petition
was assigned EAB docket number NPDLS 01-09.
The
Petitioners’
motion
to consolidate
their second
petition
for
review
with
their
original
Petition
is hereby granted.
GOVERNMENT OFTHE
DISTRICT OF COLUMBIA
9
MUNICIPAL SEPARATE STORM SEWER
SYSTEM
regulatory provisions.
For
example, long-standing
Agency regulations
prohibit the issuance of a permit “when imposition of conditions cannot
ensure
compliance
withthe applicable
water quality requirements of all
affected states.” 40
C.F.R.
§
122.4(d)
(emphasis
added).
In addition,
section 122.44(d) provides that the permit must contain effluent limits as
necessary to protect water quality standards.
Id.
§
122.44(d)(I).
Long-
standing
Agency
regulations
have
also
authorized
the
use of
“best
management practices” (“BMPs”)
to control
or abate
the discharge of
pollutants
in
a
variety
of circumstances
including
when
“numeric
effluent
limitations are
infeasible.”
Id.
§
122.44(k).
Although
EPA
initially
attempted to exempt
municipal
storm
sewer
systems
from
the
requirement to
obtain
an
NPDES permit
for
discharge ofpollutants into navigable waters of the United
States,t in the
Water Quality
Act of
1987
(“WQA”),
Congress amended the
CWA to
specifically
cover
storm
water
discharges
from
conveyances
such
as
MS4s.
Among
other
amendments,
the
WQA
added
section
‘102(p)
governing permitting for MS4s and certain other storm water
systems.
In
particular,
Congress
required
EPA
to
establish
no
later
than
February
4,
1989,
regulations
governing
the
permit
application
requirements forstorm water discharges fromMS4s serving a population
of
more
than
250,000,
and
Congress
required
applications
for
such
permits
tobe filed no laterthan February 4,
1990.
CWA
§
402(p)(4)(A),
33 U.S.C.
§
I 342(~p)(4)(A).Congress also stated insection 4O2(p)(3) that
permits
from MS4s
“shall require
controls to reduce
the
discharge of
pollutants
to
the
maximum extent practicable,
including management
practices
* * *
and such other provisions as the Administrator or the State
determines
appropriate
for
the
control
of
such
pollutants.”
CWA
§
402@)(3),
33
U.S.C.
§
L342(p)(3).
EPA
initially
promulgated
regulations
implementing
section
402(p) of the CWA in 1990.
These regulations, commonly referred to as
‘That exemption was rejected by the U.S. Court ofAppeals for the District of
Columbia.
See
NRDC r~
(‘osile.
568
F.2d
1369,
1377 (D.C. Cir.
1977),
This
histoty is
described
more
fully
in
itt
re
Cliv ofirting,
Tex.
Mun. Sepurale Slotni Sewer S~wtc’,,,.
NPDES
Appeal No.
00-IS, slip.
op.
at 9(EAI3, July
16,
2001),
10 FAD.
10
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM
SEWER SYSTEM
“Phase
I”
regulations,
established
the
NPDES
permit
application
requirements
for storm water discharges
associated
with
industrial
activity
and
discharges from
large
and
medium MS4s.
See
National
PollutionDischarge Elimination System Permit Application Regulations
for
Storm
Water
Discharges,
55
Fed.
Reg.
47,990
(Nov.
16,
1990)
(codified
at
40
C.F.R.
Pt.
122).
In
the
preamble
to
the
Phase
I
regulations,
the
Agency
explained
that
the
MS4
permitting
program
requires a substantial amount of flexibility butnot “to such an extent that
all
municipalities
do
not
face essentially
the
same responsibilities and
commitments
for
achieving
the
goals
of
the
CWA.”
55
Fed.
Reg.
at 48,038.
To achieve these ends, the Phase I regulations made a number
of changes
to the existing NPDES regulations
to allow MS4s to focus
less on end-of-pipe technology-based controls
and to
focus more on the
development of site-specific SWMPs.
In
the
Phase
I rulemaking,
the
Agency
established
a
two-part
permit
application
process
for
the
development
of MS4
permits
that
would
assist permittees in developing
SWMPs capable of meeting
the
statutory
and
regulatory
goals.
Id.
The
two
parts
of
the
permit
application
cover six general
elements
necessary
for
an MS4
permit:
adequate legal authority,source identification, discharge characterization,
proposedSWMP, assessment ofcontrols, and fiscalanalysis.
See
Office
of Water,
U.S.
EPA, EPA
833-B-92-002,
Guidance
Manual for
the
Preparation of
Part 2 ofthe NPDES Permit Applicationfor Discharges
from
Municipal
Separate Storm
Sewer
Systems
at
2-I
to
2-4
(1992)
(hereinafter “Part
2
Guidance Manual”);
see also
In re
City ofIrving.
Tex.
Mun. Separate Storm Sewer Sys.,
NPDES Appeal No. 00-18, slip.
op. at
13-15 (EAB, July
16, 2001),
10
E.A.D.
—
(describing in greater
detail the elements addressing adequate legal authority, proposed SWMP,
and assessment of controls).
As part of a subsequent rulemaking, commonly referred to as the
“Phase II” regulations, section
122.44(k)
was amended to authorize use
ofBMPs not only when“numeric
effluent limitationsare infeasible” as
was previously
authorized, but
also
when “authorized
under section
402(p)
of the
CWA
for
the
control
of storm
water
discharges.”
See
National
Pollutant
Discharge
Elimination
System
—
Regulations
for
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
11
MUNICIPAL SEPARATE
STORM SEWER
SYSTEM
Revision
of
the
Water Pollution
Control
Program
Addressing
Storm
Water Discharges, 64 Fed. Reg. 68,722,68,847 (Dec. 8, 1999) (codified
at
40 C.F.R.
§
122.44(k)(2)-(3)).
C.
Summary ofIssues Raised in the Petitions
As
noted, Petitioners
identi~’their bases for requesting review
of the Permit in nine categories,
which were separately numbered intheir
original
Petition
as
issues
one
through
nine.
We
will
follow
this
numbering system
in
our discussion
since
the parties
have used
it
to
identi& their arguments. The following is a briefsummary of these nine
issues, or categories of arguments, raised by Petitioners:
I.
Compliance
with
Water
quality
Standards.
Under
this
heading, the Petitioners raise several arguments pertaining to whether the
Permit is adequately protective of the
District’s water quality standards,
In
essence,
Petitioners
argue
that
the
Permit
does
not
have
effluent
limitations
that
assure
compliance
with
the
District’s
water
quality
standards.
Petition at
3.
The Region, in contrast,
argues that the Permit
does protect water quality standards.
Region’s Response at
10;
see also
Transcript of Oral Argument at 29, 32-33 (Dec.
18, 2001) (hereinafter
“Tr. at
“)~9
‘l’he
Region also
quotes
an
argument
it made in
its
response
to comments
where the Region
stated that
the
Permit
is not necessarily required to assure compliance
with state water
quality standards but
need only
“control the discharge of pollutants to
meet
such
provisions
EPA
or
the
State
determines
appropriate.”
Region’s
Second
Response
to Comments
at
10,
quoted
in
Region’s Response
at
9.
In
support
of this
argument
the Region
explained
that the Ninth
Circuit Court of Appeals
has
held
that
“EPA
*
*
$
has
authority to require
less than strict compliance with
state water quality
standards.”
Region’s
Response at
9 (quoting
Defenders
ofWi/d/Ve v. Browner,
191
F.3d
I 159,
1166
(9th
Cir.
1999));
see
u/so
Region’s
Reply
at
7
n.4,
However,
at
oral
argument,
the
Region
slated that,
in
issuing
this
Permit, it
is
not
relying
on
the
Ninth
Circuit’s conclusion that
EPA
has authority to
require
less
than
strict compliance with
state water quality standards.
Tr. at 31.
Specifically, the Region stated that
it intends tIlts
Pennit
to
satisfy water quality
standards..
Tr.
at 32-33.
12
GOVERNMENT OFTHE DISTRICT OFCOLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
2.
Hickev
Run.
Petitioners argue that the Permit is deficient in
that
(a)
it contains an aggregate numeric effluent
limit for four outfalls
into Hickey Run (which is a tributary of the Anacostia River) and (b)
it
contains
monitoring
requirements
that
the
Petitioners
allege
are
inadequate.
3.
Reductions tothe “Maximum Extent Practicable”.
Under this
heading, Petitioners argue that the Region’s determination that the Permit
will
reduce
storm
water
pollutant
discharges
to
the
maximum
extent
practicable
(“MEP”)
as
required
by
CWA
§
402(p)
was
clearly
erroneous.
4.
Deferral
of Complete
Program.
Under
this
heading,
the
Petitioners raise arguments concerning the Permit’s deferral of the time
for the District to submit implementation and enforcement plans for its
SWMP and concerning the Permit’s deferral of an “upgraded” SWMP.
5.
Failure
to
Require
Compliance
Within
Three
Years.
Petitioners
argue
that
the Permit fails to require
compliance
within the
three-year time period set
forth in CWA
§
402(p)(4).
6.
Storm Water Implementation Plan.
Petitioners argue that the
Permit
in
Part
JII.E
uses
language
allowing
for
a
“cost
benefit
and
affordability” analysis that the Petitionersargue
is contrary to the CWA.
7.
Funding.
Petitioners
raise
several
additional
arguments
concerning the “cost benefit and affordability analysis” under Part
ll1.E
of the Permit as it pertains to funding of the implementation plan.
8.
Modifications.
The
Petitioners
argued
in
their
original
Petition
that
the
Permit
“illegally
authorizes
numerous
substantive
changes
in
permit
requirements
without
a
formal
permit
revision.”
Petition
at
9.
In
its
response,
the Region
stated that
it
withdraws
the
provisions ofthe Permit that are affected by Petitioners’ arguments inthis
category, and
the
Region
proposed amendments to
address
this issue.
Response at
25.
After the Region issued
its amendments on January
12,
2001, the
Petitioners filed both a petition for review of the amendments
GOVERNMENT OFTHE
DISTRICT OF COLUMBIA
13
MUNICIPAL SEPARATE STORM SEWER SYSTEM
and a supplemental
brief,
both ofwhich
argue
that
the modifications
of
the Permit fail to address most of the concerns raised by
Petitioners
in
their original Petition.
9.
Waivers
and
Exemotions.
The
Petitioners
argue
that
the
District’s storm waterregulations that are incorporated into the Permit by
reference
require the granting ofvarious waivers or exemptions that
the
Petitioners argue
are in conflict with the CWA and EPA rules.
Each of these arguments
will
be
separately
considered
in the
discussion that follows.
We begin, however, with a brief discussion of
the standards
we use in evaluating petitions filed under 40
C.F.R. pan
124
for review of NPDES permits.
II.
DISCUSSION
A.
Standard ofReview
The Board generally will not grant review ofpetitions filed under
40
C.F.R.
§
124.19(a), unless it appears from the petition that the permit
condition that is at issue is based on a clearly erroneous finding of fact or
conclusion of law or involves an important policy
consideration which
the Board,
in
its
discretion,
should
review.bo
40
C.F.R.
§
124.19(a)
0prior to the amendments to streamline the NPDES regulations
(seesupra
note
3), the rules governing petitions for review ofNPDES permitting decisions were set out
in
40 C.E.R.
§
124.91.
These
rules did not provide
for an appeal directly to the
Board.
Instead,
a
person
seeking review of an NPDES permitting decision was required
to first
request
an evidentiary hearing before the Regional Administrator.
In re CityofMoscow.
Idaho.
NPDES Appeal No. 00-10, slip op. at
9 n.20 (EAB, July 27,2001),
10 E.A.D.
The outcome of the request
for an evidentiary hearing or
the outcome ofan evidentiary
hearing
--
if the request was granted
--
was
then appealable
to the
Board.
However,
under
those
rules
there
was
no
review
as
a
mailer
of
right
from
the
Regional
Administrator’s decision or the denial of an evidentiary
hearing.
See In re City ofPot:
S.
Joe,
7 E.A.D.
275, 282 (EAB
1997);
In reF/a Pulp & PaperAss
ti,
6 E.A.D.
49,51
(EAB
1995);
In re J&L Specialty Prods,
C’orp..
5
E.A.D. 31,41
(EAB
1994).
Petitions
for review of NPDES permits are
now regulated by 40 C.F.R.
§
124.19,
as amended by
65
Fed.
Reg.
30,886,
30,911 (May
IS,
2000).
Even
though
the regulations
governing
(continued-
14
GOVERNMENTOF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
(2001);
seealso
City
ofMoscow,
Idaho,
NPDES Appeal No. 00-10,
slip
op.
at
8-9
(EAB,
July
27,
2001),
10
E.A.D.
—
(hereinafter
“Moscow
MS4”);
In
re
City
of Irving,
Ta.
Mun.
Separate
Storm
Sewer
Sys..
NPDES
Appeal
No.
00-18,
slip
op.
at
16
(EAB,
July
16,
2001),
10
E.A.D.
—
(hereinafter
“Irving M54”).
Whilethe
Board
has
broad power
to review decisions under section 124.19, the Agency intended this power
to be exercised “only sparingly.”
45
Fed. Reg. 33,290,
33,412 (May
19,
1980);
see also Moscow MS4,
slip
op.
at 9,
10
E.A.D.
_;
In re Rohm &
I-laos
Co.,
RCRA Appeal No. 98-2,
slip op.
at
7
(EAB, Oct.
5, 2000),
9 E.A.D.
_;
In re AESP.R. L.P.,
PSD Appeal Nos. 98-29 to 98-31, slip
op. at
7 (EAB, May 27, 1999),
8
E.A.D.
,
aff‘d sub nom. Sur Contra
La
Contaminacion v.
EPA,
202
F.3d
443
(1st Cir. 2000).
Agency
policy
favors final adjudication of most permits at
the
regional level.
45
Fed. Reg. at
33,412;
see also
Moscow MS4,
slip
op.
at 9,
10
E.A.D.
;
Irving MS4,
slip op. at
16,
10
E.A.D.
_;
In re New
England
Plating
Co.,
NPDES
Appeal No.
00-07,
slip op.
at
7
(EAB,
Mar.
29,
2001),
9
E.A.D.
;
In
re
Town
of Ashland
Wastewater
Treatment
Facility,
NPDES
Appeal No.
00-15,
slip op. at
9-10
(EAB,
Feb.
26, 2001),
9
E.A.D.
_;
In re
Town ofHopedale,
Bd. of Water &
Sewer
Comm’rs,
NPDES
Appeal
No.
00-4,
slip
op.
8-9
n.l3
(EAB,
Feb.
13,
2001),
9
E.A.D.
—.
On
appeal
to the
Board, the petitioner
bears
the burden of demonstrating
that
review
is warranted.
Moscow
MS4,
slip
op.
at
9,
10
E.A.D.
_;
see
also AES P.R.,
slip
op.
at
7,
8
E.A.D.
_;
In reHaw. Elec. Light Co.,
PSD Appeal Nos. 97-15 to 97-23,
slip
op.
at
8
(EAB,
Nov.
25,
1998),
8
E.A.D.
In
re
Kawaihae
Cogeneration Project,
7
E.A.D.
107,
114
(EAB
1997).”
“C
continued)
NPDES
appeals changed
in
the
sense
that
the
evidentiary
hearing
provisions
were
eliminated, the standard of review
has not changed.
Moscow MS4,
slip op. at
9
n.20,
/0
FAD.
(citing
In re Town ofAs/i/and Wastewater Treatment Facility,
NPDES Appeal
No.00-IS,
slip op.
at
9 n.j
I
(EAB, Feb.
26, 200!),
9 E.A.D.
,~.
“Standing to appeal
a
final permit
determination
is limited
under 40 C.F.K
§
124.19
to those
persons
“who filed
comments on Ithel
draft permit or participated
in
the
public
hearing.”
Any
person
who failed
to comment
or participatc
in
the
public
(continued
~)
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
IS
MUNICIPAL SEPARATE STORM SEWER SYSTEM
Persons seeking review must demonstrate to the Board,
among
other things,
“that
any
issues being raised were raised during the public
comment period to the extent required by these
regulations
*
* i.”
40
C.F.R.
§
124.19(a) (2001).
Participation
during the
comment period
must conform with
the requirements of section
124.13, which requires
that
all
reasonably
ascertainable
issues
and
all
reasonably
available
arguments supporting a petitioner’s position be raised by
the close of the
public
comment period.
40
C.F.R.
§
124.13
(2001);
see also,
Moscow
M54,
slip op. at
9,
10
E.A.D.
;
In re
New
England Plating,
NPDES
Appeal No. 00-7,
slip op. at 7 (EAB, Mar. 29,2001), 9 E.A.D.
;
In
re
City
ofPhoenix,
Ariz.
Squaw Peak
&
Deer
Valley
Water
Treatment
Plants,
NPDES Appeal No. 99-2, slip
op. at
14 (EAB,
Nov.
1,2000), 9
E.A.D.
—
(“Those persons seeking to
appeal
based on
their status
as
commenters or public hearing participants must also demonstrate to the
Board,
inter alia,
‘that any issues
being raised were raised
during
the
public
comment
period
(including
any
public
hearing)
to
the
extent
required by
these regulations
*
*
*.“).
The
Board traditionally
assigns a heavy
burden to petitioners
seeking review of issues that are essentially technical in nature.
Moscow
MS4,
slip
op.
at
9,
10
E.A.D.
;
see
also
In
re
Town of Ashland
Wastewater Treatment Facility,
NPDES
Appeal No. 00-IS, slip op. at 10
(EAB, Feb.
26,
2001), 9
E.A.D.
;
In
re NE Hub
Partners,
L.P.,
7
E.A.D.
561, 567 (EAB
1998),petitionfor review denied sub nom. Penn
Fuel Gas, Inc.
v. EPA,
185 F.3d 862 (3rd Cir.
1999).
When the Board
is
presented with technical
issues we look to determine whether the record
demonstrates that
the Region
duly considered
the issues raised
in the
comments
and whether the approach ultimately adopted by
the Region
is rational in light of all the information in the record.
NEHub,
7 E.A.D.
at
568.
If we
are
satisfied
that
the Region
gave
due consideration
to
comments received and adopted an approach in the final permit decision
‘‘C.
continued)
hearing on the draft permit
can appeal “only to the extent of the changes from the dra~
to the final
permit
decision.”
40 C.F.R.
§
124.19(a) (200!);
see/nrc
City oJ’f’I,ocnrr,
An;. Squaw Peak & Deer
Va/let, Waler Treatment P/ants,
NPDES
Appeal
No, 99-2. slip
op.
at
14 (EAB, Nov.
1,2000),
9
E.A.D.
—.
16
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPALSEPARATE
STORM SEWER SYSTEM
that
is rational and supportable,
we
typically
will defer to
the Region’s
determination.
Id.
For the
following
reasons,
we
conclude
that
Petitioners
have
shown that, in several respects, the Region’s decision to issue the Permit
was deficient under these standards.
Accordingly, we remand the Permit
for further proceedings consistent
with this decision.
B.
Petitioners
‘
Issue One:
WaterQuality Standards
The
Permit
contains
one
numeric
effluent
limitation
for
discharges
from
four
outfalls
into
1-lickey
Run.
Other
than
this
one
numeric
discharge
limit,
the
Permit
designates
a
variety
of
best
management
practices,
or BMPs, to control
the discharge of pollutants
from the District’s MS4.
The Petitioners raise threearguments objecting
to the Region’s approval of the Permit conditions establishing BMPs
to
control
pollutant discharges
and
ensure compliance
with the District’s
water
quality
standards.
First,
the
Petitioners
argue
that
the
Region
should have established numeric limits for most of the system’s outfalls,
rather than
relying
on
BMPs to control
pollutant discharges.
Petition
at
2-3.
Specifically,
the
Petitioners
argue
that
the
Region
made
no
showingthat numeric limits are infeasibleand that the Region should set
the
numeric
limits
equal
to
the
numeric
water
quality
standards
applicable to the receiving waters.
Petition at 4; Petitioners’
ReplyBrief
at
3.
Second, Petitioners argue
that
the Region should,
at a minimum,
have established narrative limits.
Petition at 4.
Finally, Petitioners argue
that the Region failed to make the requisite determination that the chosen
BMPs
will ensure
protection of
the District’s
watçr quality
standards.
Petition at
5;
Petitioners’ Reply at 4.
Before
turning
to
these
arguments,
we
must
first
address
a
number of issues by way of background, some of which were treated by
the parties’
briefs as being
in dispute, but which
the
parties
conceded
during oral argument.
As noted above, section 301 of the CWA requires,
among other things, that
NPDES
permits
contain
“any
more
stringent
limitation,
including
those
necessary
to
meet
water
quality
standards
*
*
*
established
pursuant
to any
State
law or
regulation
*
*
s.”
33
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
17
MUNICIPAL SEPARATE STORM SEWER SYSTEM
U.S.C.
§
131 l(b)(l)(C).
This
statutory
requirement
has
been
implemented, inpart, through
long-standing regulations that prohibit the
issuance of an NPDES permit
“when
imposition of conditions cannot
ensure
compliance
with the applicable water quality requirements ofall
affected
states.”
40
C.F.R.
§
122.4(d) (2001)
(emphasis added.).
In
addition,
section
122.44(d)
provides
that
“the
permit
must
contain
effluent
limits” for a particular pollutant “when the permitting authority
determines
*
* *
that a discharge causes, has the reasonable potential
to
cause,
or
contributes
to
an
in-stream
excursion above
the
allowable
ambient
concentration of a state
numeric
criteria within a
State
water
quality standard for an individual pollutant.”
Id.
§
122.44(d)(l)(iii).
In their filings
with the Board, Petitioners
maintain
that, based
on evidence inthe record, the Permit is required by 40 C.F.R.
§
122.44(d)
to
contain
effluent
limitations
that
protect
water
quality
standards.
Petition
at 3
(citing
1998
Water Quality Report at 48, app.
D at
3-75).
Specifically, Petitioners argue that information submitted by
the District
with
its
application
for
the
Permit
shows
that
discharges
from
the
District’s
MS4
causes,
has
the
reasonable
potential
to
cause,
or
contributes
to
in-stream
excursions
above
the
allowable
ambient
concentrations ofthe District’s
numeric water quality standards, thereby
triggering
the
requirements of section
122.44(d)(l).
They explain
as
follows:
The monitoring data submitted with D.C’s MS4
application confirms that stormsewer discharges present
major threats
to
surface
water
quality
in
the
District.
The data shows
that such discharges repeatedly exceed
the District’s water quality standards for fecal coliform
bacteria,
which are 200/100 mL max. 30-day mean for
Class A waters, and
1,000/100 mL for Class B waters.
21
DCMR
1104.6.
In
almost
all
of the
storm
water
sampling
reported
in
the
Part
2
application,
fecal
coliform counts exceeded one orboth ofthese standards,
often by wide margins. Part
2 application, Tables4.3.4-
3
to -14; 21
DCMR
1104.6.
At least
one discharge also
18
GOVERNMENT OF THE DISTRICT OFCOLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
exceeded
arsenic
criteria
for
fisheries.
Id.,
Part
2
application, table
4.3.4-10.
*
*
*
Under these
circumstances,
the
Act
and
EPA
rules require that the permit include effluent
limitations
to assure compliance withwater quality standards.
*
* *
Tihe
District’s
1998 Water Quality Report specifically
identifies storm water discharges as known or suspected
contributors to violations of water quality standards for
specific
pollutants
in
waters
throughout
the
District.
Water
Quality Report at 48, Appendix D at
3-75.
For a
number of
waters,
the
report
lists
urban runofV’storm
sewers
as the
only source of impairment.
Id.
Petition
at 3.
The Region does not argue that this evidence cited by Petitioners
is insufficient to trigger the requirements of section
122.44(d)(l), which
as noted
requires “effluent limits”
if discharges
cause
or contribute to
violations of water quality standards.
Instead, the Region maintains that
section
122.44(d)(l) does notrequire that “effluent limits” be expressed
as numeric limits.
The Region argues
that BMPs
are
a type of effluent
limit and
that
it
properly explained the basis
for its decision to use BMPs
instead of numeric effluent limits.
Specifically, the Region explained in
the Fact Sheet that “In accordance with40 CFR
§
122.44(k),
the Region
has required a seriesof BMPs,
inthe form ofa comprehensive SWMP,
in lieu of numeric limitations.”
Fact
Sheet at
7.
The Region explained
further
in the Region’s
First Response to Comments that “derivation
of
water quality-based limits by
application of the methods contained in the
Technical
Support Document for Water Quality-based Toxics Control
is
notfeasible
at this time because insufficient information is known about
the magnitude, variation, and frequency of the flow rate of boththe river
and
storm
discharges.”
Region’s
First
Response
to
Comments
at
7
(emphasis added);
see a/lw
Region’s Response at 9.
The
notion
that
effluent
limits
may
be
expressed
as
either
numeric
limits or as
some
other restriction that
limits the discharge
of
GOVERNMENT OF THE DISTRICT OFCOLUMBIA
19
MUNICIPAL SEPARATE STORM
SEWER SYSTEM
pollutants, such as BMPs, has been stated in
EPA
guidance and has been
endorsed
by
this
Board.
In
essence,
because
the
term
“effluent
limitation”
is defined
to
mean any
restriction
on
quantities,
rates,
and
concentrations
of
pollutants,’2
effluent
limits
required
by
section
l22.44(d)(l) therefore may be expressed as either numeric
limits or as
BMPs, both of which
serve to limitquantities, rates or concentrations of
pollutants.
In reAriz.
Mun. Storm WaterNPDES
Permits,
7 E.A.D.
646,
658-59
(EAB
1988)
(hereinafter
“Arizona
Municipal”)’3
(citing
Questions
and
Answers
Regarding
Implementation
of
an
Interim
Permitting
Approach
for Water Quality-Based Effluent
Limitations
in
Storm
Water Permits,
61
Fed.
Reg.
57,425,
57,426
(Nov.
6.
1996)).
Initially, the Petitioners argued
that
the Region’s
failure to use numeric
limits
violated
section
301
of the CWA and
40 C.F.R.
§~
122.4(d)
&
122.44(d).
Petition at 2-3.
At oral argument, Petitioners also stated that
where
the
water
quality
standards
are
numeric
standards,
the
“only
certain
method
to
assure
compliance
with standards
is
with
numeric
effluent
limits.”
Tr. at 6.
The Petitioners, however, also acknowledged
during oral argument that BMPs are a form ofeffluent limitation, Tr. at 7,
and that BMPs may be used to satisf~’
water quality-based requirements.
Tr.
at
914
Given
this
concession,
we do
not need
to revisit our prior
determination in
Arizona Municipal
that, as a general proposition,
BMPs
are a form ofeffluent limit that may in appropriate circumstances be used
to satisfy the requirements ofsection 122.44(d) ofthe regulations in order
to resolve the dispute at hand.
“The term “effluent limitation”
is defined by
the
regulations to mean
“any
restriction
*
on quantities, discharge rates, and concentrations of ‘pollutants’ which
are ‘discharged’
from ‘point sources’ into ‘waters ofthe United States,” thewaters of a
‘contiguous zone,’
or the ocean.”
40 C.F.R.
§
122.2 (2001).
‘3Our holding
in
Arizona Municipal
was affirmed by the Ninth Circuit Court
ofAppeal~.
See Defendersof Wild!jfe
v.
Browner.
191
E.3d 1159(9th Cir.
1999),
afg
on oilier grounds In re An:.
Mun, Siorm Waler NPDES Permits.
7
E.A.D.
646 (EAB
1988).
“However, the retitioncrs consistently argued that ifthe Region chooses BMPs
to
meet water quality-based standards, the Region “would still
have to show that they
the
BMF’sl arc going to
do the job.’~~Fr.
at
10,
This
issue
is discussed
further below.
20
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM
SEWER SYSTEM
With respect to whether deploymentofBMPs was inappropriate
under
the
circumstances
of
this
case,
we
note
that
the
regulations
specifically
authorize
the
use of BMPs
in
two
potentially
applicable
circumstances.
First, section 122.44(k)(2), as added in
1999, authorizes
BMPs
when
“authorized
under section
402Q’)
of the
CWA
for the
control of storm water discharges.”
40
C.F.R.
§
122.44(k)(2) (2001).
Second, section
1 22.44(k)(3) authorizes BMPs when“numeric
effluent
limitations
are
infeasible.”
Id.
§
122.44(k)(3);
see
also
Arizona
Municipal,
7
E.A.D.
at 656
(“Under the regulations, best management
practices
*
*
*
may
be
incorporated
into storm
water
permits
where
numeric limitations
are infeasible.”).
In the present case,
the Region
statedat oral argument that
it did not base its decision to approve liMPs
on
the
new
40
C.F.R.
§
122.44(k)(2),
which
was
added
in
the
1999
amendments’5
and
which
allows
liMPs
when
authorized
by
CWA
§
402(p).
Tr. at
48.
Instead, the Region determined that
numeric limits
were notfeasible, which is the criterion for use of BMPs under 40 C.F.R.
§
l22.44(k)(3).
Specifically,
as noted
above, the Region explained that
“djerivation
of water quality-based limits by application ofthe methods
contained in the Technical Support Document for Water Quality-based
Toxics
Control
is
not
feasible
at
this
time
because
insufficient
information
is known
about
the magnitude, variation,
and frequency of
the flow
rate of both the
river and storm discharges.”
Region’s
First
Response to Comments
at
7
(emphasis added).
This
brings
us
to
the
issues
that
remain
in
dispute.
The
Petitionersargue first that “the Region has made no showingthat numeric
limitations
are
infeasible
*
*
*
.
The
Region
did
not
even
attempt
development of numeric effluent
limits for discharges
to waters of the
District
other
than
1-Tickey
Run.”
Petition
at
4.
On
this
point,
the
Petitioners
elaborate
further
in
their
Reply
Brief that,
where
mixing
“See National
Pollutant
Discharge
Elimination System
‘—
Regulations tbr
Revision of the
Water Pollution Control
Program Addressing Stonii Water
Discharges,
64
FedS
keg.
68,722, 68,847
(Dcc.
8.
1999).
GOVERNMENT OFTHE
DISTRICT OF COLUMBIA
21
MUNICIPAL SEPARATE STORM SEWER SYSTEM
zones’6 have not been established (as is the case here for all
outfalls other
those
into
Flickey
Run),
“under
long-established
EPA
guidance
and
practice,
effluent
limits
must
be
set
to
assure
compliance
with
water
quality standards at the pointofdischarge.” Petitioners’ Reply Briefat 3.
In other words, Petitioners argue that the Agency can easily set a numeric
limit for each outfall that
is equal to the numeric water quality standard
for
the
receiving
water.
Presumably,
Petitioners
reason
that
the
discharges will not cause
or contribute to an in-stream excursion
above
an allowable standard if the discharges, themselves, must be below
the
applicable
standard.
Petitioners
argue
further
that
“this
is
not
an
exercise requiring any information beyond the water quality criterta set
in
D.C. ‘s
published
water quality
standards.”
Id.
These
arguments,
however, do not persuade us that review of the Permit should be granted
on
this ground.
In
Arizona Municipal,
we considered
a challenge to the permit
issuer’s determination pursuant to what is now section
1 22.44(k)(3)”
that
setting numeric
effluent
limits
was not
feasible
for an
MS4
system’s
discharges.
Arizona Municipal,
7
E.A.D.
at 656.
In that case, the permit
issuer made its determination of infeasibility because, due to “the unique
“Briefly
stated,
a mixing zone
is “an allocated impact zone in the receiving
water which may include a small
area or volume where acute criteria can
be
exceeded
provided there
is no lethality (zone of
initial dilution), and
a larger area or volume
where
chronicwater quality criteria can be exceeded ifthe designated use ofthewater segment
as a whole is not impaired as a result of the mixing zone.”
Guidance
on Application
of
State
Mixing Zone Policies
in
EPA-Issued P/PDES Permits,
(Aug.
1996).
“The current
section
l22.44(kX3)
was
section
l22.44(k)(2)
prior to
the
amendmentofsection
122.44(k)
in
1999.
As previously discussed, the 1999 amendments
added a new section 122.44(k)(2), allowing use of BMPs when authorized under section
4O2(p) of the Act.
The old section
l22.44(k)(2) shifted
at that
time to become the new
and current section 122.44(k)(3).
See
National
Pollutant Discharge Elimination System
—
Regulations
for Revision of the
Water
Pollution
Control
Program Addressing
Storm
Water Discharges, 64
Fed. Reg. 68,722,
68,847 (Dec.
8,
1999).
Accordingly, at the time
of the
Arizona
Municipal
decision,
the
regulatory provision
authorizing
use of
BMPs
when
numeric
limits are
infeasible
was
set
forth
in
section
I 22.44(k)(2), which
is
the
regulation
cited
in the
Arizona
Municipal
decision.
See
Arizona
Municipal,
7 l3,A ft
at 656,
22
GOVERNMENTOF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM
SEWER SYSTEM
nature of
storm
water discharges in the arid Arizona environment and the
uncertainties
associated
with
the
environmental
effects
of short-term,
periodic discharges,
‘it
would be premature to include in the final permit
any specific toxicity-related effluent
limitations
*
*
s.”
Id.
at 657.
In
considering arguments that this determination was insufficient, we noted
that
the
permit
issuer’s
reasons
were
consistent
with
Agency
policy
documents
that
“recognize
that
permitting
agencies
frequently
lack
adequate
information
to
establish
appropriate
numeric
water
quality-
based effluent limitations, and provide
for the inclusion of BMPs
until
such
information
becomes
available.”
Id.
at
658.
The
petitioners
challenged the permit issuer’s decision by arguing that the permit issuer
had an affirmative dutyto set numeric limits. We rejected this argument,
stating
that
“the
petitioners
have
failed
to
convince
us
that
this
determination was in any way unlawful or inappropriate.”
Id.
at 659.
In the present case, the Petitioners have made many of the
same
generalized
challenges
to the Region’s permitting decision as those
we
considered and rejected in
Arizona
Municipal,
asserting that the Region
has an affirmative duty to set
numeric limits.
In keeping with
Arizona
Municipal,
we
find these
general arguments to
be without merit.
The
Petitioners in this case, however, also
rely on a more specific
argument
that
numeric
limits
could
have
been
derived
under
methods
that
the
Petitioners describe as “long-established EPA guidance
and practice.”
Petitioners’
Reply Brief at
3.
As
discussed below,
this more specific
argument must also be rejected in this case because Petitioners failed to
raise it and the cited authority during the public
comment period.
The regulations governing the NPDES permitting program and
review
by
this
Board
require
that
persons
seeking
review
must
demonstrateto the Board “that any issuesbeing raised were raised during
the public comnent period to the extent required by these regulations
*
*
s.”
40
C.F.R.
§
124. 19(a)
(2001);
Moscow MS4,
slip op.
at
10,
10
E.A.D.
—.
The
regulations
provide
further
that
all
reasonably
ascertainable issues and all
reasonably available arguments supporting a
petitioner’s position
must be
raised by
the
close of the public
comment
period.
40 C.F.R.
§
124.13(2001);
see.
e.g., Moscow MS4,
slip op. at
10,
10
E.A.D.
In reNew EnglandPlating,
NPDES Appeal No.00-7, slip
GOVERNMENT OF THE DISTRICT OF COLUMBIA
23
MUNICIPAL SEPARATE STORM SEWER SYSTEM
op.
at 7
(EAB, Mar. 29, 2001),
9
E.A.D.
_;
In re
City
of
Phoenix,
Ariz.
Squaw Peak& Deer Valley
Water Treatment Plants,
NPDES Appeal No.
99-2, slip
op.
at
14
(EAB, Nov.
1, 2000),
9
E.A.D.
—.
“Accordingly,
only
those
issues and arguments raised during the comment period can
form the basis foran appeal before the Board (except to the extent that
issues or arguments were not reasonably ascertainable).”
New
England
Plating,
slip op.
at 8 (citing
In refettBlack,
Inc.,
UIC Appeal Nos.
98-3
& 98-5, slip.
op. at
8
& nn.18,
23
(EAB, May 27,
1999),
8
E.A.D.
—
(finding
that
reasonably ascertainable arguments not
raised during
the
public
comment period were not preserved forappeal)).
As
we have previously explained, “tJhe
effective, efficient and
predictable administration of the permitting process,
demands that
the
permit issuer be given the opportunity toaddress potential problems with
draft permits
before they
become
final.”
In re Encogen Cogeneration
Facility,
PSD Appeal Nos. 98-22 to 98-24, slip
op. at
8
(EAB, Mar.
26,
1999),
9
E.A.D.
—.
“In this manner, the permit
issuer can make timely
and
appropriate
adjustments
to
the
permit
determination,
or,
if
no
adjustments
are made,
the
permit issuer can
include an explanation
of
why
none are necessary.”
In re Essex County
(N.J.) Resource Recovery
Facility,
5
E.A.D.
218, 224
(EAB
1994).
In particular, the petitioner
must haveraisedduring the public comment period the specific argument
that
the petitioner seeks to raise
on
appeal;
it
is not
sufficient for
the
petitioner to have
raiseda more general or related
argument during the
public
comment
period.
See,
e.g..
In
re RockGen
Energy
Ctr.,
PSD
Appeal No. 99-I,
slip op. at II (EAB,
Aug. 25,
1999),
8
E.A.D.
—
(petition
denied because
petitioner raised
during
the
public
comment
period
three issuesregarding one type of emissions control technology,
but
had not
raised the
specific
issue
comparing that
technology
to
the
technology that was selected, which petitioner sought to raiseon appeal).
“At
a
minimum,
commenters
must
present
issues
with
sufficient
specificity
to
apprise
the
permit
issuing authority
of the
issue
raised.
Absent
such specificity,
the permit issuer cannot meaningfully
respond
to comments.”
Id.
at
17 (citing/n
re SpokaneReg
‘I Waste-to-Energy,
2
E.A.D.
809,
816
(Adm’r 1989) (“Just as
‘the opportunity to comment
is
meaningless unless
the
agency responds to significant points raised by
the
public,’
so
too
is
the
agency’s
opportunity
to
respond
to
those
24
GOVERNMENTOF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE
STORM SEWER SYSTEM
comments
meaningless
unless
the
interested
party
clearly
states
its
position.”)
(quoting
Northside Sanitary Landfill,
Inc.
v.
Thomas,
849
F.2d
1516,
1520 (D.C.
Cir.
1988)) (internal citations omitted)).
In
the present case, Petitioners raised their general objection
to
the absence of numeric effluent
limits during both the public
comment
period on the first draft permit and during the public
comment period on
the
second
draft permit.
See
Letter
from
David
S.
Baron to William
Colley,
EPA Region
III, at
2-3
(Apr.
21,
1999);
Letter
from David
S.
Baron
to William Colley,
EPA Region
III, at
1-2 (Oct.
29,
1999).
The
Petitioners, however,
have not shown
that
they
raised
their argument
concerning
the alleged
“long-established EPA
guidance
and
practice”
regarding point-of-discharge limits at any timeduring the first or second
public comment periods, and the Petitioners havenot explainedwhy
this
argument and the
cited authorities
were not
reasonably ascertainable at
that time.
In this regard,
it is significant
that the Region discussed
the
implications of “the
Technical
Support
Document
for
Water Quality-
based Toxics Control”
inthe Region’s responseto comments on the first
draft
permit.
See
Region’s
First
Response
to
Comments
at
Presumably,
Petitioners
would
recognize
this
document
cited
by
the
Region
to be among the body
of “long-established EPA guidance
and
practice”
to
which
they
now
refer.
Thus,
the
Region’s
basis
for
its
decision
was
fully
available
to
Petitioners
during
the
second
public
comment period,
and their failure
to make their more specific response
and citation
to the allegedly countervailing authority at that
time is fatal
to
their
attempt
to
make
their
case
at
this
juncture.
Accordingly,
Petitioners have failed to preserve this argument for appeal.
The Petitioners argue second that “even
if numeric limits were
infeasible, the
Region
has not shown
why it could
not include narrative
“The
Region
explained
in
its
First
Response
to Comments
as
follows:
“Derivation of water quality-based
limits
by application of the methods contained in
the
‘Technical
Support
Document
for
Water Quality-based
Toxics Control’
(TSD)
is not
feasible
at
this
time
because
insufficient information
is
known
about the magnitude.
variation,
and frequency ofthe flow rate ofboth
the river and storm water discharges.”
First Response to Comments
at 8.
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
25
MUNICIPAL SEPARATE STORM SEWER SYSTEM
provisions
in the permit requiringprotection ofwater quality standards.”
Petition at
4.
This
argument also
must
fail.
There is
no
statutory
or
regulatory
provision that requires use of narrative limits.
Moreover, the
regulations specifically authorize the use ofBMP5 where numeric limits
are
infeasible.
40
C.F.R.
§
122.44(k)(3)
(2001).
Accordingly,
we
conclude
that
the Region
was
authorized
to
use
BMPs
and
was
not
required
to
include
narrative
provisions
in
the
Permit
of
the
kind
suggested
by
Petitioners.
However,
as
discussed
below,
we
are
remandingthis Permit on other grounds,and our conclusion here that use
of narrative limits is not required should not be viewed as discouraging
the use of
narrative
limits in any reissued
permit
ifthe Region determines
that
narrative
limits
would
be
appropriate
in
addressing
the
concerns
giving rise to the
remand.
Finally,
Petitioners
argue
that
“ijf
EPA
intends
to
rely
on
BMPs, it still must demonstrate that
those management practices will be
adequate
to
assure
compliance
with
water
quality
standards
in
the
receiving
waters”
and
that
“tJhe
Agency
has
failed
to
do
so
here.”
Petition
at
S.
Petitioners elaborate further on
this last argument
in their
Reply
Brief by
noting that
the
record contains
“absolutely
no
facts or
technical analysis” to support
the Region’s statement in its
response to
comments that the Permit’s BMPs are ‘reasonably capable ofachieving
water quality standards,” and by noting that“the legal test is not whether
the BMPs are ‘reasonably capable’ ofachievingwater quality standards,
Rather,
the
permit
must
‘ensure’
compliance
with
water
quality
standards.”
Petitioners’
Reply
Brief
at
4
(citing
33
U.S.C.
§
131 l(b)(l)(C);
40
C.F.R.
§
122.4(d)).
In
its Response, the
Region
reiterated
that
it
“issued
the
Permit
based
on
its. determination
(and
certification of the Permit by
D.C.
Department of Health
*
*
*) that
the
BMPs
set
forth
in
the
District’s
SWMP
are
‘reasonably
capable
of
achieving water quality standards.”
Region’s
Response
at
10;
see a/so
Region’s Reply at
6t9
‘9As
noted
supra
note 9,
the
Petitioners also presented
a number ofarguments
addressing the Ninth Circuit’s
statement
in
Defenders of Wildlife
v.
Browner,
191
F.3d
1159,
I
66
(9th
Cir.
999),
that “EPA
*
has
authority
to require
less than
strict
(continued...)
26
GOVERNMENT OF THE
DISTRJCT OFCOLUMBIA
MUNICIPAL SEPARATE STORM SEWER
SYSTEM
At oral argument, the Region statedthat, in using the “reasonably
capable” language,
it was
not seeking to establish a new, less restrictive,
standard for MS4 permits,
and
that this
Permit
was intended to protect
water quality
standards.
In particular, the Region stated that “in
the
responseto comments, wewere not trying to set up a different standard.”
Tr.
at
39.
Instead,
the Region stated that
it
intended
the
“reasonably
capable” language
as “merely a paraphrase ofthe requirement that the
Region
found that
no
more
stringent limits were necessary to achieve
water quality standards.
That is set forth in section
30l(b)(l)(c) of
the
Act.”
Tr. at 39.
We have two concerns regarding the mannerin which the Region
has
addressed
the
question
of
the
Permit’s
meeting
water
quality
standards.
First, it is not clear that
the Region’s determination
that
the
BMPs
required under the Permit are “reasonably capable” of achieving
water quality standards fully comports withthe regulatory prohibition on
issuing
a
permit
“when
imposition
of
conditions
cannot
ensure
compliance with the applicable water qualityrequirements ofall affected
states.”
40 C.F.R.
§
122.44(d)
(2001) (emphasis added).
Simply stated,
the “reasonably
capable” formulation, accepting as it is ofthe potential
that the Permit will not, in fact, attain
water quality standards, does not
appearto be entirely comparable tothe concept ofensuringcompliance.2°
Second,
and
more
importantly,
even
accepting
the
Region’s
suggestion that
ensuring compliance was what the permit writer had
in
mind,
we
find
nothing in the
record, apart from District’s
section 40!
“(continued)
compliance with state water quality standards.”
See
Petitioners
Reply at
4-6.
We do not
reach these arguments, however, because the Region has
stated
that
it is not relying on
this discretion identified
in the Ninth Circuit’s analysis.
Tr.
at 31.
10The “reasonably capable” formulation does not appear to be comtion
usage
in EPA permits.
At oral argument, counsel for the
Region indicated that
he was unaware
of any
other permit
that
relied upon
such
a fonnulation or any
Agency guidance that
recommendedthis formulation ortreated it as comparable to a determination that
a permit
ensures
compliance with water quality
standards.
Ir.
at 41-42.
GOVERNMENTOF THE
DISTRICT OF COLUMBIA
27
MUNICIPAL SEPARATE STORM SEWER
SYSTEM
certification,2’ that supports the conclusion that the Permit would,
in fact,
achieve
water quality standards?1
Indeed, the Region acknowledged that
“unfortunately,
the permit writer didn’t commit a lot ofhis analysis to
writing
*
*
s.”
Tr.
at 46.
Although
we
traditionally assign
a
heavy
burden
to
petitioners
seeking
review
of
issues
that
are
essentially
technical
in nature,
see e.g.. Moscow MS4,
slip op
at 9,
10
E.A.D. at_,
we nevertheless
do
look to determine whether the record demonstrates
that the Region duly considered
the issues raised in the comments
and
whether the approach ultimately
adopted by the Region is rational in light
of
all
information
in the record.
Id,
slip
op.
at
10,
10
E.A.D.
—
(citing
In re NEHub Partners, L.P.,
7
E.A.D. 561,567
(EAB 1998)).
Without
an articulation by
the permit writer of his analysis, we cannot properly
perform any review
whatsoever of that analysis
and, therefore,
cannot
conclude
that
it
meets
the
requirement
of
rationality.
Moreover,
Petitioners
argue,
and
the
Region
does
not
dispute,
that
the
Region
cannot rely exclusively on District’s section 401
certification, at least
in
a
circumstance like
this
one
in
which
there
is
a
body
of
information
2’As
described
more fully
supra
note 5, section 401
oftheCWA requires that
any applicant for
a federal permit
(including
NPDES
permits
issued
by
EPA)
must
provide
the permitting
agency
a certification
from the
state
in
which
the discharge
originates that the
discharge
will comply with the state’s water quality standards.
CWA
§
401,33
U.S.C.
§
1341.
In thepresent case, the District of Columbia Department
of
Health
issued
its certification
on Januaty 6, 2000,
that the conditions
set forth
in
the
second draftpermit
would
comply with theDistrict’s water quality standards, approved
waterquality management plans and District monitoring requirements.
Index pt.
1.1 5,a,
211t bears noting that, in the context of an MS4 pern~it,compliance with
water
quality standards need not be immediate, but must occurwithin“3 yearsafter thedateof
issuance
of such permit.”
CWA
§
402(,p~4~A),
33
U.S.C.
§
1342(,p)(4)(A);
see a/so
Memorandum
by
E. Donald Elliot, EPA Assistant Administrator andGeneral
Counsel,
to Nancy J.
Marvel, Regional Counsel Region
IX, at 4-5
(Jan. 9,1991) (“In light of the
express
language,
we
believe
the
Agency
may
reasonably
interpret
the
three-year
compliance provisions in
Section 402fp)(4) to apply
to all permit conditions, including
those imposed under section
30l(b)(l)(C) water
quality standardsl.”).
Accordingly,
the determination relative to waterquality standards that the
permit issuer is required to
make at the time of issuance is that the permit will achieve compliance within three years.
As
explatned
below,
however,
even taking
this
flexibility
into
account the
record
is
deficient
here.
28
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
drawing the
certification into
question.
See
Tr.
at 43.
Accordingly,
additional record support for the Region’s determination
is needed,and,
finding such support altogetherabsent from the record, we
are remanding
the
Permit
to
the
Region
to
provide
and/or
develop
support
for
its
conclusion that
the permit
will
“ensure” compliance
with the District’s
waterqualitystandards and to make whateveradjustments in the Permit,
ifany, might be necessary in light of its
analysis.23
C.
Petitioners ‘Issue
Two: Hickey Run Numeric Effluent Limits
The second category ofissues raised by the Petitioners concerns
the Permit’seffluent limits and monitoring requirements for four outfalls
into Hickey Run.
The Petitioners object that
the prescribednumeric limit
is
set
forth
as
an
aggregate
limit
covering
all
four
outfalls,
and
the
Petitioners
object
that
the
prescribed
requirements
for
monitoring
compliance
with the numeric limit lack the specificity
required by
the
regulations.
Petitioners object tothe aggregate limit on
the grounds that,
according
to Petitioners,
the regulations “require
that effluent
limits be
outfall
specific unless
infeasible”
and “EPA has not
shown
that
outfall
specific limits are infeasible.” Petition at 5.
Petitionerselaborate on this
point
in
their
Reply
Brief,
stating
that
“EPA
rules
explicitly
require
outfall
specific effluent limits.”
Petitioners’
Reply at 6.
Petitioners also
argue
in
their Petition
that
“the
monitoring provisions
relevant
to
the
Hickey
Run
effluent
limit are
inadequate
because
the
Permit
fails
to
“specif~’the
type and
interval of required
monitoring
as
well
as
the
frequency,”
and
because
the
Permit
fails
to
specify
“the
precise
monitoring locations.”
Petition
at 6.
~As we observed above, our
determination
that the
Region
is not
required to
include narrativepermit
conditions requiringcompliance with
waterquality standards
does
not preclude the Region
from employing
such provisions
in any reissued
permit
upon
remand,
we
note
in
this
regard
that
inclusion
of enforceable narrative permil
conditions
requiring cotnpliance
with
applicable
water quality
standards within
three
years
may be particularly useful in the event that the Region has difficulty stating that.
without such a condition, compliance with
waterquality standards
is assured.
GOVERNMENTOF THE DISTRICT OF COLUMBIA
29
MUNICIPAL SEPARATE STORM SEWER SYSTEM
The Region argues in
its response
that the Hickey Run
numeric
effluent limit is the first numeric limitation used in any MS4 permit based
on a total maximum daily
load (“TMDL”)24
and that the effluent limit
is
consistent with wasteload allocation set forth in the Hickey Run TMDL
as required by
40 C.F.R.
§
l22.44(d)(1)(vii)(B).
The Region states that
it
approved the aggregate
limit for four outfalls
because
those outfalls
“combine
to make up the Hickey Run
headwaters,”
and “above
these
outfalls,
Hickey Run
does not exist outside the storm sewer pipes,” and
further that “the outfails
are
located close together and one entity
(the
MS4)
is
responsible
for all
four
outfalls
and
could
best oversee
the
implementation.”
Region’s Response at
14.
The Region also states that
the Hickey Run TMDL was not able to more precisely allocate
the load
between
the
outfalls
and
that
the
Petitioners
did
not
provide
any
additional
data or basis
from which individual outfall
limitations
might
be derived.
Id.
at
15.
Thus, the Region states
that it “had no additional
legal
or factual
basis
on
which to
make
the
Hickey
Run
limit
outfall
specific,
and
therefore
concluded
that
such
individual
limits
are
infeasible.”
Id.
at
IS.
With respect to monitoring requirements,the Region argues that
the Permit requires
monitoring of Hickey Run no
less than three times
per
year using the
test analytic method
specified
in Part
136,
and the
Region notes
that the Permit requires the District to develop a sampling
plan withthe First Annual Report.
Id.
at
16.
The Region also argues
that
“the
Permit
requires
that
all
samples
and
measurements
be
representative
of the
volume
and
nature
of the
monitored
discharges
24Under
section 303(d) of theCWA, states are requiredto identi& those water
segments where
technology-based controls
are insufficient to implement theapplicable
water quality
standards,
and which are therefore
“water quality
limited.”
33
U.S.C.
§
131 3(d)( I )(A).
Once a segment is identified as waterqualitylimited, thestate is
further
required
to establish total maximum daily
loads, or TMDLs, for the water segment.
40
C.F.R.
§
130.7 (200!).
A
TMDL is the sum of waste
load allocations for point sources
discharging
into
the impaired segment and load
allocations for
nonpoint
sources
and
natural background.
A TMDL is a measure of the total amount of a pollutant from point
sources, nonpoint sources and natural background
that a water quality limited
segment
can tolerate without violating
the applicable water quality standards,
Sc’t’
Id.
§
130.2(i)
(2001).
30
GOVERNMENT OFTHE DISTRICT OFCOLUMBIA
MUNICIPAL SEPARATE STORM SEWERSYSTEM
consistent
with 40 C.F.R.
§
122.4
l(j)(
1).
Region’s Reply at II.
Finally,
the
Region
states
that
“the
monitoring
requirements,
therefore,
are
representative of the monitored
activity
and
otherwise consistent
with
federal regulations.”
Id.
at
11-12.
We conclude that the
Petitioners have
failed to
demonstrate
in
their Petition that the Region’s decision to speci&
an aggregate numeric
limit
for the
four outfalls
forming
the headwaters of Hickey Run
was
clear error
or a
policy
choice
that
otherwise
warrants
review of this
Permit.
In particular,we cannotendorse Petitioners’ argument that “EPA
rules
explicitly
require outfall specific effluent limits.” Petitioners’ Reply
at 6.
The regulation cited
by
Petitioners reads
as follows:
“All permit
effluent
limitations, standards and prohibitions shall be established
for
each outfall
or dischargepoint
of the permitted facility
*
‘*
‘p.”
40 C.F.R.
§
122.45(a) (2001) (emphasis added).
Notably, this regulation identifies
the
location
to which the limitation is applied (i.e,
“outfall or discharge
point”)
in
the
disjunctive.
Thus,
if we
are
to
give
meaning
to
the
disjunctive phrase “or discharge point,” we must read
the regulation as
contemplating
some
flexibility
in appropriate
circumstances
to
frame
effluent
limits at
a point other than
the outfall.
Therefore, we
cannot
conclude that the Petitioners’ proffered interpretation is required nor that
the regulation precludes per se the
establishment of a
limit at
a point
other than
an outfall.
Moreover, we find no clear error inthe Region’s conclusion that,
in the
unique
circumstances of this case,
an aggregate
limit
fixed
at
a
discharge
point
proximate
to
four
closely
connected
outfalls
was
appropriate.
In this regard, we note that, here, (I) the aggregate limit is
consistent withthe aggregate waste load allocation set forth inthe Hickey
Run TMDL, (2) the four outfalls
are located close together, (3) a single
entity is responsible for all
four outfalls, (4) the four outfalls, together,
form the entire headwaters of Hickey Run,
(5)
the Region
determined
that
it was infeasible to allocate the load by outfall
or otherwise establish
an
appropriate
limit
specific
to
the
individual
outfalls,
and
(6)
the
GOVERNMENT OF THE DISTRICT OF COLUMBIA
31
MUNICIPAL SEPARATE STORM SEWER SYSTEM
Petitioners did notprovide any additional data or basis for the Region to
derive individual outfall limitations.
See
Region’s Response at
l3~l5.25
With
respect
to
monitoring
requirements,
Petitioners’
point
regarding the generality
of the Permit’s monitoring provisions
is well
taken.
At its inception, the Permit would not specify the precise location
or the
sample collection
method of monitoring tests to be performed on
Hickey Run, although the
Permit does contemplatethat greater precision
will be brought
to the Hickey Run outfall monitoring plan
as part of the
District’s First Annual Report.
Agency guidance states that the permit’s
monitoring
and
reporting
conditions
should
specify
(1)
the
sampling
location, (2) the sample collection
method,
(3) monitoring frequencies,
(4) analytic methods, and
(5)
reporting and recordkeeping requirements.
U.S. EPA NPDES Permit Writers’ Manual,
EPA-833-B-96-003,
at
115
(Dec.
1996).
This
guidance
states
further
that
the
permit
writer
is
responsible for determining the appropriate monitoring location and for
“explicitly specifying” this in the permit.
Id.
at 117.
It further states that
“specifying
the appropriate monitoring location in a NPDES permit
is
critical toproducing valid compliance data.”
Id.
In addition, by “sample
collection method,” the
guidance
means the
type of sampling,
such
as
“grab” or “composite”samples,which is distinguished from the “analytic
methods” referenced
in 40 C.F.R. part
136.
Id.
at
122.
The regulations
require that
all
permits
specify the required
monitoring “type,
interval,
and frequency.”
40
C.F.R.
§
122.48(b) (2001).
“We note
that,
since
the Region
has
determined
that
setting
limits
for
the
individual
outfalls
into Mickey Run
is
not
feasible, the Region might
have,
consistent
with theregulations, establisheda system-wide I3MP requirement in lieu of any effluent
limitation.
See
40 C.F.R.
§
122.44(a), (k)(2001)
(allowing the establishment
of BMPs
instead ofeffluent limits where effluent limitations areinfeasible).
Thus, ifsustained, the
Petitioners’ objection might very well producea resultthat is contraty to what Petitioners
request: rather than resulting in individual limits foreach outfall, theone numeric effluent
limit
in
this
Permit
might
be
deleted
in
favor
of
reliance
on
system-wide
13N’IP
requirements.
We
are
not suggesting
that
the
Region
alter
the
Pennut
in
this
regard.
Rather we
simply point out
that this
course ofaction may well have complied with
the
regulat ion.
32
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
Inthe present case, the Region
has notexplained why it departed
from
Agency
guidance
by
not
specifying
the
precise
location
for
monitoring the Hickey Run
discharges, nor
has the Region adequately
explained how the Permit conditions
satisfy the regulatory requirement
to specify the “type, interval, and frequency” of monitoring.
Although
the Region argues that the Permit satisfies the regulations by specifying
that
monitoring
must be conducted
three times per year,
see
Region’s
Response at
16, this
Permit condition does not appear to specify both
the
“interval
and
frequency”
of
monitoring
as
required
by
40
C.F.R.
§
122.48(b).
Further, the Permit’s
reference
to the
monitoring
method
specified in 40 C.F.R.
part
136 does not appear to satisfy the requirement
that
sampling
methods
be specified in the Permit.
However, the Region
argues
that
these
defects
do not require
remand because
they
will
be
cured before the Hickey Run numeric effluent limit becomes effective
—
the Permit requires the District to develop a sampling plan with the
First
Annual Report.
Region’s Response at
16.
We find
the proposed delayed
development of the Hickey
Run
monitoring requirements to be problematic in two respects.
First,
both
section
122.48(b)
and
section
122.44(i)
would
appear
to
require
that
certain
monitoring
conditions
be
included
in
all
permits.
Section
122.48(b) states
that
“All
permits
shall specify” the
monitoring type,
intervals,
and
frequency.
40
C.F.R.
§
122.48(b)
(2001).
Section
122.44(i)
states
that
“each
NPDES
permit
shall
include”
monitoring
conditions
in
addition to
those
set forth
in section
122.48
in
order
to
assure compliance
withpermit limitations.
Id.
§
122.44(i).
The Region
has not explained how its issuance of this Permit, which does not at
its
inception contain
monitoring requirements
for Hickey Run,
comports
with the
regulatory
directive
that
all
permits
include these conditions.
Second,
while
we
recognize
that
the
monitoring
requirements
are
expected to be addedat the time ofthe District’s First Annual Report and
thus should be in
place
before the Hickey Run effluent
limit becomes
effective,
we are
troubled
that
this would
be
accomplished
through
a
minor
permit
modification
without
notice
and
opportunity
for
public
comment.
See
Permit pts. lIl.E & IX.A.5 (as amended).
Given that the
regulations
appear
to
contemplate
that
monitoring
requirements
ordinarily be
included as up-front permit
conditions
—
condittons which
GOVERNMENT OFTHE DISTRICT OF COLUMBIA
33
MUNICIPAL SEPARATE STORM SEWER SYSTEM
would
thus ordinarily
be subjected to public notice and comment
—
and
the fact that we find nothing in the regulations allowing for minorpermit
modifications that authorizes use of a minor permit
modification in this
setting,26
we
conclude
that
this
Permit
does
not
meet
minimum
regulatory
requirements
and that remand of these parts of the Permit is
necessary.
We can foresee
two
possible paths available to the Region for
addressing
the
Permit’s
imprecision
in
the
Hickey
Run
monitoring
requirements
on
remand.
The
path
most
easily
reconciled
with
the
regulatory
requirements would
be to add the
missing
precision
to
the
revised permit at its inception.
An alternative path may be
to
add
the
precision
later
in
the
context
of formal,
notice
and
comment
permit
modification.
However, if the Region pursues the latter option,
it must
articulate its rationale for
the consistency ofsuch an approach
with the
regulations
discussed
above.27
Accordingly,
we
remand the
Permit’s
conditions
for
monitoring discharges
into
Hickey
Run
to
afford
the
Region
an
opportunity
to
address
these
issues
or
to
provide
a
more
detailed explanation of its analysis.
0.
Issues
Three Through Seven:
ME? Standard
In issues threethrough sevenofthe Petition, the Petitioners argue
that
the
Region
failed
to
properly
apply
the
requirement
in
section
402(p)(3)(B)(iii) of the CWA to reduce the discharge of pollutants to the
“maximum
extent
practicable.”
Petitioners
raise
the
following
sub-
issues:
In issue number three, Petitioners argue that
the
BMPs
required
by the Permit will produce no reductions in the discharges of a variety of
pollutants and that the Permit does not contain a number of controls listed
2640 C.F.R.
§
122.63
(2001).
While this
provision
allows for the
permit issuer
to impose
by minor modification “more frequent monitoring
or reporting,”
there
is no
suggestion
in the text oftheregulation that theestablishment ofmonitoring locations can
be
accomplished by minor modification.
See
infra
Part I.E
for further discussion of4U
C.F.R.
§
122.63.
~t:uthcr,
it
would appear that,
in
any case, the Permit must
be constructed
in
such
amanner that ensures monitoring requirements are in place before the Hickey Run
numeric
effluent
I
mit becomes
effective
34
GOVERNMENTOF THE DISTRICT
OF COLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
in
the Agency
guidance manual for MS4 permits.
Petition
at 6-7.
In
issue number four, the Petitioners argue that the Permit’s requirement for
evaluation and upgrade of the BMPs over time constitutes an admission
that the current UMPs are not MEP and that therefore the permit contains
an
illegal
deferral
of compliance.
Id.
at
7.
In
issue
number
five,
Petitioners argue
that this deferral of compliance through upgrades over
time does notcomply with the requirement of section 402(p) to achieve
implementation within 3
years.
Id.
at
7-9.
Finally, in issues number six
and
seven,
Petitioners
argue
that
a
“cost
benefit
and
affordability
analysis” required by Part
III.E of the Permit
is
not
authorized by
the
regulations and illegally introduces cost and affordability as grounds for
not implementing BMPs
that are required to meet MEP.
Id.
at
8-9.
I.
Issue Three: Permit Fails MEP Due to No Reductions
in Certain Pollutants
The
Petitioners
argue
that
the
Permit
fails
to
satisfy
the
requirement of section 402(p)(3)(iii) of the CWA that the Permit reduce
pollutant discharges to the “maximum extent practicable.”
Petition at 6.
Petitioners argue
that the BMPs
required by
the Permit will produce no
reductions in cadmium (Potomac, Anacostiaand Rock Creek), dissolved
phosphorous
(Potomac and
Rock
Creek)
and
copper
and
lead
(Rock
Creek).
Id.
They also argue that the reductions oftotal suspended solids,
BOD, COD,
total
nitrogen
and
total
phosphorus
are
so
small
as
to
constitute no meaningful reduction.
Id.
The
Petitioners
also argue that
the Permit fails to comply
with the EPA guidance manual for the Part
2
application, which according
to Petitioners “sets out in great detail
the
specific
control
measures
that
must
be
included in
any
SWMP,
and
requires
that those
measures be incorporated into the MS4 permit.”
Id.
at 7 (citing U.S. EPA Guidance
Manual for thePreparation
of Part 2 of
the NPDES Permit Applications for Discharges from Municipal Separate
Storm Sewer Systems at
1-9, 6-1 to -25 (1992)).
The
Region
argues
that,
in
the
absence
of
promulgated
technology-based standards defining MEP, the permitting authority must
necessarily approach the question ofwhat constitutes MEP on
a case-by.
case basis, taking into account the totality ofthe circumstances.
Here,the
GOVERNMENTOF TIlE DISTRICT
OF COLUMBIA
35
MUNICIPAL
SEPARATE STORM SEWER SYSTEM
Region concluded that “a relatively
large
number ofnew
activities to be
performed”
under
the
Permit’s
BMPs
satisfies
the
MEP
criterion.
Region’s Response at 17 (quoting Region’s First Response to Comments
at 9-10).
The Region notes that “the Current
SWMP identifies over 220
structural BMPs
that
have been
installed and
over 600
that
have been
approved for installation and/or construction.”
Id.
at
18
(citing Revised
SWMP at 6-2 & tbl.
6.2-1).
The Region notes
further
that “the SWMP
also
details
storm
water
capital
projects
over
the
next
several
years
starting
with
FY
1998
expenditures
of over
$1.3
million,
FY
1999
projects
costing
more
than
$3.1
million
and
projected
costs
from
FY2000-FY2007of $39 million.”
Id.
at
18-19.
In addition, the Region
argues
that
“the
Permit
requires
the
District
to
implement
its
current
SWMP, and then
to focus on specific
revisions to develop an upgraded
SWMP
that
(following
EPA
approval)
will
assure
pollutants
will
be
reduced to the maximum extent practicable.”
Id.
at 19
(citing Permit pt.
111).
We conclude that
the Petitioners have
failed to show
any clear
error of fact
or law in the
Region’s
analysis
or any
policy
choice
that
warrants
review.
As
we
noted
at
the
outset
of our discussion,
we
traditionally assign a heavy burdentopetitioners seeking review ofissues
that
are essentially
technical
in nature.
Moscow MS4,
slip op. at
9,
10
E.A.D.
;
see
also
In
re
Town
of Ashland
Wastewater
Treatment
Facility,
NPDES Appeal No. 00-15, slip op. at
10
(EAB,
Feb. 26,2001),
9
E.A.D.
_;
In
re NE I-tub
Partners,
L.P.,
7
E.A.D.
561,
567
(EAB
1998).
This
is
grounded
on
the
Agency
policy
that
favors
final
adjudication of most permits at the regional level.
45
Fed. Reg. 33,290,
33,412 (May
19,
1980);
see also Moscow MS4,
slip
op. at
9,
10
E.A.D.
Irving
MS4,
slip op. at 16, 10 E.A.D.
_;
In reNew EnglandPlating
Co.,
NPDES Appeal No.
00-7,
slip
op.
at
7
(EAB, Mar.
29, 2001),
9
E.A.D.
_;
Town ofAshland,
slipop. at 9-10,9 E.A.D.
In re
Town of
Hopedale, Rd. of Water
& Sewer Comm ‘rs,
NPDES Appeal No.
00-4,
slip op. 8-9 n.l3
(EAB,
Feb.
13,
2001),
10
E.A.D.
When the Board
is presented
with technical
issues, we look to
determine
whether
the
record
demonstrates
that
the
Region
duly
considered the
issues raised in the
comments
and whether the
approach
36
GOVERNMENT OF TIlE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
ultimately adopted by the Regionis rational in light ofall the information
in the record.
Moscow MS4,
slip op. at
10,
10 E.A.D.
—
(citing
NEHub,
7
E.A.D.
at
568).
If
we
are
satisfied
that
the
Region
gave
due
consideration to comments receivedand adopted an approach in the final
permit decision
that
is rational and supportable,
we typically will defer
to the Region’s position.
Id.
In
the
present
case,
we
note
at
the
outset
that
Petitioners’
emphasis on the
amount
of reduction achieved for the various pollutants
is misplaced.
The key question under section 402(p)(3)(B) ofthe statute
is
what
is
practicable.28
Here,
taking
into
account
the
full
range
of
considerations before
it,29 the Region concluded that the BMPs
required
by
the Permit collectively represent the maximum practicable effort
to
reduce pollution
from the District’s MS4.
We are
loath to second guess
“As noted previously, the
Region stated at
oral argumentthat
it
intends
this
Permit to
also satisfy water quality
standards under section
301 ofthe
Act.
Tr. at 32-33,
Although
we determine in this part that thePetitioners
have
not shown anyclear error
in
the Region’s determinationthat the BMPs specified in
this
Permit were MEP at the time
of issuance of the Permit, the Region must also
determine,
as discussed above
in
Part
fiB,
whether the
conditions ofthis Permit ensure attainment ofwater
quality standards
as
required by
40
C.F.R.
§
122.4(d).
29The circumstances that
existed
when the Region
issued this Permit
were
unusual as explained by theRegion at oralargument:
“When the District finished their
application
in
t998andwhen we issued the permit, the District was stillunderthe control
oftheFinancial Oversight and Management Authority
and there
was some difficulty
in
the
District
in
determining
which
of
the
many
parts
of
its
government
would
be
accomplishing which
task in what time frame.
Nevertheless, the Region
found that it
would be remiss in not issuing the permit with the requirements as specific as we could
set them
at that
time, but to
also require the District to further identify who would do
what
when, where thefunding would come from, and to reevaluate the controls they had
in place.”
Tr. at 50.
The Region statedfurther that, since the issuance ofthe Permit,
the
District’s Water
and Sewer Authority has
been authorized to leadthe administration
of
the storm water management program and that “(tihe District has also been proceeding
forward with the implementation ofmany new structural andother structural BMPs and
otherprograms to reducepollutants.” Tr. at 51.
We assume that these improvements will
be
incorporated in current or revisedform into the Permit
as SWMP upgrades
pursuant
to the process outlined
in the Permit for such
upgrades.
Permit pts. Ill,A &
IlIF.
GOVERNMENTOF THE DISTRICT
OF
COLUMBIA
37
MUNICIPAL SEPARATE STORM SEWER SYSTEM
the Region’s technicaljudgment in this regard.
The record demonstrates
that
the Region duly considered
the
issue raised by
Petitioners in their
comments,
and the record does not lead to the clear conclusion that any
additional
BMPs
beyond those
identified in the Permit are
practicable
taking
into
account
all
of the relevant circumstances
in the
District.30
Accordingly,
we conclude
that
the
position
adopted by
the Region
is
rational in light
of the
information
in the record and consequently we
deny review of this issue.
2.
Issue Four:
Upgrade ofthe SW/VIP over Time
The
J3MPs
specified
in
the
Permit as
the
applicable
effluent
limits
are
the
BMPs
set
forth
in
the
District’s
SWMP.
The
Permit
requires that the District’s SWMP,and the BMPs set forth inthe SWMP,
be
evaluated
and
upgraded over
time.
The Petitioners
argue
that
the
Permit’s requirement
for the
BMPs
to be evaluated and upgraded over
time
constitutes
an
admission that
the current liMPs
do
not
meet
the
MEP criterionand that therefore the permit contains an illegal deferral of
compliance with the permitting requirements of the CWA.
Petition at 7.
This argument, however,
must fail.
The Region correctly responds that
the current liMPs
are
what the Region has
determined to be MEP and
that
the
evaluation
and
upgrade
requirement
is a
“normal
process of
adjustment
that
the
Region
believes
is
necessary
and
appropriate
to
protect water quality and meet the
MEP criterion.”
Region’s Response
at
19.
The
evaluation
and
upgrade
requirement
of
the
Permit,
and
Agency policy for MS4s, recognizes that knowledge concerning effective
methods for controlling pollutant discharges and barriers restricting the
ability to control pollutant discharges will necessarily change over time.
“To the extent that the Petitioners
seek to rely on Agency guidance
that
lists
specific kinds of control measures to
be
included in the permit application and permit
(EPA, Guidance Manual for the Preparation ofPart 2 ofthe NPDES Permit Applications
for Discharges from Municipal Separate Storm Sewer Systems
at
1-9,6-Ito -25(1992))
as
somehow
showing
that
the Region
failed
to include
in
this
Permit required permit
elements, the Petitioners have failed to show how the Region’s response to comments on
this
issue
did
not
adequately
respond
to
their
comments.
More
particularly,
the
Petitioners have not even identified what conditions that they believe should be included
in
the l’ermil
under the guidance.
Accordingly, we deny review on
this ground.
38
GOVERNMENT OF THE DISTRICT
OF COLUMBIA
MUNICIPALSEPARATE STORM SEWER SYSTEM
The evaluation and upgrade requirement incorporates
into the Permit a
process for
adjusting
the Permit’s
terms
and
conditions
to
take
into
account new knowledge and changed circumstances affecting practicality
ofliMPs.
This adjustment process does not imply
that the Region has
failed
to properly
assess
MEP at the time
of the
Permit’s
issuance;
it
simply recognizes that what is practicable will change over timeand that
the Permit
should be adaptable to such changes.
In short, the Petitioners
have
not
shown clear
error
in
the
Region’s
determination of
what
is
“practicable” at the
time of Permit issuance.
3.
Issue Five: Compliance within
Three Years
The Petitioners argue
that
the evaluation
and upgrade
process
discussed
above
does
not
comply
with
the
requirement
of
section
402(p)(4)(A) of the CWA to achieve actual implementation within three
years.
Petition
at
7-8.
This
argument
also
must
fail,
The
Region
correctly
notes
that
the
Permit
requires
the
District
to
immediately
implement the liMPs that have been determined to be MEP at
the
time
of Permit issuance and,
in addition, the Permit requires
the District
to
begin
a process of continual upgrade and improvement of those
BMPs.
Region’s Response at 21.
Thus, the Permit does not authorize a deferred
implementation of the liMPs that were determinedto be MEP at the time
ofissuance of the Permit; instead, the Permit simply recognizes that what
is practicable will change during
the Permit’s term and that upgrades
of
the
Permit’s
requirements
should
not
be
delayed
until
the
Permit
is
renewed.
Accordingly, here again we deny review.
4.
Issues Six and Seven: The Implementation Plan and
Cost Benefit
Analysis
The
Petitioners
note
that
the
Permit
requires
the
District
to
submit each year a SWMP implementation plan covering the work to be
done in the
next three years
and to analyze that
work “based
on
a cost
benefit
and
affordability
analysis.”
Petition
at
8
(quoting
Permit
Pt.
lll.E).
The
Petitioners
argue
that
this
“cost
benefit
and
affordability
analysis”
is not found anywhere in the Agency’s regulations or guidance
documents.
Id.
at
8-9.
Petitioners also argue
that the
“cost benefit and
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
39
MUNICIPAL SEPARATE STORM SEWER SYSTEM
affordability” analysis
would allow
the District to
avoid
liMP
effluent
limitations
by
claiming
that
it
has
inadequate
resources
to
meet
the
implementation schedule.
Id.
at
9 (issue number seven).
Specifically,
they state that “compliance cannot be contingent on the willingness ofthe
Mayor,
the Control lioard, or Congress to appropriate
funds.”
Id.
The
Region argues that the Petitioners’
concerns are unfounded.
The Region
argues that
the “cost
benefit and
affordability analysis” is
authorized
by
the CWA because it is meant to implement the “practicability” part of the
MEP test in determining liMP requirements.
Region’s
Response at
23.
The
Region
also
argues
that
the
Permit
specifically
states
that
affordability is not a defense for compliance withthe Permit’s terms.
ld.
(citing Permit,
pt. III.E).
We conclude that the Petitionershave not shown
any clear error
of
fact or law or shown
that
a policy
choice
made by
the Region with
respect to the “cost benefit analysis” in part lII.E of the Permit warrants
review.
We base this holding, in part, on our recognition that this Permit
contains
provisions
establishing liMPs
set
forth
in the current
SWMP
that were determinedto be MEP at the time of the Permit’s issuance, and
it also contains provisions requiring upgrade ofthe current SWMP within
three years ofthe Permit’s issuance.
In this context, the required Annual
Report
and
SWMP
Implementation
Plan
serve
two
functions:
they
provide
reporting
on
compliance
with
the
Permit’s
requirement
to
implement the current
SWMP, and
they provide information,
analysis
and
preliminary
proposals
for terms
to
be
included
in
the
upgraded
SWMP when the
Permit is amended.3t
Information concerning a “cost
benefit
analysis”
of
the
various
liMPs
is
relevant
for
the
process
of
amending the Permit with an upgraded SWMP and npgraded liMPs.
As
stated by the Region, “un
terms of establishing the permit requirements
to reduce pollutants to the
maximumextentpracticable,
the Region finds
cost
and
affordability information
useful
in determining the degree of
practicability.”
Region’s Response at
24.
“As
discussed
below in
Part
tI.E of this
decision,
we are remanding those
porlions olParl
llI.E of the
Permit that purport to allow the Region to change
the ternis
of the
Pennit
by minor modification
procedures.
40
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICiPAL SEPARATE STORM SEWERSYSTEM
This
cost
benefit
information,
however,
is
not
relevant
for
determining compliance with the Permit’s requirement that the District
implement
the
BMPs
in
its
current
SWMP.
By
incorporating
the
District’s current
SWMP
into the Permit, the Region
has determined that
the
BMPs
set
forth
in
that
SWMP
are MEP.
The Region,
thus,
has
already determined that those liMPs are “practicable” and consideration
of
costs
or
benefits
is not
appropriate
when
considering
whether
the
District
has complied with the requirement to
implement those
BMPs.
This distinction between the compliance-reporting
and future planning
functions
of the
Annual
Report
and
Annual
Implementation
Plan
is
recognuzed
and
mandated
by
the
Permit’s
condition
that
states
that
“affordability
cannot be used as a defense for noncompliance.”
Permit
pt.
IH,E.
Accordingly, we see no clear error in the Region’s decision to
require
that
the
District’s
Annual
Implementation
Plan
provide
information regarding the costs and benefits ofthe various liMPs covered
by the plan, and we deny review of this condition of the
Permit.
E.
Issue
Eight:
Mod(JIcations of the Permit
Petitioners argue that the Permit “illegally authorizes substantive
changes
in
permit
requirements
without
a
formal
permit
revision.”
Petition
at
9.
In
its
Response, the
Region “notifles
the Board of the
Region’s proposal to amend the permit to address this issue and that
such
amendment would remove the issue from this appeal in accordance with
40 C.F.R. § 124.19(d).”
Region’s Response at 25.
Subsequently, on
January
12,
2001,
the Region
re-issued
the withdrawn portion of
the
Permit
with
several
amendments.
Thereafter,
the
Petitioners
filed
a
petition
for
review of the amendments to
the Pennit.
See
Petition
for
Review and Motion to Consolidate (Feb. 2,2001).
The Petitioners also
filed a supplemental briefsupportingtheir original Petition on this issue.
See
Supplemental Reply Based on Intervening Permit Modification,
As
noted above in Part I.li, we have consolidated the February 2001
petition
withthe
original
Petition, and will consider all related issues in this part
of
our analysis.
In their secondpetition,
Petitioners recall that they had
argued
in
the
first
Petition
that
the
Permit would
improperly allow
eight
types
of
GOVERNMENT OF THE DISTRICT OF COLUMBIA
41
MUNICIPAL SEPARATE STORM SEWER SYSTEM
permit modifications to be made under
the regulations governing
minor
modifications.
Second
Petition
at
5.
The
Petitioners
listed
these
allegedly improper modifications
in eight categories.
Petitioners argue
that
all
of the
types
of modifications
identified
in
its
original
list
are
major
modifications
that
must
comply
with
the
more
stringent
requirements for formal
permit
revisions,
including public
notice and
comment.
Id.
at 7-9.
Petitioners state that the Region’s amendment to
the
Permit
addressed
only
a
portion of
one
of
those
eight
types
of
modifications.
Id.
The
types of modifications originally identified
by
Petitioners as improper minor modifications
are as follows:
a.
Changes
in
deadlines
for
submission
of Annual
Review,
Annual Report,
Annual
Implementation Plan,
and Upgraded
SWMP
(Permit pt.
III.A).
b.
Changes
in
deadlines
for
implementing
outfall
monitoring and implementing upgraded SWMP (Permit
pt. Ill-A).
c.
Extension of time for implementing
illicit discharge
program (Permit
pt. III.B.lO,
at
22).
d.
EPA
approval
of
schedule
for
developing
and
implementing an enforcement plan and approval of the
plan itself (Permit pt. III.B.l I, at
22-23).
e.
EPA
determination
of minimum
levels
of
effort
required for additional SWMP program activities needed
to meet requirements of EPA rules (Permit pt. III.B. 12,
at
25).
f.
EPA
approval,
disapprpval or
revision
of Annual
Report and Annual Implementation Plan, and upgraded
SWMP (Permit Pt. III.E,
at
29).
g. Other programmodifications (Permit pt. III.H, at 30).
h.
Changes inmonitoring locations from those specified
in the Permit (Permit pt. IV.A. l,at 34; pt. VillA, at 45;
N,
lX.C, at 49).
Second
Petition
at
4;
see
a/so
Id.
at
7;
Petition
at
9-10.
Petitioners
recognize that
the
Region’s
amendment to the Permit requires that
EPA
approval of the
upgraded
SWMP (a part of item (1)
in the list)
be subject
42
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE STORM SEWER SYSTEM
to major modification procedures of
40 C.F.R.~122.62.
Second Petition
at
5.
The
Petitioners
continue
to
argue
that
all
of
the
remaining
modifications
contemplated
by
these
eight
categories,
including
the
remnant ofcategory (f) not changedby the Region’s amendment, are also
major modifications
that
cannot be made under the minor modification
procedures.
Petitioners
also
specifically
argue
that
any
changes
in
interimcompliance dates cannotextend the date ofcompliance more than
120 days
if implemented under the minor modification provisions of 40
C.F.R.
§
122.63
and that any longer extensions can onlybe accomplished
by
modification under the procedures of section
122.62.
The Region, in contrast, argues that
all of the modifications
at
issue fall within the ambit of permissible
minor modifications
under 40
C.F.R.
§
122.63.
See
Region ill’s Response to Petition for Review at 7-8
(Mar. 28,
2001)
(“Region’s
Second
Response”).
With
respect
to
the
issue of extensions of interim compliance dates,
the Region argues
that
“while
the Permit does not explicitly limit such extensions
to the
120
days allowed
by
the regulations, the Permit requires
that
such revisions
be
‘in
accordance
with
40
C.F.R.
§
122.63,’
which
sets
forth
such
a
requirement for interim compliance dates.”
Region’s Second Response
at
8.
The Region goes on to argue that the modifications challenged by
Petitioner in its categories (a), (b), (c) and (d) are interim compliance date
changes
falling within
the scope of section
122.63.
Id.
at
10-12.
The
Region maintains that
the modifications
challenged
by
Petitioner in its
categories
(e)
and
(0
are merely
the
proper
exercise
of “review
and
approval” of various
reports
and implementation
plans
and
that
such
oversight
is properly part
of the Region’s duties
in administering
this
Permit.
Id.
at
12~l3.32
The
Region
argues
that
the
modification
addressed in Petitioners’
category (g) “only
lays out the procedures by
which the SWMP
modifications will be implemented by
the District
in
context with
the compliance schedule discussed
above.
By
itself this
provision
has
no
substantive
effect.”
Id.
at
13.
With
respect
to
Petitioners’
final category concerning changes in monitoring
locations
UThe Region raises asimilar argument regarding categoiy
(d)
to the extent that
Petitioners
object
to
interim “approvals”
in that
categoty.
Region’s
Second
Response
at
II.
GOVERNMENT OF THE DISTRICT OF COLUMBIA
43
MUNICIPAL SEPARATE STORM SEWER SYSTEM
(Petitioners’ category (h)),
the Regionargues
that
“there
is
nothing in40
C.F.R.
§
122.63
that
would
prohibit
EPA
from authorizing change
in
monitoring locations
for MS4 compliance
purposes.”
Id.
The Region
also
argues
that
allowing
the
District
to
select
other
equally
representative
outfalls
for
monitoring
is
a
reasonable
exercise
of
its
authority to monitor a complex and dynamic permit.
Id.
at
14.
We
begin
with
the
regulatory
text.
Section
122.63,
which
governs minor modifications, provides as follows:
Upon the consent of the permittee,
the Director
may
modi&
a
permit
to
make
the
corrections
or
allowances for changes inthe permitted activity listedin
this
section,
without
following
the procedures
of part
124.
Anypermit modUication notprocessed asa minor
modification under this
section must be madefor cause
and with
part
124
draft permit
and
public
notice
as
required in
§
122.62.
Minor
modifications
may
only:
(a)
Correct typographical errors;
(b)
Require
more
frequent
monitoring
or
reporting by
the permittee;
(c)
Change
an
interim
compliance
date
in
a
schedule of compliance, provided the
new
date
is not
more
than
120
days
after
the
date
specified
in
the
existing permit and does not interfere withattainment of
the
final compliance date requirement;
or
(d)
Allow
for
a
change
in
ownership
or
operational
control
of
a
facility
where
the
Director
determines
that
no
other
change
iii
the
permit
is
necessaly,provided that a written agreement containing
a
specific
date
for
transfer
of
permit
responsibility,
coverage,
and
liability
between
the
current
and
new
permittees
has been submitted to the
Director.
(e)
(I) Change
the construction
schedule for
a
discharger which is a new source.
No such change shall
affect
a
discharger’s
obligation
to
have
all
pollution
44
GOVERNMENT OF THE DISTRICT OF COLUMBIA
MUNICIPAL SEPARATE
STORM SEWER SYSTEM
control
equipment
installed
and
in
operation prior
to
discharge under
§
122.29.
(2)
Delete
a
point
source
outfall
when
the
discharge
from
that outfall
is terminated and does
not
result
in
discharge
of
pollutants
from
other
outfalls
except in accordance with permit limits.
(1)
Reserved~
(g)
Incorporate
conditions
of
a
POTW
pretreatment program
*
*
*
as
enforceable conditions of
the POTW’s
permits.
40 C.F.R.
§
122.63(a)
-
(g) (200!) (emphasis added).
Significantly, this
regulation
allows
changes
to
the
Permit
without
formal
notice
and
comment
procedures
“only”
when
the
changes
fall
within
the
listed
categories,
and it expressly
requires all
other modifications
to be made
pursuant to the
formal procedures of section
122.62.
With respect to the narrow issue ofwhether the Permit authorizes
extensions of interim compliance dates that are longer than
120 days, we
conclude that the better interpretation of the Permit is one that reconciles
the
text
of
the
Permit with
the
applicable
rules.
Thus,
we
adopt the
Region’s
interpretation
that
the
reference
in
the
Permit
to
40
C.F.R.
§
122.63
serves to limitthe allowable extensions of interim compliance
dates undertaken as minor modifications to “not more than
120 days after
the
date specified
in the existing permit and
provided
that it~
does
not
interfere with attainment of the final compliance
date requirement.”
40
C.F.R.
§
122.63(c) (2001).
In
addition,
we
also
adopt
the
Region’s
interpretation that
Part
111.11
of
the
Permit (Petitioners’
category
(g))
“b~yitself
*
*
*
has no substantive effect.”
Regions’
Second Response
at
13.
Thus, Part
111.1-I may not be relied upon
as independent authority
for modifying the
Permit; rather authority
for a proposed modification
must be provided elsewhere in the Permit or in the applicable regulation.
With
respect
to both of these issues,
our interpretation of
the Permit’s
terms will be binding
on
the Region
in implementing the permit.
See
Irving MS4,
slip op.
at 26 n.20,
10 E.A,D.
(“Because
we serve as the
final decision maker for the
Agency
in this matter, our interpretations
will
be
binding
on the Region in its
implementation of the permit”).
GOVERNMENTOF THE DISTRICT OFCOLUMBIA
45
MUNICIPAL SEPARATE STORM SEWER
SYSTEM
Next,
we
consider
whether
the
Region
is
correct
that
the
modifications challenged by Petitionerinits categories (a), (b) and (c) are
interim
compliance
date
changes
falling
within
the
scope
of section
122.63(c).
See
Region’s
Second
Response
at
10-13.
That
section
authorizes the minor modification
procedures to be used
to change
“an
interim
compliance
date
in
a
schedule
of
compliance.”
40
C.F.R.
§
122.63(c) (2001).
Thus, inanalyzing the issues raised by
Petitioner and
the
Region’s
response, we
first
must
determine
whether
the
changes
authorized
by
the Permit in Petitioners’
categories (a), (b)
and
(c)
are
changes
to interimcompliance
dates in a “schedule of compliance.”
The term “schedule of compliance” is definedby the regulations
to
mean
“a
schedule
of
remedial
measures
included
in
a
‘permit,’
includingan enforceable sequence of interimrequirements (forexample,
actions, operations, or milestone events) leading to compliance
with the
CWA
and
regulations.”
40
C.F.R.
§
122.2
(2001).
Schedules
of
compliance
are
required to
be
included
as
conditions
of a
permit
“to
provide
for and
assure compliance
with all
applicable requirements
of
CWA and regulations.”
Id.
§
122.43(a).
“Schedules ofcompliance” are
governed by 40 C.F.R.
§
122.47, which
requires, among other things,that
a schedule of compliance “shall require compliance
as soon as possible,
but not later than the applicable statutory
deadline under the CWA.”
Id.
§
122.47(a)(l).
In
the
present
case,
Part
III.A
of
the
Permit
is
captioned
“Compliance
Schedule.”
In that
part of the
Permit, there
are
various
substantive requirements leading
to the implementation of an upgraded
SWMP
and
a
schedule of “deadlines”
for
steps
in
that
process.
In
particular,
deadlines
are
set
for
“First
Annual
Report,”
“Implement
outfall monitoring,” “First Annual Implementation Plan,” submission of
“Upgraded
SWMP,”
and
“Implement
Upgraded
SWMP.”
Permit
Pt.
LIlA, tbl.
I.
Part III.A of the Permit also states that “the requirements
in
Table
2
in Part
III.B of this permit are
to be used in development of the
upgraded
SWMP” and
that
“the
District’s November
4,
1998
SWMP
(or revised/upgraded SWMP)
is also
incorporated by
reference
into this
permit.”
Permit
pt.
llL.A
at
6.
Both
the
substantive
requirements
set
forth
in
Part
LI1.A
of
the
Permit
and
the
requirements
in
Table
2
in
46
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
MUNICIPALSEPARATE STORM SEWER
SYSTEM
Part
III.B
of the Permitappear to be “schedules
of remedialmeasures”
fitting the regulatory definition of “schedule of compliance.”
40 C.F.R.
§
122.2 (2001).
In addition, these deadlines
appear to
be “enforceable
sequences
ofinterim requirements (for example, actions, operations, or
milestoneevents) leading to compliance withthe CWA and regulations.”
Thus, we conclude that the Petitionershave failedto show any clear error
of fact or law,
or
important policy
decision,
warranting
review
of the
Region’s decision to characterize the deadlines set
forth in Part Ill.A as
“interim compliance
dates
in a schedule of compliance” that
may
be
modified
as
set
forth
in
40
C.F.R.
§
122.63(c).
Accordingly,
as
Petitioners’ categories (a) and (b) list deadlines set forth
in Part lIlA, we
decline to grant review of these portions of the
Permit.
We also find
credible the
Region’s argument that
the deadlines
identified by Petitioners in their category (c)
are appropriately viewed as
“interim
compliance
dates~ in
a
schedule
of
compliance”
under
40
C.F.R.
§
122.63(c).
Category
(c) refers to deadlines, and authorizations
for extensions of such deadlines,
that are set
forth in Part III.B. 10 of the
Permit.
These deadlines appear to be additional detailed sub-parts of the
deadlines identified in the schedule of compliance
set
forth in Part III.A
of the Permit.
Accordingly, we decline review of Petitioners’
category
(c).
We note, consistent with our holding above,
that any extension
of
the deadlines set forth in Parts Ill.A and III.B.I0 of the Permit may
not
be more
than
120
days from the
date
in the
existing
Permit.
40
C.F.R.
§
122.63(c) (2001).
We conclude, however, that the Petitionershave shown
that the
Region erred in
approving a
Permit condition that
authorizes
changes
listedin Petitioners’
categories (h) as minor modifications under section
122.63,
and
we
conclude
that
Petitioners
have
raised
substantial
questions
regarding
the
scope
of
changes
authorized
by
the
Pennit
conditionsidentified in Petitioners’
categories (d), (e)
and
(fl
that require
clarification.
In Petitioners’ category (h), they
object tothe Permit’sconditions
that authorize changes
to the monitoring locations that are required by the
Permit
(Pennit
pts.
IV.A.l,
VILlA,
lX.A.5
&
lX.C).
The
Region
rnuc’n.lnr,.jr
flL’
TUV
flWTntr’rn—’——’.s,a.
GOVERNMENT OF THE
DISTRICT OF COLUMBIA
49
MUNICIPAL SErARATE STORM SEWER SYSTEM
them as meritorious,33 and because the Region failed to make changes to
the Permit or to otherwise address Petitioners’
concerns regarding these
waivers and exemptions, we are remanding this portion of the Permit to
the Region to either make appropriate changes
tothe Permit or to explain
why
the Petitioners’
comments
do
not merit changes
to the Permit.
III.
CONCLUS1ON
For the foregoing reasons, this matter is remanded to the Region
for further proceedings consistent with this decision.
So ordered.
“Based
on our review,
there may be
cause
for
treating these
concerns
as
meritorious,
Petitioners observe that 21
DCMR
§
514.1 allows variances to requirements
for land disturbing activities,
erosion control requirements, and storm water control at
construction
sites,
all
of
which are
part
of
the storm
water
management
activities
incorporated
as
BMPs
into
the
Permit.
Petitioners’
Reply
at
12-13.
In
addition,
Petitioners point out that the exemption provisions of2l
DCMR
§~
527.1
and 528 also
apply to storm
water management
requirements
incorporated as BMPs
into the Permit.
Id.
at
3.
Ii
is
not clear
how these
BMPs can
be enforceable obligations of the Pennit
when the District’s regulationsthat are also incorporated into the Permitgrant the District
the right to grant waivers and exemptions from these I3MP requirements under standards
that
apparently
are not
found
in
federal
law and without
notice
to
the
Region
or
the
public.
‘the
Region
should address
these
issues
on
remand,
either by
changes
to
the
Permit
or by
an
explanation of
the
Region’s
rationale
for
why these
concerns do
not
warrant
utoditicat oils to the
Permit.
NOTICE:
PRAIRIE RIVERS
NETWORK,
Petitioner, v. THE ILLINOISPOLLUTION CONTROL BOARD;
THE
ILLINOIS ENVIRONMENTAL PROTECTION AGENCY; and BLACKBEAUTY COAL COMPANY,
Respondents.
NO. 4-01-0801
APPELLATE COURT OF ILLINOIS, FOURTH
DISTRICT
2002 III. App. LEXIS
1244
July
17, 2002, Submitted
October 24, 2002, Filed
IS
NOT
FINAL
UNTIL
21
DAY
PETITION
FOR
PRIOR HISTORY:
Administrative Review of the Illinois
Pollution Control Board. No.01112.
DISPOSITION: Affirmed.
CASE
SUMMARY
PROCEDURAL
POSTURE:
Petitioner conservationists
sought review of a decision of respondent Illinois
Pollution Control Board in which
it refused to set
aside a
National Pollutant Discharge Elimination System
(NPDES) permit issued to respondent coal company by
respondentIllinois
Environmental Protection Agency
(IEPA).
They
argued
primarily that the
IEPA should
have reopened public commentafter significantly
altering a draft permit.
OVERVIEW:
Pursuant to
33
U.S.C.S.
§
1342,
the
federal Environmental Protection Agency had authorized
the IEPA to administer
its own NPDES permit program,
according to
its own rules, within the parameters of the
FederalWater Pollution Control
Act. Nothing in the
authorizing federal statute
required the IEPA
to go
beyond
the requirement that
it allow public participation
to require
it to reopen
a public comment period. In
the
instant case, in fact,
the
final permit contained far greater
limitations on the coal company’s discharge of effluent
into a creek than the
draft permit had. The regulations
promulgated pursuant to the Illinois Environmental
Protection Act provided plentiful opportunities
forpublic
participation. Section 40(e) ofthat
act,
415
111.
Comp.
Stat.
Ann. 5/40(e)
(West
2000),
further made
it
clear that
it was the
conservationists’ burden to show irregularities
in the issuance
of the permit, and this they had failed to
do. The other issues that the
conservationists sought to
raise were either moot or inadequately argued for review.
OUTCOME:
The
court affirmed the administrative
decision.
CORE TERMS:
regulation, public comment, issuance,
Clean Water Act, public hearing, monitoring,
administrator, public participation, tentative, revised,
round, burden ofproof, issuing, water, public notice,
notice, third-party, tributary,
storm, drastically,
administer, guidelines, revision, prepare, thirdparty,
biological, unnamed, basin, tentative decision, permit
application
CORE
CONCEPTS
-
Environmental
Law: Environmental Quality
Review
Environmental Law: Water Quality
The United States Environmental Protection Agency
generally waives
its
right to reviewNational Pollutant
Discharge Elimination System
permits
issued by the
Illinois Environmental Protection Agency to coal mine
operators.
Environmental Law: Water Quality
The
ultimate objective ofthe Federal Water Pollution
Control
Act
(the Clean Water
Act), as described at
33
U.S.C.S.
§
1251(a),
is
to restore
and
maintain
the
chemical, physical,
and
biological
integrityof the
nation’s waters, and it establishes
a permit program,
the
National Pollutant Discharge Elimination System
(NPDES),
to achieve
this
goal. Under this program,
any
1
THIS
DECISION
EXPIRATION
OF
THE
REHEARING PERIOD.
I
EXHIBIT B
pollutant discharge
into navigable waters without an
authorization permit is banned.
Congress intended that
much of this authority devolve to the states.
33
U.S.C.S.
§
1251(b).
The Clean
WaterAct stipulates that any time
after the promulgation of federal guidelines
establishing
the
minimum elements
of state permit programs, a state
may submit a description of a proposed program,
along
with a statement
from the
state attorney general that state
law provides adequate authority to carry out the
program,
for evaluation by the Administrator of the
United States
Environmental Protection Agency. If the state program
satisfies the
statutory requirements of
33
U.S CS.
§
1342(b),
and the
guidelines issued under
33
U.S.C.S.
§
13140),
the Administrator must approve the
program.
The state
then assumes primary responsibility for the
issuance of permits and for the
administration and
enforcement of the NPDES program within
its
jurisdiction.
Environmental
Law: Water Quality
See
415
111.
Camp. Stat Ann.
5/13(b) (I)
(West2000).
Environmental Law: Water Quality
In Illinois,
a
party seeking
a National Pollutant Discharge
Elimination System
permit
must file an application with
the Illinois
Environmental Protection Agency (IEPA).
35
IlL Admin.
Code
tit
35,
§
309.103
(2002). If the
application is complete, the
IEPA prepares a tentative
determination regarding
the application, and if the
agency intends to issue
the permit, prepares a draft
permit.
Ill.
Admin. Code
lit
35,
§
309.108(2000).
Environmental
Law: Water Quality
Upon receiving a National Pollutant Discharge
Elimination System (NPDES)
permit application, the
Illinois Environmental Protection Agency (IEPA) must
issue
a public
notice of the permit application and the
agency’s
tentative determination to issue or
deny the
permit.
IlL Admin. Code
tit
35,
§
309.109(2002).
This
notice must provide
fora period ofnot less than 30 days
for persons to submit public comments
on the
agency’s
tentative
determination and, where applicable, on the
draftpermit.
Ill.
Admin. Code
tit.
35,
§
309.109(b)
(2002), pursuant to which all
comments shall
be
submitted to the
agency and
to the applicant and shall
be
retained by
the
agency and considered in the
formulation
of its
final determinations with respect to the NPDES
application. The IEPA also must provide notice of the
permit application to other governmental agencies.
Ill.
Admin.
Code
lit
35,
§
309.114(2002).
Environmental
Law:
Water Quality
If the Illinois
Environmental Protection Agency (IEPA)
determines
that
there exists
a significant degree ofpublic
interest in a proposed National Pollutant Discharge
Elimination
System (NPDES) permit,
the agency
shall
hold a public hearing on the
issuance or denial of the
permit.
Ill.
Admin. Code
lit
35,
§
309.115(a)
(2002).
Following
the public hearing, the
agency
may
make such
modifications in the
terms
and conditions of
proposed
permits as
may be appropriate.
IlL Admin. Code
lit.
35,
§
309.119(2002).
The IEPA must transmit
to
the
regional
administratorof the United States Environmental
Protection Agency
for his approval a copy of the permit
proposed to be issued unless the
regional administrator
has
waived his right to receive
and
review permits of its
class.
IlL Admin. Code
lit
35,
§
309.119(2002).
The
IEPA also must provide a notice of such transmission to
the applicant,
to any person who participates in the
public hearing, to any person who requested a public
hearing, and to appropriate persons on the
mailing list
established under
IlL Admin.
Code
lit.
35,
§~
309.109-
309.112.
Such notice shall briefly indicate any
significant changes that
were made from
terms
and
conditions set
forth
in the
draft
permit.
IlL Admin.
Code
lit.
35,
§
309.1/9(2002).
Environmental Law: Water Quality
After conducting
a hearing on
an application for a
National Pollutant Discharge Elimination System permit,
the Illinois Environmental Protection
Agency (IEPA)
must issue
a responsiveness summary, addressing
comments
made during
the public
hearing.
IlL Admin.
Code
lit.
35,
§
166.192(2002).
If the
IEPA
does not hold
a public hearing after the
close of the
comment period,
the
agency must, after evaluation of any comments
which
may
havebeen received, either issue or deny
the
permit.
Governments: Legislation: Interpretation
In cases involving the interpretation of a
statute by
an
agency charged with administering
it,
the
agency’s
interpretation is
afforded considerable deference,
but it is
not binding on the court and will be rejected if erroneous.
Governments:
Legislation:
Interpretation
The cardinal rule of statutory construction is to ascertain
and give effect to the intent of the legislature.
Governments:
Legislation: Interpretation
The words of a statute
are given their plain and
commonly understood meanings.
Governments: Legislation: Interpretation
Only when the meaning of the enactment is unclear from
the statutory language will the court
look beyond the
language and resort
to
aids for construction.
Governments:
Legislation: Interpretation
A
court should not depart from
the language ofthe
statute
by reading into
it
exceptions,
limitations, or
conditions
that conflict with the
intent of the legislature.
2
Environmental Law: Water Quality
Administrative Law: Agency Adjudication:
Review of
Initial Decisions
See Illinois
Environmental Protection Act
§
40(e)(I),(3),
415 III.
Comp.
Stat. Ann. 5/40(e)(I),
(3) (West 2000).
Governments: Legislation:
Interpretation
The best evidence of legislative
intent is the statutory
language itself, which must be given
its
plain and
ordinary meaning.
Enviránmental Law: Water Quality
When the petitioner in a National Pollutant Discharge
Elimination System
permit
appeal is the permit
applicant,
the petitioner has the burden of proving that
the requested permit would not violate the Illinois
Environmental Protection Act or the regulations of the
Illinois Pollution Control Board. The scope of
this
burden does not
change
when the petitioner
is
a third
party challenging the
issuance of a permit. Thus, a third-
party
petitioner must show that the permit, as issued,
would violate the Act or the Board’s regulations.
Environmental
Law: Water Quality
Administrative Law: Agency Rulemaking: State
Proceedings
Pursuant
to Federal Water Pollution Control Act (Clean
Water Act)
§
l342(b)(3),
33
U.S.C.S.
§
1342(b)(3),
any
state desiring to administer its
own
National Pollutant
Discharge Elimination System (NPDES) permit program
must demonstrate that
it has
adequate authority to insure
that the public receives notice of each applicationfor
a
permit and to provide an opportunity forpublic hearing
before a ruling on each such application. This public
participation
requirement for draftpermits
is specifically
set
forth at 40 C.F.R.
§~
124.6,
124.10, 124.11,
124.12
(2000). Notably absentfrom the Clean Water Act’s
requirements for state
NPDES
programs is any
requirement that such programs
include provisions for
the reopening of
the public commentperiod or the
preparation of a new
draft permit based
on
information
submitted during the initial commentperiod.
Environmental Law: Water Quality
Because the United States Environmental
Protection
Agency (USEPA)
has approved the
Illinois
National
Pollutant Discharge Elimination System (NPDES) permit
program as complying with
the Federal Water Pollution
Control Act (Clean Water
Act),
challenges to
the
issuance
by the Illinois
Environmental Protection
Agency
(IEPA) of an NPDES permit must be evaluated
solely
on the basis of applicable provisions of the Illinois
Environmental Protection Act and state regulations.
To
the extent
that
a challengerbelieves
that
the Illinois
NPDES
permit program does not conform to the
applicable provisions of the Clean Water Act,
it
may
challenge the USEPA approval of the Illinois program.
Environmental Law: Water Quality
See
IlL Admin.
Code
lit.
35,
§
309.119(2002).
Administrative Law: Agency
Rulemaking: Rule
Application & Interpretation
In general, administrative agencies are required to apply
their rules
as
written,
without
making ad hoc exceptions
in adjudications ofparticular cases.
Administrative
Law: Separation & Delegation ofPower:
Legislative
Controls
Agencies only have the power given to them through
enabling
legislation.
Environmental
Law:
Water Quality
Section
39
ofthe Illinois Environmental Protection
Act,
415
IlL Comp. Slat Ann. 5/39(a)
(West
2000), explicitly
provides that in
granting
National Pollutant Discharge
Elimination System permits, the Illinois
Environmental
Protection Agency may impose such conditions as may
be necessary to accomplish the purposes of that Act, and
as are not inconsistent
with
the regulations promulgated
by the Illinois Pollution Control Board thereunder.
Environmental
Law: Water Quality
Administrative
Law: Agency Rulemaking: State
Proceedings
Any
person may submit a regulatory proposal
for the
adoption,
amendment,
or repeal of a regulation.
415
Ill.
Comp.
Stat. Ann. 5/27
(West 2000);
IlL Ad~nin.Code
tit.
35,
§
102.200(2002).
Civil
Procedure: Justiciability: Mootness
When an opinion on a
question
oflaw cannot affect the
result as
to the parties or controversy
in thecase before
it,
acourt should
not resolve the question merely forthe
sake of setting a precedent to govern potential future
cases. However,
in certain, rare cases, a
moot issue may
be considered where
the
magnitude
or
immediacy ofthe
interests involved
warrants action by the court
or where
the issue is likely to recur but
unlikely to last long
enough to allow appellate review to
take place because
of the intrinsically short-lived
nature of the
controversies.
Civil
Procedure: Appeals: Briefs
Civil
Procedure: Appeals: Records on Appeal
It is a rudimentary nile of appellate practice that an
appellant may
not
make a point
merely by stating
it
without presenting any argument in support. Failure to
cite to relevant authority forfeits an issue on appeal.
Strict adherence
to the requirement of citing relevant
3
pages of the record is necessary to expedite
and facilitate
the administration ofjustice.
COUNSEL:
For
Prairie Rivers
Network,
Petitioner/Appellant: Albert Ettinger, Environmental
Law
& Policy Center,
Chicago, IL. ARGUER: For
Appellant: Albert Ettinger.
For Pollution Control Board, RELATED NAME:
Environmental Protection Agency,
RespondentlAppellee: Honorable James
E. Ryan,
Attorney
General State of
Illinois, Chicago,
IL,
Joel D.
Bertodchi, Solicitor General, Chicago,
IL, Diane M.
Potts,
Assistant Attorney General,
Chicago, IL.
ARGUER: For Appellee: Diane
M. Potts.
For Black Beauty Coal Company, Respondent/Appellee:
W. C.
Blanton, Blackwell Sanders Peper Martin
LLP,
Kansas City, MO.
For Vermilion Coal Company,
Amicus Curiae: Fred
L.
Hubbard, Attorney
at Law,
Danville, IL.
For Ill. Environmental Regulatory
Group. Amicus
Curiae: Thomas G.
Safley,
Hodge Dwyer Zeman,
Springfield, IL, Cassandra I. Karimi,Hodge Dwyer
Zeman,
Springfield,
IL,
Robert A. Messina, Ill.
Environmental
Regulatory Group, Springfield, IL.
JUDGES:
JUSTICE ROBERT J.
STEIGMANN
delivered
the opinion of the court. Honorable*2
John T.
McCullough,
S.
-
CONCUR,
Honorable John W.
Turner,
J.
- CONCUR.
OPINIONBY: Robert J.
Steigmann
OPINION: JUSTICE STEIGMANN delivered the
opinion of the
court:
In December 2000, respondent,
the
Illinois
Environmental Protection Agency
(IEPA or agency),
issued a final National Pollutant Discharge Elimination
System (NPDES)
permit to respondent Black
Beauty
Coal Company (Black Beauty).
In January 2001,
petitioner,
Prairie Rivers
Network
(
Prairie
Rivers)
,
a
river conservation group, filed a petition with
respondent,
the Illinois Pollution Control Board (Board),
requesting that the
Board set aside
the
final NPDES
permit issued to Black Beauty. In August 2001, the
Board denied
Prairie
Rivers’
petition
and affirmed
the
IEPA’s
issuance of the
final permit.
Prairie
Rivers
appeals, arguing that the Board erred
by denying
Prairie
Rivers’
petition because (1) the
IEPA
failed to provide it with a meaningful opportunity
to participate in the
fmal NPDES permit-writing process;
(2) the
final
permit did
not
include certain required
conditions; and (3) the
IEPA
improperly relied
on
documents producedby Black Beauty after the public
comment period.
We
affirm.
I. BACKGROUND
Vermilion Grove Mine
is*3
a new coal
mine
located
a few miles southeast of Georgetown, Illinois. Black
Beauty leases
the Vermilion Grove Mine from Vermilion
Coal.
In May 2000, the
IEPA received Black Beauty’s
“Application for Surface Coal Mining and Reclamation
Operations Permit,” in which Black Beauty sought
an
NPDES
permit
todischarge groundwater and storm
water into an unnamed tributary
of the Little
Vermilion
River. Black Beauty’s plans showed that
it
intended to
(1)
drill a hole
in the ground to establish the
mine
entrance,
(2) create
air shafts
for ventilation, (3) establish
sediment basins to control drainage
in
the disturbed
areas, and
(4) build apreparation plant,
a rail loop and
load-out facility, and an office building. According to the
plan, the coal would be
moved by
conveyors
from the
underground
mine to
a processing area, where it would
be cleaned,
screened, and crushed. All storm water
runofffrom the mine
would be collected into three
connected basins (designated as
“003,”
“003A,” and
“003B”).
In the event that the basin system reached its
capacity due to heavy rainfall,
the
water that could not be
held in the basins would be diverted through
a
discharge
point (outfall 003) into
the unnamed*43
tributary.
On August
4, 2000, the
IEPA
issued a public notice,
pursuant to
section
309.109 of Title 35 of the Illinois
Adminislrative Code
(Code)
(35 IlL Adm.
Code
§
309.109
(Conway Greene CD-ROM June
2002)), that
after reviewing Black Beauty’s application, the agency
had tentatively decided
to issue Black Beauty an
NPDES
permit. The public
notice also
included a copy of the
draftNPDES permit.
Although the United States Environmental Protection
Agency (US EPA) has generally waived its right to
review NPDES
permits
issued by the
IEPA to coal mine
operators, on August 29, 2000, the US EPA exercised
its
preemptive rightsunder section
123.44
(a) (1) of the
Code
of Federal Regulations (40 C.F.R.
§
123.44(a) (I)
(2000)) and requested
90 days to review
the draftpermit.
Based on the degree of public interest in its
tentative
decision, the IEPA
determined that a public hearing was
required under section
309.115 of Title
35
of the
Code
35 IlL Adm.
Code
§
309.115
(Conway Greene CD-ROM
June 2002)).
On September 20,
2000,
the agency and the
Illinois
Department of Natural Resources conducted~5
a public meeting
at Georgetown-Ridge Farm High
School to inform the public about the proposed permit
and prepare those citizens who planned on participating
4
in the
subsequent public hearing.
On September 27,
2000, a public
hearing on
the
draftpermit
was held
at the
Georgetown-Ridge Farm High School.
Prairie
Rivers
attended and participated
in
both the public
meeting and
the hearing.
On October
6, 2000,
in response to concerns raised at
the public hearing and other comments on the draft
permit,
an IEPA employee asked Black Beauty
to
provide the agency with additional information regarding
the permit.
In
response, Black Beauty hired a consultant,
Advent Group, Inc. (Advent), to perform a study and
prepari a
report.
On October
20,
2000, Advent issued
its
report,
in which Advenfs scientists concluded that the
anticipated infrequent discharge
through
outfall
003,
which would only occur during significant rainfall,
would not harm the environment.
The public comment period on
the IEPA’s tentative
decision closed on October 27, 2000.
During the public
comment period, several agencies and groups submitted
comments regarding the IEPA’s tentative decision and
suggested changes to the draft*6
NPDES permit.
On
October 27, 2000,
Prairie Rivers
submitted comments
that criticized the draft permit and advocated for
stringent monitoring conditions.
On October 30, 2000, the
US EPA objected to the draft
NPDES permit. The IEPA
considered all input and
suggested changes to the
draft permit, discussed and
reached a consensus with the US EPA, and developed
a
final NPDES permit. On December 22, 2000,
the US
EPA withdrew
its
objection to
the draft permit
and
approved the final
permit. On December 27,
2000,
the
IEPA issued the final
permit
and issued a public notice
of its decision and aresponsive
summary, which
addressed all concerns raised by citizens and
organizations,
including
Prairie Rivers
and the US EPA.
The final NPDES permit issued
to
Black Beauty
was
generally
more restrictive and
contained more conditions
than
the
draft permit.
In
particular,
the
final permit
included
the following changes:
(1) the effluent
limitation for sulfate was reduced to a more restrictive
level (1,000
milligrams per liter,
as compared to the
previous
3,500
milligrams
per
liter); (2) the potential for
Slack Beauty to avoid sulfate and chloride
monitoring
was
eliminated; (3) discharge monitoring
requirements7
were
increased
from one sample per
storm water discharge event (with a total requirement of
three perquarter),
to
daily
monitoring of all storm water
discharge events;
(4)
all references to mine discharges
being exempt from water quality
standards
were
removed; (5) additional sedimentation pond operation
and maintenance restrictions were included; and (6)
biological inventory and water quality monitoring of the
Little Vermilion River and the
unnamed tributary
were
added.
In January 2001,
Prairie
Rivers
filed a petition with
the Board, requesting that the Board set aside the final
NPDES permit issued to Black Beauty. In
that
petition,
Prairie Rivers
alleged the
following: (1) during
the
September 27, 2000, public hearing and during the
public comment period,
Prairie Rivers
and its
members
identified legal and scientific flaws in the
draft NPDES
permit;
(2)
the fmalpermit contained “certain conditions
and limits that were not contained in the draft permit that
was subject
to public review”; (3)
the
final permit
contained
“most of the
defects
that were identified by
Prairie Rivers
in the
draft permit”; (4) the final permit
contained ambiguous provisions regarding monitoring
and’8
no operation planwas
set forth regarding how
provisions related to precipitation events
would be
implemented
or enforced;
(5) a proper antidegradation
analysis had not been completed; and (6)
Prairie
Rivers’
members “will be affected adversely when
pollution discharged under the pennit injures the ecology
of the Little Vermilion watershed as a result of the
IEPA’s
failure to require
protective effluent limits,
monitoring, antidegradation analysis and mixing zone
delineation.”
In May
2001,
the
Board conducted a hearing, at which
the parties introduced evidence
and presented
oral
argument. In addition, members of the public provided
comments both during
and
after the hearing. Following
the hearing,
the
parties submitted written briefs.
In
August 2001, the Board denied
Prairie
Rivers’
petition
and affirmed the IEPA’s
issuance of the final
NPDES
permit
to Black Beauty.
In September 2001,
Prairie Rivers
filed a notice of
appeal.
This court has
allowed the
Illinois Environmental
Regulatory Group and the
Vennilion
Coal Company to
file briefs as
amici curiae.
II. ANALYSIS
A.
TheIllinois
NPDES Permit Program
“The history and goals of the Federal Water Pollution
Control Actt9
(Clean
Water Act)
and
its amendments
have been
chronicled in numerous judicial opinions. See,
e.g.,
American Frozen Food Inst
v.
Train,
176 U.S.
App.
D.C.
/05,
1/1-22,
539 F.2d107,
113-24 (1976);
California
v. EPA,
511
F.2d 963 (9th
Cir.
/975).
Congress’
ultimate
objective
was ‘to restore
and maintain
the chemical, physical,
and
biological integrity of the
Nation’s waters,’
(‘33
U.S.C.
§
1251(a)
(1976)),
and it
established apermit program, the NPDES, to achieve
this goal. Under this program, any pollutant
discharge
5
into navigable waters without
a
US
EPA authorization
permit
is banned, and the
US
EPA was instructed to
make the pollution controls inherent in its permits
increasingly stringent over time.
Although the administration and enforcement of the
permit program initially was
vested
entirely in the
US
EPA, Congress
intended
that
much of this authority
would devolve to the states.
33
U.S.C.
§
1251(b)
(Supp.
I
1977).
The Clean Water Act stipulates that any time
afterthe promulgationof US
EPA guidelines
establishing the
minimumelements of state permit
programs, a state
*
l0may
submit
a description of a
proposed program,
along with a statement from the
state
attorneygeneral that state
law provides adequate
authority
to carry out the program, for evaluation by
the
Administrator of the
US
EPA.
If the state program
satisfies the statutory requirements of section 402
(b),
33
U.S.C.
§
1342(b),
and the guidelines issued
under section
304(i),
33
U.S.C.
§
1314(i),
the Administrator must
approve the
program. The state
would then assume
primary responsibility for the
issuance of
permits and for
the administration and enforcement of the NPDES
program within
its jurisdiction.”
Citizens for a
Better
Environment v. Environmental Protection Agency,
596
F.2d
720,
721-22 (7th
Cir.
1979).
In October
1977, the
US EPAadministrator approved
Illinois’s proposal to administer the NPDES program
within Illinois.
In
Citizens for a Better Environment,
596
F. 2d at 724,
the
Seventh CircuitCourt of Appeals
invalidated the
administrator’s approval ofthe Illinois
NPDES permit program,
on the
ground that the US EPA
had failed to promulgate regulations providing for public
participation
in*
I I
state
enforcement actions. In
response, the US EPA promulgated such a regulation (40
C.F.R.
§
123.27(d)
(2000)),
and Illinois later agreed to
abide by it. In April
1981, the US EPA approved the
revision to Illinois’s NPDES program (46
Fed.
Reg.
24295-02 (1981)).
Subpart A of
part
309 ofTitle
35
of the Code, which
was
enacted by the Board (see
In re NPDES Regulations,
14
PCB 661
(Ill.
Pollution Control Board, December
5,
1974)),
specifies that the
IEPA
must issue NPDES
permits
using
the
following procedures. See
415 ILCS
5/13(b)(1)
(West 2000) (“the Board shall adopt
‘““‘
requirements, standards, and procedures which
*~ are
necessary or appropriate to enable the
State of Illinois to
implement and participate
in the
NPDESJ”).
First,
a
party seeking an NPDES permit must file an application
with the
IEPA
(35 IlL Adm.
Codes 309.103
(Conway
Greene CD-ROM June 2002)). Ifthe
application is
complete, the IEPA prepares a tentative determination
regarding the application,
and if
the agency
intends to
issue
the permit,
prepares a
draft
permit
(
35
IlL Adm.
Code~309.108(2000)).
*12
Second, the IEPA must issue
a public
notice of the
permit
application and the
agency’s tentative
determination to issue or deny the permit
(
35
IlL
Adm.
Code
§
309.109
(Conway Greene CD-ROM June 2002)).
This notice must provide for a period of not less than 30
days for persons to submit public comments
on the
agency’s
tentative determination and, where applicable,
on
the
draft
permit.
See
35/iL Adm. Code~309.109(b)
(Conway Greene CD-ROM June 2002)
(“All comments
shallbe submitted to the agency and to the applicant”
and
“shall be retained by
the agency
and considered in
the formulation of its
final determinations with respect
to
the
NPDES application”). The IEPA also
must provide
notice of the permit application to other governmental
agencies
(35 IlL Adm.
Code,ç
309.114
(Conway
Greene
CD-ROM
June
2002)).
Third, if the
LEPA determines that
“there existsa
significant degree ofpublic
interest in the proposed
permit,”
the agency
“shall hold a public hearingon the
issuance or denial” of the permit (
35 IlL Adm. Code
§
309.1/5(a)
(Conway Greene CD~ROM*13
June
2002)).
“Following the public hearing, the agency may
make such
modifications
in the
terms and conditions of
proposed permits
as may be appropriate.” (Emphasis
added.)
35 IlL Adm. Code
§
309.119
(Conway Greene
CD-ROM
June 2002). The IEPA must “transmit to the
regional administrator of
the US EPA
for his approval a
copy of the permit proposed to be issued unless the
regional administrator has waived his right to receiveand
review permits of its class.”
35
IlL Adm. Code
§
309.1/9
(Conway Greene CD-ROM June 2002). The IEPA also
must
“provide a notice of such transmission to the applicant,
to
any person who participates in the public hearing, to any
person
who requested apublic hearing, and to
appropriate persons on
the mailing list established under
sections
309.109 through
309.112.
Such
notice shall
briefly indicate any significant changes which were made
from terms and conditions set
forth in the draft
permit.”
(Emphasis added.)
35 IlL Adm. Code
§
309.1/9
(Conway
Greene CD-ROM June 2002).
In
addition,
the IEPA
must issue a responsiveness
summary,
*
14
addressing
comments made during the
public
hearing.
35 Ill. Adm.
Code
§
/66.192
(Conway
Greene CD-ROM June 2002).
If the
IEPA does not hold a public hearingafter the
close of the
comment
period,
the agency must, “after
evaluation of any comments which
may havebeen
6
received, either issue or deny the permit.”
35 IlL
Adm.
Code
§
309.112
(Conway Greene CD-ROM June 2002).
B.
Standard of Review
The
issues raised on appeal relate to the interpretation
of statutes and administrative rules.
“In cases
involving the interpretation of a statute by an
agency charged with administering
it,
the agency’s
interpretation is afforded considerable deference, but
it
is
not binding on the court and will be rejectedif
erroneous.
Citation.
The cardinal rule of statutory construction
is
to ascertain and give effect to the intent of the legislature.
Citations.
The words ofa statute
are given their plain
and commonly understood meanings. Citation.
Only
when the
meaning of
the
enactment is
unclear from the
statutory
language
will the court look beyond the
language and resort to aids for construction.”
R.L. Polk&
Lb.
v. Ryan, 296 IlL App.
3d lIZ
/39-40, 694 N.E.2d
/027,
/033,
230 IlL Dec.
749 (1998).*l5
See
also
Gem Electronics ofMonmouth, Inc.
v.
Department ofRevenue,
183 IlL 2d 470,
475,
702 N.E.2d
529,
532,
234 IlL Dec.
189 (1998)
(“A court should not
depart from the language ofthe statute by reading into
it
exceptions,
limitations,1
or conditions that conflict with
the
intentof the legislature”).
C.
Burden of Proof in
a Third-Party Appeal before the
Board
Prairie Rivers
first argues that the Board misapplied
the burden of
proof.
Prairie
Rivers
concedesthat the
Board properly considered the burden ofproofto lie with
Prairie Rivers
on
substantive
matters; however,
Prairie
Rivers
claims
that
to the extent the Board held it to that
standard regarding
its
procedural claims,
the Board erred.
We
conclude that the Board properly
determined that
Prairie Rivers
had the burden ofproof in
its third-party
appeal before the Board.
Section 40(e) ofthe
Illinois Environmental Protection
Act (Act)
provides, in
pertinent part,
as follows:
“(1) If the agency grants or denies a
permit
under
subsection (b) of section
39 of this Act, athird
party,
other than the
permit
applicant or agency, may
petition
the Board within 35
days from the
date
ofissuanceI6
of
the agency’s decision, for a hearing to
contest the
decision of the agency.
S..
(3) Ifthe Board determines that the petition is
not
duplicitous or frivolous
and
contains asatisfactory
demonstration
under subdivision (2) ofthis subsection,
the
Board
shall
hear the petition
(i) in accordance with
the
terms
ofsubsection (a) of this section
and its
procedural
rules governing
permit
denial appeals and
(ii)
exclusively on
the basis of the record before the agency.
The burden of proofshall be on the petitioner. The
agency
and
permit applicant shall be named
corespondents.”
(Emphasis added.)
415 ILCS S/40(e)
(West 2000).
As earlier discussed, the cardinal rule of statutory
construction is to ascertain and give effect to the
legislature’s intent. The best evidence of legislative intent
is the statutory language itself,
which must be given its
plain and ordinarymeaning. In construing a statute, a
court is not atliberty to
depart from the plain language of
the statute by reading into
it exceptions,
limitations,
or
conditions that the legislature did not express.
Lulay v.
Lulay,
193 IlL 2d 455,
466,
739 N.E.2d 521,
527, 250 Iii.
Dec.
758 (2000).
~
17
Section 40(e)(3) of the Act clearly provides that
in a
third-party
appeal, the burden of prooflies with the
petitioner
--in this
case,
Prairie Rivers.
When a
petitioner in apermit appeal is the permit applicant,
the
petitioner
has
the burden ofproving that the requested
permit would not violate the Act or the Board’s
regulations.
Browning-Ferris Industries
ofillinois, Inc.
v. Pollution
Control Board,
179 IlL App.
3d 598,
601,
534
N.E.2d 616, 619,
128 IlL Dec.
434
(1989).
The scope
of thisburden does not change when the petitioner
is a
third party challenging the issuance of a permit. Thus, a
third-party
petitioner must show
that the
permit,
as
issued, would violate the Act or the Board’s regulations.
See Damron v. Illinois
Environmental Protection
Agency, Illinois Pollution Control Bd.
Op.
93-2 15
(April
21, 1994) (construing
Board regulations and holding
that
when a
third party
challenges the issuance of a
permit,
it
must show
that the
permit,
as issued, would violate the
Act or applicable regulations).
Prairie Rivers
acknowledges that
in connection with
its
procedural objections to the NPDES
permit,
the Board
had to
determine
whether the IEPA complied5
18
with
applicable procedural statutes
and regulations in issuing
the permit. However,
Prairie
Rivers
then suggests
that
the Board’s determination
that
“
Prairie Rivers
had
the
burden of proving
that
the
permit, as issued, would
violate the
Act
or
Board regulations” (emphasis in
original) raises a question as to whether the Board
analyzed its procedural
objections on some basis other
than whether the record “showed
that the proper
procedures were used in issuing the permit.”
We are not
persuaded.
7
We
agree
with
Black Beauty that in
the context of a
procedural challenge to the
IEPA’s issuance of a
permit,
Prairie
Rivers
has offered no plausible interpretation of
the phrase
“that the permit, as issued,
would violate the
Act or Board regulations” other than “was issued in
violation
ofthe applicable procedural statutory and
regulatory provisions.”
In addition, the
record belies
Prairie Rivers’
suggestion that the Board analyzed its
procedural objections on some basis
other than whether
the
JEPA issued the permit in violation of applicable
procedural statutory and regulatory provisions.
In
rejecting
Prairie Rivers’
procedural challenge, the
Board
stated; in pertinent part, as
follows: ~l9
“Illinoishas specific regulations setting forth
the
procedures the
IEPA
must follow in issuing an NPDES
permit.
See
35 IlL Adm.
Code ~309.
108,
309.109,
309.115, and 309.119.
The
IEPA
complied with these
procedures.
Prairie
Rivers’
arguments that
the
IEPA
should
have provided additional opportunities pursuant
to
US
EPA
guidelines andthe
Clean
Water Act
are
notpersuasive, because these federal procedures are
inapplicable here.”
D.
Prairie Rivers’
Claim That It
Was Denied a
Meaningful Opportunity To Participate
in the
Final
Permit-Writing Process
Prairie Rivers
next argues that the Board erred by
denying
Prairie
Rivers’
petition because the IEPA
failed to provide it with a meaningful opportunity to
participate in the
fmal permit-writing process.
Specifically,
Prairie Rivers
contends that, instead of
issuing a
final NPDES pennit in response to conunents
the
IEPA
received on the
original draftpermit,
the IEPA
should have issued a second draft permit and provided
Prairie Rivers
and
interested citizens an opportunity to
comment upon the changes that had been
made
to the
original
draft permit.
Prairie
Rivers
claims~20
that the
IEPA’s failure to submit
the
“drastically revised permit”
to a another round of public comment contravened (1)
the public
participation requirement of the
Clean Water
Act
(33
U.S.C.
§
1251
et seq. (2000)); (2) Illinois case
law; and (3) article XI of the Illinois Constitution (Ill.
Const.
1970,
art.
XI).
Prairie
Rivers
also claims
that
because the
“Board permitting rules of
part
309
of
Title
35 of the
Code
do not attempt to delineate every
possible scenario,” the IEPA should be required to hold a
second round of public comment when the
final permit
“substantially deviates” from the draftpermit.
We
disagree.
I. The Clean Water Act
Prairie Rivers
first
contends
that the
IEPA’s
failure to
submit the “drastically revised”
fmal permit to a another
round of public comment contravened the public
participation requirement of
the Clean Water Act
(33
U.S.C.
§
1251
et seq. (2000)). We disagree.
Illinois administers
the federal NPDES permit
program
in this state, pursuant to section
1342(b) of the
Clean
Water Act
(33
U.S.C.
§
1342(b)
(2000)), and, as earlier
noted, it has
done so since
the US2l1
EPA first
approved the Illinois NPDES program in October
1977.
However, that does not
mean that either the
IEPA or the
Board directly administers the
Clean Water Act in
Illinois. Instead, it means only that Illinois has
demonstrated to
the US EPA’s satisfaction
that the
Illinois NPDES program
satisfies
the statutory
requirements of the Clean Water Act (see
33
U.S.C.
§
1342(b)
(2000)) and the guidelines
issued thereunder
(see
33
U.S.C
§
1314(i)
(2000)). See
Citizensfora
Better Environment,
596 F.2d at 722
(after the
US EPA
approves a state’s NPDES permit program, the state then
assumes
“primary responsibility for the
issuance of
permits
and for the administration and
enforcement of
the NPDES programwithin
its jurisdiction”).
Pursuant to section
1342(b)(3) of the Clean Water Act,
any state
desiring to administer its own NPDES permit
program must demonstrate that
it has adequate authority
“to
insure that
the public receives
notice ofeach
application for a
permit
and to provide an opportunity for
public
hearing
before a ruling on each such application.”
33
U.S.C.
§
1342(b)
(3) (2000). ~22
This public
participation
requirement for
draft permits is specifically
set
forth
in sections
124.6
and
124.10 through
124.12 of
the
federal regulations.40
C.F.R.
§~
124.6,
124.10,
124.11,
124.12(2000). Notably
absent from the Clean
Water Act’s requirements
for state
NPDES programs is
any
requirement that
suchprograms include provisions
for the
reopening of the public comment period or the
preparation of a new draft permit based on
information
submitted
during the
initial comment period. While
section
124.14(b) of the Code of Federal Regulations
authorizes a US
EPA
regional administrator to provide
additional public participation under certain
circumstances
in connection with federal NPDES permit
application processing (40 C.F.R.
§
124.14(b) (2000)),
state NPDES programs do nothave tobe administered in
accordance with that section
(see 40 C.F.R.
§
123.25
(2000)).
The federal mandate for public participation in
the
application process, in turn,
is incorporated into the
Illinois NPDES program in sections 309.109,309.113,
309.115, 309.116, and
309.117 of Title 35
of the Code
35 IlL Adm.
Code ff309109,
309.113,309.115,
309.116,
309.117 (Conway
523Greene
CD-ROM June
2002)).
Because the US EPA has approved the Illinois NPDES
permit program as
complying
with the Clean Water Act,
8
Prairie Rivers’
challenges to the IEPA’s issuance of the
NPDES permit to Black Beauty must
be
evaluated
solely
on the basis
of applicable provisions of the Act and state
regulations.
To the extent that
Prairie Rivers
believes
that the Illinois NPDES permit
program does not
conformto the applicable
provisions of the
Clean Water
Act,
Prairie Rivers
may
challenge the US EPA’s
approval ofIllinois’s program.
See,
e.g.,
Hall v.
United
States Environmental Protection Agency, 273 F.3d 1146
(2001)
(in
which an individual challenged the
US EPA’s
approval of
a revision to a county’s air quality plan);
Citizensfor a Better Environment,
596 F.2d at
722
(in
whichi public interest group challenged the US
EPA’s
approval of the
Illinois NPDES program).
2. Illinois Case Law
Prairie
Rivers
next contends
that
the Fifth
District
Appellate Court’s decision in
Village ofSauget v.
Pollution Control Board,
207 IlL App.
3d 974,
566
N.E.2d
724,
152 IlL Dec. 847
(1990),
“requires
that the
permit
be remanded to the
agency. 24)
“Specifically,
Prairie Rivers
relies on Sauget to support
its contention
that
the IEPA should have submitted the “drastically
revised
permit”
to another round ofpublic comment. We
disagree.
In Sauget, the Village ofSauget
(Sauget) applied for an
NPDES permit
for one of
its wastewatertreatment
facilities (AD facility).
In response
to the application,
the
IEPA prepared a
draft permit
covering the AD
facility
and another facility, the P/C
plant.
The US EPAthen
infonned the IEPA that
the US
EPA wished to comment
on the
draftpermit.
The US
EPA later
untimely
commented on the
draftpermit
in threeletters to the
IEPA,
but did not
provide those letters to Sauget.
In
addition, the IEPA did not provide Saugetthe US EPA’s
final letter until
about one month
after
the IEPA had
received
it.
Less
than two
weeks
later, the IEPA issued
two
fmal permits
to Sauget,
one for each facility.
Sauget.
207111
App. 3dat 976,
566 N.E.2d at
726.
Sauget and Monsanto Company (Monsanto), whose
plant was a major industrial facility served
by
the AD
facility, appealed
the
terms
of
both fmal pennitsto the
Board.
The Board determined that
the P/C
permit
was
void, andwith regard
*25to
the AD facility permit,
“struck some of the contested conditions, affirmed
others, andordered the remainder to be modified.”
Sauget, 207
IlL
App. 3dat 977, 566 N.E.2dat 726.
Sauget and Monsanto then appealed the
Board’s
ruling to
the
Fifth
District Appellate Court.
Sauget, 207 IlL App.
3dat976-77, 566 N.E.2dat 726.
On appeal, the
Fifth District concluded that the US
EPA’s
comments
were
untimely and
the US EPA
improperly failed to provide its
comments
on the draft
permit
to the applicant, Sauget, in violation of section
309.109(b) ofTitle
35 ofthe Code
(35111 Adm. Code
§
309.109(b)
(Conway Greene CD-ROM June 2002)),
stating as
follows:
“Section
309.109(b)
of Title
35
of
the Code
states
that comments submitted on
tentative determinations
shall be
submitted to the
IEPA
and
to
the applicant.
Citation.
The US
EPA has
never submitted
its
comments to Sauget. Appellees do not contest Sauget’s
statement that Sauget first received a copy of the
US
EPA’s
final comment letter of
February
14,
1986, on
March
10,
1986, when the IEPA provided Sauget with a
copy.
Monsanto
claims
that
the late notice t26of
the
US
EPA’S comments effectively denied anyone an
opportunity to respond to
the additional permit
conditions,
particularly
when the final NPDES permit,
including the USI
EPA’S additional conditions,
was
issued March 21,
1986, only
11
days
after Sauget
received a
copy of the
US
EPA’s
fmal
comment letter.
Had the
US
EPA timely submitted
its comments
on
the
draft permit, and provided the appellants with notice
ofthe same, a prepermit issuance hearing could have
been requested. Citations.
We recognize that a hearing
pursuant to these regulations is discretionary with the
IEPA, yet
under
the circumstances appellants were
denied the
opportunity
to request
that the IEPA
exert
such discretion. ~
More significant with regard to the issue atbar are the
requirements of section
309.108.
Citation.
That section
provides inpart that ifthe
IEPA’s tentative determination
is to
issue
the NPDES permit,
that determination
should
at least
include:
(3)
A
brief description of
any
other proposed special
conditions which will
have a significant impactupon the
discharge.
(c) A statement of the basis for each of the permit
conditions listed *27in
section
308.108(b).”
(Emphases in original.)
Sauget, 207
IlL
App. 3d at 980-
81,
566
N.E.2dat
728-29.
Contrary to
Prairie Rivers’
contention, Sauget is
inapposite. That case considered (1) the failure ofan
entity that
submitted comments regarding
a draft permit
and
the
IEPA
to provide
those comments to
a permit
applicant,
as required by
section 309.109(b) of Title
35
9
of the
Code
(35/IL Adm. Codeç 309.109(b)
(Conway
Greene
CD-ROM June 2002)); and (2) the IEPA’s
resulting
failure to include
in the public
notice of its
tentative determination certain proposed conditions. The
Sauget court did
not addresswhether the IEPA must
reopen the public comment period whenever
it makes
significant changes to a draft
permit. Accordingly,
the
Fifth District’s decision in Sauget does not,
as
Prairie
Rivers
claims, “require
that the permit” issued
to Black
Beauty
“be remanded
to the agency.”
3. Article Xl
of the
Illinois Constitution
Although not set
forth in a separate argument section,
Prairie Rivers
contends,
in conclusory fashion, that (1)
its right
to meaningflully participate in the NPDES permit
process is*28
“also supported by article XI of the
Illinois Constitution”; and (2) article Xl
“gives
persons
seeking clean
water at least as
much right to participate
as those
seeking
permits
to pollute”
(see
Ill. Const.
1970,
art. XI). We disagree.
In
Landfill,
Inc.
v. Pollution Control
Board,
74 IlL
2d
541, 559, 387 N.E.2d 258,265,25111.
Dec.
602 (1978),
our supreme court rejected a
party’s
argument that the
IEPA’s issuance of a landfill
permit
impinged on
the
third-party intervenors’ constitutional right toa healthful
environment under article XI of the
Illinois Constitution
(Ill. Const.
1970,
art.
XI). In so concluding, the court
reasoned
that the
“constitutional argument was
without
merit
in light of the
statutorily established mechanism for
persons not directly involved
in the
permit-application
process toprotect their interests.”
Landfill,
Inc.,
74 Ill.
2d
at 559, 387
N.E.2dat 265.
Similarly,
inthis case,
Prairie
Rivers’
constitutional argument lacks merit in light of
part 309 of Title 35
of the
Code, which establishes a
procedure forthe public to participate in the issuance
of
NPDES permits.
4. Regulations Under Section 309, Title*29
35, ofthe
Code
Last,
Prairie Rivers
does not dispute that the IEPA
complied with the applicable
state regulations in issuing
the NPDES permit
to Black Beauty. As we earlier
discussed, section 309 ofTitle 35
of the Code
authorizes
the
IEPA to make “significant changes” in a draft permit
after public
comment. See
35 IlL Adm.
Code
§
309.119
(Conway Greene CD-ROM June 2002) (“following the
public
hearing, the agency
may make such modifications
in the
terms and conditionsof proposed permits as
may
be
appropriate,” and when
the IEPA transmits
a final
permit to the US
EPA for review, the agency
must notify
the applicant andother interested parties
of “any
significant changes which were made from terms and
conditions set
forth
in
the draft permit”). Nonetheless,
Prairie Rivers
contends that because the
“Board
permitting rules ofpart
309 of
Title
35
of the Code
do
not attempt
to
delineate
every possible scenario,”
the
IEPA
should be required to hold a second round of
public comment when
the
fmal permit “substantially
deviates”
from the draft permit. We disagree.
In general, “administrative agencies are required to
apply their rules
as written, *30
without making ad hoc
exceptions
in
adjudications ofparticular cases.”
Panhandle Eastern
Pipe Line Co.
v. Environmental
Protection Agency, 314 IlL App.
3d 296,
303,
734
N.E.
2d
18,
23-24, 248 IlL
Dec.
3/0 (2000).
Prairie Rivers
cites
no
authority for its
claims
that (I) the applicable
regulations
merely
establish
a
floor for
NPDES
permitting procedures;
and(2) the IEPA has inherent
authority to afford the public
whatever additional
opportunities for participation the
agency may see fit.
Instead,
as the Board and the IEPA point out,
agencies
only have the
power given to them through
enabling
legislation
(
Granite
City Division ofNational Steel
Co.
v. Illinois Pollution
Control Board,
/55 IlL 2d 149,
/71,
613 N.E.2d
719,
729,
/84 IlL
Dec.
402 (1993)),
and
section 39 ofthe Act explicitlyprovides that in granting
permits, the
IEPA
“may
impose such conditions as may
be necessary to accomplish the
purposes of this Act, and
as
are not inconsistent with the
regulations promulgated
by the
Board hereunder”
(
415 ILCS 5/39 (a)
(West
2000)). See
also
415
ILCS 5/39(’b)
(West
1998) (the
IEPA may adopt3
1
“filing requirements
and
procedures” forNPDES permit applications, which must
be “consistent with the Act or regulations adopted by
the
Board”);
Peabody Coal Co.
v. Pollution
Control Board,
36 IlL App. 3d 5,
20,
344 N.E.2d 279,
290 (1976)
(holding that the Board does
not have authority to
delegate its NPDES rule-makingresponsibility to the
IEPA).
Accordingly, we conclude that the IEPA was not
required to issue a second
draft
permit
and reopen the
public comment period in direct contravention of
applicable regulations.
In so concluding,
we note
that
Prairie
Rivers
makes
several policy-related arguments in support of its
contention that when the fmal permit is a “drastically
revised” version of the draft permit,
the IEPA should
issue a second draft permit and provide the
public an
opportunity
to comment on the
revisedpermit.
In
particular,
Prairie Rivers
asserts the following: (I)
if the
public is never allowed a second round ofpublic
comment, it “would eviscerate the public’s right to
participate inthe NPDES permitting procedure so
severely that Illinois
could not
maintain its
NPDES
program”; (2) when “additional comments should be
allowed is a matter ofjudgment32
that requires
gauging whether the revisions raise issues or questions
that were not sufficiently aired
in the comments on the
10
initial draft permit”; (3)
even after a permit
is revisedto
benefit certain parties, “serious questions may remain
regarding the
permit
and the sufficiency or efficacy of
the revisions”; and (4) the ability ofa third
party to
appeal the
issuance of a permit “does not replace the
important
benefits
that can be
gained from additional
comments.” Whatever merit these assertions
may
possess, the
appellate court is not the
forum to
which
they should
be addressed. Instead,
Prairie Rivers
should
address
its
proposed
change
in the regulations to the
Board. See
415 ILCS
5/27(West 2000);
35 IlL Adm.
Code
§
/02.200
(Conway Greene CD-ROM June 2002)
(“any ‘person may submit aregulatory proposal for the
adoption, amendment,
or repeal of a regulation”).
E.
Prairie Rivers’
Claim That the
Final
Permit
Did Not
Include Certain Required Conditions
Prairie Rivers
next argues
that
the IEPA failed to
include in the fmal
NPDES permit certain monitoring
conditions required by the Clean WaterAct and state
regulations.*33
Specifically,
Prairie Rivers
contends
that the fmal permit improperly allowedBlack Beauty to
develop and submit the following items
afterthe fmal
permit was issued: (I) a
biological inventory of the Little
Vermilion River around the mine site;
and (2) an
operational plan to assure compliance
with the condition
set
forth in the
final permit that Black Beauty may
discharge
storm and groundwater only when there is a
three-to-one ratio between the unnamed tributary
flow
and the
discharge flow.
We
conclude
that
this
issue
is
moot.
At the time ofthe
May
2001
hearing, Black Beauty had (I) submitted to
the IEPA a biological
inventory, and (2) installed a staff
gauge
in the
tributary
to determine
whether the three-to-
one dilution ratio exists.
See
In
re Adoption of Walgreen,
/86 IlL 2d 362,
365,
7/0 N.E.2d 1226,
/227,
238
III.
Dec.
/24 (1999)
(“when an opinion on a question of law
cannot affect the result as to the parties or controversy in
the case before
it,
a court should not resolve the question
merely for the sake of setting aprecedent to govern
potential
future cases”); see also
First National Bankof
Waukegan
v. Kusper,
98 IlL 2d 226,
235, 456
N.E.2d 7,
/0,
74 IlL Dec.
505
(1 983)
*34
(a court will not
review
cases merely to establish a precedent or guide
future
litigation).
However,
in”certain,
rare cases,”
a moot issue may be
considered where “the magnitude or immediacy of the
interests involved warrants
action by
the court’or
where the issue is “likely
to recur but unlikely tolast
long enough to allow appellate review to take place
because
of the
intrinsically short-lived nature of the
controversies.”
Dixon v.
Chicago & North
Western
Transportation Co.,
15/ IlL 2d /08, / / 7-18, 601
N.E. 2d
704.
708,
176 IlL Dec.
6 (1992),
quoting
Kusper,
98 IlL
2d at 235, 456 N.E.2dat
/0-1/,
quoting
People
&
reL
Black v. Dukes, 96/IL 2d 273,
277-78, 449
N.E.2d 856,
858,
70 IlL Dec.
509 (1983).
The present issue does not
fall within either exception to the mootness
doctrine.
Indeed,
Prairie Rivers
does notcontend that an
exception to the mootness doctrine applies.
F. The IEPA’s Alleged Reliance on Documents
Produced by Black Beauty
Following the Public
Comment
Period
Last,
Prairie Rivers
argues that the Board erred by
denying
Prairie
Rivers’
petition because the TEPA
improperly relied on
“key documents” produced*35
by
Black Beauty
after the close of the public
comment
period.
Initially,
we note
that
Prairie Rivers
has failed to cite
any authority in support of its position. In addition,
although
Prairie Rivers
claims that the IEPA relied on a
“portion”
of the alleged “key documents” “to justify
issuance of the permit,”
it fails
to support
its assertion
with logical and reasoned argument or citation to
relevant pages of the record.
Prairie
Rivers
cites
the
page of the record where one of the alleged key
documents can be found; however, it has failed to direct
our
attention to the other alleged key document or
documents. Neither does
it cite any page of the
record
indicating
that the IEPA actually relied on
the
documents. It is a rudimentary rule of appellate practice
that an appellant may not make a
point
merely by
stating
it
without presenting any argument in support.
See
Rivera
v. Arana,
255 IlL Dec.
333,
322 IlL App. 3d 641,
648,
749 N.E.2d 434, 440
(2001)
(failure to cite to
relevant authority forfeits an issue
on appeal).
Strict adherence to the requirement of
citing relevant
pages of the record is necessary to expedite and facilitate
the administration ofjustice.
Maun v. Department of
Professional Regulation, 299 ilL
App. 3d 388, 399,
70/
N.E.2d
79/,
799, 233
ilL
Dec.
726 (1998);*36
Sohaey
v.
Van Cura,
240 ilL
App. 3d 266,
273, 607 N.E.2d 253,
260,
/80 Ill.
Dec.
359 (/992).
With regard to this
contention, defendant’s brief fails to comply with the
requirements set forth in Supreme
Court Rule 341(e) (7)
(188 Ill.
2d ft.
34 1(e) (7)), which provides
that the
argument sectionofan appellant’s brief “shall contain the
contentions ofthe appellantand the reasons therefor,
with citation of the
authorities and the pages of the
record relied on. Evidence shall not be
copied at length,
but reference shall be made to the pages ofthe record on
appeal
~
where evidence may be found.” Arguments
that
do not satis&
Rule 34 1(e) (7) do not merit
consideration on
appeal
(
Maun,
299 ilL
App. 3d at
399,
70/ N.E.2d at 799)
and may be rejected for that
11
reason
alone
(
Calomino
v. Board ofFire &
Police
applicant after the public comment
period or considering
Commissioners,
273 IlL
App.
3d 494,
501,
652 N.E.2d
such information in issuing
a final permit.
/126,
1132. 2/0 IlL Dec.
/50 (/995)).
In
light of Prairie
it has
forfeited this
issue on appeal.
HI.
CONCLUSION
Moreover, even assuming
that the IEPA relied on
For the reasons stated, we affirm the Board’s decision.
documents submitted by
Black Beauty
after the public
comment period,
our research has not revealedany
Affinned.
applicable state
law or regulation*37
that prohibits
the
IEPA
from seeking information
from an NPDES permit
McCULLOUGH, P.!., and TURNER, J., concur.
12
I:
‘4!f~Z~
~
Ti’
-
‘1
~96
r
A
-4
;
~
•
EXHIBIT
C
Chapter
1
Introduction
The purpose
of this manual
is to
provide the basic
regulatory framework and
technical
considerations that support the development
of wastewater discharge
permits as required under the
National Pollutant Discharge
Elimination
System
(NPDES)
Program.
It
is designed for new permit writers,
but
may also serve as
a
reference
for experienced permit writers.
In addition,
the
manual will
serve as
a
useful
source of information for anyone interested
in
learning
about
the
legal
process
and
technical
aspects
of developing NPDES
permits.
This manual updates
the
Training
Manual for NPDES Permit
Writers.1
It
is
recognized that each
United States Environmental
Protection Agency
(EPA)
Regional
office or approved
State
will
have
NPDES permitting
procedures
adapted to
address
local
situations.
Therefore, it
is
the objective
of this
manual to explain
the
minimum national NPDES
Program elements common to any State or Regional
office
that issues NPDES permits.
The specific objectives and functions of this
training
manual
are to:
-
Provide
an overview
of the
scope
and regulatory framework of the
NPDES
Program
1USEPA
(1993).
Training Manual for NPDES Permit Writers.
EPA/B-93-003.
Office
of Wastewater
Management.
&~t
NPDES PermIt Writers’
Manual.
I
Chapter
1
Introduction
•
Describe the
components of a
permit and provide
an
overview of the
permitting
process
•
Describe
the different types
of effluent limits and the
legal
and technical
considerations involved
in
limit
development
•
Describe other permit conditions
including:
—
special conditions
—
standard conditions
—
monitoring and reporting
requirements
•
Describe other permitting
considerations including:
—
variances
—
anti-backsliding
—
other applicable statutes (e.g.,
National
Environmental Policy
Act,
Endangered
Species
Act,
National
Historic Preservation Act)
•
Explain the administrative
process for
issuing,
modifying,
revoking
and
terminating NPDES
permits.
This manual
is
not intended to
be
a
stand-alone
reference document.
Instead,
it
is
intended to establish
the
framework for
NPDES
permit development and should
be
supplemented,
where necessary,
by additional
EPA
and State guidance applicable
to specific types
of dischargers
and circumstances.
To
this end,
the
NPDES
Permit
Writers’ Manual
identifies
and references
other guidance
documents throughout the
text and provides
information
on
how these documents can
be obtained.
Appendix
D
of this
manual provides the
reader with
detailed information on how to obtain
comprehensive
lists of available
EPA
publications and
how these documents can be
ordered.
1.1
History
and Evolution of the NPDES
Program
The
NPDES Program has evolved from
numerous legislative
initiatives dating
back to the
mid-1960s.
In
1965,
Congress enacted
legislation
requiring States to
develop water quality standards
for all
interstate waters by 1967.
However, despite
increasing public concern
and increased Federal
spending, only about
50 percent of
the
States had established water quality standards
by
1971.
Enforcement of the
Federal
legislation was
minimal because the
burden of proof lay with
the
regulatory
agencies
in
demonstrating that
a water quality
problem
had implications for human
health or violated water quality
standards.
Specifically,
the
agencies
had to
demonstrate
a
direct link between
a
discharger and
a water quality problem
in
order to
enforce against
a
discharger.
The lack of success
in
developing adequate water
2
-
&~
NPDES Permit Writers’
Manual
Introduction
Chapter
1
quality standards
programs,
combined
with
ineffective enforcement of Federal water
pollution
legislation prompted the
Federal government to advance
the
1970 Refuse Act
Permit Program
(RAPP),
under the Rivers and
Harbors Act of 1899,
as
a vehicle to
control
water pollution.
RAPP
required any facility that discharged wastes
into
public waterways
to
obtain
a
Federal
permit specifying abatement requirements from
the
United
States
A~myCorps of Engineers.
The Administrator of EPA
endorsed
the joint program
with
the
Corps of Engineers,
and
on December 23,
1970,
the
permit
program
was
mandated
through Presidential
Order.
EPA
and the
Corps of Engineers
rapidly
began
to prepare the administrative
and technical
basis
for the
permit
program.
However,
in
December 1971,
RAPP
was
struck down
by
a
decision of the
Federal
District Court in
Ohio
(Kalur v.
ResoO,
which
held that the
issuance
of a
permit for an individual
facility
could
require the
preparation of an environmental
impact
statement under the
National
Environmental
Policy Act (NEPA)
of 1969.
The
concept of a
permit program
survived,
however, and,
in
November 1972,
Congress
passed
a
comprehensive
recodification
and revision of Federal
water pollution
control
law,
known as the
FederatWater
Pollution
Control Act amendments
of 1972.
These
amendments
included
the
NPDES
permit
program
as the centerpiece of the efforts
for
national water pollution
control.
The enactment of the
1972 amendments
marked
a
distinct change in
the
philosophy of water
pollution control
in
the
United States.
The
amendments
maintained
the water quality-based controls,
but added an
equal emphasis
on
a
technology-based, or end-of-pipe, control
strategy.
The
1972 Act established
a
series
of goals
or policies in
Section
101
that illustrated
Congressional
intent.
Perhaps the
most
notable was the
goal that the
discharge of pollutants
into
navigable waters
be
eliminated
by 1985.
This goai
was
not
realized,
but
remains
a
principle for
establishing permit
requirements.
The Act had an
interim
goal
to
achieve “water
quality which
provides
for the
protection
and propagation of fish, shellfish,
and wildlife
and provides
for recreation in
and on
the water”
by July
1,
1983. This
is
more
commonly
known as the
“fishable, swimmable” goal.
The Act also contained
four
important
principles:
•
The discharge
of pollutants to navigable waters
is not
a
right.
•
A discharge permit is
required
to use
public resources
for waste disposal
and limits
the amount of pollutants
that may
be discharged.
&~
NPDES Permit Writers’
Manual
-
3
Chapter
I
Introduction
•
Wastewater must be treated
with
the
best treatment technology
economically achievable—regardless of the
condition of the
receiving water.
•
Effluent
limits must
be
based
on treatment technology performance, but
more stringent limits
may
be
imposed
if the
technology-based
limits do
not
prevent violations
of water quality
standards
in
the
receiving
water.
More specifically,
Title
IV of the Act created a
system for permitting
wastewater
discharges (Section 402),
known as
the
National Pollutant Discharge
Elimination
System (NPDES),
with the objective
to
implement the
goals
and objectives of the Act.
An outline of the
Titles
contained
in
the Act
is
provided as Exhibit
1-1.
EXHIBIT
1-1
Organization
of the Clean
Water Act
Title
I
—
Research
and
Related
Programs
Title
II
—
Grants
for Construction of Treatment
Works
Title
III
—
Standards
and Enforcement
-
•
Section
301
Effluent Limitations
•
Section
302
Water Quality-Related Effluent
Limitations
•
Section
303
Water Quality
Standards
and
Implementation Plans
•
Section
304 Information
and Guidelines
Effluent
•
Section
305
Water
Quality Inventory
•
Section
307 Toxic
and
Pretreatment
Effluent Standards.
Title
IV
—
Permits
and
Licenses
•
Section 402
National
Pollutant Discharge
Elimination
System
(NPDES)
•
Section
405
Disposal
of Sewage
Sludge.
Title V
—
General
Provisions
•
Section
502
Definitions
•
Section
510 State
Authority
•
Section
518 Indian Tribes.
Title VI
—
State
Water Pollution Control
Revolving
Funds
4-
.&E’A
NPDES Permit Writers’
Manual
introduction
Chapter
1
The first round
of NPDES permits issued
between
1972
and 1976 provided for
control of a
number of traditionally regulated
pollutants,
but focused
on
5-day
biochemical oxygen demand
(BOO5),
total
suspended solids
(TSS),
pH,
oil
and grease,
and some metals, by requiring
the
use of the
Best
Practicable
Control Technology
currently
available (BPT).
The Act established
a
July
1,
1977, deadline for all
facilities
to be
in compliance with
BPT.
Additionally,
the Act established
the
compliance
deadline
for
installing Best Available Technology
Economically Achievable (BAT) as
July
1,
1983.
Most of the
major permits issued
to industrial
facilities
in
the first round
of NPDES permitting
contained effluent limitations based
on
Best
Professional
Judgment
(BPJ)
because
regulations prescribing
nationally uniform, technology-based
effluent limitations were
generally unavailable.
The second
round
of permitting
in
the
late
1970s and early
1980s
began
to
emphasize the
control of toxics, but, due
to
a
lack of information
on
treatability, failed to complete the task.
EPA’s failure to develop adequate
controls for toxic discharges under
the
1972
Act prompted the
Natural Resources
Defense Council
(NRDC) to sue EPA. NRDC
v.
Train,
8
E.R.C.
2120 (D.D.C.
1976).
The
suit
was
settled through
a
court supervised
“consent decree”
in
1976. The
consent decree identified
(1) the
“priority” pollutants to
be controlled; (2) the
“primary industries” for technology-based
control; and (3) the
methods
for
regulating
toxic discharges through
the
authorities of the
1972 Act.
The
provisions of the
consent decree were
incorporated into the
framework of the
1977
amendments of the Act,
and resulted
in
the Act’s
refocus toward
toxics
control.
The
1977 amendments to the
legislation,
known formally as the
Clean Water
Act (CWA)
of 1977, shifted
emphasis
from
controlling conventional
pollutants
to
controlling
toxic discharges.
This era of toxic pollutant control
is
referred
to as the
second round of
permitting.
The
concept of BAT controls was
clarified and expanded
to include
toxic pollutants.
Hence,
the
compliance deadline
for
BAT was extended to
July
1,
1984.
The conventional pollutants
(BOD5,
TSS, pH,
fecal
coliform,
and
oil
and
grease)
controlled by BPT
in
the
first round of permitting
were
now subject
to
a
new
level
of control, termed
Best Conventional Pollutant Control Technology
(BCT). The
compliance deadline
for meeting
BCT was
also July
1,
1984.
On
February
4,
1987,
Congress
amended
the
CWA with
the
Water Quality Act
(WQA) of 1987.
The
amendments
outlined
a
strategy
to accomplish the
goal of
6~
NPDES Permit Writers’
Manual
-
5
Chapter
I
Introduction
meeting water quality standards
set
by
the
States.
The
WQA
required
all
States to
identify waters
that were
not
expected to meet water quality
standards
after
technology-based
controls
on point sources have
been
imposed.
The State
must then
prepare
an individual
control
strategy to
reduce toxics from
point
and nonpoint sources
in
order to meet the
water quality
standards.
Among
other
measures, these plans
were
expected to address
control of pollutants
beyond technology-based
levels.
The
WQA
once
again
extended
the
time
to meet BAT
and BCT
effluent
limitations.
The
new compliance deadline
was
no
later than
March
31,
1989.
The
WQA
also established
new schedules for
industrial
and municipal
storm water
discharges to be regulated
by NPDES permits.
Industrial storm water discharges
must
meet the
equivalent
of BCT/BAT effluent quality.
Discharges from
municipal
separate storm
sewer systems (MS4)
required controls to
reduce the
discharge
of
pollutants to the
maximum
extent
practicable
(MEP).
Additionally,
the
WQA required
EPA to
identify
toxics
in
sewage sludge
and establish
numerical limits
to control
these
pollutants.
The
WQA
also established
a
statutory anti-backsliding
requirement that
would not allow
an
existing
permit
to
be modified or reissued
with
less
stringent
effluent limitations,
standards, or
conditions
than
those already imposed.
There were
a
few
exceptions for technology-based
limits,
but
in
no case could
the
limits be
less
stringent than
existing
effluent guidelines
(unless
a
variance
has been granted)
or
violate water quality standards.
6
-
‘&~
NPDES
Permit Writers’
Manual
Chapter
2
Regulatory
Framework
and
Scope
of the
NPDES
Program
This chapter
provides
a
discussion of the
regulatory framework of the
NPDES
Program, identifies
the types
of activities regulated
under the
NPDES
Program, and
discusses
the
program
areas
that address
the
various types of regulated
activities.
2.1
Regulatory
Framework of the
NPDES
Program
Chapter
1
discussed how Congress,
in
Section 402 of the
CWA, required
EPA
to
develop and implement the NPDES
permit
program.
While
Congress’ intent was
established
in
the
CWA, EPA had
to develop specific
regulations to carry out the
congressional mandate.
The
primary regulations developed
by EPA to implement and
administer the NPDES Program are found
in
Title 40 of the
Code of Federal
Regulations
(CFR) Part 122.
The
CFR is
a
set of documents
listing
all
regulations issued
by every United
States government agency.
The
CFR
is
published
by the
National Archives and
Records
Service of the
General
Services Administration.
The CFR
is updated
annually based
on
the
regulations published daily
in
the
Federal Register (FR).
6~
NPDES Permit Writers’
Manual
-
7
Chapter 2
Regulatory Framework and Scope ofthe
NPDES Program
The
FR
is
the vehicle
by which
EPA and other branches of the
Federal
government provide
notice
of,- propose,
and promulgate
regulations.
Although
all
of
the
regulations can
be
found
in the
CFR,
the
background and implementation
information
related to
these regulations
can be found
in
the
preamble
to the
regulations contained
in
the
FR.
This information
is
important
to the
permit writer
because
it explains the
regulatory basis
upon which
permitting
decisions
are
made.
An
outline of the
Federal
NPDES
regulations (40 CFR Part 122)
is
provided
in
Exhibit
2-1.
Other parts of 40 CFR that are related to the
NPDES Program
include:
•
4OCFR
4OCFR
•
4OCFR
4OCFR
•
4OCFR
4OCFR
•
4OCFR
4OCFR
•
4OCFR
•
4OCFR
•
4OCFR
•
4OCFR
•
4OCFR
•
4OCFR
•
4OCFR
(State
program
requirements)
(procedures for decision
making)
(technology-based
standards)
(toxic
pollutant standards)
(water
quality management plans)
(water
quality-based standards)
(sewage secondary treatment regulations)
(citizen
suits)
(analytical
procedures)
(State sludge
disposal regulations)
(general
effluent guidelines provisions)
(general
pretreatment regulations)
Parts
405-471
(effluent limitations guidelines)
Part
501
(State sludge
permitting
requirements)
Part 503 (sewage
sludge
disposal standards).
An
index to the
NPDES regulations
is
provided
in Appendix A.
This index
the
regulatory requirements by subject
area to
provide the
permit writer easier
to
specific
provisions.
2.2
Scope of the NPDES
Program
Under the
NPDES
Program,
all
facilities which
discharge pollutants
from
any
point source
into waters of the
United States are required to obtain
a
NPDES permit.
Understanding how each
of the
key terms (“pollutant,” “point source,” and “waters of
Part
Part
Part
Part
Part
Part
Part
Part
Part
Part
Part
Part
123
124
125
129
130
131
133
135
136
257
401
403
groups
access
8
-
&EPA
NPDES Permit Writers’
Manual
Regulatory Framework and Scope of the
NPDES Program
Chapter 2
EXHIBIT
2-I
Federal
NPDES
Regulations (40
CFR Part 122)
Sobpa.t A
-
Deibtia
and General Program
Requirements
122.1
Purpose and Scope of NPDES Program
122.2
Definitions
122.3
Exclusions
122.4
ProhibitIons
122.5
Effect of a Permit
122.6
continuation of
Expired Permits
122.7
confidentIality of Information
Subpart B
-
Pemilt Application and Special NPOES Program Requirements
122,21
Applications
122.22
Signatures Requirements for Applications
122.23
Animal
Feeding Operations
122.24
Aquatic Mirnat
Production
122.25
Aquaculture
122.26
Storm
Water Discharges
122.27
SiMculture
122.28
General Permits
122.29
New
Sources and New Discharges
Subpart C
-
Permit
Conditions
122.41
Standard Conditions
122.42
Standard
Conditions Applicable
to
Specified Categories
122.43
Permit
Conditions
122.44
Permit
Limitations
(a)
Technology
Basis
U)
Pretreatment Program
(b)
Other
Basis (not WO)
(k)
Best
Management Practices
(c)
Reopeners
(I)
Mti-Baclcstding
(d)
Water Quality Basis
(m)
Private Treatment Worts
(e)
Priority Pollutants
(n)
Grants
(f)
Notification Levels
(o)
Sludge
(g)
24
Hour
Reporting
(p)
Coast Guard
(h)
Duration of Permits
(q)
Navigation
(i)
Monitoring
122.45
Calculating Limitations
(a)
Discharge Points
(f)
Mass Based Umits
(b)
Production Basis
(g)
Intake Water Pollutants
(c)
Metals
(h)
Internal Waste Streams
(d)
Continuous Discharges
(i)
Discharge
Into Wells
(e)
Non-continuous Discharges
122.46
Duration of
Permits
122.47
Schedules of Compliance
122.48
ReportIng
122.49
ConsIderation
of Other Federal t.aws
122.50
DIsposal to
Other Pcints
Subpart D
-
Transfer, Modification.
Revocation and Reissuanoe.
and Tenninatlon of Permit
122.61
Transfer of Permits
122.82
ModIfication or Revocation
and Reissuance of Permits
122.63
MInor Modifications of Permits
122.84
TermInation of Permits
&8~
NPDES Permit Writers’
Manual
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9
Chapter 2
Regulatory
Framework and Scope of the NPDES Program
the
United States”)
have been defined and interpreted
by the
regulations
is
the
key to
defining
the scope of the
NPDES
Program.
Pollutant
The
term
“pollutant”
is
defined very broadly by the
NPOES
regulations and
includes any type of industrial,
municipal,
and agricultural waste discharged into water
(see
glossary).
For regulatory purposes,
pollutants
have
been grouped into three
general
categories under the
NPDES
Program:
conventional, toxic,
and
nonconventional.
By
definition,
there
are
five
conventional
pollutants:
5-day
biochemical oxygen demand (BOD5),
total suspended solids
(TSS), fecal
coliform,
pH,
and
oil
and grease.
Toxic or “priority” pollutants
are those defined in
Section 307(a)(1)
of the
CWA
(and
listed
in
40 CFR §401.15)
and include
metals
and manmade organic
compounds.
Nonconventional
pollutants are those which
do
not fall under either of
the
above categories
and include
such
parameters as ammonia,
nitrogen,
phosphorus,
chemical
oxygen
demand (COD), and whole effluent toxicity (WET).
Point Source
Pollutants
can enter waters of the United
States from
a
variety of pathways
including
agricultural,
domestic
and industrial
sources
(see Exhibit
2-2).
For
regulatory
purposes these sources are generally categorized as
either “point sources”
or “non-point sources.”
Typical
point source
discharges include
discharges from
pubticty owned
treatment works (POTW5),
industrial
faciiities, and discharges
associated
with
urban
runoff. While provisions of the
NPDES
Program do address
certain
specific types
of agricultural
activities (i.e.,
concentrated animal feeding
operations),
the
majority of agricultural facilities are defined as non-point sources and
are exempt from
NPDES regulation.
Pollutant contributions to waters of the
United States may come from
both
“direct” and “indirect” sources.
“Direct” sources
discharge wastewater directly
into the
receiving
waterbody, whereas
“indirect” sources discharge wastewater to a
POTW,
which
in
turn discharges
into the
receiving
waterbody.
Under the
national
program,
NPDES permits are issued ~
to direct point source discharges.
industrial
and
commercial
indirect dischargers are
controlled by the
national pretreatment program
(see
Section 8.3.1).
10
-
6E~NPDES Permit Writers’
Manual
Regulatory Framework
and Scope ofthe
NPDES Program
Chapter 2
EXHIBIT
2-2
Sources of Discharge to
Waters of the United
States
I
ducks, deer, and
sewage picture
I
As
indicated
above,
the
primary focus
of the
NPDES permitting
program
is
municipal and non-municipal
(industrial) direct dischargers.
Within
these major
categories of dischargers,
however, there
are
a
number of more specific types
of
discharges that are regulated
under the
NPDES Program.
Exhibit
2-3
provides
an
overview of the
scope of the
NPDES Program and identifies
the
program
areas that
control
various categories of wastewater discharges.
Municipalities
(e.g.,
POTWs receive primarily domestic sewage from
residential
and commercial
customers.
Larger POTWs
will
also typically receive and treat
wastewater from
industrial
facilities
(indirect
dischargers) connected to thePOTW
sewerage system.
The types
of pollutants
treated by
a
POTW, therefore,
will always
include
conventional pollutants (BOD5,
TSS, pH,
oil
and grease,
fecal
coliform),
and
will
include
nonconventional and toxic
pollutants depending on
the
unique
characteristics of the
commercial
and industrial
sources discharging to the
POTW.
The treatment typically provided by POTWs
includes physical
separation and settling
(e.g.,
screening, grit
removal,
primary settling),
biological treatment (e.g., trickling
filters, activated
sludge),
and disinfection (e.g.,
chlorination,
UV,
ozone).
These
processes
produce the
treated effluent and
a
biosolids (sludge) residual.
An additional
&~
NPDES
Permit Writers’ Manual
-
11
Chapter 2
Regulatory
Framework and Scope of the
NPDES Program
EXHIBIT
2-3
NPDES Program
Areas and
Applicable
Regulations
Source
Activity
Program
Areas
Applicable
Regulations
Municipal
.
Municipal
Effluent
Discharge
NPDES
Point
Source
Control
Program
40 CFR
122
40
CFR
125
40
CFR
133
Indirect Industrial!
Commercial
Discharges
Pretreatment
Program
40
CFR
122
40
CFR 403
40
CFR 405-499
Municipal
Sludge
Use
and
Disposal
Municipal
Sewage
Sludge
Program
.
40
CFR
122
40
CFR 257
40
CFR 501
40
CFR 503
Combined
Sewer
Overflow
(CSO) Discharges
CSO
Control Program
40 CFR
122
40
CFR
125
Storm
Water Discharges
(Municipal)
Storm
Water
Program
40 CFR
122
40
CFR
125
Industrial
Process
Wastewater
Discharges
NPDES Point
Source
Control
Program
40 CFR
122
40
CFR
125
40 CFR 405-499
Non-process
Wastewater
Discharges
NPDES Point
Source
Control
Program
40
CFR
122
40
CFR
125
Storm Water
Discharges
(Industrial)
Storm
Water Program
40
CFR
122
40 CFR
125
concern
to some older POTWs
are “combined
sewer” systems (i.e.,
sewerage systems
that are designed to collect both sanitary sewage and storm water).
Exhibit 2-3
illustrates
how the
NPDES Program
is structured to
control all
of the
various types
of
pollutant
sources
and wastestreams
that contribute
to municipal point
sources.
Non-municipal
sources,
which
include industrial
and commercial
facilities, are
unique
with
respect to
the
products and processes
present at the facility.
Unlike
municipal
sources,
the types
of raw materials,
production processes, treatment
technologies utilized,
and pollutants
discharged at
industrial facilities
vary widely
and
are
dependent on
the
type of industry and specific facility
characteristics.
The
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operations,
however,
are generally carried
out within
a
more clearly
defined plant area;
thus,
collection
system
considerations
are generally much less
complex than
for
POTWs.
In addition,
residuals
(sludge) generated
by industrial
facilities are not
currently
regulated
by the
NPDES
Program.
Industrial facilities
may have discharges
of storm water that may
be contaminated
through
contact with
manufacturing
activities,
or raw material
and product storage.
Industrial facilities
may also
have
non-process
wastewater discharges such
as non-contact cooling water.
As
illustrated
in
Exhibit
23,
the
NPDES Program addresses each
of these potential
wastewater sources for
industrial
facilities.
Waters of the United
States
The
term
“waters of the
United States,” has been defined by EPA to include:
•
Navigable waters
•
Tributaries of navigable
waters
•
Interstate waters
•
Intrastate
lakes,
rivers,
and
streams:
—
Used
by interstate travelers for recreation and other purposes;
or
—
Which
are
the
source offish or shellfish sold
in
interstate commerce;
or
—
Which are
utilized for
industrial
purposes by industries
engaged
in
interstate commerce.
The
intent of this definition
is to cover all
possible waters
within
Federal jurisdiction
under the framework of the Constitution
(i.e.,
Federal
versus State
authorities).
The
definition
has been interpreted
to include
virtually all
surface waters
in the United
States,
including wetlands
and ephemeral
streams.
As
a
general mailer,
groundwater
is
not considered
a
waters of the
United States.
Therefore discharges to groundwater
are not subject
to
NPDES requirements.
1f
on the
other hand,
there
is
a
discharge to
groundwater that results
in
a
“hydrological connection” to
a
nearby surface water,
the
Director may require
the discharger to apply for
an
NPDES permit.
Note:
Because
States
maintain
jurisdiction over groundwater resources,
they may choose to require
NPDES
permits for discharges to groundwater.
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Chapter 2
Regulatory
Framework and Scope of the
NPDES Program
2.3
NPDES
Program
Areas
As
indicated
in
Exhibit 2-3,
the
national
NPDES Program
includes provisions
that address
several different types
of discharges from
municipal and industrial
sources.
This section
provides
a
brief description of how the
NPDES
Program
addresses each of these program
areas.
23.1
NPDES
Program
Areas Applicable
to Municipal Sources
The
NPDES permitting
program focuses
on
the
development of effluent limits
and conditions
for the
discharge of treated effluent.
The
NPDES Program, however,
also incorporates
other control
measures to
address
certain
types
and categories of
discharges that may
be present at some
municipal facilities.
A description of these
control
measures, and
a
discussion of how they are incorporated
into the
permitting
process
is
provided below.
National
Pretreatment
PrOgram
The
national
pretreatment
program
regulates the discharges of wastewater from
non-domestic
(i.e.,
industrial
and commercial) facilities that discharge
to POTWs
(i.e.,
“indirect” discharges).
The
pretreatment
program
requires industrial
and commercial
indirect dischargers
to “pretreat” their
wastes,
as necessary, prior
to discharge
to
POTWs, to prevent interference or upset to the
operation
of the
POTW.
The
Federal
program
also requires many indirect dischargers
to meet technology-based
requirements
similar to those for direct dischargers.
The
pretreatment
program is
generally implemented
directly by the
POTW
receiving
indirect discharges,
under
authority
granted through
the
NPDES permit.
The
Federal
regulations specifying
which
POTWs must
have
pretreatment
programs,
and the authorities and procedures
that must
be developed
by the P01W
prior to program
approval are found
in
40 CFR
Part 403.
The
implementation
of a
local pretreatment
program
is typically
included
as
a
special
condition
in
NPDES
permits issued to POTWs.
The
incorporation
of
pretreatment
special conditions
is
discussed in
Chapter
8.
Municipal
Sewage
Sludge
Program
Section 405 of the
CWA requires that
all
NPDES permits issued
to
POTWs and
other Treatment Works
Treating Domestic
Sewage (TWTDS) contain conditions
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Chapter 2
implementing 40 CFR Part 503 Standards for the
Use
and Disposal of Sewage
Sludge.
Thus,
POTWs and other TWTDS
must submit
permit applications for their
sludge
use or disposal practices.
TWTDS
include sewage sludge incinerators,
sewage sludge
surface disposal sites,
and facilities that do
not discharge to waters of
the
United States (sludge-only facilities
such
as sludge composting facilities
that treat
sewage sludge).
The
permitting
regulations can be found at 40 CFR Part
122 for
the
Federal
program.
Regulations for State
program approval
are found at 40 CFR
Parts
123 or
501
(depending
on whether the
State wishes
to
administer the
sewage sludge
program
under its
NPDES Program or under
another program,
e.g.,
a
solid waste
program).
The technical
regulations governing
sewage sludge use and disposal
are
contained
in
40 CFR Part 503.
Where
applicable,
sludge management requirements
are included as
a
special
condition
in
permits issued
to POTWs.
The
incorporation
of
special conditions
that address
sludge
requirements is discussed
in
Chapter 8.
Combined Sewer Overflows
Combined
sewer systems (CSS)
are wastewater collection
systems designed to
carry sanitary wastewaters (commercial and industrial wastewaters)
and storm
water
through
a
single conduit to
a
POTW.
As of 1995,
CSSs
serve about 43
million people
in
approximately 1,100
communities nationwide.
During
dry weather, CSSs collect
and convey domestic,
commercial,
and industrial wastewater to
a
POTW;
however,
during
periods of rainfall or snowmelt,
these systems can become overloaded.
When
this
occurs, the
CSS overflows at designed relief
points,
discharging
a
combination of
untreated sanitary wastewaters
and storm water directly
to a
surface water body.
These overflows,
called
combined
sewer overflows (CSO5), can be
a
major source of
water pollution
in
communities served by CSSs.
CSOs often contain high
levels of
suspended solids
(55), pathogenic microorganisms,
toxic pollutants,
floatables,
nutrients, and other pollutants,
causing
exceedances of water quality standards.
To address
CSOs,
EPA issued the
National
CSO
Control Strategy on August
10,
1989 (54
FR
37370).
While
the
1989 Strategy resulted
in
some progress
in
controlling
CSOs,
significant public health
risks and water quality impacts remained.
To
expedite
compliance with
the CWA and to elaborate
on
the
1989 Strategy1
EPA,
in
collaboration
with
other CSO stakeholders (communities with
CSSs, State water
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Chapter 2
Regulatory Framework
and Scope of the
NPDES Program
quality
authorities, and environmental
groups), developed and published
the
CSO
Control Policy on April
19,
1994 (59
FR
18688).
The
Policy establishes
a
uniform,
nationally
consistent approach
to developing and issuing NPDES permits that address
CSOs.
With
respect to NPDES permittees,
State water quality standards
authorities,
and NPDES permitting
and enforcement
authorities, the
CSO
Policy states the
following:
•
Permittees
should
immediately
implement the nine
minimum
controls
(NMCs), which
are technology-based
actions
or measures
designed to
reduce CSOs and their effects
on receiving
water quality,
as soon
as
practicable,
but
no later than
January
1,
1997.
•
Permittees should
give
priority to environmentally
sensitive
areas.
•
Permittees should
develop long-term control
plans
(LTCP5)
for controlling
CSOs.
A permittee
may
use one of two approaches:
(1)
demonstrate that
its
plan
is
adequate
to meet the water quality-based requirements of the
CWA
(“demonstration
approach”), or
(2) implement a
minimum level of
treatment (e.g.,
primary
clarification of at least 85
of the
collected
combined sewage flows) that
is
presumed to
meet the
water quality-based
requirements of the
CWA,
unless
data indicate otherwise (“presumptive
approach”).
•
Water quality standards
authorities should
review and revise,
as
appropriate, State water quality
standards during
the
CSO
long-term
planning process.
•
NPDES permitting
authorities should
consider
the
financial capability of
permittees when
reviewing CSO
control
plans.
The
CSO Policy
recommends that
NPDES permitting
authorities utilize
a
phased
approach
in
addressing CSOs.
Phase
I
permits should
require the
permittee to
implement the
NMC within
two years of notice from
the
NPDES permitting
authority
and to develop
a
LTCP.
Phase
II
permits should
require continued implementation
of
the
NMC and implementation
of a
LTCP.
Prior to issuing
a
permit that requires conditions
that address
CSOs,
permit
writers
should
consult the
CSO
Control Policy and associated
guidance materials.
The
incorporation of permit conditions
that address
CSOs
is
provided in
Chapter-8.
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Chapter 2
Storm Water
Program (Municipal)
EPA has determined
that storm water
runoff from major metropolitan
areas
is
a
significant source
of pollutants
discharged to
waters of the
United States.
While
rainfall
and snow
are natural events, the
nature of runoff and
its
impact on receiving
waters
is
highly dependent
on human
activities and use of the
land.
Runoff from
lands
modified
by human activities
(i.e.,
metropolitan
areas) can
affect surface water
resources
in
two
ways:
(1) natural flow
patterns can
be modified; and (2) pollution
concentrations and loadings
can be elevated.
To
address these discharges,
the
1987 amendments
to the
CWA
added
a
provision
Section
402(p)
that directed
EPA to establish
phased NPDES requirements
for storm water discharges.
Section 402(p)(2) of the Act identifies
discharges covered
under
Phase
I
of the
Storm Water Program and includes discharges from
municipal
separate storm sewer systems
(MS45) serving
a
population of 100,000
or more.
Section 402(p)(3) identifies
the
standards
for MS4 permits.
These
standards
mark the
significant difference
in
permits that address
storm water discharges from
MS4s
versus
permits that address
other
more
traditional sources
(i.e.,
POTWs and non-
municipal
sources).
In general,
Congress provided that permits for discharges from
MS4s:
•
May
be
issued
on a
system- orjurisdiction wide basis;
•
Shall effectively prohibit non-storm water discharges into the
MS4;
and
•
Shall
require controls to
reduce the discharge of pollutants
to maximum
extent practicable
(MEP).
In response,
EPA
published regulations addressing storm water discharges
from
municipal separate storm sewer systems
on November
16,
1990 (55
FR
47990).
The
regulations define
a
MS4 as any conveyance or system
of conveyances that
is
owned or operated
by a
State or local government entity designed for collecting
and
conveying
storm
water.
Under
Phase
I of the
Storm Water Program, only those MS4s
which
served
a
population of 100,000 or more were required to apply for a
NPDES
permit.
Unlike
permits that are developed and issued
to individual
POTWs (also
referred to as “municipals”),
permits that address
storm water discharges from
MS4s
may
be
issued
on
a jurisdiction-wide
basis
to the operator of the storm
water collection
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Chapter 2
Regulatory Framework and Scope ofthe
NPDES Program
system
(e.g.,
a
county or city
public works department).
Chapter 8
discusses
considerations for developing NPDES permits for storm
water discharges from
MS4s.
2.3.2
NPDES
Program
Areas Applicable to
Industrial Sources
In addition to the
development of effluent limits and conditions for discharges of
process
and
non-process wastewater from
direct dischargers, the
NPDES Program
also includes provisions for control
of storm water discharges from
industrial
sources.
A description of this
program
area
and
a
discussion of how it
is incorporated
into the
permitting
process
is provided
below.
Storm
Water
Program
(Industrial)
All storm water discharges associated
with
industrial
activity that discharge
through
municipal separate storm
sewer systems or that discharge directly
into
the
waters of the
United
States are required
to obtain
NPDES permit
coverage,
including
those which
discharge through
MS4s
located
in
municipalities
with
a
population of less
than
100,000.
Discharges of storm water to
a
sanitary sewer system
or to
a P01W
are excluded.
As with
the
Municipal
Storm Water Program discussed in
Section
2.3.1
above,
EPA
published
the initial
permit
application
requirements for certain
categories
of storm water discharges associated with
industrial
activity on
November
16,
1990
(55
FR
48065).
The
regulations
define storm water discharges associated
with
industrial
activity
as discharges from
any conveyance used
for collecting
and conveying storm water
directly
related to
manufacturing, processing, or raw materials storage
areas at an
industrial
plant.
The NPDES permitting
regulations at 40 CFR §122.26 were
promulgated
on November
16,
1990
(55.
FR
48065)
to identify
the following
11
industrial
categories required
to
apply for
NPDES permits for
storm
water discharges:
•
Facilities subject
to storm water effluent limitations guidelines
(ELG),
new
source
performance standards
(NSPS),
or toxic pollutant effluent standards
under 40 CFR Subchapter
N
•
Certain
heavy manufacturing
facilities
(lumber, paper, chemicals, petroleum
refining, leather tanning,
stone,
clay, glass, concrete, ship construction)
•
Active and inactive
mining
operations and
oil
and gas operations with
contaminated
storm water
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•
Hazardous waste treatment, storage, or disposal facilities,
including
Resource Conservation
and Recovery Ad (RCRA) Subtitle
C facilities
•
Landfills,
open
dumps, and RCRA Subtitle
D facilities
•
Recycling
facilities, including
metal scrapyards,
battery reclaimers, salvage
yards, and automotive junkyards
•
Steam
electric
power generating
facilities, including
coal handling
sites
•
Transportation facilities that have vehicle maintenance
shops,
equipment
cleaning
operations, or airport de-icing
operations
•
Major POTW
sludge
handling facilities; including
onsite application
of
sewage sludge
•
Construction activities that disturb
five acres or
more
•
Light industrial
manufacturing facilities.
Operators of industrial facilities
that are federally,
state or municipally owned
or
operated that
meet the description of the facilities
listed
in
40 CFR 122.26(b)(14)(1)-
(xi)
must also submit applications (note:
the Transportation Act of 1991
provides
exceptions
for certain
municipally
owned or operated facilities).
EPA
published final
rules
regarding the
NPDES Storm Water Regulations
on
both April
1, 1992 (57
FR
11394) and December
18,
1992
(57
FR
60444).
The
rule promulgated
on April
2,
1992 was,
in
part,
to
codify provisions of the Transportation Ad of 1991.
The
December
18,
1992 rule was
in
response
to the
mandate of the
Ninth
Circuit United
States
Court of Appeals
in
NRDC
v.
EPA
(June 4,
1992).
Each
of these final rules
are
summarized below:
•
Transportation Act of 1992—The
Transportation Act of 1991
provides
an
exemption
from Phase
I
storm water permitting
requirements for
certain
industrial
activities owned
or operated by municipalities with
a
population
of
less
than
100,000 (note:
population threshold
not tied to
a
service
population for
a
MS4).
Such municipalities
must submit
storm water
discharge permit
applications only for
airports, powerplants, and
uncontrolled sanitary landfills
that they own or operate.
•
Ninth
Circuit Court Decision—The Ninth
Circuit United States
Court of
Appeals’ opinion
in
NRDC
v.
EPA
(June 4,
1992)
invalidated
and remanded
for further proceedings two
regulatory exemptions from
the
definition of
“storm water discharges associated
with
industrial
activity”:
1.
The
exemption for construction
sites disturbing less than
five acres of
land (category
x), and
2.
The exemption of certain
“light”
manufacturing
facilities without
exposure of materials and activities to storm water (category xi).
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Chapter
2
Regulatory
Framework and
Scope of the
NPOES
Program
In response
to
these two
remands,
EPA
intends to conduct further
rulemaking proceedings on construction
activities under five
acres and light
industry without exposure.
As
ordered by the
Court,
EPA will
require
permit applications for construction
sites disturbing
less
than
five acres of
land and category xi
facilities without exposure until this
further rulemaking
is
completed.
Generally,
storm water discharges from
industrial
sources are regulated
by
Federal
or
State
issued general
permits
(see
Section
3.1
for a
description of the types
of NPDES
permits).
However,
in
some cases, storm water conditions
may
be
incorporated
into
a
comprehensive
individual
NPDES permit for a facility,
or a
storm
water-specific
individual
NPDES permit.
The
incorporation of permit conditions that
address
storm water discharges from
industrial
facilities
is
provided
in
Chapter 8.
For
more
information regarding the
scope of the
NPDES Storm Water Program,
refer to
EPA’s
storm water regulations at 40 CFR
122.26 and
the
Overview of the
Storm
Water Program.2
2USEPA
(1996).
Oven’iow of the Storm
Water Program.
EPA 833-R-96-008.
Office of Water.
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Chapter
7
Monitoring
and
Reporting
Conditions
Having developed
the
effluent limits for a
municipal or industrial
discharger,
the
permit
writer’s
next step
is
to establish
monitoring and reporting
requirements.
Requiring
the
permittee to
routinely
self-monitor its
discharge
and to report the
analytical
results of such
monitoring
provides the
permitting
authority with
the
information
necessary to evaluate
discharge characteristics and compliance status.
Periodic monitoring and reporting
also serve to
remind the
permittee
of its
compliance
responsibilities
and provides feedback regarding the
performance of the
treatment
facility(s)
operated
by the
permittee.
Permit writers
should
be aware of and concerned
with
the
potential
problems that may occur in
a
self-monitoring
program
such
as
improper
sample collection
procedures,
poor
analytical
techniques,
and poor or
improper
report preparation and documentation.
To
prevent or minimize these
problems,
the
permit writer should
clearly detail
monitoring and reporting
requirements
in
the
permit.
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Chapter 7
Monitoring
and Reporting
Conditions
The monitoring
and reporting
conditions
section of a
NPDES individual
permit
should
contain specific
requirements for the
following
items:
•
Sampling
location
•
Sample collection
method
•
Monitoring frequencies
•
Analyticai
methods
•
Reporting and recordkeeping
requirements.
Several
factors
should
be
considered
in
determining the
specific
requirements
to be imposed.
Basic factors
that may
affect sampling
location,
sampling
method,
and
sampling
frequency
are:
•
Applicability of “effluent limitations guidelines” (ELG)
•
Effluent and process
variability
•
Effect of flow and/or pollutant
load on the
receiving
water
•
Characteristics of pollutants
discharged
•
Permittee
compliance history.
These
factors
must be
carefully considered
by the
permit writer,
as any error
could
lead
to
inaccurate compliance determination,
misapplication
of national ELGs,
and/or
misapplication of State
water quality
standards.
The
following sections provide
an overview of the
considerations involved
in
determining appropriate
monitoring,
reporting,
and recordkeeping requirements,
and
describe
how to properly incorporate
the
requirements
in
a
NPDES permit.
7.1
Establishing
Monitoring
Conditions
The
NPDES Program is
structured such
that facilities that discharge
pollutants
in
waters of the
United States are required
to periodically
evaluate compliance with
the
effluent limitations established
in
their permit
and provide the results to
the
permitting
authority.
In addition,
NPDES permits can
require the
permittee to monitor
for
additional parameters or processes
not directly
linked to the
effluent discharge
such
as
storm
water, combined sewer overflows,
municipal
sludge, and/or treatment plant
influent.
This
section
describes the
regulatory requirements and authorities for
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monitoring conditions,
and
describes how these conditions can be incorporated
in
NPDES
permits.
The
regulations requiring
the establishment
of monitoring and
reporting
conditions
in
NPDES permits are found
in 40 CFR §122.44(i)
and 40 CFR §122.48.
Section
122.44(i)
requires permittees to monitor
pollutant
mass
(or other applicable
unit of measure), effluent volume, provide other measurements (as
appropriate),
and
to utilize
the
test methods established at 40 CFR §136.
Section
122.41(i)
also
establishes
that NPDES permittees (with
certain
specific exceptions) must monitor for
all
limited pollutants and report data at
least
once
per year.
EPA
regulations at 40 CFR §122.48 state that all
permits must
specify require-
ments concerning
the
proper use, maintenance,
and installation
of monitoring equip-
ment or methods (including
biological
monitoring methods when
appropriate).
All
permits must also specify
the
required monitoring including the type,
intervals,
and
frequency
sufficient to yield data
that are representative
of the
activity.
The following
sections focus
on ensuring that
permit monitoring
conditions propeily address these
regulatory requirements.
7.1.1
Monitoring
Location
The
NPDES regulations
do not specify the
exact location
to be
used for
monitoring.
The
permit writer
is
responsible for determining the
most
appropriate
monitoring location
and explicitly specifying this
in
the
permit.
Ultimately, the
permittee
is responsible for
providing
a
safe and
accessible sampling
point that
is
representative
of the
discharge
(40 CFR §122.41(j)(1)).
Specifying the
appropriate monitoring
location
in
a
NPDES permit
is
critical to
producing
valid
compliance data.
Important factors
to consider in
selecting
a
monitoring location
include:
•
The wastewater flow
should
be measurable
•
The
location should
be easily and safely accessible
•
The
sample
must be
representative of the effluent during
the
time
period
that is
monitored.
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Chapter 7
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Conditions
Technical Note
When
establishing monitoring locations for determining
NPDES
permit compliance,
permit writers must
select locations
that are representative of the expected wastewater discharge.
Locations should
be
established where the wastewater is
well
mixed,
such
as near
a parshall
flume or at
a location
in a sewer
with hydraulic turbulence.
Weirs
tend
to
enhance the settling of solids immediately upstream and the
accumulation of floating
oil or grease
immediately downstream.
Such locations
should
be
avoided
for
sampling.
The most
logical monitoring point for an effluent
is just
prior
to discharge
to the
receiving water.
This
is particularly true for ensuring
compliance with
water quality-
based effluent limits
(WQBELs).
However, there
are instances when
the
permit
writer
may
need to
specify alternate monitoring locations
in
a
permit.
One typical instance
that
necessitates establishing an
alternative monitoring
location occurs
when
a
facility
combines
a variety of process and non-process
wastewaters
prior to discharge through
a
common outfall structure.
Under certain
circumstances,
when
a
variety of wastewaters are combined,
requiring monitoring only
at the
final combined outfall may
not
be appropriate.
To
address
this
situation,
40
CFR
§122.45(h) allows
permit writers
to establish
monitoring locations
at internal
outfalls.
Examples
of situations that may
require
designation of internal monitoring
locations include:
•
To ensure
compliance
with effluent
limitations
guidelines
and
standards
(at
non-municipal
facilities)—When non-process
wastewaters
dilute
process wastewaters
regulated
under effluent guidelines,
monitoring
the
combined discharge
may
not accurately depict whether the
facility
is
complying
with
the effluent guidelines.
Under these circumstances,
the
permit writer may consider
requiring monitoring for compliance with
technology-based
effluent limits (based on
application
of effluent guidelines)
before the
process wastewater is
combined with
the other wastewaters.
•
To ensure
compliance
with secondary treatment standards
(for
POTWs only)—Certain
POTWs include treatment processes that are
ancillary
to the
secondary treatment process that may impact their ability
to
monitor for compliance with secondary treatment standards.
Under these
circumstances, the
permit writer may consider requiring
monitoring for
compliance with
secondary treatment standards just
after the
secondary
treatment process
(e.g., require
monitoring of effluentjust
after
secondary
clarification)
before any additional treatment processes.
•
To allow
detection
of
a
pollutant—instances may arise
where the
combination of process and non-process wastewaters result
in
dilution
of a
pollutant of concern
that will
not be detectable
using
approved
analytical
118-
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Conditions
Chapter
7
methods.
Establishing
monitoring for the
pollutant at
an
internal
location
will enable characterization
of the
pollutant
prior to
dilution with
other
wastewaters.
When
establishing internal
monitoring points,
permit writers need
to
consider
the
location
of wastewater treatment units within
the
facility.
This
is
particularly
true
when
establishing internal monitoring locations for
determining compliance with
technology-based
effluent limits.
A facility
will
most
likely not be able
to comply with
technology-based
effluent limits if the
permit
writer establishes the
monitoring location
prior to the wastewater treatment unit.
Permit writers
may also need to require
monitoring of influent to the wastewater
treatment units for
certain facilities.
Influent monitoring
must be
required for POTWs
to ensure compliance with the
85
percent removal
condition of the
secondary
treatment standards.
influent monitoring
at
non-POTWs may also be desired to
determine influent characteristics, and if additional
information
related to the
performance of the wastewater treatment
unit is
needed.
Exhibit
7-1
provides examples of how to specify sampling
locations
in
a
permit
either by narrative or diagram.
7.1.2
Monitoring
Frequency
The frequency
for monitoring pollutants
should
be determined on
a
case-by-
case
basis, and decisions
for selling the frequency
should
be set forth
in
the fact
sheet.
Some States
have their own recommended sampling
guidelines that can
help
a
permit
writer determine an appropriate sampling
frequency.
The
intent
is to
establish
a
frequency of monitoring that will
detect most events of noncompliance
without requiring
needless or burdensome
monitoring.
To establish
a
monitoring frequency, the
permit
writer should
estimate the
variability of the
concentration of the
parameter
by reviewing
effluent data for the
facility
(e.g., from
DMRs)
or in
the
absence of actual data, information from
similar
dischargers.
A highly variable discharge should
require
more frequent monitoring than
a
discharge that
is
relatively
consistent over time (particularly
in
terms of flow and
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Chapter 7
Monitoring
and
Reporting Conditions
EXHIBIT
7-4
Examples of Specifying Sampling Locations
in Permits
pollutant concentration).
In addition
to the
estimated variability,
other factors that
should
be considered when
establishing appropriate monitoring frequencies
include:
•
Design
capacity
of
treatment facility—As
an example, at
equivalent
average flow
rates,
a
large lagoon
system
that is
not
susceptible to
bypasses requires less frequent
monitoring than
an overioaded treatment
facility that experiences fluctuating
flow rates due
to inflitration
or large
batch
discharges from
an
industrial
user system.
The
lagoon
should
have a
relatively
low variability
compared to the
facility
receiving
batch discharges.
NARRATIVE:
Part I.
SELF-MONITORING
REQUIREMENTS
A.
Sample
Locations
1.
Discharge
from the Chemistiy-Fine Arts
Building shall
be sampled
at outfall 001
2.
Discharge
from the
Duane
Physics Building
shall be
sampled at
outfall
002
3.
Discharge
from the Research
Lab
No.
1
shall be
sampled at outfall
003
DIAGRAM:
Part
1.
EFFLUENT LIMITATIONS AND
MONITORING REQUIREMENTS
A.
Sample
Locations
Outfall
Description
001
Discharge Pipe—Discharge of wastewater generated by all
regulated metal
finishing
processes
at
the
facility.
Samples shall be
collected at
the
point indicated on
the attached
diagram.
Receiving
Stream
~aIIFIume
OuffalI
001
Final
pH
Adjustment
Tank
*sampIe
Point
•&48-01
120
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7
•
Type of treatment method
used—The type of wastewater treatment used
by the
facility will
determine the
need for
process control
monitoring and
effluent monitoring.
An industrial
facility with
biological
treatment would
have
similar monitoring frequencies to
a
secondary treatment plant with the
same units
used
for wastewater treatment.
If the treatment method is
appropriate and achieving high pollutant
removals on
a
consistent
basis, the
need for monitoring may
be
less
than
a
plant with
little
treatment or
insufficient treatment.
•
Post
compliance record/history—The
monitoring frequency
may
be
adjusted to
reflect the
compliance history of the facility.
A facility with
problems achieving compliance generally should
be required
to perform
additional monitoring to characterize the
source or cause of the
problems or
to detect noncompliance.
•
Cost of monitoring
relative to discharger’s
capabilities—The permit
writer should
not require excessive
monitoring
unless
it is necessary to
provide sufficient information
about the
discharge (analytical
costs
are
addressed
in
Section 7.1.5).
•
Frequency
of the discharge—If
wastewater is discharged
in
batches on
an
infrequent basis, the
monitoring frequency
should
be different from
a
continuously
discharged,
highly concentrated wastewater, or a wastewater
containing
a
pollutant that is found infrequently and at very low
concentrations.
The production
schedule of the facility (e.g., seasonal,
daily),
the
plant washdown
schedule,
and other similar factors should
be
considered.
•
Number of monthly samples used
in developing permit
limit—The
monitoring frequency
should
reflect the
number of monthly samples used
in
developing the
permit
limits, and/or the
monitoring frequencies
used
to
develop any applicable effluent guidelines.
•
Tiered Limits-Where
the
permit writer has included
“tiered”
limits
in an
NPDES permit, consideration
should
be
given
to
varying the
monitoring
frequency
requirements to correspond to the
applicable
tiers.
For example,
if a
facility has seasonal
discharge limits,
it may
be
appropriate to
increase
the
monitoring frequency
during
the higher
production season, and reduce
the
frequency during
the
off-season.
An
alternative method that can be
used by permit writers
to establish
monitoring
frequencies is
the
quantitative
approach
described
in
the
Technical Support Document
for
Water Quality-Based Toxics Control
(TSDf°. In short,
the
TSD31 approach
30USEPA (1991).
Technical Support Document
for
Water
Quality-Based Toxics Control.
EPA-
505/2-90-001.
Office
of water Enforcement and Permits.
31ibid.
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requires calculating
the
long-term average
pollutant concentration
(accounting for the
expected variability of the
discharge) and comparing it to the
permit limit
to determine
the
likelihood of
noncompliance.
The closer the
long-term average is to the
permit
limit, the
more frequent the
monitoring that should
be
required.
Obviously, this
quantitative
approach
requires
a
reasonable
data
set
from which
to
calculate the
long-
term
average.
Permit
writers
should
refer to
the TSD32 for more information
regarding this
approach.
A permit writer may also establish
a
tiered
monitoring schedule
that reduces
or
increases monitoring frequency during
a
permit cycle.
Tiered
monitoring, which
reduces monitoring over time,
may be useful for discharges where the
initial
sampling
shows compliance with
effluent limits,
If problems are found during
the
initial
sampling,
more frequent sampling
and more comprehensive
monitoring can
be
applied.
This
step-wise approach
could
lead
to lower
monitoring costs for permittees
while
still providing
an
adequate
degree of protection
of water quality.
Regulatory
Update
In
response
to President clintons
Regulatory Reinvention initiative, which established
the goal of
reducing monitoring and reporting burden
by 25,
EPA
issued
Interim Guidance for Performance-Based
Reductions of NPDES Permit Monitoring Frequencies
on April
19, 1996
(EPA-833-B-96-0O1).
Under this
guidance,
NPOES
reporting and monitoring requirements are reduced
based
on
a demonstration of
excellent historical performance.
Facilities can demonstrate this historical performance by meeting
a
set
of compliance and enforcement criteria
and by demonstrating their ability to consistently
discharge
pollutants below the
levels
necessary to
meet their
existing
NPDES permit limits.
Reductions
are
determined
parameter-by-parameter,
based
on
the existing monitoring frequency and
the percentage
below
the limit that parameter is
being discharged at.
The
reductions
are incorporated
into the permit at
the time of permit reissuance.
To remain eligible
for these reductions,
permittees are expected to
maintain
parameter
performance levels
and good
compliance and
enforcement
history
that were
used
as
the basis
for granting
the reductions.
7.1.3 Sample Collection Methods
In addition to establishing the frequency of monitoring,
the
permit writer must
specify the
type of sample that must
be collected.
The two
basic
sample collection
methods
include “grab”
and “composite.”
The
analytical
methods
specified
in 40 CFR Part
136 are
required for
all
monitoring performed
under the
NPDES Program, unless
the
permit
specifically
32USEPA (1991).
Technical Support Document for Water Quality-Based Toxics
Control.
EPA-
505/2-90-001.
Office of Water Enforcement and
Permits.
122
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Chapter
7
requires alternate methods.
For many analytical
procedures,
the
sample collection
method
(grab or composite)
is
not specified
in 40 CFR Part 136, thus
it should
be
specified
in
the discharge permit.
40 CFR Part 136 specifies that grab
samples must
be collected
for
pH,
temperature,
dissolved
oxygen,
chlorine, purgeable organics,
sulfides,
oil
and grease, coliform bacteria
and cyanide.
The
reason grab
samples
must
be
taken for these
parameters is
that they evaluate
characteristics
that may
change during
the time
necessary for compositing.
A “grab” sample is
a
single sample collected
at
a
particular time and place
that
represents
the
composition of the
wastestream only at that time and place.
When the
quality
and flow of the wastestream being sampled
is
not
likely to change over time,
a
grab
sample is
appropriate.
Grab samples
should
be
used
when:
•
The wastewater characteristics are
relatively constant.
•
The
parameters
to
be
analyzed
are likely to change with
storage
such
as
temperature, residual chlorine,
soluble sulfide,
cyanides,
phenols,
microbiological parameters and
pH.
•
The
parameters
to
be
analyzed
are likely to
be affected
by the
compositing
process such
as oil
and
grease and volatiles.
•
Information
on variability over a
short time period
is
desired.
•
Composite
sampling
is
impractical or the compositing
process
is liable to
introduce artifacts of sampling.
•
The
spatial parameter
variability is
to
be determined.
For example,
variability through
the
cross
section
and/or depth of a
stream or a
large
body of water.
•
Effluent flows are intermittent from
well-mixed
batch process tanks.
Each
batch dumping event should
be sampled.
Grab samples
can measure maximum effect only when
the
sample is collected
during
flows containing
the
maximum concentration of pollutants toxic to the test organism.
Another type of grab
sample
is
sequential
sampling.
A special type of
automatic sampling
device
collects relatively
small amounts of
a
sampled
wastestream,
with
the
interval between
sampling either time or flow proportioned.
Unlike
the automatic composite
sampler, the sequential
sampling
device automatically
retrieves
a
sample and holds
it
in
a
bottle separate from other automatically retrieved
samples.
Many individual
samples
can be stored
separately
in
the
unit, unlike the
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Chapter 7
Monitoring and Reporting Conditions
composite sampler which
combines
aliquots
in
a
common bottle.
This type of
sampling
is
effective
for determining variations
in
effluent characteristics
over shod
periods of time.
A “composite” sample
is
a
collection
of individual
samples
obtained
at regular
intervals,
usually based upon time or flow volume.
A composite
sample is desirable
when
the
material
being sampled
varies significantly over time either as
a
result of
flow or quality
changes.
There are two
general
types
of composites and the
permit
writer should
clearly
express
which type
is
required
in
the
permit:
•
Time composite
samples
collect
a
fixed volume at equal time intervals
and
are acceptable when
flow
variability
is
not excessive.
Automatically timed
composited
samples
are usually
preferred over manually collected
composites.
Composite samples
collected
by hand
are appropriate for
infrequent analyses
and screening.
Composite
samples
can be collected
manually
if subsamples
have
a fixed
volume at equal time
intervals when
flow
variability
is
not excessive.
•
Flow-proportional compositing
is
usually
preferred
when
effluent flow
volume varies appreciably
over time.
The equipment
and instrumentation
for flow-proportional
compositing have
more downtime due to maintenance
problems.
When manually
compositing effluent samples
according to flow where
no
flow
measuring device
exists, use the
influent flow measurement
without
any correction for time
lag.
The error
in
the
influent and effluent flow
measurement is insignificant except
in
those cases where extremely large
volumes of water are
impounded, as
in
reservoirs.
There are numerous cases where composites
are inappropriate.
Samples for
some
parameters should
not be
composited
(pH,
residual
chlorine,
temperature,
cyanides, volatile organics,
microbiological tests,
oil
and grease, total phenols).
They
are also not
recommended for
sampling
batch or intermittent processes.
Grab
samples
are needed
in
these cases to determine fluctuations in effluent quality.
For whole
effluent toxicity (WET),
composite samples
are used
unless
it is
known that the
effluent is
most toxic at a
particular time.
Some toxic chemicals
are
short-lived, degrade rapidly, and
will
not
be present in
the
most toxic form
after lengthy
compositing even with
refrigeration or other forms of preservation.
Grab
samples
should
be required for bioassays to
be
taken under those circumstances.
124
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Chapter
7
If a
sampling
protocol
is
not
specified
in
the
regulations,
the
duration of the
compositing time period
and frequency
of aliquot collection
is
established by the
permit
writer.
Whether collected
by hand or by an automatic device,
the
time frame
within
which
the
sample is
collected
should
be
specified
in the
permit.
The
number of
individual
aliquots which
compose the
composite
should
also be
specified.
NPDES
application
requirements specify a
minimum of four
aliquots for non-stormwater
discharges
lasting four or more
hours.
Eight types of composite samples
and the
advantages and disadvantages of
each
are shown
in
Exhibit 7-2.
As
shown
in
Exhibit
7-2, samples may
be composited
by time or flow
and a
representative
sample will
be assured.
However, where
both
flow and
pollutant
concentration fluctuate dramatically, a
flow-proportioned
composite
sample should
be
taken because
a greater quantity of pollutant will
be discharged
during these
periods.
As
an
alternative, time-proportioned samples may be taken with
flow
records used
for weighing
the
significance of various
samples.
Continuous monitoring
is
another option for
a
limited
number of parameters
such
as flow, total organic carbon
(TOC), temperature,
pH,
conductivity,
fluoride and
dissolved
oxygen.
Reliability,
accuracy
and cost of continuous monitoring
vary with
the
parameter.
Continuous
monitoring can be
expensive,
so continuous monitoring
will
usually only be an
appropriate requirement for the
most significant dischargers
with
variable effluent.
The environmental
significance of the
variation of any of these
parameters
in
the
effluent should
be compared to the
cost of continuous monitoring.
Technical
Note
When establishing
continuous
monitoring
requirements,
the
permit writer should
be
aware that the
NPDES
regulations concerning
pH
limits
allow
for a
period of
excursion
when
the effluent
Is
being
continuously
monitored (40 CFR §401.17).
7.1.4
Analytical Methods
The
permit writer must specify the
analytical
methods to be
used for monitoring.
These are usually indicated
as 40 CFR Part
136 in
the standard
conditions of the
permit
40
CFR §~1
22.41 (j)(4)
and
122.44(i).
In particular,
analytical
methods for
industrial
and municipal wastewater pollutants
must be conducted in
accordance
with
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Chapter 7
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EXHIBIT
7-2
Compositing
Methods
Method
Advantages
Disadvantages
Comments
Time
Composite
Constant sample
volume, constant
time
interval
between
samples
Minimal
instrumentation
and
manual
effort;
requires
no
flow
measurement
May
lack
representativeness,
especially
for
highly
variable
flows
Widely
used
in
both
automatic
samplers
and
manual
handling
EJow-Proportional
Composite
•
Constant
sample
volume,
time interval
between
samples
proportional to stream
flow
Minimal
manual effort
Requires accurate
flow
measurement reading
equipment; manual
compositing
from
flowchart
Widely
used in
automatic
as
well
as
manual
sampling
•
Constant
time interval
between
samples,
sample
volume
proportional
to total
stream
flow
at
time
of
sampling
Minimal
instrumentation
Manual
compositing
from
flowchart
in absence of prior
information
on
the
ratio of
minimum to maximum
flow;
chance of collecting
too small
or too
large individual discrete
samples
for a
given
composite
volume
Used
in automatic
samplers and
widely
used as
manual
method
•
Constant
time interval
between
samples,
sample
volume
proportional to total
stream
flow
since
last
sample
Minimal
instrumentation
Manual
compositing
from
flow
chart
in absence of prior
information
on
the
ratio of
minimum to maximum flow;
chance of collecting either too
small
or
too
large individual
discrete
samples
for
a given
composite
volume
Not widely
used
in
automatic
samplers
but may be
done
manually
Sequential Composite
•
Series
of short
period
composites,
constant
time intervals
between
samples
Useful if fluctuations
occur
and time
history
is
desired
Requires
manual
compositing
of aliquots
based
on
flow
Commonly
used;
however,
manual
compositing
is
labor
intensive
•
Series
of short
period
composites, aliquots
taken at constant
discharge
increments
Useful if fluctuations
occur
and
time history
is desired
Requires
flow
totalizer;
requires manual
compositing
of aliquots based
on
flow
Manual
compositing
is labor
intensive
Continuous
Composite
•
Constant
sample
volume
•
Sample
volume
proportional to stream
flow
Minimal
manual effort,
requires no
flow
measurement
Minimal
manual effort,
most
representative
especially for highly
variable
flows
Requires
large sample
capacity; may lack
representativeness for highly
variable
flows
Requires
accurate
flow
measurement
equipment, large
sample
volume, variable
pumping
capacity, and power
Practical but not
widely used
Not widely
used
126
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Chapter
7
the
methods specified
pursuant to 40 CFR
Part 136,
which
references one or more
of
the following:
•
Test methods in Appendix
A of 40 CFR Part 136~~
•
Standard Methods
for the Examination
of Water and Wastewater,
18th
Edition ~
•
Methods
for
the Chemical Analysis of Water and Wastewater~
-
•
Test Methods:
Methods for Organic Chemical Analysis of Municipal and
Industrial Wastewater.~
The
analytical
methods contained
in 40 CFR Part
136 are test methods
designed only for
priority and conventional pollutants,
and some
nonconventional
pollutants.
in
the
absence of analytical
methods for other parameters, the
permit
writer must
still specify the
analytical
methods
to
be
used.
An excellent source of
analytical
method information
is
the
Environmental Monitoring Methods Index (EMMI).
The
EMMI is
an official EPA database linking
50
EPA
regulatory lists, 2,600
substances and 926 analytical
methods on
EMMI.
EMMI data
correlate
EPA’s
regulated
substances with
their
associated
analytical
methods, published detection
limits,
and regulatory limits.
For
more information, call
NTIS
at (703)
321-8547 for
system
requirements.
7.1.5
Other Considerations
in Establishing Monitoring Requirements
The
regulations do
not
specifically require a
permit writer to evaluate costs
when
establishing monitoring conditions
in
a
permit.
However, as
a
practical
mafter,
the
permit writer should
consider the
cost of sampling that he/she
imposes
on
the
permittee.
The
sample frequency
and analyses
impact the
analytical cost.
The
estimated
1994-1995
costs for analytical
procedures are shown
in ExhIbit 7-3.
33Guidelines Establishing Test Procedures for the Analysis
of Pollutants Under the
Clean-Water -Act
(40 CFR Part
136).
(Use most current
version)
~American
Public
Health Association, American Water Works Association, and Water Pollution
Control
Federation
(1992).
Standard Methods
for the
Examination of Water and
Wastewater,
18th
Ed.
“USEPA (1979).
Methods for the ChemicalAnalysis of Water and Wastewater.
EPA-600/
4-79-020.
Environmental Monitoring
and
Support
Laboratory.
SEPA
(1982).
Test Methods:
Methods for Organic Chemical Analysis of Municipal
and
Industrial Wastewater.
EPA-60014-82-057.
‘&~
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127
Chapter 7
Monitoring and
Reporting Conditions
EXHIBIT 7-3
Estimated
Costs for Common
Analytical Procedures’
ROD5
$30
TSS
$15
TOC
$60
Oil and Grease
$35
Odor
$30
Color
$30
Turbidity
$30
Fecal
coliform
$15
Metals
(each)
$15
Cyanide
$35
Gasoline
(Benzene,
Toluene,
Xylene)
$100
Purgeable
Halocarbons (EPA
Method
601)
$113
Acrolein and Acrylonitrile
(EPA
Method
603)
$133
Purgeables
(EPA
Method
624)
$251
Phenols
(EPA
Method
604)
$160
Organochiorine
Pesticides
and
PCBs
(EPA
Method
608)
$157
Polynuclear Aromatic
Hydrocarbons
(EPA Method 610)
$175
Dioxin
(2,
3,
7, 8-TCDD
(EPA Method 613))
$400
Base/Neutrals and Acids
(EPA
Method
625)
$434
Priority pollution scan2
$2,000
Acute WET
$750
Chronic WET
$1,500
‘
Based
on
1994—1995
costs.
2
a
Includes
13
metals, cyanide,
dioxin,
volatiles
(purgeables),
bas
sbestos.
e/neutral and acids, pesticides
and PCBs, and
128
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Manual
Monitoring and Reporting Conditions
Chapter
7
If
simple or inexpensive indicator
parameters (e.g.,
BOD5
acts as
an
indicator for the
priority
pollutants
in
the
Wood and Gum
Chemicals category)
or alternate parameters
will
produce data
representative of the
pollutant
present
in
the
discharge, then
the
indicators or surrogate pollutants or parameters should
be considered.
Complex and
expensive sampling
requirements may
not
be appropriate if the
permit writer cannot
justify the
need for such analyses.
7:1.6
Establishing Monitoring Conditions
for Unique
Discharges
There are
a
variety of discharges that are regulated
under the
NPDES
permit
program
that are different than
traditional wastewater discharges.
A permit writer
needs to account for these unique
discharges
in
establishing monitoring requirements.
This section
discusses several of these
unique
discharges including
storm
water,
combined
sewer and sanitary sewer overflows,
WET,
and municipal sludge.
Storm Water Monitoring
Considerations
Monitoring requirements vary according to the type of permit regulating
the
storm water discharge
and the
activity.
Storm water discharges may
be regulated
by
State programs,
provided the
State
is authorized to administer the
NPDES Storm
Water Program, or
EPA
Regions.
At the
Federal
level,
several permitting
options are
available; depending on
the
type of activity,
industrial
facilities
may seek coverage
under an individual
permit, the
Baseline
Industrial General
Permit,
or the
Multi-sector
General
Permit.
In addition,
construction
activities that disturb
5 or more acres of land
are regulated
under the
Baseline Construction General
Permit.
Municipalities
serving
over
100,000 people are also regulated, but
on an individual
permit basis.
Each of
these permitting
mechanisms establishes
different monitoring programs.
Several
States have
used the
Federal
permits as models for their permit conditions.
Specific monitoring
conditions for the
Federal
general
permits are detailed
in
the
following documents:
•
“Final NPDES General Permits
for Storm Water Discharges AssoCiated
With
Industrial Activity,”
Federal Register,
September 9,
1992.
(Baseline
Industrial
General
Permit).
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Permit Writers’
Manual
-
129
Chapter 7
Monitoring and Reporting Conditions
•
“Final NPDES General Permits for Storm
Water
Discharges
from
Construction Sites,” Federal Register,
September 9,
1992.
(Baseline
Construction
General
Permit).
•
“Final NPDES Storm
Water Multi-Sector General Permit for
Industrial
Activities,” Federal Register,
September 9,
1992.
(Multi-Sector General
Permit).
Monitoring
Combined Sewer
Overflows
and
Sanitary Sewer
Overflows
EPA’s
CSO
Control Policy
(59
FR
18688) requires monitoring to characterize
the
combined
sewer system, assist
in
developing the
Long-Term Control Plan
(LTCP),
and illustrate compliance with
permit requirements.
Monitoring as
part of the
nine
minimum controls (NMC)
is
done to develop an
initial system characterizationand~
includes analyzing existing
data
on
precipitation
events, on
the combined
sewer
system
and CSOs,
on water quality,
and conducting field
inspections.
As
part of the
LTCP,
a
permittee
is required
to develop a
more complete characterization
of the
sewer system
through
monitoring and modeling.
Finally,
to
illustrate
compliance with
the
permit
requirements,
the
permittee
is
required to conduct a
post-construction
compliance
monitoring program.
Specific monitoring
requirements of this
post-
construction
compliance monitoring
program will
be unique to each permittee~sLtCP
and should
be established as specific
monitoring conditions
in
the
individual
NPDES
permit.
These
monitoring
conditions
should
require
monitoring of
a
representative
number of CSOs
for
a
representative number of wet weather
events for certain
key
parameters along with
ambient water quality monitoring
to ascertain attainment
with
water quality
standards.
EPA is currently preparing eight guidance manuals on
various aspects of the
CSO
Control Policy,
including
one on
monitoring,
Combined
Sewer Overflows:
Guidance
for Monitoring and Modeling
(draft).37
A facility’s permit may also contain
monitoring
requirements for
sanitary sewer
overflows (SSOs).
These
would be developed
on
a
case-by-case basis.
37USEPA (1995).
Combined Sower Overflows—Guidance for Monitoring and Modeling.
(DRAFT).
EPA-832/R-95-005.
130
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Permit Writers’
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and Reporting Conditions
Chapter 7
Whole
Effluent
Toxicity
Monitoring
The
use of whole effluent toxicity (WET) testing
to evaluate
the
toxicity
in
a
receiving
stream
was
discussed in
Chapter 6.
The
biomonitoring
test procedures were
promulgated
in 40 CFR Part 136
on October
16,
1995 (60
FR
53529).
WET
monitoring
conditions
included
in permits should
specify the
particular biomonitoring
test to be
used, the
test species, required test endpoint, and QNQC
procedures.
EPA
has
published
recommended toxicity test protocols
in
four
manuals:
•
Methods for Measuring the Acute
Toxicity of Effluents and Receiving
Waters
to Freshwater and Marine Organisms.~
•
Short-Term
Methods for Estimating the
Chronic Toxicity of Effluents and
Receiving
Waters
to Marine and Estuarine Organisms.39
•
Short-Term Methods for Estimating
the Chronic
Toxicity of Effluents and
Receiving
Waters
to Freshwater Organisms.4°
•
NPDES Compliance
Monitoring
Inspector
Training:
Biomonitoring.41
Samples for WET
may
be composite or grab
samples.
Twenty-four
hour
composite
samples
are suggested except when
(1) the
effluent is expected to be
more toxic
at a
certain time
of day;
(2)
toxicity may be
diluted
during
compositing; and
(3) the
size of the
sample needed exceeds
the
composite sampler volume (e.g.,
5
gallons).
WET tests are
relatively expensive
(see
Exhibit 7-3
on
costs).
Therefore
the
test frequency should
be related to
the
probability of any discharger having whole
~USEPA(1991).
Methods
for Measuring the Acute
Toxicity of Effluents and Receiving
Waters
to
Freshwater and Marine Organisms
39USEPA (1991).
Short-Temi Methods
for
Estimating the
Chronic
Toxicity
of Effluents and
Receiving
Waters
to
Marine and
Estuarine
Organisms.
EPA-600/4-91 -003.
Environmental
Monitoring
and
Support
Laboratory.
40USEPA (1991).
Short-Term Methods for Estimating
the
chronic Toxicity of Effluents and
Receiving
Waters
to
Freshwater Organisms,
Third Edition.
EPA-600/4-91 -002.
Environmental
Monitoring and Support
Laboratory.
41USEPA
(1990).
NPDES
compliance Monitoring Inspector Training:
Biomonitoring.
Office of
water.
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131
Chapter 7
Monitoring and Reporting
Conditions
effluent toxicity.
Samples should
be evenly spaced throughout the
year so that
seasonal
variability can
be ascertained.
Municipal
Sludge
Monitoring
The
purpose of monitoring municipal sludge
is
to ensure
safe use or disposal.
The
40 CFR Part 503 sludge
regulations require
monitoring of sewage
sludge tat
is
applied to land,
placed
on
a
surface
disposal site, or incinerated.
The
frequency
of
monitoring is
based
on
the
annual
amount of sludge
that
is
used or disposed
by these
methods.
POTWs that provide
the
sewage sludge to another
party for further
treatment (such
as composting) must
provide that
party with
the
information
necessary
to comply
with 40 CFR Part 503.
Sewage sludge disposed
of in
a
municipal solid
waste
landfill unit must meet the
requirements
in
40 CFR Part 258,
which
is
the
criteria
for
municipal solid waste landfills.
Exhibit
7-4 shows
the
minimum monitoring requirements for
sewage sludge
prior to use and disposal
established
in
40 CFR
Part 503.
More frequent monitoring
for any of the
required or recommended parameters
is appropriate when
the
POTW:
•
Influent load of toxics
or organic solids
is highly variable
•
Has a
significant industrial
load
•
Has a
history of process upsets
due
to toxics, or of adverse environmental
impacts due
to
sludge
use or disposal activities.
The sampling
and analysis methods specified
in
40 CFR §503.8 should
be
followed for monitoring the
required parameters.
in
the absence of any specific
methods
in
40 CFR Part 503.
guidance on appropriate
methods is
contained
in
Part 503 Implementation Guidance,42
Control of Pathogens and Vector
Attraction in
Sewage
Sludge,43
and
POTW Sludge Sampling
and Analysis
Guidance
Document.TM
42USEPA
(1995).
Part 503 Implementation Guidance.
EPA 833-R-95-001.
Office of Water.
43USEPA
(1992).
Control of Pathogens and VectorAttraction in Sewage
Sludge.
EPA-625/R-92-
013.
Office of Research
and
Development.
“USEPA
(1989).
POTW Sludge Sampling and Analysis Guidance Document
Office of Water,
Permits Division.
132
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Chapter
7
EXHIBIT
7-4
Minimum
Requirements for Sewage Sludge
Monitoring,
Based on Method of
Sludge Use or Disposal
Method
Monitoring
Requirements
Frequency
Citation
Land
Application
.
(1) Sludge weight and
total
solids
Metals:
As,
Cd,
Cu,
Pb,
Hg, Mo,
Ni,
Se,
and Zn
Pathogen Reduction
Vector Attraction Reduction
(1)
0
and
C
290k,
annually
290
and
C
1,500,
quarterly
1,500
and
C
15,000,
bimonthly
15,000
=
or
C,
monthly
40 CFR
Part
503.16
Co-disposal
in Municipal
Solid
Waste
Landfill
(1)
Sludge
weight and
total
solids
(2)
Passes
Paint-Filter Liquid
Test
(3)
Suitability of sludge
used
as
cover
(4)
Characterize in
accordance
with hazardous waste
rules
(1),
(2),
(3),
and
(4)
Monitoring requirements
or
frequency not
specified by
40
CFR Part 503.
Determined
by
local
health
authority
or
landfill
owner/operator
40
CFR
Part 258.28
Surface
Disposal:
Lined
Sites
with
leachate
collection and
Unlined Sites
(I)
Sludge
weight and
total
solids
Pathogen
Reduction
Vector Attraction Reduction
Metals: As, Cr, Ni (Unlined
Sites
Only)
(2) Methane gas
(1)
Based
on
sludge
quantity
(as above)
(2)
Continuously
40
CFR
Part
503.26
Incineration
(1) Sludge weight and
total
solids
Metals:
As, Cd, Cr, Pb, and
Ni
(2)
Be
and
Hg
(Nat.
Emissions
Standards)
(3)
THC or CO,
02, moisture,
combustion temperatures
(4) Air pollution control
device
operating_parameters
(1)
Based on
sludge quantity
(as above)
(2) As required by
subparts
C
andEof4OCFRPart6l
as
may be specified by
permitting authority
(local
air authority)
(3)
Continuously
(4)
Daily
40
CFR
Part 503.46
Notes:
3.
Monitoring
frequencies
required
under 40
CFR Part
503
may
be reduced after 2
years of monitoring,
but in no
case
shall
be
less
than once per
year.
2.
A
successful
land application
program may
necessitate
sampling
for other constituents of concern
(such
as
nitrogen)
in determining
appropriate
agronomic rates.
This wilt
be
determined by
the
permit
writer.
D
ry
weight
of
sludge
in
metric tons per year.
&~
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133
Chapter 7
MonItoring and Reporting Conditions.
7•2
Reporting
and Recordkeeping
Requirements
The
NPDES regulations at 40 CFR §~122.41(l)(4)(j)and
(I)
require
the
permittee
to
keep
records and periodically report on monitoring activities.
Discharge
Monitoring
Reports (DMR5)
(see
form
in
Exhibit
7-5)
must
be
used
by
permittees to
report self-monitoring
data.
Data
reported
include both
data
required by the
permit
and any additional
data
the
permittee
has collected
consistent with
permit
requirements.
All facilities
are required
to submit
reports
(on discharges and
sludge
use or disposal) at least
annually
per 40 CFR §122.44(i)(2).
POTW5 with
pretreatment
programs are required to submit
a
pretreatment report at
least annually
per Section 403.12(i).
However, the
NPDES
regulation
states that monitoring
frequency and
reporting
should be dependent on
the nature and
effect of the
discharge/sludge use or disposal.
Thus,
the
permit writer can
require
more frequent
than
annual
reporting.
Records
must be
kept by the
permittee
for at least
3 years and this
time
may
be extended
by
the
Director upon request.
An exception
is for
sewage sludge
records
which
must
be
kept
5
years or
longer
if required
by 40 CFR Part 503.
The
permit
writer should
designate where
records
should
be
located.
Monitoring records
include:
•
Date,
place, time
•
Name of sampler
•
Date of analysis
•
Name of analyst
•
Analytical methods
used
•
Analytical
results.
According
to 40 CFR §122.41(j),
monitoring
records must
be representative of
the
discharge.
Records
which
must be
retained include continuous strip chart record-
ings,
calibration
data,
copies of all
reports for the
permit,
and copies of all
data
used
to compile reports and applications.
Sludge regulations under 40 CFR
§~
503.17,
503.27, and
503.47 establish
recordkeeping
requirements that vary depending on
the
use and disposal method for the
sludge.
The same
recordkeeping requirements
should
be applied to other sludge
monitoring parameters not regulated
by the
40 CFR
Part
503
rule.
134
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Chapter
7
a
t
C
—o
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C?
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U
It
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Permit Writers’
Manual
-
135
Chapter
11
Administrative
Process
Previous discussions
in
this
manual focused
on
the
process of developing
NPDES permit conditions
and effluent limits.
This
chapter describes
the administrative
process that
is
associated
with
the
issuance
of
a
NPDES permit.
Exhibit 11-1
provides
a
flow diagram of the
NPDES
permit administrative
process.
In general, the
administrative
process
includes:
•
Documenting all
permit decisions
•
Coordinating
EPA and State
review of the
draft permit
•
Providing
public notice,
conducting hearings
(if
appropriate),
and responding
to comments
•
Defending
the
permit and modifying
it
(if necessary)
after issuance.
Note
that Exhibit
11-1
provides
the general framework for
both
EPA
and State
NPDES
permit
administration.
State
requirements need
not
be identical
to
Federal
regulatory
requirements,
provided they are
as
stringent.
Therefore,
some delegated
States may
have slightly different processes
for developing and issuing NPDES permits.
In
addition,
the
evidentiary hearing
and appeal
process
presented depicts
EPA
procedure.
State
procedures for NPDES
permit hearings and appeals may vary
according to State
law.
6~
NPDES
Permit Writers’
Manual
-
191
Chapter
11
Administrative Process
EXHIBIT
11-1
NPDES Permitting
Administrative Process
Significant EPA
Gonm,entW
No State 401
certification
Denied
Develop draft pemiit
limits and conditions
Significant,
Widespread,
Public Interest
l~ol
Opportunity
for Informal
appeal
to the
nvironrnental Appeals Board
No
Appeal
No
Appeal
192
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&B~°
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Permit Writers’
Manual
Administrative Process
Chapter
11
11,1
Documentation
For Development
of the Draft
Permit
When the
permit
is
issued, the
fact sheet and supporting
documentation
(administrative
record) are the
primary support for defending
the
permit
in
administrative
appeals and evidentiary
hearings.
The
process of documenting
the
permit
requires the
permit writer
to be organized
and logical throughout
the
permit
development
process.
Some of the
content of the
fact sheet and administrative
record
is-directed
by Federal
and State
regulation
and the
rest
is dictated by good
project
management.
Permit writers
should
recognize
the
importance
of:
•
Ensuring
development of
a thorough
permit
in
a
logical fashion
•
Meeting
legal requirements for preparation of an
administrative
record,
fact
sheet,
and statement
of basis
•
Helping to
substantiate
permit decisions
and provide
a
sound
basis
in
case
challenges
are made
to
the
derivation of permit terms,
conditions,
and
limitations
•
Establishing
a
permanent
record of the
basis of the
permit for
use
in
future
permit actions.
The following
sections describe the
requirements
pertaining
to the development
of permit documentation,
particularly the
administrative
record and the fact sheet.
11.1.1
Administrative
Record
The
administrative
record
is
the
foundation for issuing
permits.
If
EPA is
the
issuer,
the
contents of the
administrative record are
prescribed by regulation
(see 40
CFR §~1
24.9
and 124.18).
All supporting materials must
be
made available
to the
public, whether
a
State, Territory,
Tribe or EPA
issues the
permit.
The
importance of
maintaining
the
permit records
in
a
neat,
orderly,
complete,
and retrievable.form
cannot
be over emphasized.
The record allows
personnel
from
the
permitting
agency
to reconstruct
the justification for a
given
permit.
It also
must
be
made
available
to the
public at any time and
may be
examined
during
the
public comment period and any
subsequent
public hearing.
The
administrative
record
for a
draft
permit
consists, at a
minimum, of certain
specific
documents
as shown
in
Exhibit
11-2.
Materials
that are readily available
in
the
permit
issuing
office or published
material
that
is generally available, does
not
6~
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Permit Writers’
Manual
-
193
Chapter
11
Administrative Process
EXHIBIT 11-2
Elements of the
Draft NPDES Permit Administrative
Record
•
Application
and
supporting
data
•
Draft
permit
•
Statement of basis
or fact sheet
•
All
items cited
in the
statement of basis
or
fact sheet,
including calculations
used to
derive
the permit
limits
•
All
other items
in the
supporting
file
•
For new
sources,
any
environmental
assessment,
the
draft/final
enviromnental
impact
statement
(EIS),
or other such
background
information,
such
as
a
Findings of No
Significant
Impact
(only applies if EPA
issues the
permit).
need to
be physically included with
the
record as long as it is specifically referred
to
in
the
fact sheet or statement
of basis.
If
EPA
issues new source
draft
permits,
the
administrative record should
include any EIS or environmental
assessment
performed
in
accordance with
40 CFR §122.29(c).
The
administrative
record should
include
all
meeting reports and
correspondence
with
the
applicant
and correspondence
with other regulatory agency
personnel.
In
addition, trip
reports and telephone
memos should
be included
in
the
record.
All correspondence,
notes,
and calculations
should
indicate the
date
and the
name of the
writer, as well
as
all
other persons
involved.
Since
correspondence
is
subject to public scrutiny,
references or comments that do
not serve
an objective
purpose should
be
avoided.
Finally,
presentation of calculations and documentation
of
decisions
should
be organized
in
such a
way that they can
be reconstructed and the
logic supporting the
calculation or decisions
can
easily be found.
The
administrative
record for the
final permit consists of the
items
in Exhibit
11-3.
11.1.2
Fact
Sheets
and
Statements of Basis
A fact sheet
is
a
document that briefly sets forth
the
principle
facts
and the
significant factual,
legal,
methodological,
and policy
questions considered
in
preparing
the
draft
permit.
When the
permit
is
in the
draft
stage,
the
fact sheet and
supporting
documentation
serve to explain to the
permittee
and the general public the
rationale
and assumptions used
in
deriving the
limits.
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EXHIBIT
11-3
Elements of the
Administrative
Records
for
a
Final Permit
•
All
elements
for the
draft permit
administrative
record (see
Exhibit
11-2)
•
All
comments
received
during
the comment period
•
The
tape
or
transcript
of any public
hearing
•
Any materials
submitted
at
a hearing
•
Responses
to
comments
•
For NPDES
new source permits,
the draft
or
final
EIS
•
The
final permit.
The
NPDES
regulations set
forth
in 40 CFR §124.8(a) require that every EPA
and State-issued
permit
must be accompanied by
a
fact sheet if the
permit:
•
Involves
a
major
facility or activity
•
Incorporates
a
variance
or requires an explanation
under 40 CFR
§124.56(b) (toxic
pollutants,
internal
waste stream, and indicator
pollutants
and for
privately
owned
waste treatment facilities)
•
Is
a
NPDES
general
permit
•
is
subject to widespread
public interest
(see 40 CFR §124.8)
•
Is
a
Class
1
sludge management facility
•
Includes
a
sewage sludge
land
application
plan.
EPA
permit writers
are
required to prepare
a
statement of basis for all
permits
that do
not
merit the
detail of a fact sheet.
Such statements
briefly describe
the
derivation
of the
effluent limits and the
reasons for special
conditions
(see
40 CFR
§124.7).
However,
a
prudent
permit writer will develop
a fact sheet for any permit that
required
complex calculations or special
conditions.
This
will
be particularly true for
permit
conditions based
on
BPJ.
With
a well-documented rationale for all
decisions,
much of the
work
in
reissuing
a
permit in
the
future will
be done.
This will
avoid
any conjecture and
guessing
concerning the
development
of any conditions
that are being carried forward
from
the
expired permit
to
the
next
permit.
This
is also true
if a
modification
is
initiated during
the
life df the
permit.
A permit
rationale can be as short as
two to
three pages for a
relatively
simple
permit or as long as 20 to
100 pages for an
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extremely complicated
permit (e.g.,
several discharge points,
many
BPJ
determinations).
The
required contents of a fact sheet,
as specified
in
40
CFR
§~124.8
and 124.56,
include the
items
listed
in Exhibit
11-4.
EXHIBIT
11-4
Required
Contents of a
Fact
Sheet
.
A
brief description of the type
of facility or activity
that
is
being regulated
by
the
NPDES permit
•
The
type
and quantity of pollutants
discharged
•
A
brief
summary
of the
basis
for the
draft
permit conditions,
including
references
to the
applicable
statutory
or regulatory provisions
•
Name
and
telephone
number
of person to contact
for additional
information
•
Provisions satis~ingthe requirements of 40
CFR
§
124.56:
—
Explanation of derivation of effluent
limitations
—
Explanation of any conditions
applicable
to
toxic, internal
waste
streams, or indicator
pollutants
—
A
sketch or detailed description of the location of the discharge
—
For EPA
issued permits, the
requirements of any State
certification
•
For every
permit
to be
issued
to
a
treatment
works owned by
a person other than
a
State
or municipality,
an explanation of the
decision to
regulate the
users
under a
separate
permit
•
For every permit
that includes
a sewage
sludge
land application plan,
a brief description
of how
each of the
required elements of the land
application plan
are addressed
in
the
permit
•
If applicable, reasons why
any
requested
variances
do
not appear justified
•
A
description of the
procedures
for reaching a
final decision on
the
draft permit,
including:
—
The dates of the
public
comment period
and
the
address
—
Procedures for requesting a hearing
—
Other procedures
for public
participation.
A detailed discussion of the development of permit
limits for each
pollutant
should
be included
in
the
fact sheet.
For some permits,
a
considerable amount of
time
is spent within
the
permitting
agency debating
a
permit issue
that then becomes
an assumption
upon which
the
permit conditions
are based.
Documenting
the
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decision
process may prevent a
repeat of the
debate
in
5 years when
the
permit is
up
for
reissuance.
For each
pollutant the
following information
is
necessary:
•
Calculations
and assumptions
—
Production
—
Flow
•
Type
of limitations (i.e.,
effluent guideline-, water quality-, or BPJ-based)
•
Whether the effluent guidelines
used
were
BPT, BCT, or BAT
•
The
water quality
standards
or criteria
used
•
Whether any pollutants were
indicators
for other pollutants
•
Citations to appropriate wasteload
allocation
studies, guidance documentsr
other references.
Often,
it
is
as important to keep
a
record of items
that were not
included
in
the
draft
permit,
such as the following:
•
Why was
BPJ or effluent guidelines
used
instead of water quality-based
limitations (i.e.,
were the
limitations checked
to
see that water quality
considerations did
not govern the
setting of permit
limits)?
•
Why
was
biomonitoring
not included?
•
Why
were pollutants that were
reported
as present
in
the
permit application
not specifically limited
in
the
permit?
•
Why
is
a
previously
limited pollutant
no
longer
limited
in
the
draft permit?
Finally,
the
fact sheet should
address
the
logistics of the
permit
issuance
process including
the comment period
begin and end dates,
procedures for
requesting
a
hearing, and the
public involvement
in
the final decision.
11.2
Items
to Address
Prior to Issuance
of
a Final
Permit
This section
describes
the
public participation
activities
that must
be conducted
in
the
permit
issuance
process.
These
include providing
public notices, collecting
and
responding to public comments, and holding
public hearings as necessary.
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11.2.1
Public
Notice
The public notice
is
the
vehicie for informing
all
interested
parties
and members
of the
general public of the
contents of a
draft
NPDES
permit or of other significant
actions
with
respect to
a
NPDES permit
or permit application.
The
basic
intent of this
requirement
is
to ensure that all
interested
parties
have an opportunity to comment on
significant actions
of the permitting
agency with
respect
to
a
permit application
or a
permit.
The
exact
scope,
required contents,
and methods for effecting public notices
may
be
found
in
40 CFR §124.10.
The
NPDES permit-related
actions that must
receive public notice are shown
in
Exhibit
11-5.
EXHIBIT
11-5
Actions
That Must
Receive
Public
Notice
•
Tentative
denial of an
NPDES permit
application (not necessarily
applicable to
State
programs)
•
Preparation ofa
draft NPDES permit,
including
a
proposal
to terminate
a permit
•
Scheduling
of a public hearing
•
Granting of an evidentiary
appeal
of
an
EPA-issued permit under 40
CFR
§
124.74
•
Formal
appeal of permit
•
New
Source
Determinations (EPA only)
The permit writer should
be
primarily concerned with
the
first three items
in
Exhibit
11-5.
it
is
important to riotp
that
no public notice
is required when
a
request
for
a permit
modification, revocation, reissuance, or termination
is denied.
Public notice of the
various NPDES-related activities
is provided by the
following methods:
•
For major permits,
publication of
a
notice
in
daily or weekly newspaper
within
the
area
affected
by the facility or activity.
In addition,
for general
permits issued by
EPA, publication
in
the
Federal Register
is
required.
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•
Direct mailing
to various
interested
parties.
This mailing list should
include
the
following:
—
The
applicant
—
Any
interested
parties
on
the
mailing
list
—
Any other agency that
is
required
to
issue
a
Resource Conservation
and Recovery Act,
Underground
injection Control, Corps of Engineers,
or
PSD permit for the
same facility
—
All appropriate government authorities
(e.g.,
United States Fish and
Wildlife Services,
National Marine
Fisheries Service, neighboring
States)
—
Users identified
in
the
permit application
of a
POTW.
A public notice
must
contain the
information shown
in Exhibit
11-6.
EXHIBIT
11-6
Contents of the
Public Notice
•
Name
and address of the
office processing
the
permit
action
•
Name and address of the
permittee
or
applicant and, if different,
of the
facility
regulated
by the
permit
• A brief description of the business conducted at
the
facility
•
Name, address, and telephone number of a contact from whom interested
persons
can
obtain additional information
•
A brief description of the comment procedures required
•
For EPA-issued permits, the
location
and
availability of the administrative record
•
Any
additional
information
considered
necessary.
Public notice of the
preparation of the draft
permit
(including a
notice of intent to
deny a
permit
application)
must allow
at least 30 days for public comment.
The
draft
permit
is usually submitted for public
notice after
it has undergone
internal
review
by
the
regulatory agency that is
issuing
the
permit.
State/Tribal
issued
permits will
typically
undergo public notice after
EPA has reviewed
and commented on
the
draft
permit.
In the special
case of those EPA-issued permits that require an
environmental
impact
statement (ElS),
public notice
is
not
given
until
after
a
draft
EIS
is
issued.
11.2.2
Public
Comments
Public notice of a
draft
permit
elicits
comments from
concerned individuals or
agencies.
Frequently,
such
comments are simply requests for
additional information.
However,
some comments are of a
substantive nature and suggest
modifications to
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the
draft
permit
or indicate that the draft
permit
is inappropriate for various reasons.
In
such
cases, those parties
providing comments must submit all
reasonable arguments
and factual
material
in
support of their positions.
If the
approach
is technically correct
and clearly
stated
in
the fact sheet,
it will
be difficult for
commenters to find fault with
the
permit.
Commenters
may always suggest alternatives,
however.
In addition,
an
interested
party may also request a
public hearing.
-
To
the
extent possible,
it is desirable to respond to
all
public comments as
quickly as possible.
In some cases it may
be possible to diffuse a
potentially
controversial
situation
by providing further explanation of permit terms
and conditions.
It
is also good
public practice to
inform
parties
who provide public comments that their
comments have been
received
and are being considered.
The
permitting
agency
is obliged
to
respond to
all
significant comments
(in
accordance
with
40 CFR §124.17)
at the
time
a final permit decision
is
reached (in
the
case of EPA-issued permits) or at the
same time
a
final permit is
actually
issued (in
the
case of State-issued
permits).
The
response should
incorporate
the following
elements:
•
Changes
in
any of the
provisions of the
draft permit
and the
reasons for the
changes
•
Description
and response
to
all
significant comments on
the
draft
permit
raised
during the
public comment period
or during
any hearing.
In the
event that any information submitted
during
the
public comment
period
raises substantial
new questions
about the draft
permit, one of the following
actions
may occur:
•
A new draft
permit
with revised fact sheet or statement
of basis
is
prepared.
•
A final permit with
necessary
changes
explained
is
issued.
•
The
comment period
is
reopened
but is
limited only to new findings.
if any of these actions are
taken,
a
new public notice,
as described earlier, must
be
given.
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11.2.3
Public
Hearing
A public hearing
may be requested
in writing
by any
interested
party.
The
request should
state the
nature of the
issues proposed
to be raised
during
the
hearing.
However,
a
request for
a
hearing
does not automatically
necessitate that
a
hearing
be
held.
A
public hearing
should
be held
when
there
is
a
significant amount
of interest expressed during
the
30-day public comment
period
or when
it is
necessary
to
clarify the
issues involved
in
the
permit
decision.
Thus,
the
decision of whether or not to hold
a
public hearing
is
actually
a
judgment call.
Such decisions
are
usually
made
by someone other than
the
permit
writer.
However,
the permit writer will
be responsible for ensuring that
all
of the
factual
information
in
support of the
draft
permit is
well
documented.
Public notice of a
public hearing
must
be given
at
least 30 days prior
to the
public meeting
(public notice of the
hearing
may
be
given
at the
same time
as public
notice of the
draft
permit
and the two
notices
may
be combined).
Scheduling
a
hearing automatically
extends the
comment
period
until at least
the
close of the
hearing
40
CFR §124.12(c).
The
public notice of the
hearing
should
contain
the
following information:
•
Brief description of the nature and
purpose of the
hearing,
including the
applicable
rules and procedures
•
Reference
to the
dates of any other public notices
relating to the
permit
•
Date,
time,
and place of the
hearing.
A presiding officer
is
responsible for the
hearing’s
scheduling
and orderly
conduct.
Anyone
may submit written or oral comments concerning the
draft
permit
at
the
hearing.
The
presiding officer
should
set reasonable
time limits for oral
statements.
The public comment period
may
be extended
by so stating
during
the
hearing,
It
should
be
noted
that
a
transcript
or
recording
of the
hearing
must
be
available
to interested
persons.
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11.2.4
State/Tribal
Roles
in Reviewing Draft Permit
State/Tribal
issued draft permits
must
be submitted
to
EPA for
review if they
relate to:
•
Discharges
into the
territorial seas
•
Discharges that may affect waters of
a
State
other than
the
one
in
which
the discharge originates
•
General
permits
•
Discharges from
a
POTW with
a
daily average discharge exceeding
1
million gallons
per day
•
Discharges of uncontaminated cooling
water with
a
daily average discharge
exceeding
500 million gallons
per day
•
Discharges from
any major discharger or from
any NPDES primary
industrial
category
•
Discharges of from
other sources with
a
daily average discharge exceeding
500,000 gallons
per day (however.
EPA may waive
review for
non-process
wastewater),
and
-
Class
I
sludge
management facilities.
Permits
issued
by EPA
require State/Tribal
review
and certification
under
Section
401
of the
CWA.
Such certification ensures that
the
permit will
comply with
applicable
Federal
CWA standards
as
well as with
State
or Tribal water quality
standards.
This State/Tribal
certification
also ensures that State and Tribal
initiatives
or policies are
addressed
in
EPA-issued
NPDES permits, and functions to promote
consistency between
State- and EPA-issued permits.
Under CWA Section 401(a)(1),
EPA may
not
issue
a
permit
until
a
certification
is
granted
or waived.
If EPA is
preparing
the draft
permit, State
certification
is
usually
accomplished
by allowing States to review and certify
the
application
prior to
draft
permit preparation.
Regulations
in
40 CFR §124.53 State
Certification
and §124.54
Special
provisions for State
certification and concurrence
on
applications for section
CWA
301(h) variances
describe
procedures
a
permit
writer should follow to obtain
State or Tribal
certification.
Under 40 CFR §124.53, when
a
draft
permit
is
prepared
by
EPA, but
State
certification has not yet
been granted,
EPA must
send
the
State a
copy of the
draft permit along with
a
notice requesting State
certification.
If the
State
does
not
respond within 60 days,
the
State
is deemed to
have waived
its
right to
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certify.
if the
State chooses
to certify
the
draft
permit, the
State
may only require
changes
to the
draft permit
to incorporate
more
stringent State
laws.
If the
State
requires such
changes, the
State
must send
EPA a
letter justifying the
changes
and
citing
State
regulations that support
the
changes.
When a
permit applicant
requests
a
CWA
Section
301(h) variance, the
State
certification process
is very similar to the
process just described for
permit
applications and draft
permits
(refer
to Section 40
CFR §124.54).
11.2.5
Schedule
for
Final
Permit Issuance
The final permit
may
be
issued
after the
close of the
public notice
period
and
after State/Tribal
certification has been received
(for permits issued by
EPA).
The
public notice
period includes:
•
A
30-day period
that gives notice of intent to
issue
or deny the
permit
•
A 30-day period
advertising
a
public hearing
(if applicable)
•
Any
extensions or reopening of the comment period.
Final
EPA
permit decisions
are effective
immediately upon issuance
unless
comments
request changes
in the
draft
permit,
in
which
case
the
effective
date of the
permit
is
30 days
after
issuance
(or
a
later
date
if specified
in
the
permit).
As
discussed earlier,
any comments that are received
must be answered
at the
time of
final permit
issuance
(in
the case of NPDES
States or Tribes)
or after
a
final decision
is reached
(in
the
case of EPA).
11.3
Administrative
Actions
After
Final
Permit Issuance
Once
the final
permit has been issued,
the
issuing
authority should
integrate
the
permit limitations and any special conditions
into the
NPDES tracking system
(i.e.,
the
permit compliance system
(PCS)).
This
will
ensure that the facility’s
performance will
be tracked and the
permitting
agency will
be alerted to
the
need for corrective
action
in
the
event of violations
of permit limitations,
terms,
or conditions.
After final permit
issuance, interested
parties have
other opportunities to
change
the
permit thorough permit appeals,
major/minor permit modifications,
permit
termination or permit
transfer.
These
administrative
procedures are described
below.
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11.3.1
Permit Appeals
In the
process of developing
a
draft
permit and during
the public notice period,
the
permit writer should
carefully
consider the
legitimate concerns of the
permittee as
well
as the
concerns of any third
party who may have
an interest
in the
permit
terms
and conditions.
However, there will
inevitably
be situations
in
which
a
permit is
issued
in
spite of the
objections of the
permittee
or a
third
party.
In such
instances,
the
permittee
or an
interested
party may choose to legally contest or appeal
the
NPDES
permit.
Various
mechanisms are available
to resolve legal
challenges to NPDES
permits.
In the case of EPA-issued permits,
the
administrative
procedure involved
is
called an evidentiary hearing.
Many NPDES States and Tribes
have similar
administrative
procedures designed to
resolve challenges to the
conditions of a
permit.
These
procedures
involve hearings
presided over by an administrative law judge.
For
the
sake of convenience, these
hearings will
hereafter
be referred
to as evidentiary
hearings.
They will
naturally
be
known
by different names in
different State or Tribe
jurisdictions.
However, permit writers
will, from
time-to-time, be involved
in
permit
appeals and will
need to address
the types of issues discussed below.
Aside from
preparation
of the administrative
record and notices, the
permit
writer may
not
be concerned with
procedural
matters relating to evidentiary hearings.
All requests
for evidentiary hearings are
coordinated through
the
office of the
EPA
Regional
Counsel
or
the
appropriate State
legal
personnel.
The
permit writer’s
first
involvement with
the
hearing process will
come as
a
result of designation of the
trial
staff and his/her role will
be
limited
to that of a
witness and technical
advisor to legal
counsel.
A permit writer may be required
to
give a
deposition during
which
the appellant
attorney conducts the
questioning that would otherwise occur in the
hearing.
The
deposition
is
transcribed
and presented as evidence.
The appellant attorney may
ask
some of the
same questions at the
hearing.
To
prepare for
a
deposition and testimony,
the
permit writer should
be familiar
with
those laws,
regulations,
and policies that may affect the
permit.
The
permit writer
should
be thoroughly familiar with
the technical
basis for the
permit
conditions.
For
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example, if the
effluent limits
are based on water quality requirements, the
permit
writer should
thoroughly study
any applicable
basin
plan
or water quality
simulation
used
to develop
the
effluent limits and
be
prepared
to defend any assumptions
inherent
in
the
plan
or simulation.
If
BPJ limits
are based
on
proposed
effluent
guidelines,
it will
be necessary
to carefully
review
not
only the
guidelines themselves
but
all
applicable
data, including
the development
document for
the
specific
guidelines.
The
technical
defense of other BPJ
requirements
is much more difficult.
The
permit
writer should
be sure that
(1)
the
information
on which
BPJ
limits are based
are
unimpeachable,
(2) the
limits were
derived from the
data
in
a
logical
manner,
in
accordance with
established procedures,
and
(3) the
BPJ limits so derived are
technically sound
and meet BCT
or BAT standards for economic reasonableness.
As
technical
advisor to legal
counsel,
the
permit writer’s
most
important function
is to
develop direct testimony
in
support of contested permit conditions.
No attempt
should
be
made
to support technically indefensible conditions.
Contested
permit
conditions
that are not technically defensible
and are not
based on any legal
requirement should
be brought to counsel’s
attention,
with
advice that EPA or the
State
agency withdraw
those conditions.
The
second most
important advisory
function
of the
permit
writer is
assisting
counsel
in
the
development
of questions for cross-examination of the
opposing
witnesses.
Questions should
be restricted
to the
subject
material covered
by the
witness’
direct
testimony
and
should
be designed to
elicit an
affirmative or negative
response,
rather than
an essay-type response.
If a
question
must
be phrased
in such
a
way
that the
witness could
attempt
lengthy explanations,
counsel should be
forewarned.
Finally,
the
permit writer should
remember that
in
requesting an evidentiary
hearing, the
permittee
has declared an adversary
relationship
with
the
regulatory
agency,
and the
permit writer must
therefore refrain from
discussions
about the
case
without
prior consultation with
legal counsel.
In the
role of witness and/or technical
advisor,
the
permit writer should:
-
Cultivate credibility
•
Never imply
or admit weakness
in
his or her area
of expertise
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Chapter
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Administrative Process
•
Never attempt to testify about subjects outside
his or her area
of expertise
-
Always
maintain
good communication
with
counsel.
Where
the
permitee
is granted
relief at the evidentiary
hearing, the
Administrative Law Judge generally will
order appropriate relief.
Where
a
request for
an evidentiary hearing is
denied,
the
permittee
may file a
notice of appeal
and petition
for review with
the
Environmental Appeals Board
(EAB), which
may or may not
grant
an
evidentiary hearing based
on
the
factual
and legal
issues alleged.
Similarly, where
a
permittee
is
denied
relief at an evidentiary hearing, the
permittee
may appeal
to
the
EAB
to overturn the
hearing
decision.
Finally,
under certain
circumstances
decisions
of the
EAB
against the
permittee
may
be appealed
in
Federal court.
11.3.2
Permit Modification, Revocation,
Termination, and Transfer
After
the final permit
is
issued,
the
permit may
still
need to
be
modified or
revoked
prior to the
expiration date.
Modifications differ from
revocations
and
reissuance.
In
a
permit modification, only the
conditions
subject to change are
reconsidered while
all
other
permit
conditions remain
in
effect.
Conversely,
the
entire
permit may be reconsidered
when
it is
revoked
and
reissued.
A permit modification
may be triggered
in
several ways.
For example,
a
representative of the
regulatory
agency may conduct an
inspection of the
facility that
indicated a
need for the
modification
(i.e.,
the
improper classification
of an
industry), or information submitted
by the
permittee
may suggest the
need for a
change.
Of course,
any interested
person may request that
a
permit
modification
be
made.
There are two
classifications of modifications:
major
and minor.
From a
procedural standpoint, they differ primarily
with
respect to the
public notice
requirement.
Major modifications
require public notice; minor modifications do
not.
Virtually all
modifications that result
in
less stringent conditions
must be treated
as major modifications,
with
provisions for public notice and comment.
Generally
speaking,
a
permit will
not need to be modified
during
the term of the
permit
if the
facility
can fully comply
with
permit conditions.
Conditions that would necessitate
a
major modification of
a
permit are described
in
40 CFR §122.62 and shown
in
Exhibit
11-7.
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EXHIBIT
11-7
Conditions
Requiring Major Modification
•
Reopener—Conditions in the permit
that
required
it
to be reopened under certain
circumstances.
•
Technical
Mistakes—To correct technical
mistakes
or mistaken interpretations
of law
made
in developing the permit conditions.
•
Failure to
Notif~’—Uponfailure
of
an
approved
State
to
notify
another
State whose
waters
•
may be affected by a discharge from the approved State.
•
Alterations—When alterations or changes in operations occur that justify new conditions that
are
different from
the
existing permit.
-
New Information—When information
is received
that was
not
available at
the time
of permit
issuance.
New
Regulations—When
standards
or regulations
on which
the permit
was based
have been
changed by promulgation ofamended standards or regulations or by judicial decision.
-
Compliance
Schedules for Innovative
or Alternative
Facilities—To
modify the compliance
schedule
in
light of the additional
time
that may be required to
construct this type
of
facility;
or
when
good cause for modification
of
a compliance
schedule exists,
such
as
an
Act of God,
strike,
or
flood.
•
Pretreatment—To require
that an
approved program
be implemented
or to
change the
schedule for
program
development.
•
Failed
BPJ
Compliance—When
BPJ technology
is installed
and properly operated
and
maintained but the permittee is unable to meet its limits, the limits may be
reduced to reflect
actual
removal;
but in
no
case may
they be
less
than the guideline
limits.
If BPJ operation
and maintenance costs are totally disproportionate to the costs considered in a subsequent
guideline, the permittee may be allowed to backslide to the
guideline
limits.
Non-Limited Pollutants—When the level
of discharge of any
pollutant that
is
not
limited
in
the permit exceeds
the
level
that can
be
achieved by
the technology-based
treatment
requirements appropriate to the permit.
-
Variance
Requests—When requests for variances,
net effluent
limitations, pretreatment,
etc.,
are filed within the specified time but
not
granted until after permit
issuance.
•
Adjust limits
to
reflect net pollutant treatment—Upon request of a permittee
who
qualifies
for
effluent
limitations
on
a
net basis under 40
CFR §~122.45(g)and (h).
•
Insert
CWA §307(a)
toxic
or
40
CFR Part
503
sludge use/disposal
requirements.
-
Notification
Levels—To establish
notification
levels
for toxic
pollutants
that
are not
limited
in the permit but
must
be
reported
ifconcentrations in the discharge exceed these
levels.
Minor modifications
are generally
non-substantive changes
(e.g., typographical
errors that require
more stringent
permit conditions).
The conditions for
minor
modifications, described
in 40 CFR
§1 22.63,
are shown
in
Exhibit
11-8.
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EXHIBIT
11-8
Conditions
Requiring Minor Modification
•
Typographical
errors
must be corrected.
•
More frequent monitoring
or reporting is
necessary.
•
An
interim compliance date
in
the schedule of compliance
needs revision,
provided
the
new date
is not
more than
120
days after the
date specified
in the
permit
and
does
not
interfere
with
attainment of the
final compliance
date
requirement.
-.
Ownership
has
changed but no other change is
necessary.
•
The construction schedule for a new source discharger needs
revision.
•
A
point source
outfall that
does
not result in
the
discharge
of pollutants
from other
outfalls
must
be deleted
from
the
permit.
•
An
approved local
pretreatment program must be
incorporated
into
the
permit.
11.3.3
Termination of Permits
Situations
may arise during
the life
of the
permit that are cause
for termination
(i.e.,
cancellation,
revocation)
of the
permit.
Such circumstances include
the following
(see
40 CFR §122.62(b)):
•
Noncompliance
by the
permittee with
any condition
of the
permit
-
Misrepresentation
or omission of relevant facts by the permittee
-
A determination that the
permitted
activity endangers
human health
or
the
environment,
either
in
an emergency or other situation
•
A temporary or permanent
reduction
or elimination
of a
discharge
(e.g.,
plant closure).
Once
the
permit
is terminated,
it can
be
placed into effect again only by the
reissuance
process,
which
requires a
new permit application.
All of the
above
situations may also be addressed through
the
permit
modification
process on
a
case-by-case
determination.
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11.3.4
Transfer of Permits
Regulatory agencies will
occasionally receive
notification of
a
change
in
ownership of a
facility covered
by
a
NPDES
permit.
Such changes
require that
a
permit
be transferred
by one
of two
provisions:
•
Transfer by Modification
or Revocation—The transfer
may
be
made
during
the
process of modification, either major or
minor.
It
may also be
addressed by revoking
and
subsequently reissuing
the
permit.
•
Automatic
Transfer—A
permit
may
be automatically transferred to
a
new
permittee
if three conditions
are
met:
—
The
current
permittee
notifies the
Director 30 days
in
advance of the
transfer
date.
—
The notice includes
a written
agreement between
the
old
and new
owner on
the
terms of the transfer.
—
The
Director of the
regulatory agency does
not
indicate that the
subject
permit will
be
modified
or revoked.
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209
BEFORE THE ADMINISTRATOR
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
IN THEMAflEROF
ORANGE RECYCLINGANDETHANOL
PRODUCTION FACILITY, PENCOR-
MASADA OXYNOL, LLC
Permit ID: 3-3309-00101/00001
Facility NYSDEC ID: 3330900101
Issued by the New
York State
Department of Environmental Conservation
)
ORDER RESPONDING TO
)
PETITIONER’S REQUESTTHAT
THE ADMINISTRATOR OBJECT
)
TO ISSUANCE OF A
STATEOPERATING PERMIT
)
)
)
)
Petition No.:
11-2000-07
)
ORDER PARTIALLY GRANTING
AND PARTIALLY DENYING
PETITION
FOR OBJECTION TO PERMIT
TheNewYork
State
Department of Environmental Conservation, Region 3 (NYSDEC)
issued a state operating permit to
Pencor-Masada Oxynol, LLC on July 25, 2000, authorizing
construction of the Orange
Recycling and Ethanol
Production Facility (Masada))
The Masada permit
was issued pursuantto title
V of the Clean Air Act (CAA or the Act), 42 U.S.C.
§~
7661-7661f,
CAA
§~
501-507, the federal implementing
regulations, 40 CFR Part
70,
and
the
New York State
permitting
regulations. Between Juneand September, 2000, the Environmental
Protection Agency
(EPA) received 35
petitions
from29 differentpetitioners, requesting
that
EPA object to the issuance of
the Masada
permit.
Undersection 505(b) ofthe Act, EPA
may
object to the
issuance
ofa
permit if
the
Administrator finds
that
it is “not in compliance with the applicable
requirements
ofthe
Act,
including
the
requirements
ofan applicable
state
implementation plan.”
The Act
and
EPA’s implementing
regulations
provide that, ifthe
Administrator
does not objóct in
writing, “any person” may
petition the
Administrator to object to the permit.
CAA
§
505(b)(2); 40 CFR 70.8(d).
Pencor-Masada
Oxynol, LLC
is the corporate owner of the Orange Recycling and Ethanol
Production Facility to be built in Middletown, New York.
In the interests of clarity, this Order uses
the
term
“Masada” to
encompass both
the corporate owner and the
Middletown facility at issue here.
The phrase
“the Masada permit”
refers to the permit issued
by
NYSDEC
for the
Middletown facility.
EXHIBIT D
The
petitions with respect tothis facility raise a number
of
distinct
claims.2
For organizational
purposes, these
claims havebeen
divided
into
two categories,
the fust addressing administrative/public
participation issues and
the second
addressing technical/regulatory
issues. More specifleally, the
petitioners allege
that
the
NYSDEC
did
notcomply
with
the applicable public participation
requirements
in issuing
the
Masada permit because NYSDEC did
not:
(1) noti&the public ofthe
extended
opportunity
for comment;
(2)
make
available
to
the public
requisite information necessary to
review
the pem1it
(3)
offer the public an opportunity
tocomment on significant
changes
to
the draft
permit; (4) properly
inform
the public of
its right to
petition
to the EPAAdministrator,
(5)
substantively
reyiew
public comnents; (6)
grant
requests for a
second
public hearing, and
(7) translate
the public
notices and key documents
for the non-English
speaking members
of
the
community.
The
petitioners also assert that
the
Masada permit
did notcomply
with
the applicable
technical/regulatory requirements in that
the
permit:
(1) fails to assure
compliance
with major
source
preconstruction
permitting
requirements under the Act; (2) does
not assure compliance with several
allegedly applicable
federal
emissions standards, (3)
omits required provisions
governing
chemical
accident prevention
requirements,
namely section
112(r) of the
Act and EPA’s implementing regulations
at 40 CFR
Part
68, and
(4) does notcomply with the
Executive Order 12898
on
environmental
justice.
The petitioners have requested
that
EPA object to the issuance ofthe Masada
permit pursuant to
§
505(b)(2) ofthe Act
and
40 CFR 70.8(c) for these reasons.
EPA has performedan independent
review
ofthe petitioners’ claims. Based on reviewof
all
the information before me, including the
Masada
permit ofJuly 25, 2000, the
permit application, and
the
infommtion
provided by the petitioners
in the petitions, I hereby
grant
the
petitions
in part, and deny
in
part
In sum, lam
granting the petitions
insofar
as they
claim that (1) NYSDEC
must
provide an
opportunity
for public review ofselected portionsofthe final
operating
permit issued to Masada,
and
(2)
that
applicable
reporting
and recordkeeping
requirements of NSPS Subpart Db (governing
Industrial, Commercial and Institutional Steam
Generating Units)
should
be
included in the
permit.
The
petitioners’ other
requests
are denied
for the reasons set forth in
this
Order.
2
Robert C. LaFleur, president of Spectra Environmental Group, Inc. (Spectra), submitted the
most
detailed
petition.
Spectra’s petition raised many
of the same issues posed
by other petitioners.
For
purposes of this Order, unless specified otherwise,
the term “petitioner”
refers
to the petition received from
Spectra.
However,
this Order also responds to the petitions submitted by Lois Broughton,
Wanda Brown,
Louisa and
George Centeno with Leslie Mongilia, Maria Dellasandro,
R. Dimieri,
Lori Dimieri,
Dawn
Evesfield, Marvin Feman, Deborah Glover,
Anne Jacobs,
Barbara Javalli-Lesiuk, Marie Karr, June Lee, Ruth
MacDonald, Bernice Mapes, Donald
Maurizzio, Alice Meola,
Daniel Nebus,
Jeanette Nebus
,
Mr. and
Mrs.
Hillary Ragin, M. Schoonover and
Mildred Sherlock, LaVinnie Sprague,
Matthew Sprague, Hubert van
Meurs,
Alfred and Catherine Viggiani, Paul Weimer and Leonard Wodka.
EPA has been unable to verify
the
correct name and address for Dawn Evesfield, R.
Dimieri and Lori Dimieri.
2
I.
STATUTORY
AND REGULATORY
FRAMEWORK
Major stationary sources of
air
pollution and
other sources covered by title V are required
to
obtain an
operating permit that
includes emission
limitations and
such other
conditions as are
necessary
to
assure
compliance
with
applicable requirements ofthe Act.
~
CAA
§~
502(a) and 504(a).
Section 502(d)( 1) ofthe
Act calls upon each State to develop and submit to EPA an operating permit
program
to
meet
the
requirements
of
title V.
EPA granted interim
approval
to the title V operating
permit
program
submitted by
the
State of New York effective December 9,
1996.
61f~j
57.589 (Nov.
7, 1996); see also 61 f~jJ~g.63928 (Dec. 2, 1996) (conection); 40
CFR Part 70,
Appendix A.
The title
V operating permit program
does not generally impose new substantive air quality
control requirements (which are referred to as “applicable requirements”), butdoesrequire
permits
to
contain monitoring,
recordkeeping, report4
and other compliance requirements
to assure compliance
by sourceswith
existing applicable
requirements.
57
f~j
~
32250, 32251
(July 21,
1992).
One
purpose ofthe title V
program
is to enable the source, EPA, States, andthe public to clearly
understand the
regulatory
requirements applicable to the source
and
whether the source is meeting
thoserequirements. Thus, the tideV
operating permits
program is a vehicle forassuring
that
existing
air
quality control
requirements
are appropriately applied to
facility
emissionunits ina single documentand
assuring
compliance with these requirements.
InNew York
State,
titleV operating
permits
are issued tonew
sources
through the same
process which authorizes them to construct the facility. The
procedures
for issuing
constmction
permits, the
State’s
New
Source
Review (NSR) program, were in place
prior
to
approval ofthe title
V program, and have
been
combinedwiththe State’s
title V program,
so that this
program meets the
combined requirements of
both
NSRand tide V. While combining the programs offers
simultaneous
review ofthe NSR requirements and the titleV requirements, it does not alter the
underlying
requirements
of these two programs:NSR establishes case-by-case control
requirements
for certain
new sources, while titleV assures
(through permithng
monitoring,
certification, etc.), compliance with
all Clean AirAct
requirements (including NSR, whereapplicable).
Under section 505(a) ofthe Act and 40 CFR
§
70.8(a), States are required
to
submit toEPA
for review
all
operating permits proposed
for
issuance,
following
the close ofthe public comment
period.
EPA is
authorized under section 505(b)
ofthe Act and 40 CFR
§
70.8(c) to review proposed
permits,
and object to
permits that
fail
to
comply
with
applicable
requirements of the Act, including the
State’s implementation plan (and the associated public
participation requirements),
or the
requirements
of40 CFR Part 70.
If EPA does not object to
a
permit
on
its own initiative,
section 505(b)(2) ofthe Act and 40
CFR 70.8(d) provide
that any person may petition
the
Administrator, within
60
days
of the expiration
of EPA’s 45-day review period, to object to the permit. When a petitioner asks EPA to object to a
3
title V
permit,
a petitioner
must
provide
enough
information for EPA
to discern
the basis forits petition.
Under section
505(bX2)
of
the Act
and
40
CFR
§
70.8(c),
EPA
can only object
to
a
title V
pennit in
response
to a citizen petition based on the samegrounds on which EPA
could
have objected on
its own
initiative.
The
statute provides that apetition for review does
not
stay
the
effectiveness
ofthe
permit
or
its
requirements
if the
permit was
issued after
the expiration ofEPA’s 45-day review
period and prior
to
an EPA objection.
IfEPA objects to a permit in response
to
a petition
and
the
permit
has
been
issued, EPAor
the
permitting
authority
will modi~terminate,
or revoke
and
reissue such a permit
consistent with the procedures in 40
CFR
§~
70.7(g~4)
or
(5Xi)
and
(ii) for
reopening a permit
for
cause.
H.
ISSUES RAISED BY THE PETITIONERS
Asdiscussed above,
this Order divides
the issues raised into
two categories:
administrative/public participation issues,
and
technical/regulatory
issues.
This is solely for clarity, and
should not be read as
conferring different
legal status to the
issues
in either category.
A.
Administrative Issues
The petitioners have requested
that EPA object to Masada’s permit based
on a
number
of
alleged flaws in the
administrative processing
ofthe permit.
These administrative
issues each relate to
whether the NYSDEC provided adequate procedures for public notice
pursuant
to 40
CFR
§
70.7(h)
and 6 NYCRR
part
621.
Spectra’s petition identified five such issues.
Ms. Nebus and Ms. Glover
raised some ofthe same issues, as well as
two others.
Public
participation
is an important part ofthe
title V process, and is an appropriate subject ofan objection by EPA
pursuant
to 40
CFR
§
70.8(c)(3)(iii).
Eachofthe administrative allegations are
discussed below.
1.
Extended
Comment Period
Petitioner
Spectra asserts that
the
NYSDEC
never explicitly advised
members
ofthe public of
their right
tosubmit
written comments
up until
the close ofthe public hearing.
The issue
raised
in this
claim
points
to NYSDEC’s failure to
explicitly
advise the
public ofthe rightto submit written comments
after the NYSDEC public
comment period closed
on
October
22,
1999,
and prior
to
the public
hearing
ofDecember 29,
1999.
Both
New
York state and EPA regulations provide for reasonable public notice oftitle V
permits.
6 NYCRR
621 .6(a)(2), 40 CFR 70.7(h).
Where a public
hearing
is scheduled, NYSDEC
needs to
give
a 30-thy notice
to
the public prior to the hearing.
40 CFR 70.7(h).
NYSDEC satisfied
this
requirement by publishing a hearing announcement notice on November 24,
1999.
Neither the part
70 regulations nor the State niles
require NYSDEC
to
explicitly advise the public
that comments may
be submitted up until the close ofthe hearing.
See 40 CFR
part
70.7(h); NYCRR
§~
621.6
and
621.7.
Given
that
comments were solicited for the thy ofhearing, it is
implicit
that comments submitted
4
up
to
that
date would
also
be accepted without prejudice.
Indeed, no
party has
informed EPA ofany
specific comments
that were not considered
by NYSDEC
due
to
untimeliness and there has
been
no
allegation
that any
ofthe petitioners
suffered harm.
Accordingly,
EPA denies the petition on
this
point.
2.
Unavailability of
Certain Documents
Spectra
claims that certain importantdocuments were
not
made
available
to the
public.
Spectra lists EPA letters ofOctober 20,
1999,
December 6,
1999, and December 22,
1999 among
those not available.
Spectra
also
names a submittal
from
Masada
to NYSDEC
on November 2,
1999
as
not available.
Spectra furtheralleges that
the
revised applications (August 1999) and support
documents (Masada’s June
1999 pilot plant emissions
testing data)
were not
made
available to the
public or EPA
during
the public comment period.
Spectra
claims that
the public was completely
unaware
of
these
documents during the public
comment period, and this was “information
necessary to
meaningfully review the
proposed
project,” therefore
NYSDEC
violated 40
CFR 70.7(h)(2).
As the Administrator stated in the
Borden Chemical Inc.
petition response, petition VI-01-01,
available at
httnil/www.epa.gov/rethono7/programs/artd/air/titles/petitiondb/netitions (under
Borden_response
1999), “access to
infonnation is a
necessaryprerequisite
to
meaningful
public
participation.”
Public involvement is
required throughout
the
CAA title V permit process (see,
e.g.,
CAA
section 502(b), 503Xe) and
505(b)), EPA’s implementing
regulations
(see 40 CFR
§~
70.7
and
70.8) and New York regulations (6
NYCRR
621).
However, EPA disagrees with Spectra, fmding
that the
documents
in
questions
were neither legally nor
technically necessary
forthe public to
meaningfully
review and comment on the draft permit. NYSDEC
made
available
Masada’s complete
permit application, including July and August
1999
amendments,
the
draft per-mit,
and the State
Environmental Quality
Review Determination.
As
explained
below,
based
on
our
review ofthe
information provided
by
NYSDEC
in
this case,
I
findthat
the public
had
access to sufficient
documentation
to
formulate comments
and
meaningfully participate
in the
permit process.
The
documents named
by
Spectra
fall in
two
categories: those
that
were
generated prior to the
public comment period,
and those that were generated
later.
Regarding
the pre-comment
period
documents, NYSDEC
informed EPA
that
it believes
that
the application revisions ofJuly 26
and
August 6,
1999, were
part
of the
permit application that
was
placed
in the
Middletown library
at the
beginning
of the comment
period
and
that
the draft
permit reflected all
the
last minute revisions.3
The
September 22, 1999, Notice of Complete Application, published in the
State’s Environmental News
Bulletin,
notes
that ‘The draft permit
and
permit applications are available
for
review
during normal
business hours at theDEC
Region
3 Office.”
It further notes
that “the
application consists
ofa two
volume
part 360 solid waste engineering report’plan dated
July
1999; an air emissions
estimate dated
‘EPA
confirmed this
via a telephone conversation between L. Steele, EPA Region 2, and T. Miller,
NYSDEC
Region 3,
on
January
5,2001,
and a
subsequent
conversation between
L.
Steele and M.
Merriman,
NYSDEC
Region 3, on
January 8,2001.
5
December 1998,
revised July
1999; and an air
quality
modeling report,
dated March
1999, amended
August
1999.”
The otherearly
document
Spectra names
is the June
1999
report ofthe pilot plant emission
testing data.
NYSDEC
states that this
document was not in the public
docket becausetheir staff
never
requested the
actual pilot testing data as part
ofthe
Part
70
permit application review.
They
explain
that
it
was
not
necessary for Part
70
purposes as
they
relied on
Masada’s summaries
ofthe data for
permit review purposes.
EPA finds
that
the
informationin this report
was adequately summarized
by
the
documents
provided by
Masada,
and therefore there was no need
for
NYSDEC
to obtain the
raw
data.
Cf
Aknan v. Koch,
75 N.Y.2d 561, 573-74 (1986) (holding
that “there
is no
requirement
that
an
environmental impact
statementJ
contain
all
the raw data supporting its
analysis
so long as
that
analysis
is sufficient
to
allow informed considerationand comment on the issues raised”).
The other
documents
cited by
Spectra
were generated between October 20,
1999
and
December 22,
1999, spanning the time
between the public comment period
and
the public
hearing.
On
October 20,
EPA Region2 commented
to NYSDEC
on
the draft
permit.
On November 2,
Masada
responded to NYSDEC, addressing
many of EPA’s comments.
On December 6, EPA Region 2 made
additional comments
to NYSDEC, as
part
of the
regular process
of
permit
review.
This response
relied on
information
provided by
Masada as well as EPA
headquarters.
On December 22, EPA
Region 2 responded
to
Mayor DeStefano’s letter ofOctober 22,
1999.
None ofthese
documents introduced new information that was material
to
the design or
operation of
the
Masada project.
Although some
ofthe information in the November 2,
1999 letter
was
ultimately usefl.rl in
clarilj,’ing
the applicability of
some requirements (see
ll.Blc below), it
did
not
amend the permit application.
These documents reflect the on-going
dialogue between EPA
and
NYSDEC
that
is
envisioned in section 505 ofthe
Clean Air Act
The Act provrdes the public an
opportunity
to review and comment upon the
draftpermit,
but
does
not require that
the public
be
afforded an opportunity to respond to EPA’s
comments or NYSDEC’s response.
Cf
Rvbachek v.
LEA,
904 F.2d
1276, 1286 (9th Cir.
1990) (denying
claims
ofnotice
and
comment violations
because
the
petitioners’
“unviolated right
was
to
comment on the
proposed regulations, not
to
comment
in a
never-ending
wayon
EPA’s
responses
to their comments.”).
In addition, the December 22,
1999
letter
from
EPA Region 2 to Mayor DeStefano
was
notrelied
upon
by
NYSDEC
in
making
its
permitting decision and NYSDEC
did not violate the notice and
comment
procedures
by thing
to
make
EPA’ s
letter
publicly
available.
When NYSDEC transmitted the proposed permit to EPA, it updated
the
Middletown library
docket
with
several
additional documents, including
many
ofthe
documents
discussed above.
NYSDEC’s June 2,2000,
letter to concerned citizens
announced that
EPA’s
October
20,
1999 letter,
Masada’s
November 2,
1999
response,
EPA’s
December
6,
1999 comments,
and several
other
documents
hadbeen sent
to
the Middletown library.
Spectra indeed acknowledges
that
it received and
6
“subsequently commented on the previously unavailable EPA
and
Masada
correspondence.”
Spectra
petition,
at 27.
EPA encourages NYSDEC
to
manage their
files as
carefully as possible, so that information
requests
can be met expeditiously.
EPA appreciates NYSDEC’s willingness to use local libraries as
document repositories for certain projects.
Although there
is no specific federal requirementto do so,
this
is a resourceful
way to meet citizens’
needs.
During
the
Masada
project review,
there may have
been
delays
in addingnew
documents to
the public file
placed
in the
Middletown library as
they
anived
iitthe office,
and
NYSDEC’s document management
procedures may
not be flawless.
Nonetheless,
the public in
this instance bad access
to
and
in fact commented upon the complete
draft permit,
the
application, and
ultimately
the
documents
at
issue.
Therefore, EPA
finds no
violation of40 CFR
70.7(hX2), and denies the petition
with
respect to
this
issue.
3.
Onportunity
for
Comment on
Changes to
Permit
The Spectra petition claims
that
“the
public...was not provided an
opportunity
to review the
‘latest
draft
title V
permit’
for the Project” (Spectra petition, p.
12)
and
“the
public comment period
was based on a September
draft permit that
is a shell ofwhat
was ultimately granted
to Masada.”
(EL
at 26).
Spectra expresses
the concern
that
NYSDEC excluded the public
from meaningfully
reviewing
and commenting on
the proposedpermit sent to EPA in
May
2000.
Petitioner Nebus
raises similar
issues in her petitions ofJuly 23
and August
7,
arguing that
such significant modifications ofa
draft
permit without additional public notice violate
40 CFR
§
70.7(h).
The
CA.A
and its implementing
regulations
at
part
70 provide for public
comment
on
“draft”
permits and generally
do not
require permitting authorities
to conduct a second round of
comments
when sending the
revised “proposed” permit
to EPA
forreview.4
It is a basicprinciple of
administrative
law
that
agencies
are encouraged to leam from public comments and, where appropriate,
make changes that are a“logical outgrowth”
of the
original proposal.
See,
e.g.,
Siena Club
v.
Costle,
657
F.2d 298,
352
(DC
Cir.
1981).
However,
there are
well
recognized limits tothe
concept of
“logical outgrowth”
in the context ofAgency
rulemaking that,
by
analogy, apply to title
V permits
as
well.
As the US Couitof
Appeals
for the DC
Circuit
has explained, “ifthe final
rule deviates too
sharply
from
the
proposal,
affected parties will be deprived
of notice
and an opportunity
to respond to
the proposal.”
Small Refiner Lead Phase-Down Task
Forte v. EPS
705 F.2d 506, 547 (DC Cir.
1983) (vacating portion offThal
CAA rule governing leaded gasoline because agency notice was “too
general” and
did
not apprise
interested parties
“with reasonable specificity” ofthe range ofalternatives
The CAA
in
part
502 (b)(6) specifiesthat one required element of a title V permit program is
“adequate, streamlined, and reasonable procedures...for public notice, including offering
an opportunity for
public comment and
a hearing.” 40 CFR 70.7 (h) mirçors this language of the Act, stating that, “all
penniL
proceedings...shall provide adequate procedures for public notice
including offering
an opportunity for
public comment and
a
hearing on the draft permit.”
7
being considered).
~
~
Shell Oil
Company v. EPA.
950 F.2d 741
(DC Cir.
1991) (remanding
final
RCRA “mixture
and derived flom” rule because “interested parties cannot be expected to divine
the EPA’s
unspoken
thoughts”);
Ober v.
EPA. 84 F.3d
304, 312
(91h
Cir.
1996)
(requiringan
additional round ofpublic
comment
on EPA’s approval of
Arizona’s
PM- 10
Implementation
Plan
because public never had an
opportunity
to comment on state?
s post-comment period justifications
which were
critical
to EPA’s approval decision).
Courts have noted
that providing
the public
meaningful
notice improves the
quality
of
agency
decisionmaking, promotes flimess to affected parties,
and
enhances
the
quality
of
judicial
review.
Small Refiner, 705 F.2d at 547.
I find that
these
fundamental principles apply
with equal force in the
context
of
title V
permitting.
Otherwise,
if a
final
permit no
longer
resembled
the permit
that
the
public
commented upon, then the public would
be
deprived ofthe
opportunity
to
comment guaranteed by the
CAA
and EPA’s rules.
Determining
how much
notice
is sufficient is
inherently a matter ofjudgrnent
In this case,
however, the
operational constraints imposed
on the
facility
in the
proposed permit were so
significantly
different from those
in
the
draftpermit that I find that additional
public
notice
on this particular aspect of
the permit is
required.
The NYSDEC’s
reason
for
including operational
constraints in Masada’s draft
permit was to effectively
limit
the
potential to
emit (PTE)
and
preventthis source flumbeing a “major
source”5
ofair emissions forPSD
and/or NSR purposes.
The
PTE
is a
critical fuctor
in
determining
the
applicability
ofthe CAA
major source
permitting requirements.
Many large
fhdilities are potentially
subject to major source preconstruction requirements, unless they installpollution control
equipment
and/or
accept operational constraints, such as
limitations
in the hours of
operation,
raw material
throughput or production
rate,
that
limit
the facility’s PIE below majorsource
thresholds.
Masada’s
title V application and
permit
do
not list the major souree
preconstruction
requirements as applicable requirements.
Therefore, forpollutants
where the
source’s unconstrained
capacity exceeds
major source thresholds, the
permit must constrain
the
facility to
emit air
pollution only
at levels
that
would not
trigger major source applicable
requirements.
In
ogler to
be
cognizable as
limits
on the
source’s PIE, such constraints must always be stated
in a
practically enforceable form
in a
source’s construction permit as
well as
its
operating permit(s).
Since
the source
is
subject to title
V
permitting,
any
preconstnrction permit requirements, including PIE limits, quali1~’
as applicable
requirements under part
70, and mustbe set
forth
in the
source’s operatingpermit.
Generally, applicable
requirements in permits are subject
to
many degrees
of technical
and
legal
review
before
and
during rulemaking
or
permitting procedures.
However,
in the case ofPTE
limits,
the
A major source is defined under 40
CFR
§
52.21
as any stationary source (or any group of
stationary sources
that are located on one or more contiguous or adjacent properties, and are under
common control of the same (or persons under common control)) belonging to
a single major industrial
grouping that emitsor has the potential to emit:
I) 250 tons per year (tpy) ormore ofany air pollutant
regulated under title I of the Act;
or
2)100 tpy of any regulated air pollutant ifthe source
belongs to one
of
the categories of stationary sources
as listed under title I of the Act.
8
State generally fashions
the
necessary
operational constraints and subjects them
to
review forthe
first
time during
the
permitting process.
In
the
case
of
the
Masada
facility,
the
PTE-limiting terms were
originally drafted by NYSDEC, as is
normally
done.
When EPA staffcommented
on
the
draft permit,
they raised several concerns
with the enforceability
ofthe PIE limits.
Subsequent comments
from
citizens raised similar concerns.
After
the close ofthe public
comment
period, NYSDEC
revised
the PIE
limits
with input from
EPA and
Masada,
in order to better defme the operational constraints
and associated
method for
verifying
the
source’s
emissions.
While the
need
to improve the PIE
limits
was identified by
the
concerns raised
in the comment period, the final
permit ultimately adopts a fundamentally different
approach to limit
the
source’s PIE than the
one found
in the
draft permit.
It is for
this reason that
I am
requiring a new review period for these new PIE limits.
As explained further
in section II.B. l.c
below, it
is EPA’s judgment that this new approach
is a
valid and enforceable way to
limit
PIE in
certain cases, but additional public notice is required
to
finally determine whether it is appropriate
to
apply this approach to this
facility
and whether the permit does
so
in
an appropriate manner.
Masada’s draftpermit expressed annual emissions limits on
sulfl.rr
dioxide (SO2)
and nitrogen
oxides (NOx ~in terms ofa
12-month rolling average.
These limits, under EPA policy, would have to
rely on
short term (e.g., pounds/hour) emissions rates, coupled with restrictions on the source’s hours
of operation (e.g., hours/year).
Indeed, much of EPA Region2’s comments, as well as
the public
comments filed on the draft
permit, focused on the
specificsof these short-term emissions rates and
operational limitations.
In contrast, the permit ultimately issued by NYSDEC does not rely on short
term emissions rates as the basis for calculating an operational limit to restrict the source’s PIE.
Instead,
it relies on real time data from continuous emissions monitors (CEM5).
Short-term emissions
rates are
still in the permit, but the issued permit reflects a change to indicate that these limits are no
longer used for PTE-limiting
purposes.
EPA observes that the approach used
in the issued pennit is a relatively new (and more
flexible) approach that takes advantage of continuous emissions monitoring systems.
While the draft
permit
calculated emissions as a function of
two factors
—
short-term emissions rate and hours of
operation
-
the
issued permit directly measures
emissions
with real-time accurate emissions
measurements.
Furthermore, whereas the draftpermit relied on a 12-month rolling average, the final
permit instead relies on a365-day
rolling total, resulting
in
adifferent reporting and recordkeeping
regime, and effectively enabling more
frequent
compliance checks.
To support this approach, the
final
permit requires extensive data
collection
procedures and quality assurancemeasures.
Similarly, rather
than impose exact limits on the hours of operation, the proposed permitallows the source to operate as
long as
its
365-day measured total is below the major source cutoff.
Thus, specific limits
on hours of
operation were
excluded
from the PIE limiting language.
EPA finds
that, as to the terms ofthe permit which were intended to express operational~
constraints on
this facility that effectively limit Masada’s PIE below major source thresholds,
9
specifically
permit
conditions
36
and
41, there has notbeen adequate adherence to the applicable
public
participation
requirements.
The draft
permit gaveno
indication that such a differentand relatively
new
approach might ultimately be contained
in the
issued permit.
In fact
it suggested that the PTE
limit
would be a
typical limit based
on short-term emissions rates
and limits
on
hours of
operation.
EPA’s
and
the public’s
comments are clearly based
on
this understanding.
As such,
EPA finds that
it is
unreasonable
to
conclude
that
the public
bad an opportunity
to
comment
on
whether
the PIE
limit
ultimately found in
Masada’s permit assures
compliance with applicable
requirements.
Therefore, EPA
is
granting
the requestto object to the permit according
to
40 CFR 70.8(c)(3xiii),
with respect
to
this
issue.
Pursuant
to
Sections
505(b)
and 505(e) ofthe Act, 42 U.S.C.
§~
766 ld(b) and (e),
and
40
C.F.R.
§~
70.7(g)(4) or
(5)
and 70.8(d), EPA objects to the title V
operating permit
issued
to
Masada
by
the NYSDEC on July
25,
2000.
NYSDEC shall
modilS’
the
permit
by
re-opening
the
above
cited
portion ofthe
permit
to provide forpublic participation based on the changes
made after
the
initial
public
comment period.
This process includes a new
30-day
comment period
for
the public,
a new
review period for EPA, and
a newpetition
period
forcommenteis.
Only
the
portions that speak to
the
monitoring, recordkeeping, and
operational
requirements
that cap the fhcility’s PIE need
to be
renoticed,
and
comments do not need to be
accepted
on other
aspects
ofthe permit.
In
this
new public
notice, NYSDEC should
clarify that only
conditions 36
and 41, and at
least pages
3,5,
and
10-15 of
the facility
description, are
being reopened pursuant
to
this Order.
4.
Notification
of
Petition Period
Petitions received
from Spectra
and
from
Ms. Nebus claim
that
NYSDEC failed to properly
inform
the
public
with
respect
to the commencement ofthe public’s 60-day period for petitioning the
EPA
Administrator
to object to the
issuance
ofthe
Masada
title V
permit.
NYSDEC sent a letter to
all
concerned citizens dated June 2, 2000, announcing that
EPA has
completed
its review and
found the
proposed
permit
to be acceptable.
NYSDEC
further
stated,
regarding
the
opportunity
forcitizens to
petition,
“you
will be notified
when this
(the
60-day) period begins.”
When
the final
permit was
issued
on July
25,
2000,
NYSDEC then advised the public
that their
June 2,
2000
letter erred
in its statement
about the commencement ofthe
60-day
petition period.
The July
25,
2000, letter indicated that
the
60-day
petition period
began
on
June 19,2000
andwould end on
August 21,2000.
Spectra
and
Ms.
Nebus claim
that
NYSDEC
shortened the
statutory 60-day petition period as a result
oftheir
error
and
seeks an EPA objection
to
the
issuance
ofthe
final permit
on the basis
that
NYSDEC failed
to
properly
inform
the
public
ofits
right
to
petition.
Section
505(b) ofthe Act provides those who commented during the public reviewperiod have
60 days
to
petition the EPA Administrator
to
object to the issuance ofa title V
permit
if EPA did not so
object during
its 45-day review period.
This 60-day petition period
immediately follows EPA’s 45-day
review period.
Neither the Act nor the
current
part 70
regulations
require the State
to
inform
the public
ofthe commencement ofEPA’s 45-day review
period and
of
the
citizen’s 60-day
petition
period.
10
Nonetheless, NYSDEC
took
it upon itself to notify the public when the petition period began.
However,
NYSDEC
misread the part
70 regulations and misinformed the
public.
NYSDEC’s mistake
may have
caused coniflision regarding the
time period
in
which the public
may
petition the EPA
Administrator.
Spectra
alleges a violation of40 CFR 70.8(d) as a resultofNYSDEC’s error which
may have, in
effect,
shortened the public’s petition period for those who relied solely on
NYSDEC’s
advice and not the rules themselves.
NYSDEC did not and could not shorten the statutory period for
public petitions.
Its
inaccurate statement may have misled the public.
However, as
discussed
below,
I
find this
to be a
harmless error that did not cost any
petitionerthe opportunity to file a tide
V petition.
See e.g.
Massachusetts Trustees
of
Eastern Gas
& Fuel
Associates v. United States,
377
U.S. 235,
248
(1964)
(an en-or can be dismissed as harmless “when a mistake ofthe administrative
body
is one
that clearly had no
bearing on the procedure used or the substance ofthe decision reached”).
NYSDEC’s
notice would not have
mattered
to those who were aware ofthe
statutory
requirement
since
they knew whenthe 60-day petition period commenced.
However, those who relied
on NYSDEC’s notification had 36
fewer days to prepareand
file theirpetitions.
Despite NYSDEC’s
error,
many members
ofthe
community
were aware ofthe proper filing deadline and
submitted timely
petitions to the
Administrator.
While EPA acknowledges that
NYSDEC’s error
may
have caused
some
confusion to the public,
it was unintentional and inadvertent.
Nevertheless,
this error may
have
contributed
to
the filing ofa petition on
September
11,
2000 (21
days late) from Louisa Centeno,
George Centeno, and Leslie Mongilia ofNew
Hampton,
New York.
To ensure
that NYSDEC’s error
does not
frustrate
the public participation
process,
I
am exercising my
discretion
to
consider their letter
as a petition to
reopen the
permit for cause
under 40 CFR 70.7(f) and (g).
I therefore address their
concerns on
their merits
in the
below
Order.
On the basis
that
NYSDEC’s error resulted in no harm
being
done to the public’s
opportunity
to file petitions concerning the Masada project,
I decline to
object to the
permit
on these
grounds.
5.
Lack ofSubstantive Review of
Comments
Spectra claims that
“petitioners’ comments have not
been
substantively reviewed or responded
to
by NYSDEC or EPA as they post-dated EPA’s conclusions
and findings
on the
matters
raised.”
Spectra petition,
at
13.
In particular, the petition
claims that
NYSDEC’s
responsiveness summary did
not
fully address such fundamental issues
as PSD/NSR
applicability
raised during the public
comment
period.
Spectra argues that this is an indication that these fundamentalissues and questions were not
yet
resolved prior
to the
issuance
ofthe final
permit
In responding
to
the
PSD
and
NSPS applicability
issues, NYSDEC referred to EPA’s
letters
ofDecember
6,
1999 and March 29, 2000
letters
addressing PSD
and NSPS applicability without any additional explanation ofNYSDEC’s position or
justification.
The petitioner
alleges that NYSDEC
did not
perform a substantive
review ofall
comments
received, and therefore
did
not intend to
consider
public
comments in its final
permit decision.
EPA
recognizes
the
importance
of public
scmtiny
in the permitting process as
evidenced in
the
public
review
and administrative
petition opportunities offered in title V ofthe
CAA
and
its
11
implementing
regulations. The law requires
that
the public be allowed
to review proposed projects
and
offer comments relevant to
requirements applicable
to
the
sourve.
Such
comments would most
certainly
assist the State
in
making
a sound
permit
decision.
The law also
requires
the
State to
consider
comments
received,
but it
does
not require
that all
comments
be incorporated into the final permit.
It
also
does not
indicate
how much detail
must be
included
in a
permitting
authority’s response to
any
comment received.
As
a
general
matter, EPA
recognizes that
governmental bodies are entitled to a
“presumption
of
regularity.”
See e.g.
Citizens
to
Preserve Overton Park. Inc..
et al. v. Volpe.
Secretary of
Transnortation,
401
U.S. 402,415 (1971).
In the absence ofspecific evidence, EPA will
not
speculatethat
NYSDEC has
failed
to
consider all comments.
As a result, EPA finds
that
NYSDEC did not violate either the
part
70
regulations or the State code at 6
NYCRR 621
.9(eX1) in
referring to EPA’s analyses ofDecember 6,
1999,
and March 29,2000,
to respond
to
the PSD and
NSPS issues raised by
commenters.
EPA denies the petition on this issue.
6.
Imprnner Denial
of
Request for a Second
Public
Hearing
Ms. Nebus claims NYSDEC violated the
public participation requirements of40 CFR
§70.7(h) by not responding to
her
numerous
requests,
during and after
the public comment period,
for
a
second public hearing.
The
second
hearing request denial was given
to
her verbally
by
NYSDEC
after her numerous
written
and telephone requests
to
NYSDEC.
Ms. Glover similarly complained
that
the December
29th
public
hearing “did
not
providethe
opportunity
forall affected parties
to
formally
submit comments
on
the
proposed facility
...
to
ask
questions
and
share concerns
for theirhealth and
safety.”
Ms. Glover
also stated that
anotherpublic hearing was requested on December
29,
1999 and
on
several
subsequent
occasions.
The petitioners alleged
that
NYSDEC acted inappropriately in not
granting their requests
for a
second public hearing.
EPA
disagrees that
DEC’s
fiuilure
to
grant a second hearing
request
is
a violation ofthe
applicable public participation
requirements.
Although
NYSDEC
could havebeen
more responsive
to
the petitioners’ requests for a second hearing (e.g., responded by telephone or mail), neither 40
CFR
§70.7(h) nor 6
NYCRR Part
621.6 and 621.7 require NYSDEC to honor
requests
for a second
public
hearing.
The New York regulations at 6
NYCRR Part
621
list criteria for
determining
whether a
public
hearing will
be held on an application.
NYSDEC utilized those criteria and determined
to
hold a
public
hearing on December
29,
1999.
New
York
regulations
do
not require multiple hearings,
and
thus
the state can
exercise
its
discretion whether
to
conduct a
second hearing.
In this case,
the public
had an
opportunity
to participate in the
title
V
permit process
by
submitting written comments
to
NYSDEC and by
speaking during the December
29th hearing.
Many
concemed citizens,
including
Ms. Nebus and Ms. Glover, availed themselves oftheseopportunities.
Thus,
NYSDEC
was
able
to
hear the
community’s
views about the
proposed
facility and incorporate their concerns
into
the State’s
decisionmaking process.
As
a result, the decision whether
to
hold a second public hearing
rested with
NYSDEC
and
EPA
denies
the petitioners’ allegations
that
NYSDEC violated the applicable public
participation requirements
by not
granting requests
for
additional
public
hearings.
12
7.
Failure to Translate Public Documents for Soanish
Speakirm Community
Ms.
Nebus
and
Mrs.
Glover allege that
Spanish speaking members ofthe Middletown
community were not aware ofthe proposed
Masada
project and its potential
impacts on health and
other issues and could not voice their concerns in the form of
written
comments or at the hearing.
I
interpret this
complaint to broadly
suggest that NYSDEC violated the public participation procedures
by Ihiling
to
translate
the public notices or the key
documents
related
to the
Masada
facility
into
Spanish.
Similarly, they suggest
that translators should have been made
available at the December 29t~~
hearing.
EPA
disagrees
with
petitioners
that
NYSDEC violated the
federal or State public participation
procedures required
by title V ofthe Act by not providing
Spanish translation for the public notices,
certain documents,
and during
the December 29i~~,
1999
hearing.
First, there is no record
of
this
concern being
raised to
NYSDEC
during
the comment
period,
and thus, under
40 CFR 70.8(d), it
is
inappropriate to
raise the issue
for the
first time
in a petition
to
the Administrator.
Second, the record
shows there was ample
public
participation on the
Masada permit.
The public commentperiod started
on September 22,
1999
and comments were received up
until
the
December 29, 1999 hearing.
During
this
3-month period, the public was afforded the
opportunity
to review records
held in the NYSDEC
regional office,
to submit comments on
the project, and to express
concerns
at the
hearing.
NYSDEC
developed a mailing list including over eighty citizens and
interested parties, received eighteen letters on
the
draft permit and estimates that at least
500 people
attended
the public
hearing.
Finally, neither the
part 70
regulations nor the State rules require NYSDEC
to provide translation ofthese
permit
documents or
during this public hearing.
See 40 CFR part 70.7(h); NYCRR
§~
621.6 and 621.7.
Therefore, the petitioners have not demonstrated that the lack of
translations
during the comment period
or
translators at the public hearing violated the public
participation provisions ofeither the State
or
federal rules implementing the Act.6
B.
Technical
Issues
1.
Prevention of
Significant Deterioration (PSI)’)
Program
Applicability
Part C
ofthe Clean Air Act
establishes
the prevention of
significant deterioration
CPSD”)
program,
a preconstruction review program that applies to areas ofthe
country that have attained
the
NAAQS.
42 U.S.C.
§~
7470-7479.
In such areas,
a major stationary source may not begin
construction or undertake certain
modifications without
first obtaining a
PSD
pennit.
42
U.S.C.
§~
7475(a)( 1), 7479(1)
& (2)(C).
The
PSD program includes two central requirements that must be
satisfied
before the
permitting
authority
may
issue
a PSD permit.
In broad overview, the
program limits
‘As
discussed
in section C.
1
below, thepetitioners may
file a
complaint under Title VI of the Civil
Rights Act of 1964,
as amended, and EPA’s Title
VI regulations ifthey
believe that the state discriminated
against them
in
violation of those laws
by
issuing the permit
to
Masada.
13
the impact of new ormodified major stationary
sources
on
ambient
air quality
and
requires
the
application ofthe
best
available
control
technology
(BAD).
42
U.S.C.
§
7475.
NYSDEC
determined that Masada was
not subject
to
the preconstruction
permitting
requirements ofthe PSD
program.7
This
determination was based on NYSDEC’s
finding that
the
facility would not
emit any pollutant
in major
amounts, above
which PSD applicability would be
triggered.
Specifically, the PSD
program
applies to the
construction
ofmajor new
stationary sources
and modifications
of
existing stationary sources.
Under the Act and
EPA’s
implementing
regulations,
sources in certain
identified
categories are considered
majorif they have the potential to emit
100
tons
per year (tpy)
or more of a
regulated pollutant.
42
U.S.C.
§
7479,40 CFR 52.2l(bXl)(i)(a).
Sources
in other categories are considered major if they have the potential to emitmore than 250
tpy.
In
determining that
the
Masada
facility is
not a major source subject
to PSD,
NYSDEC looked at
several
key questions: (1) what
is the “primary
activitf
of
the
Masada
facility, which
determines
whether the PSD major source cutoff is
100
or
250
tpy; (2)
if the
major source
cutoff for Masada is
250
tpy,
is
there an embedded
source
in a
100 tpy
category (e.g., an embedded
chemical process
plant) whose emissions
exceed
100 tpy;
and (3) is
the
permit sufficient
to
assure that
the emissions of
the
Masada
facility will not exceed the applicable
major
source
cutoff (either
100 or 250 tpy)?
Petitioners
Spectra, Ms. Glover and Ms. Nebus
make several claims addressing each of these
questions.
Such claims are addressed separately below.
a.
What
is
the primary activity of the Masada facility?
In
determining
the
primaiy activity of acomplex industrial facility, a permittingauthority should
consider the
facility’s operation as a whole.
NYSDEC evaluated the
Masada fhcilityand concluded
that
its
primary activity was refuse systems (Standard Industrial Classification
(SIC) code 4953).
Petitioners
Spectra,
Glover and Nebus
challenge
this conclusion,
suggesting that
the
facility is primarily
a
chemical plant designed to manufacture ethanol,
and should
be
identified as
an
industrial chemical
processing facility (SIC Code 2869).
Because under 40 CFR 52.2 l(b)(lXi)(a), the
100 tpy
major
source
threshold applies to
“chemical process plants,”
but not
to
refuse
processing
facilities, this claim
must be evaluated
to
determine
if NYSDEC properly classified the
source,
and
came
to
the
appropriate conclusion
that
PSD
did not apply
to the
Masada facility.
EPA finds
that
the
petitioners have not
demonstrated that the primary activity
ofthe
facility is
chemical manufacturing.
Whilecertain factors tend
to
support
the
pelitioners’ claims, an examination
of
the
facility’s operations as awhole results
in the opposite conclusion.
As discussedbelow,
this
conclusion
rests
on
a
number
offactors, including the relative
share
ofthe
value of services rendered
compared to the products sold, and the contractual relationship between the facility and
Middletown
andthe neighboring communities.
The federal PSD regulations are codified at 40 CFR 52.21.
Pursuant to 40
CFR 52.21(u), EPA has
delegated NYSDEC the authority to
run this program in
New York.
14
Spectra asserts
that the facility is a chemical
process
plant
because it makes
ethanol and carbon
dioxide as products, and that numerous chemical processes such as
acidhydrolysis,
ion exchange, etc.
occur at the facility.
They point out that the original permit application submitted
by
Masada
listed both
SIC codes 4953
and2869.
Spectra also asserts that
the facility
uses
municipal solid
waste
(MSW)
only as
an ingredient,
and
uses
it in a
different mannerthan traditional refuse systems.
Spectraasserts
that Masada will
not “dispose” ofwaste, but rather will
“convert” it to products, and argues
that
disposal is
necessary for a facility
to be classified as a
refuse system.
Finally, Spectra argueathatmost
of the personnel and payroll
at
Masada will be dedicated to chemical processes.
For
its part, Masada has argued that its principal product is a service rendered: the service of
waste disposal.
In support of this argument,
Masada provided revenue estimates
that over 70 percent
of the revenue from
the
Middletown facility will come from tipping
feespaid
by the
municipalities, and
only 30 percent from the production
ofproducts
like ethanol and
carbon
dioxide.
However, Spectra
calls these
figures “suppositious,”
“not binding,” and “speculative at best”
As the entity delegated authority
to run the federal PSD program in New York, NYSDEC
must
rely
on
EPA regulations
in
assigning aprimary activity
to
the Masada
facility.
EPA
has long applied
the “primary
activity” test to
categorize complex
industrial sources
for PSD.
In
cases
where more than
one
activity is
present at a
source, the primary activity
is
determined by
the source’s “principal product
(or
group ofproducts) produced or distributed, or services rendered.~tIn
determining the principal
products or services rendered, EPA considers,
on a case-by-case basis, the particular circumstances at
the source.
The
Standard
Industrial
Classification (SIC) Manual (published by the U.S. Government
Printing Office, most recently in
1987)
contains similar language
to
that used
by EPA,
and provides
fiirtherdiscussion that,
for its
purposes,
the principal product is to be detennined by the relative share
ofvalue added, including the value ofproduction for
manufacturing, and the value of receipts
for
services.
Generally,
EPA
believes
that this
is an approach
appropriate for
determining the principal
product or
service,
and therefore, in establishing the primary
activity for the
source.9
Thus,
in applying the primary activity test
to
the
Masada
facility, EPA believes it is appropriate
to consider the revenue from refuse processing,
in
addition to the revenue from sale
of
chemical
products.
EPA expressed
this view in a December 6,
1999
letter from Kathleen Callahan, Director,
Division of Environmental Planning and
Protection,
EPA Region H,
to
Robert Warland,Director,
Division of
Air
Resources, NYSDEC, (“December 6
letter”), which stated that “Masada’s information
indicates that more than 70 percent
ofthe revenue generated by the project results from tipping fees
associated with the collection of municipal solid waste and
sewage sludge.”
The December 6 letter also
‘45
Fed.
Reg. 52695 (Aug.
7,
1980).
See also US.
EPA
Office of Air Quality Planning and
Standards,
New Source Review Workshop Manual,
Draft,
1990, page
A-3.
EPA
further
notes that there is
no
dispute in
this
case that the
various
interrelated
activities
at
the Masada facility
constitute
a
single
source
for
PSD
purposes.
15
indicated
that
EPA believes that the presence ofa
coniractual
relationship
between Masada,
the city of
Middletown,
and the
sunounding towns to dispose
of
waste
is
itselfevidence that
the
primary activity
of
the facility is refirse
systems.
In
the
original
request for
proposals
to
which Masada responded, the
city
sought an
agreement
with a facility
to
dispose of its
waste,
not to
produce
any
product1° Although the
production of
ethanol
may be integrated
into
the disposal fhcility to
make
the waste
disposal
more cost-
effective, it i~
EPA’s judgment that the
facility is being built primarily
to
firIfill these municipalities’
need
to dispose ofsolid waste.
EPA Region 2’s
December
6 letter concluded
that “the proposed facility is primarily a
municipal
waste collection and processing
plant.”
NYSDEC relied
in part on
this letter
in
confirming
its
determination
that
PSD did not apply.
Nothing in the
Spectra petition refirtes
this conclusion.
Neither
the
mere presence
of
chemical processing activity
nor the
mere production
of
chemical by-products
is
sufficient to
determine the source’s primary
activity.
The arguments set forth in the
December
6
letter,
and furtherdiscussed
here
represent an appropriate basis
for NYSDEC to make a determination that
the
facility is a refuse
system, and
therefore
subject to a 250 tpy
PSD
cutoff:
Furthermore, Spectra’s statements about
the
speculative nature of Masada’s
revenue
claims
do
not provide
sufficient evidence
to
overturn
NYSDEC’s primary
activity determination.
Masada
is
legally obligated to provide NYSDEC
with the
information needed
to
make
a PSD applicability
determination,
and
to provide
the best informationavailable.
While Masada acknowledges that the
tipping
agreements are not yet in effect, EPA
does
not
find that
NYSDEC
erred in accepting Masada’s
revenue projections, which appear
to
be
based
on the
best available information.
Indeed, the rather
large 70-30 dominance
oftipping fees
in the revenue
estimate,
in EPA’s judgment, provides reasonable
certainty that
the
majority
ofrevenue
fitm Masada will come from tipping fees.
In addition, as
noted
above,
this
was
only
one factor of
several that
supported NYSDEC’s determination.
1 also reject a
related claim
by
Spectra that payroll
or
personnel activity should take precedence over revenue in
establishing
the
primary activity, as Spectra’s approach would ignore
the facility’s operations as a
whole and Spectra has not demonstrated that suchan approach is
necessary
based on the applicable
requirements.
EPA also
rejects
the
remaining arguments
by the
Spectrapetitioners
on
the
primary activity.
EPA does not
find
conclusive the fact
that
the
original permit application listed both
SIC codes
4953
and
2869.
Regardless ofthe number ofSIC
codes listed
in the application,
NYSDEC must
make a
primaryactivity determination,
and
ultimately
did so, choosing
refuse systems.
The arguments
that this
source is different
from traditional refuse systems, that
the source
uses
MSW as an
ingredient,
and
that
it will not
“dispose”
ofMSW, but
rather “convert” it to products
are insufficient to
demonstrate
that
the
facility is not appropriately classified as a refuse system.
EPA observes that, while the
Masada process
is
technologically innovative, and differs fitm many traditional
types
of
waste processing facilities,
it is
‘°
Request for
Solid
waste
Facility Development and
Management
Proposals, issued by
thecity
of
Middletown
on
September I,
1994.
16
still primarily engaged
in
waste minimization.
The
semantic
difference between
“disposal” and
“conversion” has no
regulatory
consequence, becauseboth are methods
of~~m~
g solid waste,
and
both occur
at
the
Masada facility.
For these reasons, EPA finds
that
NYSDEC
acted appropriately in classif~’ing
the Masada
facility as a
refUse system.
b.
is there an embedded source in a
100 ipy category whose emissions exceed 100 ipy?
As discussed above, in evaluating Masada’s request for a
permit, NYSDEC determined
that
PSD did not apply.
The basis for
thisdetermination
was that
the
potential-to-emit
for the facility was
below the relevant PSD major source cutoffs for a
source
whose
primary activity
is
refuse systems
(SIC 4953).
However,
the PSD applicability test contains an additional step
for facilities
in a 250
tpy
source category such as refuse
systems.
The additional
step requires an evaluation ofthe facility
to
determine
if
there
is a
portion
ofthe
plant
(which EPA
calls
an “embedded”
or
“nested” facility
or
source) which
could be classified
in one of the categories with a 100 tpy major source cutoff.
Ifan
embedded facility
exists,
the
emissions
from the embedded facility must be
estimated
separately, and
if
they exceed the
100
tpy
cutoff, the embedded facility is itselfconsidered a
major source
and subject to
the PSD requirements.”
At
the
Masada
facility, NYSDEC
determined that
there was no embedded facility subject to
the PSD requirements.
The
permit record
indicates
that
the most likely
candidate
for an embedded
facility is a
“chemical process plant,” which
is a
source categoiy with a
100
tpy
major source cutoff
under applicable EPA regulations,
40 CFR 52.2 l(b)(1)(i)(a).
Indeed, NYSDEC
noted in early
discussions
with EPA
that
there is
“Industrial
Organic Chemicals activity” at the
source.~~
However,
NYSDEC determined that, while there is an embedded chemical processplant, the emissions ofany
PSD
pollutant
from it would be below the major
source size.
NYSDEC
reasoned that
the
gasifier’s’3
See, for example, EPA’s New Source
Review Workshop Manual,
Draft,
October
1990, at A.23,
and the July 6,
1992, letter from Edwin Erickson, EPA Region
3 Regional
Administrator, to George Freeman,
Reserve Coal
Properties Company (available at http://www.epa.gov/rgytgmj/programs/artdlair/
n
sr/nsrmemo
sip
rim
act
.
pd 1)
2
April
7,
1999 letter from Robert
J. Stanton, NYSDEC
Region 3 to S. Riva, EPA Region
2.
I)
Some
confusion surrounds the terms “gasifier” and “boiler.”
For clarity, the term “gasifier” is
used in this Order
to
refer
to the unit where
the gasification
of
lignin, and its
subsequent oxidation, occurs.
Energy is
recovered from this process to produce steam
used for other parts of the Masada process.
For
this reason, various parties
refer to
the gasifier
as the gasifier/boiler.
The term “package boiler” is used
in
this Order
to refer
to a
separate natural gas boiler where natural gas
is combusted
to
produce additional
steam
needed for the Masada process.
Together,
these two units
are sometimes
referred
to
as the facility’s
boilers.
Emissions
from
the gasifier and the package boiler are
eventually vented
to the same
stack, which
is sometimes
referred
to
as the gasifier/boiler stack.
17
emissions are
best attributed
to
waste
processing
operations
ofthe facility and that, therefore, the
emissions
from
the embedded
chemical
plant would be well below the
100 tpy source cutoff,
and PSD
would not apply.
The
Spectra petitioners argue that
the
erfiissions from
the
gasifler
at
the
Masada
Facility should
be attributed to the embedded chemical plant emissions, not waste processing.
They
argue that
the
gasifler is an essential
part
ofthe overall
ethanol
production
operation.
It
gasifies
the
lignin,’4 combusts
the gases,
and
recovers
some of the
energy produced, using
it to provide steam
back to the various
waste and chemical processing operations.
Furthermore,because virtually all ofthe lignin is eliminated
in the
gasifler’,
and without the
gasifier
the
lignin would likely have
to
be landfllled,
petitioners argue that
the gasifrer
plays an
essential waste
disposal function
in
support
of the
ethanol
production.
As
such,
they believe its
emissions
should
be attributed
toethanol
manufacture.
EPA has considered the petitioners’ arguments and nonetheless finds
that Spectrahas not
demonstrated that there
is a chemical
process plant
with
emissions exceeding
the PSD
major source
cutoff.
There is little dispute that ethanol production falls within the category ofa chemical process
plant.
EPA has determined that the source category “chemical processplant” includes activities defined
within SIC major group 28.15
This
group includes “...establishments producingbasic chemicals...such
as acids,
alkalis, salts
and
organic chemicals.”6
Thus, although the primary activity ofthe Masada
facility is
refuse processing,
the presence ofethanol
(an organic chemical) production
indicates that an
embedded chemical process plant is
also present
However, EPA believes that the gasifler emissions
do not belong with the embedded chemical plant because the gasifler is essential to the Masada
facility’s primary activity
-
waste processing.’7
The key
determinations
in
assessing
the embedded chemical plant’s emissions are (1) the
primary
activity ofthe
facility,
and (2) the activities at
the facility which are principallydevoted to
activities other than
this primary activity.
Activities not principally devotedto the primary activity
may
be considered partofan embedded source.
In the case ofthe Masada, as stated
above, the
primary
activity ofthe facility as a whole
is
refuse processing.
Determination ofthis primary activity is always
4
“Lignin”
is the term
Masada uses to describe the general process residue that remains after the
hydrolysis of the municipal waste
—
residue that is eventually
combusted in the gasifier.
Lignin is not a
technical term and has no
meaning within the context of EPA or NYSDEC
regulations.
‘~
Memo from Ed Reich,
Director, Division of Stationary Source Enforcement, EPA
Office of Air,
Noise, and Radiation, to Thomas Devine, Director, Air and Hazardous Materials Division, EPA Region 4,
dated August21,
1981.
6
“Standard Industrial Classification Manual,”
1987, U.S.
Government Printing Office, at
p.132.
“As noted
in the preamble to the PSD regulations, “(where
a single unit is used to support two
otherwise distinct
sets of activities, the unit is to be included within the source
which relies most heavily on
its support.” 45
Fed. Reg.
52695 (Aug. 7,
1980).
18
the first step
in analyzing embedded facilities.
Following this, activities not principally devoted
to the
primary activity
are considered.
At the Masada
facility, there are a
number
of processes
including
hydrolysis
and separation,’8 sulfuric
acid reconcentration, andfermentation anddistillation, which are
principally devoted to
chemical
processing.
Although
these
activities play a dual
role of refuse
processing
(i.e., converting some ofthe waste to usable products),
it
is EPA’s
judgment that
these
activities primarily serve
to produce marketable ethanol and
other
products
—
a chemical process plant.
Likewise,
there is a natural gas
package
boiler which
exists primarily
to supply energy needed to
reconcentrate the acid forhydrolysis, and there are tanks for product storage.
These activities should
also
be considered primarily as
part
ofthe embedded
chemical
plant.
Emissions from
these activities
have
been
evaluated to determinewhether they exceed the
100 tpy
cutofffor a chemical process plant.
EPA finds
that
Spectra has failed
to
demonstrate that NYSDEC was correct
in finding that
they do
not.’9
The
remaining processes, including
sorting and drying
the
incoming
waste as well as
gasification/combustion are, in EPA’s
judgment, primarily devoted
to
refuse processing.
Indeed, in
petitioner Spectra’s
own words, “theprincipal purpose ofthe supposed
gasifier is to
eliminate
the
residue from the Project’s chemical processesto avoid the
need for landfill disposal.”
Spectra petition,
at 24.
However, petitioners
err
in
suggesting that
because achemical process
has occurred
before
gasification in
this
instance, that the gasifler
must
be
a “support facility”
to a
chemical plant
As
noted
above, the
primary
activity ofthe Masada
facility
is refuse processing,
and the gasifier,
by substantially
reducing
the volume of the
lignin,
is
primarily performing a refuse processing function.
Even
if energy is
recovered
from gasification/combustion as a
side benefit and used for
ethanol production, and even if
the presence ofa waste
stream
and
integrated disposal process makes ethanol production economical
at
this
site,
this does
not
change
the
detennination that
the
primary
activity is
refuse
processing.
On the question of
“support
facilities” raised by
Spectra,
EPA
observes that the gasiflerplays a
dual
role of waste
elimination and steam generation.
While
both ofthese roles arguably “support”the
chemical process plant, the question ofsupport
is not the relevant factor in deciding how to attribute
the
emissions
of the gasifier.
Questions
of
“support
facilities”
often arise in making major source
8
In response to the Spectra petitioners’ comment about EPA
Region 2’s prior assessment that the
hydrolysis step is
part of the refuse processing function (which the December 6 letter relied upon in
allocating gasifier emissions to refuse
processing), EPA
has reconsidered, and now believes that the
hydrolysis step properly belongs with the chemical processing plant.
It is EPA’sjudgment that the
hydrolysis step
is included principally to produce
sugars for conversion to ethanol.
While the hydrolysis
step serves
a limited waste reduction function, EPA finds
it unlikely that thehydrolysis step would be
present were it not for the productionof ethanol.
However, this determination does not impact the PSD
determination because there are no emissions from the hydrolysis step.
‘~
Emissions
from the hydrolysis step, the acid concentration/recycling step, the fermentation/
distillation
step,
the package boiler,
and the
storage tanks are
well below the major source cutoffs.
The
primary emissions,
according to Masada’s estimates, are
less than
I
tpy of VOC from the tanks, and less
than 9 tpy of NO,
from
the package boiler.
19
determinations
under the PSD program when
questions
arise as to
whether facilities are
part
of
the
same
industrial grouping.
Where a facility conveys, stores, or
otherwise assists in the production ofthe
principal
product at another
source,
it may,
under some
circumstances, be deemed
a
support
facility
and treated as part ofthe same source as
the facility it
supports.
This policy
is used, for example, in
determining whether two
adjacent facilities should be
treated as one source for PSD applicability
purposes.
However,
the support
facility
test
is not relevant to the Masada facility because
there
is no
question
that
the chemical processing activities and the waste
reduction activities
at
Masada
facility are
a
single source.
The boundaries ofthe major source have never been at issue.
The support
facility test
is.not
used to evaluate embedded sources.
Because both the
boundary
of
the source and
the
primary
activity have already been established, the Spectra petitioners’ view that
the gasifier“supports” the
chemical process
is
simply not relevant
The gasifier
is most appropriately
associated with
the
primary
activity
—
refuse processing
—
not the embedded chemical plant.
Mother possible
candidate
for an
embedded
source in a 100 tpy PSD
category
is a “fuel
conversion plant”
Spectra mentions this
in footnote
14 oftheir petition, but
presents
no elaboration on
this point
and no
evidence to support
this claim.
Based
on ourreview, EPA policy has historically
defined this
category as “plants which
accomplish a change
in state for a
given fossil
fuel.
The large
majority ofthese plants are likely to accomplish these changes through
coal gasification,
coal
liquefaction or
oil shaleprocessing.’~°
In this case, where fossil
fuels are not involved, and where
the
processing
involves hydrolysis, a
chemical process, it is
EPA’s judgment that the Masada facility
is not
a fuel conversion plant.
In any event,
for
reasons described above, even if a portion ofthe facility
were
determined to be a nested source in a
100
tpy category,
the gasifier
emissions would be associated
with
the primary activity, not the nested source,
andthe
remaining emissions would
not
exceed
100
tpy.2’
Therefore, EPA finds
that
NYSDEC
acted appropriately in
determining that the Masada facility
does
not
contain an embedded source subject to PSD, and that PSD does
not apply to
the facility in
general.
20
See
January 20,
1976 memo from D. Kent Berry, EPA
Headquarters, to Asa Foster, EPA Region
lv.
21
Yet another possible
candidate for an embedded source in
a
100 tpy category is
a municipal
waste
incinerator capable of charging more than 50
tonsof refuse per day.
CAA section
169(l).
The
gasifier, and possibly certain other associated activities, may comprise an embedded incinerator because
they combust
a substance,
lignin, which has its origin in part from municipal waste.
Petitioners did not raise
this
issue directly, but it arises indirectly in evaluating the assertion by Spectra that the facility should be
subject to
the New Source Performance Standard (NSPS) for municipal waste combustors.
Unless
otherwise specified,
EPA
generally interprets the source category definition here in a similar fashion to the
NSPS definition for that source category.
For reasons
described below (in the NSPS section discussthg the
municipal waste combustor standard),
EPA does not believe the gasifier, or any other part of the M-asada
facility, meets thedefinition of a MWC.
Thus, EPA
finds that there
is no embedded municipal
waste
incinerator at the Masada facility for PSD applicability
purposes.
20
c.
Is the permit sufficient to assure that the emissions ofthe Masadafacility will not exceed
the applicable PSD major source cutofffor any pollutant?
The questionof whether Masada’s emissions will exceed applicable
PSD cutofl~
focuses on the
“potential-to-emit” (PTE)
of the
facility.
PTE
is a source’s maximum capacity
(determined
on an
annual
basis) to
emit a pollutant under its
physical and operational design.
40 CFR 52.21
(b)(4).
In
detemiining maximum capacity to emit,
a source may
consider e,forceable
limits
on
its operation
and
emissions,
such as those
in a
title
V permit. There is a
significant amount ofbackground information in
the
administrative record
for the NYSDEC
permit addressing
and
estimating Masada’s
PTE, including
the following:
(I) a
preliminary information package summarizing
the proposed project, sent to NSYDEC on
September 24, 1998.
(2) Masada’s emissions estimate document and application for a title V
permit
filed with
NYSDEC
on December 21,
1998.
(3)
A
revised emissions estimate document
and revised
title
V application,
submitted
in
July and
August
1999
(NYSDEC deemed the application “complete” on August 25,
1999).
(4) Masada’s response, submitted on November 2,
1999 to EPA Region 2’s October 20,
1999
request for
additional
details
about the facility.
(5) Additional permit language
developed by
Masada,
EPA, and NYSDEC
during March
2000 to
limit
the
source’s PTE.
(6) a NYSDEC document submitted in May 2000 which addressed
various
public comments
raised during a
public
hearing
and
written commentperiod, including comments about
Masada’s emissions estimates.
The title V permit conditions at
the Masada facility are designed
to ensure that
the
PTE
at the
facility
will be no more than
246
tpy
ofsulfur dioxide,
below the major source cutoff of250 tpy.
They
similarly are designed to ensure that
the facility
will have
the potential
to
emit
99.5
tpy
of
nitrogen
oxides, below the major source cutoffof
100 tpy.22
NYSDEC sent EPAa proposed
title V permit
based
on these limits on May 4, 2000.
On May
17, 2000, EPA indicated,
in a letter
from Steven Riva ofEPA
Region
2 to Michael
Merriman
of
22
Notwithstanding the above determination that the Masada facility fallswithin a 250 tpy
source
category,
the Clean Air Act and NYSDEC regulations (6NYCRR 231)
establish
a
100 tpy major source cutoff
for NO, for attainment areas which fall within the Ozone Transport Region,
as is the case here.
21
NYSDEC Region
3
that the proposed permit meets all applicable title V requirements.
It stated that
“this proposed title V permit contains
substantive
permit requirements for stack testing monitoring, and
recordkeeping,
as well as the rolling
cumulative total methodology that will limit
the “potential-to-emif’
of
this proposed
facility.
This
statement indicates
that EPA and NYSDEC
were in agreementthat
the
proposed Facility’s emissions would not exceed the PSD major
source cutoff~
for
any
pollutant.
The Spectra petitioners
raise numerous
concerns that address this detenniriation.
First,
they
allege
that Masada has
not provided sufficient
process and engineering information
to
accurately
determine the Project’s
PTE.
Similarly, they allege
that
the emissions
estimates that are
provided are
not thorough enough and not reliable, claiming numerous general and
specific technical defects,
and
providingtheir
own estimate
of
NOx emissions
forthe gasifier
and package boiler.
Part
of
their
reliability
argument
is basedon the
factthat
the
project is still
in the
design phase, and
that specific
contracts
and vendor
guarantees
are
not
locked in sufficiently
well to
establish
the project’s
operational
parameters, and that the design of the project has
changed during
the
pennit process.
They also allege
that Masada cannot correlate process
feedstockto emissions output.
Ms.
Nebus and Mr.
van Meurs
raise similar
concems about the
unknown technology that will be used at the Masada
facility.
Because of the alleged uncertainties and
technical defects, petitioners also assert that the PTE
limits
in the
permit
are not likely
to be met.
They express concem that the
permit appears
to
rely on
after-the-fact monitoring, rather than engineering practices, test data, or vendor guarantees, to assure
that
emissions stay below major source cutoffs.
They feel that
Masada’s allegedly
inaccurate estimates
Of emissions are incompatible
with PTE limits
so close
to
the major source
size because
ofthe
“small
margin of
safety.”
They thither assert
that
the use ofPTE
limits
for
plantwide
emissions of
sulfur
dioxide
and nitrogen oxides
is itself
unlawful because it is
inappropriate to use a plant-wide applicability
limit
(PAl)
foravoiding
initial
PSD review ofentirely new sources and because it uses
post-
construction monitoring as the basis fora preconstruction
determination that NSR does
not apply.
Before addressing
Spectra’s claims,
it is helpful to
briefly
describe
the PTE
limit itself.
The PTE
limit
in the
Masada permit is based on what the permit record refers to as a “rolling cumulative total”
methodology.
Historically, many 17TE limits have relied
on
a
short-term emissions limit
(e.g.,
pounds
per hour), coupled as necessary with an operational limit
(e.g., a
limit
on
hours ofoperation), which,
taken together,
limit annual
emissions
below major source levels.
However, in the case of
Masada, the
PTE limit does
not rely on the
short-term limit
to
establish the source as a minor source.23
Instead, the
limit relies on
continuous emission
monitors
(CEM5) to
track
the total
daily emissions from the facility.
The emissions must be
recorded
each day,
and must also be added to the total from the previous 364
days
to
determine
an annual emissions
total each day
(i.e., a
rolling cumulative total).
If,
on
any day,
this total exceeds
the major
source size,
the source would be
subject
to a potential
enforcement action
(including penalties) for being in violation of
its title V pennit
forthe entire
year, and would need, among
23
There
are pounds/hour mass limits
in the permit, as required by
the New
York State
Implementation Plan (SIP), but these
are
not used for the
purposes of establishing the PTE limit.
22
other
things,
to apply fora PSD permit as a
major source.
Therefore,
like
any source with a PTE limit,
complyingwith the
limit
is
designed
to
keep
the
Masada
facility a minor source,
and a violation that
exceeds the
major
source
thresholds would
require the
source to
obtain a major NSR permit.
This
serves to constrain the
source’s
operation on a
daily
basis.24
Ifthe source has
no
room
to
operate
under the PTE
limiting emissions cap,
it
must cease
operation or face a violation
and a requirement
to
apply for PSD
permitting as a major source. Contrary
to
petitioners
claims that
the
PTE limit
will not
keep
the
source
below major levels, EPA finds
that this
rolling cumulative methodology
is an effective
means
of
limiting
PTE.
It simply
achieves practical enforceability
(e.g.
the ability
to establish
compliance
at any given time)
by
relying
on direct
real-time measurements and calculations necessary to
determine mass
emissions,
ratherthan on a mass
emissions
rate coupled
with a
limit
on
hours
of
operation.
Regarding petitioner’s
concern that
the PTE
limit relies on after
the fact
monitoring,
EPA notes
that
all PU limits
rely on
after the
fact monitoring of some kind.
Indeed,
the use of CEMs
in the
Masacla permit
is a more
rigoroustype
of
monitoring
than forsome other kinds of PU
limits.
EPA
acknowledges
that
the emission
factors for the Masada process
may
involve
certain elements
of
uncertainty.
However EPA believes
that this
CEM-based approach adequately addresses
this
uncertainty by requiring thorough real-time
monitoring ofthe emissions.
In
cases like Masada, where
the
process
involves new
technology and the facility
is the
first
of its
kind,
it is
unrealistic
to expect
precise
emission
factors prior to
construction.
A strength ofthis
rolling cumulative
approach is
that
it
compensates for
uncertainemission factors by linking
the
source’s operational constraints
to the
actual
measured
emissions, not the emissions factor, which itself
often contains inherent uncertainty
when
applied
to an
individual
case.
Similarly,
in responseto
Spectra’s concerns about
the lack of vendor
guarantees,
EPA notes
that
a PTE limit
need not always be
based on vendor guarantees.
While vendor
guarantees can be useful
in
estimating
emissions, particularly when
control devices are
utilized,
a
vendor
guarantee
is not a necessary prerequisite
to
issuing a permit limiting
PTE.25
Again,
the
rolling cumulative
approach, by using
real-time emissions data, compensates
for uncertain emission factors, which still
contain uncertainty even if
guaranteed by
a vendor.
24
This
limit also has the effect of requiring the source to employ pollution controls to reduce
emissions of NO, and SO2, and to ensure that these controls are functioning properly in order to preserve
its ability to operate below the daily PTE limit.
However, the permit also specifically requires the utilization
of
dry
lime injection and a spray dryer absorber system for SO2 control from the gasifier, selective non-
catalytic reduction (SNCR) for NO, controls from the gasifier, and a baghouse for particulate control from
the gasifier.
Low-NO, burners are required
for NO, control from the package boiler.
To ensure
that these
control devices are being used
as required and
are
working properly, the permit requires that operating
parameters will be
incorporated after
testing is
done to establish them.
~ Masada has indicated, in
its November
2, 2000, submittal to EPA that it intends to obtain vendor
guarantees, but says they will not enter into a formal contract wfth
a vendor until final approvals for the
project are obtained.
In any event, it
is the permit conditions which are binding on
the source,
and Masada
must
abide by these regardless of what arrangements it makes with
its vendor.
23
Regarding the petitioners’ numerous concerns about the accuracy
andreliability ofthe
emissions estimates used in developing the PTE limit, EPA finds that the estimates are credible
for the
purposes
of
establishing a
PTE limit
of the type used
in this
permit
As noted above, EPA
acknowledges
that
the
exact emission factors for the Masada process are somewhat uncertain because
the
facility is the first of
its kind.
Although
the facility must
make a credible effort to
project what its
emissions will be,
it is simply not possible for the facility,
particularly
in
this case,
to
compute
precisely
its emissions
until the facility is operational.
To
the
extent
that
Masada
has underestimated emissions,
the
PTE limit serves
to
constrain
facility operations to
keep emissions below the major source cutoff.26
In this
way, the
limit itselfis
not
critically sensitive
to
the accuracy ofthe preconstruction projections of
emissions.
This
approach is
certainly
not without
some risk
to
Masada,
who
must stay within these
emissions limits even if they have
underestimated
them.
However, as the Court found in
United States
v.
Louisiana-Pacific Corp., 682 F. Supp.
1141,
1166
(D. Cob.
1988),
“...the
regulatory framework at issue
may be unusually difficult to comply with because it
requires a source
to
guess what its
emissions will be
prior to
construction and the
commencement ofoperations.
Nonetheless, them must be no question
that the burden of
guessing
correctly remains
with the
source,
and that a mistake
in
this
process can
indeed result
in
penalty.
Otherwise, future sourcesthat
are unsure of
whether
they will
qua1if~,
as a major
source will
haveno
incentive toapply
for PSD permits,
which, undisputably,
is a burden.
Rather, they
will
build first and Wait
for the
issuance
of
an NOV notice
ofviolation
before
initiating
the
permit application process.”
Having said
that, EPAnonetheless
understands the Spectrapetitioners’ comment that unreliable
estimates may result in a PTE
limit that cannot be actually
met by the source
during its planned
operations.
Indeed
EPA has historically
commented adverselyon orobjected
to
permits
that have
limited PTE using unreasonable underestimates
of
emissions factors
or
constraints
on
operation
which,
in reality, would
constrainthe source’s operation so greatly that
it would not be viable.
EPA finds
that
this
is not the
case
at
this
source.
NYSDEC
acted properly when it
determined that the PTE limit
is
achievable,
based
on the
best
infonnation available.
The Agency has
reviewed
the emissions estimates
relied
upon in evaluatingthe PIE
limits
for
NOx and SO2 and finds that
they
serve as a reasonable
basis
for
determining that the PIE limits can be met
by the
source operating as planned.
While there
may be
some
uncertainty
in the
exact calculations, as is often the case with
any
preconstnrction
estimate, the provisions ofthe Pit
limit, as noted
above,
compensate
for
this uncertainty
by
constraining the
source’s operations as
necessary
to account for
any underestimate.
Any marginal
difference between the
estimates
and the
real
emissions would not
impact
the
source’s ability
to
actually
operate as planned.
Similarly, contrary to
Spectra’s assertion, Masada’suncertain emissions estimates
do notnecessarily
require that
the
PIE limit be
set
at some level belowthe major source
size
in order
26
On
the other hand, it
is also possible that
Masada
has overestimated emissions.
To the extent
that their emissions
are
actually less
than they projected, the PTE limit affords the
source greater flexibility
to operatewhile still remaining a minor source.
24
to
provide a margin of
safety.
The relevant uncertainty
in a
limit like this
is
not the uncertainty in the
emissions
estimates;
it is the
uncertainty
in the
emissions measurement system.
EPA finds
that the CEM
system, operatedproperly as required by the permit, provides reliable
data
to
assure
that
Masada’s
emissions
stay
below the major source
size.
In addition, conservative
measures are
included in the
permit
for
treatment ofmissing CEM
data,as well
as
limits on how much data can be missing.
Regarding the specific
technical
defects
alleged by
Spectra, EPA finds
that
none ofthem negate
EPA’s basic conclusion:
that
the emissions estimates
are sufficiently representative ofthe source’s
operation and are therefore credible
for establishing permit
limits on
PTE.
The
specific defects
in the
emissions
estimate that
are
alleged by
Spectra,
taken
together, do not,
in EPA’s judgment, rise to the
level of
undermining this basic finding.
The points raised by
Spectra range from alleged
defects with no
factual basis,
to
legitimate points that illustrate a point
which EPA has
already agreed
--
that
there is
some degree
of
uncertainty
in
Masada’s estimates.
However, in EPA’s view, no
single alleged
defect,
or combination of allegeddefects presented by
Spectra, is enough to prove
that Masada has so grossly
underestimated
its emissions that a PIE
limit using
the
“rolling cumulative total” methodology should
not
be based on the estimates.
Spectra
also
claims that
the Pm
limit itself
is
unlawfiil because it is a
plantwide emissions cap.
Spectra claims that this PIE
limit
isa
special type of lhnit
referred
to
as a Plantwide Applicability Limit
(PAL),
and
goes
on to
argue that a PAL
is
only
legal for an
existing
major source, not a
proposed
source.
They
misconstrue
the nature of the PTE
limits imposed
by NYSDEC
in
Masada’s pennit.
The
PTE limit
simply
assures that
the
source’s total emissions
do not exceed
major source
cutoffs.
It does
not
create a PAL, which
is a
term
of art
referring
to a
limit that
allows modifications at an
existing major
source without
major source
preconstruction review.27
The
PTE
limit
for the
Masada facility, while
covering
multiple units, clearly
does
not
authorize future changes
without review.
Therefore,
it is not a
PAL
and
any claims
about the legality of a
PAL
for
this kind
of source are
irrelevant
here.
The PIE
limit
developed here is both appropriate and
authorized
by
applicable regulations.
In summary,
EPA finds unconvincing the
petitioners’ assertions that the PIE limit
is
improper,
illegal, or
cannot
be met.
EPAbelieves
that the emissions estimate document, as supplemented with
additional
information requested by
various
agencies, is a
credible effort
to
estimate
emissions
based
on
the best available
information, and
is a legally
acceptable permit application on which a PSD
applicability
determination may be made.
Furthennore, EPA believes that the PIE
limits
for SO2
and
NOx
are enforceable, and compliance with
these
limits can easilybe verified
at
any time with real-time
CEM
data.
As such,
the
limits provide assurance that
the facility,
operating
incompliance
with the
permit,
will not emit these pollutants in major amounts.
Therefore EPA concludes
that
the
Masada
facility, as
permitted,
will not be a major source, and not
subject to
PSD.
“More details about the proposed regulations addressing the operation of PALs may be
found
in
the
1996 New
Source Review Reform
proposal.
58 Fed.
Reg. 38250 (July 23,
1996).
25
2.
Annllcability of
Federal Emissions Standards
The Spectra petitioners assert that,
due to
the uncertainty in emissions estimates and the alleged
problems with limits
on
PIE,
it
is “not possible to determine whether or not the project is
subject to
various potentially applicable requirements.”
Spectra provides
a
list
ofrequirements, consisting of
federal
New Source Performance Standards
(NSPS) and
National
Emission
Standards
for
Hazardous
Air Pollutants
(NESHAPS), that
it feels
were not properly evaluated,
including
the
following:28
•
.
40
CFR
Part 60
(NSPS)
Subpart Eb
(Large Municipal Waste Combustors)
•
40 CFR Part 60
(NSPS) Subpart 0 (Sewage Sludge Incinerators)
•
40
CFR
Part
60
(NSPS) Subpart VV
(Equipment
Leaks ofVOC in the Synthetic Organic
Chemicals
Manufacturing Industry)
•
40 CFR
Part 63 (NESHAP) Subpart
EEE
(Hazardous
Waste Combustors)
•
40
CFR Part 61
(NESHAP)
Subpart
E (National Emissions
Standards
for Mercury)
In the
Appendix to their petition,
the Spectra petitioners also
list
NSPS
subparts RRR
and NNN.
Spectra
also broadly argues
that other standards
not specifically identified may also
have been
left out
of the
permit.
EPA
addresses
each of
these
allegations
separately below, including
the
applicability of
40 CFR
part 60, Subpart
Db,
the NSPS
for Industrial-Commercial-Institutional
Steam
Generating
Units, as it relates
to
comments raised
by
Spectra in
its
petition.
a.
40
CFR Part
60 (NSPS) Subpart Eb (Large Municipal
Waste Combustors)
Masada’s pennit
application and supporting materials assert
that
the gasifier
combusts “lignin,”
which is the
term
they use todescribe the general process residue
that remains after
the hydrolysis step.
They
distinguish lignin from municipal
waste,
and assert that the gasifier is not a municipal waste
combustor subject to subpart Eb because it combusts lignin,
not municipal solid waste
(MSW).
The
draft permit did
not incorporate
subpart Eb
requirements, and EPA
in its December 6
letter
affirmed
that
“NYSDEC has identified
and applied the appropriate
federal NSPS
to
this proposed facility.”
Spectra argues that
the
lignin
is simply
“sugar-free MSW” because hydrolysis removes
recoverable sugars fiDm
the
municipal waste stream, but
the remaining material
is otherwise
indistinguishable
from MSW.
They argue that
simplyreferring to lignin as a by-product
of
chemical
processing of
MSW
is not sufficient to allow
lignin
to
avoid being classified as MSW.
Spectra
also
“Petitioners describe the list they
submitted
as “a starting point” but state that it is “not intended
to be exhaustive.”
Without greater specificity, general claims about the inability to evaluate the
applicability ofpotential requirements
is not sufficiently detailed to maintain
a title
V count.
26
argues that theuse ofthe
term
“gasifier/boilei-”
does not change the real
purpose
ofthe
gasifierunit,
which they
describeas “heat transfer.”29
Although petitioners do not refer to the definitions in the NSPS, these definitions
are important
in resolving their claims.30
MSW means “household, commercial/retail, and/or institutional waste.”
The
definition provides
a specific
exemption for
“industrial process or manufacturing wastes,” among others.
This
exemption is particularly
important here because, as noted above, EPA has determined that part
of
the Masada
facility is an embedded
chemical process plant.
The hydrolysis step
is part
of
this
chemical
process plant,
and
is the
step which
results
in the formation oflignin residue.
It is
EPA’s judgment that
the lignin
residue is a process
waste from the embedded chemical plant,
and is therefore exempt from
the definition ofMSW.
Although the input to the chemical process plant
is
itself
a waste, the exemption
in the NSPS
definition
is not
restricted to wastes from
processes using specific
types offeedstocks.
Any industrial process waste, unless
specifically included in the definition, is exempt.
Accordingly, the
waste
that
results
from
the Masada process is exempt.
The definition ofMSW does specifically include refuse derived fuel (RDF) within the meaning
of “household,
commercial/retail, and/or institutional
waste.”
RDF means “a type
of MSW
produced
by processing MSW
through shredding and size classiflcatioa”
This aspect
of the definition must
also
be addressed
to
see
if
it is at odds with the exemption noted above.
EPA finds that the lignin
is not
RDF, and
thus, there
is no
conflict with the exemption noted above.
The types ofmaterial
initially being
collected by
the Masada fhciity do
fall within the definitionofMSW, and the processing that occurs as
an
initial step does result
in the production of
RDF within
the
meaning ofthe NSPS.
However,the
Masada facility does
not then combust the RDF.
The
RDF undergoes an acid hydrolysis step which
significantly alters its chemical
properties and creates what the parties in this case
refer to as iignin” or
“lignin
residue.”
Information provided by Masada in its
November 2,
1999,
response comparing
the
percentage (by dry weight)
of
various elements in MSW versus lignin
residue indicates
that
acid
hydrolysis processes like
Masada’s increase the sulfur content by
210 percent, the
caEbon content by
33
percent, and oxygen by
5 percent.
Similarly there
are significant decreases in hydrogen (37
percent), nitrogen
(32 percent), and
ash
(43
percent).
These significant chemical changes, which result from
the hydrolysis process, are well outside
the shredding
and
size
classification
processes referenced in the RDF definition.
Because
the
chemical
separation (hydrolysis)
of
recoverable sugars fivm RDF, results
in
significant chemical changes
to
the
original RDF,
EPA finds
that the lignin is not RDF under the NSPS.
Because lignin
is not
RDF,
and
29
Here, it is
unclear whether Spectra believes that the purpose of the gasifier is to eliminate lignin
or provide energy to the chemical process.
However, regardless of Spectra’s position, the relevant
discussion for NSPS applicability
is whether the gasifier
is combusting MSW.
The
question of whether
a
combustion
unit recovers energy through heat transfer is not relevant to whether the unit
is covered by the
NSPS for MWCs.
“The relevant definitions are found in 40 CER 60.5 lb.
27
because industrial process
waste is specifically exempted
fixm the MSW definition,
EPA finds that
lignin does not fall
within the definition
ofMSW.3’
EPA does not thither consider the question ofwhether the gasifler
is a
processwhich falls
under
the NSPS definition ofa municipal
waste combustor unit, because for reasons discussed above,
the material charged
to the
gasifler (lignin residue) does
not
full
within
the definition of MSW.
Thus,
EPA finds
that NYSDEC acted properly in determining that the Masada facility
is not subject
to
NSPS
subpart Eb.
b.
40 CFR Part 60 (NSPS) Subpart 0 (Sewage Sludge Incinerators) and 40
CFR Part 61
(NESHAP) Subpart E (National Emissions Standards for Mercury)
The Spectra petitioners claim that Masada has“failed
to
expressly demonstrate that
the
proposed facility will not
be subject to
40
CFR 60, Subpart 0” and assert that it should
apply unless
Masada demonstrates that
sewage
sludge
will
not be
incinerated
(or
incinerated
in
amounts below the
NSPS cutoffof 1000 kg per day).
They allege that Masada does not appear
to
know
whether
its
sewage will be hydrolyzed or later combusted along with
lignin.
Petitioners likewise claim that Masada
has failed
to
provide data on mercury in the
incoming
sewage sludge.
They state
that part 61
subpart E
applies
to
any plant that dries
or
incinerates wastewatertreatment plant sludge containing mercury.
information from Masada indicates that, like the RDF discussed above,
the sewage sludge used
in
the Masada
process undergoes significant chemical transformation
prior to
gasification.
According
to
its November 2,
1999, submittal to EPA, the sludge
is blended and then hydrolyzed in sulfuric
acid.
Contrary
to petitioner’s
claims, Masada has indicated in its November submittal that all ofthe sewage
sludge, septage, and leachate undergoes this process. This process results in the formation ofcarbon
dioxide and soluble compounds.
The carbon dioxide
is
recovered, and the
liquid containing the soluble
compounds is used to facilitate hydrolysis.
What remains
is a
dewatered material, which Masada refers
to as “acidified
biosolids.”
These biosolids are fed to the gasifler.
As with the material that resulted
from
the hydrolysis of MSW,
EPA
concludes
that this material, which results from the hydrolysis
of
blended sewage sludge, is
significantly
different from sewage sludge such that gasification/combustion
of
this material
is not subject
to
the NSPS for sewage sludge incineration, nor is
it subjectto the NESHAP
for mercuryemissions from plants that
incinerate
sewage sludge.
c.
40 CFR Part 60 (NSPS) Subpart VV Equipment
Leaks of VOC
in the Synthetic
Organic
Chemicals Manufacturing Industry (SOCMI)
“In
a
footnote, the Spectra
petitioners argue that Masada’s lignin is hydrolyzed solid waste with
no
beneficial
use (including as
a
fuel), in contrast to other types of lignin.
The determination whether
Masada’s lignin
is
MSW under the NSPS has nothingto do with whether lignin has
a beneficial use.
Therefore, EPA
is
not considering
this comment further in its evaluation of whether the NSPS applies.
28
The
Spectra petitioners
list
subpart VV
in
its
list ofpotentially applicable
requirements, and
argues that the standards ofSubpart VV must be incorporated
into
any
issued pennit.
Spectra does
not allege any specific instance ofthe failure
to
properly apply
subpart VV, and EPA notes that the
issued
permit does incorporate subpart VV standards.
Therefore, EPA dismisses this claim as moot.
d.
40 CFR Part
63 (NESHAP)
Subpart EEE (Hazardous Waste Combustors)
The
Spectra petitioners
assert that
the
facility is subject to the requirements applicable to
sources
burning hazardous waste
in a combustor, 40 CFR
part 63, subpart EEE.
Specifically, they
argue that
the
source has
not
demonstrated that the lignin or residual municipal
solid waste that
will be
burned
in the gasifier will not
contain hazardous waste.
Spectra is correct
that
the
NESHAP requirements
apply to all hazardous waste combustors,
defined in 40 CFR 63.1201
to include an incinerator
that “burns hazardous
waste at
any time.”
However, Masada maintains that the source will not bum
any
hazardous waste and
in
fact
is expressly
prohibited from accepting
any
hazardous waste under its NY state solid waste permit.
EPA has no
information
—
nor has
Spectra
presented any
—
to suggest that
the
facility will accept
any hazardous
waste.
Like all
waste handlers, Masada
will have to
determine whether the material that
it is
handling
is
classified as a hazardous
waste.
More
specifically,
Masada will have to ensure that
the waste they are
processing is not
hazardous at the time they accept the waste and after
it has undergone the acid
hydrolysis process and is
placed into the combustion unit.
This
obligation,
however, is independently
applicable
(subject
to government oversight and
potential enforcement
action) and is notan applicable
requirement
that
should be incorporated
into the source’s title V permit.
Therefore, based on
Masada’ s representationthat
the source will not
burn
any
hazardous waste,
I
conclude
that Spectra
has
not shown that the
NESHAP requirements
apply to
this
source.
e.
40 CFR Part 60 (NSPS)
Subparts NNN (SOCMI Reactor Processes) and RRR
(SOCMJ
Distillation Operations)
In the attachment to the Spectra petition, the Spectra petitioners assert that NSPS subparts for
SOCM! Reactor Processes (subpart RRR) and SOCMI Distillation Operations (subpart NNN) should
also apply to the Masada facility.
They do
not cite any more specific basis
forthis assertion.
EPA has
reviewed the applicability ofthese
two
standards, and has determined that neither of
them applies to the
Masada
facility.
EPA issued a determination
on
October
7, 1996,
which clarified
that subparts
RRR
and NNN do not apply
to
processes which
produce ethanol through biological processes like
Masada’ s
process. The determination states
that these two roles were developed for specific processes
involving synthesis of
organic chemicals using petroleum-based feedstocks
and not
biological
fermentation processes.32
As
the October
1996 memorandum
makes clear, because the Masada
32
Memorandum regarding “Applicability Determination for Biomass Ethanol
Production,” dated
October 7,
1996, from Reggic Cheatham,
Chief, Chemical Industry Branch, EPA Office of Enforcement and
29
facility doesnot
produce
ethanol
from a petroleum-based feedstock,
it is not subject to NSPS
subpart
NNN nor is
it subject to subpart RRR.
Therefore EPA finds that
the
pemiit is
not deficient with
respect to these two
standards.
f
40
CFR Part
60 (NSPS) Subpart Db (Industrial-Commercial-Institutional Steam
Generating Units)
EPA has examined
the
Spectra petitioner’s broad claim that
other standards not specifically
identified may also have been left out ofthe permit
EPA found one instance of a requirement that
was
left out ofthe permit
-
NSPS subpart Db (Standards ofPerfonnance for Industrial-Commerdal-
Institutional
Steam
Generating
Units).
This standard
was properly applied
to the package
boiler,
and
appropriate limits were included
in the permit.
However, as discussed below, subpart Db also contains
requirements that apply
to the gasifier.
Subpart Db applies to any steam generating unit that commencedconstruction, modification,
or
reconstnrction after June
19,
1984, and has a
heat
input capacity ofgreater than 100
million
BTU/hour,
regardless of fuel.
Whereas subparts
Eb and 0 did not apply
because
the
fuel
charged
to the
gasifler
was not covered by
the regulations,
general subpart
Db applicability does not depend on the type of
fuel used.
Clearly, the gasifier
unit is used to generate steamand its capacity
of
245
million BTU/hour
is
within
the NSPS
specified range.33
Whereas general applicability ofSubpart Db does not depend on the firel, Subpart
Db imposes
specific emission
limits
which
arc based on the typeof fuel combusted.
Standards are specified
for
combustion of coal, oil, natural gas, wood, and MSW.
EPA finds that none
of
these standards,
including the MSW standard, apply to the combustion oflignin.
The MSW standard does
not
apply
under subpart Db
for the
same reason that
subpart Eb did
not apply, as
discussed above: the fuel
combusted (lignin
residue)
is not MSW.34
However, EPA notes
that there are certain basic reporting
and recordkeeping requirements
in 40 CFR 60.49b, which apply
regardless
ofthe fuel
combusted.35
Compliance
Assistance
to
George Czerniak, Air Enforcement and
Compliance
Assurance Branch,
EPA
Office of Enforcement and
Compliance
Assistance.
The
determination was later amended to
clarifr
that
such
biological
processes are still subject
to NSPS subpart VV
for equipment leaks.
See Memorandum
dated September
8,
1998
from
Reggie Cheatham,
Chief, Chemical Industry Branch, EPA Office of
Enforcement
and Compliance
Assistance
to Air Branch Chiefs, EPA Regions
1-10.
As noted
above,
subpart VV
has been addressed
in the Masada permit.
~ The
gasifier
is also
subject to NSPS
subpart Dc when burning natural gas,
as
it does at startup.
The requirements
for subpart
Dc are already i~
the issued
permit, and are not at
issue in
any of the
petitions.
~‘
Although the definition of MSW used in Db differs slightly from the definitions used in Eb, it
is
EPA’s judgment that neither covers lignin
residue, for reasons
discussed above..
~ Specifically, EPA finds that the requirements of sections 60.49b(a), (d), and (o) apply.
30
The purpose
of these requirements is to
assure that
facilities potentially regulated by
subpart Db (some
of
which
are capable ofburning multiple fuel types) are properly subjected
to
the appropriate emissions
standards
when
burning a given fuel.
These reporting and recordkeeping
requirements clearly apply
even if the source primarily combusts a
fuel
that is
not fUrther regulated by
subpart Db emissions
standards, as
is
the
case here.
Therefore, EPA is
granting
the request to object to
the permit
with
respect to this issue.
Pursuant to Sections 505(b) and 505(e) ofthe Act, 42
U.S.C.
§~
7661d(b) and
(e), and 40 CFR 70.7(g)(4) or
(5)
and 70.8(d), NYSDEC
is required
to
modi& the permit to
incorporate the
reporting and
recordkeeping requirements of40 CFR 60.49b.36
Where possible,
these
requirements should be
harmonized
with reporting
and recordkeeping requirements already contained in
the permit.
g.
Accidental Release Provisions (40 CFR Part
68)
In separate petitions,
petitioners Daniel Nebus and
Jeanette Nebus both raise concerns about
the possible effects of an explosion at the
Masada facility.
While
the
petitioners raise several
general
questions about
such effects,
the relevant question for
this title
V
petition
is whether the
facility has
complied with the
Clean
Air Act requirements for accidental releases of
“regulated substances,” which
are extremely
hazardous substances
listed under section
11 2(r)(3) ofthe Act.
On
this point,
the
petitioners assert
that section
112(r) requirements are
“missing from the plan.”
Mr.
Nebus
is
particularly
concemed about an explosion of ethanol, but also
identifies
several
other substances stored
in tanks
at the Masada facility,
including
sulfuric acid, gasoline,
fuel oil and
ammonia
The regulations implementing
112(r), codified at 40 CFR
Part 68,
apply to sources that have
regulated substances
presentabove
certain thresholds.
EPA has reviewed Masada’s application and
supporting information
and has
located no
evidence
—
nor has Spectra pointed to
any
—
that
any
regulatedsubstance
will be present at the
Masada facility
in
quantities above
the
112(r)
thresholds.
The
only
substance identified by
Mr.
Nebus that
is listed in the
part 68 regulations
is
anunonia.
However,
the regulation applies to
ammonia in concentrations
of 20 percent or
greater.
NYSDEC detennined
that
part
68 did not apply because the
ammonia
present does not exceed
the 20 percent concentration
threshold.37
Based on
this information,
EPA finds
that Spectra has failed
to show
that the part 68
requirements
apply to the
Masada
facility.
Thus, the permit,
as issued, is sufficient
under 40 CFR
68.21538
36
Under 40 CFR 70.7(d)(l)(iii), permit amendments that require
more frequent reporting by the
permittee are
eligible
for the administrative permit amendment
process.
“
EPA confirmed this via
a telephone conversation on March
7, 2001
between Thomas Miller,
NYSDEC
Region
3, and
Lauren Steele,
EPA Region 2.
~‘
Compliance with the requirements of part 68 does not, however, relieve Masada of its legal
obligation
to meet
the
general duty requirements of section
I 12(r)(l) of the Act to identify hazards that may
result
in an accidental release,
to design
and maintain a
safe facility taking such steps as are necessary to
prevent releases, and to minimize the consequences of an actual accidental release.
As the Administrator
31
h.
Additional
Requirements
With
respect to all
other applicable requirements
not
specifically addressed elsewhere in this
Order, none ofthe petitioners have presented specific infonnation
to
identi~’
any missing
or
improperly
included requirements.
In
response to
the
Spectra petitioners’ general claim that
there are other
potentially applicable
requirements,
but that
there is
not
sufficient infbrmation to evaluatetheir
applicability, EPA has
examined the record, and has determinedthat
sufficient inibmiation is
available
to conclude that, except
as specifically noted above,
the
permit
is
adequate
to assure
compliance
with
alJ
applicable
requirements.39
C.
Other Issues
1.
Environmental
Justice and Non-Discrimination under Title VI
ofthe
Civil Rights Act
Petitioners Deborah Glover
and Jeannette Nebus allege that
the
permit should be denied
because
US EPA and NYSDEC
have
not complied
with Executive Order 12898,
entitled “Federal
Actions to Address Environmental Justice
in Minority Populations
and
Low-Income Populations.”
Petition of
Deborah
Glover, dated
August
19,
2000,
pp.
2
and 4.
Ms. Clover notes that
the City of
Middletown has a
large minority
and
low-income population and that
US EPA and NYSDEC did not
appropriately
identi& “the multiple and cumulative exposures”
in this area.
She
also alleges that
the
many non-English speaking residents were preduded from meaningfUlly pailicipating in the NYSDEC
public
process as
the notices were not in
Spanish
nor were
translatorsmade available
at the
hearing.
Ms.
Nebus also argues that
cmcial
public
documents were not translated and that
the
local minority
and
low-income
population has been “totally disregarded.”
Executive Order 12898, signed
on February
11, 1994,
focuses federal attention
on the
environmental and human health
conditions of
minority and low-income populations with the goal
of
achieving environmental
protection for all
communities.
The Order is
intended
to promote non-
discrimination in federal
programs substantially affecting human health and
the environment,
and
to
provide minority and low-income
communities access
to public
information on, and an opportunity
for
stated
in the Shintech Inc. Tide V Order, Permit No. 2466-VO (Sept. 10,
1997), at
12, n.9,
“section
I 12(r)(l)
remains a self-implementing requirement ofthe Act, and EPA
expects and requires all
covered sources to
comply with the general duty provisions of I 12(r)( I).”
~ Although
not identified by
the petitioners, this review
also considered the recently-promulgated
NSPS
for Commercial and Industrial Solid
Waste Incineration Units (40 CFR part 60, subpart CCCC).
These
standards do
not apply to facilities that recover energy for industrial
purposes.
Masada recovers energy to
produce
steam, which is used elsewhere
at the plant, and is thus
not covered by this rule.
I also note that
EPA has
listed “industrial boilers,” “institutional/commercial boilers,” and “process heaters” on the list of
source categories for which hazardous air
pollutant emission standards are being developed under section
112 of the Act.
66 Fed.
Reg. 8223 (Jan. 30,
2001).
However, these standards have not yet been proposed
and clearly are
not under consideration in this Order.
32
public participation
in, matters relating
to
human health or the environment.
It generally directs federal
agencies to
make
environmental
justice part oftheir mission
by
identifying and addressing, as
appropriate,
disproportionately high and
adverse
human
health or environmental effects oftheir
programs,
policies, and
activities on
minority
and low-income populations.
At issue
here is whether EPA should object to the
permit
issued by NYSDEC
because
it did
not
implement
the
Order.
However,
the Order’s provisions apply only to the
actions offederal
agencies.
As noted in the Administrator’s Order responding to the Shintech title V
petition, Permit
No.
2366-VU, 2467-VU, 2468-VU (Sept.
10,
1997), at p.8, n.5,
“while
Executive Order 12898
was
intended for
internal
management ofthe executive branch and not to
create
legal
rights, federal
agencies
are required
to implement
its
provisions
‘consistent with, and
to the extent permitted
by, existing law.”
Sections 6-608
and 6-609, 59
Fed. Reg.
at 7629, 32-33 (Feb.
14,
1994).
Thus, the Order does not
apply
to actions
taken by New York State.
The
Masada
facility received a combined
permit
incorporating
the
requirements
of New York’s
title V program
and
its minor source construction
program.
New York’s title V program received interim approval in 1996.
61
Ed.
~g.
57589
(Nov.
7,
1996);
see also
61
~
j~g.
63928 (Dec. 2,
1996) (correction); 40 CFR
Part
70, Appendix
A).
New York State
therefore
is responsible for issuing and
administering Masada’s permit
under section
502 of the Act.
Similarly,
New York’s
minor
source construction program, codified at 6
NYCRR
201,
was
approved by
EPA in
1997 as
part
ofthe state’s implementation plan.
62
Fed.
Reg. 67006
(Dec. 23,
1997).
As the
U.S. Environmental Appeals
Board recently stated, permits
issued under a
state’s
approved
minor
source
constniction program “are regarded as creatures of state law
that can
be
challenged only under the state system ofreview.”
In re: Carltort Inc. North Shore Power Plant. PSD
Appeal No. 00-9 (Feb. 28, 2001), slip op. at
5,40
Consequently, Executive Order
12898
does not apply to the State’s issuance of the permit at
issue here.
As explained above, to
justi~
exercise
of an objection by EPA to a
title Vpennit
pursuant
to Section
505(b)(2)
ofthe
Act,
42
U.S.C.
§
7661 d(b)(2), the petitioner
must demonstrate
that the
permit
is not in compliance
with
the
requirements
of the Act.
Since the Order by
its terms does
not
extend to the State’s
issuance
of permits,
it
is not an applicable requirement of the Act.
Thus, the
request
to
object on
this ground
is denied.
However, ifNYSDEC
is a
recipient
of EPA
financial assistance, its programs and activities,
including
its
issuance ofthe
Masada permit, are subject
to
the requirements
ofTitle VI of the
Civil
~°
Pursuant to 40 CFR
§
52.21(u),
NYSDEC has been delegated authority to administer the
federal
PSD program.
~
47
~$.
~
31613
(July21,
1982).
However, New York’s decision that the
source does
not require a
PSD permit means that there is no federal PSD permit for this source.
See
e.g.
In re:
Carlton.
Inc. North
Shore Power Plant PSD Appeal No.
00-9 (Feb. 28, 2001), slip op.
at 5 (dismissing challenge to
permit
issued under Illinois’
approved minor NSR program because “the Board’sjurisdiction
is limited to
federal PSD permits that
are
actually
issued;
it does not extend to state decisions reflected in state-issued
permits,
even where those decisions lead
to the conclusion
not to require
a
PSD permit at all”) (emphasis
in
original).
33
Rights Act of 1964, as amended,
and EPA’s implementing
regulations, which
prohibit
discrimination on
the basis of race,
color, or national origin.
42 U.S.C.
§
2000d et seq.; 40
C.F,R. Part
7.
The
petitioners may file a complaint under
Title VI
and
EPA’s
Title VI regulations if they believe that the
state discriminated against them
inviolation of those
laws by
issuing the
permit
to
Masada.
The
complaint, however, must
meet
the
jurisdictional
criteria that are described
in EPA’s Title VI
regulations
in
order for EPA to
accept it for
investigation.4’
2.
Environmental Impacts
Many petitioners, including Ms.
Dellasandro, Mr. Feman, Ms. Glover,
Ms. Lee, Mr. Sprague,
Ms.
Sprague, Mr. Weimer and
Mr.
Wodka, broadly criticized
the location of the
Masada facility,
suggesting that, by
locating within the city
limits
of
Middletown, the source
will be too close to
children
and
other
industrial facilities.
Similarly,
another
widespread concernwas that
this facility will
contaminate
the
community’s air and water.
This issue was raised by
Mr. Centeno, Ms. Centeno,
Ms.
Dellasandro, Ms. Jacobs,
Ms. Lee, Ms.
Mongilia, Mr.
Sprague, Ms.
Sprague,
and Mr. Wodka.
The Clean AirAct and NYSDEC’s applicable implementing regulations require review ofthe
types ofconcerns raised
by
these petitioners.
While recognizing that
new sources of
air pollution will
have effects
on
local ambient air quality, this review assures that such ambient
impacts are within levels
that provide
adequate protection
forpublic health.
This
process focuses primarily
on the
National
Ambient Air Quality
Standards (NAAQS).
EPA sets these standards
to
protect the public health with
an adequate margin
of safety.
See
CAA
§
109(b).
States are required
to adopt plans,
known as State
Implementation
Plans
(SIPs)
to
attain
and maintain these
NAAQS for
six key
pollutants,
known as
criteria pollutants.
As part
of these
plans, States are required to adopt aries to assure that new and
modified
sources
do not
interferewith attainment
or maintenance ofthe NAAQS,
and
do not conflict
with the SIP.
See
40 CFR
§51.160-165.
NYSDEC
has submitted,
and
EPA
has
approved,
regulations that fulfil these requirements.42
~‘
Under Title VI,
a
recipient of federal financial
assistance may not discriminate on the
basis of
race, color, or national origin.
Pursuant to EPA’s Title VI
administrative regulations, EPA’s Office of Civil
Rights
conducts
a preliminary review ofTitle VI complaints for acceptance,
rejection, or referral.
40
C.F.R.
§
7. l20(d)( I).
A complaint should meet jurisdictional requirements
as described in EPA’s Title VI regulations.
First,
it must be in writing.
Second, it must describe alleged discriminatory acts that may violate EPA’s Title
VI
regulations.
Title VI
does not cover discrimination on the grounds
of income or economic status.
Third,
it must be timely filed.
Under EPA’s Title VI regulations,
a complaint must be filed
within
180 calendar days
of the alleged discriminatory
act.
40 C.F.R.
§
7. 120(b)(2).
Fourth, because EPA’s Title VI regulations only
apply to recipients of EPA financial assistance,
it must identify an EPA recipient that allegedly committed
a
discriminatory act.
40 C.F.R.
§
7.15.
42
The relevant regulations
are found primarily
in 6 NYCCRparts 200
and
201.
Additional guidance
is available discussing ambient
impact assessments
in more detail.
See NYSDEC’s
Air Guide
serious of
documents.
34
The
primaly requirement
in the New York SIP
for
addressing minor sources states that,
“the
commissioner
will not issue
a
permit... unless
he determines
that...
the
operation
of the source will not
prevent the
attainment
or
maintenance
of
any
applicable ambient air
quality standard.”
6
NYCRR
201.4.
None of the aforementioned petitioners raise any specific
claims that, in
approving
construction
ofthe
Masada
facility, NYSDEC
failed to meet
this requirement.
Indeed
the
pennitting record
demonstrates that
the NYSDEC
commissioner did make the
required determination.
The NYSDEC
determination was based
on an air
quality
(i.e.,
modeling) analysis designed
to
simulate
the ambient
impacts of the
Masada
facility at
its planned location.
The
analysis
was submitted
by
Masada, and
was
conducted
pursuant
to New York State
guidelines.
Under
these guidelines, modeling must
generally
reflect worst case operating and meteorological
conditions,
and must consider
the effects of other
sources
in the
area.
A report issued
by NYSDEC
concludes
that:
“The applicant’s air
quality analysis has
met
Department guidelines
in
assessment
of
criteria and
non criteria
pollutants
in
the
facility vicinity.
It can flnther be
concluded
that
the facility should
meet all
criteria AAQS Ambient
Air
Quality Standards..””
The
findings statement included with
Masada’s final operating permit
reiterates the
results
of
this
review.
The
model
results
themselves showed
that
the
resulting ambient levels
of
pollution
were well
within
acceptable
levels
and
well below the NAAQS.
Based on this
modeling, NYSDEC determinedthat
the
Masada
facility would not
interfere
with
attainment
or
maintenance
of the
NAAQS, and issued the
construction permit.
In
order to maintain a legitimate grounds
for objection to the
title V permit,
the
petitioners would
have
to raise specific allegations
that this
analysis, or the determination by NYSDEC,
failed to comply withapplicable
regulations.
In the absence of such allegations, and based on the
actions by NYSDEC
described above, EPA finds
that
the aforementioned petitioners’ have not
demonstrated
that the
State has
failed to
make
the
required determination, and thus
I
deny the
petitions
on
this
basis.
I also note
that NYSDEC conducted a similar reviewpursuant
to
its State air toxics regulations
and policies.
While these regulations are
not
considered
applicable
requirements
for
purposes
of title V
of the Act, NYSDEC
further determined that
the
impacts
of
toxic
pollutants were also
all well below
the maximum
levels
defined
in the State
guidelines.44
Regarding concerns about
water
quality raised
by
some
ofthe
aforementioned petitioners,
no
issues were identifed
that
point
to the
failure
of the
Masada permit
to
incoiporate all
applicable
~ Letter and
Review from Alan Elkerton, NYSIDEC Division
ofAir Resources, to Tom Miller,
NYSDEC Region 3, April 9,
1999.
~J~
As
distinct from criteria pollutants, State programs to review
ambient impacts of other
pollutants, such
as the NYSDEC regulations establishing guideline concentrations for a
number of toxic
pollutants,
are not required
under the Act, and are not applicable requirements for title V operating permits.
States may
elect to include these requirements
in
a “State-only” portion ofa title V permit.
35
requirements under
the
Clean Air Act.
As
such, the EPA dismisses
these claims.
The petitioners
concerns may be addressed
by
other environmental laws, but
compliance with
those
laws is nota
proper objection issue under title V of the Clean
Air Act,
and
is not
addressed farther in
this Order.
3.
Additional
Issues
The
Spectra
petitioners also
incorporate
into
their petition,
by reference only, “each
and
evely
comment contained in the 2000
Supplemental Comments as a basis for objecting
to the permit as
ifthey
w~re
frilly
reprinted
herein.”
Further,
they
argue that
each issue in
their original
1999 comments
is
also
incorporated
into
their
petition.
Part
of the basis
for such a claim is
that
the issues
raised have
never
been
substantively
addressed
by NYSDEC.
EPA
disagrees with this
claim, as noted above.
In
addition,
it
is
inappmpriate
fora petitioner to simply
incorporate their
prior
comments into theirtitle V
petition.
Under section
505(bX2),
it is the responsibility of a
petitioner
to
demonstrate to the Agency
that
the terms of a
pemiit are
not
in
compliance
with
the
requirements
of the Act.
As the Administrator
stated
in
the
Shintech Inc. title V Order,
Permit No. 2366-VO, 2467-VO, 2468-VO (Sept.
10,
1997),
at 20, “EPA has no
generalized
duty to review the permit
and
to
determine
and rectifji all
inaccuracies
and
inconsistencies.”
Likewise, I find that
wholesale
incorporation
of an entire setof prior
comments
does
not pmvide
a specific enough
basis
for objection to
meet
the petitioner’s burden.
For
these reasons, I reject the Spectra petition
with respect
to any issues included in the referenced sets of
comments but not specifically raised
in
the
petition.
Finally,
several
ofthe
petitioners
raise additional issues which are not
germane
to
a petition
under title V because they do not
pertain
to applicable
requirements or
permitting requirements
of40
CFR
part 70.
Forexample,
•
Spectra notes
that Masada withdrew plans
to
constructa similar facility
in
Birmingham, Alabama
and
charges that
various elected officials contacted
EPA and NYSDEC
to
influence approvals for
the Masada project.
•
Ms. Glover alleges
that
NYSDEC
arid Masada had
a “callous indifference to the concerns of
the
citizens
of Middletown.”
She also mentions EPA’s
NO~
SIP call and
NYSDEC’s
compliance with
other environmental statutes.
•
Ms. Nebus also
argues that NYSDEC has
been
“capriciousand
arbitrary
in their
dealings” with
her.
She
further expresses concern about the
exhaust from diesel trucks associated with
the facility
and suggests that
NYSDEC should test the nearby Monhagan Brook for contamination.
None of
these
claims, even
if
true,
could
form the basis ofan EPA title V
objection
since
they do not
allege
that Masada’s permit
is not in compliance with the
CAA requirements
applicable to
this source.
As
such,
these issues are not
germane,
and EPA doesnot
address
them thither
in
this Order.
III.
CONCLUSION
36
For the reasons set
forth above and
pursuant
to sections 505(b) and 505(e) of the Act, 42
U.S.C.
§~
766ld(b) and (e), and 40
CFR 70.7(g)(4) or
(5)
and
70.8(d),
1 deny the petitions submitted
by the following
persons:
Lois
Broughton, Wanda
Bmwn,
Louisa and George
Centeno with Leslie
Mongilia,
Maria Dellasandro,
It
Dimieri,
Lori Dimieri,
Dawn Evesfield,
Marvin
Feman, Deborah
Glover,
Aime Jacobs, Barbara Javalli-Lesiuk, Marie Karr, June Lee, Ruth MacDonald, Bernice
Mapes, Donald Maurinio, Mice Meola, Daniel Nebus, Mr. and
Mrs. Hillary Ragin, M. Schoonover,
Mildred
Sherlock, LaVinnie
Sprague, Matthew Sprague, Hubert van Meurs,
Alfred
and Catherine
Viggiani, Paul Weimer and
Leonard Wodka.
I
grant
the petitions from
Spectra
and Jeanette Nebus to
object to the NYSDEC
permit
on the basis of inadequate public notice with respect to the PTE
limits,
and
Spectra’spetition with respect to the
applicability of the NSPS Db recordkeeping requirements.
NYSDEC
shall
take
appropriate
steps, as discussed above,
to resolve these objections.
I deny the
remainder of Spectra’s
and
Ms. Nebus’ petitions.
Mav2.2001
Is’
Dated:
Christine Todd Whitman,
Administrator
37
Pre-filed
Testimony
of Cynthia
Skrukrud,
Ph.D.
My
name is Cindy
Skrukrud. I am employed as the Clean Water Advocate for the Illinois
Chapter ofthe Sierra Club.
I have reviewed and commented on NPDES permits for the Club
since 2000.
I first began to study NPDES permits issued in the Fox and Kishwaukee watersheds
in
1996
while employed by the MeHenry County Defenders,
a county-based environmental organization.
I have participated in commenting on a number ofdraft permits and participated in a number of
heahngs on draft NPDES permits. This
is true although McHenry County
Defenders
and the
Sierra Club comment on only a small fractionofthe draft permits that are noticed,
and hearings
on draft NPDES permits are fairly rare.
The Sierra Club, Illinois Chapter, along with Prairie Rivers Network, is proposing amendments
to
Part 309 subpart A ofthe Illinois Administrative Code Title 35
Environmental Protection Act
in
order to better ensure fall public participation in the issuance ofNPDES
permits in
Illinois.
The process of the issuance ofNPDES permits necessitates that the Illinois EPA and
the
discharger hold lengthy discussions about the nature of the proposed discharge
in order to
develop a draft permit. Consequently,
a lot of information has been exchanged between the
Agency and the discharger by the time the public receives notice oftheproposal to issue
a new,
modified or reissued permit. In order to
allow the public the opportunity
to be fully engaged in
the decision on whether or not to issue a permit for a given discharge, the public needs an
informative public notice of the draft permit and access to
the complete administrative record
(“permit file” using
current Illinois EPA terminology). The public should
also be kept informed
ofany proposed changes in the draft permit that develop prior to the Agency’s final decision to
issue or deny the permit.
Because the impact ofthe proposed discharge on the receiving water body is usually the public’s
utmost concern, our proposed amendments require that more information about the receiving
waters be included in the fact sheet. It is vital that the public know the information about the
receiving water the Agency is using to base its decision. Because members ofthe public may
have more intimate knowledge ofa water body than the Agency does, they may be able to
provide information about the waterbody and
its uses, which the Agency lacks. This information
could include site specific knowledge ofthe use ofthe water body by children (a factor important
to
the Agency’s consideration ofdisinfection requirements in the permit) or by endangered and
threatened species of aquatic and other terrestrial life.
The public needs to be able to
fully understand the conditions ofthe permit. That the public has
the opportunity to review
and comment on the conditions that will appear in the final permit is
critical. The public mustbe able to know about and comment onwhat will be discharged, the
limits on the discharge, and how those limits are
to
be monitored. Over the time period for which
a
NPDES
permit
is issued (typically
5
years), the monitoring requirements are the only means by
which the public (and the Agency) can gauge the impact which the discharge is having on the
1
Public participation
in the NPDES process is too important
to be
subject to
unnecessary
or inappropriate limitation.
Prairie Rivers Network
urges the Pollution Control
Board to
adopt these changes to ensure that the public
will always have full
and fair opportunity to
participate
in
this process.
2
Pre-filed
Testimony
of Albert Ettinger
I am Senior StaffAttorney at the Environmental Law & Policy Center ofthe Midwest
and Water
Issues Coordinator and
General Counsel
for the Illinois
Chapter of the Sierra Club.
I
have worked in
Illinois on matters relating
to water pollution
and implementation of the federal
Clean Water Act since
1982.
1 am
the primary drafter of the petition
to amend the Part 309
Subpart A.
Earlier drafts
of
the petition were discussed with
officials
of
Illinois EPA and members of
various interest
groups concerned
with the NPDES permitting
process.
Various changes
were
made to
the draft in response to views
express
in these
discussions but
no
consensus was reached
as to the proposal.
The proposal amends
the most
recent version of the rule
as
published on
the Board’s Web
site.
I would
be pleased to answer
any questions
by the Board or members of the public
regarding
the
proposal,
the reasons that it is being
offered, or its expected
effect.
Petition to the Illinois Pollution Control Board
for Regulations
The
undersigned residents
of Illinois
hereby
petition
the Pollution Control
Board to amend Illinois
Administrative Code Title
35 Environmental
Protection
Act; Subtitle C: Water Pollution;
Chapter I:
Pollution Control Board; Part
309. The
amendments
sought are to improve
Illinois’ implementation of the
Clean Water Act, 33 U.S.C.
Section
1251 et seq., and National Pollutant Discharge Elimination System
(NPDES) by amending the relevant regulations to require that:
•
The public
is properly informed ofdraft NPDES permits and is provided a fair opportunity
to
comment on
substantial termsofpermits before they are
issued;
i
hearings are held whennecessazy to allow the public an opportunity to comment on draft permits
and important revisions to draft permits;
•
the administrative record regarding each
permit shows that the pennit was
properly issued and
that
the
pennit
does not
purport
to allow discharges
that
would cause or contribute to a violation
of
Illinois water
quality standards;
•
necessary monitoringof NPDES limits
and
conditions be required
in
permiLs; and,
•
Illinois
permit procedures and NPDES permits
comply with the Clean Water Act.
Name
6.
dkc~
Address
c.
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t
Petition to
the Illinois Pollution Control Board for Re2ulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative Code Title
35 Environmental Protection Act; Subtitle C: Water Pollution; Chapter I:
Pollution Control
Board;
Part
309. The amendments sought
are to improve
Illinois’
implementation of the
Clean
Water Act,
33 U.S.C. Section
1251
et seq., and National Pollutant Discharge Elimination
System
(NPDES) by amending
the relevant regulations to require that:
•
The public is properly informed of draftNPDES permits
and is provided a fair
opportunity to
comment on substantial terms
of permits before they are
issued;
•
hearings are held when necessary to allow the public an opportunity to comment on draft permits
and important revisions to draft permits;
•
the
administrative record
regarding
each permit
shows
that the permit
was properly issued and
that the permit does not
purport
to allow discharges that would cause
or contribute
to a violation
of Illinois water quality standards;
•
necessary monitoring of NPDES
limits and conditions be required in permits; and,
•
Illinois permit procedures and NPDES permits comply
with the Clean Water Act.
Name
Address
/&/9/
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I.
Petition to the Illinois Pollution Control Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative Code Title
35
Environmental
Protection Act; Subtitle
C: Water Pollution; Chapter I:
Pollution Control Board; Part 309. The amendments sought are to improve Illinois’ implementation of the
Clean Water Act,
33 U.S.C. Section
1251
et seq., and National Pollutant Discharge Elimination
System
(NPDES) by amending the relevant regulations to require that:
•
The public is properly informed of draft NPDES permits and is provided a fair opportunity
to
comment on substantial terms ofpermits
before they are issued;
•
hearings are held when necessary to allow
the public
an opportunity to comment on draft permits
and important revisions to draft permits;
•
the administrative record regarding
each permit
shows that
the permit was properly issued and
that the permit does not purport to allow discharges that would cause or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring ofNPDES
limits and conditions
be required in permits; and,
•
Illinois permit procedures and NPDES permits comply with the Clean Water Act.
Name
1.
;
2.r~4j,
&.
3.
:.L~i44~?
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8.
9.
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Address
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Petition to the Illinois Pollution Control Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative
Code Title 35
Environmental Protection
Act;
Subtitle C: Water Pollution;
Chapter I:
Pollution Control Board; Part 309. The amendments sought are to improve Illinois’
implementation ofthe
Clean Water Act,
33 U.S.C.
Section
1251
et seq., and National Pollutant Discharge Elimination
System
(NPDES) by
amending the relevant regulations to require that:
•
The
public
is properly informed of draft NPDES permits
and is provided a fair opportunity to
comment on
substantial terms of permits before they are issued;
•
hearings are held
when necessary to allow the public an opportunity to comment on draft permits
and important revisions to draft permits;
•
the administrative record regarding
each permit shows
that the permit was
properly issued and
that the permit does not purport to allow discharges that would cause
or contribute
to a violation
of Illinois water quality standards;
•
necessary monitoring of NPDES
limits and conditions be required in permits;
and,
•
Illinois permit
procedures and NPDES permits comply with the Clean Water Act.
Name
Address
Ct
8L
?-g~2~
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7.
IL
Petition to the Illinois Pollution Control Board for Regulations-
Thejnt~sigi~d
residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative Code Title 35
Environmental
Protection
Act; Subtitle C: Water Pollution; Chapter I:
Pollution Control Board;
Part
309. The amendments sought are
to improve Illinois’ implementation of the
Clean Water Act, 33
U.S.C.
Section
1251
et seq., and National Pollutant Discharge Elimination System
(NPDES)
by
amending the relevant regulations
to require that:
•
The public
is properly informed of draft NPDES permits
and
is provided a fair opportunity to
comment
on substantial terms of permits before they
are issued;
•
hearings are held when necessary to allow
the public
an opportunity to comment
on draft permits
and important
revisions to draftpermits;
•
the administrative record regarding each
permit
shows
that the permit was properly issued
and
that
the permit does not purport to allow discharges that would cause
or contribute to a violation
of Illinois
water quality standards;
•
necessary monitoring of NPDES
limits
and
conditions
be required in permits;
and,
•
Illinois permit procedures
and
NPDES permits
comply with the Clean Water Act.
Name
Address
i.
IamAertus
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(07/V
Petition to the Illinois
Pollution ControlBóard
for Regulations-
The undersigned residents of Illinois hereby petition the
Pollution Control Board to amend Illinois
Administrative
Code Title 35
Environmental Protection Act; Subtitle
C: Water Pollution; Chapter I:
Pollution Control Board;
Part
309. The amendments sought
are
to
improve
Illinois’
implementation of the
Clean Water Act,
33
U.S.C.
Section
1251
et
seq., and National Pollutant
Discharge Elimination System
-
(NPDES) by
amending the relevant regulations
to require
that:
•
The public is properly informed of draft NPDES permits
and
is
provided a fair opportunity to
comment on
substantial terms of permits
before they are issued;
•
hearings are held when necessary to allow the public
an opportunity to comment
on
draft permits
and important
revisions to draft permits;
•
the administrative record regarding each
permit
shows
that the permit was properly issued
and
that the permit does
not purport to allow discharges that would cause or contribute
to a violation
of Illinois water quality standards;
•
necessary monitoring of NPDES hmits and conditions be required in permits;
and,
•
Illinois permit procedures
and
NPDES permits
comply with the Clean Water Act.
Name
Address
2.
A
6.
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Petition to
the Illinois Pollution Control Board for Regulations
-
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative
Code Title 35 Environmental Protection Act;
Subtitle
C: Water Pollution; Chapter I:
Pollution Control Board; Part 309. The amendments sought are
to improve Illinois’ implementation of the
Clean Water Act, 33
U.S.C.
Section
1251
et seq.,
and National Pollutant Discharge
Elimination System
-
(NPDES) by
amending the
relevant regulations
to require that:
•
The public
is properly
informed of draft NPDES permits
and is provided a fair opportunity to
comment on substantial terms of permits before they are issued;
•
hearings are held when necessary to allow
the public
an opportunity to comment
on draft permits
and important
revisions
to draft permits;
•
the administrative
record regarding
each permit
shows that the permitwas properly issued and
that the permit does not purport to allow discharges that would cause or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring of NPDES
limits and conditions be required in permits; and,
•
Illinois permit procedures and NPDES permits
comply with the Clean Water Act.
Name
Address
1.
Rst.
.5-,
LJtL2J2a~
2.
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Petition to the Illinois Pollution
Control Board for Regulations
~.
The undersigned residents
of Illinois
hereby petition the Pollution Control Board to amend Illinois
Administrative Code Title
35
Environmental Protection
Act; Subtitle
C: Water Pollution; Chapter I:
Pollution Control Board;
Part
309. The amendments sought
are to improve Illinois’
implementation ofthe
CleanWater Act, 33
U.S.C.
Section
1251
et seq., and National Pollutant Discharge Elimination System
(NPDES) by amending the relevant regulations to require that:
•
The public
is properly informed of draft NPDES permits
and is provided
a fair opportunity
to
comment on
substantial terms of permits before they are issued;
~
hearings are held whennecessary to allow the public
an opportunity to comment on draft permits
and important revisions to draft permits;
•
the
administrative record regardingeach permit shows that the permit was
properly issued and
that the permit does not purport to allow discharges that would cause or contribute to
a violation
ofillinois water quality standards;
•
necessary monitoring ofNPDES
limits and conditions be required in permits;
and,
•
Illinois permit procedures and NPDES
permits
comply with
the Clean Water Act.
Name
Address
______________________
)so~E
Cc.4.4L/(
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Petition to the Illinois Pollution
Control Board for Regulations
-
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative
Code Title 35
Environmental Protection Act; Subtitle
C:
Water Pollution; Chapter
I:
Pollution Control Board;
Part 309. The amendments sought arc
to improve Illinois’
implementation of the
Clean Water Act, 33
U.S.C.
Section
1251
et seq.,
and
National Pollutant Discharge Elimination
System
(NPDES)
by amending the relevant regulations
to require that:
•
The public
is properly informed of draft NPDES permits
and is provided a fair opportunity to
comment on
substantial
terms ofpermits
before they
are issued;
•
hearings are held when necessary to allow
the public
an opportunity to
comment on draft permits
and
important revisions to draftpermits;
•
the administrative
record regarding each permit
shows
that
the permit was properly issued
and
that
the permit
does not
purport
to
allow discharges that
would cause or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring of NPDES limits and conditions be required in permits; and,
•
lilinois permit procedures and NPDES permits
comply with the Clean Water Act.
Name
Address
1.
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2.
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Petition to the Illinois Pollution
Control Board for Regulations
-
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative
Code Title 35
Environmental Protection Act;
Subtitle C:
Water Pollution; Chapter I:
Pollution Control Board;
Part
309. The amendments sought are
to improve Illinois’
implementation of the
Clean Water Act,
33
U.S.C.
Section
1251
et
seq., and National Pollutant
Discharge Elimination System
(NPDES)
by
amending the relevant regulations to require that:
•
The public is properly informed of draft NPDES penuits and
is provided a fair opportunity to
comment
on
substantial terms of permits
before they are issued;
•
hearings are held when necessary to allow
the public
an opportunity to comment
on
draft permits
and
important revisions to draft permits;
•
the administrative record regarding
each permit shows
that the permit was properly
issued
and
that the permit does
not purport to allow discharges that would cause or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring of NPDES limits
and
conditions be required in permits;
and,
•
Illinois permit procedures and NPDES permits
comply
with the Clean Water Act.
Name
Address
1.
~~/Gn
~Ot11r
y5j
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¶~
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Petition to the Illinois Pollution Control Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to
amend Illinois
Administrative Code Title
35
Environmental Protection Act; Subtitle C:
Water Pollution; Chapter I:
Pollution Control Board;
Part
309. The amendments sought are to improve Illinois’ implementation of the
Clean
Water Act, 33 U.S.C.
Section
1251 et seq.,
and National
Pollutant
Discharge Elimination System
(NPDES) by amending the relevant regulations to require that:
•
The public is property informed of draft NPDES permits and is provided a fair opportunity to
comment on
substantial terms of permits before they
are
issued;
•
hearings
are
held when necessary to
allow
the public
an opportunity to comment
on
draft permits
and important revisions to draft permits;
•
the administrative record regarding each permit shows that the permit was properly issued and
that the permit does not purport to allow discharges that
would cause or contribute to
a violation
of Illinois
water quality standards;
•
necessary monitoring of NPDES limits and conditions be required in
permits; and,
•
Illinois permit procedures and NPDES
permits comply with the Clean Water Act.
Name
Address
2.
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Petition to the Illinois Pollution Control Board for Regulations
The undersigned residents of Illinois hereby petition the
Pollution Control Board to amend Illinois
Administrative Code Title 35 Environmental
Protection Act; Subtitle
C: Water Pollution; Chapter
1:
Pollution Control Board;
Part
309.
The amendments sought
are to improve Illinois’
implementation of the
Clean
Water Act, 33
U.S.C.
Section
1251
et seq.,
and National Pollutant Discharge Elimination
System
(NPDES) by
amending the relevant regulations to require that:
•
The public is properly informed of
draft NPDES permits
and is provided a fair opportunity
to
comment on
substantial
terms ofpermits before they are
issued;
•
hearings are held when necessary to allow the public an opportunity
to comment on draft permits
and important revisions to
draft permits;
•
the administrative record regarding each
permit shows that the permit was properly issued and
that the permit does not purport to allow discharges that would cause or contribute to
a violation
ofIllinois water quality standards;
•
necessary monitoring ofNPDES
limits and conditions be required in
pennits; and,
•
Illinois permit procedures and NPDES permits
comply
with the Clean Water Act.
Name
Address
I._____________________
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Petition to the Illinois Pollution
Control Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative
Code Title 35
Environmental Protection Act; Subtitle
C: Water Pollution; Chapter
1:
Pollution Control
Board;
Part
309. The amendments sought are
to improve Illinois’
implementation of the
Clean Water Act,
33 U.S.C.
Section
1251
et seq., and National Pollutant Discharge Elimination
System
(NPDES)
by amending the relevant regulations
to require
that:
•
The public
is properly informed of draft NPDES permits and is provided a fair opportunity to
comment on
substantial terms of
permits
before they are issued;
•
hearings are
held when necessary to
allow the public
an opportunity
to comment
on draft permits
and important revisions
to draft permits;
•
the administrative
record regarding
each permit
shows
that the permit was properly issued
and
that
the permit does not purport
to allow discharges that
would
cause or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring
ofNPDES
limits and conditions be required in permits; and,
•
Illinois permit procedures and NPDES permits
comply with the Clean Water Act.
Name
Address
4
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8.
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3.
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701
Petition
to the Illinois
Pollution Control Board
for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control
Board to amend
Illinois
Administrative
Code Title 35
Environmental Protection
Act; Subtitle C:
Water Pollution; Chapter
1:
Pollution Control Board;
Part
309.
The amendments sought arc
to improve
Illinois’ implementation of the
Clean Water Act, 33
U.S.C.
Section
1251
et
seq., and National Pollutant
Discharge Elimination System
(NPDES)
by amending the relevant regulations
to require that:
•
The public
is properly
informed of draft NPDES permits
and is provided a fair opportunity to
comment
on substantial terms of permits
before they
are issued;
•
hearings are
held when necessary to allow
the public
an opportunity to comment on
draft permits
and
important revisions
to draftpermits;
•
the administrative
record regarding
each permit
shows
that the permit was properly issued
and
that the permit does
not purport to allow
discharges that would cause or contribute to a violation
of Illinois water quality
standards;
•
necessary monitoring of NPDES limits and conditions be required in permits; and,
•
Illinois permit procedures and
NPDES permits
comply with the Clean Water Act.
Address
(7
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Name
1.______
2.C~
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5.
______
cL
(05$
Petition
to the Illinois Pollution
Control Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative
Code Title 35 Environmental Protection Act;
Subtitle
C: Water Pollution; Chapter 1:
Pollution Control Board;
Part 309. The amendments sought are
to improve Illinois’
implemcntation of the
Clean Water Act, 33
U.S.C.
Section
1251
et seq.,
and National Pollutant Discharge Elimination
System
(NPDES) by
amending the relevant regulations
to require
that:
•
The public
is
properly informed of draft NPDES permits and
is provided a fair opportunity to
comment
on
substantial
terms
of permits
before they are issued;
•
hearings are held when necessary to allow the
public
an opportunity to comment on draftpermits
and important revisions
to draft permits;
•
the administrative
record regarding each pennit
shows
that the permit
was properly issued
and
that the permit does
not purport to allow discharges that would cause or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring
of NPDES limits
and conditions be
required in permits; and,
•
Illinois permit procedures and
NPDES permits
comply with the Clean Water Act.
Name
Address
7~3rtL
Cm
~-
o-IM
av~~4
9.
~*~y
fr~
M ~4
(ra;I
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I.____
_____________
6.
~6~j~i-c2
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8.
Petition
to the Illinois
POllution Control
Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to
amend Illinois
Administrative
Code Title 35
Environmental Protection Act; Subtitle
C: Water Pollution; Chapter
1:
Pollution Control
Board; Part
309. The amendments
sought are to improve Illinois’ implementation
of the
Clean Water Act,
33
U.S.C.
Section
1251
et
seq., and National Pollutant Discharge Elimination
System
(NPDES)
by amending the relevant regulations to require that:
•
The public
is properly informed of draft NPDES permits and is provided a fair opportunity to
comment on
substantial terms of permits
before they are issued;
•
hearings are held when necessary to
allow the public
an opportunity
to comment on draft permits
and important revisions
to draft permits;
•
the administrative
record regarding
each permit shows that the permit was properly
issued and
that the permit does
not purport to allow discharges that would cause or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring ofNPDES
limits and conditions be required in permits; and,
•
Illinois permit procedures and NPDES
permits
comply
with the
Clean Water Act.
Name
Address
I.
2.
Lc?,4pp~
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3.
Ku-i”
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IL
Petition to the Illinois
Pollution Control Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to
amend Illinois
Administrative
Code Title 35
Environmental
Protection
Act; Subtitle
C: Water Pollution; Chapter I:
Pollution Control Board; Part
309. The amendments
sought are
to improve Illinois’
implementation of the
Clean Water Act, 33
U.S.C.
Section
1251
et seq., and National Pollutant Discharge Elimination System
(NPDES) by amending the relevant regulations
to require that:
•
The
public
is properly informed of draft NPDES permits and is provided a fair opportunity to
comment on
substantial terms of permits before they
are
issued;
•
hearings are held when necessary to
allow the public
an opportunity
to comment
on draft permits
and important revisions
to draft permits;
•
the administrative record regarding each permit
shows that
the permit was properly issued and
that the pcnnit does not purport to allow discharges that
would cause or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring
of NPDES
limits and conditions be required in permits; and,
•
Illinois pennit procedures and NPDES permits
comply with the Clean Water Act.
6.
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Petition to the Illinois
Pollution
Control Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative
Code Title 35
Environmental Protection
Act; Subtitle
C: Water Pollution; Chapter
I:
Pollution Control Board; Part
309. The amendments sought are
to
improve Illinois’
implementation of the
Clean Water Act,
33
U.S.C.
Section
1251
et
seq., and National Pollutant Discharge Elimination
System
(NPDES)
by amending the relevant regulations
to require that:
•
The public
is properly informed of draftNPDES permits and is provided a fair opportunity to
comment on substantial terms of permits
before they
are issued;
•
hearings are held when necessary to allow the
public
an opportunity to comment
on draft permits
and important revisions to draft permits;
•
the administrative
record regarding each permit
shows
that the permit was properly issued
and
that the permit
does not purport to
allow discharges
that would cause or contribute to a violation
of
Illinois water quality standards;
•
necessary monitoring of NPDES limits and conditions be required in permits; and,
•
Illinois permit procedures and NPDES permits comply
with the Clean Water Act.
Name
Address
1.
2.
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Petition to the Illinois Pollution
Control Board
for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to
amend Illinois
Administrative
Code Title 35
Environmental Protection Act;
Subtitle
C: Water Pollution; Chapter I:
Pollution Control Board; Part 309. The amendments sought arc to
improve Illinois’ implementation of the
Clean Water Act, 33
U.S.C.
Section
1251
et
seq., and National Pollutant
Discharge Elimination
System
(NPDES)
by amending the relevant regulations
to require
that:
•
The public is properly informed of draftNPDES permits
and is provided a fair opportunity to
comment on
substantial terms of permits
before they are issued;
•
hearings are held when necessary to allow the public an opportunity
to comment on
draft permits
and important revisions to draft permits;
•
the
administrative record regarding
each permit shows that the permit was properly issued
and
that the permit
does not purport
to allow discharges that
would
cause
or contribute to a violation
of
Illinois water quality standards;
•
necessary
monitoring of NPDES limits and conditions be required in permits; and,
•
Illinois permit procedures and NPDES permits
comply with the Clean Water Act.
Name
Address
4.
5.
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Petition
to
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Control Board for Regulations~
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The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative
Code Title 35
Environmental Protection Act;
Subtitle
C: Water Pollution; Chapter
1:
Pollution Control
Board;
Part
309.
The amendments sought are
to improve Illinois’
implementation of the
Clean Water Act,
33
U.S.C.
Section
1251
et
seq.,
and National
Pollutant Discharge Elimination
System
(NPDES)
by amending the relevant regulations
to require
that:
•
The public
is properly
informed of draft NPDES permits
and is provided a fair opportunity to
comment on
substantial terms of permits
before they
are issued;
•
hearings are
held when necessary to allow the public an opportunity to comment on
draft permits
and important revisions to draft permits;
•
the administrative
record regarding
each permit
shows
that the permit
was properly issued
and
that
the permit
does not purport
to allow discharges that would cause
or contribute to a violation
of Illinois water quality standards;
•
necessary monitoring of NPDES
limits and conditions be required in permits;
and,
•
Illinois permit procedures and NPDES
permits comply with the Clean Water Act.
Name
Address
1.
Jc~0~C~
2~.
7,
8.
//ctsn
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9.
Petition to the Illinois Pollution
Control Board for Regulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative Code Title 35
Environmental Protection Act; Subtitle
C: Water Pollution; Chapter 1:
Pollution Control Board; Part 309. The amendments sought are to improve Illinois’
implementation of the
Clean Water Act, 33
U.S.C.
Section
1251 et seq., and National Pollutant Discharge Elimination System
(NPDES)by amending the relevant regulations
to require that:
•
The public is properly informed ofdraft NPDES permits
and is provided a fair opportunity to
comment on
substantial terms of permits before they are issued;
i
hearings are held when necessary to allow the public
an opportunity
to comment on draft permits
and important revisions
to draft permits;
•
the
administrative record regarding each permit shows that the permit was properly issued
and
that the permit does not purport to allow discharges that would
cause or contribute to a violation
ofIllinois water quality standards;
•
necessary monitoring of NPDES limits and conditions be required in permits; and,
•
Illinois permit procedures and NPDES permits comply with the Clean Water Act.
Name
Address
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Petition to
the Illinois Pollution Control Board for ReQulations
The undersigned residents of Illinois hereby petition the Pollution Control Board to amend Illinois
Administrative Code Title 35
Environmental Protection Act;
Subtitle C:
Water Pollution; Chapter I:
Pollution Control Board; Part
309. The amendments sought are
to improve Illinois’
implementation of the
Clean Water Act,
33 U.S.C. Section
1251
et seq., and National Pollutant Discharge
Elimination System
(NPDES) by amending the relevant regulations to require that:
•
The public is properly informed of draft
NPDES permits
and is provided a fair
opportunity
to
comment on substantial terms
of permits before they are issued;
•
hearings are
held when necessary to allow
the public
an opportunity to comment on draft permits
and important revisions to draft permits;
•
the administrative record regarding each permit shows that the permit was properly issued and
that the permit does not purport to allow discharges that would cause or contribute to a violation
ofIllinois water quality standards;
•
necessary monitoring ofNPDES limits and conditions be required in permits;
and,
•
Illinois permit procedures and
NPDES permits comply
with the Clean Water Act.
Name
Address
2’ts
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4.
10.
Petition to the Illinois Pollution Control Board for Renilations
The undersigned residents
of Illinois hereby
petition the Pollution Control Board to amend illinois
Administrative Code Title 35
Environmental Protection Act; Subtitle C: Water Pollution; ChapterI:
Pollution Control Board; Part 309. The
amendments sought are to improve
illinois’
implementation of the
Clean Water
Act,
33 U.S.C. Section
1251
et seq.,
and
National Pollutant Discharge Elimination
System
(NPDES) by
amending
the
relevant regulations
to
require that:
•
The public is
properlyinfonned of draftNPDES
permits and
is provided a fair opportunity to
comment on substantial tenns
of
permits
before they
are issued;
i
hearings ate
held when
necessary
to allow the public an
opportunity
to
comment
on
draft permits
and important
revisions to
draft permits;
•
the
administrative
record regarding each
permit
shows
that
the
permit was properlyissued
and
that the permit does
not
purport
to allow discharges that would cause or contribute to a violation
of illinois water
quality standards;
•
necessary monitoring of NPDES limits
and conditions be required in permits; and,
•
Illinois permit procedures and NPDES permits comply with the Clean Water Act.
Address
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CERTIFICATE OF SERVICE
I,
Albert
F.
Ettinger, certify
that
on January
13, 2003, I filed the above petition to the
Illinois Pollution Control Board
to
amend Illinois Administrative Code Title 35
Environmental
Protection Act; Subtitle C:
Water Pollution; Chapter I:
Pollution Control Board; Part 309 subpart
A.
This petition consists of:
-
The language of the proposed rules and rule amendments;
-
A statement of reasons supporting
the proposed
rules and
rule changes
together
with 4 exhibits (A-D) to the statement;
-
A synopsis
of the testimony to be presented by the proponents at the hearing
consisting
of the pre-filed testimony of Cynthia Skrukrud Ph.D., Beth Wentzel
and Albert Ettinger;
-
A petition signed by at least 200 persons
An
original and
9 copies of the complete petition was filed,
on recycled paper, with the Illinois
Pollution
Control Board, James
R.
Thompson Center,
100 West Randolph,
Suite 11-500,
Chicago,
IL 60601,
and copies
were also served on:
Division of Legal
Counsel
Illinois Environmental Protection Agency
1021
N. Grand Ave.
East
P.O. Box.
19276
Springfield,
Illinois 62794-9276
Office of Legal
Services
Illinois Department
of Natural Rosources
One Natural Resources
Way
Springfield,
Illinois 62702-1271
Division Chief of Environmental
Enforcement
Office of the Attorney
General
188
W. Randolph St., 20t~~
Fir
Chicago, Illinois 60601
Altert
F.
nger
Environmental
Law
and Policy Center
35 East Wacker Drive, Suite 1300
Chicago,
IL 60601
(312) 795
3707