1. R03-11(Site-Specific Rulemaking-Water)
      2. NOTICE
      1. COUNTY OF SANGAMON
      2. PROOF OF SERVICE

CL~RR~
~NCE
MAR
~4
2003
IWNOIS
R03-11
(Site-Specific Rulemaking-Water)
Dorothy Gunn, Clerk
Illinois Pollution Control Board
James R. Thompson Center, Suite 11-500
100
West Randolph Street
Chicago, IL 60601
David M. Walter
N. LaDonna Driver
Hodge, Dwyer & Zeman
3150 Roland Avenue
Post Office Box
5776
Springfield, Illinois
62705-5776
John Knittle, Hearing Officer
Illinois Pollution Control Board
1717 Philo
Road, Suite
25
Urbana, Illinois 61802
Matthew Hortenstine
122 B. Washington
P.O. Box 668
Effingham, Illinois 62401
Please takenotice that I have today filedwith the Office ofthe Clerk ofthe Illinois Pollution
Control Board the original and nine (9) copies ofthe PREFILED
TESTIMONY OF THE
ILLINOIS
ENVIRONMENTAL
PROTECTION AGENCY,
a copyofwhich is served
upon you.
ILLINOIS ENVIRONMENTAL PROTECTION AGENCY
B~~D4Q~
~
Deborah J. W
hams
Assistant Counsel
Division of Legal Counsel
Date:
March 20, 2003
Illinois Environmental Protection Agency
1021 North Grand Avenue East
P.O. Box
19276
Springfield, IL
62794-9276
217/782-5544
Pollution Control Board
)
)
IN
THE MATTER OF:
PROPOSED
SITE-SPECIFIC WATER
POLLUTION REGULATIONS
APPLICABLE TO THE CITY OF
EFFINGHAM, BLUE BEACON
INTERNATIONAL, INC. AND
TRUCKOMAT CORPORATION
)
)
)
)
)
)
NOTICE
THIS FILING IS
SUBMITTED ON RECYCLED PAPER

BEFORE
THE
ILLINOIS POLLUTION CONTROL BOARD
IN
THE
MATTER OF:
)
)
R03-11
PROPOSED SITE-SPECIFIC WATER
)
(Site Specific Rulemaking-Water)
POLLUTION
REGULATIONS APPLICABLE
)
TO
THE CITY OF
EFFINGHAM, BLUE
)
BEACON INTERNATIONAL, INC. AND
)
TRUCKOMAT CORPORATION
)
PREFILED TESTIMONY OF THE ILLINOIS ENVIORNMENTAL
PROTECTION AGENCY
INTRODUCTION
On
October 22,
2002, the City of Effingham (“City”),
Blue
Beacon International,
Inc. (“BBI”),
and Truckomat Corporation (“Truckomat”)(referred to collectively as
“Effingham” or “Petitioners”) filed a site-specific rulemaking proposal with
the
Illinois
Pollution Control Board
(“Board”)
pursuant to Section 27 of the
Illinois
Environmental
Protection Act (“Act”). 415
ILCS 5/27.
Effingham’s proposal would change the fluoride
standard applicable to the discharge from the City’s wastewater treatment plant from
1.4
milligrams per liter
(“mg/L”)
to 4.5
mg/L.
Specifically, Petitioners
have requested relief
from
35
III. Adm.
Code
304.105 as it applies to the water quality standard for fluoride at
35
Ill.
Adm. Code 302.208(g).
Prior to filing its proposal with the
Board,
Petitioners submitted draft
proposals to
the
Illinois
Environmental
Protection Agency (“Agency” or “Illinois EPA”) for review and
comment.
The Petitioners revised their draft proposal
in response to Agency comments
and held at least two telephone
conferences with
Illinois EPA staff members to address
the Agency’s concerns with the draft proposal.
As
a
result, the Agency is
in substantial
agreement that the
rulemaking change proposed
by the
Petitioners
is necessary,

contains sufficient conditions to safeguard the environment now and
in
the future and
meets the requirements of Section 27(a) of the Act.
The Illinois
EPA’s testimony will
address
the basis for our concurrence with
this proposal, some specific comments on
the
language of the
proposal, and
a recommendation that the
Board make changes to
the language of the
relief requested.
BACKGROUND
AND COMMENTS ON PROPOSAL
The City of Effingham
is located at the confluence of two major interstate
highways (Interstates 57 and 70).
Petitioners
BBI and Truckomat are in
the business of
providing truck washing services to the interstate traffic that passes through the area.
The truck washing process utilizes hydrofluoric acid as a
brightener.
The resulting
high
fluoride wastewater from
these industrial facilities
is discharged into the
City’s sewer
system.
Like most wastewater treatment plants, the City does
not treat for fluoride.
In
addition, the City adds fluoride to
its water supply for dental health purposes.
As
a
result of these factors, the effluent from
Effingham’s publicly owned treatment works
(“P01W”) contains levels offluoride that may cause exceedances of the general use
water quality standard
in
the
receiving
streams.
The impacted waterbodies are the
unnamed tributary of Salt Creek into which the POTW discharges,
Salt Creek itself,
and
the
Little Wabash River into which the Salt Creek flows.
Petitioners have estimated that
the
impact of
its
fluoride discharge may reach as far as 44 miles downstream from
the
point of discharge.
The public water supply intake for the City of Flora is located 37
miles downstream from
Effingham’s discharge.
The tributary of the Salt Creek that receives Effingham’s effluent is defined as a
zero flow stream during
7 day,
10 year low flow conditions (“7Q10”).
As a result, no
mixing zone
is allowed
in establishing an effluent limit for the City in
its
National
2

Pollutant Discharge Elimination System (“NPDES”) permit and
a water quality based
effluent limit
(“WQBEL”) has been imposed which
is equivalent to the general use water
quality standard of 1.4 mg/L which took effect in
June 2001.
The City will not be able to
comply with this
limit and has requested an alternative effluent limit of 4.5
mg/L.
An
effluent limit of 4.5
mg/L would ensure that with taking evaporation into account, the
water quality in the Salt Creek and its
unnamed tributary would not exceed 5.0
mg/L.
The Petitioners have stated that the brightener used by BBI and Truckomat
containing hydrofluoric acid
is necessary to remain competitive in the truck
washing
industry and that it
is not technically feasible or economically reasonable to change
brighteners
or provide treatment at the truck wash locations or the City’s POTW.
Additionally,
Petitioners have
been able to demonstrate that fluoride at the
levels
discharged
by the City is not toxic to aquatic life likely to occur in streams similar to the
Little Wabash River, Salt Creek or its
unnamed tributary that receives the
Effingham
effluent.
Toxicity test results
on fluoride indicate that even the
most sensitive species
tested can tolerate the
levels likely to be found
in
the receiving
waters.
The Petitioners
investigated the
existing quality of the
receiving stream because of the Agency’s
concern that during the September 1999 facility related stream survey, net-spinning
caddisflies (which are particularly sensitive to fluoride) were present approximately 3.7
miles downstream of the discharge and they were
not found at the sampling
locations
closer to the discharge.
At that time,
low dissolved oxygen concentrations were also
observed
in
the tributary stream segment immediately downstream from the
Effingham
discharge.
Based on the June
20, 2002
rapid bioassessment, the macroinvertebrate
community has improved and net-spinning caddisflies are relatively abundant.
There is
3

no evidence that fluoride in the Effingham POTW effluent is harming the aquatic
community immediately downstream from the discharge.
Petitioners were also able to
demonstrate that the current levels of fluoride being discharged do not have
an adverse
impact on the City of Flora’s water supply intake.
In the
petition for site-specific rulemaking,
the petitioners discussed compliance
alternatives that were all
rejected due to cost and/or technical infeasibility.
The Illinois
EPA agrees that petitioners have shown that there are no cost-effective compliance
alternatives available at this time.
CLARIFICATIONS
OF EFFINGINGHAM’S PROPOSAL
Despite being in substantial agreement with Petitioners’ proposal, the
Illinois EPA
would like to point out two minor misstatements contained
in the document to the
Board.
On
Page
11
of its proposal,
Effingham states “there do not appear to be any
sources of fluoride
in the subject streams,
other than the
City,
BBI, Truckomat and,
presently, Fedders.”
The Illinois
EPA believes that the municipal sources discharging to
Salt Creek and the
Little Wabash River most
likely add fluoride to their drinking water
supply as does
Effingham.
However,
the fluoride levels of these municipalities
are
below the water quality standard, therefore are
not regulated
in
an NPDES permit.
The
Illinois
EPA
does not believe this fact changes any of the conclusions in the
Petition.
On page 25,
Petitioners state “the water in the
Little Wabash River downstream
from
Effingham,
Illinois,
is very hard, with
hardness values of more than 300 mg/L
during
low flow conditions.”
The Illinois
EPA has calculated the critical hardness during
low flow conditions as 130 to
143 mg/L for the
Little Wabash River.
This value is
calculated
by taking the
10th
percentile hardness values during the
10th
percentile
low
4

flows.
The Illinois
EPA does
not disagree with
Effingham’s general conclusion that the
water downstream from
Effingham’s discharge
is
hard.
RELIEF REQUESTED AND CONSISTENCY WITH
FEDERAL LAW
The Illinois
EPA was able to thoroughly evaluate Effingham’s technical
justification for its proposal and found
itself in substantial
agreement with
the information
presented.
The only remaining
concern
the Agency has with the proposal is the format
in
which the relief has been requested.
Effingham
is asking the
Board to grant site-
specific relief from 35
III. Adm. Code
304.105 as it applies to the water quality standard
for fluoride at 302.208(g) of 1.4 mg/L and to allow an alternative effluent limit of 4.5
mg/L.
Pursuant to the
Board’s recent opinions
in several Adjusted Standard cases,
Petitioners have refrained
from asking the
Board to change the water quality standard
applicable in the
receiving
stream even though as a result of its discharge, the current
standard will
be violated.
See,
In the Matter of:
Material Service Corporation Petition
for an Adjusted Standard from
35
III. Adm. Code
302.208, 406.202 and 304.105, AS 02-
1
(June
6, 2002); In the Matter of:
Petition of Rhodia,
Inc., Thorn Creek Basin Sanitary
District, Takasago
Corporation (U.S.A.)
and Consumers
Illinois Water Company for an
Adiusted
Standard from
35
III. Adm. Code
302.208 and
304.105, AS 01-9
(January
10,
2002); In the Matter of:
Petition of the City of Springfield,
Office of Public Utilities for an
Adiusted Standard from 35
III. Adm. Code
302.208(e), AS 94-9
(December 1, 1994)
and
In the Matter of:
Petition of Rhone-Poulenc Basic Chemicals Company and Thorn
Creek Basin Sanitary District for an Adiusted Standard from
35
III. Adm. Code
302.208
and
304.105, AS 94-7 (June 23,
1994).
Although the Board
has recently expressed a
great deal of reluctance to grant site-specific regulatory relief from water quality
5

standards, there are many more examples in which the
Board has done so
in the
past.1
The Illinois
EPA would like to take the opportunity to explain for the
Board,
in some
detail, why it has recommended
in the
past,
and again recommends here today, that
regulatory relief in cases like Effingham’s must be granted from the water quality
standard, rather than simply as an alternative effluent standard.
The Board has
responded to petitions for
adjusted standards and site-specific rulemakings
involving
water quality standards in waters of the State in various ways including granting relief
applicable to the entire waterbody where there
is only one discharger or where there are
multiple or unknown
numbers of dischargers, granting relief applicable to the waterbody
that only can be taken advantage of by the petitioner and granting relief (as
requested
in
this case) from the requirement that a discharger’s effluent can not cause a violation of
a water quality standard.
Recently the
Board has shied
away from granting relief from
1
See,
In the Matter of:
Petition of Borden Chemicals and Plastics Operating
Limited Partnership foran
Adjusted Standard from
35111. Adm. Code 302.211(b) through (e), AS
01-6 (February
7, 2002)(applies to
waterbody);
In the Matter
of: Petition
of Illinois-American Water Company’s Alton Public Water Supply
Replacement Facility Discharge to the Mississippi
River for Adjusted Standard From 35
III. Adm.
Code
304.124,
304.106, and
302.203, AS 99-06 (September 7, 2000)(adjusted Standard from 302.203 only
applicable to Petitioner);
In the Matter
of: Petition
of Abbott
Laboratories forAdjusted Standard
From 35
Ill. Adm.
Code 302.208 and 304.105, AS 99-5
(July 8,
1999)(Abbott was the only discharger);
In the
Matter
of: Petition
of Illinois Department of Transportation,
District
8 for an Adiusted
Standard from
35
III.
Adm. Code 302.208,
304.124 and 302.203,
AS 96-12
(October 3,
1996)(applies to waterbody);
In the
Matter
of:
Petition
of Central Illinois Light Company (Duck Creek Station) foran Adiusted Standard from
35
III. Adm. Code 302.208 and 35
Ill. Adm.
Code 304.105, AS 96-8 (June 20,
1996)(applies only to
petitioner);
In the Matter
of:
Petition of Illinois Power Company (Baldwin Power Plant) for Adjusted
Standard from
35
III. Adm. Code 302.208 and 35
III. Adm.
Code 304.105, AS
96-01 (May 2,
1996)(applies
only to petitioner);
In the
Matter of:
Petition of Acme
Steel Company and LW Steel Company for an
Adiusted Standard
From 35
III. Adm. Code 302.211, AS 94-08 (July 7,
1 995)(general use changed to
secondary contact for petitioners);
In the
Matter of:
Petition of Akzo Chemicals foran Adjusted Standard
from
35
III. Adm.
Code 304.105 and
302.208, AS
93-8 (September 1,
1994)(relief limited to petitioner); In
the Matter
of:
Petition of Borden Chemicals & Plastics Operating
Limited Partnership for an Adjusted
Standard from
35
III. Adm. Code 302.208, AS 93-2 (November
18,
1993)(applies to
receiving stream that
receives other agricultural and wastewater discharges); In the Matter of:
Petition
of Southern
Illinois
Power Cooperative (Marion Power) forAdjusted Standards from
35
III. Adm.
Code 302.208(e) AS 92-10
(July
1,
1993)(applies to waterbody);
In
the Matter of Granite City
Division of National Steel Petition for
Adjusted Standard from 35
III. Adm. Code 302.208:
Numeric Standard for Fluoride, AS 90-4
(April 8,
1993)(Granite City was the only discharger to Horseshoe Lake);
In the Matter
of:
Petition of Nutrasweet
Company and
Consumers Illinois Water Company for an Adjusted Standard from
35
III. Adm.
Code
304.105 or 302.208, AS 89-3 (February 28,
1991)(applies to waterbody)(See slip.
op. at
5 and
10).
6

water quality standards in cases where there may be other dischargers to the same
water body.
From the perspective of the
Illinois
EPA, there are important technical and
legal reasons that the
Board should
not grant relief solely from 304.105 in cases where
the
relief granted will
cause the general use standard to be violated.
Legal obiections to granting relief from
304.105
Petitioners have requested a site-specific rulemaking that would be codified
within
Part 304 of the
Board’s regulations,
a Part generally reserved for site-specific
technology limits, rather than Part 303 (Water Use Designations and Site-Specific Water
Quality Standards).
The technology based effluent limit for fluoride is 15.0 mg/L and the
City has no difficulties achieving this
level of reduction.
In a case like this one, where
the discharge from
Effingham’s POT\N is causing a violation of the existing water quality
standard, granting the
relief requested to Effingham protects the discharger from
enforcement, but does
nothing to prevent the violation
of the water quality standard.
Technically, the receiving
stream in
this case could
be classified as impaired for the
general use standard for fluoride as a result the relief requested,
even though
Effingham’s petition has demonstrated that there is
no impairment to the aquatic life or
public water supply uses of the stream.
The
legal basis for the
Illinois
EPA’s
recommendation that the Board to grant relief from the water quality standard
rather
than
35
III. Adm. Code 304.105
is because of the Agency’s belief that failure to do so is
inconsistent with federal law.
The Section 303 of the Clean Water Act requires the State to establish water
quality standards that protect existing
and potential
uses.
33 U.S.C. §1313.
Anytime
the
State sets or changes
a water quality standard,
it is required to submit that water
7

quality standard to the
United States Environmental
Protection Agency (“U.S.
EPA”) for
review and approval.
Historically,
U.S.
EPA
indicated to the
Illinois EPA that by granting
relief solely from
35
III. Adm. Code
304.105, the Agency was attempting to make an end
run around
its
requirement to gain U.S. EPA approval to changes
in water quality
standards.
See,
Exhibit A (August 26,
1985 letter form
U.S.
EPA
Region V to Illinois
EPA) and
Nutrasweet and
Consumers Illinois Water Company, AS 89-3, Slip op.
at
5
(February 28,
1991).
In effect, when the
Board grants a petitioner relief from
304.105
only, it has found
a discharger to be exempt from the requirement not to violate the
water quality standard.
The Illinois
EPA believes
it is
inconsistent with federal law for
the
Board to grant a discharger indefinite or permanent
permission to violate a water
quality standard.
In addition,
Section 402 of the Clean Water Act (as
well as Section 39
ofthe Act)
prohibits the Agency from
issuing NPDES permits that will violate water
quality standards.
33 U.S.C. §~1
342.
The Illinois
EPA believes
it lacks authority to
issue an NPDES permit to Effingham that would cause a violation of the existing water
quality standard for fluoride.
In order to
remedy the Agency’s perceived deficiency in the relief granted
in the
past by the
Board, the Agency has always submitted adjusted standards or site-specific
regulations granting relief either from water quality standards or the requirement that
one’s effluent not cause a violation of water quality standards to
U.S. EPA for review
and approval.
Prior to 1997, the
States acted under a federal regulation
and policy
interpretation that held that changes to water quality standards became effective for
purposes of the Clean Water Act when they became effective under State law.
Under
this system,
Illinois EPA sent adjusted
standards and site-specific regulations to U.S.
8

EPA for approval and assumed they were approved
by default
unless the U.S.
EPA
objected to them.
This regulation
and interpretation was
invalidated by the Court in
Alaska
Clean Water Alliance v.
Clark, 45 ERC 1664, 27 Envtl.
L.
Rep. 21,330 (W.D.
Wash
1997).
In settlement of that litigation,
U.S. EPA
promulgated
new regulations that
provide that State changes to water quality standards
are only effective after they have
been formally approved by U.S.
EPA.
The new regulations require
U.S. EPA to
approve (within 60 days) or reject (within 90 days) changes to water quality standards
promulgated after May 3, 2000.
40 C.F.R.
131.21(c).
The Illinois
EPA has submitted
the recent adjusted standards granted by the Board solely from
35
III. Adm. Code
304.105 to U.S. EPA for approval and
no approvals have been received thus far in
cases where relief has not been granted from a water quality standard.
The Illinois
EPA
can
not speak on behalf of U.S.
EPA,
but it is the Agency’s view that it is preferable to
set site specific water quality standards
rather than to grant license to violate those
standards
and that to do otherwise
is
inconsistent with
the Clean Water Act.
Technical Obiections to Relief from
304.105
The Illinois
EPA also argues that the relief
in this matter needs to be granted for
the water body itself from
35
Ill. Adm. Code
302.208(g) for technical reasons.
When
adjusted standards or site-specific regulations allow a discharger to exceed what would
ordinarily be water quality based effluent limits,
it is important that the standards justify
that process of establishing limits.
A discharger receiving WQBELs
is generally one
who
is discharging into a water body with
no mixing zone.
To accomplish
the setting of
a new WQBEL for that discharger, the water quality standard for the affected water
bodies must be changed.
When the
Board grants permanent
relief solely from 35
III.
9

Adm.
Code 304.105, saying that the effluent need not comply with
the existing water
quality standard,
no new standard
is legally created for the
receiving waters.
As a
practical matter, however,
this type of relief
results in two completely different water
quality standards being applicable to the same stream segment and both supposedly
protecting the general use designation
in that segment.
This is inadequate for the
following reasons.
When the
Board grants one discharger relief from
meeting
a WQBEL without
changing the water quality standard applicable to the receiving
stream, the status of
WQBELs for other dischargers to affected water bodies is confused.
If the
Board clearly
designates a new water quality standard for the water body, the Agency will be able to
apply it and all other standards to any other dischargers if need
be.
These other
standards would include federal technology based limits, state effluent standards, the
antidegradation standard and mixing zones.
Any other discharger would be subject to
meeting appropriate limits based on all
standards
including the site-specific standard.
The Illinois
EPA recognizes the
Board’s concern that relief will be unfairly granted to
other dischargers who have
not presented the Board with sufficient evidence of the
need for such relief.
The Illinois
EPA feels this concern
is somewhat misplaced since
the
Illinois
EPA
only recommends that the Board grant relief
in site-specific rulemakings
or adjusted standards when
a thorough technical evaluation has revealed that the
requested relief is adequate to protect all
existing and potential uses of the water body
in
question.
If an adjusted standard or site-specific rule
is indeed
protective of the appropriate
uses (generally, aquatic life), the Agency must ensure that the other dischargers receive
10

limits that protect that use.
If, for example,
a discharger seeks an adjusted standard for
Total Dissolved Solids at 1,500 mg/L to a zero 7Q10 flow stream, the
Board should
designate the new standard for that stream (if protective of uses) at 1,500 mg/L,
and
in
any subsequent streams in the downstream continuum at a concentration
in accordance
with
natural dilution
until the generally applicable standard
is met.
This designation may
allow
a downstream discharger to discharge above the normally allowable limit
provided
he complies
with the other standards and regulations
and does nothing to cause the
new standard to be exceeded.
The Illinois EPA believes
it would be a rare
instance
when
another discharger would gain relief
in
this manner,
probably only in cases where
the
last water body in the continuum offered substantial
mixing potential.
A second
reason to firmly designate a
new numeric standard for the water body
is to make it known to all that a certain value has been found appropriate for the
specified
receiving
stream.
This comes to play in the Agency’s efforts in assessing use
support conditions through the Clean Water Act Sections 305(b) and 303(d) programs.
It is important that the assessment made in the regulatory relief process be made
known to all concerned with the water body.
The site-specific rulemaking
and adjusted
standard processes are an in-depth assessment of the
interplay between
a discharger
and the receiving
stream.
This process determines whether an increase above the
general standard will
harm the water body.
It would be
an absurd
result to the Board’s
regulatory relief process
if, following a favorable
recommendation by the
Illinois
EPA in
a site specific proceeding, the Agency would subsequently be legally required to list a
given water body as impaired for
a
given substance because
it does not meet the
standard of general applicability for that substance.
If the
Illinois
EPA was forced to
11

undertake a total maximum daily loading (“TDML”) setting process for the waterbodies
impacted
by Effingham’s discharge,
it is
not clear how the site specific relief would be
viewed by that process or what impact that would have on other dischargers who might
later be required to offset the relief granted to Effingham in this case.
If the Board does
not set a new numeric standard for the
receiving stream, the status of the applicable
standard
in that water body is clouded and may result in
the Agency designating a
stream segment as impaired for the same parameter from which the
Board
has granted
site specific relief.
For example,
imagine that relief from
304.105 as it applies to the
water quality standard for sulfate
is granted to three out of four dischargers to a given
water body to a
level of 800 mg/L.
At a later time, that waterbody placed the State’s
listing of impaired waters and
a TMDL is conducted.
The fourth discharger may be
obligated to receive a
load limit that requires it to reduce
its
discharge to make
up for
the
relief granted to the first three.
If the
Board
is still concerned about the
impact of granting regulatory relief to
Petitioners who have
not come before the
Board to request or justify such relief, the
alternative available
could
be to place as a condition to establishing the
site specific
water quality standard that any party wishing to take advantage of the new water quality
standard must also come to the
Board to request such relief.
It is preferable to the
Illinois
EPA that a new water quality standard
is established that is applicable only to the
Petitioners,
rather than granting the
Petitioners a license to violate the water quality
standard.
Additionally,
the Illinois
EPA can find no basis in
the Clean Water Act for
giving
permanent relief from compliance with a water quality standard.
12

The petitioners are proposing to eliminate the water quality standard by setting
an effluent standard.
The water quality standard, for this
receiving
stream, should
be
changed to more accurately reflect the
impact of the
relief afforded by the site-specific
rulemaking.
In other words,
the fluoride water quality standard of the receiving
waters
should
be adjusted to reflect the concentrations
present.
In addition,
Petitioner’s requested
relief includes the phrase “subject to the
averaging rule of Section 304.104.” This
language should
be removed since any
regulatory relief granted
by the
Board
in this matter will establish
an alternative effluent
limit or water quality standard, while the
averaging rule
in Part 304 merely addresses
how compliance with
the effluent ultimately placed
in NPDES permit is determined.
It is
the Agency’s intention to use 4.5 mg/L fluoride as a daily maximum permit limit should
this site-specific rulemaking
be adopted and
304.104(b)(2) may be available to the
Petitioners to determine compliance with that effluent limit.
As an alternative to the relief requested
by Petitioners
in the
case, the
Illinois
EPA proposes, the following language for a site-specific rulemaking:
Section 303.XXX.
Unnamed Tributary of Salt Creek,
Salt Creek,
and
Little
Wabash River.
The fluoride general use water quality standard of Section
302.208(g) shall not apply to the waters of the State which are located from the
point of discharge of the
POTW located at 903
E. Eiche Avenue
in
Effingham,
Illinois, owned by the City of Effingham, to an unnamed tributary of Salt Creek,
said point
being
located in
Effingham County, T8N,
R6E, Sec.
28,
Lat: 39°06’24”,
Long:
88°31’55”,to the confluence of said
unnamed tributary with Salt Creek;
to
the confluence of Salt Creek with the
Little Wabash River; to the confluence of
Buck Creek and the
Little Wabash River.
Fluoride levels
in such waters shall
meet a water quality standard for fluoride (STORET Number 00951) as set forth
below:
a)
From the point of discharge of the City of Effing ham POTW to the
unnamed tributary to the confluence of the unnamed tributary with Salt
Creek and from the
confluence of the
unnamed tributary with
Salt Creek to
13

the confluence of Salt Creek with the
Little Wabash River, the fluoride
water quality standard shall be 5.0
mg/L.
b)
From the confluence of Salt Creek with the
Little Wabash River to a
point
on the Little Wabash River located 2.8 miles downstream of Louisville,
Illinois, the fluoride water quality standard shall be
3.2
mg/L.
c)
From
a point on the
Little Wabash River located 2.8 miles downstream of
Louisville,
Illinois to the confluence of Buck Creek and the Little Wabash
River,
a
point on the
Little Wabash
River located approximately 9.8
miles
downstream of Louisville,
Illinois, the fluoride water quality standard shall
be 2.0 mg/L.
CONCLUSION
The Petitioner was unable to find any adverse environmental impacts of the
relief
requested including to the public water supply intake at the City of Flora located 37
miles downstream.
In order to guarantee that the Flora public water supply will
not be
adversely impacted by the relief requested, the City has agreed to the placement of
language in
its
NPDES permit that requires the POTW to monitor fluoride concentration
at the
Flora water supply intake when the
Little Wabash River nears seven day,
10 year
low flow (“7Q10”) conditions.
Discussions with the
Petitioners and additional modeling
performed also led to the
conclusion that it will
be necessary to place
an effluent limit of
4.5
mg/L in the
City’s NPDES permit to guarantee that the water quality standard will
not violate 5.0 mg/L taking evaporation into account.
Through the permit
renewal
process, the
Illinois
EPA has the authority to require the petitioners to review, over the
coming years, any new information on brighteners that may allow for replacement or
reduction of fluoride to the wastewater reaching Effingham’s POTW.
With
the inclusion
of these additional safeguards, the Illinois
EPA
is confident that granting site specific
regulatory relief to the
receiving stream impacted by the effluent from the City of
14

Effingham’s POTV\/
is technologically feasible, economically reasonable and will cause
no adverse environmental impacts because it is protective of the
existing
and potential
uses of the
Little Wabash
River,
Salt Creek and
its
unnamed tributary.
However, the
Illinois
EPA strongly believes that the granting of relief solely from
35
III. Adm. Code
304.105 to these Petitioners would result
in
a license to violate the existing water quality
standard for fluoride and would be inconsistent with
the Clean Water Act.
Scott Twait of the Water Quality Standards Unit of the
Division of Water Pollution
Control at the
Illinois EPA will be available at the hearing
in this matter to answer any
questions the
Board may have about the technical justifications provided in Effingham’s
site-specific rulemaking proposal and Deborah J. Williams of the
Division of Legal
Counsel will
be available for cross-examination on this testimony and to answer any of
the Board’s questions regarding
legal issues.
Respectfully submitted,
Deborah J.
illiams
Assistant Counsel
Division of Legal Counsel
March
20,
2003
Illinois
Environmental
Protection Agency
1021
North Grand Avenue East
P.O.
Box
19276
Springfield,
Illinois 62794-9276
15

Exhibit A

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,~.ççO
ST~47.
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
REGION5
______
230 SOUTH
DEARBORN ST.
~
CHICAGO, ILLINOIS 60604
~(
PRO1
RECEiVED
AuG
26
1985
AUU2~J
1985
Mr.
Roger
Kanerva
IEPA
Manager, Envi ronmental Programs
:ENV!RONMENTAL
PROGRAMS
Illinois Environmental. Protection Agency
2200 Churchill Road
Springfield,
Illinois
62706
Dear Mr. Kanerva:
As a result of
a
recent NPDES permitreview for 3oht~DeereFoundry
(Rock
Island County),
I became aware of a 1981 site-specific rule change
(Section 304.205) to the State’s effluent limitation rules, which exempts
the discharger from meeting water quality standards (Section 305.105) for
total
dissolved solids, iron, and temperature.
Although this rule was a
revision
to
the
State’s
effluent
standards,
it is my opinion that this
change clearly constitutes
a
de facto water quality standards change which
was never
submitted to the U.S.
Environmental Protection Agency
for review
and approval.
In
addition, if the perinittee were to discharge these parameters at the
permitted levels, the resultant in—stream concentrations at critical
low
flow (7Q10) would not be protective
of the designated general
use
for the
unnamed tributary to Sugar Creek.
Further, the available Illinois
Pollution Control Board records do not provide sufficient information to
justify such a water quality standards revision.
We would
like to avoid disapproval
of the water quality standards exemption
for John.Deere Foundryas currently adopted.
In order to do this,
Illinois
must either modify the usedesignation forthe affected receiving streams
based upon use attainability analyses or it must rescind or revise the rule
in order to adopt criteria which are protective of the designated general
use.
We would like to receive your proposal. for resolving this issue within the
next 30days.
This would enable us to carry out our statutory responsibili-
ties for water quality standards review and approval.
In the interim, we
will continue to object to the John Deere Foundry
permit on the basis that
the proposed effluent limits are not protective of the designated general
use.

—2—
As with the Lockport issue, this is
a serious matter which
requires your
personal attention.
If you have any questions or concerns regarding this
matter, please feel free to contact me.
Sincerely yours,
Charles H. Sutfin
Director, Water Division
cc:
Jacob Dumelle

STATE OF ILLINOIS
)
COUNTY OF SANGAMON
)
)
PROOF OF SERVICE
I, the undersigned,
on oath state that I have served the attached PREFILED
TESTIMONY OF THE ILLINOIS
ENVIRONMENTAL
PROTECTION AGENCY
upon the persons to whom it is directed, by placing a copy in an envelope addressed to:
John Knittle, Hearing Officer
Illinois Pollution Control Board
1717 Philo Road, Suite 25
Urbana, Illinois 61802
Matthew Hortenstine
122 B.
Washington
P.O.
Box 668
Effingham,
Illinois 62401
and mailing it from Springfield, Illinois on March 18
2003
sufficient postage affixed.
SUBSCRIBED AND SWORN
TO BEFORE
ME
this(~Q~ay
ofMarch,
2003
~
Notary Public
OFFICIAL
SEAL
BRENDA BOEHNER
NOTARY
PUBLIC,
STATE
OF
ILLINOIS
s;MV
COMMISSION
EXPIRES
11 .14-2Q95~
by First Class U.S. Mail with
Dorothy Gunn, Clerk
Illinois Pollution Control Board
James R. Thompson Center, Suite 11-500
100 West Randolph Street
Chicago, IL 60601
David M. Walter
N. LaDonna Driver
Hodge, Dwyer & Zeman
3150 Roland Avenue
Post Office Box 5776
Springfield, Illinois 62705-5776
THIS FILING IS SUBMITTED ON RECYCLED PAPER

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