ILLINOIS POLLUTION CONTROL BOARD
January
5,
1989
IN
THE MATTER
OF:
PETITION OF THE CITY OF
)
JULIET FOR A SITE SPECIFIC
RULE FOR THE EAST SIDE
)
R84-2O
JOLIET WASTEWATER TREATMENT
FACILITY
ADOPTED RULE.
FINAL ORDER.
OPINION AND ORDER
OF THE BOARD
(by
J.
Theodore Meyer):
This matter
is before
the Board
on
a May 29,
1984 petition
for site
specific rulemaking filed by the
City of Joliet.
Joliet asks that
its East
Side Wastewater Treatment Plant
(EWTP), which discharges
into Hickory Creek,
be exempted from the effluent limitations for biochemical
oxygen
demand
(BOO)
and suspended solids
(SS) applicable
to Hickory Creek.
Those
limitations,
found
at
35
111. Adn. Code 304.120(c),
are 10 milligrams per liter
(rng/l)
and
12 mg/i,
respectively.
Instead,
Joliet requests that the discharges from EWTP
be subject
to the
BOD and SS
limitations applicable
to the Des Plaines
River.
Those standards,
set forth
at
35
Ill. Adm. Code 304.120(b),
are
20
mg/i
BOD and
25 mg/I
SS.
The merit hearing in this matter was held
on September 25,
1984 at Joliet
City
Hall.
The Illinois
Environmental
Protection Agency
(Agency) submitted
supplemental
information on November
5,
1986,
and Joliet provided additional
information
on
November 10,
1986 and January
15,
1987.
On October
14, 1987
the Department
of
Energy and
Natural
Resources
(DENR)
submitted its economic
impact study
(EcIS), entitled “The Economic
Impact of Proposed Site Specific
Changes
to Water Pollution Regulations Affecting Joliet,
Illinois.”
(Ex.
0.)
An economic
impact
hearing was
held at Joliet City
Hall
on March
29,
1988.
The comerit period closed
on
April
29,
1988.
On June 30,
1988 the Board proposed for
First Notice
a rule giving Joliet
the requested relief for five years.
This five—year period will
allow Joliet
to conduct water quality monitoring
for approximately three years, and still
have time to petition the Board
for permanent relief
if the monitoring results
are positive.
The proposed rule was established
in
the
Illinois Register on
July
15,
1988 at
12
Ill. Reg.
11669.
The Board
received only one public cornent during the
First Notice
period.
The Department
of Comerce and Community Affairs
stated that the
proposed rule will
have no effect
on
small
businesses
regulated by the rule.
(P.C. ~8.) The Board notes
that the proposed rule regulates only Joliet’s
EWTP.
95—201
—2—
After the close
of the
First Notice period
it came to the Board’s
attention that under
a
proposed federal
consent decree, Joliet would
pay
a
$160,000 civil
penalty to resolve
a federal enforcement action alleging Clean
Water Act violations of the EWTP.
(U.S.
v. Joliet,
DC
N.
Ill.
No. 88—5561.)
The consent decree also requires Jolfet
to
attain and maintain compliance with
its permit, upgrade facilities
to meet secondary treatment standards,
construct
a single—stage nitrification facility, and take measures
to
ensure
proper operation and maintenance of the EWTP.
On
September
22,
1988 the
Board
adopted
an order directing Joliet and the Agency to comment
on
any relation
between this rulemaking and the
federal
consent decree.
The Agency
filed its
response on
October
26,
1988, and
Joliet submitted its response on October
23,
1988.
Both the Agency and Joliet maintained
that the consent decree and
this
rulemaking are
related and consistent.
Joliet
stated that
the primary purpose
of the consent decree
is
to assure
that the city continues with
the
construction program identified
in
its municipal compliance plan.
(That
compliance plan
is discussed below, and
is Exhibit
F
in this docket.)
This
rulemaking
is
a
part of that municipal
compliance plan,
and thus
is
an
approved
part of the consent decree.
The Agency stated that the site-specific
relief sought
by Joliet
in this proceeding was approved by the Agency during
the settlement discussions between Joliet and the Agency,
and that the United
States Environmental
Protection Agency (USEPA) also concurs
with the
site—
specific relief.
Joliet summarized the situation by declaring that the
construction of facilities,
the
request for site-specific relief,
and the
terms
of the consent decree have been coordinated to result
in compliance with
the effluent limitations for the Des
Plairies River.
Based
upon these
responses, the
Board found
that the
federal
consent
decree and this rulemaking are consistent, and proposed the site-specific
rule
for
Second Notice
on November
3,
1988.
On December 21,
1988 the Joint
Committee on Administrative Rules
(JCAR)
filed
its certification of
No
Objection.
No changes to
the
rule have been made during Second
Notice, and
the rule adopted today
is unchanged from the
proposal
issued
for First
Notice
on
June
30,
1988.
Background
Joliet’s EWTP
is an
activated sludge plant with
a design average flow of
22.5 MGD.
The plant has a primary treatment capacity of 33 MGD,
a secondary
treatment capacity of
up to
45 MGD, and provides disinfection only for flows
from 45
to
66 MGD.
The treatment
units
include mechanical
trash
screens
and
comminutors, velocity control
(non-aerated) grit chambers,
rectangular primary
clarifiers, aeration tanks with diffused aeration equipment,
peripheral
feed
final
clarifiers,
return sludge pumping equipment, and chlorination
facilities.
Primary sludge
arid waste activated sludge are digested
in the
primary anaerobic digesters.
The digested sludge
is concentrated
in
the
secondary digester and applied
to
farmland.
The
plant
is
located along
Hickory Creek near its confluence with the
Des
Plaines River.
Hickory Creek
flows
into the Des Plaines just below Brandon
Dam.
Plant effluent
is discharged
into Hickory Creek through outfall
001,
95—202
—3—
which
is
located 450 feet upstream from the Des
Plairies.
Outfall
002 operates
as
an emergency bypass, with those
flows
receiving only disinfection.
This
second outfall, located upstream from outfall
001,
was
used only twice between
1981 and
1984.
(Transcript
of
September 25,
1984 (Tr.
I)
at 37.)
Most of the
land along Hickory Creek below the plant’s outfalls
is
owned by Joliet.
Access
to the creek
is
limited by the plant
to the north and dense vegetation
to the
south.
There
is
a
foot bridge over the creek about
1500 feet upstream
of the outfalls.
(Tr.
I
at
15—16,
51.)
The
lower portion
of Hickory Creek,
where the
EWTP
is located,
has been channelized by the Illinois Department of
Transportation for flood control
purposes.
(Transcript
of March
29,
1988
hearing (Tr.
II)
at
53;
Tr.
I
at 43.)
Between January 1984
arid October 1985, the average BUD
in the plant
effluent was
16.5 mg/i, and
the average
SS was
17.3 nig/l.
(Ex.
F
at
5.)
The
concentration
of BUD in the creek
is more than twice
as
high downstream from
outfall
001
(85 mg/i) than
it
is upstream from the outfall
(39 mg/l).
(Tr.
I
at
19-20.)
The levels
of
SS are roughly the
sane.
Joliet states
that the
increased
BUD concentration
is due to backmixing from the Des Plaines
River.
Dennis Duffield, Director of Public
Works and Utilities for Joliet, testified
that the
flow of the creek
literally changes direction,
so that sometimes the
river backs
up into
the creek.
(Tr.
I
at
17.)
The testimony of Richard
Pershali,
the principal author
of the EcIS,
supports Joliet’s contention.
Mr.
Pershall
explained that the backmixing
is
a hydrologic phenomenon.
Because
the Des Plaines
is
at
a higher elevation than Hickory Creek, water
from the
river flows into the creek to
a point
a few hundred feet upstream of the
EWTP.
(Tr.
II
at 27-28.)
Joliet has been working with the Agency
to evaluate alternatives
to
upgrade the existing wastewater collection
and treatment system since the mid—
1970s.
As
a condition of the
National
Pollutant Discharge Elimination system
(NPDES)
permit for the EWTP,
Joliet
is
required to develop
and submit for
review
a municipal compliance plan to upgrade its wastewater facilities
to
meet existing
rules and regulations.
That plan, prepared by Clark Dietz,
Inc.
and revised
in July 1986, has
been admitted into
trie
record
of this case as
Exhibit
F.
The recommended additions
and modifications
to the
system are to
be completed
in seven
phases between 1984 and
2007.
The total
project cost in
May 1985 dollars
is estimated
at $55,688,000.
(Ex.
F.
at
1.)
The phases
of
the plan are:
(1) construction of separate storm sewers
throughout Joliet;
(2) the elimination
of combined sewer overflows (CSO)
where storm
sewers have
been constructed,
and the reduction in frequency of CSO5 at other locations;
(3) upgrading the EWTP,
including addition of
final
clarifiers
and an
anaerobic digester, modification of the chlorination facilities,
and
construction of an
interceptor
at McDonough Street
to
transfer some flow from
the EWTP
to
the West Side Wastewater Treatment
Plant
(WWTP);
(3A) approval
of
this site specific rule change or construction
of
a new effluent
sewer
so that
the EWTP may discharge at levels applicable
to the Des
Plaines
River;
(4)
the
monitoring and evaluation
of the existing CSOs,
so
as
to
identify priorities
for the elimination of
the CSOs;
(5) design
and construction of
improvements
at the EWTP to
provide for nitrification;
(6)
a
final
assessment
of the
improvements
in water quality as
a result
of the construction
of
storm sewers;
and
(7)
any
additional work
if required, based upon the results
of the
final
assessment
of phase
6.
(Ex.
F
at
48—55.)
The Agency approved this plan
in
95—203
-4-
July 1986,
and Joliet has begun work on many of the phases.
(See Ir.
II
at
46-52.)
Compliance Alternatives
There are five identified alternatives available to Joliet
for reducing
BOO and SS discharges from the EWTP.
The
first three alternatives
involve
additions to the plant
in the form of advanced wastewater technologies, and
include multi-media
filtration,
carbon absorption/multi—media filtration and
chemical coagulation.
The fourth and
fifth alternatives, although failing to
reduce effluent levels,
relieve Joliet
from meeting water quality standards
for Hickory Creek
by routing the plant’s outfall
to
the Des Plaines River
which
has higher standards of
20 and 25 mg/l
for BUD and 55, respectively.
One alternative for rerouting
the outfall
is for
it
to
run south under the
creek, then west
in order that
it discharges downstream
from Hickory Creek.
The other alternative would involve routing
it directly west
so that
it
discharges
in the Des Plaines, upstream from Hickory Creek.
The
EciS examined
these five alternatives, and made the following estimates of costs for
each
alternati ye:
Multi—Media Filtration
(Alt.
1)
$
9,258,719
Carbon
Absorption
(Alt.
2)
$19,377,263
Chemical
Coagulation
(Alt.
3)
$17,834,638
Relocate Outfall
(under Hickory Creek)
(Alt.
4)
$
855,890
Relocate Outfall
(directly west)
(Alt.
5)
$
491,958
(Ex.
0 at
29-45;
Ec.
0, Table
4.)
Joliet
has rejected the advanced treatment technologies (Alt.
1—3)
as too
expensive.
(Petition at
10; Tr.
I
at 23.)
If
its petition
for
a
site
specific rule is not granted, Joliet will
construct Alternative
4 and thus
extend the outfall
pipe under Hickory Creek and
then west to
the
river.
(Tr.
I
at
21—23;
Ex.
F at
53.)
Joliet does not believe that Alternative
5, which
calls for routing the outfall directly southwest of the EWIP to the
Des
Plaines just below the dam,
can be constructed
as estimated
in the EcIS.
Mr.
Duffield stated that the discharge at that point would
be immediately adjacent
to the storm sewer outfall
which
is located
in the toe of the riverwali
.
(Tr.
II
at
54.)
Another disadvantage with Alternative
5
is that some or
all
of the
effluent would end up
in Hickory Creek
as Des Plaines River backwater, since
the outfall
would
be upstream from the mouth of the creek.
(Ex.
0 at
44.)
A
sixth
alternative
is
to
run the outfall
directly west of the plant
to
the Des
Plaines, above
Brandon Dam.
However, both Joliet and the
EcIS rejected this
option.
Since the existing
river wall
is
20 feet higher than the treatment
plant
property,
a pump would be required, adding
significantly to the cost of
the project.
(Tr.
I
at
26—27;
Ex.
U
at 44.)
5~~204
—5—
Economic
Impact
Joliet does not contend that compliance with the BUD
and SS limitations
is not technically feasible, but argues that
the cost of compliance
is
economically unreasonable when compared to the
small
benefit to the
environment.
Joliet points out that
it
is undertaking a significant effort
to
upgrade
its treatment facilities
and that
its municipal compliance plan will
result
in
a better class
of treatment than
is
now provided.
The upgrading of
the EWTP will
result
in
a
longer detention and aeration time so that ammonia
nitrogen will
be
removed.
Mr. Duffield testified that the
proposal would
at
least
retain
the
same
level
of
SOD
in
the
effluent,
if
not
reduce
that
level.
(Tr.
II
at
63-64.)
Therefore,
Joliet
asks
that
instead
of
directing
funds
to the construction
of
a new outfall
the City be allowed
to use those
funds towards the upgrading of their wastewater
system, with
a greater
positive
impact
on the environment.
(Tr.
11
at
70.)
In addition to evaluating compliance alternatives and estimating
their
costs,
the
EcIS calculated
the costs
to Joliet’s utility customers of
implementing
each alternative.
Assuming an average monthly bill
of
$10.10,
utility bills would
increase as
follows:
Monthly
Increase
Increase
Multi-Media Filtration
(Alt.
1)
$3.38
34
Carbon Absorption
(Alt.
2)
$5.93
59
Chemical
Coagulation (Alt.
3)
$5.20
52
Relocate Outfall
(under
Hickory Creek)
(Alt.
4)
$
.21
2
Relocate Outfall
(directly
west)
(Alt.
5)
$
.10
1
(Ex.
D
at
4.)
The
EcIS also assessed the benefits
of
reduced
levels
of BOO
and
SS in
regard
to six direct benefit categories:
(1)
recreational
opportunities;
(2) aquatic
life;
(3) stream maintenance;
(4) flood control;
(5) agriculture; and
(6) human health.
The
EcIS concluded that only
recreational opportunities and stream maintenance could
be quantified:
the
other four categories are significantly impacted
by
reduced
pollutant
levels.
(Ex.
U.
58-66.)
The benefit to recreational
opportunities was
calculated
at
$460
(Ex.
U
at 59—60),
and the benefit
to stream maintenance was
valued
at $2332
(Ex.
D at 64—56).
The EcIS thus found
a large disparity
between the costs of each alternative and the associated benefits.
Costs
Benefits
Alternative
1
$
9,258,719
$2792
95—205
-6-
Alternative
2
$19,377,263
$2792
Alternative
3
$17,834,638
$2792
Alternative
4
$
855,890
$2792
Alternative
5
$
491,958
$2792
(Ex.
0
at
5;
73—73.)
The
cost
of
Alternative
5,
the
least
costly
option,
is
176
times
as
great
as
the
value
of
direct
benefits.
Joliet
believes
that
the
Ec1S
supports
its
contention
that
the EWTP
outfall
should
remain
in
its current location
and that the
additional
expense
to relocate the outfall
does not provide benefits even approaching the cost.
(Tr.
II
at 55.)
However, Joliet disputes the cost estimates made by the
EcIS
for
Alternatives
4
and
5.
(Tr.
II
at
52—53.)
The
EcIS
estimated
the
cost
of
Alternative
4
at
$855,390,
while
Clark
Dietz
estimated
the
cost
of
relocating
the outfall
under
Hickory Creek
at
S3,425,000.
(Ex.
F
at
52.)
Mr. Duffield
testified
that
he
feels
that
Clark
Dietz’s
estimate
is
very
conservative,
but
stated
that
the
actual
cost
would
approach
$2,000,000.
(Tr.
II
at
53.)
The
difference
in
estimates
is
partly
attributable
to
the fact that the
Clark
Dietz estimate done
for
Joliet
provides
for
a
longer
run
of
pipe
out
into the
river rather than ending the
pipe
at
the
river
bank
as
the
EcIS
assumed.
(Tr.
II
at
53.)
Mr.
Duffield stated
tnat he thought that Clark Dietz had proposed
to extend
the
outfall
out
into
the
river
so
as
to get good mixing of the
effluent with the
flow of
the Des Plaines.
(Tr.
II
at 62.)
The difference
in
estimates for Alternative
4
is
also partly due to Joliet’s belief
that
construction of the outfall
will
be very difficult, since the pipe will
run
under the channelized portion of Hickory
Creek and
then out into the
river.
This will
involve rock excavation in the river, since the pipe will
be
buried.
(Tr.
II
at
53,
60, 62.)
As previously noted, Joliet does not believe
that Alternative
5 can be
constructed as
proposed.
(Tr.
II
at
54,
60—61.)
At the economic impact hearing
Mr.
Pershall
presented some cost estimates
to bring the outfall
into the Des Plaines.
He estimated that
to bring the
outfall structure
300 feet into the river
(1/3 its width) would cost
$1,030,00U.
Bringing the structure 450 feet into the
river
(1/2 its width)
would
cost $1,112,500.
(Tr.
II
at
19.)
Mr.
Pershall
testified that there
is
no federal
or
state requirement that the
outfall
be actually in the
river, and
that most wastewater treatment plants
only bring the outfall
to
the edge of
the river.
(Tr.
II
at
20.)
Environmental
Impact
The record
in this case contains no information on
the water quality
in
the stretch of
Hickory Creek downstream from the EWTP outfall, and
very little
information
on
the water quality of the Des Plaines near its confluence with
Hickory Creek.
Joliet
states that due to the substantial
backrnixing of the
Des Plaines
in the lower
stretch
of the creek, the water quality
in the creek
at this point would be expected to closely resemble that of the Des Plaines.
Joliet has provided 1976 data from
a monitoring station
in the
Des Plaines
downstream of Hickory Creek which shows
a mean value of 9.0 mg/i
of dissolved
95—2Of~
—7—
oxygen
(DO)
and 3.03 mg/I
of ammonia nitrogen.
(That
monitoring station was
closed by the Agency
in
1976 due to budgetary constraints.)
At the merit
hearing the Agency asked
if the effluent from the
EWIP causes any water
quality standard violations
of DO or ammonia nitrogen
in Hickory Creek.
Joliet
stated that it had no information on that,
and promised to
do sampling
and investigate the issue further.
(Tr.
I
at 46-47.)
However, no such
information has been received.
In sum, Joliet’s position is that since the
downstream portion
of Hickory
Creek
is
so closely
integrated with the
Des
Plaines
River,
little benefit can be achieved by extending the outfall
from
the plant
into the river.
(Petition at
9.)
The EcIS used water
pollution models
in
an attempt
to
predict the impact
of BUD and
SS on
the water quality
in Hickory Creek.
The
EcIS concluded that
the environmental degradation associated with current
levels
of effluent
is
minimal.
The BUD model, using various concentrations of effluent BUD, showed
that under
all
average conditions the DO
in Hickory Creek remained above
5
mg/l,
which
is considered
sufficient
to
support
a healthy aquatic
environment.
(Ex.
D at 49-53.)
Suspended solids discharged from the EWTP
will
not routinely settle
in the
creek because of their minute particle
size.
Turbidity
is
not
expected
to cause problems because current
concentrations
are well below harmful
levels.
(Ex.
U
at
53—55.)
In
its post—hearing comments, the Agency again expressed its concern that
the levels
of DO and ammonia nitrogen might
be adversely affected by Joliet’s
proposal, and
pointed out that Joliet had promised to investigate the
matter.
The
Agency stated that
it continues
to support Joliet’s request for
effluent relief,
but intends to require water quality monitoring as
a specific
NPDES permit condition.
(Public Comment
(P.C.)
#6
at
1-2.)
The Agency points
out that Hickory Creek
is channelized for flood control purposes
and is
therefore unlikely to
support
a diverse aquatic community regardless
of water
quality.
The Agency insists that this fact does not justify degradation of
water quality, but
states that
it does
not anticipate that Joliet’s
investigation of water quality impacts will
reveal
any water quality
problems.
(P.C.
#6
at
3.)
The
Agency does contend that the BOO model
contained
in the EcIS should
be discounted by the Board.
First, the Agency states that Mr.
Pershall
indicated that
he did not
really model
SOD and
its effects
on
the creek’s DO,
but rather did
a
simple mass balance calculation of the DO after the effluent
mixes with the creek.
(Tr.
II
at
34—35.)
Second, the
Agency maintains that
the
ECIS’S assumption that the DO
in the effluent varies directly with
the SOD
Concentration
is simplistic and typically inaccurate.
Third, the Agency notes
that the SOD model
assumed that there
is
no entrapment of the creek flow at
its mouth, while Joliet
has documented the likelihood
of such occurrences.
Finally, the Agency submits that the model
addressed only average stream
conditions, giving the model
limited utility
in
a low flow situation where
adverse impacts are more likely
to occur.
(P.C. ~6 at
3.)
The
Board
notes that the Des Plaines River
is
part of the Illinois
&
Michigan
(I&M)
National
Heritage Corridor.
The hearing officer specifically
solicited comments on whether that status should
have any bearing
on the
proposed regulation.
Responses to this request were received from the Agency
95—207
-8-
(P.C.
#6), the
I&M National
Heritage Corridor Commission
(P.C.
#2), the
Illinois Department
of Conservation (P.C.
#3), the United
States Environmental
Protection Agency (USEPA)
(P.C.
#4), and
Joliet
(P.C.
#5).
These
comments
agree that the Des
Plaines’
status
as
part of
the Corridor should have little
impact
on the Board’s consideration of Joliet’s proposal.
The Agency and
Joliet
state that they believe approval
of the rule would not adversely affect
the character of the
river.
Additionally, both
the Corridor Commission and
the Department
of Conservation point
out that the
federal legislation which
created the Corridor specifically states
that such status
is
not to change
existing environmental
standards.
(Public Law
98-398,
Sec.
115(a).)
The comments submitted by the Department
of Conservation and USEPA also
addressed
the merits
of the proposal.
The Department
of
Conservation opposes
Joliet’s request, based
upon its
concern that
a greater
BOO load
in
the lower
stretches
of Hickory Creek would adversely impact the area’s fish.
The
Department states
that
a
1983 fisheries sample below Brandon Dam included
12
species of fish,
a
substantial
improvement over the 4 species collected
in
1974.
The Department
feels
that granting Joliet’s petition would
he
in direct
opposition
to the Department’s efforts
to
improve the DO
situation and the
fisheries.
(P.C. #3.)
On the other hand, by
a
letter from Valdas Adamkus,
Regional
Administrator, USEPA states that overall, Joliet’s proposal appears
appropriate.
USEPA feels that the petition is not contradictory to
federal
or
state antidegradation provisions,
and appears consistent with
federal
antibacksliding provisions.
USEPA concurs with Joliet’s contention the
expenditures
to relocate the outfall
to the river
do not
appear justified at
this time.
However, USEPA does note the concerns with assuring protection of
water quality
in Hickory Creek
in the future.
USEPA believes that as
a
condition of approval, adequate monitoring
be
required downstream
from the
EWTP to characterize both average and potential
low flow conditions
in the
creek.
USEPP, concludes that granting temporary relief should recognize the
potential need
for additional
treatment
in
the future,
if necessary
to protect
water quality or
potential
uses.
(P.C.
#4.)
Concl usions
After considering
the record
in this case, the Board concludes that
Joliet has demonstrated that relief
is warranted.
Therefore,
the
Board will
adopt
a regulation exempting Joliet’s EWTP from the SOD and SS
limitations
applicable to Hickory Creek.
Instead,
the SOD and
SS limitations applicable
to the Des
Plaines
River will
apply
to the EWTP.
The Board believes that the
cost of relocating the outfall
to the Des
Plairies
is
not justified by any
predicted environmental benefits at this time.
The Board also notes
that
Joliet
is
spending significant
sums to upgrade
its wastewater collection
and
treatment system by carrying out the municipal
compliance plan, with resulting
environmental
benefits.
Further, the Board
notes that Joliet’s chosen
compliance
alternative
(relocating the outfall) would
not reduce the
levels
of
BOO and
SS discharged from the EWTP, but simply discharge the effluent
directly to the Des Plaines.
Thus, the denial
of Joliet’s petition would,
at
95—208
—9.-
best,
improve the water quality of only the
450 feet
of Hickory Creek between
the present location of the outfall
and the creek’s confluence with the Des
Plaines.
However, the
Board shares the concerns
voiced by the Agency, the
Department of Conservation,
and USEPA about the effect of the proposal
on
water quality standards, especially levels
of DO and ammonia nitrogen.
The
little information
in the record on water quality
is either outdated
or
speculative.
Therefore, the regulation adopted today will
be
temporary, and
will
expire
on January
1,
1994.
This period will allow Joliet
to conduct
water quality monitoring for approximately three years, and
still
have time to
petition the Board for permanent relief
if the monitoring results are
positive.
Joliet should
work with the Agency to develop
a monitoring
program.
That program shall
include
information on, among other things,
average and low flow conditions
in Hickory Creek downstream from the EWTP,
especially levels of DO and ammonia nitrogen.
The program shall
also address
the effects
of the
EWTP discharge on the area
fish and
their ability to move
between the Des Plaines and the upstream portion of Hickory Creek.
By
promulgating
a temporary regulation the
Board
is able to grant
relief to
Joliet while addressing the water quality concerns raised
in this proceeding.
ORDER
The Board
hereby adopts,
as final,
the following amendment
to be
filed
with
the Secretary of
State.
TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE
C:
WATER
POLLUTION
CHAPTER
1:
POLLUTION CONTROL BOARD
PART 304
EFFLUENT STANDARDS
SUBPART C:
TEMPORARY EFFLUENT STANDARDS
Section
304.302
City of Joliet
East Side
Wastewater Treatment
Plant
This Section
applies only to the
City of Joliet’s East Side Wastewater
Treatment
Plant which discharges
into Hickory Creek
in Will County,
Illinois.
The discharges of that plant
shall
not be
subject to the standards
of Section
304.120(c), provided that those discharges meet the five day
biochemical
oxygen demand (SOD)
and suspended solids limitations of
Section
304.120(b).
This Section will expire
on January
1,
1994.
(Source:
Added
at
13 Ill. Reg.
,
effective
________________
IT
IS
SO ORDERED.
95—209
-10-
1, Dorothy M.
Gunn, Clerk
of the
Illinois Pollution Control
Board, hereby
certify that the abov
Proposed Opinion and Order was adopted
on
the
51~ day of
______________,
1989,
by
a vote of
7
~
Dorothy M.
Gun
Clerk
Illinois Pollution Control Board
95—210