1. but not to that which went into the stream or to stream quality
      2. itself, we find no violation on this date.
      3. 6. September 30, 1970.
      4. 7. October 14, 1970.
      5. 8. February 18, 1971.

ILLINOIS POLLUTION CONTROL BOARD
September16, 1971
ENVIRONMENTAL PROTECTION AGENCY
v.
)
PCB 71-51C
CITY OF CHAMPAIGN,
ILLINOIS et al
Dennis K.
Muncy of Champaign,for
the Environmental Protection Agency
Albert Tuxhorn of Champaign,
for City of Champaign
Opinion of the Board
(by Mr.
Currie):
This
case was originally brought as
a consolidated action by
a complaint filed by the Environmental Protection Agency
(“Agency”)
on March
16,
1971,
against the City of Champaign
(“City”)
and the
City of Urbana for causing or allowing the pollution of Boneyard
Creek.
On May
13,
1971,
the Hearing Officer entered an order of
severance dividing the complaint against the cities into
two sep-
arate cases and,
subsequently,
the Board of Trustees of the
University
of Illinois
(“University”)
,
and Alpha Material and
Fuel Company,
a corporation
(“Alpha”)
,
were joined to these pro-
ceedings.
A number of preliminary questions
and jurisdictional
objections have been raised and will be considered here first
before we discuss the merits of the case.
The City,
in its Motion
and
Amendment to Motion to Strike
and Dismiss First Amended Complaint, raises
a series of objections
to the procedure followed by the Agency
in filing this
case,
all
of which we
reject.
The City claims that the Agency failed to comply with
the
provisions of Section 8—102 of Article VIII
of Chapter
85,
Ill,
Rev.
Stat.
1969, regarding the required notice in actions against
local public entities,
That section, however, pertains specifically
to
a “civil action for damages,” which
is not the case here.
This
proceeding
is
an adjudication before an administrative agency and
the procedures
to be followed are clearly defined
in the Illinois
Environmental Protection Act
and in the Procedural
Rules
of the
Illinois Pollution Control Board.
Similarly,
the City~sreference
to
Section
2-102
of
Chapter
85
is
totally
inapplicable
since
that
section
deals
with
“punitive
or exemplary damages,”
a technical
term having to do with additional payments
in private civil damage
actions.
The
penalties
which
the
Board
may
invoke
pursuant
to
the Environmental Protection Act are,
on the other hand,
not
in the
nature of “damages,” but are, rather, administrative sanctions the
precedent for which has been well established for many years.
The City further contends that the Agency did not serve
piocess on the City pursuant to the requirements
of the Civil
Practice Act in that the Agency failed to leave
any summons with
either the Mayor or the City Clerk.
The original combined complaint
2
—411

against both Cities had been Served on
the
Mayor
and Council of
the
City of Champaign by registered
Nail
pursuant to Rule 305
Ca)
of the Procedural Rules
of
the I,P.C.B.
and, after the cases were
severed, the First Amended Complaint was served by registered mail
on the City Attorneys who had already entered
their
appearances.
These procedures
are thoroughly adequate and are consistent with
the Statute and with the rules of the Board,
The notice requirements
of the Civil Practice Act are inapplicable.
We also reject the City~stechnical argument that the
complaint
is insufficient
in that it fails
to specifically allege that “any
contaminant” was caused,
threatened, or allowed to be discharged.
Pleadings before this body shall be judged by their substance and
not by their form.
Similarly,
the City~sargument that the complaint
is insufficient for failure
to specify
the pollutants
involved, for
failure to allege sufficient
facts
to apprise respondent of the
particular provisions
of the statutes or regulations allegedly
violated,
for failure to allege the
facts complained of with sufficient
particularity,
for failure
to allege sufficient
facts
to support the
“many conclusions of law and
fact” contained therein and for failure
to allege sufficient
facts to raise any
duty or legal obligation owed
by
the City to the complainant,
are all rejected.
Even if true
(and
we
are. not convinced that they
are true)
the points raised by these
arguments could have
all been covered,
and actually were covered,
by
the ample discovery procedures afforded to all parties by the
Hearing Officer pursuant to the Rules of the Pollution Control Board.
The
City also raises various constitutional arguments
challenging the entire Environmental Protection Act and the very
existence
of the Pollution Control Board,
Basically,
the City
argues that the complaint which is brought pursuant to the Act
denies the respondent due process and equal protection of the
laws
in violation of the U.S.
and Illinois Constitutions;
that
the Board,
“which acts
as
a court,”
has been unconstitutionally delegated
judicial powers;
that the section of the Act providing for a review of
Board decisions by the Appellate
Court, thereby skipping the Circuit
Court
level,
unconstitutionally
“discourages review”
and “places
an
undue burden on respondents”;
that the Board~sauthority
to impose
“civil penalties”
is unconstitutional
and that respondent
is unconstitu-
tionally “denied the right to jury trial and other procedural safeguards.”
While we have answered similiar arguments before,
we will briefly
address ourselves to the contentions of
the City individually:
1.
~
The City asserts that the Environmental Protection
Act denies
it due process and equal protection of the
laws.
It claims that
the Board has been delegated judicial powers
“comparable
bo those of the Circuit Court” in violation of the Illinois Constitution.
Presumably this argument refers to the Board~s authority to
conduct hearings
and to impose appropriate penalties.
As we have
pointed out at length,
(see E.P.A.
v.
Modern Plating Corporation,
2 —412

PCB
70—38,
71-6,
May
3,
1971)
the precedent
for the
creation of quasi-judicial tribunals in this state
is well-established,
Workmen~s compensation cases, handled by
the Industrial Commission,
are the most obvious examples
of the proper
and reasonable exercise
of quasi—judicial powers by an administrative agency but similiar
functions have been and still are being performed by the Illinois
Commerce Commission,
the Fair Employment Practices Commission,
the
Department of Finance, and,
indeed,
by our
own predecessor,
the
Sanitary Water Board.
2. Jur
Trial.
In
addition,
for the reasons detailed
in the
Modern
P ating
ecision,
we reject the
jury trial argument
as
incorrect.
As we said in Modern Plating:
“An administrative order
to pay money
to either
a governmental
or non-governmental entity which Order is granted without the right
of
a
jury trial
is
not
a novel concept nor
in violation of constitutional
principles.
The constitutional right
to
a trial by
jury
is guaranteed
by the
6th Amendment of the United States Constitution in all criminal
prosecutions
and the 7th AmendmentLin
suits
at common law.~ An adminis-
trative order to pay
a penalty
is not the consequence of a criminal
prosecution,
and such payment does
not constitute
a criminal penalty
.Nor is ~he proceeding before
an administrative agency
a suit at
common
law.
3.
Penalties.
The City~s further argument
that the Board has
been granted the power
to levy “civil penalties. ..far in excess
of many
of the
fines provided for the Criminal Code
of the State
of Illinois
for misdemeanors”
has
no merit.
While we recognize
that certain misdemeanors
are more serious than others, we are
not prepared to compare the seriousness to the community of an
isolated case
of pollution with
the seriousness
of any given mis-
demeanor.
The heavy-thumbed butcher who cheatingly
tips the scales
commits
a misdemeanor, but who would seriously compare the penalty
he risks
to the penalty provided
for one who endangers the health
and welfare of the entire community by causing or allowing pollution
of our environment?
The legislature has
a good deal
of latitude
in making the sanction fit the offense,
and
its judgment here is
not unreasonable.
4.
Review.
Finally,
the City~scontention that “denial of the
right of review in the Circuit Courts...
discourages review, places
an undue burden on respondents
and denies equal protection of the
laws,”
is patently wrong.
If anything,
the ouportunity afforded
to respondents under the Environmental ProtCction Act to have adverse
administrative rulings
reviewed directly by the Appellate Court
encourages rather than discourages review.
Under our Act, there is no
need for
a repetitive,
lengthy and costly rehashing of the
same
~
(PCB
70—38,
71—6,
May
3,
1971)
p.6
2
—413

litigated matters at the Circuit Court level since the public hearing
conducted by the Board pursuant
to the Act and its
own Procedural
Rules guarantees to
the parties
a full,
fair,
impartial, complete,
inexpensive and speedy trial on the merits with all
the
procedural
and substantive constitutional guarantees which could be afforded by
any court
in the land.
To the contrary,
a requirement that the
parties conduct
a new trial at the Circuit Court
level would cause
the undue burden referred to by the
City and would result in expensive
and time-consuming protracted litigation while
the
issues raised by
the
case would be undecided and the public,
and presumably the environ-
ment, would suffer.
But the short answer is that direct review in
the Appellate Court is flatly authorized by the Illinois Constitution
and cannot therefore be ~aid
to violate that same document.
The
federal Constitutional question
is settled against the City by the
long
accepted and upheld practice
of direct appellate review of
comparable federal agencies.
5.
Parties.
The City has also stated that
the complainant in
this
case
is the Environmental Protection Agency whereas the Act
requires that such actions be brought in the name of the People of
the State of Illinois.
We reiterate
once again that our primary
concern
is with substance and not form,
In any event,
we
specifically
refer the City
to Rule 303
(b)
of the Pxocedural Rules
of the Illinois
Pollution Control Board which states that:
“Misnomer of
a party
is not
a ground
for
dismissal,
the
name
of
any party may be corrected at any time.”
There
are,
additionally, several preliminary matters raised by
the Third Party Respondents,
to which we now turn.
II.
The University
has scattered several points among
a
series of objections
and briefs challenging the Board~s
authority
in this case.
We shall
deal beiefly with each
point.
As the Hearing Officer correctly ruled,
the Third Party Complaint
as ordered by the Hearing Officer and served by
the City on the
University
in this case was
an appropriate means
of joining the Third
Parties pursuant to Rule
309 of
the Procedural Rules
of the Illinois
Pollution Control Board to
a proceeding already authorized for hearing
by the Board.
The procedure thus followed insured
a “convenient,
expeditious,
and complete determination”
of the
claims, and, since
the Third Party complaint raised no new or additional charges
of
pollution to change the substance
of
the initial complaint upon *qhich
the Board had authorized
a hearing, the University cannot claim prejudice
or surprise.
In effect,
the Third Party complaint incorporated the
First Amended Complaint by reference, thereby fully apprising the
University of the essentials of
the case against it.
Additional infor-
mation relied upon by Respondents
and Third Party Respondents to
adequately prepare their cases could have been,
and in fact actually
was,
as we have already indicated, obtained by
the ample discovery
allowed prior to the hearing on
the merits.
2
414

We
also note
that consultation with all parties was
conducted
before
a final hearing date on the merits was established and that
no motion for
a continuance on behalf of the University was ever
submitted to
the Hearing Officer or to the
Board.
Finally,
we
reject the University~sobjections based on sufficiency
of the
complaint for
the same reasons we rejected
similar
objections
by
the City.
The University has submitted documents entitled
(1)
Entry of
Special Appearance of Third Party Respondent,
the Board of Trustees
of the University
of Illinois,
and Motion to Expunge and Strike or,
in the alternative,
to Dismiss
for Want
of Jurisdiction,
and
(2)
Brief in Support of Motion on Special Appearance of Third Party
Respondent,
the Board of Trusteesof
the University of Illinois,
to Expunge and Strike or,
in the alternative,
to Dismiss
for Want
of Jurisdiction.
The principal thrust of these arquments
seems
to be that the University
of Illinois is exempt from and not
subject to the operation of the Environmental Protection Act.
This
is wrong.
Section
47 of the Act quite clearly states that:
“The State of Illinois and
all its agencies,
institutions,
officers and subdivisions shall
comply with
all requirements, prohibitions,
and
other provisions
of
the Act and of regulations
adopted thereunder.”
In its
Brief,
the University states that “if
all of the
provisions of the Environmental Protection Act were made applicable
to the State of Illinois,
its agencies,
institutions, officers
and
subdivisions,
there would exist
an impossible
and illogical situation
in which the
State, through the Pollution Control Board, would be
levying Lines against the State
itself,
and the group
it supports,
for failure to take an action which could not be taken because
the state had not appropriated
the money therefor.
Presumably
the state would then have to aopropriate the money
to pay the fine,”
It was clearly the intent of the Legislature
in adopting
Section
47 of the Act to ensure that all state agencies would
comply with
all,
provisions
of
the Act
and
the Rules and Regulations
promulgated thereunder.
To construe
this section as merely requiring
reporting by the Agencies would be tantamount
to emasculation of
the
section and would virtually exempt state agencies
from compliance
with state
laws pertaining
to
the protection of the environment.
As
the statute says,
the State should ensure that its own hands
are
clean before penalizing others for soiling the environment.
The Legislature,
in adopting
the Environmental Protection Act,
recognized the inadvisability
of
exempting certain special interest
groups from compliance with the Act.
The City of Chicago and the
2~-415

Metropolitan Sanitary District of Greater Chicago,
for
example,
which had been generally exempted from prior state environmental
legislation, are no longer granted such exemptions under the new
Act.
Similarly, state agencies at all levels must comply
with
all
requirements
of the Act,
Many state agencies, such
as penal
institutions, must comply with applicable regulations promulgated
by
the state Department of Health, among others,
and we
see no
inconsistency in requiring state agencies
to adhere to the
provisions
of the Environmental Protection Act as well,
especially
since the Legislature so clearly intended this result.
We need not decide whether
it would be appropriate,
if other
facts so indicated,
to impose money penalties on another state
agency,
for as discussed below we see no cause
for money penalties
in this
case.
The University~s argument that equipment cannot
be purchased unless the General Assembly appropriates money
for it does
not destroy the appropriateness of an order to comply;
it does under-
line the heavy responsibility of the General Assembly to fulfill
its specific promise
of
state compliance by making the necessary
appropriations.
The University further challenges
the jurisdiction of the
Board by asserting that if the University
is amenable
to suit on
the claim asserted by the Agency, such
suit may only be brought
in the
Court
of Claims.
In support of this assertion,
the University
states that this
is
a proceeding which “sounds
in tort”
and that
the
Court
of Claims has exclusive jurisdiction over all tort claims
against the Board of Trustees
of the University of Illinois.
In actuality,
these proceedings are neither criminal
in
nature nor are they actions
in tort.
This
is an administrative
adjudication under authority of the Illinois Environmental Protection
Act, which
quite clearly states,
as we have indicated above,
that
all state agencies must comply with
all the provisions
of the Act
and Rules adopted thereunder.
Exclusive jurisdiction of
“tort”
claims against the University may well
be in the Court of Claims but
the action we
are dealing with here is not
a
“tort” claim but
rather
a new,
statutory action, which did not exist at commOn
law,
The Pollution Control Board
is the proper body to hear
this matter,
as the Environmental Protection Act plainly provides.
III.
Finally, we address ourselves
to the motions filed by the
Third Party
Respondent,
Alpha
Material
& Fuel Company.
Alpha~smotion for
a summary order
of
dismissal, based on
technical objections
to the nature and form of the
Third Party
2 —416

complaint,
is denied.
As we stated above,
the Hearing Officer
correctly ordered
the Respondent
to serve
a Third Party Complaint
on the University
and Alpha as
a means
of joining these parties to
a proceeding already
instituted,
The claims against these third
parties were neither duplicitous nor frivolous.
The Third Party
Complaint, together with the First Amended Complaint and the
voluminous documentation exchanged on discovery, was more
than
adequate to fully apprise Alpha of the charges against it and of
the issues
in
the case.
Alpha~sMotion challenging the jurisdiction
of the Board is
based on arguments we have already considered,
Alpha repeats the
City~s
assertion that
the Act improperly confers legislative and
judicial powers upon the Board, which we once again reject as
erroneous.
Alpha states that Sections
12 and 13 of the Act are invalid
because they unlawfully delegate “arbitrary” powers to the Agency
and the Board
and, essentia~~lly,because they
are vague,
lacking
in preciseness
and indefinite.
In EPA v.
Granite
City Steel
Co.
(PCB 70—34, March
17,
1971) we considered these points and rejected
them.
The Act defines the clear limits of the
Board~s authority
and
is as precise
as
a statute can be without including numerical
standards,
Furthermore,
as to whether or not
the Act requires testimony at
the hearings
to be given under oath, we point out that such testimony
was,
as
a matter of
fact, given under oath.
Therefore
we’ do not
see
the need to comment on the question of whether or not testimony
before the Board must at all times be given under
oath.
Alph&s
objections contained in paragraph five of its
Motion Challenging Jurisdiction
filed on June
1,
1971, are also
rejected.
The procedures followed and
the time allowed the
parties for discovery and
for preparation of their cases herein were
more than adequate.
Furthermore,
at no time did Alpha ever request
additional time or
a continuance to prepare its
case more
fully,
and, when specifically asked by the Hearing Officer whether
it was
ready
to proceed on June
8,
1971, Alpha replied that
it was.
Never-
theless, additionaltime
was granted to all parties by the Hearing
Officer Lto assure adequate preparation
of their
cases,
and
a more
meaningful exchange on discovery and
the
full public hearings on
the merits of the
case did
not begin until June
28,
1971.
Further
delay would have been counterproductive.
The objection raised by Alpha to the provision of the Act
allowing direct review of Board decisions by the Appellate
Court
is rejected once again
for the same reasons stated above.
Finally, Alpha claims that Sections
27
and 35 of the Act
violate
the U.S.
and Illinois Constitutions by depriving Alpha of
7~417

equal protection of the
laws since they apply differently in
different geographic areas
of the State.
While these sections
are not even remotely at issue in this case,we would point out
that if Alpha’s argument
were accepted, it might also be utilized
to hold that different speed limits
for different highways
in
different portions
of the state are also unconstitutional.
We
are dealing with the health and welfare of the public and the
quality of the environment and therefore must take into consideration
a variety of circumstances
and conditions which may well be
different in different areas
of the state.
Not
to take
such
variations into consideration might lead to unfairness,
or at worst,
impossibility in attempting
to
apply
the
law
effectively.
Alpha’s
contention
is
therefore
rejected.
We
now
consider
the
merits
of
the
case.
IV.
The
Agency
has
alleyed
that
on
eight
separate
occasions
the
City
violated
Section
12
(a)
of
the
Environmental
Protection
Act
(“Act”)
and
Rules
1,05
and
1.08
of
the
Rules
ax~d
Regulations
of
the Sanitary Water Board, SWB-l4,
continued
in
effect
by
Section
49
(c)
of the Act.
Section
12
(a)
of
the
Act states
that
“no person shall cause
or
threaten
or allow
the
discharge
of any contaminants
into the environment
in
any
State
so
as
to cause or tend to
cause
water pollution in Illinois, either
alone
or in combination with matter
from
other
sources,
or
so
as
to violate regulations or standards adopted
by the Pollution
Control Board,.,”
Rule
1.05 of SWB-l4 states the
applicable
criteria
for “aquatic
life sectors”
in terms
of
maximum
and/or
minimum permissible levels of dissolved oxygen, pH,
temperature
and toxic substances.
Rule
1.08
of
SWB—l4 is the State’s
imuiementation and enforcement plan designed
to
control and
orevent pollution of the waters of
the State of Illinois.
The specific dates of the alleged violations are August
7 and 18,
September
18,
21,
23
and 30, and October
14,
all
during
1970,
and,
in addition, February
18,
1971.
In its
Third Party Complaint,
the City alleged that the University
caused
the violations of August
7 and 18 and that Alpha was
responsible for
the violations
of September
18,
21 and
23,
if,
indeed, there were violations
on any of those dates
at.
all.
By stipulation, however, Alpha admitted causing
a violation
on September
21
and the
City
agreed to amend its Third Party
Complaint
by
deleting
any allegations against Alpha pertain-
ing
to the alleged violations of September
18 and 23,
We will examine each
of
the dates of alleged violations
individually,
leaving till afterwards
the question
of
the City’s
responsibility for them,
1.
August
7,
1970
The Agency
alleges that or~August
7,
1970,
the City
“caused or allowed”
the discharge of waste waters from
a sewer
it operates and maintains located south of Green Street between
2
418

Locust and First Streets
into Boneyard Creek
“so as to cause
or
tend
to
cause
pollution”
of
Boneyard
Creek
in
violation
of
Section
12
(a)
of
the
Act
and
Rules
1.05
and
1.08
of
SWB-l4.
In
support
of
its
allegation,
the
Agency
offered
ten
samples
taken
over
a
period
of
3
1/2
hours
on
the
morning
of
August
7,
1970.
The
results
of
the
laboratory
analyses
performed
on
the
10
samples
as
indicated
on
the
Special
Analyses
Report
Forms
of
the
Agency
(E.P.A.
Exhibits
4
through
13,
inclusive)
were
as
follows:
EPA
Exhibit
Samples
No
Time
Taken
Temperature
pH
Suspended
Solids
1
Ex—4
9:03
a.m.
88°F
2.2
36
mg/i
2
Ex—5
9:30
a.m.
84°F
2.3
33
mg/i
3
Ex—6
9:50
a.m.
84°F
2.4
30
mg/i
4
Ex—7
10:10
a.m.
82°F
2.5
27
mg/i
5
Ex—8
10:30
a.rn.
80°F
2.7
16
mg/i
6
Ex—9
10:50
a.m.
80°F
3.0
21
mg/i
7
Ex—lO
li~i5 a.m.
80°F
6.0
34
mg/i
8
Ex—li
11:30
a.m.
82°F
6.1
34
mg/i
9
Ex—l2
11:50
a.m.
82°F
2.9
33
mg/i
10
Ex—l3
12:20
p.m.
84°F
11.8
52
mg/i
According
to
Mr.
Wallin
(R.
122)
,
the ten samples were
all
taken
from
the
same
location,
south
of
Green
Street
between
Locust
and
First
Streets,
some
30
feet
downstream
from
the
point
at
which
the
Boneyard
Creek
and
the
City’s
storm
sewer
system
merge
(R.
122).
Test
results
indicated
pH
readings
ranging
from
extremely
low,
2.2
(E.P.A.
Ex.
4)
to
extremely
high,
11.8
(E.P.A.
Ex.
13).
Temperature
changes
of
as
much
as
4° F.
in
less
than
an
hour
were
recorded
and
suspended
solid
measurements
were
as
low
as
16
mg/i
(E.P.A.
Ex.
8)
and
as
high
as
52
mg/i
(E.P.A.
Ex.
13).
Testimony
indicated
that
the
water
was
slightly
turbid
(R.
113),
with
blackish
deposits,
thick
film,
and
the
evident
formation
of
sludge
banks
on
the
bottom
(R.
113).
Mr.
Wailin
testified
that
a
normal,
unpolluted
stream
should
have
pH
readings
ranging
between
6.5
and
8.5
(R.
133)
;that
waters
showing
pH
values
as
high
or
as
low
as
the
extremes
measured
on
August
7
would
be
detrimental
if
not
fatal
to
aquatic
life
(R.
140,
182);
and
that
low
values
would
also
be
corrosive
to
concrete
and
corrugated
metals.
He
further
testified
that
clear,
unpolluted
streams
should
produce
suspended solids test
results
of
between
5
and
10
mg/i
(R.
143)
and
that
higher
read-
ings would
tend
to cause the formation of
“sludge banks” which
would
also
be
extremely
detrimental
to
aquatic
life
by
causing
2 —419

the clogging of
the air intake structures of small fresh water
aquatic iife organisms and resulting
in the reduction of food
sources
for higher aquatic iife,
such as fish
(R.
145)
Mr.
Waiiin further testified that he believed
the University’s
Abbott Power Plant was
the actual source of the contaminants
on August
7 due to regeneration
of its demineralizer system
and to operation of
its dust control device
(R.
215)
and
the
City alleged as much
in its Third Party Complaint.
But no
proof was adduced by any party to substantiate this claim or
to exclude the possibility of alternative
sources,
Counsel for
the City and for the Third Party Respondents
repeatediv stressed
the apparent deficiencies
in the testing
methods employed by
the Agency
and the departure of such methods
from the techniques specified
in Standard Methods for the
Examination of Water
and Waste Water, Twelfth Edition,
1965
(“Standard Methods”).
(R,
273—299),
They pointed out that
Rule
1,01 of SWB-i4 indicates that Standard Methods should be
empioyed where applicable although other methods may be required
in certain cases.
(R.
638-9).
Specifically,
Standard Methods
was
not followed with respect
to turbidity or color tests,
emptying and preparation of the sample bottles, temperature
measurements
(the Agency used an
alcohol
thermometer whereas
Standard Methods calls
for the use of
a mercury thermometer)
and time elapsed between extraction of the sample and laboratory
analysis of pH concentrations,
They also argue that the samples
were taken too near the outfalis under regulations allowing a
mixing zone.
We will discuss the alleged violations
in terms
of suspended solids,
temperature changes,
pH,
and settleable
solids,taking into consideration these variations
from Standard
Methods:
(a)
Suspended Solids:
Suspended solids readings ranged
from 16 to
52,
At present we have no stream standard for suspended
solids;
if one
is desirable, we invite the Agency to propose
it,
Rule 1,08 of SWB-l4, specifically subparagraph
lib,
is an
effluent standard for treatment works.
We cannot find
an effluent
violation where measurements have been taken not of the effluent
but of the water some
30
feet downstream from the outfall.
It
is also doubtful
that
this standard, which specifically refers
to treatment plants,
is applicable
to storm sewers.
It would
be helpful
if the Agency would propose
a clarification.
As
for the general allegation of water pollution under ~ 12
(a)
of the Act,
the Agency failed
to
adequately
show
the detrimental
relationship between the recorded levels
of suspended solids
and the gills of aquatic life organisms,
much less the bottom
biota
in Boneyard Creek, which
are affected principally by the
settleable portion of the suspended solids.
Therefore, we
find
no suspended solids violation.
2
420

(b)
Temperature
Changes:
Temperature
variations
of
4°F
within
less
than
one hour exceed the limits specified
in
Rule
1.08
(4)
of
SWB-l4,
In the
case of thermal discharges
to
the Illinois
River,
we have held the 600’
mixing zone described
in Technical Release 20—22 accurately expressed the purposes
of the Sanitary Water Board.
(In
the matter of Commonwealth Edison
ç~pany,
Dresden
Unit
No.
3,
PCB 70—21,
3/3/71).
In the present case
measurements were taken only
30 feet from the outfall
(R.
248).
When
dealing with small streams
such
as
the Boneyard however,
it
is reasonable
to question whether
a 600’
mixing zone could have been intended.
Conceivably,
the mixing
zone could be the entire length of the
stream if there are numerous outfalls,
so the regulation would
apply nowhere.
The Agency’s witness stated that he believed
30 feet was enough
to insure adequate admixture
(R.
248).
In
any case,
the City’s argument that
the
standard does
not apply
even beyond 600
feet
if there is
no
dilution water is incorrect
since the mixing
zone concept is based on assumption
that dilution
will occur; and the regulations make clear that the less there
is to dilute with,
the less may be discharged.
But
we
need not decide the size of the mixing zone applicable
to
temperature changes
in the Boneyard,
since
the Agency failed
to follow the prescribed testing method.
Not only were temperature
measurements made with an alcohol rather than
a mercury thermometer,
so that it could not
be
shaken down below the air temperature,
but tests were made
in the sampling
jar rather than in the
stream as required
(R.
280).
We do
not
know how
serious
an
effect these departures had
on
the results, but the alleged violation
is of only
a few degrees,
and we have nothing to show the change
cannot be explained by testing inaccuracy.
We therefore
find that
no temperature violation was established.
We urge the Agency
to propose
a suitable regulation
if the required testing methods
should be modified.
(c)
pH:
The reported pH values ranging from
2.2
to 11.8
greatly exceed thelimits prescribed by Rule
1.05 of SWB-i4
(6,0
to
9.0).
That rule applies to
“aquatic life sectors”
and,
since
the Boneyard has never been excluded from such designation,
the
standards for aquatic life sectors are applicable
(see Springfield
Sanitary District v.
EPA, PCB
#70-32,
1971).
We recognize that
the Boneyard
is
not presently in a condition to support aquatic
life;
but that
is the reason the case was brought,
not an excuse
for leaving the creek polluted.
The regulations require that streams
now in bad shape be upgraded to support aquatic
life.
As we pointed out above, we have previously acknowledged the
reasonableness of the 600
foot mixing
zone in some cases.
Tests here were taken
30
feet from the outfall.
Rule 1,05
however,
contains
its own definition of
a mixing
zone,
excluding
from protection only
“areas immediately adjacent to outfalls.”
Whether in the context of the small Boneyard the area “immediately
adjacent” extends
600
feet seems doubtful.
But we need not decide
2
421

whether
30
feet
is
“immeidately
adjacent”
since
such
extreme
pH levels
as here measured clearly constitute water pollution under
Sec.
12(a)
of the Act because they are likely to be lethal to fish
life and corrosive
to metals
and concrete and extremely hazardous
to people as well.
Neither TR 20-22 nor SWB-l4 can be read to repeal
Sec.
12(a)
of the
statute
by
allowing
water
pollution
within
600
feet
of
an
outfall;
the
statute
is clear that
water
pollution
is
forbidden
at
every
point
on
the
stream.
Standard
Methods
says
that
pH
readings can change rapidly and
that, therefore, testing for pH should be done in the field
(Standard Methods,
p.
32-3).
The samples taken by the Agency
here were allowed to sit around for several hours before they
were transported to the Agency’s laboratory.
However,
no proof
was introduced
to show that such extreme values
as these could
be accounted
for by the testing deficiencies.
The United States
Department
of the Interior publication A Practical Guide to Water
Quality Studies
of Streams
(1969),
of which we take official notice,
states that if there are delays in testing pH values,
“such data
may vary by
0.3
to 0.5 units or more from the values in the stream”
(p.
32).
This
is
a much smaller range of deviation than would be
necessary to explain the readings in the present case.
We find the
extremely low and high pH values found August
7 constitute water
pollution as described in Section
12(a)
of the Act.
We find no violation of Rule 1.08 since that rule contains
no pH standard.
(d)
Settleable Solids:
Since no effluent settleable solids tests were run,
Rule
1.08 does
not govern.
In addition,
Rule 1.05 contains no set-
tleable solids standard so no violation of that rule can be
found either.
We would point out, however, that Rule
1.03 of
SWB-i4 does apply to settleable solids and that
it explicitly applies
at all places,
not being limited by
a
600 foot mixing zone.
Further,
that rule clearly indicated that no nuisance of
a pollutional
nature will be allowed anywhere.
Violations
of Rule
1,03
of SWB-l4 were not charged here.
Our procedural rules require
invocation of the regulations relied on, but we have forgiyen their
omission in the absence of surprise.
In any event,
the presence
of settleable solids and their harm to the biota was amply shown
and their only source on the date in question was
the City’s sewer
system.
It is thus our opinion that the evidence justifies
a
finding of water pollution under Sec.
12(a)
of the Act due
to the
presence of settleable solids
in the Boneyard.
In summary, therefore, we
find water pollution under Sec.
12(a)
of
the Act on August
7,
1970 by virtue of extremely low and
extremely highpH
levels and of settleable solids that interfe~e
with aquatic
life.
2.
August
18,
1970.
The Agency collected only one sample on August
18,
1970,
that being taken from the exact location from which the August
7 samples
were
taken.
(R.
193-6).
The sample was taken at
4:45 pm and results of
laboratory analyses revealed
a pH reading of 10.1
2
422

and
a suspended solids reading of
40 mg/l
(EPA Exhibit
17).
Dark color,
odor,
and turbidity observations were made
(R.
195)
but there was no showing that these were sufficient
to interfere
with aquatic life.
Sludge banks were observed but could have been
there
for quite some time,
and they were not shown to be related
to the
City’s discharge.
The City maintained that the University was
responsible for any violation although no proof
to that effect
was adduced and other sources could have existed.
The Agency dropped its allegation that Rule
1.05 had been
violated
(R.
526) although
the stream had been sampled.
Finally,
the Agency did not allege any violation
of Rule 1.03 of SWB-l4.
For reasons outlined above,
we
find no suspended solids viola-
tion on August
18,
1970.
We think, moreover,
that
a single pH
reading of 10.1,
far less extreme than the repeated results on
August
7,
does
not sustain
a water pollution finding in light of
the uncertainty
of the tests performed.
3.
September
18,
1970.
On this date the Agency collected two samples.
The First
was taken
at 4:25 pm from the main channel of the Boneyard at
a point located near the First Street Bridge, somewhat down-
stream from the sewer located on the west bank of the Boneyard,
north of Green Street between Locust and First Streets.
Labora-
tory analysis
of this sample revealed readings of 10.1 pH and
18 mg/l suspended solids.
The
other sample
was
taken from street water entering a
storm sewer catch basin at the northwest corner of Healey and
Locust Streets.
Results of analyses showed 12.0 pH and
3,220
mg/i suspended solids,
As above we
find no suspended
solids violation; we cannot find
the City violated any effluent standard on the basis
of
a sample
of its influent.
Indeed it
is unclear whether we
can deal adequately
at present with discharges
to storm sewers either at the inlet or
at the outlet of the sewer.
We should welcome
a proposal foL
new
regulations.
The
pH test results here
are even less reliable than on the
earlier dates,
since
the bottle containing the
sample was kept
under artificial refrigeration
for three full days before lab
tests were run on its contents.
Moreover,
there was but one stream
sample,
and its
pH was
less extreme than on August
7.
We think
the pH evidence insufficient on September
18
and hence
find
rio
violation on that day.
4.
~mber
21,
1970.
Three samples were taken on September
21,
1970:
the
first,
at
approximately 4:10
pm, was taken from Street water entering
a
storm sewer catch basin at the northwest corner of Healey and

Locust Streets and
lab analyses showed pH levels of
12.0 and
total suspended solids of 1.060 mg/i
(EPA Exhibit 21).
The
second
sample
was
taken
at
4:17
pm
from
the
effluent
being
discharged
from
the
twelve-inch
tile
located
on
the
west
bank
of the Boneyard some eight feet north of the Green Street storm
sewer
tunnel.
Laboratory
analyses
of
this
second
sample
showed
a pH reading of 12.0 and
824 mg/i suspended solids
(EPA Exhibit
20),
The third and final sample taken on September
21,
1960 was taken
at 4:18 pm at
a point some eight feet upstream of
the outfall
from which the second sample had been taken,
and tests results
were 21 mg/i total suspended solids
(EPA Exhibit 22).
As correctly
pointed out by the City,
no samples whatsoever were taken down-
stream of the outfall.
The pH reading of 12.0
and suspended solids reading of
824 mg/i are extremely high, but here they came from an effluent
sample.
It is impossible to determine the effect such high
readings would have
on a stream without first knowing the amounts
of discharges and the volume of dilution water.
EPA v. Denny,
#71-32
(August
30,
1971),
In
addition,
while
the
suspended
solid
levels
greatly
exceeded
the
standards
for
treatment
plants
specified in Rule
1.08
(which, as we have noted, does not contain
a
pH standard), we are not here dealing with treatment plants,
but rather with storm sewers.
While
a discharger cannot avoid
these standards simply by having no treatment plant to handle waste
sources of the type contemplated by the regulations,
storm sewer
discharges are not intended to be covered.
And there were no samples
taken below the outfall from which water pollution could be found.
Nevertheless, Alpha
admitted
in
its
Supplemental
Answer
that
improper operation of its truck washout facility on September 21
caused a violation of Rule
1.08 and of Section 12(a), and
the City
agreed
by
stipulating
(R.
599)
that
the
statements
in
Alpha’s
Supplemental
Answer were true.
Furthermore,
the evidence substantiates
the
Sec.
12(a)
violation due to the white turbidity settling on the bottom
(R. 3634)
traceable to the City’s outfall,
Therefore, we find that excessive amounts of settieable
solids
entered Boneyard Creek from the City’s sewers on September 21,
1970
polluting
the
creek
under
Sec.
12(a)
of
the
Act,
and
that
on
the same date Alpha violated Rule
1.08 of
SWB-l4 and ~ 12(a) of the
Act.
5.
September
23,
1970,
The Agency took one sample on this date at 4:03 pm from
water entering the same catch basin located at the northwest
corner of Healey and Locust Streets.
Results of lab analyses
run on this sample showed pH levels of 11.8
and total suspended
solids of 1,692 mg/i
(EPA Exhibit 23).
Since the only evidence
offered by the Agency relates to water which went into
the sewer
2
424

but not to that which went into the stream or to stream quality
itself, we find no violation on this date.
6.
September 30,
1970.
In support of its allegation of violations occurring on
September 30, 1972,
relating toa sewer located on the east side
of the Fifth Street Bridge, the Agency introduced only one sample,
taken from approximately two feet inside a twelve-inch storm tile
bearing the designation “#22”.
Results of tests run on the sample
were
65 mg/i total iron and pH of 5.6
(EPA Exhibit 24).
A wit-
ness testified that the discharge was slightly red ~nd contained
particles of rust which settled rapidly and covered a portion of the
stream bed for 10 to 15 feet downstream •(R.386).
As we have already noted,
in order to properly evaluate the
effect of measured effluents, the Board must also be given some
idea of the amount of dilution involved.
Therefore, our observa-
tions concerning the pH level in the effluent on September 21,
1970, are equally applicable here.
There is no effluentstandard for iron at the present time, ex-
cept as a settleable solid, but we need not decide whether that
applies here since these particles apparently settled on the creek
bed to interfere with aesthetic uses of the Creek and aquatic life,
causing pollution under Sec.
12(a)
of the Act.
But notwithstanding
such finding, the City denies ownership of the tile in question,
and since no proof was put forth by the Agency concerning such
ownership, we must find that the Agency has not proved that any
violation occurred on September 30,
1970.
The Agency
flQW
concedes
this point
(Brief, p.4).
7.
October 14,
1970.
With respect to its allegation that the City caused or allowed
the discharge of waste waters from a sewer located at the southwest
corner of Second and Springfield Avenue on October 14, 1970, in
violation of
law, the Agency offered one sample, taken some two
feet beyond the point of discharge from the sewer.
Test results
showed a fecal coliform reading of 1,220,000 per 100 milliliters
and BOD of 19 mg/l
(E.P.A. Exhibit 25).
The E.P.A.’s witness testified that the fecal coliform test
results were indicative of a discharge of raw sewage into the stream
(R.
597),
We believe that such an extremely high fecal coliform
reading suggests the strong possibility of a severe health hazard.
The water was polluted under Section 12.
But there was no evidence
to show that this stream condition was traceableto effluent from
the City’s sewers,
and therefore we cannot find the City responsible.
8.
February 18,
1971.
The Agency took one sample from the Creek on February l8~
1971 from approximately the same location as the sample of October
14, 1970.
Test results showed a fecal coliform reading of 120,000
per 100 milliters and BOD of 21 mg/i
(E.P.A. Exhibit 26).
2
425

As on October 14,
1970,
the high fecal coliform readings indicate
a health hazard, but again there was no evidence tying this condition
to the City’s sewers,
Summary
In
summary,
we
find
the
following:
1.
~j,~l2j,Q
-
Water pollution under ~ 12(a) of
the Act
by virtue of extremely high and low pH and setteable solids;
2.
September 21,1970
-
Water pollution under ~ 12(a)
of the
Act by virtue of setteable solids; violations by Alpha
of Rule 1.08 and of ~ 12(a),
In addition to the specific instances of pollution found
above both the City and the University have stipulated to the
polluted nature of Boneyard Creek generally and
to their part
in
its condition,
although both disclaim legal responsibility in this
proceeding.
The stipulation signed by both
(at p,3)
states:
The Boneyard has,
for more than 40 years, been
a polluted
drainage ditch oi water source unsuited
for domestic, commercial,
agricultural or recreational uses or to livestock, wild animals,
birds,
fish or other aquatic life.
.
.
.
A substantial portion
of the polluted waters discharged into
the Boneyard flow
through various outlets of storm sewers owned by
the City of
Champaign.
.
.
.
The University of Illinois has contributed
to the pollutional problems of the Boneyard by virtue of
discharge from its Abbott Power Plant to the extent and manner
and nature
set forth
in the alternative motion of the Board
of Trustees of the University of Illinois
to dismiss the
Third Party Complaint for want of jurisdiction and in the
affidavits
and exhibits attached
thereto.
.
The affidavit of Mr.
Kretschmer, Director of
the University’s De-
partment of Plant
and Services,
concedes the necessity
for control
equipment
to bring
the power plant into compliance with the laws
and regulations, reporting that its fiscal year
1971 budget re-
quest “included an item of $100,000.00 for installing the necessary
equipment for treatment of the demineralizer waste waters of
the Abbott Power Plant to insure that, when discharged,
such waters
would be of the quality prescribed by state and local water pollution
laws and regulations.”
Moreover,
on the basis
of samples collected
in April,
1970,
the
Sanitary Water Board on June 17 of that year
informed the University that “a pollutional discharge is occurring
from the Abbott Power Plant
to a storm sewer system tributary to

the Boneyard Creek” in violation of statute
(Letter of C.W.
Kiassen
to V.L.
Kretschmer, June
17,
1970).
The University’s response
was
to concur that
“the
results obtained from the samples collected
during
your
investigation,
in
general,
agree
with
information
we
have previously collected”
and
to promise
to eliminate the problem
(Letter
of V.L, Kretschmer
to C.W. Kiassen, June
29,
1970).
(Both these letters
and the affidavit are appended to the University’s
Entry of Special Appearance of Third Party Respondent,
the Board of
Trustees
of
the
University
of
Illinois,
and
Motion
tO Expunge and
Strike
or,
in
the
Alternative,
to
Dismiss
for
Want
of
Jurisdiction.)
In short,
we
find that the University has conceded and never
denied
the
existence
of Boneyard pollution from its power plant and
has committed itself
to solving the problem.
We further find that
the City has conceded that material from its storm sewers contributes
to the pollution of the Boneyard.
To the issue of the City’s legal
responsibility
for what comes from its sewers we now turn.
V.
Section 12(a)
of the A~ctmakes
it
a violation to “cause or
allow”
the discharge
of any contaminants
into the environment
so
as
to
cause
water
pollution
in
Illinois.
The
City
points
to
the
evidence that the City did not generate
the waste but only transported
it
(R.
530)
and
to
the
stipulation
signed
by
the
Agency
agreeing
that
In no instance has
the City of Champaign originated,
authorized,
acquiesced
in,
licensed,
or ignored any poliutional ~ischarges
into
the Boneyard
or failed
to take any positive action to
prevent any continued poliutional discharge of which it had
knowledge or which has been called to its attention.
(R.
614)
Citing the compilation Words
and Phrases to the
effect that
“To
‘allow’
a thing to be done
is to acquiesce in or tolerate; know-
ledge, express
or implied, being essential”
(Brief,
p.
42)
the
City argues that because
“if all illegal connections to the storm
sewer were eliminated,
as they are in the process of being so
eliminated,
no effort
on the part of the Respondent could prevent
pollution from storm water urban runoff,”
to impose upon
municipalities the duty to insure against the occurrence of such
pollution is unthinkable.”
(Brief,
p.
48).
To hold that the City has an obligation to take affirmative
action to limit the pollution attributable
to material flowing
through
its
sewers,
however,
does
not
necessarily
make
the
City
an “insurer”
that no such pollution will ever occur.
It cannot
be
a complete defense that the City
did not itself generate
any
wastes
or discharge anything into
its own
sewers;
so to hold would
absolve any municipality
from the need to
treat domestic sewage
depOsited by others into
its sanitary sewers,
a plainly untenable
proposition.
We think the City,
by undertaking
to carry storm
waters from lands within its borders, assumed
a certain duty to
avoid unnecessary pollution as
a result.
Indeed in
the practical
2
—427

sense,
if not in the legal,
the City has accepted this principle,
for it has taken action on numerous occasions, according
to its own
statement,
to prevent others from dumping unauthorized pollutants
into its storm
sewers;
its stipulation, quoted above, stresses
that the City has never failed
“to take any positive action to prevent
any continued pollutional discharge of which it had knowledge or
which has been called to
its attention.”
We believe this principle
is embodied in the statutory term
“allow.”
As
the Agency says in its brief
(p.
12),
“To allow an
act is generally an act of omission and not commission.
People
v. Harnson,
170 N.Y.S.
876, at
877, 183 App.
Div.
812.
The verb
denotes an abstinence
from prevention.
Board of Education
v.
Board of Education,
3 Ohio
S.
&
C.P. Dec.
70
at
71.”
W~
have
consistently
so held in
regard
to the identical word
“allow”
in connection with
the
statutory ban on open burning
(Environmental Protection Act,
Section 9(c)).
E.g., Environmental Protection Agency
v. Amigoni,
#70-15
(Feb.
17,
1971):
An owner of
a refuse disposal facility
must
be responsible
for the actions of those
whom he allows to dump refuse on his
property.
If
such persons use
open
burning to dispose
of
their refuse
on his
facility, it will
be
presumed that
such
is allowed
and consented to
by
the owner of
the refuse facility.
The owner of such
a facility has
a duty to supervise its
operations
and to stop open burning on his premises whether by
himself or by those who he allows to do so.
Similarly,
in~Environmental Protection Agency v~Clay Products
Co.,
#71—41
(June 237T~7Y~
As we held in EPA v. Cooling,
#70—2
(December
9,
1970)
,
the
statute and the regulations are not limited to deliberate
violations,
Care must be exercised to prevent fires from
occurring and to extinguish
them if they do.
We believe these principles are equally applicable
to water
pollution.
The use of the word
“allow” expresses
a legislative
policy requiring affirmative action by
the owner of such property
as refuse dumps or sewers to prevent unnecessary pollution.
This
does not make him an insurer;
it does not mean the Board will
impose monetary penalties every time somebody pours oil into
a city’s
sewer in the middle of the night.
The question of technical
and
practical feasibility of control enters into the determination
of
a city’s obligation here, just as
it does in every other case
under
the statute
(Sections 31 (c)
,
33
(c)).
We will not require the
City to do what is unreasonable; but we do hold that the statute
requires
it to do its level best to prevent pollution from
its
sewers.
This conclusion
is buttressed by the fact that the City,
as owner,
is in a far more advantageous
position than is the Agency
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428

to perform routine policing of
its own sewer system.
This
is not
to say,
as the City argues, that
the Agency is attempting by this
~proceeding
to shift its own responsibilities
to the City,
The
Agency remains ultimately responsible to see to it that the pollution
laws are enforced.
But the statute is quite clear that the Agency
is not expected to go it alone:
Section
44 specifies
that “It shall
be
the duty of all state and local law—enforcement
officers to
enforce such Act and regulations.
.
.
.“
The battle cannot be
won unless all levels of government cooperate
to reduce pollution.
Defining the precise scope of
a sewer owner’s responsibility
cannot be done in
a single case.
Preliminary guidelines,
however,
can be stated.
Most clearly,
it is the City’s obligation
to do what
it can to prevent others from discharging inappropriate materials
into its sewers.
The enforcement of
a sewer discharge ordinance,
such as Champaign has,
is one step in furtherance of this duty.
It is not enough to take action after an instance of creek pollution
has been brought to the City’s attention;
the City must not only
correct what it knows about,
it must also make
an effort to find
out what needs correction.
It must police
the creek itself
to deter-
mine its condition;
it must police the sewers to determine any
illegal sources of pollution;
it must then take corrective action,
which may include the filing of complaints with this Board as well
as local remedies.
In the case of the pollution caused by the University and by
Alpha,
the City has quite commendably traced and discovered the
source of pollution and brought to us for appropriate action the
parties responsible.
However,
the City’s concession that the
Boneyard is polluted as
a result of
its sewers creates an obligation
to institute a program of policing and enforcement, beyond any that
was described in the record,
to prevent further pollution from the
sewers
to the extent practicable.
We do not hold that the City
must necessarily terminate every bacterial discharge, or that
it must run all its stormwater through
a sewage treatment plant.
The issues of practicable methods
of reducing pollution can be
addressed when the City reports to us its findings as to the causes
of Boneyard’s pollution.
We shall therefore order
the City
to
institute
a program of surveillance and policing and to report to
us within six months as to the sources of pollution and what can
be done about them.
As
for Alpha, that company has completed an improvement
program that results in complete recycling of its wastewater and
should eliminate further discharges.
We commend the company for
2
429

its effective action,
and we believe effective operation of the new
system can
be
stimulated
by
the
entry
of
an
order forbidding future
discharges.
As for
the University,
its intentions appear clearly
in the
direction
of
cleaning
up
the
power
plant
problem
as
soon
as
it
can get the appropriation.
We urge the General Assembly to make
that appropriation, and we think
it appropriate to stress our con-
cern by entering an order requiring
the University to correct the
problem within the shortest practicable time.
Moreover,
the
University’s
plans at present,
as described
in the record,
are not
sufficiently specific; we shall order that the University
tell us
in the immediate future just what
it intends
to build, what
effluents can be expected, and when completion will be achieved.
We do not
find
a case for imposing money penalties against
any of the respondents
at this
time.
Alpha promptly and effectively
remedied
its problem, which resulted
from
a one—shot accident;
the
University has done what
it can until
its moneys
are appropriated;
the City has
in good faith pursued many problems created by others
through the use of its sewers,
and we think no significant purpose
would be served by taking money from any
of them now.
This opinion constitutes the Board’s findings
of fact
and
conclusions
of
law.
ORDER
It
is
the order
of the Pollution Control Board that:
1.
The City of Champaign shall, by no later than March16,
1972, submit to the Environmental Protection Agency and
to the Pollution Control Board
a report containing, but
not limited to,
the following:
a)
A description of the condition
of the Boneyard and,
to the extent reasonably
determinable,
the sources
of its pollution;
b)
A description of steps taken by the City in the
intervening period to deal with cases of pollution
of Boneyard Creek;
c)
A detailed program for the policing of Boneyard Creek
and of
its sewers
in order to prevent the discharge
of unnecessary pollutants
into the Creek through the
Storm sewer system operated and maintained by the City;
d)
A detailed program designed
to clean up and improve
the quality of the water in Boneyard Creek within
a
reasonable but fixed period
of time, to
the extent
practicable;
2
430

2.
The University of Illinois shall,
by no later than
December
3,
1971,
submit to the Environmental Protection
Agency and the Pollution Control Board
a report containing,
but not limited to,
the following:
a)
A program detailing the corrective measures to be taken
in the future by the University
to control the dis-
charge of contaminants
from the Abbott Power Plant
into sewers tributary to the Boneyard C~-eek.
Such
plan shall include measures
for the interim control
of pH and settleable solids and shall indicate
a fixes
time schedule for
the implementation and completion
of the program.
3.
Alpha Material and Fuel Company shall cease and desist
the discharge of contaminants
into the Boneyard Creek
so as to cause or tend to cause water pollution of the
Creek.
4.
Upon receipt of the above required reports the Board
will decide what further proceedings are appropriate~
I,
Regina
B.
Ryan, Clerk of the Pollution Control Board, certity
that the Board adopted the above Opinion this
16
day of
1971.

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