ILLINOIS POLLUTION CONTROL BOARD
September
 11,
 1986
CITY OF LOCKPORT
 )
Petitioner,
v.
 )
 PCB 85—50
ILLINOIS ENVIRONMENTAL
 )
PROTECTION AGENCY,
 )
Respondent.
OPINION AND ORDER OF THE BOARD
 (by R.
 C.
 Flemal):
This matter comes before
 the Board upon the June
 14, 1985,
Amended Petition
 for Variance filed by the City of Lockport
(“Lockport”).
 Lockport seeks
 a five—year variance
 from 35
 Ill.
Adm.
 Code 302.209
 (Fecal Coliform)
 and 304.121
 (Bacteria)
 so that
it may forego the necessity of chlorinating the discharge from
its sewage treatment plant.
Lockport filed
 its initial Petition for Variance on April
18,
 1985.
 On May
 2, 1985,
 the Board
 found this petition
 to be
deficient,
 and allowed Lockport
 45 days
 in which
 to file an
amended petition curing those deficiencies.
 It was
 in response
to
 the May
 2,
 1985,
 Board Order
 that Lockport filed
 its June
 14,
1985, Amended Petition.
Two citizen objections
 to
 the granting of variance
 to
Lockport, apparently submitted independently of one another, were
received by the Board on May 14 and May 22,
 1985.
 One was simply
withdrawn prior
 to hearing.
 The other was withdrawn, renewed,
arid
 then withdrawn again,
 all prior
 to hearing.
The Illinois Environmental Protection Agency (“Agency”)
filed
 its initial Recommendation in this matter
 on June
 14,
 1985,
and its Amended Recommendation (“Amen.
 Rec.”)
 on January
 6,
1986.
 Both documents recommend the granting of the requested
variance relief
 to Lockport, subject to conditions.
BACKGROUND
Lockp’ort has a population of approximately 10,000,
 and
 is
located near
 the Chicago Sanitary and Ship (“S&S”)
 Canal on the
banks
 of
 the Illinois and Michigan (“I&M”) Canal
 in Will County,
Illinois.
Lockport’s sewage treatment plant (“plant”)
 is designed
 to
serve
 a population equivalent of 15,000, and has an average flow
72.256
—2—
of 2.0 million gallons per day (“mgd”)
 (R.
 at 9).
 Influent to
the plant passes through a bariminutor
 and grit chamber before
entering primary settling tanks
 (Id.).
 Flows less than 4.25 wgd
 are provided with secondary treatment by the activated sludge
process operating
 in
 a contact stabilization mode
 (Id.).
Effluent from the secondary settling tanks,
 and flows in excess
of 4.25 uigd from the primary settling tanks,
 are combined
 in the
chlorine contact tank (Id.).
 Final treated effluent is
discharged through an outfall directly to Deep Run Creek
 (R.
 at
9—10).
Deep Run Creek, which drains a basin of less than one square
mile between the I&M Canal
 and the S&S Canal, receives overflow
from
 the I&M Canal
 at its headwaters and from the S&S Canal via
several
 infiltration points
 (Id.).
 Below the plant, Deep Run
Creek is approximately eighty feet wide and one foot deep,
 and
 is
bordered by the Santa
 Fe Railroad tracks on one side and the S&S
Canal embankment on the other
 (Id.’J.
 Deep P~u~c~
 Creek,
 empt!~.ee
into the S&S Canal below the Lockport locks
 (approximately one
mile below the treatment plant discharges)
 (Amen.
 Pet.,
 par.
 2).
Lockport is
 in the process of upgrading
 its sewage treatment
works.
 The total cost of the project was estimated
 in 1985 to be
$10,007,220
 (Amen.
 Pet.,
 p.
 2).
 Lockport’s share of this cost
was estimated to be $3,795.853
 (Id.).
THE REQUESTED RELIEF
Lockport seeks relief
 from the fecal coliform effluent
standard
 of
 35
 Ill. Adm. Code 304.121 and the fecal coliform
water quality standard
 of 35 Ill. Adm. Code 302.209.
 Section
304.121 limits
 the level of fecal coliform that may be discharged
in
 an effluent to 400 per 100 ml.
 Section 302.209 states
 in full
that:
Based on
 a minimum of five samples taken over
not more than a thirty day period,
 fecal coliform
(STORET number 31616)
 shall not exceed
 a geometric
mean of 200 per
 100 t~1,nor shall more than 1~
 of
the samples during any thirty day period exceed
 400
per 100 ml.
72.257
—3—
Lockport seeks
 the requested variance for
 a period o~five
years or
 until
 the Board adopts
 a new biological standard
 (Amen.
Pet., p.
 1).
 Lockport seeks this variance
 in order
 to avoid
 the
necessity of chlorinating flows from its plant which have
received secondary treatment.
 Currently,
 the plant can provide
secondary treatment for flows of less than 4.25 mgd.
 Lockport
proposes
 to forego chlorination of flows below this amount, but
continue chlorination of
 all
 flows exceeding 4.25 mgd
 (R.
 at 12—
13).
 After
 the plant
 is upgraded,
 it will
 be capable of
providing secondary treatment to flows
 of up to 6.14 mgd
 (R.
 at
12).
 After
 that occurs, Lockport proposes to chlorinate only
those flows exceeding 6.14 mgd or those exceeding the volume of
wastewater receiving secondary treatment, whichever
 is less
 (R.
at 12—13).
ENVIRONMENTAL IMPACT
Deep Run Creek
 is a man—made stream, approximately 3.7 miles
in length
 (R. at 13).
 It presently supports
 a small minnow
population,
 and due
 to its limited canopy cover, limited pool
development, and shallowness,
 is considered
 to be habitat limited
(Id.).
 Lockport and
 the Agency agree that given
 these
characteristics,
 the Creek’s relative inaccessibility,
 and the
fact that there are no known sanctioned public uses of the Creek,
the addition of (secondary)
 treated but unchlorinated effluent
will not adversely affect
 the environment or public health
 (Rec.,
p.
 4).
Lockport added
 that it believes the granting of variance
here would improve conditions
 in 9eep Run Creek by reducing the
potential effects of chior—arnines
 in
 the discharge.
1There
 is presently pending before
 the Board,
 in the R85—29
docket,
 a proposal which would readopt the fecal coliform
regulations
 as they existed prior
 to the Board’s action
 in the
Matter of Amendments to Chapter
 3: Water Pollution (Effluent
Disinfection)
 (R77—l2, Docket D) and also amend
 them so as
 to
require chlorination on a seasonal basis only.
 There are at
present no proposals before
 the Board which suggest the adoption
of either alternative biological standards or alternative
disinfection technologies.
 Thus,
 there currently are no
proposals before the Board which,
 if adopted would obviate the
need for chlorination.
2A by—product of the chlorination process.
72.258
—4—
HARDSHIP
Lockport contends that requiring
 it to comply with
 302.209
and 304.121 would
 impose an arbitrary or
 unreasonable hardship on
it.
 The June 14,
 1985, Amended Petition
 filed by Lockport does
not clearly delineate the aspects
 in which Lockport will suffer
hardship
 if denied variance relief.
 On page
 1 of the Amended
Petition, Lockport states:
A variance
 is requested... for
 the express purpose
of deferring or eliminating the need
 to construct
new chlorination facilities at Lockport’s sewage
treatment plant.
However, on page 4 Lockport states:
chlorination facilities will
 be provided for
stormwater overflows as part of the upgrading
 of
the Lockport sewage treatment plant;
 these
facilities can also be used to chlorinate
 the
effluent which receives full secondary treatment.
Confusion surrounding
 the hardship was somewhat diminished
by the stipulation of fact read
 into the record at hearing.
 That
document, stipulated
 to by counsel for Lockport and
 the Agency,
contains the following statement:
“Lockport
 is seeking relief from this
 fecal coliform
standard
 to avoid having
 to chlorinate flows
 from its
plant which receive secondary treatment.
 The City,
in its improvement project, will provide the physical
facilities necessary to
 treat all of its flows, but
by not chlorinating flows which receive secondary
treatment,
 it wills save approximately $5,000
 a year
in chlorination costs.
Apparently,
 contrary to its assertion otherwise, Lockport
 is
therefore not seeking variance
 in order
 to avoid the construction
of new chlorination facilities at the plant.
 Thus,
 the Board
will assume that Lockport’s upgraded plant will
 indeed contain
 chlorination equipment,
 arid that Lockport seeks variance in order
to avoid the necessity of using
 it to chlorinate effluent which
has received secondary treatment.
COMPLIANCE PLAN
Lockport does not offer
 a compliance plan
 in its Amended
Petition, even though such a plan is required by 35
 Ill. Adm.
Code 104.121(f).
 Rather, Lockport only generally states that
 it
will comply by the end of the variance term or apply
 for site—
specific relief
 (Amen.
 Pet.,
 par.
 10).
 The Agency, noting
 the
72.259
—5—
absence of a compliance plan, observed
 that “(Lockport)
 is
apparently hoping that a regulatory change will eliminate the
need for disinfection”
 (Rec.,
 p.
 7).
CONCLUS ION
Lockport has not met an essential prerequisite
 to the
granting of variance relief:
 the identification of, and
committment to,
 a compliance plan.
 It is
 riot enough for
 a
petitioner
 to generally promise
 to attain compliance by the end
of
 a variance period;
 a compliance plan must include a detailed
description of
 the method of control
 to be undertaken
 to achieve
compliance,
 including a time schedule
 for attaining each
increment of progress.
 Lockport’s Amended Petition
 is clearly
deficient
 in this regard.
Moreover,
 it
 is also inappropriate for
 a petitioner
 to
 seek
variance relief on the basis of potential changes in the law
which may result from pending
 regulatory proceedings.
 As has
been noted by the Illinois Appellate Court, “If the speculative
prospect of future changes
 in the law were
 to constitute an
arbitrary and unreasonable hardship, then the law itself would be
emasculated with variances,
 as there
 is always
 the prospect for
future change”.
 Citizens Utilities Company of Illinois
 v.
Illinois Pollution Control Board,
 No.
 3—84—0412 and No.
 3—83—
0498, consol.
 (June 17,
 1985).
The
 Board further believes Lockport has not shown that it
would
 suffer arbitrary or unreasonable hardship if denied the
variance relief it seeks.
 The sole hardship asserted by Lockport
is the $5,000 annual cost of chlorinating its secondary treated
effluent.
 Though not an insignificant sum, an annual expenditure
of $5,000
 to
 a municipality the size of Lockport is not
 in this
instance
 a substantial
 enough amount
 to warrant
 a Board finding
that arbitrary or
 unreasonable hardship would result from
 compliance being required.
The Board
 is also concerned about an underlying
 issue which,
though largely unstated, permeates the record
 in this case.
 That
is the matter of the relative merits of chlorination as a
disinfection practice.
 Lockport relies heavily on the fact that
in the Matter of Amendments to Chapter
 3: Water Pollution
(Effluent Disinfection)
 (R77—l2), the Board deleted the fecal
coliform water
 quality standards for general use and secondary
contact waters and relaxed the
 feca.
 coliform effluent
limitation.
 As noted
 in Lockport’s Amended Petition, the
Illinois Supreme Court
 in People
 v. Pollution Control Board,
 103
Ill.
 2d 411, 469 N.E.
 2d 1102
 (1984)
 reversed
 the Board’s repeal
of the fecal coliform water quality standard relating
 to general
use waters
 and
 its revision of the fecal coliform effluent
limitation.
 The Supreme Court remanded the matter
 to the Board
72.260
—6—
for further
 consideration.
 As described
 in footnote
 2,
 the fecal
coliform regulations presently pending before the Board as
 a
result of the Supreme Court
 remand
 are
 in the R85—29 docket.
Lockport apparently assumes, based on the Board’s action
 in
R77—12, that the Board believes the disadvantages of chlorination
as
 a disinfection practice
 to outweigh its merits.
 Lockport’s
assumption, stated another way, might be that the Board still
stands by the rationale and specific conclusions of its Opinion
and Order
 in R77—12, Docket
 D.
 This assumption is implicit
 in
Lockport’s assertion that, under the R77—l2, Docket D Opinion and
Order,
 it would
 not have had
 to chlorinate
 its effluent because
its discharge
 is more than twenty miles upstream of any public
water supply or bathing beach
 (Amen. Pet., par.
 5).
Lockport therefore seems
 to justify its requested variance
relief
 in part on
 the Board’s action in R77—l2, Docket D.
 The
Board’s difficulty with this position
 is that
 it assumes that the
Board already has, or will
 in this proceeding,
 determine the
relative merits of chlorination as
 a disinfection practice.
 In
response,
 the Board notes
 that it has not already made this
determination;
 the Supreme Court remand of R77—l2, Docket D
essentially wiped
 the slate clean
 insofar
 as Board action in the
fecal coliform area
 is concerned, and there has been no final
action
 taken
 at this time
 in the matter
 of R85—29.
 The Board
similarly notes that it will not judge
 the merits of chlorination
in this proceeding,
 for
 a regulatory proceeding, and not
 a
variance case,
 is the proper forum
 for such
 a determination.
This Opinion constitutes the Board’s findings of fact and
conclusions of law in this matter.
ORDER
The City of Lockport’s request for variance from 35
 Ill.
Adm.
 Code 302.209 and 304.121
 is denied.
IT
 IS SO ORDERED.
I, Dorothy
 M.
 Gunn,
 Clerk of the Illinois Pollution Control
Board, hereby certify that_the above Opinion an
 Order was
adopted on the
 //(4-
 day of
____________,
 1986,
by
 a vote of
____________.
o~_
Dorothy M. Gu~n,Clerk
Illinois Pollution Control Board
72.261