1. 28-10k
      2. 28-1 09
      3. Pollution, are amended in conformity therewith:
      4. (bb) Lake Sangchris

I~~fNOiS
POLLUTION
CONTROL BOARD
October 13, 1977
IN
THE
MATTER
OF:
PROPOSED SPECIFIC
THERMAL
)
R76—11
STANDARDS FOR LAKE SANGCHRIS
OPINION AND ORDER OF THE BOARD
(by Mr. Goodman)
:*
The Proposal for Regulatory Amendment
in this
matter was filed
by Commonwealth Edison Company
(Edison)
on April
19,
1977,
accompa-
nied
by the signatures of more
than
200 citizens requesting its
consideration and adoption.
Ill.
Rev.
Stat., Ch. 111-1/2, §1028
(1977);
Ill.
PCB Regs.,
Ch,
1,
§204 (a) (1977).
At its regular meet-
ing of April 22,
1976,
the Board authorized hearings on the matter.
The Board also ordered publication of Edison’s Proposal, which was
published
in Environmental Register
#124, published April
27,
1976.
On September
1,
1977,
the Board entered an Order setting a pro-
posed final draft of
the
Reguiatio~ ‘for publication and a 30-day
public
continent period.
The proposed final draft
was published
in
Environmental Register #155,
datu~ISeptember
12, 1977.
No comments
were received.
The Board therefore adopts
as final this Opinion
and Order, ending over four years
of
consideration
in this matter.
Edison’s Petition,
filed under Rule 203(i) (10)
of Chapter
3:
Water Pollution, asks that the Board set specific thermal standards
for discharges
from Edison’s Kincaid
power generating station to
the lake.
Edison asked that the Board set such limits by amending**
Rule 203(i) (11), Exceptions
to Rule 203(i),
to include new Rules
203(1)
(11) (bb) (1) and
(2)
,
as follows:
(bb) Lake Sangchris:
The thermal discharge to Lake Sangchris
shall meet
*
The
Board
wishes
to thank Vincent P.
Flood, Jr., Attorney,
Hearing Officer in this matter,
for his assistance
in the preparation
and drafting of
this
Opinion
and
Order.
~
The procedures for proceedings under
Rule 203(i) (10)
of
Chapter
3 have been changed since the inception of this case,
that
change
to
effect
only
case
filed
after
April
1,
1977.
See,
Ill.
PCB Regs,,
Ch.
1,
Part
VI(A),
§~1-4,
R77—ll
adopted May 12,
1977.
See, also,
PCB R77—7,
adopted
June
28,
1977, amending Rule 203(i)
(10)
(cc);
future proceedings will be
adjudicatory,
and not
Regula-
tory;
see,
also,
R77—l
(March 17,
1977).
28-107

—2—
the following standards and conditions:
(1)
The effluent temperature shall not exceed
99°F.during more than seven percent of
the hours in the 12-month period ending
with any month and shall
at no time exceed
111°F.
(2)
All conditions adopted by Board Order
in
PCB R76-
this
proceeding).
BACKGROUND
The thermal discharge from Edison’s Kincaid station into Lake
Sangchris has been before the Board on two prior occasions.
In
Citizens
for a Better Environment
v. Commonwealth Edison,
PCB 73-245,
-24~(consolidated)
,
~13 PCB 69
(1974), the Board determined that the
thermal discharges from Kincaid station are in fact subject to the
Board’s thermal limitations.
Ill.
PCB Regs.,
Ch.
3,
§203(i)
(1-4)
(1977).
Although the Board did not
find that the thermal discharges
into Sangchris had caused any environmental damage,
13 PCB
at
80,
81,
the Board nonetheless stated that Edison’s discharge must
(1)
comply with Rule 203(i);
(2)
become subject to
a Variance pending
implementation of
a compliance plan for such discharges;
or
(3)
be
the subject of
a Regulatory change
if Edison thought the thermal
limitations were neither necessary nor reasonable.
We noted in Sangchris’ next appearance before the Board that
Edison chose the last of those possibilities.
On January 22,
1975,
Edison submitted a Regulatory Proposal to exempt all “artificial
cooling lakes”* from the Board’s thermal discharge limitations.
In the Matter of:
Water Quality and Effluent Standards Amendments,
Coolin9 Lakes,
P75—2,
18 PCB 381
(Order),
18 PCB
661,
686
(Opinion)
Although the Board did not grant the general relief requested
by Edison
in that Proposal, we did set standards by which individual
artificial cooling lakes could receive specific thermal standards
appropriate under the circumstances.
While Edison had also asked
for such standards for Lake Sangchris,** the Board found that Edison
had failed in one specific regard:
While Edison had successfully
shown that thermal discharges into the lake had not historically
*
Sangchris
falls within the class,
“artificial cooling
lakes”;
see,
18 PCB at
686.
**
The standard asked by Edison in R75—2
was:
The temperature of the condenser cooling discharge from Kincaid
station shall not exceed 107°Fexcept that for
5 percent of the hours
in any 12-month period ending with any month during which time ex-
cursions shall be allowed up to a temperature not to exceed 122°F.
28-10k

—3—
caused
environmental
p:~c~iems,
Edison had not demonstrated that
the requested specific
I’
~aa1 discharge limitations were those
which had led to our en~.Lronmentalfindings.
The Board stated
that, “amy
standard which we may set for Lake Sangchris would
be,
in effect,
the historic fact for that lake.”
18 PCB at 712.
Not having received the requested specific thermal standard in
R75-2,
Edison saw its burden
in this matter as threefold:
1.
A demonstration that the environmental findings
of the Board with regard to Lake Sangchris had not changed
since our decision in R75-2.
2.
A demonstration that the cost of alternative
or supplementary cooling methods for condenser coo1~nq
water discharges from Kincaid to Sangchris remains,
as
found in R75—2, unreasonable.
3.
A demonstration of the actual discharge tempera-
tures
from Kincaid to Sangchris during the period for
which we found no environment--~i.,harm (the “historic fact”).
Edison’s case
in this matter was organized accordingly,
and we shall
follow the same order
in reviewi:;~jthe evidence before us.
ENVIRONMENTAL CONSIDERATIONS
In Both PCB 73-245, -248
(consolidated)
and R75-2, the Board
found that Lake Sangchris was “environmentally acceptable.”
That
finding was more conclusive in R75-2, where the Board examined
extensive testimony and documentary evidence regarding the lake.
(In fact,
most of the evidence received by the Board
in R75-2 either
concerned Sangchris directly or extrapolated from data gathered
there.)
*
Although the Record in R75-2 contained other useful reports
concerning Sangchris,
the most valuable testimony came from studies
performed by the Illinois Natural History Survey, which was then
(and still is) engaged in a long-term study of the lake.
We
shall
not reiterate all of our findings with regard to Lake Sangchris
in
this Opinion.
Our Opinion in R75-2 contains numerous specific
discussions and should be referred to for more complete coverage.
18 PCB at 695,
696—700,
702—705,
707—712.
*
The Board noted
JE~75-2that Edison “bore the brunt of
the evidentiary burden” there and commended
it for the completeness
and comprehensiveness of its presentation.
18 PCB at 695.
28-1 09

—4--
Irs~
~‘
~c
need
note
only
those
findings with regard to Sang-
chrL~wh~onhave
been updated by
the
Natural History Survey and/or
discussed in this
proceeding.
There have been,
since the Board’s
consideration in
R75-2,
few chenges
in
Lake
Sangchris’
biota,
(R.75)
A representative
of the Natural
History
Survey characterized the
lake as
~romarkably stable” with few
changes during three years of
sampli.ij,
(Id.).
While fish populations fluctuate, this
is thought
to be a
iatural
condition,
unrelated to operations
at Kincaid or
its thermal load upon the lake,
(R. 76-77).
The only general anomaly
noted in
the
Record was to the effect that the lake is apparently
aging slowly;
it
is “of an age where the fish population ought to
be going drastically downwards,
and it is not.”
(R.84).
In fact,
some of the potential problems noted
in ou~
Opinion
in R75—2 have
apparently been resolved.
We noted,
18 PCB at
709,
that there was a problem in the lake with bluegill stunting.
Testi—
many indicated,
however, that this is
a common problem with lakes
and reservoirs
in Illinois;
the
fish simply
outbreed the available
food supply,
(R,72,73).
Carp reproduction failure, also noted as
a problem, may in fact be due to pesticide discharges into the lake
from surrounding
farmlands,
(Economic
Impact
Ex.
1,
p.32).
At
any
rate,
the presence
of
carp
is
i~
n~cessarily
desirable.
Exhibit
9 in this proceedinc~,
the
Annual
Report for FY 75,
submitted
b
the Natural History
Survey,
contains an extensive
description of the ecology of Lake Sangchris covering most fish,
as well as all other flora and fauna of the lake,
(see,
§S2-4,
6-10),
That
report covers much that was discussed in R75-2, as
well as considerable new data,
and does not indicate any signifi-
cant problem.
Although there are thermal effects, they are not
deleterious.
(See,
e.g., pp.4.42-4.44).
The conclusions
we
reached
in
R75—2
remain
unchanged.
COMPLIANCE COSTS
In R75—2 the Board also examined closely the costs
of compli-
ance without
existinq
thermal
sLandards
by
Kincaid
station.
The
Board
discussed
various
alternatives,
including
cooling
towers,
spray canals,
and variations
on
those
methods.
18
PCB
at
689-695.
In this case we have not only more extensive data on the costs and
problems associated with those technologies, but also have the costs
or problems
which
might be associated with other potential compliance
methods
principally
modification of station operation to assure
compliance.
The source of this additional data is the Economic
Impact Study
prepared
by tte Illinois Institute for Environmental
Quality under Public Act 79—790,
(requiring such studies).
In
addition
to meeting the requirement of P.A.
79-790,
the Institute
study give’
ocn~iderable,
helpful detail from the technical/merits
records
~oncerninq Sangchris to illustrate and justify the economic
alternatives ~
resented.
28-110

—5--
We estimated in
that a mechanical draft cooling tower
at Lake Sangchris would.
st approximately $25 mIllion,
18 PCB at
690.
Edison~sestimate
,~f ~22.086 million and $24.646 million
are reported in the Institute’s Economic Impact Study,
(Economic
Impact Ex.
I at 23,26).
A similar sized mechanical draft cooling
tower for Central Illinois Public Service Company
S
Newton power
station
is estimated at $27.976 million, and the Institute gave an
estimate of $l2/kW which,
in 1976 construction dollars, would amount
to $24.8 million.
The figures given
in R75—2 for natural draft cooling towers
have similarly inflated.
We
there
estimated,
18
PCB
at
691,
a cost
of approximately $31 million; estimates
in the Economic Impact
Study
are greater, amounting to $43.4l7 million ~conomic
Impact
Ex.
1, Table 5),
or $37,156 million for Newton,
kid.,
Table 8).
Since our last discussion of spray canals,
the cost has also
gone up; the Institute has found that,
“The unit did not meet the
manufacturer’s expectations..~at least
520 modular spray units
would
be required at the Kincaid station.”
(Economic Impact Ex.
1
at 26.)
In R75-2 we estimated that only 130 modules would be
required for Kincaid.
Although th’
~osts have not risen propor-
tionately
(from 38 million to 40 mislion),
it would appear that
spray modules would probably be a~
-
xtremely expensive alternative
to Lake Sangchris
as a cooling ms~hanismfor the station.
The Institute estimated that if Kincaid were to attempt to
meet existing standards by modifying operations ~t Kincaid,
the
maximum
plant loading would be
275
mW
with
three pumps operating,
and 360 mW with four pumps,
(id., at 11).
Using an average auxil-
iary power cost to estimate the cost of such reduced operation,
the Institute estimated that annual costs for such compliance
would be $25.6 million for a three pump operation and $18.9 million
for a four pump operation,
(Id.,
at 14),
Without reiterating the Institute’s entire study, we should
note that it also discussed other alternatives, such as
the cost
of compliance with an absolute standard of 99°F., (e.g., Table 14,
alternative
C,
D).
The Institute also considered the cost to
consumers, business, and
industry
for
the
various
possible
alterna-
tives,
on total and annual bases.
The study went so far as to
consider replacement costs,
which are
not
included
in
rate—making
calculations,
(Id., at
54),
The
study
noted
that,
“tjhe
real
impact will be felt when replacement generating capacity is built
at a cost increase of about 4.6 times.”
(Id.,
at
64.)
28-111

—6—
Although the Instif
~e did initially question Edison’s proposal
of 111°F.,preferring
as. excursion figure of 107°F.,this was later
somewhat modified at hearing,
(Economic Impact Ex.
1, p.64;
Economic
Impact R,14,45).
The essence of the Institute’s
study was that,
“Both economic and environmental considerations favor the proposed
standard.”
(Economic
Impact
Ex.
1 at
64.)
Ernest L. Hardin, the
study’s principal author,
stated at hearing that,
“ilin
the absence
of significant environmental damage,
the proposed standard is clearly
the
least
costly.”
(Economic
Impact,
R.l9.)
The Institute did qualify its recommendation in the Economic
Impact Study, however,
to the extent that it felt that more study
is needed with regard to the effects of very hich temperatures on
the aquatic biota,
(Id.),
The Institute stated that, while Sangchris
is “certainly the most studied cooling lake in Illinois,’
IL
would
still prefer the Board to “defer setting a maximum temperature limit
until
more is known of the effects of peak and sustained high tempera-
ture discharges.
Lessons learned at Lake Sangchris can be applied
elsewhere.”
(Id,)
OTHER ECONOMIC IMPACT
The Institute study also discusses the economic impact of the
proposed Regulation,
other alternatives,
and compliance with the
existing standard on the various sectors delineated in Section 6(b)
of the Act.
This analysis weighed both the costs and benefits
associated
with
the
various
alternatives
with
respect
to
the
entire
spectrum of possibilities shown there.
In essence, that analysis
showed that while there might be little immediate effect on electric
utility rates,
a longer term examination of the costs associated
with compliance at any standard other than that proposed by Edison
is unfavorable.
Although the study is designed so that costs and
benefits can be independently weighed
(see, p.48),
the study,
“suggests that the environmental certainties of the existing cooling
lake operation are to be slightly preferred over the more costly
alternatives which would limit the heat discharged into the lake
by modifying the load carried by Kincaid station.
The offstream
cooling alternative shows
a significant increase in the environmental
costs and
a declining trend in benefits.
.
.“
(Id.)
We agree.
Our analysis of the Institute’s study and the testi-
mony presented with regard to it by the Institute and Edison leads
us to conclusion that no significant environmental benefit is to be
gained by requiring discharge temperatures lower than those histori-
cally experienced,
and that the high costs associated with such
additional limitations are therefore unjustifiable.
28-112

—7—
TEM~
ERATURE
EXPERIENCE
As noted above, the Board found in R75-2 that the only ingredient
missing and needed for the Board to set a specific thermal standard
was hard evidence as to the actual
temperatures
of Kincaid thermal
discharges.
Based on our analysis above,
that remains true:
The
environmental quality of Lake Sangchris remains good, and the costs
and
economic
impact
associated
with
meeting
existing
standards
are
unreasonable.
In this case, however, Edison has supplied the neces-
sary discharge temperature data.
Edison used 1975
to provide temperature figures in addition
to those submitted in R75-2.
Data from that year
indicated
that
99°F.was exceeded
5.2
percent
of
the time, with a maximum tempera-
ture experience
in 1975 of 110.5°F. (rounded to 111°F.).
(See, e.g.,
R.17)
Edison found, however, that the
1975 capacity factor of Kincaid
was only 43 percent,
as compared
to a
five—year
average
of
64
percent.
Edison therefore arrived at the requested
7 percent excursion limit
by multiplying the 5.3 percent
excorsion
experience
of
1975
by
the
ratio of that five—year average capacity
factor
to
the
1975
capacity
factor,
(Id.).
The Record in R75-2 did contain a
significant
number
of tempera-
ture readings for Kincaid and Sangchris,
(including locations in
Sangchris so close to the discharge canal as
to
effectively
reflect
discharge
temperatures,
there being
little
temperature
change
in
the
discharge canal).
(See,
e.g., Exhibits 6-E,
6—I,
6-J,
6-K,
7,
10, and
various testimony in R75-2.)
In this case Edison has also
entered exhibits demonstrating discharge temperatures,
(Exs.
6,
8).
These exhibits support the testimony referred to above on discharges
from Kincaid into Sangchris.
Additional data for 1969 and 1973
was also supplied,
(Ex. 11).
Apparently to assure itself of receiving the requested limit,
Edison has been quite conservative in
its request.
Edison discounted
some very high readings as “aberrations,” assuming that the monitoring
equipment was not functioning,
(e.g., Economic Impact R.52).
Similarly,
the 1969 data indicates that it could be difficult to
meet the requested standard;
in
1969,
107°F.
was
exceeded
322
times.
In addition,
the Institute has assumed that higher temperatures
than those requested either have been or would be experienced during
hot, dry summers.
To meet the requested standard, there is
a
potential
annual cost for load reduction of about $2.8 million,
(Economic
Impact
Ex.
1 at
18).
28-113

—8—
We find that the temperatures requested in Edison’s Proposal
here are
in fact temperatures conservatively representative of
historic operating conditions at Kincaid station.
In light of
that finding,
and in conjunction with our other findings as to
environmental and economic effects of the existing and proposed
standard, we feel that Edison’s Proposal has been justified.
The Agency,
while recommending a change in its “comments”
in lieu of a Brief, has suggested that the Board set either month-
by-month discharge limitations or condition the specific standard
requested upon a requirement that the capacity and operating load
of Kincaid station remain unchanged.
We feel that neither of
these limitations
is necessary inasmuch as the standard requested
by Edison will itself limit the station during the critical summer
months to historic operating conditions,
and temperatures ~o1eterious
to aquatic life are unlikely to occur outside of the summer months.
It is plain that the limits requested by Edison pertain primarily
to the hot summer months, and that the
7 percent excursion limit
will be used largely during those months.
We shall,
therefore,
set the standard as requested by Edison.
We also note that the standard set here effectively removes
any thermal limitations which might be implied from Rules
201
(mixing zones)
and 402
(violation of water quality standards).
Inasmuch as we have set no conditions
as
a part of this proceeding,
the second portion of Edison’s request
is superfluous and shall be
dropped.
Finally,
the
Hearing
Officer
denied,
(R.l3),
Commonwealth
Edison’s motion of July
27,
1976, requesting that the hearings
in
this matter be held jointly and concurrently with those required
under Rule 203(i)
(5)
of
Chapter
3..
It
is
expected,
however,
that
the
existing
Record
with
regard
to
Lake
Sangchris
will
satisfy
the
showing requirements of that Rule and that Edison’s burden under
203(i) (5) may be satisfied at hearing by a motion to include the
existing record into the record of any such proceeding.
This Opinion constitutes the findings of fact and conclusions
of
law
of
the
Board
in
this
matter.
ORDER
The following new Rule 203(i) (11) (bb),
Lake Sangchris,
is
hereby
adopted,
and
the
existing
Regulations
of
Chapter
3:
Water
28-114

—9—
Pollution, are amended in conformity therewith:
(bb)
Lake Sangchris
The thermal discharge to Lake Sangchris shall meet
the following standards and conditions:
(1)
The effluent temperature shall not exceed
99°F.during more than seven
(7) percent
of the hours in the 12-month period ending
with any month and shall at no time exceed
111°F.
I,
Christan
L.
Moffett,
Clerk
of
the
Illinois
Pollution
Control
Board, hereby certify theAal?ove Opinion and Order were adopted on
the
j3~I1
_day ~
1977 by a vote of___________
CAc~7~
~
Christan
L. Moft)~,)Clerk
Illinois po1lutié~—~ontrolBoard
28-115

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