1. City of Carbondale
      2. City of Marion

ILLINOIS
POLLUTION
CONTROL
BOARD
August
8,
1972
City of
LaHarpe
)
v.
)
PCB
72-168
Environmental
Protection
Agency
City of Carbondale
V.
PCB 72-203
Environmental
Protection
Agency
~
City
of
Marion
)
v.
)
PCB
72-225
Environmental
Protection
Agency
Opinion
and Order
of the
Board
(by Mr.
Dumelle)
The
three
applications
embrace
a
common
topic
and
ask
a variance
from
the
water
quality
standards
to
permit
the use
of
copper
sulfate
in
their
drinking
water
reservoirs
to prevent
algae
nuisances.
The
Agency has
recommended
a grant
subject
to
certain
conditions
and we
concur
for
reasons
given
later.
City
of
LaHarpe
The
City of
LaHarpe
in
Hancock
County
has
a population
of
1,240.
The
petition
for variance
was
received
by
the
Board~
on
April
21,
l9~?2and a hearing
held
in LaHarpe
on
July
14,
1972.
The
reservoir
is
10 acres
in
area,
has
an
average
depth
of
15
feet
and
a
capacity
of
45
million
gallons.
The
Agency
report
by
Ronald
W.
Jahns
indicates
that
copper
sulfate
treatment
at
this
reservoir
has
been practiced
since
at least
1949.
The
Agency
report,
which
was
stipulated
to
by
the
City
of LaHarpe,
cites
excessive
algae
growth
two years
ago
with
clogging
of
the
filter
bed,
improper
settling
in
the
clarifier
and numerous
complaints
of taste
and odor
from
users
of the
City’s water.
Dosages
of
300
to
600 pounds
of
copper
sulfate
applied
5-~-
115

—2-
In the usual way of
towing
the
crystals
in
a sack behind
a motor boat have
stopped
the problem.
It is further
stipulated that no
fish
kills have
been
caused by the copper
sulfate treatment
and
that the reservoir
is
well stocked with fish.
The
concentra-
tions
of copper
resulting from the treatment
are
given as 0.3
mg/l for
300 lbs.
of chemical
used
and
0.6
mg/l for
600 lbs.
City of Carbondale
The
City of Carbondale,
population 22, 816,
is
in
Jackson County.
The
variance petition
was received
May
ii,
1972.
No
hearing
has
been
held.
The
reservoir
is
144 acres
In area with an
original
average
depth of 9.6
feet.
Original
capacity was
350
mIllion gallons
which the Agency states
Is
now
330
million
gallons.
The
City of Carbondale,
in Its petition,
states
that excessive
algae
growth
produce taste and
odor
problems
In the water
supply.
Use of copper
sulfate
In the reservoir,
which is used as water
supply
Intermittently when
Crab Orchard Lake is low,
has been 4,900 lbs.
in 1969,
4,
700 lbs.
in 1970
and
5,100 lbs.
in
1971.
The
statement is
made that no
fish
kills
have
occurred in these three years.
The
Agency
recommend
applications of 1.700 lbs.
per treatment
and
states that the
copper levels
will
not exceed
0.165 mg/i.
City of Marion
The
City of Marion,
population ii,
724,
is
In Williamson
County.
The
variance petition
was
received by the Board
on June 2,
1972.
A public hearing
was held on July
27,
1972
in
Marion.
The variance Is requested for the large
reservoir
about four miles
south of Marion which is
stated to
have
a
capacity
of 482
million gallons.
No
area or
average
depth is
given.
Mr.
Russell
Fisher,
thief
operator of the Marion water plant testified
that
copper
sulfate had been
applied for the past
six
years
to his knowledge
to this reservoir.
Commissioner
Paul Joyner in
his
petition for the
variance
discusses
an algae bloom
condition
In April of this year which
caused the
drinking water to be
“unfit to drink” because of taste
and
odor
problems.
He
also
stated that some $2, 500
in
activated carbon had to be
used to treat the water
that month.
In his testimony
on this point he
stated
that copper
sulfate would have been lower
in cost
had
Carbondale been
able to
use It.
No ifi
effects
on aquatic life because of copper
sulfate treatment are
known
to Mr.
Joyner
or
Mr.
Fisher.
The
Agency recommends
up to 4,000 lbs.
of copper
sulfate per treatment
every
six
weeks
and
states that concentrations will
not
exceed 0.3
mg/i as copper.
5—116

—3-
Discussion
The
Agency
recommendations
in these
three
cases
are
virtually
identical.
A grant
of the variance
is
recommended
and dosage
limits
are
specified.
We
concur
in
the grant
but
do
so
reluctantly
because
of
what
appears
to be
an
in-
complete
discussion
by
the
Agency
or
by
the various
cities
of
alternative
methods
of treatment
or
of possible
harm.
However,
the
algae
bloom
season’
is
now
almost
over
and no
discernible
harm
from
using
copper
sulfate
appears
in
these
records.
Ample time
remains
before
next
summer
for
both
the
Agency
and all
Illinois
water
supply
users
to prepare
fuller
discussions
on
both alterna-
tive
methods
and possible
harm
from
the present
practice.
The
Agency
recommendations
state
flatly
that the
“only
alternative
to use
of
copper
sulfate
for
algae
treatment
is
chlorine.
‘~
In
the
Marion
hearing,
Mr.
Dennis
Stover,
representing
the
Agency,
affirmed
this
opinion,
Yet a highly
respected
sanitary
engineering
text,
Water
Purification
and Wastewater
Treat-
ment
Vol.
2
by
Fair,
Geyer
and Okun
(1968)
lists
three
other
methods
for
algae
control.
These
three
methods
are
(1)
spreading
of activated
carbon
on
the
reservoir
surface
to
shut
out
sunlight
(2)
dosing
with lime
in
amounts
sufficient
to produce
caustic
alkalinity
to
deprive
the
algae
of
needed
carbon
dioxide
and
(3) use
of viruses
selective
to
algae,
(33-41
to
33-47).
Two
other
references
provide
information
on
possible
additional
alterna-
tives,
A
paper
by
Symons,
Weihel
and Robeck
in
Water
Quality
Behavior
in
Reservoirs
by
the
U. S.
Department
of
Health,
Education
and
Welfare
(1969)
mertions the possibility
that
algal
toxins
may have
inhibited
algae
blooms
on
the
Ohio
River
(p.
19).
An
article
by
howard
in Reclamation
Era
(February
1972)
(p.
6-7)
describes
how air
injection
into
Casitas
Lake
near
Ventura,
California
brought
coaler
water
to the
surface
and thus
inhibited
algae
growth.
The
annual
costs
for
copper
sulphate
and citric
acid
treatment
of the
reservoir
were
$20, 000 and
dropped
to
$12, 000
for
air
injection
(exclusive
of
capital
charges).
It is
possible
that
none
of
the
alternatives
listed
above
are
suitable
for
application
in the
instant
cases.
But nothing
in the
records
of these
cases
showed
that
they were
considered
by
any of
the
parties.
The
record
i.s
not
clear
on
whether
these
reservoirs
are
“flow-through’
impoundments.
If these
reservoirs
feed
streams
below them,
then
the
high
copper
concentrations
proposed
(0. 6
mg/i)
may
destroy
some
forms
of
aquatic
life.
McKee
and
Wolfe
in their
authoritative
work,
Water
Quality
Criteria,
report
“.
.
.
concentrations
(of
copper)
of
0.
015 to
3.
0 mg/i
have
been
reported
as
toxic,
particularly
in
soft
water,
to
many
kinds o~
fish,
crustacea,
mollusks,
insects,
phytoplankton,
and
zod~lankton” (p.
171).
Clearly
a biological
survey
is
indicated
in the
streams
below
these
reservoirs,
if any
such
streams
exist,
to
determine
which
may have
occurred
in
the past
from
the use
of
copper
sulfate.
5—
1
i
7

-4-
Lastly
no
data
are presented
by
any of
the
parties
as
to the possibility
of limiting
these
algae
blooms
by
limiting
a critical
nutrient,
such
as
phosphorus.
In
adopting
the
revised
Water
Quality
Standards
(R7l-l4)
on
March
7,
1972
we
set
a phosphorus
limit
for
reservoirs
and lakes
at
0.
05
:mg/l
to prevent
just
such
obnoxious
blooms.
The
Agency
should
investigate
phosphorus
concentrations
in
the
instant
reservoir
waters
and
take
action
to
reduce
controllable
upstream
phos-
phorus
inputs
under
its
powers
to
abate
water
quality
standards
violations
if
such
are
found to
exist.
The
Federal
Environmental
Protection
Agency
in
its
letter
of July
10,
1972
(entered
into
the
City
of
Marion
record)
makes
the
point
that
nutrient
removal
upstream
may
well be
a superior
alternate
method
of eliminating
algae
blooms.
We
ought
not
to pollute
and
then
be forced
to poison
to
eliminate
the
effects
of
the
pollution.
And the
fact
that
the
Agency
requests
in its
recommen-
dations
data
on
copper
levels
in
each
reservoir
before
and after
copper
sulfate
treatment
leads
us to believe
that
data
of
this
type
are
lacking.
Perhaps
what
is
needed
is
a research
study
by
the
Institute
for
Environmental
Quality
which the
Agency
might
well
request.
In recent
months
we
have
found that
old
practices
are
not
necessarily
environmentally
sound
practices.
Metallic
mercury
discharged
in
effluents
is
converted
in
sediments
by bacteria
to
the
highly
toxic
methyl.
mercury
which
is
then
concentrated
into
fish
flesh.
Copper
sulfate
usage
may
have
some
environ-
metal
consequences
which
are
undesirable
and
about
which
we know
little
on
the
basis
of these
records.
Fair,
Geyer
and Okun
sum
up
the
case
against
chemical
treatment
succinctly:
There
is
a growing
awareness
of
the
dangers
of
indiscriminate
and
largescale
use
of chemicals
for
the
destruction
of
specific
popu-
lations
of
living
things.
It
is
generally
true
that
dislocations
of
biological
equilibria
should
be
avoided
where
possible.
Useful
or
otherwise
wanted
members
of
normal
plant
and
animal
communities
should
not
be
killed.
Relief
from
nuisance
growths
or
otherwise
runaway
proliferation
of
unwanted
organisms
should
not
be
obtained
at that
price.
Thinking
has
turned
more
and
more
to
the
promotion
of
biological
self-regulating
mechanisms
that
will
right
the
imbalance
and
not
create
a
new
imbalance
---
in ab-
normal
ecological
systems.
The
introduction
of
specific
parasites
that
keep
unwanted
components
of
the
plant
or
animal
community
in
check
is
one
example.
Breaking
the
food
chain
or
otherwise
modifying
the
existing
environment
to
the
disadvantage
of the
organisms
to be
controlled
is
another.
Biological
control,
in
5—118

—5--
comparison
with
chemical
destruction,
is
more
likely
to
be
a
reversible
or
an
incomplete
reaction.
Equilibrium
is
restablished
of
its
own
accord.
Damage
does
not
become
irrevocable.
An
important
example
is
interference
with
the
biological
destruction
of
bottom
deposits
when
lakes
and
imp~
)undages
ar-c
treated
with
copper
salts.
(p.
33—37)
rJ~j~
opinion
constitutes
the
Board’s
findings
of
fact
and
conclusions
of
law.
0
RDER
Variances
are
granted
to the
cities
of
Marion,
Carbondale
and
LaHarpe
to
exceed
the
water
quality
standard
of
0.
02
mg/I
in
their
water
supply
reservoirs
by
treating
with
copper
sulfate
to
prevent
algae
blooms
subject
to the
following
conditions:
1)
Dosage
shall
be
limited
as
follows:
a)
For
Marion,
to one
treatment
every
six
weeks
until
November
30,
1
972
not
to
exceed
4,
000
lbs.
of
copper
s
U fate
per
1
realm ent.
I))
F~o
r
(arhondal
e,
to one
treatment
during
August
1
972
not
to
exceed
1,
700
lbs.
of
copper’
sulfate.
r)
Vor
Lailarpe,
to
one
treatment
per
month
for
the
months
ot
August
through
November,
1072
not
to
exceed
600
lbs.
of
copper
sulfate
per
treatment.
2)
Copper
concentrations
at.
the
raw
water
intake
to
the
water
treatment
plant
shall
never
exceed
1.
0
mg/i.
3)
(opper
concentration
in
the
reservoir
shall
be
measured
immediately
before
and
after
each
copper
sulfate
treatment
and
the
results
subriiitted
to
the
Agency
on
a
monthly
basis.
I,
Chri stan
L.
Mnffett,
Clerk
of
the
Illinois
Pollution
Control
Board,
hereby
certify
the
above
Opinion
and
Order
were
adopted
by
the Board
on
-,
‘~
day of
August,
1972
by
a
vote
of
.3
~
6:~L~
L
~1//)
~
~
Christan
L.
Moffett,
~It~k
Illinois
Pollution
Control
Board
5
119

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