1. machine showers, The new North filter will remove suspended
      2. “The table below shows the design conditions and processefficiency predicted:
      3. DESIGN CRITERIA FLOW RATE
      4. Average Maximum
      5. Flow (gpm) 465 1000Suspended solids to side-hill screens
      6. (lb/l000 gal) 6 lb 126 lbPercent removal for screens 0—10 90
      7.  
      8. ORDER
      9. on or before October 5, 1975.
      10. IT IS SO ORDERED.

ILLINOIS POLLUTION CONTROL BOARD
June 26, 1975
THE FLINTKOTE COMPANY,
Petitioner,
v.
)
PCB 74—89
ENVIRONMENTAL PROTECTION AGENCY,
Respondent.
Mr. Edward Benecki, Gosnell, Benecki and Borden Ltd., appeared
on behalf of Petitioner.
Mr. Henry J. Handzel, Jr.,
appeared on behalf of the Respondent.
OPINION AND ORDER OF THE BOARD
(by Mr.
Goodman):
This matter comes before the Pollution Control Board
(Board)
upon the March
8,
1974 petition of the Flintkote
Company
(Flintkote) for a variance from section 12(a)
of the
Environmental Protection Act
(Act)
and Rules 203(a),
402,
403,
404(a) (ii)
and 404 (b) (ii), and certain portions of
408(a) of the Water Regulations for its felt mill.
On April
8,
1974, Flintkote filed a motion to amend its
variance petition which was granted.
On May 15,
1974,
Flintkote filed
a “petition for exception to variance period,”
and requested a formal hearing and granted a waiver of the
90-day decision rule on May 28,
1974.
Finally, Petitioner
filed its final amended petition for variance on September
5,
1974.
On April
9 and June 17,
1974,
the Environmental Protection
Agency
(Agency)
respectively filed its recommendation and
amended recommendation.
Each recommendation was replied to
by Flintkote.
A pre-hearing conference was held in Mt. Carmel,
Illinois,
on August 13,
1974,
at which time Flintkote proposed to
amend its petition.
On March
31,
1975,
a hearing was held at which time a
Stipulation and Agreement was submitted to the Board as
a
joint exhibit.
In the case of E.P.A.
v. the Flintkote Company, PCB 72-
152, Flintkote
was
granted a similar variance from corres-
ponding provisions of SWB—9 of the Sanitary Water Board
Regulations and the Water Regulations of the Board until
17 —377

—2—
May 10,
1974.
At that time it was anticipated that Flintkote’s
compliance plan would extend beyond May 10,
1974, and that
Flintkote would have to apply for another variance.
The two
stage compliance plan would eventually result in a zero—
discharge to the Wabash River and two unnamed
ditches tributary
to the Wabash River by Petitioner’s Mount Carmel,
Illinois,
felt plant.
In 1973, Flintkote was discharging between 500,000 and
700,000 gpd containing an
average of 3,600 pounds
of BOD5
effluent at between 500 and 1,000
ppm
and 4,000
pounds of
suspended
solids ranging between 200 and 1,800 ppm in various
grab samples.
In PCB 72-152, Flintkote was assessed a
penalty
of
$8,000 for
its violations which was duly paid by
the Petitioner.
Additionally, Flintkote posted a $150,000
corporate bond
to guarantee performance of its compliance
plan.
Phase
I of the compliance plan was completed and became
operational on or about June
10,
1974.
Pursuant to Phase
I,
a
partial loop was constructed to achieve a 75
reduction in
the daily flow to the Wabash River,
There has been
a signif-
icant reduction in Flintkot&s waste water discharge.
Flintkote now discharges 125,000 gallons per day with up to
500 pounds suspended solids and 3,000 pounds per day BOD5,
Phase II of the plan will be completed by October
5,
1975, and result in a completely closed system.
See “Submission
of
Phase II Engineering Program” PCB 74-89 which is hereby
incorporated by reference as though fully set forth herein.
“The program contemplates the installation of new side
hill screens, white water storage tank,
filter,
shower water
tank,
centrifugal separators,
seal tank and four pumps.
The
purpose of the new equipment is to collect the white water
now being discharged into the river,
to screen and filter
it, and then return it to the process for reuse.
Existing
sunip pumps will pump the white water effluent to the new
side hill screens which will flow by gravity to the existing
shower water chest, which will be converted to a surge
chest.
A new pump will be installed on the existing shower
water chest which will be converted to a surge chest.
Clarified white water will be returned to the process
and)
excess white water from the cylinder vat will be pumped ?d
the stock preparation white water chest by an existing pump.
The demand for white water at the hydrapulper will be met
from the screened white water tank by a new pump
(P—3)
as
determined by the level in the stock preparation white water
chest.
Existing wash-down pumps will be repiped to use
white water from new pump P-3 for wash-down.
“The existing No.
4 shower water pump will be relocated
to supply clarified white water
from the North filter to the
machine
showers,
The new North filter will remove suspended
17
378

—3--
solids that might adversely affect the operation of the
machine showers.
These showers will be replacedwith white
water type showers to assure minimum disruption of machine
operation.
“Centrifugal
separators
will
be installed on the suction
sides
of
three
vacuum
pumps
to
remove
the
water
pulled
from
the
sheet
and
felt
in
the
machine
press
section.
This
water
will be collected in a new seal tank and be pumped to the
effluent ditch,
Since this water has been screened by the
felts,
the suspeided solids content should meet the initial
requirements of the State.
“A Parshall flume will be installed in the existing
effluent ditch to measure the effluent flowing to the river.
“Under Phase
I, all cooling water will be picked up in
the white water system,
in the future, with a completely
closed system,
the cooling waters would be collected and
discharged directly to the river.
“The Phase II operation is described in the report as
fallows, reference being made to flow sheets PSI,
FS2 and
r a
“The
mill
presently
discharges
from
500,000
to
700,000
gallons
per
day
to
an
effluent
ditch
that
eventually
flows
to me
sanash Paver
Praor to Thscharge
the mall effluent
is collected and pumped to
a flat screen.
This screen
removes large solids and some fiber prior to discharging to
the effluent ditch,
This ditch has an effluent weir to
furnish manual flow measurements.
“The intent of the proposed system as shown on FS2 and
FS3 is to reduce the mill effluent by screening and settling
waste white water and reusing this water in the process of
producing roofing felt,
“The system recommended for Phase
i is shown on Flow~
sheets 22—l059A~FS2and FS3•~’RecommendedWater Refuse
Flowsheet.’
The system includes the following equipment to
reduce the effluent to the river to 125,000 gallons per day
and to reduce suspended solids
to 1,000 pounds per day.
“The mill effluent will be pumped by the existing sump
pumps to two s~de~hillgravity screens sized to handle 500
gpm each.
These screens will be located in the beater room.
They will discharge through the floor into the existing
shower water chest located in the basement below.
“Screened white water from the side hill screens will
be pumped to a
30
ft. diameter by 14
ft. high straight side,
clarifier tank.
The clarifier rake
mechanism
and
mixing
zone
are
not
included but can be installed at
a
later
date
if required.
17—379

—4—
“The screened white water storage tank will be used to
store the screened white water, thus providing surge capacity
for the high water demand for the hydrapulper operation.
It
will also provide sufficient retention time for gravity
separation of much of the suspended solids in the white
water.
Flocculating aids may be added to improve the settle-
ability of the suspended solids,
“The tank bottom will
be conical in shape to receive
the possible future rake mechanism.
The suction piping of
the new
white~water transfer pump
(P-3)
will be connected to
the center of the conical
bottom,
thus providing a means for
removing settled solids,
The settled solids will be returned
to the process
with white water,
It is an?icipated that
pumping the white water containing
the solids
from the cone
will prevent excessive build-up
of solids in
the storage
tank.
“Since the white water from the press section of the
paper machine will be collected and discharged to the effluent
ditch,
it
is anticipated that there will be no overflow from
the storage tank.
“The table below shows the design conditions and process
efficiency predicted:
DESIGN CRITERIA
FLOW RATE
Average
Maximum
Flow
(gpm)
465
1000
Suspended solids to side-hill screens
(lb/l000 gal)
6 lb
126 lb
Percent removal for screens
0—10
90
Suspended solids to screened water storage
tank
(lb/l000 gal)
6
lb
13 lb
Predicted suspended solids in press water to
effluent ditch
(lb/l000 gal)
.5
lb
3 lb
“New pump
(P-2) will supply white water from
the screened
white water storage tank
to
a new North-type gravity filter
that will be installed to
remove suspended solids
from the
paper machine shower water,
The rotating drum of the North
filter will be equipped with
a fine mesh stainless steel
filter screen to filter out
the
suspended
solids contained
in the shower water,
“Three white water type shower pipes will be installed
on the paper machine.
These shower pipes will be equipped
with nozzles especially designed for white water.
“A chemical feed package as shown on FS3, consisting of
a 300-gallon tank,
a metering pump, and an agitator would be
17
380

—5—
capable of adding coagulant aids or other clarification aids
if necessary.
It also can add chemical slimicides to control
the growths that will tend to develop in the white water
system.
“A chlorination system as shown on FS3 will be provided.
The effluent during Phase I
(125,000 gpd) will require
chlorination
to insure disinfection
of this discharge.
The
control of microorganisms will depend on the ability of the
chlorination system to feed sufficient quantities
of chlorine
and to maintain a chlorine residual throughout the white
water system.
For design purposes,
a feed rate of
6 parts
per million
(ppm)
is anticipated to maintain a residual of
2
to
3 ppm.
The chlorinator
is sized to be capable of pro-
viding shock doses of chlorine
(10 to
20 ppm)
to each chlor-
ination point.
This shock dosing would last for 10
to 15
minutes, probably not more frequently than once
a shift.
“Four chlorine meters have been provided.
Three of
these are proposed to eject chlorine into the new supply
pumps, P-i and P-3 as well as new effluent pump P-4.
One
additional chlorine meter has been included for ejection at
a slime problem location after start—up.
If extremely
tenacious slimes develop, slimicides would have to be used
to penetrate the slime envelope that protects the organisms.
However,
if chlorine is used properly and dosed frequently
enough, slimicides will not be required.”
(Environmental
Protection Agency v.
Flintkote Company, PCB 72-152, May 10,
l973).h1
The May 10, 1973 Order stated:
IT IS THE ORDER of the Pollution Control Board:
1.
Stipulation entered into between The Flintkote
Company and the Environmental Protection Agency, incor—
porating therein document captioned “Pollution
Abatement Study for The Flintkote Company” by
Rust Engineering Company
is approved and
incorporated therein.
2.
Variance is granted to the Flintkote Company until
May 10,
1974 from the provisions of SWB-9 and the
Water Regulations of the Illinois Pollution Control
Board,
as applicable,
to enable implementation of
Phase I and Phase II of the compliance program
herein provided.
Permits for construction
of the
abatement system shall be applied for within ten
days from the date of this order.
Phase
I shall
be completed within
13 months and 10 days from the
date of this Order and Phase II shall be completed
within 27 months from the date the permits are
issued for construction
of Phase
I.
Variance

—6—
herein granted may be extended upon application
submitted to the Board no less than 90 days before
the expiration of any variance herein allowed,
which shall be extended only upon a demonstration
that Flintkote is making satisfactory
progress
toward the completion of its
abatement program as
defined herein, requiring substantial compliance
with all time tables for completion of Phase I and
the submission of
a sound engineering program for
implementation of Phase II.
3.
Corporate bond in the amount of $150,000 in form
satisfactory to the Agency shall be posted within
35 days of the date of this Ordbr,
to guarantee
compliance
with
all
of
the
provisions
of
this
Order
and
the
Stipulation
entered
into
between
the
parties.
Upon
completion
of
all
conditions
of
the
bond,
the Agency will execute and deliver
a bond
release to Flintkote,
4,
Flintkote,
during construction
of Phase
I,
shall
submit to the Agency and the Board, periodic
progress reports at 30-day intervals which shall
indicate the status of all design and construction
progress with respect to Phases
I and II.
5,
Penalty in the amount of $8,000 is assesed against
the Flintkote Company for violation of Section
12(a)
of the Environmental Protection Act and SWB-
9,
as alleged in the complaint.
Penalty payment,
by certified check or money order payable to the
State of illinois,
shall be made within
35 days
and sent to:
Fiscal Services Divsion,
illinois
Environmental Protection Agency,
2200 Churchill
Drive, Springfield,
Illinois
62706,
The Board finds that Flintkote has made satisfactory
progress toward completion
of its compliance plan and has
substantially complied with the Board~sOrder of May 10,
1973,
in PCB 72~l52. The assessed penalty was paid,
the
bond posted, permit applications for Phase
I were submitted
on
ti.me, and the required progress reports were timely
submitted.
Phase
I
was
completed
on
schedule
and
Phase
II
commenced
immediately
thereafter
and
has
continued
to
date.
The
expected
reduction
of
suspended
solids
did
not
occur
at
the end of Phase
I and Petitioner admits that on occassion
the 2800 pound per day limitation on the discharge of POD5 has
been exceeded.
The nature of Flintkot&s discharge varies
from day to day,
as indicated by the chart on page
6 of the
Stipulation, due to Petitioners~ raw material feed stock of
wood pulp and paper.
Flintkote has expended considerable sums of money on a
program which is acceptable to both the Agency and the
17
382

—7—
Board.
To deny this program, when it is so near to completion,
would work a severe hardship on Petitioner.
Completion of the compliance plan
will
result in total
recycle which is to be encouraged as the ultimate treatment.
There having been no showing in the record of adverse citizen
reaction,
together with the continuing reduction in discharges,
the Board finds that Petitioner has
met its burden in proving
lack of environmental harm.
This opinion constitutes the findings of
fact and law
of the Board.
ORDER
1.
Flintkote is hereby granted a variance, until
October
5,
1975,
for
its
discharge of process
waters from Section 12(a)
of the Act, and Rules
203(a),
402,
403, and 404(a)
(ii) and 404(b) (ii)
of
the Water Regulations as they relate to the discharge
of BOD5
and
suspended solids;
and
2.
Flintkote is hereby granted a variance from Rule
408(a)
of the Water Regulations until October
5,
1975,
limited to allowing Flintkote to continue
the discharge of its present quality effluent.
Said variance is granted upon the following conditions:
(a)
Flintkote
shall
not substantially change the
character
and
nature of its raw material
feedstock without giving the Agency and the
Board prior 30-day written notice; and
(b)
Flintkote~seffluent, with the exception of
cyanide and mercury, shall not,
at any time,
exceed
5 times,
on either a grab or composite
sample basis, the numerical standard provided
in Rule 408(a); and
(c)
Flintkote’s discharge of cyanide shall not
exceed 1.0 mg/l at any time;
and
(d)
Flintkot&s discharge of 408(a)
contaminants
shall not cause
a violation of Rules 203(f)
and 402 of the Water Regulations in the
Wabash River; and
(e)
This variance shall not extend to the 1imita~
tions set forth in Rule 408(a)
regarding pH
and mercury, which shall remain in full force
and effect;
and
17 —383

—8—
3.
Flintkote’s waste water discharge during this
variance shall be limited to:
(a)
125,000 gallons per day;
(b)
250 pounds per day of suspended solids as a
monthly average, not to exceed 500 pounds on
any day; and
(c)
2,800 pounds per day of BOD5 and
4.
Flintkote shall take grab samples every six hours
for 24 hour periods each week and mathematically
compute 24 hour composites from same for suspended
solids,
BOD5 and free chlorine.
The results of
said samples shall be included in monthly progress
reports which Flintkote shall continue to submit
to the Agency and the Board, detailing progress on
Phase
II; and
5.
The bond posted
in
PCB 72-152 shall remain in full
force and effect until completion of conditions
of
the bond at which time the Agency shall execute
and deliver
a bond release to Flintkote;
and
6.
Flintkote, during the term of this variance, shall
not use in its compliance plan or in its manu-
facturing processes any of the contaminants listed
in Rule 408 of the Water Regulations except as may
be found to occur in Flintkote’s normal raw material
feed stock of wood pulp and paper as reported in
PCB 71-68 and PCB 72-152;
and
7.
Flintkote shall complete Phase II and cease all
discharges, other than non—contact cooling water,
on or before October
5,
1975.
IT
IS SO ORDERED.
I, Christan L. Moffett,
Clerk of the Illinois Pollution
Control Board, hereby ce,~tifythe above Opinion and Order
were
~1opted
on the
“day of~,
1975 by a vote
Christan L. Moffett,
~J4rk
Illinois Pollution C&~ol Board
17
384

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