ILLINOIS POLLUTION CONTROL BOARD
June 21, 1973
THE CELOTEX
CORPORATION
)
#73-123
v.
ENVIRONMENTAL PROTECTION AGENCY
)
JOHN L. PARKER AND E. GERALD REYNOLDS,
APPEARED
ON
BEHALF
OF
THE CELOTEX CORPORATION
FREDERICK ENTIN, ASSISTANT ATTORNEY GENERAL,
APPEARED
ON BEHALF
OF ENVIRONMENTAL PROTECTION AGENCY
OPINION
AND
ORDER OF THE BOARD (BY
SAMUEL
P.
LAWTON, JR.):
The Celotex Corporation has filed an amended petition for
variance seeking relief from the provisions of Rule 3-3.111 of the
Rules and Regulations Governing the Control of Air Pollution and
from Chapter 2, Rule 203(a) of the Air Pollution Control Regulations
to enable particulate emissions in excess of the above Rules from
its asphalt saturator and filler dryer and heater, both located in
its Wilmington plant, until March 21, 1974.
Hearing was held on the petition on May 23, 19!3. The Agency
has filed a recommendation based on the original petition in which it
recommends allowance of the variance, but on a shorter time frame
than proposed by petitioner. On the basis of the amended variance
petition and the views expressed by Agency personnel at the hearing,
it does not appear that the Agency has
any
serious differences with
the petitioner relative to the variances proposed.
We grant the variances as requested in the petition until
March 21, 1974.
The Celotex Corporation is a Division of the Jim Walter Corpora-
tion, a national producer of building.materials. The Celotex Corpora-
tion manufactures roofing and other building material composed chiefly
of asphalt-treated felt products. Wilmington has a population of
4,335 and is located approximately 16 miles south of Joliet,
in Will
County. The principal component parts of the Celotex plant (Petition-
er’s Ex. 4-6) consists of a felt mill and a roofing mill. In
the
felt mill, wood and paper are pulped and formed into sheet felt
which becomes the base for the roofing products (R. 31). This, in
turn, is fed to the roofing mill where it is saturated
with hot li-
quid asphalt contained in a dip tank known as the asphalt saturator. ThE
liquid asphalt flow rate to the saturator is approximately 16,500 pounds
per hour (R. 32). The saturated felt is then either cooled or rolled
for use as roofing felt or building paper or is coated with
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stabilized
asphalt and surfaced
with granules and
sand to
make
composition roofing.
In the coating and. surfacing operation, the
sand used as a filler is simultaneously dried and heated in a
rotary kiln, Dry sand exits the kiln at
25,000
pounds per hour.
The dry sand is then sized in screening equipment and blended with
asphalt, following which the mixture is applied to
the asphalt
saturated deit.
The emission sources, which
are the
subject of this
proceeding, are located within and adjacent to
the
roofing mill
(R.
28—29)
,
(Petitioner~s Ex, 4)
These emission sources are the
three exhaust stacks from the asphalt saturator and
the
filler dryer
and heater exhaust stack and related equipment.
Air contaminants
discharged from the asphalt saturator constitute particulate
matter
esti.mated at 45 pounds per hour, both solid and liquid, and small
quantities
of 502 and hydrocarhons,for which latter emissions no
variance is sought.
The 45 pounds per hour estimated emission rate for oarticuiatss
is based on similar asphalt saturating processes (14. 121—123).
The
air contaminants discharged from the filler dryer and heater constitute
solid particulate matter and water vapor~~ The estimated particulate
emission rate is 25 pounds per hour based primarily on screen analyses
To control emissions from the aspha:Lt saturator
Detit:ioner
proposes the installation
of 40 ,000 CFM high energy air fi:Ltration
system
known
as a HEAF unit.
Ex:taust gases from the three saturator
stacks will
be
drawn through a perforated drum covered with a fibur~
glass mat. and then will pass through a York dc—mister pad, which is
a packed bed acting as a detrainer
~or liquid droplets.
it :i a aetimated
that this
unit
will remove between
90
and
95
of particulate emissions
from
the saturator (R.
l26~l34),
The unit will
cost
approximately
$61,800 (R, 129).
Particulate
emissions from the filler dryer and
heater and associated equipment will be controlled by the installatic,n
of an aerody;ae series ~‘SV” dust collector,
through which emissions
from the filler dryer and heater stack will he passed, and, in addition,
a baghouse of approximately 4,000 CFM to handle emissions from the trans-
fer points, bucket elevator and Rotex screen.
Anticipated efficiency of
the aerodyne would. he
95.
The aerodyne unit, with fans, will cost
in excess
of $4,000 and the
baghouse
approximately $3,400.
Baghouse
removal efficiency is estimated at
99.
P:Lans have been made with Commonwealth Edison~ ~
for
the necessary electrical
power which will
entail the installation of
a new
transformer. The proposed schedule
for
compliance is as
follows:
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—
346
Item
Completion Date
Equipment order
June 6, 1973
Equipment delivery including
engineering design and construction
permit
~pp1i~fi~n~
26 weeks December 6, 1973
Equipment installation
6 weeks January 17, 1974
I week
January 24, 1974
Debugging and final stack test
4 weeks March 21, 1974
We believe an adequate dhowir~gof hardship has been made to
justify the allowance of the variances proposed. A denial of variance
does not necessitate shut-down of the plant. The Company presumably
has the option to remain in violation and take its chances on the
possible imposition of a penalty. ~This, however, does not present
an alternative which the Board would favor. The record does support
petitioner’s contentions that suspension of operation or termination
of the facilities involved would have a serious econortic impact on
the Company, its employees and its customers, causing disruption of
the line of production relating to operations beyond thos.e immediately
involved in the resent proceeding. Furthermore, the schedule for com-
pliance is a relatively short one, considering the ragnitude of the
instailatic.n involved and the degree of compliance that w.ill be achieved
once the program is completed.
The record likewise supports the economic dependency of the Wil-
mington community on the continuing operation of the petitioner’s
facility. We believe the hardship on the Company, its employees and
customers and the comrnun.ity, if the variance is denied, is far greater
than any continuing burden on the surrounding area in allowing the
present particulate ~emissions to continue until the abatement program
is completed in March of 1974. While there was some evidence that
petitioner’s emissions produced a nuisance impact on portions of the
community, the evidence was not extensive nor particularly persuasive,
and. em do not feel of a sufficient magnitude to justify a denial of the
vamiances sought. The Agency has indicated that it does not oppose
the variance allowance.
This opinion constitutes the findings of fact and conclusions
of law of the Board.
I. Variances from Rule 3-3,111 of the Rules and Regulations
Governing the Control of Air Pollution and Rule 203(a) of
tie Air Pollution Control Regulations, are granted to The
Celotex Corporation to enable the emission of marticulates
in e.xces.s of the foregoing Rules until March 21, 1974,
pending installation
of abatement equipment as set
forth in the amended petition of petitioner and speci-
fied in the
foregoing
Opinion, with respect to its
asphalt saturator and filler dryer and heater facilities.
2. Petitioner shall file on or before July 6, 1973, in
form satisfactory
to the Agency, a performance bond in
the amount of $70,000, guaranteeing installation of
all abatement equipment as specified in its
petition
and the record herein, by March 21, 1974. The bond
shall be mailed to: Fiscal Services Division, Illinois
Environmental Protection Agency, 2200 Churchill Drive,
Springfield, Illinois 62706.
I, Christan Moffett, Clerk of the Pollution Control Boa~d, certify
that the above Opinion and Order was adopted on the
,2i~
day of
June,
1973, by a vote of
4
to
c~
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