ILLINOIS POLLUTION CONTROL BOARD
September
6,
1979
IN THE MATTER OF:
PARTICULATE EMISSIONS FROM STEEL
)
R78—10
MILLS
(Proposed Revision of Rule
203(d) of Chapter 2)
ORDER OF THE BOARD
(by Mr. Goodman):
The Board hereby adopts the following amendments to the
Air Pollution Control Regulations.
In addition the Board
hereby deletes Rules 203(d)(2) and 203(d) (6) and renumbers
Rule 203(d)
as follows:
Rule 203(d) (1)
shall
remain; Rule
203(d) (3) shall be Rule 203(d)(2); Rule 203(d)(4)
shall
be
Rule 203(d) (3);
Rule 203(d) (5) shall be Rule 203(d) (4); Rule
203(d)(6)
shall
be deleted, and the following Rule shall be
Rule 203(d) (5);
Rule 203(d) (7)
shall be Rule 203(d) (6); Rule
203(d) (8) shall be Rule 203(d)(7);
and Rule 203(d)(9)
shall
be Rule 203(d) (8);
and Rule 203(d) (10) shall be Rule 203(d) (9).
203(d)
Process Emissions
(5)
Steel Manufacturing Processes.
Except where noted,
Rules
203(a),
203(b) and 203(c)
shall not apply to the
following steel manufacturing processes.
The following
rules shall apply:
(A)
Beehive Coke Ovens.
No person shall cause or
allow the use of beehive ovens
in any coke manu-
facturing process.
(B)
By-Product Coke Plants.
(1)
Rule 202 shall not apply to by—product coke
plants.
(ii)
Charging:
No person shall cause or allow the
emission of visible particulate matter from
any coke oven charging operation when coal
is
being charged,
except for a total of no more
than 170 seconds over five
(5) consecutive oven
35—34 7
2
charges,
or in the case of existing five meter
coke batteries having three charging ports,
for
a total of no more than 200 seconds over five
(5)
consecutive oven charges.
(iii)
Pushing:
All coke facilities shall be equipped
with pushing systems with particulate control
equipment which shall he designed to capture
at least
90
of
all particulate emissions
from pushing operations.
The particulate
control equipment shall
be operated and
maintained
in a manner to achieve the design
efficiency.
If
a stationary hood system is
used,
the particulate emissions from the out-
let of said particulate control equipment
shall not exceed 0.03 grains per dry standard
cubic foot
0.07
grams per cubic meter at dry,
standard conditions
(dscmfl.
If a closely
hooded mobile system is used in connection
with the operation of an existing coke oven
battery with the emissions exhausted directly
to the particulate control equipment,
the par-
ticulate emissions from the outlet of said
particulate control equipment shall not exceed
0.06 gr/dscf
(0.14 g/dscm).
(iv)
Coke Oven Doors:
(aa) No person shall cause or allow visible
emissions from more than 10
of all coke
oven doors at any time.
Compliance
shall be determined by a one pass obser-
vation of all coke oven doors
on any one
battery.
(bb) No person shall cause or allow the
operation of a coke oven unless there
is
on the plant premises at all times
an
adequate inventory of spare coke oven
doors and seals and unless there
is a
readily available coke oven door repair
facility.
(v)
Coke Oven Lids:
No person shall cause or
allow visible emission from more than
5
of
all coke oven lids at any time.
Compliance
shall be determined by a one pass observation
of all coke oven lids.
(vi)
Coke Oven Offtake Piping:
No person shall
cause or allow visible emissions from more
than 10
of all coke oven offtake piping at
any time.
Compliance shall he determined by
35—348
3
a one pass observation of all coke oven off—
take piping.
(vii)
Coke Oven Combustion Stack:
No person shall
cause or allow
the
emission of particulate
matter from a coke oven combustion stack to
exceed 0.05 gr/dscf
(0.11 g/dscm).
(viii)
Quenching:
All coke oven quench towers
shall
be equipped with grit arrestors or equipment
of comparable effectiveness.
The make—up
water shall not directly include coke by-pro-
duct plant effluent.
Total dissolved solids
concentrations in the make-up water shall not
exceed 1500 rng/l.
Provided however that the
limitations on the quality of quench make—up
water shall not apply where the operator
employs an equivalent method of control as
determined by the Agency.
(ix)
Work Rules:
No person shall cause or allow
the operation of
a by-product coke plant
except in accordance with operating and
maintenance work rules approved by the Agency.
(C)
Sinter Processes.
Emissions of particulate matter
from sinter processes shall be controlled as follows:
(i)
Breaker Box:
No person shall cause or allow
the emission of particulate matter into the
atmosphere from the breaker stack of any sinter
process
to exceed the allowable emission rate
specified by Rule 203(a).
(ii)
Main Windbox:
No person shall cause or allow
the emission of particulate matter into the
atmosphere from the main windbox of any exis-
ting sinter process
to exceed 1.2 times the
allowable emission rate specified by Rule 203(a).
(iii)
Balling
Mill Drum,
Mixing Drum,
Pug Mill and
Cooler:
No person shall
cause or allow the
emission of visible particulate matter into the
atmosphere from any Balling Mill Drum,
Mixing
Drum,
Pug Mill or Coolet
to exceed 30
opacity.
(iv)
Hot and Cold Screens:
(aa) Particulate emissions from all hot and
cold screens shall
be controlled by air
pollution control equipment or an equiva-
lent dust suppression system.
Emissions
from said air pollution control equipment
shall not exceed 0.03 gr/dscf
(0.07 g/dscm).
35—34
9
4
(bb) Provided, however, that
if the owner or
operator can establish that the particu-
late emissions from the hot screens and
cold screens do not exceed the aggregate
of the allowable emissions as specified
by Rule 203(a)
for new emission sources
or Rule 203(b) for existing emission
sources, whichever is applicable,
then
Rule 203(d)(5)(C)(iv)(aa) shall not
apply.
(D)
Blast Furnace Cast Houses.
(i)
Particulate emissions from the blast furnace
casting operation into the ambient air shall
not exceed the allowable emission rate speci-
fied in Rule 203(a), calculated and measured
as follows:
(aa) For purposes of this rule,
the casting
operation for each furnace shall be
considered as
a separate operation and
the process weight
(“P”)
in the calcula-
tion shall be the total weight of the
iron and slag entering the cast house
during the casting operation.
(bb) Measurement method.
(bb—1)
Application
This
Lest procedure shall he used
to determine compliance with Rule
203(d)(5)(D)(1) Blast Furnace Cast
Houses.
f
the United States Envir-
onmental Protection Agency adopts a
test procedure to sample particulate
emissions from blast furnace cast
houses, that test procedure may be
substituted for the one specified
in this paragraph upon publication
in the Federal Register.
(bb—2)
Measurement Equipment for this
Test Procedure
The measurement equipment used for
this test procedure shall consist of
the following:
(aaa)
High Volume Air Samplers with
0.3 micron glass
fiber filters
shall be used for the determina—
35—350
tion of cast house particulate
emission concentrations.
(bbb)
Velocity measurements shall
be determined by the use of
a
suitable instrument designed
for the accurate determination
of velocities within the range
encountered during the sampling
duration.
(ccc)
Temperature measurements shall
be determined by the use of
a
suitable
instrument designed for
the accurate determination of
temperature within the range
encountered during the sampling
duration.
(bb-3)
Test Procedure
(aaa)
Sampling Time Duration:
Sampling and opacity obser-
vations will initiate with the
opening
of the tap hole and
terminate with the plugging of
the tap hole.
(bbb)
Opacity Observations:
Opacity observations
of the
cast house roof monitor par-
ticulate emissions into the
atmosphere shall be performed
during the test runs by use of
the USEPA Method
9 Procedure
as published in the Federal
Register, Thursday, August 18,
1977.
(ccc)
Number of Test Runs:
The average
of six complete
sampling runs during normal
operating conditions will be
the minimum required to deter-
mine compliance with Rule
203(d) (5) (D) (i).
(ddd)
Sampled Emission:
During the test period, par—
35—351
6
ticulate emissions from the
casting operation shall be
directed into the cast house
to the extent feasible and
shall not create an unsafe or
hazardous condition.
Those
emissions in and/or directed
to the cast house shall
be
allowed to escape only at samp-
ling area locations.
Compliance
with this requirement shall be
determined by an agency—certified
observer,
and any significant
visible emission from the cast
house anyplace other than a samp-
ling location will invalidate
the test.
(eec)
Sampler Locations:
Samplers shall he located as
close as practicable to the
discharge point of the cast
house emissions to the atmos-
phere and shall be oriented in
the direction of the air flow.
The sampler grid pattern shall
be divided
up such that the
cross sectional area per
sampler shall not exceed one
hundred
(100) square feet
(9.29
square meters).
If necessary
to insure representative samples,
the Agency may specify an area
of
less than one hundred
(100)
square feet (9.29 square meters).
Each sampler shall be located at
the approximate center of each
sampling area.
The concentra-
tion of particulate matter as
determined by each sampler shall
be considered as the concentra-
tion for each respective area.
(fff)
Velocity Measurement Loca-
tions:
Velocity measurements shall be
made as close as possible to
each sampling point location
without interfering with the
n,easurement.
The average
velocity measured at each
35—352
7
sampling point for the entire
sample run shall
be used as
the average velocity for each
entire sampler area respectively.
(ggg)
Temperature Measurement
Locations:
The same as velocity measurement
locations.
(hhh)
Emission Exhaust Pressure
Measurements:
This pressure shall be con-
sidered the barometric pressure
as measured at the cast house
floor.
(iii)
Recording of Operating
Parameters:
The following information
shall be recorded for those
casts tested:
(ui—i)
Material charge weights
to the blast furnace for the
operating turn during which
cast house tests are performed;
(iii—2)
Cast weights,
total
weight of iron plus
slag enter-
ing the cast house during each
casting operation sampled;
(iii—3)
All information con-
tained
in blast furnace cas-
ting logs or other similar
records, size of the tap hole
drill bit used
for each cast
and the length of the tap hole
for each previous cast.
(bb—4)
Calculations
(aaa)
Mass Emission Rate
(lbs./hr.)
The mass emission rate
(lbs./hr.)
for each test run shall
consist
of the sum of the mass emissions
as determined per each sample
area.
Should the sample time
35—35 3
8
duration be greater than one
hour, the ratio calculated for
one hour divided by the sample
time duration
(hours)
shall be
multiplied by the sum of the
mass emissions to obtain the
pounds per hour rate.
(ii)
Provided, however, that Rule
203 (d)(5)(D)(i)
shall
not apply at the option of the operator
if
the operator has installed and is operating
and maintaining collection equipment designed
to collect
a minimum of fifty percent
(50)
of particulate emissions from the tap hole,
the trough to the skimmers,
and the iron
spouts.
Such emissions shall be evacuated to
pollution control equipment.
Emissions from
said pollution control equipment shall not
exceed
0.02 gr/dscf
(0.046 g/dscrn).
(E)
Basic Oxygen Furnaces.
Emissions of particulate
matter from Basic Oxygen Processes shall be con-
trolled as follows:
(i)
Charging, Refining and Tapping.
Particulate
emissions from all basic oxygen furnaces shall
be collected and ducted
Lo pollution control
equipment.
Emissions from basic oxygen fur-
nace operations during
the entire cycle (opera-
tions from the beginning of the charging pro-
cess Lhrough the end of the Lapping process)
shall not exceed the allowable emission rate
specified by Rule 203(a) for new emission
sources or Rule 203(b)
for existing emission
sources, whichever is applicable.
For purposes
of computing the process weight rate for this
Rule 203(d)(5)(E)(i), nongaseous material
charged to the furnace and process oxygen shall
be included.
No material shall be included
more than once.
(ii)
Hot Metal Transfer, Hot Metal Desulfurization,
and Ladle Lancing:
(aa) Particulate emissions from hot metal
trans—
fers to a mixer or ladle, hot metal desul—
furization operations,
and ladle lancing
shall be collected and ducted to pollution
control equipment, and emissions from the
pollution control equipment shall not ex-
ceed 0.03 gr/dscf
(0.07 g/dscm).
35—354
9
(bb) Provided,
however, that
if the owner or
operator can establish that the total par-
ticulate emissions from hot metal trans-
fers, hot metal
desulfurization operations
and
ladle
lancing
operations
combined
do
not
exceed
the
allowable
emissions
as
spec-
ified by Rule 203(a) for new emission
sources or Rule 203(b) for existing emis-
sion sources, whichever is applicable,
where the process weight rate
(P)
is the
hot metal charged to the BOF vessel, then
Rule 203(d)(5)(E)(ii)(aa)
shall not apply.
(F)
Hot Metal Desulfurization Not Located in the BOF.
The particulate emissions from hot metal desulfuri—
zation shall be
collected and ducted to pollution
control equipment,
and emissions from the pollution
control equipment shall not exceed 0.03 gr/dscf
(0.07 g/dscm).
(G)
Electric Arc Furnaces.
The total particulate emis-
sions from meltdown and refining,
charging,
tapping,
slagging, electrode port leakage, and ladle
lancing
shall not exceed the allowable emission rate
specified by Rule 203(a) or Rule 203(b), whichever
is applicable.
(H)
Argon—Oxygen Decarburization Vessels.
The total
particulate emissions from all charging, refining,
alloy addition,
and tapping operations
shall not
exceed the allowable emission rate specified by
Rule 203(a) for new emission sources or Rule
203(b) for existing emission sources, whichever is
applicable.
(I)
Liquid Steel Charging.
Particulate emissions from
liquid steel charging in continuous casting opera-
tions
shall be controlled by chemical or mechanical
shrouds or methods of comparable effectiveness.
(J)
Hot
Scarf
ing Machines.
All hot scarfing machines
shall be controlled by pollution control equipment.
Emissions
from said pollution control equipment
shall not exceed 0.03 gr/dscf
(0.07 g/dscm)
during
hot scarfing operations.
(K)
Measurement Methods.
Particulate emissions from
emission sources subject to Rule 203(d)(5) shall
be determined in accordance with procedures pub-
lished in 40 CFR Part 60, Appendix A,
Methods 1—5,
front one—half of the sampling train.
42 Fed.
Reg.
41754, et
~
(August 18,
1977).
Visible
emission evaluation for determining compliance
35—355
10
shall be conducted in accordance with procedures
published in 40 CFR Part 60, Appendix
A,
Method
9.
42 Fed.
Reg.
41754, et
~
(August 18,
1977).
(L)
Compliance Dates.
(i)
Every owner or operator of an emission source
the construction or modification of which
is
commenced after September
6,
1979 shall comply
with
the
emission standards and limitations
of this Rule 203(d) (5)
upon commencement of
operation.
(ii)
Every owner or operator of an emission source
the construction or operation of which was
commenced prior to September
6,
1979 shall
comply with the emission standards and limita-
tions of this Rule 203(d)(5) no later than
December 31, 1982.
(iii)
From the effective date of this Rule 203(d) (5)
through December 31,
1982,
full compliance
with an approved Compliance Program and
Project Completion Schedule pursuant to Rule
104 for all sources of particulate emissions
subject to Rule 203(d)(5) and 203(f)
as
amended under common ownership or control
in
the same air quality control region shall
constitute compliance with the emission
standards and limitations contained
in this
Part II
if such Compliance Program and Project
Completion Schedule:
(aa) provides for compliance by all sources
of particulate matter subject to Rules
203(d)(5) and 203(f),
as amended,
under
common ownership or control in the same
air quality region,
as expeditiously as
practicable considering what is economic-
ally reasonable and technically feasible,
and
(bb) provides for reasonable further progress
in achieving the reductions
in particulate
emissions required by Rules 203(d) (5) and
203(f),
as amended,
including annual in-
crements of reductions such that at least
one—third of the total reductions are
achieved by December 31,
1980 and at least
two—thirds of the total reduction are
achieved by December 31,
1981, unless the
owner or operator demonstrates
in a hear-
ing before the Board that such increments
35—356
i-i
are technically infeasible or economically
unreasonable or unless the owner or operator
demonstrates
in a hearing before the Board
that some alternate schedule represents
reasonable further progress within the
meaning
of Section 172(b)
of the Clean Air
Act,
42 U.S.C.
§7502(h).
(iv)
The provisions of Rule 203(d)(5)(L)(iii)
shall not apply to any facility subject to a
rule which is not in
full
force and effect as
a matter of
state
law because of judicial
action,
and
in such event the facility shall
remain subject to the regulations in effect
at the time these amendments are adopted.
(M)
The provisions of Rule 203(d)(5)(L) are not sever-
able.
Should any portion thereof be found invalid
or be disapproved by U.S. E.P.A.
as
a revision of
the state
implementation plan pursuant to the
Clean Air Act, then the entire Rule 203(d)(5)(L)
shall be null and void, the provisions of Rules
203(d)(5)(A) and
(B) shall become immediately
effective, and the provisions
of existing Rules
203(a),
(b),
and
(c)
and prior Rule 203(d)(2)
(in
effect from April 14,
1972 to the effective date
of this Rule) shall be reinstated.
Mr. Werner dissented.
I, Christan
L.
Moffett, Clerk of the Illinois Pollution
Cont o~.Board, hereby certify the above Order was adopted on
the
_____
day of ~
1979 by a vote of
d/_/
Christan L. Moffett,
rk
Illinois Pollution
n rol Board
35—
357