Wisconsin Administrative Code
Department of Natural Resources
NR 400-499 - Environmental Protection - Air Pollution Control
Chapter NR 440 - Standards of performance for new stationary sources
Subchapter II - Standards of Performance
Section NR 440.315 - Basic oxygen process steelmaking facilities for which construction is commenced after January 20, 1983
Universal Citation: WI Admin Code ยง NR 440.315
Current through August 26, 2024
(1) APPLICABILITY AND DESIGNATION OF AFFECTED FACILITIES.
(a)
The provisions of this section apply to the following affected facilities in an
iron and steel plant: top-blown BOPFs and hot metal transfer stations and
skimming stations used with bottom-blown or top-blown BOPFs.
(b) This section applies to any facility
identified in par. (a) that commences construction, modification or
reconstruction after January 20, 1983.
(c) Any BOPF subject to the provisions of
this section is subject to those provisions of s.
NR 440.31 applicable to affected facilities commencing
construction, modification or reconstruction after January 20, 1983.
(2) DEFINITIONS. As used in this section, terms not defined in this subsection have the meanings given in s. NR 440.02.
(a) "Basic
oxygen process furnace" or "BOPF" means any furnace with a refractory lining in
which molten steel is produced by charging scrap metal, molten iron, and flux
materials or alloy additions into a vessel and by introducing a high volume of
oxygen-rich gas. Open hearth, blast and reverberatory furnaces are not included
in this definition.
(b)
"Bottom-blown furnace" means any BOPF in which oxygen and other combustion
gases are introduced to the bath of molten iron through tuyeres in the bottom
of the vessel or through tuyeres in the bottom and sides of the
vessel.
(c) "Fume suppression
system" means the equipment comprising any system used to inhibit the
generation of emissions from steelmaking facilities with an inert gas, flame or
steam blanket applied to the surface of molten iron or steel.
(d) "Hot metal transfer station" means the
facility where molten iron is emptied from the railroad torpedo car or hot
metal car to the shop ladle. This includes the transfer of molten iron from the
torpedo car or hot metal car to a mixer (or other intermediate vessel) and from
a mixer (or other intermediate vessel) to the ladle. This facility is also
known as the reladling station or ladle transfer station.
(e) "Primary emission control system" means
the combination of equipment used for the capture and collection of primary
emissions, e.g., an open hood capture system used in conjunction with a
particular cleaning device such as an electrostatic precipitator or a closed
hood capture system used in conjunction with a particulate matter cleaning
device such as a scrubber.
(f)
"Primary emissions" means particulate matter emissions from the BOPF generated
during the steel production cycle which are captured by, and do not thereafter
escape from the BOPF primary control system.
(g) "Primary oxygen blow" means the period in
the steel production cycle of a BOPF during which a high volume of oxygen-rich
gas is introduced to the bath of molten iron by means of a lance inserted from
the top of the vessel. This definition does not include any additional, or
secondary, oxygen blows made after the primary blow.
(h) "Secondary emission control system" means
the combination of equipment used for the capture and collection of secondary
emissions, e.g.:
1. An open hood system for
the capture and collection of primary and secondary emissions from the BOPF,
with local hooding ducted to a secondary emission collection device such as a
baghouse for the capture and collection of emissions from the hot metal
transfer and skimming station; or
2. An open hood system for the capture and
collection of primary and secondary emissions from the furnace, plus a furnace
enclosure with local hooding ducted to a secondary emission collection device,
such as a baghouse, for additional capture and collection of secondary
emissions from the furnace, with local hooding ducted to a secondary emission
collection device, such as a baghouse for the capture and collection of
emissions from hot metal transfer and skimming stations; or
3. A furnace enclosure with local hooding
ducted to a secondary emission collection device such as a baghouse for the
capture and collection of secondary emissions from a BOPF controlled by a
closed hood primary emission control system, with local hooding ducted to a
secondary emission collection device, such as baghouse, for the capture and
collection of emissions from hot metal transfer and skimming
stations.
(i) "Secondary
emissions" means particulate matter emissions that are not captured by the BOPF
primary control system, including emissions from hot metal transfer and
skimming stations. This definition also includes particulate matter emissions
that escape from openings in the primary emission control system, such as from
lance hole openings, gaps or tears in the ductwork of the primary emission
control system, or leaks in hoods.
(j) "Skimming station" means the facility
where slag is mechanically raked from the top of the molten iron.
(k) "Steel production cycle" means the
operations conducted within the BOPF steelmaking facility that are required to
produce each batch of steel, including the following operations: scrap
charging, preheating (when used), hot metal charging primary oxygen blowing,
sampling (vessel turndown and turnup), additional oxygen blowing (when used),
tapping and deslagging. Hot metal transfer and skimming operations from the
next steel production cycle are also included when the hot metal transfer
station or skimming station is an affected facility.
(L) "Top-blown furnace" means any BOPF in
which oxygen is introduced to the bath of molten iron by means of an oxygen
lance inserted from the top of the vessel.
(3) STANDARDS FOR PARTICULATE MATTER.
(a) Except as provided under pars. (b) and
(c), on and after the date on which the performance test under s.
NR 440.08 is
required to be completed, no owner or operator subject to the provisions of
this section may cause to be discharged into the atmosphere from any affected
facility any secondary emissions that:
1.
Exit from the BOPF shop roof monitor (or other building openings) and exhibit
greater than 10% opacity during the steel production cycle of any top-blown
BOPF or during hot metal transfer or skimming operations for any bottom-blown
BOPF, except that an opacity greater than 10% but less than 20% may occur once
per steel production cycle.
2. Exit
from a control device used solely for the collection of secondary emissions
from a top-blown BOPF or from hot metal transfer or skimming operations for a
top-blown BOPF and contain particulate matter in excess of 23 mg/dscm (0.010
gr/dscf).
3. Exit from a control
device used solely for the collection of secondary emissions from a top-blown
BOPF or from hot metal transfer or skimming operations for a top-blown or a
bottom-blown BOPF and exhibit more than 5% opacity.
(b) A fume suppression system used to control
secondary emissions from an affected facility is not subject to par. (a) 2. and
3.
(c) A control device used to
collect both primary and secondary emissions from a BOPF is not subject to par.
(a) 2. and 3.
(4) MONITORING OF OPERATIONS.
(a) Each owner or
operator of an affected facility shall install, calibrate, operate, and
maintain a monitoring device that continually measures and records for each
steel production cycle the various rates or levels of exhaust ventilation at
each phase of the cycle through each duct of the secondary emission capture
system. The monitoring device or devices are to be placed at locations near
each capture point of the secondary emission capture system to monitor the
exhaust ventilation rates or levels adequately, or in alternative locations
approved in advance by the department.
(b) If a chart recorder is used, the owner or
operator shall use chart recorders that are operated at minimum chart speed of
3.8 cm/hr (1.5 in/hr).
(c) All
monitoring devices required by par. (a) shall be certified by the manufacturer
to be accurate to within " 10% compared to Method 2 of 40 CFR part 60, Appendix
A, incorporated by reference in s.
NR 440.17(1). The owner or operator
shall recalibrate and check the devices annually and at other times as the
department may require, in accordance with the written instructions of the
manufacturer and by comparing the device against Method 2.
(d) Each owner or operator subject to the
requirements of par. (a) shall report on a semiannual basis all measurements of
exhaust ventilation rates or levels over any 3-hour period that average more
than 10% below the average rates or levels of exhaust ventilation maintained
during the most recent performance test conducted under s.
NR 440.08 in
which the affected facility demonstrated compliance with the standard under
sub. (3) (a) 2. The accuracy of the respective measurements, not to exceed the
values specified in par. (c), may be considered when determining the
measurement results that are to be reported.
(e) If a scrubber primary emission control
device is used to collect secondary emissions, the owner or operator shall
report on a semiannual basis all measurements of exhaust ventilation rate over
any 3-hour period that average more than 10% below the average levels
maintained during the most recent performance text conducted under s.
NR 440.08 in
which the affected facility demonstrated compliance with the standard under
sub. (3) (a) 1.
(5) TEST METHODS AND PROCEDURES.
(a) In conducting the
performance tests required in s.
NR 440.08, the
owner or operator shall use as reference methods and procedures the test
methods in Appendix A of 40 CFR part 60, incorporated by reference in s.
NR 440.17, or other methods and procedures as specified
in this subsection, except as provided in s.
NR 440.08(2).
(b) The owner or operator shall determine
compliance with the particulate matter standard in sub. (3) as follows:
1. Start and end times of each steel
production cycle during each run shall be recorded.
Note: See sub. (6) (c) and (d) for the definitions of start and end times of a cycle.
2. Method 5 shall be used to determine the
particulate matter concentration. Sampling shall be conducted only during the
steel production cycle and for a sufficient number of steel production cycles
to obtain a total sample volume of at least 5.67 dscm (200 dscf) for each
run.
3. Method 9 and the procedures
of s.
NR 440.11 shall be used to determine opacity, except
sections 2.4 and 2.5 of Method 9 shall be replaced with the following
instructions for recording observations and reducing data:
a. Section 2.4. Opacity observations shall be
recorded to the nearest 5% at 15-second intervals. During the initial
performance test conducted pursuant to s.
NR 440.08,
observations shall be made and recorded in this manner for a minimum of 3 steel
production cycles. During any subsequent compliance test, observations may be
made for any number of steel production cycles, although, where conditions
permit, observations will generally be made for a minimum of 3 steel production
cycles.
b. Section 2.5. Opacity
shall be determined as an average of 12 consecutive observations recorded at
15-second intervals. For each steel production cycle, divide the observations
recorded into sets of 12 consecutive observations. Sets need not be consecutive
in time, and in no case may 2 sets overlap. For each set of 12 observations,
calculate the average by summing the opacity of 12 consecutive observations and
dividing this sum by 12.
(c) In complying with the requirements of
sub. (4) (c), the owner or operator shall conduct an initial test as follows:
1. For devices that monitor and record the
exhaust ventilation rate, compare velocity readings recorded by the monitoring
device against the velocity readings obtained by Method 2. Take Method 2
readings at a point or points that would properly characterize the monitoring
device's performance and that would adequately reflect the various rates of
exhaust ventilation. Obtain readings at sufficient intervals to obtain 12 pairs
of readings for each duct of the secondary emission capture system. Compare the
averages of the 2 sets to determine whether the monitoring device velocity is
within " 10% of the Method 2 average.
2. For devices that monitor the level of
exhaust ventilation and record only step changes when a set point rate is
reached, compare step changes recorded by the monitoring device against the
velocity readings obtained by Method 2. Take Method 2 readings at a point or
points that would properly characterize the performance of the monitoring
device and that would adequately reflect the various rates of exhaust
ventilation. Obtain readings at sufficient intervals to obtain 12 pairs of
readings for each duct of the secondary emission capture system. Compare the
averages of the 2 sets to determine whether the monitoring device step change
is within " 10% of the setpoint rate.
(d) To comply with sub. (4) (d) or (e), the
owner or operator shall use the monitoring device of sub. (4) (a) to determine
the exhaust ventilation rates or levels during the particulate matter runs.
Each owner or operator shall then use these rates or levels to determine the
3-hour averages required by sub. (4) (d) and (e).
(6) COMPLIANCE PROVISIONS.
(a) When determining compliance with mass and
visible emission limits specified in sub. (3) (a) 2. and 3., the owner or
operator of a BOPF shop that normally operates 2 furnaces with overlapping
cycles may elect to operate only one furnace. If an owner or operator chooses
to shut down one furnace, he or she shall be allowed a reasonable time period
to adjust the production schedule before the compliance tests are conducted.
The owner or operator of an affected facility may also elect to suspend shop
operations not subject to this section during compliance testing.
(b) During compliance testing for mass and
visible emission standards, if an owner or operator elects to shut down one
furnace in a shop that normally operates 2 furnaces with overlapping cycles,
the owner or operator shall operate the secondary emission control system for
the furnace being tested at exhaust ventilation rates or levels for each duct
of the secondary emission control system that are appropriate for
single-furnace operating. Following the compliance test, the owner or operator
shall operate the secondary emission control system at exhaust ventilation
rates or levels for each duct of the system that are no lower than 90% of the
exhaust ventilation values established during the most recent compliance
test.
(c) For the purpose of
determining compliance with visible and mass emission standards, a steel
production cycle begins when the scrap or hot metal is charged to the vessel
(whichever operation occurs first) and terminates 3 minutes after slag is
emptied from the vessel into the slag pot. Consecutive steel production cycles
are not required for the purpose of determining compliance. Where a hot metal
transfer or skimming station is an affected facility, the steel production
cycle also includes the hot metal transfer or skimming operation for the next
steel production cycle for the affected vessel. Visible emission observations
for both hot metal transfer and skimming operations begin with the start of the
operation and terminate 3
(d) For
the purpose of determining compliance with visible emission standards specified
in sub. (3) (a) 1. and 3., the starting and stopping times of regulated process
operations shall be determined and the starting and stopping times of visible
emissions data sets shall be determined accordingly.
(e) To determine compliance with sub. (3) (a)
1., the owner or operator shall select the data sets yielding the highest and
second highest 3-minute average opacities for each steel production cycle.
Compliance is achieved if the highest 3-minute average for each cycle observed
is less than 20% and the second highest 3-minute average is 10% or
less.
(f) To determine compliance
with sub. (3) (a) 2., the owner or operator shall determine the concentration
of particulate matter in exhaust gases exiting the secondary emission
collection device with Method 5 of Appendix A, 40 CFR part 60, incorporated by
reference in s.
NR 440.17(1). Compliance is achieved if
the concentration of particulate matter does not exceed 23 mg/dscm (0.010
gr/dscf).
(g) To determine
compliance with sub. (3) (a) 3., the owner or operator shall construct
consecutive 3-minute averages for each steel production cycle. Compliance is
achieved if no 3-minute average is more than 5%.
Disclaimer: These regulations may not be the most recent version. Wisconsin may have more current or accurate information. We make no warranties or guarantees about the accuracy, completeness, or adequacy of the information contained on this site or the information linked to on the state site. Please check official sources.
This site is protected by reCAPTCHA and the Google
Privacy Policy and
Terms of Service apply.