Attachment A

Subpart EEEEE--National Emission Standards for Hazardous 

Air Pollutants for Iron and Steel Foundries

What This Subpart Covers

63.7680  What is the purpose of this subpart?

63.7681  Am I subject to this subpart?

63.7682  What parts of my foundry does this subpart cover?

63.7683  When do I have to comply with this subpart?

Emissions Limitations

63.7690	What emissions limitations must I meet?

Work Practice Standards

63.7700	What work practice standards must I meet?

Operation and Maintenance Requirements 

63.7710	What are my operation and maintenance requirements?

General Compliance Requirements

63.7720	What are my general requirements for complying with this
subpart?

Initial Compliance Requirements

63.7730	By what date must I conduct performance tests or other initial
compliance demonstrations?

63.7731	When must I conduct subsequent performance tests?

63.7732	What test methods and other procedures must I use to demonstrate
initial compliance with the emissions limitations?

63.7733	What procedures must I use to establish operating limits?

63.7734	How do I demonstrate initial compliance with the emissions
limitations that apply to me?

63.7735	How do I demonstrate initial compliance with the work practice
standards that apply to me?

63.7736	How do I demonstrate initial compliance with the operation and
maintenance requirements that apply to me?

Continuous Compliance Requirements

63.7740	What are my monitoring requirements?

63.7741	What are the installation, operation, and maintenance
requirements for my monitors?

63.7742	How do I monitor and collect data to demonstrate continuous
compliance?

63.7743	How do I demonstrate continuous compliance with the emissions
limitations that apply to me?

63.7744	How do I demonstrate continuous compliance with the work
practice standards that apply to me?

63.7745	How do I demonstrate continuous compliance with the operation
and maintenance requirements that apply to me?

63.7746	What other requirements must I meet to demonstrate continuous
compliance?

63.7747	How do I apply for alternative monitoring requirements for a
continuous emissions monitoring system? 

Notifications, Reports, and Records

63.7750	What notifications must I submit and when?

63.7751	What reports must I submit and when?

63.7752	What records must I keep?

63.7753	In what form and for how long must I keep my records?

Other Requirements and Information

63.7760	What parts of the General Provisions apply to me?

63.7761	Who implements and enforces this subpart?

Definitions

63.7765	What definitions apply to this subpart?

Tables to Subpart EEEEE of Part 63

Table 1 to Subpart EEEEE of Part 63 - Applicability of General
Provisions to Subpart EEEEE

What this Subpart Covers

§63.7680  What is the purpose of this subpart?

	This subpart establishes national emission standards for hazardous air
pollutants (NESHAP) for iron and steel foundries.  This subpart also
establishes requirements to demonstrate initial and continuous
compliance with the emissions limitations, work practice standards, and
operation and maintenance requirements in this subpart.

§63.7681  Am I subject to this subpart?

	You are subject to this subpart if you own or operate an iron and steel
foundry that is (or is part of) a major source of hazardous air
pollutant (HAP) emissions.  Your iron and steel foundry is a major
source of HAP for purposes of this subpart if it emits or has the
potential to emit any single HAP at a rate of 10 tons or more per year
or any combination of HAP at a rate of 25 tons or more per year or if it
is located at a facility that emits or has the potential to emit any
single HAP at a rate of 10 tons or more per year or any combination of
HAP at a rate of 25 tons or more per year as defined in §63.2. 

§63.7682  What parts of my foundry does this subpart cover?

	(a)  The affected source is each new or existing iron and steel
foundry.

	(b)  This subpart covers emissions from metal melting furnaces, scrap
preheaters, pouring areas, pouring stations, automated conveyor and
pallet cooling lines, automated shakeout lines, and mold and core making
lines.  This subpart also covers fugitive emissions from foundry
operations.

	(c)  An affected source is existing if you commenced construction or
reconstruction of the affected source before December 23, 2002.

	(d)  An affected source is new if you commenced construction or
reconstruction of the affected source on or after December 23, 2002.  An
affected source is reconstructed if it meets the definition of
“reconstruction” in §63.2.

§63.7683  When do I have to comply with this subpart?

	(a)  Except as specified in paragraph (b) of this section, if you have
an existing affected source, you must comply with each emissions
limitation, work practice standard, and operation and maintenance
requirement in this subpart that applies to you no later than April 23,
2007.  Major source status for existing affected sources must be
determined no later than April 23, 2007.

	(b)  If you have an existing affected source, you must comply with the
work practice standards in §63.7700(b) or (c), as applicable, no later
than April 22, 2005.

	(c)  If you have a new affected source for which the initial startup
date is on or before April 22, 2004, you must comply with each emissions
limitation, work practice standard, and operation and maintenance
requirement in this subpart that applies to you by April 22, 2004.

	(d)  If you have a new affected source for which the initial startup
date is after April 22, 2004, you must comply with each emissions
limitation, work practice standard, and operation and maintenance
requirement in this subpart that applies to you upon initial startup. 

	(e)  If your iron and steel foundry is an area source that becomes a
major source of HAP, you must meet the requirements of §63.6(c)(5).

	(f)  You must meet the notification and schedule requirements in
§63.7750.  Note that several of these notifications must be submitted
before the compliance date for your affected source.  

Emissions Limitations

§63.7690  What emissions limitations must I meet?

	(a)  You must meet each the emissions limits or standards in paragraphs
(a)(1) through (11) of this section that applies apply to you.  When
alternative emission limitations are provided for a given emission
source, you are not restricted in the selection of which applicable
alternative emission limitation is used to demonstrate compliance.

	(1)  For each electric arc metal melting furnace, electric induction
metal melting furnace, or scrap preheater at an existing iron and steel
foundry, you must not discharge emissions through a conveyance to the
atmosphere that exceed either the limit for particulate matter (PM) in
paragraph (a)(1)(i) of this section or, alternatively the limit for
total metal HAP in paragraph (a)(1)(ii) of this section:

	(i)  0.005 grains of PM per dry standard cubic foot (gr/dscf), or

	(ii)  0.0004 gr/dscf of total metal HAP.

	(2)  For each cupola metal melting furnace at an existing iron and
steel foundry, you must not discharge emissions through a conveyance to
the atmosphere that exceed either the limit for PM in paragraph
(a)(2)(i) or (a)(2)(ii) of this section or, alternatively the limit for
total metal HAP in paragraph (a)(2)(iii) or (a)(2)(iv) of this section:

	(i)  0.006 gr/dscf of PM, or

	(ii) 0.10 pound PM per ton metal charged (lb/ton), or

	(iii)  0.0005 gr/dscf of total metal HAP, or

	(iv)  0.008 lb/ton of total metal HAP. 

	(3)  For each cupola metal melting furnace or electric arc metal
melting furnace at a new iron and steel foundry, you must not discharge
emissions through a conveyance to the atmosphere that exceed either the
limit for PM in paragraph (a)(3)(i) of this section or, alternatively
the limit for total metal HAP in paragraph (a)(3)(ii) of this section:

	(i)  0.002 gr/dscf of PM, or

	(ii)  0.0002 gr/dscf of total metal HAP.

	(4)  For each electric induction metal melting furnace or scrap
preheater at a new iron and steel foundry, you must not discharge
emissions through a conveyance to the atmosphere that exceed either the
limit for PM in paragraph (a)(4)(i) of this section or, alternatively
the limit for total metal HAP in paragraph (a)(4)(ii) of this section:

	(i)  0.001 gr/dscf of PM, or

	(ii)  0.00008 gr/dscf of total metal HAP.

	(5)  For each pouring station at an existing iron and steel foundry,
you must not discharge emissions through a conveyance to the atmosphere
that exceed either the limit for PM in paragraph (a)(5)(i) of this
section or, alternatively the limit for total metal HAP in paragraph
(a)(5)(ii) of this section:

	(i)  0.010 gr/dscf of PM, or

	(ii)  0.0008 gr/dscf of total metal HAP.

	(6)  For each pouring area or pouring station at a new iron and steel
foundry, you must not discharge emissions through a conveyance to the
atmosphere that exceed either the limit for PM in paragraph (a)(6)(i) of
this section or, alternatively the limit for total metal HAP in
paragraph (a)(6)(ii) of this section:

	(i)  0.002 gr/dscf of PM, or

	(ii)  0.0002 gr/dscf of total metal HAP.

	(7)  For each building or structure housing any iron and steel foundry
emissions source at the iron and steel foundry, you must not discharge
any fugitive emissions to the atmosphere from foundry operations that
exhibit opacity greater than 20 percent (6-minute average), except for
one 6-minute average per hour that does not exceed 27 percent opacity.  

	(8)  For each cupola metal melting furnace at a new or existing iron
and steel foundry, you must not discharge emissions of volatile organic
hazardous air pollutants (VOHAP) through a conveyance to the atmosphere
that exceed 20 parts per million by volume (ppmv) corrected to 10
percent oxygen.

 	(9)  As an alternative to the work practice standard in §63.7700(e)
for a scrap preheater at an existing iron and steel foundry or in
§63.7700(f) for a scrap preheater at a new iron and steel foundry, you
must not discharge emissions of VOHAP through a conveyance to the
atmosphere that exceed 20 ppmv.

	(10)  For one or more automated conveyor and pallet cooling lines that
use a sand mold system or automated shakeout lines that use a sand mold
system at a new iron and steel foundry, you must not discharge emissions
of VOHAP through a conveyance to the atmosphere that exceed a
flow-weighted average of 20 ppmv.

	(11)  For each triethylamine (TEA) cold box mold or core making line at
a new or existing iron and steel foundry, you must meet either the
emissions limit in paragraph (a)(11)(i) of this section or,
alternatively the emissions standard in paragraph (a)(11)(ii) of this
section: 

	(i)  You must not discharge emissions of TEA through a conveyance to
the atmosphere that exceed 1 ppmv, as determined according to the
performance test procedures in §63.7732(g)when scrubbing with fresh
acid solution; or

	(ii)  You must reduce emissions of TEA from each TEA cold box mold or
core making line by at least 99 percent, as determined when scrubbing
with fresh acid solutionaccording to the performance test procedures in
§63.7732(g).  	

(b)  You must meet each operating limit in paragraphs (b)(1) through (5)
of this section that applies to you.

	(1)  You must install, operate, and maintain a capture and collection
system for all emissions sources subject to an emissions limit or
standard for VOHAP or TEA in paragraphs (a)(8) through (11) of this
section.  

	(i)  Each capture and collection system must meet accepted engineering
standards, such as those published by the American Conference of
Governmental Industrial Hygienists.

	(ii)  You must operate each capture system at or above the lowest value
or settings established as operating limits in your operation and
maintenance plan.

	(2)  You must operate each wet scrubber applied to emissions from a
metal melting furnace, scrap preheater, pouring area, or pouring station
subject to an emissions limit for PM or total metal HAP in paragraphs
(a)(1) through (6) of this section such that the 3-hour average pressure
drop and scrubber water flow rate does not fall below the minimum levels
established during the initial or subsequent performance test.

	(3)  You must operate each combustion device applied to emissions from
a cupola metal melting furnace subject to the emissions limit for VOHAP
in paragraph (a)(8) of this section, such that the 15-minute average
combustion zone temperature does not fall below 1,300 degrees Fahrenheit
(F).  Periods when the cupola is off blast and for 15 minutes after
going on blast from an off blast condition are not included in the
15-minute average.

	(4)  You must operate each combustion device applied to emissions from
a scrap preheater subject to the emissions limit for VOHAP in paragraph
(a)(9) of this section or from a TEA cold box mold or core making line
subject to the emissions limit for TEA in paragraph (a)(11) of this
section, such that the 3-hour average combustion zone temperature does
not fall below the minimum level established during the initial or
subsequent performance test.

	(5)  You must operate each wet acid scrubber applied to emissions from
a TEA cold box mold or core making line subject to the emissions limit
for TEA in paragraph (a)(11) of this section such that:

	(i)  The 3-hour average scrubbing liquid flow rate does not fall below
the minimum level established during the initial or subsequent
performance test; and

	(ii)  The 3-hour average pH of the scrubber blowdown, as measured by a
continuous parameter monitoring system (CPMS), does not exceed 4.5 or
the pH of the scrubber blowdown, as measured once every 8 hours during
process operations, does not exceed 4.5.

	(c)  If you use a control device other than a baghouse, wet scrubber,
wet acid scrubber, or combustion device, you must prepare and submit a
monitoring plan containing the information listed in paragraphs (c)(1)
through (5) of this section.  The monitoring plan is subject to approval
by the Administrator.

	(1)  A description of the device;

	(2)  Test results collected in accordance with §63.7732 verifying the
performance of the device for reducing emissions of PM, total metal HAP,
VOHAP, or TEA to the levels required by this subpart;

	(3)  A copy of the operation and maintenance plan required by
§63.7710(b);

	(4)  A list of appropriate operating parameters that will be monitored
to maintain continuous compliance with the applicable emissions
limitation(s); and

	(5)  Operating parameter limits based on monitoring data collected
during the performance test.

Work Practice Standards

§63.7700  What work practice standards must I meet?

	(a)  For each segregated scrap storage area, bin or pile, you must
comply with the certification requirements in paragraph (b) of this
section, or prepare and implement a plan for the selection and
inspection of scrap according to the requirements in paragraph (c) of
this section.  You may have certain scrap subject to paragraph (b) of
this section and other scrap subject to paragraph (c) of this section at
your facility provided the scrap remains segregated until charge
make-up.

	(b)  You must prepare and operate at all times according to a written
certification that the foundry purchases and uses only metal ingots, pig
iron, slitter, or other materials that do not include post-consumer
automotive body scrap, post-consumer engine blocks, post-consumer oil
filters, oily turnings, lead components, mercury switches, plastics, or
free organic liquids.  For the purpose of this paragraph (b), “free
organic liquids” is defined as material that fails the paint filter
test by EPA Method 9095A, “Paint Filter Liquids Test” (Revision 1,
December 1996), as published in EPA Publication SW-846 “Test Methods
for Evaluating Solid Waste, Physical/Chemical Methods” (incorporated
by reference – see § 63.14).  Any post-consumer engine blocks,
post-consumer oil filters, or oily turnings that are processed and/or
cleaned to the extent practicable such that the materials do not include
lead components, mercury switches, chlorinated plastics, or free organic
liquids can be included in this certification.

	(c)  You must prepare and operate at all times according to a written
plan for the selection and inspection of iron and steel scrap to
minimize, to the extent practicable, the amount of organics and HAP
metals in the charge materials used by the iron and steel foundry.  This
scrap selection and inspection plan is subject to approval by the
Administrator.  You must keep a copy of the plan onsite and readily
available to all plant personnel with materials acquisition or
inspection duties.  You must provide a copy of the material
specifications to each of your scrap vendors.  Each plan must include
the information specified in paragraphs (c)(1) through (3) of this
section. 

	(1)  A materials acquisition program to limit organic contaminants
according to the requirements in paragraph (c)(1)(i) or (ii) of this
section, as applicable.

	(i)  For scrap charged to a scrap preheater, electric arc metal melting
furnace, or electric induction metal melting furnaces, specifications
for scrap materials to be depleted (to the extent practicable) of the
presence of used oil filters, chlorinated plastic parts, organic
liquids, and a program to ensure the scrap materials are drained of free
liquids; or

	(ii)  For scrap charged to a cupola metal melting furnace,
specifications for scrap materials to be depleted (to the extent
practicable) of the presence of chlorinated plastic, and a program to
ensure the scrap materials are drained of free liquids.

	(2)  A materials acquisition program specifying that the scrap supplier
remove accessible mercury switches from the trunks and hoods of any
automotive bodies contained in the scrap and remove accessible lead
components such as batteries and wheel weights.  You must either obtain
and maintain onsite a copy of the procedures used by the scrap supplier
for either removing accessible mercury switches or for purchasing
automobile bodies that have had mercury switches removed, as applicable,
or document your attempts to obtain a copy of these procedures from the
scrap suppliers servicing your area.

	(3)  Procedures for visual inspection of a representative portion, but
not less than 10 percent, of all incoming scrap shipments to ensure the
materials meet the specifications.

	(i)  The inspection procedures must identify the location(s) where
inspections are to be performed for each type of shipment.  Inspections
may be performed at the scrap supplier’s facility.  The selected
location(s) must provide a reasonable vantage point, considering worker
safety, for visual inspection.

	(ii)  The inspection procedures must include recordkeeping requirements
that document each visual inspection and the results.

	(iii)  The inspection procedures must include provisions for rejecting
or returning entire or partial scrap shipments that do not meet
specifications and limiting purchases from vendors whose shipments fail
to meet specifications for more than three inspections in one
calendercalendar year.

	(iv)  If inspections are performed at the scrap supplier’s facility,
the inspection procedures must include an explanation of how the
periodic inspections ensure that not less than 10 percent of scrap
purchased from the supplier is subject to inspection.

	(d)  For each furan warm box mold or core making line in a new or
existing iron and steel foundry, you must use a binder chemical
formulation that does not contain methanol as a specific ingredient of
the catalyst formulation as determined by the Material Safety Data
Sheet.  This requirement does not apply to the resin portion of the
binder system.

	(e)  For each scrap preheater at an existing iron and steel foundry,
you must meet either the requirement in paragraph (e)(1) or (2) of this
section.  As an alternative to the requirement in paragraph (e)(1) or
(2) of this section, you must meet the VOHAP emissions limit in
§63.7690(a)(9).

	(1)  You must install, operate, and maintain a gas-fired preheater
where the flame directly contacts the scrap charged; or 

	(2)  You must charge only material that is subject to and in compliance
with the scrap certification requirement in paragraph (b) of this
section.

	(f)  For each scrap preheater at a new iron and steel foundry, you must
charge only material that is subject to and in compliance with the scrap
certification requirement in paragraph (b) of this section.  As an
alternative to this  requirement, you must meet the VOHAP emissions
limit in §63.7690(a)(9).

Operation and Maintenance Requirements

§63.7710  What are my operation and maintenance requirements?

	(a)  As required by §63.6(e)(1)(i), you must always operate and
maintain your iron and steel foundry, including air pollution control
and monitoring equipment, in a manner consistent with good air pollution
control practices for minimizing emissions at least to the levels
required by this subpart.

	(b)  You must prepare and operate at all times according to a written
operation and maintenance plan for each capture and collection system
and control device for an emissions source subject to an PM, metal HAP,
TEA, or VOHAP emissions limit in §63.7690(a).  Your operation and
maintenance plan also must include procedures for igniting gases from
mold vents in pouring areas and pouring stations that use a sand mold
system.  This operation and maintenance plan is subject to approval by
the Administrator.  Each plan must contain the elements described in
paragraphs (b)(1) through (6) of this section.

	(1)  Monthly inspections of the equipment that is important to the
performance of the total capture system (i.e., pressure sensors,
dampers, and damper switches).  This inspection must include
observations of the physical appearance of the equipment (e.g., presence
of holes in the ductwork or hoods, flow constrictions caused by dents or
accumulated dust in the ductwork, and fan erosion).  The operation and
maintenance plan must also include requirements to repair the defect or
deficiency as soon as practicable.

	(2)  Operating limits for each capture system for an emissions source
subject to an emissions limit or standard for VOHAP or TEA in
§63.7690(a)(8) through (11).  You must establish the operating
according to the requirements in paragraphs (b)(2)(i) through (iii) of
this section.

	(i)  Select operating limit parameters appropriate for the capture
system design that are representative and reliable indicators of the
performance of the capture system.  At a minimum, you must use
appropriate operating limit parameters that indicate the level of the
ventilation draft and damper position settings for the capture system
when operating to collect emissions, including revised settings for
seasonal variations.  Appropriate operating limit parameters for
ventilation draft include, but are not limited to:  volumetric flow rate
through each separately ducted hood, total volumetric flow rate at the
inlet to the control device to which the capture system is vented, fan
motor amperage, or static pressure.  Any parameter for damper position
setting may be used that indicates the duct damper position related to
the fully open setting.

	(ii)  For each operating limit parameter selected in paragraph
(b)(2)(i) of this section, designate the value or setting for the
parameter at which the capture system operates during the process
operation.  If your operation allows for more than one process to be
operating simultaneously, designate the value or setting for the
parameter at which the capture system operates during each possible
configuration that you may operate (i.e., the operating limits with one
furnace melting, two melting, as applicable to your plant).

	(iii)  Include documentation in your plan to support your selection of
the operating limits established for your capture system.  This
documentation must include a description of the capture system design, a
description of the capture system operating during production, a
description of each selected operating limit parameter, a rationale for
why you chose the parameter, a description of the method used to monitor
the parameter according to the requirements of §63.7740(a), and the
data used to set the value or setting for the parameter for each of your
process configurations.

	(3)  Preventative maintenance plan for each control device, including a
preventative maintenance schedule that is consistent with the
manufacturer’s instructions for routine and long-term maintenance. 

	(4)  A site-specific monitoring plan for each bag leak detection
system.  For each bag leak detection system that operates on the
triboelectric effect, the monitoring plan must be consistent with the
recommendations contained in the U.S. Environmental Protection Agency
guidance document “Fabric Filter Bag Leak Detection Guidance”
(EPA-454/R-98-015).  This baghouse monitoring plan is subject to
approval by the Administrator.  The owner or operator shall operate and
maintain the bag leak detection system according to the site-specific
monitoring plan at all times.  The plan must address all of the items
identified in paragraphs (b)(4)(i) through (v) of this section.

	(i)  Installation of the bag leak detection system.

	(ii)  Initial and periodic adjustment of the bag leak detection system
including how the alarm set-point will be established.

	(iii)  Operation of the bag leak detection system including quality
assurance procedures.

	(iv)  How the bag leak detection system will be maintained including a
routine maintenance schedule and spare parts inventory list.

	(v)  How the bag leak detection system output will be recorded and
stored.

	(5)  Corrective action plan for each baghouse.  The plan must include
the requirement that, in the event a bag leak detection system alarm is
triggered, you must initiate corrective action to determine the cause of
the alarm within 1 hour of the alarm, initiate corrective action to
correct the cause of the problem within 24 hours of the alarm, and
complete the corrective action as soon as practicable.  Corrective
actions taken may include, but are not limited to:

	(i)  Inspecting the baghouse for air leaks, torn or broken bags or
filter media, or any other condition that may cause an increase in
emissions.

	(ii)  Sealing off defective bags or filter media.

	(iii)  Replacing defective bags or filter media or otherwise repairing
the control device.

	(iv)  Sealing off a defective baghouse compartment.

	(v)  Cleaning the bag leak detection system probe or otherwise
repairing the bag leak detection system.

	(vi)  Making process changes.

	(vii)  Shutting down the process producing the PM emissions.

	(6)  Procedures for providing an ignition source to mold vents of sand
mold systems in each pouring area and pouring station unless you
determine the mold vent gases either are not ignitable, ignite
automatically, or cannot be ignited due to accessibility or safety
issues.  You must document and maintain records of this determination. 
The determination of ignitability, accessibility, and safety may
encompass multiple casting patterns provided the castings utilize
similar sand-to-metal ratios, binder formulations, and coating
materials.  The determination of ignitability must be based on
observations of the mold vents within 5 minutes of pouring, and the
flame must be present for at least 15 seconds for the mold vent to be
considered ignited.  For the purpose of this determination:

	(i)  Mold vents that ignite more than 75 percent of the time without
the presence of an auxiliary ignition source are considered to ignite
automatically; and

	(ii)  Mold vents that do not ignite automatically and cannot be ignited
in the presence of an auxiliary ignition source more than 25 percent of
the time are considered to be not ignitable. 

General Compliance Requirements

§63.7720  What are my general requirements for complying with this
subpart?

	(a)  You must be in compliance with the emissions limitations, work
practice standards, and operation and maintenance requirements in this
subpart at all times, except during periods of startup, shutdown, or
malfunction.

	(b)  During the period between the compliance date specified for your
iron and steel foundry in §63.7683 and the date when applicable
operating limits have been established during the initial performance
test, you must maintain a log detailing the operation and maintenance of
the process and emissions control equipment.

	(c)  You must develop and implement a written startup, shutdown, and
malfunction plan according to the provisions in §63.6(e)(3).  The
startup, shutdown, and malfunction plan also must specify what
constitutes a shutdown of a cupola and how to determine that operating
conditions are normal following startup of a cupola.

Initial Compliance Requirements

§63.7730  By what date must I conduct performance tests or other
initial compliance demonstrations?

	(a)  As required by §63.7(a)(2), you must conduct a performance test
no later than 180 calendar days after the compliance date that is
specified in §63.7683 for your iron and steel foundry to demonstrate
initial compliance with each emissions limitation in §63.7690 that
applies to you.

	(b)  For each work practice standard in §63.7700 and each operation
and maintenance requirement in §63.7710 that applies to you where
initial compliance is not demonstrated using a performance test, you
must demonstrate initial compliance no later than 30 calendar days after
the compliance date that is specified for your iron and steel foundry in
§63.7683.

	(c)  If you commenced construction or reconstruction between December
23, 2002 and April 22, 2004, you must demonstrate initial compliance
with either the proposed emissions limit or the promulgated emissions
limit no later than October 19, 2004 or no later than 180 calendar days
after startup of the source, whichever is later, according to
§63.7(a)(2)(ix).

	(d)  If you commenced construction or reconstruction between December
23, 2002 and April 22, 2004, and you chose to comply with the proposed
emissions limit when demonstrating initial compliance, you must conduct
a second performance test to demonstrate compliance with the promulgated
emissions limit by October 19, 2007 or after startup of the source,
whichever is later, according to §63.7(a)(2)(ix).

§63.7731  When must I conduct subsequent performance tests?

	(a)  You must conduct subsequent performance tests to demonstrate
compliance with all applicable PM or total metal HAP, VOHAP, and TEA
emissions limitations in §63.7690 for your iron and steel foundry no
less frequently than every 5 years and each time you elect to change an
operating limit or to comply with a different alternative emission
limit, if applicable.  The requirement to conduct performance tests
every 5 years does not apply to an emissions source for which a
continuous emissions monitoring system (CEMS) is used to demonstrate
continuous compliance.

	(b)  You must conduct subsequent performance tests to demonstrate
compliance with the opacity limit in §63.7690(a)(7) for your iron and
steel foundry no less frequently than once every 6 months.

§63.7732  What test methods and other procedures must I use to
demonstrate initial compliance with the emissions limitations?

 	(a)  You must conduct each performance test that applies to your iron
and steel foundry based on your selected compliance alternative, if
applicable, according to the requirements in §63.7(e)(1) and the
conditions specified in paragraphs (b) through (hi) of this section.

	(b)  To determine compliance with the applicable emissions limit for PM
in §63.7690(a)(1) through (6) for a metal melting furnace, scrap
preheater, pouring station, or pouring area, follow the test methods and
procedures in paragraphs (b)(1) through (56) of this section.

	(1)  Determine the concentration of PM according to the test methods in
40 CFR part 60, appendix A that are specified in paragraphs (b)(1)(i)
through (v) of this section.

	(i)  Method 1 or 1A to select sampling port locations and the number of
traverse points in each stack or duct.  Sampling sites must be located
at the outlet of the control device (or at the outlet of the emissions
source if no control device is present) prior to any releases to the
atmosphere.

	(ii)  Method 2, 2A, 2C, 2D, 2F, or 2G to determine the volumetric flow
rate of the stack gas.

	(iii)  Method 3, 3A, or 3B to determine the dry molecular weight of the
stack gas.

	(iv)  Method 4 to determine the moisture content of the stack gas.

	(v)  Method 5, 5B, 5D, 5F, or 5I, as applicable, to determine the PM
concentration.  The PM concentration is determined using only the
front-half (probe rinse and filter) of the PM catch.

	(2)  Collect a minimum sample volume of 60 dscf of gas during each PM
sampling run.  A minimum of three valid test runs are needed to comprise
a performance test.

	(3)  For cupola metal melting furnaces, sample only during times when
the cupola is on blast.

	(4)  For electric arc and electric induction metal melting furnaces,
sample only when metal is being meltedduring normal production
conditions, which may include, but are not limited to the following
cycles:  charging, melting, alloying, refining, slagging, and tapping.

	(5)  For scrap preheaters, sample only during normal production
conditions, which may include, but are not limited to the following
cycles:  charging, heating, and dischargingwhen scrap is being
preheated. 

	(6)  Determine the total mass of metal charged to the furnace or scrap
preheater during each performance test run and calculate the PM emission
rate using Equation 1 of this section:

			EFPM = CPM × ( Q/ Mcharge ) × (ttest/7000)				Eq. 1

Where:

EFPM =		Mass emission rate of PM, lb/ton;

CPM =		Concentration of PM measured during performance test run,
gr/dscf;

Q	=		Volumetric flow rate of exhaust gas, dry standard cubic feet per
minute (dscfm);

Mcharge	 =	Mass of metal charged during performance test run, tons

ttest	=	Duration of performance test run, minutes; and

7000	=	Unit conversion factor, grains per pound (gr/lb). 

	

(c)  To determine compliance with the applicable emissions limit for
total metal HAP in §63.7690(a)(1) through (6) for a metal melting
furnace, scrap preheater, pouring station, or pouring area, follow the
test methods and procedures in paragraphs (c)(1) through (56) of this
section.

	(1)  Determine the concentration of total metal HAP according to the
test methods in 40 CFR part 60, appendix A that are specified in
paragraphs (c)(1)(i) through (v) of this section.

	(i)  Method 1 or 1A to select sampling port locations and the number of
traverse points in each stack or duct.  Sampling sites must be located
at the outlet of the control device (or at the outlet of the emissions
source if no control device is present) prior to any releases to the
atmosphere.

	(ii)  Method 2, 2A, 2C, 2D, 2F, or 2G to determine the volumetric flow
rate of the stack gas.

	(iii)  Method 3, 3A, or 3B to determine the dry molecular weight of the
stack gas.

	(iv)  Method 4 to determine the moisture content of the stack gas.

	(v)  Method 29 to determine the total metal HAP concentration.

	(2)  Collect a minimum sample volume of 60 dscf of gas during each
total metal HAP sampling run.  A minimum of three valid test runs are
needed to comprise a performance test. 

	(3)  For cupola metal melting furnaces, sample only during times when
the cupola is on blast.

	(4)  For electric arc and electric induction metal melting furnaces,
sample only during normal production conditions, which may include, but
are not limited to the following cycles:  charging, melting, alloying,
refining, slagging, and tapping when metal is being melted.

	(5)  For scrap preheaters, sample only during normal production
conditions, which may include, but are not limited to the following
cycles:  charging, heating, and dischargingwhen scrap is being
preheated.  

	(6)  Determine the total mass of metal charged to the furnace or scrap
preheater during each performance test run and calculate the total metal
HAP emission rate using Equation 2 of this section:

			EFTMHAP = CTMHAP × ( Q/ Mcharge ) × (ttest/7000)			Eq. 2

Where:

EFTMHAP =	Emission rate of total metal HAP, lb/ton;

CTMHA{ =	Concentration of total metal HAP measured during performance
test run, gr/dscf;

Q	=		Volumentric flow rate of exhaust gas, dscfm

Mcharge	 =	Mass of metal charged during performance test run, tons

ttest	=	Duration of performance test run, minutes; and

7000	=	Unit conversion factor, gr/lb. 

	

(d)  To determine compliance with the opacity limit in §63.7690(a)(7)
for fugitive emissions from buildings or structures housing any iron and
steel foundry emissions source at the iron and steel foundry, follow the
procedures in paragraphs (d)(1) and (2) of this section.

	(1)  Using a certified observer, conduct each opacity test according to
the requirements in EPA Method 9 (40 CFR part 60, appendix A) and
§63.6(h)(5).   The certified observer may identify a limited number of
openings or vents that appear to have the highest opacities and perform
opacity observations on the identified openings or vents  in lieu of
performing observations for each opening or vent from the building or
structure.  Alternatively, a single opacity observation for the entire
building or structure may be performed, if the fugitive release points
afford such an observation.  

	(2)  During testing intervals when PM performance tests, if applicable,
are being conducted, Cconduct eachthe opacity test such that the opacity
observations overlap are recorded duringwith the PM performance tests. 

	(e)  To determine compliance with the applicable VOHAP emissions limit
in §63.7690(a)(8) for a cupola metal melting furnace or in
§63.7690(a)(9) for a scrap preheater, follow the test methods and
procedures in paragraphs (e)(1) through (4) of this section.

	(1)  Determine the VOHAP concentration for each test run according to
the test methods in 40 CFR part 60, appendix A that are specified in
paragraphs (e)(1)(i) through (v) of this section.

	(i)  Method 1 or 1A to select sampling port locations and the number of
traverse points in each stack or duct.  Sampling sites must be located
at the outlet of the control device (or at the outlet of the emissions
source if no control device is present) prior to any releases to the
atmosphere.

	(ii)  Method 2, 2A, 2C, 2D, 2F, or 2G to determine the volumetric flow
rate of the stack gas.

	(iii)  Method 3, 3A, or 3B to determine the dry molecular weight of the
stack gas.

	(iv)  Method 4 to determine the moisture content of the stack gas.

	(v)  Method 18 to determine the VOHAP concentration.  Alternatively,
you may use Method 25 to determine the concentration of total gaseous
nonmethane organics (TGNMO) or Method 25A to determine the concentration
of total organic compounds (TOC), using hexane as the calibration gas.

	(2)  Determine the average VOHAP, TGNMO, or TOC concentration using a
minimum of three valid test runs.  Each test run must include a minimum
of 60 continuous operating minutes.

	(3)  For a cupola metal melting furnace, correct the measured
concentration of VOHAP, TGNMO, or TOC for oxygen content in the gas
stream using Equation 1 3 of this section:

 

Where:

CVOHAP	=	Concentration of VOHAP in ppmv as measured by Method 18 in 40
CFR part 60, appendix A or the concentration of TGNMO or TOC in ppmv as
hexane as measured by Method 25 or 25A in 40 CFR part 60, appendix A;
and 

%O2	=		Oxygen concentration in gas stream, percent by volume (dry
basis).

	(4)  For a cupola metal melting furnace, measure the combustion zone
temperature of the combustion device with the CPMS required in
§63.7740(d) during each sampling run in 15-minute intervals.  Determine
and record the 15-minute average of the three runs.

	(f)  Follow the applicable procedures in paragraphs (f)(1) through (3)
of this section to determine compliance with the VOHAP emissions limit
in §63.7690(a)(10) for automated pallet cooling lines or automated
shakeout lines.

	(1)  Follow these procedures to demonstrate compliance by direct
measurement of total hydrocarbons (a surrogate for VOHAP) using a
volatile organic compound (VOC) CEMS.  

	(i)  Using the VOC CEMS required in §63.7740(g), measure and record
the concentration of total hydrocarbons (as hexane) for 180 continuous
operating minutes.  You must measure emissions at the outlet of the
control device (or at the outlet of the emissions source if no control
device is present) prior to any releases to the atmosphere.

	(ii)  Reduce the monitoring data to hourly averages as specified in
§63.8(g)(2).

	(iii)  Compute and record the 3-hour average of the monitoring data.

	(2)  As an alternative to the procedures in paragraph (f)(1) of this
section, you may demonstrate compliance with the VOHAP emissions limit
in §63.7690(a)(10) by establishing a site-specific TOC emissions limit
that is correlated to the VOHAP emissions limit according to the
procedures in paragraph (f)(2)(i) through (ix) of this section.

	(i)  Determine the VOHAP concentration for each test run according to
the test methods in 40 CFR part 60, appendix A that are specified in
paragraph (f)(2)(ii) through (vi) of this section.

	(ii)  Method 1 or 1A to select sampling port locations and the number
of traverse points in each stack or duct.  Sampling sites must be
located at the outlet of the control device (or at the outlet of the
emissions source if no control device is present) prior to any releases
to the atmosphere.

	(iii)  Method 2, 2A, 2C, 2D, 2F, or 2G to determine the volumetric flow
rate of the stack gas.

	(iv)  Method 3, 3A, or 3B to determine the dry molecular weight of the
stack gas.

	(v)  Method 4 to determine the moisture content of the stack gas.

	(vi)  Method 18 to determine the VOHAP concentration.  Alternatively,
you may use Method 25 to determine the concentration of TGNMO using
hexane as the calibration gas.

	(vii)  Using the CEMS required in §63.7740(g), measure and record the
concentration of total hydrocarbons (as hexane) during each of the
Method 18 (or Method 25) sampling runs.  You must measure emissions at
the outlet of the control device (or at the outlet of the emissions
source if no control device is present) prior to any releases to the
atmosphere.

	(viii)  Calculate the average VOHAP (or TGNMO) concentration for the
source test as the arithmetic average of the concentrations measured for
the individual test runs, and determine the average concentration of
total hydrocarbon (as hexane) as measured by the CEMS during all test
runs.

	(ix)  Calculate the site-specific VOC emissions limit using Equation 2
4 of this section:

 

Where:

CVOHAP,avg	=	Average concentration of VOHAP for the source test in ppmv
as measured by Method 18 in 40 CFR part 60, appendix A or the average
concentration of TGNMO for the source test in ppmv as hexane as measured
by Method 25 in 40 CFR part 60, appendix A; and 

CCEM		=		Average concentration of total hydrocarbons in ppmv as hexane
as measured using the CEMS during the source test.

	(3)  For two or more exhaust streams from one or more automated
conveyor and pallet cooling lines or automated shakeout lines, compute
the flow-weighted average concentration of VOHAP emissions for each
combination of exhaust streams using Equation 3 5 of this section:

 

Where:				

Cw =		Flow-weighted concentration of VOHAP or VOC, ppmv (as hexane);

Ci =		Concentration of VOHAP or VOC from exhaust stream “i”, ppmv
(as hexane);

n	=		Number of exhaust streams sampled; and

Qi =		Volumetric flow rate of effluent gas from exhaust stream “i,”
in dry standard cubic feet per minute (dscfm).

	(g)  To determine compliance with the emissions limit or standard in
§63.7690(a)(11) for a TEA cold box mold or core making line, follow the
test methods in 40 CFR part 60, appendix A, specified in paragraphs
(g)(1) through (4) of this section.

	(1)  Determine the TEA concentration for each test run according to the
test methods in 40 CFR part 60, appendix A that are specified in
paragraphs (g)(1)(i) through (v) of this section.

	(i)  Method 1 or 1A to select sampling port locations and the number of
traverse points in each stack or duct.  If you elect to meet the 99
percent reduction standard, sampling sites must be located both at the
inlet to the control device and at the outlet of the control device
prior to any releases to the atmosphere.  If you elect to meet the
concentration limit, the sampling site must be located at the outlet of
the control device (or at the outlet of the emissions source if no
control device is present) prior to any releases to the atmosphere.

	(ii)  Method 2, 2A, 2C, 2D, 2F, or 2G to determine the volumetric flow
rate of the stack gas.

	(iii)  Method 3, 3A, or 3B to determine the dry molecular weight of the
stack gas.

	(iv)  Method 4 to determine the moisture content of the stack gas.

	(v)  Method 18 to determine the TEA concentration.  Alternatively, you
may use NIOSH Method 2010 (incorporated by reference-see §63.14) to
determine the TEA concentration provided the performance requirements
outlined in Section 13.1 of EPA Method 18 are satisfied.  The Method 18
sampling option and time must be sufficiently long such that either the
TEA concentration in the field sample is at least 5 times the limit of
detection for the analytical method or the test results calculated using
the laboratory’s reported analytical detection limit for the specific
field samples are less than 1/5 of the applicable emissions limit.  When
using Method 18, tThe adsorbent tube approach, as described in Sections
8.2.4 of Method 18, may be required to achieve the necessary analytical
detection limits.  The sampling time must be at least 1 hour in all
cases.  

	(2)  If you use a wet acid scrubber , cConduct the test as soon as
practicable after adding fresh acid solution and the system has reached
normal operating conditions.

	(3)  If you use a wet acid scrubber that is subject to the operating
limit in §63.7690(b)(5)(ii) for pH level, determine the pH of the
scrubber blowdown using the procedures in paragraph (g)(3)(i) or (ii) of
this section.

	(i)  Measure the pH of the scrubber blowdown with the CPMS required in
§63.7740(f)(2) during each TEA sampling run in intervals of no more
than 15 minutes.  Determine and record the 3-hour average; or

	(ii)  Measure and record the pH level using the probe and meter
required in §63.7740(f)(2) once each sampling run.  Determine and
record the average pH level for the three runs.  							

	(4)  If you are subject to the 99 percent reduction standard, calculate
the mass emissions reduction using Equation 4 6 of this section:

                (Eq. 46)

Where:

Ei =	Mass emissions rate of TEA at control device inlet, kilograms per
hour (kg/hr); and

Eo =	Mass emissions rate of TEA at control device outlet, kg/hr.

	(h)  To determine compliance with the PM or total metal HAP emissions
limits in §63.7690(a)(1) through (6) when one or more regulated
emissions sources are combined with either another regulated emissions
source subject to a different emissions limit or other non-regulated
emissions sources, you may demonstrate compliance using one of the
procedures in paragraphs (h)(1) through (3) of this section. 

	(1)  Meet the most stringent applicable emissions limit for the
regulated emissions sources included in the combined emissions stream
for the combined emissions stream.

	(2)  Use the procedures in paragraphs (h)(2)(i) through (iii) of this
section.

	(i)  Determine the volumetric flow rate of the individual regulated
streams for which emissions limits apply.

	(ii)  Calculate the flow-weighted average emissions limit, considering
only the regulated streams, using Equation 3 5 of this section, except
Cw is the flow-weighted average emissions limit for PM or total metal
HAP in the exhaust stream, gr/dscf; and Ci is the concentration of PM or
total metal HAP in exhaust stream “i”, gr/dscf.

	(iii)  Meet the calculated flow-weighted average emissions limit for
the regulated emissions sources included in the combined emissions
stream for the combined emissions stream.

	(3)  Use the procedures in paragraphs (h)(3)(i) through (iii) of this
section.

	(i)  Determine the PM or total metal HAP concentration of each of the
regulated streams prior to the combination with other exhaust streams or
control device.

	(ii)  Measure the flow rate and PM or total metal HAP concentration of
the combined exhaust stream both before and after the control device and
calculate the mass removal efficiency of the control device using
Equation 4 6 of this section, except Ei is the mass emissions rate of PM
or total metal HAP at the control device inlet, lb/hr and Eo is the mass
emissions rate of PM or total metal HAP at the control device outlet,
lb/hr.

	(iii)  Meet the applicable emissions limit based on the calculated PM
or total metal HAP concentration for the regulated emissions source
using Equation 5 7 of this section: 

 

Where:

Creleased =	Calculated concentration of PM (or total metal HAP)
predicted to be released to the atmosphere from the regulated emissions
source, in gr/dscf; and

Ci =	Concentration of PM (or total metal HAP) in the uncontrolled
regulated exhaust stream, in gr/dscf.

	(i)  To determine compliance with an emission limit for situations when
multiple sources are controlled by a single control device, but only one
source operates at a time, or other situations that are not expressly
considered in paragraphs (b) through (h) of this section, a
site-specific test plan should be submitted to the Administrator for
approval according to the requirements in §63.7(c)(2) and (3).  

§63.7733  What procedures must I use to establish operating limits?

	(a)  For each capture system subject to operating limits in
§63.7690(b)(1)(ii), you must establish site-specific operating limits
in your operation and maintenance plan according to the procedures in
paragraphs (a)(1) through (3) of this section.

	(1)  Concurrent with applicable emissions and opacity tests, measure
and record values for each of the operating limit parameters in your
capture system operation and maintenance plan according to the
monitoring requirements in §63.7740(a).

	(2)  For any dampers that are manually set and remain at the same
position at all times the capture system is operating, the damper
position must be visually checked and recorded at the beginning and end
of each run.

	(3)  Review and record the monitoring data.  Identify and explain any
times the capture system operated outside the applicable operating
limits.

	(b)  For each wet scrubber subject to the operating limits in
§63.7690(b)(2) for pressure drop and scrubber water flow rate, you must
establish site-specific operating limits according to the procedures
specified in paragraphs (b)(1) and (2) of this section.

	(1)  Using the CPMS required in §63.7740(c), measure and record the
pressure drop and scrubber water flow rate in intervals of no more than
15 minutes during each PM test run.

	(2)  Compute and record the 3-hour average pressure drop and average
scrubber water flow rate for each valid sampling run in which the
applicable emissions limit is met.

	(c)  For each combustion device applied to emissions from a scrap
preheater or TEA cold box mold or core making line subject to the
operating limit in §63.7690(b)(4) for combustion zone temperature, you
must establish a site-specific operating limit according to the
procedures specified in paragraphs (c)(1) and (2) of this section.

	(1)  Using the CPMS required in §63.7740(e), measure and record the
combustion zone temperature during each sampling run in intervals of no
more than 15 minutes.

	(2)  Compute and record the 3-hour average combustion zone temperature
for each valid sampling run in which the applicable emissions limit is
met.

	(d)  For each acid wet scrubber subject to the operating limit in
§63.7690(b)(5), you must establish a site-specific operating limit for
scrubbing liquid flow rate according to the procedures specified in
paragraphs (d)(1) and (2) of this section.

	(1)  Using the CPMS required in §63.7740(f), measure and record the
scrubbing liquid flow rate during each TEA sampling run in intervals of
no more than 15 minutes.

	(2)  Compute and record the 3-hour average scrubbing liquid flow rate
for each valid sampling run in which the applicable emissions limit is
met. 

	(e)  You may change the operating limits for a capture system, wet
scrubber, acid wet scrubber, or combustion device if you meet the
requirements in paragraphs (e)(1) through (3) of this section.

	(1)  Submit a written notification to the Administrator of your request
to conduct a new performance test to revise the operating limit.

	(2)  Conduct a performance test to demonstrate compliance with the
applicable emissions limitation in §63.7690.

	(3)  Establish revised operating limits according to the applicable
procedures in paragraphs (a) through (d) of this section.

	(f)  You may use a previous performance test (conducted since December
22, 2002) to establish an operating limit provided the test meets the
requirements of this subpart.

§63.7734  How do I demonstrate initial compliance with the emissions
limitations that apply to me?

	(a)  You have demonstrated initial compliance with the emissions limits
in §63.7690(a) ifby meeting the applicable conditions in paragraphs
(a)(1) through (121) of this section.  When alternative emission
limitations are provided for a given emission source, you are not
restricted in the selection of which applicable alternative emission
limitation is used to demonstrate compliance.:

	(1)  For each electric arc metal melting furnace, electric induction
metal melting furnace, or scrap preheater at an existing iron and steel
foundry,

	(i)  The average PM concentration in the exhaust stream, determined
according to the performance test procedures in §63.7732(b), did not
exceed 0.005 gr/dscf; or

	(ii)  The average total metal HAP concentration in the exhaust stream,
determined according to the performance test procedures in §63.7732(c),
did not exceed 0.0004 gr/dscf.

	(2)  For each cupola metal melting furnace at an existing iron and
steel foundry,

	(i)  The average PM concentration in the exhaust stream, determined
according to the performance test procedures in §63.7732(b), did not
exceed 0.006 gr/dscf; or

	(ii)  The average total metal HAP concentration in the exhaust stream,
determined according to the performance test procedures in §63.7732(c),
did not exceed 0.0005 gr/dscf., or

	(iii)  The average PM mass emission rate, determined according to the
performance test procedures in §63.7732(b), did not exceed 0.10 lb/ton;
or

	(iv)  The average total metal HAP mass emission rate, determined
according to the performance test procedures in §63.7732(c), did not
exceed 0.008 lb/ton. 

	(3)  For each cupola metal melting furnace or electric arc metal
melting furnace at a new iron and steel foundry,

	(i)  The average PM concentration in the exhaust stream, determined
according to the performance test procedures in §63.7732(b), did not
exceed 0.002 gr/dscf; or

	(ii)  The average total metal HAP concentration in the exhaust stream,
determined according to the performance test procedures in §63.7732(c),
did not exceed 0.0002 gr/dscf.

	(4)  For each electric induction metal melting furnace or scrap
preheater at a new iron and steel foundry,

	(i)  The average PM concentration in the exhaust stream, determined
according to the performance test procedures in §63.7732(b), did not
exceed 0.001 gr/dscf; or

	(ii)  The average total metal HAP concentration in the exhaust stream,
determined according to the performance test procedures in §63.7732(c),
did not exceed 0.00008 gr/dscf.

	(5)  For each pouring station at an existing iron and steel foundry,

	(i)  The average PM concentration in the exhaust stream, measured
according to the performance test procedures in §63.7732(b), did not
exceed 0.010 gr/dscf; or

	(ii)  The average total metal HAP concentration in the exhaust stream,
determined according to the performance test procedures in §63.7732(c),
did not exceed 0.0008 gr/dscf.

	(6)  For each pouring area or pouring station at a new iron and steel
foundry,

	(i)  The average PM concentration in the exhaust stream, measured
according to the performance test procedures in §63.7732(b), did not
exceed 0.002 gr/dscf; or

	(ii)  The average total metal HAP concentration in the exhaust stream,
determined according to the performance test procedures in §63.7732(c),
did not exceed 0.0002 gr/dscf.

	(7)  For each building or structure housing any iron and steel foundry
emissions source at the iron and steel foundry, the opacity of fugitive
emissions from foundry operations discharged to the atmosphere,
determined according to the performance test procedures in §63.7732(d),
did not exceed 20 percent (6-minute average), except for one 6-minute
average per hour that did not exceed 27 percent opacity.

	(8)  For each cupola metal melting furnace at a new or existing iron
and steel foundry, the average VOHAP concentration, determined according
to the performance test procedures in §63.7732(e), did not exceed 20
ppmv corrected to 10 percent oxygen.

	(9)  For each scrap preheater at an existing iron and steel foundry
that does not meet the work practice standards in §63.7700(e)(1) or (2)
and for each scrap preheater at a new iron and steel foundry that does
not meet the work practice standard in §63.7700(f), the average VOHAP
concentration determined according to the performance test procedures in
§63.7732(e), did not exceed 20 ppmv.

	(10)  For one or more automated conveyor and pallet cooling lines that
use a sand mold system or automated shakeout lines that use a sand mold
system at a new foundry,

	(i)  You have reduced the data from the CEMS to 3-hour averages
according to the performance test procedures in §63.7732(f)(1) or (2);
and

	(ii)  The 3-hour flow-weighted average VOHAP concentration, measured
according to the performance test procedures in §63.7332(f)(1) or (2),
did not exceed 20 ppmv.

	(11)  For each TEA cold box mold or core making line in a new or
existing iron and steel foundry, the average TEA concentration,
determined according to the performance test procedures in §63.7732(g),
did not exceed 1 ppmv or was reduced by 99 percent.

	(b)  You have demonstrated initial compliance with the operating limits
in §63.7690(b) if:

	(1)  For each capture system subject to the operating limit in
§63.7690(b)(1)(ii),

	(i)  You have established appropriate site-specific operating limits in
your operation and maintenance plan according to the requirements in
§63.7710(b); and

	(ii)  You have a record of the operating parameter data measured during
the performance test in accordance with §63.7733(a); and

	(2)  For each wet scrubber subject to the operating limits in
§63.7690(b)(2) for pressure drop and scrubber water flow rate, you have
established appropriate site-specific operating limits and have a record
of the pressure drop and scrubber water flow rate measured during the
performance test in accordance with §63.7733(b). 

	(3)  For each combustion device subject to the operating limit in
§63.7690(b)(3) for combustion zone temperature, you have a record of
the combustion zone temperature measured during the performance test in
accordance with §63.7732(e)(4).

	(4)  For each combustion device subject to the operating limit in
§63.7690(b)(4) for combustion zone temperature, you have established
appropriate site-specific operating limits and have a record of the
combustion zone temperature measured during the performance test in
accordance with §63.7733(c).

	(5)  For each acid wet scrubber subject to the operating limits in
§63.7690(b)(5) for scrubbing liquid flow rate and scrubber blowdown pH,

	(i)  You have established appropriate site-specific operating limits
for the scrubbing liquid flow rate and have a record of the scrubbing
liquid flow rate measured during the performance test in accordance with
§63.7733(d); and

	(ii)  You have a record of the pH of the scrubbing liquid blowdown
measured during the performance test in accordance with §63.7732(g)(3).

§63.7735  How do I demonstrate initial compliance with the work
practice standards that apply to me?	

	(a)  For each iron and steel foundry subject to the certification
requirement in §63.7700(b), you have demonstrated initial compliance if
you have certified in your notification of compliance status that: “At
all times, your foundry will purchase and use only metal ingots, pig
iron, slitter, or other materials that do not include post-consumer
automotive body scrap, post-consumer engine blocks, post-consumer oil
filters, oily turnings, lead components, mercury switches, plastics, or
free organic liquids.” 

	(b)  For each iron and steel foundry subject to the requirements in
§63.7700(c) for a scrap inspection and selection plan, you have
demonstrated initial compliance if you have certified in your
notification of compliance status that:

	(1)  You have submitted a written plan to the Administrator for
approval according to the requirements in §63.7700(c); and

	(2)  You will operate at all times according to the plan requirements.

	(c)  For each furan warm box mold or core making line in a new or
existing foundry subject to the work practice standard in §63.7700(d),
you have demonstrated initial compliance if you have certified in your
notification of compliance status that:

	(1)  You will meet the no methanol requirement for the catalyst portion
of each binder chemical formulation; and

	(2)  You have records documenting your certification of compliance,
such as a material safety data sheet (provided that it contains
appropriate information), a certified product data sheet, or a
manufacturer’s hazardous air pollutant data sheet, onsite and
available for inspection.

	(d)  For each scrap preheater at an existing iron and steel foundry
subject to the work practice standard in §63.7700(e)(1) or (2), you
have demonstrated initial compliance if you have certified in your
notification of compliance status that:

	(1)  You have installed a gas-fired preheater where the flame directly
contacts the scrap charged, you will operate and maintain each gas-fired
scrap preheater such that the flame directly contacts the scrap charged,
and you have records documenting your certification of compliance that
are onsite and available for inspection; or

	(2)  You will charge only material that is subject to and in compliance
with the scrap certification requirements in §63.7700(b) and you have
records documenting your certification of compliance that are onsite and
available for inspection.

	(e)  For each scrap preheater at a new iron and steel foundry subject
to the work practice standard in §63.7700(f), you have demonstrated
initial compliance if you have certified in your notification of
compliance status that you will charge only material that is subject to
and in compliance with the scrap certification requirements in
§63.7700(b) and you have records documenting your certification of
compliance that are onsite and available for inspection.

§63.7736  How do I demonstrate initial compliance with the operation
and maintenance requirements that apply to me?

	(a)  For each capture system subject to an operating limit in
§63.7690(b), you have demonstrated initial compliance if you have met
the conditions in paragraphs (a)(1) and (2) of this section.

	(1)  You have certified in your notification of compliance status that:

	(i)  You have submitted the capture system operation and maintenance
plan to the Administrator for approval according to the requirements of
§63.7710(b); and

	(ii)  You will inspect, operate, and maintain each capture system
according to the procedures in the plan.

	(2)  You have certified in your performance test report that the system
operated during the test at the operating limits established in your
operation and maintenance plan.

	(b)  For each control device subject to an operating limit in
§63.7690(b), you have demonstrated initial compliance if you have
certified in your notification of compliance status that:

	(1)  You have submitted the control device operation and maintenance
plan to the Administrator for approval according to the requirements of
§63.7710(b); and

	(2)  You will inspect, operate, and maintain each control device
according to the procedures in the plan.

	(c)  For each bag leak detection system, you have demonstrated initial
compliance if you have certified in your notification of compliance
status that:

	(1)  You have submitted the bag leak detection system monitoring plan
information to the Administrator within the written O&M plan for
approval according to the requirements of §63.7710(b);  

	(2)  You will inspect, operate, and maintain each bag leak detection
system according to the procedures in the plan; and

	(3)  You will follow the corrective action procedures for bag leak
detection system alarms according to the requirements in the plan.

	(d)  For each pouring area and pouring station in a new or existing
foundry, you have demonstrated initial compliance if you have certified
in your notification of compliance status report that:

	(1)  You have submitted the mold vent ignition plan to the
Administrator for approval according to the requirements in
§63.7710(b); and

	(2)  You will follow the procedures for igniting mold vent gases
according to the requirements in the plan.

Continuous Compliance Requirements	

§63.7740  What are my monitoring requirements?

	(a)  For each capture system subject to an operating limit in
§63.7690(b)(1), you must install, operate, and maintain a CPMS
according to the requirements in §63.7741(a) and the requirements in
paragraphs (a)(1) and (2) of this section.

	(1)  If you use a flow measurement device to monitor the operating
limit parameter, you must at all times monitor the hourly average rate
(e.g., the hourly average actual volumetric flow rate through each
separately ducted hood or the average hourly total volumetric flow rate
at the inlet to the control device).

	(2)  Dampers that are manually set and remain in the same position are
exempt from the requirement to install and operate a CPMS.  If dampers
are not manually set and remain in the same position, you must make a
visual check at least once every 24 hours to verify that each damper for
the capture system is in the same position as during the initial
performance test.

	(b)  For each negative pressure baghouse or positive pressure baghouse
equipped with a stack that is applied to meet any PM or total metal HAP
emissions limitation in this subpart, you must at all times monitor the
relative change in PM loadings using a bag leak detection system
according to the requirements in §63.7741(b).

	(c) For each baghouse, regardless of type, that is applied to meet any
PM or total metal HAP emissions limitation in this subpart, you mustand
conduct inspections at their specified frequencies according to the
requirements specified in paragraphs (bc)(1) through (8) of this
section.

  	(1)  Monitor the pressure drop across each baghouse cell each day to
ensure pressure drop is within the normal operating range identified in
the manual.

	(2)  Confirm that dust is being removed from hoppers through weekly
visual inspections or other means of ensuring the proper functioning of
removal mechanisms.

	(3)  Check the compressed air supply for pulse-jet baghouses each day.

	(4)  Monitor cleaning cycles to ensure proper operation using an
appropriate methodology.

	(5)  Check bag cleaning mechanisms for proper functioning through
monthly visual inspection or equivalent means.

	(6)  Make monthly visual checks of bag tension on reverse air and
shaker-type baghouses to ensure that bags are not kinked (kneed or bent)
or lying on their sides.  You do not have to make this check for
shaker-type baghouses using self-tensioning (spring-loaded) devices.

	(7)  Confirm the physical integrity of the baghouse through quarterly
visual inspections of the baghouse interior for air leaks.

	(8)  Inspect fans for wear, material buildup, and corrosion through
quarterly visual inspections, vibration detectors, or equivalent means.

	(cd)  For each wet scrubber subject to the operating limits in
§63.7690(b)(2), you must at all times monitor the 3-hour average
pressure drop and scrubber water flow rate using CPMS according to the
requirements in §63.7741(c).

	(de)  For each combustion device subject to the operating limit in
§63.7690(b)(3), you must at all times monitor the 15-minute average
combustion zone temperature using a CPMS according to the requirements
of §63.7741(d).

	(ef)  For each combustion device subject to the operating limit in
§63.7690(b)(4), you must at all times monitor the 3-hour average
combustion zone temperature using CPMS according to the requirements in
§63.7741(d).

	(fg)  For each wet acid scrubber subject to the operating limits in
§63.7690(b)(5),

	(1)  You must at all times monitor the 3-hour average scrubbing liquid
flow rate using CPMS according to the requirements of §63.7741(e)(1);
and

	(2)  You must at all times monitor the 3-hour average pH of the
scrubber blowdown using CPMS according to the requirements in
§63.7741(e)(2) or measure and record the pH of the scrubber blowdown
once per production cycle using a pH probe and meter according to the
requirements in §63.7741(e)(3).

	(gh)  For one or more automated conveyor and pallet cooling lines and
automated shakeout lines at a new iron and steel foundry subject to the
VOHAP emissions limit in §63.7690(a)(10), you must at all times monitor
the 3-hour average VOHAP concentration using a CEMS according to the
requirements of §63.7741(g).

§63.7741  What are the installation, operation, and maintenance
requirements for my monitors?

	(a)  For each capture system subject to an operating limit in
§63.7690(b)(1), you must install, operate, and maintain each CPMS
according to the requirements in paragraphs (a)(1) through (3) of this
section.

	(1)  If you use a flow measurement device to monitor an operating limit
parameter for a capture system, you must meet the requirements in
paragraphs (a)(1)(i) through (iv) of this section.

	(i)  Locate the flow sensor and other necessary equipment such as
straightening vanes in a position that provides a representative flow
and that reduces swirling flow or abnormal velocity distributions due to
upstream and downstream disturbances.

	(ii)  Use a flow sensor with a minimum measurement sensitivity of 2
percent of the flow rate.

	(iii)  Conduct a flow sensor calibration check at least semiannually.

	(iv)  At least monthly, visually inspect all components, including for
integrity, all electrical connections for continuity, and all mechanical
connections, for leakageproper functioning. 

	(2)  If you use a pressure measurement device to monitor the operating
limit parameter for a capture system, you must meet the requirements in
paragraphs (a)(2)(i) through (vi) of this section.

	(i)  Locate the pressure sensor(s) in or as close as possible to a
position that provides a representative measurement of the pressure and
that minimizes or eliminates pulsating pressure, vibration, and internal
and external corrosion.

	(ii)  Use a gauge with a minimum measurement sensitivity of 0.5 inch of
water or a transducer with a minimum measurement sensitivity of 1
percent of the pressure range.

	(iii)  Check the pressure tap for pluggage daily.  If a
“non-clogging” pressure tap is used, check for pluggage monthly. 

	(iv)  Using a manometer or equivalent device such as a magnahelic or
other pressure indicating transmitter, check gauge calibration quarterly
and transducer calibration monthlyquarterly. 

	(v)  Conduct calibration checks any time the sensor exceeds the
manufacturer’s specified maximum operating pressure range, or install
a new pressure sensor.

	(vi)  At least monthly, visually inspect all components for integrity,
including all electrical connections for continuity, and mechanical
connections, for proper functioning. 

all mechanical connections for leakage.

	(3)  Record the results of each inspection, calibration, and validation
check.

	(b)  For each negative pressure baghouse or positive pressure baghouse
equipped with a stack that is applied to meet any PM or total metal HAP
emissions limitation in this subpart, yYou must install, operate, and
maintain a bag leak detection system according to the requirements in
paragraphs (b)(1) through (7) of this section. 

	(1)  The system must be certified by the manufacturer to be capable of
detecting emissions of particulate matter at concentrations of 10
milligrams per actual cubic meter (0.0044 grains per actual cubic foot)
or less.

	(2)  The bag leak detection system sensor must provide output of
relative particulate matter loadings and the owner or operator shall
continuously record the output from the bag leak detection system using
electronic or other means (e.g., using a strip chart recorder or a data
logger).

	(3)  The system must be equipped with an alarm that will sound when an
increase in relative particulate loadings is detected over the alarm set
point established in the operation and maintenance plan, and the alarm
must be located such that it can be heard by the appropriate plant
personnel.

	(4)  The initial adjustment of the system must, at minimum, consist of
establishing the baseline output by adjusting the sensitivity (range)
and the averaging period of the device, and establishing the alarm set
points and the alarm delay time (if applicable).

	(5)  Following the initial adjustment, do not adjust the sensitivity or
range, averaging period, alarm set point, or alarm delay time without
approval from the Administrator.  Except, once per quarter, you may
adjust the sensitivity of the bag leak detection system to account for
seasonable effects including temperature and humidity according to the
procedures in the operation and maintenance plan required by
§63.7710(b).

	(6)  For negative pressure, induced air baghouses, and positive
pressure baghouses that are discharged to the atmosphere through a
stack, the bag leak detector sensor must be installed downstream of the
baghouse and upstream of any wet scrubber.

	(7)  Where multiple detectors are required, the system’s
instrumentation and alarm may be shared among detectors.

	(c)  For each wet scrubber subject to the operating limits in
§63.7690(b)(2), you must install and maintain CPMS to measure and
record the pressure drop and scrubber water flow rate according to the
requirements in paragraphs (c)(1) and (2) of this section.

	(1)  For each CPMS for pressure drop you must:

	(i)  Locate the pressure sensor in or as close as possible to a
position that provides a representative measurement of the pressure drop
and that minimizes or eliminates pulsating pressure, vibration, and
internal and external corrosion.

	(ii)  Use a gauge with a minimum measurement sensitivity of 0.5 inch of
water or a transducer with a minimum measurement sensitivity of 1
percent of the pressure range.

	(iii)  Check the pressure tap for pluggage daily.  If a
“non-clogging” pressure tap is used, check for pluggage monthly. 

	(iv)  Using a manometer or equivalent device such as a magnahelic or
other pressure indicating transmitter, check gauge and transducer
calibration quarterlyUsing a manometer, check gauge calibration
quarterly and transducer calibration monthly.

	(v)  Conduct calibration checks any time the sensor exceeds the
manufacturer’s specified maximum operating pressure range, or install
a new pressure sensor.

	(vi)  At least monthly, visually inspect all components for integrity,
including all electrical connections for continuity, and mechanical
connections, for proper functioning. 

all mechanical connections for leakage.

	(2)  For each CPMS for scrubber liquid flow rate, you must:

	(i)  Locate the flow sensor and other necessary equipment in a position
that provides a representative flow and that reduces swirling flow or
abnormal velocity distributions due to upstream and downstream
disturbances. 

	(ii)  Use a flow sensor with a minimum measurement sensitivity of 2
percent of the flow rate.

	(iii)  Conduct a flow sensor calibration check at least semiannually
according to the manufacturer’s instructions.

	(iv)  At least monthly, visually inspect all components, including all
electrical and mechanical connections, for proper functioning inspect
all components for integrity, all electrical connections for continuity,
and all mechanical connections for leakage.

	(d)  For each combustion device subject to the operating limit in
§63.7690(b)(3) or (4), you must install and maintain a CPMS to measure
and record the combustion zone temperature according to the requirements
in paragraphs (d)(1) through (8) of this section.

	(1)  Locate the temperature sensor in a position that provides a
representative temperature.

	(2)  For a noncryogenic temperature range, use a temperature sensor
with a minimum tolerance of 2.2ºC or 0.75 percent of the temperature
value, whichever is larger.

	(3)  For a cryogenic temperature range, use a temperature sensor with a
minimum tolerance of 2.2ºC or 2 percent of the temperature value,
whichever is larger.

	(4)  Shield the temperature sensor system from electromagnetic
interference and chemical contaminants.

	(5)  If you use a chart recorder, it must have a sensitivity in the
minor division of at least 20ºF.

	(6)  Perform an electronic calibration at least semiannually according
to the procedures in the manufacturer’s owners manual.  Following the
electronic calibration, conduct a temperature sensor validation check,
in which a second or redundant temperature sensor placed nearby the
process temperature sensor must yield a reading within 16.7ºC of the
process temperature sensor’s reading.

	(7)  Conduct calibration and validation checks any time the sensor
exceeds the manufacturer’s specified maximum operating temperature
range, or install a new temperature sensor.

	(8)  At least monthly, visually inspect all components, including all
electrical and mechanical connections, for proper functioninginspect all
components for integrity and all electrical connections for continuity,
oxidation, and galvanic corrosion.

	(e)  For each wet acid scrubber subject to the operating limits in
§63.7690(b)(5), you must:

	(1)  Install and maintain CPMS to measure and record the scrubbing
liquid flow rate according to the requirements in paragraph (c)(2) of
this section; and

	(2)  Install and maintain CPMS to measure and record the pH of the
scrubber blowdown according to the requirements in paragraph (e)(2)(i)
through (iv) of this section.

	(i)  Locate the pH sensor in a position that provides a representative
measurement of the pH and that minimizes or eliminates internal and
external corrosion.

	(ii)  Use a gauge with a minimum measurement sensitivity of 0.1 pH or a
transducer with a minimum measurement sensitivity of 5 percent of the pH
range.

	(iii)  Check gauge calibration quarterly and transducer calibration
monthly using a manual pH gauge.

	(iv)  At least monthly, visually inspect all components, including all
electrical and mechanical connections, for proper functioninginspect all
components for integrity, all electrical connections for continuity, and
all mechanical connections for leakage.

	(3)  As an alternative to the CPMS required in paragraph (e)(2) of this
section, you may use a pH probe to extract a sample for analysis by a pH
meter that meets the requirements in paragraphs (e)(3)(i) through (iii)
of this section.

	(i)  The pH meter must have a range of at least 1 to 5 or more;

	(ii) The pH meter must have a accuracy of +0.1; and

	(iii)  The pH meter must have a resolution of at least 0.1 pH. 

	(f)  You must operate each CPMS used to meet the requirements of this
subpart according to the requirements specified in paragraphs (f)(1)
through (3) of this section.

	(1)  Each CPMS must complete a minimum of one cycle of operation for
each successive 15-minute period.  You must have a minimum of three of
the required four data points to constitute a valid hour of data.

	(2)  Each CPMS must have valid hourly data for 100 percent of every
averaging period.

	(3)  Each CPMS must determine and record the hourly average of all
recorded readings and the 3-hour average of all recorded readings.

 	(g)  For each automated conveyor and pallet cooling line and automated
shakeout line at a new iron and steel foundry subject to the VOHAP
emissions limit in §63.7690(a)(10), you must install, operate, and
maintain a CEMS to measure and record the concentration of VOHAP
emissions according to the requirements in paragraphs (g)(1) through (3)
of this section.

	(1)  You must install, operate, and maintain each CEMS according to
Performance Specification 8 in 40 CFR part 60, appendix B.

	(2)  You must conduct a performance evaluation of each CEMS according
to the requirements of §63.8 and Performance Specification 8 in 40 CFR
part 60, appendix B.

	(3)  You must operate each CEMS according to the requirements specified
in paragraph (g)(3)(i) through (iv) of this section.

	(i)  As specified in §63.8(c)(4)(ii), each CEMS must complete a
minimum of one cycle of operation (sampling, analyzing, and data
recording) for each successive 15-minute period.

	(ii)  You must reduce CEMS data as specified in §63.8(g)(2). 

	(iii)  Each CEMS must determine and record the 3-hour average emissions
using all the hourly averages collected for periods during which the
CEMS is not out-of-control.

Record the results of each inspection, calibration, and validation
check.

§63.7742  How do I monitor and collect data to demonstrate continuous
compliance?

	(a)  Except for monitoring malfunctions, associated repairs, and
required quality assurance or control activities (including as
applicable, calibration checks and required zero and span adjustments),
you must monitor continuously (or collect data at all required
intervals) any time a source of emissions is operating.

	(b)  You may not use data recorded during monitoring malfunctions,
associated repairs, and required quality assurance or control activities
in data averages and calculations used to report emissions or operating
levels or to fulfill a minimum data availability requirement, if
applicable.  You must use all the data collected during all other
periods in assessing compliance.

	(c)  A monitoring malfunction is any sudden, infrequent, not reasonably
preventable failure of the monitoring system to provide valid data. 
Monitoring failures that are caused in part by poor maintenance or
careless operation are not malfunctions.

§63.7743  How do I demonstrate continuous compliance with the emissions
limitations that apply to me?

	(a)  You must demonstrate continuous compliance by meeting the
applicable conditions in paragraphs (a)(1) through (12) of this section.
 When alternative emission limitations are provided for a given emission
source, you must comply with the alternative emission limitation most
recently selected as your compliance alternative..:

	(1)  For each electric arc metal melting furnace, electric induction
metal melting furnace, or scrap preheater at an existing iron and steel
foundry,

	(i)  Maintaining the average PM concentration in the exhaust stream at
or below 0.005 gr/dscf; or

	(ii)  Maintaining the average total metal HAP concentration in the
exhaust stream at or below 0.0004 gr/dscf.

	(2)  For each cupola metal melting furnace at an existing iron and
steel foundry,

	(i)  Maintaining the average PM concentration in the exhaust stream at
or below 0.006 gr/dscf; or

	(ii)  Maintaining the average total metal HAP concentration in the
exhaust stream at or below 0.0005 gr/dscf, or.   	

	(iii)  Maintaining the average PM mass emission rate at or below 0.10
lb/ton; or

	(iv)  Maintaining the average total metal HAP mass emission rate at or
below 0.008 lb/ton. 

	(3)  For each cupola metal melting furnace or electric arc metal
melting furnace at new iron and steel foundry,

	(i)  Maintaining the average PM concentration in the exhaust stream at
or below 0.002 gr/dscf; or

	(ii)  Maintaining the average total metal HAP concentration in the
exhaust stream at or below 0.0002 gr/dscf. 

	(4)  For each electric induction metal melting furnace or scrap
preheater at a new iron and steel foundry,

	(i)  Maintaining the average PM concentration in the exhaust stream at
or below 0.001 gr/dscf; or

	(ii)  Maintaining the average total metal HAP concentration in the
exhaust stream at or below 0.00008 gr/dscf.

	(5)  For each pouring station at an existing iron and steel foundry,

	(i)  Maintaining the average PM concentration in the exhaust stream at
or below 0.010 gr/dscf; or

	(ii)  Maintaining the average total metal HAP concentration in the
exhaust stream at or below 0.0008 gr/dscf.

	(6)  For each pouring area or pouring station at a new iron and steel
foundry, 

	(i)  Maintaining the average PM concentration in the exhaust stream at
or below 0.002 gr/dscf; or

	(ii)  Maintaining the average total metal HAP concentration in the
exhaust stream at or below 0.0002 gr/dscf.

	(7)  For each building or structure housing any iron and steel foundry
emissions source at the iron and steel foundry, maintaining the opacity
of any fugitive emissions from foundry operations discharged to the
atmosphere at or below 20 percent opacity (6-minute average), except for
one 6-minute average per hour that does not exceed 27 percent opacity.

	(8)  For each cupola metal melting furnace at a new or existing iron
and steel foundry, maintaining the average VOHAP concentration in the
exhaust stream at or below 20 ppmv corrected to 10 percent oxygen.

	(9)  For each scrap preheater at an existing new iron and steel foundry
that does not comply with the work practice standard in §63.7700(e)(1)
or (2) and for each scrap preheater at a new iron and steel foundry that
does not comply with the work practice standard in §63.7700(f),
maintaining the average VOHAP concentration in the exhaust stream at or
below 20 ppmv.

  	(10)  For one or more automated conveyor and pallet cooling lines or
automated shakeout lines that use a sand mold system at a new iron and
steel foundry, 

	(i)  Maintaining the 3-hour flow-weighted average VOHAP concentration
in the exhaust stream at or below 20 ppmv.

  	(ii)  Inspecting and maintaining each CEMS according to the
requirements of §63.7741(g) and recording all information needed to
document conformance with these requirements; and

	(iv)  Collecting and reducing monitoring data for according to the
requirements of §63.7741(g) and recording all information needed to
document conformance with these requirements.

	(11)  For each TEA cold box mold or core making line at a new or
existing iron and steel foundry, maintaining a 99 percent reduction in
the VOHAP concentration in the exhaust stream or maintaining the average
VOHAP concentration in the exhaust stream at or below 1 ppmv.

	(12)  Conducting subsequent performance tests at least every 5 years
for each emissions source subject to an emissions limit for PM, total
metal HAP, VOHAP, or TEA in §63.7690(a) and subsequent performance
tests at least every 6 months for each building or structure subject to
the opacity limit in §63.7690(a)(7).

	(b)  You must demonstrate continuous compliance for each capture system
subject to an operating limit in §63.7690(b)(1) by meeting the
requirements in paragraphs (b)(1) and (2) of this section.

	(1)  Operating the capture system at or above the lowest values or
settings established for the operating limits in your operation and
maintenance plan; and

	(2)  Monitoring the capture system according to the requirements in
§63.7740(a) and collecting, reducing, and recording the monitoring data
for each of the operating limit parameters according to the applicable
requirements in this subpart.

	(c)  For each baghouse equipped with a bag leak detection system,

	(1)  Inspecting and maintaining each baghouse according to the
requirements of §63.7740(c)(1) through (8) and recording all
information needed to document conformance with these
requirements.Maintaining records of the times the bag leak detection
system alarm sounded, and for each valid alarm, the time you initiated
corrective action, the corrective action taken, and the date on which
corrective action was completed; and

	(2)  If the baghouse is equipped with a bag leak detection system,
maintaining records of the times the bag leak detection system alarm
sounded, and for each valid alarm, the time you initiated corrective
action, the corrective action taken, and the date on which corrective
action was completedInspecting and maintaining each baghouse according
to the requirements of §63.7740(b)(1) through (8) and recording all
information needed to document conformance with these requirements.

	(d)  For each wet scrubber that is subject to the operating limits in
§63.7690(b)(2), you must demonstrate continuous compliance by:

	(1)  Maintaining the 3-hour average pressure drop and 3-hour average
scrubber water flow rate at levels no lower than those established
during the initial or subsequent performance test;

	(2)  Inspecting and maintaining each CPMS according to the requirements
of §63.7741(c) and recording all information needed to document
conformance with these requirements; and

	(3)  Collecting and reducing monitoring data for pressure drop and
scrubber water flow rate according to the requirements of §63.7741(f)
and recording all information needed to document conformance with these
requirements.

	(e)  For each combustion device that is subject to the operating limit
in §63.7690(b)(3), you must demonstrate continuous compliance by:

F;

	(2)  Inspecting and maintaining each CPMS according to the requirements
of §63.7741(d) and recording all information needed to document
conformance with these requirements; and

	(3)  Collecting and reducing monitoring data for combustion zone
temperature according to the requirements of §63.7741(f) and recording
all information needed to document conformance with these requirements.

	(f)  For each combustion device that is subject to the operating limit
in §63.7690(b)(4), you must demonstrate continuous compliance by:

	(1)  Maintaining the 3-hour average combustion zone temperature at a
level no lower that established during the initial or subsequent
performance test;

	(2)  Inspecting and maintaining each CPMS according to the requirements
of §63.7741(d) and recording all information needed to document
conformance with these requirements; and

	(3)  Collecting and reducing monitoring data for combustion zone
temperature according to the requirements of §63.7741(f) and recording
all information needed to document conformance with these requirements.

	(g)  For each acid wet scrubber subject to the operating limits in
§63.7690(b)(5), you must demonstrate continuous compliance by:

	(1)  Maintaining the 3-hour average scrubbing liquid flow rate at a
level no lower than the level established during the initial or
subsequent performance test;

	(2)  Maintaining the 3-hour average pH of the scrubber blowdown at a
level no higher than 4.5 (if measured by a CPMS) or maintaining the pH
level of the scrubber blowdown during each production shift no higher
than 4.5;

	(3)  Inspecting and maintaining each CPMS according to the requirements
of §63.7741(e) and recording all information needed to document
conformance with these requirements; and

	(4)  Collecting and reducing monitoring data for scrubbing liquid flow
rate and scrubber blowdown pH according to the requirements of
§63.7741(f) and recording all information needed to document
conformance with these requirements.  If the pH level of the scrubber
blowdown is measured by a probe and meter, you must demonstrate
continuous compliance by maintaining records that document the date,
time, and results of each sample taken for each production shift.

§63.7744  How do I demonstrate continuous compliance with the work
practice standards that apply to me?

	(a)  You must maintain records that document continuous compliance with
the certification requirements in §63.7700(b) or with the procedures in
your scrap selection and inspection plan required in §63.7700(c).  Your
records documenting compliance with the scrap selection and inspection
plan must include an copy (kept onsite) of the procedures used by the
scrap supplier for either removing accessible mercury switches or for
purchasing automobile bodies that have had mercury switches removed, as
applicable.

	(b)  You must keep records of the chemical composition of all catalyst
binder formulations applied in each furan warm box mold or core making
line at a new or existing iron and steel foundry to demonstrate
continuous compliance with the requirements in §63.7700(d). 

	(c)  For a scrap preheater at an existing iron and steel foundry, you
must operate and maintain each gas-fired preheater such that the flame
directly contacts the scrap charged to demonstrate continuous compliance
with the requirement §63.7700(e)(1).  If you choose to meet the work
practice standard in §63.7700(e)(2), you must keep records to document
that the scrap preheater charges only material that is subject to and in
compliance with the scrap certification requirements in §63.7700(b).

	(d)  For a scrap preheater at a new iron and steel foundry, you must
keep records to document that each scrap preheater charges only material
that is subject to and in compliance with the scrap certification
requirements in §63.7700(b) to demonstrate continuous compliance with
the requirement in §63.7700(f). 

§63.7745  How do I demonstrate continuous compliance with the operation
and maintenance requirements that apply to me?

	(a)  For each capture system and control device for an emissions source
subject to an emissions limit in §63.7690(a), you must demonstrate
continuous compliance with the operation and maintenance requirements of
§63.7710 by:

	(1)  Making monthly inspections of capture systems and initiating
corrective action according to §63.7710(b)(1) and recording all
information needed to document conformance with these requirements;

	(2)  Performing preventative maintenance for each control device
according to the preventive maintenance plan required by §63.7710(b)(3)
and recording all information needed to document conformance with these
requirements;

	(3)  Operating and maintaining each bag leak detection system according
to the site-specific monitoring plan required by §63.7710(b)(4) and
recording all information needed to demonstrate conformance with these
requirements; 

	(3)  Initiating and completing corrective action for a bag leak
detection system alarm according to the corrective action plan required
by §63.7710(b)(5) and recording all information needed to document
conformance with these requirements; and

	(4)  Igniting gases from mold vents according to the procedures in the
plan required by §63.7710(b)(6).  (Any instance where you fail to
follow the procedures is a deviation that must be included in your
semiannual compliance report.)

	(b)  You must maintain a current copy of the operation and maintenance
plans required by §63.7710(b) onsite and available for inspection upon
request.  You must keep the plans for the life of the iron and steel
foundry or until the iron and steel foundry is no longer subject to the
requirements of this subpart. 

§63.7746  What other requirements must I meet to demonstrate continuous
compliance?

	(a)  Deviations.  You must report each instance in which you did not
meet each emissions limitation in §63.7690 (including each operating
limit) that applies to you.  This requirement includes periods of
startup, shutdown, and malfunction.  You also must report each instance
in which you did not meet each work practice standard in §63.7700 and
each operation and maintenance requirement of §63.7710 that applies to
you.  These instances are deviations from the emissions limitations,
work practice standards, and operation and maintenance requirements in
this subpart.  These deviations must be reported according to the
requirements of §63.7751. 

	(b)  Startups, shutdowns, and malfunctions.  During periods of startup,
shutdown, and malfunction, you must operate in accordance with your
startup, shutdown, and malfunction plan.

	(1)  Consistent with the requirements of §§63.6(e) and 63.7(e)(1),
deviations that occur during a period of startup, shutdown, or
malfunction are not violations if you demonstrate to the
Administrator’s satisfaction that you were operating in accordance
with the startup, shutdown, and malfunction plan.

	(2)  The Administrator will determine whether deviations that occur
during a period of startup, shutdown, or malfunction are violations
according to the provisions in §63.6(e).

§63.7747  How do I apply for alternative monitoring requirements for a
continuous emissions monitoring system?

	(a)  You may request an alternative monitoring method to demonstrate
compliance with the VOHAP emissions limits in §63.7690(a)(10) for
automated pallet cooling lines or automated shakeout lines at a new iron
and steel foundry according to the procedures in this section.

	(b)  You can request approval to use an alternative monitoring method
in the notification of construction or reconstruction for new sources,
or at any time.

	(c)  You must submit a monitoring plan that includes a description of
the control technique or pollution prevention technique, a description
of the continuous monitoring system or method including appropriate
operating parameters that will be monitored, test results demonstrating
compliance with the emissions limit, operating limit(s) (if applicable)
determined according to the test results, and the frequency of measuring
and recording to establish continuous compliance.  If applicable, you
must also include operation and maintenance requirements for the
monitors. 

	(d)  The monitoring plan is subject to approval by the Administrator. 
Use of the alternative monitoring method must not begin until approval
is granted by the Administrator.

Notifications, Reports, and Records

§63.7750  What notifications must I submit and when?

	(a)  You must submit all of the notifications required by
§§63.6(h)(4) and (5), 63.7(b) and (c); 63.8(e); 63.8(f)(4) and (6);
63.9(b) through (h) that apply to you by the specified dates. 

	(b)  As specified in §63.9(b)(2), if you start up your iron and steel
foundry before April 22, 2004, you must submit your initial notification
no later than August 20, 2004. 

	(c) If you start up your new iron and steel foundry on or after April
22, 2004, you must submit your initial notification no later than 120
calendar days after you become subject to this subpart.		

	(d)  If you are required to conduct a performance test, you must submit
a notification of intent to conduct a performance test at least 60
calendar days before the performance test is scheduled to begin as
required by §63.7(b)(1). 

	(e)  If you are required to conduct a performance test or other initial
compliance demonstration, you must submit a notification of compliance
status according to the requirements of §63.9(h)(2)(ii).  For opacity
performance tests, the notification of compliance status may be
submitted with the semiannual compliance report in §63.7751(a) and (b)
or the semiannual Part 70 Monitoring report in §63.7551(d).  

	(1)  For each initial compliance demonstration that does not include a
performance test, you must submit the notification of compliance status
before the close of business on the 30th calendar day following
completion of the initial compliance demonstration.

	(2)  For each initial compliance demonstration that does include a
performance test, you must submit the notification of compliance status,
including the performance test results, before the close of business on
the 60th calendar day following the completion of the performance test
according to the requirement specified in §63.10(d)(2).

§63.7751  What reports must I submit and when?

	(a)  Compliance report due dates.  Unless the Administrator has
approved a different schedule, you must submit a semiannual compliance
report to your permitting authority according to the requirements
specified in paragraphs (a)(1) through (5) of this section.

	(1)  The first compliance report must cover the period beginning on the
compliance date that is specified for your iron and steel foundry by
§63.7683 and ending on June 30 or December 31, whichever date comes
first after the compliance date that is specified for your iron and
steel foundry.

	(2)  The first compliance report must be postmarked or delivered no
later than July 31 or January 31, whichever date comes first after your
first compliance report is due.

	(3)  Each subsequent compliance report must cover the semiannual
reporting period from January 1 through June 30 or the semiannual
reporting period from July 1 through December 31.

	(4)  Each subsequent compliance report must be postmarked or delivered
no later than July 31 or January 31, whichever date comes first after
the end of the semiannual reporting period.

	(5)  For each iron and steel foundry that is subject to permitting
regulations pursuant to 40 CFR part 70 or 40 CFR part 71, and if the
permitting authority has established dates for submitting semiannual
reports pursuant to 40 CFR 70.6(a)(3)(iii)(A) or 40 CFR
71.6(a)(3)(iii)(A), you may submit the first and subsequent compliance
reports according to the dates the permitting authority has established
instead of the dates specified in paragraphs (a)(1) through (4) of this
section.

	(b)  Compliance report contents.  Each compliance report must include
the information specified in paragraphs (b)(1) through (3) of this
section and, as applicable, paragraphs (b)(4) through (8) of this
section.

	(1)  Company name and address.

	(2)  Statement by a responsible official, with that official’s name,
title, and signature, certifying the truth, accuracy, and completeness
of the content of the report.

	(3)  Date of report and beginning and ending dates of the reporting
period.

	(4)  If you had a startup, shutdown, or malfunction during the
reporting period and you took action consistent with your startup,
shutdown, and malfunction plan, the compliance report must include the
information in §63.10(d)(5)(i).

	(5)  If there were no deviations from any emissions limitations
(including operating limit), work practice standards, or operation and
maintenance requirements, a statement that there were no deviations from
the emissions limitations, work practice standards, or operation and
maintenance requirements during the reporting period.

	(6)  If there were no periods during which a continuous monitoring
system (including a CPMS or CEMS) was out-of-control as specified by
§63.8(c)(7), a statement that there were no periods during which the
CPMS was out-of-control during the reporting period.

	(7)  For each deviation from an emissions limitation (including an
operating limit) that occurs at an iron and steel foundry for which you
are not using a continuous monitoring system (including a CPMS or CEMS)
to comply with an emissions limitation or work practice standard
required in this subpart, the compliance report must contain the
information specified in paragraphs (b)(1) through (4) and (b)(7)(i) and
(ii) of this section.  This requirement includes periods of startup,
shutdown, and malfunction.

	(i)  The total operating time of each emissions source  during the
reporting period.

	(ii)  Information on the number, duration, and cause of deviations
(including unknown cause) as applicable and the corrective action taken.
 

	(8)  For each deviation from an emissions limitation (including an
operating limit) or work practice standard occurring at an iron and
steel foundry where you are using a continuous monitoring system
(including a CPMS or CEMS) to comply with the emissions limitation or
work practice standard in this subpart, you must include the information
specified in paragraphs (b)(1) through (4) and (b)(8)(i) through (xi) of
this section.  This requirement includes periods of startup, shutdown,
and malfunction.

	(i)  The date and time that each malfunction started and stopped.

	(ii)  The date and time that each continuous monitoring system was
inoperative, except for zero (low-level) and high-level checks.

	(iii)  The date, time, and duration that each continuous monitoring
system was out-of-control, including the information in §63.8(c)(8).

	(iv)  The date and time that each deviation started and stopped, and
whether each deviation occurred during a period of startup, shutdown, or
malfunction or during another period.

	(v)  A summary of the total duration of the deviations during the
reporting period and the total duration as a percent of the total source
operating time during that reporting period.

	(vi)  A breakdown of the total duration of the deviations during the
reporting period into those that are due to startup, shutdown, control
equipment problems, process problems, other known causes, and unknown
causes.

	(vii)  A summary of the total duration of continuous monitoring system
downtime during the reporting period and the total duration of
continuous monitoring system downtime as a percent of the total source
operating time during the reporting period.

	(viii)  A brief description of the process units.

	(ix)  A brief description of the continuous monitoring system.

	(x)  The date of the latest continuous monitoring system certification
or audit.

	(xi)  A description of any changes in continuous monitoring systems,
processes, or controls since the last reporting period.

	(c)  Immediate startup, shutdown, and malfunction report.  If you had a
startup, shutdown, or malfunction during the semiannual reporting period
that was not consistent with your startup, shutdown, and malfunction
plan and the source exceeds any applicable emission limitation in
§63.7690, you must submit an immediate startup, shutdown, and
malfunction report according to the requirements of §63.10(d)(5)(ii).  

	(d)  Part 70 monitoring report.  If you have obtained a title V
operating permit for an iron and steel foundry pursuant to 40 CFR part
70 or 40 CFR part 71, you must report all deviations as defined in this
subpart in the semiannual monitoring report required by 40
CFR 70.6(a)(3)(iii)(A) or 40 CFR 71.6(a)(3)(iii)(A).  If you submit a
compliance report for an iron and steel foundry along with, or as part
of, the semiannual monitoring report required by 40 CFR
70.6(a)(3)(iii)(A) or 40 CFR 71.6(a)(3)(iii)(A), and the compliance
report includes all the required information concerning deviations from
any emissions limitation or operation and maintenance requirement in
this subpart, submission of the compliance report satisfies any
obligation to report the same deviations in the semiannual monitoring
report.  However, submission of a compliance report does not otherwise
affect any obligation you may have to report deviations from permit
requirements for an iron and steel foundry to your permitting authority.

§63.7752  What records must I keep?

	(a)  You must keep the records specified in paragraphs (a)(1) through
(4) of this section:

	(1)  A copy of each notification and report that you submitted to
comply with this subpart, including all documentation supporting any
initial notification or notification of compliance status that you
submitted, according to the requirements of §63.10(b)(2)(xiv).

	(2)  The records specified in §63.6(e)(3)(iii) through (v) related to
startup, shutdown, and malfunction.

	(3)  Records of performance tests and performance evaluations as
required by §63.10(b)(2)(viii).

	(4)  Records of the annual quantity of each chemical binder or coating
material used to coat or make molds and cores, the Material Data Safety
Sheet or other documentation that provides the chemical composition of
each component, and the annual quantity of HAP used in these chemical
binder or coating materials at the foundry as calculated from the
recorded quantities and chemical compositions (from Material Data Safety
Sheets or other documentation).  

	(b)  You must keep the following records for each CEMS.

	(1)  Records described in §63.10(b)(2)(vi) through (xi).

	(2)  Previous (i.e., superseded) versions of the performance evaluation
plan as required in §63.8(d)(3).

	(3)  Request for alternatives to relative accuracy tests for CEMS as
required in §63.8(f)(6)(i).

	(4)  Records of the date and time that each deviation started and
stopped, and whether the deviation occurred during a period of startup,
shutdown, or malfunction or during another period.

	(c)  You must keep the records required by §§63.7743, 63.7744, and
63.7745 to show continuous compliance with each emissions limitation,
work practice standard, and operation and maintenance requirement that
applies to you.

§63.7753  In what form and for how long must I keep my records?

	(a)  You must keep your records in a form suitable and readily
available for expeditious review, according to the requirements of
§63.10(b)(1).

	(b)  As specified in §63.10(b)(1), you must keep each record for 5
years following the date of each occurrence, measurement, maintenance,
corrective action, report, or record.

	(c)  You must keep each record onsite for at least 2 years after the
date of each occurrence, measurement, maintenance, corrective action,
report, or record according to the requirements in §63.10(b)(1).  You
can keep the records for the previous 3 years offsite.

Other Requirements and Information

§63.7760  What parts of the General Provisions apply to me?

	Table 1 to this subpart shows which parts of the General Provisions in
§§63.1 through 63.15 apply to you.

§63.7761  Who implements and enforces this subpart?

	(a)  This subpart can be implemented and enforced by us, the U.S.
Environmental Protection Agency (EPA), or a delegated authority such as
your State, local, or tribal agency.  If the U.S. EPA Administrator has
delegated authority to your State, local, or tribal agency, then that
agency, in addition to the U.S. EPA, has the authority to implement and
enforce this subpart.  You should contact your U.S. EPA Regional Office
to find out if implementation and enforcement of this subpart is
delegated to your State, local, or tribal agency.

	(b)  In delegating implementation and enforcement authority of this
subpart to a State, local, or tribal agency under 40 CFR part 63,
subpart E, the authorities contained in paragraph (c) of this section
are retained by the Administrator of the U.S. EPA and are not
transferred to the State, local, or tribal agency.

	(c)  The authorities that cannot be delegated to State, local, or
tribal agencies are specified in paragraphs (c)(1) through (4) of this
section.

	(1)  Approval of alternatives to non-opacity emissions limitations in
§63.7690 and work practice standards in §63.7700 under §63.6(g).

	(2)  Approval of major alternatives to test methods under
§63.7(e)(2)(ii) and (f) and as defined in §63.90.

	(3)  Approval of major alternatives to monitoring under §63.8(f) and
as defined in §63.90.

	(4)  Approval of major alternatives to recordkeeping and reporting
under §63.10(f) and as defined in §63.90.

Definitions

§63.7765  What definitions apply to this subpart?

   Terms used in this subpart are defined in the Clean Air Act (CAA), in
§63.2, and in this section.

	Automated conveyor and pallet cooling line means any dedicated conveyor
line or area used for cooling molds received from pouring stations.

	Automated shakeout line means any mechanical process unit designed for
and dedicated to separating a casting from a mold.  These mechanical
processes include, but are not limited to, shaker decks, rotary
separators, and high-frequency vibration units.  Automated shakeout
lines do not include manual processes for separating a casting from a
mold, such as personnel using a hammer, chisel, pick ax, sledge hammer,
or jackhammer. 

	Bag leak detection system means a system that is capable of
continuously monitoring relative particulate matter (dust) loadings in
the exhaust of a baghouse to detect bag leaks and other upset
conditions.  A bag leak detection system includes, but is not limited
to, an instrument that operates on triboelectric, electrodynamic, light
scattering, light transmittance, or other effect to continuously monitor
relative particulate matter loadings.

	Binder chemical means a component of a system of chemicals used to bind
sand together into molds, mold sections, and cores through chemical
reaction as opposed to pressure.

	Capture system means the collection of components used to capture gases
and fumes released from one or more emissions points and then convey the
captured gas stream to a control device or to the atmosphere.  A capture
system may include, but is not limited to, the following components as
applicable to a given capture system design:  duct intake devices,
hoods, enclosures, ductwork, dampers, manifolds, plenums, and fans.

	Cold box mold or core making line means a mold or core making line in
which the formed aggregate is hardened by catalysis with a gas.

	Combustion device means an afterburner, thermal incinerator, or scrap
preheater.

	Conveyance means the system of equipment that is designed to capture
pollutants at the source, convey them through ductwork, and exhaust them
using forced ventilation.  A conveyance may, but does not necessarily
include, control equipment designed to reduce emissions of the
pollutants.  Emissions that are released through windows, vents, or
other general building ventilation or exhaust systems are not considered
to be discharged through a conveyance.

	Cooling means the process of molten metal solidification within the
mold and subsequent temperature reduction prior to shakeout.

	Cupola means a vertical cylindrical shaft furnace that uses coke and
forms of iron and steel such as scrap and foundry returns as the primary
charge components and melts the iron and steel through combustion of the
coke by a forced upward flow of heated air.

	Deviation means any instance in which an affected source or an owner or
operator of such an affected source:

	(1)  Fails to meet any requirement or obligation established by this
subpart including, but not limited to, any emissions limitation
(including operating limits), work practice standard, or operation and
maintenance requirement;

	(2)  Fails to meet any term or condition that is adopted to implement
an applicable requirement in this subpart and that is included in the
operating permit for any iron and steel foundry required to obtain such
a permit; or

	(3)  Fails to meet any emissions limitation (including operating
limits) or work practice standard in this subpart during startup,
shutdown, or malfunction, regardless of whether or not such failure is
permitted by this subpart.

A deviation is not always a violation.  The determination of whether a
deviation constitutes a violation of the standard is up to the
discretion of the entity responsible for enforcement of the standards.  

	Electric arc furnace means a vessel in which forms of iron and steel
such as scrap and foundry returns are melted through resistance heating
by an electric current flowing through the arcs formed between the
electrodes and the surface of the metal and also flowing through the
metal between the arc paths.

	Electric induction furnace means a vessel in which forms of iron and
steel such as scrap and foundry returns are melted though resistance
heating by an electric current that is induced in the metal by passing
an alternating current through a coil surrounding the metal charge or
surrounding a pool of molten metal at the bottom of the vessel.

	Emissions limitation means any emissions limit or operating limit.

	Exhaust stream means gases emitted from a process through a conveyance
as defined in this subpart.

	Free organic liquids means material that fails the paint filter test by
EPA Method 9095A (incorporated by reference – see §63.14).  That is,
if any portion of the material passes through and drops from the filter
within the 5-minute test period, the material contains free liquids.

	Fresh acid solution means a sulfuric acid solution used for the control
of triethylamine emissions that has a pH of 2.0 or less.

	Fugitive emissions means any pollutant released to the atmosphere that
is not discharged through a conveyance as defined in this subpart.

	Furan warm box mold or core making line means a mold or core making
line in which the binder chemical system used is that system commonly
designated as a furan warm box system by the foundry industry.

	Hazardous air pollutant means any substance on the list originally
established in 112(b)(1) of the CAA and subsequently amended as
published in the Code of Federal Regulations.

	Iron and steel foundry means a facility or portion of a facility that
melts scrap, ingot, and/or other forms of iron and/or steel and pours
the resulting molten metal into molds to produce final or near final
shape products for introduction into commerce.  Research and development
facilities and operations that only produce non-commercial castings are
not included in this definition.

	Metal melting furnace means a cupola, electric arc furnace, or electric
induction furnace that converts scrap, foundry returns, and/or other
solid forms of iron and/or steel to a liquid state.  This definition
does not include a holding furnace, an argon oxygen decarburization
vessel, or ladle that receives molten metal from a metal melting
furnace, to which metal ingots or other material may be added to adjust
the metal chemistry.	

	Mold or core making line means the collection of equipment that is used
to mix an aggregate of sand and binder chemicals, form the aggregate
into final shape, and harden the formed aggregate.  This definition does
not include a line for making green sand molds or cores.

	Mold vent means an intentional opening in a mold through which gases
containing pyrolysis products of organic mold and core constituents
produced by contact with or proximity to molten metal normally escape
the mold during and after metal pouring.

	Off blast means those periods of cupola operation when the cupola is
not actively being used to produce molten metal.  Off blast conditions
include cupola start-up when air is introduced to the cupola to preheat
the sand bed and other cupola start-up procedures as defined in the
startup, shutdown, and malfunction plan.  Off blast conditions also
include idling conditions when the blast air is turned off or down to
the point that the cupola does not produce additional molten metal.

	On blast means those periods of cupola operation when combustion
(blast) air is introduced to the cupola furnace and the furnace is
capable of producing molten metal.  On blast conditions are
characterized by both blast air introduction and molten metal
production.  

	Pouring area means an area, generally associated with floor and pit
molding operations, in which molten metal is brought to each individual
mold.  Pouring areas include all pouring operations that do not meet the
definition of a pouring station.

	Pouring station means the fixed location to which molds are brought in
a continuous or semicontinuous manner to receive molten metal, after
which the molds are moved to a cooling area.

	Responsible official means responsible official as defined in §63.2.

	Scrap preheater means a vessel or other piece of equipment in which
metal scrap that is to be used as melting furnace feed is heated to a
temperature high enough to eliminate moisture and other volatile
impurities or other tramp materials by direct flame heating or similar
means of heating. Scrap dryers, which solely remove moisture from metal
scrap, are not considered to be scrap preheaters for purposes of this
subpart.

	Scrubber blowdown means liquor or slurry discharged from a wet scrubber
that is either removed as a waste stream or processed to remove
impurities or adjust its composition or pH before being returned to the
scrubber.

	Total metal HAP means, for the purposes of this subpart, the sum of the
concentrations of antimony, arsenic, beryllium, cadmium, chromium,
cobalt, lead, manganese, mercury, nickel, and selenium as measured by
EPA Method 29 (40 CFR part 60, appendix A).  Only the measured
concentration of the listed analytes that are present at concentrations
exceeding one half the quantitation limit of the analytical method are
to be used in the sum.  If any of the analytes are not detected or are
detected at concentrations less than one half the quantitation limit of
the analytical method, the concentration of those analytes will be
assumed to be zero for the purposes of calculating the total metal HAP
for this subpart 

	Work practice standard means any design, equipment, work practice, or
operational standard, or combination thereof, that is promulgated
pursuant to section 112(h) of the CAA.	

					

Tables to Subpart EEEEE of Part 63

(As stated in §63.7760, you must meet each requirement in the following
table that applies to you.) 

Table 1 to Subpart EEEEE of Part 63.  Applicability of General
Provisions to Subpart EEEEE

Citation	Subject	Applies to Subpart EEEEE?	Explanation

63.1	Applicability	Yes.

	63.2	Definitions	Yes.

	63.3	Units and abbreviations	Yes.

	63.4	Prohibited activities	Yes.

	63.5	Construction/

reconstruction	Yes.

	63.6(a)-(g)	Compliance with standards and maintenance requirements	Yes.

	63.6(h)	Opacity and visible emissions standards	Yes.

	63.6(i)(i)-(j)	Compliance extension and Presidential compliance
exemption	Yes.

	63.7(a)(3),

(b)-(h)	Performance testing requirements	Yes.

	63.7(a)(1)-(a)(2)	Applicability and performance test dates	No	Subpart
EEEEE specifies applicability and performance test dates.

63.8(a)(1)-(a)(3),(b), (c)(1)-(c)(3),  (c)(6)- (c)(8), (d), (e),
(f)(1)-(f)(6),(g)(1)-(g)(4)	Monitoring requirements	Yes	Subpart EEEEE
specifies requirements for alternative monitoring systems.

63.8(a)(4)	Additional monitoring requirements for control devices in
§63.11	No	Subpart EEEEE does not require flares.

63.8(c)(4)	Continuous monitoring system (CMS) requirements	No	Subpart
EEEEE specifies requirements for operation of CMS and CEMS.

63.8(c)(5)	Continuous opacity monitoring system (COMS) Minimum
Procedures	No	Subpart EEEEE does not require COMS.

63.8(g)(5)	Data reduction	No	Subpart EEEEE specifies data reduction
requirements.

63.9	Notification requirements	Yes.	Except: for opacity performance
tests, Subpart EEEEE allows the notification of compliance status to be
submitted with the semiannual compliance report or the semiannual part
70 monitoring report

63.10(a), (b)(1)-(b)(2)(xii) -

(b)(2)(xiv),

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＀摧㠇TȀSubpart EEEEE specifies reporting requirements.

63.10(e)(4)	Reporting COMS data	No	Subpart EEEEE does not require COMS.

63.11	Control device requirements	No	Subpart EEEEE does not require
flares.

63.12	State authority and delegations	Yes.

	63.13-63.15	Addresses of State air pollution control agencies and EPA
regional offices.

Incorporation by reference.

Availability of information and confidentiality	Yes.

	

 PAGE   

 PAGE   1 

		(Eq. 13)

(Eq. 24)

	(Eq. 35)

∑ Ci × Qi} / {∑ Qi}

(Eq. 57)

 

