Document ID: EPA-HQ-OAR-2003-0048-0090
Agency: epa
Document Type: Supporting & Related Material
Title: 
Posted Date: 2004-02-25T05:00Z

18
operating
requirements
for
thermal
oxidizers.

(
b)
You
must
demonstrate
initial
compliance
with
each
compliance
option,
operating
requirement,
and
work
practice
requirement
that
applies
to
you
according
to
Tables
5
and
6
of
this
subpart
and
according
to
§
§
63.2260
through
63.2269
of
this
subpart.

(
c)
You
must
submit
the
Notification
of
Compliance
Status
containing
the
results
of
the
initial
compliance
demonstration
according
to
the
requirements
in
§
63.2280(
d).

§
63.2261
By
what
date
must
I
conduct
performance
tests
or
other
initial
compliance
demonstrations?

(
a)
You
must
conduct
performance
tests
upon
initial
startup
or
no
later
than
180
calendar
days
after
the
compliance
date
that
is
specified
for
your
source
in
§
63.2233
and
according
to
§
63.7(
a)(
2),
whichever
is
later.

(
b)
You
must
conduct
initial
compliance
demonstrations
that
do
not
require
performance
tests
upon
initial
startup
or
no
later
than
30
calendar
days
after
the
compliance
date
that
is
specified
for
your
source
in
§
63.2233,
whichever
is
later.

§
63.2262
How
do
I
conduct
performance
tests
and
establish
operating
requirements?

(
a)
You
must
conduct
each
performance
test
according
to
the
requirements
in
§
63.7(
e)(
1),
the
requirements
in
paragraphs
(
b)
through
(
o)
of
this
section,
and
according
to
the
methods
specified
in
Table
4
of
this
subpart.
19
(
b)
Periods
when
performance
tests
must
be
conducted.

(
1)
You
must
not
conduct
performance
tests
during
periods
of
startup,
shutdown,
or
malfunction,
as
specified
in
§
63.7(
e)(
1).

(
2)
You
must
test
under
representative
operating
conditions
as
defined
in
§
63.2292.
You
must
describe
representative
operating
conditions
in
your
performance
test
report
for
the
process
and
control
systems
and
explain
why
they
are
representative.

(
c)
Number
of
test
runs.
You
must
conduct
three
separate
test
runs
for
each
performance
test
required
in
this
section,
as
specified
in
§
63.7(
e)(
3).
Each
test
run
must
last
at
least
1
hour
except
for:
testing
of
a
temporary
total
enclosure
(
TTE)
conducted
using
Methods
204A
through
204F,
which
require
three
separate
test
runs
of
at
least
3
hours
each;
and
testing
of
an
enclosure
conducted
using
the
alternative
tracer
gas
method
in
appendix
A
to
this
subpart,
which
requires
a
minimum
of
three
separate
runs
of
at
least
20
minutes
each.

(
d)
Location
of
sampling
sites.

(
1)
Sampling
sites
must
be
located
at
the
inlet
(
if
emission
reduction
testing
or
documentation
of
inlet
methanol
or
formaldehyde
concentration
is
required)
and
outlet
of
the
control
device
and
prior
to
any
releases
to
the
atmosphere.
For
HAP­
altering
controls
in
sequence,
such
as
a
wet
control
device
followed
by
a
thermal
oxidizer,
20
sampling
sites
must
be
located
at
the
functional
inlet
of
the
control
sequence
(
e.
g.,
prior
to
the
wet
control
device)

and
at
the
outlet
of
the
control
sequence
(
e.
g.,
thermal
oxidizer
outlet)
and
prior
to
any
releases
to
the
atmosphere.

(
2)
Sampling
sites
for
process
units
meeting
compliance
options
without
a
control
device
must
be
located
prior
to
any
releases
to
the
atmosphere.
Facilities
demonstrating
compliance
with
a
production­
based
compliance
option
for
a
process
unit
equipped
with
a
wet
control
device
must
locate
sampling
sites
prior
to
the
wet
control
device.

(
e)
Collection
of
monitoring
data.
You
must
collect
operating
parameter
monitoring
system
or
continuous
emissions
monitoring
system
(
CEMS)
data
at
least
every
15
minutes
during
the
entire
performance
test
and
determine
the
parameter
or
concentration
value
for
the
operating
requirement
during
the
performance
test
using
the
methods
specified
in
paragraphs
(
k)
through
(
o)
of
this
section.

(
f)
Collection
of
production
data.
To
comply
with
any
of
the
production­
based
compliance
options,
you
must
measure
and
record
the
process
unit
throughput
during
each
performance
test.

(
g)
Nondetect
data.

(
1)
Except
as
specified
in
paragraph
(
g)(
2)
of
this
section,
all
nondetect
data
(
as
defined
in
§
63.2292)
must
be
21
treated
as
one­
half
of
the
method
detection
limit
when
determining
total
HAP,
formaldehyde,
methanol,
or
total
hydrocarbon
(
THC)
emission
rates.

(
2)
When
showing
compliance
with
the
production­
based
compliance
options
in
Table
1A
of
this
subpart,
you
may
treat
emissions
of
an
individual
HAP
as
zero
if
all
three
of
the
performance
test
runs
result
in
a
nondetect
measurement
and
the
method
detection
limit
is
less
than
or
equal
to
1
parts
per
million
by
volume,
dry
(
ppmvd).
Otherwise
nondetect
data
(
as
defined
in
§
63.2292)
for
individual
HAP
must
be
treated
as
one­
half
of
the
method
detection
limit.

(
h)
Calculation
of
percent
reduction
across
a
control
system.
When
determining
the
control
system
efficiency
for
any
control
system
included
in
your
emissions
averaging
plan
(
not
to
exceed
90
percent)
and
when
complying
with
any
of
the
compliance
options
based
on
percent
reduction
across
a
control
system
in
Table
1B
of
this
subpart,
as
part
of
the
performance
test,
you
must
calculate
the
percent
reduction
using
Equation
1
of
this
section:

(
Eq.
1)
PR
CE
ER
ER
ER
in
out
in
=
×
 
(
)
100
Where:

PR
=
percent
reduction,
percent
CE
=
capture
efficiency,
percent
(
determined
for
reconstituted
wood
product
presses
and
board
22
coolers
as
required
in
Table
4
of
this
subpart)
ERin
=
emission
rate
of
total
HAP
(
calculated
as
the
sum
of
the
emission
rates
of
acetaldehyde,
acrolein,
formaldehyde,
methanol,
phenol,
and
propionaldehyde),
THC,
formaldehyde,
or
methanol
in
the
inlet
vent
stream
of
the
control
device,
pounds
per
hour
ERout
=
emission
rate
of
total
HAP
(
calculated
as
the
sum
of
the
emission
rates
of
acetaldehyde,
acrolein,
formaldehyde,
methanol,
phenol,
and
propionaldehyde),
THC,
formaldehyde,
or
methanol
in
the
outlet
vent
stream
of
the
control
device,
pounds
per
hour
(
i)
Calculation
of
mass
per
unit
production.
To
comply
with
any
of
the
production­
based
compliance
options
in
Table
1A
of
this
subpart,
you
must
calculate
your
mass
per
unit
production
emissions
for
each
performance
test
run
using
Equation
2
of
this
section:

(
Eq.
2)
MP
ER
P
CE
HAP
=
×
Where:

MP
=
mass
per
unit
production,
pounds
per
oven
dried
ton
OR
pounds
per
thousand
square
feet
on
a
specified
thickness
basis;
(
see
paragraph
(
j)
of
this
section
if
you
need
to
convert
from
one
thickness
basis
to
another)
ERHAP
=
emission
rate
of
total
HAP
(
calculated
as
the
sum
of
the
emission
rates
of
acetaldehyde,
acrolein,
formaldehyde,
methanol,
phenol,
and
propionaldehyde)
in
the
stack,
pounds
per
hour
P
=
process
unit
production
rate
(
throughput),
oven
dried
tons
per
hour
OR
thousand
square
feet
per
hour
on
a
specified
thickness
basis
CE
=
capture
efficiency,
percent
(
determined
for
reconstituted
wood
product
presses
and
board
coolers
as
required
in
Table
4
of
this
subpart)
23
(
j)
Thickness
basis
conversion.
Use
Equation
3
of
this
section
to
convert
from
one
thickness
basis
to
another:

(
Eq.
3)
MSF
MSF
A
B
B
A
=
×
Where:

MSFA
=
thousand
square
feet
on
an
A­
inch
basis
MSFB
=
thousand
square
feet
on
a
B­
inch
basis
A
=
old
thickness
you
are
converting
from,
inches
B
=
new
thickness
you
are
converting
to,
inches
(
k)
Establishing
thermal
oxidizer
operating
requirements.
If
you
operate
a
thermal
oxidizer,
you
must
establish
your
thermal
oxidizer
operating
parameters
according
to
paragraphs
(
k)(
1)
through
(
3)
of
this
section.

(
1)
During
the
performance
test,
you
must
continuously
monitor
the
firebox
temperature
during
each
of
the
required
1­
hour
test
runs.
For
regenerative
thermal
oxidizers,
you
may
measure
the
temperature
in
multiple
locations
(
for
example,
one
location
per
burner)
in
the
combustion
chamber
and
calculate
the
average
of
the
temperature
measurements
prior
to
reducing
the
temperature
data
to
15­
minute
averages
for
purposes
of
establishing
your
minimum
firebox
temperature.
The
minimum
firebox
temperature
must
then
be
established
as
the
average
of
the
three
minimum
15­
minute
firebox
temperatures
monitored
during
the
three
test
runs.

Multiple
three­
run
performance
tests
may
be
conducted
to
establish
a
range
of
parameter
values
under
different
24
operating
conditions.

(
2)
You
may
establish
a
different
minimum
firebox
temperature
for
your
thermal
oxidizer
by
submitting
the
notification
specified
in
§
63.2280(
g)
and
conducting
a
repeat
performance
test
as
specified
in
paragraph
(
k)(
1)
of
this
section
that
demonstrates
compliance
with
the
applicable
compliance
options
of
this
subpart.

(
3)
If
your
thermal
oxidizer
is
a
combustion
unit
that
accepts
process
exhaust
into
the
flame
zone,
then
you
are
exempt
from
the
performance
testing
and
monitoring
requirements
specified
in
paragraphs
(
k)(
1)
and
(
2)
of
this
section.
To
demonstrate
initial
compliance,
you
must
submit
documentation
with
your
Notification
of
Compliance
Status
showing
that
process
exhausts
controlled
by
the
combustion
unit
enter
into
the
flame
zone.

(
l)
Establishing
catalytic
oxidizer
operating
requirements.
If
you
operate
a
catalytic
oxidizer,
you
must
establish
your
catalytic
oxidizer
operating
parameters
according
to
paragraphs
(
l)(
1)
and
(
2)
of
this
section.

(
1)
During
the
performance
test,
you
must
continuously
monitor
during
the
required
1­
hour
test
runs
either
the
temperature
at
the
inlet
to
each
catalyst
bed
or
the
temperature
in
the
combustion
chamber.
For
regenerative
catalytic
oxidizers,
you
must
calculate
the
average
of
the
temperature
measurements
from
each
catalyst
bed
inlet
or
within
the
combustion
chamber
prior
to
reducing
the
25
temperature
data
to
15­
minute
averages
for
purposes
of
establishing
your
minimum
catalytic
oxidizer
temperature.

The
minimum
catalytic
oxidizer
temperature
must
then
be
established
as
the
average
of
the
three
minimum
15­
minute
temperatures
monitored
during
the
three
test
runs.
Multiple
three­
run
performance
tests
may
be
conducted
to
establish
a
range
of
parameter
values
under
different
operating
conditions.

(
2)
You
may
establish
a
different
minimum
catalytic
oxidizer
temperature
by
submitting
the
notification
specified
in
§
63.2280(
g)
and
conducting
a
repeat
performance
test
as
specified
in
paragraphs
(
l)(
1)
and
(
2)
of
this
section
that
demonstrates
compliance
with
the
applicable
compliance
options
of
this
subpart.

(
m)
Establishing
biofilter
operating
requirements.
If
you
operate
a
biofilter,
you
must
establish
your
biofilter
operating
requirements
according
to
paragraphs
(
m)(
1)

through
(
3)
of
this
section.

(
1)
During
the
performance
test,
you
must
continuously
monitor
the
biofilter
bed
temperature
during
each
of
the
required
1­
hour
test
runs.
To
monitor
biofilter
bed
temperature,
you
may
use
multiple
thermocouples
in
representative
locations
throughout
the
biofilter
bed
and
calculate
the
average
biofilter
bed
temperature
across
these
thermocouples
prior
to
reducing
the
temperature
data
to
15­

minute
averages
for
purposes
of
establishing
biofilter
bed
26
temperature
limits.
The
biofilter
bed
temperature
range
must
be
established
as
the
minimum
and
maximum
15­
minute
biofilter
bed
temperatures
monitored
during
the
three
test
runs.
You
may
base
your
biofilter
bed
temperature
range
on
values
recorded
during
previous
performance
tests
provided
that
the
data
used
to
establish
the
temperature
ranges
have
been
obtained
using
the
test
methods
required
in
this
subpart.
If
you
use
data
from
previous
performance
tests,

you
must
certify
that
the
biofilter
and
associated
process
unit(
s)
have
not
been
modified
subsequent
to
the
date
of
the
performance
tests.
Replacement
of
the
biofilter
media
with
the
same
type
of
material
is
not
considered
a
modification
of
the
biofilter
for
purposes
of
this
section.

(
2)
For
a
new
biofilter
installation,
you
will
be
allowed
up
to
180
days
following
the
compliance
date
or
180
days
following
initial
startup
of
the
biofilter
to
complete
the
requirements
in
paragraph
(
m)(
1)
of
this
section.

(
3)
You
may
expand
your
biofilter
bed
temperature
operating
range
by
submitting
the
notification
specified
in
§
63.2280(
g)
and
conducting
a
repeat
performance
test
as
specified
in
paragraph
(
m)(
1)
of
this
section
that
demonstrates
compliance
with
the
applicable
compliance
options
of
this
subpart.

(
n)
Establishing
operating
requirements
for
process
units
meeting
compliance
options
without
a
control
device.

If
you
operate
a
process
unit
that
meets
a
compliance
option
27
in
Table
1A
of
this
subpart,
or
is
a
process
unit
that
generates
debits
in
an
emissions
average
without
the
use
of
a
control
device,
you
must
establish
your
process
unit
operating
parameters
according
to
paragraphs
(
n)(
1)
through
(
2)
of
this
section.

(
1)
During
the
performance
test,
you
must
identify
and
document
the
process
unit
controlling
parameter(
s)
that
affect
total
HAP
emissions
during
the
three­
run
performance
test.
The
controlling
parameters
you
identify
must
coincide
with
the
representative
operating
conditions
you
describe
according
to
§
63.2262(
b)(
2).
For
each
parameter,
you
must
specify
appropriate
monitoring
methods,
monitoring
frequencies,
and
for
continuously
monitored
parameters
averaging
times
not
to
exceed
24
hours.
The
operating
limit
for
each
controlling
parameter
must
then
be
established
as
the
minimum,
maximum,
range,
or
average
(
as
appropriate
depending
on
the
parameter)
recorded
during
the
performance
test.
Multiple
three­
run
performance
tests
may
be
conducted
to
establish
a
range
of
parameter
values
under
different
operating
conditions.

(
2)
You
may
establish
different
controlling
parameter
limits
for
your
process
unit
by
submitting
the
notification
specified
in
§
63.2280(
g)
and
conducting
a
repeat
performance
test
as
specified
in
paragraph
(
n)(
1)
of
this
section
that
demonstrates
compliance
with
the
compliance
options
in
Table
1A
of
this
subpart
or
is
used
to
establish
emission
28
averaging
debits
for
an
uncontrolled
process
unit.

(
o)
Establishing
operating
requirements
using
total
hydrocarbon
(
THC)
CEMS.
If
you
choose
to
meet
the
operating
requirements
by
monitoring
THC
concentration
instead
of
monitoring
control
device
or
process
operating
parameters,

you
must
establish
your
THC
concentration
operating
requirement
according
to
paragraphs
(
o)(
1)
through
(
2)
of
this
section.

(
1)
During
the
performance
test,
you
must
continuously
monitor
THC
concentration
using
your
CEMS
during
each
of
the
required
1­
hour
test
runs.
The
maximum
THC
concentration
must
then
be
established
as
the
average
of
the
three
maximum
15­
minute
THC
concentrations
monitored
during
the
three
test
runs.
Multiple
three­
run
performance
tests
may
be
conducted
to
establish
a
range
of
THC
concentration
values
under
different
operating
conditions.

(
2)
You
may
establish
a
different
maximum
THC
concentration
by
submitting
the
notification
specified
in
§
63.2280(
g)
and
conducting
a
repeat
performance
test
as
specified
in
paragraph
(
o)(
1)
of
this
section
that
demonstrates
compliance
with
the
compliance
options
in
Tables
1A
and
1B
of
this
subpart.

§
63.2263
Initial
compliance
demonstration
for
a
dry
rotary
dryer.

If
you
operate
a
dry
rotary
dryer,
you
must
demonstrate
that
your
dryer
processes
furnish
with
an
inlet
moisture
29
content
of
less
than
or
equal
to
30
percent
(
by
weight,
dry
basis)
and
operates
with
a
dryer
inlet
temperature
of
less
than
or
equal
to
600oF.
You
must
designate
and
clearly
identify
each
dry
rotary
dryer.
You
must
record
the
inlet
furnish
moisture
content
(
dry
basis)
and
inlet
dryer
operating
temperature
according
to
§
63.2269(
a),
(
b),
and
(
c)

and
§
63.2270
for
a
minimum
of
30
calendar
days.
You
must
submit
the
highest
recorded
24­
hour
average
inlet
furnish
moisture
content
and
the
highest
recorded
24­
hour
average
dryer
inlet
temperature
with
your
Notification
of
Compliance
Status.
In
addition,
you
must
submit
with
the
Notification
of
Compliance
Status
a
signed
statement
by
a
responsible
official
that
certifies
with
truth,
accuracy,
and
completeness
that
the
dry
rotary
dryer
will
dry
furnish
with
a
maximum
inlet
moisture
content
less
than
or
equal
to
30
percent
(
by
weight,
dry
basis)
and
will
operate
with
a
maximum
inlet
temperature
of
less
than
or
equal
to
600oF
in
the
future.

§
63.2264
Initial
compliance
demonstration
for
a
hardwood
veneer
dryer.

If
you
operate
a
hardwood
veneer
dryer,
you
must
record
the
annual
volume
percentage
of
softwood
veneer
species
processed
in
the
dryer
as
follows:

(
a)
Use
Equation
1
of
this
section
to
calculate
the
annual
volume
percentage
of
softwood
species
dried:
30
(
Eq.
1)
SW
SW
T
%
(
)
=
100
Where:

SW%
=
annual
volume
percent
softwood
species
dried
SW
=
softwood
veneer
dried
during
the
previous
12
months,
thousand
square
feet
(
3/
8­
inch
basis)
T
=
total
softwood
and
hardwood
veneer
dried
during
the
previous
12
months,
thousand
square
feet
(
3/
8­
inch
basis)

(
b)
You
must
designate
and
clearly
identify
each
hardwood
veneer
dryer.
Submit
with
the
Notification
of
Compliance
Status
the
annual
volume
percentage
of
softwood
species
dried
in
the
dryer
based
on
your
dryer
production
for
the
12
months
prior
to
the
compliance
date
specified
for
your
source
in
§
63.2233.
If
you
did
not
dry
any
softwood
species
in
the
dryer
during
the
12
months
prior
to
the
compliance
date,
then
you
need
only
to
submit
a
statement
indicating
that
no
softwood
species
were
dried.
In
addition,
submit
with
the
Notification
of
Compliance
Status
a
signed
statement
by
a
responsible
official
that
certifies
with
truth,
accuracy,
and
completeness
that
the
veneer
dryer
will
be
used
to
process
less
than
30
volume
percent
softwood
species
in
the
future.

§
63.2265
Initial
compliance
demonstration
for
a
softwood
veneer
dryer.

If
you
operate
a
softwood
veneer
dryer,
you
must
develop
a
plan
for
review
and
approval
for
minimizing
31
fugitive
emissions
from
the
veneer
dryer
heated
zones,
and
you
must
submit
the
plan
with
your
Notification
of
Compliance
Status.

§
63.2266
Initial
compliance
demonstration
for
a
veneer
redryer.

If
you
operate
a
veneer
redryer,
you
must
record
the
inlet
moisture
content
of
the
veneer
processed
in
the
redryer
according
to
§
63.2269(
a)
and
(
c)
and
§
63.2270
for
a
minimum
of
30
calendar
days.
You
must
designate
and
clearly
identify
each
veneer
redryer.
You
must
submit
the
highest
recorded
24­
hour
average
inlet
veneer
moisture
content
with
your
Notification
of
Compliance
Status
to
show
that
your
veneer
redryer
processes
veneer
with
an
inlet
moisture
content
of
less
than
or
equal
to
25
percent
(
by
weight,
dry
basis).
In
addition,
submit
with
the
Notification
of
Compliance
Status
a
signed
statement
by
a
responsible
official
that
certifies
with
truth,
accuracy,
and
completeness
that
the
veneer
redryer
will
dry
veneer
with
a
moisture
content
less
than
25
percent
(
by
weight,
dry
basis)

in
the
future.

§
63.2267
Initial
compliance
demonstration
for
a
reconstituted
wood
product
press
or
board
cooler.

If
you
operate
a
reconstituted
wood
product
press
at
a
new
or
existing
affected
source
or
a
reconstituted
wood
product
board
cooler
at
a
new
affected
source,
then
you
must
either
use
a
wood
products
enclosure
as
defined
in
§
63.2292
32
or
measure
the
capture
efficiency
of
the
capture
device
for
the
press
or
board
cooler
using
Methods
204
and
204A
through
204F
of
40
CFR
part
51,
appendix
M
(
as
appropriate)
or
using
the
alternative
tracer
gas
method
contained
in
appendix
A
to
this
subpart.
You
must
submit
documentation
that
the
wood
products
enclosure
meets
the
press
enclosure
design
criteria
in
63.2292
or
the
results
of
the
capture
efficiency
verification
with
your
Notification
of
Compliance
Status.

§
63.2268
Initial
compliance
demonstration
for
a
wet
control
device.

If
you
use
a
wet
control
device
as
the
sole
means
of
reducing
HAP
emissions,
you
must
develop
and
implement
a
plan
for
review
and
approval
to
address
how
organic
HAP
captured
in
the
wastewater
from
the
wet
control
device
is
contained
or
destroyed
to
minimize
re­
release
to
the
atmosphere
such
that
the
desired
emission
reduction
is
obtained.
You
must
submit
the
plan
with
your
Notification
of
Compliance
Status.

§
63.2269
What
are
my
monitoring
installation,
operation,

and
maintenance
requirements?

(
a)
General
continuous
parameter
monitoring
requirements.
You
must
install,
operate,
and
maintain
each
continuous
parameter
monitoring
system
(
CPMS)
according
to
paragraphs
(
a)(
1)
through
(
3)
of
this
section.

(
1)
The
CPMS
must
be
capable
of
completing
a
minimum
of
one
cycle
of
operation
(
sampling,
analyzing,
and
33
recording)
for
each
successive
15­
minute
period.

(
2)
At
all
times,
you
must
maintain
the
monitoring
equipment
including,
but
not
limited
to,
maintaining
necessary
parts
for
routine
repairs
of
the
monitoring
equipment.

(
3)
Record
the
results
of
each
inspection,

calibration,
and
validation
check.

(
b)
Temperature
monitoring.
For
each
temperature
monitoring
device,
you
must
meet
the
requirements
in
paragraphs
(
a)
and
(
b)(
1)
through
(
6)
of
this
section.

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

(
2)
Use
a
temperature
sensor
with
a
minimum
accuracy
of
4oF
or
0.75
percent
of
the
temperature
value,
whichever
is
larger.

(
3)
If
a
chart
recorder
is
used,
it
must
have
a
sensitivity
with
minor
divisions
not
more
than
20oF.

(
4)
Perform
an
electronic
calibration
at
least
semiannually
according
to
the
procedures
in
the
manufacturer's
owners
manual.
Following
the
electronic
calibration,
you
must
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
30oF
of
the
process
temperature
sensor's
reading.

(
5)
Conduct
calibration
and
validation
checks
any
time
34
the
sensor
exceeds
the
manufacturer's
specified
maximum
operating
temperature
range
or
install
a
new
temperature
sensor.

(
6)
At
least
quarterly,
inspect
all
components
for
integrity
and
all
electrical
connections
for
continuity,

oxidation,
and
galvanic
corrosion.

(
c)
Wood
moisture
monitoring.
For
each
furnish
or
veneer
moisture
meter,
you
must
meet
the
requirements
in
paragraphs
(
a)(
1),
(
2),
(
4)
and
(
5)
and
paragraphs
(
c)(
1)

through
(
4)
of
this
section.

(
1)
For
dry
rotary
dryers,
use
a
continuous
moisture
monitor
with
a
minimum
accuracy
of
1
percent
(
dry
basis)

moisture
or
better
in
the
25
to
35
percent
(
dry
basis)

moisture
content
range.
For
veneer
redryers,
use
a
continuous
moisture
monitor
with
a
minimum
accuracy
of
3
percent
(
dry
basis)
moisture
or
better
in
the
15
to
25
percent
(
dry
basis)
moisture
content
range.
Alternatively,

you
may
use
a
continuous
moisture
monitor
with
a
minimum
accuracy
of
5
percent
(
dry
basis)
moisture
or
better
for
dry
rotary
dryers
used
to
dry
furnish
with
less
than
25
percent
(
dry
basis)
moisture
or
for
veneer
redryers
used
to
redry
veneer
with
less
than
20
percent
(
dry
basis)
moisture.

(
2)
Locate
the
moisture
monitor
in
a
position
that
provides
a
representative
measure
of
furnish
or
veneer
moisture.

(
3)
Calibrate
the
moisture
monitor
based
on
the
35
procedures
specified
by
the
moisture
monitor
manufacturer
at
least
once
per
semiannual
compliance
period
(
or
more
frequently
if
recommended
by
the
moisture
monitor
manufacturer).

(
4)
At
least
quarterly,
inspect
all
components
of
the
moisture
monitor
for
integrity
and
all
electrical
connections
for
continuity.

(
5)
Use
Equation
1
of
this
section
to
convert
percent
moisture
measurements
wet
basis
to
a
dry
basis:

(
)(
)
MC
MC
/
100
1
MC
/
100
100
dry
wet
wet
=
 
(
Eq.
1)

Where:

MCdry
=
percent
moisture
content
of
wood
material
(
weight
percent,
dry
basis)
MCwet
=
percent
moisture
content
of
wood
material
(
weight
percent,
wet
basis)

(
d)
Continuous
emission
monitoring
system(
s).
Each
CEMS
must
be
installed,
operated,
and
maintained
according
to
paragraphs
(
d)(
1)
through
(
4)
of
this
section.

(
1)
Each
CEMS
for
monitoring
THC
concentration
must
be
installed,
operated,
and
maintained
according
to
Performance
Specification
8
of
40
CFR
part
60,
appendix
B.
You
must
also
comply
with
Procedure
1
of
40
CFR
part
60,
appendix
F.

(
2)
You
must
conduct
a
performance
evaluation
of
each
CEMS
according
to
the
requirements
in
40
CFR
63.8
and
according
to
Performance
Specification
8
of
40
CFR
part
60,
36
appendix
B.

(
3)
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.

(
4)
The
CEMS
data
must
be
reduced
as
specified
in
§
63.8(
g)(
2)
and
§
63.2270(
d)
and
(
e).

Continuous
Compliance
Requirements
§
63.2270
How
do
I
monitor
and
collect
data
to
demonstrate
continuous
compliance?

(
a)
You
must
monitor
and
collect
data
according
to
this
section.

(
b)
Except
for,
as
appropriate,
monitor
malfunctions,

associated
repairs,
and
required
quality
assurance
or
control
activities
(
including,
as
applicable,
calibration
checks
and
required
zero
and
span
adjustments),
you
must
conduct
all
monitoring
in
continuous
operation
at
all
times
that
the
process
unit
is
operating.
For
purposes
of
calculating
data
averages,
you
must
not
use
data
recorded
during
monitoring
malfunctions,
associated
repairs,

out­
of­
control
periods,
or
required
quality
assurance
or
control
activities.
You
must
use
all
the
data
collected
during
all
other
periods
in
assessing
compliance.
A
monitoring
malfunction
is
any
sudden,
infrequent,
not
reasonably
preventable
failure
of
the
monitoring
to
provide
valid
data.
Monitoring
failures
that
are
caused
in
part
by
37
poor
maintenance
or
careless
operation
are
not
malfunctions.

Any
period
for
which
the
monitoring
system
is
out­
of­
control
and
data
are
not
available
for
required
calculations
constitutes
a
deviation
from
the
monitoring
requirements.

(
c)
You
may
not
use
data
recorded
during
monitoring
malfunctions,
associated
repairs,
and
required
quality
assurance
or
control
activities;
data
recorded
during
periods
of
startup,
shutdown,
and
malfunction;
or
data
recorded
during
periods
of
control
device
downtime
covered
in
any
approved
routine
control
device
maintenance
exemption
in
data
averages
and
calculations
used
to
report
emission
or
operating
levels,
nor
may
such
data
be
used
in
fulfilling
a
minimum
data
availability
requirement,
if
applicable.
You
must
use
all
the
data
collected
during
all
other
periods
in
assessing
the
operation
of
the
control
system.

(
d)
Except
as
provided
in
paragraph
(
e)
of
this
section,
determine
the
3­
hour
block
average
of
all
recorded
readings,
calculated
after
every
3
hours
of
operation
as
the
average
of
the
evenly
spaced
recorded
readings
in
the
previous
3
operating
hours
(
excluding
periods
described
in
paragraphs
(
b)
and
(
c)
of
this
section).

(
e)
For
dry
rotary
dryer
and
veneer
redryer
wood
moisture
monitoring,
dry
rotary
dryer
temperature
monitoring,
biofilter
bed
temperature
monitoring,
and
biofilter
outlet
THC
monitoring,
determine
the
24­
hour
block
average
of
all
recorded
readings,
calculated
after
every
24
38
hours
of
operation
as
the
average
of
the
evenly
spaced
recorded
readings
in
the
previous
24
operating
hours
(
excluding
periods
described
in
paragraphs
(
b)
and
(
c)
of
this
section).

(
f)
To
calculate
the
data
averages
for
each
3­
hour
or
24­
hour
averaging
period,
you
must
have
at
least
75
percent
of
the
required
recorded
readings
for
that
period
using
only
recorded
readings
that
are
based
on
valid
data
(
i.
e.,
not
from
periods
described
in
paragraphs
(
b)
and
(
c)
of
this
section).

§
63.2271
How
do
I
demonstrate
continuous
compliance
with
the
compliance
options,
operating
requirements,
and
work
practice
requirements?

(
a)
You
must
demonstrate
continuous
compliance
with
the
compliance
options,
operating
requirements,
and
work
practice
requirements
in
§
§
63.2240
and
63.2241
that
apply
to
you
according
to
the
methods
specified
in
Tables
7
and
8
of
this
subpart.

(
b)
You
must
report
each
instance
in
which
you
did
not
meet
each
compliance
option,
operating
requirement,
and
work
practice
requirement
in
Tables
7
and
8
of
this
subpart
that
applies
to
you.
This
includes
periods
of
startup,
shutdown,

or
malfunction
and
periods
of
control
device
maintenance
specified
in
paragraphs
(
b)(
1)
through
(
3)
of
this
section.

These
instances
are
deviations
from
the
compliance
options,

operating
requirements,
and
work
practice
requirements
in
39
this
subpart.
These
deviations
must
be
reported
according
to
the
requirements
in
§
63.2281.

(
1)
During
periods
of
startup,
shutdown,
or
malfunction,
you
must
operate
in
accordance
with
the
SSMP.

(
2)
Consistent
with
§
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
SSMP.
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).

(
3)
Deviations
that
occur
during
periods
of
control
device
maintenance
covered
by
any
approved
routine
control
device
maintenance
exemption
are
not
violations
if
you
demonstrate
to
the
Administrator's
satisfaction
that
you
were
operating
in
accordance
with
the
approved
routine
control
device
maintenance
exemption.

Notifications,
Reports,
and
Records
§
63.2280
What
notifications
must
I
submit
and
when?

(
a)
You
must
submit
all
of
the
notifications
in
§
§
63.7(
b)
and
(
c),
63.8(
e),
(
f)(
4)
and
(
f)(
6),
63.9
(
b)

through
(
e),
and
(
g)
and
(
h)
by
the
dates
specified.

(
b)
You
must
submit
an
Initial
Notification
no
later
than
120
calendar
days
after
the
effective
date
of
the
subpart
or
after
initial
startup,
whichever
is
later,
as
40
specified
in
§
63.9(
b)(
2).

(
c)
If
you
are
required
to
conduct
a
performance
test,

you
must
submit
a
written
notification
of
intent
to
conduct
a
performance
test
at
least
60
calendar
days
before
the
performance
test
is
scheduled
to
begin
as
specified
in
§
63.7(
b)(
1).

(
d)
If
you
are
required
to
conduct
a
performance
test,

design
evaluation,
or
other
initial
compliance
demonstration
as
specified
in
Tables
4,
5,
and
6
of
this
subpart,
you
must
submit
a
Notification
of
Compliance
Status
as
specified
in
§
63.9(
h)(
2)(
ii).

(
1)
For
each
initial
compliance
demonstration
required
in
Table
5
or
6
of
this
subpart
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
the
completion
of
the
initial
compliance
demonstration.

(
2)
For
each
initial
compliance
demonstration
required
in
Tables
5
and
6
of
this
subpart
that
includes
a
performance
test
conducted
according
to
the
requirements
in
Table
4
of
this
subpart,
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
§
63.10(
d)(
2).

(
e)
If
you
request
a
routine
control
device
41
maintenance
exemption
according
to
§
63.2251,
you
must
submit
your
request
for
the
exemption
no
later
than
30
days
before
the
compliance
date.

(
f)
If
you
use
the
emissions
averaging
compliance
option
in
§
63.2240(
c),
you
must
submit
an
Emissions
Averaging
Plan
to
the
Administrator
for
approval
no
later
than
1
year
before
the
compliance
date
or
no
later
than
1
year
before
the
date
you
would
begin
using
an
emissions
average,
whichever
is
later.
The
Emissions
Averaging
Plan
must
include
the
information
in
paragraphs
(
f)(
1)
through
(
6)
of
this
section.

(
1)
Identification
of
all
the
process
units
to
be
included
in
the
emissions
average
indicating
which
process
units
will
be
used
to
generate
credits,
and
which
process
units
that
are
subject
to
compliance
options
in
Tables
1A
and
1B
of
this
subpart
will
be
uncontrolled
(
used
to
generate
debits)
or
under­
controlled
(
used
to
generate
debits
and
credits).

(
2)
Description
of
the
control
system
used
to
generate
emission
credits
for
each
process
unit
used
to
generate
credits.

(
3)
Determination
of
the
total
HAP
control
efficiency
for
the
control
system
used
to
generate
emission
credits
for
each
credit­
generating
process
unit.

(
4)
Calculation
of
the
RMR
and
AMR,
as
calculated
using
Equations
1
through
3
of
§
63.2240(
c)(
1).
42
(
5)
Documentation
of
total
HAP
measurements
made
according
to
§
63.2240(
c)(
2)(
iv)
and
other
relevant
documentation
to
support
calculation
of
the
RMR
and
AMR.

(
6)
A
summary
of
the
operating
parameters
you
will
monitor
and
monitoring
methods
for
each
debit­
generating
and
credit­
generating
process
unit.

(
g)
You
must
notify
the
Administrator
within
30
days
before
you
take
any
of
the
actions
specified
in
paragraphs
(
g)(
1)
through
(
3)
of
this
section.

(
1)
You
modify
or
replace
the
control
system
for
any
process
unit
subject
to
the
compliance
options
and
operating
requirements
in
this
subpart.

(
2)
You
shut
down
any
process
unit
included
in
your
Emissions
Averaging
Plan.

(
3)
You
change
a
continuous
monitoring
parameter
or
the
value
or
range
of
values
of
a
continuous
monitoring
parameter
for
any
process
unit
or
control
device.

§
63.2281
What
reports
must
I
submit
and
when?

(
a)
You
must
submit
each
report
in
Table
9
of
this
subpart
that
applies
to
you.

(
b)
Unless
the
Administrator
has
approved
a
different
schedule
for
submission
of
reports
under
§
63.10(
a),
you
must
submit
each
report
by
the
date
in
Table
9
of
this
subpart
and
as
specified
in
paragraphs
(
b)(
1)
through
(
5)
of
this
section.

(
1)
The
first
compliance
report
must
cover
the
period
43
beginning
on
the
compliance
date
that
is
specified
for
your
affected
source
in
§
63.2233
ending
on
June
30
or
December
31,
and
lasting
at
least
6
months,
but
less
than
12
months.

For
example,
if
your
compliance
date
is
March
1,
then
the
first
semiannual
reporting
period
would
begin
on
March
1
and
end
on
December
31.

(
2)
The
first
compliance
report
must
be
postmarked
or
delivered
no
later
than
July
31
or
January
31
for
compliance
periods
ending
on
June
30
and
December
31,
respectively.

(
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
for
the
semiannual
reporting
period
ending
on
June
30
and
December
31,
respectively.

(
5)
For
each
affected
source
that
is
subject
to
permitting
regulations
pursuant
to
40
CFR
part
70
or
71,
and
if
the
permitting
authority
has
established
dates
for
submitting
semiannual
reports
pursuant
to
§
70.6(
a)(
3)(
iii)(
A)
or
§
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
according
to
the
dates
in
paragraphs
(
b)(
1)
through
(
4)
of
this
section.
44
(
c)
The
compliance
report
must
contain
the
information
in
paragraphs
(
c)(
1)
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
actions
consistent
with
your
SSMP,
the
compliance
report
must
include
the
information
specified
in
§
63.10(
d)(
5)(
i).

(
5)
A
description
of
control
device
maintenance
performed
while
the
control
device
was
offline
and
one
or
more
of
the
process
units
controlled
by
the
control
device
was
operating,
including
the
information
specified
in
paragraphs
(
c)(
5)(
i)
through
(
iii)
of
this
section.

(
i)
The
date
and
time
when
the
control
device
was
shut
down
and
restarted.

(
ii)
Identification
of
the
process
units
that
were
operating
and
the
number
of
hours
that
each
process
unit
operated
while
the
control
device
was
offline.

(
iii)
A
statement
of
whether
or
not
the
control
device
maintenance
was
included
in
your
approved
routine
control
device
maintenance
exemption
developed
pursuant
to
§
63.2251.

If
the
control
device
maintenance
was
included
in
your
45
approved
routine
control
device
maintenance
exemption,
then
you
must
report
the
information
in
paragraphs
(
c)(
5)(
iii)(
A)

through
(
C)
of
this
section.

(
A)
The
total
amount
of
time
that
each
process
unit
controlled
by
the
control
device
operated
during
the
semiannual
compliance
period
and
during
the
previous
semiannual
compliance
period.

(
B)
The
amount
of
time
that
each
process
unit
controlled
by
the
control
device
operated
while
the
control
device
was
down
for
maintenance
covered
under
the
routine
control
device
maintenance
exemption
during
the
semiannual
compliance
period
and
during
the
previous
semiannual
compliance
period.

(
C)
Based
on
the
information
recorded
under
paragraphs
(
c)(
5)(
iii)(
A)
and
(
B)
of
this
section
for
each
process
unit,
compute
the
annual
percent
of
process
unit
operating
uptime
during
which
the
control
device
was
offline
for
routine
maintenance
using
Equation
1
of
this
section.

(
Eq.
1)
RM
DT
DT
PU
PU
p
c
p
c
=
+
+

Where:

RM
=
Annual
percentage
of
process
unit
uptime
during
which
control
device
is
down
for
routine
control
device
maintenance
PUp
=
Process
unit
uptime
for
the
previous
semiannual
compliance
period
46
PUc
=
Process
unit
uptime
for
the
current
semiannual
compliance
period
DTp
=
Control
device
downtime
claimed
under
the
routine
control
device
maintenance
exemption
for
the
previous
semiannual
compliance
period
DTc
=
Control
device
downtime
claimed
under
the
routine
control
device
maintenance
exemption
for
the
current
semiannual
compliance
period
(
6)
The
results
of
any
performance
tests
conducted
during
the
semiannual
reporting
period.

(
7)
If
there
are
no
deviations
from
any
applicable
compliance
option
or
operating
requirement,
and
there
are
no
deviations
from
the
requirements
for
work
practice
requirements
in
Table
8
of
this
subpart,
a
statement
that
there
were
no
deviations
from
the
compliance
options,

operating
requirements,
or
work
practice
requirements
during
the
reporting
period.

(
8)
If
there
were
no
periods
during
which
the
continuous
monitoring
system(
s)
(
CMS),
including
CEMS
and
CPMS,
was
out­
of­
control
as
specified
in
§
63.8(
c)(
7),
a
statement
that
there
were
no
periods
during
which
the
CMS
was
out­
of­
control
during
the
reporting
period.

(
d)
For
each
deviation
from
a
compliance
option
or
operating
requirement
and
for
each
deviation
from
the
work
practice
requirements
in
Table
8
of
this
subpart
that
occurs
at
an
affected
source
where
you
are
not
using
a
CMS
to
comply
with
the
compliance
options,
operating
requirements,

or
work
practice
requirements
in
this
subpart,
the
47
compliance
report
must
contain
the
information
in
paragraphs
(
c)(
1)
through
(
6)
of
this
section
and
the
information
in
paragraphs
(
d)(
1)
and
(
2)
of
this
section.
This
includes
periods
of
startup,
shutdown,
and
malfunction
and
routine
control
device
maintenance.

(
1)
The
total
operating
time
of
each
affected
source
during
the
reporting
period.

(
2)
Information
on
the
number,
duration,
and
cause
of
deviations
(
including
unknown
cause,
if
applicable),
as
applicable,
and
the
corrective
action
taken.

(
e)
For
each
deviation
from
a
compliance
option
or
operating
requirement
occurring
at
an
affected
source
where
you
are
using
a
CMS
to
comply
with
the
compliance
options
and
operating
requirements
in
this
subpart,
you
must
include
the
information
in
paragraphs
(
c)(
1)
through
(
6)
and
the
information
in
paragraphs
(
e)(
1)
through
(
11)
of
this
section.
This
includes
periods
of
startup,
shutdown,
and
malfunction
and
routine
control
device
maintenance.

(
1)
The
date
and
time
that
each
malfunction
started
and
stopped.

(
2)
The
date
and
time
that
each
CMS
was
inoperative,

except
for
zero
(
low­
level)
and
high­
level
checks.

(
3)
The
date,
time,
and
duration
that
each
CMS
was
out­
of­
control,
including
the
information
in
§
63.8(
c)(
8).

(
4)
The
date
and
time
that
each
deviation
started
and
stopped,
and
whether
each
deviation
occurred
during
a
period
48
of
startup,
shutdown,
or
malfunction;
during
a
period
of
control
device
maintenance
covered
in
your
approved
routine
control
device
maintenance
exemption;
or
during
another
period.

(
5)
A
summary
of
the
total
duration
of
the
deviation
during
the
reporting
period
and
the
total
duration
as
a
percent
of
the
total
source
operating
time
during
that
reporting
period.

(
6)
A
breakdown
of
the
total
duration
of
the
deviations
during
the
reporting
period
into
those
that
are
due
to
startup,
shutdown,
control
system
problems,
control
device
maintenance,
process
problems,
other
known
causes,

and
other
unknown
causes.

(
7)
A
summary
of
the
total
duration
of
CMS
downtime
during
the
reporting
period
and
the
total
duration
of
CMS
downtime
as
a
percent
of
the
total
source
operating
time
during
that
reporting
period.

(
8)
A
brief
description
of
the
process
units.

(
9)
A
brief
description
of
the
CMS.

(
10)
The
date
of
the
latest
CMS
certification
or
audit.

(
11)
A
description
of
any
changes
in
CMS,
processes,

or
controls
since
the
last
reporting
period.

(
f)
If
you
comply
with
the
emissions
averaging
compliance
option
in
§
63.2240(
c),
you
must
include
in
your
semiannual
compliance
report
calculations
based
on
operating
49
data
from
the
semiannual
reporting
period
that
demonstrate
that
actual
mass
removal
equals
or
exceeds
the
required
mass
removal.

(
g)
Each
affected
source
that
has
obtained
a
title
V
operating
permit
pursuant
to
40
CFR
part
70
or
71
must
report
all
deviations
as
defined
in
this
subpart
in
the
semiannual
monitoring
report
required
by
§
70.6(
a)(
3)(
iii)(
A)

or
§
71.6(
a)(
3)(
iii)(
A).
If
an
affected
source
submits
a
compliance
report
pursuant
to
Table
9
of
this
subpart
along
with,
or
as
part
of,
the
semiannual
monitoring
report
required
by
§
70.6(
a)(
3)(
iii)(
A)
or
§
71.6(
a)(
3)(
iii)(
A),
and
the
compliance
report
includes
all
required
information
concerning
deviations
from
any
compliance
option,
operating
requirement,
or
work
practice
requirement
in
this
subpart,

submission
of
the
compliance
report
shall
be
deemed
to
satisfy
any
obligation
to
report
the
same
deviations
in
the
semiannual
monitoring
report.
However,
submission
of
a
compliance
report
shall
not
otherwise
affect
any
obligation
the
affected
source
may
have
to
report
deviations
from
permit
requirements
to
the
permitting
authority.

§
63.2282
What
records
must
I
keep?

(
a)
You
must
keep
the
records
listed
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
50
Notification
of
Compliance
Status
that
you
submitted,

according
to
the
requirements
in
§
63.10(
b)(
2)(
xiv).

(
2)
The
records
in
§
63.6(
e)(
3)(
iii)
through
(
v)

related
to
startup,
shutdown,
and
malfunction.

(
3)
The
records
in
§
63.2250(
e)
relating
to
control
device
maintenance
and
documentation
of
your
approved
routine
control
device
maintenance
exemption,
if
you
request
such
an
exemption
under
§
63.2251.

(
4)
Records
of
performance
tests
and
performance
evaluations
as
required
in
§
63.10(
b)(
2)(
viii).

(
b)
You
must
keep
the
records
required
in
Tables
7
and
8
of
this
subpart
to
show
continuous
compliance
with
each
compliance
option,
operating
requirement,
and
work
practice
requirement
that
applies
to
you.

(
c)
For
each
CEMS,
you
must
keep
the
following
records.

(
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
testing
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.
51
(
d)
If
you
comply
with
the
emissions
averaging
compliance
option
in
§
63.2240(
c),
you
must
keep
records
of
all
information
required
to
calculate
emission
debits
and
credits.

(
e)
If
you
operate
a
catalytic
oxidizer,
you
must
keep
records
of
annual
catalyst
activity
checks
and
subsequent
corrective
actions.

§
63.2283
In
what
form
and
how
long
must
I
keep
my
records?

(
a)
Your
records
must
be
in
a
form
suitable
and
readily
available
for
expeditious
review
as
specified
in
§
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
on
site
for
at
least
2
years
after
the
date
of
each
occurrence,
measurement,

maintenance,
corrective
action,
report,
or
record
according
to
§
63.10(
b)(
1).
You
can
keep
the
records
offsite
for
the
remaining
3
years.

Other
Requirements
and
Information
§
63.2290
What
parts
of
the
General
Provisions
apply
to
me?

Table
10
of
this
subpart
shows
which
parts
of
the
General
Provisions
in
§
§
63.1
through
63.13
apply
to
you.

§
63.2291
Who
implements
and
enforces
this
subpart?

(
a)
This
subpart
can
be
implemented
and
enforced
by
52
the
U.
S.
EPA
or
a
delegated
authority
such
as
your
State,

local,
or
tribal
agency.
If
the
EPA
Administrator
has
delegated
authority
to
your
State,
local,
or
tribal
agency,

then
that
agency
has
the
authority
to
implement
and
enforce
this
subpart.
You
should
contact
your
EPA
Regional
Office
to
find
out
if
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
section
40
CFR
part
63,
subpart
E,
the
authorities
contained
in
paragraph
(
c)
of
this
section
are
retained
by
the
EPA
Administrator
and
are
not
transferred
to
the
State,
local,
or
tribal
agency.

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

(
1)
Approval
of
alternatives
to
the
compliance
options,
operating
requirements,
and
work
practice
requirements
in
§
§
63.2240
and
63.2241
as
specified
in
§
63.6(
g).
For
the
purposes
of
delegation
authority
under
40
CFR
part
63,
subpart
E,
"
compliance
options"
represent
"
emission
limits";
"
operating
requirements"
represent
"
operating
limits";
and
"
work
practice
requirements"

represent
"
work
practice
standards."

(
2)
Approval
of
major
alternatives
to
test
methods
as
specified
in
§
63.7(
e)(
2)(
ii)
and
(
f)
and
as
defined
in
53
§
63.90.

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

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

§
63.2292
What
definitions
apply
to
this
subpart?

Terms
used
in
this
subpart
are
defined
in
the
Clean
Air
Act,
in
40
CFR
63.2,
the
General
Provisions,
and
in
this
section
as
follows:

Affected
source
means
the
collection
of
dryers,

refiners,
blenders,
formers,
presses,
board
coolers,
and
other
process
units
associated
with
the
manufacturing
of
plywood
and
composite
wood
products.
The
affected
source
includes,
but
is
not
limited
to,
green
end
operations,

refining,
drying
operations,
resin
preparation,
blending
and
forming
operations,
pressing
and
board
cooling
operations,

and
miscellaneous
finishing
operations
(
such
as
sanding,

sawing,
patching,
edge
sealing,
and
other
finishing
operations
not
subject
to
other
NESHAP).
The
affected
source
also
includes
onsite
storage
of
raw
materials
used
in
the
manufacture
of
plywood
and/
or
composite
wood
products,

such
as
resins;
onsite
wastewater
treatment
operations
specifically
associated
with
plywood
and
composite
wood
products
manufacturing;
and
miscellaneous
coating
operations
(
defined
elsewhere
in
this
section).
The
affected
source
54
includes
lumber
kilns
at
PCWP
manufacturing
facilities
and
at
any
other
kind
of
facility.

Agricultural
fiber
means
the
fiber
of
an
annual
agricultural
crop.
Examples
of
agricultural
fibers
include
(
but
are
not
limited
to)
wheat
straw,
rice
straw,
and
bagasse.

Biofilter
means
an
enclosed
control
system
such
as
a
tank
or
series
of
tanks
with
a
fixed
roof
that
contact
emissions
with
a
solid
media
(
such
as
bark)
and
use
microbiological
activity
to
transform
organic
pollutants
in
a
process
exhaust
stream
to
innocuous
compounds
such
as
carbon
dioxide,
water,
and
inorganic
salts.
Wastewater
treatment
systems
such
as
aeration
lagoons
or
activated
sludge
systems
are
not
considered
to
be
biofilters.

Capture
device
means
a
hood,
enclosure,
or
other
means
of
collecting
emissions
into
a
duct
so
that
the
emissions
can
be
measured.

Capture
efficiency
means
the
fraction
(
expressed
as
a
percentage)
of
the
pollutants
from
an
emission
source
that
are
collected
by
a
capture
device.

Catalytic
oxidizer
means
a
control
system
that
combusts
or
oxidizes,
in
the
presence
of
a
catalyst,
exhaust
gas
from
a
process
unit.
Catalytic
oxidizers
include
regenerative
catalytic
oxidizers
and
thermal
catalytic
oxidizers.

Combustion
unit
means
a
dryer
burner,
process
heater,

or
boiler
used
for
combustion
of
organic
hazardous
air
55
pollutant
emissions.

Control
device
means
any
equipment
that
reduces
the
quantity
of
a
hazardous
air
pollutant
that
is
emitted
to
the
air.
The
device
may
destroy
the
hazardous
air
pollutant
or
secure
the
hazardous
air
pollutant
for
subsequent
recovery.

Control
devices
include,
but
are
not
limited
to,
thermal
or
catalytic
oxidizers,
combustion
units
that
incinerate
process
exhausts,
biofilters,
and
condensers.

Control
system
or
add­
on
control
system
means
the
combination
of
capture
and
control
devices
used
to
reduce
hazardous
air
pollutant
emissions
to
the
atmosphere.

Conveyor
strand
dryer
means
a
conveyor
dryer
used
to
reduce
the
moisture
of
wood
strands
used
in
the
manufacture
of
oriented
strandboard,
laminated
strand
lumber,
or
other
wood
strand­
based
products.
A
conveyor
strand
dryer
is
a
process
unit.

Conveyor
strand
dryer
zone
means
each
portion
of
a
conveyor
strand
dryer
with
a
separate
heat
exchange
system
and
exhaust
vent(
s).
Conveyor
strand
dryers
contain
multiple
zones
(
for
example,
three
zones),
which
may
be
divided
into
multiple
sections.

Deviation
means
any
instance
in
which
an
affected
source
subject
to
this
subpart,
or
an
owner
or
operator
of
such
a
source:

(
1)
Fails
to
meet
any
requirement
or
obligation
established
by
this
subpart
including,
but
not
limited
to,
56
any
compliance
option,
operating
requirement,
or
work
practice
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
affected
source
required
to
obtain
such
a
permit;
or
(
3)
Fails
to
meet
any
compliance
option,
operating
requirement,
or
work
practice
requirement
in
this
subpart
during
startup,
shutdown,
or
malfunction,
regardless
of
whether
or
not
such
failure
is
permitted
by
this
subpart.

Dryer
heated
zones
means
the
zones
of
a
softwood
veneer
dryer
or
fiberboard
mat
dryer
that
are
equipped
with
heating
and
hot
air
circulation
units.
The
cooling
zone(
s)
of
the
dryer
through
which
ambient
air
is
blown
are
not
part
of
the
dryer
heated
zones.

Dry
rotary
dryer
means
a
rotary
dryer
that
dries
wood
particles
or
fibers
with
a
maximum
inlet
moisture
content
of
less
than
or
equal
to
30
percent
(
by
weight,
dry
basis)
and
operates
with
a
maximum
inlet
temperature
of
less
than
or
equal
to
600oF.
A
dry
rotary
dryer
is
a
process
unit.

Dry
forming
means
the
process
of
making
a
mat
of
resinated
fiber
to
be
compressed
into
a
reconstituted
wood
product
such
as
particleboard,
oriented
strandboard
(
OSB),

medium
density
fiberboard
(
MDF),
or
hardboard.

Fiber
means
the
discrete
elements
of
wood
or
similar
cellulosic
material,
which
are
separated
by
mechanical
57
means,
as
in
refining,
that
can
be
formed
into
boards.

Fiberboard
means
a
composite
panel
composed
of
cellulosic
fibers
(
usually
wood
or
agricultural
material)

made
by
wet
forming
and
compacting
a
mat
of
fibers.

Fiberboard
density
generally
is
less
than
0.50
grams
per
cubic
centimeter
(
31.5
pounds
per
cubic
foot).

Fiberboard
mat
dryer
means
a
dryer
used
to
reduce
the
moisture
of
wet­
formed
wood
fiber
mats
by
operation
at
elevated
temperature.
A
fiberboard
mat
dryer
is
a
process
unit.

Flame
zone
means
the
portion
of
the
combustion
chamber
in
a
combustion
unit
that
is
occupied
by
the
flame
envelope.

Furnish
means
the
fibers,
particles,
or
strands
used
for
making
boards.

Glue­
laminated
beam
means
a
structural
wood
beam
made
by
bonding
lumber
together
along
its
faces
with
resin.

Green
rotary
dryer
means
a
rotary
dryer
that
dries
wood
particles
or
fibers
with
an
inlet
moisture
content
of
greater
than
30
percent
(
by
weight,
dry
basis)
at
any
dryer
inlet
temperature
or
operates
with
an
inlet
temperature
of
greater
than
600oF
with
any
inlet
moisture
content.
A
green
rotary
dryer
is
a
process
unit.

Group
1
miscellaneous
coating
operations
means
application
of
edge
seals,
nail
lines,
logo
(
or
other
information)
paint,
shelving
edge
fillers,

trademark/
gradestamp
inks,
and
wood
putty
patches
to
plywood
58
and
composite
wood
products
(
except
kiln­
dried
lumber)
on
the
same
site
where
the
plywood
and
composite
wood
products
are
manufactured.
Group
1
miscellaneous
coating
operations
also
include
application
of
synthetic
patches
to
plywood
at
new
affected
sources.

Hardboard
means
a
composite
panel
composed
of
interfelted
cellulosic
fibers
made
by
dry
or
wet
forming
and
pressing
of
a
resinated
fiber
mat.
Hardboard
generally
has
a
density
of
0.50
grams
per
cubic
centimeter
(
31.5
pounds
per
cubic
foot)
or
greater.

Hardboard
oven
means
an
oven
used
to
heat
treat
or
temper
hardboard
after
hot
pressing.
Humidification
chambers
are
not
considered
as
part
of
hardboard
ovens.
A
hardboard
oven
is
a
process
unit.

Hardwood
means
the
wood
of
a
broad­
leafed
tree,
either
deciduous
or
evergreen.
Examples
of
hardwoods
include
(
but
are
not
limited
to)
aspen,
birch,
poplar,
and
oak.

Hardwood
veneer
dryer
means
a
dryer
that
removes
excess
moisture
from
veneer
by
conveying
the
veneer
through
a
heated
medium
on
rollers,
belts,
cables,
or
wire
mesh.

Hardwood
veneer
dryers
are
used
to
dry
veneer
with
less
than
30
percent
softwood
species
on
an
annual
volume
basis.

Veneer
kilns
that
operate
as
batch
units,
veneer
dryers
heated
by
radio
frequency
or
microwaves
that
are
used
to
redry
veneer,
and
veneer
redryers
(
defined
elsewhere
in
this
section)
that
are
heated
by
conventional
means
are
not
59
considered
to
be
hardwood
veneer
dryers.
A
hardwood
veneer
dryer
is
a
process
unit.

Kiln­
dried
lumber
means
solid
wood
lumber
that
has
been
dried
in
a
lumber
kiln.

Laminated
strand
lumber
(
LSL)
means
a
composite
product
formed
into
a
billet
made
of
thin
wood
strands
cut
from
whole
logs,
resinated,
and
pressed
together
with
the
grain
of
each
strand
oriented
parallel
to
the
length
of
the
finished
product.

Laminated
veneer
lumber
(
LVL)
means
a
composite
product
formed
into
a
billet
made
from
layers
of
resinated
wood
veneer
sheets
or
pieces
pressed
together
with
the
grain
of
each
veneer
aligned
primarily
along
the
length
of
the
finished
product.
Laminated
veneer
lumber
includes
parallel
strand
lumber
(
PSL).

Lumber
kiln
means
an
enclosed
dryer
operated
at
elevated
temperature
to
reduce
the
moisture
content
of
lumber.

Medium
density
fiberboard
(
MDF)
means
a
composite
panel
composed
of
cellulosic
fibers
(
usually
wood
or
agricultural
fiber)
made
by
dry
forming
and
pressing
of
a
resinated
fiber
mat.

Method
detection
limit
means
the
minimum
concentration
of
an
analyte
that
can
be
determined
with
99
percent
confidence
that
the
true
value
is
greater
than
zero.

Miscellaneous
coating
operations
means
application
of
60
any
of
the
following
to
plywood
or
composite
wood
products:

edge
seals,
moisture
sealants,
anti­
skid
coatings,
company
logos,
trademark
or
grade
stamps,
nail
lines,
synthetic
patches,
wood
patches,
wood
putty,
concrete
forming
oils,

glues
for
veneer
composing,
and
shelving
edge
fillers.

Miscellaneous
coating
operations
also
include
the
application
of
primer
to
OSB
siding
that
occurs
at
the
same
site
as
OSB
manufacture
and
application
of
asphalt,
clay
slurry,
or
titanium
dioxide
coatings
to
fiberboard
at
the
same
site
of
fiberboard
manufacture.

MSF
means
thousand
square
feet
(
92.9
square
meters).

Square
footage
of
panels
is
usually
measured
on
a
thickness
basis,
such
as
3/
8­
inch,
to
define
the
total
volume
of
panels.
Equation
6
of
§
63.2262(
j)
shows
how
to
convert
from
one
thickness
basis
to
another.

Nondetect
data
means,
for
the
purposes
of
this
subpart,

any
value
that
is
below
the
method
detection
limit.

Non­
HAP
coating
means
a
coating
with
HAP
contents
below
0.1
percent
by
mass
for
OSHA­
defined
carcinogens
as
specified
in
29
CFR
1910.1200(
d)(
4),
and
below
1.0
percent
by
mass
for
other
HAP
compounds.

One­
hour
period
means
a
60­
minute
period.

Oriented
strandboard
(
OSB)
means
a
composite
panel
produced
from
thin
wood
strands
cut
from
whole
logs,
formed
into
resinated
layers
(
with
the
grain
of
strands
in
one
layer
oriented
perpendicular
to
the
strands
in
adjacent
61
layers),
and
pressed.

Oven­
dried
ton(
s)
(
ODT)
means
tons
of
wood
dried
until
all
of
the
moisture
in
the
wood
is
removed.
One
oven­
dried
ton
equals
907
oven­
dried
kilograms.

Partial
wood
products
enclosure
means
an
enclosure
that
does
not
meet
the
design
criteria
for
a
wood
products
enclosure,
as
defined
in
this
subpart.

Particle
means
a
discrete,
small
piece
of
cellulosic
material
(
usually
wood
or
agricultural
fiber)
produced
mechanically
and
used
as
the
aggregate
for
a
particleboard.

Particleboard
means
a
composite
panel
composed
primarily
of
cellulosic
materials
(
usually
wood
or
agricultural
fiber)
generally
in
the
form
of
discrete
pieces
or
particles,
as
distinguished
from
fibers,
which
are
pressed
together
with
resin.

Plywood
and
composite
wood
products
(
PCWP)

manufacturing
facility
means
a
facility
that
manufactures
plywood
and/
or
composite
wood
products
by
bonding
wood
material
(
fibers,
particles,
strands,
veneers,
etc.)
or
agricultural
fiber,
generally
with
resin
under
heat
and
pressure,
to
form
a
structural
panel
or
engineered
wood
product.
Plywood
and
composite
wood
products
manufacturing
facilities
also
include
facilities
that
manufacture
dry
veneer
and
lumber
kilns
located
at
any
facility.
Plywood
and
composite
wood
products
include
(
but
are
not
limited
to)

plywood,
veneer,
particleboard,
oriented
strandboard,
62
hardboard,
fiberboard,
medium
density
fiberboard,
laminated
strand
lumber,
laminated
veneer
lumber,
wood
I­
joists,

kilndried
lumber,
and
glue­
laminated
beams.

Plywood
means
a
panel
product
consisting
of
layers
of
wood
veneers
hot
pressed
together
with
resin.
Plywood
includes
panel
products
made
by
hot
pressing
(
with
resin)

veneers
to
a
substrate
such
as
particleboard,
MDF,
or
lumber.

Press
predryer
means
a
dryer
used
to
reduce
the
moisture
and
elevate
the
temperature
of
a
wet­
formed
fiber
mat
before
the
mat
enters
a
hot
press.
A
press
predryer
is
a
process
unit.

Pressurized
refiner
means
a
piece
of
equipment
operated
under
pressure
for
preheating
(
usually
by
steaming)
wood
material
and
refining
(
rubbing
or
grinding)
the
wood
material
into
fibers.
Pressurized
refiners
are
operated
with
continuous
infeed
and
outfeed
of
wood
material
and
maintain
elevated
internal
pressures
(
i.
e.,
there
is
no
pressure
release)
throughout
the
preheating
and
refining
process.
A
pressurized
refiner
is
a
process
unit.

Primary
tube
dryer
means
a
single­
stage
tube
dryer
or
the
first
stage
of
a
multi­
stage
tube
dryer.
Tube
dryer
stages
are
separated
by
vents
for
removal
of
moist
gases
between
stages
(
for
example,
a
product
cyclone
at
the
end
of
a
single­
stage
dryer
or
between
the
first
and
second
stages
of
a
multi­
stage
tube
dryer).
The
first
stage
of
a
multi­
63
stage
tube
dryer
is
used
to
remove
the
majority
of
the
moisture
from
the
wood
furnish
(
compared
to
the
moisture
reduction
in
subsequent
stages
of
the
tube
dryer).

Blowlines
used
to
apply
resin
are
considered
part
of
the
primary
tube
dryer.
A
primary
tube
dryer
is
a
process
unit.

Process
unit
means
equipment
classified
according
to
its
function
such
as
a
blender,
dryer,
press,
former,
or
board
cooler.

Reconstituted
wood
product
board
cooler
means
a
piece
of
equipment
designed
to
reduce
the
temperature
of
a
board
by
means
of
forced
air
or
convection
within
a
controlled
time
period
after
the
board
exits
the
reconstituted
wood
product
press
unloader.
Board
coolers
include
wicket
and
star
type
coolers
commonly
found
at
MDF
and
particleboard
plants.
Board
coolers
do
not
include
cooling
sections
of
dryers
(
e.
g.,
veneer
dryers
or
fiberboard
mat
dryers)
or
coolers
integrated
into
or
following
hardboard
bake
ovens
or
humidifiers.
A
reconstituted
wood
product
board
cooler
is
a
process
unit.

Reconstituted
wood
product
press
means
a
press,

including
(
if
applicable)
the
press
unloader,
that
presses
a
resinated
mat
of
wood
fibers,
particles,
or
strands
between
hot
platens
or
hot
rollers
to
compact
and
set
the
mat
into
a
panel
by
simultaneous
application
of
heat
and
pressure.

Reconstituted
wood
product
presses
are
used
in
the
manufacture
of
hardboard,
medium
density
fiberboard,
64
particleboard,
and
oriented
strandboard.
Extruders
are
not
considered
to
be
reconstituted
wood
product
presses.
A
reconstituted
wood
product
press
is
a
process
unit.

Representative
operating
conditions
means
operation
of
a
process
unit
during
performance
testing
under
the
conditions
that
the
process
unit
will
typically
be
operating
in
the
future,
including
use
of
a
representative
range
of
materials
(
e.
g.,
wood
material
of
a
typical
species
mix
and
moisture
content
or
typical
resin
formulation)
and
representative
operating
temperature
range.

Resin
means
the
synthetic
adhesive
(
including
glue)
or
natural
binder,
including
additives,
used
to
bond
wood
or
other
cellulosic
materials
together
to
produce
plywood
and
composite
wood
products.

Responsible
official
means
responsible
official
as
defined
in
40
CFR
70.2
and
71.2.

Rotary
strand
dryer
means
a
rotary
dryer
operated
at
elevated
temperature
and
used
to
reduce
the
moisture
of
wood
strands
used
in
the
manufacture
of
OSB,
LSL,
or
other
wood
strand­
based
products.
A
rotary
strand
dryer
is
a
process
unit.

Secondary
tube
dryer
means
the
second
stage
and
subsequent
stages
following
the
primary
stage
of
a
multistage
tube
dryer.
Secondary
tube
dryers,
also
referred
to
as
relay
dryers,
operate
at
lower
temperatures
than
the
primary
tube
dryer
they
follow.
Secondary
tube
dryers
are
65
used
to
remove
only
a
small
amount
of
the
furnish
moisture
compared
to
the
furnish
moisture
reduction
across
the
primary
tube
dryer.
A
secondary
tube
dryer
is
a
process
unit.

Softwood
means
the
wood
of
a
coniferous
tree.
Examples
of
softwoods
include
(
but
are
not
limited
to)
Southern
yellow
pine,
Douglas
fir,
and
White
spruce.

Softwood
veneer
dryer
means
a
dryer
that
removes
excess
moisture
from
veneer
by
conveying
the
veneer
through
a
heated
medium,
generally
on
rollers,
belts,
cables,
or
wire
mesh.
Softwood
veneer
dryers
are
used
to
dry
veneer
with
greater
than
or
equal
to
30
percent
softwood
species
on
an
annual
volume
basis.
Veneer
kilns
that
operate
as
batch
units,
veneer
dryers
heated
by
radio
frequency
or
microwaves
that
are
used
to
redry
veneer,
and
veneer
redryers
(
defined
elsewhere
in
this
section)
that
are
heated
by
conventional
means
are
not
considered
to
be
softwood
veneer
dryers.
A
softwood
veneer
dryer
is
a
process
unit.

Startup
means
bringing
equipment
online
and
starting
the
production
process.

Startup,
initial
means
the
first
time
equipment
is
put
into
operation.
Initial
startup
does
not
include
operation
solely
for
testing
equipment.
Initial
startup
does
not
include
subsequent
startups
(
as
defined
in
this
section)

following
malfunction
or
shutdowns
or
following
changes
in
product
or
between
batch
operations.
Initial
startup
does
66
not
include
startup
of
equipment
that
occurred
when
the
source
was
an
area
source.

Startup,
shutdown,
and
malfunction
plan
(
SSMP)
means
a
plan
developed
according
to
the
provisions
of
§
63.6(
e)(
3).

Strand
means
a
long
(
with
respect
to
thickness
and
width),
flat
wood
piece
specially
cut
from
a
log
for
use
in
oriented
strandboard,
laminated
strand
lumber,
or
other
wood
strand­
based
product.

Temporary
total
enclosure
(
TTE)
means
an
enclosure
constructed
for
the
purpose
of
measuring
the
capture
efficiency
of
pollutants
emitted
from
a
given
source,
as
defined
in
Method
204
of
40
CFR
part
51,
appendix
M.

Thermal
oxidizer
means
a
control
system
that
combusts
or
oxidizes
exhaust
gas
from
a
process
unit.
Thermal
oxidizers
include
regenerative
thermal
oxidizers
and
combustion
units.

Total
hazardous
air
pollutant
(
HAP)
emissions
means,

for
purposes
of
this
rulemaking,
the
sum
of
the
emissions
of
the
following
six
compounds:
acetaldehyde,
acrolein,

formaldehyde,
methanol,
phenol,
and
propionaldehyde.

Tube
dryer
means
a
single­
stage
or
multistage
dryer
operated
at
elevated
temperature
and
used
to
reduce
the
moisture
of
wood
fibers
or
particles
as
they
are
conveyed
(
usually
pneumatically)
through
the
dryer.
Resin
may
or
may
not
be
applied
to
the
wood
material
before
it
enters
the
tube
dryer.
A
tube
dryer
is
a
process
unit.
67
Veneer
means
thin
sheets
of
wood
peeled
or
sliced
from
logs
for
use
in
the
manufacture
of
wood
products
such
as
plywood,
laminated
veneer
lumber,
or
other
products.

Veneer
redryer
means
a
dryer
heated
by
conventional
means,
such
as
direct
wood­
fired,
direct­
gas­
fired,
or
steam
heated,
that
is
used
to
redry
veneer
that
has
been
previously
dried.
Because
the
veneer
dried
in
a
veneer
redryer
has
been
previously
dried,
the
inlet
moisture
content
of
the
veneer
entering
the
redryer
is
less
than
25
percent
(
by
weight,
dry
basis).
Batch
units
used
to
redry
veneer
(
such
as
redry
cookers)
are
not
considered
to
be
veneer
redryers.
A
veneer
redryer
is
a
process
unit.

Wet
control
device
means
any
equipment
that
uses
water
as
a
means
of
collecting
an
air
pollutant.
Wet
control
devices
include
scrubbers,
wet
electrostatic
precipitators,

and
electrified
filter
beds.
Wet
control
devices
do
not
include
biofilters
or
other
equipment
that
destroys
or
degrades
hazardous
air
pollutants.

Wet
forming
means
the
process
of
making
a
slurry
of
water,
fiber,
and
additives
into
a
mat
of
fibers
to
be
compressed
into
a
fiberboard
or
hardboard
product.

Wood
I­
joists
means
a
structural
wood
beam
with
an
Ishaped
cross
section
formed
by
bonding
(
with
resin)
wood
or
laminated
veneer
lumber
flanges
onto
a
web
cut
from
a
panel
such
as
plywood
or
oriented
strandboard.

Wood
products
enclosure
means
a
permanently
installed
68
containment
that
was
designed
to
meet
the
following
physical
design
criteria:

1.
Any
natural
draft
opening
(
NDO)
shall
be
at
least
four
equivalent
opening
diameters
from
each
HAP­
emitting
point,
except
for
where
board
enters
and
exits
the
enclosure,
unless
otherwise
specified
by
the
Administrator.

2.
The
total
area
of
all
NDOs
shall
not
exceed
5
percent
of
the
surface
area
of
the
enclosure's
four
walls,
floor,
and
ceiling.

3.
The
average
facial
velocity
(
FV)
of
air
through
all
NDOs
shall
be
at
least
3,600
meters
per
hour
(
200
feet
per
minute).
The
direction
of
airflow
through
all
NDOs
shall
be
into
the
enclosure.

4.
All
access
doors
and
windows
whose
areas
are
not
included
in
2
and
are
not
included
in
the
calculation
of
FV
in
3
shall
be
closed
during
routine
operation
of
the
process.

5.
The
enclosure
is
designed
and
maintained
to
capture
all
emissions
for
discharge
through
a
control
device.

Work
practice
requirement
means
any
design,
equipment,

work
practice,
or
operational
standard,
or
combination
thereof,
that
is
promulgated
pursuant
to
section
112(
h)
of
the
Clean
Air
Act.
69
70
Table
1A
to
Subpart
DDDD
of
Part
63.
Production­
Based
Compliance
Options
For
the
following
process
units...
You
must
meet
the
following
production­
based
compliance
option
(
total
HAPa
basis)...

(
1)
fiberboard
mat
dryer
heated
zones
(
at
new
affected
sources
only)
0.022
lb/
MSF
1/
2"

(
2)
green
rotary
dryers
0.058
lb/
ODT
(
3)
hardboard
ovens
0.022
lb/
MSF
1/
8"

(
4)
press
predryers
(
at
new
affected
sources
only)
0.037
lb/
MSF
1/
2"

(
5)
pressurized
refiners
0.039
lb/
ODT
(
6)
primary
tube
dryers
0.26
lb/
ODT
(
7)
reconstituted
wood
product
board
coolers
(
at
new
affected
sources
only)
0.014
lb/
MSF
3/
4"

(
8)
reconstituted
wood
product
presses
0.30
lb/
MSF
3/
4"

(
9)
softwood
veneer
dryer
heated
zones
0.022
lb/
MSF
3/
8"

(
10)
rotary
strand
dryers
0.18
lb/
ODT
(
11)
secondary
tube
dryers
0.010
lb/
ODT
aTotal
HAP,
as
defined
in
§
63.2292,
includes
acetaldehyde,
acrolein,
formaldehyde,
methanol,
phenol,
and
propionaldehyde.
lb/
ODT
=
pounds
per
oven­
dried
ton;
lb/
MSF
=
pounds
per
thousand
square
feet
with
a
specified
thickness
basis
(
inches).
Section
63.2262(
j)
shows
how
to
convert
from
one
thickness
basis
to
another.
Note:
There
is
no
production­
based
compliance
option
for
conveyor
strand
dryers.
71
Table
1B
to
Subpart
DDDD
of
Part
63.
Add­
on
Control
Systems
Compliance
Options
For
each
of
the
following
process
units...
You
must
comply
with
one
of
the
following
six
compliance
options
by
using
an
emissions
control
system...

Fiberboard
mat
dryer
heated
zones
(
at
new
affected
sources
only);
green
rotary
dryers;
hardboard
ovens;
press
predryers
(
at
new
affected
sources
only);
pressurized
refiners;
tube
dryers;
reconstituted
wood
product
board
coolers
(
at
new
affected
sources
only);
reconstituted
wood
product
presses;
softwood
veneer
dryer
heated
zones;
rotary
strand
dryers;
conveyor
strand
dryer
zone
one
(
at
existing
affected
sources);
and
conveyor
strand
dryer
zones
one
and
two
(
at
new
affected
sources)
(
1)
reduce
emissions
of
total
HAP,
measured
as
THC
(
as
carbon)
a,
by
90
percent;
or
(
2)
limit
emissions
of
total
HAP,
measured
as
THC
(
as
carbon)
a,
to
20
parts
per
million
by
volume,
dry
(
ppmvd);
or
(
3)
reduce
methanol
emissions
by
90
percent;
or
(
4)
limit
methanol
emissions
to
less
than
or
equal
to
1
ppmvd
if
uncontrolled
methanol
emissions
entering
the
control
device
are
greater
than
or
equal
to
10
ppmvd;
or
(
5)
reduce
formaldehyde
emissions
by
90
percent;
or
(
6)
limit
formaldehyde
emissions
to
less
than
or
equal
to
1
ppmvd
if
uncontrolled
formaldehyde
emissions
entering
the
control
device
are
greater
than
or
equal
to
10
ppmvd.

aYou
may
choose
to
subtract
methane
from
THC
as
carbon
measurements.
72
Table
2
to
Subpart
DDDD
of
Part
63.
Operating
Requirements
If
you
operate
a(
n)
...
you
must...
or
you
must...

(
1)
thermal
oxidizer
maintain
the
3­
hour
block
average
firebox
temperature
above
the
minimum
temperature
established
during
the
performance
test
maintain
the
3­
hour
block
average
THC
concentrationa
in
the
thermal
oxidizer
exhaust
below
the
maximum
concentration
established
during
the
performance
test.

(
2)
catalytic
oxidizer
maintain
the
3­
hour
block
average
catalytic
oxidizer
temperature
above
the
minimum
temperature
established
during
the
performance
test;
AND
check
the
activity
level
of
a
representative
sample
of
the
catalyst
at
least
every
12
months
maintain
the
3­
hour
block
average
THC
concentrationa
in
the
catalytic
oxidizer
exhaust
below
the
maximum
concentration
established
during
the
performance
test.

(
3)
biofilter
maintain
the
24­
hour
block
biofilter
bed
temperature
within
the
range
established
according
to
§
63.2262(
m)
maintain
the
24­
hour
block
average
THC
concentrationa
in
the
biofilter
exhaust
below
the
maximum
concentration
established
during
the
performance
test.

(
4)
control
device
other
than
a
thermal
oxidizer,
catalytic
oxidizer,
or
biofilter
petition
the
Administrator
for
site­
specific
operating
parameter(
s)
to
be
established
during
the
performance
test
and
maintain
the
average
operating
parameter(
s)
within
the
range(
s)
established
during
the
performance
test
maintain
the
3­
hour
block
average
THC
concentrationa
in
the
control
device
exhaust
below
the
maximum
concentration
established
during
the
performance
test.

(
5)
process
unit
that
meets
a
compliance
option
in
table
1a
of
this
subpart,
or
a
process
unit
that
generates
debits
in
an
emissions
average
without
the
use
of
a
control
device
maintain
on
a
daily
basis
the
process
unit
controlling
operating
parameter(
s)
within
the
ranges
established
during
the
performance
test
according
to
§
63.2262(
n)
maintain
the
3­
hour
block
average
THC
concentrationa
in
the
process
unit
exhaust
below
the
maximum
concentration
established
during
the
performance
test.

aYou
may
choose
to
subtract
methane
from
THC
measurements.
73
Table
3
to
Subpart
DDDD
of
Part
63.
Work
Practice
Requirements
For
the
following
process
units
at
existing
or
new
affected
sources...
You
must...

(
1)
dry
rotary
dryers
process
furnish
with
a
24­
hour
block
average
inlet
moisture
content
of
less
than
or
equal
to
30
percent
(
by
weight,
dry
basis);
AND
operate
with
a
24­
hour
block
average
inlet
dryer
temperature
of
less
than
or
equal
to
600oF.

(
2)
hardwood
veneer
dryers
process
less
than
30
volume
percent
softwood
species
on
an
annual
basis.

(
3)
softwood
veneer
dryers
minimize
fugitive
emissions
from
the
dryer
doors
through
(
proper
maintenance
procedures)
and
the
green
end
of
the
dryers
(
though
proper
balancing
of
the
heated
zone
exhausts).

(
4)
veneer
redryers
process
veneer
that
has
been
previously
dried,
such
that
the
24­
hour
block
average
inlet
moisture
content
of
the
veneer
is
less
than
or
equal
to
25
percent
(
by
weight,
dry
basis).

(
5)
group
1
miscellaneous
coating
operations
use
non­
HAP
coatings
as
defined
in
§
63.2292
74
Table
4
to
Subpart
DDDD
of
Part
63.
Requirements
for
Performance
Tests
For...
You
must...
Using...

(
1)
each
process
unit
subject
to
a
compliance
option
in
Table
1A
or
1B
of
this
subpart
or
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
select
sampling
port's
location
and
the
number
of
traverse
ports
Method
1
or
1A
of
40
CFR
part
60,
appendix
A
(
as
appropriate).

(
2)
each
process
unit
subject
to
a
compliance
option
in
Table
1A
or
1B
of
this
subpart
or
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
determine
velocity
and
volumetric
flow
rate
Method
2
in
addition
to
Method
2A,
2C,
2D,
2F,
or
2G
in
appendix
A
to
40
CFR
part
60
(
as
appropriate).

(
3)
each
process
unit
subject
to
a
compliance
option
in
Table
1A
or
1B
of
this
subpart
or
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
conduct
gas
molecular
weight
analysis
Method
3,
3A,
or
3B
in
appendix
A
to
40
CFR
part
60
(
as
appropriate).

(
4)
each
process
unit
subject
to
a
compliance
option
in
Table
1A
or
1B
of
this
subpart
or
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
measure
moisture
content
of
the
stack
gas
Method
4
in
appendix
A
to
40
CFR
part
60;
OR
Method
320
in
appendix
A
to
40
CFR
part
63;
OR
ASTM
D6348­
03
(
incorporated
by
reference,
see
§
63.14(
f))

(
5)
each
process
unit
subject
to
a
compliance
option
in
Table
1B
of
this
subpart
for
which
you
choose
to
demonstrate
compliance
using
a
total
HAP
as
THC
compliance
option
measure
emissions
of
total
HAP
as
THC
Method
25A
in
appendix
A
to
40
CFR
part
60.
You
may
measure
emissions
of
methane
using
EPA
Method
18
in
appendix
A
to
40
CFR
part
60
and
subtract
the
methane
emissions
from
the
emissions
of
total
HAP
as
THC.

(
6)
each
process
unit
subject
to
a
compliance
option
in
Table
1A;
OR
for
each
process
unit
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
measure
emissions
of
total
HAP
(
as
defined
in
§
63.2292)
Method
320
in
appendix
A
to
40
CFR
part
63;
OR
the
NCASI
Method
IM/
CAN/
WP­
99.02
(
incorporated
by
reference,
see
§
63.14(
f));
OR
ASTM
D6348­
03
provided
that
%
R
as
determined
in
Annex
A5
of
ASTM
D6348­
03
is
equal
or
greater
than
70%
and
less
than
or
equal
to
130%.
75
(
7)
each
process
unit
subject
to
a
compliance
option
in
Table
1B
of
this
subpart
for
which
you
choose
to
demonstrate
compliance
using
a
methanol
compliance
option
measure
emissions
of
methanol
Method
308
in
appendix
A
to
40
CFR
part
63;
OR
Method
320
in
appendix
A
to
40
CFR
part
63;
OR
the
NCASI
Method
CI/
WP­
98.01
(
incorporated
by
reference,
see
§
63.14(
f));
OR
the
NCASI
Method
IM/
CAN/
WP­
99.02
(
incorporated
by
reference,
see
§
63.14(
f)).

(
8)
each
process
unit
subject
to
a
compliance
option
in
Table
1B
of
this
subpart
for
which
you
choose
to
demonstrate
compliance
using
a
formaldehyde
compliance
option
measure
emissions
of
formaldehyde
Method
316
in
appendix
A
to
40
CFR
part
63;
OR
Method
320
in
appendix
A
to
40
CFR
part
63;
OR
Method
0011
in
"
Test
Methods
for
Evaluating
Solid
Waste,
Physical/
Chemical
Methods"
(
EPA
Publication
No.
SW­
846)
for
formaldehyde;
OR
the
NCASI
Method
CI/
WP­
98.01
(
incorporated
by
reference,
see
§
63.14(
f));
OR
the
NCASI
Method
IM/
CAN/
WP­
99.02
(
incorporated
by
reference,
see
§
63.14(
f)).
76
(
9)
each
reconstituted
wood
product
press
at
a
new
or
existing
affected
source
or
reconstituted
wood
product
board
cooler
at
a
new
affected
source
subject
to
a
compliance
option
in
Table
1B
or
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
meet
the
design
specifications
included
in
the
definition
of
wood
products
enclosure
in
§
63.2292
OR
determine
the
percent
capture
efficiency
of
the
enclosure
directing
emissions
to
an
add­
on
control
device
Methods
204
and
204A
through
204F
of
40
CFR
part
51,
appendix
M
to
determine
capture
efficiency
(
except
for
wood
products
enclosures
as
defined
in
§
63.2292).
Enclosures
that
meet
the
definition
of
wood
products
enclosure
or
that
meet
Method
204
requirements
for
a
PTE
are
assumed
to
have
a
capture
efficiency
of
100
percent.
Enclosures
that
do
not
meet
either
the
PTE
requirements
or
design
criteria
for
a
wood
products
enclosure
must
determine
the
capture
efficiency
by
constructing
a
TTE
according
to
the
requirements
of
Method
204
and
applying
Methods
204A
through
204F
(
as
appropriate).
As
an
alternative
to
Methods
204
and
204A
through
204F,
you
may
use
the
tracer
gas
method
contained
in
appendix
A
to
this
subpart.

(
10)
each
reconstituted
wood
product
press
at
a
new
or
existing
affected
source
or
reconstituted
wood
product
board
cooler
at
a
new
affected
source
subject
to
a
compliance
option
in
Table
1A
of
this
subpart
determine
the
percent
capture
efficiency
a
TTE
and
Methods
204
and
204A
through
204F
(
as
appropriate)
of
40
CFR
part
51,
appendix
M.
As
an
alternative
to
installing
a
TTE
and
using
Methods
204
and
204A
through
204F,
you
may
use
the
tracer
gas
method
contained
in
appendix
A
to
this
subpart.

(
11)
each
process
unit
subject
to
a
compliance
option
in
Tables
1A
and
1B
of
this
subpart
or
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
establish
the
sitespecific
operating
requirements
(
including
the
parameter
limits
or
THC
concentration
limits)
in
Table
2
of
this
subpart
data
from
the
parameter
monitoring
system
or
THC
CEMS
and
the
applicable
performance
test
method(
s).
77
Table
5
to
Subpart
DDDD
of
Part
63.
Performance
Testing
and
Initial
Compliance
Demonstrations
for
the
Compliance
Options
and
Operating
Requirements
For
each...
For
the
following
compliance
options
and
operating
requirements
...
You
have
demonstrated
initial
compliance
if...

(
1)
process
unit
listed
in
Table
1A
of
this
subpart
meet
the
production­
based
compliance
options
listed
in
Table
1A
of
this
subpart
the
average
total
HAP
emissions
measured
using
the
methods
in
Table
4
of
this
subpart
over
the
3­
hour
performance
test
are
no
greater
than
the
compliance
option
in
Table
1A
of
this
subpart;
AND
you
have
a
record
of
the
operating
requirement(
s)
listed
in
Table
2
of
this
subpart
for
the
process
unit
over
the
performance
test
during
which
emissions
did
not
exceed
the
compliance
option
value.

(
2)
process
unit
listed
in
Table
1B
of
this
subpart
reduce
emissions
of
total
HAP,
measured
as
THC,
by
90
percent
total
HAP
emissions,
measured
using
the
methods
in
Table
4
of
this
subpart
over
the
3­
hour
performance
test,
are
reduced
by
at
least
90
percent,
as
calculated
using
the
procedures
in
§
63.2262;
AND
you
have
a
record
of
the
operating
requirement(
s)
listed
in
Table
2
of
this
subpart
for
the
process
unit
over
the
performance
test
during
which
emissions
were
reduced
by
at
least
90
percent.

(
3)
process
unit
listed
in
Table
1B
of
this
subpart
limit
emissions
of
total
HAP,
measured
as
THC,
to
20
ppmvd
the
average
total
HAP
emissions,
measured
using
the
methods
in
Table
4
of
this
subpart
over
the
3­
hour
performance
test,
do
not
exceed
20
ppmvd;
AND
you
have
a
record
of
the
operating
requirement(
s)
listed
in
Table
2
of
this
subpart
for
the
process
unit
over
the
performance
test
during
which
emissions
did
not
exceed
20
ppmvd.
78
(
4)
process
unit
listed
in
Table
1B
of
this
subpart
reduce
methanol
or
formaldehyde
emissions
by
90
percent
the
methanol
or
formaldehyde
emissions
measured
using
the
methods
in
Table
4
of
this
subpart
over
the
3­
hour
performance
test,
are
reduced
by
at
least
90
percent,
as
calculated
using
the
procedures
in
§
63.2262;
AND
you
have
a
record
of
the
operating
requirement(
s)
listed
in
Table
2
of
this
subpart
for
the
process
unit
over
the
performance
test
during
which
emissions
were
reduced
by
at
least
90
percent.

(
5)
process
unit
listed
in
Table
1B
of
this
subpart
limit
methanol
or
formaldehyde
emissions
to
less
than
or
equal
to
1
ppmvd
(
if
uncontrolled
emissions
are
greater
than
or
equal
to
10
ppmvd)
the
average
methanol
or
formaldehyde
emissions,
measured
using
the
methods
in
Table
4
of
this
subpart
over
the
3­
hour
performance
test,
do
not
exceed
1
ppmvd;
AND
you
have
a
record
of
the
operating
requirement(
s)
listed
in
Table
2
of
this
subpart
for
the
process
unit
over
the
performance
test
during
which
emissions
did
not
exceed
1
ppmvd.
If
the
process
unit
is
a
reconstituted
wood
product
press
or
a
reconstituted
wood
product
board
cooler,
your
capture
device
either
meets
the
EPA
Method
204
criteria
for
a
PTE
or
achieves
a
capture
efficiency
of
greater
than
or
equal
to
95
percent.

(
6)
reconstituted
wood
product
press
at
a
new
or
existing
affected
source,
or
reconstituted
wood
product
board
cooler
at
a
new
affected
source
compliance
options
in
Tables
1A
and
1B
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
you
submit
the
results
of
capture
efficiency
verification
using
the
methods
in
Table
4
of
this
subpart
with
your
Notification
of
Compliance
Status.

(
7)
process
unit
listed
in
Table
1B
of
this
subpart
controlled
by
routing
exhaust
to
a
combustion
unit
compliance
options
in
Table
1B
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
you
submit
with
your
Notification
of
Compliance
Status
documentation
showing
that
the
process
exhausts
controlled
enter
into
the
flame
zone
of
your
combustion
unit.

(
8)
process
unit
listed
in
Table
1B
of
this
subpart
using
a
wet
control
device
as
the
sole
means
of
reducing
HAP
emissions
compliance
options
in
Table
1B
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
you
submit
with
your
Notification
of
Compliance
Status
your
plan
to
address
how
organic
HAP
captured
in
the
wastewater
from
the
wet
control
device
is
contained
or
destroyed
to
minimize
re­
release
to
the
atmosphere.
79
Table
6
to
Subpart
DDDD
of
Part
63.
Initial
Compliance
Demonstrations
for
Work
Practice
Requirements
For
each...
For
the
following
work
practice
requirements...
You
have
demonstrated
initial
compliance
if...

(
1)
dry
rotary
dryer
process
furnish
with
an
inlet
moisture
content
less
than
or
equal
to
30
percent
(
by
weight,
dry
basis)
AND
operate
with
an
inlet
dryer
temperature
of
less
than
or
equal
to
600oF
you
meet
the
work
practice
requirement
AND
you
submit
a
signed
statement
with
the
Notification
of
Compliance
Status
that
the
dryer
meets
the
criteria
of
a
"
dry
rotary
dryer"
AND
you
have
a
record
of
the
inlet
moisture
content
and
inlet
dryer
temperature
(
as
required
in
§
63.2263).

(
2)
hardwood
veneer
dryer
process
less
than
30
volume
percent
softwood
species
you
meet
the
work
practice
requirement
AND
you
submit
a
signed
statement
with
the
Notification
of
Compliance
Status
that
the
dryer
meets
the
criteria
of
a
"
hardwood
veneer
dryer"
AND
you
have
a
record
of
the
percentage
of
softwoods
processed
in
the
dryer
(
as
required
in
§
63.2264).

(
3)
softwood
veneer
dryer
minimize
fugitive
emissions
from
the
dryer
doors
and
the
green
end
you
meet
the
work
practice
requirement
AND
you
submit
with
the
Notification
of
Compliance
Status
a
copy
of
your
plan
for
minimizing
fugitive
emissions
from
the
veneer
dryer
heated
zones
(
as
required
in
§
63.2265).

(
4)
veneer
redryers
process
veneer
with
an
inlet
moisture
content
of
less
than
or
equal
to
25
percent
(
by
weight,
dry
basis)
you
meet
the
work
practice
requirement
AND
you
submit
a
signed
statement
with
the
Notification
of
Compliance
Status
that
the
dryer
operates
only
as
a
redryer
AND
you
have
a
record
of
the
veneer
inlet
moisture
content
of
the
veneer
processed
in
the
redryer
(
as
required
in
§
63.2266).

(
5)
group
1
miscellaneous
coating
operations
use
non­
HAP
coatings
as
defined
in
§
63.2292
you
meet
the
work
practice
requirement
AND
you
submit
a
signed
statement
with
the
Notification
of
Compliance
Status
that
you
are
using
non­
HAP
coatings
AND
you
have
a
record
showing
that
you
are
using
non­
HAP
coatings.
80
Table
7
to
Subpart
DDDD
of
Part
63.
Continuous
Compliance
With
the
Compliance
Options
and
Operating
Requirements
For...
For
the
following
compliance
options
and
operating
requirements...
You
must
demonstrate
continuous
compliance
by...

(
1)
each
process
unit
listed
in
Table
1B
of
this
subpart
or
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
compliance
options
in
Table
1B
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
and
the
operating
requirements
in
Table
2
of
this
subpart
based
on
monitoring
of
operating
parameters
collecting
and
recording
the
operating
parameter
monitoring
system
data
listed
in
Table
2
of
this
subpart
for
the
process
unit
according
to
§
63.2269(
a)­(
b)
and
§
63.2270;
AND
reducing
the
operating
parameter
monitoring
system
data
to
the
specified
averages
in
units
of
the
applicable
requirement
according
to
calculations
in
§
63.2270;
AND
maintaining
the
average
operating
parameter
at
or
above
the
minimum,
at
or
below
the
maximum,
or
within
the
range
(
whichever
applies)
established
according
to
§
63.2262.

(
2)
each
process
unit
listed
in
Tables
1A
and
1B
of
this
subpart
or
used
in
calculation
of
an
emissions
average
under
§
63.2240(
c)
compliance
options
in
Tables
1A
and
1B
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
and
the
operating
requirements
in
Table
2
of
this
subpart
based
on
THC
CEMS
data
collecting
and
recording
the
THC
monitoring
data
listed
in
Table
2
of
this
subpart
for
the
process
unit
according
to
§
63.2269(
d);
AND
reducing
the
CEMS
data
to
3­
hour
block
averages
according
to
calculations
in
§
63.2269(
d);
AND
maintaining
the
3­
hour
block
average
THC
concentration
in
the
exhaust
gases
less
than
or
equal
to
the
THC
concentration
established
according
to
§
63.2262.

(
3)
each
process
unit
using
a
biofilter
compliance
options
in
Table
1B
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
conducting
a
repeat
performance
test
using
the
applicable
method(
s)
specified
in
Table
4
of
this
subpart
within
2
years
following
the
previous
performance
test
and
within
180
days
after
each
replacement
of
any
portion
of
the
biofilter
bed
media
with
a
different
type
of
media
or
each
replacement
of
more
than
50
percent
(
by
volume)
of
the
biofilter
bed
media
with
the
same
type
of
media.
81
Table
7
to
Subpart
DDDD
of
Part
63.
Continuous
Compliance
With
the
Compliance
Options
and
Operating
Requirements
For...
For
the
following
compliance
options
and
operating
requirements...
You
must
demonstrate
continuous
compliance
by...

(
4)
each
process
unit
using
a
catalytic
oxidizer
compliance
options
in
Table
1B
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
checking
the
activity
level
of
a
representative
sample
of
the
catalyst
at
least
every
12
months
and
taking
any
necessary
corrective
action
to
ensure
that
the
catalyst
is
performing
within
its
design
range.

(
5)
each
process
unit
listed
in
Table
1A
of
this
subpart,
or
each
process
unit
without
a
control
device
used
in
calculation
of
an
emissions
averaging
debit
under
§
63.2240(
c)
compliance
options
in
Table
1A
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
and
the
operating
requirements
in
Table
2
of
this
subpart
based
on
monitoring
of
process
unit
controlling
operating
parameters
collecting
and
recording
on
a
daily
basis
process
unit
controlling
operating
parameter
data;
AND
maintaining
the
operating
parameter
at
or
above
the
minimum,
at
or
below
the
maximum,
or
within
the
range
(
whichever
applies)
established
according
to
§
63.2262.

(
6)
process
unit
listed
in
Table
1B
of
this
subpart
using
a
wet
control
device
as
the
sole
means
of
reducing
HAP
emissions
compliance
options
in
Table
1B
of
this
subpart
or
the
emissions
averaging
compliance
option
in
§
63.2240(
c)
implementing
your
plan
to
address
how
organic
HAP
captured
in
the
wastewater
from
the
wet
control
device
is
contained
or
destroyed
to
minimize
re­
release
to
the
atmosphere.
82
Table
8
to
Subpart
DDDD
of
Part
63.
Continuous
Compliance
With
the
Work
Practice
Requirements
For...
For
the
following
work
practice
requirements...
You
must
demonstrate
continuous
compliance
by...

(
1)
dry
rotary
dryer
process
furnish
with
an
inlet
moisture
content
less
than
or
equal
to
30
percent
(
by
weight,
dry
basis)
AND
operate
with
an
inlet
dryer
temperature
of
less
than
or
equal
to
600oF
maintaining
the
24­
hour
block
average
inlet
furnish
moisture
content
at
less
than
or
equal
to
30
percent
(
by
weight,
dry
basis)
AND
maintaining
the
24­
hour
block
average
inlet
dryer
temperature
at
less
than
or
equal
to
600oF;
AND
keeping
records
of
the
inlet
furnish
moisture
content
and
inlet
dryer
temperature.

(
2)
hardwood
veneer
dryer
process
less
than
30
volume
percent
softwood
species
maintaining
the
volume
percent
softwood
species
processed
below
30
percent
AND
keeping
records
of
the
volume
percent
softwood
species
processed.

(
3)
softwood
veneer
dryer
minimize
fugitive
emissions
from
the
dryer
doors
and
the
green
end
following
(
and
documenting
that
you
are
following)
your
plan
for
minimizing
fugitive
emissions.

(
4)
veneer
redryers
process
veneer
with
an
inlet
moisture
content
of
less
than
or
equal
to
25
percent
(
by
weight,
dry
basis)
maintaining
the
24­
hour
block
average
inlet
moisture
content
of
the
veneer
processed
at
or
below
25
percent
AND
keeping
records
of
the
inlet
moisture
content
of
the
veneer
processed.

(
5)
group
1
miscellaneous
coating
operations
use
non­
HAP
coatings
as
defined
in
§
63.2292
continuing
to
use
non­
HAP
coatings
AND
keeping
records
showing
that
you
are
using
non­
HAP
coatings.
83
Table
9
to
Subpart
DDDD
of
Part
63.
Requirements
for
Reports
You
must
submit
a(
n)...
The
report
must
contain...
You
must
submit
the
report...

(
1)
compliance
report
the
information
in
§
63.2281(
c)
through
(
g).
semiannually
according
to
the
requirements
in
§
63.2281(
b).

(
2)
immediate
startup,
shutdown,
and
malfunction
report
if
you
had
a
startup,
shutdown,
or
malfunction
during
the
reporting
period
that
is
not
consistent
with
your
SSMP
(
i)
actions
taken
for
the
event.
by
fax
or
telephone
within
2
working
days
after
starting
actions
inconsistent
with
the
plan.

(
ii)
the
information
in
§
63.10(
d)(
5)(
ii).
by
letter
within
7
working
days
after
the
end
of
the
event
unless
you
have
made
alternative
arrangements
with
the
permitting
authority.
84
Table
10
to
Subpart
DDDD
of
Part
63.
Applicability
of
General
Provisions
to
Subpart
DDDD
Citation
Subject
Brief
Description
Applies
to
Subpart
DDDD
§
63.1
Applicability
Initial
applicability
determination;
applicability
after
standard
established;
permit
requirements;
extensions,
notifications
Yes
§
63.2
Definitions
Definitions
for
part
63
standards
Yes
§
63.3
Units
and
Abbreviations
Units
and
abbreviations
for
part
63
standards
Yes
§
63.4
Prohibited
Activities
Prohibited
activities;
compliance
date;
circumvention,
fragmentation
Yes
§
63.5
Construction/
Reconstruction
Applicability;
applications;
approvals
Yes
§
63.6(
a)
Applicability
GP
apply
unless
compliance
extension;
GP
apply
to
area
sources
that
become
major
Yes
§
63.6(
b)(
1)­(
4)
Compliance
Dates
for
New
and
Reconstructed
Sources
Standards
apply
at
effective
date;
3
years
after
effective
date;
upon
startup;
10
years
after
construction
or
reconstruction
commences
for
section
112(
f)
Yes
§
63.6(
b)(
5)
Notification
Must
notify
if
commenced
construction
or
reconstruction
after
proposal
Yes
§
63.6(
b)(
6)
[
Reserved]

§
63.6(
b)(
7)
Compliance
Dates
for
New
and
Reconstructed
Area
Sources
that
Become
Major
Area
sources
that
become
major
must
comply
with
major
source
standards
immediately
upon
becoming
major,
regardless
of
whether
required
to
comply
when
they
were
an
area
source
Yes
§
63.6(
c)(
1)­(
2)
Compliance
Dates
for
Existing
Sources
Comply
according
to
date
in
subpart,
which
must
be
no
later
than
3
years
after
effective
date;
for
section
112(
f)
standards,
comply
within
90
days
of
effective
date
unless
compliance
extension
Yes
§
63.6(
c)(
3)­(
4)
[
Reserved]
85
§
63.6(
c)(
5)
Compliance
Dates
for
Existing
Area
Sources
that
Become
Major
Area
sources
that
become
major
must
comply
with
major
source
standards
by
date
indicated
in
subpart
or
by
equivalent
time
period
(
e.
g.,
3
years)
Yes
§
63.6(
d)
[
Reserved]

§
63.6(
e)(
1)­(
2)
Operation
&
Maintenance
Operate
to
minimize
emissions
at
all
times;
correct
malfunctions
as
soon
as
practicable;
operation
and
maintenance
requirements
independently
enforceable;
information
Administrator
will
use
to
determine
if
operation
and
maintenance
requirements
were
met
Yes
§
63.6(
e)(
3)
Startup,
Shutdown,
and
Malfunction
Plan
(
SSMP)
Requirement
for
SSM
and
SSMP;
content
of
SSMP
Yes
§
63.6(
f)(
1)
Compliance
Except
During
SSM
You
must
comply
with
emission
standards
at
all
times
except
during
SSM
Yes
§
63.6(
f)(
2)­(
3)
Methods
for
Determining
Compliance
Compliance
based
on
performance
test,
operation
and
maintenance
plans,
records,
inspection
Yes
§
63.6(
g)(
1)­(
3)
Alternative
Standard
Procedures
for
getting
an
alternative
standard
Yes
§
63.6(
h)(
1)­(
9)
Opacity/
Visible
Emission
(
VE)
Standards
Requirements
for
opacity
and
visible
emission
standards
NA
§
63.6(
i)(
1)­(
14)
Compliance
Extension
Procedures
and
criteria
for
Administrator
to
grant
compliance
extension
Yes
§
63.6(
i)(
15)
[
Reserved]

§
63.6(
i)(
16)
Compliance
Extension
Compliance
extension
and
Administrator's
authority
Yes
§
63.6(
j)
Presidential
Compliance
Exemption
President
may
exempt
source
category
from
requirement
to
comply
with
rule
Yes
§
63.7(
a)(
1)­(
2)
Performance
Test
Dates
Dates
for
conducting
initial
performance
testing
and
other
compliance
demonstrations;
must
conduct
180
days
after
first
subject
to
rule
Yes
86
§
63.7(
a)(
3)
Section
114
Authority
Administrator
may
require
a
performance
test
under
CAA
section
114
at
any
time
Yes
§
63.7(
b)(
1)
Notification
of
Performance
Test
Must
notify
Administrator
60
days
before
the
test
Yes
§
63.7(
b)(
2)
Notification
of
Rescheduling
If
have
to
reschedule
performance
test,
must
notify
Administrator
as
soon
as
practicable
Yes
§
63.7(
c)
Quality
Assurance/
Test
Plan
Requirement
to
submit
sitespecific
test
plan
60
days
before
the
test
or
on
date
Administrator
agrees
with;
test
plan
approval
procedures;
performance
audit
requirements;
internal
and
external
QA
procedures
for
testing
Yes
§
63.7(
d)
Testing
Facilities
Requirements
for
testing
facilities
Yes
§
63.7(
e)(
1)
Conditions
for
Conducting
Performance
Tests
Performance
tests
must
be
conducted
under
representative
conditions;
cannot
conduct
performance
tests
during
SSM;
not
a
violation
to
exceed
standard
during
SSM
Yes
§
63.7(
e)(
2)
Conditions
for
Conducting
Performance
Tests
Must
conduct
according
to
rule
and
EPA
test
methods
unless
Administrator
approves
alternative
Yes
§
63.7(
e)(
3)
Test
Run
Duration
Must
have
three
test
runs
for
at
least
the
time
specified
in
the
relevant
standard;
compliance
is
based
on
arithmetic
mean
of
three
runs;
specifies
conditions
when
data
from
an
additional
test
run
can
be
used
Yes
§
63.7(
f)
Alternative
Test
Method
Procedures
by
which
Administrator
can
grant
approval
to
use
an
alternative
test
method
Yes
§
63.7(
g)
Performance
Test
Data
Analysis
Must
include
raw
data
in
performance
test
report;
must
submit
performance
test
data
60
days
after
end
of
test
with
the
notification
of
compliance
status;
keep
data
for
5
years
Yes
§
63.7(
h)
Waiver
of
Tests
Procedures
for
Administrator
to
waive
performance
test
Yes
87
§
63.8(
a)(
1)
Applicability
of
Monitoring
Requirements
Subject
to
all
monitoring
requirements
in
standard
Yes
§
63.8(
a)(
2)
Performance
Specifications
Performance
Specifications
in
Appendix
B
of
Part
60
apply
Yes
§
63.8(
a)(
3)
[
Reserved]

§
63.8(
a)(
4)
Monitoring
with
Flares
Requirements
for
flares
in
§
63.11
apply.
NA
§
63.8(
b)(
1)
Monitoring
Must
conduct
monitoring
according
to
standard
unless
Administrator
approves
alternative
Yes
§
63.8(
b)(
2)­(
3)
Multiple
Effluents
and
Multiple
Monitoring
Systems
Specific
requirements
for
installing
monitoring
systems;
must
install
on
each
effluent
before
it
is
combined
and
before
it
is
released
to
the
atmosphere
unless
Administrator
approves
otherwise;
if
more
than
one
monitoring
system
on
an
emission
point,
must
report
all
monitoring
system
results,
unless
one
monitoring
system
is
a
backup
Yes
§
63.8(
c)(
1)
Monitoring
System
Operation
and
Maintenance
Maintain
monitoring
system
in
a
manner
consistent
with
good
air
pollution
control
practices
Yes
§
63.8(
c)(
1)(
i)
Operation
and
Maintenance
of
CMS
Must
maintain
and
operate
CMS
in
accordance
with
§
63.6(
e)(
1)
Yes
§
63.8(
c)(
1)(
ii)
Spare
Parts
for
CMS
Must
maintain
spare
parts
for
routine
CMS
repairs
Yes
§
63.8(
c)(
1)(
iii)
SSMP
for
CMS
Must
develop
and
implement
SSMP
for
CMS
Yes
§
63.8(
c)(
2)­(
3)
Monitoring
System
Installation
Must
install
to
get
representative
emission
of
parameter
measurements;
must
verify
operational
status
before
or
at
performance
test
Yes
88
§
63.8(
c)(
4)
Continuous
Monitoring
System
(
CMS)
Requirements
CMS
must
be
operating
except
during
breakdown,
out­
of
control,
repair,
maintenance,
and
high­
level
calibration
drifts;
COMS
must
have
a
minimum
of
one
cycle
of
sampling
and
analysis
for
each
successive
10­
second
period
and
one
cycle
of
data
recording
for
each
successive
6­
minute
period;
CEMS
must
have
a
minimum
of
one
cycle
of
operation
for
each
successive
15­
minute
period
Yes
§
63.8(
c)(
5)
COMS
Minimum
Procedures
COMS
minimum
procedures
NA
§
63.8(
c)(
6)­(
8)
CMS
Requirements
Zero
and
high­
level
calibration
check
requirements;
out­
ofcontrol
periods
Yes
§
63.8(
d)
CMS
Quality
Control
Requirements
for
CMS
quality
control,
including
calibration,
etc.;
must
keep
quality
control
plan
on
record
for
5
years.
Keep
old
versions
for
5
years
after
revisions
Yes
§
63.8(
e)
CMS
Performance
Evaluation
Notification,
performance
evaluation
test
plan,
reports
Yes
§
63.8(
f)(
1)­(
5)
Alternative
Monitoring
Method
Procedures
for
Administrator
to
approve
alternative
monitoring
Yes
§
63.8(
f)(
6)
Alternative
to
Relative
Accuracy
Test
Procedures
for
Administrator
to
approve
alternative
relative
accuracy
tests
for
CEMS
Yes
§
63.8(
g)
Data
Reduction
COMS
6­
minute
averages
calculated
over
at
least
36
evenly
spaced
data
points;
CEMS
1
hour
averages
computed
over
at
least
4
equally
spaced
data
points;
data
that
can't
be
used
in
average;
rounding
of
data
Yes
§
63.9(
a)
Notification
Requirements
Applicability
and
State
delegation
Yes
§
63.9(
b)(
1)­(
2)
Initial
Notifications
Submit
notification
120
days
after
effective
date;
contents
of
notification
Yes
§
63.9(
b)(
3)
[
Reserved]
89
§
63.9(
b)(
4)­(
5)
Initial
Notifications
Submit
notification
120
days
after
effective
date;
notification
of
intent
to
construct/
reconstruct;
notification
of
commencement
of
construct/
reconstruct;
notification
of
startup;
contents
of
each
Yes
§
63.9(
c)
Request
for
Compliance
Extension
Can
request
if
cannot
comply
by
date
or
if
installed
BACT/
LAER
Yes
§
63.9(
d)
Notification
of
Special
Compliance
Requirements
for
New
Source
For
sources
that
commence
construction
between
proposal
and
promulgation
and
want
to
comply
3
years
after
effective
date
Yes
§
63.9(
e)
Notification
of
Performance
Test
Notify
Administrator
60
days
prior
Yes
§
63.9(
f)
Notification
of
VE/
Opacity
Test
Notify
Administrator
30
days
prior
No
§
63.9(
g)
Additional
Notifications
When
Using
CMS
Notification
of
performance
evaluation;
notification
using
COMS
data;
notification
that
exceeded
criterion
for
relative
accuracy
Yes
§
63.9(
h)(
1)­(
6)
Notification
of
Compliance
Status
Contents;
due
60
days
after
end
of
performance
test
or
other
compliance
demonstration,
except
for
opacity/
VE,
which
are
due
30
days
after;
when
to
submit
to
Federal
vs.
State
authority
Yes
§
63.9(
i)
Adjustment
of
Submittal
Deadlines
Procedures
for
Administrator
to
approve
change
in
when
notifications
must
be
submitted
Yes
§
63.9(
j)
Change
in
Previous
Information
Must
submit
within
15
days
after
the
change
Yes
§
63.10(
a)
Recordkeeping/
Reporting
Applies
to
all,
unless
compliance
extension;
when
to
submit
to
Federal
vs.
State
authority;
procedures
for
owners
of
more
than
1
source
Yes
§
63.10(
b)(
1)
Recordkeeping/
Reporting
General
Requirements;
keep
all
records
readily
available;
keep
for
5
years
Yes
90
§
63.10(
b)(
2)(
i)­
(
iv)
Records
Related
to
Startup,
Shutdown,
and
Malfunction
Occurrence
of
each
of
operation
(
process
equipment);
occurrence
of
each
malfunction
of
air
pollution
equipment;
maintenance
on
air
pollution
control
equipment;
actions
during
startup,
shutdown,
and
malfunction
Yes
§
63.10(
b)(
2)(
vi)
and
(
x)­(
xi)
CMS
Records
Malfunctions,
inoperative,
out­
of­
control
Yes
§
63.10(
b)(
2)(
vii)­
(
ix)
Records
Measurements
to
demonstrate
compliance
with
compliance
options
and
operating
requirements;
performance
test,
performance
evaluation,
and
visible
emission
observation
results;
measurements
to
determine
conditions
of
performance
tests
and
performance
evaluations
Yes
§
63.10(
b)(
2)(
xii)
Records
Records
when
under
waiver
Yes
§
63.10(
b)(
2)(
xiii)
Records
Records
when
using
alternative
to
relative
accuracy
test
Yes
§
63.10(
b)(
2)(
xiv)
Records
All
documentation
supporting
initial
notification
and
notification
of
compliance
status
Yes
§
63.10(
b)(
3)
Records
Applicability
determinations
Yes
§
63.10(
c)(
1)­
(
6),(
9)­(
15)
Records
Additional
records
for
CMS
Yes
§
63.10(
c)(
7)­(
8)
Records
Records
of
excess
emissions
and
parameter
monitoring
exceedances
for
CMS
No
§
63.10(
d)(
1)
General
Reporting
Requirements
Requirement
to
report
Yes
§
63.10(
d)(
2)
Report
of
Performance
Test
Results
When
to
submit
to
Federal
or
State
authority
Yes
§
63.10(
d)(
3)
Reporting
Opacity
or
VE
Observations
What
to
report
and
when
NA
§
63.10(
d)(
4)
Progress
Reports
Must
submit
progress
reports
on
schedule
if
under
compliance
extension
Yes
91
§
63.10(
d)(
5)
Startup,
Shutdown,
and
Malfunction
Reports
Contents
and
submission
Yes
§
63.10(
e)(
1)­(
2)
Additional
CMS
Reports
Must
report
results
for
each
CEM
on
a
unit;
written
copy
of
performance
evaluation;
3
copies
of
COMS
performance
evaluation
Yes
§
63.10(
e)(
3)
Reports
Excess
Emission
Reports
No
§
63.10(
e)(
4)
Reporting
COMS
data
Must
submit
COMS
data
with
performance
test
data
NA
§
63.10(
f)
Waiver
for
Recordkeeping/
R
eporting
Procedures
for
Administrator
to
waive
Yes
§
63.11
Flares
Requirements
for
flares
NA
§
63.12
Delegation
State
authority
to
enforce
standards
Yes
§
63.13
Addresses
Addresses
where
reports,
notifications,
and
requests
are
send
Yes
§
63.14
Incorporation
by
Reference
Test
methods
incorporated
by
reference
Yes
§
63.15
Availability
of
Information
Public
and
confidential
information
Yes
Appendix
A
to
Subpart
DDDD
of
Part
63
 
Alternative
Procedure
to
Determine
Capture
Efficiency
from
Enclosures
Around
Hot
Presses
in
the
Plywood
and
Composite
Wood
Products
Industry
Using
Sulfur
Hexafluoride
Tracer
Gas
1.0
Scope
and
Application.

This
procedure
has
been
developed
specifically
for
the
rule
for
the
plywood
and
composite
wood
products
(
PCWP)
industry
and
is
used
to
determine
the
capture
efficiency
of
a
partial
hot
press
enclosure
in
that
industry.
This
procedure
is
applicable
for
the
determination
of
capture
efficiency
for
enclosures
around
hot
presses
and
is
an
alternative
to
the
construction
of
temporary
total
enclosures
(
TTEs).
Sulfur
hexafluoride
(
SF6)
is
used
as
a
tracer
gas
(
other
tracer
gases
may
be
used
if
approved
by
the
Administrator).
This
gas
is
not
indigenous
to
the
ambient
atmosphere
and
is
nonreactive.

This
procedure
uses
infrared
spectrometry
(
IR)
as
the
analytical
technique.
When
the
infrared
spectrometer
used
is
a
Fourier­
Transform
Infrared
spectrometer
(
FTIR),
an
92
alternate
instrument
calibration
procedure
may
be
used;
the
alternate
calibration
procedure
is
the
calibration
transfer
standard
(
CTS)
procedure
of
EPA
Method
320.
Other
analytical
techniques
which
are
capable
of
equivalent
Method
Performance
(
Section
13.0)
also
may
be
used.
Specifically,
gas
chromatography
with
electron
capture
detection
(
GC/
ECD)
is
an
applicable
technique
for
analysis
of
SF6.

2.0
Summary
of
Method.

A
constant
mass
flow
rate
of
SF6
tracer
gas
is
released
through
manifolds
at
multiple
locations
within
the
enclosure
to
mimic
the
release
of
HAP
during
the
press
process.
This
test
method
requires
a
minimum
of
three
SF6
injection
points
(
two
at
the
press
unloader
and
one
at
the
press)
and
provides
details
about
considerations
for
locating
the
injection
points.
An
infrared
spectrometer
(
or
GC/
ECD)
is
used
to
measure
the
concentration
of
SF6
at
the
inlet
duct
to
the
control
device
(
outlet
duct
from
enclosure).
Simultaneously,
EPA
Method
2
is
used
to
measure
the
flow
rate
at
the
inlet
duct
to
the
control
device.
The
concentration
and
flow
rate
measurements
are
used
to
calculate
the
mass
emission
rate
of
SF6
at
the
control
device
inlet.
Through
calculation
of
the
mass
of
SF6
released
through
the
manifolds
and
the
mass
of
SF6
measured
at
the
inlet
to
the
control
device,
the
capture
efficiency
of
the
enclosure
is
calculated.

In
addition,
optional
samples
of
the
ambient
air
may
be
taken
at
locations
around
the
perimeter
of
the
enclosure
to
quantify
the
ambient
concentration
of
SF6
and
to
identify
those
areas
of
the
enclosure
that
may
be
performing
less
efficiently;
these
samples
would
be
taken
using
disposable
syringes
and
would
be
analyzed
using
a
GC/
ECD.

Finally,
in
addition
to
the
requirements
specified
in
this
procedure,
the
data
quality
objectives
(
DQO)
or
lower
confidence
limit
(
LCL)
criteria
specified
in
Appendix
A
to
40
CFR
part
63,
subpart
KK,
Data
Quality
Objective
and
Lower
Confidence
Limit
Approaches
for
Alternative
Capture
Efficiency
Protocols
and
Test
Methods,
must
also
be
satisfied.
A
minimum
of
three
test
runs
are
required
for
this
procedure;
however,
additional
test
runs
may
be
required
based
on
the
results
of
the
DQO
or
LCL
analysis.

3.0
Definitions.

3.1
Capture
efficiency
(
CE).
The
weight
per
unit
time
of
SF6
entering
the
control
device
divided
by
the
weight
per
unit
time
of
SF6
released
through
manifolds
at
multiple
93
locations
within
the
enclosure.

3.2
Control
device
(
CD).
The
equipment
used
to
reduce,
by
destruction
or
removal,
press
exhaust
air
pollutants
prior
to
discharge
to
the
ambient
air.

3.3
Control/
destruction
efficiency
(
DE).
The
volatile
organic
compound
or
HAP
removal
efficiency
of
the
control
device.

3.4
Data
Quality
Objective
(
DQO)
Approach.
A
statistical
procedure
to
determine
the
precision
of
the
data
from
a
test
series
and
to
qualify
the
data
in
the
determination
of
capture
efficiency
for
compliance
purposes.
If
the
results
of
the
DQO
analysis
of
the
initial
three
test
runs
do
not
satisfy
the
DQO
criterion,
the
LCL
approach
can
be
used
or
additional
test
runs
must
be
conducted.
If
additional
test
runs
are
conducted,
then
the
DQO
or
LCL
analysis
is
conducted
using
the
data
from
both
the
initial
test
runs
and
all
additional
test
runs.

3.5
Lower
Confidence
Limit
(
LCL)
Approach.
An
alternative
statistical
procedure
that
can
be
used
to
qualify
data
in
the
determination
of
capture
efficiency
for
compliance
purposes.
If
the
results
of
the
LCL
approach
produce
a
CE
that
is
too
low
for
demonstrating
compliance,
then
additional
test
runs
must
be
conducted
until
the
LCL
or
DQO
is
met.
As
with
the
DQO,
data
from
all
valid
test
runs
must
be
used
in
the
calculation.

3.6
Minimum
Measurement
Level
(
MML).
The
minimum
tracer
gas
concentration
expected
to
be
measured
during
the
test
series.
This
value
is
selected
by
the
tester
based
on
the
capabilities
of
the
IR
spectrometer
(
or
GC/
ECD)
and
the
other
known
or
measured
parameters
of
the
hot
press
enclosure
to
be
tested.
The
selected
MML
must
be
above
the
low­
level
calibration
standard
and
preferably
below
the
mid­
level
calibration
standard.

3.7
Method
204.
The
U.
S.
EPA
Method
204,
"
Criteria
For
and
Verification
of
a
Permanent
or
Temporary
Total
Enclosure"
(
40
CFR
part
51,
Appendix
M).

3.8
Method
205.
The
U.
S.
EPA
Method
205,
"
Verification
of
Gas
Dilution
Systems
for
Field
Instrument
Calibrations"
(
40
CFR
part
51,
Appendix
M).

3.9
Method
320.
The
U.
S.
EPA
Method
320,
"
Measurement
of
Vapor
Phase
Organic
and
Inorganic
Emissions
by
Extractive
Fourier
Transform
Infrared
(
FTIR)
Spectroscopy"
(
40
CFR
part
94
63,
Appendix
A).

3.10
Overall
capture
and
control
efficiency
(
CCE).
The
collection
and
control/
destruction
efficiency
of
both
the
PPE
and
CD
combined.
The
CCE
is
calculated
as
the
product
of
the
CE
and
DE.

3.11
Partial
press
enclosure
(
PPE).
The
physical
barrier
that
"
partially"
encloses
the
press
equipment,
captures
a
significant
amount
of
the
associated
emissions,
and
transports
those
emissions
to
the
CD.

3.12
Test
series.
A
minimum
of
three
test
runs
or,
when
more
than
three
runs
are
conducted,
all
of
the
test
runs
conducted.

4.0
Interferences.

There
are
no
known
interferences.

5.0
Safety.

Sulfur
hexafluoride
is
a
colorless,
odorless,
nonflammable
liquefied
gas.
It
is
stable
and
nonreactive
and,
because
it
is
noncorrosive,
most
structural
materials
are
compatible
with
it.
The
Occupational
Safety
and
Health
Administration
PEL­
TWA
and
TLV­
TWA
concentrations
are
1,000
parts
per
million.
Sulfur
hexafluoride
is
an
asphyxiant.
Exposure
to
an
oxygen­
deficient
atmosphere
(
less
than
19.5
percent
oxygen)
may
cause
dizziness,
drowsiness,
nausea,
vomiting,
excess
salivation,
diminished
mental
alertness,
loss
of
consciousness,
and
death.
Exposure
to
atmospheres
containing
less
than
12
percent
oxygen
will
bring
about
unconsciousness
without
warning
and
so
quickly
that
the
individuals
cannot
help
themselves.
Contact
with
liquid
or
cold
vapor
may
cause
frostbite.
Avoid
breathing
sulfur
hexafluoride
gas.
Self­
contained
breathing
apparatus
may
be
required
by
rescue
workers.
Sulfur
hexafluoride
is
not
listed
as
a
carcinogen
or
a
potential
carcinogen.

6.0
Equipment
and
Supplies.

This
method
requires
equipment
and
supplies
for:
(
a)
the
injection
of
tracer
gas
into
the
enclosure,
(
b)
the
measurement
of
the
tracer
gas
concentration
in
the
exhaust
gas
entering
the
control
device,
and
(
c)
the
measurement
of
the
volumetric
flow
rate
of
the
exhaust
gas
entering
the
control
device.
In
addition,
the
requisite
equipment
needed
for
EPA
Methods
1
­
4
will
be
required.
Equipment
and
supplies
for
optional
ambient
air
sampling
are
discussed
in
95
Section
8.6.

6.1
Tracer
Gas
Injection.

6.1.1
Manifolds.
This
method
requires
the
use
of
tracer
gas
supply
cylinder(
s)
along
with
the
appropriate
flow
control
elements.
Figure
1
shows
a
schematic
drawing
of
the
injection
system
showing
potential
locations
for
the
tracer
gas
manifolds.
Figure
2
shows
a
schematic
drawing
of
the
recommended
configuration
of
the
injection
manifold.
Three
tracer
gas
discharge
manifolds
are
required
at
a
minimum.

6.1.2
Flow
Control
Meter.
Flow
control
and
measurement
meter
for
measuring
the
quantity
of
tracer
gas
injected.
A
mass
flow,
volumetric
flow,
or
critical
orifice
control
meter
can
be
used
for
this
method.
The
meter
must
be
accurate
to
within
±
5
percent
at
the
flow
rate
used.
This
means
that
the
flow
meter
must
be
calibrated
against
a
primary
standard
for
flow
measurement
at
the
appropriate
flow
rate.

6.2
Measurement
of
Tracer
Gas
Concentration.

6.2.1
Sampling
Probes.
Use
Pyrex
or
stainless
steel
sampling
probes
of
sufficient
length
to
reach
the
traverse
points
calculated
according
to
EPA
Method
1.

6.2.2
Sampling
Line.
Use
a
heated
Teflon
sampling
line
to
transport
the
sample
to
the
analytical
instrument.

6.2.3
Sampling
Pump.
Use
a
sampling
pump
capable
of
extracting
sufficient
sample
from
the
duct
and
transporting
to
the
analytical
instrument.

6.2.4
Sample
Conditioning
System.
Use
a
particulate
filter
sufficient
to
protect
the
sampling
pump
and
analytical
instrument.
At
the
discretion
of
the
tester
and
depending
on
the
equipment
used
and
the
moisture
content
of
the
exhaust
gas,
it
may
be
necessary
to
further
condition
the
sample
by
removing
moisture
using
a
condenser.

6.2.5
Analytical
Instrument.
Use
one
of
the
following
analytical
instruments.

6.2.1.1
Spectrometer.
Use
an
infrared
spectrometer
designed
to
measuring
SF6
tracer
gas
and
capable
of
meeting
or
exceeding
the
specifications
of
this
procedure.
An
FTIR
meeting
the
specifications
of
Method
320
may
be
used.

6.2.1.2
GC/
ECD.
Use
a
GC/
ECD
designed
to
measure
SF6
tracer
gas
and
capable
of
meeting
or
exceeding
the
specifications
of
this
procedure.

6.2.6
Recorder.
At
a
minimum,
use
a
recorder
with
96
linear
strip
chart.
An
automated
data
acquisition
system
(
DAS)
is
recommended.

6.3
Exhaust
Gas
Flow
Rate
Measurement.
Use
equipment
specified
for
EPA
Methods
2,
3,
and
4
for
measuring
flow
rate
of
exhaust
gas
at
the
inlet
to
the
control
device.

7.0
Reagents
and
Standards.

7.1
Tracer
Gas.
Use
SF6
as
the
tracer
gas.
The
manufacturer
of
the
SF6
tracer
gas
should
provide
a
recommended
shelf
life
for
the
tracer
gas
cylinder
over
which
the
concentration
does
not
change
more
than
±
2
percent
from
the
certified
value.
A
gas
mixture
of
SF6
diluted
with
nitrogen
should
be
used;
based
on
experience
and
calculations,
pure
SF6
gas
is
not
necessary
to
conduct
tracer
gas
testing.
Select
a
concentration
and
flow
rate
that
is
appropriate
for
the
analytical
instrument's
detection
limit,
the
minimum
measurement
level
(
MML),
and
the
exhaust
gas
flow
rate
from
the
enclosure
(
see
section
8.1.1).
You
may
use
a
tracer
gas
other
than
SF6
with
the
prior
approval
of
the
Administrator.
If
you
use
an
approved
tracer
gas
other
than
SF6,
all
references
to
SF6
in
this
protocol
instead
refer
to
the
approved
tracer
gas.

7.2
Calibration
Gases.
The
SF6
calibration
gases
required
will
be
dependent
on
the
selected
MML
and
the
appropriate
span
selected
for
the
test.
Commercial
cylinder
gases
certified
by
the
manufacturer
to
be
accurate
to
within
1
percent
of
the
certified
label
value
are
preferable,
although
cylinder
gases
certified
by
the
manufacturer
to
2
percent
accuracy
are
allowed.
Additionally,
the
manufacturer
of
the
SF6
calibration
gases
should
provide
a
recommended
shelf
life
for
each
calibration
gas
cylinder
over
which
the
concentration
does
not
change
more
than
±
2
percent
from
the
certified
value.
Another
option
allowed
by
this
method
is
for
the
tester
to
obtain
high
concentration
certified
cylinder
gases
and
then
use
a
dilution
system
meeting
the
requirements
of
EPA
Method
205,
40
CFR
part
51,
Appendix
M,
to
make
multi­
level
calibration
gas
standards.
Low­
level,
mid­
level,
and
high­
level
calibration
gases
will
be
required.
The
MML
must
be
above
the
low­
level
standard,
the
high­
level
standard
must
be
no
more
than
four
times
the
low­
level
standard,
and
the
mid­
level
standard
must
be
approximately
halfway
between
the
high­
and
low­
level
standards.
See
section
12.1
for
an
example
calculation
of
this
procedure.
Note:
If
using
an
FTIR
as
the
analytical
instrument,
the
tester
has
the
option
of
following
the
CTS
procedures
of
Method
320;
the
calibration
standards
(
and
procedures)
specified
in
Method
320
may
be
used
in
lieu
of
the
97
calibration
standards
and
procedures
in
this
protocol.

7.2.1
Zero
Gas.
High
purity
nitrogen.

7.2.2
Low­
Level
Calibration
Gas.
An
SF6
calibration
gas
in
nitrogen
with
a
concentration
equivalent
to
20
to
30
percent
of
the
applicable
span
value.

7.2.3
Mid­
Level
Calibration
Gas.
An
SF6
calibration
gas
in
nitrogen
with
a
concentration
equivalent
to
45
to
55
percent
of
the
applicable
span
value.

7.2.4
High­
Level
Calibration
Gas.
An
SF6
calibration
gas
in
nitrogen
with
a
concentration
equivalent
to
80
to
90
percent
of
the
applicable
span
value.

8.0
Sample
Collection,
Preservation,
Storage,
and
Transport.

8.1
Test
Design.

8.1.1
Determination
of
Minimum
Tracer
Gas
Flow
Rate.

8.1.1.1
Determine
(
via
design
calculations
or
measurements)
the
approximate
flow
rate
of
the
exhaust
gas
through
the
enclosure
(
acfm).

8.1.1.2
Calculate
the
minimum
tracer
gas
injection
rate
necessary
to
assure
a
detectable
SF6
concentration
at
the
exhaust
gas
measurement
point
(
see
section
12.1
for
calculation).

8.1.1.3
Select
a
flow
meter
for
the
injection
system
with
an
operating
range
appropriate
for
the
injection
rate
selected.

8.1.2
Determination
of
the
Approximate
Time
to
Reach
Equilibrium.

8.1.2.1
Determine
the
volume
of
the
enclosure.

8.1.2.2
Calculate
the
air
changes
per
minute
of
the
enclosure
by
dividing
the
approximate
exhaust
flow
rate
(
8.1.1.1
above)
by
the
enclosed
volume
(
8.1.2.1
above).

8.1.2.3
Calculate
the
time
at
which
the
tracer
concentration
in
the
enclosure
will
achieve
approximate
equilibrium.
Divide
3
by
the
air
changes
per
minute
(
8.1.2.2
above)
to
establish
this
time.
This
is
the
approximate
length
of
time
for
the
system
to
come
to
equilibrium.
Concentration
equilibrium
occurs
when
the
tracer
concentration
in
the
enclosure
stops
changing
as
a
function
of
time
for
a
constant
tracer
release
rate.
Because
the
press
is
continuously
cycling,
equilibrium
may
be
exhibited
by
a
repeating,
but
stable,
cyclic
pattern
rather
than
a
single
constant
concentration
value.
Assure
98
sufficient
tracer
gas
is
available
to
allow
the
system
to
come
to
equilibrium,
and
to
sample
for
a
minimum
of
20
minutes
and
repeat
the
procedure
for
a
minimum
of
three
test
runs.
Additional
test
runs
may
be
required
based
on
the
results
of
the
DQO
and
LCL
analyses
described
in
40
CFR
part
63,
subpart
KK,
Appendix
A.

8.1.3
Location
of
Injection
Points.
This
method
requires
a
minimum
of
three
tracer
gas
injection
points.
The
injection
points
should
be
located
within
leak
prone,
VOC/
HAP­
producing
areas
around
the
press,
or
horizontally
within
12
inches
of
the
defined
equipment.
One
potential
configuration
of
the
injection
points
is
depicted
in
Figure
1.
The
effect
of
wind,
exfiltration
through
the
building
envelope,
and
air
flowing
through
open
building
doors
should
be
considered
when
locating
tracer
gas
injection
points
within
the
enclosure.
The
injection
points
should
also
be
located
at
a
vertical
elevation
equal
to
the
VOC/
HAP
generating
zones.
The
injection
points
should
not
be
located
beneath
obstructions
that
would
prevent
a
natural
dispersion
of
the
gas.
Document
the
selected
injection
points
in
a
drawing(
s).

8.1.4
Location
of
Flow
Measurement
and
Tracer
Sampling.
Accurate
CD
inlet
gas
flow
rate
measurements
are
critical
to
the
success
of
this
procedure.
Select
a
measurement
location
meeting
the
criteria
of
EPA
Method
1
(
40
CFR
part
60,
Appendix
A),
Sampling
and
Velocity
Traverses
for
Stationary
Sources.
Also,
when
selecting
the
measurement
location,
consider
whether
stratification
of
the
tracer
gas
is
likely
at
the
location
(
e.
g.,
do
not
select
a
location
immediately
after
a
point
of
air
in­
leakage
to
the
duct).

8.2
Tracer
Gas
Release.
Release
the
tracer
gas
at
a
calculated
flow
rate
(
see
section
12.1
for
calculation)
through
a
minimum
of
three
injection
manifolds
located
as
described
above
in
8.1.3.
The
tracer
gas
delivery
lines
must
be
routed
into
the
enclosure
and
attached
to
the
manifolds
without
violating
the
integrity
of
the
enclosure.

8.3
Pretest
Measurements.

8.3.1
Location
of
Sampling
Point(
s).
If
stratification
is
not
suspected
at
the
measurement
location,
select
a
single
sample
point
located
at
the
centroid
of
the
CD
inlet
duct
or
at
a
point
no
closer
to
the
CD
inlet
duct
walls
than
1
meter.
If
stratification
is
suspected,
establish
a
"
measurement
line"
that
passes
through
the
centroidal
area
and
in
the
direction
of
any
expected
stratification.
Locate
three
traverse
points
at
16.7,
50.0
and
83.3
percent
of
the
measurement
line
and
sample
from
99
each
of
these
three
points
during
each
run,
or
follow
the
procedure
in
section
8.3.2
to
verify
whether
stratification
does
or
does
not
exist.

8.3.2
Stratification
Verification.
The
presence
or
absence
of
stratification
can
be
verified
by
using
the
following
procedure.
While
the
facility
is
operating
normally,
initiate
tracer
gas
release
into
the
enclosure.
For
rectangular
ducts,
locate
at
least
nine
sample
points
in
the
cross
section
such
that
the
sample
points
are
the
centroids
of
similarly­
shaped,
equal
area
divisions
of
the
cross
section.
Measure
the
tracer
gas
concentration
at
each
point.
Calculate
the
mean
value
for
all
sample
points.
For
circular
ducts,
conduct
a
12­
point
traverse
(
i.
e.,
six
points
on
each
of
the
two
perpendicular
diameters)
locating
the
sample
points
as
described
in
40
CFR
part
60,
Appendix
A,
Method
1.
Perform
the
measurements
and
calculations
as
described
above.
Determine
if
the
mean
pollutant
concentration
is
more
than
10
percent
different
from
any
single
point.
If
so,
the
cross
section
is
considered
to
be
stratified,
and
the
tester
may
not
use
a
single
sample
point
location,
but
must
use
the
three
traverse
points
at
16.7,
50.0,
and
83.3
percent
of
the
entire
measurement
line.
Other
traverse
points
may
be
selected,
provided
that
they
can
be
shown
to
the
satisfaction
of
the
Administrator
to
provide
a
representative
sample
over
the
stack
or
duct
cross
section.

8.4
CD
Inlet
Gas
Flow
Rate
Measurements.
The
procedures
of
EPA
Methods
1­
4
(
40
CFR
part
60,
Appendix
A)
are
used
to
determine
the
CD
inlet
gas
flow
rate.
Molecular
weight
(
Method
3)
and
moisture
(
Method
4)
determinations
are
only
required
once
for
each
test
series.
However,
if
the
test
series
is
not
completed
within
24
hours,
then
the
molecular
weight
and
moisture
measurements
should
be
repeated
daily.
As
a
minimum,
velocity
measurements
are
conducted
according
to
the
procedures
of
Methods
1
and
2
before
and
after
each
test
run,
as
close
to
the
start
and
end
of
the
run
as
practicable.
A
velocity
measurement
between
two
runs
satisfies
both
the
criterion
of
"
after"
the
run
just
completed
and
"
before"
the
run
to
be
initiated.
Accurate
exhaust
gas
flow
rate
measurements
are
critical
to
the
success
of
this
procedure.
If
significant
temporal
variations
of
flow
rate
are
anticipated
during
the
test
run
under
normal
process
operating
conditions,
take
appropriate
steps
to
accurately
measure
the
flow
rate
during
the
test.
Examples
of
steps
that
might
be
taken
include:
1)
conducting
additional
velocity
traverses
during
the
test
run;
or
2)
continuously
monitoring
a
single
point
of
average
velocity
during
the
run
and
using
these
data,
in
conjunction
with
the
pre­
and
post­
test
traverses,
to
calculate
an
average
100
velocity
for
the
test
run.

8.5
Tracer
Gas
Measurement
Procedure.

8.5.1
Calibration
Error
Test.
Immediately
prior
to
the
emission
test
(
within
2
hours
of
the
start
of
the
test),
introduce
zero
gas
and
high­
level
calibration
gas
at
the
calibration
valve
assembly.
Zero
and
calibrate
the
analyzer
according
to
the
manufacturer's
procedures
using,
respectively,
nitrogen
and
the
calibration
gases.
Calculate
the
predicted
response
for
the
low­
level
and
mid­
level
gases
based
on
a
linear
response
line
between
the
zero
and
highlevel
response.
Then
introduce
the
low­
level
and
mid­
level
calibration
gases
successively
to
the
measurement
system.
Record
the
analyzer
responses
for
the
low­
level
and
midlevel
calibration
gases
and
determine
the
differences
between
the
measurement
system
responses
and
the
predicted
responses
using
the
equation
in
section
12.3.
These
differences
must
be
less
than
5
percent
of
the
respective
calibration
gas
value.
If
not,
the
measurement
system
must
be
replaced
or
repaired
prior
to
testing.
No
adjustments
to
the
measurement
system
shall
be
conducted
after
the
calibration
and
before
the
drift
determination
(
section
8.5.4).
If
adjustments
are
necessary
before
the
completion
of
the
test
series,
perform
the
drift
checks
prior
to
the
required
adjustments
and
repeat
the
calibration
following
the
adjustments.
If
multiple
electronic
ranges
are
to
be
used,
each
additional
range
must
be
checked
with
a
mid­
level
calibration
gas
to
verify
the
multiplication
factor.
Note:
If
using
an
FTIR
for
the
analytical
instrument,
you
may
choose
to
follow
the
pretest
preparation,
evaluation,
and
calibration
procedures
of
Method
320
(
section
8.0)
(
40
CFR
part
63,
Appendix
A)
in
lieu
of
the
above
procedure.

8.5.2
Response
Time
Test.
Conduct
this
test
once
prior
to
each
test
series.
Introduce
zero
gas
into
the
measurement
system
at
the
calibration
valve
assembly.
When
the
system
output
has
stabilized,
switch
quickly
to
the
high­
level
calibration
gas.
Record
the
time
from
the
concentration
change
to
the
measurement
system
response
equivalent
to
95
percent
of
the
step
change.
Repeat
the
test
three
times
and
average
the
results.

8.5.3
SF6
Measurement.
Sampling
of
the
enclosure
exhaust
gas
at
the
inlet
to
the
CD
should
begin
at
the
onset
of
tracer
gas
release.
If
necessary,
adjust
the
tracer
gas
injection
rate
such
that
the
measured
tracer
gas
concentration
at
the
CD
inlet
is
within
the
spectrometer's
calibration
range
(
i.
e.,
between
the
MML
and
the
span
value).
Once
the
tracer
gas
concentration
reaches
101
equilibrium,
the
SF6
concentration
should
be
measured
using
the
infrared
spectrometer
continuously
for
at
least
20
minutes
per
run.
Continuously
record
(
i.
e.,
record
at
least
once
per
minute)
the
concentration.
Conduct
at
least
three
test
runs.
On
the
recording
chart,
in
the
data
acquisition
system,
or
in
a
log
book,
make
a
note
of
periods
of
process
interruption
or
cyclic
operation
such
as
the
cycles
of
the
hot
press
operation.
Table
1
summarizes
the
physical
measurements
required
for
the
enclosure
testing.

Note:
If
a
GC/
ECD
is
used
as
the
analytical
instrument,
a
continuous
record
(
at
least
once
per
minute)
likely
will
not
be
possible;
make
a
minimum
of
five
injections
during
each
test
run.
Also,
the
minimum
test
run
duration
criterion
of
20
minutes
applies.

8.5.4
Drift
Determination.
Immediately
following
the
completion
of
the
test
run,
reintroduce
the
zero
and
mid­
level
calibration
gases,
one
at
a
time,
to
the
measurement
system
at
the
calibration
valve
assembly.
(
Make
no
adjustments
to
the
measurement
system
until
both
the
zero
and
calibration
drift
checks
are
made.)
Record
the
analyzer
responses
for
the
zero
and
mid­
level
calibration
gases
and
determine
the
difference
between
the
instrument
responses
for
each
gas
prior
to
and
after
the
emission
test
run
using
the
equation
in
section
12.4.
If
the
drift
values
exceed
the
specified
limits
(
section
13),
invalidate
the
test
results
preceding
the
check
and
repeat
the
test
following
corrections
to
the
measurement
system.
Alternatively,
recalibrate
the
test
measurement
system
as
in
section
8.5.1
and
report
the
results
using
both
sets
of
calibration
data
(
i.
e.,
data
determined
prior
to
the
test
period
and
data
determined
following
the
test
period).
Note:
If
using
an
FTIR
for
the
analytical
instrument,
you
may
choose
to
follow
the
post­
test
calibration
procedures
of
Method
320
(
section
8.11.2)
in
lieu
of
the
above
procedures.

8.6
Ambient
Air
Sampling
(
Optional).
Sampling
the
ambient
air
surrounding
the
enclosure
is
optional.
However,
taking
these
samples
during
the
capture
efficiency
testing
will
identify
those
areas
of
the
enclosure
that
may
be
performing
less
efficiently.

8.6.1
Location
of
Ambient
Samples
Outside
the
Enclosure
(
Optional).
In
selecting
the
sampling
locations
for
collecting
samples
of
the
ambient
air
surrounding
the
enclosure,
consider
potential
leak
points,
the
direction
of
the
release,
and
laminar
flow
characteristics
in
the
area
surrounding
the
enclosure.
Samples
should
be
collected
from
all
sides
of
the
enclosure,
downstream
in
the
prevailing
room
air
flow,
and
in
the
operating
personnel
occupancy
102
areas.

8.6.2
Collection
of
Ambient
Samples
(
Optional).
During
the
tracer
gas
release,
collect
ambient
samples
from
the
area
surrounding
the
enclosure
perimeter
at
predetermined
location
using
disposable
syringes
or
some
other
type
of
containers
that
are
non­
absorbent,
inert,
and
that
have
low
permeability
(
i.
e.,
polyvinyl
fluoride
film
or
polyester
film
sample
bags
or
polyethylene,
polypropylene,
nylon
or
glass
bottles).
The
use
of
disposable
syringes
allows
samples
to
be
injected
directly
into
a
gas
chromatograph.
Concentration
measurements
taken
around
the
perimeter
of
the
enclosure
provide
evidence
of
capture
performance
and
will
assist
in
the
identification
of
those
areas
of
the
enclosure
that
are
performing
less
efficiently.

8.6.3
Analysis
and
Storage
of
Ambient
Samples
(
Optional).
Analyze
the
ambient
samples
using
an
analytical
instrument
calibrated
and
operated
according
to
the
procedures
of
this
appendix
or
ASTM
E
260
and
ASTM
E
697.
Samples
may
be
analyzed
immediately
after
a
sample
is
taken,
or
they
may
be
stored
for
future
analysis.
Experience
has
shown
no
degradation
of
concentration
in
polypropylene
syringes
when
stored
for
several
months
as
long
as
the
needle
or
syringe
is
plugged.
Polypropylene
syringes
should
be
discarded
after
one
use
to
eliminate
the
possibility
of
cross
contamination
of
samples.

9.0
Quality
Control.

9.1
Sampling,
System
Leak
Check.
A
sampling
system
leak
check
should
be
conducted
prior
to
and
after
each
test
run
to
ensure
the
integrity
of
the
sampling
system.

9.2
Zero
and
Calibration
Drift
Tests.

Section
Quality
Control
Measure
Effect
8.5.4
Zero
and
calibration
drift
tests.
Ensures
that
bias
introduced
by
drift
in
the
measurement
system
output
during
the
run
is
no
greater
than
3
percent
of
span.

10.0
Calibration
and
Standardization.

10.1
Control
Device
Inlet
Air
Flow
Rate
Measurement
Equipment.
Follow
the
equipment
calibration
requirements
103
specified
in
Methods
2,
3,
and
4
for
measuring
the
velocity,
molecular
weight,
and
moisture
of
the
control
device
inlet
air.

10.2
Tracer
Gas
Injection
Rate.
A
dry
gas
volume
flow
meter,
mass
flow
meter,
or
orifice
can
be
used
to
measure
the
tracer
gas
injection
flow
rate.
The
selected
flow
measurement
device
must
have
an
accuracy
of
greater
than
±
5
percent
at
the
field
operating
range.
Prior
to
the
test,
verify
the
calibration
of
the
selected
flow
measurement
device
using
either
a
wet
test
meter,
spirometer,
or
liquid
displacement
meter
as
the
calibration
device.
Select
a
minimum
of
two
flow
rates
to
bracket
the
expected
field
operating
range
of
the
flow
meter.
Conduct
three
calibration
runs
at
each
of
the
two
selected
flow
rates.
For
each
run,
note
the
exact
quantity
of
gas
as
determined
by
the
calibration
standard
and
the
gas
volume
indicated
by
the
flow
meter.
For
each
flow
rate,
calculate
the
average
percent
difference
of
the
indicated
flow
compared
to
the
calibration
standard.

10.3
Spectrometer.
Follow
the
calibration
requirements
specified
by
the
equipment
manufacturer
for
infrared
spectrometer
measurements
and
conduct
the
pretest
calibration
error
test
specified
in
section
8.5.1.
Note:
if
using
an
FTIR
analytical
instrument
see
Method
320,
section
10.

10.4
Gas
Chromatograph.
Follow
the
pre­
test
calibration
requirements
specified
in
section
8.5.1.

10.4
Gas
Chromatograph
for
Ambient
Sampling
(
Optional).
For
the
optional
ambient
sampling,
follow
the
calibration
requirements
specified
in
section
8.5.1
or
ASTM
E
260
and
E
697
and
by
the
equipment
manufacturer
for
gas
chromatograph
measurements.

11.0
Analytical
Procedures.

The
sample
collection
and
analysis
are
concurrent
for
this
method
(
see
section
8.0).

12.0
Calculations
and
Data
Analysis.

12.1
Estimate
MML
and
Span.
The
MML
is
the
minimum
measurement
level.
The
selection
of
this
level
is
at
the
discretion
of
the
tester.
However,
the
MML
must
be
higher
than
the
low­
level
calibration
standard,
and
the
tester
must
be
able
to
measure
at
this
level
with
a
precision
of

10
percent.
As
an
example,
select
the
MML
as
10
times
the
instrument's
published
detection
limit.
The
detection
limit
104
of
one
instrument
is
0.01
parts
per
million
by
volume
(
ppmv).
Therefore,
the
MML
would
be
0.10
ppmv.
Select
the
low­
level
calibration
standard
as
0.08
ppmv.
The
high­
level
standard
would
be
four
times
the
low­
level
standard
or
0.32
ppmv.
A
reasonable
mid­
level
standard
would
then
be
0.20
ppmv
(
halfway
between
the
low­
level
standard
and
the
highlevel
standard).
Finally,
the
span
value
would
be
approximately
0.40
ppmv
(
the
high­
level
value
is
80
percent
of
the
span).
In
this
example,
the
following
MML,
calibration
standards,
and
span
values
would
apply:
MML
=
0.10
ppmv
Low­
level
standard
=
0.08
ppmv
Mid­
level
standard
=
0.20
ppmv
High­
level
standard
=
0.32
ppmv
Span
value
=
0.40
ppmv
12.2
Estimate
Tracer
Gas
Injection
Rate
for
the
Given
Span.
To
estimate
the
minimum
and
maximum
tracer
gas
injection
rate,
assume
a
worst
case
capture
efficiency
of
80
percent,
and
calculate
the
tracer
gas
flow
rate
based
on
known
or
measured
parameters.
To
estimate
the
minimum
tracer
gas
injection
rate,
assume
that
the
MML
concentration
(
10
times
the
IR
detection
limit
in
this
example)
is
desired
at
the
measurement
location.
The
following
equation
can
be
used
to
estimate
the
minimum
tracer
gas
injection
rate:

((
QT­
MIN
x
0.8)/
QE)
x
(
CT
÷
100)
x106
=
MML
QT­
MIN
=
1.25
x
MML
x
(
QE
/
CT)
x10­
4
Where:
QT­
MIN
=
minimum
volumetric
flow
rate
of
tracer
gas
injected,
scfm
QE
=
volumetric
flow
rate
of
exhaust
gas,
scfm
CT
=
Tracer
gas
(
SF6)
concentration
in
gas
blend,
percent
by
volume
MML
=
minimum
measured
level,
ppmv
=
10
x
IRDL
(
for
this
example)
IRDL
=
IR
detection
limit,
ppmv
Standard
conditions:
20

C,
760
mm
Hg.

To
estimate
the
maximum
tracer
gas
injection
rate,
assume
that
the
span
value
is
desired
at
the
measurement
location.
The
following
equation
can
be
used
to
estimate
the
maximum
tracer
gas
injection
rate:

((
QT­
MAX
x
0.8)/
QE)
x
(
CT
÷
100)
x106
=
span
value
QT­
MAX
=
1.25
x
span
value
x
(
QE
/
CT)
x10­
4
Where:
105
QT­
Max
=
maximum
volumetric
flow
rate
of
tracer
gas
injected,
scfm
Span
value
=
instrument
span
value,
ppmv
The
following
example
illustrates
this
calculation
procedure:

Find
the
range
of
volumetric
flow
rate
of
tracer
gas
to
be
injected
when
the
following
parameters
are
known:
QE
=
60,000
scfm
(
typical
exhaust
gas
flow
rate
from
an
enclosure)
CT
=
2
percent
SF6
in
nitrogen
IRDL
=
0.01
ppmv
(
per
manufacturer's
specifications)
MML
=
10
x
IRDL
=
0.10
ppmv
Span
value
=
0.40
ppmv
QT
=
?

Minimum
tracer
gas
volumetric
flow
rate:
QT­
MIN
=
1.25
x
MML
x
(
QE
/
CT)
x10­
4
QT­
MIN
=
1.25
x
0.10
x
(
60,000/
2)
x10­
4
=
0.375
scfm
Maximum
tracer
gas
volumetric
flow
rate:
QT­
MAX
=
1.25
x
span
value
x
(
QE
/
CT)
x10­
4
QT­
MAX
=
1.25
x
0.40
x
(
60,000/
2)
x10­
4
=
1.5
scfm
In
this
example,
the
estimated
total
volumetric
flow
rate
of
the
two
percent
SF6
tracer
gas
injected
through
the
manifolds
in
the
enclosure
lies
between
0.375
and
1.5
scfm.

12.3
Calibration
Error.
Calculate
the
calibration
error
for
the
low­
level
and
mid­
level
calibration
gases
using
the
following
equation:

Err
=
|
Cstd
­
Cmeas|
÷
Cstd
x
100
Where:
Err
=
calibration
error,
percent
Cstd
=
low­
level
or
mid­
level
calibration
gas
value,
ppmv
Cmeas
=
measured
response
to
low­
level
or
mid­
level
concentration
gas,
ppmv
12.4
Calibration
Drift.
Calculate
the
calibration
drift
for
the
zero
and
low­
level
calibration
gases
using
the
following
equation:

D
=
|
Cinitial
­
Cfinal|
÷
Cspan
x
100
106
Where:
D
=
calibration
drift,
percent
Cinitial
=
low­
level
or
mid­
level
calibration
gas
value
measured
before
test
run,
ppmv
Cfinal
=
low­
level
or
mid­
level
calibration
gas
value
measured
after
test
run,
ppmv
Cspan
=
span
value,
ppmv
12.5
Calculate
Capture
Efficiency.
The
equation
to
calculate
enclosure
capture
efficiency
is
provided
below:

CE
=
(
SF6­
CD
÷
SF6­
INJ)
x
100
Where:
CE
=
capture
efficiency
SF6­
CD
=
mass
of
SF6
measured
at
the
inlet
to
the
CD
SF6­
INJ
=
mass
of
SF6
injected
from
the
tracer
source
into
the
enclosure
Calculate
the
CE
for
each
of
the
initial
three
test
runs.
Then
follow
the
procedures
outlined
in
section
12.6
to
calculate
the
overall
capture
efficiency.

12.6
Calculate
Overall
Capture
Efficiency.
After
calculating
the
capture
efficiency
for
each
of
the
initial
three
test
runs,
follow
the
procedures
in
40
CFR
part
63,
subpart
KK,
Appendix
A
to
determine
if
the
results
of
the
testing
can
be
used
in
determining
compliance
with
the
requirements
of
the
rule.
There
are
two
methods
that
can
be
used:
the
DQO
and
LCL
methods.
The
DQO
method
is
described
in
section
3
of
40
CFR
part
63,
subpart
KK,
Appendix
A
and
provides
a
measure
of
the
precision
of
the
capture
efficiency
testing
conducted.
Section
3
of
40
CFR
part
63,
subpart
KK,
Appendix
A
provides
an
example
calculation
using
results
from
a
facility.
If
the
DQO
criteria
are
met
using
the
first
set
of
three
test
runs,
then
the
facility
can
use
the
average
capture
efficiency
of
these
test
results
to
determine
the
capture
efficiency
of
the
enclosure.
If
the
DQO
criteria
are
not
met,
then
the
facility
can
conduct
another
set
of
three
runs
and
run
the
DQO
analysis
again
using
the
results
from
the
six
runs
OR
the
facility
can
elect
to
use
the
LCL
approach.

The
LCL
method
is
described
in
section
4
of
40
CFR
part
63,
subpart
KK,
Appendix
A
and
provides
sources
that
may
be
performing
much
better
than
their
regulatory
requirement,
a
screening
option
by
which
they
can
demonstrate
compliance.
The
LCL
approach
compares
the
80
percent
lower
confidence
limit
for
the
mean
measured
CE
value
to
the
applicable
regulatory
requirement.
If
the
LCL
capture
efficiency
is
107
higher
than
the
applicable
limit,
then
the
facility
is
in
initial
compliance
and
would
use
the
LCL
capture
efficiency
as
the
capture
efficiency
to
determine
compliance.
If
the
LCL
capture
efficiency
is
lower
than
the
applicable
limit,
then
the
facility
must
perform
additional
test
runs
and
rerun
the
DQO
or
LCL
analysis.

13.0
Method
Performance.

13.1
Measurement
System
Performance
Specifications.

13.1.1
Zero
Drift.
Less
than
±
3
percent
of
the
span
value.

13.1.2
Calibration
Drift.
Less
than
±
3
percent
of
the
span
value.

13.1.3
Calibration
Error.
Less
than
±
5
percent
of
the
calibration
gas
value.

13.2
Flow
Measurement
Specifications.
The
mass
flow,
volumetric
flow,
or
critical
orifice
control
meter
used
should
have
an
accuracy
of
greater
than
±
5
percent
at
the
flow
rate
used.

13.3
Calibration
and
Tracer
Gas
Specifications.
The
manufacturer
of
the
calibration
and
tracer
gases
should
provide
a
recommended
shelf
life
for
each
calibration
gas
cylinder
over
which
the
concentration
does
not
change
more
than
±
2
percent
from
the
certified
value.

14.0
Pollution
Prevention
[
Reserved].

15.0
Waste
Management
[
Reserved].

16.0
References.

1.
40
CFR
part
60,
Appendix
A,
EPA
Method
1
 
Sample
and
velocity
traverses
for
stationary
sources.

2.
40
CFR
part
60,
Appendix
A,
EPA
Method
2
 
Determination
of
stack
gas
velocity
and
volumetric
flow
rate.

3.
40
CFR
part
60,
Appendix
A,
EPA
Method
3
 
Gas
analysis
for
the
determination
of
dry
molecular
weight.

4.
40
CFR
part
60,
Appendix
A,
EPA
Method
4
 
Determination
of
moisture
content
in
stack
gases.

5.
SEMI
F15­
93
Test
Method
for
Enclosures
Using
Sulfur
Hexafluoride
Tracer
Gas
and
Gas
Chromotography.

6.
Memorandum
from
John
S.
Seitz,
Director,
Office
of
108
Air
Quality
Planning
and
Standards,
to
EPA
Regional
Directors,
Revised
Capture
Efficiency
Guidance
for
Control
of
Volatile
Organic
Compound
Emissions,
February
7,
1995.
(
That
memorandum
contains
an
attached
technical
document
from
Candace
Sorrell,
Emission
Monitoring
and
Analysis
Division,
"
Guidelines
for
Determining
Capture
Efficiency,"
January
9,
1994).

7.
Technical
Systems
Audit
of
Testing
at
Plant
"
C,"
EPA­
454/
R­
00­
26,
May
2000.

8.
Material
Safety
Data
Sheet
for
SF6.
Air
Products
and
Chemicals,
Inc.
Website:
www3.
airproducts.
com.
October
2001.

17.0
Tables,
Diagrams,
Flowcharts,
and
Validation
Data.
109
Table
1.
Summary
of
Critical
Physical
Measurements
for
Enclosure
Testing
Measurement
Measurement
instrumentation
Measurement
frequency
Measurement
site
Tracer
gas
injection
rate
Mass
flow
meter,
volumetric
flow
meter
or
critical
orifice
Continuous
Injection
manifolds
(
cylinder
gas)

Tracer
gas
concentration
at
control
device
inlet
Infrared
Spectrometer
or
GC/
ECD
Continuous
(
at
least
one
reading
per
minute)
for
a
minimum
of
20
minutes
Inlet
duct
to
the
control
device
(
outlet
duct
of
enclosure)

Volumetric
air
flow
rate
EPA
Methods
1,
2,
3,
4
(
40
CFR
part
60,
Appendix
A)
°
Velocity
sensor
(
Manometer/
Pitot
tube)
°
Thermocouple
°
Midget
Impinger
sampler
°
Orsat
or
Fyrite
Each
test
run
for
velocity
(
minimum);
Daily
for
moisture
and
molecular
weight
Inlet
duct
to
the
control
device
(
outlet
duct
of
enclosure)
110
Hot
Press
Loader
SF
6
Source
Flowmeter
Unloader
SF
6
Source
Flowmeter
See
Figure
2
for
typical
manifold
detail
Figure
1.
Plan
view
schematic
of
hot
press
and
enclosure
showing
SF6
manifold
locations.
111
(
3)
1/
4"
holes
every
8"
4"
sch.
40
pipe
Elevation
10'
6"

Figure
2.
Schematic
detail
for
manifold
system
for
SF6
injection.
112
For
the
reasons
stated
in
the
preamble,
title
40,
chapter
I,

part
429
of
the
Code
of
Federal
Regulations
is
amended
as
follows:

PART
429­­[
AMENDED]

1.
The
authority
citation
for
part
429
continues
to
read
as
follows:

Authority:
Secs.
301,
304(
b),
(
c),
(
e),
and
(
g),
306(
b)
and
(
c),
307(
a),
(
b),
and
(
c)
and
501
of
the
Clean
Water
Act
(
the
Federal
Water
Pollution
Control
Act
Amendments
of
1972,

as
amended
by
the
Clean
Water
Act
of
1977)
(
the
"
Act");
33
U.
S.
C.
1911,
1314(
b),
(
c),
(
e),
and
(
g),
1316(
b)
and
(
c),

1917(
b)
and
(
c),
and
1961;
86
Stat.
815,
Pub.
L.
92­
500;
91
Stat.
1567,
Pub
L.
95­
217.

2.
Section
429.11
is
amended
by
revising
paragraph
(
c)
to
read
as
follows:

§
429.11
General
definitions.

*
*
*
*
*

(
c)
The
term
"
process
wastewater"
specifically
excludes
non­
contact
cooling
water,
material
storage
yard
runoff
(
either
raw
material
or
processed
wood
storage),

boiler
blowdown,
and
wastewater
from
washout
of
thermal
oxidizers
or
catalytic
oxidizers,
wastewater
from
biofilters,
or
wastewater
from
wet
electrostatic
precipitators
used
upstream
of
thermal
oxidizers
or
catalytic
oxidizers
installed
by
facilities
covered
by
Subparts
B,
C,
D
or
M
to
comply
with
the
national
emissions
113
standards
for
hazardous
air
pollutants
(
NESHAP)
for
plywood
and
composite
wood
products
(
PCWP)
facilities
(
40
CFR
part
63,
subpart
DDDD).
For
the
dry
process
hardboard,
veneer,

finishing,
particleboard,
and
sawmills
and
planing
mills
subcategories,
fire
control
water
is
excluded
from
the
defin
ition.

*
*
*
*
*