Wisconsin Administrative Code
Department of Natural Resources
NR 400-499 - Environmental Protection - Air Pollution Control
Chapter NR 440 - Standards of performance for new stationary sources
Subchapter II - Standards of Performance
Section NR 440.565 - Pressure sensitive tape and label surface coating operations
Universal Citation: WI Admin Code ยง NR 440.565
Current through August 26, 2024
(1) APPLICABILITY AND DESIGNATION OF AFFECTED FACILITY.
(a) The
affected facility to which the provisions of this section apply is each coating
line used in the manufacture of pressure sensitive tape and label
materials.
(b) Any affected
facility which inputs to the coating process 45 Mg (50 tons) of VOC or less per
12-month period is not subject to the emission limits of sub. (3) (a), however,
the affected facility is subject to the requirements of all other applicable
subsections of this section. If the amount of VOC input exceeds 45 Mg (50 tons)
per 12-month period, the coating line will become subject to sub. (3) (a) and
all other subsections of this section.
(c) This section applies to any affected
facility which begins construction, modification, or reconstruction after
December 30, 1980.
(2) DEFINITIONS AND SYMBOLS.
(a) As used in this
section, terms not defined in this subsection have the meanings given in s.
NR 440.02, unless the context requires otherwise.
1. "Coating line" means any number or
combination of adhesive, release, or precoat coating applicators, flashoff
areas and ovens which coat a continuous web, located between a web unwind
station and a web rewind station, to produce pressure sensitive tape and label
materials.
3. "Coating solids
applied" means the solids content of the coated adhesive, release, or precoat
as measured by Method 24 of 40 CFR part 60, Appendix A, incorporated by
reference in s.
NR 440.17(1).
4. "Flashoff area" means the portion of a
coating line after the coating applicator and usually before the oven
entrance.
5. "Fugitive volatile
organic compounds" means any volatile organic compounds which are emitted from
the coating applicator and flashoff areas and are not emitted in the
oven.
6. "Hood or enclosure" means
any device used to capture fugitive volatile organic compounds.
7. "Oven" means a chamber which uses heat or
irradiation to bake, cure, polymerize, or dry a surface coating.
8. "Precoat" means a coating operation in
which a coating other than an adhesive or release is applied to a surface
during the production of a pressure sensitive tape or label product.
9. "Solvent applied in the coating" means all
organic solvent contained in the adhesive, release and precoat formulations
that is metered into the coating applicator from the formulation
area.
10. "Total enclosure" means a
structure or building around the coating applicator and flashoff area or the
entire coating line for the purpose of confining and totally capturing fugitive
VOC emissions.
11. "VOC" means
volatile organic compound.
(b) As used in this section, symbols not
defined in this subsection have the meanings given in s.
NR 440.03.
1. "a" means
the gas stream vents exiting the emission control device.
2. "b" means the gas stream vents entering
the emission control device.
3.
"Caj" means the concentration of VOC (carbon equivalent) in each gas stream (j)
exiting the emission control device, in parts per million by volume.
4. "Cbi" means the concentration of VOC
(carbon equivalent) in each gas stream (i) entering the emission control
device, in parts per million by volume.
5. "Cfk" means the concentration of VOC
(carbon equivalent) in each gas stream (k) emitted directly to the atmosphere,
in parts per million by volume.
6.
"G" means the calculated weighted average mass (kg) of VOC per mass (kg) of
coating solids applied each calendar month.
7. "Mci" means the total mass (kg) of each
coating (i) applied during the calendar month as determined from facility
records.
8. "Mr" means the total
mass (kg) of solvent recovered for a calendar month.
9. "Qaj" means the volumetric flow rate of
each affluent gas stream (j) exiting the emission control device, in dry
standard cubic meters per hour.
10.
"Qbi" means the volumetric flow rate of each effluent gas stream (i) entering
the emission control device, in dry standard cubic meters per hour.
11. "Qfk" means the volumetric flow rate of
each effluent gas stream (k) emitted to the atmosphere, in dry standard cubic
meters per hour.
12. "R" means the
overall VOC emission reduction achieved for a calendar month (in
percent).
13. "Rq" means the
required overall VOC emission reduction (in percent).
14. "Woi" means the weight fraction of
organics applied of each coating (i) applied during a calendar month as
determined from Method 24 of 40 CFR part 60, Appendix A, incorporated by
reference in s.
NR 440.17(1), or coating manufacturer's
formulation data.
15. "Wsi" means
the weight fraction of solids applied of each coating (i) applied during a
calendar month as determined from Method 24 of 40 CFR part 60, Appendix A,
incorporated by reference in s.
NR 440.17(1), or coating manufacturer's
formulation data.
(3) STANDARD FOR VOLATILE ORGANIC COMPOUNDS.
(a) On and after the date on which the
performance test required by s.
NR 440.08 has
been completed each owner or operator subject to this section may:
1. Cause the discharge into the atmosphere
from an affected facility not more than 0.20 kg VOC/kg of coating solids
applied as calculated on a weighted average basis for one calendar month;
or
2. Demonstrate for each affected
facility;
a. A 90% overall VOC emission
reduction as calculated over a calendar month; or
b. The percent overall VOC emission reduction
specified in sub. (4) (b) as calculated over a calendar month.
(4) COMPLIANCE PROVISIONS.
(a) To determine
compliance with sub. (3) the owner or operator of the affected facility shall
calculate a weighted average of the mass of solvent used per mass of coating
solids applied for one calendar month period according to the following
procedures:
1. Determine the weight fraction
of organics and the weight fraction of solids of each coating applied by using
Reference Method 24 of 40 CFR part 60, Appendix A, incorporated by reference in
s.
NR 440.17, or by the coating manufacturer's formulation
data.
2. Compute the weighted
average by the following equation:
3. For
each affected facility where the value of G is less than or equal to 0.20 kg
VOC per kg of coating solids applied the affected facility is in compliance
with sub. (3) (a) 1.
(b)
To determine compliance with sub. (3) (a) 2. the owner or operator shall
calculate the required overall VOC emission reduction according to the
following equation:
If Rq is less than or equal to 90% the required overall VOC emission reduction is Rq. If Rq is greater than 90% the required overall VOC emission reduction is 90%.
(c) Where the compliance with the emission
limits specified in sub. (3) (a) 2. is achieved through the use of a solvent
recovery system the owner or operator shall determine the overall VOC emission
reduction for a one calendar month period by the following equation:
If the R value is equal to or greater than the Rq value specified in par. (b) compliance with sub. (3) (a) 2. is demonstrated.
(d) Where compliance with the
emission limit specified in sub. (3) (a) 2. is achieved through the use of a
solvent destruction device the owner or operator shall determine calendar
monthly compliance by comparing the monthly required overall VOC emission
reduction specified in par. (b) to the overall VOC emission reduction
demonstrated in the most recent performance test which complied with sub. (3)
(a) 2. If the monthly required overall VOC emission reduction is less than or
equal to the overall VOC reduction of the most recent performance test the
affected facility is in compliance with sub. (3) (a) 2.
(e) Where compliance with sub. (3) (a) 2. is
achieved through the use of a solvent destruction device, the owner or operator
shall continuously record the destruction device combustion temperature during
coating operations for thermal incineration destruction devices or the gas
temperature upstream and downstream of the incinerator catalyst bed during
coating operations for catalytic incineration destruction devices. For thermal
incineration destruction devices the owner or operator shall record all 3-hour
periods (during actual coating operations) during which the average temperature
of the device is more than 28°C (50°F) below the average temperature of
the device during the most recent performance test complying with sub. (3) (a)
2. For catalytic incineration destruction devices, the owner or operator shall
record all 3-hour periods (during actual coating operations) during which the
average temperature of the device immediately before the catalyst bed is more
than 28°C (50°F) below the average temperature of the device during the
most recent performance test complying with sub. (3) (a) 2. and all 3-hour
periods (during actual coating operations) during which the average temperature
difference across the catalyst bed is less than 80% of the average temperature
difference of the device during the most recent test complying with sub. (3)
(a) 2.
(f) After the initial
performance test required for all affected facilities under s.
NR 440.08,
compliance with the VOC emission limitation and percentage reduction
requirements under sub. (3) is based on the average emission reduction for one
calendar month. A separate compliance test is completed at the end of each
calendar month after the initial performance test and a new calendar month's
average VOC emission reduction is calculated to show compliance with the
standard.
(g) If a common emission
control device is used to recover or destroy solvent from more than one
affected facility the performance of that control device is assumed to be equal
for each of the affected facilities. Compliance with sub. (3) (a) 2. is
determined by the methods specified in pars. (c) and (d) and is performed
simultaneously on all affected facilities.
(h) If a common emission control device is
used to recover solvent from an existing facility (or facilities) as well as
from an affected facility (or facilities) the overall VOC emission reduction
for the affected facility (or facilities) for the purpose of compliance, shall
be determined by the following procedures:
1.
The owner or operator of the existing facility (or facilities) shall determine
the mass of solvent recovery for a calendar month period from the existing
facility (or facilities) prior to the connection of the affected facility (or
facilities) to the emission control device.
2. The affected facility (or facilities)
shall then be connected to the emission control device.
3. The owner or operator shall determine the
total mass of solvent recovery from both the existing and affected facilities
over a calendar month period. The mass of solvent determined in subd. 1. from
the existing facility shall be subtracted from the total mass of recovery
solvent to obtain the mass of solvent recovery from the affected facility (or
facilities). The overall VOC emission reduction of the affected facility (or
facilities) can then be determined as specified in par. (c).
(i) If a common emission control
device is used to destruct solvent from an existing facility (or facilities) as
well as from an affected facility (or facilities) the overall VOC emission
reduction for the affected facility (or facilities), for the purpose of
compliance, shall be determined by the following procedures:
1. The owner or operator shall operate the
emission control device with both the existing and affected facilities
connected.
2. The concentration of
VOC (in parts per million by volume) after the common emission control device
shall be determined as specified in sub. (5) (c).
(j) Startups and shutdowns are normal
operation for this source category. Emissions from these operations are to be
included when determining if the standard specified at sub. (3) (a) 2. is being
attained.
(5) PERFORMANCE TEST PROCEDURES.
(a) The
performance test for affected facilities complying with sub. (3) without the
use of add-on controls shall be identical to the procedures specified in sub.
(4) (a).
(b) The performance test
for affected facilities controlled by a solvent recovery device shall be
conducted as follows:
1. The performance test
shall be a one calendar month test and not the average of 3 runs as specified
in s.
NR 440.08(6).
2. The weighted average mass of VOC per mass
of coating solids applied for a one calendar month period shall be determined
as specified in sub. (4) (a) 2.
3.
Calculate the required percent overall VOC emission reduction as specified in
sub. (4) (b).
4. Inventory VOC
usage and VOC recovery for a one calendar month period.
5. Determine the percent overall VOC emission
reduction as specified in sub. (4) (c).
(c) The performance test for affected
facilities controlled by a solvent destruction device shall be conducted as
follows:
1. The performance of the solvent
destruction device shall be determined by averaging the results of 3 test runs
as specified in s.
NR 440.08(6).
2. Determine for each affected facility prior
to each test run the weighted average mass of VOC per mass of coating solids
applied being used at the facility. The weighted average shall be determined as
specified in sub. (4) (a). In this application the quantities of Woi, Wsi and
Mci shall be determined for the time period of each test run and not a calendar
month as specified in sub. (2).
3.
Calculate the required percent overall VOC emission reduction as specified in
sub. (4) (b).
4. Determine the
percent overall VOC emissions reduction of the solvent destruction device by
the following equation and procedures:
a. The owner or
operator of the affected facility shall construct the overall VOC emission
reduction system so that all volumetric flow rates and total VOC emissions can
be accurately determined by the applicable test methods and procedures
specified in sub. (7) (b).
b. The
owner or operator of an affected facility shall construct a temporary total
enclosure around the coating line applicator and flashoff area during the
performance test for the purpose of capturing fugitive VOC emissions. If a
permanent total enclosure exists in the affected facility prior to the
performance test and the department is satisfied that the enclosure is totally
capturing fugitive VOC emissions then no additional total enclosure will be
required for the performance test.
c. For each affected facility where the value
of R is greater than or equal to the value Rq calculated in sub. (4) (b)
compliance with sub. (3) (a) 2. is demonstrated.
(6) MONITORING OF OPERATIONS AND RECORDKEEPING.
(a) The owner or
operator of an affected facility subject to this section shall maintain a
calendar month record of all coatings used and the results of the reference
test methods specified in sub. (7) (a) or the manufacturer's formulation data
used for determining the VOC content of those coatings.
(b) The owner or operator of an affected
facility controlled by a solvent recovery device shall maintain a calendar
month record of the amount of solvent applied in the coating at each affected
facility.
(c) The owner or operator
of an affected facility controlled by a solvent recovery device shall install,
calibrate, maintain and operate a monitoring device for indicating the
cumulative amount of solvent recovery by the device over a calendar month
period. The monitoring device shall be accurate within "2.0%. The owner or
operator shall maintain a calendar month record of the amount of solvent
recovery by the device.
(d) The
owner or operator of an affected facility operating at the conditions specified
in sub. (1) (b) shall maintain a 12 month record of the amount of solvent
applied in the coating at the facility.
(e) The owner or operator of an affected
facility controlled by a thermal incineration solvent destruction device shall
install, calibrate, maintain and operate a monitoring device which continuously
indicates and records the temperature of the solvent destruction device's
exhaust gases. The monitoring device shall have an accuracy of the greater of "
0.75% of the temperature being measured expressed in degrees Celsius or " 2.5
°C.
(f) The owner or operator
of an affected facility controlled by a catalytic incinerator solvent
destruction device shall install, calibrate, maintain, and operate a monitoring
device which continuously indicates and records the gas temperature both
upstream and downstream of the catalyst bed.
(g) The owner or operator of an affected
facility controlled by a solvent destruction device which uses a hood or
enclosure to capture fugitive VOC emissions shall install, calibrate, maintain
and operate a monitoring device which continuously indicates that the hood or
enclosure is operating. No continuous monitor is required if the owner or
operator can demonstrate that the hood or enclosure system is interlocked with
the affected facility's oven recirculation air system.
(h) Records of the measurements required in
subs. (4) and (6) must be retained for at least two years following the date of
the measurements.
(7) TEST METHODS AND PROCEDURES.
(a) The VOC
contents per unit of coating solids applied and compliance with sub. (3) (a) 1.
shall be determined by either Method 24 of 40 CFR part 60, Appendix A,
incorporated by reference in s.
NR 440.17(1), and the equations
specified in sub. (4) or by manufacturer's formulation data. In the event of
any inconsistency between a Method 24 test and manufacturer's formulation data,
the Method 24 test will govern. The department may require an owner or operator
to perform Method 24 tests during such months as it deems appropriate. For
Method 24, the coating sample shall be a one liter sample taken into a one
liter container at a point where the sample will be representative of the
coating applied to the web substrate.
(b) Method 25 of 40 CFR part 60, Appendix A,
incorporated by reference in s.
NR 440.17(1), shall be used to determine
the VOC concentration, in parts per million by volume, of each effluent gas
stream entering and exiting the solvent destruction device or its equivalent
and each effluent gas stream emitted directly to the atmosphere. Methods 1, 2,
3, and 4 of 40 CFR part 60, Appendix A, incorporated by reference in s.
NR 440.17(1), shall be used to determine
the sampling location, volumetric flow rate, molecular weight and moisture of
all sampled gas streams. For Method 25, the sampling time for each of 3 runs
shall be at least one hour. The minimum sampling volume shall be 0.003 dscm
except that shorter sampling times or smaller volumes, when necessitated by
process variables or other factors, may be approved by the
department.
(c) If the owner or
operator can demonstrate to the department's satisfaction that testing of
representative stacks yields results comparable to those that would be obtained
by testing all stacks the department will approve testing of representative
stacks on a case-by-case basis.
(8) REPORTING REQUIREMENTS.
(a) For all affected facilities subject to
compliance with sub. (3) the performance test data and results from the
performance test shall be submitted to the department as specified in s.
NR 440.08(1).
(b) Following the initial performance test,
the owner or operator of each affected facility shall submit quarterly reports
to the department of exceedances of the VOC emission limits specified in sub.
(3). If no exceedances occur during a particular quarter, a report stating this
shall be submitted to the department semiannually.
(c) The owner or operator of each affected
facility shall also submit reports at the frequency specified in s.
NR 440.07(3) when the incinerator
temperature drops as defined under sub. (4) (e). If no such periods occur, the
owner or operator shall state this in the report.
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