Current through Register Vol. 41, No. 3, September 23, 2024
A. The provisions governing test methods and
procedures shall be as follows:
1. With
regard to the emissions standards in
9VAC5-40-6670 A,
9VAC5-40-6680, and
9VAC5-40-6690, the provisions of
9VAC5-40-30 (Emission testing)
apply.
2. With regard to the
emission limits in
9VAC5-40-6570 through
9VAC5-40-6660 and
9VAC5-40-6670 B, the following
provisions apply:
a.9VAC5-40-30 D and G;
b.
40 CFR
60.8(b) through (f) with the
exception of paragraph (a); and
c.
Subsections B through F of this section.
B. Class I units shall submit dioxin/furan
emission test results for at least one test conducted during or after 1990. The
emission tests shall have been conducted according to the procedures specified
under subsection D of this section.
C. Emission testing shall be conducted on the
following schedule.
1. Initial emission tests
for the pollutants listed in
9VAC5-40-6730 C shall be conducted
no later than 180 days after the final compliance date specified in
9VAC5-40-6710 A.
2. Annual emission tests for the pollutants
listed in 9VAC5-40-6730 C shall be conducted
no later than 13 months after the initial emission test and no later than 13
months after the previous emission test thereafter.
D. Emission testing shall be conducted as
follows.
1. Specific testing requirements are
as follows.
a. For dioxins/furans: Reference
Method 1 shall be used to determine the sampling location. Reference Method 23
shall be used to measure the pollutant concentration; oxygen (or carbon
dioxide) shall be measured simultaneously using Reference Method 3A or 3B. The
minimum sampling time shall be four hours per test run while the municipal
waste combustion unit is operating at full load.
b. For cadmium: Reference Method 1 shall be
used to determine the sampling location. Reference Method 29 shall be used to
measure the pollutant concentration; oxygen (or carbon dioxide) shall be
measured simultaneously using Reference Method 3A or 3B. Compliance testing
shall be performed while the municipal waste combustion unit is operating at
full load.
c. For lead: Reference
Method 1 shall be used to determine the sampling location. Reference Method 29
shall be used to measure the pollutant concentration; oxygen (or carbon
dioxide) shall be measured simultaneously using Reference Method 3A or 3B.
Compliance testing shall be performed while the municipal waste combustion unit
is operating at full load.
d. For
mercury: Reference Method 1 shall be used to determine the sampling location.
Reference Method 29 shall be used to measure the pollutant concentration;
oxygen (or carbon dioxide) shall be measured simultaneously using Reference
Method 3A or 3B. Compliance testing shall be performed while the municipal
waste combustion unit is operating at full load.
e. For opacity: Reference Method 9 shall be
used to determine the sampling location, and Reference Method 9 shall be used
to measure the pollutant concentration. Reference Method 9 shall be used to
determine compliance with the opacity limits, using a three-hour observation
period (30 six-minute averages).
f.
For particulate matter: Reference Method 1 shall be used to determine the
sampling location, and Reference Method 5 or 29 shall be used to measure the
pollutant concentration. The minimum sample probe volume shall be 1.0 cubic
meters. The probe and filter holder heating systems in the sampling train shall
be set to provide a gas temperature no greater than 160 ± 14°C. The
minimum sampling time is one hour.
g. For hydrogen chloride: Reference Method 1
shall be used to determine the sampling location. Reference Method 26 or 26A
shall be used to measure the pollutant concentration; oxygen (or carbon
dioxide) shall be measured simultaneously using Reference Method 3A or 3B. Test
runs shall be at least one hour long while the municipal waste combustion unit
is operating at full load.
h. For
fugitive ash: No sampling location applies. Reference Method 22 (visible
emissions) shall be used to measure the pollutant concentration. The three
one-hour observation periods shall include periods when the facility transfers
fugitive ash from the municipal waste combustion unit to the area where the
fugitive ash is stored or loaded onto containers or trucks.
i. For sulfur dioxide, nitrogen oxide, and
carbon monoxide, continuous emission monitoring systems shall be used. Emission
tests are not required except for quality assurance requirements in appendix F
of 40 CFR Part 60.
2.
Emission tests for all pollutants shall consist of at least three test runs as
specified in 40 CFR
60.8. The average of the pollutant emission
concentrations from the three test runs shall be used to determine compliance
with the applicable emission limits.
3. Oxygen (or carbon dioxide) measurements
shall be obtained at the same time as the pollutant measurements to determine
diluent gas levels, as specified in
9VAC5-40-6750 B.
4. The percent reduction in potential
hydrogen chloride emission shall be calculated using the following equation:
%PHCI = (Ei
- Eo) * (100/Ei)
where:
%PHCI = percent reduction of the
potential hydrogen chloride emissions
Ei = hydrogen chloride emission
concentration as measured at the air pollution control device inlet, corrected
to 7.0% oxygen, dry basis
Eo = hydrogen chloride emission
concentration as measured at the air pollution control device outlet, corrected
to 7.0% oxygen, dry basis
5.
The reduction efficiency for mercury emissions shall be calculated using the
following equation:
Hg = (Ei -
Eo)*(100/Ei)
where:
Hg = percent reduction of
potential mercury emissions
Ei = mercury emission
concentration as measured at the air pollution control device inlet, corrected
to 7.0% oxygen, dry basis
Eo = mercury emission
concentration as measured at the air pollution control device outlet, corrected
to 7.0% oxygen, dry basis
6.
The owner may apply to the board for approval under
40 CFR
60.8(b) to use a reference
method with minor changes in methodology, use an equivalent method, use an
alternative method the results of which the board has determined are adequate
for demonstrating compliance, waive the requirement for an emission test
because the owner has demonstrated compliance by other means, or use a shorter
sampling time or smaller sampling volume.
E. Alternative emission testing schedules may
be established as follows.
1. A Class II unit
that has conducted emission tests for dioxins/furans, cadmium, lead, mercury,
particulate matter, opacity, hydrogen chloride, and fugitive ash over three
consecutive years, and has demonstrated compliance with the emission limits is
not required to conduct an emission test for that pollutant for the next two
years. An emission test shall be conducted within 36 months of the anniversary
date of the third consecutive emission test that shows compliance with the
emission limit. Thereafter, emission tests shall be performed every third year
but no later than 36 months following the previous emission tests. If an
emission test shows noncompliance with an emission limit, annual emission tests
for that pollutant shall be conducted until all emission tests over three
consecutive years show compliance with the emission limit for that
pollutant.
2. An alternative test
schedule for dioxins/furans emissions may be established if the following
criteria are met:
(i) the affected facility
contains multiple municipal waste combustion units onsite that are subject to
this article; and
(ii) those
municipal waste combustion units have demonstrated levels of dioxins/furans
emissions less than or equal to 15 nanograms per dry standard cubic meter
(total mass) for Class I units, or 30 nanograms per dry standard cubic meter
(total mass) for Class II units, for two consecutive years. If these criteria
are met, annual emission tests shall be conducted on only one municipal waste
combustion unit per year. emission tests conducted under the provisions of this
subdivision shall be conducted as follows.
a.
The annual emission test shall be conducted no more than 13 months following an
emission test on any municipal waste combustion unit subject to this article.
Each year a different municipal waste combustion unit subject to this article
shall be tested. All municipal waste combustion units subject to this article
shall be tested in a sequence determined by the owner. Once a testing sequence
has been determined it shall not be changed without approval of the
board.
b. If each annual emission
test shows levels of dioxins/furans emissions less than or equal to 15
nanograms per dry standard cubic meter (total mass) for Class I units, or 30
nanograms per dry standard cubic meter (total mass) for Class II units,
emission tests may be conducted on only one municipal waste combustion unit
subject to this article per year.
c. If any annual emission test indicates
levels of dioxins/furans emissions greater than 15 nanograms per dry standard
cubic meter (total mass) for Class I units, or 30 nanograms per dry standard
cubic meter (total mass) for Class II units, subsequent annual emission tests
shall be conducted on all municipal waste combustion units subject to this
article. The owner may return to testing one municipal waste combustion unit
subject to this article per year if it can demonstrate dioxins/furans emissions
levels less than or equal to 15 nanograms per dry standard cubic meter (total
mass) for Class I units, or 30 nanograms per dry standard cubic meter (total
mass) for Class II units, for all municipal waste combustion units at a
stationary source subject to this article for two consecutive years.
F. No owner
of an affected facility shall deviate from the 13-month testing schedules
specified in
9VAC5-40-6740 C and
9VAC5-40-6740 E 2 a without
applying to the board for an alternative schedule, and the board approves the
request for alternate scheduling prior to the date on which the owner would
otherwise have been required to conduct the next emission test.