R 336.2160
R 336.2160 Mercury low mass emitter monitoring methodology.
Cite as Mich. Admin. Code R 336.2160
Rule 1160. (1) Unless the federal MATS is an applicable requirement, beginning April
16, 2015, the monitoring methodology shall meet all of the requirements of this rule.
(2) The owner or operator of an affected unit that emits less than 464 ounces (29 pounds)
of mercury per year may use the mercury low mass emitter monitoring methodology after
performing initial certification testing. The owner or operator of the affected unit shall
perform the initial certification testing and ongoing quality assurance as described in
subrules (2) and (3) of this rule. The initial test shall be performed within 60 days of the
effective date of these rules or 90 days prior to the compliance date, whichever is later.
(3) For the initial certification testing, the following shall apply:
(a) The owner or operator shall perform mercury emission testing to determine the
mercury concentration, for example, total vapor-phase mercury, in the effluent.
(b) Testing shall be performed using 1 of the following mercury reference methods:
ASTM D6784-02, adopted by reference in R 336.2150, Method 29, method 30A, or
method 30B of Part 60, adopted by reference in R 336.1299. A test shall consist of a
minimum of 3 runs at maximum routine load while firing fuel or fuels with the highest
mercury content.
(c) The minimum run time shall be 1 hour if method 30A is used. If method 29, ASTM
D6784-02, or method 30B is used, paired samples are required for each test run and the
runs shall be long enough to ensure that sufficient mercury is collected to analyze. When
method 29 or ASTM D6784-02 is used the test results shall be based on the vapor-phase
mercury collected in the back half of the sampling train. For each method 29, ASTM
D6784-02, or method 30B test run, the paired trains shall meet the relative deviation
requirement specified in method 30B. If the relative deviation specification is met, the
result of the 2 samples shall be averaged arithmetically.
(d) If the unit is equipped with flue gas desulfurization or add-on mercury emission
controls, the controls shall be operating normally during the testing, and for the purpose of
establishing proper operation of the controls, parametric data shall be recorded.
(e) A complete test plan and test notification shall be provided to the department 30 days
prior to the testing.
(4) Based on the results of emission testing, the following equation shall be used to
provide a conservative estimate of the annual mercury mass emissions for the unit:
E = N · K · CHg · Qmass
Where:
E = Estimated annual mercury mass emissions in ounces per year.
N = 8760 hours or the maximum number of operating hours per year allowed by the unit's
federally enforceable permit.
K = 9.978 x 10-10 ounces-scm/µg-standard cubic foot (scf).
CHg = Highest mercury concentration (µg/scm) from any test run or 0.05 µg/scm,
whichever is greater.
Qmass = Maximum potential flow rate.
(a) If the estimated annual mercury mass emissions are 464 ounces per year or less, the
unit is eligible to use the monitoring methodology of this rule, and mercury continuous
emission monitoring is not required.
(b) The results of the testing performed under this rule shall be submitted as a certification
application to the department, not later than 45 days after the test is completed. The
calculations demonstrating that the unit emits less than 464 ounces per year shall be
provided, and the default mercury concentration that will be used for mercury mass
emission reporting shall be specified.
(c) Following initial certification the following steps shall be taken:
(i) The default mercury concentration used to estimate the unit's annual mercury mass
emissions shall be reported for each unit operating hour and shall be used to calculate
hourly mercury emissions.
(ii) The mercury emission testing described in this rule shall be repeated periodically for
the purpose of quality assurance, as follows:
(A) If the results of the certification testing under this rule show that the unit emits 144
ounces (9 pounds) per year or less, the first retest is required by the end of the fourth quarter
following the calendar quarter of the certification test.
(B) If the results of the certification test under this section show that the unit emits more
than 144 ounces per year but less than 464 ounces per year, the first retest is required by
the end of the second quarter following the calendar quarter of the certification test.
(C) Retesting shall be required either by the end of the second or fourth quarter following
the quarter of the previous test, depending on the results of the previous test. To determine
whether the next retest is required within 2 or 4 quarters, substitute the highest mercury
concentration from the current test or 0.50 µg/scm, whichever is greater, into the equation
under subrule (3) of the rule. If the estimated annual mass emissions exceed 144 ounces,
the next test is due within 2 quarters. If the estimated annual mass emissions are 144 ounces
or less, the next test is due within 4 quarters.
(d) The updated mercury default concentration shall be applied beginning with the first
unit operating hour after the completion of the retest.
(e) If the unit is equipped with flue gas desulfurization system or add-on mercury controls,
the owner or operator shall record the parametric data for each unit operating hour.
(f) An additional retest is required when there is a change in coal rank of the primary fuel
or other significant fuel change.
(g) At the end of each calendar year, if the cumulative annual mercury mass emission
from an affected unit exceeds 464 ounces, the owner or operator shall install, certify,
operate, and maintain a mercury continuous emission monitoring system, or sorbent trap
monitoring system, not later than 180 days after the end of the calendar year in which the
emissions exceeded 464 ounces.