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 440.23 - Nitric acid plants
Universal Citation: WI Admin Code ยง NR 440.23
Current through August 26, 2024
(1) APPLICABILITY AND DESIGNATION OF AFFECTED FACILITY.
(a) The provisions of this section
are applicable to each nitric acid production unit, which is the affected
facility.
(b) Any facility under
par. (a) that commences construction or modification after August 17, 1971, is
subject to the requirements of this section.
(2) DEFINITIONS. As used in this section, terms not defined in this subsection have the meanings given in s. NR 440.02.
(a) "Nitric
acid production unit" means any facility producing weak nitric acid by either
the pressure or atmospheric pressure process.
(b) "Weak nitric acid" means acid which is 30
to 70% in strength.
(3) STANDARD FOR NITROGEN OXIDES.
(a) On and
after the date on which the performance test required to be conducted by s.
NR 440.08 is
completed, no owner or operator subject to the provisions of this section may
cause to be discharged into the atmosphere from any affected facility any gases
which:
1. Contain nitrogen oxides, expressed
as NO2, in excess of 1.5 kg per metric ton of acid produced (3.0 lb per ton),
the production being expressed as 100% nitric acid.
2. Exhibit 10% opacity, or greater.
(4) EMISSION MONITORING.
(a) The source owner or operator
shall install, calibrate, maintain and operate a continuous monitoring system
for measuring nitrogen oxides (NOx). The pollutant gas mixtures under
Performance Specification 2 of Appendix B of 40 CFR part 60, incorporated by
reference in s.
NR 440.17, and for calibration checks under s.
NR 440.13(4) shall be nitrogen dioxide
(NO2). The span value shall be 500 ppm of NO2. Method 7 shall be used for the
performance evaluation under s.
NR 440.13(3). Acceptable alternative
methods to Method 7 are given in sub. (5) (c).
(b) The owner or operator shall establish a
conversion factor for the purpose of converting monitoring data into units of
the applicable standard (kg/metric ton, lb/ton). The conversion factor shall be
established by measuring emissions with the continuous monitoring system
concurrent with measuring emissions with the applicable reference method tests.
Using only that portion of the continuous monitoring emission data that
represents emission measurements concurrent with the reference method test
periods, the conversion factor shall be determined by dividing the reference
method test data averages by the monitoring data averages to obtain a ratio
expressed in units of the applicable standard to units of the monitoring data,
i.e., kg/metric ton per ppm (lb/ton per ppm). The conversion factor shall be
reestablished during any performance test under s.
NR 440.08 or
any continuous monitoring system performance evaluation under s.
NR 440.13(3).
(c) The owner or operator shall record the
daily production rate and hours of operation.
(e) For the purpose of reports required under
s.
NR 440.07(3), periods of excess
emissions that shall be reported are defined as any 3-hour period during which
the average nitrogen oxides emissions (arithmetic average of 3 contiguous
one-hour periods) as measured by a continuous monitoring system exceed the
standard under sub. (3) (a).
(5) TEST METHODS AND PROCEDURES.
(a) In conducting the performance tests
required in s.
NR 440.08, the
owner or operator shall use as reference methods and procedures the test
methods in Appendix A of 40 CFR part 60, incorporated by reference in s.
NR 440.17, or other methods and procedures as specified
in this subsection, except as provided in s.
NR 440.08(2). Acceptable alternative
methods and procedures are given in par. (c).
(b) The owner or operator shall determine
compliance with the NOx standard in sub. (3) as follows:
1. The emission rate (E) of NOx shall be
computed for each run using the following equation:
E = (Cs Qsd)/(PK)
where:
E is the emission rate of NOx as NO2, kg/metric ton (lb/ton) of 100% nitric acid
Cs is the concentration of NOx as NO2, g/dscm (lb/dscf)
Qsd is the volumetric flow rate of effluent gas, dscm/hr (dscf/hr)
P is the acid production rate, metric ton/hr (ton/hr) or 100% nitric acid
K is the conversion factor, 1000 g/kg (1.0 lb/lb)
2. Method 7 shall be used to
determine the NOx concentration of each grab sample. Method 1 shall be used to
select the sampling site and the sampling point shall be the centroid of the
stack or duct or at a point no closer to the walls than 1 m (3.28 ft). Four
grab samples shall be taken at approximately 15-minute intervals. The
arithmetic mean of the 4 sample concentrations shall constitute the run value
(Cs).
3. Method 2 shall be used to
determine the volumetric flow rate (Qsd) of the effluent gas. The measurement
site shall be the same as for the NOx sample. A velocity traverse shall be made
once per run within the hour that the NOx samples are taken.
4. The methods of sub. (4) (c) shall be used
to determine the production rate (P) of 100% nitric acid for each run. Material
balance over the production system shall be used to confirm the production
rate.
(c) The owner or
operator may use the following as alternatives to the methods and procedures
specified in this subsection:
1. For Method 7,
Method 7A, 7B, 7C or 7D may be used. If Method 7C or 7D is used, the sampling
time shall be at least 1 hour.
(d) The owner or operator shall use the
procedure in sub. (4) (b) to determine the conversion factor for converting the
monitoring data to the units of the standard.
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