(a) Each owner or operator subject to the
provisions of this article shall comply with the test methods and procedures
requirements provided in this section.
(b) When a closed-vent system is tested for
compliance with the "no detectable emissions", requirements in Section
66265.1033(k),
the test shall comply with the following requirements:
(1) monitoring shall comply with Reference
Method 21 in 40 CFR, Part
60 ;
(2)
the detection instrument shall meet the performance criteria of Reference
Method 21;
(3) the instrument shall
be calibrated before use on each day of its use by the procedures specified in
Reference Method 21;
(4)
calibration gases shall be:
(A) zero air
(less than 10 ppm of hydrocarbon in air);
(B) a mixture of methane or n-hexane and air
at a concentration of approximately, but less than, 10,000 ppm methane or
n-hexane;
(5) the
background level shall be determined as set forth in Reference Method
21;
(6) the instrument probe shall
be traversed around all potential leak interfaces as close to the interface as
possible as described in Reference Method 21; and
(7) the arithmetic difference between the
maximum concentration indicated by the instrument and the background level is
compared with 500 ppm for determining compliance.
(c) Performance tests to determine compliance
with Section
66265.1032(a) and
with the total organic compound concentration limit of Section
66265.1033(c)
shall comply with the following:
(1)
performance tests to determine total organic compound concentrations and mass
flow rates entering and exiting control devices shall be conducted and data
reduced in accordance with the following reference methods and calculation
procedures:
(A) method 2 in 40 CFR, Part
60,
incorporated by reference in Section
66260.11 of this chapter, for
velocity and volumetric flow rate;
(B) method 18 in 40 CFR, Part
60,
incorporated by reference in Section
66260.11 of this division, for
organic content;
(C) each
performance test shall consist of three separate runs; each run conducted for
at least one hour under the conditions that exist when the hazardous waste
management unit is operating at the highest load or capacity level reasonably
expected to occur. For the purpose of determining total organic compound
concentrations and mass flow rates, the average of results of all runs shall
apply. The average shall be computed on a time-weighted basis;
(D) total organic mass flow rates shall be
determined by the following equation:
Click
here to view image
| where: |
|
| Eh = |
Total organic
mass flow rate, kg/h; |
| Qsd = |
Volumetric flow rate of gases entering
or exiting control device, as determined by Method 2, dry standard
m3 /hour; |
| n= |
Number of organic compounds in the vent
gas; |
| Ci = |
Organic
concentration in ppm, dry basis, of compound i in the vent gas, as determined
by Method 18; |
| MWi = |
Molecular weight
of organic compound in the vent gas, kg/kg-mol; |
| 0.0416= |
Conversion factor for molar volume,
kg-mol/m3 (at 293 K and 760 mm Hg); |
| 10-6 = |
Conversion
from ppm, ppm-1. |
(E)
the annual total organic emission rate shall be determined by the following
equation:
EA = (Eh)
(H)
where:
EA= Total organic mass emission
rate, kg/y;
Eh = As determined in paragraph
(c)(1)(D) of this section;
H= Total annual hours of operations for the affected unit,
h.
(F) total organic
emissions from all affected process vents at the facility shall be determined
by summing the hourly total organic mass flow rates (Eh,
as determined in subsection (c)(1)(D) of this section) and by summing the
annual total organic mass emission rates (EA, as
determined in paragraph (c)(1)(E) of this section for all affected process
vents at the facility; and
(2) the owner or operator shall record such
process information as may be necessary to determine the conditions of the
performance tests. Operations during periods of startup, shutdown, and
malfunction shall not constitute representative conditions for the purpose of a
performance test;
(3) the owner or
operator of an affected facility shall provide, or cause to be provided,
performance testing facilities as follows:
(A)
sampling ports adequate for the test methods specified in subsection (c)(1) of
this section.
(B) safe sampling
platform(s);
(C) safe access to
sampling platform(s); and
(D)
utilities for sampling and testing equipment; and
(4) for the purpose of making compliance
determinations, the time-weighted average of the results of the three runs
shall apply. In the event that a sample is accidentally lost or conditions
occur in which one of the three runs must be discontinued because of forced
shutdown, failure of an irreplaceable portion of the same train, extreme
meteorological conditions, or other circumstances beyond the owner's or
operator's control, compliance may, upon the Department's written approval, be
determined using the average of the results of the two other
runs.
(d) To show that a
process vent associated with a hazardous waste distillation, fractionation,
thin-film evaporation, solvent extraction, or air or steam stripping operation
is not subject to the requirements of this article, the owner or operator shall
make an initial determination that the time-weighted, annual average total
organic concentration of the waste managed by the waste management unit is less
than 10 ppmw using one of the following two methods:
(1) direct measurement of the organic
concentration of the waste using the following procedures:
(A) the owner or operator shall take a
minimum of four grab samples of waste for each waste stream managed in the
affected unit under process conditions expected to cause the maximum waste
organic concentration;
(B) for
waste generated on-site, the grab samples shall be collected at a point before
the waste is exposed to the atmosphere such as in an enclosed pipe or other
closed system that is used to transfer the waste after generation to the first
affected distillation, fractionation, thin-film evaporation, solvent
extraction, or air or steam stripping operation. For waste generated offsite,
the grab samples shall be collected at the inlet to the first waste management
unit that receives the waste, provided the waste has been transferred to the
facility in a closed system such as a tank truck and the waste is not diluted
or mixed with other waste;
(C) each
sample shall be analyzed and the total organic concentration of the sample
shall be computed using Method 9060 or 8260 of SW-846 (incorporated by
reference under Section
66260.11); and
(D) the arithmetic mean of the results of the
analyses of the four samples shall apply for each waste stream managed in the
unit in determining the time-weighted, annual average total organic
concentration of the waste. The time-weighted average shall be calculated using
the annual quantity of each waste stream processed and the mean organic
concentration of each waste stream managed in the unit;
(2) use of knowledge of the waste to
determine that its total organic concentration is less than 10 ppmw.
Documentation of the waste determination is required. Examples of documentation
that shall be used to support a determination under this provision include
production process information documenting that no organic compounds are used,
information that the waste is generated by a process that is identical to a
process at the same or another facility that has previously been demonstrated
by direct measurement to generate a waste stream having a total organic content
less than 10 ppmw, or prior speciation analysis results on the same waste
stream where it can also be documented that no process changes have occurred
since that analysis that could affect the waste total organic
concentration.
(e) The
determination that distillation, fractionation, thin- film evaporation, solvent
extraction, or air or steam stripping operations manage hazardous wastes with
time-weighted annual average total organic concentrations less than 10 ppmw
shall be made as follows:
(1) by the
effective date that the facility becomes subject to the provisions of this
article or by the date when the waste is first managed in a waste management
unit, whichever is later; and
(A) for
continuously generated waste, annually; or
(B) whenever there is a change in the waste
being managed or a change in the process that generates or treats the
waste.
(f) When
an owner or operator and the Department do not agree on whether a distillation,
fractionation, thin-film evaporation, solvent extraction, or air or steam
stripping operation manages a hazardous waste with organic concentrations of at
least 10 ppmw based on knowledge of the waste, the procedures in Method 8260 of
SW-846 (incorporated by reference under section
66260.11) shall be used to resolve
the dispute.