35 Ill. Adm. Code 218.APPENDIX G
G TRE Index Measurements for SOCMI Reactors and Distillation Units
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE B: AIR POLLUTION
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: EMISSIONS STANDARDS AND LIMITATIONS FOR STATIONARY SOURCES
PART 218 ORGANIC MATERIAL EMISSION STANDARDS AND LIMITATIONS FOR THE CHICAGO AREA
SECTION 218.APPENDIX G TRE INDEX MEASUREMENTS FOR SOCMI REACTORS AND DISTILLATION UNITS
Section 218.APPENDIX G TRE
Index Measurements for SOCMI Reactors and Distillation Units
For purposes of Subpart Q,
Sections 218.431 through 218.435, the following apply:
a) The following test methods shall be used to determine
compliance with the total resource effectiveness ("TRE") index value:
1) Method 1 or 1A, incorporated by reference at Section 218.112
of this Part, as appropriate, for selection of the sampling site.
A) The sampling site for the vent stream molar composition
determination and flow rate prescribed in subsections (a)(2) and (a)(3) of this
Appendix shall be, except for the situations outlined in subsection (a)(1)(B),
after the final recovery device, if a recovery system is present, prior to the
inlet of any control device, and prior to any post-reactor or post-distillation
unit introduction of halogenated compounds into the vent stream. No traverse
site selection method is needed for vents smaller than 10 cm in diameter.
B) If any gas stream other than the reactor or distillation unit
vent stream is normally conducted through the final recovery device:
i) The sampling site for vent stream flow rate and molar
composition shall be prior to the final recovery device and prior to the point
at which any nonreactor or nondistillation unit vent stream or stream from a
nonaffected reactor or distillation unit is introduced. Method 18 incorporated
by reference at Section 218.112 of this Part, shall be used to measure organic
compound concentrations at this site.
ii) The efficiency of the final recovery device is determined by
measuring the organic compound concentrations using Method 18, incorporated by
reference at Section 218.112 of this Part, at the inlet to the final recovery
device after the introduction of all vent streams and at the outlet of the
final recovery device.
iii) The efficiency of the final recovery device determined
according to subsection (a)(1)(B)(ii) of this Appendix shall be applied to the
organic compound concentrations measured according to subsection (a)(1)(B)(i)
of this Appendix to determine the concentrations of organic compounds from the
final recovery device attributable to the reactor or distillation unit vent
stream. The resulting organic compound concentrations are then used to perform
the calculations outlined in subsection (a)(4) of this Appendix.
2) The molar composition of the vent stream shall be determined
as follows:
A) Method 18, incorporated by reference at Section 218.112 of this
Part, to measure the concentration of organic compounds including those
containing halogens;
B) ASTM D1946-77, incorporated by reference at Section 218.112 of
this Part, to measure the concentration of carbon monoxide and hydrogen; and
C) Method 4, incorporated by reference at Section 218.112 of this
Part, to measure the content of water vapor.
3) The volumetric flow rate shall be determined using Method 2,
2A, 2C, or 2D, incorporated by reference at Section 218.112 of this Part, as
appropriate.
4) The emission rate of VOM (minus methane and ethane) (E[VOM])
in the vent stream shall be calculated using the following formula:
where:
E
VOM
=
Emission rate of VOM (minus
methane and ethane) in the sample, kg/hr.
K
2
=
Constant, 2.494 x 10
-6
(l/ppmv) (g-mole/scm) (kg/g) (min/hr), where standard temperature for
(g-mole/scm) is 20° C.
C
j
=
Concentration of compound j,
on a dry basis, in ppmv as measured by Method 18 incorporated by reference at
218.112 of this Part, as indicated in Section 218.433(c)(3) of this Part.
M
j
=
Molecular weight of sample j,
g/g-mole.
Q
s
=
Vent stream flow rate (scm) at
a temperature of 20° C.
5) The total vent stream concentration (by volume) of compounds
containing halogens (ppmv, by compound) shall be summed from the individual
concentrations of compounds containing halogens which were measured by Method
18, incorporated by reference at Section 218.112 of this Part.
6) The net heating value of the vent stream shall be calculated
using the following:
where:
H
T
=
Net heating value of the
sample (MJ/scm), where the net enthaply per mole of vent stream is based on
combustion of 25°C and 760 mmHG, but the standard temperature for determining
the volume corresponding to one mole is 20ºC, as in the definition of Q
s
(vent stream flow rate).
K
1
=
Constant, 1.740 x 10
-7
(ppmv)
-1
(g-mole/scm), (MJ/KCal), where standard temperature for (g-mole/scm) is 20°C.
B
ws
=
Water vapor
content of the vent stream, proportion by volume; except that if the vent
stream passes through a final stream jet and is not condensed, it shall be
assumed that B
ws
= 0.023 in order to correct to 2.3 percent
moisture.
C
j
=
Concentration on a dry basis
of compound j in ppmv, as measured for all organic compounds by Method 18,
incorporated by reference at Section 218.112 of this Part, and measured for
hydrogen and carbon monoxide by using ASTM D1946-77, incorporated by
reference at Section 218.112 of this Part.
H
j
=
Net heat of combustion of
compound j, kCal/g-mole, based on combustion at 25ºC and 760 mmHG. The heats
of combustion of vent stream components shall be determined using ASTM
D2382-83, incorporated by reference at Section 218.112 of this Part, if
published values are not available or cannot be calculated.
b)
1) The TRE index value of the vent shall be calculated using the
following:
where:
TRE
=
TRE index value.
E
VOM
=
Hourly emission rate of VOM
(kg/hr) as calculated in subsection (a)(4) of this Appendix.
Q
s
=
Vent stream flow rate scm/min
at a standard temperature of 20°C.
H
T
=
Vent stream net heating value
(MJ/scm), as calculated in subsection (a)(6) of this Appendix.
E
VOM
=
Hourly emission rate of VOM
(minus methane and ethane), (kg/hr) as calculated in subsection (a)(4) of
this Appendix.
a,b,c,d
=
Value of coefficients presented
below are:
Value of
Coefficients
Type of Stream
Control Device Basis
a
b
c
d
Nonhalogenated
Flare
2.129
0.183
-0.005
0.359
Thermal incinerator zero (0) Percent heat Recovery
3.075
0.021
-0.037
0.018
Thermal incinerator 70 Percent heat Recovery
3.803
0.032
-0.042
0.007
Halogenated
Thermal incinerator and scrubber
5.470
0.181
-0.040
0.004
2) Every owner or operator of a vent stream shall use the
applicable coefficients identified for values a, b, c, and d in subsection
(b)(1) of this Appendix to calculate the TRE index value based on a flare, a
thermal incinerator with zero (0) percent heat recovery, and a thermal
incinerator with 70 percent heat recovery, and shall select the lowest TRE
index value.
3) Every owner or operator of a reactor or distillation unit with
a halogenated vent stream, determined as any stream with a total concentration
of halogen atoms contained in organic compounds of 200 ppmv or greater, shall
use the applicable coefficients identified for values a, b, c and d in
subsection (b)(1) of this Appendix to calculate the TRE index value based on a
thermal incinerator and scrubber.
c) Every owner or operator of a source seeking to comply with
Section 218.432(b) of this Part shall recalculate the flow rate and VOM
concentration for each affected vent stream whenever process changes are made.
Examples of process changes include, but are not limited to, changes in
production capacity, feedstock type, or catalyst type, or whenever there is
replacement, removal, or addition of recovery equipment. The flow rate and VOM
concentration shall be recalculated based on test data, or on best engineering
estimates of the effects of the change to the recovery system.
d) Whenever a process change, as defined in Section 218.435(c) of
this Subpart, yields a TRE index value of 1.0 or less, the owner or operator
shall notify and submit a report to the Agency according to the requirements
specified in Section 218.435(c) of this Subpart, within 180 calendar days after
the process change and shall conduct a performance test according to the
methods and procedures required by Section 218.433 of this Part.
e) For the purpose of demonstrating that a process vent stream
has a VOM concentration below 500 ppmv, the following shall be used:
1) The sampling site shall be selected as specified in Section
218.433(c)(1) of this Part.
2) Method 18 or Method 25A of 40 CFR Part 60, Appendix A,
incorporated by reference at Section 218.112 of this Part, shall be used to
measure concentration; alternatively, any other method or data that has been
validated according to the protocol in Method 301 of 40 CFR Part 63, Appendix
A, incorporated by reference at Section 218.112 of this Part, may be used.
3) Where Method 18 is used, the following procedures shall be
used to calculate ppmv concentration:
i) The minimum sampling time for each run shall be 1 hour in
which either an integrated sample or four grab samples shall be taken. If grab
sampling is used, then the samples shall be taken at approximately equal
intervals in time, such as 15 minute intervals during the run.
ii) The concentration of VOM shall be calculated using Method 18
according to Section 218.433(c)(4) of this Part.
4) Where Method 25A is used, the following procedures shall be
used to calculate ppmv VOM concentration:
i) Method 25A shall be used only if a single VOM is greater than
50 percent of total VOM, by volume, in the process vent stream.
ii) The vent stream composition may be determined by either
process knowledge, test data collected using an appropriate Reference Method or
a method of data collection validated according to the protocol in Method 301
of 40 CFR Part 63, Appendix A, incorporated by reference at Section 218.112 of
this Part. Examples of information that constitute process knowledge include
calculations based on material balances, process stoichiometry, or previous
test results provided the results are still relevant to the current process
vent stream conditions.
iii) The VOM used as the calibration gas for Method 25A shall be
the single VOM present at greater than 50 percent of the total VOM by volume.
iv) The span value for Method 25A shall be 50 ppmv.
v) Use of Method 25A is acceptable if the response from the
high-level calibration gas is at least 20 times the standard deviation of the
response from the zero calibration gas when the instrument is zeroed on the
most sensitive scale.
vi) The concentration of VOM shall be corrected to 3 percent
oxygen using the procedures and equation in Section 218.433(c)(3) of this Part.
5) The owner or operator shall demonstrate that the concentration
of VOM, including methane and ethane, measured by Method 25A is below 250 ppmv
to qualify for the low concentration exclusion in Section 218.431 of this Part.