(1) MATERIAL
DETERMINATION PROCEDURE TO DETERMINE AVERAGE VOLATILE ORGANIC (VO)
CONCENTRATION OF A HAZARDOUS SECONDARY MATERIAL AT THE POINT OF MATERIAL
ORIGINATION.
(a)
Determining average
VO concentration at the point of material origination.A remanufacturer
or other person that stores or treats the hazardous secondary material shall
determine the average VO concentration at the point of material origination for
each hazardous secondary material placed in a hazardous secondary material
management unit exempted under the provisions of s.
NR 661.1082(3) from using air emission
controls in accordance with standards specified in ss.
NR 661.1084 to 661.1087, as applicable to the hazardous secondary material management unit.
The remanufacturer or other person that stores or treats the hazardous
secondary material shall make the determinations according to all of the
following:
1. Make an initial determination
of the average VO concentration of the material stream before the first time
any portion of the material in the hazardous secondary material stream is
placed in a hazardous secondary material management unit exempted under the
provisions of s.
NR 661.1082(3) from using air emission
controls, and thereafter make an initial determination of the average VO
concentration of the material stream for each averaging period that a hazardous
secondary material is managed in the unit.
2. Perform a new material determination
whenever changes to the source generating the material stream are reasonably
likely to cause the average VO concentration of the hazardous secondary
material to increase to a level that is equal to or greater than the applicable
VO concentration limits specified in s.
NR 661.1082.
(b)
Determination of average VO
concentration using direct measurement or knowledge. For a material
determination that is required under par. (a), the average VO concentration of
a hazardous secondary material at the point of material origination shall be
determined using either direct measurement as specified in par. (c) or by
knowledge as specified in par. (d).
(c)
Direct measurement to determine
average VO concentration of a hazardous secondary material at the point of
material origination.
1.
`Identification.' The remanufacturer or other person that stores or treats the
hazardous secondary material shall identify and record in a log that is kept at
the facility the point of material origination for the hazardous secondary
material.
2. `Sampling.' Samples of
the hazardous secondary material stream shall be collected at the point of
material origination in a manner such that volatilization of organics contained
in the material and in the subsequent sample is minimized and an adequately
representative sample is collected and maintained for analysis by the selected
method. The remanufacturer or other person that samples the hazardous secondary
material shall sample according to all of the following:
a. The averaging period to be used for
determining the average VO concentration for the hazardous secondary material
stream on a mass-weighted average basis shall be designated and recorded. The
averaging period can represent any time interval that the remanufacturer or
other person that stores or treats the hazardous secondary material determines
is appropriate for the hazardous secondary material stream but may not exceed
one year.
b. A sufficient number of
samples, but no less than 4 samples, shall be collected and analyzed for a
hazardous secondary material determination. All of the samples for a given
material determination shall be collected within a one-hour period. The average
of the 4 or more sample results constitutes a material determination for the
material stream. One or more material determinations may be required to
represent the complete range of material compositions and quantities that occur
during the entire averaging period due to normal variations in the operating
conditions for the source or process generating the hazardous secondary
material stream. Examples of such normal variations are seasonal variations in
material quantity or fluctuations in ambient temperature.
c. All samples shall be collected and handled
in accordance with written procedures prepared by the remanufacturer or other
person that stores or treats the hazardous secondary material and documented in
a site sampling plan. This plan shall describe the procedure by which
representative samples of the hazardous secondary material stream are collected
such that a minimum loss of organics occurs throughout the sample collection
and handling process, and by which sample integrity is maintained. A copy of
the written sampling plan shall be maintained at the facility. An example of
acceptable sample collection and handling procedures for a total volatile
organic constituent concentration may be found in Method 25D in appendix A of
40 CFR part 60, incorporated by reference in s.
NR 660.11.
d.
Sufficient information, as specified in the site sampling plan required under
subd. 2. c., shall be prepared and recorded to document the material quantity
represented by the samples and, as applicable, the operating conditions for the
source or process generating the hazardous secondary material represented by
the samples.
3.
`Analysis.' Each collected sample shall be prepared and analyzed in accordance
with Method 25D in appendix A of 40 CFR part 60, incorporated by reference in
s.
NR 660.11, for the total concentration of volatile
organic constituents, or using one or more methods when the individual organic
compound concentrations are identified and summed and the summed material
concentration accounts for and reflects all organic compounds in the material
with Henry's law constant values at least 0.1
mole-fraction-in-the-gas-phase/mole-fraction-in-the-liquid-phase (0.1 Y/X),
which can also be expressed as 1.8 x 10 -6 atmospheres/gram-mole/m 3, at
25°C. At the discretion of the remanufacturer or other person that stores
or treats the hazardous secondary material, the test data obtained may be
adjusted by any appropriate method to discount any contribution to the total
volatile organic concentration that is a result of including a compound with a
Henry's law constant value of less than 0.1 Y/X at 25°C. To adjust these
data, the measured concentration of each individual chemical constituent
contained in the material is multiplied by the appropriate constituent-specific
adjustment factor (f m25D). If the remanufacturer or other person that stores
or treats the hazardous secondary material elects to adjust the test data, the
adjustment shall be made to all individual chemical constituents with a Henry's
law constant value greater than or equal to 0.1 Y/X at 25°C contained in
the material. Constituent-specific adjustment factors (f m25D) can be obtained
by contacting the Waste and Chemical Processes Group, Office of Air Quality
Planning and Standards, Research Triangle Park, NC 27711. Other test methods
may be used if they meet the requirements specified in subd. 3. a. or b. and
provided the requirement to reflect all organic compounds in the material with
Henry's law constant values greater than or equal to 0.1 Y/X, which can also be
expressed as 1.8 x 10 -6atmospheres/gram-mole/m 3 at 25°C, is met.
a. Any EPA standard method that has been
validated in accordance with "Alternative Validation Procedure for EPA Waste
and Wastewater Methods," appendix D of 40 CFR part 63, incorporated by
reference in s.
NR 660.11.
b.
Any other analysis method that has been validated in accordance with the
procedures specified in Section 5.1 or Section 5.3, and the corresponding
calculations in Section 6.1 or Section 6.3 of Method 301 in appendix A of 40
CFR part 63, incorporated by reference in s.
NR 660.11. The data are acceptable if they meet the
criteria specified in Section 6.1.5 or Section 6.3.3 of Method 301. If
correction is required under Section 6.3.3 of Method 301, the data are
acceptable if the correction factor is within the range 0.7 to 1.30. Other
sections of Method 301 are not required.
4. `Calculations.'
a. The average VO concentration (C) on a
mass-weighted basis shall be calculated by using the results for all material
determinations conducted in accordance with subds. 2. and 3. and the following
equation:
Where:
See PDF for
diagram
C = Average VO concentration of the hazardous secondary
material at the point of material origination on a mass-weighted basis,
ppmw.
i = Individual material determination "i" of the hazardous
secondary material.
n = Total number of material determinations of the
hazardous secondary material conducted for the averaging period (not to exceed
1 year).
Qi = Mass quantity of hazardous
secondary material stream represented by C i, kg/hr.
QT = Total mass quantity of
hazardous secondary material during the averaging period, kg/hr.
Ci = Measured VO concentration of
material determination "i" as determined in accordance with the requirements
specified in subd. 3., which is the average of the 4 or more samples specified
in subd. 2. b., ppmw.
b. For
the purpose of determining C i, for individual material samples analyzed in
accordance with subd. 3., the remanufacturer or other person that stores or
treats the hazardous secondary material shall account for VO concentrations
determined to be below the limit of detection of the analytical method by using
the following VO concentration:
1) If Method
25D in appendix A of 40 CFR part 60, incorporated by reference in s.
NR 660.11, is used for the analysis, one-half the blank
value determined in the method at Section 4.4 of Method 25D in appendix A of 40
CFR part 60.
2) If any other
analytical method is used, one-half the sum of the limits of detection
established for each organic constituent in the material that has a Henry's law
constant values at least 0.1
mole-fraction-in-the-gas-phase/mole-fraction-in-the-liquid-phase (0.1 Y/X),
which can also be expressed as 1.8 x 10 - 6atmospheres/gram-mole/m 3, at
25°C.
(d)
Use of knowledge by the
remanufacturer or other person that stores or treats the hazardous secondary
material to determine average VO concentration of a hazardous secondary
material at the point of material origination.
1. The remanufacturer or other person that
stores or treats the hazardous secondary material shall prepare documentation
that presents the information used as the basis for the knowledge of the
hazardous secondary material stream's average VO concentration. Examples of
information that may be used as the basis for knowledge include material
balances for the source or process generating the hazardous secondary material
stream; constituent-specific chemical test data for the hazardous secondary
material stream from previous testing that are still applicable to the current
material stream; previous test data for other locations managing the same type
of material stream; or other knowledge based on information included in
shipping papers or material certification notices.
2. If test data are used as the basis for
knowledge, then the remanufacturer or other person that stores or treats the
hazardous secondary material shall document the test method, sampling protocol,
and the means by which sampling variability and analytical variability are
accounted for in the determination of the average VO concentration. For
example, a remanufacturer or other person that stores or treats the hazardous
secondary material may use organic concentration test data for the hazardous
secondary material stream that are validated in accordance with Method 301 in
appendix A of 40 CFR part 63, incorporated by reference in s.
NR 660.11, as the basis for knowledge of the
waste.
3. A remanufacturer or other
person that stores or treats the hazardous secondary material using chemical
constituent-specific concentration test data as the basis for knowledge of the
hazardous secondary material may adjust the test data to the corresponding
average VO concentration value that would have been obtained had the material
samples been analyzed using Method 25D in appendix A of 40 CFR part 60,
incorporated by reference in s.
NR 660.11. To adjust these data, the measured
concentration for each individual chemical constituent contained in the
material is multiplied by the appropriate constituent-specific adjustment
factor (f m25D).
4. In the event
that the department and the remanufacturer or other person that stores or
treats the hazardous secondary material disagree on a determination of the
average VO concentration for a hazardous secondary material stream using
knowledge, then the results from a determination of average VO concentration
using direct measurement as specified in par. (c) shall be used to establish
compliance with the applicable requirements of this subchapter. The department
may perform or request that the remanufacturer or other person that stores or
treats the hazardous secondary material perform this determination using direct
measurement. The remanufacturer or other person that stores or treats the
hazardous secondary material may choose one or more appropriate methods to
analyze each collected sample in accordance with the requirements specified in
par. (c) 3.
(3)
PROCEDURE TO DETERMINE THE MAXIMUM ORGANIC VAPOR PRESSURE OF A HAZARDOUS
SECONDARY MATERIAL IN A TANK.
(a) A
remanufacturer or other person that stores or treats hazardous secondary
material shall determine the maximum organic vapor pressure for each hazardous
secondary material placed in a tank using Tank Level 1 controls in accordance
with standards specified in s.
NR 661.1084(3).
(b) A remanufacturer or other person that
stores or treats hazardous secondary material shall use either direct
measurement as specified in par. (c) or knowledge of the waste as specified in
par. (d) to determine the maximum organic vapor pressure that is representative
of the hazardous secondary material composition stored or treated in the
tank.
(c) Direct measurement to
determine the maximum organic vapor pressure of a hazardous secondary material
shall be conducted using all of the following procedures:
1. A sufficient number of samples shall be
collected to be representative of the hazardous secondary material contained in
the tank. All samples shall be collected and handled in accordance with written
procedures prepared by the remanufacturer or other person that stores or treats
the hazardous secondary material and documented in a site sampling plan. This
plan shall describe the procedure by which representative samples of the
hazardous secondary material are collected such that a minimum loss of organics
occurs throughout the sample collection and handling process and by which
sample integrity is maintained. A copy of the written sampling plan shall be
maintained at the facility. An example of acceptable sample collection and
handling procedures may be found in Method 25D in appendix A of 40 CFR part 60,
incorporated by reference in s.
NR 660.11.
2.
Any appropriate one of the following methods may be used to analyze the samples
and compute the maximum organic vapor pressure of the hazardous secondary
material:
a. Method 25E in appendix A of 40
CFR part 60, incorporated by reference in s.
NR 660.11.
b.
Methods described in American Petroleum Institute Publication 2517, Third
Edition, February 1989, "Evaporative Loss from External Floating-Roof Tanks,"
incorporated by reference in s.
NR 660.11.
c.
Methods obtained from standard reference texts.
d. ASTM Method 2879-92, incorporated by
reference in s.
NR 660.11.
e.
Any other method approved by the department.
(d) A remanufacturer or other person that
stores or treats hazardous secondary material may use knowledge to determine
the maximum organic vapor pressure of the hazardous secondary material.
Documentation shall be prepared and recorded that presents the information used
as the basis for the knowledge by the remanufacturer or other person that
stores or treats the hazardous secondary material that the maximum organic
vapor pressure of the hazardous secondary material is less than the maximum
vapor pressure limit specified in s.
NR 661.1084(2) (a)
1. for the applicable tank design capacity
category. An example of information that may be used is documentation that the
hazardous secondary material is generated by a process for which at other
locations it previously has been determined by direct measurement that the
hazardous secondary material's waste maximum organic vapor pressure is less
than the maximum vapor pressure limit for the appropriate tank design capacity
category.
(4) PROCEDURE
FOR DETERMINING NO DETECTABLE ORGANIC EMISSIONS FOR THE PURPOSE OF COMPLYING
WITH THIS SUBCHAPTER.
(a) A remanufacturer or
other person that stores or treats hazardous secondary material shall conduct a
test to determine no detectable organic emissions for the purpose of complying
with this chapter in accordance with the procedures specified in Method 21 in
appendix A of 40 CFR part 60, incorporated by reference in s.
NR 660.11. Each potential leak interface, a location
where organic vapor leakage could occur, on the cover and associated closure
devices shall be checked. Potential leak interfaces that are associated with
covers and closure devices include the interface of the cover and its
foundation mounting, the periphery of any opening on the cover and its
associated closure device, and the sealing seat interface on a spring-loaded
pressure relief valve.
(b) The test
shall be performed when the unit contains a hazardous secondary material having
an organic concentration representative of the range of concentrations for the
hazardous secondary material expected to be managed in the unit. During the
test, the cover and closure devices shall be secured in the closed
position.
(c) The detection
instrument shall meet the performance criteria of Method 21 in appendix A of 40
CFR part 60, incorporated by reference in s.
NR 660.11, except the instrument response factor criteria
in Section 3.1.2(a) of Method 21 shall be for the average composition of the
organic constituents in the hazardous secondary material placed in the
hazardous secondary management unit, not for each individual organic
constituent.
(d) The detection
instrument shall be calibrated before use on each day of its use by the
procedures specified in Method 21 in appendix A of 40 CFR part 60, incorporated
by reference in s.
NR 660.11.
(e) Calibration gases shall be all of the
following:
1. Zero air that is less than 10
ppmv hydrocarbon in air.
2. A
mixture of methane or n-hexane and air at a concentration of approximately, but
less than, 10,000 ppmv methane or n-hexane.
(f) The background level shall be determined
according to the procedures in Method 21 in appendix A of 40 CFR part 60,
incorporated by reference in s.
NR 660.11.
(g) Each potential leak interface shall be
checked by traversing the instrument probe around the potential leak interface
as close to the interface as possible, as described in Method 21 in appendix A
of 40 CFR part 60, incorporated by reference in s.
NR 660.11. In the case when the configuration of the
cover or closure device prevents a complete traverse of the interface, all
accessible portions of the interface shall be sampled. In the case when the
configuration of the closure device prevents any sampling at the interface and
the device is equipped with an enclosed extension or horn, such as some
pressure relief devices, the instrument probe inlet shall be placed at
approximately the center of the exhaust area to the atmosphere.
(h) The arithmetic difference between the
maximum organic concentration indicated by the instrument and the background
level shall be compared with the value of 500 ppmv except when monitoring a
seal around a rotating shaft that passes through a cover opening, in which case
the comparison shall be as specified in par.
(i). If the difference is less than 500 ppmv,
then the potential leak interface is determined to operate with no detectable
organic emissions.
(i) For the
seals around a rotating shaft that passes through a cover opening, the
arithmetic difference between the maximum organic concentration indicated by
the instrument and the background level shall be compared with the value of
10,000 ppmw. If the difference is less than 10,000 ppmw, then the potential
leak interface is determined to operate with no detectable organic
emissions.