Current through Register Vol. 56, No. 24, December 18, 2024
(a) The
method in this section is applicable for the detection of fugitive VOC leaks.
Any alternative test method shall be submitted to the Department for review
pursuant to
N.J.A.C.
7:27B-3.2(c), (d) and
(e).
(b) This method is based upon the detection
of VOC leaks from individual sources by a portable instrument. The instrument
detector type is not specified but shall meet the performance criteria of (d)4
below. This procedure is intended to locate and classify leaks only and shall
not be used to measure mass emission rates from individual sources.
(c) The following is a summary of this
method:
1. The detector is calibrated with a
standard gas mixture to establish the response of the instrument. A
representative sample of fugitive emissions is drawn into the instrument. The
response is read directly from the instrument meter.
2. For purposes of this procedure a single
test shall be sufficient to establish the presence of a leak.
(d) The following is a list of
equipment used in this method:
1. Probe:
glass, stainless steel, or Teflon tubing as required by source gas conditions
and equipped with 0.4 inch (one centimeter) tip spacer;
2. Pump: a leakless Teflon-coated diaphragm
pump capable of maintaining an appropriate flow to the detector;
3. Dilutor: (if circumstances require)
capable of diluting the sample gas into the range of the instrument such that
concentration levels of 10,000 ppm can be measured. The dilutor tip shall be
equipped with a 0.4 inch (one centimeter) spacer;
4. Monitoring instrument, as set forth below:
i. The monitoring instrument shall be
certified as safe for operation in explosive atmospheres;
ii. The monitoring instrument detector shall
be capable of measuring the leak concentration specified in the appropriate
section in N.J.A.C. 7:27-16. Detector types which meet this requirement include
but are not limited to catalytic oxidation, flame ionization, infra-red
absorption, and photoionization; and
iii. The instrument shall be readable to
within five percent of the specified leak concentration and shall have a
response time less than or equal to of 30 seconds for 95 percent of
scale;
5. Standard
calibration gas--8,000 ppmv Hexane or Methane in air.
(e) The procedure for this section shall be
as follows:
1. A presampling survey shall be
conducted to locate components where potential leaks could occur;
2. Calibration shall be conducted as follows:
i. The instrument should be operated
according to the manufacturer's directions;
ii. Adjust the analyzer to zero by using
ambient air; and
iii. Introduce the
8,000 ppm calibration gas into the instrument sample probe. Adjust the
instrument meter readout and chart recorder to correspond to the calibration
value. If necessary, use a dilution system to bring the calibration gas into
the instrument range.
3.
Sampling and analyses shall be conducted as follows:
i. Place the instrument probe with the 0.4
inch (one centimeter) spacer at the surface of the component interface where
leakage is suspected. Move the probe along the interface periphery while
observing the instrument readout. If an increased meter reading is observed,
slowly probe the interface where leakage is indicated until the maximum meter
reading is obtained. Leave the probe at the maximum reading location for
approximately two times the instrument response time. If the concentration
reading is in excess of the range of the instrument, add the dilution assembly
and sample as above using a correction factor to convert the measurements to
the undiluted bases. Record the date, time and identity of the leaking
components. See Appendix F for the required reporting form. (Any alternative
form shall be submitted to the Department for review pursuant to
N.J.A.C.
7:27B-3.2(c) and
(e).)