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EPH and VPH now used in
Massachusetts, Connecticut and
Maine
AAI passed the complete full initial
quality assurance trial of the original EPH/VPH methodology established
and provided by the Massachusetts DEP. Since that time EPH and VPH
has undergone changes and Massachusetts has allowed labs to modify the
procedures to a more performance based methodology. Most recently AAI
has modified the method to use Gas Chromatography and Mass Spectrometry
to more accurately and specifically identify and quantitate the target
analytes for both methods.
The EPH method is based on a solvent
extraction, silica gel solid phase extraction - fractionation
process and combined gas Chromatography/Mass Spectrometry (GC/MS)
analysis. Unlike other GC/FID procedures, the GC/MS method is not
subject to 'false positive' bias in reporting the target analytes in the
PAH fraction. In this fraction, without the advantage of Mass
Spectrometry regular hydrocarbons may give false positives in this
portion of the test. This is a significant factor since the target
analytes are the most hazardous part of the contamination that is being
evaluated.
VPH analysis is based on a purge-and-trap
gas chromatography (GC) procedure using Photo Ionization and Flame
Ionization detectors (PID/FID). The VPH method is designed to
measure the collective concentrations of aliphatic and aromatic
petroleum hydrocarbons. As in the case with EPH, by producing
discrete data, the VPH method also provides for the measurement of
individual VPH target analytes, Benzene, Toluene, Ethyl benzene, Xylenes
(BTEX) , as well as Methyl-tert-butyl ether and Naphthalene. GC/MS
for this part of the analyses gives AAI the ability to identify Benzene, MTBE,
Naphthalene etc. with the highest level of certainty, so that you
can advise your client or the regulators about the significance of the
results that AAI produce. If you have no choice except to use
PID and FID, please let AAI know in advance since we need to schedule
the PID/FID instrument.
EDB Analysis
GC/MS
Historically, ethylene dibromide (EDB)
has been used as a lead scavenger in gasoline and aviation fuel.
Characterized as a probable human carcinogen, US EPA has set a Maximum
Containment (MCL) level of 0.05 parts per billion (ppb) in drinking
water. To provide our clients with reporting limits below the
EPA's enforced MCL of 0.05 ppb AAI analyzes samples for the
presence of EDB by a modified US EPA Method 8260B in SIM mode.
This allows for the detection limit of EDB with increased sensitivity,
because in SIM mode the MS gathers data for only the masses of interest
rather than looking for all masses over a wide range. With this method
AAI can achieve a quantitation level as low 4.0 parts per trillion(ppt)
This is more than ten times lower than the MCL and allows for samples to
be diluted while still maintaining reporting limit integrity.
10/20/2009 12:19
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