Laboratory Products
Investigating the Performance and Discussing the Suitability of FTIR for TOC Emissions Monitoring
Author: Marc Coleman,*1, Antti Heikkil?2, David Butterfield1 Dominic Duggan3 and Rod Robinson1
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Fourier transform infrared (FTIR) spectroscopy is
becoming increasingly used for emission monitoring
applications for a range of inorganic gases. However,
where TOC monitoring is also required generally a
flame ionisation detector (FID) is used. The standard
reference method (SRM) [2] is based on the use of
flame ionisation detection. Whilst there are no
technical issues in using FTIR and FID in tandem there
are the practicalities and cost of the transportation
and set-up of two analysers. Consequently, it would
be advantageous to be able to measure all the
required species by FTIR alone ? in addition, the FTIR
also has the advantage of providing speciation
information. Many UK VOC emissions are regulated
and fall under either the waste incineration directive
(WID) [3] or large combustion plant directive (LCPD)
[4]. Consequently, regulatory monitoring must be
carried out following the SRM or with an alternative
reference method (ARM) where equivalence to the
former has been demonstrated.
Towards assessing the suitability of FTIR for TOC
monitoring we have tested the performance of the
Gasmet DX4000 (distributed in the UK by Quantitech
Ltd) against that of a Sick Bernath FID for measuring
VOC compositions generated in NPL?s Stack Simulator
Facility. The FID is certified under MCERTS for TOC
measurements whilst the DX4000 FTIR is certified for a
range of inorganic gases (for example, NO, SO2, HCl)
but, at the time of writing this article, no VOC species.
Many performance parameters of the FTIR are well
characterised due to the original MCERTS testing,
for example, noise, drift and temperature sensitivity)
so for the purposes of this investigation need not
be repeated, consequently, we have focussed mainly
on responses to different VOC mixtures and
cross-sensitivities.
The Stack Simulator Facility developed at NPL was
used for the work so that testing was carried out
under real stack conditions. The facility has been
designed with a cross-stack pathlength of 1.5 m, four
5? BSP sample ports, 300 L capacity and is capable of
velocities and temperatures of up to 10 m.s-1 and 200
?C, respectively [5]. These specifications allow testing
of instruments [6] and procedures [7], and the
carrying out of proficiency testing schemes under real
sampling conditions. The approach of the testing was
to create test mixtures in the Stack Simulator based
on the performance requirements for a low range
(0 ? 20 mgC.m-3) TOC continuous emissions monitor
(CEM) as detailed under BS EN 15267-38.
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