is placed in direct contact with the sample, light passing through
this at angles above a critical angle will be reflected at the sample
interface. In the process of reflection, an evanescent wave
penetrates the sample medium, giving rise to partial absorption
of the beam according to the vibrational frequencies of the sample.
The missing link, therefore, for in situ FT-IR analysis is a means
of transmitting the radiation between the spectrometer and the
internal reflection element. One option is the use of optical light
guides, hollow conduits internally coated with a reflecting material
such as nickel or gold.4 “Light pipes” have been used in
conjunction with ATR probes for reaction monitoring, but their
versatility is hampered by their rigid construction. Alternatively,
reaction vessels can be constructed with integral internal reflection
elements in dedicated spectrometer systems, but again, these are
somewhat restrictive.5
Figure 1. Acid-catalyzed reaction of but-2-enoic acid and butan-
2-ol, to give the corresponding ester, sec-butyl but-2-enoate.
Table 1. Spectroscopic Variables for the Fiber Probe
and Flow Cell Analysis
spectral spectral
range,
resoln, J-stop, B-stop,
throughput,
accessory
cm-1
cm-1
mm
mm gain %
fiber probe 4000-1000
flow cell 4000-700
4
4
11.00 15.00
11.00 8.00
2
1
∼13
∼48
Process development activity tends to involve the use of a wide
range of reactor designs and capacities, and to gain access to a
significant proportion of these reactors, a flexible approach to in
situ IR sampling is required, something that is now possible due
to recent developments in fiber-optic technology. In the simplest
terms, optical fibers are a medium for transmitting radiant power
and consist of a core and cladding. Radiation traveling in the core
is confined to the core by reflection with the cladding that has a
lower index of refraction. Fiber links are now commonplace for
applications in visible and near-IR spectroscopy, but their perfor-
mance decreases markedly in the mid-IR because the vast majority
of materials have fundamental absorptions in this region. This
problem is exacerbated by the low throughput of available fibers,
the inherently low energy of mid-IR sources, and the relative
insensitivity of mid-IR detectors. Recently, however, chalcogenide
fibers have become commercially available and are beginning to
be used in this context.
apparent IR activity, and minimal safety hazards.7 The reaction
scheme is given in Figure 1. A series of three separate reactions
was monitored using the fiber probe, and a further series of three
reactions was monitored using an overhead ATR flow cell with a
recirculating loop. Particular emphasis is given to the quantifica-
tion of the reaction product (sec-butyl but-2-enoate) and the
approach taken to improve its quantitative prediction with a
minimum of analytical development.
EXPERIMENTAL SECTION
Instrumentation. All spectra were recorded using a Perkin-
Elmer System 2000 spectrometer fitted with a liquid nitrogen-
cooled narrow band mercury-cadmium-telluride (MCT) detec-
tor. The spectrometer was operated in the infrared data manager
(IRDM) environment using the time-resolved facility (TRIR).
Spectra were stored as the mean of 64 co-added scans collected
at 10 min intervals and were ratioed against an air background
recorded immediately prior to analysis. The spectroscopic
variables used for the fiber probe and the flow cell are summarized
in Table 1.
Chalcogenide glasses are vitreous materials made from group
IV metals As, Ge, and Sb, together with the chalcogen elements
S, Se, and Te. Chalcogenide transmission is good over the range
4000-1000 cm-1, apart from lattice vibrations and absorption due
to hydrogen-containing impurities at 2250-2100 cm-1, although
high-attenuation characteristics have restricted their practical use
to lengths of 2 m. Nevertheless, 10 m chalcogenide fibers have
been reported6 for environmental analysis over a restricted spectral
range.
The cooled mid-IR fiber probe consisted of two single-strand
750 µm, 1.5 m chalcogenide fibers with a numerical aperture of
0.4, in conjunction with a two-reflection 45° ZnSe internal reflection
element (Figure 2a) and an adjustable optical interface for the
spectrometer (Figure 2b). The composition of the fiber-optic
material used was As0.4, Se0.2, Te0.4, with minimal losses of 0.001
dB m-1 at 6 µm. The glass transition temperature of this material
was 136 °C, although the fibers do change their transmission
characteristics at temperatures as low as 70 °C. The step index
fibers were polymer clad and armor plated with spirally wound
stainless steel, offering a bend radius of 15 cm. Larger diameter
fibers could have been employed, enabling greater utilization of
the available radiation, but this would have restricted the system
flexibility. The fiber was deliberately overfilled in both numerical
aperture and area, and a high-quality optical design was used to
image the radiation back to the fiber. The probe features an
integral internal water cooling system that maintains the fiber at
35 °C when the probe is immersed in a sample at 200 °C. Clearly,
this is a safe margin with respect to the 70 °C fiber transition
temperature. Cooling water was circulated via stainless steel
The analysis of elevated temperature reactions raises further
issues, however. Low glass transition temperatures, in combina-
tion with low softening temperature cladding materials, have
restricted the use of chalcogenide fibers to temperatures of ∼70
°C, thus rendering a significant proportion of typical process
development reactions inaccessible. To address this shortcoming,
a fully flexible fiber-optic probe heatable to temperatures up to
230 °C has recently been developed.
This paper describes the concept and construction of a novel
water-cooled mid-IR fiber probe and its use in the monitoring of
a laboratory-scale esterification reaction at 110 °C. The acid-
catalyzed reaction of but-2-enoic acid and butan-2-ol was selected
on account of its reaction temperature being greater than 70 °C,
(4) Doyle, W. M.; Jennings, N. A. Spectrosc. Int. 1 9 9 1 , 2, 48-52.
(5) Full, A. P.; Puig, J. E.; Gron, L. U.; Kaler, E. W.; Minter, J. R.; Mourey, T.
H.; Texter, J. Macromolecules 1 9 9 2 , 25, 5157-5164.
(6) Ewing, K. J.; Bilodeau, T.; Nau, G.; Aggarawal, I. D.; King, T.; Clark, R.;
Robitille, G. Air and Waste Management/ SPIE Conference Proceedings,
McLean, VA, November 1994.
(7) Harwood, L. M.; Moody, C. J. Experimental Organic Chemistry; Blackwell:
Oxford, 1989; pp 445-446.
Analytical Chemistry, Vol. 68, No. 7, April 1, 1996 1117