Scheme 1. Synthesis of tri-n-butyltin azide
The growing awareness of the environmental fate of
organic tin compounds has reflected in the large number of
analytical methods developed for their determination and
specification.10,11 Most methods are too complex to be carried
out routinely in a production plant (goal: determination of
the completion of the reaction).
Finally, detailed knowledge of the reaction kinetics, as
determined from continuous online measurements of reactant
and product concentrations, may help to improve the reaction
conditions and thus increases process safety.
3.1.2. Experimental Section. Tri-n-butyltin chloride was
charged at room temperature in a stirred reactor, and the
reaction system was inerted with nitrogen. Then, the contents
of the reactor was heated to 50 °C. After a first calibration
of the reaction calorimeter, sodium azide was added over 5
min. The reaction mixture was stirred during 21 h at the
same temperature. After a repeat calibration, the reaction
mass was cooled to 25 °C.
3.1.3. Results and Discussion. 3.1.3.1. Normalization of
Spectra. Reaction profiles constructed from normalized
spectra are less noisy. Therefore, trends are more easily
recognizable and interpretable after normalization of the
spectra. Normalizations can help correct fluctuations or
systematic increases or decreases in peak intensity due to
(i) variations in the amount, the composition, or the
morphology of solid, crystalline materials in the reaction
mixture; (ii) the temporary or permanent adherence of
crystals or other particles to the diamond or the sapphire
window of the probes; (iii) the temporary or permanent
formation of thin films on the diamond window of the FTIR
probe; or (iv) changes in the distance between the laser focal
point and the sapphire window of the Raman probe.
Useful peaks for spectra normalizations are peaks resulting
from solvent molecules or from functional groups which are
located far away from the reaction centers of the molecules
involved in the reaction. More general, any peak arising from
species or functional groups which do not undergo any
change in concentration or absolute mass and which can be
regarded as constant is suited for a normalization. Further-
more, the selected peak ideally should be of medium
intensity, i.e., still in the linear range, and located somewhere
in the center of the observed spectral region or close to a
region with significant changes or another region of particular
interest.
the measured wavenumbers and the functional groups was
determined from general spectroscopy books.1-3
3.1. Synthesis of Tri-n-butyltin Azide. 3.1.1. Introduc-
tion. The goal of this study was to evaluate the potential of
online spectroscopic tools for monitoring chemical processes
and detecting deviations from nominal operating conditions.
The literature-known synthesis of tri-n-butyltin azide from
tri-n-butyltin chloride and sodium azide (Scheme 1) was
studied as a model reaction.4
The principal industrial applications of trialkyltin com-
pounds include biocides in marine antifouling paints, fun-
gicides, herbicides, insecticides, miticides, and antifeedants
in agriculture. Tri-n-butyltin azide is of some importance as
a reagent for the preparation of pharmaceutical tetrazole
compounds.5-7 Online monitoring of such a heterogeneous
reaction system by spectroscopic methods may be advanta-
geous for various reasons.
The reaction of crystalline sodium azide with liquid tri-
n-butyltin chloride takes place at the solid-liquid interface
and is therefore very sensitive to changes of reaction
conditions or surface properties. Standard offline methods
may be used to monitor reaction progress; however, they
require repeated sample-taking and -handling during the
analytic process. These operations should be avoided due to
the high toxicity of the reaction mixture and also for reasons
of safety and ecology.
All compounds involved in this reaction have low
maximum allowed concentration (MAK) values. Organotin
compounds have a wide range of toxicity, the most toxic
being trialkyltins as evident from their broad spectrum of
application as biocides. They are capable of blocking the
oxidative phosphorylation in the mitochondria cell.8 Thus,
they influence the basic energetic functions in living cell
systems. Triorganotin compounds can react with active
centers in the cell by forming coordinating links with amino
acids of the cell proteins. Moreover, these compounds can
cause severe skin irritation.9 Further, azides are highly
poisonous and usually sensitive to traces of strong acids and
metallic salts which may catalyze explosive decomposition.
For example, the isolation of explosive silver azide must be
avoided during the offline titration of the unreacted tri-n-
butyltin chloride with silver nitrate.
The normalizations were carried out taking the region
1110.6-1221.1 cm-1 (τCH2 and ωCH2) for the Raman
spectra and the region 815-910 cm-1 (FCH2 an FCH3) for
the FTIR spectra, i.e., the spectra were stretched or com-
pressed so that the peak maxima and the baselines of all the
spectra attained maximum overlap in these regions.
3.1.3.2. Raman Data. The most important changes in the
Raman spectra are summarized hereafter (see Figures 1-3):
(1) Socrates, G. Infrared Characteristic Group Frequencies; Wiley: Chichester,
1994.
(2) Colthup, N. B.; Daly, L. H.; Wiberley, S. E. Introduction to Infrared and
Raman Spectroscopy; Academic Press: New York, 1975.
(3) Scheinmann, F. An Introduction to Spectroscopic Methods for the
Identification of Organic Compounds; Pergamon Press: Oxford, 1970.
(4) Kricheldorf, H. R.; Leppert, E. Synthesis 1976, 329-330.
(5) Kozima et al. J. Organomet. Chem. 1975, 92, 303, 305, 309.
(6) Sisido et al. J. Organomet. Chem. 1971, 33, 337, 343, 344.
(7) Duncia, J. V.; Pierce, M. E.; Santella, J. B. J. Org. Chem. 1991, 56, 2395-
2400.
(9) Schering, A. G. Organozinn-Verbindungen, Hinweise zur Toxikologie und
sicheren Handhabung 1985, Bergkamen.
(10) Attar, K. M. Appl. Organomet. Chem. 1996, 10, 317-337.
(11) Harrington, C. F.; Eigendorf, G. K.; Cullen, W. R. Appl. Organomet. Chem.
1996, 10, 339-362.
(8) Plum, H. Int. EnViron. Saf. 1982, December, 20-23.
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