Experimental
Materials
Commercially available starting materials were obtained from
Sigma-Aldrich Co. and used as received. Solvents were purchased
from Merck (HPLC grade) and used without further purification.
Water was purified with a Millipore system.
Continuous radiolysis
Solutions were freshly prepared by using water purified with a
Millipore (Milli-Q) system. Sample solutions (0.2 and 2 M) of
the compounds were saturated with N O prior to irradiation.
2
Continuous radiolyses were performed at room temperature (22 ±
∑
∑
◦
6
0
Scheme 5 Proposed mechanism for the reaction of HO /H with bu-
tane-2,3-diol (13). The compounds quantified by the 2,4-DNP procedures
2
C) on 250 mL samples using a Co-Gammacell, with dose
-1
rates ca. 6 Gy min . The absorbed radiation dose was determined
(
Fig. 4) are shown in red.
3+
with the Fricke chemical dosimeter, by taking G(Fe ) = 1.56 mmol
-
1 24
J . HPLC analyses were recorded on an Agilent 1100 Liquid
Chromatograph, equipped with a quaternary pump delivery
system, a column thermostat and a variable-wavelength detector.
position of the HO-group, and the remaining 29% from the methyl
site. In analogy with the ethane-1,2-diol case, we suggest that 71%
of the reducing species also partly result from hydrogen abstraction
from the OH site, because the fragmentation of 16 (oxidising
species) is fast enough in aqueous solution to compete with the
Quantification and identification of the carbonyl compounds
19
bimolecular oxidation of iodide ions.
The quantification of the carbonyl compounds was performed
via the corresponding 2,4-dinitrophenylhydrazone derivatives,
14
following a published protocol adapted to our case. 1 mL
of an irradiated sample was diluted with 500 mL 0.4% v/v
Conclusions
conc. H
3
PO (in 9 : 1, acetonitrile : water, v/v). 500 mL of 2,4-
4
The results of the experiments described herein emphasise the
extraordinary selectively of the enzymatic reactions catalysed by
diol dehydratase and the related enzymes glycerol dehydratase
dinitrophenylhydrazine (2,3-DNP) 40 mM in acetonitrile was
added and the resulting solution was vortexed for 12 h. Af-
ter derivatisation, the reaction mixture was diluted to 1 : 10
acetonitrile : water, (1 : 1, v/v) and 20 mL was injected for HPLC
and ribonucleotide reductase (coenzyme B12-dependent and B12
-
5
independent) acting on their substrate vicinal diols compared
to the chemical reactions of diols with hydroxyl radicals described
herein, despite similarities of mechanism. For the diol dehydratase-
catalysed reaction with propane-1,2-diol, selectivity with respect
to H atom abstraction is achieved by tight binding of the diol by
analysis using a GraceSmart RP 18 5 mm column (150 mm ¥
◦
4
.6 mm), at 30 C, with detection at l = 338 nm. Mobile phase A
was 0.1% trifluoroacetic acid in water and mobile phase B was 0.1%
trifluoroacetic acid in acetonitrile. The separation was obtained at
-
1
2
+
a flow rate of 1 mL min with a gradient program as follows:
0 min 40% B, followed by a 25 min step to increase eluent B
four amino acid residues aided by a Ca ion with the placement
1
of the 5¢-deoxyadenosyl radical close to a specific hydrogen at C-1
20
to 100%. Washing was carried out at 100% B and equilibration
at 40% B. Total time of analysis was 35 min. The identification
of the carbonyl compounds was performed by derivatisation of
commercially available compounds followed by HPLC analysis
and spike experiments.
of the diol. A special feature of the conversion of the substrate
7
to the product radical is a 1,2-hydroxyl shift that may occur by
a ‘push-pull’ mechanism via an oxirane-like species, which can
be qualitatively described as a complex of water with an alkene
4,5
radical cation. Our ongoing studies are exploring how far the
model chemistry and enzymatic chemistry correspond with respect
to the substrate radical to product radical conversion.
Acknowledgements
Some general considerations can be drawn from the radiation
chemistry of this study, which affords a deeper insight into the
reactivity of vicinal diols with radical species. The findings may
be relevant to the multiple uses of diols, such as the applications
of propane-1,2-diol, which are generally deemed safe, as a food
and pharmaceutical additive (E1520), anti-freeze component and
The support and sponsorship of COST Action CM0603 on
‘Free Radicals in Chemical Biology (CHEMBIORADICAL)’ are
gratefully acknowledged.
21
antiseptic substance. However, studies of ethanol-induced free
radical generation in animals have shown that the derived a-
hydroxyethyl radical and acetaldehyde may be responsible for
Notes and references
1
J. A. Berson, Angew. Chem., Int. Ed., 2002, 41, 4655.
2 Fine Chemicals through Heterogeneous Catalysis, ed. R. A. Sheldon and
22,23
DNA and protein damage.
The reaction mechanisms proposed
H. van Bekkum, Wiley-VCH Verlag, 2001, pp. 232–239.
R. H. Abeles, A. M. Brownstein and C. H. Randles, Biochim. Biophys.
Acta, 1960, 41, 531.
G. Speranza, W. Buckel and B. T. Golding, J. Porphyrins Phthalocya-
nines, 2004, 8, 290.
3
4
in the present work are intended to contribute to the scenario of
free radical-induced modifications of biological macromolecules
with multidisciplinary implications.
1
106 | Org. Biomol. Chem., 2012, 10, 1102–1107
This journal is © The Royal Society of Chemistry 2012