deriving the intrinsic properties of this particular proton acceptor
also resides in the comparison with other proton acceptors, besides
water, which may not only exert a different driving force but are
chemically different so that one may expect different properties
at zero driving force in terms of reorganization energies and pre-
exponential factors. Among the various proton acceptors one may
think of, a particular mention should be made of nitrogen bases in
view of their ubiquitous role in natural processes. Their frequent
involvement in H-bonded structures is a favorable factor for the
occurrence of a CPET mechanism because the distance between
the proton and the base corresponding to an H-bond is about
the right distance for easy proton tunneling. As a representative
of the family of H-bonding nitrogen bases, we selected pyridine
as the proton acceptor for the present analysis of the kinetics of
photochemically triggered oxidation of phenol by RuIII(bpy)3.
Fig. 2 Variation of the pseudo-second order phenol oxidation rate
constant with temperature in 5 ¥ 10-5 M equimolar solutions of pyridine
and (H or D) pyridinium ion (see Experimental Section) at 20 ◦C, in
light (squares in a, pH = 5.4) and heavy (circles in b, pD = 5.7) water
compared with the variation of the pseudo-second order phenol oxidation
rate constant with temperature in the absence of pyridine at pH = 2 (upward
triangles in a) and pD = 2.4 (downward triangles in b).
Results and discussion
Two series of laser flash experiments (see Experimental Section)
were carried out. In the first series, the phenol oxidation second
order rate constant was measured at a fixed temperature, namely
20 ◦C, as a function of the pyridine concentration at a pH (or
pD) equal to the pK of pyridine both in light and heavy water
(Fig. 1). As expected, raising the pyridine concentration results,
after an initial plateau, in an increase of the pseudo-second order
rate constant. It would seem that the variations in D2O exhibit a
shallow dip before the final rise of the rate constant. However, the
scatter in the experimental data points (Dlog k = 0.2) is such that
it does not allow one to consider this feature as significant.
At small concentrations of pyridine where the contribution of
the Py-CPET pathway is deemed to be negligible, one expects that
the rate constant should equal the value found in pure water for
the water-CPET pathway, as for example the value found at pH
2. This is indeed the case with H2O (Fig. 2a), indicating that at a
pH equal to the pyridine pK in light water (5.2),4 the OH--PET
pathway is not operating just because OH- concentration is too
low. The situation is different in D2O (Fig. 2b) because the pyridine
pK is higher (5.7),4 opening a narrow but significant route for an
OD--PET pathway.
It is noted that this contribution increases upon going to lower
temperatures, in line with a parallel increase of the pK in D2O.4
It follows that the third-order rate constant for the Py-CPET
pathway may be extracted from the raw data shown in Fig. 3 using
eqn (1) in the case of H2O:
k = kHH
+ kPHy −CPET Py
[ ]
(1)
O−CPET
2
and eqn (2) in the case of D2O:
(2)
Fig. 1 Variation of the pseudo-second order phenol oxidation rate
constant with the concentration of pyridine in equimolar solutions of
pyridine and (H or D) pyridinium ion (see Experimental Section) at 20 ◦C,
in light (squares) and heavy (circles) water. The left-hand data points were
obtained in the absence of pyridine.
In another series of experiments, the temperature was varied at
fixed values of the pyridine concentration both in light and heavy
water (Fig. 2), at a pH (or pD) equal to the pK of pyridine both in
light and heavy water.
As with phosphate,3 the overall oxidation rate is the sum of three
contributions, corresponding respectively to a concerted pathway
in which the solvent, H2O or D2O, is the proton acceptor that
we name H2O (D2O)-CPET, a “PET” pathway (see Scheme 1) in
which OH- is the proton acceptor, and—the object of the present
study—a CPET pathway in which the purposely added base, here
pyridine, functions as the proton acceptor (Py-CPET pathway).
Fig. 3 Variation of the pseudo-second order phenol oxidation rate
constant with temperature in equimolar solutions of pyridine and (H or
D) pyridinium ion (see Experimental Section) at 20 ◦C, in light (squares)
and heavy (circles) water at fixed equal concentrations of pyridine and H-
or D-pyridinium cation (M): 2.5 ¥ 10-2 (a), 1.5 (b).
This journal is
The Royal Society of Chemistry 2011
Org. Biomol. Chem., 2011, 9, 4064–4069 | 4065
©