(water + organic reactants and products). Thus, water may
not actually be a real “solvent” for this reaction, and the re-
action does not take place “in” but rather on water. This is
widely unregarded in publications about Suzuki coupling in
water or water-containing solvent mixtures; it seems to be
assumed that at least some small part of the reactant is
somehow dissolved in water and will react. In this work,
such reactions will nevertheless be regarded as reactions “in
water” or “with water as the only solvent”, to avoid confu-
sion among many different terms.
The biphasic nature of such Suzuki reaction mixtures
raises the question as to whether the actual reaction mainly
takes place in the water phase, the organic phase, or at the
phase boundary. Qualitative arguments in favor and against
any of these cases can be thought of (Table 1). The answer
The locality of the reaction also has a strong impact on
possible ways to develop and optimize catalytic systems and
reaction conditions for higher activity and efficiency in reac-
tions in pure water. All of these considerations may also
apply to aqueous solvent mixtures (water/alcohols), which
have also been widely applied for the Suzuki reaction, and
also give biphasic reaction mixtures. Nevertheless, the focus
of this work is on the use of only water.
Although there is a vast amount of available publications
on the Suzuki reaction in (pure) water, the biphasic nature
of the reaction mixture and the question of the reactionꢃs lo-
cality are widely unregarded, and a clear answer is still miss-
ing. Mostly, Pd complexes as the homogeneous catalyst have
been tailored to be water-compatible (i.e., soluble) for
higher activity.[6,8–10] Some Pd complexes have been found to
decompose under the reaction conditions, which
has been observed also for very stable precur-
Table 1. Factors affecting the locality of the catalytic process of Suzuki coupling in bi-
phasic reaction mixtures (water/organic reactants).
sors,[11,12] thereby generating the actual catalytically
active free Pd0 species, which is likely to be trans-
ferred into the organic layer for the major part. In
other words, a water-soluble precatalyst does not
necessarily lead to the active species also being dis-
solved in the water phase. This is practically never
considered in the mentioned cases. Because of bind-
ing Pd0 very strongly and therefore being part of
the active species, P ligands can be regarded as a
typical exception for this phenomenon (under mild
reaction conditions). In some work, low reaction
rates have, however, been observed for hydropho-
bic reactants in comparison to comparable hydro-
philic substrates.[13] To overcome the miscibility
“problem” detergents and co-solvents have been
Phase
water
Present species
Favorable
Unfavorable
base, phenyl
boronate, salts,
ionic Pd species
presence of boronate,
stabilization of ionic
species including saline
side products
low/no availability
of reactant,
decomposition
reactions
organic
reactant, product,
neutral and ionic
Pd species, free
excess of reactant,
no/weak solvation
of ionic species
“clustering” of
ionic species
phenyl boronic acid
phase
boundary
all
availability of
all components
diffusion limitations,
constricted mobility
as to where the reaction takes place has important conse-
quences. If the reaction takes place in the organic layer, the
reactant is the “solvent”, which influences all the manifold
and intricate processes occurring during C–C coupling catal-
ysis (side reactions, solvation of intermediates, deactivation
of Pd through agglomeration, and many more). The delicate
interplay of these processes may significantly be changed
when going from one substrate to another chemically differ-
ent substance. Moreover, the reactant “solvent” is consumed
and replaced by the (also chemically different) product as
“solvent”, having similar consequences.
On the other hand, if the reaction takes place in water,
the aqueous phase can be reused after removing the hydro-
phobic products and adding new reagents, at least until the
cumulated amount of saline side products in the water
phase stalls the catalytic activity. The products would then
also contain no or only very low amounts of Pd, making fur-
ther time- and material-consuming purification processes
unnecessary, such as, for example, for pharmaceutical prod-
ucts, the heavy metal contents of which must meet very low
law-enforced restrictions.[6] If the reaction takes place in
water, however, this also implies that the reaction rate is
limited by the low concentration of the hydrophobic reac-
tant in the aqueous layer, which has been observed in some
cases in the literature (see below).
used,[14] as well as Pd complexes or particles in conjunction
with amphiphilic, micellar polymers.[15] On the other hand,
occasionally fast reactions of hydrophobic substrates have
been observed with Pd on hydrophobic supports,[16] namely
active carbon.[17,18] Overall however, there seems to be no
clear trend as to whether hydrophilicity or lipophilicity of a
reactant, catalyst, or support is beneficial; it may depend on
the respective example.
As stated, the question as to whether the catalytic cycle
occurs in the aqueous or the organic layer is of fundamental
importance, but is widely unregarded. We have conducted
and present here experiments on the Suzuki coupling of hy-
drophobic bromo- and chloroarenes in water, by using dif-
ferent catalyst precursors, to achieve insight into the locality
of the catalytic process, and get useful information on a pos-
sible optimization of the reaction conditions. This is the first
time such systematic investigations into the details of the
phase distribution of the reactants, and their influence on
the reaction and its mechanism, have been conducted. The
experiments will be interpreted in light of the question in
which of the two liquid phases the reaction occurs. In the
present work, we hope to bring this question into the minds
of researchers working with different aspects (synthesis, cat-
alysis design, reaction mechanisms, kinetics) in this field.
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ꢂ 2012 Wiley-VCH Verlag GmbH & Co. KGaA, Weinheim
Chem. Eur. J. 2012, 18, 15485 – 15494