5
6
P. Carniti et al.
particular aerobic oxidative procedures [32–37] and the use
of system I /H O deserves interest [38–40]. Hydrogen
both the resins were dried at 100 °C under vacuum
(*20 Torr) in a rotative oven (BUCHI mod. GKR-50).
Particles between 25 and 35 mesh, obtained as reported in
¨
2
2 2
peroxide is accepted as a green oxidant and it has several
advantages over other oxidants: it is relatively cheap, non-
toxic, and it breaks into benign byproducts. Some hazard-
ous with its use is connected with highly concentrated
solution of H O , higher than 70–80% aqueous H O .
Ref. [49], were used for the catalytic tests.
H-ZSM5 and LZ-Y82 zeolites, SiAl and SiZr oxides,
NBO and NBP were first crushed in a mortar and then
sieved, collecting the 25–35 mesh fraction. The amount of
water in the catalysts was determined by drying at 100 °C
under vacuum (*20 Torr) in a rotative oven up to constant
weight. The knowledge of the water content in each cata-
lyst permitted evaluating the exact quantity of dry sample
employed in the catalytic test. Before use, they were dried
at 120 °C in an oven overnight (about 16 h).
Specific surface area and pore volume were determined
by conventional N2 adsorption/desorption at -196 °C
using an automatic analyzer of surface area (Carlo Erba
Sorptomatic). Prior to the analysis, the samples (H-ZSM5,
LZ-Y82, SiAl. SiZr, NBO, and NBP) were outgassed at
350 °C overnight (16 h) to eliminate moisture and volatile
compounds from the surface and pores. BET equation was
used for the calculation of the surface area and pore volume
values.
2
2
2 2
Moreover, the use of solid acids [41] instead of concen-
trated liquid acids, accounting for an heterogeneous syn-
thetic process for the direct introduction of iodine into
organics, is in the direction of the development of greener
reactive processes. The enormous advantages of the het-
erogeneous catalysis in comparison with the homogeneous
one have been well assessed in very numerous processes of
the fine, primary, and secondary chemistry [42–45]. In our
knowledge, experimental data concerning the direct
iodination of aromatics over solid acids have not been
appreciably revealed in the literature [46, 47].
In this work, we present the direct iodination of phenol,
chosen as representative aromatic substrate. The electro-
?
philic I species was generated from diodine by the pres-
ence of the catalytic action of some different solid acids;
the formed iodide ions were reoxidized by the oxidant
agent H O . The protocol employed to perform the reac-
2-Phenylethylamine (PEA, from Fluka, pure reagent,
99%), was utilized as basic probe for the acid site titrations
of the samples. The experiments were performed in a liquid
chromatographic line (HPLC), consisting of a pump
(Waters model 510) and an UV detector (Waters model
2487, k = 254 nm). The catalyst sample was placed in a
small stainless steel tube (length 12 cm, i.d. 2 mm)
mounted in place of the chromatographic column. The tube
was surrounded by a glass jacket thermostated by circu-
lating water at 17 °C.
2
2
tions is mild and very simple from the operative point of
view, as compared with the most reported methods using
homogeneous catalysts. The present approach could open a
new interesting perspective in the functionalization of
activated and deactivated arenes by iodine atom introduc-
tion assisted by an heterogeneous catalytic action.
2
Experimental
The apparatus can work in dynamic mode by successive
injections of pulses of defined and constant PEA concen-
tration (20 lL, 0.15 M) up to surface saturation or in re-
circulating mode. In the recirculating mode, solution of
PEA recirculated onto the sample until adsorption equi-
librium was achieved. The PEA concentration was varied
adding small quantities of PEA (50 lL, 0.15 M) to the
recirculating solution. Details on the method and operative
conditions have been given elsewhere [48–50]. The col-
lected data allowed to draw adsorption isotherms. 1:1
Stoichiometry for the PEA adsorption on the acid site was
assumed, the total number of acid sites per catalyst mass
2
.1 Materials and Characterization
The catalysts studied were three resins in acidic form
Amberlite IR-120 (H) and Amberlite 200, named A120 and
(
A200, respectively, and SAC-13, Nafion supported on sil-
ica), two acidic zeolites (MFI and faujasite types, named H-
ZSM5 and LZ-Y82, respectively), two amorphous mixed
oxides (silica-alumina and silica-zirconia, named SiAl and
SiZr, respectively), and two Nb-containing materials (nio-
bium oxide and niobium phosphate, named NBO and NBP,
respectively). They all are commercial materials. The cat-
alysts and their characteristics are listed in Table 1.
-
1
were expressed as mequiv g
.
A120 Amberlite was supplied in acidic form, it needed
only to be rinsed, under stirring, with distilled water to
eliminate any mineral acidic residue. The procedure was
repeated up to complete absence of both acidity and colour
in the wash waters. A200 Amberlite was supplied in
Na-form, it was activated by ionic exchange with HCl
2.2 Catalytic Reaction
The tests of catalytic iodination of phenol were performed
in a recirculation reaction line schematically shown in
Fig. 1. The line comprised: a peristaltic pump (Watson-
Marlow), a glass pre-heater and fixed-bed flow reactor
(20 cm long, 2 cm internal diameter) thermostated by
1
0%, then rinsed with distilled water up to neutrality. Then,
1
23