3
38
K. Waki et al. / Chemosphere 41 (2000) 337±343
charge of the TiO
to an excess of protons from H
2
particle surface becomes positive due
O or from the solution
0.6% of the calculated values. The photocatalyst titani-
um dioxide was Degussa P-25 (particle size, 20±30 nm by
TEM; 83% anatase and 17% rutile by X-ray diraction;
2
upon irradiation. Accordingly, the negatively charged
atoms of organic compounds may be adsorbed easily on
2
� 1
surface area, 53 m g by BET method).
the surface of TiO
and the áOH radicals photogenerated on the TiO
2
particles due to Coulombic forces,
sur-
2
2.2. Photodegradation procedures and analytical methods
face are expected to attack predominantly at the posi-
tions having the highest frontier electron density.
In this study, the photocatalytic mineralization of
compounds containing one or more hydrazo moieties,
For the photocatalyzed conversion of the gas-gener-
ating agents, an aqueous dispersion (50 ml) of the sub-
2
strates (1 mM) and 100 mg of TiO particles were placed
0
i.e., oxalyldihydrazide, N; N -bis(hydrazocarbonyl)-
in a 124 ml pyrex reactor; the mixture was then dispersed
by sonication for 5 min and then was illuminated with a
75 W Hg lamp under continuous agitation, which gave a
hydrazide, N; N-bis(ethoxycarbonyl)hydrazide, mal-
0
onyldihydrazide and N-malonyl-bis[(N -ethoxycarbonyl)
hydrazide] was examined under UV irradiation in
�
2
light intensity of 2.01 mW cm in the wavelength range
310±400 nm (the maximum emission: k 365 nm). The
headspace volume in the reaction vessel was purged with
oxygen for 15 min prior to irradiation.
aqueous TiO
3
2
dispersions. The formation of NH4 (or
�
2 2
NO ) ions, the evolution of CO and N gases, and the
generation of carboxylic acid intermediates were moni-
tored during the photodegradation process. Simulation
of frontier electron density and point charge was also
carried out. Mechanistic steps are discussed from the
standpoint of the chemical structure of the substrates,
the point charges and the frontier electron densities. The
compounds investigated in this work are commonly used
as gas-generating agents. They have characteristic mo-
lecular structures, and therefore studies of their pho-
tooxidation should provide much information enabling
the details of the photocatalytic mechanism for N-con-
taining compounds to be understood.
2 2
The temporal evolution of N and CO gases was
monitored by gas chromatography with an Ookura
Riken chromatograph (model 802; TCD detector)
through a Molecular sieve 5A (for N
pack Q (for CO gas) column with helium as the carrier
2
gas) or a Pora-
2
�
gas. The concentration of NH4 and NO3 ions formed
was assayed with a JASCO HPLC equipped chro-
matograph with a CD-5 conductivity detector using a
Y-521 cationic column or an I-524 anionic column.
Molecular orbital (MO) calculations were carried out
at the single determinant (Hartree±Fock) level with the
optimal conformation having minimum energy obtained
at the AM1 level (Nohara et al., 1997). All semi-
empirical calculations were performed with MOPAC
version 6 in the CAChe package implemented on a
Power Macintosh system. All MO calculations were
simulated for the initial processes of áOH radical attack
2
. Experimental
2
.1. Chemicals and reagents
Oxalyldihydrazide was supplied by Tokyo Kasei Ind.
and adsorption of molecules on the TiO
2
surface.
0
and was recrystallized from water. N; N -bis(hydrozo-
carbonyl)hydrazide was synthesized by addition of
bis(ethoxylcarbonyl) hydrazide to an excess of hydrazine
3. Results and discussion
(
10 times by weight) under slow agitation for 24 h (yield,
0
�
5
was prepared by elimination of HCl from hydrazine
5%, m.p. 214°C). N; N -bis(ethoxycarbonyl)hydrazide
The formation of CO
2
, N
2
, NH4 and NO3 during
photodegradation of the substrates and the detected
intermediates of carboxylic acids in the photodegrada-
tion of hydrazine substrates is summarized in Table 1.
The photomineralization in the photodegradation of
oxalyldihydrazide is illustrated in Fig. 1. The apparent
(
1 mol) and ethyl chloroformate (2 mol) in the presence
of NaOH (2 mol). The precipitate was washed with iced
water to remove NaCl and then was dried (yield 80%).
The obtained powder was recrystallized twice from
ethanol (m.p. 214°C). Malonyldihydrazide was prepared
by the reaction of malonodiethyl ester with an excess of
hydrazine under stirring for 24 h. Recrystallization was
®rst-order rate constant of
N
2
gas formation
(k 1.1 ´ 10 min ) was higher than that of CO gas
(k 6.0 ´ 10 min ).
The two hydrazo moieties of oxalyldihydrazide were
converted to N gas with a yield of 81% after 4 h of il-
�
�
2
� 1
� 1
2
3
0
from water (m.p. 156°C). N-malonyl-bis[(N -ethoxycar-
bonyl)hydrazide] was prepared by elimination of HCl
from malonodihydrazide (1 mol) and ethyl chlorofor-
mate (2 mol) in the presence of NaOH (2 mol). The
sample was recrystallized with ethanol and tetra-
hydrofuran (yield 19%, m.p. 190°C). The purities of all
compounds prepared were checked by elemental analy-
sis of C, H and N atoms, which were found to be within
2
lumination. NH4 ions were also generated in a small
�
amount (ca. 10%) and no formation of NO3 ions was
observed in the photodegradation process. The fronter
electron densities and point charges for oxalyldihyd-
razide were calculated to estimate the position adsorbed
of the substrates over TiO
2
catalyst as well as the