1584 Antonio E. Alegria et al.
XO) followed by HX injection (20). Also, purine catabolites,
including HX, accumulate in solid tumors that are exposed to
hyperthermia (21). Thus, photolysis of PDT dyes in the
presence of both diaziridinylquinone and HX, or in combina-
tion with hyperthermia, could enhance quinone reduction
and macromolecule alkylation and thus improve PDT of solid
tumors.
In this work, we conduct a proof-of-principle test of a
mechanism whereby PDT could damage biomolecular targets
under hypoxic conditions. Specifically, we demonstrate that
A Shimadzu 10A analytical HPLC system, equipped with a Shimadzu
SPD-10 multiwavelength absorbance detector, was used at a wave-
length of 267 nm. Standard curves were prepared with HX, X and UA
solutions and used to obtain the concentrations of those species in
irradiated samples.
Samples of HX, X and UA of the irradiated solutions were also
collected from the HPLC analysis peaks and submitted to electrospray
ionization mass spectrometry (ESI-MS). These were performed on a
Micromass Quattro Micro API triple quadrupole mass spectrometer
with an ESI source (Micromass, Inc., Manchester, UK). Samples were
injected into the MS by direct infusion through capillary tubing at a
)
1
flow rate of 4 lL min . The full scan ESI conditions for the
monitored compounds were as follows: negative ionization mode,
capillary voltage (3.07 kV), cone voltage (20.00 V), extractor voltage
4
aluminum phthalocyanine tetrasulfonate (AlPcS ), under
nitrogen-saturated conditions (to simulate solid tumor regions
where oxygen participation is limited) photooxidizes HX to
produce X and X to produce UA in the presence of AZDClQ
but not in its absence. In addition, the presence of HX
increases the photosensitized formation of aziridinylquinone-
DNA covalent adducts under these conditions, thus suggesting
a Type-I process that could be exploited in the PDT of
solid tumors.
(
desolvation gas flow of 400 L h
2 V), source temperature (90ꢁC), desolvation temperature (300ꢁC) and
)1
.
Photosensitized semiquinone formation. Samples with the same
composition as that described above were photolyzed, at pH 7.4, for
increasing periods of time followed by transference of these to
deaerated EPR quartz flat cells. EPR spectra were then recorded on
a Bruker ER-200D spectrometer at 100 kHz magnetic field modula-
•)
tion. Semiquinone (Q ) concentrations were obtained by comparing
the semiquinone overmodulated EPR double-integrated spectral area
with that corresponding to
pyrrolin-1-oxide spin standard.
a 3-carbamoyl-2,2,5,5-tetramethyl-3-
Quinone covalent binding to DNA. The procedure used in this
determination was adopted from that described by Lusthof et al. (24)
and used previously by us (16,25). Solutions of DNA, dyes and
quinone were prepared, some were photolyzed and the samples were
MATERIALS AND METHODS
4
Materials. The dye, AlPcS , was obtained from Frontier Scientific
and used as received. AZDClQ, HX, X and UA were purchased
from Sigma-Aldrich Chemicals and used as received. The quinone
then left standing for 20 h at room temperature under an N
2
atmosphere and shielded from light by aluminum foil. The nonphoto-
lyzed samples served as matched controls for the photolysis. Then,
quinone-bound and -free DNA were separated from unbound quinone
on a Sephadex spun exclusion column (26). The DNA fractions were
analyzed by absorption spectroscopy. The presence of a quinone
absorption band at wavelengths above 300 nm was taken as evidence
of DNA-bound quinone. For example, the DNA-2,5-bis(1-aziridinyl)-
2,5-dichloro-diaziridinyl-1,4-benzoquinone was either purchased from
Sigma-Aldrich Chemicals or synthesized and characterized, starting
from the tetrachloro quinone, as reported elsewhere (22). Calf-
thymus DNA and Sephadex G-25 (superfine, DNA grade), were
purchased from Sigma-Aldrich Chemicals. All other chemicals were
of the highest purity commercially available and were used without
further purification. Aqueous DNA stock solutions were freshly
prepared in water each day and their concentration determined from
the absorbance at 260 nm and using a molar absorption coefficient
1
3
,4-benzoquinone adduct has an absorption maximum wavelength at
43 nm (24). For each photolyzed sample, Sephadex spun exclusion
chromatography was continued until no, or a small constant value of,
quinone absorption was detected in the matched but nonphotolyzed
control solution. Samples and controls were then extracted with an
equal volume of chloroform and then with an equal volume of diethyl
ether, followed by DNA precipitation and redissolution in water, as
described elsewhere (27). Samples and controls treated in this manner
were then submitted to absorption spectroscopic analysis. Sample pH
values were measured before and after photolysis and before Sephadex
extraction and were found to be constant. The molar ratio of
covalently bound quinone to DNA bases was estimated from the
quinone maximum absorbance in the 340–360 nm region, assuming
the same molar absorption coefficient as that of the parent quinone,
and DNA absorbance at 260 nm.
3
)1
)1
of 6.6 · 10
M
cm . Deionized and Chelex-treated water was used
in the preparation of all stock and sample solutions. All reagent
stock solutions were deaerated by flushing with water-saturated
nitrogen prior to mixing with other reagents. Oxygen was then
excluded from samples by keeping a positive pressure of N
the sample.
Sample photoirradiation. Nitrogen-saturated samples (1.00 mL)
2
gas in
)
1
containing 875 lM quinone in the presence or absence of 1 mg mL
calf-thymus DNA, in the presence or absence of 2 mM HX and a dye
concentration to produce an absorbance of 1, at the dye maximum
wavelength of 675 nm (6 lM), in 20 mM phosphate buffer at either pH
5.5 or 7.4, were photolyzed in quartz cuvettes of 1.00 cm light path
under continuous stirring. The pH value of 5.5 was selected to simulate
hypoxic tumor pH conditions (23). Wanting to keep the same
constituents at the two pH values and recognizing that phosphate
would not be an efficient buffer at pH 5.5, the pH value was measured
before and after irradiation and found to remain constant within ± 0.1
pH units. In addition, to avoid interference with the reactions,
phosphate was always used. Photoirradiation was allowed to occur for
periods of time ranging from 0 to 20 min at 675 ± 10 nm with a
radiant power of 8 mW. Samples were protected from external light
during and after preparation. Irradiations were performed using a 1000-
W xenon arc lamp coupled to a Schoeffel grating monochromator.
HX and X photooxidation. Samples were prepared and photolyzed
as indicated above followed by HPLC analysis of HX and the products
X and UA. HPLC analyses were performed using two Alltech
Platinum EPS C-18 (4.6 · 250 mm) columns and gradient elution
going from 100% ammonium acetate at pH 7.4 to 1:1 ammonium
acetate (pH 7.4):methanol in 15 min followed by 100% methanol. In
order to exclude oxygen from the eluant mixture, solvents were purged
with argon 30 min before injection and during the chromatographic
RESULTS AND DISCUSSION
HX and X photo-oxidation
When a nitrogen-saturated sample containing 2 mM HX,
8
4
75 lM AZDClQ and AlPcS (A = 1 at 675 nm) in 20 mM
phosphate buffer at pH 7.4 was photolyzed, the HX concen-
tration decreased while the X and UA concentrations
increased with irradiation time (Fig. 1). In addition to the
retention time, ESI-MS analyses of the collected HPLC peaks
show molecular masses, using negative ionization mode, of
[M-H]135.2, 151.4 and 167.3 corresponding to HX, X and
UA, respectively.
HX and X have been reported to be oxidized anaerobically
to yield X and UA, in the case of HX oxidation, and UA in
the case of X oxidation. For example, the anaerobic non-
photosensitized oxidation of HX or X by XO, which is
followed by UA detection, has been reported previously
)
1
analysis. The flow rate of elution was 1 mL min . The column was
washed daily with methanol for 1 h and then with water for 40 min
and stored in methanol:water (1:4, v ⁄ v). The column was re-
equilibrated to initial conditions for 60 min before injection.