The Journal of Organic Chemistry
Article
has been generally considered to be the activation of the
hydroxamic acid by various activating agents), and the chlorine
or hydrogen ortho to the reaction site at CnBQ is crucial for the
stability of the anionic intermediates. (3) There exists a pKa−
activation energy correlation for this CnBQ-activated Lossen
rearrangement reaction, which can explain why the correlation
exists between the rate of the rearrangement and the acidity of
the conjugate acid of the anionic leaving group.
Potential Biological and Environmental Implications.
Halogenated quinones represent a class of toxicological
intermediates that can create a variety of hazardous effects in
vivo, including acute hepatoxicity, nephrotoxicity, and carcino-
genesis.20−22 Chlorinated benzoquinones (CnBQs) are the
major genotoxic and carcinogenic quinoid metabolites of the
widely used pesticides chlorophenols such as the wood
preservative pentachlorophenol (PCP) and 2,4,5-trichlorophe-
nol. CnBQs have also been observed as reactive oxidation
intermediates or products in processes used to oxidize or
destroy chlorophenols and other polychlorinated persistent
organic pollutants (POPs) in various chemical and enzymatic
systems.20−22 Recently, several CBQs were identified as new
chlorination disinfection byproducts in drinking water and in
swimming pool waters.23,24
Hydroxamic acids have attracted considerable interest
recently because of their capacity to inhibit a variety of
enzymes, such as metalloproteases and lipoxygenase, and
transition metal-mediated oxidative stress.4,9,25,26 Many of the
activities of these hydroxamic acids are thought to be due to
their metal-chelating properties. In addition to metal chelation,
hydroxamic acids are considered to be good α-nucleophiles.
We have shown previously that hydroxyl (or alkoxyl) and
carbon-centered quinone ketoxy radicals (leading to DNA
damage) and chemiluminescence can be produced during the
metal-independent decomposition of H2O2 (or organic hydro-
peroxides) by TCBQ and other halogenated quinoid
carcinogens.27−32 Recently, we found that the formation of
these reactive free radicals and TCBQ-induced cellular toxicity
were markedly inhibited by benzohydroxamic acid (BHA) and
other hydroxamic acids,33,34 via the unusually facile two-
consecutive-step Lossen rearrangement mechanism.9 It has
been well documented that such radical damage processes
(radical oxidations) occur as autocatalyzed chain reactions.35
Whereas, most often, the focus of radical suppression is by
inhibiting radical propagation,36 the presented strategy relies on
inhibiting radical initiation reactions, i.e., the halogenated
quinone-supported homolytical cleavage of peroxides. This is
conceptually similar to the iron-chelating efforts for prevention
of food spoilage.37
As demonstrated in the present and previous study,
hydroxamic acids, in addition to BHA, might be especially
suited for detoxification of halogenated quinone carcinogens via
the Lossen rearrangement mechanism. Of particular interest in
this regard is the fact that two hydroxamic acids are already
approved for clinical applications, deferoxamine for iron
overload and suberoylanilide hydroxyamic acid (Vorinostat),
recently approved for cutaneous T-cell lymphoma.4,9,25,26 Thus,
further investigation is needed to determine whether
hydroxamic acids can be used safely and effectively as
prophylactics for the prevention or treatment of human
diseases such as liver and bladder cancer associated with the
toxicity of polyhalogenated quinoid carcinogens.
EXPERIMENTAL AND COMPUTATIONAL
METHODS
■
Chemicals. 2,5-Dichloro-1,4-benzoquinone (2,5-DCBQ), 2,6-di-
chloro-1,4-benzoquinone (2,6-DCBQ), 2-chloro-1,4-benzoquinone
(2-CBQ), tetrachloro-1,4-benzoquinone (TCBQ), benzohydroxamic
aicd (BHA), phenyl isocycanate (Ph-NCO), N,N′-diphenylurea, and
aniline were used as purchased. 2-Chloro-5-hydroxy-1,4-benzoquinone
(CBQ-OH), 2,3-dichloro-1,4-benzoquinone (2,3-DCBQ), and 2,3,5-
trichloro-1,4-benzoquinone (TrCBQ) were synthesized by our
research group according to the literature methods.38,39
Analysis of the Reaction of 2,5-DCBQ/BHA. The reaction
products of 2,5-DCBQ/BHA were analyzed with high-performance
liquid chromatography combined with electrospray ionization quadru-
pole time-of-flight mass spectrometry (HPLC/ESI-Q-TOF-MS). The
HPLC system was equipped with a photodiode array detector. For
direct MS analysis, a small portion (20 μL) of reaction solution of 1
mM 2,5-DCBQ with 1, 2, or 4 mM BHA in 1 mL of Chelex-treated
CH3COONH4 buffer (100 mM, pH 7.0) at room temperature during
the reaction period of 0−30 min was injected into the mass
spectrometer. All other MS experimental parameters were the same
as described previously.9 The yield of 2-chloro-5-hydroxy-1,4-
benzoquinone (CBQ-OH) from 2,5-DCBQ/BHA was quantified by
HPLC using synthesized CBQ-OH as standard according to the
previous method.28 For HPLC/MS analysis, the reaction solution was
injected into an LC-18 C18 column (5 μm, 4.6 × 250 mm) eluted by
the mobile phase (50 mM aqueous acetic acid and acetonitrile at
50:50) at a rate of 1.0 mL/min, and the chromatographic eluant was
monitored at 200−600 nm and then led to the mass spectrometer
through a splitter.
Isolation of the Major Reaction Products (P1 and P2) of 2,5-
DCBQ/BHA and the Identification of Decomposition Products
of P1 in Aqueous Solution. P1 and P2 were isolated by both
semipreparative HPLC and column chromatography. Milligram-scale
collection of P1 and P2 (Scheme 2) was performed with semi-
preparative HPLC apparatus equipped with a UV detector. The
reaction solution of 2,5-DCBQ/BHA (1:1 or 1:2, 1 mM 2,5-DCBQ)
in 1 mL of Chelex-treated CH3COONH4 buffer (100 mM, pH 7.0) at
room temperature after a reaction time of 5 min was injected into a
Prep-C18 semipreparative HPLC column (15 cm × 10.0 mm, 3 μm).
The mobile phase was 50 mM aqueous acetic acid−acetonitrile
(50:50) at a flow rate of 3.0 mL/min. The fractions were monitored at
275 nm and collected manually. Then collected fractions were
evaporated to eliminate acetonitrile and then extracted with ethyl
acetate. The collected ethyl acetate layer was dried over anhydrous
MgSO4 and evaporated to dryness under vacuum. Gram-scale P1 and
P2 were isolated by column chromatography. A solution of 2,5-DCBQ
(5 mM, 0.885 g) in acetonitrile (10 mL) was added dropwise to 100
mL of Chelex-treated CH3COONH4 buffer (100 mM, pH 7.0)
containing BHA (5 mM, 0.685 g) at room temperature. After the
mixture was stirred for 5 min, the solid was separated by filtration and
purified by silica gel column chromatography with tetrahydrofuran/
petroleum ether (1:9) as eluent. Preparation of P2 was carried out as
for P1 except that the molar ratio of 2,5-DCBQ/BHA was 1:2 and the
purification was carried out by recrystallization from tetrahydrofuran/
petroleum ether. Product P1 was golden-yellow and P2 was purple-red,
1
and their purity was 98% as determined using HPLC. H NMR and
13C NMR spectra of P1 and P2 were recorded at 400 and 101 MHz,
respectively, using tetramethylsilane ((CH3)4Si) as internal standard
and DMSO-d6 as solvent. Product P1: 1H NMR δ = 6.50 (s, 1H), 7.36
(s, 1H), 7.54 (m, 2H), 7.64 (m, 1H), 7.88 (m, 2H), 12.85 (s, 1H); 13C
NMR δ = 127.7, 128.8, 130.6, 132.6, 143.5, 158.3, 165.8, 178.7, 179.4.
1
Product P2: H NMR δ = 6.32 (s, 2H), 7.55 (m, 4H), 7.64 (m, 2H),
7.89 (m, 4H), 12.85 (s, 2H); 13C NMR δ = 127.7, 128.8, 130.5, 132.6.
158.4, 165.5, 180.5. For details, see Supporting Information.
P1 (1 mM) in PB buffer (0.1 mM, pH 8.0) was heated in 60 °C
water bath for 2 min and then spotted on analytical thin-layer
chromatography (TLC) plates or injected into an HPLC instrument.
TLC was carried out on silica gel plates with F-254 indicator.
Reactions were monitored by TLC using ethyl acetate−petroleum
H
dx.doi.org/10.1021/jo5022713 | J. Org. Chem. XXXX, XXX, XXX−XXX