Fischmann et al.
(thiosulfate:cyanide sulfur transferase).4-6 Biological forma-
tion of thiosulfonate compounds, such as thiotaurine (2-
aminoethanethiosulfonate)7 and alaninethiosulfonate,8 has
also been established. Some deep-sea invertebrates that live
near hydrothermal vents produce thiotaurine from hypotau-
rine (2-aminoethanesulfinate), to detoxify the high concentra-
tions of H2S.6,9 Thiotaurine has been used as a pretreatment
for sulfur mustard (mustard gas) poisoning10 while thiosul-
fonic acids (and their S-esters) are biologically active as
fungicides and bactericides.11
The coordination chemistry of thiosulfonates has not
been extensively studied. The limited examples of thiosul-
fonate-metal complexes include Au(I),12-17 Cu(I),18,19
Fe(II),20 Ru(II),21,22 Ag(I),23 Hg(II),23 Pt(II),24,25 and Ir(III)26
complexes. To our knowledge there have not been any
quantitative studies on the formation of Cu(II) thiosulfonates
complexes. The monothiosulfonato-Cu(I) complexes
(CuMeS2O2, CuEtS2O2, and CuPrS2O2) were, however,
obtained via reduction of copper(II) by thiosulfonates.18,19
In an extension of our previous work, in which a series of
thiosulfate complexes were stabilized through the use of the
tripodal tetradentate ligand tris(2-aminoethyl)amine (tren) and
several N-functionalized derivatives of tren,3 we present
herein the first detailed investigation of copper(II) thiosul-
fonate complexes. We report the syntheses, characterization,
and X-ray crystal structures of three copper(II) complexes
of composition [Cu(Me3tren)(RS2O2)](ClO4), where Me3tren
) tris(2-methylaminoethyl)amine and R ) Me, Ph, and
MePh, and compare structural features of these complexes,
for example, intramolecular hydrogen bonding, with those
of thiosulfate copper(II) complexes bearing these tripodal
polyamine ligands.3 Taking advantage of the fact that, as
was the case for thiosulfate, coordination of thiosulfonate
to copper(II) is characterized by an intense L f Cu(II) charge
transfer transition in the 300-400 nm spectral region,
-
constants for binding of methanethiosulfonate (MeS2O2 ) to
the tren and Me3tren copper(II) complexes have been
determined and are compared to those reported previously
for the corresponding thiosulfate complexes.3
Experimental Section
Materials and Reagents. Me6tren, Bz3tren, [Cu(tren)(H2O)]-
(ClO4)2, [Cu(Me6tren)(H2O)](ClO4)2, [Cu(Me3tren)(H2O)](ClO4)2,
and [Cu(Bz3tren)(H2O)](ClO4)2 were synthesized as described
previously (tren ) tris(2-aminoethyl)amine, Me3tren ) tris(2-
methylaminoethyl)amine, and Me6tren ) tris(2,2-dimethylamino-
ethyl)amine).3 The syntheses of NaMeS2O2 ·H2O,7 NaPhS2O2,8 and
NaMePhS2O28 were based on literature procedures. Other chemicals
were used as received from commercial suppliers. Deoxygenated
water was prepared by boiling freshly distilled water under nitrogen
for 2 h.
Instrumentation. UV-visible-NIR spectra were recorded on
a Varian Cary 5G spectrophotometer fitted with a water-jacketed
cell holder. An externally circulating water bath (Varian) maintained
the temperature to a precision of (0.1 °C. FTIR spectra were
recorded using either a Perkin-Elmer 1600 FTIR or a Bruker
Equinox IFS 55 FTIR to a resolution of 4 cm-1. A Bruker Equinox
IFS 55 FTIR fitted with a Specac Goldengate ATR stage was used
for recording ATR-IR spectra. The pH of stock solutions for
spectrophotometric studies was fixed using a Titrando autoburette,
fitted with a Metrohm electrode. Elemental analyses were performed
by Campbell Microanalytical Services, University of Otago, New
Zealand.
[Cu(Me3tren)(MePhS2O2)]ClO4. [Cu(Me3tren)(H2O)](ClO4)2 (9
mg, 0.02 mmol) was dissolved in a minimum amount of MeCN to
give a blue solution, and NaMePhS2O2 (10 mg, 0.050 mmol) was
added. The mixture was filtered, yielding a green solution. Slow
diffusion of Et2O into the filtrate resulted in crystallization of green
plates after several days. Analysis via single crystal X-ray crystal-
lography confirmed the formation of [Cu(Me3tren)(MePhS2O2)]-
ClO4. Yield: 1 mg (11%).
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Toxicol. 2000, 20, S3-S5.
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A better yielding synthesis of this compound was developed as
follows. [Cu(Me3tren)(H2O)](ClO4)2 (0.18 g, 0.40 mmol) was
dissolved in 15 mL of hot iPrOH, and NaMePhS2O2 (0.083 g, 0.40
mmol) was added in portions while stirring. Upon addition of the
first portion of the thiosulfonate salt, an immediate blue to green
color change occurred. At the completion of the addition of the
thiosulfonate salt, the solution was dark green and clear. Stirring
was continued for a few minutes, and a green solid was found to
precipitate. The solid was collected by filtration of the solution after
it had been allowed to stand at room temperature (RT) for a few
minutes. The microcrystalline green product was dried at the pump
and washed with Et2O. Yield: 0.12 g (56%). Characterization.
Microanalyses: Found (%): C, 35.8; H, 5.8; N, 10.4. Calculated
for C16H31ClCuN4O6S2 (%): C, 35.7; H, 5.8; N, 10.4. Selected IR
bands [KBr disk: ν (cm-1)]: 3254 s, 2883 m, 1251 m, 1124 s,
1102 s, 1066 s, 988 m, 856 m, 825 m, 708 m, 662 s, 624 m.
[Cu(Me3tren)(PhS2O2)]ClO4. [Cu(Me3tren)(H2O)](ClO4)2 (9
mg, 0.02 mmol) was dissolved in minimum MeCN to give a blue
solution, and NaPhS2O2 (10 mg, 0.05 mmol) was added. Slow
diffusion of Et2O into the green filtrate obtained following filtration
of this mixture caused green blocks of the desired product to
crystallize after several days, along with white/colorless needles,
which were assumed to be NaPhS2O2. Analysis of the green blocks
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10566 Inorganic Chemistry, Vol. 47, No. 22, 2008