Communications
Inorganic Chemistry, Vol. 39, No. 4, 2000 633
Scheme 1
solution of 1 ([Fe] ) 8 µM) in toluene ([NO] ) 8 mM) (Figure
1). Stepwise addition of O2 led to decreased absorbance in the
Soret band region at 406 nm due to 1 and increases at 432 nm
due to 2 as well as increased absorbance at 306 nm indicating
the buildup of N2O3 (ꢀ ) 2 × 103 M-1 cm-1).11 The spectral
changes at 432 nm and calculated [N2O3] values were used to
determine K3 ) 160 ( 20 according to Hoshino’s method12
(Supporting Information, Figure S-1). One can also estimate the
K2 for the reaction of NO2 with 1 from the relationship K2 )
K1K3. If one assumes K1 in toluene to be similar to that reported
in acetonitrile (6.7 × 103 M-1),13 then K2 is ∼1.1 × 106 M-1 in
toluene.
Further manipulations of 2 demonstrated that this easily
undergoes dissociation of NO. For example, the solution of 2 for
which the optical and IR spectra displayed in Figure 1 were
recorded was removed from the IR cell, diluted under Ar with
CHCl3, and then evaporated in vacuo back to the original volume.
The IR spectrum of the resulting solution (Figure 1b) shows no
Figure 2. Formation of 2 from 1 in toluene at 22 ( 1 °C, obtained by
addition of air (5, 10, 15, 20, 30, 40, 50, 100 µL) to a 117 mL cell
containing 1 (8 µM) in toluene (25 mL), with NO (500 Torr, 8 mM).
The initial spectrum of 1 in the absence of NO is shown as a dotted line.
The spectrum of 1 in the presence of 8 mM NO, the first solid line, is
nearly the same, with subsequent spectra representing addition of air.
It is difficult to reconcile the present results with reports that
1 reacts under these conditions to give 2, unless the previous
observations were due to trace higher nitrogen oxides in the NO
gas streams of (Scheme 1). This hypothesis was tested by adding
air (∼150 µL, 2.6 µmol of O2) directly to the NO/Fe(TPP)(NO)
solution described above. The resulting UV-visible and IR
spectra are identical to those reported for 2 (Figure 2).2,4 NO
autoxidation in aprotic solvents gives NO2,10 and this reacts with
excess NO to give N2O3, so it is the equilibrium mixture of these
species (K1 ) [N2O3]/[NO][NO2]) to which the oxidation of 1 is
attributed. Preliminary stopped-flow kinetics studies show the
reaction of 1 with N2O3 to have a second-order rate constant >106
M-1 s-1 (Scheme 1).
ν
NO band, and the Q-band spectrum (Figure 1a) displays features
(510 nm (ꢀ ∼ 104 M-1 cm-1), 576 (3.5 × 103, sh), 650 (1.7 ×
103), and 688 (2 × 103)) characteristic of an FeIII(TPP)(X) type
complex.14 Since 2 is re-formed promptly upon reintroduction of
NO, we assign this species as Fe(TPP)(NO2) (3), formed by NO
dissociation (eq 2).
Fe(TPP)(NO )
Fe(TPP)(NO)(NO2) h
+ NO
(2)
2
3
Analogous spectral changes were observed upon controlled
removal of NO from the headspace of a toluene solution of 2,
NO, and a known amount of NO2, followed by equilibration. This
procedure allowed estimation of K4 at (3 ( 2) × 10-2 M-1 very
similar to the value previously reported for dissociation of NO
from Fe(TpivPP)(NO2) in CH3CN.14a
The equilibrium constant K3 was evaluated from the spectral
changes as microliter aliquots of air were introduced into a dilute
(9) (a) Kadish, K. M.; Adamian, V. A.; Van Caemelbecke, E.; Tan, Z.;
Tagliatesta, P.; Bianco, P.; Boschi, T.; Yi, G.-B.; Khan, M. A.; Richter-
Addo, G. B. Inorg. Chem. 1996, 35, 1343-1348. (b) Miranda, K. M.;
Bu, X.; Lorkovic, I. M.; Ford, P. C. Inorg. Chem. 1997, 36, 4838-
4848.
In summary, Fe(TPP)(NO), unlike Ru(P),5,9 does not ap-
preciably bind a second NO in room temperature solutions nor
does it promote NO disproportionation to give 2.15 The latter is
formed readily from Fe(TPP)(NO) by reaction with (the much
more soluble) NO2 (N2O3) present in many NO gas streams or
formed by NO reaction with trace O2. Thus, unless care is taken,
NOx impurities are likely to play a major role in the observed
chemistry of transition metal complexes whenever NO is used in
large excess. Qualitatively, NO is more readily dissociated from
2 than is NO2.
(10) (a) Nottingham, W. C.; Sutter, J. R. Int. J. Chem. Kinet. 1993, 25, 375-
381. (b) Ford, P. C.; Wink, D. A.; Stanbury, D. M. FEBS Lett. 1993,
326, 1-3.
(11) Lorkovic, I. M.; Ford, P. C. Unpublished results.
(12) (a) Hoshino, M.; Ozawa, K.; Seki, H.; Ford, P. C. J. Am. Chem. Soc.
1993, 115, 9568-9575. (b) A lower [N2O3] is required to effect the
conversion of 1 to 2 at the same [NO] in CHCl3 than in toluene, so K3
must have a larger value in the former.
(13) (a) Shaw, A. W.; Vosper, A. J. J. Chem. Soc. A 1971, 1592-1595. (b)
Redmond, T. F.; Wayland, B. B. J. Phys. Chem. 1968, 72, 1626-1629.
(14) (a) Frangione, M.; Port, J.; Baldiwala, M.; Judd, A.; Galley, J.; DeVega,
M.; Linna, K.; Caron, L.; Anderson, E.; Goodwin, J. A. Inorg. Chem.
1997, 36, 1904-1911. (b) Munro, O. Q.; Scheidt, W. R. Inorg. Chem.
1998, 37, 2308-2316. (c) Phillippi, M. A.; Baenziger, N.; Goff, H. M.
Inorg. Chem. 1981, 20, 3904-3911.
Acknowledgment. This work was supported by the National
Science Foundation (CHE 9726889) and by a CULAR grant from
Los Alamos National Laboratory.
(15) (a) It has been suggested15b that trace H2O may interact with 1 to inhibit
its reactivity with NO. However, solutions of 1 plus NO prepared in an
oven-dried silanized UV/vis cell by vacuum line transfer of toluene from
highly activated 3 Å molecular sieves (to minimize such traces)
demonstrated no differences in reactivity. (b) Farmer, P. J. Personal
communication.
Supporting Information Available: Supplemental Figure S-1 that
demonstrates the determination of K3. This material is available free of
IC9910413