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Relatively long-lived chromium(V) species are produced by the action of glutathione on carcinogenic chromium(VI).

X-Band EPR studies on aqueous solutions of potassium dichromate and gamma-L-glutamyl-L-cysteinylglycine (reduced glutathione) at pH 6-8 have shown the formation of several relatively long-lived chromium(V) species. The major species formed at high glutathione:Cr(VI) ratios is characterised by an EPR band at g = 1.995, but the dominant complex at equimolar ratios produces a signal at g = 1.985.

Carcinogens↗

The reduction of chromium (VI) to chromium (III) by glutathione: an intracellular redox pathway in the metabolism of the carcinogen chromate.

The capacity of glutathione (GSH) to reduce Cr(VI) to Cr(III) in vitro was investigated. The reaction was determined spectrophotometrically by following the absorption of Cr(VI) at 370 nm. At stoichiometric conditions (molar ratio Cr(VI)/GSH of 1:3) the reduction was strongly dependent on the solution's pH. It was much slower at pH 7.4 than at pH values below 5. An excess of GSH (100- or 1000-fold) accelerated the reaction. In any case, 3 GSH molecules were required to reduce 1 molecule of chromate. Incubation of human red blood cells (RBC) with an excess of Na2CrO4 (10 mM) decreased the GSH content of the cells to 10% of the original amount. This depletion of GSH was similar to that obtained when RBC were incubated with 62 mM diethylmaleate (DEM), a well known GSH depleting agent. Sephadex G-100 chromatography of lysates from human RBC incubated with radioactive chromate (51Cr(VI] showed a strong affinity of 51Cr for hemoglobin: 97% of the applied dose was bound to hemoglobin whilst only minor amounts of 51Cr were found in the low-molecular fractions. However, incubations of prepared lysates (as opposed to intact cells) with 10 mM Na2 51CrO4 markedly raised the chromium content of low-molecular fractions (probably GSH-Cr-complexes), probably indicative of a role of GSH in the intra-cellular reduction of Cr(VI) to Cr(III), the latter being regarded as the ultimately toxic species of this metal.

Chromates↗

Heavy metal accumulation and metallothionein concentration in the frog Rana ridibunda after exposure to chromium or a mixture of chromium and cadmium.

The accumulation of two heavy metals (chromium (Cr) and cadmium (Cd)) in the liver, kidney and gut of Rana ridibunda exposed to Cr or to a mixture of Cr and Cd was investigated. The concentration of metallothioneins (MTs) in the same tissues was also studied. Both metals accumulated mainly in the kidney. Cr accumulation in the liver and gut was not affected by the presence of Cd. Furthermore, Cr concentration in the kidney was doubled when Cd was present. MT concentration did not increase after Cr treatment but it increased two- to six-fold over control values in mixture-exposed frogs, the highest value being observed in the gut. MTs in the gut could act as a barrier preventing ingested heavy metals from entering the blood stream. MT concentration correlated positively with Cd concentrations in both the liver and the gut of mixture-exposed animals.

Animals↗

Formation of reactive oxygen species and DNA strand breakage during interaction of chromium (III) and hydrogen peroxide in vitro: evidence for a chromium (III)-mediated Fenton-like reaction.

The role of reactive oxygen species in causing DNA damage through interaction of chromium (III) and hydrogen peroxide was examined using plasmid relaxation assay and EPR spectroscopy. Marked DNA strand breakage was induced by CrCl3 plus H2O2 in a phosphate buffer at pH 6-8.9; whereas, only slight DNA strand breakage was observed during similar treatment at pH less than 4. DNA breakage also increased as the reaction temperature and Cr(III)/H2O2 concentrations increased. Control experiments with Cr(III) or H2O2 alone did not cause DNA breakage. Sodium azide, D-mannitol, Tris-HCl, or catalase completely inhibited Cr(III)/H2O2-induced DNA breakage, but superoxide dismutase did not. The D2O enhancing effect on DNA breaks was not observed. Cr(III) pre-incubated with a 30-fold molar excess of EDTA did not cause any significant DNA breakage in the presence of H2O2. In a phosphate buffer containing Cr(III) and H2O2, singlet oxygen and hydroxyl radicals were detected using EPR spectrometry with the spin traps 2,2,6,6-tetramethyl-4-piperidone and 5,5-dimethyl-1-pyrroline 1-oxide (DMPO), respectively. DMPO/.OH adducts and DNA breakage induced by Cr(III)/H2O2 were markedly higher than those induced by Cr(VI)/H2O2. Furthermore, ascorbate decreased Cr(III)/H2O2-induced DNA breakage. EPR studies revealed that ascorbate (mole ratio to Cr(III) = 0.5:1) attenuated the DMPO/.OH signal generated by Cr(III)/H2O2/DMPO, but a Cr(V) signal and ascorbate radicals were detected. NADPH, GSH, and GSSG also decreased DMPO/.OH generated by Cr(III)/H2O2/DMPO; however, they were less efficient than ascorbate and no Cr(V) signals were detected. This study shows that Cr(III)/H2O2 generates oxidative damage to DNA through a Fenton-like reaction: Cr(III) + H2O2-->Cr(IV) + .OH + OH.

Ascorbic Acid↗

Formation of the amino acid-DNA complexes by hexavalent and trivalent chromium in vitro: importance of trivalent chromium and the phosphate group.

We have recently shown that a substantial fraction of all Cr-DNA adducts in chromate-exposed cells are represented by ternary complexes involving amino acids or glutathione bridged by Cr-(III) to DNA. The tridentate amino acids such as cysteine, glutamic acid, and histidine were predominantly found cross-linked to DNA. The mechanism by which Cr can cross-link these amino acids to DNA has been modeled by reacting DNA and trivalent and hexavalent chromium with cysteine and histidine. The formation of a Cr(III)-amino acid binary complex was required before Cr(III) reacted with DNA to yield a ternary complex. Cr(III)-pretreated DNA did not bind cysteine or histidine even after prolonged incubations. Reduction of Cr(VI) in the presence of DNA gave rise to an extensive cross-linking of cysteine and histidine. Addition of DNA to Cr(VI) mixtures at the start of reduction or after the reduction was complete had little effect on the level of ternary complexes indicating that Cr(III)-amino acid binary complexes were DNA-attacking species. In order to identify DNA groups involved in the ternary complex formation, pre-formed Cr(III)-histidine complexes were reacted with nucleosides and nucleotide monophosphates followed by separation and analysis of the products. The incubation of the Cr(III)-histidine complexes with nucleotide monophosphates but not with nucleosides gave rise to ternary complexes that contained both histidine and Cr, showing the primary importance of the phosphate group in this reaction. All four DNA nucleotides were capable of the ternary complex formation with Cr(III) and histidine. No apparent base preference in the amino acid cross-linking was also found in the reaction of Cr(III)/cysteine and Cr(VI)/cysteine mixtures with oligonucleotides of base-specific composition.

Amino Acids↗

Effects of sediment characteristics on the toxicity of chromium(III) and chromium(VI) to the amphipod, Hyalella azteca.

We evaluated the influence of sediment characteristics, acid-volatile sulfide (AVS) and organic matter (OM), on the toxicity of chromium (Cr) in freshwater sediments. We conducted chronic (28-42-d) toxicitytests with the amphipod Hyalella azteca exposed to Cr(VI) and Cr(III) in water and in spiked sediments. Waterborne Cr(VI) caused reduced survival of amphipods with a median lethal concentration (LC50) of 40 microg/L. Cr(VI) spiked into test sediments with differing levels of AVS resulted in graded decreases in AVS and sediment OM. Only Cr(VI)-spiked sediments with low AVS concentrations (< 1micromol/g) caused significant amphipod mortality. Waterborne Cr(III) concentrations near solubility limits caused decreased survival of amphipods at pH 7 and pH 8 but not at pH 6. Sediments spiked with high levels of Cr(III) did not affect amphipod survival but had minor effects on growth and inconsistent effects on reproduction. Pore waters of some Cr(III)-spiked sediments contained measurable concentrations of Cr(VI), but observed toxic effects did not correspond closely to Cr concentrations in sediment or pore waters. Our results indicate that risks of Cr toxicity are low in freshwater sediments containing substantial concentrations of AVS.

Amphipoda↗

In vivo distribution of chromium from chromium picolinate in rats and implications for the safety of the dietary supplement.

Chromium picolinate, [Cr(pic)(3)], is the second most popular nutritional supplement after calcium supplements. However, the supplement, unlike simple inorganic Cr(III) salts, has been shown in the presence of biological reducing agents in vitro to catalytically generate appreciable quantities of hydroxyl radicals, resulting in DNA damage. The complex has also been shown to be remarkably stable in vitro at neutral, basic, or weakly acidic pHs. Thus, the significance of this ability to generate hydroxyl radicals depends on whether the complex is absorbed by cells intact along with the stability and concentration of the complex in cells. Consequently, male Sprague Dawley rats have been injected with (51)Cr- and (3)H-labeled [Cr(pic)(3)]. The tissue distribution, urinary and fecal loss, and subcellular hepatocyte distribution and concentration of the labels suggest that [Cr(pic)(3)] has a lifetime of less than 1 day in vivo, minimizing the potential threat from the supplement itself.

Animals↗

Diversity of chromium-resistant and -reducing bacteria in a chromium-contaminated activated sludge.

AIMS: This study attempts to establish a relationship between the Cr(VI) resistance of the culturable microbial community and the Cr(VI) resistance and Cr(VI)-reducing ability of representative strains of each population, in order to assess whether these are exclusive characteristics of one microbial group or abilities shared among many groups. METHODS AND RESULTS: A group of 48 Cr(VI)-resistant isolates, with different colony types, was isolated from chromium-contaminated activated sludge. Sodium dodecyl sulphate-polyacrylamide gel electrophoresis protein patterns and fatty acid methyl ester analysis identified six populations, representing 54% of the isolated bacteria, as belonging to the genera Acinetobacter and Ochrobactrum. The remaining populations included strains identified as species of the beta-Proteobacteria and high G + C Gram-positive bacteria. The Cr(VI) resistance and reduction ability of the strains were tested. All but two isolates grew in the presence of 1 mmol l(-1) Cr(VI). During enrichment, all isolates were able to survive to 2 mmol l(-1) Cr(VI) and complete Cr(VI) reduction was achieved. Representative strains of each population were able to partially reduce (5.4-39.1%) the Cr(VI) present in the growth medium. CONCLUSIONS: Most of the identified isolates have never been reported to be Cr(VI)-resistant and/or Cr(VI)-reducing strains. The mechanisms of Cr(VI) resistance and reduction may differ from group to group; therefore, it is evident that both Cr(VI) resistance and reduction are shared abilities and not an exclusive characteristic of a single group, possibly reflecting horizontal genetic transfer resulting from selective pressure in this contaminated environment. SIGNIFICANCE AND IMPACT OF THE STUDY: To our knowledge, this is the first study of a microbial community under chronic chromate stress and, as the success of microbial-based metal remediation technologies requires a better understanding of the microbial community and the population response to metal stress, it may contribute to the implementation of a strategy of bioremediation of chromate-contaminated environments.

Bacteria↗

An environmental hazard assessment of low-level dermal exposure to hexavalent chromium in solution among chromium-sensitized volunteers.

To evaluate the potential for elicitation of allergic contact dermatitis from contact with standing water in the environment, 26 persons known to be allergic to hexavalent chromium [Cr(VI)] were exposed to 25 to 29 mg/L Cr(VI) by immersion of one arm for 30 minutes per day on 3 consecutive days in a potassium dichromate bath. Sixteen of the 26 volunteers demonstrated either no or an equivocal response to the Cr(VI) challenge. Ten of the volunteers developed a few papules or vesicles (1 to approximately 15), mild redness, and pruritus on the Cr(VI)-challenged arm. Histopathological examination of the papules revealed spongiosis and perieccrine and perivascular inflammation. The responses were diagnosed as acute perieccrine reactions. It was concluded that exposure to similar concentrations of Cr(VI) in the environment does not pose an allergic contact dermatitis hazard, even to Cr-sensitized persons.

Biopsy↗

Hair chromium as an index of chromium exposure of tannery workers.

The use of hair chromium (Cr) concentrations as an index of Cr exposure of tannery workers was investigated. As has been shown earlier, Cr from Cr III compounds used in the leather tanning industry is absorbed because concentrations of Cr in serum and urine of tannery workers are significantly increased compared with corresponding concentrations for unexposed controls. Hair samples were collected from 71 male tannery workers from four southern Ontario tanneries and from 53 male controls not exposed to Cr in the workplace. Subjects were matched for age, race, and socioeconomic status. Hair samples were washed, ashed in a low temperature asher, and analysed by flameless atomic absorption. The median hair Cr concentrations for the tannery workers (551 ng/g) was significantly higher (p = 0.0001) than for the controls (123 ng/g). For the tannery workers, hair Cr concentrations were positively and significantly correlated with serum Cr (r = 0.52, p less than 0.01) and with the preshift and postshift urinary Cr/creatinine ratios (r = 0.43, p less than 0.01; r = 0.64, p less than 0.01, respectively). These data indicate that trivalent Cr absorbed from leather tanning compounds results in raised concentrations of Cr in hair and that hair Cr concentrations may be used as an index of industrial Cr exposure.

Adult↗

Mild peripheral neuropathy but biochemical chromium sufficiency during 16 months of "chromium-free" total parenteral nutrition.

A 6-yr, 4-month-old boy was started on total parenteral nutrition (TPN) because of chronic diarrhea. The TPN regimen (3 liter/day) initially included supplemented Cr (3 micrograms/day) in addition to standard components (including FreAmine III). At age 8 yr, 8 months, the serum Cr level was elevated: 3.7 ng/ml (normal 0.03-0.85). A repeat level at the same time by another commercial laboratory was also high (7.0). Cr supplementation was stopped. At age 10 yr, he was noted to have mild peripheral neuropathy although glucose tolerance was excellent (alpha-linolenic acid was undetectable in the plasma). Cr status was reevaluated in a research lab. The serum level was 1.4 ng/ml (normal 0.05-0.4). The urine chromium excretion was 1.27 micrograms/day (normal 0.22). The TPN regimen (unsupplemented with Cr) provided 4 micrograms/day. Normal Cr intake is about 60 micrograms/day with 0.4% absorption (net 0.24 microgram/day). We conclude that Cr contamination of standard PN fluid may prevent biochemical evidence of low Cr status. In addition, alpha-linolenic acid-free parenteral nutrition for 46 months was not associated with clinically significant neurological dysfunction.

Child↗

Reductive activation with cysteine represents a chromium(III)-dependent pathway in the induction of genotoxicity by carcinogenic chromium(VI).

Induction of DNA damage by carcinogenic hexavalent chromium compounds [Cr(VI)] results from its reduction to lower oxidation states. Reductive metabolism of Cr(VI) generates intermediate Cr(V/IV)species, organic radicals, and finally Cr(III), which forms stable complexes with many biological ligands, including DNA. To determine the biological significance of different reaction products, we examined genotoxic responses and the formation of DNA damage during reduction of Cr(VI) by its biological reducer, cysteine. We have found that cysteine-dependent activation of Cr(VI) led to the formation of Cr-DNA and cysteine-Cr-DNA adducts as well as interstrand DNA cross-links. The yield of binary and ternary DNA adducts was relatively constant at different concentrations of Cr(VI) and averaged approximately 54 and 45%, respectively. Interstrand DNA cross-links accounted on average for 1% of adducts, and their yield was even less significant at low Cr(VI) concentrations. Reduction of Cr(VI) in several commonly used buffers did not induce detectable damage to the sugar-phosphate backbone of DNA. Replication of Cr(VI)-modified plasmids in intact human fibroblasts has shown that cysteine-dependent metabolism of Cr(VI) resulted in the formation of mutagenic and replication-blocking DNA lesions. Selective elimination of Cr-DNA adducts from Cr(VI)-treated plasmids abolished all genotoxic responses, indicating that nonoxidative, Cr(III)-dependent reactions were responsible for the induction of both mutagenicity and replication blockage by Cr(VI). The demonstration of the mutagenic potential of Cr-DNA adducts suggests that these lesions can be explored in the development of specific and mechanistically important biomarkers of exposure to toxic forms of Cr.

Biomarkers↗

The association of chromium in household dust with urinary chromium in residences adjacent to chromate production waste sites.

Several previous studies of exposure to chromium waste in New Jersey have shown that Cr levels are elevated in household dust in homes adjacent to waste sites and that Cr levels in the urine of residents near sites are also elevated compared to control populations. It has not been possible until now, however, to examine these external and internal measures of exposure together in a large population to determine whether the external exposure is predictive of the internal exposure. We investigated the relationship between various adjusted and unadjusted measures of spot urine Cr concentration and household dust Cr from residents and residences adjacent to known Cr waste sites. Statistically significant bivariate relationships were found between log-transformed urine Cr concentration and Cr dust concentration (micrograms of Cr per gram of dust) but not Cr dust loading (nanogram Cr per square centimeter). Log-transformed urine concentration was used as the dependent variable in multiple regression analysis of the total population (n = 329), the population [less than/equal to] 10 years old (n = 67), and the population >10 years old (n = 262), with Cr dust concentration as a mandatory independent variable. Other potential direct influences on urine Cr were investigated as potential confounders of this relationship. In the final models for the entire population and those [less than/equal to] 10 years old, but not for those >10 years old, Cr dust concentration remained significant. This suggests that exposure of young children to Cr in household dust accounts for much of the relationship in the entire population.

Adolescent↗

Immune response and disease resistance of calves fed chromium nicotinic acid complex or chromium chloride.

Twenty-one Holstein bull calves (< 7 d of age at the initiation of the experiment) fed a milk replacer diet were used to assess the effects of supplemental Cr on immune response. Treatments consisted of milk replacer without supplemental Cr (control) or milk replacer with 0.4 ppm of supplemental Cr from CrCl3 or a Cr-nicotinic acid complex. On d 64, increases in skinfold thickness after an intradermal injection of phytohemagglutinin were measured to evaluate cell-mediated immune response. Calves supplemented with Cr-nicotinic acid complex had a greater response than did controls at 6, 12, 24, and 48 h after injection. Calves supplemented with CrCl3 had a greater response than did controls at 24 and 48 h after injection. In vitro blastogenic responses of lymphocytes to phytohemagglutinin or pokeweed mitogen and antibody response to porcine red blood cells were not affected by treatment. Following a disease challenge with an intranasal dose of infectious bovine rhinotracheitis on d 75, body temperature tended to be lower for calves supplemented with Cr-nicotinic acid complex than for control calves. Calves supplemented with either Cr source had lower serum cortisol concentrations at 5 d after challenge. Chromium supplementation enhanced cell-mediated immune function.

Animals↗

Urinary excretion of chromium by humans following ingestion of chromium picolinate. Implications for biomonitoring.

This study investigated the variability in urinary chromium (Cr) excretion following the ingestion of Cr picolinate by human volunteers. A pharmacokinetic model was used to estimate the bioavailability of Cr from ingested Cr picolinate using known distribution patterns and elimination rates of Cr by humans. The possible advantages of using sequential, individual spot, or 24-hr urine sample collection for biomonitoring of Cr exposure were examined. Background concentrations of urinary Cr determined from the spot samples in this study compared well with values reported by others. The variability in urinary excretion of Cr in untreated volunteers indicated that it is virtually impossible to distinguish exposures to most occupational and virtually all environmental exposures to Cr. Sequential urine sampling was found superior to both 24-hr and spot urine collection for indicating exposure to Cr picolinate. The extent of absorption of Cr from the picolinate matrix in the gastrointestinal tract was 2.80 +/- 1.14% (SD). It was estimated that 10 mg of soil containing between 7,400 and 52,000 mg Cr(III)/kg would have to be ingested by an adult to result in urinary excretion of Cr clearly above the upper bound of Cr in urine from background populations (1.8 microgram Cr/liter), depending on certain assumptions regarding bioavailability. This study supports the results of other recent work that demonstrated urinary excretion of Cr resulting from low-level environmental exposure is unlikely to be distinguished from that resulting from dietary uptake.

Administration, Oral↗

Synthesis of ansa-[n]silacyclopentadienyl-cycloheptatrienyl-chromium complexes (n = 1, 2): novel precursors for polymers bearing chromium in the backbone.

Reaction of [(eta5-C5H4Li)(eta7-C7H6Li)Cr]tmeda with a variety of dialkyl(dichloro)silanes in aliphatic solvents afforded the corresponding [1]silatrochrocenophanes. Structural characterization by X-ray diffraction analysis of the [1]silatrochrocenophanes bearing Me2Si, (iPr)2Si, and silacyclobutane bridges revealed tilt angles alpha of 15.56(12) degrees , 15.8(1) degrees , and 16.33(17) degrees , respectively. Analogously, a [2]silatrochrocenophane (6) was prepared in excellent yield by reaction of [(eta5-C5H4Li)(eta7-C7H6Li)Cr]tmeda with 1,2-dichloro-1,1,2,2-tetramethyldisilane. This complex also was characterized structurally and exhibited a tilt angle alpha of 2.60(15) degrees. The [1]silatrochrocenophane bearing the Me2Si bridge underwent facile and regioselective carbon-silicon bond cleavage with [Pt(PEt3)4] to give a very high yield of an oxidative addition product. The ring-opening polymerization of these novel [1]silatrochrocenophanes afforded ring-opened chromium-based polymers.

Journal Article↗

Pressure-induced switch of the direction of the unique Jahn-Teller axis of the chromium(II) hexaqua cation in the deuterated ammonium chromium Tutton salt.

Inelastic neutron scattering (INS) spectra are presented for chromium(II) Tutton salts, as a function of the temperature and pressure. Transitions are observed between the levels of the 5Ag (Ci) ground term and the data modeled with a conventional S = 2 spin Hamiltonian. At 10 K and ambient pressure, the zero-field-splitting parameters of the ammonium salt, (ND4)2Cr(D2O)6(SO4)2, are determined as D = -2.431(4) cm(-1) and E = 0.091(4) cm(-1), evolving to D = -2.517(4) cm(-1) and E = 0.127(5) cm(-1) upon application of 7.5(1.0) kbar of quasi-hydrostatic pressure. By contrast, the change in the INS spectrum of the rubidium salt in this pressure range is comparitively minor. The results are interpreted using a 5Ee vibronic-coupling Hamiltonian, in which low-symmetry strain, perturbing the adiabatic potential-energy surface, is pressure-dependent. It is argued that, for the ammonium salt, the change with pressure of the anisotropic strain impinging upon the [Cr(D2O)6]2+ cation is sufficient to cause a switch of the long and intermediate Cr-OD2 bonds, with respect to the crystallographic axes.

Journal Article↗

Synthesis and Characterization of Six-Coordinate Nitrido Complexes of Vanadium(V), Chromium(V), and Manganese(V). Isolation of a Dinuclear, Mixed-Valent &mgr;-Nitrido Chromium(III)/Chromium(V) Species.

Photolysis of a series of octahedral monoazido complexes of the type [LM(III)(didentate ligand)(N(3))](n)(+)X(n) of vanadium(III), chromium(III), and manganese(III) in the solid state or in solution yields quantitatively the corresponding six-coordinate nitrido complexes [LM(V)(didentate ligand)(N)](n)(+)X(n) and 1 equiv of dinitrogen. L represents the macrocycle 1,4,7-triazacyclononane or its N-methylated derivative (L'), the didentate ligands are pentane-2,4-dionate (acac), 2,2,6,6-tetramethylheptane-3,5-dionate (tacac), picolinate (pic), phenanthroline (phen), and oxalate (ox), and X(-) represents perchlorate or hexafluorophosphate. The following nitrido complexes were prepared: [LV(V)(N)(acac)](ClO(4)) (6), [LCr(V)(N)(acac)](ClO(4)) (13), [LCr(V)(N)(tacac)](ClO(4)) (14), [LCr(V)(N)(pic)](ClO(4)) (15), [LCr(V)(N)(phen)](ClO(4))(2) (16), [LCr(V)(N)(ox)] (19), [L'Mn(V)(N)(acac)]PF(6) (21). Photolysis of [LCr(III)(N(3))(ox)] (17) in the solid state produces the &mgr;-nitrido-bridged mixed-valent species [L(2)Cr(2)(ox)(2)(&mgr;-N)](N(3)) (18). The structures of the precursor complex [L'Mn(acac)(N(3))]BPh(4) (20), of 13, and of [L'Mn(V)(N)(acac)]BPh(4) (21) have been determined by X-ray crystallography. Complex 13 crystallizes in the orthorhombic space group Pnma, with cell constants a = 27.187(5) Å, b = 9.228(2) Å, c = 7.070(1) Å, V = 1773.7(6) Å(3), and Z = 4; complex 20 crystallizes in the triclinic space group P&onemacr; with a = 14.769(5) Å, b = 16.83(1) Å, c = 16.96(1) Å, alpha = 108.19(5) degrees, beta = 105.06(4) degrees, gamma = 99.78(4) degrees, V = 3719(2) Å(3), and Z = 4; and complex 21 crystallizes in the monoclinic space group P2(1)/n with a = 10.443(3) Å, b = 16.035(4) Å, c = 21.463(5) Å, beta = 95.76(1) degrees, V = 3575.9(14) Å(3), and Z = 4. The Cr(V)&tbd1;N and Mn(V)&tbd1;N distances are short at 1.575(9) and 1.518(4) Å, respectively, and indicate a metal-to-nitrogen triple bond.

Journal Article↗