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PubMed1987

Formation of cyanide after i.v. administration of the oxime HI 6 to dogs.

HI 6(pyridinium, 1-[[[4-(aminocarbonyl)pyridinio]methoxy]-2- [(hydroxyimino)methyl]-dichloride belongs to a series of bisquaternary pyridinium oximes that are effective against poisoning with extremely toxic organophosphates. Since HI 6 has been shown to be unstable at pH 7.4 and to release significant amounts of cyanide, a study was undertaken to determine the degree of cyanide formation from HI 6 in vivo. When HI 6 (100 mumol/kg) was administered i.v. to dogs, the animals showed no signs of cyanide toxicity but exhibited some cholinomimetic symptoms, including retching, hypersalivation and enhanced intestinal motility. Cyanide content in whole blood was monitored after production of methemoglobinemia (30%) by 4-dimethylaminophenol in order to sequester cyanide within red cells. Maximal cyanide contents of 20 mumol/l were found in blood after 90 min. Calculation of the area under the concentration versus time curve for blood cyanide indicates that about 4% of HI 6 produced cyanide. Determination of the pharmacokinetic parameters of HI 6 (VD = 0.31 l/kg; kel = 0.76 h-1) and of cyanide (VD = 0.086 l/kg; kel = 0.52 h-1) together with the apparent first order rate constant of cyanide formation from HI 6 in vitro (0.17 h-1, pH 7.4, 37 degrees) allowed the simulation of a cyanide concentration curve that fitted with the experimental data points, indicating that cyanide formation in vivo was not bio-catalyzed. It is concluded that cyanide formation from HI 6 may not be regarded as a potential hazard, since cyanide elimination exceeded markedly its formation. Whether this conclusion also holds true for man has to be established.

Aminophenols↗
PubMed2003

Biotransformation of cyanide to methane and ammonia by Klebsiella oxytoca.

Klebsiella oxytoca, isolated from cyanide-containing industrial wastewater, was shown to be able to biodegrade cyanide to non-toxic endproducts using cyanide as the sole nitrogen source. In this study, ammonia was one of the detected endproduct of cyanide biodegradation by the concentrated resting cells of K. oxytoca. Moreover, cyanide has been shown to be biotransformed to methane through the actions of concentrated resting cells. Biodegradation of cyanide by cell-free extracts was not observed, which might be due to the inactivation of nitrogenase (an oxygen-labial enzyme) caused by the oxygen exposure after cell disruption. Results show that the cyanide consumption by resting cells of K. oxytoca was induced when the pretreatment of these cells with cyanide was conducted. However, the cyanide-degrading capability of resting cells pretreated with ammonia was inhibited. The inhibition of cyanide degradation by resting cells of K. oxytoca was affected by the ammonia concentration. This might result from the suppression of nitrogenase activity of K. oxytoca by ammonia since nitrogenase was suggested to be the sole cyanide-degrading enzyme during the cyanide degradation process. Results from this study also show that the processes of cyanide biodegradation and ammonia production by resting cells occurred simultaneously. This suggests that the utilization of cyanide as nitrogen source by K. oxytoca might proceed using ammonia as an assimilatory substrate.

Ammonia↗
PubMed1989

Binding of isotopically labeled substrates, inhibitors, and cyanide by protocatechuate 3,4-dioxygenase.

Binding of ligands to the active site Fe3+ of protocatechuate 3,4-dioxygenase is investigated using EPR-detected transferred hyperfine coupling from isotopically labeled substrates, inhibitors, and cyanide. Broadening is observed in EPR resonances from the anaerobic enzyme complex with homoprotocatechuate (3,4-dihydroxyphenylacetate), a slow substrate, enriched with 17O (I = 5/2) in either the 3-OH or the 4-OH group. This shows that this substrate binds directly to the Fe3+ and strongly suggests that an iron chelate can be formed. Cyanide is known to bind to the enzyme in at least two steps, forming first a high spin and then a low spin complex (Whittaker, J. W., and Lipscomb, J. D. (1984) J. Biol. Chem. 259, 4487-4495). Hyperfine broadening from [13C]cyanide (I = 1/2) is observed in the EPR spectra of both complexes, showing that cyanide is an Fe3+ ligand in each case. Cyanide binding is also at least biphasic in the presence of protocatechuate (PCA). The initial high spin enzyme-PCA-cyanide complex forms rapidly and exhibits a unique EPR spectrum. Broadening from PCA enriched with 17O in either the 3-OH or the 4-OH group is detected showing that PCA binds to the iron, probably as a chelate complex. In contrast, no broadening from [13C]cyanide is detected for this complex suggesting that cyanide binds at a site away from the Fe3+. Steady state kinetic measurements of cyanide inhibition of PCA turnover are consistent with two rapidly exchanging cyanide binding sites that inhibit PCA binding and which can be simultaneously occupied. Formation of the nearly irreversible, low spin enzyme-PCA-cyanide complex is competitively inhibited by PCA. Transient kinetics of the formation of this complex are second order in cyanide implying that two cyanides bind. Broadening in the EPR spectrum of this complex is detected from [13C]cyanide, but not from [17O]PCA, suggesting that PCA is displaced. This study provides the first direct evidence for chelation of the active site Fe3+ by substrates and for a small molecule binding site away from the iron in intradiol dioxygenases.

Binding Sites↗
PubMed1977

Pharmacokinetics of cyanide in poisoning of dogs, and the effect of 4-dimethylaminophenol or thiosulfate.

Cyanide in blood, plasma, and urine of dogs after administration of K14CN was determined with the isotope dilution technique. The addition of large amounts of inactive KCN as soon as possible to a sample to be analyzed inhibited the decrease of the original cyanide concentration. After administration of several lethal doses of cyanide into the stomach or by slow intravenous infusion a concentration of about 40 micron cyanide in plasma was found at the moment of respiratory arrest. Since 60% of the cyanide in plasma was bound to proteins the concentration of free cyanide which stopped respiration was about 16 micron. Quick formation of ferrihemoglobin by i.v. injection of 4-dimethylaminophenol after plasma cyanide had risen to or above 40 micron decreased the cyanide concentration in plasma and restored respiration, while cyanide was accumulated in red cells by formation of ferrihemoglobin cyanide. Equilibrium constants calculated for the reaction between ferrihemoglobin and cyanide in vivo indicated that the reaction approached equilibrium in a few minutes. Up to 60% of the radioactive cyanide absorbed was found as non-cyanide radioactivity in the urine.

Animals↗
PubMed1988

The origin of hydrogen cyanide in breath.

The excretion of hydrogen cyanide in breath and blood concentrations of cyanide were measured in eight normal subjects. There was no correlation between breath and blood levels of cyanide. Furthermore, breath cyanide concentrations calculated from blood values were much lower than measured values, which suggested a local production of hydrogen cyanide in the oropharynx. When saliva was incubated at 37 degrees C hydrogen cyanide was formed in the presence of air but not in a nitrogen atmosphere. No hydrogen cyanide was formed with boiled saliva and the production of hydrogen cyanide by native saliva was inhibited by catalase and by 6-n-propyl-thiouracil. Centrifugation of saliva resulted in a supernatant and a sediment, which were both required for the formation of hydrogen cyanide. Dialysis of the supernatant abolished its cyanide forming ability, which could be restored by addition of thiocyanate. We conclude that most of the hydrogen cyanide found in breath from normal human beings originates from oxidation of thiocyanate by salivary peroxidase in the oropharynx. As a consequence measurements of breath hydrogen cyanide can only be used to detect heavy exposure to cyanide.

Adult↗
PubMed2007

Cyanide in the chemical arsenal of garlic mustard, Alliaria petiolata.

Cyanide production has been reported from over 2500 plant species, including some members of the Brassicaceae. We report that the important invasive plant, Alliaria petiolata, produces levels of cyanide in its tissues that can reach 100 ppm fresh weight (FW), a level considered toxic to many vertebrates. In a comparative study, levels of cyanide in leaves of young first-year plants were 25 times higher than in leaves of young Arabidopsis thaliana plants and over 150 times higher than in leaves of young Brassica kaber, B. rapa, and B. napus. In first-year plants, cyanide levels were highest in young leaves of seedlings and declined with leaf age on individual plants. Leaves of young plants infested with green peach aphids (Myzus persicae) produced just over half as much cyanide as leaves of healthy plants, suggesting that aphid feeding led to loss of cyanide from intact tissues before analysis, or that aphid feeding inhibited cyanide precursor production. In a developmental study, levels of cyanide in the youngest and oldest leaf of young garlic mustard plants were four times lower than in the youngest and oldest leaf of young Sorghum sudanense (cv. Cadan 97) plants, but cyanide levels did not decline in these leaves with plant age as in S. sudanense. Different populations of garlic mustard varied moderately in the constitutive and inducible expression of cyanide in leaves, but no populations studied were acyanogenic. Although cyanide production could result from breakdown products of glucosinolates, no cyanide was detected in vitro from decomposition of sinigrin, the major glucosinolate of garlic mustard. These studies indicate that cyanide produced from an as yet unidentified cyanogenic compound is a part of the battery of chemical defenses expressed by garlic mustard.

Brassicaceae↗
PubMed1985

The effects of cyanide and its interactions with norepinephrine on isolated aorta strips from the rabbit, dog, and ferret.

Effects of sodium cyanide on isolated strips of rabbit, dog, and ferret aorta were determined. In the rabbit aorta strip, cumulatively added cyanide caused small contractions beginning at approximately 10(-11) M cyanide and reaching a maximum response at 10(-5) M. A concentration of cyanide between 10(-5) M and 10(-3) M produced relaxation. When cyanide was cumulatively added to norepinephrine (NE)-contracted rabbit aorta strips, no contractions were observed. Cyanide concentrations above 10(-5) M produced relaxation in the NE-contracted vessels. Sensitivity of the aorta strips to NE differed among the species examined. The ED50 for contractions in the dog and ferret aorta was 4 X 10(-4) M and in the rabbit was 5 X 10(-6) M. Pretreatment with cyanide in concentrations up to 10(-2) M did not reduce contractions of dog aorta to NE, although 10(-2) M cyanide abolished contractions of rabbit aorta to NE and reversed NE-contractions of ferret aorta to relaxation. The antagonism of cyanide for NE-induced contractions was completely reversible with cyanide concentrations up to 10(-3) M. Cyanide pretreatment of strips of aorta increased the rate of contraction to NE. A concentration of 10(-2) M cyanide caused small contractions of aorta strips from each species. Thus, cyanide exerts dose and species dependent responses on vascular smooth muscle.

Animals↗
PubMed2004

Receptor mechanisms mediating cyanide generation in PC12 cells and rat brain.

Cyanide is generated in neurons and this report examines the two different receptors which mediate cyanide formation in neuronal tissue. An opiate receptor blocked by naloxone increases cyanide production both in rat brain and in rat pheochromocytoma (PC12) cells. A muscarinic receptor in PC12 cells releases cyanide and the effect is blocked by atropine. In rat brain, in vivo, a muscarinic agonist inhibits cyanide generation, possibly by acting on receptor subtypes different from those in PC12 cells. Cyanide generation by a muscarinic agonist in PC12 cells is blocked by pertussis toxin but that caused by an opiate is not. Thus, two different receptors and two different second messenger systems can mediate cyanide generation in PC12 cells. In parallel with the in vivo data, cultured primary rat cortical cells also show decreased cyanide release following muscarinic stimulation. Both blockade of cyanide generation by muscarinic receptor activation and cyanide release by opiate agonists from cortical cells are pertussis toxin insensitive. Similarly, little cyanide generation was seen following cholera toxin treatment. These data indicate that opiate receptors increase and muscarinic receptors decrease cyanide production in rat brain tissue by G-protein independent mechanisms. This work supports the suggestion that the powerful actions of cyanide may be important for neuromodulation in the CNS.

Analysis of Variance↗
PubMed2004

Characterization and availability of cyanide in solid mine tailings from gold extraction plants.

The aim of this study was to investigate the availability and fate of cyanide in gold mill solid tailings. For this purpose, aged (6-9 years) and recently discharged (3 months) tailings were sampled at various depths from two gold mining sites in Quebec (Canada). A physicochemical characterization of the tailings along with a bacterial enumeration was performed and batch-leaching tests with water and caustic solution were conducted to assess the soluble cyanide fraction. Following the standard acid reflux/distillation method, the total cyanide concentration (CN(T)) in fresh tailings was higher (average of 19.5 +/- 2.0 compared to 3.2 +/- 0.7 mg/kg) and the pH more alkaline (10.6 +/- 0.1 compared to 7.6 +/- 0.2) compared to aged ones. In aged tailings, the enumeration of total heterotrophic (10(4)-10(6) cfu/g) and cyanide-resistant bacteria (10(2)-10(5) cfu/g) showed a significant indigenous microflora, but no growth on agar plates was detected in fresh tailings, suggesting an evolution and a gradual acclimatization of bacterial populations with weathering. Elevated concentrations of CN(T), weak acid dissociable cyanide (CN(WAD)), cyanate (CNO-), and thiocyanate (SCN-) were measured in the supernatant solution of the fresh tailings samples collected in-situ, highlighting their reactivity, whereas these species were not detectable in aged tailings. Accordingly, when batch-leaching tests were performed with fresh samples, 68-72% of the total cyanide was released into aqueous solution with more than 20% being CN(WAD). Again, CN(T) and CN(WAD) were not detectable during leaching of aged tailings. In fresh tailings, approximately 50% of the cyanides were quantifiable with the standard acid reflux/distillation method (readily soluble cyanides, and weak to moderately strong complexes), whereas in aged tailings only 15 to 33% of the actual total cyanide content was measured by the standard method. These results stress the necessity of performing a preliminary alkaline extraction prior to total cyanide determination. In summary, this study revealed a difference in physicochemical properties, cyanide concentration and speciation, viable bacterial populations and cyanide leaching behavior between aged and fresh solid mine tailings. The findings indicate that the more reactive cyanide species initially associated with the solid tailings have naturally degraded within the mine tailings impoundment area, resulting primarily from volatilization (decrease in pH), leaching, and bacterial degradation.

Bacteria↗
PubMed1996

Reaction of E. coli catalase HPII with cyanide as ligand and as inhibitor.

Cyanide forms an inhibitory complex with the haem d-containing E. coli catalase HPII, spectrally similar to the cyanide complex of beef liver enzyme but with absorption bands shifted 90 nm towards the red end of the spectrum. Both the Kd and Ki values are approximately 7 microM in the wild-type enzyme. The cyanide reaction is slow, with a bimolecular 'on' constant approx. 2000 x smaller than that of eukaryotic enzyme, and an 'off' constant diminished by a similar amount. Catalases with a mutated distal histidine (H128) fail to bind cyanide at cyanide concentrations below 50 mM. Catalases with a mutated distal asparagine (N201) show only small changes in cyanide affinity from the wild type. The major fraction of HPII N201A has a Kd approximately 40 microM, and a minor fraction has a lower cyanide affinity; the major fraction of HPII N201Q has a Kd approximately 15 microM. The Kd and Ki for HPII N201D is approximately 8 microM, essentially identical with that of the wild type but N201D appears to bind cyanide somewhat more rapidly than does wild-type enzyme. The HPII mutant N201H can be obtained in both haem d and protohaem forms; it exhibits two types of cyanide binding behaviour. In its protohaem form it binds cyanide poorly (Kd > or = 0.25 mM). After peroxide treatment converts t into haem d or a closely related species it binds cyanide with a much higher affinity (Kd approximately 15 microM). Cyanide binding to HPII requires a distal histidine to provide hydrogen-bonding stability, but not a distal asparagine. Rates of cyanide binding and release are controlled by haem group accessibility through the channel leading to the outside. In HPII N201H channel opening may depend upon oxidation of the haem from the starting protohaem to the final haem d form.

Animals↗
PubMedDate not supplied

Terrorism involving cyanide: the prospect of improving preparedness in the prehospital setting.

The potential for domestic or international terrorism involving cyanide has not diminished and in fact may have increased in recent years. This paper discusses cyanide as a terrorist weapon and the current state of readiness for a cyanide attack in the United States. Many of the factors that render cyanide appealing to terrorists are difficult to modify sufficiently to decrease the probability of a cyanide attack. For example, the relative ease with which cyanide can be used as a weapon without special training, its versatile means of delivery to intended victims, and to a large degree, its ready availability cannot be significantly modified through preparedness efforts. On the other hand, the impact of an attack can be mitigated through preparedness measures designed to minimize the physical, psychological, and social consequences of cyanide exposure. Although the nation remains ill-equipped to manage a cyanide disaster, significant progress is being realized in some aspects of preparedness. Hydroxocobalamin-a cyanide antidote that may be appropriate for use in the prehospital setting for presumptive cases of cyanide poisoning-currently is under development for potential introduction in the US. If it becomes available in the US, hydroxocobalamin could enhance the role of the prehospital emergency responder in providing care to victims of a cyanide disaster. Additional progress is required in the areas of ensuring local and regional availability of antidotal treatment and supportive interventions, educating emergency healthcare providers about cyanide poisoning and its management, and raising public awareness of the potential for a cyanide attack and how to respond.

Cyanides↗
PubMed1994

Alternative routes of enzymic cyanide metabolism in Pseudomonas fluorescens NCIMB 11764.

Cell-free extracts from Pseudomonas fluorescens NCIMB 11764 catalysed the degradation of cyanide into products that included CO2, formic acid, formamide and ammonia. Cyanide-degrading activity (CDA) was localized to cytosolic cell fractions and was observed at substrate concentrations as high as 100 mM (2600 mg CN-I-1). At least two different CDAs could be distinguished by: (i) the determination of reaction product stoichiometries, (ii) requirements for NADH and oxygen, and (iii) kinetic analysis. The first activity produced CO2 and NH3 as reaction products, was dependent on oxygen and NADH for activity, and displayed an apparent Km for cyanide of 1.2 mM. The second activity generated formic acid (and NH3) plus formamide as reaction products, was oxygen independent, and had an apparent Km of 12 mM for cyanide. The first enzymic activity was identified as cyanide oxygenase as previously described [Harris, R. E. & Knowles, C. J. (1983) FEMS Microbiol Lett 20, 337-341] whereas the second activity is believed to consist of two enzymes, a cyanide nitrilase (dihydratase) and hydratase (EC 4.2.1.66). In addition to these enzymes, cyanide-grown cells were also induced for formate dehydrogenase (EC 1.2.1.2) thereby providing a means of recycling NADH utilized by cyanide oxygenase. A mutant strain having lost the ability to grow on cyanide as a nitrogen source was isolated and shown to be defective in cyanide oxygenase, but not the cyanide nitrilase/hydratase enzymes. This finding together with results showing that the substrate affinity of cyanide oxygenase was tenfold greater than for the nitrilase/hydratase enzymes, indicates that it is this enzyme that is most important in cyanide assimilation.(ABSTRACT TRUNCATED AT 250 WORDS)

Ammonia↗
PubMed2005

Bacterial degradation of cyanide and its metal complexes under alkaline conditions.

A bacterial strain able to use cyanide as the sole nitrogen source under alkaline conditions has been isolated. The bacterium was classified as Pseudomonas pseudoalcaligenes by comparison of its 16S RNA gene sequence to those of existing strains and deposited in the Coleccion Espanola de Cultivos Tipo (Spanish Type Culture Collection) as strain CECT5344. Cyanide consumption is an assimilative process, since (i) bacterial growth was concomitant and proportional to cyanide degradation and (ii) the bacterium stoichiometrically converted cyanide into ammonium in the presence of l-methionine-d,l-sulfoximine, a glutamine synthetase inhibitor. The bacterium was able to grow in alkaline media, up to an initial pH of 11.5, and tolerated free cyanide in concentrations of up to 30 mM, which makes it a good candidate for the biological treatment of cyanide-contaminated residues. Both acetate and d,l-malate were suitable carbon sources for cyanotrophic growth, but no growth was detected in media with cyanide as the sole carbon source. In addition to cyanide, P. pseudoalcaligenes CECT5344 used other nitrogen sources, namely ammonium, nitrate, cyanate, cyanoacetamide, nitroferricyanide (nitroprusside), and a variety of cyanide-metal complexes. Cyanide and ammonium were assimilated simultaneously, whereas cyanide strongly inhibited nitrate and nitrite assimilation. Cyanase activity was induced during growth with cyanide or cyanate, but not with ammonium or nitrate as the nitrogen source. This result suggests that cyanate could be an intermediate in the cyanide degradation pathway, but alternative routes cannot be excluded.

Acetates↗
PubMed1985

Investigations of cyanide as an infrared probe of hemeprotein ligand binding sites.

The measurement of infrared spectra for cyanide liganded to hemeproteins and hemins has been investigated. The hemeproteins included human methemoglobin A, lamprey methemoglobin, metchlorocruorin, horse metmyoglobin, and horseradish peroxidase. The hemins were dicyanide and monopyridine monocyanide species of deuteroporphyrin IX iron(III) and its 2,4-divinyl(proto) and 2,4-diacetyl derivatives. C-N stretch bands of low intensity detected near 2100 cm-1 exhibit changes in frequency, width, intensity, and isotope shift with changes in cyanide compound structure. Infrared band parameters are particularly sensitive to a change in oxidation state (Fe2+ versus Fe3+) and are affected to a lesser extent by changes in porphyrin ring substituent, ligand trans to the cyanide, and protein structure. Evidence of multiple conformers (i.e. multiple C-N stretch bands) was found for several hemeproteins. The cyanide infrared spectra provide direct evidence for cyanide binding as a metal cyanide (Fe--C identical to N) and against HCN being the ligand in nitrile-like bonding (Fe--N identical to C--H) in all the hemeprotein and hemin cyanides studied. With the reduced horseradish peroxidase cyanide, differences between infrared spectra for D2O and H2O solutions can result from hydrogen bonding between a protein amino acid residue and the distal atom of the cyanide (Fe--C identical to N...H+--R). The binding of cyanide to reduced iron (Fe2+) of a hemeprotein was only observed in the case of the reduced peroxidase. These findings demonstrate that cyanide infrared spectra can not only determine when cyanide is bound to a metalloprotein but can also provide information on how the cyanide is bonded to metal and on characteristics of the ligand binding site.

Animals↗
PubMed2007

Piezoelectric quartz crystal microbalance sensor for trace aqueous cyanide ion determination.

Using selective reaction chemistry, our present research has developed an online, real-time sensor capable of monitoring toxic cyanide at both drinking water standard and environmental regulatory concentrations. Through the use of a flow cell, aqueous samples containing cyanide are reacted with a gold electrode of a piezoelectric crystal to indirectly sense cyanide concentration by the dissolution of metallic gold. The quartz crystal is an AT-cut wafer sandwiched between two neoprene O-rings within the liquid flow cell. The presence of cyanide in solution results in the selective formation of a soluble dicyano-gold complex according to the Elsner reaction: 4Au + 8CN- + 2H2O + O2 <=> 4Au(CN)2- + 4OH-. The resulting loss of gold from the electrode is detected by the piezoelectric crystal as a resonant frequency change. Since free cyanide is a weak acid (pKa = 9.3), available protons compete for cyanide ligands. Therefore, increased sample pH provides higher sensitivity. The detection limits at pH 12 are 16.1 and 2.7 ppb for analysis times of 10 min and 1 h, respectively. The incorporation of the flow cell improves both analyte sensitivity and instrument precision, with an average signal intensity drift of only 5% over a 2-h analysis. The calibrations show excellent linearity over a variety of cyanide concentrations ranging from low ppb to hundreds of ppm. This detection method offers the advantage of selectively detecting cyanides posing a biohazard while avoiding detection of stable metal cyanides. This aspect of the system is based on competitive exchange of available metals and gold with cyanide ligands. Stable metal cyanide complexes possess a higher formation constant than cyanoaurate. This detection system has been configured into a flow injection analysis array for simple adaptation to automation. Anions commonly found in natural waters have been examined for interference effects. Additionally, the sensor is free from interference by aqueous cyanide analogues including thiocyanate. The developed detection system provides rapid cyanide determinations with little sample preparation or instrument supervision.

Journal Article↗
PubMed1999

Cyanide interaction with redox modulatory sites enhances NMDA receptor responses.

Activation of NMDA receptors plays an important role in cyanide neurotoxicity. Cyanide indirectly activates the receptor by inducing neuronal release of glutamate and also enhances receptor-mediated responses by a direct interaction with the receptor complex. This study investigated the mechanism in cerebellar granule cells by which cyanide enhances NMDA-induced Ca2+ influx. Cyanide (50 microM) increased the influx of Ca2+ over the NMDA concentration range of 0.5-500 microM. Experiments showed that cyanide does not interact with the receptor's glycine or PKC mediated phosphorylation regulatory sites. N-ethylmaleimide, a thiol alkylating agent which inactivates the redox regulatory sites of the receptor, blocked the enhancing effect of cyanide. Pretreatment of cells with 5,5-dithio-bis-2-nitrobenzoic acid (DTNB), a compound that oxidizes the receptor redox sites, had no effect on the response to cyanide. On the other hand, the nonpermeant reducing agents, dithiothreitol or cysteine, further increased the cyanide effect. These observations can be explained by cyanide interacting with redox sensitive disulfide groups that are not accessible to the non-permeant reducing agents. It is proposed that cyanide interacts with a redox site(s) located either on the intracellular receptor domain or in the transmembrane hydrophobic domain. Furthermore the enhancement by cyanide of the excitotoxic actions of NMDA involves receptor sites that are sensitive to oxidation/reduction and this interaction contributes to the neurotoxic action of cyanide.

Animals↗
PubMed2000

Cyanide-induced apoptosis involves oxidative-stress-activated NF-kappaB in cortical neurons.

The central nervous system is one of the main target organs in cyanide toxicity. Primary cultured cortical neurons were used to study the cellular mechanisms underlying cyanide-induced cytotoxicity. After exposure to KCN (100-300 microM) for 24 h, cortical neurons underwent apoptosis as characterized by positive TUNEL staining. Reactive oxygen species (ROS) play an important role in cyanide-induced neuronal apoptosis; immediately after cyanide (100-300 microM) treatment, ROS generation was observed and continued to be elevated for up to 3 h. NMDA receptor activation and subsequent Ca(2+) influx contribute in part to cyanide-induced ROS formation, since the selective NMDA receptor antagonist MK801 and intracellular Ca(2+) chelator BAPTA blocked ROS generation. Interestingly, caspases, recently reported to be involved in neuronal apoptosis, play a role in the late phase of ROS production after cyanide stimulation. Z-VAD, a nonspecific caspase inhibitor, blocked ROS generated 1 h after cyanide treatment, but it had no effect on ROS generated immediately after cyanide treatment. Nuclear factor kappaB (NF-kappaB), a redox-sensitive transcription factor, was activated dose dependently after cyanide treatment. Blockade of ROS generation by MK801, Z-VAD, and various antioxidants also blocked the activation of NF-kappaB. SN50, a synthetic peptide which inhibits the nuclear translocation of NF-kappaB, blocked cyanide-induced apoptotic cell death. These results indicate that NF-kappaB plays an important role in cyanide-induced apoptosis in cortical neurons, and the caspases may contribute in part to the activation of NF-kappaB after cyanide treatment by inducing the late phase of ROS generation.

Animals↗
PubMed1991

Metabolism of cyanide by Phanerochaete chrysosporium.

The oxidation of veratryl alcohol (3,4-dimethoxybenzyl alcohol) by lignin peroxidase H2 (LiP H2) from the white rot fungus Phanerochaete chrysosporium was strongly inhibited by sodium cyanide. The I50 was estimated to be about 2-3 microM. In contrast, sodium cyanide binds to the native enzyme with an apparent sodium cyanide dissociation constant Kd of about 10 microM. Inhibition of the veratryl alcohol oxidase activity of LiP H2 by cyanide was reversible. Ligninolytic cultures of P. chrysosporium mineralized cyanide at a rate that was proportional to the concentration of cyanide to 2 mM. The N-tert-butyl-alpha-phenylnitrone-cyanyl radical adduct was observed by ESR spin trapping upon incubation of LiP H2 with H2O2 and sodium cyanide. The identity of the spin adduct was confirmed using 13C-labeled cyanide. Six-day-old cultures of the fungus were more tolerant to sodium cyanide toxicity than spores. Toxicity measurements were based on the effect of sodium cyanide on respiration of the fungus as determined by the metabolism of [14C]glucose to [14C]CO2. We propose that this tolerance of the mature fungus was due to its ability to mineralize cyanide and that this fungus might be effective in treating environmental pollution sites contaminated with cyanide.

Alcohol Oxidoreductases↗