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An extremely bent cyanide bridge in crystals of [(CN)3Pt(mu-CN)Cu(NH3)4]. Influence of electrostatic forces on the nature and geometry of bridging cyanides in the solid state.

The dinuclear heterometallic complex [(CN)3Pt(mu-CN)Cu(NH3)4] has been obtained in the solid state, and its structure has been determined by X-ray diffraction techniques at two temperatures (102 and 233 K). C4H12CuN8Pt crystallizes in the orthorhombic system, with a = 14.554(3) A, b = 7.1901(12) A, c = 10.369(2) A, and V = 1085.1(3) A3 at 102 K (a = 14.5091(10) A, b = 7.2739(4) A, c = 10.4570(7) A, and V = 1103.61(12) A3 at 233 K), in space group Pnma, with Z = 4. The Pt and Cu atoms are linked by a CN bridge that presents a very bent C identical to N-Cu angle (120.1(6) degrees at 102 K). The C identical to N and N-Cu distances at 102 K are 1.147(10) and 2.394(7) A, respectively. [(CN)3Pt(mu-CN)Cu(NH3)4] is embedded in an extensive electrostatic net formed by (N)H...N(C) interactions which, it is concluded, play an important role in the extreme deviation from linearity observed for the C identical to N-Cu angle.

Journal Article↗

Cyanide-sensitive and Cyanide-resistant Respiration in the Germination of Cocklebur Seeds.

Interrelation between the CN-sensitive cytochrome path and the CN-resistant, benzohydroxamic acid (BHM)-sensitive, or n-propylgallate (nPG)-sensitive alternative path in seed respiration during germination was examined using the nondormant upper and lower seeds of Xanthium pensylvanicum Wallr. The operation of both paths was required not only for normal germination of the lower seed but also for KCN- or NaN(3)-induced germination of both. From the sensitivity to BHM of the germination response, it became obvious that the alternative path exerts its physiological activity as soon as it develops during the early period of water imbibition. Pretreatments with KCN and NaN(3) for promoting germination, strikingly decreased only the engagement of the cytochrome path in the subsequent respiration without affecting that of the alternative path. Nevertheless, no germination occurred without the operation of the cytochrome path. This suggested that excess operation of the cytochrome path is detrimental to germination, being maximal following the BHM-sensitive phase.The alternative and cytochrome paths operated in a proportion of 1 to 5 in a period just before the lower seeds started to germinate. However, there was little difference between the upper seeds of relatively low germination potential and the lower seeds of relatively high potential with respect to both the developmental pattern of the alternative path and the balance of the alternative and cytochrome paths. The higher germination potential of the lower seeds may be related to their high capacities for the alternative path.

Journal Article↗

NTP Toxicity Studies of Sodium Cyanide (CAS No. 143-33-9) Administered by Dosed Water to F344/N Rats and B6C3F1 Mice.

Cyanide and its salts are used extensively in industry and manufacturing and are found in water and food consumed by humans. Chronic exposure to low levels of cyanide is suspected to be responsible for various neuropathic and thyrotoxic conditions in humans. Data in the literature indicate that long-term exposure to near-lethal concentrations of cyanide may produce lesions in rodents similar to those linked to chronic cyanide exposure in humans. However, few data are available on the effects of subchronic exposure to cyanide concentrations that are not acutely toxic. To address this lack of data, 13-week toxicity studies on cyanide were conducted with male and female F344/N rats and B6C3F1 mice administered low doses of sodium cyanide in drinking water. Animals were evaluated for histopathology, clinical chemistry, hematology, urine chemistry, and reproductive toxicity. In addition, the mutagenicity of sodium cyanide was assessed in Salmonella typhimurium. Groups of 10 rats and 10 mice per sex were administered sodium cyanide in drinking water at concentrations of 0, 3, 10, 30, 100, and 300 ppm for 13 weeks. No deaths attributed to sodium cyanide administration occurred in either species. In animals exposed to 300 ppm, male rats had slightly lower final mean body weights and mean body weight gains and female mice had slightly lower final mean body weights than the respective controls. Water consumption by rats and mice in the 100 and 300 ppm groups was 10% to 30% lower than that by the controls; however, no clinical signs attributable to sodium cyanide administration or to dehydration were observed. No gross or microscopic changes specifically related to cyanide toxicity occurred at any site in males or females of either species. In particular, no lesions were found in the brain or thyroid gland. Differences between absolute and relative organ weights of exposed and control animals were minor and sporadic and were not exposure concentration dependent; these differences were not considered to be related to sodium cyanide administration. Hematologic, clinical chemistry, and urinalysis evaluations of rats and mice revealed minimal changes that were not considered biologically significant, although the decreased urine volume and increased urine specific gravity observed in male rats in the 300 ppm group of the supplemental clinical pathology study were consistent with the observed decreases in water consumption. The concentration of urinary thiocyanate (the primary metabolite of cyanide) increased with increasing exposure concentration at all time points. Sperm motility and vaginal cytology examinations were performed on rats and mice in the 0, 30, 100, and 300 ppm groups. Sodium cyanide caused a slight reduction in cauda epididymal weight in all groups of exposed male rats and in male mice exposed to 300 ppm. In male rats, the number of spermatid heads per testis in the 300 ppm group was less than the number in the controls, and sperm motility in all exposed groups was marginally lower than in the controls. Sodium cyanide produced no adverse effects on estrous cyclicity in female mice, but at higher concentrations (100 and 300 ppm), sodium cyanide caused a significant increase in the amount of time spent by female rats in proestrus and diestrus relative to estrus and metestrus. Sodium cyanide was not mutagenic in Salmonella typhimurium strain TA100, TA1535, TA97, or TA98 with or without exogenous metabolic activation. In summary, administration of low concentrations of sodium cyanide in drinking water to rats and mice for 13 weeks resulted in no clinically significant body weight, organ weight, histopathologic, or clinical pathology changes. The absorption of administered cyanide was confirmed by increases in urinary thiocyanate excretion. Concentrations of 100 ppm and greater resulted in reduced water consumption. Thus, higher concentrations of sodium cyanide could not be administered by the drinking water route of administration. Alterations in reproductive parameters indicate that subchronic exposure to low concentrations of sodium cyanide may produce mild but significant adverse effects on rat reproductive systems. These changes are probably insufficient to decrease fertility in rats; however, humans are considered to be relatively more sensitive to such changes than rats, and the potential for reproductive toxicity in humans from low concentrations of cyanide warrants further investigation. NOTE: These studies were supported in part by funds from the Comprehensive Environmental Response, Compensation, and Liability Act trust fund (Superfund) by an interagency agreement with the Agency for Toxic Substances and Disease Registry, U.S. Public Health Service.

Journal Article↗

Evaluation and testing of analytical methods for cyanide species in municipal and industrial contaminated waters.

Total cyanide analysis by distillation is used most commonly to assess cyanide content of water samples. This manual method is robust but slow and provides no information about cyanide speciation, a significant limitation in that cyanide species have substantially different toxicity characteristics. Seven alternative methods for the analysis of cyanide species or groups of species were evaluated in reagent water and five different contaminated water matrices, including five species-specific methods--weak acid dissociable (WAD) cyanide, free cyanide by microdiffusion, available cyanide, automated WAD cyanide by thin film distillation, metal cyanides by ion chromatography--and two automated techniques for total cyanide--total cyanide bythin film distillation and total cyanide by low-power UV digestion. The species-specific cyanide analytical techniques achieved low, ppb-level detection limits and exhibited satisfactory accuracy and precision for most contaminated waters. Analysis of low concentrations of cyanide species in raw wastewater was problematical for the available cyanide and ion chromatography methods, which experienced significant interference problems and/or low recoveries. There was recovery of significant diffusible cyanide in microdiffusion tests with nickel-cyanide-spiked samples, reflecting dissociation of this weak metal-cyanide complex during the test and demonstrating that the test can recover some fraction of WAD cyanide in addition to free cyanide. The automated total cyanide methods, which involve UV digestion, achieved low detection limits for most waters but exhibited low recoveries for some waters.

Chromatography, Ion Exchange↗

Cyanide hazards to plants and animals from gold mining and related water issues.

Cyanide extraction of gold through milling of high-grade ores and heap leaching of low-grade ores requires cycling of millions of liters of alkaline water containing high concentrations of potentially toxic sodium cyanide (NaCN), free cyanide, and metal-cyanide complexes. Some milling operations result in tailings ponds of 150 ha and larger. Heap leach operations that spray or drip cyanide onto the flattened top of the ore heap require solution processing ponds of about 1 ha in surface area. Puddles of various sizes may occur on the top of heaps, where the highest concentrations of NaCN are found. Solution recovery channels are usually constructed at the base of leach heaps, some of which may be exposed. All these cyanide-containing water bodies are hazardous to wildlife, especially migratory waterfowl and bats, if not properly managed. Accidental spills of cyanide solutions into rivers and streams have produced massive kills of fish and other aquatic biota. Freshwater fish are the most cyanide-sensitive group of aquatic organisms tested, with high mortality documented at free cyanide concentrations >20 microg/L and adverse effects on swimming and reproduction at >5 microg/L. Exclusion from cyanide solutions or reductions of cyanide concentrations to nontoxic levels are the only certain methods of protecting terrestrial vertebrate wildlife from cyanide poisoning; a variety of exclusion/cyanide reduction techniques are presented and discussed. Additional research is recommended on (1) effects of low-level, long-term, cyanide intoxication in birds and mammals by oral and inhalation routes in the vicinity of high cyanide concentrations; (2) long-term effects of low concentrations of cyanide on aquatic biota; (3) adaptive resistance to cyanide; and (4) usefulness of various biochemical indicators of cyanide poisoning. To prevent flooding in mine open pits, and to enable earth moving on a large scale, it is often necessary to withdraw groundwater and use it for irrigation, discharge it to rapid infiltration basins, or, in some cases, discharge it to surface waters. Surface waters are diverted around surface mining operations. Adverse effects of groundwater drawdown include formation of sinkholes within 5 km of groundwater drawdown; reduced stream flows with reduced quantities of wate available for irrigation, stock watering, and domestic, mining and milling, and municipal uses; reduction or loss of vegetation cover for wildlife, with reduced carrying capacity for terrestrial wildlife; loss of aquatic habitat for native fishes and their prey; and disruption of Native American cultural traditions. Surface discharge of excess mine dewatering water and other waters to main waterways may contain excess quantities of arsenic, total dissolved solids, boron, copper, fluoride, and zinc. When mining operations cease, and the water pumps are dismantled, these large open pits may slowly fill with water, forming lakes. The water quality of pit lakes may present a variety of pressing environmental problems.

Animals↗

Laser lithotripsy and cyanide.

BACKGROUND AND PURPOSE: Holmium:YAG lithotripsy of uric acid calculi produces cyanide. The laser and stone parameters required to produce cyanide are poorly defined. In this study, we tested the hypotheses that cyanide production: (1) varies with holmium:YAG power settings; (2) varies among holmium:YAG, pulsed-dye, and alexandrite lasers; and (3) occurs during holmium:YAG lithotripsy of all purine calculi. MATERIALS AND METHODS: Holmium:YAG lithotripsy of uric acid calculi was done using various optical fiber diameters (272-940 microm) and pulse energies (0.5-1.5 J) for constant irradiation (0.25 kJ). Fragmentation and cyanide were quantified. Cyanide values were divided by fragmentation values, and fragment sizes were characterized. To test the second hypothesis, uric acid calculi were irradiated with Ho:YAG, pulsed-dye, and alexandrite lasers. Fragmentation and cyanide were measured, and cyanide per fragmentation was calculated. Fragment sizes were characterized. Finally, Ho:YAG lithotripsy (0.25 kJ) of purine and nonpurine calculi was done, and cyanide production was measured. RESULTS: Fragmentation increased as pulse energy increased for the 550- and 940-microm optical fibers (P < 0.05). Cyanide increased as pulse energy increased for all optical fibers (P < 0.002). Cyanide per fragmentation increased as pulse energy increased for the 272-microm optical fiber (P = 0.03). Fragment size increased as pulse energy increased for the 272-microm, 550-microm, and 940-microm optical fibers (P < 0.001). The mean cyanide production from 0.25 kJ of optical energy was Ho:YAG laser 106 microg, pulsed-dye 55 microm, and alexandrite 1 microg (P < 0.001). The mean cyanide normalized for fragmentation (microg/mg) was 1.18, 0.85, and 0.02, respectively (P < 0.001). The mean fragment size was 0.6, 1.1, and 1.9 mm, respectively (P < 0.001). After 0.25 kJ, the mean amount of cyanide produced was monosodium urate stones 85 microg, uric acid 78 microg, xanthine 17 microg, ammonium acid urate 16 microg, calcium phosphate 8 microg, cystine 7 microg, and struvite 4 microg (P < 0.001). CONCLUSIONS: Cyanide production varies with Ho:YAG pulse energy. To minimize cyanide and fragment size, Ho:YAG lasertripsy is best done at a pulse energy < or = 1.0 J. Cyanide production from laser lithotripsy of uric acid calculi varies among Ho:YAG, pulsed-dye, and alexandrite lasers and is related to pulse duration. Cyanide is produced by Ho:YAG lasertripsy of all purine calculi.

Cyanides↗

Mechanism of antagonizing cyanide-induced lethality by alpha-ketoglutaric acid.

alpha-Ketoglutaric acid (alpha-KG) has been shown to be an effective antagonist for cyanide-induced lethality. The mechanism of this antagonism is hypothesized to result from alpha-KG binding with cyanide. Several investigative approaches were taken to determine the existence of this binding. First, mixtures of various molar ratios of alpha-KG:cyanide were injected into a high pressure liquid chromatograph. The addition of cyanide reduced the peak area of alpha-KG at a molar ratio of greater than 1:5. Second, blood from naive male ICR mice was spiked with alpha-KG and cyanide. Headspace above these blood samples was injected into a gas chromatograph and analyzed for released hydrogen cyanide. alpha-KG reduced the peak area of hydrogen cyanide released into the headspace at molar ratios of greater than 1:2.5. Third, the effect of cyanide on the ultraviolet spectrum of alpha-KG was determined as an indication of binding. In the presence of cyanide the absorption peak at 316 nm for alpha-KG was eliminated. Inhibition of cytochrome oxidase is an accepted target enzyme for cyanide-induced lethality. Fourth, further evidence of alpha-KG's mechanism was determined by the effect of alpha-KG on brain cytochrome oxidase (BRCYTOX) and its ability to antagonize cyanide-induced inhibition of BRCYTOX. BRCYTOX activity was determined in the presence of alpha-KG and was found to be unaffected between 0.01 and 0.06 M of alpha-KG. Greater concentrations of alpha-KG inhibited BRCYTOX activity. The complete inhibition of BRCYTOX activity by 10(-5) M cyanide was prevented with 0.05 and 0.06 M alpha-KG. Fifth, BRCYTOX activity of animals pretreated with saline and then an LD80 dose (8.5 mg/kg) of cyanide was 80% inhibited, while BRCYTOX activity of animals pretreated with 2 g alpha-KG/kg, i.p., and then an LD80 dose (7.75 mg/kg) of cyanide was not different from control values. Thus, these data suggest that alpha-KG does bind with cyanide, and this binding can account for the antagonism of cyanide-induced lethality.

Animals↗

Chemistry, toxicology, and human health risk of cyanide compounds in soils at former manufactured gas plant sites.

Cyanide-containing wastes are commonly found in soils at former manufactured gas plant (MGP) sites, also known as town gas sites. The complex forms of cyanide are responsible for the blue-stained soils and rocks found at these sites. Most concentrations of cyanide at MGP sites are below 2000 ppm, although concentrations greater than 20,000 ppm have been observed. An understanding of the chemistry of the MGP cyanide-containing compounds, their fate, and transport as well as their toxicology is critical to accurately assessing potential human health risks from these compounds. In this paper, the authors demonstrate that the most prevalent types of cyanide compounds found at former MGP sites are the relatively nontoxic iron-complexed forms, such as ferric ferrocyanide, rather than the highly toxic free cyanide forms. Moreover, the chemical conditions at most former MGP sites limit the extent to which free cyanide may be released into air and water from complex cyanides. Using a screening analysis, the authors estimate potential risks from a multiroute exposure to complex and free cyanides in soil, air, and groundwater at former MGP sites and demonstrate that such risks are likely to be insignificant. Unfortunately, the lack of readily available measurement techniques to characterize cyanides in soil can result in erroneous conclusions about potential risks from cyanide compounds in soils at former MGP sites, particularly if health-based soil criteria for free cyanide (e.g., the Massachusetts Department of Environmental Protection criterion for free cyanide is 100 ppm (MA. DEP, 1995)) are applied. The authors recommend development of routine methods for field sampling and laboratory testing techniques to demonstrate that cyanides in soil at former MGP sites are predominated by iron-complexed species and that free cyanide is less than levels of concern.

Animals↗

Accumulation of labeled cyanide in neuronal tissue.

Since cyanide is a reactive chemical substance and has the potential of forming a variety of adducts in biological systems, the rate of accumulation of labeled cyanide was studied in neural tissue, a major target for the toxic action of cyanide. Accumulation of 14CN in mouse brain slices and in rat pheochromocytoma (PC12) cells was about five times more rapid in the first few minutes than at later times. In both tissues, incubation at low temperature (4 degrees C) decreased the secondary phase without affecting the initial phase. In PC12 cells, determination of the subcellular distribution of cyanide revealed that the cytoplasmic fraction was the least sensitive to temperature and therefore may represent the initial rapid phase of cyanide accumulation. Accumulation of cyanide in mitochondrial and microsomal fractions was temperature sensitive. Cyanide accumulation is proportional to the concentration in the medium (0.1-1 mM) in both mouse brain and PC12 cells suggesting that the cyanide sinks in neural tissue have a large capacity and are nonspecific. Cyanide interaction with neural tissue is not uniform since cyanide accumulated more in hypothalamus than in other brain areas. Despite this, mitochondrial enzyme activity was no greater in hypothalamus than in other brain areas. No increase in thiocyanate, the main metabolite of cyanide, could be detected in brain tissue incubated 30 min with 1 mM cyanide, showing that accumulated 14C is not in the form of thiocyanate. Cyanide appears to equilibrate rapidly across the plasma membrane and then slowly accumulates in mitochondria and membrane elements of the neuronal cell. Competition for cyanide among subcellular elements may be a factor in the toxic action of cyanide.

Analysis of Variance↗

Natural attenuation potential of cyanide via microbial activity in mine tailings.

Biological removal by indigenous microflora of cyanide, contained in old (6-9 years) and fresh tailings (3 months), was studied in order to assess its natural attenuation potential via biodegradation. To investigate the presence of indigenous microflora in tailings, total heterotrophic and cyanide resistant bacteria were counted using the spread-plate method. The free cyanide mineralization potential was estimated using K14CN in the presence of various unlabeled cyanide concentrations (0, 5, and 10 mg CN/kg). The biodegradation of cyanide contained initially in the samples was also investigated by monitoring formate, formamide, ammonia and total cyanide (CNT) concentrations over 111 days. The enumeration of total heterotrophic and cyanide-resistant bacteria in old tailings showed an average population of 105 cfu/g. However, no growth was detected in fresh tailings. Nevertheless, cyanide mineralization tests indicated the presence, in both old and fresh tailings, of a cyanide-degrading microflora. In old tailings, maximum mineralization percentages of free cyanide ranging from 85% to 100% were obtained after 65 days at all concentrations tested. A mineralization percentage of 83% after 170 days was also observed in fresh tailings. No decrease of total cyanide concentration in old tailings was observed when the biodegradation of endogenous cyanide was tested whereas a significant decrease was recorded in fresh tailings after 96 days. The presence of strong metal-cyanide complexes resistant to biodegradation could explain the absence of biodegradation in old tailings. This study demonstrated the presence of an indigenous free cyanide-degrading microflora in both old and fresh tailings, and suggests that natural attenuation of cyanide in gold mine tailings is likely to occur via microbial activity.

Bacteria↗

Comparative metabolism of methacrylonitrile and acrylonitrile to cyanide using cytochrome P4502E1 and microsomal epoxide hydrolase-null mice.

Methacrylonitrile (MAN) and acrylonitrile (AN) are metabolized via glutathione (GSH) conjugation or epoxide formation. We have recently shown that CYP2E1 is essential for AN epoxidation and subsequent cyanide liberation. Current studies were designed to compare the enzymatic basis of MAN vs. AN metabolism to cyanide using wild-type (WT), CYP2E1-, and mEH-null mice. Mice received a single gavage dose of 0.047, 0.095, 0.19, or 0.38 mmol/kg of MAN or AN, and blood cyanide was measured at 1 or 3 h later. Blood cyanide levels in WT mice treated with AN or MAN were dose and time dependent. At equimolar doses, significantly higher levels of cyanide were detected in the blood of MAN- vs. AN-treated mice. Further, while significant reduction in blood cyanide levels occurred in MAN-treated CYP2E1-null vs. WT mice, AN metabolism to cyanide was largely abolished in CYP2E1-null mice. Pretreatment of mice with 1-aminobenzotriazole (ABT, CYP inhibitor) demonstrated that CYPs other than CYP2E1 also contribute to MAN metabolism to cyanide. Blood cyanide levels in mEH-null mice treated with aliphatic nitriles are generally lower than levels in similarly treated WT mice. Western blot analysis showed that expression of sEH was greater in male vs. female mice. The role of various epoxide hydrolases (EHs) in the production of cyanide from aliphatic nitriles is apparently structure and dose dependent. Regardless of genotype, significantly higher levels of cyanide were measured in the blood of male vs. female mice treated with MAN or AN. In conclusion, these data showed that (1) at equimolar doses, higher blood cyanide levels were detected in mice treated with MAN vs. AN; (2) while CYP2E1 is the only enzyme responsible for AN metabolism to cyanide, other CYPs also contribute to MAN metabolism; and (3) significantly higher levels of cyanide were measured in the blood of male vs. female treated with either nitrile. Higher blood cyanide levels in male vs. female mice and in MAN- vs. AN-treated mice may explain the gender-related differences in the toxicity of these chemicals and the greater potency of MAN vs. AN.

Acrylonitrile↗

Phytotoxicity of cyanide to weeping willow trees.

BACKGROUND: Cyanide is found predominantly in industrial effluents generated by metallurgical operations. It is an extremely toxic compound, so that problems and catastrophic accidents have recently occurred all around the globe. The goal of this study was to determine the toxicity of cyanide to a Chinese willow species, and to determine the removal capacity. METHODS: The toxicity of potassium cyanide (KCN) to weeping willow trees (Salix babylonica L.) was tested. The normalized, relative transpiration of the plants was used to determine the phytotoxicity of cyanide. The cyanide removal capacity of weeping willows was also determined. RESULTS AND DISCUSSION: In hydroponic solution, no chlorosis of leaves and only a small reduction in normalized relative transpiration was observed when weeping willows were exposed to low doses of cyanide (< or = 0.93 mg CN/L). Severe signs of toxicity were found for the treatment groups exposed to higher doses of cyanide (> or = 9.3 mg CN/L). Weeping willows grown in sandy soils survived the entire period (216 hours) without any toxic effect when irrigated with low doses of cyanide (3.72 mg CN/L). High doses of cyanide (> or = 18.6 mg CN/L) in irrigation water were fatal for the weeping willows within 216 hours. EC50 values for a 50% inhibition of the transpiration of the trees were estimated to be between 3.27 and 8.23 mg CN/L, depending on the duration of the exposure. CONCLUSIONS: The results obtained for the Chinese willow species Salix babylonica were very similar to those obtained for the European species S. viminalis in earlier studies. Phytotoxic effects were only found at high doses of cyanide. A large proportion of applied cyanide was removed from the contaminated media in the presence of weeping willows. This gives rise to the conclusion that the metabolism of cyanide by weeping willows is possible. RECOMMENDATIONS AND OUTLOOK: Cyanide elimination with trees seems to be a feasible option for cleaning soils and water contaminated with cyanide. A full-scale treatment has been installed in Denmark. For phytoremediation projects in China, weeping willow could be a suitable species. The tree can tolerate and remove cyanide, and it is a native Chinese species. Besides, the tree is of outstanding beauty and is planted as a common park tree in many parts of the world.

Biodegradation, Environmental↗

Experimentally induced chromosome aberrations in plants. I. The production of chromosome aberrations by cyanide and other heavy metal complexing agents.

The finding of Lilly and Thoday that potassium cyanide produces structural chromosome changes in root tips of Vicia faba was confirmed. Like mustards, diepoxides, and maleic hydrazide, potassium cyanide seems to act on cells at early interphase. A tendency of cyanide breaks to be concentrated in heterochromatic segments of the chromosomes was evident. The production of chromosome aberrations by cyanide proved to be practically unaffected by the temperature during treatment. In agreement with Lilly and Thoday, the effect of potassium cyanide was found to be dependent on oxygen tension during treatment. The effect of potassium cyanide increases with increasing oxygen concentration up to 100 per cent oxygen. In the absence of oxygen, potassium cyanide was not completely inactive, but produced a low, though significant frequency of aberrations. Pretreatments with 2.4-dinitrophenol did not influence the effect of potassium cyanide. When bean roots were treated with potassium cyanide before a treatment with 8-ethoxycaffeine, or at the same time as they were treated with 8-ethoxycaffeine, the effect of 8-ethoxycaffeine was almost completely suppressed. The effects of a number of other heavy metal complexing agents were also tested. Sodium fluoride, potassium thiocyanate, carbon monoxide, o-phenanthroline, 2.2-bipyridine, and sodium azide were without radiomimetic effect under the conditions employed, and so was a mixture of sodium azide and sodium fluoride. A low, but quite significant, radiomimetic effect was obtained after treatments with sodium diethyldithiocarbamate, cupferron, and 8-hydroxyquinoline. Under anaerobic conditions, the effects of cyanide and cupferron were both quantitatively and qualitatively indistinguishable. Unlike the effect of cyanide, the effect of cupferron was not enhanced by the presence of oxygen. The effects of the same heavy metal complexing agents were tested on the activities of the enzymes catalase and peroxidase. The activities of both of these enzymes were found to be totally inhibited only by potassium cyanide. In the other cases, little correlation was found between ability to inhibit the activities of these enzymes and ability to produce chromosome aberrations. In a number of experiments, hydrogen peroxide was found to be without radiomimetic effect, whether alone or in combination with potassium cyanide. t-Butyl hydroperoxide proved to be active. The effect of t-butyl hydroperoxide was substantially increased by pretreatments with 2.4.-dinitrophenol. The results are discussed, and it is concluded that the observations made do not support the hypothesis that hydrogen peroxide is involved in the production of chromosome aberrations by potassium cyanide. The possibility that organic peroxides are involved cannot be excluded on the bases of the experimental results. As an alternative hypothesis, it is suggested that iron or other heavy metals are present in the chromosomes and that cyanide and other heavy metal complexing agents produce chromosome aberrations by reacting with these metals.

Caffeine↗

Antidotal treatment of cyanide poisoning.

Cyanide poisoning may result from different exposures: residential fires, industrial accidents, drug and plant intoxication. Clinical features include coma, respiratory arrest and cardiovascular collapse. The biological hallmark is lactic acidosis. A plasma lactate concentration > or = 10 mmol/L in fire victims without severe burns and > or = 8 mmol/L in pure cyanide poisoned patients is a sensitive and specific indicator of cyanide intoxication. Many antidotes are available and efficient. However, therapeutic strategies are still debated. Our objective was to compare conventional treatments to hydroxocobalamin. This article reviews the literature on cyanide poisoning treatment. Conventional treatment of cyanide poisoning includes decontamination, supportive and specific treatment. Decontamination should be adapted to the route of poisoning and never postpone supportive treatment. Basic life support includes immediate administration of high flow of oxygen, airway protection and cardiopulmonary resuscitation. Advanced life support includes mechanical ventilation, catecholamine and sodium bicarbonate infusion. Supportive treatment is efficient but does not modify the time course or the body burden of cyanide. Numerous antidotes are available. Oxygen counteracts efficiently cyanide action at the mitochondrial level. Sodium thiosulfate, methemoglobin forming agents and cobalt compounds act efficiently by complexing or transforming cyanide into non-toxic stable derivatives. However, regarding the main clinical condition of cyanide poisoning, i.e. smoke inhalation, we should take into account not only the efficiency of antidotes but also their safety. Sodium thiosulfate is both efficient and safe, but acts with delay. Methemoglobin-forming agents are potent, but due to the transformation of hemoglobin into methemoglobin, they impair tissue delivery of oxygen. Experimental data showed increased mortality in carbon monoxide- and cyanide-poisoned rats treated with these agents. Cobalt EDTA and hydroxocobalamin are efficient and act immediately. Cobalt EDTA is more potent on a molar basis; however, numerous side effects limit its use to evidenced cyanide poisoning. In a prospective study, hydroxocobalamin appeared safe in fire victims with or without cyanide poisoning. The only reported side effect was a red coloration of skin and urine. In conclusion, antidotes are beneficial in cyanide poisoning. In suspected cyanide-poisoned patients, we recommend the use of hydroxocobalamin as first-line antidote, owing to its safety. In massive cyanide poisoning, due to the limited potency of hydroxocobalamin, continuous infusion of sodium thiosulfate should be associated.

Antidotes↗

Cyanide utilization and degradation by microorganisms.

Various microorganisms can produce (cyanogenesis) or degrade cyanide. They degrade cyanide either to detoxify it, or to use it as a source of nitrogen for growth. Significant amounts of cyanide are formed as a secondary metabolite by a wide range of fungi and a few bacteria by decarboxylation of glycine. When cyanide has been formed by the snow mould fungus it is degraded by conversion to carbon dioxide and ammonia via an unknown pathway. In contrast, cyanogenic bacteria either do not further catabolize cyanide or they convert it into beta-cyanoalanine by addition to cysteine or O-acetylserine. Several non-cyanogenic fungi that are pathogens of cyanogenic plants are known to degrade cyanide by hydration to formamide by the enzyme cyanide hydratase. Such fungi can be immobilized and used in packed-cell columns to continuously detoxify cyanide. ICI Biological Products Business market a preparation of spray-dried fungal mycelia, 'CYCLEAR', to detoxify industrial wastes. Novo Industri have also introduced a cyanidase preparation to convert cyanide directly into formate and ammonia. Bacteria have been isolated that use cyanide as a source of nitrogen for growth. Because cyanide, as KCN or NaCN, is toxic for growth, the bacteria (Pseudomonas fluorescens) have to be grown in fed-batch culture with cyanide as the limiting nutrient. Cyanide is converted to carbon dioxide and ammonia (which is then assimilated) by an NADH-linked cyanide oxygenase system.

Bacteria↗

Cyanide detoxification in rats exposed to acetonitrile and fed a low protein diet.

Different neurological syndromes have been associated with exposure to cyanide. Dietary cyanide exposure from cassava roots combined with a low intake of the sulfur amino acids necessary for cyanide detoxification has been implicated in the causation of konzo, an upper motoneuron disease identified in Africa. We have investigated the effect of a low protein diet on the capacity for cyanide detoxification. Rats were fed normal chow containing 18% protein or a low protein diet with 5% protein. To expose rats to cyanide the drinking water was supplemented with 40 or 80 mM acetonitrile (CH3CN) for up to 4 weeks. Weight gain was monitored and 24-hr urines were collected for analyses of total sulfur, inorganic sulfate, thiocyanate, and 2-aminothiolazine-4-carboxylic acid (ATC). Blood was collected for analyses of cyanide and cyanate. Rats on a normal diet grew throughout the experiment, while those on a low protein diet initially lost weight and then stabilized at a constant weight. Rats exposed to acetonitrile all progressively lost weight, those on a low protein diet at the highest rate. Signs of neurological damage were not observed. Rats not exposed to acetonitrile excreted < 0.2% of sulfur as thiocyanate and those on a low protein diet reduced their total sulfur excretion to one-third that of rats of the normal diet. Rats on the normal diet did not change total sulfur excretion during exposure to acetonitrile, although thiocyanate now contributed more than two-thirds of excreted sulfur. Rats on a low protein diet exposed to acetonitrile increased both total sulfur and thiocyanate excretion to the levels of rats on a normal diet. Rats exposed to acetonitrile had manyfold increases of circulating concentrations of cyanide and cyanate and of urinary excretion of ATC. There was a positive correlation between blood cyanide concentrations and the plasma concentration of cyanate. It is concluded that the rat has a high capacity for detoxification of cyanide. During adaptation to a low protein intake, sulfur is conserved but cyanide detoxification is still possible at the cost of extensive protein catabolism. It is thus possible that subclinical cyanide exposure could interfere with normal growth and development. The observation of a relationship between circulating cyanide on the one hand and circulating cyanate and urinary excretion of ATC on the other highlights the possibility that cyanide metabolites may mediate neurotoxic effects of cyanide.

Acetonitriles↗