Biological degradation of cyanide compounds.

The fate of cyanide in leach wastes at gold mines: An environmental perspective

When compared with Chlorella vulgaris, Scenedesmus obliquus and Selenastrum capricornutum, C. sorokiniana presented the highest tolerance to acetonitrile and the highest O2 production capacity. It also supported the fastest acetonitrile biodegradation when mixed with a suitable acetonitrile-degrading bacterial consortium. Consequently, this microalga was tested in symbiosis with the bacterial culture for the continuous biodegradation of acetonitrile at 2 g l−1 in a stirred tank photobioreactor and in a column photobioreactor under continuous illumination (250 μE m−2 s−1). Acetonitrile removal rates of up to 2.3 g l−1 day−1 and 1.9 g l−1 day−1 were achieved in the column photobioreactor and the stirred-tank photobioreactor, respectively, when operated at the shortest retention times tested (0.4 days, 0.6 days, respectively). In addition, when the stirred-tank photobioreactor was operated with a retention time of 3.5 days, the microbial culture was capable of assimilating up to 71% and nitrifying up to 12% of the NH4+ theoretically released through the biodegradation of acetonitrile, thus reducing the need for subsequent nitrogen removal. This study suggests that complete removal of N-organics can be combined with a significant removal of nitrogen by using algal–bacterial systems and that further residual biomass digestion could pay-back part of the operation costs of the treatment plant.

Combined carbon and nitrogen removal from acetonitrile using algal-bacterial bioreactors.

Cyanide compounds are contaminants of growing importance that could be remediated biologically via phytoremediation, provided the plants possess suitable mechanisms for managing these pollutants without toxicity. The transport and metabolism of two cyanide compounds, potassium cyanide and potassium ferrocyanide, by willow (Salix eriocephala L. var. Michaux) were compared using a hydroponic system that preserved cyanide speciation and solubility. The cyanide compounds were labelled with 15N to quantify transport while a novel tissue extraction procedure was used to relate tissue 15N to cyanide content and speciation. These analyses revealed that although little free cyanide was detected in the aerial tissues of plants exposed to either of these two cyanide compounds, significant enrichments in 15N were observed, suggesting transport and subsequent metabolism of free cyanide as well as ferrocyanide. The results for ferrocyanide are of interest because this molecule is resistant to microbial degradation and if oxidized to ferricyanide is purportedly membrane impermeable. Nevertheless, these results and mass balance calculations for tissue 15N and solution cyanide confirming 100% recovery for the added ferrocyanide are suggestive of ferrocyanide uptake and metabolism. This study provides new information describing the biological transport and metabolism of these two cyanide compounds in plants. Moreover, the data also suggest that phytoremediation of cyanide may be possible and ecologically safe due to the lack of cyanide bioaccumulation in aerial tissues.

https://onlinelibrary.wiley.com/doi/pdf/10.1046/j.0016-8025.2003.01069.x

Transport and metabolism of free cyanide and iron cyanide complexes by willow

Biosorption of iron(III)–cyanide complex anions to Rhizopus arrhizus: application of adsorption isotherms

A study was conducted to determine the effect of various factors on the rate and extent of potassium cyanide and potassium hexacyanoferrate (II, complex form) removal from aqueous and soil-containing systems. In a sterile aqueous system at neutral pH, the concentration of free cyanide was reduced by 42% in 334 h as a result of the protonation of CN− and the volatilization of the HCN formed. In the presence of aerobic mixed consortium of the Institute of Gas Technology and a methylotrophic culture, Isolate 3, the concentration of free cyanide was reduced by 59% and 66% in 357 h, respectively, as a result of combined chemical conversion and microbial degradation. In the sterile aqueous system amended initially with the complex form of cyanide, a less-than-20% reduction in cyanide occured. The sorption equilibria for free and complex cyanides in slurries of the topsoil and manufactured gas plant (MGP) soil was reached in less than 22 and 4 days, respectively. The extent of desorption of cyanides from topsoil and MGP soil into water decreased with time. In sterile systems containing topsoil and MGP soil that were previously equilibrated to cyanides, only a 2% reduction in cyanide concentration occurred in 336 h due to chemical conversion. In the presence of microbial cultures, the concentration of cyanide was reduced by less than 15% and 7% in the slurries of topsoil and MGP soil, respectively. The comparison of the rate and extent of cyanide removal from the aqueous and soil-containing systems in the presence of micro-organisms suggests that cyanides were retained by the solid phase of the soil-containing systems and therefore were less available for biodegradation.

V. J. Srivastava

Papers

Chemical and biological removal of cyanides from aqueous and soil-containing systems