María José Huertas

Alkaline cyanide degradation by Pseudomonas pseudoalcaligenes CECT5344 in a batch reactor. Influence of pH.

Water containing cyanide was biologically detoxified with the bacterial strain Pseudomonas pseudoalcaligenes CECT5344 in a batch reactor. Volatilization of toxic hydrogen cyanide (HCN) was avoided by using an alkaline medium for the treatment. The operational procedure was optimized to assess cyanide biodegradation at variable pH values and dissolved oxygen concentrations. Using an initial pH of 10 without subsequent adjustment allowed total cyanide to be consumed at a mean rate of approximately 2.81 mg CN(-) L(-1) O.D.(-1) h(-1); however, these conditions posed a high risk of HCN formation. Cyanide consumption was found to be pH-dependent. Thus, no bacterial growth was observed with a controlled pH of 10; on the other hand, pH 9.5 allowed up to 2.31 mg CN(-) L(-1) O.D.(-1) h(-1) to be converted. The combination of a high pH and a low dissolved oxygen saturation (10%) minimized the release of HCN. This study contributes new basic knowledge about this biological treatment, which constitutes an effective alternative to available physico-chemical methods for the purification of wastewater containing cyanide or cyano-metal complexes.

Metals in Cyanobacteria: Analysis of the Copper, Nickel, Cobalt and Arsenic Homeostasis Mechanisms

Traces of metal are required for fundamental biochemical processes, such as photosynthesis and respiration. Cyanobacteria metal homeostasis acquires an important role because the photosynthetic machinery imposes a high demand for metals, making them a limiting factor for cyanobacteria, especially in the open oceans. On the other hand, in the last two centuries, the metal concentrations in marine environments and lake sediments have increased as a result of several industrial activities. In all cases, cells have to tightly regulate uptake to maintain their intracellular concentrations below toxic levels. Mechanisms to obtain metal under limiting conditions and to protect cells from an excess of metals are present in cyanobacteria. Understanding metal homeostasis in cyanobacteria and the proteins involved will help to evaluate the use of these microorganisms in metal bioremediation. Furthermore, it will also help to understand how metal availability impacts primary production in the oceans. In this review, we will focus on copper, nickel, cobalt and arsenic (a toxic metalloid) metabolism, which has been mainly analyzed in model cyanobacterium Synechocystis sp. PCC 6803.

Cyanide metabolism of Pseudomonas pseudoalcaligenes CECT5344: role of siderophores

Cyanide is one of the most potent and toxic chemicals produced by industry. The jewelry industry of Córdoba (Spain) generates a wastewater (residue) that contains free cyanide, as well as large amounts of cyano-metal complexes. Cyanide is highly toxic to living systems because it forms very stable complexes with transition metals that are essential for protein function. In spite of its extreme toxicity, some organisms have acquired mechanisms to avoid cyanide poisoning. The biological assimilation of cyanide needs the concurrence of three separate processes: (i) a cyanide-insensitive respiratory chain, (ii) a system for iron acquisition (siderophores) and (iii) a cyanide assimilation pathway. Siderophores are low-molecular-mass compounds (600-1500 Da) that scavenge iron (Fe(3+)) ions (usually with extremely high affinity) from the environment under iron-limiting conditions. There are two main classes of siderophores: catechol and hydroxamate types. The catechol-type siderophores chelate ferric ion via a hydroxy group, whereas the hydroxamate-type siderophores bind iron via a carbonyl group with the adjacent nitrogen. In the presence of cyanide, bacterial proliferation requires this specific metal uptake system because siderophores are able to break down cyano-metal complexes. Pseudomonas pseudoalcaligenes CECT5344 is able to use free cyanide or cyano-metal complexes as nitrogen source. A proteomic approach was used for the isolation and identification, in this strain, of a protein that was induced in the presence of cyanide, namely CN0, that is involved in siderophore biosynthesis in response to cyanide. An overview of bacterial cyanide degradation pathways and the involvement of siderophores in this process are presented.

Alkaline cyanide biodegradation by Pseudomonas pseudoalcaligenes CECT5344

Pseudomonas pseudoalcaligenes CECT5344 uses cyanide, cyanate, beta-cyanoalanine, and other cyanoderivatives as nitrogen sources under alkaline conditions, which prevents volatile HCN (pK(a) 9.2) formation. The cyanide consumed by this strain is stoichiometrically converted into ammonium. In addition, this bacterium grows with the heavy metal, cyanide-containing waste water generated by the jewellery industry, and is also a cyanide-resistant strain which induces an alternative oxidase and a siderophore-based mechanism for iron acquisition in the presence of cyanide. The detection of cyanase and beta-cyanoalanine nitrilase activities in cyanide-induced cells suggests their implication in the cyanide degradation pathway.