The microorganisms are capable of accumulating heavy metal ions from water as biosorbent agents, offering a potential alternative for the detoxification and recovery of toxic/precious metals in industrial wastewater. In the present work, metal-resistant bacterial strains were isolated and identified from activated sludge of a waste treatment plant in the Municipality of Santa Rosa Jauregui, Querétaro. To obtain bacteria tolerant to metals, 37 bacterial strains and two isolates were selected based on their ability to show high tolerance (strains C-13 and C-16), maximum adsorption capacity for the studied metals. In this article, the term biosorption is used to encompass uptake by whole (dead) biomass via physicochemical mechanisms such as adsorption or ion exchange. The adsorption capacity was measured with alkaline and acid treatments to determine the conditions for maximum adsorption. The adsorption capacity with acid treatment was lower than biosorbent with alkaline treatment. A second part of the study was the biosorption of heavy metals (Cd, Cr, Mn, and Pb) from aqueous dead biomass of Bacillus sp (strain C13 and C16) isolated from the activated sludge in the first stage

The goal of this study was to further develop an incubation-quantitative polymerase chain reaction (qPCR) method for quantifying viable Ascaris eggs by characterizing the detection limit and number of template copies per egg, determining the specificity of the method, and testing the method with viable and inactivated larvated eggs. The number of template copies per cell was determined by amplifying DNA from known numbers of eggs at different development stages; the value was estimated to be 32 copies. The specificity of the method was tested against a panel of bacteria, fungi, protozoa and helminths, and no amplification was found with non-target DNA. Finally, fully larvated eggs were inactivated by four different treatments: 254 nm ultraviolet light, 2,000 ppm NH3-N at pH 9, moderate heat (48 °C) and high heat (70 °C). Concentrations of treated eggs were measured by direct microscopy and incubation-qPCR. The qPCR signal decreased following all four treatments, and was in general agreement with the decrease in viable eggs determined by microscopy. The incubation-qPCR method for enumerating viable Ascaris eggs is a promising approach that can produce results faster than direct microscopy, and may have benefits for applications such as assessing biosolids.

A native cyanide-degrading bacterial consortium was isolated from goldmine tailing sediments. Mine tailings are toxic effluents due to their metal–cyanide complexes. The bacterial consortium was able to degrade an initial sodium cyanide concentration ranging from 5 to 120 mg L⁻¹ in alkaline synthetic wastewater (pH > 9.2), for a maximum of 15 days. The free cyanide biodegradation efficiency was 98% for the highest initial free cyanide concentration tested and followed a first-order kinetic profile, with an estimated kinetic rate constant of 0.12 ± 0.011 d⁻¹. The cyanide-degrading consortium was streaked with serial dilutions on a specific medium (R2A). 16S rRNA gene sequencing and mass spectrometry proteomic fingerprinting of the isolates showed that the bacterial strains belonged to Microbacterium paraoxydans, Brevibacterium casei, Brevundimonas vesicularis, Bacillus cereus and Cellulosimicrobium sp. The first four genera had previously been identified as cyanide-degrading bacteria. Microbacterium and Brevibacterium had previously been found in alkaline conditions, showing resistance to heavy metals. As for Cellulosimicrobium, to our knowledge, this is the first study to implicate it directly or indirectly in cyanide biodegradation. In this research, these genera were identified as functional bacteria for cyanide degradation, and they might be suitable for mine tailing biotechnological tertiary treatment.

The aim of this study was to enrich cultures capable of anaerobic methyl tert-butyl ether (MTBE) biodegradation and to determine their compositions using biomolecular tools. MTBE biodegradation as the sole carbon source was observed under Fe(III) and SO₄^2–reducing conditions and with both electron acceptors present together. The estimated MTBE biodegradation rates ranged from 3.80 to 9.20 mg·L^–1·d^–1when Fe(III) was the sole electron acceptor, from 1.46 to 1.70 mg·L^–1·d^–1when Fe(III) and SO₄^2–were present together, and from 1.13 to 1.71 mg·L^–1·d^–1when SO₄^2–was the sole electron acceptor. Five to eight members were identified in the three consortia, and their characteristics were congruent with the electron acceptor conditions. A clone 99% similar to a recently described MTBE degrader, Ochrobactrum cytisi, was detected in both cultures containing Fe(III). Other 16S rRNA gene sequences detected were highly similar at the species or genus level to additional known MTBE degraders, including Pseudomonas spp. (cometabolic), Sphinogomonas, Achromobacter, and Rhodococcus. Results suggest that the buildup of intermediates and (or) the presence of sulfides had an inhibitory effect on biodegradation. Anaerobic MTBE biodegradation remains poorly understood, and degrading strains still have not been identified to date. This work represents the first detailed 16S rRNA gene profiling of highly enriched iron- and sulfate-reducing MTBE-degrading consortia. These results may provide useful biomarkers to support current efforts for confirming anaerobic MTBE biodegradation in the field.