Magnetite Alters the Metabolic Interaction between Methanogens and Sulfate-Reducing Bacteria.

It is known that the presence of sulfate decreases the methane yield in the anaerobic digestion systems. Sulfate-reducing bacteria can convert sulfate to hydrogen sulfide competing with methanogens for substrates such as H2 and acetate. The present work aims to elucidate the microbial interactions in biogas production and assess the effectiveness of electron-conductive materials in restoring methane production after exposure to high sulfate concentrations. The addition of magnetite led to a higher methane content in the biogas and a sharp decrease in the level of hydrogen sulfide, indicating its beneficial effects. Furthermore, the rate of volatile fatty acid consumption increased, especially for butyrate, propionate, and acetate. Genome-centric metagenomics was performed to explore the main microbial interactions. The interaction between methanogens and sulfate-reducing bacteria was found to be both competitive and cooperative, depending on the methanogenic class. Microbial species assigned to the Methanosarcina genus increased in relative abundance after magnetite addition together with the butyrate oxidizing syntrophic partners, in particular belonging to the Syntrophomonas genus. Additionally, Ruminococcus sp. DTU98 and other species assigned to the Chloroflexi phylum were positively correlated to the presence of sulfate-reducing bacteria, suggesting DIET-based interactions. In conclusion, this study provides new insights into the application of magnetite to enhance the anaerobic digestion performance by removing hydrogen sulfide, fostering DIET-based syntrophic microbial interactions, and unraveling the intricate interplay of competitive and cooperative interactions between methanogens and sulfate-reducing bacteria, influenced by the specific methanogenic group.

An integrated metagenomic model to uncover the cooperation between microbes and magnetic biochar during microplastics degradation in paddy soil.

The free radicals released from the advanced oxidation processes can enhance microplastics degradation, however, the existence of microbes acting synergistically in this process is still uncertain. In this study, magnetic biochar was used to initiate the advanced oxidation process in flooded soil. paddy soil was contaminated with polyethylene and polyvinyl chloride microplastics in a long-term incubation experiment, and subsequently subjected to bioremediation with biochar or magnetic biochar. After incubation, the total organic matter present in the samples containing polyvinyl chloride or polyethylene, and treated with magnetic biochar, significantly increased compared to the control. In the same samples there was an accumulation of "UVA humic" and "protein/phenol-like" substances. The integrated metagenomic investigation revealed that the relative abundance of some key genes involved in fatty acids degradation and in dehalogenation changed in different treatments. Results from genome-centric investigation suggest that a Nocardioides species can cooperate with magnetic biochar in the degradation of microplastics. In addition, a species assigned to the Rhizobium taxon was identified as a candidate in the dehalogenation and in the benzoate metabolism. Overall, our results suggest that cooperation between magnetic biochar and some microbial species involved in microplastic degradation is relevant in determining the fate of microplastics in soil.

Preliminary investigation of microorganisms potentially involved in microplastics degradation using an integrated metagenomic and biochemical approach.

Plastic pollution is becoming an emerging environmental issue due to inappropriate disposal at the end of the materials life cycle. When plastics are released, they undergo physical and chemical corrosion, leading to the formation of small particles, commonly referred to as microplastics. In this study, a microbial community derived from the leachate of a bioreactor containing a mixture of soil and plastic collected during a landfill mining process underwent an enrichment protocol in order to select the microbial species specifically involved in plastic degradation. The procedure was set up and tested on polyethylene, polyvinyl chloride, and polyethylene terephthalate, both in anaerobic and aerobic conditions. The evolution of the microbiome has been monitored using a combined approach based on microscopy, marker-gene amplicon sequencing, genome-centric metagenomics, degradation assays, and GC-MS analyses. This procedure permitted us to deeply investigate the metabolic pathways potentially involved in plastic degradation and to depict the route for microplastics metabolization from the enriched microbial community. Six enzymes, among the ones already identified, were found in our samples (alkane 1-monooxygenase, cutinase, feruloyl esterase, triacylglycerol lipase, medium-chain acyl-CoA dehydrogenase, and protocatechuate 4,5-dioxygenase) and new enzymes, addressed as MHETases most probably for the presence of the catalytic triad (His-Asp-Ser), were detected. Among the enzymes involved in plastics degradation, alkane 1-monooxygenase was found in high copy number (between ten and 62 copies) in the metagenomes that resulted most abundant in the microbiome enriched with polyethylene, while protocatechuate 4,5-dioxygenase was found between one and eight copies in the most abundant metagenomes of the microbial culture enriched with polyethylene terephthalate. Degradation assays, performed using both bacterial lysates and supernatants, revealed interesting results on polyethylene terephthalate degradation. Moreover, this study demonstrates to what extent different types of microplastics can affect the microbial community composition. The results obtained significantly increase the knowledge of the plastic degradation process.