Suitability of different growth substrates as source of nitrogen for sulfate reducing bacteria

Key role of macrophyte-dominated habitats over cyanobacteria-dominated habitats in stability of microbial sulfur cycling in freshwater lakes

Despite extensive studies on sulfate-reducing bacteria (SRB) and sulfur-oxidizing bacteria (SOB) in marine and deep stratified ecosystems, their spatiotemporal dynamics and ecological roles in shallow freshwater lakes remain poorly understood, especially with habitat shifts driven by eutrophication and climate change. Here, we monitored seasonal changes in sediment and porewater chemical parameters, and applied high-throughput sequencing and co-occurrence network analysis to compare SRB and SOB communities in surface sediments from cyanobacteria-dominated (ZSB) and macrophyte-dominated (XKB) habitats of Lake Taihu across four seasons. In ZSB, seasonal variations in acid volatile sulfide (AVS), dissolved sulfide (∑H2S), and Fe(II) were the primary drivers of sulfur bacterial communities. In contrast, SRB in XKB were mainly influenced by total nitrogen (TN) and total phosphorus (TP), while SOB were regulated by spatial heterogeneity, with AVS as the key driver. Spore-forming SRB such as Desulfotomaculum were distinctly enriched in ZSB, indicating an adaptive strategy to environmental fluctuations. Notably, Cupriavidus, a genus rarely linked to sulfur oxidation, was the dominant SOB genus in both habitats. Co-occurrence network analysis showed that dominant genera in ZSB acted as network hubs, indicating greater vulnerability to environmental changes in cyanobacteria-dominated habitats. Conversely, XKB displayed evenly distributed interaction networks without dominant network hubs, enhancing resilience to environmental fluctuations. These findings provide new insight into how macrophyte-dominated habitats enhance the resilience of shallow freshwater lakes to algal bloom expansion via stabilized sulfur cycling. Hydrological and hydrodynamic factors should be considered in future to better elucidate sulfur cycling in freshwater lakes.

Discovery of a Novel Bacillus sp. JO01 for the Degradation of Poly(butylene adipate-co-terephthalate)( PBAT) and Its Inhibition by PBAT Monomers

Poly(butylene adipate-co-terephthalate) (PBAT) is a type of biodegradable plastic composed of both aliphatic and aromatic hydrocarbon polymers, which grants it the advantages of processability and flexibility along with increased interest. Studies have suggested that PBAT biodegradation mechanisms involve enzymatic breakdown by lipases. Our initial efforts in this study were therefore focused on identifying a novel PBAT-degrading bacterial strain with high degradation activity. Nine bacterial strains from various sources were screened and assessed for their ability to degrade PBAT. Bacillus sp. JO01 strain, exhibiting high similarity (99%) with Bacillus toyonensis BCT-7112, demonstrated superior PBAT degradation activity under various temperature conditions from 25 to 42°C. Time-dependent PBAT degradation by Bacillus sp. JO01 indicated a maximum yield at 30°C, reaching 66% of film degradation measured. Besides PBAT, the strain showed degradability on PCL, PHB, and PBS. Physical characterization of the degraded PBAT films via scanning electron microscopy revealed that surface alterations such as cracks were reduced, as was the molecular weight. Bacillus sp. JO01 did not consume PBAT monomers, such as adipic acid (AA), 1,4-butanediol, and terephthalic acid (TPA). However, AA and TPA showed inhibitory effects on the degradation of PBAT films by Bacillus sp. JO01, resulting in 30% inhibition of degradation at 16 mM of AA and at 32 mM of TPA. This study highlights Bacillus sp. JO01 as a superior strain for PBAT degradation and suggests that PBAT monomers have an inhibitory effect on the degrading strains, which is an important consideration for the bulk degradation of bioplastics.

Reveling the micromolecular biological mechanism of acetate, thiosulfate and Fe0 in ecological floating beds for treating low C/N wastewater: Insight into nitrogen removals and greenhouse gases reductions

Selecting an appropriate electron donor to enhance nitrogen removal for treating low C/N wastewater in ecological floating beds (EFBs) is controversy. In this study, a systematic and comprehensive evaluation of sodium acetate (EFB-C), sodium thiosulfate (EFB-S) and iron scraps (EFB-Fe) was performed in a 2-year experiment on long-term viability including nitrogen removal and greenhouse gas emissions associated with key molecular biological mechanisms. The results showed that EFB-C (43-85 %) and EFB-S (40-88 %) exhibited superior total nitrogen (TN) removal. Temperature and hydraulic retention time (HRT) have significant impacts on TN removal of EFB-Fe, however, it could reach 86 % under high temperature (30-35 °C) and a long HRT (3 days), and it has lowest N2O (0-6.2 mg m-2 d-1) and CH4 (0-5.3 mg m-2 d-1) fluxes. Microbial network analysis revealed that the microbes changed from competing to cooperating after adding electron donors. A higher abundance of anammox genera was enriched in EFB-Fe. The Mantel's test and structural equation model provided proof of the differences, which showed that acetate and thiosulfate were similar, whereas Fe0 was different in the nitrogen removal mechanism. Molecular biology analyses further verified that heterotrophic, autotrophic, and mixotrophic coupled with anammox were the main TN removal pathways for EFB-C, EFB-S, and EFB-Fe, respectively. These findings provide a better understanding of the biological mechanisms for selecting appropriate electron donors for treating low C/N wastewater.

Enrichment of psychrophilic and acidophilic sulfate-reducing bacterial consortia - a solution toward acid mine drainage treatment in cold regions

Failure of sulfate-reducing bacteria (SRB)-mediated treatment of acid mine drainage (AMD) in cold regions due to inhibition of bacteria by acidic pH and low temperature can be overcome by enriching psychrophilic and acidophilic microbial consortia from local metal-rich sediments. In this study, we enriched microbial consortia from Arctic mine sediments at varying pH (3-7) and temperatures (15-37 °C) under anaerobic conditions with repeated sub-culturing in three successive stages, and analyzed the microbial community using 16S rRNA gene sequencing. The enriched SRB genera resulted in high sulfate reduction (85-88%), and significant metal removal (49-99.9%) during the initial stages (stage 1 and 2). Subsequently, sub-culturing the inoculum at pH 3-4.5 resulted in lower sulfate reduction (9-34%) due to the inhibition of SRB by accumulated acetic acid (0.3-9 mM). The microbial metabolic interactions for successful sulfate and metal removal involved initial glycerol co-fermentation to acetic acid at acidic pH (by Desulfosporosinus, Desulfotomaculum, Desulfurospora, and fermentative bacteria including Cellulomonas and Anaerovorax), followed by acetic acid oxidation to CO₂ and H₂ (by Desulfitobacterium) at neutral pH, and subsequent H₂ utilization (by Desulfosporosinus). The results, including the structural and functional properties of enriched microbial consortia, can inform the development of effective biological treatment strategies for AMD in cold regions.

Trends in mercury concentrations and methylation in Minamata Bay, Japan, between 2014 and 2018

Methylmercury concentrations in Minamata Bay are high, but the cause is unclear. We conducted a basic study on the behavior of methylmercury in Minamata Bay seawater; the findings suggest that mercury methylation may occur throughout the year in Minamata Bay. Seawater temperature, salinity, and concentrations of dissolved organic carbon were the environmental factors that affected methylation, and the degree of methylation was closely related to bacterial community structure. The concentration of methylmercury in suspended particulate matter was highest 10 m below the surface and decreased with greater depths. We did not observe a correlation between methylmercury concentrations in suspended particulate matter and concentrations of dissolved methylmercury.

How to tackle the stringent sulfate removal requirements in mine water treatment-A review of potential methods

Sulfate (SO₄^2-) is a ubiquitous anion in natural waters. It is not considered toxic, but it may be detrimental to freshwater species at elevated concentrations. Mining activities are one significant source of anthropogenic sulfate into natural waters, mainly due to the exposure of sulfide mineral ores to weathering. There are several strategies for mitigating sulfate release, starting from preventing sulfate formation in the first place and ending at several end-of-pipe treatment options. Currently, the most widely used sulfate-removal process is precipitation as gypsum (CaSO₄·2H₂O). However, the lowest reachable concentration is theoretically 1500 mg L^-1 SO₄^2- due to gypsum's solubility. At the same time, several mines worldwide have significantly more stringent sulfate discharge limits. The purpose of this review is to examine the process options to reach low sulfate levels (< 1500 mg L^-1) in mine effluents. Examples of such processes include alternative chemical precipitation methods, membrane technology, biological treatment, ion exchange, and adsorption. In addition, aqueous chemistry and current effluent standards concerning sulfate together with concentrate treatment and sulfur recovery are discussed.

Optimization of the operation of packed bed bioreactor to improve the sulfate and metal removal from acid mine drainage

The present study discusses the potentiality of using anaerobic Packed Bed Bioreactor (PBR) for the treatment of acid mine drainage (AMD). The multiple process parameters such as pH, hydraulic retention time (HRT), concentration of marine waste extract (MWE), total organic carbon (TOC) and sulfate were optimized together using Taguchi design. The order of influence of the parameters towards biological sulfate reduction was found to be pH > MWE > sulfate > HRT > TOC. At optimized conditions (pH - 7, 20% (v/v) MWE, 1500 mg/L sulfate, 48 h HRT and 2300 mg/L TOC), 98.3% and 95% sulfate at a rate of 769.7 mg/L/d. and 732.1 mg/L/d. was removed from the AMD collected from coal and metal mine, respectively. Efficiency of metal removal (Fe, Cu, Zn, Mg and Ni) was in the range of 94-98%. The levels of contaminants in the treated effluent were below the minimum permissible limits of industrial discharge as proposed by Bureau of Indian Standards (IS 2490:1981). The present study establishes the optimized conditions for PBR operation to completely remove sulfate and metal removal from AMD at high rate. The study also creates the future scope to develop an efficient treatment process for sulfate and metal-rich mine wastewater in a large scale.