Deciphering the removal of antibiotics and the antibiotic resistome from typical hospital wastewater treatment systems

Deciphering the profiles and hosts of antibiotic resistance genes and evaluating the risk assessment of general and non-general hospital wastewater by metagenomic sequencing

Hospital wastewater (HWW) is a substantial environmental reservoir of antibiotic resistance genes (ARGs) and poses risks to public health and aquatic ecosystems. However, research on the diversity, transmission mechanisms, pathogenic hosts, and risks of ARGs in different HWW types is limited. This study involved the collection of HWW samples from 15 hospitals in Hefei, China, which were subsequently categorized as general hospitals (GHs) and non-general hospitals (NGHs). A 280.28-Gbp sequencing dataset was generated using a metagenomic sequencing strategy and analyzed using metagenomic assembly and binning approaches to highlight these issues in GHs and NGHs. Results showed significant differences between GHs and NGHs in ARG distribution, microbial community composition, and hosts of ARGs. Potential pathogens such as Rhodocyclaceae bacterium ICHIAU1 and Acidovorax caeni were more abundant in GHs. Furthermore, plasmid-mediated ARGs (45.21%) were more prevalent than chromosome-mediated ARGs (25.74%) in HWW, with a significantly higher proportion of plasmid-mediated ARGs in GHs compared to NGHs. The co-occurrence of ARGs and mobile genetic elements was more frequent in GHs. Additionally, the antibiotic resistome risk index was higher in GHs (38.73 ± 12.84) than NGHs (22.53 ± 11.80), indicating a greater risk of ARG transmission in GHs. This pioneering study provides valuable insights into the transmission mechanisms and hosts of ARGs in hospital settings, emphasizing the increased risk of ARG transmission in GHs.

Antibacterial Activity of Ciprofloxacin-Based Carbon Dot@Silver Nanoparticle Composites

The combined green synthesis of carbon dots (CDs) from the hydrothermal conversion of ciprofloxacin and silver nanoparticles (AgNPs) using sodium alginate as a reducing and stabilizing agent results in arrangements of nanostructures (CD@AgNP composites) with positive surface charge that electrostatically interact with Gram-positive and Gram-negative bacteria in the planktonic form and also biofilm forms, inhibiting their growth and adhesion on surfaces. Outstanding performance for CD-based materials results in a 5-log reduction in colony-forming units (CFU/mL) of E. coli after 1 h of treatment and a decrease of 99.32% in the consolidated biofilm of S. aureus. These nanostructures result in the intrinsic fluorescence of CDs and an overall eco-friendly preparation process that can be explored in disinfection procedures based on the direct administration of a sanitizer based on nanoparticles dispersed in an aqueous solution. This process is justified by the adequate conversion of antibiotics in positively charged CDs and composites with AgNPs, resulting in nanocomposites in which the prevailing cationic effect facilitates their incorporation and diffusion into bacterial membrane cells.

Understanding the pivotal role of ubiquitous Yellow River suspend sediment in efficiently degrading metronidazole pollutants in water environments

Sulfite-based advanced oxidation technology has received considerable attention for its application in organic pollutants elimination. However, the potential of natural sediments as effective catalysts for sulfite activation has been overlooked. This study investigates a novel process utilizing suspended sediment/sulfite (SS/S(IV)) for degradation of metronidazole (MNZ). Our results demonstrate that MNZ degradation efficiency can reach to 93.1 % within 90 min with 12.0 g SS and 2.0 mM sulfite. The influencing environmental factors, including initial pH, SS dosage, S(IV) concentration, temperature, and co-existing substances were systematically investigated. Quenching experiments and electron paramagnetic resonance analyses results indicate that SO3•- is the primary active substance responsible for MNZ degradation, with involvement of SO4•-, SO5•-, and •OH. X-ray photoelectron spectroscopy and Mössbauer spectra reveal that Fe (III)-silicates play a crucial role in activating S(IV). Furthermore, analysis of degradation intermediates and pathways of MNZ is conducted using liquid chromatography with mass spectrometry (LC -MS). The toxicity of MNZ and its intermediates were also systematically evaluated by the T.E.ST. program and wheat seeds germination test. This study offers valuable insight into the activation of sulfite by natural sediments and could contribute to the development of SS-based advanced oxidation processes (AOPs) for the in-situ remediation of antibiotics-contaminated water environments.