Assessing the quality of sewage sludge: CASE study of the Kumasi wastewater treatment plant

High efficiency removal of antibiotic resistance gene with designer zinc-finger protein

The use of agricultural biomass-based fertilizers, and the release of feces into the environment leads to last-lasting pollution of antibiotic resistance genes that cannot be removed from waters via traditional methods, resulting in significant health threats. To solve this issue, an antibiotic resistance gene removal method was proposed and tested that used sequence-specific DNA-binding designer zinc finger proteins, which target an 18-bp DNA sequence for specific antibiotic resistance gene binding and removal. Targeting the sulfonamide-resistant sul1 gene, sul1-binding zinc-finger protein was designed, overexpressed, and purified. This protein showed specific binding with sul1 over tetA that do not have the targeted sequence. This protein was further immobilized on agarose-based resins to prepare a sul1-removal column. When loaded with 10 mg protein, this column can remove over 99 % sul1 in water, suggesting high efficiency. This work presents a new method attempting to eliminate environmental and health threats posed by antibiotic resistance genes.

Occurrence, characteristics, and microbial community of microplastics in anaerobic sludge of wastewater treatment plants

Wastewater treatment plants (WWTPs) usually contain microplastics (MPs) due to daily influents of domestic and municipal wastewater. Thus, the WWTPs act as a point source of MPs distribution in the environment due to their incapability to remove MPs completely. In this study, MPs occurrence and distribution in anaerobic sludge from WWTPs in different regions (Kaifeng "KHP", Jinan "JSP", and Lanzhou "LGP") were studied. Followed by MPs identification by microscopy and Fourier transform infrared (FTIR) spectrum. The microbial communities associated with anaerobic sludge and MPs were also explored. The results showed that MPs concentrations were 16.5, 38.5, and 17.2 particles/g of total solids (TS) and transparent MPs accounted for 49.1%, 58.5%, and 48.3% in KHP, JSP, and LGP samples, respectively. Fibers represented the most common shape of MPs in KHP (49.1%), JSP (56.0%), and LGP (69.0%). The FTIR spectroscopy indicated the predominance of polyethylene polymer in 1-5 mm MPs. The Proteobacteria, Chloroflexi, Actinobacteria, Bacteroidetes, and Planctomycetes were the abundant phyla in all anaerobic sludge. The bacterial genera in KHP and LGP were similar, in which Caldilinea (>23%), Terrimonas (>10%), and Ferruginibacter (>7%) formed the core bacterial genera. While Rhodococcus (15.3%) and Rhodoplanes (10.9%) were dominating in JSP. The archaeal genera Methanosaeta (>69%) and Methanobrevibacter (>10%) were abundant in KHP and LGP sludge. While Methanomethylovorans accounted for 90% of JSP. Acetyltransferase and hydratase were the major bacterial enzymes, while reductase was the key archaeal enzyme in all anaerobic sludge. This study provided the baseline for MPs distribution, characterization, and MPs associated microbes in WWTPs.