ABSTRACT
The mycosynthesis of biogenic NPs using nanotechnology technique is an ecofriendly and economical approach. The extracellular mycelial extract of the Pleurotus florida fungi were used to biosynthesized Zn, Cu and Fe NPs using zinc sulphate, zinc chloride, copper sulphate, copper chloride ferrous sulphate and ferric chloride, precursor salts at 1.0 mM concentration. The color of reaction mixture was changed from (transparent to white, blue to green and yellow to brown) for Zn, Cu and Fe NPs during incubation period of 96 h at 25 ± 2 °C, indicating synthesis of NPs. Spectroscopy and microscopy techniques were used for the characterization of newly synthesized biogenic NPs. Whereas, the ICP-MS analysis revealed that copper chloride precursor salts produced high concentration of Cu biogenic NPs, followed by zinc chloride derived Zn NPs. The fortification with the biogenic NPs of Pleurotus florida mycelium exhibited high accumulation of the trace elements as compared to non-fortified mycelium. Supplementary Information: The online version contains supplementary material available at 10.1007/s10068-023-01307-z.
ABSTRACT
Twelve bacterial species were evaluated to know the degradation pattern of thiamethoxam in liquid medium. All the bacterial species could actively degrade phorate in a mineral salt medium containing phorate (50 µg ml(-1)) as sole carbon source. As these species have ability to degrade, we used these for the degradation of thiamethoxam--a neonicoitinoids. Screening of 12 active phorate-metabolizing bacterial species resulted in selection of Bacillus aeromonas strain IMBL 4.1 and Pseudomonas putida strain IMBL 5.2 causing 45.28 and 38.23 % thiamethoxam (50 µg ml(-1)) reduction, respectively, in 15 days as potential thiamethoxam degrading species. These two bacterial species grew optimally at 37 °C under shake culture conditions in MSMT medium raised with initial pH of 6.0-6.5 and use of these optimum cultural conditions resulted in improved thiamethoxam degradation by these bacterial species. These species caused maximum thiamethoxam degradation only in the presence of thiamethoxam as sole source of carbon and energy and the same was reduced in the presence of easily metabolize able carbon (C0 and C1) and nitrogen ((N0, N1 and N2) sources. This could be attributed to involvement of repressible metabolic pathways, reactions of which are inhibited by the presence of easily available nutrients for growth. Besides above, qualitative analysis of thiamethoxam residues by gas liquid chromatography revealed complete metabolization of thiamethoxam without detectable accumulation of any known thiamethoxam metabolites.
