AUTHOR=Rao Sarayu , Gao Xiaoyu , Ghoshal Subhasis 

TITLE=Characterization of the fate of primary and re-precipitated silver nanoparticles in lake water model systems

JOURNAL=Frontiers in Environmental Chemistry

VOLUME=Volume 6 - 2025

YEAR=2025

URL=https://www.frontiersin.org/journals/environmental-chemistry/articles/10.3389/fenvc.2025.1511440

DOI=10.3389/fenvc.2025.1511440

ISSN=2673-4486

ABSTRACT=The increasing use of silver nanoparticles (nAg) in products and associated releases to the environment necessitates a thorough understanding of the environmental fate and transformations of these potentially toxic nanomaterials to inform environmental risk assessments. Herein, the physical and chemical transformations of nAg in natural lake water samples were investigated. Lake water systems containing filtered and unfiltered lake water (FLW and UFLW) were spiked with 80 nm polyvinylpyrrolidone-coated nAg (nAgpristine) at 6 μg/L and were maintained under quiescent or mixed conditions in the dark for up to 44 days. Aliquots withdrawn from the water column contained smaller re-precipitated nAg (r-nAg, diameter ∼26 nm) formed by precipitation of Ag+ released by oxidative dissolution of nAgpristine. The number concentrations of r-nAg and nAgpristine were comparable. In FLW, agglomerates of r-nAg and the partially dissolved nAgpristine were formed under quiescent conditions and their settling accelerated after 14 days, but no settling occurred in the mixed systems. In UFLW, heteroagglomerates of r-nAg and the partially dissolved nAgpristine with natural colloids formed and induced sedimentation in both quiescent and mixed systems. A fraction of the r-nAg formed and the larger (>40 nm) or primary n-Ag (comprised of partially dissolved nAgpristine and its agglomerates with r-nAg or itself) were persistent in the water column for several weeks. Under quiescent conditions, more p-nAg remained suspended in FLW (15.7%, relative to number of nAgpristine dosed) than in UFLW (5.9%), whereas more r-nAg persisted in UFLW (2.6%) than in FLW (0.6%). Thus, the size distributions and fractions of nAg persisting in the water column can change significantly depending on water chemistry and mixing conditions.