Sediment Bacteria and Phosphorus Fraction Response, Notably to Titanium Dioxide Nanoparticle Exposure

沉积物细菌和磷组分响应,特别是对二氧化钛纳米颗粒暴露的响应

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Abstract

Titanium dioxide nanoparticle (TiO(2) NP) toxicity to the growth of organisms has been gradually clarified; however, its effects on microorganism-mediated phosphorus turnover are poorly understood. To evaluate the influences of TiO(2) NPs on phosphorus fractionation and the bacterial community, aquatic microorganisms were exposed to different concentrations of TiO(2) NPs with different exposure times (i.e., 0, 10, and 30 days). We observed the adhesion of TiO(2) NPs to the cell surfaces of planktonic microbes by using SEM, EDS, and XRD techniques. The addition of TiO(2) NPs resulted in a decrease in the total phosphorus of water and an increase in the total phosphorus of sediments. Additionally, elevated TiO(2) NPs enhanced the sediment activities of reductases (i.e., dehydrogenase [0.19-2.25 μg/d/g] and catalase [1.06-2.92 μmol/d/g]), and significantly decreased the absolute abundances of phosphorus-cycling-related genes (i.e., gcd [1.78 × 10(4)-9.55 × 10(5) copies/g], phoD [5.50 × 10(3)-5.49 × 10(7) copies/g], pstS [4.17 × 10(2)-1.58 × 10(6) copies/g]), and sediment bacterial diversity. TiO(2) NPs could noticeably affect the bacterial community, showing dramatic divergences in relative abundances (e.g., Actinobacteria, Acidobacteria, and Firmicutes), coexistence patterns, and functional redundancies (e.g., translation and transcription). Our results emphasized that the TiO(2) NP amount-rather than the exposure time-showed significant effects on phosphorus fractions, enzyme activity, phosphorus-cycling-related gene abundance, and bacterial diversity, whereas the exposure time exhibited a greater influence on the composition and function of the sediment bacterial community than the TiO(2) NP amount. Our findings clarify the responses of phosphorus fractions and the bacterial community to TiO(2) NP exposure in the water-sediment ecosystem and highlight potential environmental risks of the migration of untreated TiO(2) NPs to aquatic ecosystems.

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