Nanomaterial properties differ from those bulk materials of the same composition, allowing them to execute novel activities. A possible downside of these capabilities is harmful interactions with biological systems, with the potential to generate toxicity. An approach to assess the safety of nanomaterials is urgently required. We compared the cellular effects of ambient ultrafine particles with manufactured titanium dioxide (TiO2), carbon black, fullerol, and polystyrene (PS) nanoparticles (NPs). The study was conducted in a phagocytic cell line (RAW 264.7) that is representative of a lung target for NPs. Physicochemical characterization of the NPs showed a dramatic change in their state of aggregation, dispersibility, and charge during transfer from a buffered aqueous solution to cell culture medium. Particles differed with respect to cellular uptake, subcellular localization, and ability to catalyze the production of reactive oxygen species (ROS) under biotic and abiotic conditions. Spontaneous ROS production was compared by using an ROS quencher (furfuryl alcohol) as well as an NADPH peroxidase bioelectrode platform. Among the particles tested, ambient ultrafine particles (UFPs) and cationic PS nanospheres were capable of inducing cellular ROS production, GSH depletion, and toxic oxidative stress. This toxicity involves mitochondrial injury through increased calcium uptake and structural organellar damage. Although active under abiotic conditions, TiO2 and fullerol did not induce toxic oxidative stress. While increased TNF-alpha production could be seen to accompany UFP-induced oxidant injury, cationic PS nanospheres induced mitochondrial damage and cell death without inflammation. In summary, we demonstrate that ROS generation and oxidative stress are a valid test paradigm to compare NP toxicity. Although not all materials have electronic configurations or surface properties to allow spontaneous ROS generation, particle interactions with cellular components are capable of generating oxidative stress.
Nanomaterials are highly dynamic in biological and environmental media. A critical need for advancing environmental health and safety research for nanomaterials is to identify commonly occurring physical and chemical transformations affecting nanomaterial properties and toxicity. Silver nanoparticles, one of the most ecotoxic and well-studied nanomaterials, readily sulfidize in the environment. Here, we show that very low degrees of sulfidation (0.019 S/Ag mass ratio) universally and significantly decreases the toxicity of silver nanoparticles to four diverse types of aquatic and terrestrial eukaryotic organisms. Toxicity reduction is primarily associated with a decrease in Ag+ availability after sulfidation due to the lower solubility of Ag2S relative to elemental Ag (Ag(0)). We also show that chloride in exposure media determines silver nanoparticle toxicity by controlling the speciation of Ag. These results highlight the need to consider environmental transformation of NPs in assessing their toxicity to accurately portray their potential environmental risks.
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In this study we report on the electrokinetic behavior of colloidal aggregates of C60fullerenes (n-C60) produced through two different techniques: solvent exchange and extended mixing with water. In the first technique, used to produce colloidal materials in several recent toxicity and transport studies, an organic solvent such as tetrahydrofuran (THF) is used to dissolve the C60 before mixing with water. The second technique is more indicative of conditions that might occur in natural aquatic systems. Both types of n-C60 were observed to be negatively charged under a variety of solution chemistries; however, the n-C60 formed using THF was more strongly charged. We conclude that n-C60 likely acquires charge through charge transfer from the organic solvent (when present) and surface hydrolysis reactions. Nevertheless, C60 is capable of acquiring charge and becoming dispersed as n-C60 in water without the aid of organic solvents, a pathway that may be important in determining the mobility of fullerenes in natural systems. These findings also show that n-C60 made using THF retains a portion of the solvent in the cluster structure, subsequently influencing the characteristics of the n-C60 and possibly requiring a re-interpretation of results from recent studies on n-C60 toxicity using THF-derived materials.
The production of reactive oxygen species (ROS) by aqueous suspensions of fullerenes and nano-TiO2 (Degussa P25) was measured both in ultrapure water and in minimal Davis (MD) microbial growth medium. Fullerol (hydroxylated C60) produced singlet oxygen (1O2) in ultrapure water and both 1O2 and superoxide (O2-*) in MD medium, but no hydroxyl radicals (OH*) were detected in either case. PVP/C60 (C60 encapsulated with poly(N-vinylpyrrolidone)) was more efficient than fullerol in generating singlet oxygen and superoxide. However, two other aggregates of C60, namely THF/nC60 (prepared with tetrahydofuran as transitional solvent) and aqu/nC60 (prepared by vigorous stirring of C60 powder in water), were not photoactive. Nano-TiO2 (also present as aggregates) primarily produced hydroxyl radicals in pure water and superoxide in MD medium. Bacterial (Escherichia coli) toxicity tests suggest that, unlike nano-TiO2 which was exclusively phototoxic, the antibacterial activity of fullerene suspensions was linked to ROS production. Nano-TiO2 may be more efficient for water treatment involving UV or solar energy, to enhance contaminant oxidation and perhaps for disinfection. However, fullerol and PVP/ C60 may be useful as water treatment agents targeting specific pollutants or microorganisms that are more sensitive to either superoxide or singlet oxygen.
An advanced oxidation process of combining cobalt and
peracetic
acid (Co/PAA) was developed to degrade sulfamethoxazole (SMX) in this
study. The formed acetylperoxy radical (CH3CO3
•) through
the activation of PAA by Co (Co2+) was the dominant radical
responsible for SMX degradation, and acetoxyl radical (CH3CO2
•) might also have played a role. The efficient redox cycle of Co3+/Co2+ allows good removal efficiency of SMX even
at quite low dosage of Co (<1 μM). The presence of H2O2 in the Co/PAA process has a negative effect
on the degradation of SMX due to the competition for reactive radicals.
The SMX degradation in the Co/PAA process is pH dependent, and the
optimum reaction pH is near-neutral. Humic acid and HCO3
– can inhibit SMX degradation in the Co/PAA process,
while the presence of Cl– plays a little role in
the degradation of SMX in this system. Although transformation products
of SMX in the Co/PAA system show higher acute toxicity, the low Co
dose and SMX concentration in aquatic solution can efficiently weaken
the acute toxicity. After reaction in the Co/PAA process, numerous
carbon sources that could be provided for bacteria and algae growth
can be produced, suggesting that the proposed Co/PAA process has good
potential when combined with the biotreatment processes.
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