Abstract:The main purpose of this study was to characterize the adsorption and desorption interactions of
naphthalene, a model environmental organic pollutant, with C60 fullerene. C60 fullerene was used as a
model adsorbent for carbonaceous nanoparticles. Typical batch reactors were used to perform adsorption
and desorption experiments. Adsorption and desorption of naphthalene to and from C60 fullerene solids
in different aggregation forms was studied, where C60 was used as purchased, deposited as a thin film,
or dispe… Show more
“…As a contrast, another different aqueous nC 60 suspension was also prepared by using a familiar method in previous literature without organic solvents. The aqueous nC 60 , often termed as stir-nC 60 , was obtained by stirring 100 mg of C 60 powder in 200 mL of deionized water for 2 months via a magnetic stirrer at room temperature according to the method described by Cheng et al 23 Characterization of nC 60 Suspensions. The ultraviolet/visible (UV/vis) absorption spectra of our nC 60 suspensions were taken within a range of 200−900 nm by using a Jasco V550 spectrophotometer at room temperature and corrected for their corresponding solvent backgrounds.…”
The photoexcited aqueous fullerene (C 60 ) suspension was shown to exhibit an asymmetric photoluminescence (PL) spectrum, which, different from the symmetric spectrum observed previously in C 60 solutions or suspensions, still stems from the characteristic phosphorescence of singlet oxygen (O 2 (a 1 Δ)) owing to its dependence on oxygen concentration. In contrast to the microsecond-level lifetime of O 2 (a 1 Δ) in water solutions, that in our C 60 suspensions was measured at room temperature to be relatively long, about 2−3 ms, which is ∼1000 times longer than the value reported by Bilski et al. The physical mechanism for the asymmetric O 2 (a 1 Δ) PL from C 60 suspensions was studied in depth, indicating that it in fact originates from O 2 molecules trapped in the C 60 lattice within the suspended C 60 aggregates (nC 60 ). This mechanism, which can explain well our above results, was further validated by the nC 60 's high-resolution transmission electron microscopy (HRTEM) images with lattice fringes and the experimental temperature dependence of O 2 (a 1 Δ) lifetimes in nC 60 suspensions. Our findings suggest that the bulk-phase O 2 (a 1 Δ) in aqueous nC 60 suspensions results from the diffusion of the O 2 (a 1 Δ) generated within the interior of nC 60 aggregates.
“…As a contrast, another different aqueous nC 60 suspension was also prepared by using a familiar method in previous literature without organic solvents. The aqueous nC 60 , often termed as stir-nC 60 , was obtained by stirring 100 mg of C 60 powder in 200 mL of deionized water for 2 months via a magnetic stirrer at room temperature according to the method described by Cheng et al 23 Characterization of nC 60 Suspensions. The ultraviolet/visible (UV/vis) absorption spectra of our nC 60 suspensions were taken within a range of 200−900 nm by using a Jasco V550 spectrophotometer at room temperature and corrected for their corresponding solvent backgrounds.…”
The photoexcited aqueous fullerene (C 60 ) suspension was shown to exhibit an asymmetric photoluminescence (PL) spectrum, which, different from the symmetric spectrum observed previously in C 60 solutions or suspensions, still stems from the characteristic phosphorescence of singlet oxygen (O 2 (a 1 Δ)) owing to its dependence on oxygen concentration. In contrast to the microsecond-level lifetime of O 2 (a 1 Δ) in water solutions, that in our C 60 suspensions was measured at room temperature to be relatively long, about 2−3 ms, which is ∼1000 times longer than the value reported by Bilski et al. The physical mechanism for the asymmetric O 2 (a 1 Δ) PL from C 60 suspensions was studied in depth, indicating that it in fact originates from O 2 molecules trapped in the C 60 lattice within the suspended C 60 aggregates (nC 60 ). This mechanism, which can explain well our above results, was further validated by the nC 60 's high-resolution transmission electron microscopy (HRTEM) images with lattice fringes and the experimental temperature dependence of O 2 (a 1 Δ) lifetimes in nC 60 suspensions. Our findings suggest that the bulk-phase O 2 (a 1 Δ) in aqueous nC 60 suspensions results from the diffusion of the O 2 (a 1 Δ) generated within the interior of nC 60 aggregates.
“…It has been proposed that the resistant desorption of hydrophobic organic contaminants from the aggregates of C 60 is due to the adsorption of organic molecules within the micropores of the C 60 aggregates [12,[26][27][28]. Thus, it might be reasonable to speculate that the two groups of nC 60 samples involved in the present study are of different microporous structures, resulting from the differences in aggregate formation between these two groups during the preparation of nC 60 samples.…”
Section: Mechanistic Aspectsmentioning
confidence: 89%
“…A widely studied model fullerene material with mass production relevance [1], C 60, is highly hydrophobic and virtually insoluble in water, as the theoretical solubility of C 60 is only 1.3 Â 10 À5 mg/L [7]. Interestingly, C 60 can be made available in water as stable, nanoscale, colloidal suspensions (referred to as nC 60 herein) through various methods, such as solvent exchange, sonication, or long-term stirring without a solvent [8][9][10][11][12]. Nanoscale C 60 can be stable in aqueous environments for prolonged periods (months to years) and has a high potential for migration through soil and aquifer materials under common environmental conditions [13][14][15].…”
Abstract-Fullerene nanoparticles (nC 60 ) in aqueous environments can significantly enhance the transport of hydrophobic organic contaminants by serving as a contaminant carrier. In the present study, the authors examine the effect of the solvent-exchange process on nC 60 aggregate formation and, subsequently, on nC 60 's contaminant-mobilizing capability. A series of nC 60 samples were prepared using a modified toluene-water solvent-exchange method through the inclusion of a secondary organic solvent in the phase transfer of molecular C 60 in toluene to nC 60 in water. Two groups of solvents-a water-miscible group and a non-water-miscible group-of varied polarity were selected as secondary solvents. The involvement of a secondary solvent in the phase transfer process had only small effects on the particle size and distribution, z potential, and mobility of the nC 60 products but significantly influenced the capability of nC 60 to enhance the transport of 2,2 0 ,5,5 0 -polychlorinated biphenyl (PCB) in a saturated sandy soil column, regardless of whether the secondary solvent was water-miscible or non-water-miscible. The two groups of secondary solvents appear to affect the aggregation properties of nC 60 in water via different mechanisms. In general, nC 60 products made with a secondary water-miscible solvent have stronger capabilities to enhance PCB transport. Taken together, the results indicate that according to formation conditions and solvent constituents, nC 60 will vary significantly in its interactions with organic contaminants, specifically as related to adsorption or desorption as well as transport in porous media. Environ. Toxicol. Chem. 2013;32:329-336. # 2012 SETAC
“…The batch experiments were carried out using various initial concentrations of Cr(VI) (10,20,40,100,140, and 200 g mL The tested suspension was filtered through a cellulose membrane, and the filtrate was used for measuring the chromium concentration.…”
Section: Adsorption and Desorption Experiments Of Fes-edmentioning
confidence: 99%
“…Carbon-based materials such as activated carbon, fullerene C60, carbon nanotubes, and graphene have been widely applied in water purification technology [9][10][11][12]. In particular, activated carbon, which is a micro-porous adsorbent, is very useful for the removal of various pollutants from water [13][14][15].…”
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