Complex interplay between formation routes and natural organic matter modification controls capabilities of C_(60)nanoparticles(nC_(60)) to accumulate organic contaminants

Accumulation of organic contaminants on fullerene nanoparticles（nC（60）） may significantly affect the risks of C（60） in the environment.The objective of this study was to further understand how the interplay of nC（60） formation routes and humic acid modification affects contaminant adsorption of nC（60）.Specifically,adsorption of 1,2,4,5-tetrachlorobenzene（a model nonionic,hydrophobic organic contaminant） on nC（60） was greatly affected by nC（60）formation route- the formation route significantly affected the aggregation properties of nC（60）,thus affecting the available surface area and the extent of adsorption via the pore-filling mechanism.Depending on whether nC（60） was formed via the ＂top-down＂ route（i.e.,sonicating C（60） powder in aqueous solution） or ＂bottom-up＂ route（i.e.,phase transfer from an organic solvent） and the type of solvent involved（toluene versus tetrahydrofuran）,modification of nC（60） with Suwannee River humic acid（SRHA） could either enhance or inhibit the adsorption affinity of nC（60）.The net effect depended on the specific way in which SRHA interacted with C（60） monomers and/or C（60） aggregates of different sizes and morphology,which determined the relative importance of enhanced adsorption from SRHA modification via preventing C（60） aggregation and inhibited adsorption through blocking available adsorption sites.The findings further demonstrate the complex mechanisms controlling interactions between nC（60） and organic contaminants,and may have significant implications for the life-cycle analysis and risk assessment of C（60）.

水环境中天然有机物对纳米颗粒吸附铅和镉的不同作用

为阐明天然有机物(NOM)在纳米颗粒(NPs)吸附重金属中的作用,研究了蛋白质(牛血清白蛋白,BSA)、碳水化合物(海藻酸钠,NaAlg)和腐殖酸(HA)对二氧化钛纳米颗粒(TNPs)和氧化铈纳米颗粒(CNPs)聚集沉降和吸附Cd^(2+)和Pb^(2+)的影响.结果表明,当Pb^(2+)和Cd^(2+)在20—120 mg·L-1范围内,HA和NaAlg显著促进了TNPs和CNPs对这些金属离子的吸附(P<0.05),而BSA对这些金属吸附的影响甚微.TNPs-HA和TNPs-NaAlg对Pb^(2+)的吸附分别提高了14%—41%和16%—57%,对Cd^(2+)的吸附分别提高了12%—112%和22%—143%.与CNPs相比,CNPs-HA和CNPs-NaAlg对Pb^(2+)的吸附增加了21%—71%和23%—65%,对Cd^(2+)的吸附增加了26%—45%和45%—91%.并且NPs和NPs-NOM对Pb^(2+)和Cd^(2+)的吸附符合Freundlich吸附模型.离子强度的增加抑制了NPs-HA/NaAlg和NPs对Pb^(2+)和Cd^(2+)的吸附,而pH的增加对NPs-HA/NaAlg和NPs吸附Pb^(2+)和Cd^(2+)起促进作用.