Page 258 - Environmental Nanotechnology Applications and Impacts of Nanomaterials
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Nanoparticle Transport, Aggregation, and Deposition  243

        (or equivalently, mobility) will have the effect of reducing concentra-
        tions in environmental systems. Aggregation may occur between
        nanoparticles or with other materials (heteroaggregation). In either
        case, a reduction in stability associated with an increase in aggrega-
        tion rate has direct consequences for the removal of nanoparticles
        from air and water in engineered systems (e.g., water and wastewater
        treatment systems) as well as in the environment.
          The role of aggregation in determining toxicity may be less evident.
        Reductions in active surface area that occur during aggregation and an
        increased proximity of particle surface area within aggregates may
        fundamentally reduce reactivity compared with nanoparticles in an
        unaggregated state. Recent evidence suggests that destabilized
        nanoparticles experience a decreased ability to produce reactive oxygen
        species [23] and this may have implications regarding their toxicity [24].
        Aggregation may also alter the bioavailability of the nanomaterial if
        larger materials are less capable of entering cells. Conversely, aggre-
        gation may be at the heart of the toxic response as in the case of carbon
        nanotube agglomeration within lungs, which has been observed to lead
        to suffocation in laboratory animals where these materials were inten-
        tionally introduced [25, 26]. It is possible that heteroaggregation of
        nanoparticles with organic molecules or other materials may essentially
        imbed the nanomaterial in another functionality or may alter the avail-
        ability of the nanomaterial due to changes in size or chemistry.
        Aggregation will be equally important in environmental engineering
        applications of nanomaterials. The proposed use of nanoparticles for
        groundwater remediation is one example where nanoparticle aggrega-
        tion may decrease the effective surface area of the particles, which
        reduces their ability to effectively oxidize or react with other com-
        pounds. Aggregation may affect the mobility of the nanomaterial and
        therefore the ability to deliver nanoparticles to a desired location in the
        subsurface. In summary, the environmental applications, exposures,
        and effects of nanoparticles are therefore likely to depend on the con-
        ditions under which nanoparticles remain as discrete units or aggre-
        gate into clusters.
          Some nanomaterials have an inherently small affinity for water.
        For example, the fullerene C 60  is negligibly soluble in water. Such
        nanomaterials may be modified to make them compatible with a given
        end-use or processing requirements in aqueous systems. Nanoparticles
        may be further modified to maintain a stable suspension. Particle
        suspensions are commonly stabilized through changes in solution
        chemistry or modification of particle surface chemistry [27]. How-
        ever, functionalizing nanoparticles surfaces may compromise the
        characteristics of the nanoparticles that make them desirable in the
        first place.
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