Page 457 - Environmental Nanotechnology Applications and Impacts of Nanomaterials
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434   Potential Impacts of Nanomaterials

        have shown to have the highest mobility and can migrate 10 meters in
        unfractured sand aquifers (Lecoanet et al., 2004). Studies have also shown
        that fullerol toxicity can increase in the presence of light (Pickering and
        Wiesner, 2005). These studies underline the importance of basic nano-
        materials chemistry to predict potential adverse effects.


        Conclusion
        Many of the studies discussed in this chapter clearly indicate that nano-
        materials interact with biological systems. Composition, size, and sur-
        face property are important attributes that are needed to predict
        biological effects. It is intriguing to realize that although materials of
        vastly different chemical compositions have similar interactions with
        biological systems—the clearest example being preferential cellular
        uptake of anionic iron oxide nanoparticles and QD. Size also seems to
        be an important factor. The precise nature of toxicity seen is a function
        of the chemistry of the particle. The physical chemical properties of
        many nanoparticle surface modifications may be the factor that deter-
        mines their ultimate safety. A great deal of literature exists for those
        nanomaterials with commercial applications, including titanium diox-
        ide particles for sunscreens and iron oxide particles or QD for imaging.
        Similarly, pivotal disposition and cell targeting data are often available
        for those nanomaterials intended for use in drug delivery, such as seen
        with QD, fullerenes, and carbon nanotubes. There is a serious lack of
        information about human health and environmental implications of
        manufactured nanomaterials. This emerging field of nanotoxicology
        will continue to grow as new products are produced. The need for toxi-
        cology studies will increase for use in risk assessment. Knowledge of
        exposure and hazard are needed for understanding risks associated
        with nanomaterials. This chapter has explored the beginning threads
        of nanomaterial toxicology for a variety of nanomaterials.



        References
        Akerman, M.E., Chan, W.C.W., Laakkonen, P., Bhatia, S.N., and Ruoslahti, E. (2002)
          “Nanocrystal targeting in vivo,” Proceeding of the National Academy of Sciences Natl.
          Acad. Sci., 99(20):12617–12621.
        Allen, D.G., Riviere, J.E., and Monteiro-Riviere, N.A. (2001) “Cytokine induction as a meas-
          ure of cutaneous toxicity in primary and immortalized porcine keratinocytes exposed
          to jet fuels, and their relationship to normal human epidermal keratinocytes,” Toxicology
          Letters., 119:209–217.
        Anzai, Y., Piccoli, C.W., Outwater, E.K., Stanford, W., Bluemke, D.A., Nurenberg, P., Saini,
          S., Maravilla, K.R., Feldman, D.E., Schmiedl, U.P., Brunberg, J.A., Francis, I.R., Harms,
          S.E., Som, P.M., and Tempany, C.M. (2003) “Evaluation of neck and body metastases
          to nodes with ferumoxtran 10-enhanced MR imaging: phase III safety and efficacy
          study,” Radiology, 228:777–788.
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