Page 336 - Environmental Nanotechnology Applications and Impacts of Nanomaterials
P. 336

Nanomaterials for Groundwater Remediation  321
























        Figure 8.12 Surface modification by strong polyelectrolyte polymers
        enhances transport of nanoiron (RNIP) transport through saturated
        porous media. Polymer-modified iron (striped bars) is highly trans-
        portable through water-saturated sand columns, while unmodified
        nanoiron (black bars) does not transport well through the column, par-
        ticularly at high concentrations (3 g/L).

        Effect of modifier type on transport. Different types of modifiers will pro-
        vide different modes of stabilizing nanoparticles against aggregation and
        attachment to aquifer media grains. These differences lead to different
        elutability and transport distances. For example, the eluted masses of bare
        MRNIP (a polyaspartate-modified nanoiron), a triblock copolymer-
        modified nanoiron, and a surfactant-modified (SDBS) nanoiron through
        a 12.5-cm sand-filled column are shown in Figure 8.13. At 3 g/L, bare RNIP
        has very low transportability (1.4 ! 3% mass elution) through a saturated
        sand column at low ionic strength. Retrieving the sand from the column
        and analyzing for iron revealed that most particles were trapped within
        the first 1 to 2 cm of the column. MRNIP-, polymer-, and SDBS-modified
        RNIP elution was much higher, with the triblock copolymer and MRNIP
        elution at 95 percent and 98 percent, respectively. SDBS was not as effec-
        tive as the polymer but still improved RNIP elution to approximately 50
        percent. These results indicate that surface modification is essential for
        reasonable transport, even at low ionic strength. These differences could
        be used to synthesize particles with specific transport distances that can
        then be used for controlled delivery of nanoparticles to specific regions in
        the subsurface.

        Geochemical effects on transport (pH, ionic strength, and ionic composition).
        Each of the modified particles also responds differently to changes in
                                                      +
                                                             +
        ionic strength and to ionic composition. Both Na and K cations and
   331   332   333   334   335   336   337   338   339   340   341