Effect of emplaced nZVI mass and groundwater velocity on PCE dechlorination and hydrogen evolution in water-saturated sand
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Reactivity of nZVI increased linearly with nZVI concentration above 10 g/L, but was non-linear below 10 g/L.

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nZVI reactivity with PCE is more sensitive to solution redox potential than solution pH.

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Mass transfer limits the reactivity of emplaced nZVI under typical groundwater flow velocity.

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Lowering pH increases H2 evolution from nZVI more than reactivity with PCE.

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Design of nZVI remediation strategies should consider mass loading and flow velocity on performance and lifetime.

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