Sulfidation doses of nanoscale zerovalent iron particles need to be tuned to achieve high reactivity to different chlorinated solvent compounds

03 November 2025, Version 1
This content is an early or alternative research output and has not been peer-reviewed by Cambridge University Press at the time of posting.

Abstract

The sulfur content in sulfidated nanoscale iron (S-nZVI) alters the degradation efficiency of trichloroethene (TCE), a common groundwater contaminant, but its impact on other chlorinated hydrocarbon contaminants (CHCs) has not been characterized. In this study, the anaerobic degradation of carbon tetrachloride (CT), chloroform (CF), trichloroethane (1,1,1-TCA) and TCE was assessed using S-nZVI at seven S loadings ([S/Fe] = 0.01−0.303). S-nZVI0.01 yielded the highest degradation rate constants for CT, 1,1,1-TCA, and CF, 1.77−10.9 times higher than nZVI and other S-nZVI. In contrast, S-nZVI0.075 yielded the highest rate constant for TCE. S-nZVI0.01 provides the most rapid electron release, and because CT, 1,1,1-TCA, and CF have higher electron affinity than water, their degradation is quickest at this [S/Fe]. TCE degradation was faster only at higher [S/Fe], where S-nZVI reactivity to water was diminished, and S-nZVI0.075 provided a 20-fold enhancement in electron selectivity to TCE over H2O. Although TCE was completely dechlorinated, the other CHCs were only partially dechlorinated. The degradation products dichloromethane and 1,1-dichloroethane were dechlorinated in the presence of their parent CHCs and at specific [S/Fe], although they were not dechlorinated as sole compounds. The results demonstrate that dechlorination rates and extents of CHCs can be optimized by tuning the sulfidation dose.

Keywords

Sulfidated nZVI
chlorinated hydrocarbons
dechlorination
electron selectivity
groundwater remediation

Supplementary materials

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Mu et al 2025 Supporting Information
Description
Additional information on particle synthesis and characterization; analytical methods and data analysis including BET surface aera, [S/Fe]particle relative to [S/Fe]dosed, Fe0 content, maximum available electrons, , observed rate constant, timed based CHC removal, H2 generation rate and extent, impact on surrounding pH, XPS spectra of reacted S-nZVI, electron selectivity and time based byproduct generation during CHC degradation.
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