Chlorinated aromatic pollutants have caused wide concerns in recent years due to its serious threat to human health and the ecological environment, and its environmental behavior in soil has drawn lots of attentions. In addition, some studies showed the presence of dioxin in pristine sites, the congener profiles in these places are different from those in polluted sites, indicating the possible formation of dioxin through natural processes. This current paper reviewed the research progress about the polymerization of chlorinated aromatic pollutants, even forming dioxin, catalyzed by a natural clay mineral, e.g., montmorillonite, under environmentally relevant conditions. Initially, the chlorinated aromatic compound forms a cation-π bonding with the transition metal in montmorillonite interlayer. Then, one electron is transferred from chlorinated aromatic pollutant to the transition-metal ion. It results in the formation of the organic radical cation and the reduced transition metal. This organic radical can further react with another neutral molecule or radical to form a series of polymerization products, including dioxins. The unique structure of montmorillonite would promote the reaction by stabilizing the radical cation with its unique planar structure and the negative charge in the interlayer microenvironment. For comparison, the reaction cannot happen if only ferric ion exists. Since montmorillonite is one of the most widely distributed clay minerals, chlorinated aromatic pollutants are also ubiquitous in the environment. Furthermore, the reaction can occur under mild conditions. Therefore, this reaction may provide a possible route for the transport and transformation of chlorinated aromatic pollutants and their derivatives in natural environment. It also provides some evidences for natural formation of dioxin. However, more direct observation and investigation are needed to further study the reaction rate and specific polymerization route for some chlorinated aromatic pollutants. We also need to investigate the extent to which this reaction can explain the dioxin natural formation. In this review, we summarized the important factors that would affect the polymerization reactions. For example, the metal cation species in montmorillonite interlayer can affect the rate of electron transfer and the adsorption of chlorinated aromatic pollutants on montmorillonite. Furthermore, the existing form and reaction sites of the metal cation are obviously affected by the presence ofwater molecule and environmental pH. The reactivity of metal cation is reduced by the hydration process, as water molecule can compete with the organic chemicals for the complexation sites of transition metals, hence impeding the direct interaction between organic compound and the metal cation. In addition, molecular mass of chlorinated aromatic pollutants, and chlorine content and position of the chlorinated substitutions also affect the reaction rate and route by changing the adsorption capacity on montmorillonite and the reaction activity/adsorption sites of original molecules. However, currently most research was conducted in the lab, the data from field studies are limited, in real environment, this reaction may be much more complicated. So the mechanism for these effects is still deficient and it needs further in-depth investigation to fully consider more environment factors. In conclusion, this paper not only reviewed the research on the chlorinated aromatic pollutants catalyzed by montmorillonite, but also provided possible directions for future research and some new insights on the transport and transformation of chlorinated aromatic pollutants in the environment, which would be important to evaluate the potential risk and strategies to control chlorinated aromatic compounds, and improve the understanding of the sources for dioxins in the environment.
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