Combining iron with a tetraamido-macrocyclic
ligand (Fe-TAML) as
a catalyst and with hydrogen peroxide (H2O2)
as the bulk oxidant is a process that has been suggested for the oxidative
abatement of micropollutants during water treatment. In this study,
the reactivity of the Fe-TAML/H2O2 system was
evaluated by investigating the degradation of a group of electron-rich
organic model compounds with different functional groups in a secondary
wastewater effluent. Phenolic compounds and a polyaromatic ether are
quickly and substantially abated by Fe-TAML/H2O2 in a wastewater effluent. For tertiary amines, a moderate rate of
abatement was observed. Primary and secondary amines, aromatic ethers,
aromatic aldehydes, and olefins are oxidized too slowly in the investigated
Fe-TAML/H2O2 systems to be significantly abated
in a secondary wastewater effluent. Trichlorophenol is readily oxidized
to chloromaleic acid and chlorofumaric acid, which support a one-electron
transfer reaction as the initial step of the reaction between Fe-TAML/H2O2 and the target compound. Fe-TAML/H2O2 does not oxidize bromide to hypobromous acid; however,
iodide is oxidized to hypoiodous acid, and as a consequence, the H2O2 consumption is accelerated by a catalytic reaction
in iodide-containing water. Overall, Fe-TAML/H2O2 is a rather selective oxidant, which makes it an interesting system
for the abatement of electron-rich phenolic-type pollutants.