Fe-TAML/peroxide
catalysis provides simple, powerful, ultradilute
approaches for removing micropollutants from water. The typically
rate-determining interactions of H2O2 with Fe-TAMLs
(rate constant k
I) are sharply pH-sensitive
with rate maxima in the pH 9–10 window. Fe-TAML design or process
design that shifts the maximum rates to the pH 6–8 window of
most wastewaters would make micropollutant eliminations even more
powerful. Here, we show how the different pH dependencies of the interactions
of Fe-TAMLs with peroxide or hypochlorite to form active Fe-TAMLs
(k
I step) illuminate why moving from H2O2 (pK
a, ca. 11.6)
to hypochlorite (pK
a, 7.5) shifts the
pH of the fastest catalysis to as low as 8.2. At pH 7, hypochlorite
catalysis is 100–1000 times faster than H2O2 catalysis. The pH of maximum catalytic activity is also moderated
by the pK
a’s of the Fe-TAML axial
water ligands, 8.8, 9.3, and 10.3, respectively, for [Fe{4-NO2C6H3-1,2-(NCOCMe2NSO2)2CHMe}(H2O)
n
]− (2) [n = 1–2],
[Fe{4-NO2C6H3-1,2-(NCOCMe2NCO)2CF2}(H2O)
n
]− (1b), and [Fe{C6H4-1,2-(NCOCMe2NCO)2CMe2}(H2O)
n
]− (1a). The new bis(sulfonamido)-bis(carbonamido)-ligated 2 exhibits the lowest pK
a and
delivers the largest hypochlorite over peroxide catalytic rate advantage.
The fast Fe-TAML/hypochlorite catalysis is accompanied by slow noncatalytic
oxidations of Orange II.