TY - JOUR
T1 - Removing methyl-tert-butyl ether (MTBE) from water
T2 - 228th ACS National Meeting
AU - Mezyk, Stephen P.
AU - Cooper, William J.
AU - Martin, Ned H.
AU - Cramer, Chris
AU - O'Shea, Kevin E.
AU - Von Sonntag, Clemens
PY - 2004/12/1
Y1 - 2004/12/1
N2 - Free radical bimolecular rate constants for MTBE reaction with the hydroxyl radical (•OH), the solvated electron and the hydrogen atom (H•) and the subsequent reaction of the oxidized carbon-centered radicals with oxygen were measured. The measured reaction rate constants for hydrated electron (< 8 × 106/M-sec) and hydrogen atom (3.49 × 106/M-sec) reaction showed that these species would not be important in the removal of contaminated MTBE in natural waters. However, the competition-kinetics derived overall •OH reaction rate constant of K2+3 = 1.71 × 109/M-sec showed that this oxidative process was the dominant initial degradation pathway. The decay of these MTBE peroxyl radicals in solution was complex. The multiple decays of the three different tetroxides accounted for the mixture of major (TBF, tert-butyl alcohol, acetone, methyl acetate) and minor (formaldehyde, 2-methyl-2-methoxy propanal, pyruvaldehyde, hydroxy-iso-butyraldehyde, iso-butyraldehyde and hydroxy acetone) degradation products observed experimentally. These products would themselves undergo analogous free-radical-induced decomposition chemistry, until ultimately, mineralization of MTBE could be achieved. This is an abstract of a paper presented at the 228th ACS National Meeting (Philadelphia, PA 8/22-26/2004).
AB - Free radical bimolecular rate constants for MTBE reaction with the hydroxyl radical (•OH), the solvated electron and the hydrogen atom (H•) and the subsequent reaction of the oxidized carbon-centered radicals with oxygen were measured. The measured reaction rate constants for hydrated electron (< 8 × 106/M-sec) and hydrogen atom (3.49 × 106/M-sec) reaction showed that these species would not be important in the removal of contaminated MTBE in natural waters. However, the competition-kinetics derived overall •OH reaction rate constant of K2+3 = 1.71 × 109/M-sec showed that this oxidative process was the dominant initial degradation pathway. The decay of these MTBE peroxyl radicals in solution was complex. The multiple decays of the three different tetroxides accounted for the mixture of major (TBF, tert-butyl alcohol, acetone, methyl acetate) and minor (formaldehyde, 2-methyl-2-methoxy propanal, pyruvaldehyde, hydroxy-iso-butyraldehyde, iso-butyraldehyde and hydroxy acetone) degradation products observed experimentally. These products would themselves undergo analogous free-radical-induced decomposition chemistry, until ultimately, mineralization of MTBE could be achieved. This is an abstract of a paper presented at the 228th ACS National Meeting (Philadelphia, PA 8/22-26/2004).
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M3 - Conference article
AN - SCOPUS:23744511795
SN - 1524-6434
VL - 44
SP - 381
EP - 386
JO - ACS, Division of Environmental Chemistry - Preprints of Extended Abstracts
JF - ACS, Division of Environmental Chemistry - Preprints of Extended Abstracts
IS - 2
Y2 - 22 August 2004 through 26 August 2004
ER -