TY - JOUR
T1 - Insight into Methyl tert-Butyl Ether (MTBE) stable isotope fractionation from abiotic beference experiments
AU - Elsner, Martin
AU - Mckelvie, Jennifer
AU - Couloume, Georges Lacrampe
AU - Lollar, Barbara Sherwood
PY - 2007/8/15
Y1 - 2007/8/15
N2 - Methyl group oxidation, SN2-type hydrolysis, and S N1-type hydrolysis are suggested as natural transformation mechanisms of MTBE. This study reports for the first time MTBE isotopic fractionation during acid hydrolysis and for oxidation by permanganate. In acid hydrolysis, MTBE isotopic enrichment factors were εC = -4.9‰ ± 0.6‰ for carbon and εH = -55‰ ±7‰ for hydrogen. Position-specific values were εC,reactive position = -24.3‰ ± 2.3‰ and εH,reactive position = -73‰ ± 9‰, giving kinetic isotope effects KIEC = 1.025 ± 0.003 and KIEH = 1.08 ± 0.01 consistent with an SN1-type hydrolysis involving the tert-butyl group. The characteristic slope of Δδ2Hbulk/ Δδ13Cbulk ≈ εbulk,H/ εbulk,C = 11-1 ± 1-3 suggests it may identify S N1-type hydrolysis also in settings where the pathway is not well constrained. Oxidation by permanganate was found to involve specifically the methyl group of MTBE, similar to aerobic biodegradation. Large hydrogen enrichment factors of εH = -109‰ ± 9‰ and εH,reactive position = -342‰ ± 16‰ indicate both large primary and large secondary hydrogen isotope effects. Significantly smaller values reported previously for aerobic biodegradation suggest that intrinsic fractionation is often masked by additional non-fractionating steps. For conservative estimates of biodegradation at field sites, the largest e values reported should, therefore, be used.
AB - Methyl group oxidation, SN2-type hydrolysis, and S N1-type hydrolysis are suggested as natural transformation mechanisms of MTBE. This study reports for the first time MTBE isotopic fractionation during acid hydrolysis and for oxidation by permanganate. In acid hydrolysis, MTBE isotopic enrichment factors were εC = -4.9‰ ± 0.6‰ for carbon and εH = -55‰ ±7‰ for hydrogen. Position-specific values were εC,reactive position = -24.3‰ ± 2.3‰ and εH,reactive position = -73‰ ± 9‰, giving kinetic isotope effects KIEC = 1.025 ± 0.003 and KIEH = 1.08 ± 0.01 consistent with an SN1-type hydrolysis involving the tert-butyl group. The characteristic slope of Δδ2Hbulk/ Δδ13Cbulk ≈ εbulk,H/ εbulk,C = 11-1 ± 1-3 suggests it may identify S N1-type hydrolysis also in settings where the pathway is not well constrained. Oxidation by permanganate was found to involve specifically the methyl group of MTBE, similar to aerobic biodegradation. Large hydrogen enrichment factors of εH = -109‰ ± 9‰ and εH,reactive position = -342‰ ± 16‰ indicate both large primary and large secondary hydrogen isotope effects. Significantly smaller values reported previously for aerobic biodegradation suggest that intrinsic fractionation is often masked by additional non-fractionating steps. For conservative estimates of biodegradation at field sites, the largest e values reported should, therefore, be used.
UR - http://www.scopus.com/inward/record.url?scp=34548085959&partnerID=8YFLogxK
U2 - 10.1021/es070531o
DO - 10.1021/es070531o
M3 - Article
C2 - 17874775
AN - SCOPUS:34548085959
SN - 0013-936X
VL - 41
SP - 5693
EP - 5700
JO - Environmental Science and Technology
JF - Environmental Science and Technology
IS - 16
ER -