Geraniol (2,6-dimethyl-2,6-octadien-8-ol) reactions with ozone and OH radical: Rate constants and gas-phase products
The bimolecular rate constants, k OH+geraniol, (231±58)×10 −12 cm 3 molecule −1 s −1 and k O 3 + geraniol , (9.3±2.3)×10 −16 cm 3 molecule −1 s −1, were measured using the relative rate technique for the reaction of the hydroxyl radical (OH) and ozone (O 3) with 2,6-dimethyl-2,6-octadien-8-ol (geran...
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Veröffentlicht in: | Atmospheric environment (1994) 2007-02, Vol.41 (6), p.1188-1199 |
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Sprache: | eng |
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Zusammenfassung: | The bimolecular rate constants,
k
OH+geraniol, (231±58)×10
−12
cm
3
molecule
−1
s
−1 and
k
O
3
+
geraniol
, (9.3±2.3)×10
−16
cm
3
molecule
−1
s
−1, were measured using the relative rate technique for the reaction of the hydroxyl radical (OH) and ozone (O
3) with 2,6-dimethyl-2,6-octadien-8-ol (geraniol) at (297±3)
K and 1 atmosphere total pressure. To more clearly define part of geraniol's indoor environment degradation mechanism, the products of the geraniol+OH and geraniol+O
3 reactions were also investigated. The identified geraniol+OH and geraniol+O
3 reaction products were: acetone, hydroxyacetaldehyde (glycolaldehyde, HC(
O)CH
2OH), ethanedial (glyoxal, HC(
O)C(
O)H), and 2-oxopropanal (methylglyoxal, CH
3C(
O)C(
O)H). The use of derivatizing agents O-(2,3,4,5,6-pentafluorobenzyl)hydroxylamine (PFBHA) and N,O-bis(trimethylsilyl) trifluoroacetamide (BSTFA) were used to propose 4-oxopentanal as the other major geraniol+OH and geraniol+O
3 reaction product. The elucidation of this other reaction product was facilitated by mass spectrometry of the derivatized reaction products coupled with plausible geraniol+OH and geraniol+O
3 reaction mechanisms based on previously published volatile organic compound+OH and volatile organic compound+O
3 gas-phase reaction mechanisms. |
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ISSN: | 1352-2310 1873-2844 |
DOI: | 10.1016/j.atmosenv.2006.09.042 |