The pathway with the name Trinexapac-ethyl
 has the following structure: 
Result: 
C1CC1/C(=C/2\C(=O)CC(CC2=O)C(=O)O)/O
 no rule associatedC(=O)=O
CCOC(=O)C1CC(=O)/C(=C(\C2CC2)/O)/C(=O)C1
 SimpleRule(uri = https://envipath.org/package/32de3cf4-e3e6-4168-956e-32fa5ddb0ce1/simple-rule/57d978b5-f55f-462e-a9dc-c5908d165973, SMIRKS = [#6:2]-[#8:1]-[#6:6](-[#1,#6:3])=[O:7]>>[H][#8]-[#6:2].[#8-:1]-[#6:6](-[#1,#6:3])=[O:7]) C1CC1/C(=C/2\C(=O)CC(CC2=O)C(=O)O)/O

Description: In four aerobic soil biodegradation studies with trinexapac-ethyl, the presence of the degradation product trinexapac-acid was confirmed. In Study c, maximum formation rate was 96 and 98% of AR, Mineralisation measured as volatile CO2 and bound residues were maximally 56% and 20% after 90 and 59 days for [14C-ring]-trinexapac-ethyl, and 49% and 13% for [14C-carbonyl]-trinexapac-ethyl. In Study d, performed with 1,2,6-14C-trinexapac-ethyl, trinexapac-acid was found in 93% of AR.
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