Biodegraded
oils have been widely discovered throughout the world, whereas the
alteration of the molecular composition of oils at extreme levels
(>PM8) has been insufficiently documented. A suite of crude oils
from Carboniferous volcanic reservoirs in the eastern Chepaizi Uplift,
Junggar Basin, experienced severe to extreme biodegradation (from
PM6+ to PM9+), which provided an ideal case for the present study.
This investigation showed that the variations in molecular composition
were not strictly consistent with their stepwise fashion in established
schemes. The idea that 25-norhopanes are derived from hopanes was
confirmed by the sharp decreases in the C29 hopane/gammacerane
(C29H/G) and C30 hopane/gammacerane (C30H/G) values at the level of extreme biodegradation, which were associated
with the increases in their counterparts of C28 25-norhopane/gammacerane
(C28 25-NH/G) and C29 25-norhopane/gammacerane
(C29 25-NH/G). 25-Norhopanes were also biodegraded at an
extreme level, with C29 25-NH being more susceptible than
C28 25-NH. The preferential biodegradation of individual
homohopanes by carbon number occurred at an extreme level, whereas
C29H featured more bioresistance than C30H and
shared a similar susceptibility to biodegradation as 18α-30-norneohopane
(C29Ts). The formation of 22R isomers
for 25-norhopanes seemed to be favored over that of 22S isomers, although the 22S isomer was degraded faster
that the 22R epimer for the C31, C32, and C33 homohopanes. However, the constant values
of 22S/(22S + 22R) for the C34 homohopane implied no preferential biodegradation
of 22S or 22R isomers for this extended
hopane. Lower molecular weight tricyclic terpanes (TTs) were preferentially
removed at extreme biodegradation levels, and the late eluting stereoisomers
were degraded faster than the early eluting stereoisomers for C26TT, C28TT, and C29TT. C24 tetracyclic terpane (C24Tet) is much more resistant to
biodegradation than TTs. Pregnanes have a similar susceptibility to
biodegradation as gammacerane, but they are more resistant than C23TT. The biodegradation of regular steranes was characterized
by their faster depletion than diasteranes and the preferential depletion
of C27 regular sterane to the C29 homologue
and the 20R isomers to the 20S isomers.
At the extreme level, even C20 and C21 triaromatic
steroids (TAS) were distinctively reduced, coexisting with the relatively
highly degraded steranes and terpanes, although water washing can
also be responsible for the decreases in (C20 + C21)-TAS/C26–28-TAS values.