As a resource treatment method, pyrolysis realizes the
recovery
of oil and immobilization of heavy metals in oily sludge (OS). The
results showed that the composition of OS had little effect on the
trend of the whole pyrolysis process, but it had different effects
on the mass loss and maximum weight loss rate at each pyrolysis stage.
SEM–EDS results showed that the pyrolysis residue had a porous
internal structure, which was similar to that of activated carbon.
The elements S, Ca, O, Fe, Al, and Si were embedded in the carbon
skeleton. After OS pyrolysis, the oil content of the solid residue
was far less than 2%, which met the pollution control requirements
for comprehensive utilization specified in China’s oil and
gas industry standard. At the same time, the ratio of exchangeable
fraction decreased and the ratio of residual fraction increased after
OS pyrolysis. The potential ecological hazard coefficient (
E
r
) of Cd in OS2, OS2-500, and OS2-600 was greater
than 40, which were strong and medium hazards. The
E
r
values of OS2-700 and other metals were far lower than
40, which were low hazards. With the increase of pyrolysis temperature,
the comprehensive ecological hazard index (RI) of heavy metals in
the residue gradually decreased and the RI value of OS2-700 decreased
to 28.01. Therefore, the pyrolysis residue had an internal porous
structure and controllable environmental risk. It could be used as
an adsorption material for heavy metals to realize the comprehensive
utilization of OS.