dc.description.abstract |
The aromatization of low valued readily available hydrocarbons in refinery has been of
great interest over the past two decades to manufacture highly valued marketable products.
In the recent past, the pyrolysis of municipal solid wastes (MSW) has been considered as a
potential and innovative alternative for treating MSW, which resulting in different
chemicals and fuel range hydrocarbons. Waste plastic disposal and excessive use of fossil
fuels have caused environment concerns in the world. Both plastics and petroleum-derived
fuels are hydrocarbons that contain the elements of carbon and hydrogen. The difference
between them is that plastic molecules have longer carbon chains than those in LPG, petrol,
and diesel fuels. Therefore, it is possible to convert waste plastic into fuels. The overall
objectives of this study is to investigate the effect of thermocatalytic pyrolysis of waste
plastics over commercial and natural catalyst in order to produce environmentally friendly
fuel and valuable aromatics benzene, toluene, ethyl benzene and xylene (BTEX).
In this study, thermal and catalytic pyrolysis of waste plastics polyethylene (PE),
polypropylene (PP) and polystyrene (PS) were carried out in a semi-batch in a nitrogen
atmosphere. The valuable BTEX were effectively produced from waste plastics using
commercial ZSM-5 and fly ash synthesized catalyst. The BTEX yield was enhanced
significantly using multiphase catalytic pyrolysis of polyethylene, polypropylene and
polystyrene. The BTEX content was significantly increased due to effective interaction
between catalyst and target molecules i.e., lower paraffins within the reactor.
Low cost natural catalyst was synthesized from fly ash (FA) in 5 different synthesized form
i.e., fly ash in natural form (FAN), fly ash calcined at 600 oC (FA-600), 700 oC (FA-700),
800 oC (FA-800) and 900 oC (FA-900). The thermal and catalytic pyrolysis both were
conducted in a specially designed semi-batch reactor at the temperature range of 500–800
oC. The catalytic pyrolysis were performed in three different phases within the reactor batch
by batch systematically, keeping the catalyst in a vapor phase (A-Type), liquid phase (Btype) and liquid and vapor phase/multiphase (C-Type), respectively. The optimum
pyrolysis temperature for the production of BTEX was found to be 700 oC for both thermal
and catalytic pyrolysis of waste plastic PE, PP and PS. Total aromatics (BTEX) of 10.75
wt. % for PE, 30.91 wt. % for PP and 13.58 wt. % for PS were obtained for thermal
pyrolysis at a temperature of 700 oC. In contrary, the aromatic (BTEX) contents were
significantly increased for the catalytic pyrolysis in A-type, B-type and C-type reactor
arrangement. C-type reactor arrangement gives maximum BTEX content for all types of
waste plastic due to selective cracking in both liquid and vapor phase. BET surface area
analysis and SEM-EDX suggests that FA-800 catalyst could be the superior catalyst due to
its maximum surface area 310.10 m2
/g and (Si/Al) ratio of 16.03. The maximum BTEX of
39.47 wt. % for PE, 53.12 wt. % for PP and 26.86 wt. % for PS was obtained for commercial
catalyst ZSM-5 in C-type reactor arrangement. Whereas, it was 22.10 wt. % for PE, 43.43
wt. % for PP and 20.92 wt. % for PS using FA-800 catalyst. The results indicate that the
performance of FA-800 catalyst is comparable to commercial ZSM-5 in terms of liquid
yield and aromatics/BTEX content. The test results for catalyst stability indicates that the
commercial ZSM-5 and synthesized FA-800 catalyst is stable upto 2nd run and slight change
was observed in liquid yield and BTEX content. Regenerated catalyst showed similar
results as that of fresh catalyst. Physicochemical properties of the pyrolysis oil shows that
it can be used as alternative fuels and as a source of valuable chemicals such as benzene,
toluene, ethyl benzene or xylene |
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