Palm oil production is a major agricultural industry in Malaysia. In 2006, there were
more than 4.2 million ha. of palm oil plantations which produced 16 million tons of oil
(Chou, 2007). In total, about 110 million tons of renewable non-oil biomass (trunk,
fronds, shells, palm press fiber and the empty fruit bunches) are produced each year.
Furthermore, approximately 0.65 tons of raw Palm Oil Mill Effluent (POME) is produced for every
ton of fresh fruit bunches. In 2006, palm oil mills in Malaysia produced more than 58
million tons of POME (Chou, 2007). POME is an acidic, brownish, colloidal
suspension, characterized by high content of organics and solids and is discharged at a temperature of 80-90 °C (Table
1). Wastewater treatment facility is one of the most important components in the
palm oil industry. This facility is normally used to treat a large volume of POME generated during the
production of Crude Palm Oil (CPO) before the effluent is safely discharged to the
surrounding environment through water canal or river (Saifuddin and Fazlili, 2009). Specifically,
the amount of POME generated is approximately 3.8
m3 for each ton of CPO produced (Ma and Ong, 1988). The problems associated with aerobic treatment of POME using a
pond system are long retention time (90-120 days), large area requirement and high demand
for maintenance, loss of nutrition and high emission of methane. It is important to develop
an alternative concept for POME treatment (Ma, 2000).
Ultrasonication has been widely used to degrade organic compounds from wastewater
for many years; many reports were published about the sonochemical degradation of
individual organic compounds (Songlin Wang et
al., 2008). However, very little was reported about
the effect of ultrasonic irradiation to real wastewater like POME. Sonochemical
decomposition of organic pollutants in aqueous solution is a consequence of the formation and collapse
of high-energy cavitation bubbles. Upon collapse, the solvent vapor is subjected to an
enormous increase in temperature and pressure (Vicenzo Naddeo
et al., 2007). Under such extreme conditions, the solvent molecules undergo hemolytic bond breakage to generate
radicals. When water is sonicated, +H and -OH radicals are produced; the latter is a strong
oxidizing agent and can react with organic pollutants (Chu
et al., 2001). |