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Thesis - faculty.ait.ac.th - Asian Institute of Technology

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(b) UV-Radiation<br />

UV-radiation is generally coupled wi<strong>th</strong> hydrogen peroxide or ozone to form an<br />

oxidation complex. UV oxidize only certain organic compounds present in le<strong>ac</strong>hate and is<br />

a good disinfectant. When decomposition <strong>of</strong> dioxins in a landfill by advanced oxidation<br />

processes were studied, O3/H2O2 and UV/O3/H2O2 processes were tested to evaluate <strong>th</strong>eir<br />

performances in decomposing dioxins present in a landfill le<strong>ac</strong>hate. The data suggested<br />

<strong>th</strong>at <strong>th</strong>e UV/O3/H2O2 process had better removal efficiency <strong>of</strong> total dioxins <strong>th</strong>an O3/H2O2<br />

process in terms <strong>of</strong> toxicity (Sota, et al., 1999).<br />

(c) Ozonation<br />

The chemical oxidation wi<strong>th</strong> ozone is an innovative technology for <strong>th</strong>e treatment <strong>of</strong><br />

effluents and le<strong>ac</strong>hate <strong>th</strong>at are highly contaminated wi<strong>th</strong> organic chemicals because <strong>of</strong> its<br />

capability to completely convert <strong>th</strong>e organic contaminants to carbon dioxide.<br />

Ozone due to its strong oxidizing ability is effective and pr<strong>ac</strong>tical as a pre-treatment<br />

to remove refr<strong>ac</strong>tory species and as a polishing step to treat organic or increase <strong>th</strong>e<br />

biodegradability <strong>of</strong> refr<strong>ac</strong>tory compounds. The oxidation potential <strong>of</strong> ozone is sufficient for<br />

<strong>th</strong>e direct degradation <strong>of</strong> organic substances. The oxidation <strong>of</strong> organic compounds by<br />

ozone is a zero order re<strong>ac</strong>tion, i.e. <strong>th</strong>e re<strong>ac</strong>tion rate is constant until about 20 % <strong>of</strong> <strong>th</strong>e<br />

initial amount is left (Kylefors, 1997).<br />

Bjorkman and Mavinic (1977) conducted an extensive study <strong>of</strong> physio-chemical<br />

treatment <strong>of</strong> landfill le<strong>ac</strong>hate. The study included <strong>th</strong>e use <strong>of</strong> lime, alum, ozone and <strong>th</strong>eir<br />

various combinations for <strong>th</strong>e treatment <strong>of</strong> municipal solid waste. In <strong>th</strong>e study, after treating<br />

<strong>th</strong>e le<strong>ac</strong>hate wi<strong>th</strong> ozone, <strong>th</strong>e le<strong>ac</strong>hate was re-circulated in an attempt to improve effluent<br />

degradation. It was found <strong>th</strong>at counter-current re-circulation minimized <strong>th</strong>e foaming<br />

problem experienced in <strong>th</strong>e treatment process. However, it was concluded wi<strong>th</strong> ozone<br />

concentrations above 100 mg/L was effective in marginally reducing COD present in <strong>th</strong>e<br />

le<strong>ac</strong>hate.<br />

Gierlich and Kollb<strong>ac</strong>h (1998) reported <strong>th</strong>at ozone was effective in reducing 80 %<br />

ammonia. It was also suggested <strong>th</strong>at ozone treatment was more effective and economical if<br />

biological treatment was adopted as a pretreatment.<br />

Sludge disintegration has been commonly used as a pretreatment for sludge digestion.<br />

The digested sludge has <strong>th</strong>e advantage <strong>of</strong> controlling and reducing sludge bulking in<br />

conventional <strong>ac</strong>tivated sludge processes and <strong>th</strong>us providing an internal carbon source for<br />

biological nutrient removal. However, <strong>th</strong>e feasibility <strong>of</strong> using ozone to chemically<br />

oxygenate sludge to provide an internal carbon source for denitrification processes had not<br />

yet been investigated. This was <strong>th</strong>e research basis for a study conducted by Ahn, et al.<br />

(2001). In <strong>th</strong>e study, <strong>th</strong>e ozonated sludge resulted in a sludge mass reduction and<br />

improvement in <strong>th</strong>e settleability <strong>of</strong> <strong>th</strong>e sludge. The effect <strong>of</strong> sludge ozonation was<br />

determined in terms <strong>of</strong> ei<strong>th</strong>er mineralization or solubilization and changes in residual solid<br />

char<strong>ac</strong>teristics. Bo<strong>th</strong> <strong>th</strong>e solubilization and mineralization increases wi<strong>th</strong> increase in ozone<br />

dosage.<br />

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