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

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(Yoon, et al., 1998). This shows <strong>th</strong>at <strong>th</strong>e complex higher molecular weight compounds<br />

could be degraded effectively using membrane biore<strong>ac</strong>tor systems. For <strong>th</strong>e yeast and<br />

b<strong>ac</strong>teria effluent, <strong>th</strong>e increase <strong>of</strong> <strong>th</strong>e COD <strong>of</strong> below 5 k MW fr<strong>ac</strong>tion could be explained by<br />

<strong>th</strong>e biodegradation <strong>of</strong> high molecular weight organic substances to compounds below 5 k<br />

MW, as confirmed by <strong>th</strong>e decrease <strong>of</strong> <strong>th</strong>e COD <strong>of</strong> <strong>th</strong>e 5 k MW UF retentate. Similar<br />

results were obtained while treating le<strong>ac</strong>hate in aerobic and anaerobic system by Gourdon,<br />

et al. (1989). The studies also revealed <strong>th</strong>at recalcitrant organics were non-degradable in<br />

anaerobiosis, while it could be degraded to 50% in aerobic conditions.<br />

The COD removal after <strong>th</strong>e membrane biore<strong>ac</strong>tor treatment was from 7,500 mg/L to<br />

about 1,950 mg/L in bo<strong>th</strong> <strong>th</strong>e re<strong>ac</strong>tors. Among <strong>th</strong>e COD <strong>of</strong> 7,500 mg/L, about 5,500 mg/L<br />

was removed by <strong>th</strong>e membrane biore<strong>ac</strong>tor system, ei<strong>th</strong>er <strong>th</strong>rough degradation for energy<br />

consumption or <strong>th</strong>rough assimilation.<br />

To fur<strong>th</strong>er understand <strong>th</strong>e degradable components present in <strong>th</strong>e le<strong>ac</strong>hate and <strong>th</strong>eir<br />

molecular weight distribution, ano<strong>th</strong>er sample was analyzed wi<strong>th</strong> BOD along wi<strong>th</strong> COD<br />

after fr<strong>ac</strong>tionation. Figure 4.41 and 4.42 gives <strong>th</strong>e COD and BOD contribution <strong>of</strong><br />

compounds at different molecular weight. Table H-4 <strong>of</strong> Appendix H gives <strong>th</strong>e detailed<br />

calculation <strong>of</strong> <strong>th</strong>e results. In <strong>th</strong>e second sample showed a slight difference from <strong>th</strong>e first<br />

sample. The > 50 k fr<strong>ac</strong>tion decreased from 91% to 72% and corresponding increase <strong>of</strong> <strong>th</strong>e<br />

< 5 k from 0 to 18%.<br />

When <strong>th</strong>e analysis <strong>of</strong> <strong>th</strong>e molecular weight fr<strong>ac</strong>tions having organic matter below<br />

MW 500 <strong>of</strong> <strong>th</strong>e le<strong>ac</strong>hate was done, it has been shown <strong>th</strong>at <strong>th</strong>ey contain syn<strong>th</strong>etic organics<br />

and solvents such as aromatic and alcoholic groups. Phenols, amines and chlorinated<br />

organics were also found in <strong>th</strong>is fr<strong>ac</strong>tion. As suggested earlier, <strong>th</strong>e fr<strong>ac</strong>tions in 5 k to 10 k<br />

and higher molecular weight contained humic and fulvic substances, along wi<strong>th</strong> products<br />

<strong>of</strong> municipal dumping and natural fermentation (Slater, et al., 1985). In ano<strong>th</strong>er study on<br />

le<strong>ac</strong>hate sample suggested <strong>th</strong>at relatively high concentrations <strong>of</strong> carbohydrates could be<br />

observed in a high molecular weight fr<strong>ac</strong>tions and substantial quantities <strong>of</strong> aromatic<br />

hydroxyl and carboxylic compounds present in <strong>th</strong>e lower molecular weight fr<strong>ac</strong>tion (Chian,<br />

1977).<br />

112

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