In this dissertation, laboratory experiments were conducted to compare the efficacies to treat stabilized landfill leachate, by several photochemical oxidation processes, such as UV/H2O2, UV/O3, and UV/H2O2/O3. The leachate came from a municipal sanitary landfill located in northwest China and the average values of its main parameters were: pH8.2; COD2628mgL-1; BOD5430mgL-1; NH3-N3100mgL-1. NH3-N of raw leachate was initially desorbed at pH11.0, and then the photochemical oxidation processes were applied. The results showed only 18~27%COD removal was reached by UV/H2O2 with hydrogen peroxide doses between 1 and 8gL-1, however, 55~80%COD removal was obtained by UV/O3 with an ozone dosage of 3.5gL-1, and 65~86%COD removal was achieved by UV/H2O2/O3 with an ozone dosage of 3.5gL-1 in the presence of hydrogen peroxide doses between 0.35 and 3.5 gL-1.Biodegradability of landfill leachate, measured as BOD5/COD, increased from less than 0.19 to nearly 0.4 by UV/O3 with an ozone dosage of 450 mgL-1. UF separation showed that the predominant COD distribution before and after UV/O3 oxidation were higher than10KD(>83%) and lower than 3KD(>98%) respectively, which revealed the significant reduction of nonbiodegradable organic matters of leachate. In addition, results of Batch Activated Sludge processes treatment showed a substantial argument for the increase on biodegradability of oxidized leachate, which demonstrated that UV/O3 would be beneficial to the subsequent biological treatment processes.A Pseudo-first-order kinetics model for COD removal by UV/O3 was proposed and proved.
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