Benitez F Javier, Acero Juan L, Garcia Juan, Leal Ana I
Departamento de Ingeniería Química y Energética, Universidad de Extremadura, Facultad de Ciencias, Avda. Elvas S/N, 06071 Badajoz, Spain.
Water Res. 2003 Oct;37(17):4081-90. doi: 10.1016/S0043-1354(03)00350-6.
Wastewaters generated in the cork processing industry were treated in continuous reactors by means of single treatments separately-a chemical ozonation and an activated sludge system-and then by both sequential processes-ozonation followed by aerobic degradation, and aerobic degradation followed by ozonation. The removals obtained in the ozonation alone were 12-54%, 65-81%, and 55-89% for the COD, total phenolics, and absorbance at 254 nm, respectively, while the consumed ozone yield ranged from 40% to 61%, and the biodegradability (BOD(5)/COD) varied from an initial 0.60 to final values between 0.68 and 0.93. The optimum hydraulic retention time and ozone partial pressure were 3 h and 3 kPa, respectively. The stoichiometric ratio was 0.56 g of organic substrate degraded per g of ozone consumed, while the rate constants obtained for the ozone disappearance and for the organic matter degradation were 4490 L g COD(-1) h(-1) and 1970 L g O(3)(-1)h(-1) respectively. The presence of hydrogen peroxide or UV radiation in addition to ozone increased the values of organic matter removal as well as the stoichiometric ratio and the rate constants. The aerobic treatment by the activated sludge system yielded COD removals between 13% and 37% for hydraulic retention times between 24 and 96 h, and the Contois model gave values of q(max)=0.14 g COD g VSS(-1)h(-1) and K(1)=22.6 g COD g VSS(-1) for the main kinetic parameters. The sequential processes increased the substrate removal efficiencies in comparison with the individual processes. These enhancements were greater in the aerobic degradation-ozonation sequence than in the ozonation-aerobic degradation sequence.
软木加工行业产生的废水在连续反应器中进行处理,先是分别采用单一处理方法——化学臭氧化和活性污泥系统,然后采用两种顺序处理工艺——先臭氧化后好氧降解,以及先好氧降解后臭氧化。单独臭氧化处理对化学需氧量(COD)、总酚和254nm处吸光度的去除率分别为12% - 54%、65% - 81%和55% - 89%,而消耗的臭氧产率在40%至61%之间,生物降解性(BOD(5)/COD)从初始的0.60变化到最终的0.68至0.93之间。最佳水力停留时间和臭氧分压分别为3小时和3千帕。化学计量比为每消耗1克臭氧降解0.56克有机底物,而臭氧消失和有机物降解的速率常数分别为4490L g COD(-1) h(-1)和1970L g O(3)(-1)h(-1)。除臭氧外,添加过氧化氢或紫外线辐射可提高有机物去除率、化学计量比和速率常数的值。活性污泥系统的好氧处理在水力停留时间为24至96小时时,COD去除率在13%至37%之间,康托伊斯模型给出的主要动力学参数q(max)= 0.14 g COD g VSS(-1)h(-1)和K(1)=22.6 g COD g VSS(-1)。与单独处理相比,顺序处理提高了底物去除效率。好氧降解 - 臭氧化顺序的提高幅度大于臭氧化 - 好氧降解顺序。