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Degradation of phthalate esters in an activated sludge wastewater treatment plant

机译:活性污泥废水处理厂中邻苯二甲酸酯的降解

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Efficient removal of phthalate esters (PE) in wastewater treatment plants (WWTP) is becoming an increasing priority in many countries. In this study, we examined the fate of dimethyl phthalate (DMP), dibutyl phthalate (DBP), butylbenzyl phthalate (BBP), and di-(2-ethylhexyl) phthalate (DEHP) in a full scale activated sludge WWTP with biological removal of nitrogen and phosphorus. The mean concentrations of DMP, DBP, BBP, and DEHP at the WWTP inlet were 1.9, 20.5, 37.9, and 71.9 μg/L, respectively. Less than 0.1%, 42%, 35%, and 96% of DMP, DBP, BBP, and DEHP was associated with suspended solids, respectively. The overall microbial degradation of DMP, DBP, BBP, and DEHP in the WWTP was estimated to be 93%, 91%, 90%, and 81%, respectively. Seven to nine percent of the incoming PE were recovered in the WWTP effluent. Factors affecting microbial degradation of DEHP in activated sludge were studied using [U-~(14)C-ring] DEHP as tracer. First order rate coefficients for aerobic DEHP degradation were 1.0 x 10~(-2), 1.4 x 10~(-2), and 1.3 x 10~(-3) at 20, 32, and 43℃, respectively. Aerobic degradation rates decreased dramatically under aerobic thermophilic conditions ( < 0.1 x 10~(-2)h~(-1) at 60℃). The degradation rate under anoxic denitrifying conditions was 0.3 x 10~(-2)h~(-1), whereas the rate under alternating conditions (aerobic-a-noxic) was 0.8 x 10~(-2)h~(-1). Aerobic DEHP degradation in activated sludge samples was stimulated 5-9 times by addition of a phthalate degrading bacterium. The phthalate degrading bacterium was isolated from activated sludge, and maintained a capacity for DEHP degradation while growing on vegetable oil. Collectively, the results of the study identified several controls of microbial PE degradation in activated sludge. These controls may be considered to enhance PE degradation in activated sludge WWTP with biological removal of nitrogen and phosphorus.
机译:在许多国家,有效去除废水处理厂(WWTP)中的邻苯二甲酸酯(PE)变得越来越重要。在这项研究中,我们研究了在生物活性去除污泥中,邻苯二甲酸二甲酯(DMP),邻苯二甲酸二丁酯(DBP),邻苯二甲酸丁苄酯(BBP)和邻苯二甲酸二(2-乙基己基)酯(DEHP)的命运。氮和磷。 WWTP入口处的DMP,DBP,BBP和DEHP的平均浓度分别为1.9、20.5、37.9和71.9μg/ L。少于0.1%,42%,35%和96%的DMP,DBP,BBP和DEHP与悬浮固体相关。污水处理厂中DMP,DBP,BBP和DEHP的总体微生物降解率分别估计为93%,91%,90%和81%。在污水处理厂的废水中回收了百分之七到九的进入PE。以[U-〜(14)C-ring] DEHP为示踪剂,研究了活性污泥中DEHP微生物降解的影响因素。在20、32和43℃下,好氧DEHP降解的一阶速率系数分别为1.0 x 10〜(-2),1.4 x 10〜(-2)和1.3 x 10〜(-3)。在有氧嗜热条件下(60℃<0.1 x 10〜(-2)h〜(-1),有氧降解速率显着降低。在缺氧反硝化条件下的降解速率为0.3 x 10〜(-2)h〜(-1),而在交替条件下(好氧-无氧)的降解速率为0.8 x 10〜(-2)h〜(-1) )。通过添加邻苯二甲酸盐降解细菌,可将活性污泥样品中的好氧DEHP降解刺激5-9倍。从活性污泥中分离出邻苯二甲酸盐降解细菌,并在植物油上生长的同时保持了DEHP降解的能力。总体而言,研究结果确定了活性污泥中微生物PE降解的几种控制方法。这些控制措施可被视为通过生物去除氮和磷来增强活性污泥废水处理厂中PE的降解。

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