为了探索市政生活污水处理厂剩余活性污泥资源化方式,以市政污泥为原料,采用热解法制备污泥基生物炭(SBC),探究SBC最佳制备条件以及对多环芳烃萘的吸附影响因素。结果表明:SBC的最佳制备条件为污泥粒径0.25mm,升温速率2.5℃/min,热解温度800℃,停留时间1h,在该条件下市政污泥的产炭率、产油率和产气率分别为61.36%、15.55%和23.09%;SBC对萘的最佳吸附条件为转速200r/min,温度35℃,投加量0.4g,在该条件下萘的去除率可达85.06%;SBC对萘的吸附过程符合准二级动力学模型,Langmuir等温吸附模型可以更好地描述SBC对萘的吸附。扫描电子显微镜和BET比表面积分析表明,SBC表面粗糙,具有丰富的孔隙结构,能有效吸附废水中的萘。
In order to explore the resource utilization mode of surplus activated sludge from municipal sewage treatment plants,sludge-based biochar (SBC) was prepared by pyrolysis method with municipal sludge as raw material,and the optimal preparation conditions of SBC and the factors influencing the adsorption of polycyclic aromatic naphthalene were explored.The results showed that the optimal preparation conditions of SBC were sludge particle size of 0.25mm,heating rate of 2.5℃/min,pyrolysis temperature of 800℃ and residence time of 1h.Under these conditions,the carbon production rate,oil production rate and gas production rate of municipal sludge were 61.36%,15.55% and 23.09%,respectively.The optimal adsorption conditions for naphthalene by SBC were as follows:rotational speed of 200r/min,temperature of 35℃ and dosage of 0.4g.Under these conditions,the removal rate of naphthalene could reach 85.06%.The adsorption process of SBC on naphthalene conformed to quasi-second-order adsorption kinetics,and Langmuir isothermal adsorption model could better describe the adsorption of SBC on naphthalene.SEM and BET analysis revealed that SBC had rough surface and abundant pore structure,which could effectively adsorb naphthalene in wastewater.
[1] Aghlmand R,Kian Z,Gheibi M,et al.Economic evaluation of different biological municipal wastewater treatment systems and implementation of AHP method based on operating costs[J].Ann Syst Biol,2021,4(1):21-25.
[2] 于天宇,胡思雨.热解污泥生物炭的现状与发展[J].建筑与预算,2019(2):45-48.
[3] 蔡炳良,辛玲玲.污泥热解技术特性分析[J].中国环保产业,2011(8):51-54.
[4] Li F,Wu X,Ji W,et al.Effects of pyrolysis temperature on properties of swine manure biochar and its environmental risks of heavy metals[J].Journal of Analytical and Applied Pyrolysis,2020,152:104945.
[5] Regkouzas,Panagiotis,Diamadopoulos,et al.Adsorption of selected organic micro-pollutants on sewage sludge biochar[J].Chemosphere,2019,224:840-851.
[6] 李珊英,陶玉强,姚书春,等.我国湖泊沉积物多环芳烃的分布特征及来源分析[J].第四纪研究,2015,35(1):118-130.
[7] Redolfi M,Blin-simiand N,Duten X,et al.Naphthalene oxidation by different non-thermal electrical discharges at atmospheric pressure[J].Plasma Science and Technology,2019,21(5):151-161.
[8] Du Z H,Lin X.Research progress in application of low temperature plasma technology for wastewater treatment[J].IOP Conference Series:Earth and Environmental Scienc,2020,512(1):012031-012037.
[9] 李淑琪.臭氧氧化技术去除水中萘的研究[D].北京:中国地质大学,2020.
[10] 王旺阳,刘聪,袁珮.吸附法去除环境中多环芳烃的研究进展[J].化工进展,2017,36(1):355-363.
[11] 黄华,王雅雄,唐景春,等.不同烧制温度下玉米秸秆生物炭的性质及对萘的吸附性能[J].环境科学,2014,35(5):1884-1890.
[12] 龚香宜,熊武芳,连婉,等.稻壳生物炭对水中萘的吸附特性研究[J].应用化工,2020,49(9):2154-2158.
[13] 张明,徐立恒,吕黎.浒苔生物炭对水中萘的吸附作用[J].科技导报,2015,33(14):78-81.
[14] Liu C C,Yin Z H,Hu D,et al.Biochar derived from chicken manure as a green adsorbent for naphthalene removal[J].Environmental Science and Pollution Research International,2021,28(27):36585-36597.
[15] 彭成法,肖汀璇,李志建.热解温度对污泥基生物炭结构特性及对重金属吸附性能的影响[J].环境科学研究,2017,30(10):1637-1644.
[16] 王格格,李刚,陆江银,等.热解工艺对污泥制备生物炭物理结构的影响[J].环境工程学报,2016,10(12):7289-7293.
[17] 马锋锋,赵保卫,念斌.玉米秸秆生物炭对水中氨氮的吸附特性[J].兰州交通大学学报,2015,34(1):125-131;135.
[18] 林旭萌,宿程远,黄纯萍,等.污泥质生物炭对2,4-二氯苯酚的吸附性能[J].环境工程,2019,37(8):154-158;87.
基金资助
辽宁省“兴辽英才计划”项目(XLYC2007007)