欢迎登录材料期刊网

材料期刊网

高级检索

采用自制的负载铈-锰双金属型活性炭( Ce-Mn/AC)吸附兰炭废水,通过静态吸附平衡实验研究pH值及Ce-Mn/AC投加量对兰炭废水化学需氧量( COD)去除率的影响;通过吸附动力学、吸附等温线及吸附热力学模型方程拟合兰炭废水在Ce-Mn/AC的吸附过程,考察其吸附特性,并采用气相色谱-质谱联用仪( GC-MS)及紫外光谱仪(UV-vis)分析其可能的吸附机理。结果表明:在Ce-Mn/AC投加量为10 g·L-1,不调节pH值时,Ce-Mn/AC对兰炭废水的吸附量为82.9 mg·L-1,COD去除率为84.6%;吸附动力学符合拟二级动力学模型,Freundlich模型可更好地描述Ce-Mn/AC对兰炭废水的吸附平衡过程,△G<0,△H>0及△S>0,表明兰炭废水在Ce-Mn/AC上的吸附是自发吸热的、以化学吸附为主的过程;兰炭废水中难降解的多环芳烃及含氮杂环有机物先于单环芳烃吸附在Ce-Mn/AC上,因而经此吸附工艺后可很大程度地减小兰炭废水后续工艺中难降解物对废水处理系统的影响,并提供了一定的基础数据及理论,吸附解吸实验表明,Ce-Mn/AC具有较优的重复使用性能。

Semi-coking wastewater was treated by self-made Ce-Mn/AC. The effects of pH and dosage of Ce-Mn/AC on COD removal rate of semi-coking waste water were studied by static examination of equilibrium adsorption. The adsorption properties of semi-coking wastewater on Ce-Mn/AC was investigated by using adsorption kinetics model, adsorption isotherm and adsorption thermodynamics model to fit the adsorption process, and the probable adsorption mechanism was induced by GC-MS and UV-vis analysis. The results show that the semi-coking wastewater adsorption capacity on Ce-Mn/AC was 82. 9 mg·g-1, and the COD removal rate was 84. 6% when under the Ce-Mn/AC dosage was 10 g· L-1 without adjusting the pH value of semi-coking wastewater. The adsorption kinetics fitted pseudo-second-order model, Freundlich model could better describe adsorption of semi-coking waste water by Ce-Mn/AC,△G<0,△H>0 and △S>0 indicated that the adsorption was spontaneous, endothermic and mainly by chemisorption process. Refractory organic compounds such as polycyclic aromatic hydrocarbons and nitrogen heterocyclic compounds were adsorbed before monocyclic aromatic compounds, so the effect of refractory organic compounds on the following semi-coking wastewater-treatment system was greatly induced and some data and theory foundation were provided. Adsorption and desorption experiments indicated that the adsorbent had a better property for repeated use.

参考文献

[1] 张智芳;高雯雯.气相色谱-质谱法分析隔油絮凝处理后兰炭废水中有机污染物[J].应用化工,2014(3):573-575,582.
[2] 高剑;刘永军;童三明;杨义普.兰炭废水中有机污染物组成及其去除特性分析[J].安全与环境学报,2014(6):196-201.
[3] 郝亚龙;吕永涛;苗瑞;王磊.半焦生产高浓度难降解有机废水处理技术工艺试验研究[J].西安建筑科技大学学报(自然科学版),2012(4):558-562.
[4] 张彩凤;郭晓滨;王颖.催化湿式氧化处理兰炭废水的工艺研究[J].山东化工,2011(4):37-39.
[5] 毕强;薛娟琴;郭莹娟;李国平;雷美美.电芬顿法去除兰炭废水COD[J].环境工程学报,2012(12):4310-4314.
[6] 毕强;薛娟琴;郭莹娟;李国平;薛云峰.电絮凝法去除兰炭废水中的COD[J].工业水处理,2012(9):41-44.
[7] 孟庆锐;安路阳;李超;王春旭;王钟欧.O3催化氧化深度处理兰炭废水的试验研究[J].环境科学与技术,2013(2):133-136.
[8] 吕永涛;王磊;陈祯;孙婷;吴红亚;王韬;王志盈.Fenton氧化-吹脱法预处理兰炭废水的研究[J].工业水处理,2010(11):56-58.
[9] Yu, Xubiao;Wei, Chaohai;Wu, Haizhen;Jiang, Zhengming;Xu, Ranghua.Improvement of biodegradability for coking wastewater by selective adsorption of hydrophobic organic pollutants[J].Separation and Purification Technology,2015:23-30.
[10] 帅伟;吴艳林;胡芸;吴超飞;韦朝海.焦化废水生物处理尾水的活性炭吸附及条件优化研究[J].环境工程学报,2010(6):1201-1207.
[11] I. Vazquez;J. Rodriguez-Iglesias;E. Maranon;L. Castrillon;M. Alvarez.Removal of residual phenols from coke wastewater by adsorption[J].Journal of hazardous materials,20071/2(1/2):395-400.
[12] 张小璇;任源;韦朝海;陈金贵.焦化废水生物处理尾水中残余有机污染物的活性炭吸附及其机理[J].环境科学学报,2007(7):1113-1120.
[13] 程杨;杨月红;于珊珊;张玉琴;宁平;石磊;张怀予.高温焙烧底泥吸附重金属Mn2+和Ni2+的动力学与热力学研究[J].硅酸盐通报,2015(7):1850-1856.
[14] Maryam Ahmadzadeh Tofighy;Toraj Mohammadi.Adsorption of divalent heavy metal ions from water using carbon nanotube sheets[J].Journal of hazardous materials,20111(1):140-147.
[15] 熊佰炼;崔译霖;张进忠;张明晓;邢赜.改性甘蔗渣吸附废水中低浓度Cd~(2+)和Cr~(3+)的研究[J].西南大学学报(自然科学版),2010(1):118-123.
[16] Lianggui Wang.Removal of Disperse Red dye by bamboo-based activated carbon: optimisation, kinetics and equilibrium[J].Environmental Science and Pollution Research,20137(7):4635-4646.
[17] 胡记杰;肖俊霞;任源;谭展机;吴超飞;韦朝海.焦化废水原水中有机污染物的活性炭吸附过程解析[J].环境科学,2008(6):1567-1571.
[18] 张万辉;韦朝海;晏波;任曼;彭平安.焦化废水中溶解性有机物组分的特征分析[J].环境化学,2012(5):702-707.
上一张 下一张
上一张 下一张
计量
  • 下载量()
  • 访问量()
文章评分
  • 您的评分:
  • 1
    0%
  • 2
    0%
  • 3
    0%
  • 4
    0%
  • 5
    0%