Lima Eder C, Royer Betina, Vaghetti Julio C P, Simon Nathalia M, da Cunha Bruna M, Pavan Flavio A, Benvenutti Edilson V, Cataluña-Veses Renato, Airoldi Claudio
Instituto de Química, Universidade Federal do Rio Grande do Sul, Av. Bento Gonçalves 9500, Caixa Postal 15003, CEP 91501-970, Porto Alegre, RS, Brazil.
J Hazard Mater. 2008 Jul 15;155(3):536-50. doi: 10.1016/j.jhazmat.2007.11.101. Epub 2007 Dec 4.
The Brazilian pine-fruit shell (Araucaria angustifolia) is a food residue, that was used as biosorbent for the removal of non-hydrolyzed reactive red 194 (NRR) and hydrolyzed reactive red 194 (HRR) forms from aqueous solutions. Chemical treatment of Brazilian pine-fruit shell (PW), with chromium (Cr-PW), with acid (A-PW), and with acid followed by chromium (Cr-A-PW) were also tested as alternative biosorbents for the removal of NRR and HRR from aqueous effluents. It was observed that the treatment of the Brazilian pine-fruit shell with chromium (Cr-PW and Cr-A-PW) leaded to a remarkable increase in the specific surface area and average porous volume of these biosorbents when compared to unmodified Brazilian pine-fruit shell (PW). The effects of shaking time, biosorbent dosage and pH on biosorption capacity were studied. In acidic pH region (pH 2.0) the biosorption of NRR and HRR were favorable. The contact time required to obtain the equilibrium was 24h at 25 degrees C. The equilibrium data were fitted to Langmuir, Freundlich, Sips and Redlich-Peterson isotherm models. For NRR reactive dye the equilibrium data were best fitted to the Sips isotherm model using PW and A-PW as biosorbents, and Redlich-Peterson isotherm model using Cr-PW and Cr-A-PW as biosorbents. For HRR reactive dye the equilibrium data were best fitted to the Sips isotherm model using PW, A-PW and Cr-A-PW and the Redlich-Peterson isotherm model for Cr-PW as biosorbent.
巴西松果壳(南洋杉)是一种食物残渣,被用作生物吸附剂,用于从水溶液中去除未水解的活性红194(NRR)和水解的活性红194(HRR)形式。还测试了用铬(Cr-PW)、酸(A-PW)以及先酸后铬(Cr-A-PW)对巴西松果壳(PW)进行化学处理,作为从废水去除NRR和HRR的替代生物吸附剂。观察到,与未改性的巴西松果壳(PW)相比,用铬处理巴西松果壳(Cr-PW和Cr-A-PW)导致这些生物吸附剂的比表面积和平均孔体积显著增加。研究了振荡时间、生物吸附剂用量和pH对生物吸附容量的影响。在酸性pH区域(pH 2.0),NRR和HRR的生物吸附是有利的。在25℃下达到平衡所需的接触时间为24小时。平衡数据拟合到朗缪尔、弗伦德利希、西普斯和雷德利希-彼得森等温线模型。对于NRR活性染料,以PW和A-PW作为生物吸附剂时,平衡数据最适合西普斯等温线模型;以Cr-PW和Cr-A-PW作为生物吸附剂时,平衡数据最适合雷德利希-彼得森等温线模型。对于HRR活性染料,以PW、A-PW和Cr-A-PW作为生物吸附剂时,平衡数据最适合西普斯等温线模型;以Cr-PW作为生物吸附剂时,平衡数据最适合雷德利希-彼得森等温线模型。