Jain Shailesh K, Shakil Najam A, Dutta Anirban, Kumar Jitendra, Saini Mukesh K
a ICAR-Division of Agricultural Chemicals , Indian Agricultural Research Institute , New Delhi , India.
b ICAR-Directorate of Medicinal & Aromatic Plants Research , Anand , Gujarat , India.
J Environ Sci Health B. 2017 May 4;52(5):326-337. doi: 10.1080/03601234.2017.1281653. Epub 2017 Feb 22.
Bentonite was modified by quaternary ammonium cations viz. cetytrimethylammonium (CTA), cetylpyridinium (CP), rioctylmethylammonium (TOM) and pcholine (PTC) at 100% cation exchange capacity of bentonite and was characterized by X-ray diffraction, CHNS elemental analyser and Fourier transform infrared spectroscopy. The sorption of imidacloprid on organobentonites/bentonite was studied by batch method. Normal bentonite could adsorb imidacloprid only upto 19.31-22.18% while all organobentonites except PTC bentonite (PTCB), enhanced its adsorption by three to four times. Highest adsorption was observed in case of TOM bentonite (TOMB) (76.94-83.16%). Adsorption kinetic data were fitted to pseudo-first-order, pseudo-second-order and intraparticle diffusion models. For normal bentonite data were best fitted to pseudo-first-order kinetic, while for organobentonites fitted to pseudo-second-order kinetics. Sorption data were analysed using Freundlich, Langmuir, Temkin and Dubinin-Radushkevich isotherm models. Data were well fitted to Freundlich adsorption isotherm. Product of Freundlich adsorption constant and heterogeneity parameter (K.1/n) was in following order: TOMB (301.87) > CTA bentonite (CTAB) (152.12) > CP bentonite (CPB) (92.58) > bentonite (27.25). Desorption study confirmed hysteresis and concentration dependence. The present study showed that the organobentonite could be a good sorbent for removal of imidacloprid from natural water sample also. Percentage adsorption and Distribution coefficient (mL g) value of different adsorbent was in following order: TOMB (74.85% and 297.54) > CTAB (55.78% and 126.15) > CPB (45.81% and 84.55) > bentonite (10.65% and 11.92).
膨润土在其100%阳离子交换容量下用季铵阳离子即十六烷基三甲基铵(CTA)、十六烷基吡啶鎓(CP)、三辛基甲基铵(TOM)和对胆碱(PTC)进行改性,并通过X射线衍射、CHNS元素分析仪和傅里叶变换红外光谱进行表征。采用分批法研究了吡虫啉在有机膨润土/膨润土上的吸附情况。普通膨润土对吡虫啉的吸附量仅为19.31 - 22.18%,而除PTC膨润土(PTCB)外的所有有机膨润土都将其吸附量提高了三到四倍。在TOM膨润土(TOMB)的情况下观察到最高吸附量(76.94 - 83.16%)。吸附动力学数据拟合到伪一级、伪二级和颗粒内扩散模型。对于普通膨润土,数据最适合伪一级动力学,而对于有机膨润土则适合伪二级动力学。使用弗伦德利希、朗缪尔、特姆金和杜比宁 - 拉杜舍维奇等温线模型分析吸附数据。数据很好地拟合了弗伦德利希吸附等温线。弗伦德利希吸附常数与非均质性参数的乘积(K.1/n)顺序如下:TOMB(301.87)> CTA膨润土(CTAB)(152.12)> CP膨润土(CPB)(92.58)>膨润土(27.25)。解吸研究证实了滞后现象和浓度依赖性。本研究表明,有机膨润土也可能是从天然水样中去除吡虫啉的良好吸附剂。不同吸附剂的吸附百分比和分配系数(mL g)值顺序如下:TOMB(74.85%和297.54)> CTAB(55.78%和126.15)> CPB(45.81%和84.55)>膨润土(10.65%和11.92)。