Department of Environmental Sciences, The Connecticut Agricultural Experimental Station, 123 Huntington St., P.O. Box 1106, New Haven, CT 06504-1106, United States.
Department of Environmental Sciences, The Connecticut Agricultural Experimental Station, 123 Huntington St., P.O. Box 1106, New Haven, CT 06504-1106, United States.
Water Res. 2015 Sep 1;80:179-88. doi: 10.1016/j.watres.2015.04.040. Epub 2015 May 9.
We studied the adsorption of triazine herbicides and several reference heteroaromatic amines from water onto a temperature series of hardwood biochars (300-700 °C, labeled B300-B700). Adsorption on biochars correlated poorly with pyrolysis temperature, H/C, O/C, mean minimum fused ring size, surface area (N2 or CO2), microporosity, and mesoporosity, but correlated well with a weighted sum of microporosity and mesoporosity. Steric effects were evident by the negative influence of solute molecular volume on adsorption rate. For a given compound, adsorption rate maximized for the biochar with the greatest mesoporosity-to-total-porosity ratio, suggesting that mesopores are important for facilitating diffusion into pore networks. The cationic forms of amines adsorb more slowly than the neutral forms. To further probe steric and electronic effects, adsorption on a biochar (B400) was compared to adsorption on graphite-a nonporous reference material with an unhindered, unfunctionalized graphene surface-and in comparison with reference compounds (benzene, naphthalene, pyridine, quinoline and 1,3-triazine). Relative to benzene, the surface area-normalized adsorption of the triazine herbicides was disfavored on B400 (favored on graphite) by 11-19 kJ/mol, depending on concentration. It is estimated that steric suppression of B400 adsorption comprises 6.2 kJ/mol of this difference, the remainder being the difference in polar electronic effects. Based on the behavior of the reference amines, the difference in polar effects is dominated by π-π electron donor-acceptor (EDA) interactions with sites on polyaromatic surfaces, which are more electropositive and/or more abundant on graphite. Overall, our results show that mesoporosity is critical, that adsorption rate is a function of solute molecular size and charge, that steric bulk in the solute suppresses equilibrium adsorption, and that π-π EDA forces play a role in triazine polar interactions with biochar.
我们研究了三嗪类除草剂和几种参考杂环胺类从水中到一系列硬木生物炭(300-700°C,标记为 B300-B700)的吸附。吸附在生物炭上与热解温度、H/C、O/C、平均最小熔合环尺寸、表面积(N2 或 CO2)、微孔和中孔相关性较差,但与微孔和中孔的加权和相关性较好。通过溶质分子体积对吸附速率的负面影响,空间位阻效应是明显的。对于给定的化合物,吸附速率在具有最大中孔与总孔体积比的生物炭上最大化,这表明中孔对于促进扩散到孔网络中很重要。胺的阳离子形式比中性形式吸附得更慢。为了进一步探讨空间位阻和电子效应,我们将在生物炭(B400)上的吸附与在石墨(一种无孔参考材料,具有无阻的、无官能化的石墨烯表面)上的吸附进行比较,并与参考化合物(苯、萘、吡啶、喹啉和 1,3-三嗪)进行比较。与苯相比,取决于浓度,三嗪类除草剂的表面积归一化吸附在 B400 上受到抑制(在石墨上受到促进)11-19 kJ/mol。据估计,B400 吸附的空间位阻抑制包括 6.2 kJ/mol 的差异,其余的差异是极性电子效应的差异。基于参考胺的行为,极性效应的差异主要是由于π-π 电子给体-受体(EDA)相互作用与多环芳烃表面上的位点之间的相互作用,这些位点在石墨上更带正电和/或更丰富。总的来说,我们的结果表明,中孔是关键的,吸附速率是溶质分子尺寸和电荷的函数,溶质的空间位阻会抑制平衡吸附,而π-π EDA 力在三嗪与生物炭的极性相互作用中起作用。