Department of Civil Engineering, Center for Environmental Engineering Research and Education (CEERE), University of Calgary, 2500 University Drive, NW, Calgary, Alberta, T2N 1N4, Canada.
Department of Civil Engineering, Center for Environmental Engineering Research and Education (CEERE), University of Calgary, 2500 University Drive, NW, Calgary, Alberta, T2N 1N4, Canada.
J Environ Manage. 2019 Mar 1;233:175-183. doi: 10.1016/j.jenvman.2018.12.015. Epub 2018 Dec 20.
Biofiltration is an excellent alternative for the treatment of diffuse emissions of methane (CH) that cannot be treated by physical/chemical means or recovered for energy. Despite the advances on CH biological treatment technologies, they are limited by the low aqueous solubility of CH into the biofilm where CH mineralization occurs. In this study, the CH adsorption kinetics, adsorption capacity and transport behavior of CH was studied in batch experiments and in a fixed-bed column by varying the biochar and compost mixtures under 5-levels, 3 different water contents (dry, 15% and 30% water holding capacity), and 2 inlet flow rates. Experimental results were formally tested using analysis of variance (ANOVA) in order to draw objective conclusions based on statistical inference. As CH biofiltration requires water addition to maintain microbial activity, these results indicate adsorption capacity is not lost with water addition if biochar content is the dominant packing material. The Langmuir isotherm described the data best (R = 0.99). Maximum adsorption capacity by monolayer adsorption, or q, is relatively similar with or without the addition of water as long as the biochar component is the dominant material at 3.5 mg CH/g medium for a 7:1 biochar: compost, v/v mixture. Empirical regression models for q, k, (Thomas model) and τ and K (Yoon-Nelson model) were developed for the break through curves of CH. The current work demonstrates the applicability of utilizing biochar, a relatively inexpensive adsorbent, can compensate for the low solubility of CH and overcome the rate-limiting step of mass transfer from the gas phase and into the methanotrophic biofilm. Further, biochar may be a reliable back-up system for CH storage especially for fluctuating inlet loads that may be encountered in industrial applications adsorbing up to 13 mg CH/g biochar under dry conditions.
生物过滤是处理无法通过物理/化学手段处理或回收能源的甲烷(CH)弥散排放的绝佳选择。尽管 CH 生物处理技术取得了进展,但它们受到 CH 在发生 CH 矿化的生物膜中的低水溶性的限制。在这项研究中,通过在 5 个水平、3 种不同含水量(干燥、15%和 30%的水持水量)和 2 个入口流速下改变生物炭和堆肥混合物,在分批实验和固定床柱中研究了 CH 的吸附动力学、吸附容量和传输行为。使用方差分析(ANOVA)对实验结果进行了正式测试,以便根据统计推断得出客观结论。由于 CH 生物过滤需要加水来维持微生物活性,如果生物炭含量是主要填充材料,则不会因加水而导致吸附容量损失。Langmuir 等温线最好地描述了数据(R=0.99)。只要生物炭成分是 7:1 生物炭:堆肥(v/v)混合物的主要材料,通过单层吸附的最大吸附容量,或 q,在添加水或不添加水的情况下都相对相似,为 3.5mg CH/g 介质。为 CH 的穿透曲线开发了 q、k(Thomas 模型)和 τ 和 K(Yoon-Nelson 模型)的经验回归模型。目前的工作表明,利用生物炭(一种相对廉价的吸附剂)的适用性可以弥补 CH 的低溶解度,并克服从气相到甲烷营养生物膜的传质限速步骤。此外,生物炭可能是 CH 储存的可靠备用系统,特别是对于工业应用中可能遇到的波动入口负荷,在干燥条件下,生物炭可吸附高达 13mg CH/g 的 CH。