Predicting per- and polyfluoroalkyl substances removal in pilot-scale granular activated carbon adsorbers from rapid small-scale column tests

Zachary R. Hopkins, Detlef R. U. Knappe
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Abstract

Per- and polyfluoroalkyl substances (PFAS) occur widely in drinking water, and consumption of contaminated drinking water is an important human exposure route. Granular activated carbon (GAC) adsorption can effectively remove PFAS from water. To support the design of GAC treatment systems, a rapid bench-scale testing procedure and scale-up approach are needed to assess the effects of GAC type, background water matrix, and empty bed contact time (EBCT) on GAC use rates. The overarching goal of this study was to predict PFAS breakthrough curves obtained at the pilot-scale from rapid small-scale column test (RSSCT) data. The scale-up protocol was developed for pilot data obtained with coagulated/settled surface water (TOC = 2.3 mg/L), three GACs, and two EBCTs. Between 7 and 11 PFAS breakthrough curves were available for each pilot column. RSSCT designs were investigated that assumed intraparticle diffusivity is independent of GAC particle size (i.e., constant diffusivity [CD]) or linearly dependent on GAC particle size (i.e., proportional diffusivity [PD]). CD-RSSCTs effectively predicted the bed volumes of water that could be treated at the pilot-scale to reach 50% breakthrough (BV50%) of individual PFAS. In contrast, PD-RSSCTs overpredicted BV50% obtained at the pilot-scale by a factor of ~2–3. The shape of PFAS breakthrough curves obtained with CD-RSSCTs deviated from those obtained at the pilot-scale, indicating that intraparticle diffusivity was dependent on GAC particle diameter (dp). Using the pore surface diffusion model (PSDM), intraparticle diffusivity was found to be proportional to (dp)0.25 when considering data up to about 70% PFAS breakthrough. This proportionality factor can be used to design RSSCTs or scale up existing CD-RSSCT data using the PSDM. Using pilot-scale data obtained with groundwater and wastewater-impacted groundwater as well as with additional GACs, the developed RSSCT scale-up approach was validated for PFAS breakthrough percentages up to 70%. The presented methodology permits the rapid prediction of GAC use rates for PFAS removal.

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通过快速小规模柱测试预测中试规模颗粒活性炭吸附器中全氟化烃和多氟化烃物质的去除率
全氟烷基和多氟烷基物质(PFAS)广泛存在于饮用水中,饮用受污染的饮用水是人类接触这种物质的重要途径。颗粒活性炭(GAC)吸附可以有效去除水中的 PFAS。为了支持 GAC 处理系统的设计,需要一种快速的台架试验程序和放大方法来评估 GAC 类型、背景水基质和空床接触时间 (EBCT) 对 GAC 使用率的影响。本研究的总体目标是根据快速小规模色谱柱测试 (RSSCT) 数据预测在中试规模获得的 PFAS 突破曲线。根据混凝/沉降地表水(TOC = 2.3 mg/L)、三种 GAC 和两种 EBCT 得出的中试数据制定了放大方案。每个中试塔可获得 7 至 11 条 PFAS 突破曲线。研究了假定颗粒内扩散率与 GAC 粒径无关(即恒定扩散率 [CD])或与 GAC 粒径线性相关(即比例扩散率 [PD])的 RSSCT 设计。CD-RSSCT 可以有效预测在中试规模下达到 50%(BV50%)单个 PFAS 浓度的处理水床体积。相比之下,PD-RSSCT 对中试规模下获得的 BV50% 的预测高出约 2-3 倍。使用 CD-RSSCT 所获得的 PFAS 突破曲线的形状偏离了在中试规模下获得的曲线,这表明颗粒内扩散性取决于 GAC 颗粒直径 (dp)。使用孔隙表面扩散模型 (PSDM),当考虑到 PFAS 突破率高达 70% 左右的数据时,发现颗粒内扩散率与 (dp)0.25 成正比。该比例系数可用于设计 RSSCT 或使用 PSDM 放大现有的 CD-RSSCT 数据。利用地下水和受废水影响的地下水以及额外的 GAC 所获得的中试规模数据,所开发的 RSSCT 放大方法对高达 70% 的 PFAS 突破率进行了验证。该方法可快速预测去除 PFAS 的 GAC 使用率。
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