School of Engineering, RMIT University, Melbourne, 3000, Australia.
School of Chemistry, University of Melbourne, Victoria, 3010, Australia.
Chemosphere. 2020 Jun;249:126072. doi: 10.1016/j.chemosphere.2020.126072. Epub 2020 Feb 5.
The ability to immobilise PFAS in soil may be an essential interim tool while technologies are developed for effective long-term treatment of PFAS contaminated soils. Serial sorption experiments were undertaken using a pine derived biochar produced at 750 °C (P750). All experiments were carried out either in individual mode (solution with one PFAS at 5 μg/L) or mix mode (solution with 5 μg/L of each: PFOS, PFOA, PFHxS and PFHxA), and carried out in 2:1 water to soil solutions. Soils had biochar added in the range 0-5% w/w. Kinetic data were fitted to the pseudo-second order model for both amended soils, with equilibrium times ranging 0.5-96 h for all congeners. PFOS sorption was 11.1 ± 4.5% in the loamy sand compared to 69.8 ± 4.9% in the sandy clay loam. While total sorption was higher in the unamended loamy sand than sandy clay loam for PFHxA, PFOA and PFOS, the effect of biochar amendment for each compound was found to be significantly higher in amended sandy clay loam than in amended loamy sand. Application of biochar reduced the desorbed PFAS fraction of all soils. Soil type and experimental mode played a significant role in influencing desorption. Overall, the relationship between sorbent and congener was demonstrated to be highly impacted by soil type, however the unique physiochemical properties of each PFAS congener greatly influenced its unique equilibrium, sorption and desorption behaviour for each amended soil and mode tested.
将 PFAS 固定在土壤中可能是一种必要的临时手段,同时也在开发用于有效处理 PFAS 污染土壤的长期技术。采用在 750°C 下生产的松树衍生生物炭(P750)进行了一系列的吸附实验。所有实验均在单一模式(一种 PFAS 在 5μg/L 的溶液)或混合模式(每种 PFAS 浓度均为 5μg/L 的溶液:PFOS、PFOA、PFHxS 和 PFHxA)下进行,水与土壤的比例为 2:1。土壤中添加了 0-5%w/w 的生物炭。对于两种改良土壤,动力学数据均符合准二级模型拟合,所有同系物的平衡时间范围为 0.5-96 小时。与砂壤土相比,壤土砂中 PFOS 的吸附率为 11.1±4.5%,而砂壤土中的吸附率为 69.8±4.9%。对于 PFHxA、PFOA 和 PFOS,未改良的壤土砂中的总吸附量高于砂壤土,但生物炭改良后,砂壤土中的吸附量均高于壤土砂。生物炭的应用降低了所有土壤中解吸的 PFAS 分数。土壤类型和实验模式在影响解吸方面起着重要作用。总的来说,吸附剂和同系物之间的关系受到土壤类型的强烈影响,然而,每个 PFAS 同系物的独特物理化学性质极大地影响了其在每种改良土壤和测试模式下的独特平衡、吸附和解吸行为。