Department of Environmental and Sustainable Engineering, University at Albany, State University of New York, Albany, NY, 12222, United States.
Department of Environmental and Sustainable Engineering, University at Albany, State University of New York, Albany, NY, 12222, United States.
Environ Pollut. 2024 Dec 15;363(Pt 2):125235. doi: 10.1016/j.envpol.2024.125235. Epub 2024 Nov 2.
To test the effectiveness of phytoremediation of per- and polyfluoroalkyl substances (PFAS), we cultivated a mixture of nine grass-legume species native to Maine, US, in two types of soil amended with biosolids containing both pre-existing and spiked PFAS. To investigate how biochar amendment affects plant uptake of PFAS, two types of biochar at varying doses (i.e., 0%, 0.05%, 0.2%, 1%) were added to the biosolids before mixing with soil and cultivating plants. Our findings indicate that six representative PFAS, including short- and long-chain perfluoroalkyl carboxylic acids (PFCAs) (C-C) and perfluoroalkylsulfonic acids (PFSAs) (C, C, and C), were effectively transferred from the biosolids amended soil (BAS) system to the harvestable grass-legume shoots. During the initial growth stage (Day 33), PFOA, PFHxS and PFOS were primarily detected in the grass shoots, showing a removal efficiency of 2-3%. As the growth period extended to Day 92, the uptake of short-chain PFBS, PFHxA, and PFHpA became increasingly dominant with an average removal efficiency of 5-20%. Notably, more than 10% of PFOA was uptaken by the shoots harvested from the Scantic soil amended with Biochar 2. These results were observed in grass-legume shoots when the soil was amended with a low dose of biochar (0.05%). However, when 1% biochar was added, PFAS were effectively stabilized, preventing their transfer to the above-ground plant compartments. Aside from different effect of different dose of the biochar, this study also revealed that plant's uptake of PFAS is highly dependent on soil properties. Overall, this study demonstrated the feasibility of using a grass-legume mix for removing PFAS from contaminated soil and raised the need of developing site-specific treatment strategies to maximize the performance of phytoremediation.
为了测试植物修复全氟和多氟烷基物质(PFAS)的有效性,我们在美国缅因州种植了九种草本豆科植物的混合物,这些植物生长在两种添加了含有既有和添加的 PFAS 的生物固体的土壤中。为了研究生物炭改良如何影响植物对 PFAS 的吸收,我们将两种不同剂量(即 0%、0.05%、0.2%和 1%)的生物炭添加到与土壤混合并种植植物之前添加的生物固体中。我们的研究结果表明,六种代表性的 PFAS,包括短链和长链全氟烷基羧酸(PFCAs)(C-C)和全氟烷基磺酸(PFSAs)(C、C 和 C),有效地从添加生物固体的土壤(BAS)系统转移到可收获的草本豆科植物中。在初始生长阶段(第 33 天),主要在草茎中检测到 PFOA、PFHxS 和 PFOS,其去除效率为 2-3%。随着生长周期延长到第 92 天,短链 PFBS、PFHxA 和 PFHpA 的吸收变得越来越占主导地位,平均去除效率为 5-20%。值得注意的是,从添加生物炭 2 的 Scantic 土壤中收获的草茎中吸收了超过 10%的 PFOA。当土壤中添加低剂量生物炭(0.05%)时,在草本豆科植物中观察到了这些结果。然而,当添加 1%的生物炭时,PFAS 被有效稳定,防止其转移到地上植物部分。除了不同剂量生物炭的不同效果外,本研究还表明,植物对 PFAS 的吸收高度依赖于土壤性质。总的来说,本研究证明了使用草本豆科植物混合物从受污染土壤中去除 PFAS 的可行性,并提出了需要制定特定于地点的处理策略来最大限度地提高植物修复的性能。