Microplastics: A potential booster for PFAS in biosolids

IF 3 4区 环境科学与生态学 Q2 ENVIRONMENTAL SCIENCES
Samreen Siddiqui
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Microplastics are now recognized as a major contemporary global problem (Mitrano &amp; Wagner, <span>2021</span>; Sendra et al., <span>2021</span>), with a current estimate of 1.5 million tons of MP waste in the waterways globally (Boucher &amp; Friot, <span>2017</span>).</p><p>Per- and polyfluoroalkyl substances (PFAS), often referred to as “forever chemicals” due to their persistence in the environment, present a hidden threat to human health (Fenton et al., <span>2021</span>). These man-made chemicals, lauded for their water and stain-repelling properties, lurk unseen in a vast array of consumer products. However, their presence comes at a cost. Most recently (January 2024) method 1633, which created a stable and uniform approach for the analytical identification of PFAS, was approved by USEPA to identify 40 PFAS compounds. On 10 April 2024, the USEPA announced the final National Primary Drinking Water Regulation (NPDWR) for six PFAS (PFOA, PFOS, PFHxS, PFNA, PFBS, and HFPO-DA). This enables USEPA to establish legally enforceable levels, called Maximum Contaminant Levels, for six PFAS in drinking water.</p><p>In addition to being a primary source of pollution, MPs can also act as a carrier (via sorption and desorption) for other contaminants including PFAS. Some of the plastic types, including polytetrafluoroethylene and polyvinyl fluoride, can contribute PFAS directly to the environment. However, this is a very small contribution compared with the potential adsorption pathway via widespread MP pollution globally. This does not disregard PFAS concerns, as some authors have suggested (Lohmann et al., <span>2020</span>). Rather, MPs might also increase the overall availability of PFAS in biosolids. As MPs degrade, they could release any absorbed PFAS, making them more bioavailable (available for uptake by organisms).</p><p>There are also concerns that MPs can be more efficient in adsorbing PFAS in the presence of other organic and inorganic matter, when compared with controlled environments, due to their large surface area and strong hydrophobic nature (Scott et al., <span>2021</span>). The adsorption of PFAS to MPs was identified as thermodynamically spontaneous due to the increased entropy at 25 °C, based on Gibb's free energy (Δ<i>G</i> = −16 to −23 kJ/mol), reaching equilibrium within 7–9 h (Salawu et al., <span>2024</span>). This suggests that PFAS may partition to the MP surface within a few hours in fresh and marine water. Biofilms, composed of algae, bacteria, and other microorganisms in the environment, can further influence the sorption properties of MPs (Lagarde et al., <span>2016</span>). This is particularly concerning because both PFAS and MPs tend to accumulate together in wastewater, with a higher proportion ending up in solid waste. These concentrated conditions create favorable environments for increased PFAS sorption by MPs. This becomes a point of concern when the biosolid waste is further used in land application (56%), comprising agricultural land (31%), reclamation sites (e.g., mining sites) (1%), and other (24%); landfilling (27%), comprising municipal solid waste (24%) and monofil (3%); incineration (16%); and other (1%) within the continental USA (USEPA, <span>2023</span>). Application of biosolids with MP-sorbed PFAS may enhance bioavailability to crops, which can bioconcentrate in the longer run. Recently, a study reported that 23 years of biosolids application resulted in MP concentrations of 360 to 500 particles per kg of soil located on the Waterville plateau in Douglas County, north-central Washington state (Adhikari et al., <span>2024</span>). This highlights the potential for biosolids to be a source of MPs and PFAS in the environment.</p><p>Currently, there are no regulations that can provide guidance on most of the contaminants of emerging concerns (CECs), including MPs and PFAS in wastewater. Regulating MPs and PFAS, as well, most likely, as other persistent emerging contaminants, in biosolid waste is crucial. This could not only protect public health but also drive research efforts toward developing effective removal technologies. Due to the low mass of MPs, they cannot easily be separated in the wastewater removal process. There is thus a need for cost-effective wastewater treatment technologies that can help MP removal from biosolids before their application to fields. This commentary calls on researchers to learn more about MPs–PFAS interactions and help create effective solutions. To safeguard our health and environment, we need a multipronged approach, including regulation, research, and technological innovations. Implementing clear regulations for MPs and PFAS levels in biosolids is crucial. This will guide responsible management practices and protect public health. Continued research is vital to understanding the long-term consequences of MPs and PFAS exposure, as well as developing cost-effective treatment technologies for wastewater to remove MPs before biosolid creation. Exploring and developing innovative technologies for biosolids treatment that effectively remove CECs, including MPs and PFAS, is essential. 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引用次数: 0

Abstract

Imagine enjoying a refreshing glass of water, only to discover tiny plastic particles swirling within. This unsettling reality is becoming increasingly common as microplastics (MPs), plastic fragments smaller than a grain of rice (<5 mm diam.), infiltrate our environment at an alarming rate. From the deepest trenches of the ocean to the peaks of mountains, these invisible invaders pose a significant potential threat to wildlife and even human health (Li et al., 2023; Zolotova et al., 2022). Microplastics are now recognized as a major contemporary global problem (Mitrano & Wagner, 2021; Sendra et al., 2021), with a current estimate of 1.5 million tons of MP waste in the waterways globally (Boucher & Friot, 2017).

Per- and polyfluoroalkyl substances (PFAS), often referred to as “forever chemicals” due to their persistence in the environment, present a hidden threat to human health (Fenton et al., 2021). These man-made chemicals, lauded for their water and stain-repelling properties, lurk unseen in a vast array of consumer products. However, their presence comes at a cost. Most recently (January 2024) method 1633, which created a stable and uniform approach for the analytical identification of PFAS, was approved by USEPA to identify 40 PFAS compounds. On 10 April 2024, the USEPA announced the final National Primary Drinking Water Regulation (NPDWR) for six PFAS (PFOA, PFOS, PFHxS, PFNA, PFBS, and HFPO-DA). This enables USEPA to establish legally enforceable levels, called Maximum Contaminant Levels, for six PFAS in drinking water.

In addition to being a primary source of pollution, MPs can also act as a carrier (via sorption and desorption) for other contaminants including PFAS. Some of the plastic types, including polytetrafluoroethylene and polyvinyl fluoride, can contribute PFAS directly to the environment. However, this is a very small contribution compared with the potential adsorption pathway via widespread MP pollution globally. This does not disregard PFAS concerns, as some authors have suggested (Lohmann et al., 2020). Rather, MPs might also increase the overall availability of PFAS in biosolids. As MPs degrade, they could release any absorbed PFAS, making them more bioavailable (available for uptake by organisms).

There are also concerns that MPs can be more efficient in adsorbing PFAS in the presence of other organic and inorganic matter, when compared with controlled environments, due to their large surface area and strong hydrophobic nature (Scott et al., 2021). The adsorption of PFAS to MPs was identified as thermodynamically spontaneous due to the increased entropy at 25 °C, based on Gibb's free energy (ΔG = −16 to −23 kJ/mol), reaching equilibrium within 7–9 h (Salawu et al., 2024). This suggests that PFAS may partition to the MP surface within a few hours in fresh and marine water. Biofilms, composed of algae, bacteria, and other microorganisms in the environment, can further influence the sorption properties of MPs (Lagarde et al., 2016). This is particularly concerning because both PFAS and MPs tend to accumulate together in wastewater, with a higher proportion ending up in solid waste. These concentrated conditions create favorable environments for increased PFAS sorption by MPs. This becomes a point of concern when the biosolid waste is further used in land application (56%), comprising agricultural land (31%), reclamation sites (e.g., mining sites) (1%), and other (24%); landfilling (27%), comprising municipal solid waste (24%) and monofil (3%); incineration (16%); and other (1%) within the continental USA (USEPA, 2023). Application of biosolids with MP-sorbed PFAS may enhance bioavailability to crops, which can bioconcentrate in the longer run. Recently, a study reported that 23 years of biosolids application resulted in MP concentrations of 360 to 500 particles per kg of soil located on the Waterville plateau in Douglas County, north-central Washington state (Adhikari et al., 2024). This highlights the potential for biosolids to be a source of MPs and PFAS in the environment.

Currently, there are no regulations that can provide guidance on most of the contaminants of emerging concerns (CECs), including MPs and PFAS in wastewater. Regulating MPs and PFAS, as well, most likely, as other persistent emerging contaminants, in biosolid waste is crucial. This could not only protect public health but also drive research efforts toward developing effective removal technologies. Due to the low mass of MPs, they cannot easily be separated in the wastewater removal process. There is thus a need for cost-effective wastewater treatment technologies that can help MP removal from biosolids before their application to fields. This commentary calls on researchers to learn more about MPs–PFAS interactions and help create effective solutions. To safeguard our health and environment, we need a multipronged approach, including regulation, research, and technological innovations. Implementing clear regulations for MPs and PFAS levels in biosolids is crucial. This will guide responsible management practices and protect public health. Continued research is vital to understanding the long-term consequences of MPs and PFAS exposure, as well as developing cost-effective treatment technologies for wastewater to remove MPs before biosolid creation. Exploring and developing innovative technologies for biosolids treatment that effectively remove CECs, including MPs and PFAS, is essential. This is a collective responsibility, demanding action from researchers, policymakers, and the public alike.

微塑料:生物固体中 PFAS 的潜在助推器。
想象一下,在享受一杯清爽的水时,却发现里面有微小的塑料颗粒在旋转。这种令人不安的现实正变得越来越普遍,因为微塑料(MPs),即直径小于米粒(5 毫米)的塑料碎片,正以惊人的速度渗入我们的环境。从海洋深处的海沟到高山之巅,这些看不见的入侵者对野生动物甚至人类健康都构成了巨大的潜在威胁(Li 等人,2023 年;Zolotova 等人,2022 年)。微塑料现已被公认为当代全球的一个主要问题(Mitrano &amp; Wagner, 2021; Sendra et al.这些人造化学物质因其防水防污的特性而备受赞誉,却潜伏在大量消费品中,不为人知。然而,它们的存在是有代价的。最近(2024 年 1 月),美国环保局批准了 1633 方法,该方法为分析鉴定 PFAS 提供了一种稳定统一的方法,可鉴定 40 种 PFAS 化合物。2024 年 4 月 10 日,美国环保局宣布了针对六种 PFAS(PFOA、PFOS、PFHxS、PFNA、PFBS 和 HFPO-DA)的最终《国家主要饮用水法规》(NPDWR)。这使得美国环保局能够针对饮用水中的六种 PFAS 制定法律强制执行水平,即最大污染物水平。除了作为主要污染源,MPs 还可以作为其他污染物(包括 PFAS)的载体(通过吸附和解吸)。包括聚四氟乙烯和聚氟乙烯在内的一些塑料类型会直接向环境中排放 PFAS。不过,与全球广泛存在的 MP 污染的潜在吸附途径相比,这只是很小的一部分。这并不像一些作者所认为的那样(Lohmann 等人,2020 年),可以忽略对 PFAS 的关注。相反,MPs 还可能增加生物固体中 PFAS 的总体可得性。随着 MPs 降解,它们可能会释放出任何被吸收的全氟辛烷磺酸,使其生物利用率更高(可被生物体吸收)。还有人担心,与受控环境相比,MPs 由于其表面积大、疏水性强,在存在其他有机和无机物质的情况下,吸附全氟辛烷磺酸的效率更高(Scott 等人,2021 年)。根据吉布斯自由能(ΔG = -16 至 -23 kJ/mol),全氟辛烷磺酸在 25 °C时熵增加,因此全氟辛烷磺酸对 MPs 的吸附被确定为热力学自发吸附,在 7-9 小时内达到平衡(Salawu 等人,2024 年)。这表明,在淡水和海水中,全氟辛烷磺酸可在几小时内分馏到 MP 表面。由环境中的藻类、细菌和其他微生物组成的生物膜会进一步影响 MPs 的吸附特性(Lagarde 等人,2016 年)。这一点尤其令人担忧,因为全氟辛烷磺酸和多溴联苯醚往往会在废水中积聚在一起,最终进入固体废物的比例更高。这些浓缩条件为 MPs 增加对 PFAS 的吸附创造了有利环境。在美国大陆,当生物固体废弃物被进一步用于土地施用(56%),包括农田(31%)、开垦场地(如采矿场)(1%)和其他(24%);填埋(27%),包括城市固体废弃物(24%)和单层垃圾(3%);焚烧(16%)和其他(1%)时,这就成为一个值得关注的问题(美国环保局,2023 年)。施用吸附了多溴联苯醚的生物固体可能会提高作物对 PFAS 的生物利用率,从长远来看,作物会发生生物富集。最近,一项研究报告称,在华盛顿州中北部道格拉斯县的沃特维尔高原,23 年的生物固体施用导致每公斤土壤中的 MP 浓度达到 360 至 500 微粒(Adhikari 等人,2024 年)。这凸显了生物固体可能成为环境中 MPs 和 PFAS 的来源。目前,还没有任何法规可以为大多数新出现的污染物 (CEC) 提供指导,包括废水中的 MPs 和 PFAS。对生物固体废物中的 MPs 和 PFAS 以及很可能存在的其他持久性新兴污染物进行监管至关重要。这不仅能保护公众健康,还能推动研究工作,开发有效的去除技术。由于多溴联苯质量小,在废水去除过程中不易分离。因此,有必要开发具有成本效益的废水处理技术,以帮助生物固体在施用到田地之前去除其中的 MP。本评论呼吁研究人员更多地了解 MPs-PFAS 的相互作用,并帮助制定有效的解决方案。为了保护我们的健康和环境,我们需要多管齐下,包括监管、研究和技术创新。
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来源期刊
Integrated Environmental Assessment and Management
Integrated Environmental Assessment and Management ENVIRONMENTAL SCIENCESTOXICOLOGY&nbs-TOXICOLOGY
CiteScore
5.90
自引率
6.50%
发文量
156
期刊介绍: Integrated Environmental Assessment and Management (IEAM) publishes the science underpinning environmental decision making and problem solving. Papers submitted to IEAM must link science and technical innovations to vexing regional or global environmental issues in one or more of the following core areas: Science-informed regulation, policy, and decision making Health and ecological risk and impact assessment Restoration and management of damaged ecosystems Sustaining ecosystems Managing large-scale environmental change Papers published in these broad fields of study are connected by an array of interdisciplinary engineering, management, and scientific themes, which collectively reflect the interconnectedness of the scientific, social, and environmental challenges facing our modern global society: Methods for environmental quality assessment; forecasting across a number of ecosystem uses and challenges (systems-based, cost-benefit, ecosystem services, etc.); measuring or predicting ecosystem change and adaptation Approaches that connect policy and management tools; harmonize national and international environmental regulation; merge human well-being with ecological management; develop and sustain the function of ecosystems; conceptualize, model and apply concepts of spatial and regional sustainability Assessment and management frameworks that incorporate conservation, life cycle, restoration, and sustainability; considerations for climate-induced adaptation, change and consequences, and vulnerability Environmental management applications using risk-based approaches; considerations for protecting and fostering biodiversity, as well as enhancement or protection of ecosystem services and resiliency.
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