Photodegradation of steroid hormone micropollutants with palladium-porphyrin coated porous PTFE of varied morphological and optical properties

IF 12.4 1区 环境科学与生态学 Q1 ENGINEERING, ENVIRONMENTAL Water Research Pub Date : 2024-12-22 DOI:10.1016/j.watres.2024.123034
Minh N. Nguyen , Andrey Turshatov , Bryce S. Richards , Andrea I. Schäfer
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Abstract

In flow-through reactors, the photodegradation rate can be improved by enhancing contact and increasing the photocatalyst loading. Both can be attained with a higher surface-to-volume ratio. While previous studies focused on thin membranes (30 – 130 µm) with small pore sizes of 20 – 650 nm, this work employed poly(tetrafluoroethylene) (PTFE) supports, of which pore sizes are in the order of 10 µm, while the porosities and thicknesses are variable (22.5 − 45.3 % and 0.2 − 3 mm, respectively). These porous materials were anticipated to allow a higher loading of porphyrin photosensitisers and better light penetration for subsequent photodegradation of steroid hormone micropollutants via singlet oxygen (1O2) generation. The reactor surface refers to the surface within the PTFE pores, while the reactor volume is the total void space inside these pores. The surface-to-volume ratios between 105 and 106 m2/m3 are higher than those of typical microreactors (103 to 104 m2/m3). The weighted average light transmittance varied from 38 % with the thinnest and most porous support to 4.8 % with the thickest support. Good light penetration combined with minimal absorption by PTFE enhanced the light utilisation of the porphyrins when coated in the porous supports.
Changes in the support porosity of the coated supports minimally affected steroid hormone removal, because the collision frequency in the very large pores remained relatively constant. However, varying the support thickness, porphyrin loading (0.3 − 7.7 μmol/g), and water flux (150 − 3000 L/m2.h), hence the resulting hydraulic residence time, influenced the collision frequency and steroid hormone removal. Results showed that the supports did not outperform membranes most likely because the larger pore size in the former limited contact between the hormones and 1O2.
From photostability testing of the pristine supports, perfluoroalkyl substances (PFAS) released from the supports were found at 10 − 300 ng/L concentrations during accelerated ageing. While PFAS formation was detectable, the quantities during water treatment operations would be extremely low. In summary, this study elucidates the capability and limitations of porous supports coated with photosensitisers to remove waterborne micropollutants.

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钯卟啉包被不同形态和光学性质的多孔聚四氟乙烯光降解类固醇激素微污染物
在流式反应器中,通过更好的接触和光催化剂负载的增加可以提高光降解率。两者都可以获得更高的表面体积比。之前的研究主要集中在孔径为20 - 650纳米的薄膜(30 - 130µm)上,而这项工作是用聚四氟乙烯(PTFE)支撑进行的。孔隙大小在10µm左右,孔隙度为22.5 − 45.3%,厚度为0.2 − 3mm。预计这些多孔材料将增强卟啉光敏剂的负载,并通过单线态氧(1O2)产生更好的光穿透性,以便随后光降解类固醇激素微污染物。反应器表面是指PTFE孔内的表面,而反应器体积是指这些孔内的总空隙空间。表面体积比在105 ~ 106 m2/m3之间,高于典型微反应器(103 ~ 104 m2/m3)。加权平均透光率从最薄多孔支架的38%到最厚支架的4.8%不等。良好的透光性与最小的聚四氟乙烯吸收相结合,增强了涂覆在多孔支架中的卟啉的光利用率。涂层支架孔隙率的变化对类固醇激素去除的影响不大,因为在非常大的孔隙中碰撞频率保持相对恒定。然而,改变载体厚度、卟啉负载(0.3 − 7.7 μmol/g)和水通量(150 − 3000 L/m2.h),所得到的HRT会影响碰撞频率和类固醇激素的去除。结果与膜没有竞争,很可能是由于较大的孔径限制了微污染物和活性氧之间的接触。从原始支架的光稳定性测试中发现,在加速老化过程中,从支架释放的全氟烷基物质(PFAS)浓度为10 − 300 ng/L。这表明,虽然在水处理作业期间释放了一些全氟化砷,但其数量极低。总之,本研究阐明了光敏剂涂层多孔支架去除水性微污染物的能力和局限性。
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来源期刊
Water Research
Water Research 环境科学-工程:环境
CiteScore
20.80
自引率
9.40%
发文量
1307
审稿时长
38 days
期刊介绍: Water Research, along with its open access companion journal Water Research X, serves as a platform for publishing original research papers covering various aspects of the science and technology related to the anthropogenic water cycle, water quality, and its management worldwide. The audience targeted by the journal comprises biologists, chemical engineers, chemists, civil engineers, environmental engineers, limnologists, and microbiologists. The scope of the journal include: •Treatment processes for water and wastewaters (municipal, agricultural, industrial, and on-site treatment), including resource recovery and residuals management; •Urban hydrology including sewer systems, stormwater management, and green infrastructure; •Drinking water treatment and distribution; •Potable and non-potable water reuse; •Sanitation, public health, and risk assessment; •Anaerobic digestion, solid and hazardous waste management, including source characterization and the effects and control of leachates and gaseous emissions; •Contaminants (chemical, microbial, anthropogenic particles such as nanoparticles or microplastics) and related water quality sensing, monitoring, fate, and assessment; •Anthropogenic impacts on inland, tidal, coastal and urban waters, focusing on surface and ground waters, and point and non-point sources of pollution; •Environmental restoration, linked to surface water, groundwater and groundwater remediation; •Analysis of the interfaces between sediments and water, and between water and atmosphere, focusing specifically on anthropogenic impacts; •Mathematical modelling, systems analysis, machine learning, and beneficial use of big data related to the anthropogenic water cycle; •Socio-economic, policy, and regulations studies.
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