白腐真菌对 OPFR 的去除:去除剂的筛选和去除机制的探索

Diana Losantos, Montserrat Sarra, Glòria Caminal
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引用次数: 0

摘要

有机磷阻燃剂(OPFR)在废水(WW)排放物中的持续存在引起了人们对环境和健康的极大关注,凸显了传统去除方法的局限性。真菌,尤其是白腐真菌(WRF),为去除 OPFR 提供了一种前景广阔的替代方法。本研究试图从四种白腐真菌和两种子囊菌群真菌中找出能够有效去除 WW 中五种常见 OPFR 的候选真菌:磷酸三丁酯 (TnBP)、磷酸三丁氧基乙酯 (TBEP)、磷酸三氯乙酯 (TCEP)、磷酸三氯丙酯 (TCPP) 和磷酸三乙酯 (TEP)。目的是开发一种用于处理 WW 的共培养方法,同时解决 WW 中同化性较低的碳源的利用问题。对所有候选真菌的碳源吸收和 OPFR 去除情况进行了研究,同时分析了降解率最高的真菌对生物质吸附的贡献。此外,还确定了参与 OPFR 降解的酶系统,以及真菌接触后样品的毒性。在碳源吸收研究中,乙酸酯(1.4 g-L-1)模拟了较少同化的有机物,所有受试真菌都能在 4 天内消除乙酸酯。不过,在对四种 OPFR(不包括 TCPP)的去除进行初步筛选时,WRF 的表现优于子囊菌属真菌。灵芝和 Trametes versicolor 能在 4 天内去除 90% 以上的 TnBP 和 TBEP,Pleorotus ostreatus 和 Pycnoporus sanguineus 也能有效去除。TCEP 的去除具有挑战性,只有 G. lucidum 实现了部分去除(47%)。随后使用选定的 WRF 和添加的 TCPP 进行筛选,发现与 TCEP 相比,TCPP 更容易降解,其中 T. versicolor 的去除效率最高(77%)。这一观察结果以及所有候选真菌对 TEP 的降解效果都很差,表明 OPFR 的极性与其对真菌降解的敏感性成反比。吸附研究证实,性能最好的真菌对每种选定的 OPFR 都有主要降解能力。酶系统测试确定了细胞内负责 OPFR 降解的 CYP450 系统,因此羟化、脱烷基和脱卤反应可能参与了降解途径。最后,毒性测试表明,真菌降解得到的转化产物比母体化合物毒性更强,因此有必要对它们及其毒性贡献进行鉴定。总之,这项研究为水生生物反应器降解 OPFR 提供了宝贵的见解,对未来使用混合菌群处理 WW 具有重要意义,并强调了降低所产生的毒性的重要性。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
OPFR removal by white rot fungi: screening of removers and approach to the removal mechanism
The persistent presence of organophosphate flame retardants (OPFRs) in wastewater (WW) effluents raises significant environmental and health concerns, highlighting the limitations of conventional treatments for their remotion. Fungi, especially white rot fungi (WRF), offer a promising alternative for OPFR removal. This study sought to identify fungal candidates (from a selection of four WRF and two Ascomycota fungi) capable of effectively removing five frequently detected OPFRs in WW: tributyl phosphate (TnBP), tributoxy ethyl phosphate (TBEP), trichloroethyl phosphate (TCEP), trichloro propyl phosphate (TCPP) and triethyl phosphate (TEP). The objective was to develop a co-culture approach for WW treatment, while also addressing the utilization of less assimilable carbon sources present in WW. Research was conducted on carbon source uptake and OPFR removal by all fungal candidates, while the top degraders were analyzed for biomass sorption contribution. Additionally, the enzymatic systems involved in OPFR degradation were identified, along with toxicity of samples after fungal contact. Acetate (1.4 g·L-1), simulating less assimilable organic matter in the carbon source uptake study, was eliminated by all tested fungi in 4 days. However, during the initial screening where the removal of four OPFRs (excluding TCPP) was tested, WRF outperformed Ascomycota fungi. Ganoderma lucidum and Trametes versicolor removed over 90% of TnBP and TBEP within 4 days, with Pleorotus ostreatus and Pycnoporus sanguineus also displaying effective removal. TCEP removal was challenging, with only G. lucidum achieving partial removal (47%). A subsequent screening with selected WRF and the addition of TCPP revealed TCPP’s greater susceptibility to degradation compared to TCEP, with T. versicolor exhibiting the highest removal efficiency (77%). This observation, plus the poor degradation of TEP by all fungal candidates suggests that polarity of an OPFR inversely correlates with its susceptibility to fungal degradation. Sorption studies confirmed the ability of top-performing fungi of each selected OPFR to predominantly degrade them. Enzymatic system tests identified the CYP450 intracellular system responsible for OPFR degradation, so reactions of hydroxylation, dealkylation and dehalogenation are possibly involved in the degradation pathway. Finally, toxicity tests revealed transformation products obtained by fungal degradation to be more toxic than the parent compounds, emphasizing the need to identify them and their toxicity contributions. Overall, this study provides valuable insights into OPFR degradation by WRF, with implications for future WW treatment using mixed consortia, emphasizing the importance of reducing generated toxicity.
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