INRS-ETE, Université du Québec, 490, Rue de la Couronne, Québec G1K 9A9, Canada.
INRS-ETE, Université du Québec, 490, Rue de la Couronne, Québec G1K 9A9, Canada.
Environ Pollut. 2018 Mar;234:190-213. doi: 10.1016/j.envpol.2017.11.060. Epub 2017 Nov 24.
Due to recalcitrance of some pharmaceutically active compounds (PhACs), conventional wastewater treatment is not able to remove them effectively. Therefore, their occurrence in surface water and potential environmental impact has raised serious global concern. Biological transformation of these contaminants using white-rot fungi (WRF) and their oxidoreductase enzymes has been proposed as a low cost and environmentally friendly solution for water treatment. The removal performance of PhACs by a fungal culture is dependent on several factors, such as fungal species, the secreted enzymes, molecular structure of target compounds, culture medium composition, etc. In recent 20 years, numerous researchers tried to elucidate the removal mechanisms and the effects of important operational parameters such as temperature and pH on the enzymatic treatment of PhACs. This review summarizes and analyzes the studies performed on PhACs removal from spiked pure water and real wastewaters using oxidoreductase enzymes and the data related to degradation efficiencies of the most studied compounds. The review also offers an insight into enzymes immobilization, fungal reactors, mediators, degradation mechanisms and transformation products (TPs) of PhACs. In brief, higher hydrophobicity and having electron-donating groups, such as amine and hydroxyl in molecular structure leads to more effective degradation of PhACs by fungal cultures. For recalcitrant compounds, using redox mediators, such as syringaldehyde increases the degradation efficiency, however they may cause toxicity in the effluent and deactivate the enzyme. Immobilization of enzymes on supports can enhance the performance of enzyme in terms of reusability and stability. However, the immobilization strategy should be carefully selected to reduce the cost and enable regeneration. Still, further studies are needed to elucidate the mechanisms involved in enzymatic degradation and the toxicity levels of TPs and also to optimize the whole treatment strategy to have economical and technical competitiveness.
由于一些药物活性化合物(PhACs)的顽固性,传统的废水处理方法无法有效地去除它们。因此,它们在地表水和潜在的环境影响中的存在引起了全球的严重关注。利用白腐真菌(WRF)及其氧化还原酶生物转化这些污染物已被提出作为一种低成本和环保的水处理方法。真菌培养物对 PhACs 的去除性能取决于多种因素,如真菌种类、分泌的酶、目标化合物的分子结构、培养基组成等。在过去的 20 年中,许多研究人员试图阐明去除机制以及温度和 pH 等重要操作参数对 PhACs 酶处理的影响。
本综述总结和分析了使用氧化还原酶从加标纯水和实际废水中去除 PhACs 的研究,并提供了与最受研究的化合物的降解效率相关的数据。该综述还深入探讨了酶固定化、真菌反应器、介体、PhACs 的降解机制和转化产物(TPs)。简而言之,分子结构中具有较高疏水性和供电子基团(如胺基和羟基)的 PhACs 更易于被真菌培养物有效降解。对于难降解的化合物,使用氧化还原介体(如丁香醛)可以提高降解效率,但它们可能会导致出水毒性并使酶失活。酶在载体上的固定化可以提高酶的性能,从可重复使用性和稳定性方面考虑。然而,需要仔细选择固定化策略,以降低成本并实现酶的再生。
仍需要进一步的研究来阐明酶降解涉及的机制以及 TPs 的毒性水平,并优化整个处理策略,以实现经济和技术竞争力。