Amaro Helena M, Salgado Eva M, Nunes Olga C, Pires José C M, Esteves Ana F
LEPABE - Laboratory for Process Engineering, Environment, Biotechnology and Energy, Faculty of Engineering, University of Porto, Rua Dr Roberto Frias, 4200-465, Porto, Portugal; ALiCE - Associate Laboratory in Chemical Engineering, Faculty of Engineering, University of Porto, Rua Dr. Roberto Frias, 4200-465, Porto, Portugal.
LEPABE - Laboratory for Process Engineering, Environment, Biotechnology and Energy, Faculty of Engineering, University of Porto, Rua Dr Roberto Frias, 4200-465, Porto, Portugal; ALiCE - Associate Laboratory in Chemical Engineering, Faculty of Engineering, University of Porto, Rua Dr. Roberto Frias, 4200-465, Porto, Portugal.
J Environ Manage. 2023 Jul 1;337:117678. doi: 10.1016/j.jenvman.2023.117678. Epub 2023 Mar 21.
Water is the most valuable resource on the planet. However, massive anthropogenic activities generate threatening levels of biological, organic, and inorganic pollutants that are not efficiently removed in conventional wastewater treatment systems. High levels of conventional pollutants (carbon, nitrogen, and phosphorus), emerging chemical contaminants such as antibiotics, and pathogens (namely antibiotic-resistant ones and related genes) jeopardize ecosystems and human health. Conventional wastewater treatment systems entail several environmental issues: (i) high energy consumption; (ii) high CO emissions; and (iii) the use of chemicals or the generation of harmful by-products. Hence, the use of microalgal systems (entailing one or several microalgae species, and in consortium with bacteria) as environmental agents towards wastewater treatment has been seen as an environmentally friendly solution to remove conventional pollutants, antibiotics, coliforms and antibiotic resistance genes. In recent years, several authors have evaluated the use of microalgal systems for the treatment of different types of wastewater, such as agricultural, municipal, and industrial. Generally, microalgal systems can provide high removal efficiencies of: (i) conventional pollutants, up to 99%, 99%, and 90% of total nitrogen, total phosphorus, and/or organic carbon, respectively, through uptake mechanisms, and (ii) antibiotics frequently found in wastewaters, such as sulfamethoxazole, ciprofloxacin, trimethoprim and azithromycin at 86%, 65%, 42% and 93%, respectively, through the most desirable microalgal mechanism, biodegradation. Although pathogens removal by microalgal species is complex and very strain-specific, it is also possible to attain total coliform and Escherichia coli removal of 99.4% and 98.6%, respectively. However, microalgal systems' effectiveness strongly relies on biotic and abiotic conditions, thus the selection of operational conditions is critical. While the combination of selected species (microalgae and bacteria), ratios and inoculum concentration allow the efficient removal of conventional pollutants and generation of high amounts of biomass (that can be further converted into valuable products such as biofuels and biofertilisers), abiotic factors such as pH, hydraulic retention time, light intensity and CO/O supply also have a crucial role in conventional pollutants and antibiotics removal, and wastewater disinfection. However, some rationale must be considered according to the purpose. While alkaline pH induces the hydrolysis of some antibiotics and the removal of faecal coliforms, it also decreases phosphates solubility and induces the formation of ammonium from ammonia. Also, while CO supply increases the removal of E. coli and Pseudomonas aeruginosa, as well as the microalgal growth (and thus the conventional pollutants uptake), it decreases Enterococcus faecalis removal. Therefore, this review aims to provide a critical review of recent studies towards the application of microalgal systems for the efficient removal of conventional pollutants, antibiotics, and pathogens; discussing the feasibility, highlighting the advantages and challenges of the implementation of such process, and presenting current case-studies of different applications of microalgal systems.
水是地球上最宝贵的资源。然而,大量的人为活动产生了达到威胁水平的生物、有机和无机污染物,而这些污染物在传统废水处理系统中无法得到有效去除。高浓度的常规污染物(碳、氮和磷)、诸如抗生素等新兴化学污染物以及病原体(即抗生素抗性病原体及其相关基因),危及生态系统和人类健康。传统废水处理系统存在若干环境问题:(i)高能耗;(ii)高二氧化碳排放;以及(iii)化学品的使用或有害副产物的产生。因此,使用微藻系统(包含一种或几种微藻物种,并与细菌联合)作为处理废水的环境媒介,已被视为一种去除常规污染物、抗生素、大肠菌群和抗生素抗性基因的环保解决方案。近年来,多位作者评估了微藻系统用于处理不同类型废水的情况,如农业废水、城市污水和工业废水。一般来说,微藻系统能够实现较高的去除效率:(i)对于常规污染物,通过吸收机制分别去除总氮、总磷和/或有机碳的效率高达99%、99%和90%;(ii)对于废水中常见的抗生素,如磺胺甲恶唑、环丙沙星、甲氧苄啶和阿奇霉素,通过最理想的微藻机制生物降解,去除率分别为86%、65%、42%和93%。尽管微藻物种去除病原体的过程复杂且具有很强的菌株特异性,但也有可能分别实现99.4%和98.6%的总大肠菌群和大肠杆菌去除率。然而,微藻系统的有效性在很大程度上依赖于生物和非生物条件,因此操作条件的选择至关重要。虽然所选物种(微藻和细菌)的组合、比例和接种物浓度能够有效去除常规污染物并产生大量生物质(可进一步转化为生物燃料和生物肥料等有价值的产品),但诸如pH值、水力停留时间、光照强度和二氧化碳/氧气供应等非生物因素在常规污染物和抗生素去除以及废水消毒方面也起着关键作用。然而,必须根据目的考虑一些基本原理。虽然碱性pH值会促使一些抗生素水解并去除粪大肠菌群,但它也会降低磷酸盐的溶解度并促使氨形成铵。此外,虽然二氧化碳供应会增加大肠杆菌和铜绿假单胞菌的去除率以及微藻的生长(从而提高常规污染物的吸收),但它会降低粪肠球菌的去除率。因此,本综述旨在对近期关于微藻系统高效去除常规污染物、抗生素和病原体的研究进行批判性综述;讨论其可行性,突出该工艺实施的优点和挑战,并展示微藻系统不同应用的当前案例研究。