Jiangsu Key Laboratory of Ocean-Land Environmental Change and Ecological Construction, School of Marine Science and Engineering, Nanjing Normal University, Nanjing 210023, China; Centre for Urban Sustainability and Resilience, Department of Civil, Environmental and Geomatic Engineering, University College London, Gower St, London, WC1E 6BT, United Kingdom.
Centre for Urban Sustainability and Resilience, Department of Civil, Environmental and Geomatic Engineering, University College London, Gower St, London, WC1E 6BT, United Kingdom; Faculty of Health, Science, Social Care and Education, School of Life Sciences, Pharmacy and Chemistry, Kingston University, Penrhyn Road, Kingston Upon Thames, Surrey, KT1 2EE, United Kingdom.
Chemosphere. 2024 Sep;364:143145. doi: 10.1016/j.chemosphere.2024.143145. Epub 2024 Aug 22.
Microplastic (MP) pollution poses a significant environmental challenge, underscoring the need for improved water treatment methods. This study investigates the effectiveness of coagulation, flocculation, and sedimentation processes for removing microbeads, focusing on key factors that influence removal efficiency. Among the coagulants tested, polyaluminium chloride (PAC) demonstrated superior performance by enhancing the aggregation of microplastics with flocs. Optimal treatment conditions were determined to be 0.4 mmol/L PAC and 3 mg/L polyacrylamide (PAM) at pH 8 (before adding PAC), with rapid stirring at 240 rpm for 1 min, followed by slow stirring at 35 rpm for 13 min, and a sedimentation period of 25 min. Under these conditions, removal efficiencies exceeded 95 % for a range of microbeads (10-1000 μm: Polystyrene (PS), Polypropylene (PP), Polyvinyl chloride (PVC), Polyamide (PA), Polyethylene (PE), and Polyurethane (PU)) from natural water samples. Without PAM, PAC alone achieved a 97 % removal rate for PS microbeads. The addition of PAM maintained high removal efficiency, while aluminium sulphate and ferric chloride were less effective, with removal rates of 67 % and 48 % for PS microbeads, respectively. PAM enhanced MP removal across various coagulants and microbead types, with maximum efficiency observed at PAM concentrations of ≥3 mg/L. The treatment also demonstrated that organic matter in Regent's Park pond water could further improve MP removal. Size significantly impacts removal efficiency: larger microbeads (1 mm to >250 μm) were removed more effectively (95 %) compared to smaller ones (10 to <250 μm), which had a lower removal rate of 49 %. Denser microbeads like PVC (density 1.38 g/cm³) settled more efficiently than lighter microbeads such as PE (density 0.97 g/cm³). These findings suggest a need for advanced technologies to better remove lighter, smaller MPs from water.
微塑料 (MP) 污染对环境构成了重大挑战,突显了改进水处理方法的必要性。本研究探讨了混凝、絮凝和沉淀工艺去除微珠的效果,重点研究了影响去除效率的关键因素。在所测试的混凝剂中,聚合氯化铝 (PAC) 通过增强微塑料与絮体的聚集,表现出卓越的性能。确定的最佳处理条件为 PAC 为 0.4 mmol/L 和聚丙烯酰胺 (PAM) 为 3 mg/L,pH 值为 8(在添加 PAC 之前),快速搅拌速度为 240 rpm 持续 1 分钟,然后以 35 rpm 的速度缓慢搅拌 13 分钟,沉淀时间为 25 分钟。在这些条件下,从天然水样中去除一系列微珠(10-1000 μm:聚苯乙烯 (PS)、聚丙烯 (PP)、聚氯乙烯 (PVC)、聚酰胺 (PA)、聚乙烯 (PE) 和聚亚安酯 (PU))的去除效率超过 95%。没有 PAM,PAC 单独对 PS 微珠的去除率达到 97%。添加 PAM 保持了高去除效率,而硫酸铝和氯化铁的效果较差,PS 微珠的去除率分别为 67%和 48%。PAM 提高了各种混凝剂和微珠类型的 MP 去除效率,在 PAM 浓度≥3 mg/L 时达到最大效率。该处理还表明,摄政公园池塘水中的有机物可以进一步提高 MP 的去除率。尺寸对去除效率有显著影响:较大的微珠(1 毫米至>250 微米)的去除效率更高(95%),而较小的微珠(10 至<250 微米)的去除效率较低(49%)。密度较大的微珠(如 PVC,密度 1.38 g/cm³)比密度较小的微珠(如 PE,密度 0.97 g/cm³)更容易沉降。这些发现表明需要先进的技术来更好地从水中去除更轻、更小的 MPs。