Department of Civil and Environmental Engineering, Auburn University, Auburn, AL, 36849, USA.
School of Fisheries, Aquaculture and Aquatic Sciences, Auburn University, Auburn, AL, 36849, USA.
Environ Sci Pollut Res Int. 2024 Oct;31(50):60555-60567. doi: 10.1007/s11356-024-35268-5. Epub 2024 Oct 10.
Phosphorus (P) overloading in aquatic environments has long-been recognized as the leading cause of water quality deterioration, harmful algal bloom, and eutrophication. This study investigated P removal performance by five cost-effective carbonaceous materials (CMs) in flow-through packed column systems. These CMs include biochars pyrolyzed from feedstocks of Eucalyptus (E-biochar) and Douglas fir (D-biochar), commercial biochar (C-biochar), iron oxide-coated biochar (Fe-biochar), and commercial activated carbon (AC). The physicochemical properties of CMs, such as specific surface area (SSA), pore volume, pore diameter, elemental composition, and surface charge, were characterized. The packed column experimental results showed that P removal performance followed the order: E-biochar < D-biochar < C-biochar < Fe-biochar < AC. Specifically, the sorption capacity of 1 mg/L of P in packed columns was 0.0036 mg P/g E-biochar, 0.0111 mg P/g D-biochar, 0.0369 mg P/g D-biochar, 0.077 mg P/g Fe-biochar, and 0.088 mg P/g AC, respectively. The largest SSA (1012 m/g) and pore volume (0.57 cm/g) of AC accounted for the most outstanding P removal efficiency mainly by physical sorption, while electrostatic interaction explained the high P removal by Fe-biochar (SSA as low as 32.4 m/g). Our findings provide direct practical implications for effectively removing P in water by cost-effective CMs.
磷(P)在水环境污染中一直被认为是导致水质恶化、有害藻类繁殖和富营养化的主要原因。本研究采用五种经济有效的碳质材料(CMs)在流动填充柱系统中研究了 P 的去除性能。这些 CMs 包括由桉树(E-生物炭)和花旗松(D-生物炭)作为原料热解得到的生物炭、商业生物炭(C-生物炭)、氧化铁涂层生物炭(Fe-生物炭)和商业活性炭(AC)。对 CMs 的物理化学性质,如比表面积(SSA)、孔体积、孔径、元素组成和表面电荷进行了表征。填充柱实验结果表明,P 的去除性能依次为:E-生物炭 < D-生物炭 < C-生物炭 < Fe-生物炭 < AC。具体而言,在填充柱中 1mg/L 的 P 的吸附容量分别为 0.0036mg P/g E-生物炭、0.0111mg P/g D-生物炭、0.0369mg P/g D-生物炭、0.077mg P/g Fe-生物炭和 0.088mg P/g AC。AC 的最大 SSA(1012 m/g)和孔体积(0.57 cm/g)导致了最突出的 P 去除效率,主要是通过物理吸附,而静电相互作用解释了 Fe-生物炭对 P 的高去除效率(SSA 低至 32.4 m/g)。我们的发现为通过经济有效的 CMs 有效去除水中的 P 提供了直接的实际意义。