College of Land Science and Technology, China Agricultural University, Beijing, 100083, PR China.
College of Land Science and Technology, China Agricultural University, Beijing, 100083, PR China.
Chemosphere. 2024 Sep;364:143300. doi: 10.1016/j.chemosphere.2024.143300. Epub 2024 Sep 7.
Phosphorus (P) has been widely recognized as a substance that is difficult to transport due to its tendency to become easily fixed in the soil. However, many reports demonstrate that groundwater P pollution is rising in humus-rich areas. Research is urgently needed to confirm (or reject) the hypothesis that increased P pollution is related to humus, as there is currently limited quantitative research on this topic. In this study, we conducted a series of batch equilibrium adsorption-desorption experiments and column experiments to quantify the effects of montmorillonite colloids (MCs) and humic acids (HCs, the main components of humus) on the P transport behavior. The results indicate that P's adsorption and desorption behavior on MCs can be well simulated using the Langmuir and Temkin models (R > 0.91). Compared to the non-HC treatments, HCs significantly increased MCs' P adsorption and desorption capacity 5.18 and 7.21 times, respectively. Moreover, HCs facilitated the transport ability of the MC-P mixture through the saturated quartz sand column. In a 0.1 M NaCl solution, the MC-P mixture is nearly completely adsorbed on the surface of quartz sand, with a penetration rate of only 0.5%. In contrast, the HC-MC-P mixture can evidently penetrate further at a rate of 26.1%. The transport parameters fitted using HYDRUS-1D further indicated that the presence of humic acids significantly decreased the deposition coefficients of colloids, thereby enhancing the co-transport of colloids and P through the quartz sand porous medium. The potential mechanism of P pollution in humus-rich areas is likely enhanced by the formation of an HC-colloid-P mixture, which greatly increases the adsorption amount of P on colloids and enhances the electrostatic and spatial repulsion between colloids as well as between colloids and quartz sand. It reduces the aggregation and adsorption of colloids, ultimately transferring P into groundwater through colloid-facilitated co-transport. The findings of this study clarified the relationship between the transport of P, colloids, and HCs, which provides a theoretical basis for explaining the P pollution mechanism in humus-rich areas.
磷(P)由于其在土壤中易固定的倾向而被广泛认为是一种难以迁移的物质。然而,许多报告表明,富含有机质地区的地下水 P 污染正在上升。需要进行研究来确认(或否定)增加的 P 污染与腐殖质有关的假说,因为目前针对这一主题的定量研究有限。在这项研究中,我们进行了一系列批平衡吸附-解吸实验和柱实验,以量化蒙脱石胶体(MCs)和腐殖酸(HCs,腐殖质的主要成分)对 P 迁移行为的影响。结果表明,P 在 MCs 上的吸附和解吸行为可以用 Langmuir 和 Temkin 模型很好地模拟(R>0.91)。与非 HC 处理相比,HCs 分别显著增加了 MCs 的 P 吸附和解吸容量 5.18 倍和 7.21 倍。此外,HCs 促进了 MC-P 混合物在饱和石英砂柱中的传输能力。在 0.1 M NaCl 溶液中,MC-P 混合物几乎完全被吸附在石英砂表面,穿透率仅为 0.5%。相比之下,HC-MC-P 混合物的穿透率明显更高,为 26.1%。使用 HYDRUS-1D 拟合的传输参数进一步表明,腐殖酸的存在显著降低了胶体的沉积系数,从而增强了胶体和 P 通过石英砂多孔介质的共传输。富含有机质地区 P 污染的潜在机制可能是由于形成 HC-胶体-P 混合物而增强,这大大增加了胶体对 P 的吸附量,并增强了胶体之间以及胶体与石英砂之间的静电和空间排斥作用。它减少了胶体的聚集和吸附,最终通过胶体促进的共传输将 P 转移到地下水中。本研究结果阐明了 P、胶体和 HCs 传输之间的关系,为解释富含有机质地区 P 污染机制提供了理论依据。