Luiz de Queiroz College of Agriculture, University of São Paulo (ESALQ-USP), Av. Pádua Dias 11, CEP, 13418-900, Piracicaba, São Paulo, Brazil.
Luiz de Queiroz College of Agriculture, University of São Paulo (ESALQ-USP), Av. Pádua Dias 11, CEP, 13418-900, Piracicaba, São Paulo, Brazil.
J Environ Manage. 2021 Jan 15;278(Pt 2):111575. doi: 10.1016/j.jenvman.2020.111575. Epub 2020 Nov 2.
The availability of phosphorus (P) in estuarine ecosystems is ultimately controlled by the nature of interactions between dissolved P and the soil components (e.g., soil minerals), especially iron (Fe) oxyhydroxides. P retention on Fe oxyhydroxides and its subsequent availability depends on mineral crystallinity and susceptibility to dissolution. However, in estuarine soils, geochemical conditions (e.g., redox oscillation and high soil organic matter content) may alter the fate of P and decrease the environmental quality of estuarine waters. The large input of Fe-rich tailings into the Rio Doce Estuary in Brazil in 2015 after a rupture of a Fe ore tailings dam (i.e., "Mariana mine disaster") offers a unique framework to evaluate the Fe oxyhydroxides role in P availability in estuarine soils, their potential effects on the cycling of P and eutrophication. We observed a significant correlation between Fe minerals and the P content in the estuary soils, suggesting that P enrichment was promoted by the deposited Fe-rich tailings. Adsorption isotherm curves indicated that mine tailings had a strong affinity for P due to presence of crystalline Fe oxyhydroxides in the tailings. Significant losses of Fe (62%) and P (56%) from the estuarine soil was observed two years after the initial impact and in response to redox conditions oscillations. Additionally, the content of high crystallinity Fe oxyhydroxides decreased significantly, whereas that of low crystallinity Fe oxyhydroxides showed an increase over time. These changes were associated with the dissimilatory Fe reduction, which led an increase in the concentrations of readily available P (2015: 2.30 ± 0.41 mg kg; 2017: 3.83 ± 1.82 mg kg; p < 0.001) in the studied soils. Moreover, in 2017, the dissolved P content exceeded the recommended environmental safety limits by five times. Our results indicate that Fe oxyhydroxides are a continuous source of dissolved P for the ecosystem, and Fe-rich tailings deposited in the estuarine ecosystem may be linked to a potential eutrophication.
在河口生态系统中,磷 (P) 的可利用性最终受溶解态 P 与土壤成分(例如土壤矿物质)之间相互作用的性质控制,特别是铁 (Fe) 氢氧化物。Fe 氢氧化物对 P 的保留及其随后的可利用性取决于矿物结晶度和溶解的易感性。然而,在河口土壤中,地球化学条件(例如氧化还原振荡和高土壤有机质含量)可能会改变 P 的命运并降低河口水域的环境质量。2015 年,巴西里奥杜塞伊罗河口的一座铁矿尾矿坝破裂后,大量富含铁的尾矿涌入该河口(即“马里亚纳矿难”),为评估 Fe 氢氧化物在河口土壤中 P 可利用性的作用、它们对 P 循环和富营养化的潜在影响提供了一个独特的框架。我们观察到河口土壤中 Fe 矿物与 P 含量之间存在显著相关性,这表明 P 的富集是由沉积的富含铁的尾矿促进的。吸附等温线曲线表明,由于尾矿中存在结晶态 Fe 氢氧化物,尾矿对 P 具有很强的亲和力。在最初受冲击后两年,以及在氧化还原条件振荡的响应中,观察到来自河口土壤的 Fe(62%)和 P(56%)大量流失。此外,高结晶度 Fe 氢氧化物的含量显著下降,而低结晶度 Fe 氢氧化物的含量随时间增加。这些变化与异化 Fe 还原有关,这导致了易利用的 P 浓度增加(2015 年:2.30±0.41mg kg;2017 年:3.83±1.82mg kg;p<0.001)。此外,在 2017 年,溶解态 P 的含量超过了推荐的环境安全限值的五倍。我们的结果表明,Fe 氢氧化物是生态系统中溶解态 P 的连续来源,而沉积在河口生态系统中的富含铁的尾矿可能与潜在的富营养化有关。