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在黑臭底泥修复过程中,硝酸盐还原驱动的硫化亚铁氧化过程中磷的固定。

Phosphorus immobilization in sulfide-ferrous oxidation process driven by nitrate reduction during black-odorous sediment remediation.

机构信息

Department of Environmental Science and Engineering, College of Natural Resource and Environment, South China Agricultural University, Guangzhou 510642, China.

Department of Environmental Science and Engineering, College of Natural Resource and Environment, South China Agricultural University, Guangzhou 510642, China; Guangdong Laboratory for Lingnan Modern Agriculture, South China Agricultural University, Guangzhou 510642, China; Guangdong Provincial Key Laboratory of Agricultural & Rural Pollution Abatement and Environmental Safety, Guangzhou 510642, China.

出版信息

Bioresour Technol. 2024 Sep;407:131130. doi: 10.1016/j.biortech.2024.131130. Epub 2024 Jul 18.

Abstract

During remediation of black-odorous sediment, the pathways of phosphorus immobilization require clarification alongside the oxidation of sulfide and ferrous. This study separated the oxidation stages of sulfide and ferrous through controlled sodium nitrate dosing ratios and methods, and analyzed the changes in phosphorus species and immobilization effects throughout these processes. Results showed that iron-bound phosphorus was the primary contributor to the phosphorus immobilization in the oxidation process, with increased 19% in ferrous oxidation stage and affected the transformation between phosphorus sources or sinks in the adsorption experiment. Additionally, the increase in abundance of phosphorus uptake and transport genes, and denitrifying phosphorus accumulation genes in sediment after ferrous oxidation (1 %-18 % and 87 %-164 %, respectively) indicated the potential for biological phosphorus immobilization. These results demonstrated that higher degrees of sediment oxidation correlate with stronger phosphorus immobilization capacities, providing theoretical bases for phosphorus immobilization during the restoration of black-odorous water bodies.

摘要

在黑臭底泥修复过程中,需要阐明磷的固定途径,同时还要氧化硫化物和亚铁。本研究通过控制硝酸钠投加比和方法,将硫化物和亚铁的氧化阶段分开,并分析了整个过程中磷形态的变化和固定效果。结果表明,铁结合磷是氧化过程中磷固定的主要贡献者,亚铁氧化阶段增加了 19%,并影响了吸附实验中磷源或汇的转化。此外,亚铁氧化后沉积物中磷摄取和运输基因(分别增加 1%18%和 87%164%)和反硝化磷积累基因的丰度增加,表明存在生物磷固定的潜力。这些结果表明,较高程度的底泥氧化与较强的磷固定能力相关,为黑臭水体修复过程中的磷固定提供了理论依据。

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