堆積物の還元容量の安定性を支配するメカニズムを解明(Study Reveals Mechanisms Governing Sediment Reducing Capacity Stability)

2026-10-08 中国科学院(CAS)

中国科学院水生生物研究所の李清曼教授らの研究チームは、湖沼・貯水池の底質における還元能(RC)の安定性を支配するメカニズムを解明した。洪湖、霞山貯水池、玉東貯水池、漳河貯水池から採取した表層底質を用い、酸化・無酸素条件を交互に切り替える54日間の培養実験を実施し、還元性有機物、二価鉄、還元型硫黄化合物の変化と鉄の化学形態を分析した。その結果、還元性有機物と還元型硫黄が優勢な底質では、酸化還元条件の変化に伴う還元能の変動が大きく、還元性有機物と鉄の相互作用が重要であることが判明した。一方、二価鉄が主要な還元成分となる底質では、反応性の高い三価鉄が電子受容体として働き、還元性物質の蓄積を抑制することで還元能が比較的安定していた。研究チームは、底質の種類に応じて、還元性有機物や硫化物の蓄積抑制、反応性三価鉄の維持など、異なる管理策を提案した。本研究は、水域底質のリスク評価と効果的な環境管理に貢献する。

堆積物の還元容量の安定性を支配するメカニズムを解明(Study Reveals Mechanisms Governing Sediment Reducing Capacity Stability)
Conceptual model of RC dynamics, component changes, and iron cycling in RedOr-Sn and RedOr-Fe(II) sediments. (Image by IHB)

<関連情報>

酸化還元反応の交互作用が堆積物の還元能力の動態を左右する:還元性有機物質の優位性と二価鉄/硫黄の相乗作用 Redox Alternation Drives Dynamics of Sediment Reducing Capacity: Dominance of Reducing Organic Substances and Ferrous-Iron/Sulfur Synergistic Mechanisms

Xuemei Chen;Ruilian Guo;Zhenjun Liu;Yang Jiao;Sen Gu;Qingman Li
Environmental Science & Technology  Published:August 10, 2026
DOI:https://doi.org/10.1021/acs.est.5c14069

Abstract

Sediment reducing capacity (RC) regulates benthic habitat function and the biogeochemical cycling of carbon, nutrients, and pollutants. However, the compositional complexity and dynamic responses of RC to redox alternation remain inadequately characterized. Through laboratory stimulation experiments of redox alternation with 20 freshwater sediments from four water bodies with distinct trophic status in China (Honghu Lake: HL, n = 3; Xiashan Reservoir: XR, n = 6; Yudong Reservoir: YR, n = 7; and Zhanghe Reservoir: ZR, n = 4), we monitored the dynamics of RC and its fractions (RCpH7.0, RCpH2.0), and quantified the responses of major reducing components (reducing organic substances (RedOr), Fe(II), and sulfides (Sn, −2 ≤ n < 0)). Redox alternation triggered asynchronous RC responses, with depletion during oxic phases and recovery under anoxia. RC fluctuation amplitude exhibited sediment-type dependence, with RedOr-Sn sediments (HL/XR) showing greater variability than RedOr-Fe(II) systems (YR/ZR). Component-specific contributions differed significantly between sediment types (p < 0.05). RedOr contributed most to RC variation in RedOr-Sn sediments (45.9–71.2% vs 35.7–52.2% in RedOr-Fe(II)), whereas Fe(II) contributed 45.8–61.5% in RedOr-Fe(II) sediments (18.9–26.6% in RedOr-Sn), and Sn accounted for 8.73–27.5% in RedOr-Sn sediments (1.62–2.62% in RedOr-Fe(II)). These differences reflected anoxia-driven differences in component reactivity and abundance. RedOr-Sn sediments exhibited concurrent enrichment of RedOr, Fe(II), and Sn, whereas RedOr-Fe(II) sediments showed mainly enhanced Fe(II) reactivity with limited RedOr/Sn changes. Mechanistically, the observed RC patterns were consistent with distinct Fe cycling pathways. In RedOr-Sn sediments, limited labile Fe(III) was associated with greater apparent involvement of magnetite, whereas easily reducible/reducible Fe(III) fractions were more prominent in RedOr-Fe(II) systems. Our findings demonstrate the high lability of eutrophic sediment RC and establish redox alternation as an efficient diagnostic tool for identifying reductive sediment types and pinpointing regulatory targets.

1102水質管理
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