日本地球惑星科学連合2016年大会

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セッション記号 M (領域外・複数領域) » M-IS ジョイント

[M-IS06] 生物地球化学

2016年5月22日(日) 13:45 〜 15:15 A03 (アパホテル&リゾート 東京ベイ幕張)

コンビーナ:*楊 宗興(東京農工大学)、柴田 英昭(北海道大学北方生物圏フィールド科学センター)、大河内 直彦(海洋研究開発機構)、山下 洋平(北海道大学 大学院地球環境科学研究院)、座長:稲垣 善之(森林総合研究所)、藤井 一至(森林総合研究所)、和穎 朗太(農業環境技術研究所 物質循環研究領域)、仁科 一哉(国立環境研究所)

14:15 〜 14:30

[MIS06-15] 異なる階層レベルにある有機物・鉱物の相互作用を理解することはできるのか?火山灰土壌(黒ボク土)を使ったケーススタディー

*和穎 朗太1浅野 眞希2梶浦 雅子1 (1.農業環境技術研究所 物質循環研究領域、2.筑波大学 生命環境系)

キーワード:土壌炭素、微細構造、有機物・鉱物の相互作用

Organic matter (OM) in soil is subject to both microbial transformation and interaction with soil minerals, during which soil aggregates are formed at the spatial scales of nano to mili meters. Due to the variations in mineral and OM compositions as well as the nature of the interaction between the two, organo-mineral particles or aggregates have a range of size and density. Physical fractionation is an effective approach to study organo-mineral interaction and the factors controlling the storage and turnover of soil OM. However, it remains unclear how the findings from fractionation studies are related to the concept of aggregate hierarchy (e.g., larger aggregates are maintained by transient binding agents while smaller ones are held together by more persistent binders). Here we present three studies that use the fractionation approach to examine how short- and long-term soil OM dynamics are linked to the hierarchy concept using Japanese volcanic-ash soils that is known for strong aggregation and OM stabilization capacity.
First, we demonstrated that the isolation of low-density fraction, a readily accessible OM outside of aggregates, was necessary to examine the factors controlling decomposition temperature sensitivity. Second, using sequential density fractionation, we isolated soil aggregates that are resistant to mechanical shaking and showed density-dependent changes in the chemistry of OM (d13C, d 15N, d14C as well as C:N ratio) and that of mineral phases (organically complexed metals and short-range-ordered minerals). Third, we found the particle size dependent changes in organo-mineral chemistry in the same soil only after achieving maximum dispersion of these aggregates by sodium saturation followed by sonication. Clay-sized particles after the dispersion, however, still showed aggregated features by SEM and TEM. We will discuss possible factors controlling OM stabilization in these fractions and the presumed relationship between the fractions obtained from different levels of aggregate hierarchy (sonication-resistant particles vs. shaking-resistant aggregates).