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) 09:00 〜 10:30 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:大河内 直彦(海洋研究開発機構)、岩田 智也(山梨大学生命環境学部)、角皆 潤(名古屋大学大学院環境学研究科)

09:30 〜 09:45

[MIS06-03] 塩田バイオマット内の炭素・硫黄循環が高塩海水の化学組成に与える影響

*伊左治 雄太1川幡 穂高1黒田 潤一郎2吉村 寿紘1小川 奈々子2鈴木 淳3渋谷 岳造2J. Jimenez-Espejo Francis2Lugli Stefano4Manzi Vinicio5Roveri Marco5大河内 直彦2 (1.東京大学大気海洋研究所、2.海洋研究開発機構、3.産業技術総合研究所、4.Dipartimento di Scienze Chimiche e Geologiche, Univ. degli Studi di Modena e Reggio Emilia、5.Physics and Earth Science Dept., Univ. of Parma)

キーワード:高塩環境、バイオマット、物質循環

Salinity is one of the most important environmental factors limiting the habitability of the marine organisms. As the seawater evaporates and the salinity increases, unique ecosystem is formed by specific organisms tolerable to substantial fluctuations in osmotic pressure, pH, and redox condition. In particular, microbial mat often formed in shallow hypersaline aquatic environment is known to be densely inhabited by microorganisms such as cyanobacteria, phototrophic and chemotrophic sulfur bacteria, sulfate reducing bacteria, methanogens, and others (e.g. Ollivier et al., 1994). Intensive studies have been made to reveal the biogeochemical processes of these microorganisms and their mutual interactions (e.g. Des Marais, 2003), but only few studies have focused on its effect on the chemical composition of the overlying brine water. In this study, we analyzed brine water collected from the modern saline pan in Trapani, Sicily, to understand the influence of the microbial activity on the overlying brine water with different salinity.
Major ion concentrations, DIC (dissolved inorganic carbon) concentration, and its carbon isotopic composition (δ13CDIC) were measured on 9 brine water samples with different salinity (38-276). Although intensive carbon fixation by photosynthesis occurs in the ponds where microbial mat is formed (salinity 97-159), corresponding DIC concentration showed little decrease (1250-1000 µmol L-1). This may be because mineralization of the fixed carbon by sulfate reduction occurs in the mat, releasing DIC in the brine water (e.g. Des Marais, 2003). This interpretation is supported by the low δ13CDIC value (~-10‰), because sulfate reduction supplies relatively 13C-depleted DIC. Alternative explanation is the chemically enhanced atmospheric invasion of CO2, which can cause considerable depletion in δ13CDIC (Baertschi, 1952; Lazar et al., 1992). By contrast, increase in the δ13CDIC value (~7.2‰) is observed in the ponds with higher salinity (>270) where no microbial mat is developing. This may be attributed to non-equilibrium escape of CO2 due to higher salinity and lower pH (Stiller et al., 1985; Barkan et al., 2001). These results suggest that δ13CDIC of hypersaline environment varies substantially due to both biological and physical processes.
Despite the intense sulfate reduction taking place in the mat, variation in SO42- concentration follows the ideal seawater evaporation path (Timofeeff et al., 2001). This may be because sulfide originating from the sulfate reduction is re-oxidized biotically by sulfur oxidizing bacteria or abiotically by the oxygen produced by cyanobacteria inhabiting the upper layer (e.g. Oren et al., 2009). Taken together, although DIC and SO42- are utilized intensively by the microorganisms in the mat, their content in the brine water are relatively unchanged due to efficient recycling in the mat.