日本地球惑星科学連合2015年大会

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インターナショナルセッション(口頭発表)

セッション記号 A (大気水圏科学) » A-GE 地質環境・土壌環境

[A-GE04] Subsurface Mass Transport and Environmental Assessment

2015年5月24日(日) 11:00 〜 12:45 301A (3F)

コンビーナ:*森 也寸志(岡山大学大学院環境生命科学研究科)、斎藤 広隆(東京農工大学大学院農学研究院)、川本 健(埼玉大学大学院理工学研究科)、濱本 昌一郎(東京大学大学院農学生命科学研究科)、張 銘(産業技術総合研究所地圏資源環境研究部門)、座長:斎藤 広隆(東京農工大学大学院農学研究院)、濱本 昌一郎(東京大学大学院農学生命科学研究科)

11:45 〜 12:00

[AGE04-07] Interactive effects of EC and pH on nitrous oxide emissions and denitrification

*Thi kim thanh HA1Morihiro MAEDA1 (1.Graduate School of Environmental and Life Science, Okayama University)

キーワード:Denitrification, EC, nitrous oxide, paddy soil, pH

Long-term fertilizer applications and saline water irrigation lead to the accumulation of salts and changes in soil pH. These changes may in turn affect N2O emissions from soil. Interactive effects of EC and pH on N2O emissions were studied by using paddy soil in Ushimado, Okayama Prefecture, Japan. Closed incubation experiments were conducted in 100-mL glass bottles for 72 h at 25oC. Each bottle contained 5 g of air-dried soil and 25 mL of solution, which includes KNO3 (10 mg NO3-N L-1) and NaCl (0 M, 0.005 M, 0.01 M, 0.05 M, 0.1 M, 0.2 M) for adjusting different electric conductivity (EC) levels under different pH: acid (HCl 0.005 M), neutral (no adjustment), and alkaline (NaHCO3 0.005 M). Nitrous oxide concentration in the headspace of the bottle was measured 3 h, 24 h, 48 h, and 72 h after incubation with gas chromatograph (GC-8A, Shimadzu, Kyoto, Japan). After gas collection, the solution was taken out for measuring pH, EC and concentrations of NH4+ and NO3-. Results indicated that pH was a significant factor controlling N2O emissions (P < 0.05). Nitrous oxide emissions were greater in higher EC treatments under the acid treatment. Nitrous oxide emissions peaked at 24 h of incubation and fell sharply afterwards due to further dentrification process. At 24 h, the highest N2O emissions was measured in 0.2 M NaCl (7.5 mg kg soil-1), followed by in 0.1 M, 0.05 M, 0.01 M, 0.005 M and 0 M treatments, which were 6.7, 5.1, 3.8, 2.0, and 1.2 mg N kg soil-1, respectively. Nitrous oxide reductase was sensitive to both high EC and low pH condition. In neutral and alkaline treatments, there was no significant effect of EC on N2O emissions during 72 h incubation (P > 0.05). The N2O emissions were 0 mg kg soil-1 at 3 h after incubation then ranged from 0.02 to 0.11 mg N kg soil-1. Ammonium concentration increased over the incubation periods. Higher EC promote NH4+ release. There was no significant difference in NO3- removal among treatments at different EC levels (P > 0.05). We conclude that low pH increased N2O emissions and higher EC under acid conditions promoted N2O emissions.