日本地球惑星科学連合2019年大会

講演情報

[E] 口頭発表

セッション記号 A (大気水圏科学) » A-HW 水文・陸水・地下水学・水環境

[A-HW22] 流域の物質輸送と栄養塩循環-源流域から沿岸海域まで-

2019年5月30日(木) 09:00 〜 10:30 201B (2F)

コンビーナ:小林 政広(国立研究開発法人森林研究・整備機構 森林総合研究所)、吉川 省子(農業・食品産業技術総合研究機構 農業環境変動研究センター)、安元 純(琉球大学 農学部 地域農業工学科)、Adina Paytan(University of California Santa Cruz)、座長:Adina Paytan(University of California, Santa Cruz)

09:45 〜 10:00

[AHW22-09] ベトナム中部の野菜畑における浅層地下水のアンモニア態窒素汚染

★招待講演

*前田 守弘1藤村 拓也1Hoang Ngoc Tuong Van 2井上 大介3近森 秀高1兵藤 不二夫1 (1.岡山大学、2.フエ大学、3.大阪大学)

キーワード:アンモニア態窒素、異化型硝酸還元アンモニウム、窒素無機化

Nitrogen contamination in shallow groundwater occurs in a coastal area in Central Vietnam. In agricultural fields close to the residential area, high concentrations of NH4+ and NO3 in groundwater was attributed to unintended inflow of livestock wastes and/or domestic wastewater. On the other hand, NH4+ concentration reaches to several milligrams N per liter even in vegetable fields away from the residential area. The objective of this study was to determine NH4+ contamination mechanisms of the shallow groundwater without domestic wastewater inflow. In this study, we tested three hypotheses: (i) NH4+ derived from fertilizer or manure applied to the fields was transported to groundwater thorough soil, (ii) nitrate (NO3-) produced as a result of nitrification in topsoil was transferred to deep soil and again transformed to NH4+, or (iii) nitrogen mineralization occurred in deep soil. Soil samples were collected up to 240 cm from a vegetable production field in Quang Thang Commune, Central Vietnam in June (dry season) and November (rainy season) of 2016 and 2017. The groundwater table existed at 57 or 67 cm in June and 33 cm from the soil surface in November. Concentrations of NH4+ in PVC pipe wells fluctuated between 1 and 3 mg N L-1 in accordance with the detection of soil NH4+ content (5-20 mg kg-1) in the 150-240 cm layer. On the other hand, soil NH4+ was not detected in the 30-80 cm layer whereas it was 2-6 mg kg-1 in the 0-10 cm layers, indicating that NH4+ was not transferred to layers deeper than 30 cm. The absence of a functional gene of dissimilatory nitrate reduction to NH4+ (DNRA) in the 150-240 cm soil layer shows that DNRA did not occur in this deep layer. Natural abundance values of 15N (δ15N) for soil NH4+ (+3.6 to 5.5‰) were similar to those in soil total N (+1.9 to 3.6‰) in the 150-240 cm layer. In addition, anaerobically incubated soil from the 140-160 cm layer was mineralized by 1-2 mg NH4+-N kg-1 for 8 weeks. These experimental results suggest that the high concentration of NH4+ found in wells was originated from mineralization of deep soil.