日本地球惑星科学連合2022年大会

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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-GE30] 地質媒体における流体移動、物質移行 及び環境評価

2022年5月24日(火) 10:45 〜 12:15 展示場特設会場 (2) (幕張メッセ国際展示場)

コンビーナ:小島 悠揮(岐阜大学工学部)、コンビーナ:濱本 昌一郎(東京大学大学院農学生命科学研究科)、斎藤 広隆(東京農工大学大学院農学研究院)、コンビーナ:加藤 千尋(弘前大学農学生命科学部)、座長:小島 悠揮(岐阜大学工学部)、濱本 昌一郎(東京大学大学院農学生命科学研究科)、斎藤 広隆(東京農工大学大学院農学研究院)、加藤 千尋(弘前大学農学生命科学部)


11:45 〜 12:00

[AGE30-05] Seasonal variations in soil CO2 concentrations and fluxes at two different soybean fields

*杉浦 有香1濱本 昌一郎1、二瓶 直登2、平 敏伸3、平山 孝3、松波 寿弥4、市橋 泰範5西村 拓1 (1.東京大学大学院農学生命科学研究科、2.福島大学 食農学類、3.福島県農業総合センター、4.農研機構 東北農業研究センター、5.理化学研究所バイオリソース研究センター)


キーワード:ガス環境、土壌呼吸、モニタリング

Agricultural field is one of the important sources of greenhouse gas emissions. It is known that CO2 emissions from soils are influenced by environmental factors such as soil moisture, soil temperature, and organic matter content. These factors are variable with different soil types, therefore it is essential to understand the relationship between soil type and soil CO2 dynamics. Previous studies have also shown that continuous monitoring is required to accurately understand the effects of soil moisture on CO2 gas emissions. In this study, we aimed to clarify the effect of soil types on CO2 dynamics in soybean fields. Measurements were conducted in two different soybean fields; volcanic ash soil and lowland soil located in Fukushima City and Koriyama City in Japan, respectively. Each field consisted of three treatments: unplanted (NC), cow manure (CM), and chemical fertilizer (CF). O2and CO2 concentrations were monitored at two depths (10 cm, 25 cm) at one-hour intervals during the soybean growing season from June to October in 2021. At both sites, volumetric water content, soil temperature, electrical conductivity, and water potential at four depths (2 cm, 10 cm, 18 cm, and 25 cm) were measured at 30-minute or 1-hour intervals. Basic physical properties, gas diffusion coefficient, air permeability, and water retention curves were measured using undisturbed samples collected at four depths (5 cm, 10 cm, 18 cm, and 25 cm). The measured CO2 concentrations and gas diffusion coefficients were used to calculate the CO2 fluxes at depths of 0-10 cm and 10-25 cm. The rate of CO2 production was evaluated by subtracting CO2 flux at 10-25 cm depth from the one at 0-10 cm depth.
The difference in time-series variations of CO2 concentration among soils was small at 10 cm depth, while CO2 concentration at 25 cm depth was higher in lowland soil than in volcanic ash soil. This was because of the smaller air-filled porosity (i.e., lower gas diffusion coefficient) in the lowland soil than in volcanic ash soil. For the CM plot, the rate of CO2 production was higher in the volcanic ash soil. Because during the monitoring periods, volcanic ash soil showed higher air-filled porosity than lowland soil, especially at 0-10 cm depth, larger oxygen supply from the atmosphere to soil enhanced soil respiration in the volcanic ash soil. Relations between CO2 flux at 0-10 cm depth and volumetric water content showed an optimum volumetric water content that maximized CO2 flux in each field. The optimum water content ranged from 0.5 to 0.6 as water saturation, regardless of the soil type and treatment.