稻壳制成的生物炭能影响热带稀树草原土壤的 pH 值、电导率和土壤呼吸作用吗?

A. Abukari, Prince Cobbinah
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引用次数: 0

摘要

生物炭作为一种改善土壤健康、增加碳(C)储存和促进农业土壤养分循环的可持续工具,正日益受到人们的关注。本研究评估了生物炭对热带稀树草原土壤呼吸作用、pH 值和导电率(EC)的影响。研究采用了四种不同的生物炭处理方法(0、2、4 和 6 吨/公顷)。处理温度为 26°C,2、5 和 10 天后记录二氧化碳含量。培养 0、5、10 和 45 天后,评估导电率和 pH 值。随着生物炭施用量的增加,二氧化碳的进化速度也在增加。在培养的头两天,与 0 吨/公顷生物炭相比,2 吨/公顷生物炭的二氧化碳进化率上升了 129,4 吨/公顷生物炭的二氧化碳进化率上升了 146,6 吨/公顷生物炭的二氧化碳进化率上升了 168 微克二氧化碳/克土壤/天。培养五天后,与对照组相比,2 吨/公顷生物炭产生的二氧化碳进化量为 99 微克,4 吨/公顷生物炭产生的二氧化碳进化量为 116 微克,6 吨/公顷生物炭产生的二氧化碳进化量为 120 微克 CO2/g 土壤/天。培养 10 天后,二氧化碳的进化量比对照处理高的情况是:生物炭 2 吨/公顷时为 61 微克,4 吨/公顷时为 79 微克,6 吨/公顷时为 87 微克二氧化碳/克土壤/天。同样,二氧化碳排放量也呈上升趋势。在整个培养期间,生物炭处理的土壤导电率和 pH 值均高于对照处理。施用生物炭后,二氧化碳的进化量有所增加,但经过 10 天的培养后,随着生物炭用量的增加,加入生物炭后的二氧化碳进化百分比有所下降。在 2 吨/公顷、4 吨/公顷和 6 吨/公顷的条件下,生成的 C 百分比分别为施用生物炭 C 的 1.74%、1.66% 和 0.82%。虽然随着生物炭用量的增加,二氧化碳蒸发量与生物炭 C 总量的比率通常会降低,但本研究表明,添加生物炭可提高土壤呼吸作用、EC 值和 pH 值。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Can Biochar Made from Rice Husk Affect Savanna Soils’ pH, Electrical Conductivity, and Soil Respiration?
Biochar is now gaining awareness as a sustainable tool for soil health improvement, boosting carbon (C) storage and the enhancement of nutrient cycling in agricultural soils. This study assesses the effects of biochar on soil respiration, pH, and electrical conductivity (EC) in savanna soils over a 45-day incubation trail in the laboratory. Four different biochar treatments (0, 2, 4, and 6 t/ha) were used in the study. The treatments were established at 26°C, and after 2, 5, and 10 days, the CO2 levels were recorded. After incubation for 0, 5, 10, and 45 days, the EC and pH were assessed. As the rate of application of biochar increased, the rate of CO2 evolution increased as well. During the first two days of incubation, the CO2 evolution rate rose by a value of 129 at 2 t/ha biochar, 146 at 4 t/ha biochar, and 168 ug CO2/g soil/d at 6 t/ha biochar above the 0 t/ha biochar. Following five days of incubation, the amounts of CO2 evolution that were higher than the control were 99 with 2 t/ha, 116 with 4 t/ha, and 120 ug CO2/g soil/d with 6 t/ha of biochar. The increase in CO2 evolution above the control treatment at 10 days of incubation was 61 with 2 t/ha, 79 with 4 t/ha, and 87 ug CO2/g soil/d with 6 t/ha of biochar. Analogously, rising patterns in CO2 emissions were noted. Throughout the whole incubation period, the biochar treatments' soil EC and pH were greater than those of the control treatment. After applying biochar, there were increases in the evolution of CO2, however after 10 days of incubation, the percentage of C evolved from the addition of biochar decreased as the rates of biochar increased. At two t/ha, four t/ha, and six t/ha, the percentage C developed was 1.74 %, 1.66%, and 0.82% of the applied biochar C, respectively. Although the CO2 evolved ratio to the total amount of biochar C typically reduced with increasing biochar rates, this study shows that the addition of biochar increases soil respiration, EC, and pH.
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