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快速土壤复湿促进了尿素添加下有限的一氧化二氮排放和抑制了氨挥发。

Rapid soil rewetting promotes limited NO emissions and suppresses NH volatilization under urea addition.

机构信息

Microelement Research Center, Huazhong Agricultural University, Wuhan, 430070, China; State Environmental Protection Key Laboratory of Soil Health and Green Remediation, Ministry of Ecological Environment, Wuhan, 430070, China; Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtze River), Ministry of Agriculture and Rural Affairs, Wuhan, 430070, China.

Microelement Research Center, Huazhong Agricultural University, Wuhan, 430070, China; State Environmental Protection Key Laboratory of Soil Health and Green Remediation, Ministry of Ecological Environment, Wuhan, 430070, China; Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtze River), Ministry of Agriculture and Rural Affairs, Wuhan, 430070, China.

出版信息

Environ Res. 2022 Sep;212(Pt C):113402. doi: 10.1016/j.envres.2022.113402. Epub 2022 May 5.

Abstract

The alternation of dry and wet is an important environmental factor affecting the emission of nitrous oxide from soil. However, the consistent or opposite effects on NH and NO emissions caused by adding exogenous urea in this process have not been fully considered. Here, we controlled the initial (slow drying) and final (adding water) water-filled pore space (WFPS) at 70%, 60%, or 50% through microculture experiment to simulate a process of slow drying-fertilization and rapid wetting of the soil from rice harvest to dryland crop fertilization. Through measuring soil chemical properties and the abundance and composition of related microbial communities during drying process, we studied the pathways of influence of drying and rewetting on the emission of NO and NH after urea application. During the progressive drying process (WFPS decreasing from 70% to 60% and 50%), soil NO and NH emissions decreased by 49.77%-72.13% and 17.89%-42.19%, respectively. After rapid rewetting (WFPS increasing from 60% to 70%, 50%-60% and 70%), NO emissions showed a slight increase, while NH volatilization continued to decrease. Soil NH-N and DOC contents both decreased during progressive drying, while the soil NO-N content was enhanced. The drying process changed the community structure of ureC and amoA-b and reduced their abundance but had no effect on amoA-a, nirK or nirS. Correlation analysis indicated that the reductions in NH-N content and the abundances of ureC and amoA-b were the main factors suppressing NO and NH emissions. We believe that drying process limits the related microbial activity and substrate supply during ammonia oxidation process in terms of NO emissions, while in terms of NH volatilization, it reduces the related microbial activity of urea hydrolysis process and increases the ammonium adsorption to the soil.

摘要

干湿交替是影响土壤一氧化二氮排放的重要环境因素。然而,在此过程中外加外源尿素对 NH 和 NO 排放的一致或相反影响尚未得到充分考虑。在这里,我们通过微培养实验控制初始(缓慢干燥)和最终(加水)水填充孔隙空间(WFPS)分别为 70%、60%或 50%,以模拟从水稻收获到旱地作物施肥期间土壤缓慢干燥-施肥和快速润湿的过程。通过测量干燥过程中土壤化学性质以及相关微生物群落的丰度和组成,我们研究了干燥和再润湿对施加尿素后 NO 和 NH 排放的影响途径。在逐渐干燥过程中(WFPS 从 70%降至 60%和 50%),土壤 NO 和 NH 排放分别减少了 49.77%-72.13%和 17.89%-42.19%。快速再润湿后(WFPS 从 60%增加到 70%、50%-60%和 70%),NO 排放略有增加,而 NH 挥发继续减少。土壤 NH-N 和 DOC 含量在逐渐干燥过程中均下降,而土壤 NO-N 含量增加。干燥过程改变了 ureC 和 amoA-b 的群落结构,降低了它们的丰度,但对 amoA-a、nirK 或 nirS 没有影响。相关分析表明,NH-N 含量的降低和 ureC 和 amoA-b 的丰度降低是抑制 NO 和 NH 排放的主要因素。我们认为,干燥过程限制了氨氧化过程中相关微生物的活性和底物供应,从而导致 NO 排放减少,而在 NH 挥发方面,它降低了尿素水解过程中相关微生物的活性,并增加了土壤对铵的吸附。

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