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人为景观下土壤活性氮氧化物通量的时空变化。

Spatiotemporal Variations of Soil Reactive Nitrogen Oxide Fluxes across the Anthropogenic Landscape.

机构信息

School of Life Sciences, University of Warwick, Coventry CV4 7AL, United Kingdom.

出版信息

Environ Sci Technol. 2023 Oct 31;57(43):16348-16360. doi: 10.1021/acs.est.3c05849. Epub 2023 Oct 19.

Abstract

Volatile reactive nitrogen oxides (NO) are significant atmospheric pollutants, including NO (nitric oxide [NO] + nitrogen dioxide [NO]) and NO (nitrous acid [HONO] + nitric acid [HNO] + nitrogen trioxide [NO] + ...). NO species are products of nitrogen (N) cycle processes, particularly nitrification and denitrification. Biogenic sources, including soil, account for over 50% of natural NO emissions to the atmosphere, yet emissions from soils are generally not included in atmospheric models as a result of a lack of mechanistic data. This work is a unique investigation of NO fluxes on a landscape scale, taking a comprehensive set of land-use types, human influence, and seasonality into account to determine large-scale heterogeneity to provide a basis for future modeling and hypothesis generation. By coupling 16S rRNA amplicon sequencing and quantitative polymerase chain reaction, we have linked significant differences in functional potential and activity of nitrifying and denitrifying soil microbes to NO emissions from soils. Further, we have identified soils subject to increased N deposition that are less microbially active despite increased available N, potentially as a result of poor soil health from anthropogenic pollution. Structural equation modeling suggests human influence on soils to be a more significant effector of soil NO emissions than land-use type.

摘要

挥发性反应性氮氧化物(NO)是重要的大气污染物,包括 NO(一氧化氮[NO] + 二氧化氮[NO])和 NO(亚硝酸[HONO] + 硝酸[HNO] + 三氧化氮[NO] +...)。NO 物种是氮(N)循环过程的产物,特别是硝化和反硝化作用。生物源,包括土壤,占大气中自然 NO 排放的 50%以上,但由于缺乏机制数据,土壤排放通常不包括在大气模型中。这项工作是对景观尺度上 NO 通量的独特研究,考虑了一套综合的土地利用类型、人为影响和季节性,以确定大规模异质性,为未来的建模和假设生成提供基础。通过耦合 16S rRNA 扩增子测序和定量聚合酶链反应,我们将硝化和反硝化土壤微生物的功能潜力和活性的显著差异与土壤中的 NO 排放联系起来。此外,我们已经确定了受到增加的 N 沉积影响的土壤,尽管有更多的可用 N,但微生物活性较低,这可能是由于人为污染导致土壤健康状况较差。结构方程模型表明,人类对土壤的影响是土壤 NO 排放的更重要的效应因子,而不是土地利用类型。

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