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气态氮和细菌对土壤中未处理和消化的奶制品应用的反应。

Gaseous nitrogen and bacterial responses to raw and digested dairy manure applications in incubated soil.

机构信息

Department of Crop and Soil Science, Washington State University, Pullman, Washington 99164-6420, USA.

出版信息

Environ Sci Technol. 2012 Nov 6;46(21):11684-92. doi: 10.1021/es301754s. Epub 2012 Oct 22.

Abstract

A study was conducted under laboratory conditions to compare rates of nitrous oxide (N(2)O) and ammonia (NH(3)) emissions when soil was amended with anaerobically digested dairy manure slurry containing <30% food byproducts, raw dairy manure slurry, or urea. Slurries were applied via surface and subsurface methods. A second objective was to correlate genes regulating nitrification and denitrification with rates of N(2)O production, slurry treatment, and application method. Ammonia volatilization from incubated soil ranged from 140 g kg(-1) of total N applied in digested slurry to 230 g kg(-1) in urea. Subsurface application of raw dairy manure slurry decreased ammonia volatilization compared with surface application. Anaerobic digestion increased N(2)O production. Cumulative N(2)O loss averaged 27 g kg(-1) of total N applied for digested slurry, compared with 5 g kg(-1) for raw dairy slurry. Genes of interest included a 16S rRNA gene selective for β-subgroup proteobacterial ammonia-oxidizers, amoA, narG, and nosZ quantified with quantitative polymerase chain reaction (qPCR) and real-time polymerase chain reaction (RT-PCR). Application of anaerobically digested slurry increased nitrifier and denitrifier gene copies that correlated with N(2)O production. Expression of all genes measured via mRNA levels was affected by N applications to soil. This study provides new information linking genetic markers in denitrifier and nitrifier populations to N(2)O production.

摘要

一项在实验室条件下进行的研究比较了在添加含有<30%食物副产品、生牛奶粪浆或尿素的厌氧消化牛奶粪浆的土壤中,一氧化二氮(N(2)O)和氨(NH(3))排放速率。粪浆通过表面和地下方法施用。第二个目标是将调节硝化和反硝化的基因与 N(2)O 产生、泥浆处理和应用方法的速率相关联。在培养土壤中氨挥发范围从消化泥浆中总氮的 140 g kg(-1)到尿素中的 230 g kg(-1)。与表面应用相比,生牛奶粪浆的地下应用降低了氨挥发。厌氧消化增加了 N(2)O 的产生。消化泥浆中总氮的累积 N(2)O 损失平均为 27 g kg(-1),而生牛奶浆为 5 g kg(-1)。感兴趣的基因包括 16S rRNA 基因,该基因选择性地针对β亚群的变形菌氨氧化菌、amoA、narG 和 nosZ,通过定量聚合酶链反应(qPCR)和实时聚合酶链反应(RT-PCR)进行定量。厌氧消化泥浆的施用增加了硝化和反硝化基因拷贝数,与 N(2)O 的产生相关。通过 mRNA 水平测量的所有基因的表达都受到土壤中 N 应用的影响。这项研究提供了新的信息,将遗传标记与硝化和反硝化种群与 N(2)O 的产生联系起来。

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