Effect of antecedent soil moisture conditions on emissions and isotopologue distribution of N2O during denitrification

被引:78
作者
Bergstermann, Anja [2 ]
Cardenas, Laura [1 ]
Bol, Roland [1 ]
Gilliam, Lucy [3 ]
Goulding, Keith [3 ]
Meijide, Ana [4 ,5 ]
Scholefield, David [1 ]
Vallejo, Antonio [4 ]
Well, Reinhard [6 ]
机构
[1] Rothamsted Res, Okehampton EX20 2SB, Devon, England
[2] Univ Gottingen, Inst Soil Sci & Forest Nutr, D-37077 Gottingen, Germany
[3] Rothamsted Res, Harpenden AL5 2JQ, Herts, England
[4] Univ Politecn Madrid, Dpto Quim & Anal Agr, ETSI Agron, E-28040 Madrid, Spain
[5] European Commiss DG Joint Res Ctr, Inst Environm & Sustainabil, Climate Change Unit, I-21027 Ispra, VA, Italy
[6] Johann Heinrich von Thunen Inst, Fed Res Inst Rural Areas Forestry & Fisheries, Inst Agr Climate Res, D-38116 Braunschweig, Germany
基金
英国生物技术与生命科学研究理事会;
关键词
Denitrification; Isotopomer signature; Fractionation factors; Nitrous oxide; Antecedent moisture conditions; Climate change; Nitrogen; Modelling; NITROUS-OXIDE PRODUCTION; ISOTOPIC COMPOSITION; DUAL-ISOTOPE; INCUBATION TECHNIQUE; NORTH PACIFIC; FRESH-WATER; NITRIFICATION; FRACTIONATION; NITRATE; REDUCTION;
D O I
10.1016/j.soilbio.2010.10.003
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
The present study determined the influence of initial moisture conditions on the production and consumption of nitrous oxide (N2O) during denitrification and on the isotopic fingerprint of soil-emitted N2O. Sieved arable soil was pre-incubated at two different moisture contents: pre-wet at 75% and pre-dry at 20% water-filled pore space. After wetting to 90% water-filled pore space the soils were amended with glucose (400 kg C ha(-1)) and KNO3 (80 kg N ha(-1)) and incubated for 10 days under a He/O-2-atmosphere. Antecedent moisture conditions affected denitrification. N-2 + N2O fluxes and the N2O-to-N-2 ratio were higher in soils which were pre-incubated under dry conditions, probably because mobilization of organic C during the pre-treatment enhanced denitrification. Gaseous N fluxes showed similar time patterns of production and reduction of N2O in both treatments, where N2O fluxes were initially increasing and maximised 3-4 days after fertilizer application, and N2 fluxes were delayed by 1-2 days. Time courses of delta N-15(bulk)-N2O and delta O-18-N2O exhibited in both treatments increasing trends until maximum N-2 fluxes occurred, reflecting isotope fractionation during intense NO3- reduction. Later this trend slowed down in the pre-dry treatment, while delta O-18-N2O was constant and delta N-15(bulk)-N2O decreased in the pre-wet treatment. We explain these time patterns by non-homogenous distribution of NO3- and denitrification activity, resulting from application of NO3- and glucose to the surface of the soil. We assume that several process zones were thus created, which affected differently the isotopic signature of N2O and the N2O and N-2 fluxes during the different stages of the process. We modelled the delta N-15(bulk)-N2O using process rates and associated fractionation factors for the pre-treated soils, which confirmed our hypothesis. The site preference (SP) initially decreased while N2O reduction was absent, which we could not explain by the N-flux pattern. During the subsequent increase in N-2 flux, SP and delta O-18-N2O increased concurrently, confirming that this isotope pattern is indicative for N2O reduction to N-2. The possible effect of the antecedent moisture conditions of the soil on N2O emissions was shown to be important. (C) 2010 Elsevier Ltd. All rights reserved.
引用
收藏
页码:240 / 250
页数:11
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