Estimation of isotope variation of N2O during denitrification by Pseudomonas aureofaciens and Pseudomonas chlororaphis: implications for N2O source apportionment

被引:17
作者
Haslun, Joshua A. [1 ,3 ]
Ostrom, Nathaniel E. [2 ,3 ]
Hegg, Eric L. [1 ,3 ]
Ostrom, Peggy H. [2 ,3 ]
机构
[1] Michigan State Univ, Biochem & Mol Biol, E Lansing, MI 48824 USA
[2] Michigan State Univ, Integrat Biol, E Lansing, MI 48824 USA
[3] Michigan State Univ, Great Lakes Bioenergy Res Ctr, E Lansing, MI 48824 USA
基金
美国国家科学基金会;
关键词
NITROUS-OXIDE PRODUCTION; ISOTOPOLOGUE FRACTIONATION; NITROSOMONAS-EUROPAEA; NONLINEAR RESPONSE; SITE PREFERENCE; FERTILIZER; REDUCTION; NITRIFICATION; AGRICULTURE; CHALLENGES;
D O I
10.5194/bg-15-3873-2018
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
Soil microbial processes, stimulated by agricultural fertilization, account for 90% of anthropogenic nitrous oxide (N2O), the leading source of ozone depletion and a potent greenhouse gas. Efforts to reduce N2O flux commonly focus on reducing fertilization rates. Management of microbial processes responsible for N2O production may also be used to reduce N2O emissions, but this requires knowledge of the prevailing process. To this end, stable isotopes of N2O have been applied to differentiate N2O produced by nitrification and denitrification. To better understand the factors contributing to isotopic variation during denitrification, we characterized the delta N-15, delta O-18 and site preference (SP; the intramolecular distribution of N-15 in N2O) of N2O produced during NO3- reduction by Pseudomonas chlororaphis subsp. aureofaciens and P. c. subsp. chlororaphis. The terminal product of denitrification for these two species is N2O because they lack the gene nitrous oxide reductase, which is responsible for the reduction of N2O to N-2. In addition to species, treatments included electron donor (citrate and succinate) and electron donor concentration (0.01, 0.1, 1 and 10mM) as factors. In contrast to the expectation of a Rayleigh model, all treatments exhibited curvilinear behaviour between delta N-15 or O-delta 18 and the extent of the reaction. The curvilinear behaviour indicates that the fractionation factor changed over the course of the reaction, something that is not unexpected for a multi-step process such as denitrification. Using the derivative of the equation, we estimated that the net isotope effects (eta) vary by as much as 100% over the course of a single reaction, presenting challenges for using delta N-15 and delta O-18 as apportionment tools. contrast, SP for denitrification was not affected by the extent of the reaction, the electron donor source or concentration, although the mean SP of N2O produced by each species differed. Therefore, SP remains a robust indicator of the origin of N2O. To improve apportionment estimates with SP, future studies could evaluate other factors that contribute to the variation in SP.
引用
收藏
页码:3873 / 3882
页数:10
相关论文
共 50 条
[31]   Nitrifier denitrification can be a source of N2O from soil: a revised approach to the dual-isotope labelling method [J].
Kool, D. M. ;
Wrage, N. ;
Zechmeister-Boltenstern, S. ;
Pfeffer, M. ;
Brus, D. ;
Oenema, O. ;
Van Groenigen, J-W .
EUROPEAN JOURNAL OF SOIL SCIENCE, 2010, 61 (05) :759-772
[32]   Fertilizers, agronomy and N2O [J].
Oluf Chr. Bøckman ;
Hans-Werner Olfs .
Nutrient Cycling in Agroecosystems, 1998, 52 :165-170
[33]   Fertilizers, agronomy and N2O [J].
Bockman, OC ;
Olfs, HW .
NUTRIENT CYCLING IN AGROECOSYSTEMS, 1998, 52 (2-3) :165-170
[34]   Is site preference of N2O a tool to identify benthic denitrifier N2O? [J].
Mothet, Aurelie ;
Sebilo, Mathieu ;
Laverman, Anniet M. ;
Vaury, Veronique ;
Mariotti, Andre .
ENVIRONMENTAL CHEMISTRY, 2013, 10 (04) :281-284
[35]   Mechanism of biochar on nitrification and denitrification to N2O emissions based on isotope characteristic values [J].
Tang, Zhanming ;
Liu, Xingren ;
Li, Guichun ;
Liu, Xiaowan .
ENVIRONMENTAL RESEARCH, 2022, 212
[36]   Isotopologue data reveal bacterial denitrification as the primary source of N2O during a high flux event following cultivation of a native temperate grassland [J].
Ostrom, Nathaniel E. ;
Sutka, Robin ;
Ostrom, Peggy H. ;
Grandy, A. Stuart ;
Huizinga, Kristin M. ;
Gandhi, Hasand ;
von Fischer, Joseph C. ;
Robertson, G. Philip .
SOIL BIOLOGY & BIOCHEMISTRY, 2010, 42 (03) :499-506
[37]   Evidence for denitrification as main source of N2O emission from residue-amended soil [J].
Li, Xiaoxi ;
Sorensen, Peter ;
Olesen, Jorgen E. ;
Petersen, Soren O. .
SOIL BIOLOGY & BIOCHEMISTRY, 2016, 92 :153-160
[38]   Seasonally distinct sources of N2O in acid organic soil drained for agriculture as revealed by N2O isotopomer analysis [J].
Petersen, Soren O. ;
Well, Reinhard ;
Taghizadeh-Toosi, Arezoo ;
Clough, Tim J. .
BIOGEOCHEMISTRY, 2020, 147 (01) :15-33
[39]   N2O Emissions from Two Austrian Agricultural Catchments Simulated with an N2O Submodule Developed for the SWAT Model [J].
Wang, Cong ;
Schuerz, Christoph ;
Zoboli, Ottavia ;
Zessner, Matthias ;
Schulz, Karsten ;
Watzinger, Andrea ;
Bodner, Gernot ;
Mehdi-Schulz, Bano .
ATMOSPHERE, 2022, 13 (01)
[40]   Influences of carbon sources on N2O production during denitrification in freshwaters: Activity, isotopes and functional microbes [J].
Li, Shengjie ;
Wang, Shuo ;
Ji, Guodong .
WATER RESEARCH, 2022, 226