Abstract
In this study, we measured nitrous oxide (N2O) fluxes from plots of fall-planted hairy vetch (HV, Vicia villosa) and spring-planted broadleaf vetch (BLV, Vicia narbonensis) grown as nitrogen (N) sources for following summer forage crabgrass (Digitaria sanguinalis). Comparisons also included 60 kg ha−1 inorganic N fertilizer for crabgrass at planting (60-N) and a control without N fertilizer. Each treatment had six replicated plots across the slope. Fluxes were measured with closed chamber systems during the period between spring growth of cover crops and first-cut of crabgrass in mid-July. HV had strong stand and aboveground biomass had 185 ± 50 kg N ha−1 (mean ± standard error, n = 6) at termination. However, BLV did not establish well and aboveground biomass had only 35 ± 15 kg N ha−1. Ratio vegetation index of crabgrass measured as proxy of biomass growth was highest in HV treatment. However, total aboveground biomass of crabgrass was statistically similar to 60-N plots. Fluxes of N2O were low prior to termination of cover crops but were as high as 8.2 kg N2O ha−1 day−1 from HV plots after termination. The fluxes were enhanced by large rainfall events recorded after biomass incorporation. Rainfall enhanced N2O fluxes were also observed in other treatments, but their magnitudes were much smaller. The high N2O fluxes from HV plots contributed to emissions of 30.3 ± 12.4 kg N2O ha−1 within 30 days of biomass incorporation. Emissions were only 2.0 ± 0.7, 3.4 ± 1.3 and 1.0 ± 0.4 kg N2O ha−1 from BLV, 60-N and control plots, respectively.
Similar content being viewed by others
Notes
Mention of trade names or commercial products in this publication is solely for the purpose of providing specific information and does not imply recommendation or endorsement by the U.S. Department of Agriculture.
References
Anugroho F, Kitou M, Nagumo F, Kinjo K, Tokashiki Y (2010) Growth, nitrogen fixation, and nutrient uptake of hairy vetch as a cover crop in a subtropical region. Weed Biol Manag 9:63–71
Babić KH, Schauss K, Hai B, Sikora S, Redžepović S, Radl V, Schloter M (2008) Influence of different Sinorhizobium meliloti inocula on abundance of genes involved in nitrogen transformations in the rhizosphere of alfalfa (Medicago sativa L.). Environ Microbiol 10:2922–2930
Basche AD, Miguez FE, Kaspar TC, Castellano MJ (2014) Do cover crops increase or decrease nitrous oxide emissions? A meta-analysis. J Soil Water Conserv 69:471–482
Beehler J, Fry J, Negassa W, Kravchenko A (2017) Impact of cover crop on soil carbon accrual in topographically diverse terrain. J Soil Water Conserv 72:272–279
Bergtold JS, Ramsey S, Maddy L, Williams JR (2017) A review of economic considerations for cover crops as a conservation practice. Renew Agric Food Syst. https://doi.org/10.1017/S1742170517000278
Blevins RL, Herbek JH, Frye WW (1990) Legume cover crops as a nitrogen source for no-till corn and grain sorghum. Agron J 82:769–772
Braker G, Conrad R (2011) Diversity, structure, and size of N2O-producing microbial communities in soils—what matters for their functioning? Adv Appl Microbiol 75:33–70
Bustin SA, Benes V, Garson JA, Hellemans J, Huggett J, Kubista M, Mueller R, Nolan T, Pfaffl MW, Shipley GL (2009) The MIQE guidelines: minimum information for publication of quantitative real-time PCR experiments. Clin Chem 55:611–622
Carter MS, Hauggard-Nielsen H, Heiske S, Jensen M, Thomsen ST, Schmidt JE, Johansen A, Ambus P (2012) Consequences of field N2O emissions for the environmental sustainability of plant-based biofuels produced within an organic farming system. Glob Change Biol Bioenergy 4:435–452
Cavigelli MA, Thien SJ (2003) Phosphorus bioavailability following incorporation of green manure crops. Soil Sci Soc Am J 67:1186–1194
Chen H, Mothapo NV, Shi W (2015) Fungal and bacterial N2O production regulated by soil amendments of simple and complex substrates. Soil Biol Biochem 84:116–126
Christensen S, Goudriaan J (1993) Deriving light interception and biomass from spectral reflectance ratio. Remote Sens Environ 43:87–95
Ciais P et al (2013) Carbon and other biogeochemical cycles. In: Stocker TF et al (eds) Climate change 2013: the physical science basis. Contribution of working group I to the fifth assessment report of the Intergovernmental Panel on Climate Change. Cambridge University Press, Cambridge, pp 465–570
Duan YF, Kong XW, Schramm A, Labouriau R, Eriksen J, Petersen SO (2017) Microbial N transformations and N2O emission after simulated grassland cultivation: effects of the nitrification inhibitor 3, 4-dimethylpyrazole phosphate (DMPP). Appl Environ Microbiol 83:e02019-16
Fageria NK, Baligar VC, Bailey BA (2005) Role of cover crops in improving soil and row crop productivity. Commun Soil Sci Plant Anal 36:2733–2757
Han Z, Walter MT, Drinkwater LE (2017a) N2O emissions from grain cropping systems: a meta-analysis of the impacts of fertilizer-based and ecologically-based nutrient management strategies. Nutr Cycl Agroecosyst 107:335–355
Han Z, Walter MT, Drinkwater LE (2017b) Impact of cover cropping and landscape positions on nitrous oxide emissions in northeastern US agroecosystems. Agri Ecosyst Environ 245:124–134
Harter J, Krause H-M, Schuettler S, Ruser R, Fromme M, Scholten T, Kappler A, Behrens S (2014) Linking N2O emissions from biochar-amended soil to the structure and function of the N-cycling microbial community. ISME J 8:660–674
Huang Y, Zou JW, Zheng XH, Wang YS, Xu XK (2004) Nitrous oxide emissions a influenced by amendment of plant residues with different C:N ratios. Soil Biol Biochem 36:973–981
Kandel TP, Elsgaard L, Karki S, Lærke PE (2013) Biomass yield and greenhouse gas emissions from a drained fen peatland cultivated with reed canary grass under different harvest and fertilizer regimes. BioEnergy Res 6:883–895
Kandel TP, Lærke PE, Elsgaard L (2016) Effect of chamber enclosure time on soil respiration flux: a comparison of linear and non-linear flux calculation methods. Atmos Environ 141:245–254
Kandel TP, Lærke PE, Elsgaard L (2018) Annual emissions of CO2, CH4 and N2O from a temperate peat bog: comparison of an undrained and four drained sites under permanent grass and arable crop rotations with cereals and potato. Agric For Meteorol 256:470–481
Kravchenko A, Toosi ER, Guber AK, Ostrom NO, Yu J, Azeem K, Rivers ML, Robertson GP (2017) Hotspots of soil N2O emission enhanced through water absorption by plant residue. Nature Geosci 10:496–500
Kutzbach L, Schneider J, Sachs T, Giebels M, Nykänen H, Shurpali NJ, Martikainen PJ, Alm J, Wilmking M (2007) CO2 flux determination by closed-chamber methods can be seriously biased by inappropriate application of linear regression. Biogeosciences 4:1005–1025
Lal R (2004) Soil carbon sequestration impacts on global climate change and food security. Science 304:1623–1627
Marusenko Y, Huber DP, Hall SJ (2013) Fungi mediate nitrous oxide production but not ammonia oxidation in aridland soils of the southwestern US. Soil Biol Biochem 63:24–36
Myhre G, Samset BH, Schulz M et al (2013) Radiative forcing of the direct aerosol effect from AeroCom Phase II simulations. Atmos Chem Phys 13:1853–1877
Nelson DW, Sommers LE (1996) Total carbon, organic carbon, and organic matter. In: Sparks DL et al (eds) Methods of soil analysis: part 3. Chemical methods. SSSA, Madison, pp 961–1010
Northup BK, Rao SC (2015) Green manure and forage potential of lablab in the U.S. Southern Plains. Agron J 107:1113–1118
Parton WJ, Gutmann MP, Merchant ER, Hartman MD, Adler PR, McNeal FM, Lutz SM (2015) Measuring and mitigating agricultural greenhouse gas production in the US Great Plains, 1870–2000. Proc Natl Acad Sci USA 112:E4681–E4688
Pimentel LG, Weiler DA, Pedroso GM, Bayer C (2015) Soil N2O emissions following cover-crop residues application under two soil moisture conditions. J Plant Nutr Soil Sci 178:631–640
Rao SC, Northup BK (2008) Planting date affects production and quality of grass pea forage. Crop Sci 48:1629–1635
Rao SC, Northup BK (2009) Capabilities of four novel warm-season legumes in the Southern Great Plains: biomass and forage quality. Crop Sci 49:1096–1102
Rao SC, Northup BK (2011a) Grass pea (Lathyrus sativus L.) as pre-plant nitrogen source for continuous conventionally tilled winter wheat. Crop Sci 51:1325–1333
Rao SC, Northup BK (2011b) Grass pea (Lathyrus sativus L.) as a nitrogen source for continuous no-till winter wheat. Crop Sci 51:1824–1831
Redmon LA, Hendrickson JR (2007) Forage systems for temperate subhumid and semi-arid areas. In: Barnes RF et al (eds) Forages: the science of grassland agriculture, vol II, 6th edn. Blackwell Publ, Ames, pp 291–302
Rosecrance RC, McCarty GW, Shelton DR, Teasdale JR (2000) Denitrification and N mineralization from hairy vetch (Vicia villosa Roth) and rye (Secale cereale L.) cover crop monocultures and bicultures. Plant Soil 227:283–290
Schomberg HH, Steiner JL, Unger PW (1994) Decomposition and nitrogen dynamics of crop residues: residue quality and water effects. Soil Sci Soc Am J 58:372–381
Spargo JT, Cavigelli MA, Mirsky SB, Meisinger JJ, Ackroyd VJ (2016) Organic supplemental nitrogen sources for field corn production after a hairy vetch cover crop. Agron J 108:1992–2002
Tao R, Wakelin SA, Liang Y, Hu B, Chu G (2018) Nitrous oxide emission and denitrifier communities in drip-irrigated calcareous soil as affected by chemical and organic fertilizers. Sci Total Environ 612:739–749
Tonitto C, David MB, Drinkwater LE (2006) Replacing bare fallows with cover crops in fertilizer-intensive cropping systems: a meta-analysis of crop yield and N dynamics. Agric Ecosyst Environ 112:58–72
Turner PA, Baker JM, Griffis TJ, Venterea RT (2016) The impact of kura clover living mulch on nitrous oxide emissions in a corn/soybean system. J Environ Qual 45:1782–1787
Wrage N, Velthof GL, Van Beusichem ML, Oenema O (2001) Role of nitrifier denitrification in the production of nitrous oxide. Soil Boil Biochem 33:1723–1732
Author information
Authors and Affiliations
Corresponding author
Electronic supplementary material
Below is the link to the electronic supplementary material.
Rights and permissions
About this article
Cite this article
Kandel, T.P., Gowda, P.H., Somenahally, A. et al. Nitrous oxide emissions as influenced by legume cover crops and nitrogen fertilization. Nutr Cycl Agroecosyst 112, 119–131 (2018). https://doi.org/10.1007/s10705-018-9936-4
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10705-018-9936-4