Fertilizer type influences tomato yield and soil N2O emissions  

https://doi.org/10.17221/678/2016-PSECitation:Vitale L., Polimeno F., Ottaiano L., Maglione G., Tedeschi A., Mori M., De Marco A., Di Tommasi P., Magliulo V. (2017): Fertilizer type influences tomato yield and soil N2O emissions  . Plant Soil Environ., 63: 105-110.
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Improvements in crop management for a more sustainable agriculture are fundamental to reduce environmental impacts of cropland and to mitigate effects on global climate change. In this study three fertilization types – ammonium nitrate (control); mineral fertilizer added with a nitrification inhibitor (3,4-dimethylpyrazole phosphate (DMPP)), and an organo-mineral fertilizer (OM) – were tested on a tomato crop in order to evaluate effects both on crop production and soil N2O emissions. Plants grown under OM fertilization had a greater relative growth rate compared to mineral fertilization, due to a higher net assimilation rate, which was related to a greater light interception rather than to a higher photosynthetic efficiency. OM fertilization determined the highest fruit production and lower soil N2O fluxes compared to NH4NO3, although the lowest soil N2O fluxes were found in response to mineral fertilizer added with a nitrification inhibitor. It can be concluded that organo-mineral fertilizer is a better nutrient source compared to mineral fertilizers able to improve crop yield and to mitigate soil N2O emission.  
References:
Ball B.C., Ball B.C., McTaggart I.P., Scott A. (2004): Mitigation of greenhouse gas emissions from soil under silage production by use of organic manures or slow-release fertilizer. Soil Use and Management, 20, 287-295  https://doi.org/10.1079/SUM2004257
 
BARTH G., VON TUCHER S., SCHMIDHALTER U. (2008): Effectiveness of 3,4-Dimethylpyrazole Phosphate as Nitriflcation Inhibitor in Soil as Influenced by Inhibitor Concentration, Application Form, and Soil Matric Potential. Pedosphere, 18, 378-385  https://doi.org/10.1016/S1002-0160(08)60028-4
 
Bell M.J., Hinton N., Cloy J.M., Topp C.F.E., Rees R.M., Cardenas L., Scott T., Webster C., Ashton R.W., Whitmore A.P., Williams J.R., Balshaw H., Paine F., Goulding K.W.T., Chadwick D.R. (2015): Nitrous oxide emissions from fertilised UK arable soils: Fluxes, emission factors and mitigation. Agriculture, Ecosystems & Environment, 212, 134-147  https://doi.org/10.1016/j.agee.2015.07.003
 
Kaiser Ernst-August, Ruser Reiner (2000): Nitrous oxide emissions from arable soils in Germany — An evaluation of six long-term field experiments. Journal of Plant Nutrition and Soil Science, 163, 249-259  https://doi.org/10.1002/1522-2624(200006)163:3<249::AID-JPLN249>3.0.CO;2-Z
 
Huang T., Gao B., Hu X.-X., Lu X., Well R., Christie P., Bakken L.R., Ju X.-Y. (2014): Ammonia-oxidation as an engine to generate nitrous oxide in an intensively managed calcareous Fluvo-aquic soil. Scientific Report, 4: 39–50.
 
Yao Z., Wei Y., Liu C., Zheng X., Xie B. (2015): Organically fertilized tea plantation stimulates N<sub>2</sub>O emissions and lowers NO fluxes in subtropical China. Biogeosciences, 12, 5915-5928  https://doi.org/10.5194/bg-12-5915-2015
 
IPCC (2007): Climate Change 2007: Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge, New York, Cambridge University Press.
 
Poorter Hendrik, Remkes Carlo (1990): Leaf area ratio and net assimilation rate of 24 wild species differing in relative growth rate. Oecologia, 83, 553-559  https://doi.org/10.1007/BF00317209
 
Radford P. J. (1967): Growth Analysis Formulae - Their Use and Abuse1. Crop Science, 7, 171-  https://doi.org/10.2135/cropsci1967.0011183X000700030001x
 
Ranucci Silvia, Bertolini Teresa, Vitale Luca, Tommasi Paul, Ottaiano Lucia, Oliva Marco, Amato Umberto, Fierro Angelo, Magliulo Vincenzo (2011): The influence of management and environmental variables on soil N2O emissions in a crop system in Southern Italy. Plant and Soil, 343, 83-96  https://doi.org/10.1007/s11104-010-0674-x
 
Rees Robert M., Baddeley John A., Bhogal Anne, Ball Bruce C., Chadwick David R., Macleod Michael, Lilly Allan, Pappa Valentini A., Thorman Rachel E., Watson Christine A., Williams John R. (2013): Nitrous oxide mitigation in UK agriculture. Soil Science and Plant Nutrition, 59, 3-15  https://doi.org/10.1080/00380768.2012.733869
 
Snyder CS, Davidson EA, Smith P, Venterea RT (2014): Agriculture: sustainable crop and animal production to help mitigate nitrous oxide emissions. Current Opinion in Environmental Sustainability, 9-10, 46-54  https://doi.org/10.1016/j.cosust.2014.07.005
 
Stolk P. C., Jacobs C. M. J., Moors E. J., Hensen A., Velthof G. L., Kabat P. (2009): Significant non-linearity in nitrous oxide chamber data and its effect on calculated annual emissions. Biogeosciences Discussions, 6, 115-141  https://doi.org/10.5194/bgd-6-115-2009
 
Vitale L., Ottaiano L., Polimeno F., Maglione G., Amato U., Arena C., Di Tommasi P., Mori M., Magliulo V. (2013): Effects of 3,4-dimethylphyrazole phosphate-added nitrogen fertilizers on crop growth and N2O emissions in Southern Italy. Plant, Soil and Environment, 59: 517–523.
 
Zerulla Wolfram, Barth Thomas, Dressel J&#x000FC;rgen, Erhardt Klaus, Horchler von Locquenghien Klaus, Pasda Gregor, R&#x000E4;dle Matthias, Wissemeier Alexander (2001): 3,4-Dimethylpyrazole phosphate (DMPP) - a new nitrification inhibitor for agriculture and horticulture. Biology and Fertility of Soils, 34, 79-84  https://doi.org/10.1007/s003740100380
 
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