Agronomic analysis of nitrogen performance indicators in intensive arable cropping systems: An appraisal of big data from commercial farms

Abstract Nitrogen (N) management is important for farmers to balance production, economic and environmental performance of their farms. This is particularly true in the intensive cropping systems of northwest Europe where tuber, root and bulb crops are cultivated in rotation with cereal crops and where an intensive livestock sector makes organic manures available at low cost for arable farmers. Here, we build upon a large database of farmer field data to assess mineral and organic fertiliser N performance, and its determinants, for the major arable crops in the Netherlands according to the guidelines provided by the EU N Expert Panel (EUNEP). The EUNEP framework quantifies N outputs and N inputs, N-use efficiency as the ratio between N outputs and N inputs (NUE in kg N output harvested per kg N input) and N surplus as the difference between N inputs and N outputs (Ns in kg N ha−1). As a next step, biophysical and crop management determinants of N performance were explored using data from different years, soil types and N management in relation to the amount, source, time and method of N applied. NUE was on average ca. 0.95 kg N kg−1 N for seed potato, sugar beet and spring onion, 0.87 kg N kg−1 N for ware potato, ca. 0.80 kg N kg−1 N for starch potato and winter wheat and, ca. 0.70 kg N kg−1 N for spring barley, all within or above the target range of 0.50–0.90 kg N kg−1 N proposed by the EUNEP. Ns was on average below the EUNEP threshold of 80 kg N ha−1 for all crops: 78 kg N ha−1 for ware potato and winter wheat, ca. 70 kg N ha−1 for starch potato, ca. 50 kg N ha−1 for spring barley, ca. 25 kg N ha−1 for sugar beet and spring onion and less than 20 kg N ha−1 for seed potato. Although average Ns was below 80 kg N ha−1, ca. 40% of the ware potato, starch potato and winter wheat fields analyzed had Ns above this threshold. The relatively high NUE combined with high Ns for most crops are the result of high N outputs (yields) combined with high N application rates. Moreover, high NUE and small Ns were mostly associated with smaller N application rates and with the use of mineral fertilisers instead of organic fertilisers, while there were no clear relationships between the two indicators on the one hand with N application time or method on the other. We conclude NUE and Ns were on average within the EUNEP target range for most crops, but there are still a considerable number of under-performing farms where increases in NUE and reductions in Ns are possible through reducing N inputs. We recommend future research to assess the benefits of organic fertilisers from a circularity perspective at regional and national levels and to cross-validate the crop-specific results presented in this study with NUE assessments at cropping systems level.

[1]  W.C.A. van Geel,et al.  Adviesbasis voor de bemesting van akkerbouw- en vollegrondsgroentengewassen , 1999 .

[2]  H. Berge,et al.  An evaluation of whole farm nitrogen balances and related indices for efficient nitrogen use , 2003 .

[3]  Mitchell C. Hunter,et al.  Agriculture in 2050: Recalibrating Targets for Sustainable Intensification , 2017 .

[4]  I. Bateman,et al.  Sustainable Intensification in Agriculture: Premises and Policies , 2013, Science.

[5]  Unravelling the variability and causes of smallholder maize yield gaps in Ethiopia , 2019, Food Security.

[6]  J. J. Schröder,et al.  Nutrient management regulations in The Netherlands , 2008 .

[7]  Andrea De Mauro,et al.  A formal definition of Big Data based on its essential features , 2016 .

[8]  N. Anten,et al.  Can big data explain yield variability and water productivity in intensive cropping systems? , 2020 .

[9]  J. Garnier,et al.  50 year trends in nitrogen use efficiency of world cropping systems: the relationship between yield and nitrogen input to cropland , 2014 .

[10]  Pytrik Reidsma,et al.  Data science at farm level: Explaining and predicting within-farm variability in potato growth and yield , 2021 .

[11]  H. Westhoek,et al.  Benchmarking Eco-Efficiency and Footprints of Dutch Agriculture in European Context and Implications for Policies for Climate and Environment , 2019, Front. Sustain. Food Syst..

[12]  Zbigniew Klimont,et al.  Integrated assessment of promising measures to decrease nitrogen losses from agriculture in EU-27 , 2009 .

[13]  G. Velthof,et al.  Towards an agronomic assessment of N2O emissions: a case study for arable crops , 2010 .

[14]  J. J. Schröder,et al.  The Position of Mineral Nitrogen Fertilizer in Efficient Use of Nitrogen and Land: A Review , 2014 .

[15]  E. Davidson,et al.  Managing nitrogen for sustainable development , 2015, Nature.

[16]  R. Bommarco,et al.  Ecological intensification: harnessing ecosystem services for food security. , 2013, Trends in ecology & evolution.

[17]  O. Oenema,et al.  Nitrogen use efficiency (NUE) : an indicator for the utilisation of nitrogen in agricultural and food systems , 2015 .

[18]  C. Weiser,et al.  Do farmers in Germany exploit the potential yield and nitrogen benefits from preceding oilseed rape in winter wheat cultivation? , 2018 .

[19]  L. Boumans,et al.  Nitrate in upper groundwater on farms under tillage as affected by fertilizer use, soil type and groundwater table , 2007, Nutrient Cycling in Agroecosystems.

[20]  K. Tesfaye,et al.  Wheat yield gaps across smallholder farming systems in Ethiopia , 2021 .

[21]  B. H. Janssen Crop yields and NPK use efficiency of a long-term experiment on a former sea bottom in the Netherlands , 2017 .

[22]  C. T. de Wit,et al.  Resource use efficiency in agriculture , 1992 .

[23]  A. Tiktak,et al.  Evaluation of the Dutch implementation of the nitrates directive, the water framework directive and the national emission ceilings directive , 2016 .

[24]  J. Neeteson,et al.  Assessment of economically optimum application rates of fertilizer N on the basis of response curves , 1987, Fertilizer research.

[25]  D. F. Cox,et al.  Statistical Procedures for Agricultural Research. , 1984 .

[26]  Hadley Wickham,et al.  ggplot2 - Elegant Graphics for Data Analysis (2nd Edition) , 2017 .

[27]  O. Oenema,et al.  Soil organic carbon contents of agricultural land in the Netherlands between 1984 and 2004 , 2009 .

[28]  L. S. Jensen,et al.  Exploring nitrogen indicators of farm performance among farm types across several European case studies , 2020, Agricultural Systems.

[29]  M. Rode,et al.  Balancing indicators for sustainable intensification of crop production at field and river basin levels. , 2019, The Science of the total environment.

[30]  M. Ittersum,et al.  Yield gaps in Dutch arable farming systems : Analysis at crop and crop rotation level , 2017 .