Cited by 84Soil Carbon and Nitrogen DynamicsAgricultural Science and FertilizationSoil and Water Nutrient Dynamics

The DOI matches its Crossref record; 3 of the 3 references it cites were found in a registry or an index.

Nitrogen fertilisers with urease inhibitors reduce nitrous oxide and ammonia losses, while retaining yield in temperate grassland

Open access
Krol, D.J., Forrestal, P.J., Wall, D., Lanigan, G.J., Sanz-Gomez, J., Richards, K.G.·2020·Science of The Total Environment

Abstract

Nitrogen fertilisation, although a cornerstone of modern agricultural production, negatively impacts the environment through gaseous losses of nitrous oxide (N 2 O), a potent greenhouse gas (GHG), and ammonia (NH 3), a known air pollutant. The aim of this work was to assess the feasibility of urea treated with urease inhibitors to reduce gaseous N losses in temperate grassland, while maintaining or improving productivity compared to conventional fertiliser formulations. Urease inhibitors were N-(n-butyl)-thiophosphoric triamide (NBPT) (urea + NBPT) and N-(n-propyl)-thiophosphoric triamide (NPPT) (urea+ NBPT + NPPT), while conventional fertilisers were urea and calcium ammonium nitrate (CAN). N 2 O emission factors were 0.06%, 0.07%, 0.09% and 0.58% from urea + NBPT, urea, urea + NBPT + NPPT and CAN, respectively, with CAN significantly higher than all the urea formulations, which were not significantly different from each other. Ammonia loss measured over one fertiliser application was significantly larger from urea, at 43%, compared with other formulations at 13.9%, 13.8% and 5.2% from urea + NBPT, urea + NBPT + NPPT and CAN, respectively. Changing fertiliser formulation had no significant impact on grass yield or N uptake in four out of five harvests. In the last harvest urea + NBPT significantly out-yielded urea, but not CAN or urea + NBPT + NPPT. Overall, urea treated with either one or both urease inhibitors significantly reduced emissions of N 2 O and NH 3, while preserving yield quantity and quality. Therefore, changing fertiliser formulation to these products should be encouraged as a strategy to reduce GHG and air pollution from agricultural practices in temperate climate.

Overview

The claims and statistics of this paper haven’t been checked yet.

Run the check — free, no account needed. It reads the open-access text and checks the sources it cites.

A few free checks a day · papers already verified open instantly · results are public

Integrity signals

Registry

Crossref · 10.1016/j.scitotenv.2020.138329

Cites

3 of 3 references verified0 citation errors · 0 not checkable

Statistics

Verification

Claims the paper makes

The claims and statistics of this paper haven’t been checked yet.

Run the check — free, no account needed. It reads the open-access text and checks the sources it cites.

A few free checks a day · papers already verified open instantly · results are public

Self-check

Percentages, sums and reported differences re-computed from the paper’s own numbers.

The self-check needs the paper’s full text.

Citations

Cites

Research works printed but not linked: 57

  1. Abalos, 2012, Effectiveness of urease inhibition on the abatement of ammonia, nitrous oxide and nitric oxide emissions in a non-irrigated Mediterranean barley field, Chemosphere, 89, 310, 10.1016/j.chemosphere.2012.04.043 · DOI
  2. Baggs, 2011, Soil microbial sources of nitrous oxide: recent advances in knowledge, emerging challenges and future direction, Curr. Opin. Environ. Sustain., 3, 321, 10.1016/j.cosust.2011.08.011 · DOI
  3. Bell, 2015, Nitrous oxide emissions from fertilised UK arable soils: fluxes, emission factors and mitigation, Agric. Ecosyst. Environ., 212, 134, 10.1016/j.agee.2015.07.003 · DOI
  4. Bell, 2016, Quantifying N2O emissions from intensive grassland production: the role of synthetic fertilizer type, application rate, timing and nitrification inhibitors, J. Agric. Sci., 154, 812, 10.1017/S0021859615000945 · DOI
  5. Beusen, 2008, Bottom-up uncertainty estimates of global ammonia emissions from global agricultural production systems, Atmos. Environ., 42, 6067, 10.1016/j.atmosenv.2008.03.044 · DOI
  6. Black, 1985, Effects of form of nitrogen, season, and urea application rate on ammonia volatilisation from pastures, N. Z. J. Agric. Res., 28, 469, 10.1080/00288233.1985.10417992 · DOI
  7. Blackmer, 1982, Diurnal variability in rate of emission of nitrous-oxide from soils, Soil Sci. Soc. Am. J., 46, 937, 10.2136/sssaj1982.03615995004600050011x · DOI
  8. Burchill, 2014, Interannual variation in nitrous oxide emissions from perennial ryegrass/white clover grassland used for dairy production, Glob. Chang. Biol., 20, 3137, 10.1111/gcb.12595 · DOI
  9. Burchill, 2016, A system N balance for a pasture-based system of dairy production under moist maritime climatic conditions, Agric. Ecosyst. Environ., 220, 202, 10.1016/j.agee.2015.12.022 · DOI
  10. Burchill, 2017, Ammonia emissions from urine patches amended with N stabilized fertilizer formulations, Nutr. Cycl. Agroecosyst., 108, 163, 10.1007/s10705-017-9847-9 · DOI
  11. Carswell, 2019, Assessing the benefits and wider costs of different N fertilisers for grassland agriculture, Arch. Agron. Soil Sci., 65, 625, 10.1080/03650340.2018.1519251 · DOI
  12. Cowan, 2019, Nitrogen use efficiency and N2O and NH3 losses attributed to three fertiliser types applied to an intensively managed silage crop, Biogeosciences, 16, 4731, 10.5194/bg-16-4731-2019 · DOI
  13. Cowan, 2020, Nitrous oxide emission factors of mineral fertilisers in the UK and Ireland: a Bayesian analysis of 20 years of experimental data, Environ. Int., 135, 10.1016/j.envint.2019.105366 · DOI
  14. Dennis, 2012, Reducing nitrate losses from grazed grassland in Ireland using a nitrification inhibitor (DCD), Biology and the environment, 112B, 79, 10.1353/bae.2012.0032 · DOI
  15. Di, 2012, How does the application of different nitrification inhibitors affect nitrous oxide emissions and nitrate leaching from cow urine in grazed pastures, Soil Use Manag., 28, 54, 10.1111/j.1475-2743.2011.00373.x · DOI
  16. Dobbie, 2001, The effects of temperature, water-filled pore space and land use on N2O emissions from an imperfectly drained gleysol, Eur. J. Soil Sci., 52, 667, 10.1046/j.1365-2389.2001.00395.x · DOI
  17. Dobbie, 2003, Impact of different forms of N fertilizer on N2O emissions from intensive grassland, Nutr. Cycl. Agroecosyst., 67, 37, 10.1023/A:1025119512447 · DOI
  18. Engel, 2015, Degradation of the urease inhibitor NBPT as affected by soil pH, Soil Sci. Soc. Am. J., 79, 1674, 10.2136/sssaj2015.05.0169 · DOI
  19. Erisman, 2008, How a century of ammonia synthesis changed the world, Nat. Geosci., 1, 636, 10.1038/ngeo325 · DOI
  20. Forrestal, 2016, Ammonia emissions from urea, stabilized urea and calcium ammonium nitrate: insights into loss abatement in temperate grassland, Soil Use Manag., 32, 92, 10.1111/sum.12232 · DOI
  21. Forrestal, 2017, Can the agronomic performance of urea equal calcium ammonium nitrate across nitrogen rates in temperate grassland?, Soil Use Manag., 33, 243, 10.1111/sum.12341 · DOI
  22. Galloway, 2004, Nitrogen cycles: past, present, and future, Biogeochemistry, 70, 153, 10.1007/s10533-004-0370-0 · DOI · Paper page
  23. Harty, 2016, Reducing nitrous oxide emissions by changing N fertiliser use from calcium ammonium nitrate (CAN) to urea based formulations, Sci. Total Environ., 563–564, 576, 10.1016/j.scitotenv.2016.04.120 · DOI
  24. Harty, 2017, Temperate grassland yields and nitrogen uptake are influenced by fertilizer nitrogen source, Agron. J., 109, 71, 10.2134/agronj2016.06.0362 · DOI
  25. Herlihy, 1979, Nitrogen mineralisation in soils of varying texture, moisture and organic matter, Plant Soil, 53, 255, 10.1007/BF02277860 · DOI
  26. Hoekstra, 2020, Scenarios to limit environmental nitrogen losses from dairy expansion, Sci. Total Environ., 707, 10.1016/j.scitotenv.2019.134606 · DOI
  27. Hyde, 2016, The interactive effects of fertiliser nitrogen with dung and urine on nitrous oxide emissions in grassland, Irish Journal of Agriculture and Food Research, 55, 1, 10.1515/ijafr-2016-0001 · DOI
  28. Kim, 2013, Background nitrous oxide emissions in agricultural and natural lands: a meta-analysis, Plant Soil, 373, 17, 10.1007/s11104-013-1762-5 · DOI
  29. Kira, 2019, Direct tracing of NH3 and N2O emissions associated with urea fertilization approaches, using static incubation cells, Sci. Total Environ., 661, 75, 10.1016/j.scitotenv.2019.01.128 · DOI
  30. Leuning, 1985, A sampler for measuring atmospheric ammonia flux, Atmos. Environ. (1967), 19, 1117, 10.1016/0004-6981(85)90196-9 · DOI
  31. Levy, 2011, Quantification of uncertainty in trace gas fluxes measured by the static chamber method, Eur. J. Soil Sci., 62, 811, 10.1111/j.1365-2389.2011.01403.x · DOI
  32. Li, 2015, Effect of a new urease inhibitor on ammonia volatilization and nitrogen utilization in wheat in north and northwest China, Field Crop Res., 175, 96, 10.1016/j.fcr.2015.02.005 · DOI
  33. Lockyer, 1984, A system for the measurement in the field of losses of ammonia through volatilisation, J. Sci. Food Agric., 35, 837, 10.1002/jsfa.2740350805 · DOI
  34. Maljanen, 2007, Fluxes of nitrous oxide and nitric oxide from experimental excreta patches in boreal agricultural soil, Soil Biol. Biochem., 39, 914, 10.1016/j.soilbio.2006.11.001 · DOI
  35. McDonald, 2014, Soil tests for predicting nitrogen supply for grassland under controlled environmental conditions, J. Agric. Sci., 152, 82, 10.1017/S0021859614000264 · DOI
  36. Meisinger, 2001, Construction and validation of small mobile wind tunnels for studying ammonia volatilization, Appl. Eng. Agric., 17, 375, 10.13031/2013.6212 · DOI
  37. Minet, 2018, Feeding dicyandiamide (DCD) to cattle: an effective method to reduce N2O emissions from urine patches in a heavy-textured soil under temperate climatic conditions, Sci. Total Environ., 615, 1319, 10.1016/j.scitotenv.2017.09.313 · DOI
  38. O’Neill, 2020, The effect of carbon availability on N2O emissions is moderated by soil phosphorus, Soil Biol. Biochem., 142, 107726, 10.1016/j.soilbio.2020.107726 · DOI
  39. Ravishankara, 2009, Nitrous oxide (N2O): the dominant ozone-depleting substance emitted in the 21st century, Science, 326, 123, 10.1126/science.1176985 · DOI
  40. Roche, 2016, Impact of fertiliser nitrogen formulation, and N stabilisers on nitrous oxide emissions in spring barley, Agriculture Ecosystems and the Environment, 233, 229, 10.1016/j.agee.2016.08.031 · DOI
  41. Russenes, 2016, Spatial variation in soil pH controls off-season N2O emission in an agricultural soil, Soil Biol. Biochem., 99, 36, 10.1016/j.soilbio.2016.04.019 · DOI
  42. Ryden, 1985, Evaluation of a system of wind tunnels for field studies of ammonia loss from grassland through volatilisation, J. Sci. Food Agric., 36, 781, 10.1002/jsfa.2740360904 · DOI
  43. Selbie, 2015, Confirmation of co-denitrification in grazed grassland, Sci. Rep., 5, 10.1038/srep17361 · DOI
  44. Smith, 1997, Free ammonia inhibition of nitrification in river sediments leading to nitrite accumulation, J. Environ. Qual., 26, 1049, 10.2134/jeq1997.00472425002600040016x · DOI
  45. Smith, 2012, The effect of N fertilizer forms on nitrous oxide emissions from UK arable land and grassland, Nutr. Cycl. Agroecosyst., 93, 127, 10.1007/s10705-012-9505-1 · DOI
  46. Stevens, 1998, Soil pH affects the processes reducing nitrate to nitrous oxide and di-nitrogen, Soil Biol. Biochem., 30, 1119, 10.1016/S0038-0717(97)00227-7 · DOI
  47. Sunderlage, 2018, Soil property and fertilizer additive effects on ammonia volatilization from urea, Soil Sci. Soc. Am. J., 82, 253, 10.2136/sssaj2017.05.0151 · DOI
  48. Sutton, 1992, Deposition of atmospheric ammonia to moorlands, Environ. Pollut., 75, 15, 10.1016/0269-7491(92)90051-B · DOI
  49. Sutton, M. A., C. M. Howard, J. W. Erisman, G. Billen, A. Bleeker, P. Grennfelt, H. Van Grinsven and B. Grizzetti, 2011. European Nitrogen Assessment, Cambridge University Press. · DOI
  50. Tian, 2015, Application effects of coated urea and urease and nitrification inhibitors on ammonia and greenhouse gas emissions from a subtropical cotton field of the Mississippi delta region, Sci. Total Environ., 533, 329, 10.1016/j.scitotenv.2015.06.147 · DOI
  51. Timilsena, 2015, Enhanced efficiency fertilisers: a review of formulation and nutrient release patterns, J. Sci. Food Agric., 95, 1131, 10.1002/jsfa.6812 · DOI
  52. Wang, 2018, Soil pH as the chief modifier for regional nitrous oxideemissions: new evidence and implications for globalestimates and mitigation, Glob. Chang. Biol., 24, 617, 10.1111/gcb.13966 · DOI
  53. Watson, 1996, Short-term effects of urea amended with the urease inhibitor N-(n-butyl) thiophosphoric triamide on perennial ryegrass, Plant and Soil, 184, 33, 10.1007/BF00029272 · DOI
  54. Watson, 1990, Effectiveness of the urease inhibitor NBPT (N-(n-butyl) thiophosphoric triamide) for improving the efficiency of urea for ryegrass production, Fertilizer Research, 24, 11, 10.1007/BF01073142 · DOI
  55. Watson, 2008, Rate and mode of application of the urease inhibitor N-(n-butyl) thiophosphoric triamide on ammonia volatilization from surface-applied urea, Soil Use Manag., 24, 246, 10.1111/j.1475-2743.2008.00157.x · DOI
  56. Watson, 2009, Modification of nitrogen fertilisers using inhibitors: opportunities and potentials for improving nitrogen use efficiency, Proceedings 658 of The International Fertiliser Society, 1–40
  57. Zaman, 2008, Reducing NH3, N2O and NO3–N losses from a pasture soil with urease or nitrification inhibitors and elemental S-amended nitrogenous fertilisers, Biol. Fertil. Soils, 44, 693, 10.1007/s00374-007-0252-4 · DOI

Metadata

Authors
Krol, D. J., Forrestal, P. J., Wall, D., Lanigan, G. J., Sanz-Gomez, J., & Richards, K. G.
Affiliations
  • Teagasc - The Irish Agriculture and Food Development Authority (IE)
  • BASF (Germany) (DE)
Venue
Science of The Total Environment
Publisher
Elsevier BV
Published
2020-07
Volume
725
Pages
138329
ISSN
0048-9697 (ISSN-L)
OpenAlex
W3014091779
Cited by
84
References
3
Citations by year
2026: 9 · 2025: 14 · 2024: 21 · 2023: 14 · 2022: 9 · 2021: 17
FWCI
6.63
Type
journal article
Language
en
Open access
Locations
  • The Science of The Total Environment (publishedVersion)
  • PubMed (publishedVersion)
  • Arrow@dit (Dublin Institute of Technology) (acceptedVersion)
  • T-Stór (Teagasc) (submittedVersion, cc-by-nc-sa)
Funders
  • BASF
  • Irish Research Council (EPSPD/2016/54)
Topics
  • Life Sciences › Agricultural and Biological Sciences › Soil Science › Soil Carbon and Nitrogen Dynamics
  • Life Sciences › Agricultural and Biological Sciences › Soil Science › Agricultural Science and Fertilization
  • Physical Sciences › Environmental Science › Environmental Chemistry › Soil and Water Nutrient Dynamics
Keywords
urease inhibitors, nitrous oxide emissions, ammonia volatilization, nitrogen fertiliser, temperate grassland, NBPT, urea, calcium ammonium nitrate, greenhouse gas emissions, air pollution, grass yield, nitrogen uptake

About these checks

Registry, retraction, Cites and statistics results are computed, not judged, with one exception: a printed reference that no index lists is read once by a model before it counts as a citation error. Claims are extracted by a model and kept only when their quote appears verbatim in the text; each cited source is then checked, with a model’s help, for whether it says what the claim relies on. Those verdicts can be wrong — read the claim’s quote and the cited source before relying on one.

Statistics and arithmetic are recomputed, not judged.

Confidence bands are shown only for fields calibrated on our annotated test set. None is calibrated yet, so no band is shown.

What counts as a claim ›How we measure confidence ›How we check this ›

Are you an author, or do you see a problem with this page? Request a review