Free Standard AU & NZ Shipping For All Book Orders Over $80!
Register      Login
Animal Production Science Animal Production Science Society
Food, fibre and pharmaceuticals from animals
RESEARCH ARTICLE

Simultaneous measurements of ammonia volatilisation and deposition at a beef feedlot

M. R. Redding A C , R. Lewis A and P. R. Shorten B
+ Author Affiliations
- Author Affiliations

A AgriScience Queensland, Department of Agriculture and Fisheries, PO Box 102, Toowoomba, Qld 4350, Australia.

B AgResearch Limited, Ruakura Research Centre, Private Bag 3123, Hamilton 3214, New Zealand.

C Corresponding author. Email: matthew.redding@daf.qld.gov.au

Animal Production Science 59(1) 160-168 https://doi.org/10.1071/AN17310
Submitted: 12 May 2017  Accepted: 24 August 2017   Published: 7 December 2017

Abstract

The nitrogen (N) excreted at intensive livestock operations is vulnerable to volatilisation, and, subsequently, may form a source of indirect nitrous oxide (N2O) emissions. The present study simultaneously investigated volatilisation and deposition of N at a beef feedlot, semi-continuously over a 129-day period. These data were examined relative to pen manure parameters, management statistics and emission-inventory calculation protocols. Volatilisation measurements were conducted using a single, heated air-sampling inlet, centrally located in a feedlot pen area, with real time concentration analysis via cavity ring-down spectroscopy and backward Lagrangian stochastic (bLS) modelling. Net deposited mineral-N was determined via two transects of soil-deposition traps, with samples collected and re-deployed every 2 weeks. Total volatilised ammonia amounted to 210 tonnes of NH3-N (127 g/animal.day), suggesting that the inventory volatilisation factor probably underestimated volatilisation in this case (inventory, 30% of excreted N; 65 g N volatilised/animal.day; a value of ~60% of excreted N is indicated). Temperature contrast between the manure and air was observed to play a significant role in the rate of emission (R2 = 0.38; 0.46 Kendall’s tau; P < 0.05). Net deposition within 600 m of the pen boundary represented only 1.7% to 3% of volatilised NH4+-N, between 3.6 and 6.7 tonnes N. Beyond this distance, deposition approached background rates (~0.4 kg N/ha.year).

Additional keywords: manure, micrometeorology.


References

Asman WAH (1998) Factors influencing local dry deposition of gases with special reference to ammonia. Atmospheric Environment 32, 415–421.
Factors influencing local dry deposition of gases with special reference to ammonia.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK1cXhvVOisbk%3D&md5=6dcc3b9acba9f3819913b4581f220af3CAS |

Bai M, Flesch TK, McGinn SM, Chen D (2015) A snapshot of greenhouse gas emissions from a cattle feedlot. Journal of Environmental Quality 44, 1974–1978.
A snapshot of greenhouse gas emissions from a cattle feedlot.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC28XktlOrsLs%3D&md5=b9b83d7af00404327572aeebbf33e136CAS |

Berendse F, Laurijsen C, Okkerman P (1988) The acidifying effect of ammonia volatilized from farm-manure on forest soils. Ecological Bulletins 39, 136–138.
The acidifying effect of ammonia volatilized from farm-manure on forest soils.Crossref | GoogleScholarGoogle Scholar |

Crenna BP, Flesch TK, Wilson JD (2008) ‘Windtrax 2.0.8.1.’ (Thunder Beach Scientific: Alberta, Canada) Available at www.thunderbeachscientific.com [Verified October 2017]

Denmead OT, Chen D, Griffith DWT, Loh ZM, Bai M, Naylor T (2008) Emissions of the indirect greenhouse gases NH3 and NOx from Australian beef cattle feedlots. Australian Journal of Experimental Agriculture 48, 213–218.
Emissions of the indirect greenhouse gases NH3 and NOx from Australian beef cattle feedlots.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1cXovV2l&md5=1c303e4f6a4efc574a2660e3c2680e7eCAS |

Department of Environment (2014) National inventory report 2012. Available at http://www.environment.gov.au/climate-change/greenhouse-gas-measurement/publications/national-inventory-report-2012 [Verified October 2017]

Eghball B, Power JF (1994) Beef-cattle feedlot manure management. Journal of Soil and Water Conservation 49, 113–122.

Flesch TK, Wilson JD (2005) Estimating trace emissions with a backward Lagrangian stochastic technique. In ‘Micrometeorology in agricultural systems’. (Eds MK Viney, JL Hatfield, JM Baker) pp. 513–531. (American Society of Agronomy, Inc.: Madison, WI)

Flesch TK, Wilson JD, Harper LA, Crenna BP (2005) Estimating gas emissions from a farm with an inverse-dispersion technique. Atmospheric Environment 39, 4863–4874.
Estimating gas emissions from a farm with an inverse-dispersion technique.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2MXntlSns78%3D&md5=daf8231766faf47f6beb46efe08cecf1CAS |

Flesch TK, Wilson JD, Harper LA, Todd RW, Cole NA (2007) Determining ammonia emissions from a cattle feedlot with an inverse dispersion technique. Agricultural and Forest Meteorology 144, 139–155.
Determining ammonia emissions from a cattle feedlot with an inverse dispersion technique.Crossref | GoogleScholarGoogle Scholar |

Fowler D, Pitcairn C, Sutton M, Flechard C, Loubet B, Coyle M, Munro R (1998) The mass budget of atmospheric ammonia in woodland within 1 km of livestock buildings. Environmental Pollution 102, 343–348.
The mass budget of atmospheric ammonia in woodland within 1 km of livestock buildings.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK1MXjvVegsg%3D%3D&md5=c1eef929a76fec5e7cda98b41c0ad902CAS |

Hacker JM, Chen D, Bai M, Ewenz C, Junkermann W, Lieff W, McManus B, Neininger B, Sun J, Coates T, Denmead T, Flesch T, McGinn S, Hill J (2016) Using airborne technology to quantify and apportion emissions of CH4 and NH3 from feedlots. Animal Production Science 56, 190–203.
Using airborne technology to quantify and apportion emissions of CH4 and NH3 from feedlots.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC28Xis1amt7k%3D&md5=8b3b5bd81d31066e25d599c0660d3d95CAS |

Hunt R (1982) ‘Plant growth curves: the functional approach to plant growth analysis.’ (Arnold: London)

Intergovernmental Panel on Climate Change (2006) ‘IPCC: task force on national greenhouse gas inventories.’ Available at http://www.ipcc-nggip.iges.or.jp/public/2006gl/vol4.html [Verified October 2017]

Isbell RF (2002) ‘The Australian soil classification.’ (CSIRO Publishing: Melbourne)

Koenig KM, McGinn SM, Beauchemin KA (2013) Ammonia emissions and performance of backgrounding and finishing beef feedlot cattle fed barley-based diets varying in dietary crude protein concentration and rumen degradability. Journal of Animal Science 91, 2278–2294.
Ammonia emissions and performance of backgrounding and finishing beef feedlot cattle fed barley-based diets varying in dietary crude protein concentration and rumen degradability.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3sXotl2gtb0%3D&md5=b0dc4e2743df3b767e3cc459391747b0CAS |

Krupa SV (2003) Effects of atmospheric ammonia (NH3) on terrestrial vegetation: a review. Environmental Pollution 124, 179–221.
Effects of atmospheric ammonia (NH3) on terrestrial vegetation: a review.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3sXjtFWls7o%3D&md5=9255527b173e6463395a64142d7ae072CAS |

Loh Z, Chen D, Bai M, Naylor T, Griffith D, Hill J, Denmead T, McGinn S, Edis R (2008) Measurement of greenhouse gas emissions from Australian feedlot beef production using open-path spectroscopy and atmospheric dispersion modelling. Australian Journal of Experimental Agriculture 48, 244–247.
Measurement of greenhouse gas emissions from Australian feedlot beef production using open-path spectroscopy and atmospheric dispersion modelling.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1cXovVOl&md5=52ed7d9f8023963e14b358aa6f547c2eCAS |

McGinn SM, Janzen HH, Coates T (2003) Atmospheric ammonia, volatile fatty acids, and other odorants near beef feedlots. Journal of Environmental Quality 32, 1173–1182.
Atmospheric ammonia, volatile fatty acids, and other odorants near beef feedlots.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3sXlslGjtbo%3D&md5=4a3732d41bfd741a5227942566a20b91CAS |

McGinn SM, Flesch TK, Crenna BP, Beauchernin KA, Coates T (2007) Quantifying ammonia emissions from a cattle feedlot using a dispersion model. Journal of Environmental Quality 36, 1585–1590.
Quantifying ammonia emissions from a cattle feedlot using a dispersion model.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2sXhtlKqtLrL&md5=0f135aa0b3a8ef02f92314d09b4987c0CAS |

McGinn SM, Janzen HH, Coates TW, Beauchemin KA, Flesch TK (2016) Ammonia emission from a beef cattle feedlot and its local dry deposition and re-emission. Journal of Environmental Quality 45, 1178–1185.
Ammonia emission from a beef cattle feedlot and its local dry deposition and re-emission.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC2sXhs1Oqsrk%3D&md5=bb78b1f82cd130d31fd4835f3f7f7919CAS |

Mosier AR, Andre CE, Viets FG (1973) Identification of aliphatic amines volatilized from cattle feedyard. Environmental Science & Technology 7, 642–644.
Identification of aliphatic amines volatilized from cattle feedyard.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaE3sXksFOgu78%3D&md5=ad8e8bca7349e9ace2dc69aa62ec810cCAS |

National Research Council (2002) ‘The scientific basis for estimating air emissions from animal feeding operations.’ (National Academy Press: Washington, DC)

R Development Core Team (2014) ‘R: a language and environment for statistical computing.’ (R Foundation for Statistical Computing: Vienna) Available at http://www.R-project.org [Verified October 2017]

Rayment GE, Lyons DJ (2011) ‘Soil chemical methods: Australasia.’ (CSIRO Publishing: Melbourne)

Redding MR, Devereux J, Phillips F, Lewis R, Naylor T, Kearton T, Hill CJ, Weidemann S (2015) Field measurement of beef pen manure methane and nitrous oxide reveals a surprise for inventory calculations. Journal of Environmental Quality 44, 720–728.
Field measurement of beef pen manure methane and nitrous oxide reveals a surprise for inventory calculations.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC2MXns1Wgsbk%3D&md5=27133f2a115e424107782cdc9f2c9354CAS |

Redding MR, Shorten PR, Lewis R, Pratt C, Paungfoo-Lonhienne C, Hill J (2016) Soil N availability, rather than N deposition, controls indirect N2O emissions. Soil Biology & Biochemistry 95, 288–298.
Soil N availability, rather than N deposition, controls indirect N2O emissions.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC28XhtVejur4%3D&md5=f8d730b0d1afb76ab0d5a71768e48e2eCAS |

Shen J, Chen D, Bai M, Sun J, Coates T, Lam SK, Li Y (2016) Ammonia deposition in the neighbourhood of an intensive cattle feedlot in Victoria, Australia. Scientific Reports 6, 32793
Ammonia deposition in the neighbourhood of an intensive cattle feedlot in Victoria, Australia.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC28XhsV2jsbzO&md5=a911e86a5d2fcf37960c8d7b54dbf807CAS |

Soil Survey Staff (1998) ‘Keys to soil taxonomy.’ (United Sates Department of Agriculture, Natural Resource Conservation Service: Washington, DC)

Sommer SG, Olesen JE (2000) Modelling ammonia volatilization from animal slurry applied with trail hoses to cereals. Atmospheric Environment 34, 2361–2372.
Modelling ammonia volatilization from animal slurry applied with trail hoses to cereals.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3cXivFSgt7w%3D&md5=c15f6e8542504152e10d412932f79015CAS |

Sommer SG, Génermont S, Cellier P, Hutchings NJ, Olesen JE, Morvan T (2003) Processes controlling ammonia emission from livestock slurry in the field. European Journal of Agronomy 19, 465–486.
Processes controlling ammonia emission from livestock slurry in the field.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3sXlsVamt7Y%3D&md5=0c90297d142f457cdad7e8ba9c35dd7eCAS |

Staebler RM, McGinn SM, Crenna BP, Flesch TK, Hayden KL, Li S (2009) Three-dimensional characterization of the ammonia plume from a beef cattle feedlot. Atmospheric Environment 43, 6091–6099.
Three-dimensional characterization of the ammonia plume from a beef cattle feedlot.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1MXhtlOrt7nE&md5=84e0617578d92deb10f4a73202301b13CAS |

Todd RW, Cole NA, Clark RN, Flesch TK, Harper LA, Baek BH (2008a) Ammonia emissions from a beef cattle feedyard on the southern high plains. Atmospheric Environment 42, 6797–6805.
Ammonia emissions from a beef cattle feedyard on the southern high plains.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1cXhtFSqsbjM&md5=b187079c8cb40eac854b616ee6f7f17aCAS |

Todd RW, Cole NA, Clark RN, Rice WC, Guo WX (2008b) Soil nitrogen distribution and deposition on shortgrass prairie adjacent to a beef cattle feedyard. Biology and Fertility of Soils 44, 1099–1102.
Soil nitrogen distribution and deposition on shortgrass prairie adjacent to a beef cattle feedyard.Crossref | GoogleScholarGoogle Scholar |

Todd RW, Cole NA, Rhoades MB, Parker DB, Casey KD (2011) Daily, monthly, seasonal, and annual ammonia emissions from southern high plains cattle feedyards. Journal of Environmental Quality 40, 1090–1095.
Daily, monthly, seasonal, and annual ammonia emissions from southern high plains cattle feedyards.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3MXptFKitLY%3D&md5=6040bbba5ee8e94ccce2a8a792da7e98CAS |

Waldrip HM, Todd RW, Li C, Cole NA, Salas WH (2013) Estimation of ammonia emissions from beef cattle feedyards using the process-based model Manure-DNDC. Transactions of the ASABE 56, 1103–1114.