Simultaneous measurements of ammonia volatilisation and deposition at a beef feedlot
M. R. Redding A C , R. Lewis A and P. R. Shorten BA 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.