Elsevier

Agricultural and Forest Meteorology

Volume 232, 15 January 2017, Pages 349-358
Agricultural and Forest Meteorology

Measurements of methane emissions from a beef cattle feedlot using the eddy covariance technique

https://doi.org/10.1016/j.agrformet.2016.09.001Get rights and content

Highlights

  • Close-path and open-path gas analyzers were compared.

  • The analyzers’ CO2 fluxes showed good agreement.

  • Methane and CO2 flux magnitudes were variable during the study.

  • A footprint analysis was helpful to explain the flux variability.

Abstract

The eddy covariance (EC) technique has been extensively used in several sites around the world to measure energy fluxes and CO2 exchange at the ecosystem scale. Recent advances in optical sensors have allowed the use of the EC approach to measure other trace gases (e.g. CH4, NH3 and N2O), which has expanded the use of eddy covariance for other applications, including measuring gas emissions from livestock production systems. The main objectives of this study were to assess the performance of a closed-path EC system for measuring CH4, CO2, and H2O fluxes in a beef cattle feedlot and to investigate the spatial variability of eddy covariance fluxes measured above the surface of a feedlot using an analytical flux footprint analysis. A closed-path EC system was used to measure CH4, CO2, and H2O fluxes. To evaluate the performance of this closed-path system, an open-path EC system was also deployed on the flux tower to measure CO2 and H2O exchange. The performance assessment of the closed-path EC system showed that this system was suitable for EC measurements. The frequency attenuations, observed for the closed-path system CO2 and CH4 cospectra in this study, are in agreement with results from previous instrument comparison studies. For the water vapor closed-path cospectra, larger attenuations were likely caused by water vapor molecule interaction with the sampling tube walls. Values of R2 for the relationship between H2O and CO2 fluxes, measured by open-path and closed-path systems, were 0.94–0.98, respectively. The closed-path EC system overestimated the CO2 by approximately 5% and underestimated the latent heat fluxes by about 10% when compared with the open-path system measurements. Measured CH4 and CO2 fluxes during the study period from the feedlot averaged 2.63 μmol m−2 s−1 and 103.8 μmol m−2 s−1, respectively. Flux values were quite variable during the field experiment and the footprint analysis was useful to interpret flux temporal and spatial variation. This study shows indication that consideration of atmospheric stability condition, wind direction and animal movement are important to improve estimates of CH4 emissions per pen surface or per head of cattle.

Introduction

Methane (CH4) is an important greenhouse gas (GHG) with a global warming potential 28 times greater than CO2 over a 100-year period (IPCC, 2014). Methane, originating from microbial fermentation in the digestive system of ruminants (enteric fermentation) and manure management, accounts for approximately 30% of the total anthropogenic CH4 emissions in the United States (USEPA, 2015). Accurate measurements of CH4 from animal production systems are crucial for reducing uncertainties in national GHG inventories and evaluating mitigation strategies to reduce GHG emissions from agriculture.

Chamber and tracer techniques are often used to measure emissions from livestock. These techniques are useful in comparison studies aiming to evaluate the effect of different diets and mitigation strategies to minimize GHG emissions (Makkar and Vercoe, 2007). However, chambers and tracer techniques are intrusive. They can alter typical animal behavior, management conditions, and gas emission rates. In addition, their application is constrained to a limited number of animals increasing measurement uncertainties (Harper et al., 2011).

Micrometeorological approaches have also been used to estimate GHG emissions from livestock production systems and offer some advantages compared to chamber and tracer techniques (Bai et al., 2015, Baum et al., 2008, Flesch et al., 2007, Laubach, 2010, Laubach et al., 2013). For instance, micrometeorological methods are non-intrusive and integrate flux measurements from larger areas and from a larger number of animals in their natural environment, reducing uncertainties in the fluxes caused by small sample sizes and changes in animal behavior (Harper et al., 2011, McGinn, 2013).

The eddy covariance (EC) technique is considered the most direct micrometeorological method to measure gas exchanges between the land and the atmosphere (Baldocchi, 2003, Dabberdt et al., 1993). EC requires fast response sensors (typically 10–20 Hz sampling rate) to capture fluxes measured by small turbulent eddies. Recent advances in optical sensors have allowed the development of fast response sensors capable of measuring other trace gases, such as CH4, nitrous oxide (N2O), and ammonia (NH3), at a rate suitable for EC measurements (Detto et al., 2011, McDermitt et al., 2011, Peltola et al., 2013, Sun et al., 2015). The EC approach has been used to measure gas exchange from different surfaces, including: agricultural sites (Abraha et al., 2015, Baker and Griffis, 2005), urban plots (Feigenwinter et al., 2012, Velasco et al., 2005), landfills (McDermitt et al., 2013), and bodies of water (Nordbo et al., 2011, Norris et al., 2012). Recent studies have also applied the EC technique to estimate CH4 emissions from grazing animals (Dengel et al., 2011, Felber et al., 2015).

The EC technique has been applied to measure gas exchange from beef cattle feedlots and the atmosphere (Baum et al., 2008, Sun et al., 2015). Whole farm emission measurements can be useful to improve current modeling approach uncertainties (Crosson et al., 2011). One of the basic assumptions of the EC technique is that measurements are taken above an extensive and homogeneous source area. In feedlots, fluxes measured using the EC approach integrate contributions from different surfaces, such as: pens, roads and alleys, which will influence the flux magnitudes (Baum et al., 2008). Flux footprint analyzes have been used to interpret flux variation in animal production systems and to investigate how changes in the underlying source surface affect flux measurements (Baum et al., 2008, Dengel et al., 2011, Sun et al., 2015). Baum et al. (2008) applied the eddy covariance technique to measure carbon dioxide (CO2) and water vapor fluxes from a commercial beef cattle feedlot in Kansas. They utilized an analytical footprint model to determine the contributions of non-pen surfaces to the EC flux. They found alleys and roads contribute to 2 and 10% of the total flux, respectively. They also reported that the effect of these surfaces on the fluxes varied depending on the wind direction. More recently, Sun et al. (2015) used the EC approach to measure NH3 fluxes in a beef cattle feedlot in Colorado. They were able to identify in their two-week measurement that the diel variation in the NH3 flux was also influenced by the flux footprint.

Most of the CH4 emission measurements from ruminants using micrometeorological techniques are restricted to short field campaigns ranging from a few days to weeks. Long-term studies are necessary to investigate how changes in environmental conditions affect GHG fluxes from livestock production systems and to reduce the uncertainties of current GHG inventories and emission factors. In addition, long-term studies could bring new insights into the factors affecting the performance of micrometeorological techniques. In this study, we evaluate the performance of a closed-path EC system to measure CH4 and CO2 emissions from a commercial beef cattle feedlot during an 8-month period. Few studies have applied the EC technique to quantify gas emissions from a beef cattle feedlot (Baum et al., 2008, Sun et al., 2015) and to our knowledge, this is the first study to utilize the EC technique to estimate long-term CH4 emissions from a confined animal feeding operation. The main objectives of this study were (i) to assess the performance of a closed-path EC system for measuring CH4, CO2, and water vapor (H2O) fluxes in a beef cattle feedlot against a well-established open-path gas analyzer, and (ii) to investigate the spatial variability of EC fluxes measured above the surface of a beef cattle feedlot using an analytical flux footprint analysis.

Section snippets

Site description

The field experiment was carried out in a commercial beef cattle feedlot in western Kansas from August 2013 to May 2014. This feedlot has a near rectangular shape with a total pen surface of approximately 59 ha surrounded by agricultural fields. The feedlot has the capacity to hold 60,000 head of cattle and was near full capacity (∼58,000) during the experiment. The experimental site is on a near flat terrain (slope <5%) and located in one of the windiest regions of the United States (National

Flux data quality control and atmospheric conditions

During the experimental period, power outages and instrument malfunction resulted in the loss of 5% of the 30-min data. Approximately, 4% of open-path system data were excluded due to the accumulation of dust particles and water on the open-path analyzer windows. Regular cleaning of the open-path system window may have limited the data gap.

The remaining half-hourly flux data were screened using the quality control protocol developed by Foken et al. (2004) to test for the development of

Conclusions

The performance assessment of the closed-path EC system showed that this system was suitable for EC measurements. The frequency attenuations, observed for the close-path system CO2 and CH4 cospectra in this study, are in agreement with results from previous studies. For the water vapor closed-path cospectra, larger attenuations were most likely caused by water vapor molecule interaction with the tubing walls. Values of R2 for the relationship between H2O and CO2 fluxes, measured by open-path

Acknowledgments

We would like to thank our collaborators in the feedlot industry for their assistance with this project and Kansas State University for funding this research project (contribution number 16-284-J from the Kansas Agricultural Experiment Station). We also appreciate the help of Kyle Stropes and Fred Caldwell with the field experiment. We are grateful to the two anonymous reviewers for their contributions to improve this manuscript.

References (48)

  • M. Abraha

    Evapotranspiration of annual and perennial biofuel crops in a variable climate

    GCB Bioenergy

    (2015)
  • M. Aubinet et al.

    Eddy Covariance: a Practical Guide to Measurement and Data Analysis

    (2012)
  • M. Bai et al.

    A snapshot of greenhouse gas emissions from a cattle feedlot

    J. Environ. Qual.

    (2015)
  • J. Baker et al.

    Examining strategies to improve the carbon balance of corn/soybean agriculture using eddy covariance and mass balance techniques

    Agric. For. Meteorol.

    (2005)
  • D. Baldocchi

    The challenges of measuring methane fluxes and concentrations over a peatland pasture

    Agric. For. Meteorol.

    (2012)
  • D.D. Baldocchi

    Assessing the eddy covariance technique for evaluating carbon dioxide exchange rates of ecosystems: past, present and future

    Global Change Biol.

    (2003)
  • K.A. Baum et al.

    Surface boundary layer of cattle feedlots: implications for air emissions measurement

    Agric. For. Meteorol.

    (2008)
  • G. Burba

    Calculating CO2 and H2O eddy covariance fluxes from an enclosed gas analyzer using an instantaneous mixing ratio

    Global Change Biol.

    (2012)
  • H. Chen

    High-accuracy continuous airborne measurements of greenhouse gases (CO2 and CH4) using the cavity ring-down spectroscopy (CRDS) technique

    Atmos. Meas. Tech.

    (2010)
  • P. Crosson

    A review of whole farm systems models of greenhouse gas emissions from beef and dairy cattle production systems

    Anim. Feed Sci. Technol.

    (2011)
  • W.F. Dabberdt

    Atmosphere-surface exchange measurements

    Science

    (1993)
  • S. Dengel et al.

    Methane emissions from sheep pasture, measured with an open-path eddy covariance system

    Global Change Biol.

    (2011)
  • M. Detto et al.

    Comparing laser-based open-and closed-path gas analyzers to measure methane fluxes using the eddy covariance method

    Agric. For. Meteorol.

    (2011)
  • W. Eugster et al.

    Eddy covariance for quantifying trace gas fluxes from soils

    Soil

    (2015)
  • S.M. Fan et al.

    Atmosphere-biosphere exchange of CO2 and O3 in the central Amazon forest

    J. Geophys. Res.—Atmos.

    (1990)
  • C. Feigenwinter et al.

    Eddy Covariance Measurements over Urban Areas, Eddy Covariance

    (2012)
  • R. Felber et al.

    Eddy covariance methane flux measurements over a grazed pasture: effect of cows as moving point sources

    Biogeosciences

    (2015)
  • P.L. Finkelstein et al.

    Sampling error in eddy correlation flux measurements

    J. Geophys. Res.—Atmos.

    (2001)
  • T.K. Flesch et al.

    Determining ammonia emissions from a cattle feedlot with an inverse dispersion technique

    Agric. For. Meteorol.

    (2007)
  • T. Foken

    Post-field Data Quality Control, Handbook of Micrometeorology

    (2004)
  • L.A. Harper et al.

    Micrometeorological techniques for measurement of enteric greenhouse gas emissions

    Anim. Feed Sci. Technol.

    (2011)
  • A. Haslwanter et al.

    Open-path vs. closed-path eddy covariance measurements of the net ecosystem carbon dioxide and water vapour exchange: a long-term perspective

    Agric. For. Meteorol.

    (2009)
  • T. Horst

    A simple formula for attenuation of eddy fluxes measured with first-order-response scalar sensors

    Bound.—Layer Meteorol.

    (1997)
  • IPCC

    Climate Change 2014: Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change

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