Quantifying NH3 and CH4 emissions from a dairy housing using backward Lagrangian stochastic modelling

Abstract

<p>Inverse dispersion modelling (IDM) using a backward Lagrangian stochastic (bLS) dispersion model has been successfully applied to quantify emissions from confined ground sources e.g. as for ammonia (NH<sub>3</sub>) loss after manure spreading. The most widely used bLS model for emission measurements of NH<sub>3</sub> and methane (CH<sub>4</sub>) from agricultural sources such as lagoons and livestock buildings is based on Flesch et al. (2004). For such applications, the model assumptions of a diffusive ground source within a homogeneous turbulence field, which implies absence of obstacles as e.g. buildings disturbing the flow, is clearly not fulfilled. It remains unclear to what extend these violations introduce bias into the emission estimates. Further, the model by Flesch et al. does not include deposition removal, which for NH<sub>3</sub>, can induce an underestimation of the emission from the source (Häni et al., 2018). Häni et al. extended the standard bLS calculation model with an optional dry deposition mechanism.</p><p>In a field campaign between mid-September and mid-December 2018, CH<sub>4</sub> and NH<sub>3</sub> emissions from a natural ventilated dairy housing with 40 cows were quantified using the IDM method with the bLS model by Häni et al. (2018). From the three-month period, results for 63 measurement days at 30-minute resolution were evaluated and thereof 71% of the data points were discarded from the emission calculation due to inapplicable turbulence conditions or instrument failure.</p><p>NH<sub>3</sub> and CH<sub>4</sub> concentrations were analysed with open-path instruments (NH<sub>3</sub>: miniDOAS,; CH<sub>4</sub>: GasFinder, Boreal Laser, Inc., Edmonton, Alberta, Canada) (aligned in parallel) with 50 m path lengths (distance between sensor and reflector). During part of the field campaign (24 days), simultaneous in-house measurements of CH<sub>4</sub> and NH<sub>3</sub> emissions using the tracer ratio method (iTM) (SF<sub>6</sub> and SF<sub>5</sub>CF<sub>3</sub>, Mohn et al., 2018) were conducted and results compared with the estimates retrieved by the IDM method. Overall, the results from the IDM method compare well to the results of the in-house measurements, with mean daily emissions of 18.3 kg CH<sub>4</sub>/d (IDM) and 17.9 kg CH<sub>4</sub>/d (iTM) and 1.08 kg NH<sub>3</sub>/d (IDM) and 1.56 kg NH<sub>3</sub>/d (iTM), respectively. Regarding NH<sub>3</sub>, the IDM method was run without the inclusion of a dry deposition mechanism. First results from IDM calculations with the inclusion of dry deposition indicate, that dry deposition modelling may explain the difference in NH<sub>3</sub> emissions between the IDM method and the iTM.</p><p><strong>References</strong></p><p>Flesch, T. K., Wilson, J. D., Harper, L. A., Crenna, B. P., and Sharpe, R. R.: Deducing ground-to-air emissions from observed trace gas concentrations: A field trial, J. Appl. Meteorol., 43, 487–502, 2004.</p><p>Häni, C., Flechard, C., Neftel, A., Sintermann, J., and Kupper, T.: Accounting for Field-Scale Dry Deposition in Backward Lagrangian Stochastic Dispersion Modelling of NH3 Emissions, Atmosphere, 9, 146, 2018.</p><p>Mohn, J., Zeyer, K., Keck, M., Keller, M., Zähner, M., Poteko, J., Emmenegger, L., and Schrade, S.: A dual tracer ratio method for comparative emission measurements in an experimental dairy housing, Atmospheric Environment, 179, 12–22, 2018.</p>