Using metal oxide gas sensors to estimate the emission rates and locations of methane leaks in an industrial site: assessment with controlled methane releases

<p>Fugitive methane (CH<span class="inline-formula">₄</span>) emissions occur in the whole chain of oil and gas production, including from extraction, transportation, storage, and distribution. Such emissions are usually detected and quantified by conducting surveys as close as possible to the source location. However, these surveys are labour-intensive, are costly, and fail to not provide continuous emissions monitoring. The deployment of permanent sensor networks in the vicinity of industrial CH<span class="inline-formula">₄</span> emitting facilities would overcome the limitations of surveys by providing accurate emission estimates, thanks to continuous sampling of emission plumes. Yet high-precision instruments are too costly to deploy in such networks. Low-cost sensors using a metal oxide semiconductor (MOS) are presented as a cheap alternative for such deployments due to their compact dimensions and to their sensitivity to CH<span class="inline-formula">₄</span>. In this study, we demonstrate the ability of two types of MOS sensors (TGS 2611-C00 and TGS 2611-E00) manufactured by Figaro^® to reconstruct a CH<span class="inline-formula">₄</span> signal, as measured by a high-precision reference gas analyser, during a 7 d controlled release campaign conducted by TotalEnergies^® in autumn 2019 near Pau, France. We propose a baseline voltage correction linked to atmospheric CH<span class="inline-formula">₄</span> background variations per instrument based on an iterative comparison of neighbouring observations, i.e. data points. Two CH<span class="inline-formula">₄</span> mole fraction reconstruction models were compared: multilayer perceptron (MLP) and second-degree polynomial. Emission estimates were then computed using an inversion approach based on the adjoint of a Gaussian dispersion model. Despite obtaining emission estimates comparable with those obtained using high-precision instruments (average emission rate error of 25 % and average location error of 9.5 m), the application of these emission estimates is limited to adequate environmental conditions. Emission estimates are also influenced by model errors in the inversion process.</p>