(368c) Multiple Greenhouse Gases Mitigation (MGM): Process Intensification to Mitigate Non-CO2 Gases and CO2 from Air | AIChE

(368c) Multiple Greenhouse Gases Mitigation (MGM): Process Intensification to Mitigate Non-CO2 Gases and CO2 from Air

Authors 

Sirigina, D. S. S. S. - Presenter, KTH Royal Institute of Technology
Nazir, S. M., KTH - Royal Institute of Technology
Goel, A., Birla Institute of Technology and Science - Pilani, Goa Campus
Background and Motivation

The Paris Agreement is an important milestone that brought together 196 countries to agree upon climate targets through emission reduction. Although the main focus has been on mitigating CO2 in the IPCC’s 1.5 °C report [1], mitigating non-CO2 greenhouse gases like CH4 and N2O will have a significantly higher climate impact. Majority of these non-CO2 GHGs are from the agricultural and farming sector, accounting for 39% and 72% of CH4 and N2O emissions worldwide in 2017 [2, 3]. One of the main challenges with these emissions is that they are very diverse and dilute. However, the confidence gained through development of Direct Air Capture (DAC) technology for CO2 capture from air [4] presents opportunities to mitigate CH4 and N2O emissions. The scope of this paper is to provide an insight into an intensified process that can mitigate multiple GHGs (CH4, N2O and CO2) from air in a single system. The proposed process concept is termed as Multiple Greenhouse Gas Mitigation (MGM) and can accelerate achieving negative emissions. The envisioned process technology can be first applied to mitigate GHGs from air closer to animal ventilation stables, that contains CH4 (2-300 ppm).

Two types of approaches have been studied to mitigate CH4 and/or N2O from air i) gas separation, capture and regeneration, and ii) catalytic conversion/decomposition. In the first approach, CH4 and N2O are generally adsorbed over porous zeolites and metal-organic frameworks (MOFs) [5, 6]. However, these processes have challenges with presence of CO2 and moisture in air [7]. The second approach is to convert CH4 and N2O over a catalyst surface (thermal or photocatalyst). Thermal catalyst can convert CH4 and N2O only at temperatures above 300 °C [8-10]. It is worth noting that the studies didn’t include results for simultaneous CH4 and N2O mitigation. However, photocatalyst have potential to convert both CH4 and N2O at room temperatures [11, 12]. Based on this concept, a solar chimney power plant (SCPP) [11] was proposed that can convert CH4 and N2O while generating electricity from solar panels. However, there is still a gap in science with respect to mitigating all the three major GHGs (CH4, N2O, CO2) in one single system.

This paper presents a first-of-its-kind process intensification concept to mitigate all the three major GHGs (CH4, N2O, CO2) from air. A simple schematic of the process is shown in Figure 1. Photocatalytic surface is used to convert the CH4 into CO2 and H2O, and N2O into N2 and O2, followed by DAC of CO2. The captured CO2 can be then compressed, transported and utilized or stored. The proposed concept can advance the development of DAC technologies and can have greater impact by mitigating CH4 and N2O that have higher global warming potential (28 and 265 respectively, following fifth assessment report AR5). In this paper, we propose the intensified process and present analysis with respect to the energy consumed per ton of CO2-equivalent mitigated.

Methods

A 0D model for the photocatalytic converter is modelled using MATLAB. The 0D model incorporates the thermodynamic and kinetic data, and radiation transport equation to predict the conversion of CH4 and N2O in air. 0D model does not consider the shape of the catalytic converter nor the flow profiles. The remainder of the process is modelled using commercial simulation software tools like Aspen Plus. The energy consumed in the process for blowers and regeneration of sorbent is estimated. The energy consumed in the DAC of CO2 is considered as the reference. The typical amine‑impregnated oxide-based DAC for CO2 [4] technology is considered in this study.

The key performance indicator in this study is the energy consumed per ton of CO2-equivalent mitigated. The tons of CO2-equivalent includes the tons of CO2 and tons of CH4 and N2O multiplied by their global warming potential.

Results

The results from this study mainly compares the estimation of the conversion, material and energy requirements in the process against the DAC for CO2. We will also make a comparison of the results against the process where each gas would been separately mitigated. The amount of greenhouse gases mitigated and the energy consumed per ton of CO2-equivalent mitigated will be calculated. The DAC for CO2 capture consumes 12 GJ/ton-CO2 for a technology that uses amine impregnated oxide‑based DAC. Preliminary results show that the energy consumed per ton of CO2-equivalent mitigated will be 4 GJ in the MGM concept. A detailed process analysis, with material (catalyst and sorbent) and energy consumed, quantum yield (as we consider photocatalysts) and amount of greenhouse gases mitigated will be presented in the final paper.

Acknowledgements

The work is part of the project “Energieffektiv negativa utsläpp frÃ¥n jordbrukssektorn” (project number 50340-1) funded by Energimyndigheten (Swedish Energy Agency). The authors would like to thank the collaborators in the project from KTH Royal Institute of Technology (Stefan Grönkvist), Uppsala University and Swedish University of Agricultural Sciences for their contributions through discussions within the project. This work is also financially supported by the Swedish governmental initiative StandUp for Energy.

References

1. IPCC, Summary for Policymakers. In: Global Warming of 1.5°C. An IPCC Special Report on the impacts of global warming of 1.5°C above pre-industrial levels and related global greenhouse gas emission pathways, in the context of strengthening the global response to the threat of climate change, sustainable development, and efforts to eradicate poverty [Masson-Delmotte, V., P. Zhai, H.-O. Pörtner, D. Roberts, J. Skea, P.R. Shukla, A. Pirani, W. Moufouma-Okia, C. Péan, R. Pidcock, S. Connors, J.B.R. Matthews, Y. Chen, X. Zhou, M.I. Gomis, E. Lonnoy, T. Maycock, M. Tignor, and T. Waterfield (eds.)]. World Meteorological Organization, Geneva, Switzerland, 32 pp. 2018.

2. © FAO. FAOSTAT Emissions database. http://www.fao.org/faostat/en/#data/GT.

3. Gütschow, J., et al., The PRIMAP-hist national historical emissions time series (1850-2017). 2019, GFZ Data Services.

4. Sanz-Pérez, E.S., et al., Direct Capture of CO2 from Ambient Air. Chemical Reviews, 2016. 116(19): p. 11840-11876.

5. Kim, J., et al., New materials for methane capture from dilute and medium-concentration sources. Nature Communications, 2013. 4(1): p. 1694.

6. Yang, J., et al., MIL-100Cr with open Cr sites for a record N2O capture. Chemical Communications, 2018. 54(100): p. 14061-14064.

7. Jackson, R.B., et al., Methane removal and atmospheric restoration. Nature Sustainability, 2019. 2(6): p. 436-438.

8. Anderson, R.B., et al., Catalytic Oxidation of Methane. Industrial & Engineering Chemistry, 1961. 53(10): p. 809-812.

9. Kapteijn, F., J. Rodriguez-Mirasol, and J.A. Moulijn, Heterogeneous catalytic decomposition of nitrous oxide. Applied Catalysis B: Environmental, 1996. 9(1): p. 25-64.

10. Gélin, P. and M. Primet, Complete oxidation of methane at low temperature over noble metal based catalysts: a review. Applied Catalysis B: Environmental, 2002. 39(1): p. 1-37.

11. de_Richter, R., et al., Removal of non-CO2 greenhouse gases by large-scale atmospheric solar photocatalysis. Progress in Energy and Combustion Science, 2017. 60: p. 68-96.

12. Ming, T., et al., Fighting global warming by greenhouse gas removal: destroying atmospheric nitrous oxide thanks to synergies between two breakthrough technologies. Environmental Science and Pollution Research, 2016. 23(7): p. 6119-6138.


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