- 1National Scientific and Technical Research Council, Buenos Aires, Argentina
- 2Institute for Physiological and Ecological Research in Agriculture (IFEVA), National Scientific and Technical Research Council, Buenos Aires, Argentina
- 3National Institute for Agricultural Technology (INTA), Center for Natural Resources Research, Buenos Aires, Argentina
- 4Brazilian Agricultural Research Corporation (EMBRAPA), Brasília, Brazil
Editorial on the Research Topic
Finding paths to net-zero carbon in climate-smart food systems
This Research Topic (Finding Paths to Net Zero Carbon in Climate-Smart Food Systems), aimed at analyzing the balance between carbon (C) emission and C storing per unit of time in agriculture and the food systems.
Global emissions of carbon (CO2eq) have increased about 40% between 1990 and 2021 (Statista, 2023), so transitioning to a net-zero world is a major challenge for humanity. Setting aside natural sources of C emissions, the energy sector accounts for around 75% of anthropogenic emissions, and the full food system for the remaining 25%. On-farm primary production, which explains about 12% of the food system (Crippa et al., 2021) includes methane (54%), nitrous oxide (28%), and carbon dioxide (18%). Whereas, carbon dioxide may last hundreds of years in the atmosphere, methane is a short-lived gas that last around 10–12 years (FAO, 2023). According to Rosa and Gabrielli (2023), while primary production would explain about 42% of C emitted by the full food system, land-use change would accounts for 31%, food processing, transport, retail, and packaging 20%, and food-waste disposal 7%. Therefore, the food system will inevitably be subjected to scrutiny in any climate-stabilization program.
The notion of net-zero carbon (NZC) in agriculture refers to the balance between the carbon (C) amount released to, and the amount of C removed from the atmosphere per unit of time. Some practices are recommended to facilitate the path to NZC: (i) use of biofuels in farm operations (Flammini et al., 2022), (ii) use of improved rice cultivation methods (Yuan et al., 2021), (iii) management of nitrogen fertilizers (Maaz et al., 2021) and use of grass-legume mixtures for fixing nitrogen and replace nitrogen fertilizers in tropical and subtropical regions (Jensen et al., 2012; Boddey et al., 2020), (iv) use of feed additives to reduce methane production in ruminants (Hegarty et al., 2021), (v) genetic selection that aims at low methane emission in cattle (Manzanilla-Pech et al., 2022), (vi) biological C storage in biomass and soil to improve C balance in farms (Chiquier et al., 2022) and (vii) rock weathering coupled to tilling operations (Searchinger et al., 2021). Rosa and Gabrielli (2023) suggest that a smart combination of techniques could mitigate C emissions by up to 45%.
The massive use of biomass as renewable energy in a NZC strategy is still an unresolved question. The large-scale need of land for biomass production could lead to deforestation, habitat alteration, biodiversity loss and soil degradation. The competition between grain- and biomass-crops for land and water will affect food production to feed about 10 billion people by 2050 (Rosa et al., 2021).
Assuming uncertainties for accounting the C-stocktaking in the path to NZC, current research methods differ depending on whether bottom-up (IPCC, 2021) or top-down (Byrne et al., 2023) approaches are used. In either approach, the estimation of C storage is still another unresolved question. The calculation of C storage is more controversial than that of C emission (Smith, 2004). Beyond discussions, several studies (Lal, 2004; Navak et al., 2019; Viglizzo et al., 2019; Chen et al., 2020) focused on the C captured by plant through photosynthesis, which in turn accumulates as above-ground (AGB), below-ground-biomass (BGB) and soil organic carbon (SOC). Two published articles in this Research Topic addressed the issue C storing: by combining biogeochemical simulation models and remote-sensing data, Baldassini et al. proposed a novel methodology to estimate on-farm C accumulation in Uruguayan soils. On the other hand, Hyman et al. demonstrated that improved pastures have stored up to 10 Mg ha−1 more SOC than degraded pastures or native savannas in acid soils of Colombia.
Beyond the biological options, there is an increasing interest on enhanced rock weathering to store C in cropping. Beerling et al. (2020) analyzed the impact of a technique that looks at capturing C by modifying the soil properties with calcium and magnesium-rich crushed silicate rocks. The improved meteorization of silicate rocks through cropping operations seems to have a significant potential to remove C from the atmosphere (Joppa, 2020; Terlouw et al., 2021). The difference between biological and geological store of C is rather clear: while biomass and SOC behave as ephemeral C sinks, rocks tend to be permanent.
Amid speculations about NZC, well-known scientists and leading climate experts like Dyke et al. (2021) have harshly criticized the notion of NZC, especially when such concept is associated with carbon-credit purchase. They argue that the application of NZC strategies allows heavy-polluting industries to “neutralize” their emissions by buying carbon-emission permits, which simply means a “greenwashing” tactic to avoid responsibilities with no net benefit to climate. They denounced the idea of NZC as a fraud and a trap because it pushes the problem onto future generations, emphasizing that the goal should be zero emissions, rather than emissions counterbalanced by carbon credits. NZ balance is for them a distraction to hide a business-based climate-change mitigation. To get an effective C removal, they argue that C capture and store would need to remove 12 billion ton of C dioxide each year, which seems to be too good to be true. In line with this thinking, the 2021 Report of the International Energy Agency (IEA, 2021) states that the massive deployment of C-removal strategies is costly and uncertain, and so the international community should stop putting it in a first place.
Beyond C emissions and C storing, some scientists and policy-makers are looking at geo-engineering as an emergency solution to limit temperature rising. However, geo-engineering, which connotes a broad-scale control on solar radiation entry, will not resolve the problem of C emissions. It is just a temporary solution with no definitive effect on the true cause of climate change (Saeed et al., 2018).
Skeptic views about the Paris Agreement, C offsetting alternatives, C sequestration, geo-engineering and NZ options are inevitable. However, if an optimistic vision tends to prevail, significant investment, policies support, financial incentives, education and training programs would inevitably be required at a global scale.
Author contributions
EV: Conceptualization, Writing – original draft. FB: Writing – review & editing. MT: Writing – review & editing. BA: Writing – review & editing.
Funding
The author(s) declare that no financial support was received for the research, authorship, and/or publication of this article.
Conflict of interest
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The author(s) declared that they were an editorial board member of Frontiers, at the time of submission. This had no impact on the peer review process and the final decision.
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Keywords: food systems, net-zero carbon (NZC), path to NZC, C emissions, C storage
Citation: Viglizzo EF, Bert FE, Taboada MA and Alves BJR (2023) Editorial: Finding paths to net-zero carbon in climate-smart food systems. Front. Sustain. Food Syst. 7:1322803. doi: 10.3389/fsufs.2023.1322803
Received: 16 October 2023; Accepted: 08 November 2023;
Published: 28 November 2023.
Edited and reviewed by: Ngonidzashe Chirinda, Mohammed VI Polytechnic University, Morocco
Copyright © 2023 Viglizzo, Bert, Taboada and Alves. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Ernesto F. Viglizzo, ZXZpZ2xpenpvJiN4MDAwNDA7Z21haWwuY29t