Hostname: page-component-78c5997874-j824f Total loading time: 0 Render date: 2024-11-12T20:47:54.002Z Has data issue: false hasContentIssue false

Offshoring insect farms may jeopardize Europe's food sovereignty

Published online by Cambridge University Press:  20 September 2024

Ren Ryba*
Affiliation:
Animal Ask, Unit 10, The Linen House, 253 Kilburn Lane, London W10 4BQ, UK
*
Author for correspondence: Ren Ryba Email: [email protected]

Abstract

Non-technical summary

Given increasing global political, security and economic challenges, politicians in the European Union (EU) are seeking to reduce the EU's dependence on imports, including feed for farmed livestock. While insect farming has been suggested as an advantageous source of livestock feed is the insect farming industry, the sector has not met optimistic expectations. In particular, labor and electricity costs are driving insect companies offshore, including to Asia and the United States. This paper explores ways that the EU could solve this problem, the most promising of which is to expand the EU's production of maize and soy.

Technical summary

In the context of the Russian invasion of Ukraine and increasing global destabilization, policy makers within the European Union have expressed the need to reduce the bloc's dependence on imported agricultural products such as livestock feed. One industry that has been promoted as an advantageous source of livestock feed is insect agriculture. However, the insect industry's growth has not kept pace with optimistic expectations, and high labor and electricity costs in Europe appear to be driving major insect companies to expand production offshore. One solution may involve supporting the automation of insect farming, though automation may have harmful social consequences by reducing employment and exacerbating inequality. A more promising solution could involve bringing additional land under cultivation to expand domestic production of maize and soy, and the most up-to-date estimates suggest that doing so may even offer environmental benefits over insect production.

Social media summary

Insect farming has been offered as a solution to EU food security, but labor and power costs complicate the picture.

Type
Commentary
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
Copyright © The Author(s), 2024. Published by Cambridge University Press

1. Introduction

In recent years, few topics have generated as much academic interest and popular optimism as insect farming. Proponents of insect farming have drawn attention to ways that insect production could benefit environmental sustainability, food system resilience, and local producers (IPIFF, 2023). These benefits, together with the potential for significant economic returns, have drawn venture capital and research effort to support the nascent insect farming industry (Halloran et al., Reference Halloran, Flore, Vantomme and Roos2018; Rabobank, 2021).

However, to deliver any benefits, the insect production industry still has substantial barriers to overcome. These include logistical challenges, food safety concerns, the disposal of frass (insect waste), and competition with conventional livestock farming for key inputs such as high-quality feed (Grasso & Bordiga, Reference Grasso and Bordiga2023; Smetana, Reference Smetana2023; Thrastardottir et al., Reference Thrastardottir, Olafsdottir and Thorarinsdottir2021).

While insects farmed for human consumption have attracted headlines, insect production in the Global North is almost entirely used to produce animal food and feed. The market share of insects farmed for human consumption is ‘negligible’, according to a recent Rabobank report (Rabobank, 2021). Rather, almost all insects in Europe and North America are farmed to produce feed for pets, farmed fish, and farmed poultry (Halloran et al., Reference Halloran, Flore, Vantomme and Roos2018). The main insects farmed for feed are larvae of three species: black soldier flies (Hermetia illucens), yellow mealworms (Tenebrio molitor), and house flies (Musca domestica) (Grasso & Bordiga, Reference Grasso and Bordiga2023; Halloran et al., Reference Halloran, Flore, Vantomme and Roos2018).

In the European Union (EU), narratives around the sustainability and social implications of insect farming need to be understood in the context of the EU's food strategies and emerging geopolitical crises. The key document outlining the EU's objectives is the farm to fork strategy, which aims to ensure that the food system is having a positive impact on the environment, food security, public health, and economic returns.

The EU's agricultural strategy can be situated in the context of global trends. While humanity is capable of feeding itself, transformations are needed to ensure that food production is inclusive and sustainable (Vos & Bellù, Reference Vos, Bellù, Campanhola and Pandey2019). The EU sees itself as a major contributor to food security, sustainability, and justice around the world (Maggio et al., Reference Maggio, Tine and Malingreau2016). The Commission's 2022 communication made frequent reference to global food security, food assistance, and support to countries in need, and ‘the transition towards sustainable, resilient and fair food systems in the EU and globally’ (European Commission, 2022). The EU can indeed exercise power over the direction of the global food system. Such power can be exercised directly, through the EU's own agricultural production and provision of food aid, or indirectly, by setting standards and regulations that are subsequently adopted by producers and governments in other countries (the ‘Brussels effect’) (Bradford, Reference Bradford2020; Maggio et al., Reference Maggio, Tine and Malingreau2016). Therefore, the EU's policy response to any agricultural issue – including insect production – will need to pay attention to the EU's role in the global community and its stated desire to improve sustainability and social justice around the world.

More urgently, the attention of the EU's policy makers has been drawn by the geopolitical and humanitarian crisis that is the Russian invasion of Ukraine. Beyond the immense human suffering, the war is also shining a light on fractures in the EU's food systems. These fractures have motivated the EU's policy makers and institutions to identify areas where the bloc can improve its food self-sufficiency. French President Emmanuel Macron expressed this view concisely, as reported by Politico (Wax, Reference Wax2022): ‘We can no longer depend on others to feed ourselves’.

A communication from the European Commission emphasized that while the EU is actually self-sufficient in most of its food, it is not self-sufficient in key inputs into its food production (European Commission, 2022). This is something of a paradox; while the EU is largely self-sufficient in food outputs, the EU relies heavily on imports for animal feed, including soybean and maize, and energy. As such, the EU has begun to pursue policies to improve its self-sufficiency in these essential inputs (European Commission, 2022).

To progress the policy goal of food self-sufficiency, the EU established a ‘Contingency plan for ensuring food supply and food security in times of crisis’. As part of this, the EU also established the European Food Security Crisis Preparedness and Response Mechanism (EFSCM), a group of Member State representatives, stakeholder organizations, and other experts, to support coordination across sectors and Member States (Bertolozzi-Caredio et al., Reference Bertolozzi-Caredio, Severini, Pierre and Zinnanti2023; European Commission, 2024).

Under the contingency plan and the EFSCM, there has been a large amount of resources invested into mapping the EU's agricultural supply chain, identifying weaknesses, and addressing those weaknesses with policy solutions (Bertolozzi-Caredio et al., Reference Bertolozzi-Caredio, Severini, Pierre and Zinnanti2023; European Commission, 2024; Loi et al., Reference Loi, Gentile, Bradley, Christodoulou, Bracken, Knuuttila, Niemi and Wejberg2024). One such study concluded that the most significant risk to the EU's food self-sufficiency is the high costs and low availability of inputs, including energy and feed for livestock and aquaculture (Bertolozzi-Caredio et al., Reference Bertolozzi-Caredio, Severini, Pierre and Zinnanti2023). In particular, the livestock and aquaculture sectors depend on imported feed ingredients, such as soymeal (Loi et al., Reference Loi, Gentile, Bradley, Christodoulou, Bracken, Knuuttila, Niemi and Wejberg2024). This pursuit of self-sufficiency in the EU may pose a challenge when considered alongside current trends in the insect farming industry.

2. The sluggish start of the insect industry

So far, insect production has not kept pace with optimistic projections. In 2019, the industry body International Platform of Insects for Food and Feed (IPIFF) projected that the annual production of all insect proteins (including for human consumption) would reach 1 million tonnes by 2025 and 3 million tonnes by 2030 (IPIFF, 2019). This projection was widely cited by both academic studies and news articles (Thrastardottir et al., Reference Thrastardottir, Olafsdottir and Thorarinsdottir2021). In contrast, IPIFF's members produced around 9,500 tonnes of insect feed products in 2022 (IPIFF, 2023). Even accounting for insects produced for human consumption (currently a negligible market share (Rabobank, 2021)) and producers that are not members of IPIFF, it is difficult to see how the insect farming industry would achieve the 100-fold growth required to reach 1 million tonnes by next year. The online forecasting aggregation platform Metaculus currently predicts that 47,000 tonnes of insect protein will be used as feed in Europe in 2028 (Metaculus, 2024). This more modest prediction, which still expects the insect farming industry to expand by several times over the next few years, is only a couple of percent of the IPIFF's original prediction for 2030.

There are many factors contributing to the insect industry's struggle to meet expectations, including regulatory hurdles and unresolved logistical challenges (Grasso & Bordiga, Reference Grasso and Bordiga2023). However, one important observation is that many small-scale startups are struggling to scale up their production to a commercial level. There is a high turnover; the majority of insect producers wind down or go bankrupt within five years (Larouche et al., Reference Larouche, Campbell, Hénault-Éthier, Banks, Tomberlin, Preyer, Deschamps and Vandenberg2023; Thrastardottir et al., Reference Thrastardottir, Olafsdottir and Thorarinsdottir2021). There appear to be some underlying economic dynamics that are preventing startups from expanding and reaching commercial production volumes.

3. Europe's insect farms are moving offshore

Offshoring occurs when production is fragmented into separate production processes carried out by different companies in different countries (whether or not those companies have the same owner). Offshoring is a result of the integration of the global economy. The past decades have seen a growing importance of offshoring in the EU in particular (Radło, Reference Radło and Ambroziak2017).

Likewise, we may be witnessing the beginning of offshoring in the EU's insect agriculture industry. Europe's biggest insect companies have recently announced plans to expand production outside of Europe (Figure 1). France-based Ÿnsect has announced deals with Jord Producers and Ardent Meals to expand insect production in the Midwest of the United States, and Ÿnsect has also announced a deal with Mexico City-based Corporativo Kosmos to expand production in Mexico. Meanwhile, Netherlands-based Protix and France-based InnovaFeed likewise have plans to expand into the United States. InnovaFeed has also announced plans to expand into South-East Asia (Roussange, Reference Roussange2022; Ÿnsect, 2022).

Figure 1. Offshoring of European insect production may be driven by Europe's higher costs for energy and agricultural wages. Insect production requires specific temperatures (top), electricity (middle), and manual labor (bottom), which are cheaper to obtain in North America and South-East Asia. The dashed lines in the top graph represent approximate optimal temperatures for rearing larvae of black soldier flies and yellow mealworms. Data: Climatic Research Unit, University of East Anglia (crudata.uea.ac.uk, ODbL 1.0 licence); Global Petrol Prices (globalpetrolprices.com, CC BY-NC-ND 3.0 licence), International Labour Organization (ilostat.ilo.org, CC BY 4.0 licence).

The decision to move insect production outside of the EU may be driven by the economic realities of insect agriculture. The financial details of insect farming operations are often kept secret, but we can glean some information from the seminal economic studies on the finances of this industry (Halloran et al., Reference Halloran, Flore, Vantomme and Roos2018; Niyonsaba et al., Reference Niyonsaba, Groeneveld, Vermeij, Höhler, van der Fels-Klerx and Meuwissen2023a; Reference Niyonsaba, Hohler, Van Der Fels-Klerx, Slijper, Alleweldt, Kara, Zanoli, Costa, Peters and Meuwissen2023b; Thrastardottir et al., Reference Thrastardottir, Olafsdottir and Thorarinsdottir2021).

Two major cost components in insect production are labor and energy. To date, the only study to provide empirical evidence on the finances of insect farms in Europe is a study of seven T. molitor farms in the Netherlands. In this study, labor emerged as one of the biggest cost components, ranging between 677 and 2913 EUR/tonne production when the farmer's own labor was included (Niyonsaba et al., Reference Niyonsaba, Groeneveld, Vermeij, Höhler, van der Fels-Klerx and Meuwissen2023a). Labor costs were exceeded on some farms only by the major upfront investments for buildings and machinery. Manual labor is required when caring for larvae (e.g. moving eggs into crates, feeding larvae, harvesting larvae, cleaning crates, and replacing beetles) and for other on-farm processes, such as administration, transport, and marketing (Grasso & Bordiga, Reference Grasso and Bordiga2023; Niyonsaba et al., Reference Niyonsaba, Groeneveld, Vermeij, Höhler, van der Fels-Klerx and Meuwissen2023a). Given the high costs of labor, insect industry stakeholders have identified high labor costs and low levels of automation as main barriers to the expansion of insect production (Niyonsaba et al., Reference Niyonsaba, Hohler, Van Der Fels-Klerx, Slijper, Alleweldt, Kara, Zanoli, Costa, Peters and Meuwissen2023b). Therefore, in developed countries, the profits of insect production may only exceed that of conventional animal protein sources when insect farms reduce wage costs by becoming highly automated (Halloran et al., Reference Halloran, Flore, Vantomme and Roos2018).

When it comes to energy, there are several on-farm processes that contribute to farms' electricity demands. The temperature and humidity level needs to be maintained within a relatively narrow range. Suitable temperatures tend to be relatively high (27–40 °C, depending on species) (Grasso & Bordiga, Reference Grasso and Bordiga2023). Electricity is also needed for slaughtering insects, which may involve energy-intensive processes such as freezing, oven baking, or blending; processing dead insects; and storing substrates and other perishable products (Grasso & Bordiga, Reference Grasso and Bordiga2023). Furthermore, for farms that invest in automation, we can expect the costs of electricity to increase accordingly.

Critically, labor and electricity tend to cost more in Europe than in other insect-producing regions (Figure 2). Consider the labor costs of 677 to 2913 EUR per tonne production, reported for T. molitor farms in the Netherlands (Niyonsaba et al., Reference Niyonsaba, Groeneveld, Vermeij, Höhler, van der Fels-Klerx and Meuwissen2023a). These costs suggest that a move from the Netherlands (with labor costs of 3841 USD per month for agricultural work; Figure 2) to, say, Thailand (198 USD per hour) could save a producer between 642 and 2762 EUR in labor costs for every tonne of production (91%). Of course, this is a simplified calculation, but it illustrates the important fact that insect producers can save lots of money for every tonne of production by moving to countries where labor – often producers' largest cost component – is cheaper.

Figure 2. The largest European insect farmers are expanding overseas. Key destinations include the United States, Mexico, and South-East Asia (Roussange, Reference Roussange2022; Watson, Reference Watson2023; Ynsect, 2022).

Moreover, the higher temperatures in many insect-producing South-East Asian countries would reduce the difference between the ambient air temperature and the optimal temperature for insect growth, thereby reducing the electricity required by insect farms in the first place. One study on mealworms farmed by the company Ÿnsect in France found that producing 1 kg of fresh insects uses 1.152 kWh at farm gate and 8.940 kWh at processing plant gate (Thévenot et al., Reference Thévenot, Rivera, Wilfart, Maillard, Hassouna, Senga-Kiesse, Le Féon and Aubin2018). In France, with energy costs of 0.136 USD per kWh in 2019, 1 tonne of fresh insects would thus cost the producer 157 USD (at farm gate) or 1216 USD (at processing plant gate) in energy costs alone. Much of this cost comes from maintaining the rearing room at 28 °C in a country where ambient temperatures average around 10 °C (mean for Lille, France from 2009 to 2013; Figure 2) (Thévenot et al., Reference Thévenot, Rivera, Wilfart, Maillard, Hassouna, Senga-Kiesse, Le Féon and Aubin2018). In contrast, ambient temperatures in Vũng Tàu, Vietnam, and Bangalore, India are 28.1 and 25.8 °C, respectively (Figure 2). As such, production in Vietnam or India rather than Western Europe enables the producer to avoid this substantial cost component. The United States does not necessarily have a warmer climate, but that country does have cheaper electricity and would therefore still represent a cost saving for producers (Figure 2).

The economic reality of labor and energy costs, and the resulting incentive to move insect production offshore, is a topic about which stakeholders within the insect industry are candid. The investor Tan Shao Ming, when discussing his support for Innovafeed's plans to expand in Southeast Asia, reports (ABC Impact, 2022): ‘We believe that there is a huge potential for Innovafeed's technology and platform to be rolled out in Southeast Asia, given the tropical climate which is conducive for the black soldier fly’. Alexandre de Caters, the Belgian co-founder of insect company Entobel, gives a similar reason when explaining his choice to base his company in Vietnam (Watson, Reference Watson2023): ‘It quickly became obvious that Europe was not the place to start for the simple reason that black soldier flies are tropical insects. […] We plan to grow further inside Vietnam, but the bigger facilities would likely be outside Vietnam in countries with tropical weather and a stable supply of feedstock such as Indonesia and Malaysia’. And Ankit Alok Bagaria, CEO of India-based company Loopworm that aims to produce insect-based aquaculture feed, emphasizes the role of both labor and energy costs (Fletcher, Reference Fletcher2023): ‘In Europe the labour cost is very high and, as the climate is not so suitable for insect growth, [European producers] have to customise and modulate the climate in their farms’.

4. Discussion

If the EU's insect companies find the idea of moving offshore attractive, how could policy makers respond? Could the automation of the insect industry, as some companies are pursuing, improve the efficiency and sustainability of the EU's food production (Thrastardottir et al., Reference Thrastardottir, Olafsdottir and Thorarinsdottir2021)?

4.1 Automation

While automation can reduce labor costs, it would also bring a series of trade-offs. First, automation would, by definition, reduce the ability of insect farms to contribute to employment (Heckmann et al., Reference Heckmann, Andersen, Eilenberg, Fynbo, Miklos, Jensen, Nørgaard and Roos2019). The irony is that local employment has been promoted by industry stakeholders as one potential benefit of insect farming in the first place (Grasso & Bordiga, Reference Grasso and Bordiga2023; IPIFF, 2023). Second, as mechanical and electrical energy is a major component of insect farms' energy use, automation may increase energy consumption (Kok, Reference Kok2021). Third, automation could have different impacts on the demand for contrasting types of labor. While this is a complex debate, it is plausible that automation of agricultural production – in the strict sense of deliberately finding ways to reduce the need for human labor – could have a disproportionate impact on low-skilled labor and could exacerbate economic inequality (Krenz et al., Reference Krenz, Prettner and Strulik2021; Rijnks et al., Reference Rijnks, Crowley and Doran2022). One analysis of Dutch yellow mealworm farms found that producers often hire low-skilled laborers who ‘have difficulties qualifying for a regular job’ (Niyonsaba et al., Reference Niyonsaba, Groeneveld, Vermeij, Höhler, van der Fels-Klerx and Meuwissen2023a). Therefore, automation of Europe's insect farms could disproportionately harm otherwise vulnerable agricultural workers. On the other hand, it is possible that automation could improve the efficiency of production, though this would hinge on how automation is applied in practice (Krenz et al., Reference Krenz, Prettner and Strulik2021; Rijnks et al., Reference Rijnks, Crowley and Doran2022).

In any case, we should be cautious about how food production technology can impact different members of society in different ways. Large, perhaps multinational, companies are more likely to have the capital and expertise to invest in automation than small, local startups (Thrastardottir et al., Reference Thrastardottir, Olafsdottir and Thorarinsdottir2021). Automation may simply end up replicating the trend towards concentration of agricultural production in the hands of a few large companies – beyond the direct implications for social justice, this could increase popular suspicion of this new type of food production (Mohorcich & Reese, Reference Mohorcich and Reese2019; Piet, Reference Piet2017). As such, while automation could indeed reduce high labor costs from the perspective of the industry, automation may create new problems for society that would render this policy response counterproductive.

It is unclear whether European consumers would accept livestock fed with insect-based feeds. One literature review drew an optimistic conclusion, finding that societal attitudes would not be a barrier to the use of insects as livestock feed (Sogari et al., Reference Sogari, Amato, Biasato, Chiesa and Gasco2019). In contrast, a recent qualitative study drew more nuanced conclusions, with participants expressing concerns about impacts on sustainability, pathogen transmission, and animal welfare (Bunker & Zscheischler, Reference Bunker and Zscheischler2023). History provides the example of genetically modified foods; companies were confident in the environmental benefits that genetic modification could bring, and these companies were thus unprepared for popular backlash (Mohorcich & Reese, Reference Mohorcich and Reese2019). Popular fears and backlash may be exacerbated if production involves complicated technology and is controlled by a few large companies, and this is exactly the path that would be followed by an industry looking to automate production of a novel agricultural output (Amato et al., Reference Amato, Riverso, Palmieri, Verneau and La Barbera2023; Mohorcich & Reese, Reference Mohorcich and Reese2019). As the popular backlash against genetically modified foods reveals, consumer education and communication are an important step in securing social approval (Mohorcich & Reese, Reference Mohorcich and Reese2019; Sogari et al., Reference Sogari, Amato, Biasato, Chiesa and Gasco2019). That said, investing in consumer education may be unattractive to investors, with a former insect company co-founder stating (Badeski, Reference Badeski2023): ‘Spending venture equity dollars on an uphill battle to educate customers is not a good use of capital’.

4.2 Expanding domestic maize and soy production

A more feasible policy response may be to bring additional land into cultivation, thereby increasing domestic production of maize and soy (European Commission, 2022). At first glance, it might appear that insect production might offer environmental benefits over crop production. However, a detailed look at the underlying dynamics leads to a counter-intuitive conclusion.

Crop modelling reveals that there are large areas of central and eastern Europe that are feasible for soy production (Rotundo et al., Reference Rotundo, Marshall, Mccormick, Truong, Styles, Gerde, Gonzalez-Escobar, Carmo-Silva, Janes-Bassett, Logue, Annicchiarico, de Visser, Dind, Dodd, Dye, Long, Lopes, Pannecoucque, Reckling and Rufino2024). Producing soy in the EU could reduce greenhouse gas emissions by reducing the production and transport of environmentally costly Brazilian soy (Rotundo et al., Reference Rotundo, Marshall, Mccormick, Truong, Styles, Gerde, Gonzalez-Escobar, Carmo-Silva, Janes-Bassett, Logue, Annicchiarico, de Visser, Dind, Dodd, Dye, Long, Lopes, Pannecoucque, Reckling and Rufino2024; Schilling-Vacaflor & Gustafsson, Reference Schilling-Vacaflor and Gustafsson2024). Likewise, maize production appears to have a disproportionately low carbon footprint in Europe when compared to maize production around the world (Holka & Bieńkowski, Reference Holka and Bieńkowski2020). Since this policy response would involve simply expanding production, rather than supporting an entirely new sector, this policy response may have higher public support.

In contrast, the environmental benefits of insect production may have been overstated (Biteau et al., Reference Biteau, Bry-Chevalier, Crummett, Ryba and Jules2024). The most up-to-date comparisons have found that producing compound animal feed using insects typically requires more energy and produces a larger carbon footprint than the production of animal feed using soy and grains (Smetana, Reference Smetana2023; Quang Tran et al., Reference Tran, Nguyen, Prokešová, Gebauer, Van Doan and Stejskal2022). The promise of insect farms to deliver environmental benefits hinges on the ability to feed insects using food waste and to use insect waste to produce fertilizer. In practice, both of these ideas still face significant logistical, economic, and safety hurdles before they can be applied at industrial scales (Biteau et al., Reference Biteau, Bry-Chevalier, Crummett, Ryba and Jules2024). This is why large insect companies operating today overwhelmingly prefer the same high-quality inputs, including grains, that are already sought by other sectors (Biteau et al., Reference Biteau, Bry-Chevalier, Crummett, Ryba and Jules2024). When high-quality feeds are used as an input for insect production, this simply adds an additional trophic level to the food chain, thus increasing the overall environmental impact (Roffeis et al., Reference Roffeis, Fitches, Wakefield, Almeida, Alves Valada, Devic, Koné, Kenis, Nacambo, Koko, Mathijs, Achten and Muys2020; Smetana, Reference Smetana2023).

For these reasons, bringing additional land under cultivation in the EU – which has been encouraged by the European Commission (2022) – appears to be a practicable and environmentally beneficial policy option.

4.3 The impact of climate change

It is worth mentioning how climate change may influence things. Higher average temperatures could slightly reduce the need for insect farmers to pay for heating costs, and Europe may see a modest decrease in electricity prices (Pilli-Sihvola et al., Reference Pilli-Sihvola, Aatola, Ollikainen and Tuomenvirta2010; van Ruijven et al., Reference van Ruijven, De Cian and Sue Wing2019). On the other hand, positive impacts of climate change may be concentrated in the disproportionately wealthy areas of Europe, whereas less wealthy states in Southern Europe may see higher energy demand and electricity prices (Pilli-Sihvola et al., Reference Pilli-Sihvola, Aatola, Ollikainen and Tuomenvirta2010; van Ruijven et al., Reference van Ruijven, De Cian and Sue Wing2019). Moreover, temperature increases will also be observed in North America and Asia, so offshoring production may remain equally attractive to insect producers as it is today.

It is plausible that widespread adoption of renewable energy sources could improve the picture for European insect production. There are concepts for insect farms that rely on side-stream heat or on-site renewable energy production (Smetana, Reference Smetana2023; Grasso & Bordiga Reference Grasso and Bordiga2023). However, such concepts are limited to small-scale production, and one life-cycle assessment concluded that ‘it is unlikely that on-site renewables will be a solution for all insect producers’ (Smetana et al., Reference Smetana, Schmitt and Mathys2019). Also, switching to renewable energy sources would equally benefit other forms of feed production, so insect farming would not have a particular advantage in this regard (Paris et al., Reference Paris, Vandorou, Balafoutis, Vaiopoulos, Kyriakarakos, Manolakos and Papadakis2022).

To conclude, we can see that relying on insect production may result in the EU simply replacing soy and maize imports with insect protein imports, which could jeopardize the EU's pursuit of food self-sufficiency. In contrast, expanding domestic crop production may be the best policy solution for the EU to improve its agricultural self-sufficiency while preserving agricultural employment and public support.

Acknowledgments

N/A.

Author contributions

N/A.

Funding statement

This research received no specific grant from any funding agency, commercial, or not-for-profit sectors.

Competing interests

The author declares no conflict of interest.

Research transparency and reproducibility

N/A.

References

ABC Impact. (2022). Singapore's ABC Impact Backs French Biotechnology Company Innovafeed in USD 250M Round to Support Global Growth and Expansion. ABC Impact. https://abcimpact.com.sg/media-release/singapores-abc-impact-backs-french-biotechnology-company-innovafeed-in-usd-250m-round-to-support-global-growth-and-expansion/Google Scholar
Amato, M., Riverso, R., Palmieri, R., Verneau, F., & La Barbera, F. (2023). Stakeholder beliefs about alternative proteins: A systematic review. Nutrients, 15(4), 837. https://doi.org/10.3390/nu15040837CrossRefGoogle ScholarPubMed
Badeski, M. (2023). Investment insights for the insect industry: Perspectives from an exited founder. https://perma.cc/ML9R-QNDWGoogle Scholar
Bertolozzi-Caredio, D., Severini, S., Pierre, G., & Zinnanti, C. (2023). Risks and vulnerabilities in the EU food supply chain. https://www.ccrup.eu/wp-content/uploads/2023/11/risks-and-vulnerabilities-in-the-eu-food-supply-chain-KJ0423968ENN.pdfGoogle Scholar
Biteau, C., Bry-Chevalier, T., Crummett, D., Ryba, R., & Jules, M. S. (2024). Insect-based livestock feeds are unlikely to become economically viable in the near future. Food and Humanity, 3(100383), 100383. https://doi.org/10.1016/j.foohum.2024.100383CrossRefGoogle Scholar
Bradford, A. (2020). The Brussels effect: How the European Union rules the world. Oxford University Press.CrossRefGoogle Scholar
Bunker, I., & Zscheischler, J. (2023). Societal acceptability of insect-based livestock feed: A qualitative study from Europe. Journal of Agricultural & Environmental Ethics, 36(4), 23.CrossRefGoogle Scholar
European Commission. (2022). Communication from the Commission to the European Parliament, the European Council, the Council, the European Economic and Social Committee and the Committee of the Regions: Safeguarding food security and reinforcing the resilience of food systems (No. COM(2022) 133 final). European Commission. https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX%3A52022DC0133Google Scholar
European Commission. (2024). State of Food Security in the EU: A qualitative assessment of food supply and food security in the EU within the framework of the EFSCM (No. 2). DG Agriculture and Rural Development. https://agriculture.ec.europa.eu/common-agricultural-policy/agri-food-supply-chain/ensuring-global-food-supply-and-food-security_enGoogle Scholar
Fletcher, R. (2023). India's first insect-for-aquafeed farmer. The Fish Site. https://thefishsite.com/articles/indias-first-insect-for-aquafeed-farmer-loopwormGoogle Scholar
Grasso, S., & Bordiga, M. (2023). Edible insects processing for food and feed: From startups to mass production. CRC Press.CrossRefGoogle Scholar
Halloran, A., Flore, R., Vantomme, P., & Roos, N. (2018). Edible insects in sustainable food systems. Springer International Publishing.CrossRefGoogle Scholar
Heckmann, L.-H., Andersen, J. L., Eilenberg, J., Fynbo, J., Miklos, R., Jensen, A. N., Nørgaard, J. V., & Roos, N. (2019). A case report on inVALUABLE: Insect value chain in a circular bioeconomy. Journal of Insects as Food and Feed, 5(1), 913.CrossRefGoogle Scholar
Holka, M., & Bieńkowski, J. (2020). Carbon footprint and life-cycle costs of maize production in conventional and non-inversion tillage systems. Agronomy, 10(12), 1877. https://doi.org/10.3390/agronomy10121877CrossRefGoogle Scholar
IPIFF. (2019). The European insect sector today: Challenges, opportunities and regulatory landscape. IPIFF. https://www.sustainabilityconsult.com/downloads-blanks/our-work/150-ipiff-vision-paper-on-the-future-of-the-insect-sector-towards-2030/fileGoogle Scholar
IPIFF. (2023). IPIFF Perspectives on the evolution of the European insect sector towards 2030: Current EU regulatory status, existing opportunities and prospects for development. IPIFF. https://ipiff.org/wp-content/uploads/2023/11/IPIFF-Brochure-1-1.pdfGoogle Scholar
Kok, R. (2021). Preliminary project design for insect production: Part 1 – overall mass and energy/heat balances. Journal of Insects as Food and Feed, 7(5), 499509.CrossRefGoogle Scholar
Krenz, A., Prettner, K., & Strulik, H. (2021). Robots, reshoring, and the lot of low-skilled workers. European Economic Review, 136, 103744.CrossRefGoogle Scholar
Larouche, J., Campbell, B., Hénault-Éthier, L., Banks, I. J., Tomberlin, J. K., Preyer, C., Deschamps, M.-H., & Vandenberg, G. W. (2023). The edible insect sector in Canada and the United States. Animal Frontiers: The Review Magazine of Animal Agriculture, 13(4), 1625.CrossRefGoogle ScholarPubMed
Loi, A., Gentile, M., Bradley, D., Christodoulou, M., Bracken, J., Knuuttila, M., Niemi, J., & Wejberg, H. (2024). The dependency of the EU's food system on inputs and their sources. Directorate-General for Internal Policies; European Parliament's Committee on Agriculture and Rural Development. https://www.europarl.europa.eu/RegData/etudes/STUD/2024/747272/IPOL_STU(2024)747272_EN.pdfGoogle Scholar
Maggio, A., Tine, V. C., & Malingreau, J.-P. (2016). Global food security: Assessing trends in view of guiding future EU policies. Foresight (Los Angeles, California ), 18(5), 551560.Google Scholar
Metaculus. (2024). In the year 2028, how many tonnes of insect protein will be used as animal feed for livestock, poultry and fish in Europe? Metaculus. https://www.metaculus.com/questions/3421/in-the-year-2028-how-many-tonnes-of-insect-protein-will-be-used-as-animal-feed-for-livestock-poultry-and-fish-in-europe/Google Scholar
Mohorcich, J., & Reese, J. (2019). Cell-cultured meat: Lessons from GMO adoption and resistance. Appetite, 143, 104408. https://doi.org/10.1016/j.appet.2019.104408CrossRefGoogle ScholarPubMed
Niyonsaba, H. H., Groeneveld, I. L., Vermeij, I., Höhler, J., van der Fels-Klerx, H. J., & Meuwissen, M. P. M. (2023a). Profitability of insect production for T. molitor farms in the Netherlands. Journal of Insects as Food and Feed, -1(aop), 18.Google Scholar
Niyonsaba, H. H., Hohler, J., Van Der Fels-Klerx, H. J., Slijper, T., Alleweldt, F., Kara, S., Zanoli, R., Costa, A. I. A., Peters, M., & Meuwissen, M. P. M. (2023b). Barriers, risks and risk management strategies in European insect supply chains. Journal of Insects as Food and Feed, 9(6), 691705.CrossRefGoogle Scholar
Paris, B., Vandorou, F., Balafoutis, A. T., Vaiopoulos, K., Kyriakarakos, G., Manolakos, D., & Papadakis, G. (2022). Energy use in open-field agriculture in the EU: A critical review recommending energy efficiency measures and renewable energy sources adoption. Renewable and Sustainable Energy Reviews, 158, 112098. https://doi.org/10.1016/j.rser.2022.112098CrossRefGoogle Scholar
Piet, L. (2017). Concentration of the agricultural production in the EU: the two sides of a coin. https://ageconsearch.umn.edu/record/261439/Google Scholar
Pilli-Sihvola, K., Aatola, P., Ollikainen, M., & Tuomenvirta, H. (2010). Climate change and electricity consumption—Witnessing increasing or decreasing use and costs?. Energy Policy, 38(5), 24092419.CrossRefGoogle Scholar
Rabobank. (2021). No Longer crawling: Insect protein to Come of age in the 2020s. Rabobank.Google Scholar
Radło, M.-J. (2017). Offshoring and outsourcing as new challenges for industry in the EU. In Ambroziak, A. A. (Ed.), The New Industrial Policy of the European Union (pp. 6785). Springer International Publishing.CrossRefGoogle Scholar
Rijnks, R. H., Crowley, F., & Doran, J. (2022). Regional variations in automation job risk and labour market thickness to agricultural employment. Journal of Rural Studies, 91, 1023.CrossRefGoogle Scholar
Roffeis, M., Fitches, E. C., Wakefield, M. E., Almeida, J., Alves Valada, T. R., Devic, E., Koné, N., Kenis, M., Nacambo, S., Koko, G. K. D., Mathijs, E., Achten, W. M. J., & Muys, B. (2020). Ex-ante life cycle impact assessment of insect based feed production in West Africa. Agricultural Systems, 178, 102710. https://doi.org/10.1016/j.agsy.2019.102710CrossRefGoogle Scholar
Rotundo, J. L., Marshall, R., Mccormick, R., Truong, S. K., Styles, D., Gerde, J. A., Gonzalez-Escobar, E., Carmo-Silva, E., Janes-Bassett, V., Logue, J., Annicchiarico, P., de Visser, C., Dind, A., Dodd, I. C., Dye, L., Long, S. P., Lopes, M. S., Pannecoucque, J., Reckling, M., … Rufino, M. C. (2024). European soybean to benefit people and the environment. Scientific Reports, 14(1), 7612. https://doi.org/10.1038/s41598-024-57522-zCrossRefGoogle ScholarPubMed
Roussange, G. (2022). Innovafeed lève 250 millions pour devenir le leader des protéines à base d'insectes. Les Echos. https://www.lesechos.fr/start-up/deals/innovafeed-leve-250-millions-pour-devenir-le-leader-des-proteines-a-base-dinsectes-1794629Google Scholar
Schilling-Vacaflor, A., & Gustafsson, M.-T. (2024). Integrating human rights in the sustainability governance of global supply chains: Exploring the deforestation-land tenure nexus. Environmental Science and Policy, 154, 103690. https://doi.org/10.1016/j.envsci.2024.103690CrossRefGoogle Scholar
Smetana, S. (2023). Circularity and environmental impact of edible insects. Journal of Insects as Food and Feed, 9(9), 11111114.CrossRefGoogle Scholar
Smetana, S., Schmitt, E., & Mathys, A. (2019). Sustainable use of Hermetia illucens insect biomass for feed and food: Attributional and consequential life cycle assessment. Resources, Conservation and Recycling, 144, 285296.CrossRefGoogle Scholar
Sogari, G., Amato, M., Biasato, I., Chiesa, S., & Gasco, L. (2019). The potential role of insects as feed: A multi-perspective review. Animals: An Open Access Journal from MDPI, 9(4), 119. https://doi.org/10.3390/ani9040119CrossRefGoogle Scholar
Thévenot, A., Rivera, J. L., Wilfart, A., Maillard, F., Hassouna, M., Senga-Kiesse, T., Le Féon, S., & Aubin, J. (2018). Mealworm meal for animal feed: Environmental assessment and sensitivity analysis to guide future prospects. Journal of Cleaner Production, 170, 12601267.CrossRefGoogle Scholar
Thrastardottir, R., Olafsdottir, H. T., & Thorarinsdottir, R. I. (2021). Yellow mealworm and black soldier fly Larvae for feed and food production in Europe, with emphasis on Iceland. Foods (Basel, Switzerland), 10(11), 2744. https://doi.org/10.3390/foods10112744Google ScholarPubMed
Tran, H. Q., Nguyen, T. T., Prokešová, M., Gebauer, T., Van Doan, H., & Stejskal, V. (2022). Systematic review and meta-analysis of production performance of aquaculture species fed dietary insect meals. Reviews in Aquaculture, 14(3), 16371655.CrossRefGoogle Scholar
van Ruijven, B. J., De Cian, E., & Sue Wing, I. (2019). Amplification of future energy demand growth due to climate change. Nature Communications, 10(1), 2762. https://doi.org/10.1038/s41467-019-10399-3CrossRefGoogle ScholarPubMed
Vos, R., & Bellù, L. G. (2019). Chapter 2 – global trends and challenges to food and agriculture into the 21st century. In Campanhola, C., & Pandey, S. (Eds.), Sustainable food and agriculture (pp. 1130). Academic Press.CrossRefGoogle Scholar
Watson, E. (2023). Entobel opens largest insect protein production facility in Asia, targets aquaculture. AgFunderNews. https://agfundernews.com/entobel-opens-largest-insect-protein-production-facility-in-asia-targets-aquacultureGoogle Scholar
Wax, E. (2022). Putin's war seduces Europe's farmers away from green deal. Politico. https://www.politico.eu/article/ukraine-russia-war-eu-food-farmer-green-deal-corn-fertilizer/Google Scholar
Ÿnsect. (2022). Press releases: Ÿnsect opens first mealworm farm in the US and enters local premium chicken feed market after Jord joins its production platform. Ÿnsect. https://www.ynsect.com/2022/03/29/ynsect-opens-first-mealworm-farm-in-the-us-and-enters-local-premium-chicken-feed-market-after-jord-joins-its-production-platform/Google Scholar
Figure 0

Figure 1. Offshoring of European insect production may be driven by Europe's higher costs for energy and agricultural wages. Insect production requires specific temperatures (top), electricity (middle), and manual labor (bottom), which are cheaper to obtain in North America and South-East Asia. The dashed lines in the top graph represent approximate optimal temperatures for rearing larvae of black soldier flies and yellow mealworms. Data: Climatic Research Unit, University of East Anglia (crudata.uea.ac.uk, ODbL 1.0 licence); Global Petrol Prices (globalpetrolprices.com, CC BY-NC-ND 3.0 licence), International Labour Organization (ilostat.ilo.org, CC BY 4.0 licence).

Figure 1

Figure 2. The largest European insect farmers are expanding overseas. Key destinations include the United States, Mexico, and South-East Asia (Roussange, 2022; Watson, 2023; Ynsect, 2022).