Challenges in farmed insect welfare: Beyond the question of sentience

Abstract

The global Insects as Food and Feed (IAFF) industry currently farms over a trillion individual insects a year and is growing rapidly. Intensive animal production systems are known to cause a range of negative affective states in livestock; given the potential scale of the IAFF industry, it is urgent to consider the welfare of the industry’s insect livestock. The majority of the literature on farmed insect welfare has focused on: (i) establishing that insect welfare ought to be of concern; or (ii) extending vertebrate welfare frameworks to insects. However, there are many overlooked challenges to studying insect welfare and applying that knowledge in IAFF industry contexts. Here, we briefly review five of these challenges. We end with practical recommendations for the future study of insect welfare.

Introduction

By 2100, there will be 10.9 billion people to feed (United Nations 2013). Insects, a high-protein source often with a small environmental footprint (van Huis & Tomberlin 2017), can help meet protein demands. The insects as food and feed (IAFF) industry currently farms over 1 trillion insects per year; by 2030, > 8 trillion individuals per year may be farmed (Rowe 2020; de Jong & Nikolik 2021; for scale: ~79 billion birds and land mammals are slaughtered for meat each year; FAOSTAT in Šimčikas 2020).

Given the growth of the IAFF industry, it is vital to consider the welfare of its insect livestock, especially if insects are sentient — i.e, they have the capacity to experience negative affective states (Bentham 1948; Singer 2002; Birch 2017; Broom 2019). Intensive production systems cause a range of negative affective states in vertebrate livestock; from many moral perspectives, those welfare impacts are of serious concern (De Grazia 1996; Singer 2002; Thompson 2020; Fischer 2021). Comparable impacts upon farmed insects, then, would raise comparable moral issues.

Are insects sentient? At present, the empirical evidence does not readily provide a conclusive answer (Adamo 2016; Barron & Klein 2016; Klein & Barron 2016; Baracchi et al. 2017; Birch 2020; Lambert et al. 2021; van Huis 2021). Moreover, most work on insect welfare acknowledges that definitive data on insect sentience will come too slowly for industry decision-makers (and trillions of insects). Additionally, there may be reasons to question the emphasis on sentience (Monsò 2018; Pali-Schöll et al. 2019; van Loon & Bovenkerk 2021).

A reasonable response to current uncertainty is to employ a precautionary principle. The strongest such principle would require that humans should treat insects as though they are sentient, though weaker principles could be formulated (Fischer 2016, 2019; Birch 2017; Knutsson & Munthe 2017; Röcklinsberg et al. 2017; van Huis 2021). Since the welfare of insects has generally been overlooked (Horvath et al. 2013; Smith & Pryor 2013; International Platform for Insects as Food and Feed [IPIFF] 2019), even weak principles could significantly impact our assessment of industry practices.

To date, much of the literature on farmed insect welfare has focused on establishing that insect welfare ought to be of concern (Gjerris et al. 2016; Röcklinsberg et al. 2017; van Huis 2021) and there is a paucity of literature on the difficulty of improving insect welfare (Pali-Schöll et al. 2019). Consequently, many challenges to studying insect welfare and applying that knowledge in IAFF industry contexts have been overlooked. Here, we briefly review five of these challenges and end with recommendations for the future study of insect welfare.

Challenge 1: Rapid industry growth and innovation

Eventual ‘world-scale’ mass production facilities are predicted to produce > 1 million tons of insect protein per year, each rearing at least 15 trillion individual insects (Kok 2017; Rowe 2020). This scale is immense but so is the potential demand: each world-scale plant would only meet 5–6% of just aquaculture’s potential demand for insect protein (Rowe 2020; de Jong & Nikolik 2021), alongside demand for insect protein as swine/broiler feed and in pet food.

Practically, the vast majority of studies on welfare-relevant factors for farmed insects occur at small, laboratory scales. The IAFF industry must base the rearing of insects-by-the-ton on studies of insects-by-the-gram (Tomberlin & Cammack 2017). Scaling is not necessarily linear and some welfare concerns may present only in mass-rearing environments, such as the increased risk of overheating in large, high-density rearing containers (Sørensen et al. 2012; Scala et al. 2020; Barrett et al. 2022). Laboratory-scale studies on welfare may thus be inaccurate/incomplete when applied to mass-production environments (Myers et al. 2008; Miranda et al. 2020; Yang & Tomberlin 2020).

Scaling will require significant technological innovation (Kok 2017), likely including emerging biotechnologies, such as genetic modification (e.g. Zhan et al. 2019). However, new technologies can create new welfare problems (Barrett et al. 2022), as they have in vertebrate livestock production (Fischer 2021). Intense genetic selection in broiler chickens (Gallus gallus domesticus) has increased growth rates by over 300%, resulting in a variety of painful skeletal disorders (Knowles et al. 2008). Zhan et al. (2019) produced genetically modified black soldier fly (Hermetia illucens) larvae whose final larval weight is nearly 300% greater than normal; the welfare impacts of this increase in weight are unknown. Assessing the welfare impacts of technological advancements in each farmed insect species, before they become commonplace for trillions of individuals, may prove incredibly challenging.

Another line of innovation involves rearing new insect species; each species may raise different welfare concerns. Currently, only seven species of insects are farmed in truly significant numbers (Rumbos & Athanassiou 2021); however, there are over 2,000 species of edible insects (Jongema et al. 2017), many of which are poorly studied. Devising welfare assessments that accurately characterise the different welfare needs of each species, in each farmed context, will be difficult.

Challenge 2: Adoption of vertebrate welfare tools

Most entomologists gravitate toward Brambell’s Five Freedoms (1965), designed for vertebrate livestock, when considering insect welfare (Erens et al. 2012; de Goede et al. 2013; van Huis 2021; Barrett et al. 2022). While some aspects of Brambell’s framework readily apply to insects (e.g. freedom from disease), others are more challenging to apply given our limited understanding of insects’ affective states (e.g. freedom from fear; van Huis 2021). Decapod welfare researchers have recently used the Five Domains model as a more practical alternative for invertebrates (Albalat et al. 2022), though the fundamental issue remains. As Figure 1 illustrates, the physical/functional domains matter as proxies for the mental domain. Every welfare framework available must confront the paucity of data regarding insects’ mental lives.

Figure 1. The Five Domains Model of animal welfare. Adapted from Mellor DJ, Hunt S and Gusset M 2015 Caring for Wildlife: The World Zoo and Aquarium Animal Welfare Strategy. WAZA Executive Office: Gland, Switzerland.

Additionally, behavioural and physiological differences between vertebrates and insects may impact the adaption of vertebrate assessment tools for insects (Boppré & Vane-Wright 2019). As one example, the vertebrate livestock industry uses percent pre-slaughter mortality as a welfare metric in pigs (Sus scrofa) (Straw et al. 1983; Knauer & Hostetler 2013). However, dead insects can completely disappear; having no bones, farmed insects can cannibalise the entire bodies of dead conspecifics.

For a physiological example, consider that terrestrial vertebrate livestock are typically endotherms (having self-regulated, stable body temperatures across a range of ambient conditions; Clark & Pӧrtner 2010). Moderate changes in environmental temperature are thus insignificant from the perspective of terrestrial vertebrate welfare. Insects, however, are typically ectotherms (having body temperatures much closer to ambient conditions; Régnière et al. 2012). As a result, moderate changes in environmental temperature can quickly impact insects’ body temperatures with, presumably, some associated effects on welfare. Welfare tools developed for vertebrates may not be sufficiently attuned to the physiological and behavioural needs of insects.

Challenge 3: Inter-population and inter-individual variation

Neutral evolutionary processes, such as genetic drift, can cause populations of initially similar individuals to differentiate genetically over time if they become isolated. Genetic differentiation can occur very quickly when animals with short generation times, such as farmed insects, are reproductively isolated by being housed in different production facilities (Ohta 1993; Thomas et al. 2010). This differentiation can be magnified by selective effects if local conditions on farms vary in fitness-relevant ways (Darwin 1859). In aggregate: evolutionary processes will produce phenotypically variable populations. These ‘strain’ effects are already known to impact farmed insect responses to environmental conditions and these differences may be welfare-relevant (Zhao et al. 2013; Ståhls et al. 2020; Rumbos et al. 2021). High degrees of inter-population variation will make it more difficult to design standardised assessment metrics that produce high welfare for insects across strains/facilities.

However, intrapopulation (e.g. inter-individual) variation may also present an overlooked challenge to insect welfare. Inter-individual variation is widespread, involves specialised diets, behavioural strategies, etc, within a common environment, and is generally an underappreciated phenomenon in shaping ecological/evolutionary dynamics; it has been documented in numerous insect orders (Bolnick et al. 2003; Dall et al. 2012). Farmed and wild contexts differ, potentially affecting the degree of inter-individual variation. Still, inter-individual variation could have welfare-relevant dimensions for farmed insects.

Fundamentally, treating all populations, or all individuals within a population, as identical in their welfare needs may compromise the welfare of some populations or individuals.

Challenge 4: Welfare needs across insect development

Developing juvenile insects molt progressively as they grow until undergoing metamorphosis and emerging in their terminal, adult form. In hemimetabolous insects, such as crickets, nymphs are (mostly) miniature versions of adults and often occupy similar ecological niches (Mito et al. 2010). Holometabolous insects, such as butterflies, undergo complete metamorphosis, e.g. pupation: larvae are morphologically distinct from their adult form and may utilise very different ecological niches (Rolff et al. 2019).

Given dramatic differences in anatomy, physiology, or behaviour across life stages in some insect species, there will be differences in their welfare needs (e.g. life stage-dependent nutritional needs for black soldier fly larvae vs adults; Barrett et al. 2022). These cognitive and welfare differences are likely to be most apparent in holometabolous insects, as pupation involves significant remodelling of almost their entire anatomy, including integrative regions of the nervous system (e.g. Fahrbach 2006), to an extent not generally seen in hemimetabolous taxa (Malaterre et al. 2002). Holometabolous species will form the majority of farmed insects (Rowe 2020); it is therefore important to understand differences in their species-specific welfare needs across development.

Challenge 5: Inter-specific trade-offs

The availability of insect protein raises questions about how to make trade-offs involving different species, with different probabilities of sentience, and radically different numbers of farmed individuals (Fischer 2019; Pali-Schöll et al. 2019). One such inter-specific trade-off concerns a standard use case for insect protein: aquaculture. There, insect protein may replace fishmeal. If the goal is to minimise negative welfare impacts, we now need to compare the welfare impacts associated with IAFF facilities rearing a much larger number of insects to commercial fishing operations capturing a much smaller number of fish.

The growth of the IAFF industry means there will be many variations of the inter-specific welfare impacts challenge (e.g. in assessing the sustainability benefits of insect farming, which may generate trade-offs when considering human and wildlife welfare; Gamborg et al. 2018; Hampton et al. 2021). It is important, therefore, to develop decision-making frameworks for such trade-offs that allow stakeholders to consider the importance of several factors: the number and kinds of individuals affected, the size and severity of the welfare impacts, and indirect effects on other goals (e.g. sustainability).

Recommendations for early studies of insect welfare

The scale of the IAFF industry, and the welfare challenges it thus poses, can be hard to appreciate. Even if negative welfare impacts were extremely uncommon — let us assume 0.0001% of individuals per facility have low welfare under conditions that serve the average individual — 15 million insects per world-scale facility would be affected each year.

However, the IAFF industry is not at this scale yet; it is just beginning to grow. Accordingly, there is time to prioritise addressing these and other challenges to guide the industry in averting serious welfare impacts on invertebrate livestock. We thus make the following recommendations for early forays into insect welfare:

• • Transparent, inter-disciplinary collaborations are essential to guide the industry down a cautious, welfare-respecting, and economical path (e.g. Thompson 2020). IAFF producers and entomologists lack the training and regulatory guideposts to address ethical concerns alone; similarly, animal ethicists and welfare biologists lack the necessary knowledge of insect biology and industry practices needed to devise useful welfare tools.

• • The vertebrate livestock welfare literature is a valuable resource but has clear limitations in applicability. It is probably safer to borrow more theoretical frameworks (e.g. the Five Domains; Albalat et al. 2022) than applied ones, but all borrowing should be done while considering insect-specific modifications.

• • Initial insect welfare tools that originate in labs, rather than production-scale facilities, need to be used cautiously as scale may affect their implementation. It is important that researchers and producers collaborate to identify best practices.

• • As the industry grows, there will be technological innovations, as well as changes in the species, populations, and life stages that are farmed. All these factors are welfare-relevant. So, frequent iteration in welfare assessment tools will be necessary.