1. Introduction
In a novel take on European food system governance, the Green Deal is evoking agroecological approaches to European food system transitions.Footnote 1 The importance of agroecology for future European Union (EU) law and policy is evidenced by the fact that it is embraced by both Green Deal’s Farm to Fork (F2F) and Biodiversity Strategies.Footnote 2 The synchronised release of these documents presents opportunities for comprehensive perspectives on food production, the environment, and the role of biodiversity that emphasise an agroecological vision for European food systems.Footnote 3 One of the primary tactics implemented for facilitating these transitions is the Green Deal’s development of a new legislative framework for sustainable food systems (SFS). This approach aims to align and adapt future and existing legislation to more sustainable outcomes using provisions and goals that work towards systemic change. If experts’ acknowledgements regarding the agroecological potential for food system transitions are accepted at the institutional level,Footnote 4 legal and regulatory frameworks of food systems should reflect these aims. Most research exploring transitions or transformation towards an agroecological Europe focuses on generating aspirational policy proposals.Footnote 5 This article contributes to existing scholarship by illustrating how agroecology can be applied to concrete regulatory policies. More specifically, it unpacks how the existing regulation of pesticides, a core agricultural policy area, can be assessed in terms of its alignment with agroecological principles. To do so, the article develops a normative framework based on agroecological theory and sustainability discourse via the concepts of strong and weak sustainability to analyse the framework.
Pesticides are indispensable within conventional industrial agricultural production.Footnote 6 To eradicate weeds, insects, and other agents considered detrimental to intensive production, conventional approaches depend on large quantities of pesticides.Footnote 7 This dependency is deepened by the fact that conventional agriculture’s lack of biodiversity has been largely linked to further pest outbursts and invasions.Footnote 8 The result of conventional pest management is a reinforcing mechanism of increasing dependencies on pesticides, making conventional production’s reductionist approach far from resilient or sustainable.Footnote 9 While this approach may have been favourable in the past due to a relative increase in yieldsFootnote 10 and lower production costs, recent developments demand fundamental changes to this approach. Pesticides are now known to be highly toxic ecological disruptors that linger in the environment in unforeseen ways.Footnote 11 They are responsible for the deterioration of biodiversity in agroecosystems, both terrestrial and aquatic,Footnote 12 and their presence in European soils is now the rule rather than the exception.Footnote 13 From a societal perspective, human health is also adversely affected by pesticide toxicity. Side effects from pesticide exposure have been linked to both acute and chronic effects, in addition to illnesses such as Parkinson’s disease and blood cancers.Footnote 14 These impacts on human health are felt most strongly by the most vulnerable farming populations. Through the F2F and Biodiversity Strategies, the Green Deal calls for changing this pest management approach in favour of agroecologically aligned pest management. Agroecological pest management focuses on mimicking ecosystemic behaviour.Footnote 15 Rather than applying toxic elements to eradicate ‘whatever’ is threatening a crop, agroecology aims to manage potential and existing threats, understanding that undesirable variables fulfil often invisible yet important ecosystemic functions.
This article is structured as follows: section two briefly presents agroecology and explores how it can be operationalised within law and regulation through the development of an analytical framework. Section three introduces the existing regulatory framework for pesticide use. The framework is then critically analysed via the application of the developed framework, assessing alignment/tensions with agroecological perspectives. The article ends by summarising the analysis, providing conclusions and future avenues for continued research.
2. An agroecological normative framework
For decades, agroecology has been considered key to transitions towards SFSs.Footnote 16 Its documented ability to address the systemic problems inherent to conventional food systemsFootnote 17 has made it the focus of international interest.Footnote 18 While agroecology has grown as an academic discipline since the 1920s, agroecological practice is deeply rooted in indigenous and peasant societies around the world, observed as early as the 16th century.Footnote 19 Its modern resurgence manifested as a result of global resistance by peasant and small-holder farmers to the unexpected consequences of globalised intensive agribusiness.Footnote 20 Generally understood to include three components in its definition, agroecology is simultaneously considered a science, a set of practices, and a social movement: it is a ‘transdisciplinary field that [encompasses] the ecological, sociocultural, technological, economic and political dimensions of food systems, from production to consumption’.Footnote 21
Agroecological theory is based on the integrated principle of social and ecological coevolution:Footnote 22 human societies are considered a part of nature, within which human beings establish their social metabolism.Footnote 23 Food systems, as part of that social metabolism, are social systems embedded within society’s broader environment. In considering food systems as embedded social systems, they should be designed to function within the confines of the environment’s biophysical limitations. Because agroecology is dependent on this harmony as a requirement for sustainable and equitable food systems, which are traditionally found amongst peasant and smallholder farming communities, there is a need for broader institutional design to manage and minimise the unsustainable material exchanges between society and nature; to address the imbalanced distributions of power and status, and to improve the distribution of resources within social systems.Footnote 24 Food systems should be ecologically and environmentally appropriate, culturally sensitive, socially just, and economically viable.Footnote 25 The embedded nature of agroecosystems within their environment, and the prioritisation of equitable, societal harmonisation with the environmentFootnote 26 is reflected by strong sustainability discourse. The key distinction between weak and strong sustainability, visually depicted in Figure 1, is how the environment is prioritised in relation to the economy.Footnote 27
General representations of weak and strong sustainability.
Weak sustainability places society, nature, and the economy on a level playing field: each component is as important as the others. This departing point is only made possible by weak sustainability’s premise that ‘natural’ capital can be substituted by man-made capital.Footnote 28 This premise makes sustainability a relative concept, where society’s intent with regard to sustainability is to reduce the impacts of economic activity by individually addressing sustainability issues in a sectoral manner (ie transportation, finance, food systems, industry, etc).Footnote 29 Moreover, weak sustainability conceives of society and the economy as capable of being separate from the environmentFootnote 30 for their functions, making the inclusion of the environment appear as a benevolent choice in the development of society and the economy. Conversely, strong sustainability discourse maintains that the natural environment embodies and provides the infrastructure that all societal processes are built upon.Footnote 31 This approach prioritises meeting environmental goals over economic growth. From a strong sustainability perspective,Footnote 32 guaranteeing societal longevity and equitable prosperity requires that societal decision-making be guided by the aim of maintaining and enhancing the well-being, protection, and resilience of the environment and environmental activity. While this topic remains debated in sustainability discourse, research shows that the actual substitutability of natural capital by man-made capital is limited,Footnote 33 calling into question the foundation of sustainability as a relative concept that can be approached in sectoral rather than systemic ways. Agroecological sustainability therefore implies a transformation away from the modern, globalised agro-industrial system that is dependent on the separation between the economy and the environment to one based on agroecological principles. These food systems prioritise local, food-sovereign,Footnote 34 cooperative, contextually embedded approaches, where institutional frameworks are receptive to the same principles and are capable of designing effective strategies to scale up agroecological transitions (eg public policies working in coordination with social movements, the localisation of food systems, the politicisation of food, etc).Footnote 35
Against this background, it is possible to construct a framework that facilitates the implementation and endorsement of agroecological approaches at institutional levels. To do that, it is helpful to draw on agroecology’s rich scholarship, which includes agroecological strategies for institutional transitions and transformation,Footnote 36 in addition to a set of thirteen principlesFootnote 37 that reflect normative (eg ‘food systems should be equitable’) and causative dimensions (eg ‘more biodiverse agricultural systems are likely to be more resilient’), which reflect agroecological theory.Footnote 38
These principles address important agroecological concepts from environmental, social, and economic perspectives and include: (1) Recycling, (2) Input reduction, (3) Soil health, (4) Animal health, (5) Biodiversity, (6) Synergy, (7) Economic diversification, (8) Co-creation of knowledge, (9) Social values and diets, (10) Fairness, (11) Connectivity, (12) Land and natural resource governance, and (13) Participation (defined in Table 1). Consolidated from an extensive literature review, these 13 agroecological principles have been formulated from agroecological history and science, including, aligning with, and complementing other less-detailed frameworks that have been formulated to communicate agroecology, like the FAO’s ten elements of agroecology.Footnote 39 Given that there is no current framework guiding Europe’s implementation of agroecology, this framework is meant to provide a baseline of departure for considering and including agroecology within law and policy and is not exhaustive of all the considerations required for agroecological transitions. For greater analytical tractability, the author has grouped these principles into three clusters that connect back to the concept of strong sustainability. Principles 1 to 6 are more closely related to Environment; principles 8, 9, 12, and 13 to Society; and principles 7, 10, and 11 to Economy (Figure 2). The principles help provide characterisations for each cluster, each with an identifiable orientation or trend that can be translated into a guiding framework for regulation and policy aims.
Adaptation of the consolidated set of thirteen agroecological principles in Wezel et al, ‘Agroecological Principles and Elements and Their Implications for Transitioning to Sustainable Food Systems. A Review’ 40 (2020) Agronomy for Sustainable Development, https://doi.org/10.1007/s13593-020-00646-z
Clustered Agroecological Principles.
A. Environment
Orientations for the environmental cluster align with a strong sustainability perspective, where societal governance acknowledges planetary biophysical limits. The cluster focuses on the re-embedding of agroecosystems into their environment, and various aspects of agroecosystemic self-organisation and regulation that correspond with the concept of biomimetics,Footnote 40 reflected by principle 6 (synergy). This includes the closing of resource cycles and improving self-sufficiency through recycling (principle 1), input reduction (principle 2), and integration of healthy agroecosystemic components (principles 3–5); protection and enhancement of soil health (principle 3) through specific practices (such as intercropping, crop rotations, and rotational grazing), in addition to decreasing disturbances to the soil (such as tilling chemical, synthetic fertilisers, and pesticides); and promoting increased biodiversity (principles 4 and 5) in soils and ecosystems adapted to local conditions.
B. Society
Orientations for the societal cluster are based on an institutional understanding of the ecosystemic structure that human societies depend on. They are guided by cognitive models that enable those institutions to organise society in a way that harmonises with those ecosystemic structures, or the surrounding environment. The cluster focuses on the design and production of actions, institutions, and norms aimed at achieving equitable, agroecologically sustainable food systems.Footnote 41 This process begins by (i) identifying and addressing power relations that lead to social inequalities and uneven access to resources. This includes addressing imbalanced dynamics and shifting power away from transnational corporations and global value chains towards peasant and small-scale producer empowerment.Footnote 42 The process continues with (ii) the top-down design of institutions that favour agroecological food systems and (iii) the bottom-up organisation of agroecological movements that facilitates their scaling.Footnote 43 Point (ii) includes facilitating the participation (principle 13) of peasant and small-holder producers in the governance of land and natural resources (principle 12)Footnote 44 as well as enabling changes to societal norms (principle 9). Point (iii) includes providing the necessary support and infrastructure for transitioning producers to organise, co-create and share relevant knowledge (principle 8).
C. Economy
Orientations for the economic cluster focus on supporting the trends in the environmental and societal clusters, transitioning from globalised markets (which negatively impact farmer incomes and decouple agroecosystems from their surrounding environment) towards resilient, local markets organised by local producers (principles 7 and 11). They also focus on ensuring a just quality of life for all food system workers, especially peasant and small-holder producers, via fair market and working conditions (principle 10). Examples include: acknowledging an increasing diversity of activities, products, and services offered through European agricultural productionFootnote 45 that implies a stark shift away from monocultural intensification and market commodification (principle 7); the shortening of supply chains, where the majority of products are marketed locally (principle 11); increasing social and economic proximity between farmers, farm workers, and local markets (principle 11); high levels of exchange and trade of products and services amongst producers (principle 11); ensuring the stability of agricultural incomes and profitability over time (principle 10); and tackling issues of generational renewal in farming communities.
The following section begins by discussing the regulatory framework for pesticides. It then shows how the agroecological framework, articulated using the three clusters, can be deployed within the context of pesticide use and pest management to assess the regulatory framework’s alignment with agroecology.
3. An agroecological analysis of the EU regulatory framework on pesticides
Pesticide regulation occurs via a large body of European legislation requiring a dual-system authorisation process prior to placing any pesticides and active chemical substances on the market. The process is iterative and continuous, requiring renewed authorisation prior to the expiry date of approved substances. While this body of legislation includes a variety of legislative instruments meant to regulate various aspects of pesticide use in the EU, this case study focuses on relevant aspects of the 2014–2020 Common Agricultural Policy in addition to the main regulatory framework. The regulatory framework includes Regulation (EC) 178/2002 laying down the general principles and requirements of food law, establishing the European Food Safety Authority and laying down procedures in matters of food safety (GFL),Footnote 46 Regulation (EC) 1107/2009 concerning the placing of plant protection products on the market (PPPs),Footnote 47 Regulation (EC) 396/2005 on maximum residue levels of pesticides in or on food and feed of plant and animal origin (MRL),Footnote 48 and Directive 2009/128 establishing a framework for Community action to achieve the sustainable use of pesticides (SUPs).Footnote 49
Within the EU, no regulation exists that defines general principles for agriculture law. Rather, agriculture and fisheries are included in the Treaty on the Functioning of the European Union (TFEU) in Articles 38–44, where it is clarified that a European internal market for agricultural products and a common agricultural policy are expected to coexist. This elaboration resulted in the Common Agricultural Policy (CAP), which constitutes the legal and political backbone of European integration.Footnote 50 Initially set up as a system for short-term market regulation based on price intervention mechanisms and guarantees for producers, the CAP has changed in response to developments occurring within the broader international context.Footnote 51 Given the article’s focus on existing regulatory dynamics, the analysis of the CAP focuses on the policy prior to the agreed CAP reform on 2 December 2021,Footnote 52 or the EU CAP 2014–2020.
When it comes to food law (GFL), the European food sector is one of the most heavily regulated sectors.Footnote 53 The GFL details important components of food system regulation: it specifies the general principles and requirements for food law; establishes the European Food Safety Authority (EFSA); and defines matters related to food safety. The focus on improving food safety resulted from issues in the 80s and 90s, like the bovine spongiform encephalopathy outbreak, which resulted in severe public mistrust of European political institutions. Through the implementation of a risk analysis-based governance approach focused on food safety, the GFL prioritises two aims: achieving the free movement of food and feed throughout the European Union and establishing rigorous levels of protection for human health.Footnote 54 Risk analysis focuses on mitigating potentially unwanted consequences and is comprised of three areas: risk assessment, management, and communication. Within the realm of the GFL, risk assessment calls for expert scientific assessments of food safety measures for the overarching purpose of reducing, eliminating, and avoiding risks to human health; when expert advice is uncertain, the law invokes the precautionary principle.Footnote 55 While pesticides are not explicitly addressed in the GFL, Articles 6 and 7 embed risk analysis, assessment, and management, and the precautionary principleFootnote 56 respectively to the field of food law, and are of importance to pesticide use and regulation.
The PPP Regulation concerns the placing of plant protection products (more commonly known as pesticides) and their active substances (ie the active chemical or micro-organism within pesticide mixtures) on the market. The aim of this Regulation is the protection of human, animal, and broader environmental health and well-being and the facilitation of European market integration. It defines the approval and monitoring process for PPPs, their active substances, and any safeners, synergists, and co-formulants present, calling for active cooperation between Member States throughout the process. This Regulation goes hand in hand with the MRL Regulation,Footnote 57 which settles matters related to legal limits for pesticide residues in food and feed. It aims to harmonise and simplify maximum residue levels for pesticides, setting a common European assessment scheme for all agricultural products (from food to animal feed). The SUPs Directive seeks to establish a framework for the sustainable use of pesticides that prioritises human and environmental health. It also emphasises the usefulness of alternative management approaches to pests, such as Integrated Pest Management (IPM) and other non-chemical approaches. To this aim, all Member States are instructed to create a National Plan with defined quantitative objectives, targets, measures, timetables, and indicators, in addition to the development and introduction of alternative approaches through which to reduce dependency on pesticides.Footnote 58
A. The environmental cluster
Environmental cluster perspectives on pest management look to (i) reduce the consumption of/dependence on most, if not all, synthetic pesticides used (principles 1 and 2); (ii) facilitate the adoption of contextualised, appropriate pest management techniques (eg biological pest control, IPM and management of landscape elements, natural/biological pesticides, the inclusion of allelopathic plantsFootnote 59 within crop rotation, etc) (principles 1 and 2)Footnote 60; and (iii) focus on fostering agroecosystemic health via the improvement of soil health (principle 3) and increasing/fostering contextually appropriate biodiversity (principle 5) that contributes to naturally occurring pest management within agroecosystems. The regulation of agroecological pest management from environmental perspectives would therefore prioritise a systemic food system perspective guided by biomimetics (principle 6).
From agroecological perspectives, (i) reducing the consumption of and dependence on pesticides, and (ii) facilitating the adoption of agroecological pest management techniques fall on two sides of the same coin. Reducing pesticide applications in conventional production leaves an otherwise fragile ecosystem highly vulnerable to pest infestations if no appropriate agroecological pest management techniques are adopted, requiring concerted action to meet pesticide reduction goals. The SUPs Directive is the only instrument present in the examined framework that explicitly states a need, or aim, to reduce pesticide use and dependency (principle 2, input reduction). The Directive justifies this aim by referring to worker protection, protection of the environment, and the prevalence and impact of pesticide residues. It then introduces specific techniques, eg IPM, as viable alternatives. A review of the Directive’s effectiveness however revealed difficulties in determining compliance to its aims across the board (setting up of national actional plans, implementation of training and certification schemes, monitoring pesticide application equipment, etc).Footnote 61 While 26 Member States managed to report setting up inspection systems for pesticide equipment and all states reported establishing training and certification systems, only five Member States had set measurable targets after eight years, while no Member States set any clear criteria for ensuring the implementation of general IPM principles.Footnote 62
Despite recognition of the importance of reducing pesticide use at the EU law level, the framework is arguably based on the premise that chemical pesticides present the main approach to pest and disease management within European food systems. This discourse is reinforced by the title given to the PPP Regulation, which communicates the belief that pesticides belong on the market, in addition to the fact that it paradoxically conveys that ensuring diversification of agriculture and horticulture requires ample availability of plant protection products and, therefore, specific rules should be established for their use. This is further supported by the historically increasing reliance on exceptional authorisations for applying banned pesticidesFootnote 63 in the absence of ‘equally efficient pesticides’ and the constant surfacing of alternatives to banned active substances. Reliance on derogations means that the banning of substances, like neonicotinoids, provides no guarantees that they will be entirely off the marketFootnote 64 or that potential risks will be reduced over time. According to a Pesticide Action Network (PAN) Europe report,Footnote 65 EU countries granted 236 derogations of banned pesticides between 2019 and 2022. Neonicotinoid insecticides, which were found to be highly toxic to key agroecosystemic pollinators, account for nearly half of those derogations and have been banned in the EU since 2018.Footnote 66 In Pesticide Action Network and Others,Footnote 67 the European Court of Justice (CJEU) issued a preliminary ruling banning the use of derogations in early 2023. Since then, 29 new derogations have been approved.Footnote 68 The reliance on derogations of banned pesticides not only offends principles 2 and 6 (input reduction and synergy respectively), but also the precautionary principle.
When it comes to supporting environmental health, the regulatory framework on pesticides should take a systemic approach to agroecosystemic health via (iii) a focus on soil health and increasing contextually appropriate biodiversity that contributes to naturally occurring pest management within agroecosystems. While both the PPP and MRL Regulations, in their recitals, scopes, and aims, regard environmental health throughout food and feed production processes, even mentioning agroecologically aligned alternatives (ie IPM principles and non-chemical practices), none of these considerations makes it into operable and enforceable provisions. The health of soils (principle 3) is a key component of food production. Considering the impact of pesticide use on soils, the quantity applied is intimately connected to soil health. Much like the sparse focus on input reduction identified within the framework, soil health as a concept is absent from the regulatory framework contrasting principles 3 and 6, soil health and synergy. Soils are first mentioned in Annex I, in a table depicting products and their respective MRLs. This table indicates that while crops are evaluated for residues, there is no attention paid to soil or ecosystemic health once crops are removed from fields (eg no mention of MRL values established for soils). While the MRL Regulation does not focus on residue levels in soils or the surrounding environment, agricultural products are inextricably connected to their agroecosystems. Calculations of product MRLs therefore also provide potential indications of residue levels present in the surrounding environment. This is important because direct ingestion of pesticides is not the only way to contract harms from them. What can be gleaned from this is that pesticides are applied for agricultural production, and the Regulation for monitoring the residue levels of agricultural product levels omits all environmental components within which those pesticides are applied. This implies that many potential risks and existing harms originating from pesticide use are systemically omitted in the regulation of their use. This is worsened by the lack of protection afforded to soils throughout the Regulation which has resulted in measurable levels of soil contamination in the EU.Footnote 69
The most important implication of this observation is that many doses of pesticides are being simultaneously applied without knowing the true risks of their compounded impacts, contrasting principles 3 and 6 (soil health and synergy). According to the CJEU’s judgement in Blaise,Footnote 70 the PPP Regulation is valid and complies with the precautionary principle. In a theoretical assessment of the Regulation that did not consider concrete cases, cocktail effects on human health and the environment are meant to be considered during both the Active Substance assessment at the EU level and the authorisation of PPPs at the Member State level.Footnote 71 The fact that they are meant to be considered, however, does not mean that they are. According to Hendlin et al, cocktail effects are understudied, and prevailing environmental risk assessment methods are deficient in accurately measuring the unintended cocktail effects of pesticides,Footnote 72 contrasting agroecology’s systemic approach and principle 6 (synergy). From the risk management perspective taken within food law and regulation, this dictates that more stringent post-authorisation procedures are needed and also begs the question of how risk is defined. This is especially relevant given that setting levels of protection, against which risks are scientifically measured, is a ‘normative political choice’,Footnote 73 and would arguably change depending on the food system approaches that are prioritised politically.
The role biodiversity plays in agricultural production is also absent in the regulation of pesticides. While briefly mentioned as something pesticide users should be aware of in the SUPs Directive, there is no mention of its importance to agroecosystems and food production or why EU regulation should be striving to decrease the impacts of pesticides on biodiversity in the first place. Biodiversity is first mentioned in Article 3 of the PPP Regulation, defined as ‘variability among living organisms from all sources, including terrestrial, marine, and other aquatic ecosystems and the ecological complexes of which they are part; this variability may include diversity within species, between species and of ecosystems’.Footnote 74 Like soils, it is not mentioned again until Article 4 on the approval criteria for active substances. This conceptualisation, however, ensures that biodiversity is seen not as one of the pinnacles to a healthy environment and productive agroecosystem, but rather as an impediment to unfettered pesticide use and conventional intensive agriculture. The sidelining of biodiversity in the SUPs Directive and the PPP Regulation conflicts with principles 5 and 6, or biodiversity and synergy. EU policy is commonly criticised for the existence of a ‘gap between the ambition of adopted regulations and the modesty of results on the ground’,Footnote 75 a phenomenon that includes pesticide regulation. Given the combined effects of a regulatory framework that demands noncommittal pesticide reductions and has historically allowed consistent derogations on the use of banned pesticides, it can be argued that the EU’s pesticide regulation has prioritised short-term harmonisation concerns over long-term environmental health.Footnote 76
B. The societal cluster
Societal cluster perspectives on pest management focus on designing and producing actions, institutions, and norms aimed at establishing agroecosystems with minimal dependence on high agrochemical and energy inputs,Footnote 77 as dictated by the environmental cluster. The cluster focuses on (i) identifying and addressing power dynamics that lead to social inequalities and uneven access to resources present in the frameworks that regulate pest management and pesticide use. The cluster then focuses on (ii) how top-down processes facilitate the participation (principle 13) of peasant, small-holder, and other transitioning producers in the regulation of pest management and pesticide use (principle 12), and how the processes engage with changes to societal norms (principle 9). Lastly, it explores (iii) how the regulation engages with the provision of support and infrastructure to peasant, small-holder, and other transitioning producers for organising, cocreating, and sharing knowledge (principle 8) around communal, cooperative management aimed at transitioning away from chemical pesticide dependency towards agroecological pest management techniques.Footnote 78
Pesticide regulation can provide various instances where (point i) power balances arguably skew towards the pesticide industry. The first example is the derogations mentioned in the previous section. Despite their problematic implications for continuing reliance on pesticides, derogations of banned pesticides become even more problematic when the pesticide industry can ask for derogations of their own products. In some Member States, the holder of the derogation is the pesticide industry itself, with agribusiness having a heavy hand in the delivery of derogations in general.Footnote 79 Research into this relationship between the pesticide industry and the reluctance found in European governance institutions is that the EU takes a pesticide industry-friendly approach: there is an arguable political hesitancy to take the necessary actions required by EU law when it comes to taking pesticides off the market, even when there is clear proof of externalities and damage.Footnote 80
Glyphosate’s muddled reapproval procedure, where undue industry influence was also identified, presents another example of industry preference.Footnote 81 In the EU, the burden of proof is placed on the applicant, meaning that pesticide regulation and its prescribed environmental risk assessments (ERAs) are dependent on the pesticide industry’s privately funded science.Footnote 82 In addition to including only 52 per cent of pertinent peer-reviewed scientific literature reporting adverse effects of glyphosate exposures, large portions of the German Federal Institute for Risk Assessment’s (BfR) assessment for glyphosate’s reapproval were copied from Monsanto’s application.Footnote 83 Despite the clear conflict of interest presented in the glyphosate case, the CJEU assessed in Blaise that the pesticide reapproval procedure’s reliance on industry studies as dictated by the PPP Regulation safeguards the precautionary principle and does not lead to bias.Footnote 84 This judgement, however, was based on an abstract review of the regulatory framework, rather than a judicial review of a concrete authorisation or approval decision, such as the glyphosate case.Footnote 85 An abstract review of the system established by the Regulation, which affirms the Member States’ duties to carry out assessments on the basis of state-of-the-art scientific knowledge cannot account for (i) the barriers posed by the strict standardisation of scientific studies to the acceptance of independent studies, or (ii) a lack of systematic independent counter-analysis of the submitted studies not being required.Footnote 86 In essence, the CJEU ruling disregarded how the regulation procedures unfolded in real-world examples, and as a result, it also disregarded the institutionalised biases benefiting industry-funded science.Footnote 87
In addition to the presence of undue industry influence, other problematic components for (point ii) participation (principle 13) were identified in the PPP Regulation protocols, namely lack of transparency and barriers to accessing key authorisation documents. These findings led to the European Citizens’ Initiative (ECI) on Glyphosate in 2018, which focused on three areas: (i) banning glyphosate-based herbicides; (ii) ensuring evaluation procedures relied on published studies; and (iii) setting EU-wide mandatory reduction targets for pesticide use.Footnote 88 While the Commission concluded that there were insufficient grounds to ban glyphosate, it did commit to strengthening transparency within assessment protocols and emphasised allocating more focus to implementing the SUPs Directive through harmonised risk indicators.Footnote 89 Moreover, the REFIT evaluation of the GFL further addressed some of these barriers to transparency, concluding that the then-existing risk communication protocols were ineffective and fomented public distrust.Footnote 90 This evaluation led to the adoption of Regulation 2019/1381 on the transparency and sustainability of the EU risk assessment in the food chain and amended the GFL and PPP Regulation, among others. Noteworthy PPP Regulation amendments focused on increasing access to information (Article 10 on public access to the dossiers; Article 16 on public access to the information for renewal) and assessments of confidentiality. This means that existing pesticide regulatory frameworks, due to recent controversies and reflections of societal values (principle 9), showcased an improvement in transparency and access to information, and as a result, potential improvements to participation (principle 13).
C. The economic cluster
The economic cluster focuses on facilitating a decreased dependence on pesticides for agricultural production at all societal levels. This can be done by providing the necessary support, equitable access to resources, and incentives to all farmers for transitioning away from pesticide dependence towards agroecological pest management (principle 7); changing market conditions to facilitate local exchange and trade of agricultural products grown using agroecological approaches (principle 11); and prioritising a just and equitable living for all farmers (principle 10), ensuring those engaging in agroecological transitions are not excluded from accessing helpful measures.
When it comes to facilitating changes towards more sustainable alternatives, the regulatory framework is up against large hurdles. In 2014, the GFL’s ‘fitness’ assessment determined if the GFL effectively considered the entire food and feed sector and adequately reflected modern policy trends.Footnote 91 The main findings of the assessment concluded that the GFL achieves its core objectives, maintaining its relevance regarding trends related to growth, competitiveness, and increased globalisation. However, the fitness checks also determined that the GFL fails to hold up against new challenges like sustainability and food waste.Footnote 92 While this gap exists, further analysis of the legal framework reveals the institutionalisation of certain approaches. This is exemplified most explicitly within the PPP Regulation, where plentiful pesticides are assessed as a condition for ensuring the diversification of agriculture and horticulture. This statement lies at the core of conventional production defined by intensive, large-scale monoculture operationsFootnote 93 based on the pursuit of economies of scale and maximum efficiency within production.Footnote 94 While this approach currently provides a certain competitive advantage within existing globalised markets, it stands in stark contrast to all agroecological principles. Attempts at supporting more sustainable approaches to production are found in the reformed CAP of 2014–2020, which came about as a response to various economic, environmental, and social issues. The CAP 2014–2020 emphasised a long-term perspective to three main objectives: competitive and viable food production; the sustainable management of natural resources; and sustainable rural development.Footnote 95
The CAP reform introduced a new arrangement into its two-pillar architecture that, in addition to its income support and safety net measures, aimed to improve the integration of environmental requirements and strengthen rural development.Footnote 96 These goals were supported by the new ‘Greening’ architecture, which made use of cross-compliance in the implementation of obligatory agricultural practices under Pillar 1’s Direct Payment scheme,Footnote 97 and various other voluntary measures located under Pillar 2’s Rural Development Policy. For farmers to receive the entirety of their income support from the CAP, they first needed to comply with a basic set of rules that ensured statutory management requirements and good agricultural and environmental conditions, or cross-compliance.Footnote 98 Following this compulsory base layer, the compulsory ‘Greening’ instrument rewards farmers for respecting three obligatory agricultural practices (ie maintenance of permanent grassland, ecological focus areas, and crop diversification).Footnote 99 Moreover, at least 30 per cent of the budget for each Rural Development Program must be reserved for locally adapted voluntary measures beneficial to the environment and climate, which would be supported by training measures, the Farm Advisory System, etc.
While some of its measures incentivise, support, and offer resources to farmers transitioning away from pesticide use, the CAP measures never explicitly mention pesticides. The CAP Pillar-1 Basic Payment Scheme receives the highest proportion of the budget, and as long as cross-compliance is fulfilled, the payment is provided regardless of how agricultural lands are managed.Footnote 100 Moreover, the three measures prioritised under the ‘Greening’ direct payment also make no mention of reducing pesticide use or increasing agroecological pest management approaches.Footnote 101 While half of CAP beneficiaries of direct payments are very small farms, 20 per cent of CAP beneficiaries, a small number of large-scale operators dedicated to conventional, intensive production, receive 80 per cent of CAP payments;Footnote 102 these economic incentives fail to promote agroecological approaches to food systems, contrasting principles 7 and 10.
Out of Pillar 2 – Rural Development Program’s list of measures, only ‘agri-environment-climate measures’, ‘subsidies for organic farming (conversion or support payments)’, and the ‘risk management toolkit’ focus on incentivising production that decreases pesticide use and dependence.Footnote 103 However, even though the agri-environmental and organic production CAP measures have been found to be the main drivers of agroecological practices due to the stability they provide to farmer incomes during vulnerable transition periods, they cannot always be relied on to fully compensate for the additional costs needed to produce organically or otherwise.Footnote 104 Moreover, farmers often lack the knowledge to implement the recommended practices which, coupled with the high penalties for making mistakes, negatively impacts agroecological adoption for farmers.Footnote 105 Relatedly, the CAP 2014–2020 emphasised the importance of knowledge sharing and access to advisory, information, training, and experimentation services (principle 8). These measures are considered key to facilitating agroecological transitions because they help farmers meet administrative requirements, offer support and community for farmers engaging in transitions, encourage farmer-to-farmer exchanges and experimentation, etc. However, very few farmers have access to these services, and there is a lack of agroecological education and qualified advisers present.Footnote 106
The CAP 2014–2020 also provided various market incentives (principle 11) aimed at facilitating local exchange and trade of agricultural products (eg physical investments; development of farms and businesses; basic services and revitalisation of villages in rural areas; setting-up of producer groups and organisations; encouragement of cooperation between farmers and those involved in the food production chain; etc). These measures contribute to farm and business development in rural areas by enabling autonomous management of food systems on a local scale, helping create short supply chains, and empowering farmers to participate in local rural development.Footnote 107 These measures, however, do not focus on decreasing pesticide use and dependency and their funds are generally difficult to access for smaller farms. While this makes them unsuitable for farmers beginning their transitions, they could offer support to producers that have already transitioned towards low-input, agroecological methods of production.Footnote 108
The few, voluntary actions incentivising farmers to decrease pesticide dependency, however, are offset by the fact that the EU heavily subsidises the pesticide industry and pesticide-reliant agricultural practices, which presents a structural barrier to decreasing pesticide use and dependency. In the face of such a mechanism, where €12 billion in pesticide sales were made to farmers in 2019 alone, regulating for agroecological alternatives becomes even more important, potentially providing more affordable approaches for producers. While the global pesticide market has doubled its profits in the past few decades and prices paid by consumers have increased fivefold since the 1960s, farmers’ incomes and share of commodity values have decreased, contravening principles 10 and 11 (fairness and connectivity).Footnote 109 Moreover, despite the complicated, multistep risk analysis approaches implemented for pesticide and active substance approval, setting ‘safe’ protocols for their use, etc, the recommended equipment for pesticide application was found to provide ineffective protection for those handling pesticides.Footnote 110 Recent investigations establishing the grave inadequacy of those recommendations for protecting farmworkers indicate the injustice and stark power differentials present in existing food systems and call for fundamental changes to pesticide regulation that can better support dignified and robust livelihoods for all actors engaged in food systems (principle 10). Despite CAP goals exemplifying actions and institutions cooperative with agroecology, its strategies were weakly implemented with mixed outcomes:Footnote 111 assessments of CAP 2014–2020 performance emphasise that the use of external inputs, like pesticides, continues to be too high.Footnote 112 To summarise the analysis (Table 2), while the existing pesticide regulatory framework has potential, it does not currently align with agroecological aims. The framework promotes guidelines for an ‘appropriate’ and safe use of pesticides but has allowed fragmented, non-committal, and potentially damaging approaches to pest management across the EU.
Summary of the pesticide regulatory framework’s agroecological alignment
4. Conclusion
Using strong sustainability as a conceptual frame, this article operationalised agroecology in the analysis of the current European legal framework on pesticides, showing how agroecology can be better understood in legal terms. Transitioning to pesticide-free agroecosystems demands a concerted, contextual, multi-pronged strategy across governance levels that is capable of addressing and regulating food system dynamics in systemic ways. What can be seen in how pesticides are currently regulated in the EU is that food systems are broken up into simplified elements, then assessed and regulated from linear perspectives that are unable to capture the systemic, dynamic, and interconnected nature of agroecosystems. This linearity has facilitated the setting aside of key elements, like soil health and biodiversity, and the dynamics between them that result in healthy agroecosystemic behaviour. The implication of this is that existing pesticide regulation, and arguably other frameworks regulating food systems, cannot understand, prioritise, or regulate for proper agroecosystemic functioning or (strong) sustainability. The inconsistent application of the precautionary principle with regard to pesticides and the political foot-dragging witnessed at the EU level demands taking a stricter stance on undue influence within regulatory processes and exploring how an agroecological definition of risk would reflect on pesticide regulation. Moreover, when it comes to economic policy measures, the CAP may provide opportunities to expand agroecological pest management on paper but continues facilitating pesticide-based approaches in production.
To comprehensively address these issues, further research into the implications of agroecological operationalisation within the EU, an industrialised, western context, is needed. Further research into the agroecological alignment of the proposed Regulation on the Sustainable Use of Pesticides, the reformed CAP for 2023–2027, and other components of the Green Deal’s legislative framework for SFSs is also necessary to assess the sustainability of European approaches to pest management, but also food system regulation. Given that agroecosystems represent one of the most important interfaces between humans and their environment, legal and political institutions must learn to think more systemically. For food systems, this includes gaining a greater understanding of the relationships between ecology, the behaviour of human systems, and the management of agroecosystemic dynamics. Without adequate measures that strengthen agroecosystemic resilience towards pests and other diseases, increased support for producers undergoing transitions, and penalisations for unwanted strategies, dependence on pesticides will continue. The operationalisation of agroecological principles within law will therefore be key to meeting future European policy goals for pesticide use and broader food system behaviour, closing the gap between current unsustainable realities and sustainable future visions.
Data availability statement
This Article was produced based on primary legal sources available at https://eur-lex.europa.eu/homepage.html, and on secondary literature available through online repositories and university subscriptions.
Acknowledgements
I will be forever grateful to two anonymous referees and Prof. Marija Bartl at European Law Open for a valuable and inspiring publication process. Thank you, Alessandra Arcuri and Yogi Hale Hendlin, for your feedback and guidance. Thanks to Lizette, Esra, Eduardo, and Antonia for your time and insightful comments.
Funding statement
This work received no specific grant from any funding agency, commercial, or not-for-profit sectors.
Competing interests
The author has no conflicts of interest to declare.
Disclosure statements
The substance of the content presented in this Article has not been published previously and is not currently being considered for publication elsewhere.
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