Do countries comply with EU animal welfare laws?

By Neil_DullaghanđŸ”č @ 2020-08-17T01:18 (+67)

Summary

Introduction

The European Union may be an arena where there are promising opportunities to improve farmed animal welfare through legislation due to historic legal precedents, high public concern for farmed animals, a professional animal protection movement, and new momentum for legislation (see our first post in this series outlining EU law as an arena for farmed animal welfare). Pushing for higher minimum farmed animal welfare standards in law has brought many victories in Europe, but laws are only as good as their implementation. As the animal welfare movement continues to push for higher legal standards for a wider range of farmed animals, one should also pay attention to whether these standards are being practiced in reality. In this report by Rethink Priorities, we focus on the European Union as an example of legislative protection of farmed animal welfare and detail the mechanisms by which compliance is sought. [1]

This is not intended to be the last word on noncompliance with animal welfare laws, but rather to shine a light on the issue and generate future research and work in this area. After outlining the general framework for compliance in the EU, we offer case studies of the major species-specific welfare directives (the conventional battery cage ban for egg-laying hens and partial restrictions on individual stalls for sows, narrow crates for calves, and restrictions on broiler stocking density and tail docking of pigs) as examples of this system succeeding and failing. It is hoped this will highlight what a robust system of compliance could look like, and what bottlenecks and opportunities can be seized on to improve animal lives. For those already familiar with how the EU compliance system works, or just want to read about how it has worked in practice, you may want to skip ahead to the case studies.

The cases below illustrate the farmed animal industry’s unwillingness to improve the lives of animals voluntarily, and even when required to do so by law. The bans on conventional battery cages and sow stalls were not widely acted upon until the EU, under pressure from already compliant countries and non-governmental organisations (NGOs), reaffirmed the deadlines would not be postponed and national authorities stepped up inspections in the face of potential trade bans and legal action. On the other hand, the partial ban on routine tail docking has been marred by perceived widespread noncompliance and a reluctance by the authorities to sanction producers, and requirements on broiler stocking density appear to not be monitored sufficiently for us to know if they are being met. The partial ban on narrow veal crates appears to have been the most successful due to the small number of countries affected.

This suggests that campaigns to pass farmed animal welfare laws may be less effective than assumed if they do not consider noncompliance. One may argue that so long as a law eventually leads to most producers providing higher animal welfare it is not cost-effective for animal welfare groups to act to ensure that all producers do so, nor that they do so by the arbitrary deadline set out in the legislation. However, as the cases below suggest, it appears that without additional pressure from animal groups, lobbyists, agricultural associations, and governments many noncompliant producers would have continued to operate for many years without curtailment, negatively affecting significant numbers of farmed animals. Furthermore, longterm noncompliance can also provide grounds and confidence for repealing the law.  One should also keep in mind that we probably should not expend energies on enforcing laws with bad welfare outcomes or trying to increase compliance with laws that are inherently unenforceable due to vague wording and impractical measures. A question thus becomes are enforceable laws that would improve welfare actually complied with sufficiently enough for us not to worry about the noncompliers?

How bad is noncompliance with animal welfare laws in the EU?

What farmed animal welfare laws does the EU have?

It is important to remember that the EU is in large part a trading bloc designed to reduce internal barriers to goods and services and to protect members from competitors abroad by erecting high tariff barriers to third countries’ competing products. Any discussion of animal welfare laws should keep in mind that they are subject to this underlying motivation. In the absence of measures from the EU institutions to level the playing field among EU countries, one should probably expect a race-to-the-bottom in search of profit at the expense of animal welfare. Therefore, one should not be surprised that animal welfare is not prioritised or complied with, but rather that it has been given any legal standing or enforcement at all. In this report we focus on the species-specific laws that place partial restrictions on three systems most classically associated with industrial farming:[2]  narrow crates for veal calves[3] (enforceable since 2007), conventional battery cages for egg-laying hens[4] (enforceable since 2012), and sow stalls (restrictive metal enclosures in which pregnant pigs are kept) for pigs[5] (enforceable since 2013), as well as setting stocking density standards for broiler chickens[6] (enforceable since 2010) and prohibiting routine tail docking of pigs (since 1994 and codified in the 2008 Pigs directive).  The law providing very general protection of “all” farm animals[7] (since 1998) and the two major regulations concerning transport (since 1977 and updated in 2005) and slaughter (since 1974 and updated in 1993 and 2013) are too vague in nature and cover too many species to confidently make claims about rates of noncompliance so they have been omitted from this report.

Farmed animal welfare noncompliance in the EU

Unlike voluntary corporate commitments, legal commitments are usually mandatory and enforceable by third parties. Despite the apparent energy to develop new animal welfare laws in the EU, there is a possibility that too little attention is paid to developing robust systems to ensure these standards are met in reality. The EU ban on (narrow) veal crates appears to now be fully complied with, as is the ban on conventional battery cages for egg-laying hens, but only after half of EU countries missed the deadline for application of the latter. Compliance with the partial ban on sow stalls of three to four member states is still being verified seven years after the deadline,[8] and the majority of countries were late.  As many as 90% of pigs in the EU are still subject to tail docking and ~35% on average per country are not provided with sufficient enrichment materials despite requirements being in place for more than two decades (Nalon and De Briyne, 2019). The Commission’s own evaluation revealed that 66% of chickens raised for meat are kept in the higher stocking densities allowed despite the required additional animal welfare conditions not being reported or met. While the Commission reports that compliance with the transport regulation is close to 100%, investigations by animal welfare organisations consistently find high levels of noncompliance, especially when it comes to ensuring that high standards are met for live animals that are transported outside of the EU (CIWF, 2018). Problems in the humane slaughter regulation with the use of the derogation for slaughter without stunning and inadequate stunning procedures have also been noted (ECA, 2018).

Even countries generally regarded as having high national animal welfare protection often fail to meet legal requirements. For example, in 2012 (before the majority of EU species-specific laws went into force), Dutch authorities published reports for broiler, pig, calf and cow farming showing compliance with animal welfare laws (national and EU) to be on average 67%, but when animal groups Dier & Recht and Varkens in Nood included laws that are not inspected nor reported on, the compliance level was at maximum 5% (Dier & Recht & Varkens in Nood, 2012) and subsequent reports have continued to document high rates of violations (Dier & Recht & Varkens in Nood 2014, 2016; Varkens in Nood, 2016). This is a country which ranks among the top in terms of legal provisions for animal welfare on the Animal Protection Index, so other EU countries are plausibly in a worse situation. However, the number and level of precision of regulations is not indicative of high concern for animals as some countries could have zero pieces of legislation on animal welfare and treat animals much better in practice. While EU laws are transposed  into national law (translated from general EU goals into specific national laws and regulations), in this report we do not make claims about whether noncompliance with EU laws is better or worse than noncompliance with national laws.

Is the EU an exception regarding compliance with animal welfare laws or is compliance with animal welfare laws very low everywhere?

Countries in the EU are likely not alone, nor the worst in the list, in noncompliance with animal welfare laws but may appear so simply by being an area of the world where there are a lot of animal welfare laws to potentially violate. A 2009 overview of animal welfare in 49 developing countries found only 19 had some kind of legislation concerning animal welfare and/or animal protection (concerning pets, farm animals and/or wildlife) (Bracke, 2009). The overview’s general impression was that enforcement is particularly strict in regions where economic dependency on biodiversity and wildlife is great (e.g. some African countries) or when biosecurity measures need to be followed up for international trade purposes (e.g. South East Asia). In most regions however, it appears that the level of legislation as well as its enforcement is positively related to the country's material wealth; many poorer countries simply do not have the manpower and resources to enforce any rules.

India is one example where high costs, unreliable power sources, and under resourced or nonexistent domestic regulating authorities impede application of animal welfare laws (Animal Charity Evaluators, 2018, 2019). Despite a general consensus that conventional battery cages are illegal according to Indian animal welfare laws, in 2017 they still appeared to be widespread (Bollard, 2017). The Prevention of Cruelty to Animals Act has not been amended or updated since it was first created in 1960 and consequently, the fine for violations is 50 rupees, which is less than $1. [9] According to Indian law, animals cannot be legally slaughtered outside of licensed slaughterhouses, but this law is not enforced or regulated for the slaughter of chickens or goats. Animals are regularly slaughtered in live markets, and most of the slaughterhouses that do exist are not legally registered (Animal Charity Evaluators, 2018, 2019).

However, even in wealthier countries we also see problems. The USA has two major federal animal welfare laws relating to farmed animals (the 28 Hour transport Law, and the Humane Methods of Slaughter Act). Limited enforcement mechanisms and inadequate financial deterrents undermine the application of the humane slaughter provisions (Committee on Oversight and Government Reform, 2010; Matheny & Leahy, 2007), which specifically exempts poultry. The 28 hour law, prohibiting lengthy transport of live animals without rest, has rarely been enforced and the fine per violation ranges only from $100-$500 per shipment (Matheny & Leahy, 2007). Animal Welfare Institute has produced numerous reports that show while federal and state humane slaughter enforcement actions rose during the Obama administration, and especially in reaction to investigations by animal welfare groups, the absolute level of enforcement is low in comparison to other aspects of food safety enforcement and varies significantly by state (AWI, 2010, 2017a, 2017b, 2019, 2020b, 2020a).In neighbouring Canada, despite the historical public support for government enforcement of humane slaughter, there is little public reporting to indicate the success and consistency of such enforcement (NFAHW, 2012, 2019). The EU has both greater resources to enforce rules and also more rules to enforce than other regions.

Is animal welfare an exception regarding compliance in the EU or is compliance in other areas in the EU equally bad?

The academic literature is replete with assertions that noncompliance with EU level legislation in general is common, from transposing the EU laws into national legislation to implementing the laws in practice (Toshkov, 2012; Borghetto & Franchino, 2010; Hartlapp & Falkner, 2009; König & Luetgert, 2009; Falkner & Treib, 2008; Kaeding, 2008; Falkner et al., 2007;  Haverland & Romeijn, 2007; Thomson et al., 2007;   Mastenbroek, 2005; Sverdrup, 2004; Knill & Lenschow, 1998 is just a snapshot of the literature). However, it is actually quite difficult to get a reliable picture of the true rates of noncompliance in the EU. Many studies use quantitative data on the timely transposition of directives into national law, which does not cover the incorrect implementation or application of laws. Other studies use implementation and application reports prepared by consultancies or academics but, understandably due to the resources needed for such work, these studies often only cover a limited number of member states, time periods, and policy sectors.

A dataset on the number of judicial warnings for legal violations brought by the EU against member states (1978-1999) found 35% were due to member states formally transposing EU directives into national law on time, but failing to implement and enforce them subsequently on the ground (Börzel & Knoll, 2012). The Commission’s own recent numbers are that 41% of pending infringement cases are due to incorrect application of directives and regulations. Agriculture appears to have lower rates of noncompliance compared to environment and taxation, but the EU Commission does not disaggregate animal welfare policies specifically from general agricultural policies when presenting this data. The European Court of Auditors (ECA) estimated that violations of agricultural compliance standards appear to range from 21% - 29% in the period 2011 - 2015, with 50% of violations related to the keeping of animals, however this only covered a subset of animal welfare requirements (ECA, 2018, 2016).[10]

The main argument that the EU does not have a noncompliance problem points to the decline in the number of judicial cases against member states from 1,332 in 2007 to 800 today. However, if the cases of noncompliance brought to courts do not constitute a “random sample” of all instances of noncompliance, such a bias in the data would also bias the findings on the causes of noncompliance. A survey of experts’ assessment of which member states violate EU law most and least is in line with the commission’s infringement data, with France, Greece, and Italy being considered the main laggards and Denmark, Finland, and Sweden the compliance leaders, although this was conducted before the major animal welfare laws came into force (Börzel & Knoll, 2012).

Who is working on this problem?

Animal welfare groups consider enforcement to be a problem. Dier & Recht and Varkens in Nood, animal welfare groups in the Netherlands, have highlighted the lack of enforcement by Dutch authorities and pointed to better enforcement protocols developed by Wageningen University. The Swedish group Djurens RĂ€tt, operating in a country with above average animal welfare standards in the EU, has highlighted that in addition to private financial issues of farmers, the lack of enforcement and controls is a major reason for noncompliance due to the limited percentage of farms that are inspected per year and the low penalties applied for noncompliance.[11] The EU acknowledges itself that enforcement of legislation has been insufficient (ECA, 2018) but is only now evaluating its 2012-2015 Strategy for the Protection and Welfare of Animals. Vier Pfoten also thinks enforcement is a huge problem, but highlights that trade dynamics are the most important factor.[12] EuroGroup for Animals places a greater emphasis creating new and revising existing laws so that they are easily enforceable in the first place. However, according to an Animal Charity Evaluators report on the allocation of movement resources in general, influencing policy and the law, including improving the implementation or enforcement of existing laws is relatively neglected within the effective animal advocacy movement.

Why does the EU have noncompliance issues?

The wider EU political science and legal literature has suggested a number of theories to explain noncompliance in general, not specific to animal welfare laws. There are three major sides in the debate: those who argue the main factor is the degree of “misfit” between the existing legislation in member countries and the new legislation proposed by the EU (Knill & Lenschow, 1998); those who argue there are “cultures of compliance” which are related to the legal traditions and administrative capacity of the state (Börzel et al., 2010; Falkner & Treib, 2008; Falkner et al., 2007); and those who argue that the number of actors in the system with veto powers (legislatures, regulatory agencies, autonomous regional governments) primarily defines compliance (König & Luetgert, 2009). Each of these theories might imply different actions to improve compliance. A “misfit” perspective  might suggest focusing on incremental improvements to narrow the gap between countries before setting a floor with EU standards. A “cultures” perspective offers fewer opportunities for action because it suggests that compliance with animal welfare standards is unlikely to improve without larger structural changes to historically noncompliant countries like Italy. A “veto player” perspective could highlight specific actors that need to be targeted (agricultural ministers, the farming associations, consumers, retailers). Unfortunately, these theories are contradictory and also suffer from using different outcome measures and sample sizes: some measure how late standards were adopted, some measure whether they were transposed into national law, and others attempt to measure how well these laws were implemented in practice (Hartlapp & Falkner, 2009; Kaeding, 2008; Haverland & Romeijn, 2007;  Thomson et al., 2007; Mastenbroek, 2005). This would be a good area for a follow up study.

One may start from the position of why would those working in animal farming ever comply with costly improvements to animal welfare that may put them at a competitive disadvantage compared to cheaper lower welfare products? There are various disincentives that can lead to lack of compliance, including a lack of understanding of the sometimes complex rules, financial costs, cost-benefit considerations, pressure from lobbies, a lack of administrative infrastructure, the burden of paperwork, or a lack of incentives as the cost of compliance might be disproportionate in relation to the level of penalties applied (Börzel & Buzogåny, 2019; Escobar & Demeritt, 2017; Tallberg, 2002).

According to a 2019 survey of Chief Veterinary Officers[13] from EU member states (see figure below), unclear regulations and farmer attitudes are the most relevant reasons for noncompliance in animal welfare (Council of the EU, 2020). After reading various reports from EU audits of national inspections systems these farmer attitudes appear to be that farmers believe that other producers are not following the rules, that farmers do not understand the purpose of the legislation, or they see the proposed measures as incompatible with industrial farming.

The next obstacles are insufficient knowledge, financial constraints, and  “lack of control resources”, which refers to inspections (EU Platform on Animal Welfare, 2019).[14] The same survey showed which enforcement methods were considered to be effective tools (see second figure below), such as national inspections (88%), national audits (76%) and EU audits (80%) (Council of the EU, 2020). Enforcement barriers are, in reality, about failures of member states to properly apply and enforce EU law.

This mostly mirrors a 2013 survey of representatives of national and regional governments, NGOs, think tanks, farmers, farm unions, slaughterhouses, and the processing and breeding industry. The study highlighted knowledge transfer, production costs, public concern, weak inspection frequency and sanctions, and collaboration between government, agri-business, and NGOs as the bottlenecks and supportive measures which determine compliance (Bock et al., 2014).

The EU compliance system

In general, the Commission enacts a directive that member states are entrusted to translate into national laws that define how the directive will be implemented and the Commission conducts audits to check that member states are enforcing the law. The EU Commission is required to make a report to the the heads of state and ministers of member states every 5 years and to make proposals on the progress of legislation. Member states are required to carry out inspections and they report their findings to the EU Commission. Veterinary experts may be dispatched by the EU Commission to make inspections of facilities in member states and audit the national inspection services.

The EU utilises a "management-enforcement ladder": a twinning of cooperative and coercive measures that, step by step, improve states' capacity and incentives for compliance. Increasing enforcement generally involves higher penalties and higher chances of being caught, while increasing management involves transition periods, education about animal welfare practices, and financial incentives. For example, a carrot used is to increase the payments that farmers receive for exceeding minimum animal welfare requirements, while a stick is reducing these payments or issuing fines. We here class the rungs in this management-enforcement ladder as “information”,“transition periods”, “incentives”, “inspections”, “infringements”. This is simply a stylised categorization of a range of activities and tools that are often overlapping and not necessarily concatenate, and are not relevant in each case.  Alternatives to Commission enforcement, such as the delegation of direct monitoring, investigation and sanctioning powers to a specialised EU agency (Collins and Earnshaw, 1992), which increasingly takes place in a narrow band of subject matters such as financial markets, medical technologies, aerospace and fisheries (Scholten, 2017), have so far failed to materialise in animal welfare. One should again remember that a major goal of members of the EU is to protect the interest groups in their countries, of which the animal farming industry may be powerful depending on the country and that animal welfare requirements are often treated as a consumer information or food safety issue.

Information

The most common concern expressed in the Chief Veterinary Officers survey above was unclear regulation. The wording of EU legislation directly or indirectly concerning animal welfare often does not conform with the scientific meanings of these terms. This can lead to confusion and variation in interpretation of the legislation (Lundmark, 2016; Lundmark et al., 2014; Lundmark et al., 2013). Measures that are unambiguous and easily verifiable by one-off inspections of fixed assets such as housing systems plausibly start off from a position of being more likely to succeed than requirements related to the daily management of the animals (feeding, watering, handling, light, etc.). Unlike the design of facilities (cages, stalls), the latter are dependent on the way animals are treated on a daily basis, which requires more inspections, more paperwork, more changes to the behaviour of farmers themselves.  That said, changing to new housing systems often requires costly retraining and management practices too.

Where such ambiguities arise, the Commission seeks to offer guidance documents and training to both farmers and inspectors on proper implementation and application. The effectiveness of such instruments is limited, which is perhaps not surprising since these are recommendations only, and anything that implies going above legal standards can only be voluntary. [15] There are usually no more than 100 participants per Commission training event - many of whom are lobby representatives - so the audience is limited compared to the number of European farmers concerned. It is difficult to assess how much of the content of these events is made available online and how widely is it read. The Commission has now begun setting up “Reference Centres” on certain animal species[16] to conduct research into animal welfare indicators and best practices, and to disseminate this knowledge. It is unclear what impact these networks of research institutions will have, but animal groups we spoke with are somewhat sceptical of how influential the provision of this science-based information will be.[17]

Animal welfare laws rarely include specific enforcement mechanisms, instead deferring to general principles outlined elsewhere. The transport regulation does include enforcement provisions (article 26) requiring a member state that finds a breach to notify the member state of departure and those that granted authorisations or certificates. The purpose is to prevent recurrence of these breaches. However, the required notifications are rarely given in a systematic way and even where they are, the member state who receives the information rarely act on them in such a way as to prevent recurrence of these breaches. As a result the same breaches are repeated year after year (CIWF, 2018). This suggests that even when enforcement provisions are included in the directly applicable legislation there is still the problem of a lack of political willingness to use them effectively.

Transition periods

EU legislation often gives producers a lengthy phase out period when a particular production system is banned is to ensure that producers will, before the ban comes into force, reach the point where their existing infrastructure and equipment come to the end of their working life and would in any event need to be replaced. While we shouldn't expect to see majorities of producers phasing out existing infrastructure and equipment earlier than economically necessary, if producers and authorities take the law seriously we should see evidence that they are not installing new soon to be illegal infrastructure before the deadline. Transition periods have been acknowledged by the Commission to not be very effective however (SEC(2012) 55 final). While long transition times before deadlines or grace periods after deadlines have passed may send a positive signal to industry that they will be given time to prepare and for details to be worked out (Knill and Tosun, 2009; Perkins and Neumayer, 2007), it is just as likely to provide industry with time to lobby for watering down the provisions or extending the deadline.

Incentives

In economic terms, animal welfare is not very important for farmers’ production decisions because while no costs are attached to the degradation of animal welfare, as long as the welfare level does not affect productivity, costs are often associated with improving animal welfare. The EU provides some financial instruments to compensate producers for higher production costs and to incentivize reform. A discussion of the problems in this system and how to reform it merits a much more substantial discussion than can be provided here, so instead we lay out the basics of how the system works today and some issues specific to animal welfare.

The figure below, from a European Court of Auditors report, illustrates the two main economic pillars: Common Agricultural Policy) (CAP) payments are provided directly to farmers primarily to ensure the economic viability of farms but can be reduced if found to be in breach of minimum standards, and additional “Rural Development Funds” can be applied for by member states and farmers to go beyond these minimums (ECA, 2018).  Together direct CAP payments, Rural Development Funds and market related expenditure account for ~37% of the total €160 billion EU budget (EC, 2020b).

The main purpose of CAP direct payments is to provide income support to farmers to compensate them for the public goods and services they provide (minimum of €196 ($227 USD) per hectare), not to directly support animal welfare.  Few countries make use of the CAP tools to address animal welfare objectives[18]. In fact, CAP payments have served to produce large quantities of animal products at an artificially lower cost, encouraging higher consumption. Rethink Priorities researcher Daniela R. Waldhorn calculated how much money the EU transferred to farmers for the production of specific animal products in 2016, as shown in the figure below.

CAP payments (subsidies) are not distributed evenly, such that 80% of the €12.9 billion in payments go to 20% of the 125,000 farms (GogƂoza, 2019). You can see how much a farm in your country received at farmsubsidy.org. Most CAP payments are linked to farmers’ compliance with basic rules for food safety, animal health and welfare, and good agricultural and environmental conditions. However, compliance is not an eligibility condition for payments but only triggers administrative penalties when not respected. “Small” farms (small being defined differently across countries) are not included in these figures as they are not subject to administrative penalties if they do not comply with cross‑compliance obligations. In some countries such “small” farms make up over 50% of farms in a country.

Member states also can draft Rural Development Programs to draw on funds from the EU based on a set of measures set out by the EU. Countries themselves define the conditions applied to the measures included, which may include Measure 14: "promoting food chain organisation, animal welfare and risk management in agriculture", but it is not mandatory. These programs are then approved by the Commission. For the 2014–2020 period, the funds allocated to the animal welfare measure of the Rural Development Funds account for €1.5 billion (1.5 % of the total EU rural development funds), an increase from the €1 billion in 2007–2013 (ECA, 2018). 10 member states have not used the rural development funds for animal welfare in the most recent reporting period. It may be understandable that countries omit animal welfare conditions from their programs altogether because there may not be enough of a market for farmers to transition to higher welfare standards and maintain competitiveness regardless of transition costs being covered, or that countries simply have other priorities when designing these programs. However, even among those who do include animal welfare conditions in their programs a lot of the available money appears to simply be left on the table, as can be seen from the difference in programmed and actual expenditure in the figure below (ECA, 2018). One plausible explanation is simply that some countries do not have the institutional capacity to effectively apply for and distribute these funds in what is often a huge and complicated bureaucratic system.

When Rural Development Funds are drawn upon, the Commission does not check whether the money is going to farmers who were planning to implement such animal welfare provisions anyway even without this financing, nor does the department of the Commission responsible for dispersing funds check with the department responsible for noncompliance to ensure stated requirements are met (ECA, 2018).  In fact, the ECA concluded that the impact of €2.5 billion for animal welfare payments between 2007 and 2020 is not able to even be assessed because the Commission does not have information on the expected or actual results and impact of rural development funds provided for animal welfare. It also seems likely to be the case that EU funds are dispersed by national governments not as an incentive to comply with standards, but as standing payments to favoured interest groups, and so do not actually serve as much of an incentive (Evans & Pegg, 2019; Gebrekidan et al., 2019).  Due to Covid-19, the deadlines for EU countries to submit annual reports on the implementation of their Rural Development Programs have been postponed so we do not know when the most up to date data will be available.

Inspections

Member states translate EU rules into obligations at the farmer level and verify whether these obligations were respected via national inspection agencies. Member states are responsible for putting in place systems which prevent, detect and correct instances of noncompliance, carrying out on‑the‑spot checks, applying penalties and recovering unduly paid funds from farmers who have breached the rules. Except in the area of competition law, the EU has only indirect enforcement powers - the supervision of the application of the law by public authorities (Rowe, 2009). The Commission is obliged to verify that the member states carry out their responsibilities via the Commission Directorate General's Health and Food Audits and Analysis unit (which we will refer to as DG SANTE for simplicity), previously called the Food and Veterinary Office (FVO), and to apply financial corrections when it is found that their systems are deficient. The ECA concluded this cross-compliance system had not been an effective policy (ECA, 2016).

DG SANTE has relatively few resources to ensure standards are being met. While the opportunities for noncompliance have increased over time due to an increase in the size of the EU and the number of laws, the Commission’s enforcement capacities have not. Brussels’ bureaucracy has always been comparatively small, equaling the administration size of a European city of 1 million people such as Cologne (Börzel & BuzogĂĄny, 2019). In 2011 it was reported that there were only nine full time equivalent employees for performing audits and inspections (EC, 2011b), and it may be as low as three individuals today.[19] The coverage of farms is around 1% of agricultural holdings making up 250 days of on-site visits per year (EC, 2013a). To put this in context, if authorities would focus exclusively on the dairy sector, visiting 1% of farms annually, it would take them 100 years to visit all dairy farms in the EU (DG SANTE, 2017). An analysis of DG SANTE audits has shown that the EU has used different standards for compliance inspections in Northern and Southern European countries (Zonderland & Enting, 2006). DG SANTE can point out problems in national inspection services but not correct for noncompliance itself, so it is unclear if increasing DG SANTE visits would necessarily provide better results.

Enforcement of EU legislation falls under the competence of member states, who are better resourced and placed to inspect their own farms than the Commission agencies, but there appears to be a wide variation in the frequency of national inspections, even in high animal welfare countries like Germany (Bundesministerium fĂŒr ErnĂ€hrung und Landwirtschaft, 2015).[20] Some states do not check farms according to risk indicators, even when performing risk-based inspections is an EU legal requirement. [21] Member state authorities usually delegate the responsibility for carrying out the risk analysis for farm and transport inspections to local authorities. None of the member states visited by the ECA by 2018 had put in place systems to check the existence, quality and implementation of the local risk analyses (ECA, 2018). Due to an exemption on inspecting small farms and different definitions of what constitutes a “small” farm, in Eastern European countries where “small” farms make up the majority of the sector, most go unchecked.[22] A 2016 DG SANTE report on broilers found most member states (65% of those studied, which accounted for 80% of the annual EU production of chicken meat) did not have effective and complete systems to monitor, collect and assess information regarding on-farm welfare at  the slaughterhouse level (FVO, 2016). Part of the problem in monitoring compliance appears to stem from a delegation of cross-checking between two levels of inspection. Official inspections by national veterinary services verify the correct application of European Union animal welfare rules while cross-compliance inspections follow up with the application of penalties.

While some states like France carried out “dual purpose” inspections by paying one visit to the farmer and using an integrated checklist of both breaches and penalties, others such as Poland had no formal cooperation between the two authorities. The number of staff available in the competent authorities of the member states to carry out animal welfare inspections has been substantially reduced in some member states in order to cut costs. This may be in contrast to the market-driven mechanisms in Europe, such as voluntary retailer schemes, which may be enforced better than national laws because the retail companies have more people per producer to do the enforcement than the government has (Broom, 2017) and because corporations are subject to regulations on consumer information (such as false advertising), hence corporations come under a much wider scope for inspections.

The Commission and national authorities can also receive information from citizens and NGOs who flag possible cases of noncompliance.  This complaint mechanism has developed into the “chief source for detecting infringements” (EC, 2003). Such NGO data is not considered official data and therefore cannot officially provoke an audit, but it may unofficially do so. For example, the Commission contacted Spanish authorities in light of noncompliance revealed by farm visits carried out by Compassion in World Farming ( Borg,2013 ), a guilty court verdict for Greece may have been instigated following investigations by Compassion in World Farming and other animal welfare groups showing widespread breaches of the slaughter regulation (CIWF, 2009), and the European Parliament debated and published a report on pig tail docking on the basis of petitions[23] filed by Dyrenes Beskyttelse (Danish Animal Welfare Society), and Humane Society International. In 2012 the investigation by Dier & Recht and Varkens in Nood mentioned above led to a debate in the Dutch House of Representatives and questions in the European Parliament (Dier & Recht & Varkens in Nood, 2012). The results of the investigation were also confirmed by a report by the ECA. Dutch politicians discussed the abuses, but no major improvements were made at the time. A second report in 2014 was also discussed in the Dutch House of Representatives alongside clear recommendations. Subsequently, budget and staff cuts to the Dutch Food and Consumer Product Safety Authority were marginally reversed, but still insufficient to ensure adequate coverage of animal farms.

Due to Covid-19 there has been a reduction in the overall number of physical on-the-spot checks and leeway has been given for the timing of inspections (which are often unannounced). This is in order to minimise physical contact between farmers and the inspectors carrying out the checks.  Member states will be able to use alternative sources of information to replace the traditional on-farm visits, such as the use of satellite images or geo-tagged photos to prove that infrastructure investments took place, however, this is not useful for inspections which must be carried out inside buildings. This could mean fewer compliance checks will be conducted during the pandemic, but it could also spur innovation and streamlining of the inspection process.

Infringements

On the national level, payments to farmers, transporters, organisers, and slaughterhouse owners/operators can be reduced, or administrative penalties applied, if they are found to be in breach of legislation. However, national penalties are often not proportionate to the seriousness of the violations. The penalty for the same infringement can vary from 0% to 20% depending on the member state (ECA, 2016).[24] The Commission cannot tell member states what penalties they should impose, but is responsible for ensuring that penalties are “effective, proportionate and dissuasive”. At present penalties are often too low and applied too infrequently to be effective or dissuasive. Eurogroup for Animals has proposed that since sanctions could play an important role in improving enforcement of EU rules, they should be harmonised at the EU level (EC, 2013b, n. 12.2). This option was discarded in EU discussions as it was argued it would either 'under' or 'over' compensate costs, and developing uniform cost models for each infringement would be a very burdensome exercise (EC, 2013b, n. 2.2.1.1.).

In cases that are brought to the attention of the Commission, it can launch (or threaten to launch) infringement proceedings that would bring a member state to the Court of Justice of the EU and possibly incur financial sanctions (e.g., up to tens of millions of euros per semester of persistent noncompliance, plus a compensatory bulk sum, and the legal costs).[25] Emphasis is placed on early compliance through negotiation, with court action and financial penalties meant to constitute exceptions and last resorts. The advantages of a centralised judicial system are clear: it is comparatively well funded and commands a large and experienced legal staff. Across the entire spectrum of EU legislation, the court sides in more than 90% of closed cases with the Commission against the member states (Börzel & Buzogåny, 2019) and the Commission can use the threat of escalation in negotiations with member states, who often back down before a court judgement in as much as 86% of all cases (Toshkov, 2016). This may be due to non-financial costs such as damage to political reputations.

However, infringement procedures are not regarded as the means to bring the best possible enforcement, given disincentives like the huge delays between first warnings and final court decisions as well as the costs per case (Pelkmans et al., 2013). The average number of pending infringement proceedings against an EU country is 25, and the average duration of infringement proceedings is 38 months, while it takes on average 28 months between the delivery of the Court’s judgment and the closure of the case confirming that the member state has complied with the judgment (EC, 2020a). Moreover, the Commission does not pursue all infringements it is alerted to and has wide discretion about using the infringement procedure, even where a member state’s breach of obligations is obvious, and retains the right to terminate the procedure at any point regardless of the member state’s compliance with its demands (Craig & Burca, 2011; Eliantonio, 2016). The number of complaints submitted to the Commission has been rising, but only 4.8% of these led to further investigation by the Commission (De Bernardin, 2019). This is not explained by the use of alternative informal complaint mechanisms (like EU Pilot)[26] instead as complaints there are rising too despite a downward trend in cases through these alternatives too (De Bernardin, 2019).

A study of infringement cases (1978-1999) found that in half of the policy sectors,  there are only a handful of infringement proceedings (Börzel & Knoll, 2012). In the sectors internal market, environment, enterprise, industry, and agriculture, by contrast, member states commit large numbers of violations. Italy is the compliance laggard in virtually all policy sectors while the Scandinavian member states, the UK, and the Netherlands have consistently good compliance records. A more recent study (2003-2014) found some countries, like Italy, Greece, in the past France, more recently Luxembourg, make up every year a disproportionately big share of all infringement proceedings (Toshkov, 2016).

With regard to animals specifically, there have been 71 cases against 24 member states since 2002, 30 of these cases concerned animals used for scientific purposes, 13 were concerning animal health requirements in the trade of  dogs, cats and ferrets, 13 concerning the housing of laying hens and 11 concerning the housing of sows.[27]  62% of closed cases came after the Commission gave just a formal notice of warning, without further steps being initiated. Only 4 countries have been referred to the court for breaching animal-related laws.[28] According to the Commission, these procedures were successful in achieving compliance with the rules (however, without providing detail) (ECA, 2018).The ECA reviewed the Commission’s 2012 to 2015 audit reports on animal welfare in 5 member states, the related action plans for dealing with noncompliance, and their follow-up, and found that these member states addressed almost half of the Commission’s recommendations in two years or less (again, without providing more detail) (ECA, 2018).

However, there also seem to be consistent instances of these “negotiations” and infringement proceedings lasting years or being “resolved” without action being taken by the noncompliant member states. According to the Commission, delays to enforcement procedures in the past have been due to the large number of member states involved (ECA, 2018). The largest number of countries that infringement proceedings were started against at one time regarding animal welfare was 14. This may be concerning given that on the issue of tail docking alone, under the current circumstances, the Commission would have to launch over 20 infringement procedures (considering the majority of member states are evidently noncompliant) (Nalon & De Briyne, 2019). The unwillingness of the Commission to bring such cases against them may mean member states adopt a lacklustre approach to EU animal welfare.

Another legal route is to use national administrative courts to bring action against national inspection authorities and noncompliant producers in order to uphold or revise animal welfare standards, as national courts are increasingly becoming an area for private enforcement (Hofman, 2019). National infringement actions often come with suspensions of activities by the alleged transgressor, unlike EU legal action. There has been relatively little comparative work on how successful this approach is. For the moment it appears that public interest group litigation before national courts to enforce key provisions of EU directives is in principle able to remedy compliance problems, but only if a set of demanding conditions is met (Slepcevic, 2009;Stephenson 2005). There are few examples of this method (although see a case won by the animal welfare group Wakker Dier in regard to provision of newly hatched chicks with food and water under the general farm protection directive). From reading audits conducted by DG SANTE of national inspection services it is clear that national authorities often fail to apply rules as stated in the directive so there may be many promising opportunities for litigation.

Case studies

We now look at how these mechanisms have worked in practice in the species-specific animal welfare directives in the EU. The restrictions on battery cages, sow stalls, and veal crates were all agreed in a similar timeframe and followed a similar structure of over a decade transition period for existing housing infrastructure to be phased out. The restrictions on pig tail docking and broiler stocking density required changes to daily monitoring and environment of animals. These were all species-specific which made it easier to get a sense of the number of animals affected, compared to the general farm protection directive and regulations on transport and slaughter which cover a wide range of animals and harder to validate conditions (like what constitutes unnecessary suffering).

Conventional battery cage ban

Conventional battery cages are systems to house chickens used for eggs production. The animals are tightly stacked together in barren cages in a closed building  with forced ventilation and with or without a lighting system. In 1999, EU countries agreed that no new conventional battery cages should be installed after 2003 and to phase out existing conventional battery cages in farms with more than 350 hens by 2012, but allowed alternative “enriched” cages which have minimum space requirements per caged bird, as well as perches, litter, and a nesting box (directive 1999/74/EC).[29] These allow slightly more movement to hens who are caged collectively, but still limit natural behaviours such as exercising. Note that we do not here make a judgement that so-called enriched cages offer hens a  life worth living or the degree to which they may be better than conventional battery cages without these furnishings.

In 1996, 93% of the 271 million hens in the EU were housed in conventional battery cages (EC, 1998). In an ideal world following the letter of the law automatically, the expected number of hens in such cages would’ve been 0 in 2012. It was estimated in 2006 that there would still be at least 150 million hens kept in conventional battery cages by 2012 (FAWC, 2007). In 2010 this estimate was revised to be 100 million hens still being kept in battery cages by 2012 (Agnew, 2010).  In reality that number was estimated to be 46–84 million (14–30% of total EU egg laying hens) by the time the deadline for the ban came along,[30] which suggests something changed that sped up the transition in the interim for 64–104 million hens (assuming the estimates in 2006 and 2010 were based on reliable data). 13 member states were found to be in breach of the ban in 2012, but by 2013 there were only allegedly 800,000 hens in conventional battery cages (0.2% of total EU egg laying hens) (EC, 2014) and by 2014 there were 0, in farms with more than 350 hens (EC, 2015).

There is not very reliable year-on-year data for the percentage of EU hens in conventional battery cages unfortunately. However, using the limited data available, which includes projections by official sources and numbers reported by media sources, there is a clear downward trend. Note that in the 10 years between 1996 and 2006 there was a 17% reduction in conventional battery caged hens, while after 2010 there were similar or higher rates of reduction within a single year. This is slightly confounded by the addition of numerous countries into the EU who had majority battery cage systems in 2004.

The rather sudden drop in the share of hens in conventional battery cages within a matter of months—and if not, then within a couple of years—does raise the question as to whether the numbers were fudged. It certainly would not be the first time a member state has massaged data to meet EU requirements (Carassava, 2004). However, the significant increase in shell egg prices in the EU following the deadline,[31] the drop in egg production,[32] and the decrease in the number of hens[33] in this period does suggest that countries really were transitioning.[34] A similar trend occurred in Germany prior to its own 2009 national ban on conventional battery cages (O’Keefe, 2012a).[35] A confounder is that the EU entered a debt crisis in this period and so we may have expected to see falls in production and some farmers going out of business anyway. The reality of the transition was of course made possible by the mass culling of layer hens by noncompliant producers and the closure of many farm operations.

One might ask why did countries take so long to act, if indeed it only took them a few years to abolish the practice? On the other hand, a farmer transitioning before the existing conventional battery cages reached the end of their normal productive lifespan and before a competitor did so would mean incurring costs and risking a competitive disadvantage years before it was necessary. Maybe we should instead ask why there was progress at all before 2012.

In 2008, 278 million hens were in cage systems, and only 20 million of these (7%) were in enriched cages (Poultry Site, 2009). One can see below that the countries which had the lowest share of their hens in conventional battery cages in 2008 did not simply have the same share in “enriched” cages by 2018, but rather increased the share of hens in cage-free systems. On the other hand, countries which had the highest percentage of their hens in conventional battery cages in 2008, and thus the largest change to make to meet the 2012 deadline, still have a caged-housing system for the majority of hens 10 years later. This is despite an assumption that because enriched cages are more expensive, it makes it less profitable for producers to keep hens caged rather than cage-free.

We can also see below that the share of chickens in cage-free systems increased dramatically from the mid 2000s. This was both the time when a mandatory egg production labelling law (Regulation (EC) No 589/2008) came into place (egg packs must carry one of the following terms: ‘free range eggs’, ‘barn eggs’ or ‘eggs from caged hens’), but also when the EU expanded to a set of Eastern European countries with very high shares of conventional battery caged hens. Since these new Eastern European countries that joined in 2004 still had high shares of hens being kept in battery cages in 2008 and enriched cages in 2018, they cannot account for the increasing share of hens in the EU that are cage-free. So the change in EU cage-free hens must almost entirely be driven by those countries shown above as early adopters of cage-free systems (Austria, Denmark, Germany, the Netherlands, Sweden, UK). The mandatory labelling may then have played a large role in increasing the share of hens in cage-free systems but it is unclear what role it played, if any, in increasing the share of hens in enriched cages rather than conventional battery cages.

So whatever X factor (retailer-led product differentiation, public concern, corporate campaigns, political leadership, egg labelling) led to the increase in cage-free hens in the mostly northern countries (Denmark, Sweden, UK, Germany, the Netherlands) still hasn't occurred in the rest.[36] This at first glance appears to offer good evidence that legislation created improvements for millions of hens in Southern and Eastern European countries that would not otherwise have come about due to the factors driving cage-free housing in the other countries.[37] The question for those interested in compliance is to what extent, if any, additional actions beyond simply enacting legislation increased the speed or scope of compliance with the legislation.

Information

Initially, in 1999, the Commission had agreed to confirm which housing systems would be acceptable and give a definitive date for implementation of the ban by January 2005.[38] However, this did not come until January 2008 (EC, 2008), after campaigns to keep the ban from Compassion in World Farming and members of the European Coalition for Farm Animals (ECFA) (CIWF, 2008). Ambiguity about the commitment to the standards at first glance seems to have been a powerful force in leading many countries to miss the deadline. A 2004 report provided to the Commission details that in almost all EU countries there were virtually no hens in enriched cage systems and this stemmed from uncertainty about whether and in what form the laying hens directive would be confirmed (AGRA & CEAS, 2004). A UK Farm Animal Welfare Council report specifically noted that the delay in the Commission’s report “has meant that the industry has not felt sufficiently confident to make the commercial decisions necessary to invest in alternatives to the conventional cage system” (FAWC, 2007).

Transition period

Existing conventional battery cage buildings were assumed to have a productive lifespan of 30 to 40 years and so even a 13 year transition period would cause substantial costs for egg producers who had recently installed new conventional battery cages. Many farmers were simply reluctant to make the investments and incur the costs of compliance early on, only to find themselves undercut by competitors who did not and could sell cheaper products. The biggest enemy of farmers are not animal groups, but their neighbours. Many were hoping the egg industry would successfully lobby for the ban to be delayed. However, the lateness of the Commission’s report put huge demand on the manufacturers of compliant cage systems that likely simply did not have the capacity to deliver and install cages so that every country could be compliant by the deadline.

Contrast this to the situation of Austria, Germany, the Netherlands and Sweden which instituted earlier national bans and were already in compliance with the EU law by 2012.[39] It is also apparent that countries that were transitioning earlier were able to benefit from a market of noncompliant countries by selling conventional battery cage hardware to producers waiting to transition later (AGRA & CEAS, 2004). However, even if in 1999 the Commission had made a binding commitment to maintain the deadline and given clear information on acceptable alternatives to conventional battery cages from the beginning, why would farmers have transitioned any earlier than absolutely necessary?

Back in 2004, industry was already assumed to make the switch to enriched cages as close to 2012 as possible (AGRA & CEAS, 2004). Note again that in 2008 many countries had upwards of 70% of hens still in conventional battery cages when the Commission confirmed that the 2012 deadline would not be postponed. This gave countries four years to comply. Given the productive lifespan of approximately 13 months for egg-laying hens, in order for a flock to be fully compliant by the deadline birds would need to have been housed in compliant cages no later than the end of 2010. DG SANTE reports from 2012 reveal that after 2009 many countries began training programmes for farmers and compiling registries of housing systems.

However, the number of countries found to be noncompliant, and decreases in the number of laying hens in certain countries between 2011 and 2012 suggests many producers were still putting new birds in conventional battery cages after 2011 suggesting they had no intention to comply with the law. Some countries were quite persistent in their efforts to find a way out, continuing to allow new conventional battery cages in 2011, even though this was supposed to have stopped in 2003.[40] In 2005, pressure was already being applied by several southern European countries to extend that deadline until at least 2017 and even as far as 2022 (FarmingUK team, 2005). Poland spearheaded an effort even in 2010 for the Commission to grant extensions until 2017 (Berkhout, 2010), but already compliant member countries, pressure from animal groups on these (mostly southern and eastern) soon to be noncompliant countries, and a resolution from the European Parliament (EP, 2010) contributed to the Commission sticking to the deadline. This might suggest that pushing a key number of countries to adopt their own earlier national bans could create the internal pressure the Commission needs to hold fast on deadlines. This is a hypothesis a future report will discuss in more detail.

Incentives

Given that many member states had more than 70% of their hens in conventional battery cages in 2008 (as shown in the chart above) and the EU entered a financial crisis in the years before the deadline, it may not be surprising that many countries missed the deadline. Higher production costs have been cited as one of the major obstacles in adhering to EU layer welfare standards before the crisis (Van Horne & Achterbosch, 2008; Van Horne et al., 2007; Van Horne & Bondt, 2006). Eggs were viewed as an excellent source of affordable protein and governments in poorer countries (such as Romania, where the average family income was €250 per month) were reluctant to enforce the ban so as to avoid creating further volatility and potential food shortages locally (Chippindale, 2010). The low market demand for higher welfare eggs in some member states had been a commercial disincentive for early adoption for producers (House of Commons, 2011), while in countries that transitioned earlier (Germany and Austria) retailer schemes were already in place to facilitate consumer awareness  of and demand for higher standards for hens.

In refusing requests to extend the deadline, the Commission specifically proposed to the Polish authorities that they use the existing possibilities within the rural development programmes for bringing housing systems into line with those standards by that deadline. It is certainly the case that some countries offered transition assistance (such as Spain and Portugal (Hanson, 2012) France,[41] Italy, [42] Belgium[43]) and EU Rural Development Funds for upgrading the rearing systems for laying hens were made available, but only some member states (like Ireland[44] and Bulgaria[45]) used them for better compliance with the legal requirements. The reason for the apparent reluctance of member states to draw on this fund and tie payments to animal welfare measures is unclear, but suggests there was money being left on the table (CIWF, 2011b; ECA, 2018). And even countries where producers did make use of financial assistance did not uniformly meet the deadline.

Inspections

The Commission was reluctant to deploy its limited inspection resources on checking compliance until two to four years before the deadline (the latest time by which countries could have put hens in conventional battery cages and still be in compliance by 2012). The data provided to the Commission by member states at the end of 2010 was “far from optimal” in the words of Joanna Darmanin, Head of Cabinet, Directorate General Health and Consumers, but the Commission has no power to penalise those member states that had failed to provide the required data, and simply requested sufficient information about the state of play before April 2011.[46]

Commissioner Dalli said inspection teams were ready to go “all out” from January 1, 2012 with increased surveillance targeted at noncompliant member states based on submitted lists of compliant and noncompliant producers (EC, 2011a). Reviewing the DG SANTE reports from 2012, nine countries were visited after the deadline,[47] though not all of these were listed as noncompliant so it is unclear whether the inspections themselves or fear of inspection actually induced compliance, if they did at all. Reportedly inspections of the 13 member states that missed the deadline were postponed because they would only have proved what these countries had freely admitted (FarmingUK Team, 2013).

DG SANTE reports detail how inspections by some national authorities were stepped up in the years immediately before and after the deadline. This included intensive monitoring, enforcement notices, and good cooperation between inspection authorities. In the case of Romania, enforcement was achieved solely through inspections without the need for sanctions, while in Bulgaria a large number of inspections was not enough to ensure compliance until sanctions were later imposed. It is also notable that in countries instituting earlier national bans, such as Sweden, the inspection systems were strengthened too (AGRA & CEAS, 2004).

Animal welfare groups also highlighted noncompliance with the ban. Noncompliant producers were found in 2012 by Association for the Free Rearing of Hens (L214) (Lewis, 2012) and Vier Pfotens (PW Reporters, 2012), while Compassion in World Farming demonstrated that operators in Greece were still flouting the ban in mid 2014 (Clarke, 2014).

Infringements

Between 2008 and 2010, DG SANTE audited 20 member states and examined the state of enforcement of the ban by national authorities (EC, 2011c). Whilst all member states had mechanisms to do so, some had not imposed sanctions on noncompliant producers or had imposed fines that were not financially onerous (ranging from the low hundreds of euros to tens of thousands).[48] It was worthwhile for producers (in Italy and Poland) to pay the fine because the profit was so large from the sale of the additional eggs produced by overstocking. In other countries there were unwritten agreements not to issue sanctions to farmers (Hungary) or a reluctance to impose large fines that would be contested in court (Malta, Romania). Subsequent DG SANTE reports in 2012 and 2011 show that some countries had increased the fines to dissuasive levels or imposed other financial penalties (Bulgaria, Netherlands, Slovenia), but others continued to issue only low penalties (Latvia, Italy). Other countries took more forceful measures such as using police to ensure illegal eggs went to rendering plants, reclaiming profits resulting from overstocking in unenriched cages, and threatening and practicing the impounding and culling of hens.

Apparently the Commission had been in a state of denial. It was quoted as saying “we are not prepared to contemplate that people will not have converted. We think they all will” and that only after member states had submitted data which demonstrated the state of noncompliance will they “start to kick it into high gear and have a strategy on how to deal with it” (House of Commons, 2011). The Commission then had few options on the table, including delaying the deadline, creating a new labelling code for “illegal” eggs, increasing inspections and beginning infringement proceedings, and an internal trade ban.[49] The Commission faced pressure to stick to the deadline from already compliant countries and from animal groups, like Compassion in World Farming’s “Keep the Ban” and “the Big Move”[50] campaigns in addition to a network of animal welfare groups in the European Network for Farm Animal Protection. Legitimising illegal eggs through a new egg label struck most as counterproductive. Despite WTO rules not providing for a ban on imports due to animal housing systems, an intra-community trade ban did appear to occur. The Czech Republic and Bulgaria effectively banned Polish egg imports because of the latter’s failure to conform (Poultry Site, 2012a, 2012b), and the UK reached a voluntary agreement with business not to sell illegal eggs[51] and on the use of UV light to scan for illegal egg imports (Gov.uk, 2011; Poultry Site, 2011).[52] EU countries informally made a non-binding 'gentleman's agreement' that national authorities would ensure all noncompliant eggs were broken, processed, and only used within the country of origin for processed products.

Once the deadline passed the Commission was quick to issue warning letters to the 13 countries not enforcing the ban (and giving them a six month grace period). By the end of that summer all but a few member states were compliant. Compassion in World Farming’s “Defend the Big Move” campaign highlighted continued breaches by Italy and Greece after the deadline had passed. In 2013, the Commission brought Italy and Greece to court, where around 20 million hens still remained in conventional battery cages. Both were found guilty in 2014 but in the end only had to pay legal costs, not financial penalties (CIWF, 2014; WATTAgNet, 2014) (possibly due to the financial crisis). The cases against them were not formally closed until October-November 2015 suggesting battery cages may have remained in use there for almost 4 years after the deadline.

Impact of enforcement

How many hens would have “automatically” ended up in compliant housing systems simply from the law existing, absent further enforcement actions? We can clearly see that there was indeed pressure by industry to postpone the deadline and producers were still being granted and installing the soon to be illegal cages even past the latest possible time one could do so and meet the deadline, suggesting they hoped to continue raising hens in battery cages for quite some time after 2012, and Poland had asked for a 5 year postponement. Approximately 33 million birds were culled 2011-2012,[53] and since it is unlikely producers would intentionally have begun raising birds they expected to be slaughtered before reaching the end of their productive lifespan we can suggest that at least these 33 million would have remained in battery cages if not for enforcement (or threat of enforcement) of the ban. A further 46–84 million hens were still in battery cages after the deadline passed and either reached the end of their planned productive lifespan, were transferred to other housing systems or were culled by 2014. Up to 20 million of these hens remained in conventional battery cages in Greece and Italy up to 4 years after the ban despite escalating EU legal action. When Compassion in World Farming exposed illegal Greek cages in July 2014, it suggested the producers were planning for another 18 months of cage production (taking them up to January 2016) (Clarke, 2014). It seems plausible some if not most noncompliant producers in these countries were simply allowed to remain noncompliant until the end of the productive lifespan of their existing battery cage installations. The other 26-64 million hens outside of Italy and Greece then may have remained in battery cages for a similar time if not for some effect from the intra-community trade ban, pressure campaigns from industry and animal welfare groups, increased inspections, increased fines, and infringement proceedings launched by the Commission.  It seems plausible then to think 33 million to 97 million hens (33 million culled before the deadline plus the upper estimate of 64 million post-deadline) would not have automatically been in compliant housing simply from the law existing. This is very roughly 9%-27% of the 365 million or so egg-laying hens in the EU per annum at that time.

The pigs directive

The first EU-wide rules on pig welfare were established in 1991 (directive 91/630/EEC) and enforceable since 1994 to curb the practice of tail docking, which is commonly used to prevent pigs biting each other’s tails. This was followed by a 2001 directive (2001/88/EC) requiring a phase-out of the use of individual stalls for pregnant sows by 2013, except for the first four weeks of gestation and one week before farrowing. The pigs directive (2008/120/EC) consolidated minimum standards for the protection of pigs, the prohibition of the tethering of sows, banned routine tail docking, established requirements for environmental enrichment for pigs and sought to improve the flooring surfaces on which pigs are kept. We take the sow stall restriction and tail docking restriction in turn.

Sow stall restrictions

The 2001 directive (2001/88/EC) laid out that no new individual stall housing systems were to be installed after 2003 and existing infrastructure was given a ten-year transition period until early 2013. From 2013, all pregnant sows in the EU were to be housed in loose group systems rather than individual stalls from four weeks after “service” up to seven days before expected farrowing

In 1998, the average percent of breeding sows in 13 EU countries in individual stalls was 45%, but all the major producers used this system for more than half of their pigs. The use of stalls was actually increasing as producers switched to stalls in advance of an EU ban on the use of tethers due to come into force in 2006 (CIWF, 2000).[54]  By 2010,  in Germany and Denmark, both large pig producers, 50%-80% of pig producers were estimated to be noncompliant, with other countries assumed to be in worse positions (Schulze zur Wiesch, 2010). The Commission also claimed that it had learned the lessons from the problems then unfolding in noncompliance with the conventional battery cage ban, and an implementation plan included “all the tools available at EU level are being used to put pressure on the member states so they comply by the legal deadline” including data collection, stakeholder meetings, providing information about financial support, training veterinarians, and preparatory work for infringements (EC, 2012).

While the UK, Sweden, and Luxembourg were compliant well ahead of the deadline due to earlier national laws restricting stalls, when the January 2013 deadline passed as many as 22/27 countries were noncompliant (see figure below from countdownto1-1-13.co.uk, which was set up by the British Pig Executive to monitor compliance)  though ~6 of these countries were at least 90% compliant. Reportedly 2 million to 5 million of the 13 million sows in the EU would be in illegal individual stalls,[55] including ~52-67% of sows in Germany and France which were two of the largest pig producers in the EU.

In February 2013, Commissioner Borg demanded member states to provide regular updates of relevant data and Farm Ministers to apply dissuasive sanctions to noncompliant producers (Pig333, 2013). In the space of a few weeks from December 2012 to February 2013, rates of compliance shot up dramatically by an average of 18% but by more than 30% in some countries. However, the UK National Pig Association (NPA), a trade association for the pig industry,  claimed that “some countries such as Italy and Spain have convinced the commission that they are compliant when we know discussions with their own producer groups suggest that’s not the case” (Case, 2013) and  a member of the UK National Farmers' Union visited a supposedly compliant pig farm in the Netherlands and discovered that sows were not being kept in groups as required by the legislation (FarmingUK Team, 2013) so it is possible some of these numbers were manipulated.

Transition period

In 2010, the pig industry, and especially Southern and Eastern countries, had sought an extension to the 2013 deadline but was refused by the Commission (PigProgress, 2010; WATTAgNet, 2010). However, even producers in countries with typical higher animal welfare standards, such as Denmark,  had been hoping for a delay (SYSADM, 2009). In 2011 it was reported that many producers in the EU had still not even started planning for the transition to “loose” housing systems, with producers in Germany claiming that implementation instructions had not been provided (Abbot, 2011; Schulze zur Wiesch, 2010). In order to comply, farmers could either decrease the numbers of pigs in farms to create more space, make large capital investments to extend existing or construct new buildings in order to maintain the same amount of pigs at the farm, or choose to stop farming pigs altogether. At that stage the conversion was no longer worthwhile for many piglet producers who may have wanted to get out of production in four or five years anyway. Pig herds were reportedly shrinking in the 12 months prior to June 2012 in all main pig producing countries (FarmingUK Team, 2012),[56] and one reason is likely that during the changeover to group housing, many companies no longer invest in new pigs or drop out of the market, so that the inventory drops significantly. Again it seems however, many producers and authorities continued business as usual during the transition period with no serious intention to be ready for the deadline.

Incentives

We found limited to no evidence of financial incentives used to promote the transition. One region in German provided funds for the switchover, but was found to still have noncompliant producers in 2013, (ImhÀuser, 2012) while industry associations in the Netherlands were refused financial aid for the less than 10% of producers who were still noncompliant in 2012 due to financial problems or lengthy approval procedures (SYSADM, 2012). Many producers across the EU cited difficulties in obtaining financing as a reason for a lack of investment in compliant housing (The Pig Site, 2011).

Inspections

DG SANTE visited 5 countries in 2010-2012,[57] and found evidence in 4 that compliance would not be met in time and in the one country where authorities were confident compliance would be met (Hungary) it would later be found noncompliant.  In April 2012 the Commission was informed by 16 member states that they would be compliant by the deadline (EC, 2012) although Compassion in World Farming suggested the true number was closer to 10 with a few countries not even able to provide data (WATTAgNet, 2012) (in the end only 5 were compliant). Commissioner Dalli informed the Agriculture Council in June 2012 that at least nine countries would miss the deadline. The Commission stated it would only take action after the deadline had passed and it was clear which countries were noncompliant (Abbot, 2012). Belgium, Hungary, Spain and Portugal had not had an inspection to establish that they were compliant by the deadline and none were scheduled for 2013, despite being noncompliant (FarmingUK Team, 2013).

The UK NPA warned that some European countries “do not have the necessary infrastructure” to identify law-breaking farms (FarmingUK Team, 2012). The Dutch authorities began checking for compliance in mid 2012 (ImhĂ€user, 2012), but had insufficient capacity to ensure wide coverage and the fines for violations were low. In Spain no national level farm inspection data was collected and sanctions were not always dissuasive, while Polish authorities in contrast conducted almost 2,447 inspections and achieved close to 100% compliance some months after the deadline (Bock et al., 2014). Further details on inspections in other countries are lacking due to the few EU audits conducted.

Infringements

There were no EU-wide measures in place to stop the trade in illegally produced pigmeat. Despite the Commission warning against such trade bans, EU Commissioner Dalli did meet with major supermarkets to discuss refusing to sell pigmeat from illegal producers (Abbot, 2012) and the UK food association agreed to essentially ban the import and selling of pigmeat from illegal producers in the EU. The UK National Pig Association launched a Wall of Fame & Shame campaign to highlight noncompliant producers and Compassion in World Farming also lobbied for enforcement of the ban via the Project Pig campaign, monitored breaches and made formal complaints to the European Commission. The UK National Pig Association seems to have been very active pressuring the EU (Deter, 2013; Henning, 2012) with many of its producers already being compliant since sow stalls were banned in 1999 due to national legislation. Even in Germany, which was found to be 30% noncompliant, the German Farmers' Association (DBV) in early 2012 called for the EU-wide implementation of the required conversion  (ImhĂ€user, 2012).

The threat of infringements was raised in June 2012 as well as a reminder that funds were available within rural development to support companies in the changeover (Deter, 2013). In August 2012 the Commission had floated the idea of a 36-month grace period for applicants for aid to convert to loose sow housing. While this was not officially adopted, given the lengthy process for infringement proceedings many countries were given a de facto extended transition period. At the end of February the Commission launched infringement proceedings against nine countries[58] while another five[59] were placed under investigation.  Eight months after the deadline passed only 13/28 countries were compliant (Robinson, 2013) and the following year six were still noncompliant and sent warning letters by the Commission (CIWF, 2014b).[60] In January 2014 France, Belgium, Greece and Cyprus received a final delay of two months from the European Commission to remedy the situation (Deter and ImhĂ€user, 2014). By January 2015 the Commission confirmed that “no further official steps have been taken against any of the non-compliant member states” (Haris, 2015, Pig Progress, 2014). Looking at the official log of infringement cases, one can see that the case against Cyprus was closed in April 2015, Slovenia October 2015, Finland in February 2016, Greece November 2016, and Belgium in February 2017. The case against France then presumably remains open, however, it is not listed in the official database. Cases against Hungary, Italy, and the Netherlands were never launched but they have also never been confirmed to be compliant so these are likely the cases the Commission is still substantiating.

Impact of enforcement

The counterfactual asks us to try and imagine a world in which the sow stall partial ban existed but there were no enforcement actions taken. Producers were given 12 years to prepare in 2001 and reportedly existing stall systems had a natural commercial life of 12-20 years[61] so any producer installing new individual stall systems after 2001 was likely hoping for a postponement of the 2013 deadline to ~2020 (which in fact was what the industry was calling for in 2010).  Given that it was reported in 2011 many producers had not begun planning for the transition, we can imagine first that if the 2013 deadline was not enforced many pregnant sows would have remained in individual stalls for much of their life until ~2020.

The approximately 640K breeding sows in UK, Luxembourg and Sweden[62] were unlikely to be affected by any enforcement related to the EU ban since national bans existed in those countries. Austria and Estonia were fully compliant in time despite no national bans so the additional 270K sows might be considered “automatically” in legal group housing by the deadline. Approximately 4 million sows were set to be in illegal individual stalls after the deadline.  How many of these could one plausibly estimate would have continued to remain noncompliant without enforcement actions? Many smaller Eastern member states were not considered to be a major issue as they had few large-scale producers and many of them did not use stalls anyway (Deter, 2013). Just six countries held 82% of noncompliant sows (Belgium, France, Germany, Poland, Spain, and the Netherlands) so these are likely the most important countries to understand.

In Germany 1.1 million sows were illegally housed representing more than half of German pork producers, a problem especially prevalent in farms with fewer than 100 animals. They were the subject of media scrutiny for noncompliance from two large German media outlets Spiegel Online and the ZDF magazine "Frontal 21" that used undercover videos made by Animal Rights Watch to demonstrate and criticise the state of noncompliance in February 2013 (Deter, 2013). In that same month the Commission began infringement proceedings against Germany due to then 30% of producers being noncompliant. By October 2013, German inspection authorities were issuing fines to bring the last remaining noncompliant producers into line and avoid further EU infringement action (Deter, 2013) and an estimated 20% of farms in just one region chose to shut down rather than convert (ImhĂ€user, 2013a). By December, 99% of farms were estimated to have converted (ImhĂ€user, 2013b) and state authorities had closed 15 companies that had not converted during inspections (Top agrar, 2013).  We could find no English or Spanish language reports on Spanish enforcement but it was no longer listed as noncompliant after August 2013. In Poland, 35% of pig farms year were still noncompliant one and a half years before the deadline but a huge scale up in inspections brought the country into compliance by June 2013(Bock et al., 2014).

In 2011 the EU audit claimed Belgium was "pursuing a positive, pro-active approach to the issue of group housing for pregnant sows" despite surveys showing half of sow producers had no plans to convert and were delaying converting until the last moment (Tuyttens et al, 2011). The case against Belgium was not closed until February 2017. The status of France and the Netherlands is still outstanding, as it is for Hungary and Italy. A majority of Dutch producers had been planning to delay as long as possible (Hoste and van der Peet-Schwering, 2008) and it was noted that there was "only a small chance of being fined, and the fines for violation are low" (Bock et al., 2014).  It seems possible then that the 1.5 million sows held by these latter five countries in illegal housing when the deadline went into action simply let producers continue until the planned end of their facilities/sows productive lifespan. This leaves another 2.5 million sows that were brought into compliance mostly within the year. If we take the 1 million sows affected by the clear German enforcement actions as the lower bound of the effect of enforcement, and 2.5 million as the upper bound, then enforcement action affected 8%-19% of sows in the EU.

Tail docking and enrichment materials

Tail biting is the result of multiple factors including the characteristics of the pigs themselves (e.g., sex, genetics) and management (e.g., confined spaces, feeding problems, lack of materials to manipulate) and causes suffering for the animals from pain and stress and as well as economic costs due to infections. Tail docking is often used as a blanket method to prevent tail biting in the first place. Tail biting can also be reduced by reducing stocking density and providing materials for the pigs to explore and manipulate with their mouths.

The EU partial ban on tail docking has been in force since 1994 stating that

“no tail docking must be carried out routinely but only when there is evidence that injuries to other pigs’ tails have occurred as a result of not tail docking. . . [and] . . . all pigs, taking into account environment and stocking density, must be able to obtain straw or any other suitable material or objects”.

The requirements were strengthened and codified in 2003 and 2008 through the pigs directive, which reiterated that tail docking must not

“be carried out routinely . . . [and] . . . before carrying out these procedures, other measures shall be taken to prevent tail-biting and other vices, taking into account environment and stocking densities. For this reason inadequate environmental conditions or management systems must be changed . . . [and] . . . pigs must have permanent access to a sufficient quantity of material to enable proper investigation and manipulation activities, such as straw, hay, wood, sawdust, mushroom compost, peat or a mixture of such, which does not compromise the health of the animals.”

However, more than 25 years after the first law, various reports in recent years estimate producers in only a couple of member states make reasonable alternative efforts to reduce tail biting before opting for tail docking. Based on numerous sources it appears that as many as 132 million pigs (90% of EU total) are tail docked, with the average share of pigs in an EU country being docked at 78% (median 92%), and the average for pigs with insufficient enrichment materials was 35% (median  40%) (De Briyne et al., 2018; Edman, 2014; Nalon & De Briyne, 2019; van Zanen, 2016).[63]

What is a “reasonable” share of pigs to be tail docked for veterinary or other health reasons? The EU countries with no historical traditions of tail docking and/or  that instituted national bans on the practice (Finland, Sweden, Lithuania),[64]  even before the EU regulation came into force, have less than  5% of pigs docked. Both Sweden and Finland have a higher legally required space allowance for pigs than stipulated in the EU directive which likely leads to less tail biting in the first place. Norway and Switzerland (countries outside the EU) have also brought the prevalence of tail docking down to 5% or lower by reducing the density of animals and providing enrichment materials and banning all tail docking suggesting EU laws are not necessary to achieve this rate of tail docking and may not have even played a role in the three EU countries with low rates. Austria, Denmark, Estonia, Germany, and Slovenia have stricter national laws than the EU directive, but fall short of a complete ban and still have high rates of tail docking.

Tail docking laws in Europe

Information

A major issue with this case is that it may be less a case of a lack of enforcement than the unenforceability of the measure itself. The requirement is so vaguely stated and so partial in nature that the gap between what compliance means likely differs for farmers, veterinarians, and animal welfare groups. A key point worth noting is that EU legislation requires only a “sufficient” quantity of material and only bans “routine” tail docking, leaving a lot of room for ambiguity of interpretation and application.[65] The Commission itself reports that many countries are still routinely and systematically tail docking, but does not specify what frequency of tail docking reaches the threshold of being considered routine nor what stocking density levels are required to reduce the incidence of tail biting. Animal advocates told us they pursued a total ban on tail docking, like in Finland, and Sweden, but were unable to secure it due to industry pushback. It is clear from the high rates of tail docked pigs that countries and producers have used this wiggle room to the greatest extent to widely ignore the spirit of the ban. While the Commission issued non-binding guidelines, materials and information in 2016 (almost a decade after the entry into force of the pigs directive) clarifying enrichment materials as edible, chewable, investigable, and manipulable, there is not much evidence that this has brought meaningful changes. Recommendations can only suggest measures that go beyond the standards already set in the directive. Producers can go beyond the legal standard voluntarily, but the Commission cannot force them to do so. For the ban on "routine tail docking" to be properly complied with as animal welfare advocates would understand (5% or less of pigs tail docked), producers would have to go beyond legal standards; but one cannot force producers to do better than what is mandated in the law.

Some statements from DG SANTE report that farmers are practicing tail docking only when it is necessary, however a telephone survey of 520 Dutch pig farmers showed they had an overall negative attitude and viewed tail docking as essentially always necessary in intensive pig farming to prevent tail biting (Bracke et al., 2013). This suggests that actions will not be voluntarily taken by farmers and that an understanding of how to manage tail biting without tail docking is lacking or unenforceable under the current language of the directive.

Incentives

The perceived economic disincentives to significantly reducing rates of tail docking and tail biting at the same time are clear: changing management systems is a costly investment, and measures to be considered before tail docking, such as a reduced stock density and the provision of manipulable materials, can eat into profits much more than one-off fixed asset expenditures as they permanently increase the cost of production. While costs of enrichment are perceived as high in those countries where tail docking is carried out on a majority of pigs, in Sweden where tail docking is virtually absent, such materials represent 0.25%–4% of costs (EC, 2016). It is not clear that finances are the main hurdle, but so long as there is basically no penalty for high rates of tail docking, we should expect that farms won't pay even a small amount to reduce the practice.

Even in countries using EU Rural Development Funds for pig welfare, pigs had their tails docked and did not have access to sufficient enrichment material. The Commission does not use the information on areas of widespread tail docking to challenge member states with regard to their use of these funds in those areas. Germany used the Rural Development Funds to provide a “Curled Tail Bonus” to incentivise lower rates of tail docking and while most pigs had intact tails in farms that received this bonus, they often were organic herds or part of an existing welfare label and therefore already reared pigs with intact tails before entering the programme (EC, 2016; ECA, 2018).

Inspections

DG SANTE audits conducted in 2000 showed most countries still practiced tail docking on the vast majority of their pigs but the Commission did not systematically collect information on tail docking for the subsequent decade[66]. Between 2016 and 2017 the Commission surveyed countries on the prevalence of tail docking but countries were not able to provide reliable data and progress on implementation was deemed to be limited (EP, 2019). For example, in Spain, the largest pig producer where 98.5% of pigs were tail docked at the time, national authorities appeared to be underreporting compared to what the Commission audits found in its own 2017 audit.

Even the Commission’s own investigations, when done, often failed to follow up on previous findings of widespread tail docking and offered different recommendations for member states with the same insufficient enrichment materials. However, even after being alerted to issues of tail docking by both DG SANTE, Animal Equality, and Compassion in World Farming, Spanish and Italian authorities took no action (Animal Equality, 2018; Waldhorn, 2018). CIWF’s  investigation in Ireland found widespread tail docking and unsuitable enrichment materials for pigs and led them to write to the Irish, UK governments, the European Commission, and the European Parliament, but as yet it is unclear what action has been taken.

Infringement

National authorities appear unwilling to issue severe, if any, financial penalties for tail docking, which again we should perhaps not be surprised by since tail docking per se is not a fineable offence. In almost all of the 2017–2019 DG SANTE country-specific reports on tail docking, the occurrence tail docking is simply not pursued as noncompliance by national authorities and no actions have been taken other than defining general compliance criteria, irrespective of the official financial penalty amount. In June 2018, the Commission performed a detailed assessment of the content and quality of the 26 Action Plans submitted by member states the Commission had requested in 2017. The action plans are not easily accessible so we do not know the content nor when they were completed, but it is reported that there was a wide variation of responses: from almost complete, to ones with very limited content (EP, 2019).

The Commission has thus far adopted a management-based approach[67] by providing e-learning tools, guidance documents, and setting up a reference centre on pigs to disseminate best practices. Terence Cassidy, head of the Animal Welfare Sector at the FVO in 2014, stated in an interview that the FVO prefer to work with the member states rather than to take them to court (Edman, 2014). The Commission even closed a complaint in 2010 issued by Compassion in World Farming against Ireland and stated “the Irish authorities are making concerted efforts to apply the prohibition on routine tail docking and the requirement to provide manipulable material”, yet three years later CIWF investigations revealed 100% of pigs in Irish farms visited were tail docked (CIWF, 2013) (it is unclear how representative the farms visited by Compassion in World Farming are of the entire Irish pig farming system). In numerous replies to petitions about high rates of tail docking, the Commission reiterated its position that it did not intend to launch infringement proceedings nor to propose amendments to the directive, as they would not “be the most effective instrument to improve compliance" (despite launching infringements for failures to comply with the housing requirements in the same Pig directive) (Marzocchi, 2014). However, the Commission may have recently begun to open to door for infringements, stating that it was considering enforcement options “including the possibility of infringements against certain member states whose Action Plans do not contain measures to improve compliance with legal requirements” (EP, 2019). Whether there will be pressure on the Commission to act on this is unclear. It is important to note that unlike the conventional battery cage ban, there is not a significant number of powerful EU countries that are already compliant. Pushing countries with otherwise high animal welfare laws like Denmark, the Netherlands, and Germany to become compliant might create the internal pressure needed for the Commission to act. However, revising the law to ban all tail docking is likely more effective.

Impact of enforcement

There appears to have been very few concrete actions taken to reduce tail docking rates and increase enrichment materials to the levels animal advocates and veterinarians suggest is sufficient to reduce tail biting. However, this perhaps is not surprising since the law itself was vague and lacked any clear indicators upon which enforcement could act. The only countries that have reduced the rate of tail docking to 5% or less are those which had national bans but also lacked historical traditions of tail docking. Producers, pig associations, authorities, and technicians continue to develop, recommend, approve and build housing in which taking measures to avoid tail biting other than tail docking is not possible due to fully slatted floors, high stocking density, and poor climate control (Ohm, 2012). If we assume a reasonable rate of tail docking if proper provisions were taken (as in Sweden, Finland, Lithuania, Norway, Switzerland) is 5%, the the number of pigs being disproportionately docked is roughly 126 million (or 86% of EU total). 90% of pigs were tail docked and on average 65% had suitable enrichment material.We don’t know the exact overlap of these two sample statistics, but if we assume complete overlap and that the 35% who lack enrichment also are tail docked and the 10% with intact tails and have sufficient materials, then there are 55% that are tail docked even with sufficient enrichment materials. If we make a generous assumption that there was no choice for these pigs but to be tail docked even after making reasonable efforts to provide alternative strategies for reducing tail biting then 35% is our lower bound for unreasonable tail docking in the EU. If we take 86% as an upper bound, assuming producers are tail docking this 55% even though they don’t need to, this suggests a very crude range of 35%-86% of EU pigs (51 million - 126 million) on average being tail docked without due regard for alternative welfare methods due to weaknesses in the EU law and subsequent enforcement.

Narrow veal crate partial ban

Following an agreement in 1996, from 1 January 1998 the use of new narrow crates for calves was banned. Already existing installations were to be phased out by 31 December 2007 such that confining calves raised for veal in narrow crates after their first 8 weeks was banned (veal calves typically live 16-20 weeks). There is scant information online about the progress of compliance with this law other than to suggest that the law is now fully complied with. DG SANTE reports do show that producers in Italy and the Netherlands were late in phasing out new narrow crates,[68] but provide no update after 2007 on compliance with phasing out the use of existing installations as required by the law. This partial ban likely started off from a position of being more likely to succeed since veal production was not allowed or not a significant part of the industry in most countries. The UK had already instituted a stricter restriction on narrow veal crates in 1990, and 80% of the calves raised for veal in 1995 when the law was agreed were in just one country in the then European Community (France) (Butler, 1995). So this was less an EU law than an anti-French calf housing law. The law was only a partial restriction on narrow crates which likely made it easier to comply with. Enforcement does not appear to have played a major role.

Broiler stocking density

In 2007 EU countries agreed a set of standards (directive 2007/43/CE) for chickens grown for meat (broilers), to be enforceable from 2010. The maximum economic potential for the production unit of broilers often comes from using the highest stocking density (ECA, 2018) but high stocking densities in broiler sheds restricts the chickens’ behaviour and causes health problems (Kryeziu ,2018; Dawkins, 2016, Spindler, et. al., 2011; Yakubu, 2009; Zhao, et. al, 2008; Dawkins, et. al, 2004, Freddes and Zuidhoif, 2002). According to this directive, stocking densities were limited to 33 kg/mÂČ (the requirement uses live body mass in kilograms (kg) rather than number of birds because these birds are usually fast growing breeds)[69] but can be increased up to a maximum of 42 kg/mÂČ if certain additional welfare requirements are met regarding the concentration of gases, the inside temperature and humidity of the building, good implementation of the directive, and if in “at least seven consecutive, subsequently checked flocks from a house the cumulative daily mortality rate was below 1% + 0.06% multiplied by the slaughter age of the flock in days”,[70] or when “the owner or keeper has provided sufficient explanation for the exceptional nature of a higher daily cumulative mortality rate or has shown that the causes lie beyond his sphere of control”. There are also minimum requirements on lighting, ventilation, humane culling, and the voluntary use of “animal-based indicators” like severity of footpad dermatitis to assess welfare.

The law had set out that by 2012 the Commission would submit a report concerning the application of this directive and its influence on the welfare of chickens. This report was not submitted until 2018. That report shows that 34% of broiler chickens are kept at stocking densities of 33 kg/mÂČ (or less) in accordance with the general rule, 40% at densities of between 34‑39 kg/mÂČ and 26% at the highest density (up to 42 kg/mÂČ) permitted, meaning that for 66% of broilers the extra welfare requirements should have been met. There is significant variation between countries as seen in the figure below.  (Note that the Commission report contains an error in its own bar charts that reports a range of "between 32 and 39" rather than "between 34 and 39", which is replicated in the Better Chicken Commitment report).

In 2017, three quarters of the EU broiler meat production was concentrated in seven Member States: Poland, UK, Germany, France, Spain, Italy and the Netherlands, which also have the largest farms (EC, 2017). More than half (55% in 2017) of broilers stocked at the highest density are in France, with 18% located in the Netherlands and 9% in Belgium. In contrast, neither Germany, Austria, nor the UK took up the derogations in the directive, and Austria and Sweden set the general rule lower than the directive (30 kg/mÂČ and 20 kg/mÂČ respectively). German standards go beyond those set out in the directive, and Austria requires producers to meet the extra welfare requirements even without stocking at higher densities. This does not mean these countries do not stock broilers at higher densities than 33 kg/mÂČ, only that they set the default maximum lower or included stricter measures for using alternative stocking densities.

While stocking at higher densities is not a violation in itself, it is unclear whether the extra welfare requirements for this 66% of birds have been met. Looking at the audits conducted by DG SANTE 2010-2020 of 22 countries,[71] 10 appeared to be at risk of breaching requirements because they did not collect mortality data, used incorrect thresholds for mortality rates, did not use equipment to check gas concentrations, and had not used enforcement actions in light of noncompliance findings. France and the Netherlands among these are concerning, given the number of broiler chickens overall and the number of broiler chickens stocked at higher densities in these countries. National audits revealed 30% compliance in France in 2009, 46% compliance in the Netherlands in 2011, 87% compliance in Germany in 2011, 86% compliance in Italy in 2011, 91% compliance in Slovakia in 2012, 100% compliance in Poland in 2011, 100% compliance in Sweden in 2012 (Bock et al., 2014). Most countries had not defined maximum gas concentrations nor published guidance to inspectors to assess if on-farm ventilation is sufficient to justify using the higher range of stocking density.

Information

The law omitted parent stock and hatcheries from the requirements, although it is recognised that the conditions of breeder hens and baby chicks influence health and mortality rates in broiler farms. The use of the cumulative daily mortality rate to reduce stocking densities in subsequent flocks is often perceived by producers as a penalty. In order to stay below the limit and avoid a reduction in stocking densities, keepers who might otherwise cull birds for animal welfare reasons may instead transport possibly unfit birds for slaughter so that they are not included as part of their farm mortality rates.

Monitoring of conditions such as abnormal levels of contact dermatitis, parasitism and systemic illness are, as required, part of routine post mortem inspection at the slaughterhouse in many countries. However the directive does not define the extent or severity of such conditions which correspond to poor welfare conditions. So although the official veterinarian is obliged to communicate the results to the keeper and the competent authority where inspection results are consistent with poor animal welfare it is at the discretion of the member state to further define measurable criteria, and provide an indicator, which might support this decision.

The EU Internal Market and Industry Commissioner, Elizabeth Bienkowska, has committed the European Commission to develop more animal welfare indicators and announced that the second EU reference centre on animal welfare would be dedicated to the poultry sector to improve compliance with the directive.

Inspections

The coverage of inspections ranges from a general rule of 10% of growers (France, Italy, Poland, Spain) to those chosen on the basis of the risk-indicators recorded at slaughterhouses (Germany, Netherlands and the UK). As DG SANTE reports indicate, inspection authorities do not appear to be always collecting data themselves on mortality rates or gas concentrations, and sometimes use thresholds for compliance that are incorrect. Member States have not always provided clear compliance criteria so that their inspectors can make a practical assessment whether farms comply with the law. There are also clear disparities in resources allocated: Spain had 7 full time inspectors in 2013, while Romania had 42 inspectors at county level, plus one inspector at national level.(Bock et al., 2014). When mortality rates are exceeded, the deaths have often occurred in the first week of production and the keepers claim these were due to conditions at the hatchery and/or in the parent flocks. The authorities often accept such claims but do not investigate conditions at the hatchery since the EU law does not provide specific requirements for hatcheries.

Infringement

The penalties for noncompliance appear to range from lows of €400 (Italy), €750 (France),€1,500 (Netherlands) to highs of €9,300 (Italy), €25,000 (Germany),  and can result in farm closures (France) or forced equipment repairs (Netherlands). The Commission reports that the inspection authorities often judged the penalties to be effective on the basis that they were substantial in relation to poultry farm income. DG SANTE reports do not appear to show widespread penalties or enforcement action being taken for producers who do not record and report the minimum welfare requirements needed to allow for higher stocking densities.

The use of penalties is low, which the Commission and industry argued was a sign that compliance was high. NGOs in Poland and the UK have suggested that the trigger system from which penalties derive is not set strictly enough and this accounts for the low use of penalties. Industry organisations in both Sweden and the UK felt that the implementation of the directive had created an uneven playing field because the stocking density derogations allow for differences between Member States. As yet the EU has not begun any legal action, which is not surprising given that the data available makes it impossible to know if the requirements that justify higher stocking densities are being met in the first place.

Impact of enforcement

Since many countries are not collecting the necessary data to know whether animal welfare requirements to stock broilers at higher densities are being met there is little ability to enforce the law. The Commission has, so far, shied away from tougher actions on countries using incorrect mortality rate thresholds and refraining from checking gas concentrations. Eurostat numbers suggest 891.4 million broilers were produced in the EU in 2013, though this number appears to actually represent the number alive at any one time, since the number of broilers slaughtered each year is estimated to be 7 billion (Eurostat, 2014). If the 66% of EU flocks at higher densities is translated over to the 7 billion broilers slaughtered each year, then 4.6 billion of these broilers may be at risk of not receiving the additional welfare requirements required for higher stocking densities. If we focus on the countries where the vast majority of broilers are (Poland, UK, Germany, France, Spain, Italy and the Netherlands) and take the estimates of compliance cited in national audits (Bock et al., 2014 and the Commission report) seriously, it would suggest only 1.5 billion of the annual slaughtered broilers are at risk. This gives us a rough range of 1.5 billion to 4.6 billion (21%-66% of EU total).

Which animal welfare enforcement tools in the EU have been most effective historically?

A quantitative analysis of the use of each enforcement tool in each country for all animal welfare laws would likely add more precision to any estimates of the effectiveness of each. Therefore, there is the possibility that such an analysis might result in a re-ranking of tools than presented below. For example, a more exhaustive dataset of all complaints brought by animal groups might reveal them to lead to action in only a tiny fraction of cases, or a database on animal welfare funding and compliance might reveal better counterfactual value that is currently possible. Based on the qualitative case studies conducted we think this rough ordering is not very likely to be far off the mark, but are eager to see more research done in this area.

Not promising

Moderately promising

Most promising

What more can be done to improve compliance?

What is the evidence base for enforcement decreasing noncompliance? Charity Entrepreneurship estimated that enforcement is likely to only increase compliance by 6-12% as a result of a 4-5 year campaign and 24% increase in costs (Cox et al., 2019). If this effect could be achieved within 2 years, which seems unlikely according to Charity Entrepreneurship, an enforcement campaign could be worthwhile. The evidence relied on for these figures seems somewhat limited and somewhat unrelated, however we do not know of more rigorous estimates to use instead. In our report, the combined sum of enforcement actions (campaigns by NGOs and industry, greater inspections, higher penalties, legal action, trade bans) appears to have benefited 9%-27% of egg laying hens within 2 years and 8%-19% of the EU breeding sow population within 2 years. Campaigns by NGOs in the absence of these other measures do not appear to have reduced the number of pigs who are tail docked.  It also appears that the UK has played a key role in pushing for enforcement of animal welfare laws (due to a strong animal rights and welfare movement and powerful industry and trade dynamics) and so Brexit may significantly reduce the chances that future breaches are dealt with harshly.

Even recognising that compliance is not automatic, one might think that there is little more that can be done to improve the situation beyond what already happens. Perhaps some countries in the EU will always just be behind on compliance for broader structural or political reasons not easily addressable by the EAA movement. For example, one might think that poorer countries will naturally always be worse due to fewer resources to enforce laws. A very basic , not to be taken too seriously, regression analysis of the number of months an EU country was noncompliant with the battery cage ban and sow stall restrictions against GDP and number of hens or sows did not suggest that the economic situation of a country is correlated with noncompliance (the same if we look at a simple binary of whether a country met or missed the deadline). While some countries repeatedly crop up as laggards (Italy, Hungary, France) they are not uniformly poorer countries and many of the poorer EU members, in Eastern Europe, have been quite effective at diverting resources to enforcement. What is clear is that even when countries are given clearer information and more funding, national inspectors do not conduct effective farm visits or impose dissuasive fines.  Two solutions then could be to increase pressure on those authorities showing leniency, and/or to standardise enforcement tools (such as fines or reporting benchmarks to meet before deadlines) to minimise the discretion that authorities can exercise. Two potentially promising avenues to increase pressure are noncompliance awareness campaigns and litigation in administrative courts. Another option is to ensure the laws are enforceable in the first place, but this will be discussed in detail in a separate report.

Noncompliance awareness campaigns to generate political pressure to enforce harsher penalties and more inspections

Where inspectors or their political directors are unwilling to crack down on cases of noncompliance, NGO investigations can highlight noncompliance to two parties: industry and the public. Already compliant producers can pressure their government, through producer associations, to crack down on domestic or international noncompliant competitors covered by the same standards (as in the EU). The public may pressure politicians enough that they can overcome any existing industry pressure against effective enforcement. Animal groups already run "accountability campaigns" (also known as "enforcement campaigns") to pressure the last few companies into reporting their progress toward meeting voluntary cage-free commitments so a similar model could be applied to animal welfare laws. An industry association, the British Pig Executive, set up a website for tracking compliance with the sow stall restriction for example, so initiatives similar to EggTrack and ChickenTrack could be built into EU laws themselves .

There are some data points to suggest there is public support for stronger enforcement measures, but more surveys could be done to build the evidence base for this.

There are many examples that can be found online of investigations by animal groups leading to media coverage and government action that increases enforcement. However, this suffers from the bias that unsuccessful actions are less likely to have been written about and easily discoverable. A more thorough academic study in this area would be needed to isolate the effect of awareness campaigns on reducing noncompliance. For those interested here are examples we came across during the course of this report.

List of noncompliance campaigns

Litigation in administrative courts could force operators or national authorities to step up compliance and enforcement

One promising route might be going through administrative courts (Zhang et al., 2010; Stephenson, 2005).Generally in administrative tribunals proceedings operate to the advantage of litigants due to cost efficiency and speedy delivery of justice. One could launch legal action against the national inspection authorities themselves for not enforcing animal welfare laws at all or consistently across all farms. Audits of national inspection authorities in the EU have demonstrated that there is a huge variety in the penalties applied to producers, even for the same offence. An example of how this can be done has been provided by the Dutch animal welfare group, Wakker Dier.

It seems like similar cases could be brought against inspection authorities in other countries.

We should expect a learning curve for all parties concerned when proceeding with a portfolio of cases. High punitive (civil) fines are not known in the EU (unlike the US) and if any are attributed that would only be possible in civil law cases not administrative ones like the case mentioned above. Payment of legal opponent costs (only applicable if you lose in civil cases) is also strictly regulated and limited. So these types of risks have a very different profile here. More research needs to be done to establish the evidence base for this type of intervention, which may involve funding trials of such cases.

The ability of individual citizens or NGOs to bring cases to national courts, however, depends on the ‘opportunity structure’ (Vanjala, 2012; Hilson 2002; Kitschelt 1986) offered by national legal systems for bringing legal action in terms of legal standing, case duration, costs, and remedies. National legal systems rarely offer favourable conditions on all these aspects. And legal access is not sufficient. For example, Spain and Greece have long offered comparatively generous access to courts for environmental NGOs, at the same time as the Commission’s annual monitoring reports have consistently singled them out as among the worst performers in implementing EU environmental law. Therefore, this does not seem like a promising route to pursue in countries suffering from deeper problems in the effectiveness of the judicial system such as a lack of resources and the training of judges (Kallia-Antoniou 2013). Based on the experience of environmental issues, such action is more likely to be successful in countries with more established and better funded animal welfare movements than in countries where such movements are young or largely absent (Slepcevic 2009; Börzel 2006). Here is a non exhaustive list of litigation around the world that may be relevant for those interested in pursuing this route

Examples of litigation

Credits

This essay is a project of Rethink Priorities. It was written by Neil Dullaghan. Thanks to Daniela R. Waldhorn, Jason Schukraft,Saulius Ơimčikas, Derek Foster, Andreas Manz, Olga Kikou, Abigail Penny, Anna Harenius, Elena Nalon, Sophie De Jonckheere, Ines Grenho Ajuda, Alice Di Concetto, Francesca Porta, Douglas Waley, Andreas Erler, Jacob Peacock, and Peter Hurford for helpful feedback. If you like our work, please consider subscribing to our newsletter. You can see all our work to date here.

Works Cited

Abbot, R. (2011). EU pig producers struggle to meet 2013 gestation sow stall deadline. WATTAgNet.

Abbot, R. (2012). Some EU countries may not meet 2013 sow stall ban. WATTAgNet.

Agnew, J. S. (2010). Welfare of laying hens (debate).

Agnew, S. (2011). Response: An instant ban on Europe’s battery eggs won’t work. The Guardian.

AGRA, & CEAS. (2004). Study on the socio-economic implications of the various systems to keep laying hens. Final Report for the European Commission.

Animal Charity Evaluators. (2018). Conversation with Amruta Ubale of Animal Equality India. Animal Charity Evaluators.

Animal Charity Evaluators. (2019). Animal Advocacy in India.

Animal Equality. (2018). Salvados—Stranger pigs. ATRESPLAYER.

AWI. (2010). Humane Slaughter Update: Comparing State and Federal Enforcement of Humane Slaughter Laws | Animal Welfare Institute. Animal Welfare Institute.

AWI. (2017a). AWI Report: Humane Slaughter Enforcement up, but Serious Problems Remain. AWI QUARTERLY (Summer).

AWI. (2017b). Humane Slaughter Update Federal and State Oversight of the Welfare of Farm Animals at Slaughte. Animal Welfare Institute.

AWI. (2019). AWI Analysis Finds Weak Enforcement of State Farm Animal Welfare Laws. AWI QUARTERLY (Winter).

AWI. (2020a). AWI Releases Latest Update on Humane Slaughter Enforcement. AWI QUARTERLY (Summer).

AWI. (2020b). Enforcement of State Farm Animal Welfare Laws. AWI QUARTERLY.

BBC News. (2012). UK battery farms break EU rules. BBC News.

Berkhout, N. (2010). Poland calls on delaying cage ban to 2017. PoultryWorld.

Bollard, L. (2017). How Can We Improve Farm Animal Welfare in India?

Borg, C. (2013). Answer to a written question—Failure by Spain to enforce the directive on pig welfare—E-012150/2013. Retrieved 24 July 2020, from

Borghetto, E., & Franchino, F. (2010). The role of subnational authorities in the implementation of EU directives. Journal of European Public Policy, 17(6), 759–780.

Börzel, T.A., & BuzogĂĄny, A. (2019). Compliance with EU environmental law. The iceberg is melting.28:315–341. Environmental Politics, 28(2).

Börzel, Tanja A., Hofmann, T., Panke, D., & Sprungk, C. (2010). Obstinate and Inefficient: Why member states Do Not Comply With European Law: Comparative Political Studies.

Börzel, Tanja A., & Knoll, M. (2012). Quantifying Non-Compliance in the EU: A Database on EU-Infringement Proceedings.

Bracke, M. B. M. (2009). Animal welfare in a global perspective (No. 240; p. ). Wageningen UR Livestock Research.

Broom, D. (2017). Animal Welfare in the European Union. Committee on Petitions of the European Parliament.

Burch, D. (2013). EU gestation stalls ban. PigProgress.

Butler, C. (1995). Europe plan for ban on veal crates. The Independent.

Case, P. (2013). Video: Spanish pig farmers flout sow stall ban, says CIWF. Farmers Weekly.

Chippindale, N. (2010). The 2012 EU ban on conventional cages and its effect. Nuffield Farming Scholarships Trust A BEMB (R & E) Trust Award.

CIWF. (n.d.). Illegal cages: Time to act.

CIWF. (2008). 2012 EU battery cage ban will be upheld.

CIWF. (2009). ECJ: Greek government failed to enforce welfare laws.

CIWF. (2011a). Defend the Big Move. Farm Animal Voice - Issue 181.

CIWF. (2011b). REVIEWING THE COSTS The economics of moving to higher welfare farming.

CIWF. (2013). WIDESPREAD BREACHES OF PIG WELFARE LAWS IN THE EU Summary Report. Compassion in World Farming.

CIWF. (2014). Greece gets away with it.

CIWF. (2018). Animal Transport: Law Enforcement Failures |. Compassion in World Farming.

Clarke, P. (2014). Video: Illegal egg farm still operating in Greece. Farmers Weekly.

Clements, M. (2014). Lessons to be learned from European Union’s cage ban. WATTAgNet.

Committee on Oversight and Government Reform. (2010). Continuing problems in USDA’s enforcement of the Humane Methods of Slaughter Act.

Council of the EU. (2020). Animal Welfare—An integral part of sustainable animal production. AGRI 54 VETER 12.

Council of the EU, S. (2011). 3070th Council meeting Agriculture and Fisheries. Press Release 6655/11, 13.

Craig, P., & Burca, G. de. (2011). EU Law: Text, Cases, and Materials (Fifth edition). Oxford University Press.

De Bernardin, D. (2019). Everything you ever wanted to know about EU infringement procedures. The European Data Journalism Network.

De Briyne, N., Berg, C., Blaha, T., Palzer, A., & Temple, D. (2018). ‘Phasing out pig tail docking in the EU - present state, challenges and possibilities’. Porcine Health Management, 4(1), 27.

D’Eath, R. B., Arnott, G., Turner, S. P., Jensen, T., Lahrmann, H. P., Busch, M. E., Niemi, J. K., Lawrence, A. B., & Sandþe, P. (2014). Injurious tail biting in pigs: How can it be controlled in existing systems without tail docking? Animal, 8(9), 1479–1497.

DG SANTE. (2011a). FINAL REPORT OF AN AUDIT CARRIED OUT IN BELGIUM FROM 27 JUNE TO 01 JULY 2011 IN ORDER TO EVALUATE THE IMPLEMENTATION OF CONTROLS FOR ANIMAL WELFARE ON FARMS AND DURING TRANSPORT. Food Safety - European Commission.

DG SANTE. (2011b). FINAL REPORT OF AN AUDIT CARRIED OUT IN ITALY FROM 09 TO 18 NOVEMBER 2011 IN ORDER TO EVALUATE THE IMPLEMENTATION OF CONTROLS FOR ANIMAL WELFARE ON FARMS AND DURING TRANSPORT.

DG SANTE. (2012a). FINAL REPORT OF AN AUDIT CARRIED OUT IN BULGARIA FROM 05 TO 13 JUNE 2012 IN ORDER TO EVALUATE THE IMPLEMENTATION OF CONTROLS FOR ANIMAL WELFARE ON FARMS AND DURING TRANSPORT. Food Safety - European Commission.

DG SANTE. (2012b). FINAL REPORT OF AN AUDIT CARRIED OUT IN FRANCE FROM 12 TO 22 NOVEMBER 2012 IN ORDER TO EVALUATE THE IMPLEMENTATION OF CONTROLS FOR ANIMAL WELFARE ON FARMS AND DURING TRANSPORT. Food Safety - European Commission.

DG SANTE. (2012c). FINAL REPORT OF AN AUDIT CARRIED OUT IN IRELAND FROM 12 TO 14 MARCH 2012 IN ORDER TO EVALUATE THE IMPLEMENTATION OF CONTROLS FOR ANIMAL WELFARE OF LAYING HENS ON FARMS. Food Safety - European Commission.

DG SANTE. (2017). Welfare of Cattle on Dairy Farms Report number    2017-6241.

Dier & Recht, & Varkens in Nood. (2012). Naleving dierenwelzijnswetgeving in de vee-industrie; Een onderzoek naar overtredingen in de vee-industrie, de impact op het dierenwelzijn en het huidige controle- en handhavingsbeleid

EC. (1998). The European Commission adopts measures to improve the welfare of laying hens. [Text]. Press Corner.

EC. (2003). 20th Annual Report on Monitoring the Application of Community Law. COM(2003) 669 Final.

EC. (2008). Animal Welfare: Commission report confirms the potential benefits of banning conventional battery cages for laying hens. Press Corner.

EC. (2011a). Animal welfare: Commission urges member states to implement ban on hen cages or risk facing legal action 20 October 2011. European Commission Press Release.

EC. (2011b). Commission, Commission Staff Working Paper—Impact Assessment. SEC/2011/0055 Final.

EC. (2011c). GENERAL REPORT OF FINDINGS FROM MISSIONS 2008-2010 ON ENFORCEMENT OF ANIMAL WELFARE STANDARDS FOR LAYING HENS KEPT IN UNENRICHED CAGES. (DG)SANCO/2010-8814/GR.

EC. (2012). Questions and Answers on the upcoming ban on individual sow stalls. Press Corner.

EC. (2013a). 40 Years of Animal Welfare.

EC. (2013b). COMMISSION STAFF WORKING DOCUMENT IMPACT ASSESSMENT Accompanying the document Proposal for a REGULATION OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL on official controls and other official activities performed to ensure the application of food and feed law, rules on animal health and welfare, plant health, plant reproductive material, plant protection products and amending Regulations.

EC. (2013c). IMPACT ASSESSMENT Accompanying the document Proposal for a REGULATION OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL on official controls and other official activities performed to ensure the application of food and feed law, rules on animal health and welfare, plant health, plant reproductive material, plant protection products and amending Regulations (EC) No 999/2001, 1829/2003, 1831/2003, 1/2005, 396/2005, 834/2007, 1099/2009, 1069/2009, 1107/2009, Regulations (EU) No 1151/2012, [
.]/2013 [Office of Publications, please insert number of Regulation laying down provisions for the management of expenditure relating to the food chain, animal health and animal welfare, and relating to plant health and plant reproductive material], and directives 98/58/EC, 1999/74/EC, 2007/43/EC, 2008/119/EC, 2008/120/EC and 2009/128/EC (Official controls Regulation). COMMISSION STAFF WORKING DOCUMENT.

EC. (2014). Number of Laying Hens 2013 by way of keeping based on the EU member states that communicated data (27)Methods of production communicated accordingly to Reg. 589/2008. EU Market Situation for EggsCommittee for the Common Organisation of the Agricultural Markets 22 May 2014.

EC. (2015). Number of Laying Hens 2014 by way of keeping based on the EU member states that communicated data (24) Methods of production communicated accordingly to Reg. 589/2008, Art. 31. EU Market Situation for Eggs Committee for the Common Organisation of the Agricultural Markets 18 June 2015.

EC. (2016). Overview report Study Visits on Rearing Pigs with Intact Tails. DG Health and Food Safety.

EC. (2020a). Single Market Scoreboard.

EC. (2020b). The common agricultural policy at a glance [Text]. European Commission - European Commission.

Edman, F. (2014). Do the member states of the European Union comply with the legal requirements for pigs regarding manipulable material and tail docking? First Cycle, G2E. Skara: SLU, Dept. of Animal Environment and Health.

Eliantonio, M. (2016). Enforcing EU environmental policy effectively: International influences, current barriers and possible solutions. In S. Drake & M. Smith, New directions in the effective environment of EU law and policy. Edward Elgar.

EP. (2010). Welfare of laying hens European Parliament resolution of 16 December 2010 on the EU laying hens industry: The ban on the use of battery cages from 2012. P7_TA(2010)0493.

EP. (2019). NOTICE TO MEMBERS Subject: Petition 0336/2012 by C.R. (Danish), concerning the routine tail-docking of piglets in Denmark Petition No 0721/2014 by Joanna Swabe (British), on behalf of Human Society International, and two signatories, on the Routine docking of pigs’ tails. Petition No 1141/2014 by Fredrick Federley (Swedish), on the cutting of pigs’ tails.

Escobar, M. P., & Demeritt, D. (2017). Paperwork and the decoupling of audit and animal welfare: The challenges of materiality for better regulation. Environment and Planning C: Politics and Space, 35(1), 169–190.

EU Platform on Animal Welfare. (2019). ANIMAL WELFARE - AN INTEGRAL PART OF SUSTAINABLE ANIMAL PRODUCTION. 6th Meeting of the EU Platform on Animal Welfare.

European Court of Auditors. (2016). Special report no 26/2016: Making cross‑compliance more effective and achieving simplification remains challenging.

European Court of Auditors. (2018). Special Report: Animal welfare in the EU: closing the gap between ambitious goals and practical implementation.

EuroStat. (n.d.). Glossary:Laying Hen Housing—Conventional battery cages—Statistics Explained.

Evans, R., & Pegg, D. (2019, January 27). Peers and MPs receiving millions in EU farm subsidies. The Guardian.

Falkner, G., Hartlapp, M., & Treib, O. (2007). Worlds of compliance: Why leading approaches to European Union implementation are only ‘sometimes-true theories’. European Journal of Political Research, 46(3), 395–416.

Falkner, G., & Treib, O. (2008). Three Worlds of Compliance or Four? The EU-15 Compared to New member states*. JCMS: Journal of Common Market Studies, 46(2), 293–313.

FarmingUK Team. (2012). Europe’s pig farmers flout Brussels stalls ban. FarmingUK.

FarmingUK Team. (2013). NFU blasts EU policing of pig and poultry welfare—FarmingUK News. FarmingUK.

FAWC. (2007). FAWC opinion on enriched cages for laying hens. GOV.UK.

FVO. (2016). Overview report Use of Slaughterhouse Data to Monitor Welfare of Broilers on Farm 2016-8999.

Gebrekidan, S., Apuzzo, M., & Novak, B. (2019, November 3). The Money Farmers: How Oligarchs and Populists Milk the E.U. for Millions. The New York Times.

Gov.uk. (2011). UK unites to stamp out battery cages. Press Release.

Guarascio, F., & Dunmore, C. (2012). EU countries face legal action over hen cage ban. Reuters.

Hanson, R. (2012). Eggs and Egg Products in Spain and Portugal. GAIN Report.

Hartlapp, M., & Falkner, G. (2009). Problems of Operationalization and Data in EU Compliance Research: European Union Politics.

Haverland, M., & Romeijn, M. (2007). Do member states Make European Policies Work? Analysing the Eu Transposition Deficit. Public Administration, 85(3), 757–778.

House of Commons. (2011). The Welfare of Laying Hens directive—Implications for the egg industry Ninth Report of Session 2010–12. Environment, Food and Rural Affairs Committee.

ImhĂ€user, R. (2012). Niedersachsen: Mehr Fördergelder fĂŒr Umbau zur Gruppenhaltung. Top Agrar Online.

Kaeding, M. (2008). Lost in Translation or Full Steam Ahead: The Transposition of EU Transport directives across member states. European Union Politics.

Knill, C., & Lenschow, A. (1998). Coping with Europe: The impact of British and German administrations on the implementation of EU environmental policy. Journal of European Public Policy, 5(4), 595–614.

König, T., & Luetgert, B. (2009). Troubles with Transposition? Explaining Trends in Member-State Notification and the Delayed Transposition of EU directives. British Journal of Political Science, 39(1), 163–194.

Lewis, J. (2012, January 1). French farmers ignore battery hen ban.

Linden, J. (2012a). EU Welfare Regulations and the Law of Unintended Consequences. The Poultry Site.

Linden, J. (2012b). GLOBAL POULTRY TRENDS 2011—EU’s Share of European Egg Total in Decline. The Poultry Site.

Lundmark, F. (2016). Mind the gaps! From Intentions to Practice in Animal Welfare Legislation and Private Standards. Ph.D. thesis. Acta Universitatis Agriculturae Sueciae.

Lundmark, F, Berg, C., & Röcklinsberg, H. (2013). ‘Unnecessary suffering’ as a concept in animal welfare legislation and standards. In The Ethics of Consumption – the citizen, the market and the law. Wageningen Academic Publishers.

Lundmark, Frida, Berg, C., Schmid, O., Behdadi, D., & Röcklinsberg, H. (2014). Intentions and Values in Animal Welfare Legislation and Standards. Journal of Agricultural and Environmental Ethics, 27(6), 991–1017.

Marzocchi, O. (2014). ROUTINE TAIL-DOCKING OF PIGS. DIRECTORATE GENERAL FOR INTERNAL POLICIES

Mastenbroek, E. (2005). EU compliance: Still a ‘black hole’?

Matheny, G., & Leahy, C. (2007). Farm-Animal Welfare, Legislation, and Trade. Law and Contemporary Problems, 70(1), 325–358. JSTOR.

Nalon, E., & De Briyne, N. (2019). Efforts to Ban the Routine Tail Docking of Pigs and to Give Pigs Enrichment Materials via EU Law: Where do We Stand a Quarter of a Century on? Animal, 9(4).

NFAHW. (2012). A National Farm Animal Welfare System for Canada. National Farmed Animal Health and Welfare Council.

NFAHW. (2019). A National Farm Animal Welfare System for Canada – 2019. National Farmed Animal Health and Welfare Council.

O’Keefe, T. (2012a). Cage ban shrinks the German egg industry. WATTAgNet.

O’Keefe, T. (2012b). EU egg producers coping with cage ban. WATTAgNet.

Pelkmans, J., Brito, A. C. de, & Harbour, M. (2013). Enforcement in the EU Single Market. Centre for European Policy Studies.

Pig333. (2013). European Union: Sow stall update.

PigProgress. (2010). Danish pig farmers ready for implementing ban on sow stalls.

Poultry Site. (2011). Country Unites to Keep out Eggs from Battery Cages. The Poultry Site.

Poultry Site. (2012a). Czechs Slap Ban on Polish Egg Imports. The Poultry Site.

Poultry Site. (2012b). Food Safety Agency Seizes Eggs from Poland. The Poultry Site.

PW Reporters. (2012). VIDEO: Battery cages still operating in France. Farmers Weekly.

Rahman, S. A., Walker, L., & Ricketts, W. (2005). Global perspectives on animal welfare: Asia, the Far East, and Oceania. Revue Scientifique Et Technique (International Office of Epizootics), 24(2), 597–612.

Schulze zur Wiesch, K.-H. (2010). Gruppenhaltung: Keine Schonfrist. Top Agrar Online.

Spindler, B., Briese, A. & Hartung, J. How much floor space needs a broiler chicken? in Proceedings of the XV International Congress of the International Society for Animal Hygiene (2011).

Sverdrup, U. (2004). Compliance and Conflict Management in the European Union: Nordic Exceptionalism. Scandinavian Political Studies, 27(1), 23–43.

SYSADM. (2009). DĂ€nemark: Verhaltene Umstellung auf Gruppenhaltung. Top Agrar Online.

SYSADM. (2012). Gruppenhaltung: NiederlÀnder und Belgier haben wenig Probleme. Top Agrar Online.

Tallberg, J. (2002). Paths to Compliance: Enforcement, Management, and the European Union. International Organization, 56(3), 609–643.

Thomson, R., Torenvlied, R., & Arregui, J. (2007). The Paradox of Compliance: Infringements and Delays in Transposing European Union directives. British Journal of Political Science, 37(4), 685–709.

Toshkov, D. (2012). Compliance with EU Law in Central and Eastern Europe. L’Europe en Formation, n° 364(2), 91–109.

Toshkov, D. (2016). Compliance and enforcement of EU law: Who wins, who loses and who settles. Paper Submitted to the Ninth Annual Conference.

Trent, N., Edwards, S., Felt, J., & O’Meara, K. (2005). International Animal Law, with a Concentration on Latin America, Asia, and Africa. State of the Animals 2005.

Valros, A., & Heinonen, M. (2015). Save the pig tail. Porcine Health Management, 1(1), 2.

van Zanen, S. E. J. (2016). Which of the European member states have the potential to join the four front-runners? [Wageningen University].

Vogeler, C. S. (2019). Why Do Farm Animal Welfare Regulations Vary Between EU member states? A Comparative Analysis of Societal and Party Political Determinants in France, Germany, Italy, Spain and the UK. JCMS: Journal of Common Market Studies, 57(2), 317–335.

Waldhorn, D. R. (2018, February 9). ¿Para quién trabaja Tejerina? Un pozo negro de subvenciones y maltrato animal. El Diario.

WATTAgNet. (2010). Sow stalls deadline will not be extended, says EU official.

WATTAgNet. (2012). EU 2013 sow stall ban already facing challenges.

WATTAgNet. (2013). 17 EU countries are not sow stall compliant.

WATTAgNet. (2014). Italy found guilty of non-compliance with cage ban.

Windhorst, H.-W. (2017). Dynamics and patterns of the EU egg industry—LOHMANN TIERZUCHT GmbH. Lohmann Tierzucht.

You, X., Li, Y., Zhang, M., Yan, H., & Zhao, R. (2014). A Survey of Chinese Citizens’ Perceptions on Farm Animal Welfare. PLoS ONE, 9(10).

Zhao, F., Zhao, Y., Geng, A., Shi, Z. & Li, B. Effects of Stocking Density on Behavior of Broilers in Cage System. in Proceedings of the VIII Livestock Environment Symposium (2008).

Zonderland, J., & Enting, J. (2006). Varkenshouderij in Brazilië, Sterke integraties en stevige merken. Practice Report 48.

  1. The majority of this study covers the time period before the United Kingdom (UK) formally exited the EU. It also covers time periods when what we now think of as the European Union was known as the European Economic Community or European Community but here we shall only use the term European Union. ↩

  2. Benefiting an estimated 6M calves, 12M sows, and 370M hens per year across EU member states. ↩

  3. Crates banned after first 8 weeks (veal calves typically live 16-20 weeks). ↩

  4. Conventional battery cages are banned, but enriched cages are allowed with minimum requirements of 116 square inches per caged bird, perches, litter, and a nesting box. ↩

  5. Gestation crates banned except during the first four weeks and last week of sow’s roughly 16-week pregnancy. Farrowing crates used for the two to four weeks the sow weans her piglets. But if they abort/fail to get pregnant, they will stay longer and they stay in farrowing crates from a few days before parturition to the end of the three to four weeks of lactation. ↩

  6. Max stocking density of 33kg/sq. m - 42kg/sq. m, plus litter, lighting, living conditions, transport, and slaughter regulations. Breed and growth rates aren’t regulated. ↩

  7. This directive contains general provisions applicable to all vertebrate farmed species but the annex to the directive does not apply to fish, reptiles and amphibians. ↩

  8. The Commission does not say which countries’ claims are still being substantiated but it seems very likely they are France, Italy, Hungary, and The Netherlands. ↩

  9. In the 2014 Supreme Court judgement banning performances involving cruelty to bulls, the judges suggests that the parliament should amend the Act and increase fines. So far there has been no concrete action taken to revisit the Act. ↩

  10. This is mostly with regard to keeping proper records of identifying individual animals and their deaths.This figure applies to 7.5 million farmers who in 2015 received approximately €47 billion in aid, representing 68 % of all farmers supported by CAP and who receive 83% of all payments. ↩

  11. Personal communication with Djurens RĂ€tt, May 2020. ↩

  12. Personal communication with Vier Pfoten, May 2020. ↩

  13. A Chief veterinary officer (CVO) is the head of a veterinary authority (typically a national government service comprising veterinarians, other professionals and paraprofessionals). They have the responsibility and competence for ensuring or supervising the implementation in their nation of animal health and welfare measures; international veterinary certification, and other standards and recommendations. ↩

  14. Unclear regulation was considered as relevant or very relevant by 67% of the respondents and the attitude of operators and farmers by 52%. Insufficient knowledge among operators and farmers, lack of inspection results, or direct financial constraints were reported as very relevant or relevant reasons for noncompliance by 43%, 29% and 24% of the respondents, respectively. ↩

  15. Nevertheless sometimes they may be used in court. in cases such as Germany they have fish welfare guidelines for fish farmers and for transporters. They are only guidelines, in this sense. But if an operator is taken to court for breaking the animal farming or animal transport law, then the judge will use the guidelines to make the decision. ↩

  16. The first on pigs, and the second primarily on “poultry” animals, with some room for work on small animals like rabbits. ↩

  17. Personal communications with Compassion in World Farming and Vier Pfoten, May 2020. ↩

  18. Note that this system does not cover all the legislative requirements on animal welfare: it includes provisions to protect calves and pigs, and others setting general requirements for all farm animals. Livestock farmers in sectors that do not typically receive the relevant CAP payments (most EU poultry farms and many pig farms in certain member states) are by definition not covered by the payment and penalty system. At EU level, the general cross-compliance requirements for animal welfare cover about 55% of all EU farms with livestock, while the specific directive requirements can cover a larger share of farms. ↩

  19. Personal communication with CIWF, May 2020. ↩

  20. Inspections were found to be least likely in Bavaria, where livestock farmers are inspected on average every 48 years, whilst in Lower Saxony, the state with the highest regional density of livestock units, farms are inspected on average every 21 years ↩

  21. Article 3 of Regulation (EC) No 882/2004: “member states shall ensure that official controls are carried out regularly, on a risk basis and with appropriate frequency, so as to achieve the objectives of this Regulation.” ↩

  22. As many as 40% of farms fall outside the EU’s remit. In Italy, pig farms with fewer than 40 pigs or 6 sows and goat, sheep and cattle (other than calves) or farms with fewer than 50 animals are excluded from the population to be checked. In Sardinia, this leads to 85 % of pig farms, 67 % of goat farms and 86 % of cattle (other than calves) farms not being subject to animal welfare checks. In Romania, although no farms were formally excluded from the scope of animal welfare checks, in practice the authorities did not check agricultural holdings that fall within the definition of “nonprofessional farms”. These holdings cover many of the animals in the pig sector (45 %) and almost all animals in the sheep and goat sector (99 %). ↩

  23. Petition 0336/2012, Petition No 0721/2014 ↩

  24. Article 39 of Delegated Regulation (EU) No 640/2014 requires that the payment reduction is, as a rule, 3 % and can be reduced to 1 % or increased to 5 % based on the assessment of the importance of the noncompliance. In the case of noncompliance due to negligence, the maximum reduction is 5 % and, in the case of reoccurrence, 15 %. In the case of intentional noncompliance, there is a minimum reduction of 20 % and it may go as far as total exclusion from one or several aid schemes for one or more calendar years. ↩

  25. The infringement proceedings consist of several stages. The first two, suspected infringements (complaints, petitions, etc.) and Formal Letters, are informal and treated as confidential. The formal infringement proceedings start when the European Commission issues a Reasoned Opinion. Should noncompliance prevail after managerial dialogue, the European Commission refers cases to the European Court of Justice (ECJ). This initiates the adjudication phase, which ends with a binding judgement. If the member states still refuse to comply, the Commission can open new proceedings (Art. 228 ECT), which may result in a second ECJ judgment linked to financial penalties ↩

  26. EU Pilot is a mechanism for informal dialogue between the Commission and the Member State concerned on issues relating to potential non compliance with EU law. It is used before a formal infringement procedure. ↩

  27. Another source of infringements is available here: https://www.lawyersforanimalprotection.eu/infringement-overview/ ↩

  28. Greece, Ireland, Italy, the Netherlands ↩

  29. Alternative housing systems can be divided into cage and non-cage systems Alternative cage systems include furnished/enriched cages and colony cages Furnished cages differ from conventional cages in the space per hen (750 cm2 compared to 550 cm2 in conventional cages), presence of a nest, presence of at least 15 cm of perch for every hen, and at least 250 cm2 of littered area per hen. Colony cages are a type of furnished cage that are not defined in the European legislation, yet some member states introduced them in their adopted regulations. These cages have a surface area of at least 25,000 cm2, with at least 800 cm2 per hen, and at least 2 perches are provided at different heights (Van Horne et al., 2007; EU, 1999) ↩

  30. The exact figure is unclear. In mid 2010, it was forecasted that about 30% of hens would still be in conventional battery cages by 2012 (Chippindale, 2010); data from April 2011 showed ~144 million, more than a third of the EU total, were still being kept in conventional battery cages (Guarascio & Dunmore, 2012). A spokesman for the European Commission in 2012 reported 46 million hens still in conventional battery cages (BBC News, 2012), about 14% of the total number of birds but other sources reported 83-84 million hens (Agnew, 2011; Lewis, 2012) Windhorst (2015) suggested 43.5 million hens in June 2012. In the figure we use the upper estimate of 84 million which is close to 25%. ↩

  31. During the first quarter of 2012, egg prices within the market for eggs broken and processed were at a high, double what is normal (O’Keefe, 2012b). ↩

  32. Just three months after the conventional battery cage ban, EU egg production was reported to be down by between 10% and 15% and there was much disruption in the market (Linden, 2012a, 2012b) ↩

  33. Between January 2011, when over 364 million layers were kept, and January 2012, when the transformation process reached a critical phase, the number of layers decreased by almost 33 million birds (Clements, 2014). ↩

  34. Also see Windhorst (2017) ↩

  35. Egg production fell in Germany by 22.5 percent from 2000 through 2009. It fell by 11.6 percent in 2009, the year the cage ban went into effect, from the year before. Egg products are not the only thing imported into Germany, shell egg imports increased by 37.4 percent from 2008 to 2010. ↩

  36. Germany and the Netherlands better anticipated the 2012 deadline, due to specific national regulations and under the pressure of the retailers who have banned all cage eggs (including enriched cages). See (Vogeler, 2019) for more on why Farm Animal Welfare Regulations Vary Between EU member states. ↩

  37. Of course one should keep in mind that many countries simply did the bare minimum to comply and that the benefits of “enriched” cages over conventional battery cages exist but are likely not as large as the comparison between cages and no cages. ↩

  38. The decision stipulated that a scientific analysis regarding the advantages and disadvantages of the individual husbandry systems and the expected socio-economic effects had to be carried out before a final decision on the entry into force of the directive ↩

  39. Ironically Sweden announced in 1988 that caged egg production would be banned with effect from 1998. However, in the meantime Sweden joined the EU and a legal battle resulted in traditional cages being permitted until 2003. ↩

  40. France and Greece were highlighted as doing this in DG SANTE reports ↩

  41. Financial support totalling €11,150,843 was provided to 279 beneficiaries in relation to upgrading laying hen establishments. ↩

  42. A government approved financing programme requiring these modifications was to be made by 31/12/2014 reminded operators that after 2012 conventional battery cages would be illegal though it seems some aimed to restock their unenriched cages at the same density as allowed for enriched cages and face the administrative fines being issued ↩

  43. Funding was available from the two Regions (Flanders and Wallonia) to convert premises. ↩

  44. The Poultry Welfare Scheme was introduced on June 2010 under Ireland's Rural Development Programme 2007–2013. It provided for aid in the form of grants of 40 per cent of total costs of replacement for premises using unenriched cages.By 2012 32 applications had been approved with 20 refurbishments completed. Up to €16m was made available. ↩

  45. Funds allocated under project No 121 approved by the Commission and the Payment Agency of the Ministry of Agriculture. The Bulgarian government allocated an additional 25% above this level of funding from State funds. Five-year loans were made available to farmers to fund refurbishment projects. ↩

  46. Multi-Stakeholder Meeting on the Implementation of Council directive 1999/74/EC, on the Protection of Laying Hens, held in Brussels on 19 January 2011 & 3070th Council meeting Agriculture and Fisheries (Council of the EU, 2011) ↩

  47. Bulgaria, Germany, France, Ireland, Latvia, Lithuania, Netherlands, Romania, Slovenia. ↩

  48. Hungary: CCA stated that there is an unwritten agreement between OVs not to issue sanctions to farmers. ↩

  49. See a full list of options considered here (Defra, 2010) ↩

  50. By mobilizing supporters to email UK, Italian, Spanish, and Polish governments.(CIWF, n.d., 2011a). You can see archived webpages on the campaign on WayBack Machine. ↩

  51. Big supermarkets agreed not to sell such rogue whole eggs, and most went further by banning them from own-brand processed food. Under the new rules, manufacturers were not permitted to source their eggs from noncompliant EU countries. ↩

  52. The Animal Health and Veterinary Laboratories Agency (AHVLA) used ultraviolet light to identify batches of eggs that were not laid in the new, more welfare friendly cages. UV light picks up small marks left in the shell immediately after it has been laid, before it hardens. Any eggs which only show a pattern of wire marks will have been laid in the old conventional battery cages, and will not be allowed to be sold as class A (whole) eggs. It is unclear if other countries used this technology. ↩

  53. Between January 2011, when over 364 million layers were kept, and January 2012 the number of layers decreased by almost 33 million birds (Clements, 2014) ↩

  54. From 1st January 1996, no new sow units were allowed to use tethering, and all existing tether systems must be phased out by 31st December 2005. ↩

  55. One report cites 75% of the EU’s 13 million sows are held on compliant holdings (WATTAgNet, 2013) while another suggests 2 million pigs/week or 40% of EU pig production will not be compliant (Burch, 2013; FarmingUK Team, 2012) Neither report mention pregnant/breeder pigs specifically. 2012 compliance numbers and Eurostat breeding sow numbers suggest the actual number of pigs was 4,093,364 ↩

  56. Falling percentages in the 12 months to June 2012 were reported by Denmark (-2.3), Germany (-1.3), Ireland (-6.6), Spain (-2.8), France (-3.2), Italy (-13), Hungary (-5), the Netherlands (-3.6), Austria (-2.8), Poland (-9.6) and Sweden (-7.2). ↩

  57. France, Latvia, Slovenia, Slovakia,Hungary, Denmark, Lithuania ↩

  58. Belgium, Cyprus, Denmark, France, Germany, Greece, Ireland, Poland, and Portugal ↩

  59. The Netherlands, Italy, Hungary, Finland, and Slovenia ↩

  60. Belgium, Cyprus, Greece, France were sent final warning letters while Slovenia and Finland were sent initial warning letters. ↩

  61. 15-20 years is suggested in Pig333 (2010), but CIWF cite 12-15 years (CIWF, 2000) ↩

  62. According to Eurostat. ↩

  63. Tail docking numbers come from personal calculations using estimates from surveys conducted by De Briyne et al., 2018; Edman, 2014; EFSA, 2007 and numbers from Eurostat Pig population - annual data. Also see various EU country-specific reports titled “Evaluate member state activities to prevent tail-biting and avoid routine tail-docking of pigs”. Enrichment materials numbers come from De Briyne et al., 2018 but omit a number of countries. Marzocchi (2014) gave a range of 81%-100% at that time. Also see Edman (2014) and detailed discussion on the pig directive below. ↩

  64. Finland has historically and traditionally not been associated with tail docking, and the practice was implicitly banned in 1996 and completely banned in 2002. There was no transitional period and no financial support given to farmers. While provision of enrichment material was not met in a third of inspections in 2010, this figure was brought down to 4% by 2014 through a “Pig Project” which offered animal welfare payments for specific measures on enrichment materials. Swedish pig production has never had a tradition of routine tail docking and the practice has been formally prohibited since 1988 except for veterinary reasons. As a result, farmers work on the basis that they cannot routinely dock tails and have learned to manage pigs with intact tails. The Swedish Animal Protection Ordinance regulates that all pigs should have permanent access to straw or similar litter material (van Zanen, 2016). Lithuania had already forbidden tail docking of pigs in their national legislation (Valros & Heinonen, 2015; D’Eath et al., 2014). ↩

  65. For example, chains, ropes and rubber or plastic ‘toys’ are often provided (if enrichment material is provided at all), which are not able to meet the behavioural needs of pigs (CIWF). ↩

  66. EU Commissioner Borg replied to a Parliamentary Question in 2014 stating that "the Commission does not have exact figures on the degree of compliance with enrichment material and avoidance of tail-docking requirements” while acknowledging that DG SANTE reports show that these provisions are not met in a majority of the member states inspected. ↩

  67. One possible reason is that the EU pig sector is currently faced with the saturation of the demand for pig meat on the internal market, coupled with an animal health crisis due to African Swine Fever (ASF). (Nalon & De Briyne, 2019) ↩

  68. DG(SANCO)/7636/2005 – MR Final, DG(SANCO)/7512/2005 – MR Final ↩

  69. For example, broiler chickens with an average live body mass of 2.144 kg can be housed under certain conditions with a maximum stocking density of 42 kg/m2 (2007/43/EC). This would mean that at the end of the fattening period a maximum of on average 19.59 broiler chickens could be housed per m2 (Krause and Schrader, 2019) ↩

  70. ‘Cumulative daily mortality rate’ means the sum of daily mortality rates, which in turn is the number of chickens which have died in a house on the same day including those that have been culled either for disease or because of other reasons divided by the number of chickens present in the house on that day, multiplied by 100. For a flock with a slaughter age of 42 days the limit is 3.52% ↩

  71. Austria, Belgium, Bulgaria, Czech republic, Denmark, Finland, France, Germany, Hungary, Italy, Latvia, Lithuania, Netherlands, Poland, Portugal, Romania, Slovakia, Slovenia, Spain, Sweden, UK ↩