Suchergebnisse

This study reflects on the recognised need for more joined-up, high-quality research on phytotherapy that addresses the current societal challenges in finding alternatives to the use of antibiotics. The study applied a multidisciplinary participatory approach in an expert workshop exercise within the FP7 EU IMPRO project. Prior to this study, a literature review was elaborated on research in the field of phytotherapy as applied to farm animals, cooperation between research bodies and initiatives to reduce the use of antibiotics by using phytotherapeutic remedies. The review was delivered to the participants of the workshop so as to receive feedback on it and enrich the discussion. Different expertise, background in research or veterinary practice, and varying positions regarding phytotherapy were the criteria in targeting participants. A structured workshop was subsequently organised, with questions to experts addressing scientific validation of phytotherapy, effective treatment under farm conditions and necessary developments for the future. Challenges identified by the experts were as follows: poor study designs, lack of reproducibility of studies, poor standardisation of products, cost-benefit concerns, lack of veterinarian training and poor data availability. To overcome obstacles, the need for improved study designs for clinical trials was given priority in order to prove the efficacy of remedies and to implement a monitoring system which enables the assessment of the effectiveness of treatments in farm practice. Reflections in this report are intended to be a resource for scientists, policy makers and end users for an effective use of phytotherapy at farm level.

Lithuania and Southern Sweden share similar natural conditions, but differ considerably in forest policies and management; thereby providing an opportune basis for comparative studies. Since the 1990s, Sweden has attempted to reduce the negative impact of its forest management on biodiversity, after decades of intensive production forestry. In contrast, Lithuania has been intensifying forestry practices associated with the post-soviet socio-economic transition. Here we assess the actual outcomes by comparing selected forest structure and composition variables known to be indicators for forest biodiversity; and estimate the prospective trends by scrutinising current forest policies and management. Our results indicate that Lithuanian forests consistently possessed higher rankings in six indices related to tree species composition, stand age, and deadwood quantities that are positively associated with forest biodiversity. The reverse is indicated by those data on stand age and tree diameter that are associated with centennial dynamics in forest utilisation intensity. With respect to policy instruments, Lithuania designates a substantially greater share of forest area to non-timber functions and legislates more severe management restrictions in forests targeting timber production. Concurrently, all estimates of forestry activities indicate more intensive forest management in Southern Sweden, including a higher share of artificial regeneration and shorter rotations. This allows concluding that, if current forest management practices persist, then an increased "biodiversity gap" may be expected between the two countries. The study concludes with discussing to what degree the identified trends are the direct product of targeted policies versus merely by-products of other factors.

The Swedish government has set the goal of taking a pioneer role and targeting a transition towards 100% renewable energy use until 2040. To reach this goal, the focus in energy production is shifting towards solar, hydro as well as wind power. Since 2010, wind power in Sweden is a fast-growing industry, promoted as one solution to reach climate goals and ensure more sustainability. Nevertheless, wind power is also criticised and the cause of several land-use conflicts all over Sweden. When it comes to the northern Swedish counties, wind power plants are overlapping with traditional Sámi herding districts. Especially here critical questions regarding a misrecognition of indigenous rights as well as the meaning and implications of justice in the current transition are raised. This Master thesis addresses the current development of wind farming on Sámi lands in northern Sweden within the energy transition and sheds light on wind-power related conflicts. Therefore, the analytical frameworks environmental justice (EJ) and frame theory (FA) are used, to identify and explain tensions and map possible leverage points. The thesis combines an empirically grounded approach to explore how actors actively involved in wind farming make meaning of environmental justice, and a theory-driven approach to identify leverage points and map injustices. For this reason, in total two methods are used to collect the empirical data material: semi-structured interviews (subjected to FA) as well as a literature review (subjected to the EJ framework). The results of the frame analysis show that within the actors actively involved in wind farming four different frames can be uncovered, which lead to differing problem definitions as well as suggested solutions. The identified frames cover due to their agenda-setting character not all injustices that were derived from literature review. Furthermore, within the frames several normative dilemmas and tensions were observed, that raise the necessity to reflect on existing frames as well as on the ...

The purpose of this dissertation is to describe and analyze how the Soviet Union attempted to win the sympathies of the Swedish population during the period 1945-1958 through the All-Union Society for Cultural Relations with Foreign Countries (VOKS) and the Sweden-Soviet Union Societies. The dissertation includes the central Soviet decision-making apparatus' general formulation of strategy and what means were to be used to win the sympathies of populations in other countries. Concerning VOKS's work targeting Sweden, this dissertation examines the general strategies and means used in practice. This dissertation links these activities with realism which serves as an analytical framework. Realism focuses states seeking their security in the international system. Security is considered achievable through strategies for using different means of force, in this case, diplomacy and its sub-instruments in the form of soft power and public diplomacy. Immediately after World War II, VOKS was seen by the Soviets as a tool for countering American and British propaganda. VOKS's reorganization in the early 1950s led to more country-specific activities. Increasingly in the 1950s VOKS sought out partners from outside organizations associated with national communist parties. This strategy aimed to optimally convey the message and to popularize the Soviet Union. This also led to a decline in VOKS's importance. VOKS during the period 1945-1958 can be viewed as a collaborative project between the state and the party. The Soviet Union, through VOKS, used the Sweden-USSR Society to popularize the country among the Swedish public. VOKS took increasingly greater control over the societies' activities, which were reviewed and approved by the Soviet Embassy in Stockholm and VOKS in Moscow. To develop these societies, VOKS increased its efforts to influence the Communist Party of Sweden (SKP) to take part in the societies' activities. At the suggestion of VOKS in Moscow, the local Sweden-USSR societies formed a national organization in the autumn of 1950 called the Sweden-Soviet Union Federation. After 1953, VOKS's interest intensified in implementing and developing cultural collaborations with other actors in addition to the societies. Near the end of VOKS's existence, representatives from the Soviet Embassy and VOKS tried to establish an intergovernmental cultural agreement with Sweden. However, no such agreement was ever signed. The Soviet Union continued to channel most of its public diplomacy toward Sweden through the societies.

[The problem of representation and bureaucracy. Minority administrators' practices of advocacy in public organizations]The issue of (un)equal representation and the politics of presence in political organizations is central to democratic legitimacy. The theory of representative bureaucracy suggests that the diversity in public organizations reinsures that the interests of different groups are represented in decision-making and implementation processes. The purpose of Nazem Tahvilzadeh's article is to enhance the understanding of if and how senior-level public administrators with ethnic minority background advocate groups whom they identify with. Advocacy is defined as the intention to benefit a certain group in order to improve their living conditions. The empirical material consists of 52 qualitative interviews in five Swedish municipalities, public documents and other written sources. The focus is on the narratives of 12 public administrators about their work and the issue of advocacy. The results show that advocacy does occur in public organizations and that it can be categorized in seven different practices targeting individuals or policy issues. The study actualizes the importance of representative public administration as a central quality of representative government.Publication history: Published original.(Published 2 December 2015)Citation: Tahvilzadeh, Nazem (2015) "Till frågan om representation och byråkratin. Minoritetsadministratörers företrädarpraktiker i offentliga organisationer", in Arkiv. Tidskrift för samhällsanalys, issue 4, pp. 121–149. DOI: http://dx.doi.org/10.13068/2000-6217.4.4 ; Frågan om (o)jämlik representation och närvarons politik i politiska organisationer är central för demokratins legitimitet. Teorin om en representativ byråkrati föreslår att mångfalden i den offentliga förvaltningen tillser att olika gruppers intressen representeras i respektive organisationers beslut och verksamhet. Syftet med Nazem Tahvilzadehs artikel är att öka förståelsen för om och i så fall hur tjänstepersoner med minoritetsetnisk bakgrund i ledande befattningar företräder grupper som de identifierar sig med. Företrädarskap definieras som ett medvetet handlande att gynna en viss grupps levnadsvillkor. Det empiriska materialet består av 52 kvalitativa intervjuer i fem svenska kommuner, offentliga dokument och andra textkällor. I fokus står 12 offentliga tjänstepersoners berättelser om deras arbete och företrädarskap. Resultaten visar att företrädarskap förekommer i offentliga organisationer och att detta kan kategoriseras i sju olika praktiker inriktat gentemot enskilda individer eller gentemot policynivå. Studien aktualiserar betydelsen av representativitet i offentlig förvaltning för representativa styrelseskicks kvalitet.Publiceringshistorik: Originalpublicering.(Publicerad 2 december 2015)Förslag på källangivelse: Tahvilzadeh, Nazem (2015) "Till frågan om representation och byråkratin. Minoritetsadministratörers företrädarpraktiker i offentliga organisationer", i Arkiv. Tidskrift för samhällsanalys, nr 4, s. 121–149. DOI: http://dx.doi.org/10.13068/2000-6217.4.4

In 1991, the Swedish Social Democratic government established the Pensioners' Council at the Ministry of Social Affairs. The Council's purpose and structure were spelled out by the Government in a Commission of Inquiry Directive. According to this, the Council is to be a forum for deliberations between the Government and pensioners' organizations. At the municipal level, Senior Citizens Councils have existed since the 1970s. They fill a similar purpose to that of the Pensioners' Council at the central level, namely to be an arena for political discussions between representatives from pensioners' organizations and the municipality. The purpose of this dissertation is two-fold. First, I describe the influence of pensioners' organizations on the establishment of the pensioners' councils and their political influence – potential as well as actual – in these councils. Second, I seek to explain the influence of pensioners' organizations from a power resources perspective. By doing so, I hope to contribute to our knowledge of the relationship between the welfare state and organized interests. Does this relationship imply the existence of a corporatist or pluralistic power structure? Finally, I also hope to contribute to our understanding of the future development of the welfare state in the light of a global economy and aging population. The empirical investigation on the central level suggests that pensioners' organizations influenced the decision to establish the Pensioners' Council. Moreover, they had actual as well as potential political influence through the council since the early 1990s. There success in influencing government policy is due to the fact that pensioners' organizations represent an important voting group and their employees have expert knowledge. At the local level, the empirical investigation suggests that pensioners' organizations had influence on decisions made by municipalities to establish Senior Citizens Councils. However, opportunities to influence vary at the local level, and pensioners' organizations actual political influence is limited. This limited influence can be explained as a consequence of pensioners' organizations lack of an important power resource at the local level – employed expertise. It is argued in the dissertation that the empirical results do not suggest an existence of a corporatist power structure in social issues. Rather, they point to a pluralistic power structure – i.e. along side producer organizations, other organizations (such as those for welfare consumers) also have an important power position. This, in turn, limits the ability of politicians to cut welfare spending. The case of pensioners' organizations therefore suggests that we cannot expect any drastic downsizing of the Swedish welfare state due to factors such as the globalization of the economy. In light of the aging population, the empirical results suggest that politicians will have to seek other solutions to be able to meet the challenge of financing welfare programs targeting the elderly than making drastic cutbacks in those programs.

Illegal hunting has constituted an expression of contested legitimacy of wildlife regulation across the world for centuries. In the following report, we critically engage with the state of the art on the illegal hunting phenomenon. We do so to reveal emerging scholarly perspectives on the crime. Specifically, we aim to capture the complexity of illegal hunting as a socio-political phenomenon rather than an economically motivated crime. To do so, we adopt a critical perspective that pays particular attention to the societal processes that contribute to the criminalization of historically accepted hunting practices. To capture perspectives on illegal hunting, fifteen researchers from various countries participated in an illegal hunting workshop in Copenhagen 16-17th June 2014. A primary contribution of the research workshop was to bring together criminologists, sociologists, anthropologists and geographers, each equipped with their own research perspective, to engage in a critical and interdisciplinary discussion on how to apprehend and constructively address the challenges of illegal hunting in contemporary society. A majority of those that attended were primarily based in the Nordic and the UK context, which motivated a strong focus on the illegal hunting that currently takes places in these countries. Similar trends of illegal hunting were identified across Europe, many of which traced from EU legislation on the reintroduction of large carnivores or other controversial wildlife conservation projects. In the workshop, proceedings took the form of individual presentations, plenary discussions and group work. Common themes that emerged from these presentations were: illegal hunting as communicating socio-political resistance; the targeting of specific species based on its symbolism or environmental history; illegal hunting as symptom of class struggles; the role of rewilding and domestication of nature on wildlife regulation; corruption, complicity and conflicts of loyalty in enforcement, and discrepancies and discontinuities in legality. These themes were framed in an understanding of illegal hunting as a complex, multifaceted expression that transgresses livelihood based motivation. Critical discussions conceptualised illegal hunting as a crime of dissent. This meant situating crimes as everyday forms of resistance against the regulatory regime. In so doing, the relationship between hunters and public authorities was highlighted as a potential source of disenfranchisement. In this interactionist perspective, illegal hunting tells us not just about the rationales of the offenders. It also elucidates the broader context in which non-compliance with regulation serves as symptoms of democratic and legitimacy deficits on the state level. Erratic transitions in legislation and a subsequent discord between legal, cultural and moral norms in society were identified as factors that contribute to the conflict. Crucially, the research workshop and the report contribute with three perspectives. First, it emphasizes the need to uncover the grey areas of complicity in wildlife crime. Previously corruption, bribery and selective law enforcement have been associated with wildlife trafficking in the global south, but this understanding is too blunt for the complicity that exists in many other contexts. Here conflicts of loyalty exist across several strata of society and differ in degrees. In highlighting this fact, we show a more opaque and contingent climate of complicity around illegal hunting in Northern Europe and elsewhere. Second, as crimes of dissent seeking to publicise injustices, illegal hunting and its associated resistance tactics are counterproductive by constituting a 'dialogue of the dead'. With this is mean that such communication is prone to distortion, misunderstanding and exaggeration and does no favors to hunters. There is consequently a need to move to a clarity of messages, as in institutionalised diogue processes. Third, hunting regulation cannot be seen in isolation to the broader differences in society in terms of values, economic factors and development. Research questions for future scholarship concluded the workshop and are summarized in the report. In terms of illuminating the junctures at which additional research is needed, these questions may provide important guidance. Above all, the report is intended as help for policy-makers, wildlife managers and law enforcement in better understanding and responding to the complexities of illegal hunting. We hope this will lead to more long-term preventative measures that address the core of the issue rather than proximate causes. The workshop was organized by the Environmental Communication Division of the Swedish University of Agricultural Sciences. The event constituted a part of the FORMAS funded research project Confronting challenges to political legitimacy of the natural resource management regulatory regime in Sweden - the case of illegal hunting in Sweden whose members include Erica von Essen, Dr. Hans Peter Hansen and Dr. Helena Nordström Källström from the Swedish University of Agricultural Sciences, Professor Tarla R. Peterson from Texas A&M University and Dr. Nils Peterson from North Carolina State University.

Knowledge and valuation of ecosystem services are important components for reaching the governmental goals for improving the natural environments. Recreational fishing has more than one million practitioners nationwide.Knowledge about the fishers and their catches increases the ability to assess whether the ecosystem services are retained. In addition, it gives means for evaluating the actions for the conservation, restoration and sustainable use of oceans, lakes and rivers. Knowledge of recreational fishing is also needed in order to follow up the details in its environmental objectives relating to outdoor recreation, tourism industry and the governmental goals in the open-air policy. The EU's common fisheries policy, the Swedish environmental policy and Swedish fisheries policy all emphasize that ecosystem-based management should be implemented. Thus, there are needs for knowledge of the ecosystems which are exploited by humans. Fish populations are important components of aquatic ecosystems, and are affected by the surrounding environment, while they themselves affect the structures of the aquatic food-webs. Fishes often have regulatory functions in the ecosystems, and thereby contribute to valuable ecosystem services in addition to the more obvious services as providing food and recreation for humans. Mostly issues regarding the impacts of fishing-related activities on fish populations have been focused on commercial fishing. A widespread and intensive commercial fishing may lead to the depletion of stocks or, at worst, a collapse of the fish populations; the fish population reaching such low levels that recovery may be difficult. In recent years the knowledge of the impact of recreational fishing on aquatic systems has increased, but still the effects of recreational fishing on ecosystem are relatively poorly studied, compared to commercial fisheries. For many, it may be difficult to accept that recreational fishing may affect fish populations; each fisher/angler favour just their own fisheries without bearing in mind that although the small influence from each individual fisherman may be small, it will be significant when many fishermen harvest from the same stock. Recreational fishing and its effects on the aquatic ecosystems are often neglected in fisheries science, mainly due to the lack of data to estimate recreational fishing harvest with a sufficient resolution to calculate the effort and landings of recreational fisheries. In this report, we try to give an overall picture of the fish species needing increased knowledge in order to get an estimate of harvest in recreational fisheries and thereby the effect on fish populations. Furthermore, we also try to give a picture of international studies and finally to give examples of methods concerning how and to what extent one may conduct studies in Sweden. Our proposal is largely based on combining different surveys in specific areas that we believe can be used to scale-up the results. We suggest data collation of recreational fishing is concentrated to areas with public waters, because in other water bodies the land owner has sovereignty under the law. The focus areas we point out are those already having some data collection, both in terms of recreational fishing and environmental monitoring / stock assessment and where there are non-fishing protective areas nearby. Collection of data should not be made in all areas at every year; three areas are suggested to become intensive areas (data collection every year) and the remaining areas data collection will take place every three years - on a rolling schedule. The sampling methods we recommend are national survey (i.e. mail and telephone surveys), recording of catches in fishing tourism, voluntary catch registration of individual anglers, collection of data from fishing competitions, on-site inventory of fishing effort (e.g. count fetter and trailers), inventory of catch per effort (e.g. by creel-surveys) and fish tagging studies. For the west coast we propose one focus area, Älgöfjorden. At the coasts of Bohuslän County and the northern part of Halland County the fishing pressure is high for lobster and crab and therefore a focus area should be established in this area. We suggest that data are collected by on-site visits for inventorying fishing effort (counting numbers of pots / buoys / fishing people), combined with catch registration can return an estimates on catch per effort, and this can then be applied to a larger area. Another potential focus area is the area around Torhamn (Blekinge) which, for example, is popular area recreational fishing for pike. Torhamn is one of three national reference areas for coastal fish monitoring on the East Coast and has been monitored since 2002. It is also desirable to study aspects of fishing mortality in recreational fisheries. To our knowledge, there are no national studies that have explored the effects of catch-and-release in natural environments over long periods of time. The Bråviken Bay is a relatively limited and well-defined area having considered high recreational fishing pressure, but large time series from fish monitoring programmes are lacking. This site will give good opportunities for studying pike, pikeperch and to some extent also sea trout, data collection is suggested to take place every third year. An adjacent area is Kvädöfjärden having fish monitoring time series from 1989. Closely situated to Kvädöfjärden is Licknevarpefjärden where fishing has been prohibited since 1970. Additional areas that are of interest to follow up with some regularity are Asköfjärden, Gålö and / or Lagnö in the Stockholm archipelago. In the future it might be fruitful to shift data collection intensity between Torhamn in Blekinge and an area in Stockholm archipelago. Such decision should be based on factors like where the most practical solutions / contact network can be found. In the Gulf of Bothnia angling with nets, traps and similar gears are relatively widespread. We suggest that Långvind Bay in Gävleborg County, is an area for the study of recreational fishing in a relatively sparsely populated county and is most likely typical for large parts of the Gulf of Bothnia. Data collection is suggested to take place every year. As for the Gulf of Bothnia the recreational fishery in the Bothnian Bay are mainly targeting the whitefish, sea trout and, to some extent also perch. By monitoring the recreational fisheries in Kinnbäcksfjärden near Piteå, we hope to be able to describe the local recreational fishing patterns and then apply these values for catch per effort for most of the coastal strip of the Bothnian Bays. Recreational fishing is widespread in all of the five largest lakes in Sweden, and there is a need for data collection in all five. In Lake Vänern, Lake Vättern and Lake Mälaren there are fish monitoring data of good quality and regularity. However, in the two smallest lakes, Lake Hjälmaren and Lake Storsjön in Jämtland County, few test fishing areas and few studies regarding recreational fishing have been made. For Lake Vättern we suggest that data collection is done every year; especially the archipelago in the northern part of the lake will be an excellent area for the study of recreational fishing for pike. In the other four lakes we propose that data collection is made every third year. By studying recreational fishing - its practitioners, scope, gear-use, and harvest, it will be possible to achieve a more detailed view of how recreational fishing is done and how it varies along the Swedish coast and in the five largest lakes. Such knowledge is important for the managers of common fisheries resources and the monitoring of environmental status and evaluating the recreational goals established by the Swedish governments.

In this report we aim to analyse the economic and environmental impacts of Pillar I direct payments, and to demonstrate alternative instruments that are better suited to achieve CAP objectives. The instruments—a targeted payment to land at risk of abandonment and a tax on mineral fertilisers—were selected on the basis of the Polluter Pays and Provider Gets Principles. We do this using two state‐of‐the‐art agricultural economic simulation models. The first model, CAPRI, is used to quantify the large‐scale or aggregate impacts for individual countries, the EU and the world. The other model, AgriPoliS, is used to quantify the fine‐scale or farm and field level impacts in a selection of contrasting agricultural regions, to consider the potential influence of the large spatial variability in agricultural and environmental conditions across the EU. The results show that direct payments are keeping more farms in the sector and more land in agricultural use than would otherwise be the case, and thus avoiding land abandonment, principally in marginal regions. Particularly the area of grassland is substantially higher, because it is generally less productive than arable land and hence more dependent on direct payments for keeping it in agricultural use. The magnitudes of the impacts of direct payments on land use therefore vary strongly across regions due to spatial variability in productivity: marginal regions with large areas of less productive land are heavily influenced by direct payments, while regions with large areas of relatively productive land are hardly affected, because this land would be farmed in any case. By keeping more farmers in the sector longer, direct payments are slowing structural change, which can hamper agricultural development. However the potential benefits of faster structural change vary considerably among our study regions. In relatively productive regions direct payments are hindering development, because too many farmers are staying in the sector and preventing the consolidation of land in larger farms, which would improve their competitiveness and increase farm profits. On the contrary, the mass departure of farms that is currently avoided, will not lead to the same general benefits in marginal regions. Instead of freed land being absorbed by remaining farms, large areas of relatively unproductive land are abandoned without payments. This land is unprofitable to maintain in agricultural land use, even if integrated into larger farms, because current market prices are too low to motivate farming it. Consequently direct payments pose a serious goal conflict: the avoidance of land abandonment on the one hand, which can have negative impacts on public goods, and restricting agricultural development on the other hand. Once again this goal conflict is rooted in the spatial variability of agricultural conditions in the EU. Maintaining extensively managed farmland, particularly semi‐natural pastures, is central for conservation of biodiversity and preservation of the cultural landscape. Therefore direct payments are contributing to the provisioning of these public goods, but principally in marginal areas. Further, abandonment of land can reduce its agricultural productivity due to erosion or afforestation. Thus, direct payments are contributing to food security by preserving the productive potential of land for the future, but only marginal land since relatively productive land is farmed in any case. Production of agricultural commodities is affected to a lesser degree by direct payments than land use per se. Nevertheless, food exports from the EU are higher and imports lower as a consequence of direct payments. However, the additional supply generated by direct payments also lowers output prices, which reduces the profitability of commodity production; thereby partially offsetting the additional revenues from direct payments. The higher agricultural output brought about by direct payments causes higher levels of environmentally damaging greenhouse‐gas emissions, nutrient surpluses and pesticide use. The higher greenhouse‐gas emissions for the EU are, to some extent, moderated by lower emissions in the rest of the world. Nevertheless, the net effect of direct payments is higher global emissions of greenhouse gases. The environmental impacts of higher nutrient surpluses and pesticide inputs are less conclusive, since these depend also on spatial factors, i.e., where the emissions occur. Although EU‐scale and regional emissions are higher due to direct payments, agricultural production is less intensive generally, on account of the lower output prices. Analysing the net effects of these two opposing forces requires additional biophysical modelling at relevant spatial scales, such as watersheds or landscapes, which is beyond the scope of this study. Pillar I direct payments generate a significant transfer of income to farmers and land owners who are not necessarily farmers; 40 billion euro annually. Of this transfer a substantial proportion goes to farmers in relatively productive regions and, further, to a minority of farmers that need them least. In relatively productive regions payments are not needed for continued agricultural production and preservation of farmland, but instead rather fuel higher land and rental prices, which hampers structural change. On the contrary, the need for support is greatest in marginal regions, because some form of payment to marginal land is needed to avoid its abandonment and the loss of associated public goods. Finally, the direct payments even come at the cost of lower market returns for farmers due to slower structural change (smaller and less competitive farms) and lower output prices (due to greater EU output). On the other hand the lower output prices lead to somewhat lower food prices, but at the greater cost of financing the direct payments. Our main conclusion is that Pillar I direct payments are generating serious goal conflicts due to spatial variability in conditions across the EU. On the one hand these payments are contributing to the provisioning of public goods by preserving marginal agricultural land. On the other hand they are hampering agricultural development, primarily in relatively productive regions. Payments to relatively productive land that would be farmed any way not only inflate land values (capitalisation) but also slow structural change, which are both likely to hinder agricultural development and hence the competitiveness of the EU on the global market. The direct payments also increase environmental pressure; by subsidising land use generally and the associated production, they are incapable of controlling environmentally damaging emissions, which is also in conflict with broad CAP objectives. The goal conflict arises because direct payments are universal, a payment principal that does not consider spatial variability in the EU and the associated trade‐offs in regard to development and environmental effectiveness. Our analysis considered two alternative policy instruments that have the potential to curb the identified goal conflicts associated with direct payments, by applying the Polluter Pays and Provider (of public goods) Gets Principles at appropriate spatial scales. Replacing direct payments with a payment targeted on marginal land (and associated public goods) prevents land abandonment at a lower cost, by avoiding payments to relatively productive land that is farmed in any case. This also allows surviving farms in regions with relatively productive land to compensate for lost direct payments through expansion and associated scale economies, as well as higher output prices. This instrument therefore finances the provisioning of public goods without adverse effects on development and the efficiency of agricultural production. The EU‐wide tax on mineral fertiliser demonstrates that this instrument has the potential to reduce nutrient surpluses. Since direct payments cause higher levels of polluting emissions, policy instruments targeting emissions at relevant spatial scales are needed to achieve cost‐effective abatement. Overall we find that Pillar I direct payments are not addressing the diversity of challenges facing European agriculture. In fact our quantitative analysis indicates that the potential for the current system to meet these challenges is seriously impaired by goal conflicts and spatial variability across the EU. A better policy requires that instruments are targeted on desired outcomes and designed according to sound principles, specifically the Polluter Pays and Provider Gets Principles. These principles would ensure that farmers are provided with appropriate incentives to i) generate public goods that otherwise would be underprovided; ii) mitigate environmentally damaging emissions at the lowest possible cost to society; and iii) continually strive to improve environmental performance. Such instruments are also fairer and promote a more competitive or viable agricultural sector by not obstructing structural change and hence agricultural development.