Suchergebnisse

This dissertation concerns Sveriges Kommunistiska Parti (SKP) [the Swedish Communist Party] – in 1967 renamed Vänsterpartiet kommunisterna (VPK) [the Left Party – the Communists] and in 1990 renamed Vänsterpartiet (V) [the Left Party] – and the Party's process of coming to terms with history and its communist legacy. The aim of the study is to describe and analyse the SKP/VPK/V's process of coming to terms with history for the period 1956-2006, and to set out and problematise the driving forces and constraining mechanisms of this process. The theoretical framework of the study consists of Gunnar Sjöblom's theory about party strategies of political parties in multi-party systems and Michael Freeden's conceptual approach to ideology analysis. During the period of study the SKP/VPK/V has, like no other political party in Sweden, been ascribed historical guilt regarding its own party history but also regarding the effects of world communism. The Party has thus found itself in a situation where it has had history as an adversary. The process of coming to terms with history has mainly revolved around three issues: independence (1956-1977), international ties (1977-1989) and a broadening beyond the communist tradition (1986-2006). The internal debate within the Party has linked these issues to calls for change aimed at ridding the party of what is considered undesirable elements of the Communist legacy. By analysing the arguments pursued in favour of these calls, it is possible to pick out a number of the driving forces behind the Party's process of coming to terms with history, namely an ambition to obtain vote maximisation, programme realisation and maximisation of parliamentary influence. The urge to distance the Party from certain aspects of its communist past has thus been related to fundamental goals that political parties in multi-party systems seek to obtain. The results of the dissertation show that it is possible to pick out five main constraining mechanisms in the Party's process of coming to terms with history. 1) The safeguarding of Party cohesion. 2) The safeguarding of the distinctive character of the Party. 3) The need to resist external pressure. 4) The desire to avoid unfair apportioning of blame. 5) The safeguarding of the right to define the substance of one's own ideology. The existence of these constraining mechanisms help to explain why the process of coming to terms with history lingered on for several decades, and also why it seems to have been a process of such complexity for the Swedish Communist and Post-Communist Party.

This study deals with the ethnopolitical mobilization among the Sami in Sweden during the first half of the 20th century. The investigation focus on why this mobilization took place, the demands the Sami made, and the strategies used to achieve these goals. Opposition towards the Swedish Sami policy was the most important reason for the political mobilization among the Sami. Both the formation of the Sami policy at the central administrative level, and the implementation of the policy at the regional and local level by the Lapp administration were criticised. During the first half of the period of investigation the Sami protests focused on policy decisions at central government level. During the later half of the period, it was the actions of the Lapp administration that triggered Sami activity. The central demands brought forward by the Sami movement concerned the position of the Sami in Swedish society. At the beginning of the period the Swedish Sami policy was based on the so called "Lapp shall remain Lapp" ideology. The Sami were looked upon as a reindeer herders by nature, who were weak and could not protect themselves against civilization, which was viewed as a threat to the cultural survival of the Sami. Therefore, they were to be protected by being segregated from the surrounding society. Only the reindeer herding Sami, however, were considered to be Sami which meant that a majority of the Sami population was not included in the Swedish Sami policy. A cultural boundary was drawn, which separated the Sami population into two large segments. Because of this, the main demands of the Sami movement were that the Sami should be granted an equal position in the Swedish society and that the Sami policy should include more aspects than just reindeer herding.Two main strategies were adopted by the Sami leaders to achieve the goals of the Sami movement. The first was to try to create a network of local Sami societies within a national Sami organization. As in Swedish society group interests were represented by a number of different organizations, Sami organizations were a precondition if the Sami were to be able to hold a dialogue with the Swedish authorities. However, during the period of investigation the Sami movement failed in its attempts to form a national Sami organization, which weakened the movement. The second strategy was directed at achieving more limited gains through goal-oriented actions, where the Sami were mobilized for shorter periods behind different demands. This second strategy was more successful during the period of investigation. However, ultimately the creation of a national Sami organization, was found to be a requirement if the Sami movement was to be able to influence the Swedish Sami policy. The formation of Svenska Samernas Riksförbund (National Union of the Swedish Sami) in 1950 was therefore an important step for the Sami movement.

The IENE 2014 conference puts emphasis on the "greening" of transport infrastructure: both in respect to a wiser use of marginal infrastructure habitats to favour biodiversity and certain ecosys- tem services, and in respect to a more permeable and safer infrastructure that minimises the direct impact on wildlife. Transportation and infrastructure are recognised as signi cant drivers in the global loss of biodiverity. Their impacts on nature are well described and there is ample evidence for the negative effects of traffic and transportation infrastructure on nature. Even though roads and railroads may occupy but a small proportion of an area, they a ect the entire landscape, cause the death of millions of wild animals, and disturb surrounding habitats through pollution, noise and alien species. The overall impact is evident, but there are means to minimise the pressure, to adjust infrastructure facilities and, to some degree, introduce beneficial services for wildlife. Such measures can and should be implemented as a standard in infrastructure development and maintenance. Knowledge about their functionality and e cacy is, however, not always satisfying. Technical innovations and new mitigation concepts need to be tested and evaluated. Their func- tionality and e ectiveness also depends on the interplay between the transport sector and other sectors of society. Communication, knowledge transfer, and public education are just as essential here, as legal frameworks, policy, technical development and environmental science. European policy (e.g., Green Infrastructure) is developing clearly in this direction, recognizing the transport sector and transportation facilities as important players in the endeavour towards a greener and sustainable future. Obviously, this calls for international collaboration in research and practice, for enhanced exchange of knowledge between disciplines, and for the development of harmonised standards and pro- cedures that can be referred to by international actors. IENE provides this interdisciplinary arena through its conferences and workshops. The IENE 2014 international conference emphasises that transport infrastructure can be planned and designed as an ecologically well-adopted, safe and e cient system, while acknowledging that certain impacts can never be avoided. IENE, together with the Swedish Transport Administration, the Swedish University of Agricultural Sciences, the Danish Road Directorate and numerous other partners, invites scientists, practitioners and planners, governmental agencies and private companies, NGO's and anybody with an interest in the above to the IENE 2014 conference in Sweden. We welcome new partner- and sponsorships and o er a well-approved and international network for communication and presentation.

In the wake of an emerging knowledge society, universities around the world have come under severe institutional pressure from changing national research policies, financing organizations´ new strategies and turbulent research dynamics. This study examines how Lund University in Sweden manages these institutional pressures. The study explores how the university leadership ? rector and the governing board ? have (1) articulated the normative foundations of the university, (2) experimented with and structured the research organization, (3) explored new internal governance structures and steering strategies, and (4) developed institutional structures for closer integration with industry and commercialization of research results. The study develops a conceptual framework focusing on processes of institutional change and on how organizations react on these processes. Especially, I elaborate on the notion of institutional evolution developed within the tradition of historical institutionalism, and the processes and mechanisms behind different evolutionary paths. In the empirical parts of the study, I first analyze processes of institutional change within modern science. The study departures from and criticizes three popular frameworks of contemporary science and research dynamics: the ?Triple Helix? framework, the concept of ?post-academic? science and the transition from a ?Mode-1? to a ?Mode-2? type of knowledge production. The study then continues by analyzing international research policy trends, the developments within Swedish research policy and the governing structures within the field of higher education. The analysis of Lund University over more than two decades reveals an organization using a growing number of different normative foundations and organizational models and structures in its daily operations. The study also demonstrates the gradual transformation of the internal governance structure with recurrent attempts to strengthen the steering core at the central university level. The analysis also points to the successive integration with regional industry, as well as the building up of technology transfer structures and mechanisms within the university during the last 10 to 15 years. The case study demonstrates how the university loyally tries to adapt to a complex and changing environment by elaborating its hybrid character. In conclusion, the analysis in this study shows, on the one hand, the emergence of a ?post-academic? research system containing new institutional logics, governance structures and borders. On the other, hand the case study of Lund University illustrates the evolutionary transformation of a Swedish ?Humboldtian? university. This is a transformation where elements of the ?Entrepreneurial University? are added on to and fused with classical European university norms and structures.

Behovet av forskning om beslutsprocesser rörande investeringar i vägar och banor har uppmärksammats av KFB och Vägverket i slutet av 1990-talet. Denna studie lämnar sitt bidrag genom att redovisa och analysera den beslutsprocess som ledde fram till att ett mitträcke och 2+1 körfält anlades på E4 norr om Gävle. Med hjälp av dokument, pressklipp och intervjuer belyses utvecklingen från Nollvisionens etablering till projektets följder i form av nya mitträcken. Faktorer som problemformulering, sökande efter alternativ och värdering av konsekvenser redovisas. Sättet att organisera processen, externa intressenters inflytande samt deltagarnas roller, aktivitet och attitydutveckling belyses. Processen prövar och realiserar en helt ny utformning av vägar. Kunskapsprocessen står i centrum. Den gäller både undersökning av genomförbarheten, problemet att övertyga skeptiker och vinna acceptans samt upplevelsen av att ha åstadkommit en väsentlig innovation vad avser trafiksäkerhet. Studien lyfter fram både det specifika med detta fall och det allmängiltiga hos planering av vägar och därmed infrastruktur. – Behovet av vidare kunskapsutveckling avseende teoretiskt och empiriskt underlag för kunskap om beslutsprocesser belyses. ; The need for conducting research on decision-making processes as regards investments in roads and lanes has been paid attention to by the Swedish Transport and Communications Research Board (KFB) and the National Swedish Road Administration in the late 1990,s. This study delivers its contribution by accounting for and analysing the decision-making process that resulted in wire railings of central reserves being set up and 2 + 1 lanes being built on the European Highway No. 4 to the north of Gävle. By means of documents, press cuttings and interviews, light is being thrown on the development, from the establishment of the Vision Zero to the consequences of the project in the form of a new type of wire railings. Factors such as formulation of problems, search for options and assessment of consequences are accounted for. Ways and means to organise the process, external interested parties' influence and the participants' roles, activities and attitude development are highlighted. This process submits to testing an entirely new design of roads and puts it into practice. The process of acquiring experiences is in the centre of attraction. It applies to both the feasibility study, including the problem of convincing sceptics and gaining their acceptance, and the experience of achieving a substantial innovation in the road safety area. The study emphasises both the specific aspect of this case and the generally applicable with road planning and accordingly infra structure. The need for further development of know-how as to a theoretic and empiric knowledge bank of decision-making processes is additionally highlighted.

This study examines the changes of total organic carbon (TOC) concentrations in 20 Swedish lakes throughout Sweden using pre-industrial (1860) TOC0 inferred from near-infrared spectrometry (TOCNIRS) of lake sediments to determine if land use change over time could be a plausible explanation for changes in lake water TOC. The study also focuses on the importance of using inferred pre-industrial data of lake water pH and TOC for acidification assessment, in particular ANC0. Most lakes in this study show a long-term decreasing trend of TOC from 1860 up to -0.45 mg/l/yr-1 to an identified breaking point where the TOC turns from decreasing to increasing. Fifteen of the lakes have a breaking point in the mid to late 20th century (1950-1980) while five lakes do not display a clear breaking point. The magnitude of the increasing trend of TOC after the breaking point is up to 0.16 mg/l/yr-1 . Changes in land use were studied by comparing historical maps with present databases of land use. Land use changes in the catchment area show substantial differences in forest cultivation; for instance the coniferous forest has increased by 26% on average. This increase is due to removal of native forest (deciduous forest) and removal of wetlands. Two major conclusions can be drawn from the effects of land use change on TOC levels: (I) No direct correlation between land use change and long-term trends of TOC could be identified in this study. Previous studies have identified the effects of land use change on the carbon storage in the catchment area that corresponds well with the findings of this study. (II) the character of the forest land plays an important role when discussing the effects of land use change for long term TOC trends. The change from open-ended forests with large trees to intense managed forest is considered as an important driving force for TOC. To determine reference conditions there is a need to make good estimations of ANC0 for acidification assessment in Swedish lakes. This study examines the precision of MAGIC model ANC0 calculations (ANC0-MAGIC) against ANC0 calculated with TOCNIRS, diatom-pH and calculated pCO2 (ANC0, diatom-NIRS). ANC0, diatom-NIRS shows a mean difference of (-31µeq/l) when comparing it with ANC0-MAGIC. In comparison, when using contemporary TOC (TOCt) mean lake value 1990-2005 (ANC0,diatom-TOC) the results show a mean difference of (-0.45 µeq/l) in comparison with ANC0-MAGIC. A better fit is generated with TOCNIRS then TOCt. This could be an indication that ANC0- MAGIC overestimates the acidification of Swedish lakes. The European Union's "Water 8 Framework Directive", which Sweden has implemented, requires that all surface waters within the Union's authority have achieved good ecological status by 2015. According to the ecological quality standard the differences between the pre-industrial pH and contemporary pH, i.e. ΔpH=pH0-pHt, should not be more than 0.4 units. This study shows that the long-term trends have to be accounted for when calculating reference conditions and ecological status for acidification

This study in contemporary history describes the transformation of the public sphere in Sweden during the period 1969-1999, and analyses the role of information technology and politics in the process. The overall aim of the study is to explain how, and why, the public sphere in Jürgen Habermas sense has deteriorated during a period of rapid technological and political change, when increasing attention has been given to information technology as a new tool for improving democracy and empowering citizens. Theoretical inspiration is drawn from two perspectives within the modern history of technology and sociology of technology; the LTS (Large Technical Systems) and STS (Science, Technology and Society) approaches, as well as from the regime theory concept within political science. This multidisciplinary framework provides the theoretical basis for the study, including terms as socio-technical systems, system builder, technification, interpretative flexibility, stabilization, closing and regime change. In addition, the analysis draws upon previous research in economic history, where focus often has been on the important role of institutions. The term path dependence is central in this tradition. The starting point for the study is the process of a mutual legitimization between citizens and political actors that traditionally has taken place within the public sphere. In return for citizens support and trust, political actors have granted format rights to the public space. Two aspects of this interdependence are addressed: Freedom of speech and citizen's access to public information, and their access to arenas where an exchange of political ideas and opinions is taking place. In the study, the former is a question of the legal system and the limits to freedom of speech in new medias such as the Internet, while the latter concerns citizen's technical means and possibilities to connect to electronic networks. Research interest is concentrated on the formal political system, focusing both actors and structural factors such as technological development, media convergence, ideological change and international integration in the transformation process. Four case studies of institutional changes during formative moments, within what is defined as the legal and the technical infrastructures, are conducted and represent the empirical base of the thesis. The case studies are centered on Swedish governmental commissions, on the government itself and on proceedings in the parliament, and concerns formation and transformation of computer law, as well as the deregulation and privatization of the technical infrastructure. In the latter process Televerket (Swedish Telecom) has been an influential promoter of competition and institutional separation between tele- and data communications, representing a major regime change in favour of market relations in the technical infrastructure. In the area of computer law, the Swedish regime dominated by SCB (Statistics Sweden) was incorporated into a joint European data protection regime, resulting in limitations of freedom of speech on the Internet. These regime changes have also transformed the role of the state, constituting a "net watchers state". Another important finding is that promotion of democracy and improvement of access to the public sphere, never was on the agenda in the political transformation processes studied, although a parallel discourse on democracy and information technology existed throughout the period studied.

The grandiose, but failed, attempts to produce silk in Sweden in the past have been largely ignored by historians. This thesis describes the history of sericulture in Sweden, including three periods of practical trials in 1735-1765, 1830-1898 and 1913-1918. For a long time, the secrets of sericulture were closely guarded in China but by the beginning of the 16th century, knowledge of silk cultivation techniques had reached a number of European countries. The pursuit of domestic silk production was often a costly undertaking instigated by royalty. Since conditions in Sweden and Denmark were partly similar, there was some degree of influence and cooperation between these neighbouring countries. The chapters dealing with attempts at silk production during the 18th century and the history of sericulture in northern Europe are primarily based on printed sources and literature. Several of the 18th century silk farmers documented their experiments, allowing us to follow their efforts and ideas on the feasibility of silk farming in Sweden. The descriptions of the two latter sets of Swedish silk production trials presented in the thesis are primarily based on archive materials, mainly consisting of minutes and annual reports. The history of sericulture in Sweden began in the mid-1730s, when Mårten Triewald conducted experiments and exhaustively described and published these. Carl Linnaeus was a significant influence in Swedish sericulture during this early period. Naturalists were hired as plantation managers and were tasked with supplying the silk industry in Sweden with home-produced raw material. The work was prompted by the desire to find an alternative for the huge Swedish imports of raw silk from China and Southern Europe. However, silk farming never became particularly common, despite the financial incentives available for producing silk and planting mulberry trees during the 1750s in the belief that some 'extravagance' was beneficial for society as a whole. When the 'Hats' position of power ended, so did the financial support for manufacturing luxury goods. Founded in 1830, the Swedish Association for Domestic Sericulture was active for nearly 70 years thanks to foreign influences and the notion that silk farming could be a popular livelihood. Members of the Swedish Royal Family served as patrons and several well-known scientists participated in the projects. The Association furnished mulberry plants and seeds, together with silkworm eggs, most of which were distributed to plantations controlled by the Association or county agricultural societies. However, the Association's annual reports show that many private individuals also planted mulberry trees and some pursued silk farming. Sericulture growing trials were carried out at a number of sites across Sweden, on the initiative of Jacob Berzelius, among others. These trials were mainly funded by Government grants, but numerous wealthy individuals also made contributions to the sericulture venture. Some income was generated by the silk products produced, which were almost solely bought by the Swedish Royal Family. The Swedish Sericulture Association was founded in southern Sweden in 1913 but this third brief foray into sericulture produced few results. All three periods of sericulture trials were initiated by enthusiasts with a firm belief that some silkworm host plants would survive the Nordic climate. There were a number of claims that the white mulberry tree had become acclimatised, but an equal number of cold winters and springs proved the opposite. Ultimately, Swedish sericulture was never economically feasible, since the natural conditions were unfavourable and the output from Swedish silk production was modest, and the cost high, in relation to imported silk. The almost 200-year history of sericulture in Sweden provides an important glimpse into the obsessions and culture of the age, but there were far too many obstacles for the dream of Swedish silk ever to become a reality.

The current report deals with the effect of transport time and associated transport conditions on animal welfare and meat quality. The work is part of the EU EU and Animal Welfare Agency /Swedish Board of Agriculture, funded project CATRA (QLK5—1999-01507: Minimising stress inducing factors on cattle during handling and transport to improve animal welfare and meat quality: www.bt.slu.se/catra/). The project was composed of eight work packages: Baseline survey, Effect of transport time (below 14 hours and long distance more than 14 hours), Effect of vibration and motion (to be conducted both in laboratory and field conditions), Optimising pre-and post-transport handling, Air quality in the vehicles, cattle transport logistics including route optimisation, and development of control system. The purpose of the project was to gather sufficient data and to develop methods for controlling and minimizing stress inducing factors during handling and transport of cattle; develop guide-lines and recommendation for end-users, such as meat and vehicle industries and the policy makers, to improve animal welfare and meat quality on the European level. This could be fulfilled through optimization of design of handling areas, transport vehicles, and transport-associated conditions, and by promoting an IT-supported effective logistic system. Hence cattle welfare and meat quality will be improved, thereby enhancing the economic competitiveness of producers and abattoirs. As part of CATRA, this part of the project is the work done in Sweden regarding the effect of transport time, with the objective of determining the effect of transport time (up to ll hours) on animal welfare and post mortem meat quality, when cattle are transported from farms to abattoirs by commercial vehicles. The ultimate objective is to optimise transport time in relation to welfare and meat quality taking into consideration other stress inducing factors. Animals on which the experiments performed were cows, heifers, bulls and calves. Response parameters that were considered were: blood parameters (cortisol, glucose, lactate, CK,), clinical parameters (heart rate, postural stability), meat parameters (bruising score, PH-24, tenderness), and ethological parameters. Input parameters considered were parameters for loading facilities (ramps, lifts), penning systems (stocking density, social group, standing orientation, design of loading compartment), air quality (air speed, relative humidity, evenness of temperature in the compartment, level of NH3, CO2), vibration, transport time, resting time, and feeding regimes. Simultaneous and continuous measurement of heart rate, body temperature, air quality parameters, and video recording was conducted from farm to the abattoirs. Blood samples were taken before and after transport, and also during resting. The results obtained indicated that the transport and handling events are stressful for the animals as a whole, and loading and un-loading are among the most stressful events in the studied conditions. Regarding transport time, the results showed that transport time after six hours is particularly stressful for the animals when transported with usual vehicles without special equipments. In this case, it was reported a significant correlation between transport time and animal stress evaluated by physiological parameters. However, less detrimental effect of transport time on meat quality has been observed. It may therefore be concluded that transport time has influences more on animal welfare than meat quality when transported in conventional vehicles. Transport preceding and initiating conditions and processes such as keeping system, preparation, loading, planning and management, as well as unloading and lairage at the end of the transport chain are important challenges bearing various possibilities to improve welfare and meat quality. Loading and unloading facilities (such as ramp, driveways, and side-block) and quality, of floor have significant influence on both welfare and meat quality. Cattle from tied housing systems are more stressed by transport than untied cattle and there is a greater risk to develop bad carcass- and meat quality. As regard to air quality, the concentration level of ammonia and carbon dioxide increase with transport time and it occasionally passes the acceptable level when only natural ventilation is used. During the field experiment no detectable methane has been found. To prevent thermal stress, the installation of mechanical ventilation system (both for cooling and heating purposes) is recommended. The conclusions deduced from the current studies are as follows: - Transport conditions, as a whole is stressful for animals and compromise their welfare. - Loading and unloading activities are the most stress inducing factors identified using the heart rate measurements and behaviour observations - Result of the analysis of blood parameters showed that level of stress correlates with transport time. Calves are most sensitive to transport time followed by bulls, and cows are relatively less sensitive to transport length. - Transport time after six hours is stressful for the animals when transported with usual vehicles without special equipments. However, less detrimental effect of transport time on meat quality has been observed, - The evenness of temperature in the loading pens depends on season and number of stops - Concentration level of ammonia and carbon dioxide increase with transport time and it occasionally passes the acceptable level.

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.