Space life sciences: A status report

The scientific research and supporting technology development conducted in the Space Life Sciences Program is described. Accomplishments of the past year are highlighted. Plans for future activities are outlined. Some specific areas of study include the following: Crew health and safety; What happens to humans in space; Gravity, life, and space; Sustenance in space; Life and planet Earth; Life in the Universe; Promoting good science and good will; Building a future for the space life sciences; and Benefits of space life sciences research

A Tale of Clean Cities: Insights for Planning Urban Sanitation from Ghana, India and the Philippines

A Tale of Clean Cities is a research project commissioned by WaterAid to Partnerships in Practice, to learn from the experience of cities in developing countries that are making good progress in planning and providing city-wide sanitation services. San Fernando in the Philippines, Visakhapatnam in India, and Kumasi in Ghana were studied

Final report for Project no. 1904. Prevention of selected diseases and parasites in organic pig hreds - by means of HACCP based management and surveillance programme (CorePig)

The project partners comprised about 20 researchers from 9 research institutes in eight countries (DK, DE, SE, UK, CH, IT, AU and FR). The project is composed of three work packages: WP1 „Coordination of the project, dissemination and Knowledge synthesis‟, WP2: „Epidemiological study in organic herds‟ and WP3: „Development and evaluation of a HACCP based surveillance and management system‟. WP1 and WP2 started in 2007, while WP3 that built on the results from WP1 and WP2 started later - in 2008. The UK and CH-partners only participated in WP1 and WP3 while the remaining partners participated in all three WP‟s. The project was initiated at the project kick-off meeting in Denmark, August 30-31st 2007, where all project partners met to discuss the planning of the project in detail. Further 6 project meetings were carried out in the project period. The second project meeting was organised in Austria, December 10-11th 2007, the third project meeting in Denmark, February 18-19th 2008, the fourth in France, July 7-9th 2008, the fifth in Italy, December 4.-7th 2008, the sixth in Sweden, June 29-30th 2009 and the final and seventh project meeting took place in Germany, April 7-10th 2010

Development of criteria and procedures for the evaluation of the European Action Plan for Organic Agriculture

This final report provides a synthesis of the results of the EU-funded ORGAP project, with the title “European Action Plan of Organic Food and Farming - Development of criteria and procedures for the evaluation of the EU Action Plan for Organic Agriculture”. This project started in May 2005 and was completed in April 2008. The overall objective of this project was to give scientific support to the implementation of the EU Organic Action Plan (EUOAP) by the development of an evaluation toolbox. In the project 10 partners from 9 countries (CH, UK, DE, IT, DK, SI, CZ, NL, ES) participated, as well as the European umbrella organisation of the Organic Agricultural Movements (IFOAM EU Regional group), ensuring a broad stakeholder consultation process and dissemination all over Europe. Chapter 1 describes the background and the objectives, structure and the outcome of the ORGAP Project. It shows that since the late 1980s, organic farming development in the European Union (EU) has been stimulated mainly by two factors, one related to strong consumer demand, supported by the EU regulation defining organic food, and the other to policy support for the provision of public goods. Responding to concerns that area payments as ‘supply-push’ measures can impact negatively on the markets for organic products, policy-makers have started to take a more integrated approach to policy using the ‘action plan’ mechanism. Action plans can be found in most EU member states. At national level, action plans provide a mechanism to ensure a balanced policy mix, reflecting different aims and the various supply-push and demand-pull policy instruments available, tailored to local conditions. In 2004 the European Commission launched the European Action Plan for Organic Food and Farming. The plan contained 21 action points, which relate to the following areas: • Consumer information and promotion campaigns; • Improved research, market intelligence and statistical data collection; • Full utilisation of the rural development programme and other existing options to support organic farming; • Improving the transparency, scope and implementation of the regulation defining organic farming In the meantime, the European Commission has started to implemented most of the actions. In chapter 2 a brief history about organic action plan development is given, in particular about the European as well as national organic action plan for organic food and farming. The European Action Plan for Organic Food and Farming (EC 2004) is the result of a three-year process of developing the Action Plan, starting in 2001. This process led to: a Commission staff paper exploring the options for an action plan in 2001; the establishment of an independent expert working group in 2002, a public internet consultation on specific options in February 2003; a European Parliament hearing on the action plan options in June 2003; and a public hearing on the action plan options in January 2004. In June 2004 the action plan was decided by the EU Council in June 2004, following significant internal debate within the Commission and the EU Parliament. The involvement of stakeholders in the development of the EUOAP was mainly in the explorative phases involving identification of organic sector development needs and possible solution phase. The actual action plan was prepared after the public hearing in January 2004, so that stakeholders were not able to comment on the action plan document or the balance of individual actual action points. During the subsequent implementation phase, primary responsibility also rests with the EU Commission, with input from the EU Council, EU Parliament and member-state government representatives, with only limited input from other stakeholder groups. The European Commission has started to implement the actions of the European Organic Action Plan, many of which have been achieved or are at an advanced stage of completion. The most significant initiatives are the publication of the new Council regulation (EC) 834/2004 on organic production and labelling of organic products and the consumer information campaign. The development of national organic action plans started in Europe in 1995 when Denmark introduced its first organic action plan. Denmark thus acted as a forerunner and pioneer in this field. Nowadays, most EU Member States have organic action plans for organic food and farming. Of those that don’t, some have plans in preparation. Under the framework of the ORGAP Project, six national (CZ, DK, DE, IT, NL, SI) and two regional (Andalucia (AND), England (ENG) action plans for organic food and farming were com-pared. As a consequence of the very different situation in the eight case-study countries, the action plans studied vary in their scope. The English and the Dutch action plans represent market-driven and demand-led approaches with a clear focus on market development measures. The German Federal Organic Farming Scheme on the other hand puts a distinct emphasis on informational policy instruments to strengthen the organic sector through consumer information as well as through research and development. Finally, the Andalusian, Czech, Danish, Italian and the Slovenian action plans represent quite broad approaches integrating a broad portfolio of measures targeted to supply and market development as well as to information and research. Apart from the Andalusian Action Plan, all other action plans studied include quantitative tar-gets. Most typically targets for organic adoption are set (CZ, DK, NL, SI and DE). However, the Dutch and Slovenian action plans include a combination of targets addressing the share of nationally produced organic products, the domestic organic market share in general, organic sales per capita and the development of tourist farms. The English action plan target was defined in terms of the proportion of the organic market for indigenous products supplied by domestic producers. To conclude, the case study action plans vary with regard to the development process, targets, objectives and the emphasis of measures on certain areas. This is due to quite different political and socio-economic framework conditions for organic farming in these countries. The comparison revealed that the weaknesses identified in the status quo analyses have only partly been translated to the targets and measures included in the action plan documents. This is on the one side a result of the national priority and budget setting and on the other side on the interdependency between EU policies and national policies. However, as all action plans were developed together with stakeholders, the composition of the stakeholder groups and the power of the initiating actor are crucial to the target and priority setting. In chapter 3 the authors write about organic action plans – what we know and do not know. This includes success factors, stakeholder involvement, coherence and consistency issues and the how to evaluate organic action plans with ORGAPET. What makes a successful action plan? This question is much more difficult to answer than it looks at first sight. Many other economic, social and policy developments influence the organic sector and often instances occur which have not been foreseen when a certain action plan was devised. Because of this a simple measurement of the state of a specific objective might be too simplistic. Under certain circumstances an organic action plan could already be regarded as a success if the measures contribute substantially to a development in the right direction. The point of reference would be here: What would have happened if the organic action plan would have not been in place? The second point to keep in mind in judging the success of an organic action plan is to be aware of the fact that such action plans are often not complete in a sense that they fully include all political measures directly relevant for organic farming. In such cases it is important to keep in mind and to analyse the broader policy and market environment relevant to organic farming in order to judge success of the action plan. Organic farming policies can of course only be successful if they are successfully implemented and need sufficient care and knowledge with respect to the often numerously legal conditions outside the specific organic farming area that influence implementation. It also means that a clear mission of implementation agencies and qualified and motivated personal involved are a key to successful organic policies and to successful organic action plans. Is the concept of an organic action plan an outdate concept? Some policy makers believe that it has been a fashion and its time is over. The authors of this report are convinced that any at-tempt to unify elements that influence organic farming and organic farming policies and to bring policies into an integrated, coherent framework will still be necessary and welcome in the future. Whether such attempts in the future will be called organic action plans is a different issue. Currently some key challenges include the question whether the general trend in agricultural prices has actually been reversed. If agricultural prices which tended to decrease in real terms throughout the 20th century are actually moving upwards due to factors such as increased demand for agricultural products, climate change and a possible slowdown of technological progress. Such general developments will also influence the development of organic farming and the development of suitable measures to support it. Some of the implications of a higher price level for conventional agriculture and a higher volatility of prices both in the conventional and organic markets might challenge the continuation of the traditional per hectare organic support policies. If climate change is actually perceived as the key challenge for decades to come then effects with respect to mitigate climate change of organic farming and with respect to the adaptive capacity of organic farming are quite important for any policy justification in support of organic farming. And finally, there is the productivity issue. If the actually demand for food stuff is increasing rapidly throughout the world then the obvious limitations of organic farming in this respect reported from industrial countries become more serious. In that context research and development supporting increasing productivity in organic farming might become much more important than in the past. It is clear that just looking at the originally envisaged targets and objectives might not be sufficient to judge whether or not an action plan has been successful. One key argument going be-yond clear targets and well balanced measures is that embedding action plan development in the wider policy area seems to be absolutely essential to be successful. However, there are a number of other issues to be dealt with which are also quite important prerequisites for successful organic action plans such as stakeholder involvement, coherence and consistency of action plans and an evaluation monitoring capacity. Stakeholder involvement may be understood and carried out in quite different ways including the provision of information, providing opportunities to comment on proposals, and empowering stakeholders to make their own choices. When preparing the toolbox aimed for evaluating the European Organic Action Plan in the OR-GAP project, attempts were made to involve both organic and mixed stakeholders in various steps in eight different national/regional settings and with different methods. These experiences form the background for recommending stakeholders with a purely organic and/or mixed portfolio to involve through group discussions in order to increase and optimize their analytical capacities and thereby their delivery of relevant information regarding the preconditions for implementing the EUOAP and for assessing its policy impacts. Parallel to this, relevant non-organic stake-holders could be involved on the basis of individual interviews or small group interviews. When deciding on which stakeholders to involve in any stage it is thus necessary to identify all stakeholders considered relevant to the issue and to clarify for each of them which perspective they represent in first priority. Therefore a general model for analysing stakeholder involvement in public policy on organic food and farming has been developed in the project. It includes a distinction of expertise involved in the three main perspectives of organic action plans realised in Europe up to now: the specific values defining organic food and farming; the market perspective as organic food in most plans is expected to develop in response to consumer demand; and a political recognition of the public goods delivered as a consequence of performing organic farming practices. With regard to each of these three perspectives, it is possible to specify expertise of stakeholders acting in the core or periphery of the perspective and to distinguish expertise of purely organic stakeholders and other stakeholders with a mixed or even non-organic expertise relevant for the development of policies in support of organic food and farming. The degree to which participatory methods realise their potential contribution depends critically on how carefully they are used and in what context. There is no one set of techniques to be mechanically applied in all contexts for all participants, but a diverse range of possible techniques which need to be flexibly adapted to particular situations and needs. Stakeholder involvement helps improving the information basis and the legitimacy of public policies. This is especially important on complex issues such as organic action plans, which involves actors with stakes in issues as different as the values of organic food and farming, the food market and the public goods of organic food and farming at one and the same time. Successful stakeholder involvement thus demands: careful preparations of which stakeholders to include at any stage of the policy process and of the methods used to promote participation; sufficient time for the stakeholder to react; this means at least 8-12 weeks of time for allowing substantial and broad participation, in particular in the case of involvement of farmers organisations, and good communication and transparency in each of the five stages of the policy process. Although this results in higher costs and more resources for those administrating the process, the outcome of such a process will improve the legitimacy and acceptability of the decisions and will facilitate very much the implementation (e.g. through public private partnerships). Such a more participative, transparent and time-balanced process helps to avoid unnecessary discussions and misunderstandings, which at the end might be more effective and cost-efficient. Project Synthesis For an evaluation of the internal and external coherence of the EU Organic Action Plan (OAP), the ORGAP project team generally made use of empirical methods and techniques suggested for analysing the synergy of programmes as well as their cross-impacts. A policy analysis of key synergies (positive and negative) was performed by means of a matrix of cross impacts as specified in the MEANS framework (EC, 1999). Two separate matrices were constructed: to appraise the internal coherence between the various measures of the EU Organic Action Plan; and to appraise the external coherence between the EUOAP and some national organic action plans. Experts involved in this evaluation process (Evaluation team) identified any synergy which may exist between pairs of measures or categories of measures. The effects of synergies or conflicts have been rated with the help of 2 electronic consultation rounds. After validation of these ratings, the calculation of the “synthetic” coefficient of synergy was performed, in order to evaluate the overall level of synergy/conflict within the European Organic Action Plan. The analysis suggests that Actions 9 (ensure integrity) and 10 (harmonisation of standards) are essential for the success of the EUOAP, given their synergetic effects. They in addition enter into synergy with many other actions. Interesting is also Action 13 (risked based-inspections) wit

Exploiting Qualitative Information for Decision Support in Scenario Analysis

The development of scenario analysis (SA) to assist decision makers and stakeholders has been growing over the last few years through mainly exploiting qualitative information provided by experts. In this study, we present SA based on the use of qualitative data for strategy planning. We discuss the potential of SA as a decision-support tool, and provide a structured approach for the interpretation of SA data, and an empirical validation of expert evaluations that can help to measure the consistency of the analysis. An application to a specific case study is provided, with reference to the European organic farming business

A systematic review of recommended modifications of CBT for people with cognitive impairments following brain injury

Due to diverse cognitive, emotional and interpersonal changes that can follow brain injury, psychological therapies often need to be adapted to suit the complex needs of this population. The aims of the study were to synthesise published recommendations for therapy modifications following brain injury from non-progressive traumatic, vascular, or metabolic causes and to determine how often such modifications have been applied to cognitive behavioural therapy (CBT) for post-injury emotional adjustment problems. A systematic review and narrative synthesis of therapy modifications recommended in review articles and reported in intervention studies was undertaken. Database and manual searches identified 688 unique papers of which eight review articles and 16 intervention studies met inclusion criteria. The review articles were thematically analysed and a checklist of commonly recommended modifications composed. The checklist items clustered under themes of: therapeutic education and formulation; attention; communication; memory; and executive functioning. When this checklist was applied to the intervention studies, memory aids and an emphasis on socialising patients to the CBT model were most frequently reported as adaptations. It was concluded that the inconsistent reporting of psychological therapy adaptations for people with brain injury is a barrier to developing effective and replicable therapies. We present a comprehensive account of potential modifications that should be used to guide future research and practice

ECUT (Energy Conversion and Utilization Technologies Program). Biocatalysis Project

Presented are the FY 1985 accomplishments, activities, and planned research efforts of the Biocatalysis Project of the U.S. Department of Energy, Energy Conversion and Utilization Technologies (ECUT) Program. The Project's technical activities were organized as follows: In the Molecular Modeling and Applied Genetics work element, research focused on (1) modeling and simulation studies to establish the physiological basis of high temperature tolerance in a selected enzyme and the catalytic mechanisms of three species of another enzyme, and (2) determining the degree of plasmid amplification and stability of several DNA bacterial strains. In the Bioprocess Engineering work element, research focused on (1) studies of plasmid propagation and the generation of models, (2) developing methods for preparing immobilized biocatalyst beads, and (3) developing an enzyme encapsulation method. In the Process Design and Analysis work element, research focused on (1) further refinement of a test case simulation of the economics and energy efficiency of alternative biocatalyzed production processes, (2) developing a candidate bioprocess to determine the potential for reduced energy consumption and facility/operating costs, and (3) a techno-economic assessment of potential advancements in microbial ammonia production

FØJOII-29: Nature Quality in Organic Farming. Midterm Status Report 2003

The work is organised in five work packages (WP 1-5, Table A1). Since the start in July 2001 the following work has been accomplished: WP 1. Starting up seminar and the annual seminars have served as a successful platform for project planning and cross-cutting activities. The general project co-ordination and planning of field work and selection of case study areas has been stimulated both at these meetings and in separate meetings with the WP responsibles. The first cross-cutting (CC4) has been accomplished in close co-operation with WP 5 and all project scientists. A homepage for the project is now available. WP 2. Eleven case areas with high concentration of organic farmers have been selected and 347 farmers have been interviewed. A database holding this information has been constructed. Organic farms show a regional specialisation similar to conventional farms. At the regional level organic farms are concentrated in counties with a higher share of dairy farms. Within counties however, there are important local differences with other factors involved. A GIS-based method for case-area delimitation in the PhD landscape study has been developed. WP 3. Inventory data from 24 organic farms in two case areas with information on vegetation composition and arthropods has been analysed. New species for Denmark was found and arthropod indicators showed a good correlation to nature quality. Colonisation experiments showed that moss diversity is favoured by grazing and reduced by fertilisation. There was significantly higher plant diversity in hedges and field boundaries on organic farms than on traditional farms. This effect is evident after only 3-4 years of Organic Farming Period and further increased after 7 years WP 4. Data from the same 24 organic farms and experimental fields of Foulum and Flakkebjerg has been collected in 2002 and 2003. Soil fauna diversity is influenced by soil type, tillage intensity and fertiliser use as well as crop and grazing history. In the experimental plots soil fauna and surface arthropods only showed little response to fertiliser use and catch crops. A 10x10-km landscape has been digitised in the ALMASS landscape model and appropriate scenarios and crop rotations are under construction. WP 5. Results from the first project workshop (CC4) in 2002 on indicators for esthetical qualities show that a more professional use of the esthetical experience is difficult for many natural scientist. Serious illness has postponed work in 2003 but the final outcome of the work package is expected to be achieved