The German Energiewende 707 ......................................................................................................... The European Journal of Public Health, Vol. 26, No. 4, 707–712 The Author 2015. Published by Oxford University Press on behalf of the European Public Health Association. All rights reserved. doi:10.1093/eurpub/ckv212 Advance Access published on 29 December 2015 ......................................................................................................... The German Energiewende—a matter for health? Robynne Sutcliffe, Ester Orban, Kelsey McDonald, Susanne Moebus Centre for Urban Epidemiology, Institute for Medical Informatics, Biometry and Epidemiology, University Hospital of Essen, University of Duisburg-Essen, Germany Correspondence: Robynne Sutcliffe, Centre for Urban Epidemiology, Institute for Medical Informatics, Biometry and Epidemiology, University Hospital of Essen, University of Duisburg-Essen, Hufelandstraße 55, 45147 Essen, Germany, e-mail: [email protected], Tel: +49 201 92239 291, Fax: +49 201 92239 333 Background: Germany’s enormous transformation away from nuclear energy and fossil fuels towards a renewable and energy efficient system—called the Energiewende—is playing an essential role in Germany’s economy and policymaking. This article summarises the current knowledge on possible health impacts of the Energiewende and describes the need and opportunities to incorporate health into energy-related policy. Methods: A structural model helped to narrow down specific topics and to conceptualise links between the Energiewende, the environment and health. A comprehensive literature search was conducted within policy documents and scientific databases with English and German language selections. Results: Of 7800 publications first identified only 46 explicitly related energy measures to health, of which 40 were grey literature. Notably, only 12% published by health authorities all others were issued by environmental, energy or consumer protection agencies, ministries or institutions. Conclusion: Our study shows that health impacts of the German Energiewende are rarely explicitly addressed. An integration of a health perspective into energy-related policy is needed including the involvement of public health authorities. A health impact assessment can be a suitable tool to support and evaluate Energiewende-related developments from a health perspective. ......................................................................................................... Introduction As evidence of the harmful effects of climate change has accumulated, Germany—on its own and as part of the European Union (EU)—is actively implementing mitigation strategies. The debate on climate change and the rising evidence that mitigation strategies are needed to reduce greenhouse gas (GHG) emissions and other climate altering pollutants1,2 led to a EU agreement on climate and energy-related policy action. The EU established a binding commitment to reduce emissions by 2020, to raise the share of EU renewable energy consumption and to improve the EU’s energy efficiency.3 In 2000, the German Federal Government implemented the Renewable Energy Sources Act (EEG), which remains the principle tool for managing and commissioning the renewable energy sector in Germany (last renewed in 2014).4 After the Fukushima disaster in 2011, the German government immediately shut down eight nuclear power plants in the country, nearly a third of Germany’s nuclear power capacity. This prompted the Energiewende. Germany’s enormous energy transformation is more than just a nuclear energy exit. The Energiewende is a complex restructuring of Germany’s energy system by expanding renewable energy and increasing energy efficiency to replace fossil fuels and nuclear power. The main targets within the Energiewende are to:5,6 reduce GHG emissions by 40% by 2020, increase the share of renewables in energy consumption and gross electricity production = to 60 and 80%, respectively, by 2050 and decrease primary energy consumption by 50% by 2050. Meeting these ambitious targets will have profound impacts on Germany’s energy supply, infrastructure, economy and technology. Despite expansion of the wind, photovoltaic (PV) and biomass sectors during the last 13 years,5 as well as previous measures to improve energy efficiency, Germany must implement additional measures and technologies across many sectors to achieve its goals. For example, the Energiewende not only sets out high energy-efficiency standards for newly constructed buildings but also calls for complete refurbishment of old houses and buildings. Another approach to increase energy efficiency is to promote clean vehicles within the transport sector, most commonly known as electric and hybrid vehicles (EVs). The plan set out by the German government is to introduce 1 million electric cars by 2020 on German roads.5,6 As Energiewende policy is not implemented by health authorities, the link between the Energiewende and health may not be immediately clear; nevertheless the public health implications of energyrelated changes are important to consider. Energy-related research has shown that renewable energy systems and energy efficient measures may provide opportunities to improve public health.7,8 For example, estimates suggest that switching to a cleaner energy system will reduce emissions of carbon dioxide (CO2) and other climate altering pollutants,1,2 thus ensuring several co-benefits for human health.8,9 Furthermore, by decreasing carbon intensity of electricity generation as well as by enhancing energy efficiency, emissions can be reduced and consequently some of the possible health burden from air pollution. Energy efficient transportation can also lead to changes in mobility demand and mode, inducing possible beneficial behavioural changes and decreased noise and air pollution. Refurbishment of houses into energy efficient buildings may improve health in cold winters by also protecting against mould and dampness.8,10–13 It is also important to acknowledge the potential for negative effects of these energy-related changes on health. For example, low carbon systems have to be maintained otherwise they can impose possible health risks on the population.8 In short, switching to a cleaner energy system will not only affect global climate change2 but also may have profound impacts on population health at the local level.9 Therefore, this research addresses the Energiewende, its corresponding changes and its possible effects on health either positive or negative. Without a doubt the German Energiewende and its rapid changes are affecting all sectors of society.5,6 Therefore, it is necessary to (1) analyse if health impacts are considered in the Energiewende and if so to what extent, 708 European Journal of Public Health (2) summarise the current knowledge on possible energy-related health impacts and (3) highlight the needs and opportunities to incorporate health into energy-related policy. Methods A structural model (figure 1) based on the WHO Driving forces, Pressure, State, Exposure, Effect and Action (DPSEEA) framework14 helped define the scope of our research. The DPSEEA model allowed us to conceptualise links between the Energiewende, the environment and health to detect and prioritise the topics and key words for the literature search (figure 1). Key words which were used for the literature search are provided in bold in figure 1: renewable energy, energy efficiency, conservation of energy resources, energy production, recycling, transport, biomass, environment, health. A comprehensive literature search was conducted within scientific databases and policy documents (grey literature) between July and October 2013 with English and German language selections. Literature published before 2000 was excluded since the Energiewende was not introduced until then. We also distinguished between explicit/implicit connections to health within the literature. Explicit connection means that there is a clear formulated reference made to health outcomes, effects or health problems, whereas an implicit connection to health suggests logical consideration within the literature. Figure 2 represents an overview of the identified literature. Scientific databases A literature search was conducted in PubMed, the Thomson Reuters Web of Knowledge, Scopus and Cochrane using combinations of terms for energy-related topics and selected health topics (as detailed later). MeSH Terms were used where relevant. Title and/or abstracts were reviewed. The inclusion criterion was that a significant pressure-state-exposure chain as seen in figure 1 was represented in the literature. Ideally this chain also included an explicit connection between exposure and health effect; however, literature with more implicit connections were also included. Key terms that helped to identify the literature were: emission and/or exposure, environment, health, human and/or impact. Grey literature The literature search also included reports, guidelines, reviews, handbooks, brochures, leaflets and website texts (grey literature) from governmental and non-governmental institutions and organisations. Online databases from German ministries and agencies, both federal and state, as well as international agencies and organisations were searched. The search was not confined conventionally to search algorithms but rather to themes of Energiewende-related policy topics: energy transition, renewable energy, energy efficiency, resource, raw material, waste, recycling, transport/mobility, (built) environment, (indoor) air quality. Literature was identified on the basis of title, table of contents and abstracts. Publications were excluded if they did not address energy and resource policy topics in relation to health and/or environment. Special key words included: emission and/or exposure, environment, health, human and/or impact. Results Of more than 7800 publications first identified, 72 publications (21 scientific studies, 19 reviews, 32 reports) were considered as relevant (figure 2), of which 46 explicitly related energy measures to health. Notably, 40 of the 46 publications came from grey literature, the vast majority (88%) stemming from environmental, energy or consumer protection agencies, ministries or institutions and only 12% being Acon Driving Forces Pressure State Exposure Health Effect ENERGIEWENDE Social policy Economic policy Climate change migaon Changes in energy and resource policy and nuclear power exit Energy producon/ generaon e.g. wind, solar, dal, biomass, … Energy consumpon/ efficiency e.g. materials, covers and paints in houses, insulaon, energy saving light bulbs, … Physical Environment Built Environment Biodiversity, Polluon to air, water, soil Buildings, Indoor climate, Mobility and transport Transport and Mobility e.g. electric vehicles, … Occupaonal Environment Occupaonal hazards, Mechanical processes Waste e.g. recycling, raw materials, … Socio-economic Environment Producon control Emission control Waste control Clean technology Environmental improvement Employment, Environmental jusce, Educaon Environmental Exposure (dose) Educaon, Awareness Exposure and suscepbility to (Air, water, soil) polluon, mould/dampness, noise/infrasound, injuries Health outcome Physical, mental and social well-being Figure 1 The Energiewende and health according to the DPSEEA framework (adapted from Corvolán et al. 200014) Treatment The German Energiewende 709 7,817 records overall idenfied 629 records through grey literature searching 7,188 records through scienfic database searching Excluded (n= 350) Excluded records (n= 6,999) Title, Keyword and Abstract screen (n= 279) Title and keyword screen (n=189) Excluded (n= 244) Excluded records (n=160) Abstract screen and full text review (n=29) Full text review (n= 35) 8 records through hand searching 72 records finally included Figure 2 Flow diagram for literature search commissioned and issued by health authorities. Up to this point it appears from our research that the public health scientific community have had limited involvement in setting Energiewende policy in Germany, whilst the relatively few public health considerations have been driven by environmental agencies. The literature search showed that energy-related research and specifically Energiewende-related research have focussed on evaluating key environmental impacts from specific energy sources, which are commonly based on a life cycle assessment (LCA). This tool is a ‘technique to assess the environmental aspects and potential impacts associated with a product or process (p.2)’,15 including ‘evaluation of possible hazards in each life cycle stage and/or major contributing process (p.3)’.15 Possible emissions to air, soil and water are calculated and external costs, such as economic, occupational and to some extent social impacts, are assessed.16 Although LCAs are a useful tool to understand health-related outcomes, health impacts were not always analysed explicitly within the identified literature using LCA. Overall, we found few explicit or implicit connections to health referenced in the Energiewende literature. Yet even in these relatively few references, we found potential positive and negative effects of the Energiewende on health. In the following paragraphs, key findings from the literature search are thematically summarised and presented. If possible specific health considerations or energyrelated interventions for the German context are given as examples. Electricity generation from renewable energy sources LCA shows that manufacturing emissions are of concern to health. For example, the production and recycling of PV panels may exposure people to toxic metals and chemical processes,17–19 the potential effects of which are still uncertain as PVs are relatively new.20 In regard to wind energy, the literature identified focuses particularly on health concerns from noise and infrasound levels as well as the production of shadow flickers or possible ice throw.21–24 The research in regard to wind energy is mainly interested in possible noise related sleep disturbances, stress and the reduction in quality of life.21–24 In Germany, appropriate guidelines have already been implemented that reduce the possible negative health impacts from wind energy such as proximity to neighbourhood and duration of rotation. Bioenergy Switching to wood-fired heating systems (on district scale or inhome heating) can reduce GHG emissions (CO2).25,26 However, wood combustion for direct heat use can be a major contributing source of fine particulate matter (black carbon, organic carbon) in urban areas and in indoor buildings,25 something which is known to be relevant for climate and health. The WHO reports that particulate matter (PM) from biomass can be associated with certain adverse health effects such as effects on the respiratory and possibly also on the cardiac system.27,28 In 2010, Germany introduced new regulations that considered appropriate standards (lower threshold of emissions) and requirements (in production, quality, use and maintenance) for such heating systems, especially for older models to reduce the possible adverse health effects.29,30 The use of bioethanol and biodiesel, as compared with traditional diesel and fossil fuels, reduces CO2 emissions;26 however, the use of those fuels to reduce harmful emissions remains controversial, as exposure to certain chemicals is still possible, especially during biochemical processes. The use of pesticides and fertilisers during cultivation may damage soil, air, water and biodiversity. Other concerns include the effects of sustainable forestry during the cultivation, origin and transportation of wood or crops and biological materials.31 Energy efficiency via the built environment Energy efficient homes can improve the indoor climate,32 and thereby may improve mental and psychosocial wellbeing.12 Furthermore, better insulation measures reduce the exposure to outside pollutants and prevent moisture accumulation that may 710 European Journal of Public Health lead to mould growth.33 However, better insulation also requires regular control of ventilation, as reduced air exchange has the potential to cause an undesired increase in exposure to indoor pollutants.8,10,12 Energy efficiency in housing has become one of the major pillars of the Energiewende, which has lead to not only the refurbishment of old buildings and the introduction of energy efficient heating systems, but also to an increase in standards for newly constructed buildings, especially public buildings. Furthermore, strong focus has been given on guidelines to inform the public about ventilation within their homes. Transport, mobility and EVs A central feature of EVs is that they are virtually emission free at local level, with the exception of minor emissions from brake and tire abrasion. A further advantage of EVs is that they are possibly quieter and thus reduce noise levels in areas with low speed levels. However, this depends on the type of vehicle.34 Recent discourse about EVs has discussed the potential for increased risk of pedestrian and cyclist accidents and injuries due to the missing noise of approaching vehicles. Empirical data for this aspect do not exist yet.34 A review by Thomson et al.35 (p. 1) demonstrated that the ‘health impact assessment (HIA) of transport interventions is still characterised by uncertainty and competing values at local or wider level’. Recycling With regard to renewable and energy-saving technologies, the impact of extraction and supply of critical raw materials together with thier waste management are of concern. During extraction and the processing of critical resources (burning of waste) possible toxic and harmful pollutants can be released into air, soil and water.36,37 The impacts of current and future recycling procedures are still difficult to assess due to lack of data and inadequate experience— especially with regard to health-related issues and occupational safety requirements. Discussion From our literature search, we observed that possible health benefits and risks are rarely explicitly, if at all, considered within the discourse of the German Energiewende. Although it appears that most Energiwende-related measures were driven by environmental concerns, it should not be neglected that this inevitably can have an impact on the health of the population. Nevertheless, the link to health is often not clarified within the identified literature, except for those specific energy-related measures that were summarised earlier and that specifically considered health effects. A reason for this may include the difficulty of estimating possible health impacts within such complex settings. Still, extensive peer-reviewed epidemiological evidence links health effects to certain concentrations of pollution13 or environmental exposures. From the evidence available, it is possible to extrapolate potential impacts on human health. In most cases within the Energiewende literature, this reference is missing; only environmental effects are described without any classification or characterisation of possible consequences for health, either positive or negative. A further rationale for the lack of explicit attention to health in the Energiewende emerged from our research. It appears as if the public health scientific community have had limited involvement in setting Energiewende policy in Germany, whereas the relatively few public health considerations have been driven by environmental agencies. This may arise due to the fact that public health authorities in Germany are not involved in the implementation of Energiewende policy, although some public health professionals are actively engaged in internal Energiewende-related discussions. As a result energy-related health impacts are still not sufficiently considered in the development of Energiewende measures and technologies.38 Our results suggest the need for a thorough examination of possible public health effects of the expanding renewable energy sector and the development of further technological improvements. Thus, public health authorities and the German public health scientific community should be involved more in the question of possible health impacts. These impacts may originate not only from environmental but also economic, social and occupational issues. Importantly, a thorough examination of the Energiewende health effects should highlight not only health risks but also health benefits arising from the emerging energy-related technologies. In this regard, public health professionals could use a HIA tool for evaluation of the Energiewende and its individual measures and future technological developments on public health. The WHO (1999) defines a HIA as ‘a combination of procedures, methods and tools by which a policy, programme or project may be judged as to its potential effects on the health of a population, and the distribution of those effects within the population’.38 A HIA not only measures health impacts in terms of quantitative data but also qualitatively, considering important participatory aspects. Integrating a HIA into current energy policy decisions can provide a systematic comparison of energy options from a health perspective.38 For example, HIA can help to identify the possible determinants of health, which are to some extent affected by energy-related decisions, such as technological development, transport and housing. At the same time, it helps disseminate information and knowledge to the population who can then implement healthy behaviours in terms of energy efficiency and sustainable living. Furthermore, HIA can facilitate cooperation and those synergies between public health authorities and other Energiewende-related sectors which are currently lacking. The Energiewende is a crosscutting issue affecting many sectors within German policymaking; therefore, existing tools such as HIA can help to bring together different sectors.38 Germany’s Energiewende is a unique and historic transition to a highly efficient energy system, which has been recognised not only nationally but also internationally. Transforming a major economy to a more efficient energy system is a step forward to reduce GHG emissions and possible adverse health consequences of climate change. As other countries especially in the European Region consider energy-related changes, the Energiewende provides important information on possible effects, including those on health. By getting directly involved in the Energiewende discourse, public health authorities can seize the opportunity to help shape policies that may have a large-scale impact on population health. Public health authorities and professionals can also provide people with concrete information on possible health benefits and risks in regard to specific Energiewende-related measures and technologies. Although our understanding of some of the Energiewende-related measures and technologies and their potential effects on health is still developing and may be difficult to assess, the health effects should be evaluated and integrated into energyrelated policy. Funding The literature study underlying this article was supported with funding from the German Federal Environment Agency (Umweltbundesamt). The responsibility for the content of this publication lies with the authors. The work was also presented at the 11th International Conference for Urban Health, Manchester, 4–7 March 2014 and at the German The German Energiewende Society for Social Medicine and Prevention (DGSMP) in Erlangen, Germany, 23–26 September 2014. Conflicts of interest: None declared. Key points Direct impacts of the Energiewende on health are relatively unexamined. Further involvement by the public health community within the Energiewende is urgently needed. Life cycle assessment (LCA) is a useful tool to examine possible emissions to air, soil and water but rarely leads to explicit examination of health impacts Health impact assessments (HIA) can help to inform energyrelated policy decisions that are attentive to public health 711 14 Corvolán C, Briggs D, Zielhuis G. (eds.) on behalf of the World Health Organization Decision-Making in Environment Health: From Evidence to Action. E&FN Spoon, London and New York 2000. 15 Environmental Protection Agency. US EPA Life Cycle Assessment: Principles and Practice. Available at: http://www.epa.gov/research/NRMRL/std/lca/pdfs/chapter1_ frontmatter_lca101.pdf (27 February 2014, date last accessed). 16 Joint Research Centre. The International Reference Life Cycle Data System (ILCD) Handbook (online version). 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Definition from the Gothenburg Consensus Paper, 1999. World Health Organization: Available at: http://www.who.int/hia/about/defin/en/ (27 March 2015, date last accessed). ......................................................................................................... The European Journal of Public Health, Vol. 26, No. 4, 712–717 The Author 2015. Published by Oxford University Press on behalf of the European Public Health Association. All rights reserved. doi:10.1093/eurpub/ckv217 Advance Access published on 3 December 2015 ......................................................................................................... Mortality in Italian veterans deployed in Bosnia–Herzegovina and Kosovo Riccardo Capocaccia1, Roberto Biselli2, Raffaella Ruggeri1,2, Cristiano Tesei1,2, Enrico Grande1, Lucia Martina1, Anna Rocchetti2, Stefania Salmaso1, Massimiliano Caldora1, Silvia Francisci1 1 Cancer Epidemiology Unit, National Center of Epidemiology, Istituto Superiore di Sanità, Rome, Italy 2 Italian Defence General Staff, General Inspectorate of the Military Health Service, Rome, Italy Correspondence: Riccardo Capocaccia, Cancer Epidemiology Unit, National Center of Epidemiology, Istituto Superiore di Sanità, Rome, Italy, e-mail: [email protected] Background and Aims: The possible increase of cancer risk in military personnel deployed in Balkans during and after the 1992–1999 wars, mainly related to the depleted uranium, was addressed by several studies on European veterans of those war theatres. This article reports on the results of the mortality study on the Italian cohort of Bosnia and Kosovo veterans (Balkan cohort). Methods: Mortality rates for the Balkan cohort (71 144 persons) were compared with those of the Italian general population as well as to those of a comparable and unselected control cohort of not deployed military personnel (114 269 persons). Ascertainment of vital status during the period 1995– 2008 of all the persons in the two cohorts has been carried out through deterministic record linkage with the national death records database, from information provided by the respective Armed Force General Staff, and through the civil registry offices of the veterans’ residence or birth municipalities. Results: The Balkan cohort experienced a mortality rates lower than both the general population (SMR = 0.56; 95% CI 0.51–0.62) and the control group (SMR = 0.88; 95% CI 0.79–0.97). Cancer mortality in the deployed cohort group was half of that from the general population mortality rates (SMR = 0.50; 95% CI 0.40–0.62) and slightly lower if compared with the control group cancer mortality rates (SMR = 0.95; 95% CI 0.77–1.18). Conclusion: Balkan veteran cohort did not show any increase in general mortality or in cancer mortality. ......................................................................................................... Introduction he presence of an increased cancer risk in military personnel Tdeployed in Balkans during and after the 1992–1999 wars has been widely debated, mainly related to the depleted uranium (DU) enforced projectiles used on the battlefields. There is a general consensus that inhalation of impact aerosol and dust in target areas represents the most significant route of exposure.1 The hazard is attributable to either the chemical toxicity of the metal and the internal exposure to alpha and beta radioactivity in body tissues.2,3 Lung cancers, leukaemias and lymphomas are the cancer types expected to be most likely associated with this kind of exposure.4 As a consequence of the public concern, specific studies to evaluate an excess cancer risk in military personnel deployed in war theatres during the 1990s and 2000s have been carried out, first on US and UK veterans of the Gulf war,5–14 and then on UK, Swedish, Danish, Canadian, Italian, Dutch and Norwegian peacekeeping soldiers deployed in the Balkans region.14–19 Italian Armed Forces have been massively involved since the year 1995 in peace restoring and peace keeping operations in Bosnia and Kosovo. A committee appointed by the Italian Ministry of Defence reported20 a significant excess of Hodgkin Lymphoma cases diagnosed in the period 1996–2001, and no increased risk for other cancers. The longitudinal Bosnia Kosovo (BK) Study has been started in 2005, through a collaboration between the Italian General Directorate of Military Health, the Italian Ministry of Health and the National Institute of Health,21 to describe the health profile of the Italian veterans cohort deployed in Bosnia and Kosovo (Balkan
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