| 1. |
- Andersson, Karin, 1952, et al.
(författare)
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Pre-study on sustainability indices for shipping
- 2017
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Rapport (övrigt vetenskapligt/konstnärligt)abstract
- Demands on reporting and communication of the sustainability performance within a company as well as externally and how the demands on continuous improvement are fulfilled, has led to a development and also standardisation of sustainability indicators and indices. In shipping, like in all sectors, numerous indices or reporting systems have been developed and are used for various purposes. The aim has often been for communication with cargo owners and passengers, but also to be used as a basis for economic incentives intended to decrease emissions in ports and fairways. With increased demands on aspects included, it is obvious that a future sustainability index for shipping needs to include social and economic aspects in addition to natural environment and resource use. The present report is a pre-study with a review on existing indices in the shipping sector, and an outlook to other areas, followed by a discussion on possible development paths of more comprehensive sustainability indices. The conclusions are: The available environmental indices for shipping are many and there are initiatives, like CSI, that cover many relevant aspects. However, the indices are not very developed what concerns working conditions or socioeconomic costs. Also, economic parameters describing the ship-owner as a company are not included. The scrapping process foreseen for a ship can be further developed and included in indices. For further development, the following is suggested: • Develop indicators that can be used for describing work environment with the goal of introduction into an index. • The development of socioeconomic cost assessments, for example in terms of ecosystem services, is interesting and could be included in indices in the future. It is recommended that this development is followed for future use. • At the moment, there is not an easy way to include the economic dimension in terms of economic stability of the company in an index, but this should be further investigated. • The possible use of MRV (Monitoring, Reporting, Verification) in indices should be evaluated.
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| 2. |
- Johansson, L., et al.
(författare)
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Modeling of Leisure Craft Emissions
- 2020
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Ingår i: Springer Proceedings in Complexity. - Cham : Springer International Publishing. - 2213-8684 .- 2213-8692. ; , s. 205-210
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Konferensbidrag (refereegranskat)abstract
- Commercial shipping fleet and its emissions can be modeled in detail, but the emission from leisure craft are often invisible for activity based, bottom-up emission inventories. A new model (FMI-BEAM) describes the emissions from the leisure craft fleet in the Baltic Sea area, complementing the existing STEAM emission modeling suite. BEAM combines information from over 3000 boat marina locations, national small boat registries, Automatic Identification System data and boat survey results to derive leisure boat emissions for over 250,000 boats around the Baltic Sea coastline. The location of marinas and boat counts were determined from satellite images and other available data. With the BEAM leisure craft simulation model the spatial and temporal distribution of air emissions can be estimated. The presented results describe our first attempt to generate fuel consumption and emission inventory for small boats which have been underrepresented in current emission inventories. Small boat activity often occurs near the coastline in vicinity of populated areas and leisure craft emissions contribute to local air quality. The emissions of carbon monoxide and hydrocarbons are high compared to the emissions of commercial shipping, because very high emission levels are allowed for old small boat engines according to current legislation. The approach described in this paper can be applied in larger scale, for example to cover European coastlines in the future.
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| 3. |
- Kukkonen, J., et al.
(författare)
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Towards a Comprehensive Evaluation of the Environmental and Health Impacts of Shipping Emissions
- 2022
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Ingår i: Springer Proceedings in Complexity. - Cham : Springer International Publishing. - 2213-8684 .- 2213-8692. ; , s. 329-336
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Konferensbidrag (refereegranskat)abstract
- We present a new concept for marine research, applied in the EU-funded project EMERGE, “Evaluation, control and Mitigation of the EnviRonmental impacts of shippinG Emissions” (2020–2024; https://emerge-h2020.eu/ ). For the first time, both the various marine and atmospheric impacts of the shipping sector have been and will be comprehensively analyzed, using a concerted modelling and measurements framework. The experimental part of the project focuses on five European geographical case studies in different ecologically vulnerable regions, and a mobile onboard case study. The EMERGE consortium has also developed a harmonised and integrated modelling framework to assess the combined impacts of shipping emissions, both (i) on the marine ecosystems and (ii) the atmospheric environment. The first results include substantial refinements of a range of models to be applied, especially those for the STEAM and OpenDrift models. In particular, the STEAM (Ship Traffic Emission Assessment Model) model has been extended to allow for the effects of atmospheric and oceanographic factors on the fuel consumption and emissions of the ships. The OpenDrift model has been improved to take into account the partitioning, degradation, and volatilization of pollutants in water. The predicted emission and discharge values have been used as input for both regional scale atmospheric dispersion models, such as WRF-CMAQ (Weather Research and Forecasting—Community Multiscale Air Quality Model) and SILAM (System for Integrated modeLling of Atmospheric composition), and water quality and circulation models, such as OpenDrift (Open source model for the drifting of substances in the ocean) and Delft3D (oceanographic model). The case study regions are Eastern Mediterranean, Northern Adriatic Sea, the Lagoon of Aveiro, the Solent Strait and the Öresund Strait. We have also conducted a substantial part of the experimental campaigns scheduled in the project. The final assessment will include the benefits and costs of control and mitigation options affecting water quality, air pollution exposure, health impacts, climate forcing, and ecotoxicological effects and bioaccumulation of pollutants in marine biota.
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| 4. |
- Lunde Hermansson, Anna, 1987, et al.
(författare)
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Strong economic incentives of ship scrubbers promoting pollution
- 2024
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Ingår i: Nature Sustainability. - Göteborg : IVL Svenska Miljöinstitutet. - 2398-9629. ; In Press
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Tidskriftsartikel (refereegranskat)abstract
- In response to stricter regulations on ship air emissions, many shipowners have installed exhaust gas cleaning systems, known as scrubbers, allowing for use of cheap residual heavy fuel oil. Scrubbers produce large volumes of acidic and polluted water that is discharged to the sea. Due to environmental concerns, the use of scrubbers is being discussed within the International Maritime Organization. Real-world simulations of global scrubber-vessel activity, applying actual fuel costs and expenses related to scrubber operations, show that 51% of the global scrubber-fitted fleet reached economic break even by the end of 2022, with a surplus of €4.7 billion in 2019 euros. Within five years after installation, more than 95% of the ships with the most common scrubber systems reach break even. However, the marine ecotoxicity damage cost, from scrubber water discharge in the Baltic Sea Area 2014–2022, amounts to >€680 million in 2019 euros, showing that private economic interests come at the expense of marine environmental damage.
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| 5. |
- Moldanova, Jana, et al.
(författare)
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Framework for the environmental impact assessment of operational shipping
- 2022
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Ingår i: Ambio. - : Springer Science and Business Media LLC. - 0044-7447 .- 1654-7209. ; 51:3, s. 754-769
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Tidskriftsartikel (refereegranskat)abstract
- Shipping is an important source of pollution affecting both atmospheric and aquatic environments. To allow for efficient mitigation of environmental degradation, it is essential to know the extent of the impacts of shipping in relation to other sources of pollution. Here, we give a perspective on a holistic approach to studies of the environmental impacts of operational shipping through presentation of an assessment framework developed and applied on a case of shipping in the Baltic Sea. Through transfer of knowledge and concepts, previously used in assessments of air pollution, now applied to assessments of marine pollution and underwater noise, the horizon of understanding of shipping-related impacts is significantly improved. It identifies the main areas of environmental degradation caused by shipping and potential improvements through legislation and technological development. However, as the vast majority of contaminants discharged into the sea are not routinely monitored and assessed, the links between pressure of contaminants from shipping and environmental state and impacts will not be caught in the current environmental regulatory frameworks.
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| 6. |
- Moldanová, Jana, et al.
(författare)
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Physical and chemical characterisation of PM emissions from two ships operating in European Emission Control Areas
- 2013
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Ingår i: Atmospheric Measurement Techniques. - : Copernicus GmbH. - 1867-8548 .- 1867-1381. ; 6:12, s. 3577-3596
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Tidskriftsartikel (refereegranskat)abstract
- In this paper emission factors (EFs) for particulate matter (PM) and some sub-components as well as gaseous substances were investigated in two onboard measurement campaigns. Emissions from two 4-stroke main engines were measured under stable-load conditions. The impact of varying engine load on the emissions was investigated on one of the engines, and the impact of fuel quality on the other, where heavy fuel oil (HFO) with sulphur content 1% and 0.5% and marine gas oil (MGO) with sulphur content 0.1% were used. Furthermore, emissions from one auxiliary engine were studied. The measured EFs for PM mass were in the range of 0.3 to 2.7 g kg−1 fuel with the lowest values for emissions from the combustion of MGO, and the highest values for HFO with a sulphur content of 1%. The PM mass size distribution was dominated by particles in accumulation mode. Emission factors for particle numbers EF(PN) in the range of 5 × 1015–1 × 1017 # kg−1 fuel were found, the number concentration was dominated by particles in the ultrafine mode and ca. 2/3 of the particle number were non-volatile. The most abundant component of the PM mass was organic carbon, making up 25–60% of the PM. The measured EFs for organic carbon (OC) were 0.6 g kg−1 fuel for HFO and 0.2 g kg−1 fuel for MGO. Elemental carbon (EC) made up 10–38% of the PM mass, with no significant differences between HFO and MGO fuels. The concentrations of metals on sampled filters were investigated with energy dispersive X-ray fluorescence (EDXRF) and the detected metal elements in exhaust when using HFO was concluded to originate from both the fuel (V, Ni, Fe) and the lubricant (Ca, Zn), while for the case of MGO combustion, most of the metals were concluded to originate from the lubricants. The measured emission factors for sulphate particles, EF (SO2−4), were low, ca. 0.1–0.2 g kg−1 fuel for HFO with 1% sulphur, 0.07–0.09 g kg−1 fuel for HFO with 0.5% sulphur and 0.003–0.006 g kg−1 fuel for MGO. This corresponds to 0.1–0.8% and 0.1–0.6% of fuel S converted to PM sulphate for HFO and MGO, respectively. Scanning transmission electron microscopy (STEM) images of the collected PM showed three different types of particles: relatively pure soot; char and char-mineral particles; and amorphous, probably organic particles containing inorganic impurities. The maps of elements obtained from STEM showed a heterogeneous composition of primary soot particles with respect to the trace metals and sulphur. Temperature-programmed oxidation (TPO) of PM showed higher soot oxidation reactivity compared to automotive diesel soot, PM from the HFO exhaust being more reactive than PM from the MGO exhaust. Oxidative potential measured as the rate of consumption of Dithiothreitol (DTT) was for the first time measured on PM from ship exhaust. The obtained values were between 0.01 and 0.04 nmol DTT min−1 μg−1 PM, which is quite similar to oxidative potentials of PM collected at urban and traffic sites. The data obtained during the experiments add information about emission factors for both gaseous and PM-bound compounds from ship engines using different fuels and under different engine-load conditions. Observed variability of the EFs illustrates uncertainties of these emission factors as a result of influences from fuel and lubricant composition, from differences between individual engines and from the differences in sampling conditions.
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| 7. |
- Ytreberg, Erik, 1980, et al.
(författare)
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EMERGE deliverable 6.1. Baltic and North Sea report
- 2023
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Rapport (övrigt vetenskapligt/konstnärligt)abstract
- Shipping is responsible for a range of different pressures affecting air quality, climate, and the marine environment. However, most social and economic analysis of shipping have focused on air pollution assessment and how shipping may impact climate change and human health. This risks policies to be biased towards air pollution and climate change, while trading off impacts on the marine environment. One example is the IMO’s global sulphur cap, which requires shipowners to use a compliant fuel with a sulphur content of 0.5% (0.1% in SECA regions) or use alternative compliance options (scrubbers) that are effective in reducing sulphur oxide (SOX) emissions to the atmosphere. The scrubber process results in large volumes of acidic discharge water. Although regulations primarily target SOX removal, other pollutants such as polycyclic aromatic hydrocarbons (PAHs) and metals are transferred from the exhausts to the wash water and subsequently discharged to the marine environment. The aim of this deliverable has therefore been to develop a holistic framework to evaluate the impacts of shipping emissions, particularly those related to scrubbers, on the marine environment, human health, climate, and economy. The structure of this deliverable follows the well-established DAPSIR (Driver-Activity-Pressure-State-Impact-Response) framework, under which information, findings and conclusions from previous work packages are synthesized and integrated, including experiments of direct emissions from shipping to the marine environment (WP2) and the atmosphere (WP3), assessment of marine environmental impacts (WP2, WP4 and WP6), as well as human health and climate change impacts (WP5 and WP6). Finally, this deliverable provides recommendations and guidance for stakeholders and policymakers. The assessment is performed using a baseline scenario (year 2018) and three future scenarios (for year 2050) based on different projected future developments of shipping transport volumes and considering the development of ships regarding fuel efficiency and ship size. In this deliverable, we focused primarily on two of the different future scenarios, scenario 3 (high scrubber pressure) and scenario 8 (high use of liquefied natural gas (LNG) and methanol). The marine environmental risk assessment, performed in the Öresund region for the baseline scenario (2018), showed unacceptable risks when ships in the area were using open loop scrubbers. In the assessment, modelled predicted environmental concentrations (PECs) of open loop scrubber discharge water exceeded the tolerable marine threshold value (predicted no-effect concentration, PNEC) in almost the entire Öresund region. The PEC value was derived based on ship activity and discharges of scrubber water in 2018, while the PNEC value was derived based on the ecotoxicological assays performed within the EMERGE project. Notably, the modelling of open loop scrubber discharge water was performed using the ship traffic activity in 2018 when less than 200 ships in the Baltic Sea used scrubbers, collectively releasing 192 million tonnes of discharge water. By 2022 there were approximately 800 ships equipped with scrubbers in the Baltic Sea. In the high scrubber future scenario (S3) in 2050 this led to an assumption of the considerably higher scrubber water discharge (1740 million tonnes), representing almost one order of magnitude higher compared to our baseline scenario in 2018. In addition, our impact assessment, following Marine Environment Protection Committee (MEPC) guidelines, shows that a ban on discharge water from scrubbers should be considered in the entire Baltic and North Sea region, since all sea basins in the region fail to reach good environmental status (GES) as defined by the EU Marine Strategy Framework Directive (Directive 2008/56/EC). However, the costs of such a measure for the shipping sector (banning discharges from scrubbers, i.e., in practice a ban on scrubbers) have been questioned within the International Maritime Organisation (IMO). Therefore, EMERGE also focused on analysing to what extent the global scrubber fleet has reached break-even on their scrubber installations and the potential monetary gain of using Heavy Fuel Oil (HFO) as compared to the more expensive Marine Gas Oil (MGO) or Very Low Sulphur Fuel Oil (VLSFO). Our results showed that 51% of the global scrubber fleet had reached break-even by the end of 2022, resulting in a summarised balance of 4.7 billion €2019. In addition, the marine ecotoxicity damage cost, by not restricting scrubbers in the Baltic Sea Area, accumulated to >680 million €2019 from 2015 to end of 2022. For air quality, both future scenarios showed a decrease in shipping contribution to PM2.5 exposure by a factor of 2 to 3 compared to our baseline scenario in 2018. Scenario 8 is somewhat more efficient in decreasing the shipping originated PM2.5 than scenario 3. Using the Greenhouse gas and Air pollution Interactions and Synergies (GAINS) model for human health impact assessment in scenario 3 revealed the loss of life expectancy in most areas around the Baltic Sea, when considering all sources, to be limited to two to four months. However, the differences in life shortening between Scenarios 3 and 8 are two to three orders of magnitude lower when compared to human health impacts resulting from all sources, indicating that scrubbers alone have a minor impact on human health in the Baltic region from air quality perspective. For Öresund case the shipping-related health impacts from PM2.5 represented approximately 10% of the total burden of air pollution, in 2050 scenario simulations this burden decreased to 7-9%. Important improvement of air quality in the scenario simulations come also from reduction of NO2 which is a criteria pollutant regulated by the Air Quality Directive, where the decrease is 3 to 5-fold. In relative terms the shipping contribution to NO2 concentration levels, however, maintains similar, approximately 25%, as the land emissions are also expected to decrease. The GAINS health impact assessment for the Baltic Sea was compared to the Solent region using a statistical technique. The latter study showed that a relatively small fraction of all premature deaths in Southampton, Portsmouth, Poole, Christchurch & Bournemouth are attributable to air pollution from shipping, corroborating the conclusion that the deployment scrubbers alone has a minor impact on human life shortening through atmospheric transport.
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| 8. |
- Ytreberg, Erik, 1980, et al.
(författare)
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Framework to evaluate external costs of shipping
- 2019
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Rapport (övrigt vetenskapligt/konstnärligt)abstract
- The activities that utilize the marine environment are today many, ranging from oil and natural gas extraction, to fishing and aquaculture to renewable energy installations and finally shipping and leisure boating. Thus, there is a need to understand the pressures and impacts from the different sectors on the marine environment to ensure sustainable use of marine resources. One framework to study this is the ecosystem service approach where the benefit the natural environment supply to human society via economic and social benefits, are mapped and assessed as well as the associated costs of environmental degradation due to different human activities (Beaumont et al. 2007). Ecosystem conditions refers to the physical, chemical and biological condition of an ecosystem at a particular point in time. In EU, member states are obligated to monitor the condition (or status) of both freshwater and marine ecosystems. This is regulated via two EU Directives; the Water Framework Directive (WFD, 2000/60/EC) which covers freshwater, transitional and coastal waters up to 1 nm from the continental baseline and the Marine Strategy Framework Directive (MSFD, 2008/56/EC) which handles all marine waters up to the Exclusive Economic Zone. The overarching aim of both WFD and MSFD is that all water bodies in the EU shall reach or maintain god status of waters, habitat and resources. This condition is termed “Good Ecological Status” (GEcS) in the WFD and “Good Environmental Status” (GES) in the MSFD. The status and conditions of ecosystems are also strongly linked to human well-being through ecosystem services as ecosystems need to be in good status in order to provide multiple ecosystem services (Pandeya et al. 2016). Shipping is an activity responsible for a range of different pressures affecting the marine environment via discharge of hazardous compounds from greywater, bilge water, scrubber water and antifouling paints; emission of nutrients from blackwater, greywater, food waste and deposition of nitrogen oxides (NOX); emissions of acidifying compounds from scrubber wash-water and deposition of sulphur oxides (SOX); spread of invasive species from hulls or ballast water; and finally, underwater noise. Shipping also affect air quality, human health, and global warming via air pollutants with transboundary properties such as fine particulate matter (PM), volatile organic compounds (VOCs), nitrogen oxides (NOX), sulfur oxides (SOX). Emissions to air of black carbon and greenhouse gases such as carbon dioxide (CO2), methane (CH4) are also important for the global warming impact. The knowledge about ecosystem and health impacts of air pollution is comparatively well developed, much because land-based emissions of air pollutants have been regulated in international and national regulations since the 80-ies in a tight science-policy regime. Since the 80-ies, analytical progress has been substantial in areas such as air pollution inventories and monitoring, emission dispersion modelling, as well as integrated assessment modelling of cost effective international air pollution control. Since the 90-ies, these analytical progresses have been complemented with additional interest from environmental economists as well as health researchers. Currently, the effect of large-scale air pollution emission changes on ecosystem-, human health-, and economic impacts can be modelled with reasonable accuracy, and analysis of these impacts are done with established methods and models. Due to the transboundary nature of air pollution emissions, emissions are governed not only by national legislation but also by international legislation and agreements. Some examples of high relevance for shipping emissions are the revised EU Sulphur-in-fuels / Fuel Quality Directive (Directive No 1999/32/EC & 2009/30/EC) and the International Maritime Organisations’ (IMO) use of sulphur and nitrogen emission control areas (SECA and NECA respectively) as well as limits on sulphur content in fuel (IMO 2017). Although shipping emission impacts on air quality are relatively well established, the knowledge base is not the same for impacts on the marine environment and a coherent environmental impact assessment of shipping has not yet been made. This risk policies to be biased towards air pollution whilst trading off impacts on marine environments. Therefore, it is important that we gain a better understanding on how shipping and other sectors affect marine ecosystems, as the pressure on marine resources and the demand for marine ecosystem services in many marine water bodies are too high. The focus of this report is the shipping industry and to assess what damage it may cause on human health, marine ecosystems and the climate. Determining the total impact of shipping is a complex task, primarily with respect to marine ecosystems, as the water emissions is very diverse ranging from hazardous compounds, acidifying substances, underwater noise, eutrophying substances to invasive species. The aim of this report is to develop a framework to determine how different pressures from shipping affect ecosystem services and human health, with an emphasis on marine environment due to larger knowledge gaps in this area. The framework could in a later stage be used to determine the resulting cost for society due to shipping induced degradation of ecosystem services and impacts on human health and climate.
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| 9. |
- Ytreberg, Erik, 1980, et al.
(författare)
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Valuating environmental impacts from ship emissions – The marine perspective
- 2021
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Ingår i: Journal of Environmental Management. - : Elsevier BV. - 0301-4797 .- 1095-8630. ; 282
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Tidskriftsartikel (refereegranskat)abstract
- Shipping is an activity responsible for a range of different pressures affecting the marine environment, air quality and human welfare. The methodology on how ship emissions impact air quality and human health are comparatively well established and used in cost-benefit analysis of policy proposals. However, the knowledge base is not the same for impacts on the marine environment and a coherent environmental and socio-economic impact assessment of shipping has not yet been made. This risk policies to be biased towards air pollution whilst trading off impacts on the marine environment. The aim of the current study was to develop a comprehensive framework on how different pressures from shipping degrade marine ecosystems, air quality and human welfare. A secondary aim was to quantify the societal damage costs of shipping due to the degradation of human welfare in a Baltic Sea case study. By adding knowledge from marine ecotoxicology and life-cycle analysis to the existing knowledge from climate, air pollution and environmental economics we were able to establish a more comprehensive conceptual framework that allows for valuation of environmental impacts from shipping, but it still omits economic values for biological pollution, littering and underwater noise. The results for the Baltic Sea case showed the total annual damage costs of Baltic Sea shipping to be 2.9 billion €2010 (95% CI 2.0–3.9 billion €2010). The damage costs due to impacts on marine eutrophication (768 million €2010) and marine ecotoxicity (582 million €2010) were in the same range as the total damage costs associated with reduced air quality (816 million €2010) and climate change (737 million €2010). The framework and the results from the current study can be used in future socio-economic assessments of ship emissions to prioritize cost efficient measures. The framework can be used globally but the damage costs presented on the marine environment are restricted to emissions on the Baltic Sea and Kattegat region as they are based on willingness to pay studies conducted on citizens around the Baltic Sea where eutrophication and emissions of chemicals are particularly threats to the state of the Baltic Sea.
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| 10. |
- Abdulhamid, Hussam, 1974, et al.
(författare)
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A combined transient in situ FTIR and flow reactor study of NOx storage and reduction over M/BaCO3/Al2O3 (M=Pt, Pd or Rh) catalysts
- 2006
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Ingår i: Journal of Catalysis. - : Elsevier BV. - 0021-9517 .- 1090-2694. ; 244:2, s. 169-182
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Tidskriftsartikel (refereegranskat)abstract
- Transient in situ DRIFTS and flow-reactor experiments were performed to study the storage and reduction of NOX over Pt/BaCO3/Al2O3, Pd/BaCO3/Al2O3, and Rh/BaCO3/Al2O3 samples using CO, H-2, C3H6, or C3H8 as the reducing agent. The DRIFTS results show that exposure of the examined samples to NO2 results in the formation of nitrite/nitrate peaks over alumina and barium and that the reduction of stored NOX is influenced by the type of precious metal and reducing agent. Using CO as the reductant results in a lower NOX reduction capacity for Pt/BaCO3/Al2O3 compared with Pd- and Rh-based samples, whereas H-2 shows a significant ability to reduce the stored NOX on all samples examined. In addition, the reduction with CO and C3H6 proceeds via the formation of isocyanate species over both barium and alumina sites. The intensity of barium-isocyanate species for Pt/BaCO3/Al2O3 is significantly lower than the corresponding intensity for the Pd- and Rh-based samples, suggesting that the interaction between barium and Pt is lower than the corresponding interaction in the Pd/BaCO3/Al2O3 and Rh/BaCO3/Al2O3 samples. (c) 2006 Elsevier Inc. All rights reserved.
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