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Found 10000 publications. Showing page 163 of 400:

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Year  
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2011

2011

Scenarios for EU-27 heavy metals and POPs emissions to air, water and soil until 2050. NILU PP

Sundseth, K.; Panasiuk, D.; Pacyna, J.M.; Pacyna, E.G.; Glodek, A.

2011

Modeling of short chain chlorinated paraffins in the Nordic environment. NILU PP

Krogseth, I.S.; Breivik,K.; Schlabach, M.; Wania, F.; Arnot, J.

Short chain chlorinated paraffins (SCCPs), also called polychlorinated n-alkanes, are mixtures of compounds of molecular formula CxH2x+2-yCly containing 10-13 carbon atoms and usually 30-70 % degree of chlorination. They have a range of industrial applications, and have been detected in numerous environmental compartments. There is concern regarding SCCPs due to their environmental persistence and their potential for bioaccumulation, adverse effects and long-range transport. SCCPs have been included in the UNECE LRTAP Convention, the priority substance list of the European Water Framework Directive, and are under consideration for the Stockholm Convention on Persistent Organic Pollutants. However, the behaviour and fate of SCCPs remain poorly understood, in part as the technical mixtures consist of thousands of isomers, enantiomers and diastereomers, which make analysis and modelling of these compounds very challenging. The purpose of this study was to explore a complementary modelling and monitoring approach to evaluate the overall understanding of the link between emissions of SCCPs, environmental levels and human exposure in the Nordic environment and to identify the more critical knowledge gaps. Data for emissions and physicochemical properties of SCCPs were gathered or estimated, and used to parameterize an integrated, non-steady state environmental fate and bioaccumulation model (CoZMoMan). Specific congeners of SCCPs were selected for the study to assess the extent of expected variation of environmental fate and behaviour within the multitude of compounds. Model results were next compared to reported environmental levels in the Nordic region. For compartments where environmental levels were scarce or lacking, targeted sampling and analysis was carried out to further evaluate the model predictions. Results from this study will be presented and discussed with emphasis on the more critical research needs with respect to the overall fate and exposure of SCCPs.

2011

PFAS - Comparison of MS/MS and MS-TOF techniques and two extraction methods on lean and fatty fish. NILU PP

Huber, S.; Lacina, O.; Hradkova, P.; Pulkrabova, J.; Herzke, D.; Kallenborn, R.; Hajslova, J.

2011

A high-throughput method to screen organic chemicals in commerce for emissions. NILU PP

Breivik, K.; Arnot, J.A.; Brown, Wania, F.; McLachlan, M.S.

2011

The impact of North American emission on carbon monoxide and ozone concentrations over Europe. NILU PP

Eckhardt, S.; Stohl, A.; Cassiani, M.; Cammas, J.-P.

2011

Determination of time- and height-resolved volcanic ash emissions for quantitative ash dispersion modeling: The 2010 Eyjafjallajökull eruption. NILU PP

Stohl, A.; Prata, A.J.; Eckhardt, S.; Clarisse, L.; Durant, A.; Henne, S.; Kristiansen, N.I.; Minikin, A.; Schumann, U.; Seibert, P.; Stebel, K.; Thomas, H.E.; Thorsteinsson, T.; Tørseth, K.; Weinzierl, B.

2011

Satellite retrievals and transport modeling of volcanic eruption clouds. NILU PP

Kristiansen, N.I.; Stohl, A.; Prata, F.; Eckhardt, S.; Seibert, P.; Webster, H.; Clarisse, L.; Henne, S.

2011

Record total ozone loss in the Arctic in winter 2010/2011. NILU PP

Goutail, F.; Lefèvre, F.; Pazmiño, A.; Pommereau, J. P.; Chipperfield, M.; Feng, W.; Van Roozendael, M.; Eriksen, P.; Stebel, K.; Dorokhov, V.; Kyrö, E.; Adams, C.; Zhao, X.; Walker, K.; Strong, K.

2011

ENVIROFI: Future Internet for Future INSPIRE. NILU PP

Schleidt, K.; Fogarty, B.; Kobernus, M.; Havlik, D. , Schade, S.

2011

2011

MEMORI. Measurement, effect, assessment and mitigation of pollutant impact on movable cultural assets. Innovative research for market transfer. NILU PP

Dahlin, E.; Grøntoft, T.; Lopez-Aparicio, S.; Bellendorf, P.; Schieweck, A.; Drda-Kühn, K.; Colombini, M.P.; Bonaduce, I.; Vandenabeele, P.; Larsen, R.; Sommer, D.V.P.; Potthast, A.; Marincas, O.; Thickett, D.; Andrade, G.; Tabuenca, A.; Odlyha, M.; Laurenson, P.; Hackney, S.; McDonagh, C.; Bowe, P.; Ackerman, J.J.

2011

The impact of North American emission on carbon monoxide and ozone concentrations over Europe. NILU PP

Eckhardt, S.; Stohl, A.; Cassiani, M.; Cammas, J.-P.

2011

Survey on possible source of HCB, PCB, and PCDD/F emission to air. An expert assessment of the Norwegian silicon and ferrosilicon production. NILU OR

Schlabach, M.

On behalf of the Norwegian Ferroalloy Producers Research Association (FFF) NILU has assessed possible airborne emissions of HCB, PCB, and PCDD/F from Norwegian silicon and ferrosilicon production.

The report concludes with that the Norwegian silicon and ferrosilicon melting process does most certainly not lead to a 'de novo' formation of organochlorines. The report summaries all performed emission measurements. It states that, even in worst case, the annual contribution from Norwegian silicon and ferrosilicon production does not exceed one percent of the total annual load. Thus the contribution is regarded as negligible.

2011

Analysis and review of air quality standards: Deliverable report 2.4. NILU OR

Liu, L.; Slørdal, L.H.; Bøhler, T.

This report provides an overview of international and national air quality standards and guidelines from different environmental agencies, such as the European Union (EU), US Environmental Protection Agency (EPA), World Health Organization (WHO), United Arab Emirates (UAE) and some other selected countries.

2011

Chemical speciation of fine airborne particles in Abu Dhabi. NILU OR

Hak, C.; Lopez-Aparicio, S.; Sivertsen, B.

Chemical speciation results of PM2.5 filter samples from eight sites in Abu Dhabi are discussed. This is the third interim report, covering a total of 40 filter samples. As one aim of this sampling study was to use the speciation results for health impact studies, samples with high particle loads and high degree of blackness were selected for analysis, and compared to samples with typical particle loads. Particles with diameters less than 2.5 µm were analysed for elements, inorganic ions and carbonaceous fractions.
The most abundant elements were found to be crustal elements, contributing on average 14% to PM2.5 mass. Reconstructing the mass of crustal oxides, approximately 44% of the fine particle mass was estimated to be associated with mineral dust. The concentrations of most heavy metals were below limit values for annual averages at all sites. For nickel, it was found that the Guideline Value may be exceeded at one traffic site.
Inorganic ions (sulphate, nitrate, ammonium, sodium, chloride) explain on average 34% of the PM2.5 mass in Abu Dhabi. Remarkably high sulphate concentrations account for the major part (on average 26%). Particulate sulphate in Abu Dhabi is likely to have both natural (as a result of the local composition of mineral dust) and anthropogenic sources which cannot be separated with the applied analytical methods. An anthropogenic contribution of ~6% comes from the secondary inorganic ions nitrate and ammonium.
Total carbon, which consists of elemental carbon, organic carbon and carbonate carbon contributed on average 14% to PM2.5 mass. About 30% of total carbon was estimated to be carbonate of likely natural origin. Elemental carbon and most organic carbon are expected to be of anthropogenic origin.
PM in Abu Dhabi has a strong signature of natural sources (mineral dust). A detailed apportionment of sources requires further analyses.

2011

VETAPOS. NILU OR

Kallenborn, R.; Schmidbauer, N.; Reimann, S.

2011

Bangladesh Air Pollution Management (BAPMAN). Ambient air pollution screening study in Dhaka 31 January - 15 February 2011. NILU OR

Randall, S.; Sivertsen, B.; Schneider, P.; Vo, D.T.; Uddin, N.; Biswas, S.; Saroar, G.; Rana, M.

An ambient air pollution screening study was performed in Dhaka from 31 January - 15 February 2011. The main objective of the study was to gain an overview of the background concentrations and the spatial distribution of the air pollution in the Dhaka city area. Thorough ambient air quality data has not been collected in the city for some years. Results show relatively high concentrations for SO2, NO2, and O3, with PM concentrations alarmingly high. PM concentrations could be attributed to local sources (predominantly brick Kilns and traffic), as well as regional influences (haze clouds) during the winter season which were compared to satellite AOD data.

2011

Final report: Air quality management feasibility study for Armenia. NILU OR

Randall, S.; Tønnesen, D.; Liu, L.

A Feasibility Study has been performed to assess the Air Quality Management (AQM) situation in Armenia for the purpose of potentially preparing a future comprehensive project proposal for establishing an Air Quality Management Program (AQMP) for the country. The study was conducted in cooperation with local Armenian Environmental authorities (primarily the Environmental Impact Monitoring Centre - EIMC) to evaluate the existing local monitoring network and collaborating institutions, in addition to performing a screening study in Yerevan based on passive samplers. Results from the study indicate that Armenia needs technical support and training in order to establish a comprehensive AQMP. Recommendations, including a detailed roadmap, are presented as suggestions for the framework of a future proposal to establish a successful AQMP in Armenia.

2011

Dispersion calculations of NOx emissions at Salten Verk. NILU OR

Haugsbakk, I.; Tønnesen, D.

Dispersion calculations have been carried out for emissions from Salten Verk in Nordland.

2011

Update and improvement of dispersion calculations for emissions to air from TCM's amine plant. Part II-Likely case nitrosamines, nitramines and formaldehyde. NILU OR

Tønnesen, D.

Inert dispersion of a unitary emission has been combined with time dependent air chemistry to provide maximum impact of nitrosamines and nitramines in air and water for emissions from the amine absorber at TCM. The calculations show that likely case impact of nitrosamines and nitramines in air is less than 2 % of the recommended guideline value. The maximum concentrations in fresh water range from0.6 % to 3.2 % of the guideline depending on the use of absorbent and flue gas. The likely case impact show that air concentrations are a factor of 3 to 4 lower than the worst case, while water concentrations are be a factor from 16 to 22 lower than the worst case depending on the type of absorbent.

2011

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