The full list of projects contains the entire database hosted on this portal, across the available directories. The projects and activities (across all directories/catalogs) are also available by country of origin, by geographical region, or by directory.

Displaying: 21 - 40 of 103 Next
21. Ecogeochemical mapping of the eastern Barents Region (Barents Ecogeochemistry)

Geochemical mapping project based on multimaterial and -elemental method covering the NW Russia and adjacent areas of Finland and Norway. NW-Russia is of strategic importance not only for Europe but also for the sosio-economic development of the whole Russia for its richness in natural resources. Their use must be based on environmentally acceptable principles. In addition, within the area exist numerous industrial centres whose environmental impacts are unknown. The information produced by the project is significant for the future development of the area and remedial measures of the environment. The project lead by the applicant, will be carried out in 1999-2003 in cooperation with Russian and Norwegian partners.

Geology PCBs Soils Catchment studies Mapping Heavy metals Radioactivity PAHs Long-range transport Acidification Pollution sources Contaminant transport Mining Radionuclides Arctic Local pollution GIS Geochemistry Dioxins/furans Data management Sediments
22. Ground water and soil monitoring

Monitoring of groundwater quality (geochemistry)

Heavy metals Acidification Geochemistry
23. AMAP / Human Health in Finnish Lapland

The general objective of the human health sub-programme is to protect and promote the health of Arctic peoples, especially children, with respect to exposure environmental contaminants.

Pathways Organochlorines PCBs Heavy metals Indigenous people PAHs Spatial trends Persistent organic pollutants (POPs) Pesticides Temporal trends Human health Human intake
24. Monitoring of the effects of air pollution and climatic change on lakes

Monitoring of the water quality reflecting long-range transboundary air pollution including acidifying compounds, metals and POPs, and climatic change. Part of the sites are also including in biological monitoring. Monitoring sites are the most upland lakes and they are not under any significant human impact. Information is distributed to the UN Convention on Long-range Transboundary Air Pollution. Monitoring is managed by Finnish Environmental Institute (SYKE).

Biology air pollution Heavy metals Climate Acidification climate change Ecosystems POPs
25. Monitoring of pollutants in fish and sediment

Monitoring aims to follow certain pollutant concentrations and their changes in fish tissue and sediment. Both inland lakes, one river and coastal areas are sampled. Lapland monitoring site is Lake Inarijärvi. Project is managed by Finnish Environment Institute (SYKE).

Biological effects Biology tissue pollutant Heavy metals Fish sediment. monitoring Persistent organic pollutants (POPs) Sediments Ecosystems
26. Oulanka, EMEP station, Northern Finland

Monitoring of air quality and deposition.

Atmospheric processes Ozone Heavy metals Long-range transport Acidification Contaminant transport Atmosphere Temporal trends
27. National deposition monitoring, Northern Finland

Monitoring of direct deposition. Project is run by Finnish Meteorological Institute (FMI).

Atmospheric processes Heavy metals Long-range transport Acidification Arctic Atmosphere Temporal trends
28. Pallas, AMAP station, Northern Finland

The overall objectives for operation of the station will follow those defined in the AMAP programme. The main interests are the levels and trends of airborne toxic pollutants (POPs and heavy metals) in northern Fennoscandia.

Atmospheric processes Organochlorines PCBs Arctic haze Heavy metals PAHs Long-range transport Acidification Contaminant transport Arctic Persistent organic pollutants (POPs) Pesticides Atmosphere Temporal trends
29. MISA. Miljøgifter i svangerskap og ammeperioden

Follow-up of mother-child cohort 515 childer and delivering women. Started 2006, will be followed due to AMAP protocol for 12 years

PCBs Heavy metals Persistent organic pollutants (POPs) HHAG Human health
30. Transport of Hg to marine coastal areas from tthe terrestrial monitoring areas near Zackenberg and Nuuk

In the Arctic the warming climate is expected to increase the meltning of glaciers, reducing the permafrost and increase the biologial activities. This may have consequences for the transportations of Hg from the terrestrcal ecosystems to the marine coastal areas. The project will investigate the influence of warming climate on the transportation of Hg to marine cooastal areas.

Heavy metals Contaminant transport Climate change
31. ARCTIC - Advanced Research on Contaminant Transfer, Impact and Consequences

Det danske bidrag til Arctic Monitoring and Assessment Programme (AMAP) under Arktisk Råd har dokumenteret at østgrønlandske isbjørne er mest forurenede mht. fedtopløselige organiske miljøgifte. Siden 1999 har Danmarks Miljøundersøgelsers Afdeling for Arktisk Miljø (DMU-AM) undersøgt isbjørnesundheden i Østgrønland via et unikt samarbejde med lokale bjørnefangere, og et tværfagligt samarbejde med biologisk, veterinær og human medicinske fagområder i Grønland og Danmark samt internationale samarbejdsrelationer med Canada, Norge og Tyskland. Undersøgelserne er mundet ud i en lang række af række internationale videnskabelige publikationer som dokumenterer tidstrend i miljøbelastningen af de grønlandske og norske isbjørne og sammenhængen mellem forurening og helbredseffekter på isbjørne. Disse har fået omtalt presseomtale verden over.

Biological effects Biology PCBs Heavy metals Long-range transport Sea ice Climate change Exposure Arctic Persistent organic pollutants (POPs) Pesticides Diet Temporal trends Marine mammals
32. AMAP 2009 and 2010 core HM and POP programme Faroe Islands

The project is a continuation of the monitoring activities of the AMAP POPs and Heavy metals programme in marine, terrestrial and freshwater environments of the Faroe Islands. The aims of the programme is to establish data for timetrend and spatial assessments as well as providing data of importance in human health risk assessment on mercury and POPs. The programme incorporates analyses on pilot whale, cod, black guillemots from the marine environment, sheep and hare from the terrestrial environment and arctic char from the freshwater environment. The compounds analysed are "legacy" POPs and mercury, cadmium and selenium. In addition, a retrospective analyses of PFOS in pilot whale tissues going back as far as possible (ie.1986) is part of the project.

Organochlorines PCBs Heavy metals Fish Long-range transport Spatial trends Terrestrial mammals Exposure Persistent organic pollutants (POPs) Seabirds Pesticides Temporal trends Marine mammals
33. Contaminants in Polar Regions – Dynamic Range of Contaminants in Polar Marine Ecosystems (COPOL)

The IPY-project ‘COPOL’ has a main objective of understanding the dynamic range of man-made contaminants in marine ecosystems of polar regions, in order to better predict how possible future climate change will be reflected in levels and effects at higher trophic levels. This aim will be addressed by 4 integrated work packages covering the scopes of 1) food web contaminant exposure and flux, 2) transfer to higher trophic levels and potential effects, 3) chemical analyses and screening, 4) synthesis and integration. To study the relations between climate and environmental contaminants within a project period of four years, a “location-substitutes-time”-approach will be employed. The sampling is focussed towards specific areas in the Arctic, representing different climatic conditions. Two areas that are influenced differently by different water masses are chosen; the Kongsfjord on the West-coast of Spitzbergen (79N, 12 E) and the Rijpfjord North-East of Svalbard (80N, 22 E). The main effort is concentrated in the Kongsfjord. This fjord has been identified as particularly suitable as a study site of contaminants processes, due to the remoteness of sources, and for influences of climatic changes, due to the documented relation between Atlantic water influx and the climatic index North Atlantic Oscillation (NAO). The water masses of the Rijpfjord have Arctic origin and serves as a strictly Arctic reference. Variable Atlantic water influx will not only influence abiotic contaminant exposure, but also food web structure, food quality and energy pathways, as different water masses carry different phyto- and zooplankton assemblages. This may affect the flux of contaminants through the food web to high trophic level predators such as seabirds and seals, due to altered food quality and energy pathways.

Biological effects Organochlorines Heavy metals Fish Climate variability Long-range transport Climate Contaminant transport Climate change Exposure Arctic Persistent organic pollutants (POPs) Local pollution Seabirds Food webs Ecosystems
34. Atmospheric Monitoring Network for Antropogenic Pollution in Polar Regions (ATMOPOL)

The project aims at establishing a long-term Arctic-Antarctic network of monitoring stations for atmospheric monitoring of anthropogenic pollution. Based upon the long and excellent experiences with different scientific groups performing air monitoring within the Arctic Monitoring and Assessment Programme (AMAP), an expanded network will be established including all AMAP stations and all major Antarctic “year-around” research stations. As an integrated project within the “International Polar Year 2007-08” initiative, the ATMOPOL co-operation intend to • Establish a long-term coordinated international Arctic-Antarctic contaminant programme. • Develop and implement a joint sampling and monitoring strategy as an official guideline for all participating stations. • Support bi-polar international atmospheric research with high-quality data on atmospheric long-range transport of contaminants (sources, pathways and fate). • Support future risk assessment of contaminants for Polar Regions based on effects of relevant contamination levels and polar organisms Based upon the well-established experiences of circum-Arctic atmospheric contaminant monitoring in the Arctic under the AMAP umbrella, a bi-polar atmospheric contaminant network will be established and maintained. In conjunction with the polar network of atmospheric monitoring stations for air pollution, surface-based and satellite instrumentation will be utilised to provide the characterization of the Arctic atmospheric-water-ice cycle. Together with numerical weather prediction and chemical transport model calculations, simultaneous measurements of pollutants at various locations in the Arctic and Antarctic will enhance our understanding of chemical transport and distribution as well as their long-term atmospheric trends. In addition to investigating the importance of atmospheric transport of pollutants an understanding of the transference and impact of these pollutants on both terrestrial and marine environments will be sought. A secretariat and a “scientific project board” will be established. During this initial phase of the project (2006), a guideline on priority target compounds, sampling strategies, equipment and instrumentation, analytical requirements, as well as quality assurance protocols (including laboratory intercalibration exercises) will be developed and implemented. The ATMOPOL initiative aims to address highly relevant environmental change processes and, thus, will strive to answering the following scientific questions: • How does climate change influence the atmospheric long-range transport of pollutants? • Are environmental scientists able to fill the gaps in international pollution inventories and identification of possible sources for atmospheric pollution in Polar Regions? • What are the differences in transport pathways and distribution patterns of various atmospheric pollutants between Arctic and Antarctic environments? Why are there such differences? What is the final fate of atmospherically transported pollutants and how does this impact on the environment and indigenous people?In order to understand the underlying atmospheric chemistry of pollution, e.g. atmospheric mercury deposition events, routine surface measurements of UV radiation as well as campaign related measurements of UV radiation profiles will also be included.The project will establish a cooperative network on atmospheric contaminant monitoring in Polar Regions far beyond the IPY 2007/08 period and is, thus, planned as an “open-end” programme. All produced data will be available for all participating institutions for scientific purposes as basis for joint publications and reports from the ATMOPOL database to be developed.

Pathways Atmospheric processes Heavy metals Long-range transport Contaminant transport Persistent organic pollutants (POPs) Atmosphere
35. Effects of lead intake in human blood

In Greenland lead contamination of the edible parts of seabirds, particularly eiders, is high because the birds have been killed with lead shot. Therefore bird-eaters are exposed to a high lead intake, probably often exceeding safe limits. In this study we will compare the lead level in human blood in a group of people from Nuuk, Greenland eating many birds with the level in a group eating few. This will enable us to assess if the high lead exposure is reflected in people and constitutes a health risk. The project is conducted in cooperation with The Medical Clinic in Nuuk and The Center for Arctic Environmental Medicine, Aarhus University.

Heavy metals Human health
36. Mercury in peat bogs

Peat samples from Greenland already collected and dated will be analysed for mercury in order to assess term time trends of mercury deposition during this century.

Heavy metals Atmosphere Temporal trends
37. Human bioaccumulation of mercury and cadmium

In Greenland the human intake of mercury and cadmium from local diet is high. In an autopsy study, mercury and cadmium concentrations in humans has been analyzed. This study will make it possible to assess to what extent the high intake of mercury and cadmium is reflected in human tissue.

Heavy metals Human health Human intake
38. Contaminants in polar bears

Polar bears are at the top of the arctic marine food chain. Owing to the high lipid content of their diet, polar bears appear particularly prone to bioaccumulate organochlorines. Polar bears from East Greenland and Svalbard have higher contaminant levels than polar bears elsewhere in the Arctic. Levels of PCBs in these areas might negatively affect reproduction and survival. So far more than 130 polar bear samples have been collected since 1999. These samples are being analysed for organochlorines and pathological effects.

Organochlorines PCBs Heavy metals Polar bear Persistent organic pollutants (POPs) Reproduction Pesticides Temporal trends Marine mammals
39. AMAP Time Trend Programme

The project includes analyses of PCBs, organochlorine pesticides, chlordanes and brominated flame retardants in seals, birds and fish from Greenland. The programme covers a period of five years to investigate temporal trends in the concentration levels of organic pollutants in Greenland.

Organochlorines Heavy metals Persistent organic pollutants (POPs) Pesticides Temporal trends
40. A simple model of transfer of atmospheric mercury to carnivores

The present study will establish a link between the mercury levels in the abiotic environment (e.g. historical records of mercury data in peat bogs, the ice sheet or marine sediments) with levels in carnivore species (polar bear, birds of prey). These results can be used in a model for predicting past and future development of the mercury loads in high trophic biota. This in turn will enable us to evaluate if changes in mercury levels in the atmosphere are reflected in species at higher trophic levels of the Arctic ecosystem. The project will expand the longevity and certainty of the biotic time series of mercury to about 150 years by analyzing museum samples of bird feathers and polar bear hair and teeth. The project is part of the project “Fate of mercury in the Arctic (FOMA)”.

Heavy metals Polar bear Seabirds