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Directory entires that have specified Svalbard as one of the geographic regions for the project/activity and are included in the AMAP, ENVINET, SAON and SEARCH directories. Note that the list of regions is not hierarchical, and there is no relation between regions (e.g. a record tagged with Nunavut may not be tagged with Canada). To see the full list of regions, see the regions list. To browse the catalog based on the originating country (leady party), see the list of countries.
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In a context of global change, arctic ecosystems are exposed to deep modifications not only of the biology and ecology of endemic species but also of the interactions they may have with an increasing number of introduced species. This project attempts to assess in Svalbard, the impacts of global changes on aphids. These phytophagous insects are particularly relevant organisms for studies on the effects of global warming and biological invasion because 1) of their extreme sensitivity to micro- and macro- changes due to their spectacular rate of increase and phenotypic plasticity and 2) of their colonizing capacity conferred by their parthenogenetic mode of reproduction and their dispersal potential
A co-operative project between France and Norway is proposed to study the physiological mechanisms (hormones and metabolic rate) involved in the regulation of parental effort (brood size) in an Arctic-breeding seabird, the kittiwake Rissa tridactyla. This project will be carried out at Kongsfjorden (Ny Ålesund, Svalbard) which constitutes one the northernmost (79° N) breeding site of the species. The main goal of this project is to understand the reasons of the very poor productivity of the species in this high-arctic area (only one chick/pair/year compared to 2-3 chicks/ pair/year in more temperate areas). To do so, we will concurrently study the metabolic cost of chick rearing and the metabolic cost of foraging. To test whether parent kittiwakes are apparently unable to rear more than one chick, we will manipulate brood size and will measure its consequences on basal metabolic rate (BMR) and foraging activity. We will experimentally manipulate the brood size by swapping chicks between nests shortly after hatching. Parent birds of the different experimental groups will be captured, weighted and a small blood sample (500 µL) will be taken for thyroid hormones. BMR will be estimated through thyroïd hormones (Chastel et al. 2003, J. Avian Biol. 34: 298-306), a method that reduces handling time imposed by the use of a respirometer, whereas activity at sea will be estimated using miniature activity recorders (Daunt et al., 2002 Mar. Ecol. Prog. Ser.245 : 239-247, Tremblay et al. 2003, J. Exp. Biol. 206: 1929-1940). Nests of the different groups (12 nests with 2 chicks and 12 nest with 1 chick) will be observed during 2 weeks after what parent birds will be recaptured, and bled again for T3 assay. On an other group of birds (N=10), we will calibrate these miniature activity recorders (N=10, weight:5 g) by observing the activities (rest, brooding, flying, etc..) of the instrumented birds in the colony. Food samples (N=12) will be collected from parent birds during capture and recapture sessions (kittiwakes spontaneously regurgitate food when handled). Breeding adults and chicks will be maked with plastic rings that allow identification from a distance.
To evaluate temporal variation in arctic fox numbers and their food resourses in the Kongsfjorden area. The number of foxes captured per 100 trap-days are used as an index of fox density termed "Fox Capture Index". The observations of denning activity i.e. observation of number of arctic fox litters and litter size at den are termed "Fox Den Index" as a second index of fox abundance. A third index is termed "Fox Observation Index". This index is based on both observations of adult foxes seen away from breeding dens pr 100 h field work and reports on request from scientists and local people on observations of adult foxes during summer. In addition, reports on observation of fox tracks in the study area were collected in 1990-2001 as a fourth index, which were called "Fox Track Index". The field census are conducted for 10 days starting at the end of June. All dead foxes in the area should be collected.
The aim of this international project is to measure and model arctic UV-radiation and assess the effects on freshwater planktonic organisms and foodwebs. The fieldwork and experiments are conducted at Ny-Alesund, Spitsbergen. The specific aim of our participation is to study the food web effects of UV-B stress by means of in-situ enclosure studies. In the laboratory we found that UV-B stressed algal cells may increase in volume and form a thicker cell wall. These changes in the algal cells may reduce their digestibility by zooplankton. Further the role of photopigments (like melanin and carotenoids), present in some zooplankters, will be studied in relation to the survival of these animals at high UV-B exposure. Research activities Grazing experiments with Daphnia pulex (melanic and hyaline) are performed in in-situ enclosures (under different UV exposures) in the Brandal Lagune during July. The green alga Chlamydomonas will be incubated in-situ under different UV exposures to assess the potential use of this alga as a biodosimeter for UV-B. Further the survival of melanic and hyaline daphnids will be tested in-situ.
The study covers many areas of ecotoxicology research on polar bears. Monitoring of POP levels and studies of effects on endocrine disruption, immune system, reproduction, and demography are all parts of the study.
Polybrominated diphenyl ethers (PBDEs) are persistent and lipophilic compounds used as flame retardants in electronic equipment, plastic material and synthetic fibbers among other things. The PBDEs are mainly used as Deca-BDE and Bromokal 70-5DE, a mixture of tetra-, penta- and hexa-BDE. Due to its chemical and physical properties PBDEs, especially TeBDEs, tend to bioaccumulate. PBDEs were first reported in sediments in USA, and in fish from a Swedish river. More recently PBDEs have also been reported in seals, birds, mussels, whales and humans. In this study an SFE-method for rapid analysis of PBDEs in marine mammals was developed. This method was used to determinate the concentrations of these environmental pollutants in Pilot Whale samples caught in the Faroe Islands, Beluga Whales from the Arctic and Polar Bears from Svalbard. Using this method several PBDEs were analysed in the different species. In addition methoxylated PBDEs (Me-O-PBDE) were identified by interpretation of the different mass spectra’s. Of the 209 theoretical possible congeners only a few PBDE seem to accumulate in the environment. Accumulation of PBDE is related to the different chemical properties of the molecule. With the help of multivariate characterisation of a compound class using semi-empirical molecular orbital calculations, literature data and actual experimental measurements, the behaviour of PBDE in the environment can be modelled and predicted. Such models are essential in order to gain more insight in the behaviour of PBDE in the environment.