As the main primary producer, phytoplankton is an important link between the physical and chemical elements and higher tropic levels in the marine food web. Changes in the environment could affect the annual succession and species composition of the phytoplankton, as well as the overall primary production in the area. Phytoplankton monitoring will give important information regarding biological changes on the lowest level in the food web with environmental impact and climatic changes.]]>
During the winter phase from November to February, there is low diversity and low production, with chlorophyll concentrations close to zero. The lowest levels are found in the ice free areas in the northern parts. During this period there are sufficient nutrients for growth, but the absent of clear stratification and light prevent large production. The species that are present are cosmopolitan representatives of dinoflagellates (Dinophyceae), large armed forms as Protoperidinium, Ceratium, Dinophysis (Protoperidinium depressum, Ceratium longipes, Ceratium tripos, Dinophysis norvegica) and athecate forms from the genus Gymnodinium and Gyrodinium and occasionally diatoms (Bacillariophyceae). ]]>
In the Barents Sea ecosystem, zooplankton form a link between phytoplankton (primary producers) and fish, mammals and other organisms at higher trophic levels. The most abundant zooplankton species — calanoid copepods, krill, and hyperiid amphipods — form the major diet of herring, capelin, polar cod, and juveniles of other fish species. The Arctic front in the Barents Sea marks the boundary between the mainly Arctic zooplankton species (Calanus glacialis and Themisto libellula) and the Atlantic/subarctic species (C. finmarchicus, Meganyctiphanes norvegica, Thysanoessa spp and Themisto spp). ]]>
More than 3,050 species of invertebrates inhabit the benthos of the Barents Sea (Sirenko, 2001). Total fauna biomass, including benthic species, generally increases near the Polar Front, in shallow regions, and near the edges of banks. The richest species diversity is found on sandy silts, and silty-sand floors. Lower biomass occurs in areas with limited upwelling, low primary production, reduced vertical flux, and areas with less suitable substrata caused by heavy sedimentation (e.g. inner parts of glacial fjords). ]]>
There has been a decline in the total biomass of benthos from 1924-1935 to 1968-1970 (Antipova, 1975b). This happened almost throughout the Barents Sea, and has been attributed to climate change by many investigators. The mechanism behind this biomass reduction is not clear, however. Some studies suggest that it is due to a change in faunal distribution during the cold period between the 1960s and 1980s (Figure 2.4.7; Bryazgin, 1973, Antipova, 1975b, Bochkov and Kudlo, 1973), while others invoke declining biomass of resident boreal-arctic species during the 1930s-1960 warm period (Galkin, 1987; Kiyko and Pogrebov, 1997a; Kiyko and Pogrebov, 1998). ]]>The areas with low abundance (less than 1000 individuals/ m2) and biomass (less than 10-25 g/m2) are usually restricted to bottom depressions such as the western deep-water areas in the Bear Island Channel and Hopen Deep, deep-water areas between Franz Josef Land and the shallow waters of the Novaya Zemlya bank and the deep-water areas in Eastern Basin. The high biomass areas (biomass hotspots) are usually located in connection with considerable rises in sea-floor topography and generally typical for the areas with hard soil and strong currents (Kiyko and Pogrebov, 1997a).
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