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Vol. 19 (2016 year), No. 1, DOI: 10.21443/1560-9278-2016-1/2

Kapkov V. I., Shoshina E. V., Belenikina O. A.
Bioremediation of marine coastal ecosystems:Using artificial reefs

The development of the biotic community on the artificial reefs in the coastal zone of the northeast Black Sea region has been studied. Colonization stages of the artificial reefs by hydrobionts depended on substance, time and depth of reef construction have been considered. Reef colonization by fouling organisms is a biotic primary succession of the benthic mature community. It has been found that in 2–3 years on an artificial reef species diversity and biomass of aquatic organisms rise sharply and reef biocenose becomes a powerful biofilter involved in the process of environment self-purification. The results of the functioning of the reef biocenose can serve as a basis for using artificial reefs in biological treatment of water in the coastal zone

(in Russian, стр.0, fig. 0, tables. 0, ref 0, Adobe PDF, Adobe PDF 0 Kb)

Vol. 19 (2016 year), No. 1, DOI: 10.21443/1560-9278-2016-1/2

Shoshina E. V., Kapkov V. I., Belenikina O. A.
Ecological factors regulating growth of seaweeds in Arctic communities

Features of seaweeds in the Arctic communities in connection with periodic and unperiodic influences of ecological factors have been analyzed. It has been shown that the existence of benthic algae biocenosis of the northern seas is mainly controlled by the primary periodic environmental factors acting as triggers that determine the direction of vegetative and generative processes, as well as contribute to the emergence of adaptive devices to extreme environmental conditions. Therefore, periodic exposure to environmental factors cause only structural changes in plant communities due to the elastic stability of fucus algae populations acquired as a result of the long process of adaptation to the northern seas conditions. Unperiodic primary factors also violate the ratio of the number by elimination and inhibit growth of certain algae age stages. However thanks to the stability of resistant the algae community can eventually restore its structural and functional organization

(in Russian, стр.0, fig. 0, tables. 0, ref 0, Adobe PDF, Adobe PDF 0 Kb)

Vol. 20 (2017 year), No. 2, DOI: 10.21443/1560-9278-2017-20-2

Kapkov V. I., Shoshina E. V., Belenikina O. A.
Using the marine unicellular algae in biological monitoring

The possibility of using marine unicellular algae from natural plankton community in biomonitoring of pollution by heavy metals has been investigated. Algae of different taxa from the Mediterranean Sea have been allocated to culture. In the laboratory the culture conditions – i. e. growth medium, temperature, photoperiod, level of artificial light and initial density – have been selected for every species. The impact of heavy metals (Hg, Cd, Cu, Pb) in the form of chloride salts on the growth of axenic algae culture has been studied in the modelling experiments. The unicellular marine algae have a very short life cycle, therefore it is possible to use them in the experiments of studying the effect of anthropogenic factors at cellular and population levels on the test-object. With biomonitoring pollution of marine environment by heavy metals and others dangerous toxicants, the major indicators of algae community condition are the cellular cycle and the condition of the photosynthetic apparatus of the cell. The subsequent lysis of cells under the influence of heavy metals leads to the excretion of secondary metabolites which can essentially affect the metal toxicity. The established scales of threshold and lethal concentration of heavy metals for algae of different taxon make it possible to use the ratio of sensitive and resistant species to heavy metals as biological markers when forecasting ecological consequences of pollution of the marine environment by heavy metals. Distinctions in the resistance of different taxon to heavy metals can result in implementing the strategy of selection of test-objects depending on the purposes of the research.

(in English, стр.7, fig. 0, tables. 3, ref 14, Adobe PDF, Adobe PDF 0 Kb)