Sandimirov S. Pollution of the Sediments of the Paz River basin / In State of the environment in the Norwegian, Finnish and Russian border area. The Finnish Environment. Finland, Jyvaskyla: Kopijyva Oy. 2007, №6, 98p.
1. Summary of the Sediment Investigations 1.1. Introduction Lake Inari and the Paz River form one o f the greatest water system in the Northern Fennoscan- dia. The drainage basin o f this system includes the adjacent areas of Russia, Norway, and Finland. Within these areas, the anthropogenic load consists mainly o f heavy metals released by the melting furnaces o f the “Pechenganikel” Plant and domestic sewage from populated areas, which are located within the drainage basin o f this system. The river is strongly regulated for hydroelectric power production. Therefore, the investigation o f the ecological situation and im provement o f environmental conditions in the Paz River basin are important for these three countries. Last century in many countries o f the world the increasing attention attracts high latitude re gions having richest mineral resources. Development o f mineral deposits, processing of mineral raw material, reception o f a final product (including, chemical fertilizers and metals) have re sulted in infringement o f natural geochemical circulation of elements in Arctic and Subarctic ecosystems. The mining and metallurgical activity has significant negative influence on fresh- waters o f high latitude, which are extremely sensitive to anthropogeneous stress owing to low levels o f masses and energy volumes (Moiseenko et al., 1996, 1997; Moiseenko, 1997). The Paz River basin is one o f industrial centres o f ecological trouble in the Northern Fenno- scandia with the advanced mining and metallurgical industry. The main pollution sources by heavy metals o f the Kola Peninsula territory are the Pechenganickel and Severonickel Compa nies. The significant part o f heavy metals entering in a lake in composition o f waste water and pre cipitated on watershed territory are connected and buried in sediments. Therefore their contents in sediments characterize total loading, allow to determine sources o f pollution and to establish historical trends. In the majority o f water systems, the element concentrations in the top several centimetres o f sediments are much higher, than element concentrations in water column. The close connection of microelements (for example, heavy metals) with seston and sediments means, that distribution, transport and availability o f these elements cannot be correctly appreci ated extremely by means o f only collection o f water samples and analysis of a soluble phase (Horowitz, 1991). Sediments accumulate many microelements and other polluting substances, therefore can be considered as an informative parameter o f water quality and, simultaneously, source o f secon dary pollution for the following reasons: • unbroken sediments contain "historical records" o f the last chemical conditions and allow to establish background levels, to which the existing conditions can be compared; • under influence o f change o f physical and chemical conditions (for example, pH, Eh, dis solved oxygen, bacterial activity) the compounds, connected with sediments, can be dissolved in water column, enter to foodweb and have secondary effects for hydrobionts; • inorganic substances, some rather inert or harmless to environment, can be destroyed or react with others, forming soluble and potentially toxic forms (for example, transmission o f elemen tary mercury into methyl-mercury (Linnik and Nabivanets, 1986; Moore and Ramamoorthy, 1987)); • sediments are one o f main sources o f pollution and should be investigated for definition o f potential transmission o f polluting substances.
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