This paper presents the state and spatial distribution of surface sediment contamination by Cr, Ni, Cd, Pb, Zn, and Cu in 77 lakes in Poland. The results indicate the contamination of lake sediments by heavy metals, but the potentially toxic effects are only found in single lakes. The spatial distribution of different metals varies, with Cr predominantly impacted by point sources and Pb, Ni, and Zn impacted by non-point sources. The analysis also reveals the presence of high concentration hot spots in the western part of Poland and low concentration cold spots in the central part. The presence of wetlands and higher proportions of national parks and nature reserves are found to limit the inflow of heavy metals into lakes.
This paper presents the state and spatial distribution of surface sediment contamination of 77 lakes in Poland by Cr, Ni, Cd, Pb, Zn, and Cu. The analyzed lakes were located within a network of nature protection areas in the territory of the European Union (EU). Spatial distribution of the heavy metals (HMs), factors favoring the delivery/accumulation of HMs in surface sediments, and pollution sources were analyzed. The results indicate the contamination of lake sediments by HMs, but the potentially toxic effects of HMs are only found in single lakes. The spatial distribution of Cr indicates predominant impacts of point sources, while for Pb, Ni, and Zn, the impact of non-point sources. The analysis showed the presence of areas with very high values of particular HMs (hot spots) in the western part of Poland, while a group of 5 lakes with very low values of Ni, Pb, and Zn (cold spots) was identified in the central part of Poland. Principal component analysis showed that presence of wetlands is a factor limiting HMs inflow to lakes. Also, lower HMs concentrations were found in lake surface sediments located in catchments with a higher proportion of national parks and nature reserves. Higher HMs concentrations were found in lakes with a high proportion of Special Protection Areas designated under the EU Birds Directive. The positive matrix factorization analysis identified four sources of HMs. High values of HMs concentrations indicate their delivery from industrial, urbanized, and agricultural areas. However, these impacts overlap, which disturbs the characteristic quantitative profiles assigned to these pollution sources.
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