We studied the contents of cadmium (Cd), lead (Pb) and mercury (Hg) in common reed (Phragmites australis), great pond snails (Lymnaea stagnalis), and in littoral bottom sediments in 18 fishponds in two regions of the Czech Republic. We also assessed the impact of environmental factors on heavy metal accumulation in these three components of littoral ecosystem. Cadmium and lead values were significantly higher in bottom sediments (median values 0.70 and 13.4 mg·kg ) were higher than in sediments (0.040 mg·kg -1 ) and these were higher than in reed stems (0.010 mg·kg). We also found higher mercury contents in reed stems and higher cadmium contents in great pond snails in eastern compared to western parts of investigated ponds. Based on the principal component analysis (PCA) performed on heavy metal values, relative reed beds rate in the pond perimeter was negatively correlated with the sample scores on the first PCA axis and the orientation of sampling site and fish stock density negatively correlated with the second PCA axis. Our results proved the important role of littoral sediments in Cd, Pb and Hg accumulation, and the suitability of great pond snails for mercury stress biomonitoring in fishponds. In conclusion, littoral reed beds play a very important role in toxic element uptake in fishponds. The results contribute to the understanding of heavy metal cycles and their accumulation in fishponds under semi-natural conditions and in less affected landscape, and can be used as reference values for comparison with more damaged sites.
Fishpond littoral, heavy metals, environmental factorsThe increase in heavy metal concentrations in the environment in the last decades is primarily due to erosion and anthropogenic activities, and because metals are very persistent pollutants, they accumulate in the soil, water sediments and in the food chain (Čelechovská et al. 2008). Wetlands and other aquatic habitats play an important role in heavy metals uptake, transport and accumulation in landscape (Jackson 1998). Especially vegetated littoral zones of water bodies can serve both as metals sinks and sources (Lakatos et al. 1999;Bragato et al. 2006). However, higher heavy metals' input to wetlands can cause serious changes in the natural ecosystem functioning, such as changes in the food chain structure, physiological and behavioral changes in aquatic organisms as well as decrease of biodiversity and extinction of sensitive taxa (Pip 2006;Bogatov and Bogatova 2009;Bonanno and Lo Giudice 2010).In this respect, bottom sediments, aquatic macrophytes and invertebrates are very important links in metal cycles in the aquatic environment and they are commonly used in the biomonitoring of heavy metals. Generally, sediments can accumulate large amounts of heavy metals and become their main reservoir in the wetlands (Svobodová et al. 2002).