Abstract

Plankton assemblages can be altered to different degrees by mining. Here, we test how diatoms and cladocerans in ponds along a river in southern Poland respond to the cessation of the long-term Pb-Zn mining. There are two groups of subsidence ponds in the river valley. One of them (DOWN) was contaminated over a period of mining, which ceased in 2009, whereas the other (UP) appeared after the mining had stopped. We used diatoms and cladocerans (complete organisms in plankton and their remains in sediments) to reveal the influence of environmental change on the structure and density of organisms. The water of UP pond was more contaminated by major ions (SO42−, Cl−) and nutrients (NO3−, PO43−) than the DOWN ponds. Inversely, concentrations of Zn, Cd, Cu and Pb were significantly higher in sediment cores of DOWN ponds in comparison to those in the UP pond. Ponds during mining had higher diversity of diatoms and cladocerans than the pond formed after the mining had stopped. CCA showed that diatom and cladoceran communities related most significantly to concentrations of Pb in sediment cores. Comparison of diatom and cladoceran communities in plankton and sediment suggests significant recovery of assemblages in recent years and reduction of the harmful effect of mine-originating heavy metals. Some features of ponds such as the rate of water exchange by river flow and the presence of water plants influenced plankton communities more than the content of dissolved heavy metals.

Highlights

  • IntroductionAmong environmental effects, draining of mines and mine tailings as well as leaching of spoil heaps have been recognized as harmful for aquatic organisms

  • In subsidence ponds we found 8 taxa in the UP pond characterized by through-flow of river water and 14 taxa in DOWN ponds characterized by stagnant water conditions and littoral zone overgrown with macrophytes

  • In the sediment samples of DOWN ponds, such diatoms as Achnanthidium minutissimum (Cd, Cu), Asterionella formosa (Zn), Aulacoseira granulata (Cd), Encyonopsis cesatii (Pb), Fragilaria cf. gracilis (Cd, Zn, Pb), Meridion circulare var. circulare (Zn, Cu, Pb), Navicula veneta (Cu), Nitzchia archibaldii (Cd, Zn, Cu, Pb), N. capitellata (Zn, Cu, Pb), N. gracilis (Cd, Zn, Pb), N. palea var. debilis (Zn), N. subacicularis (Pb), Planothidium lanceolatum (Cd, Zn, Pb), Sellaphora nigri (Cd, Zn, Pb, Cu), Surirella angusta (Pb), S. brebisonii var. kuetzingii (Cd, Zn, Pb, Cu), and Ulnaria ulna (Zn, Pb) significantly correlated with the heavy metals

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Summary

Introduction

Among environmental effects, draining of mines and mine tailings as well as leaching of spoil heaps have been recognized as harmful for aquatic organisms. The impact of such pollution can be the most distinct in small catchments, receiving large amounts of mine drainage where dilution with natural waters is limited. Mine waters usually contain many compounds in potentially harmful amounts, inducing synergistic effects on organisms [1,2,3,4]. Heavy metals (Cu, Pb, Zn) could be less toxic for biota in water (e.g., Cladocera) at high content of cations like Ca2+ and Mg2+ [5,6].

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