The concentrations of iron (Fe), zinc (Zn), and copper (Cu) in the fruiting body depends on species and vary between 58.83-340.34, 19.70-99.62, and 5.03-9.37 mg/kg for Fe, Zn, and Cu, respectively. The bioaccumulation factor has subunit values for the three studied trace metals, which show the low capacity of these species of mushrooms to accumulate metals if the concentrations in soil increase over the normal threshold for these elements. The high values of translocation factor demonstrate the mobility of Fe, Zn, and Cu in the studied mushrooms.
The highest accumulation levels were found in A. alba for Cr (267.69%); in L. perenne for Mn (51.45%), Sr (114.35%), and Ba (60.81%); and in C. dactylon for Zn (136.62%), Cu (97.65%), and F. pratensis for Sn (704.00%).
Mushrooms have a species-specific affinity for heavy metals in soil. Therefore, mushrooms may act as an effective bioaccumulator of metals, thus can be used in mycoremediation technologies to remove and recover heavy metals from soil. The response of four Russula species to copper sulfate and lead acetate treatments concerning the absorption, accumulation and translocation of Fe, Cu, Zn, Mn and Pb was studied. Differences in metal concentrations were recorded between caps and stipes of the fruiting body and varied widely between the tested species. This confirms the species-dependent features of heavy metal absorption in mushrooms. Another factor that showed an influence on the bioavailability of metals in mushrooms was the metal content of soil. Similarities between the absorption and accumulation of copper and zinc were observed for R. vesca and R. atropurpurea. The treatments influenced the bioabsorption of heavy metals by the mushrooms and the metal mobility in the fruiting body. After lead acetate treatment, R. vesca, R. atropurpurea and R. integra had an increased bioaccumulation capacity compared to the control. Hyperaccumulating species, such as R. nigricans for lead soil pollution, would lead to the best results for mycoremediation as they are capable of accumulating higher concentration of heavy metals in comparison to other mushroom species.
All over the world today is developing more and more the studies concerning biochemical and physiological features of mushrooms (macromycetes) in the view to promote them as biological tools in different types of biotechnologies grace of their bioabsorption capacity for biominerals, heavy, rare or noble metals. Generally the researches are focused on the elemental content of mushrooms (Barros, 2008; Jentschke, 2000; Krupa, 1997, 2004; Yamaca, 2007).
This paper is about the level of bioabsorption for some heavy metals inside fruiting body, correlated to the substrate content and pH value. It is possible that one macromycetes species to contain in a high concentration one metal, but to have a low capacity of bioabsorption, the storage level being influenced by the substrate or environmental factors.
This study aim is to establish the reality concerning the bioabsorption capacity for heavy metals of following six macromycetes species: Coprinus picaceus, Coprinus cinereus, Pseudotrametes gibbosa, Lyophyllum crassifolium, Paxillus involutus and Phellinus tremulae, grown in condition of natural pH of their substrate in a forestry ecosystem of Dambovita county in south of Romania. The elemental content of biological and environmental samples was determined by Atomic Absorption Spectrometry (AAS).
So, maximum concentration of cobalt was find in fruiting body of Pseudotrametes gibbosa (0,1 ppm), minimum being at fruiting body of Coprinus cinereus (0,002). It was find nickel only in fruiting body of Phellinus tremulae and Pseudotrametes gibbosa.
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