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Joint International Conference on Long-term Experiments ...

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STUDY OF VERTICAL MOVEMENT OF SOME MICROELEMENTS<br />

IN THE SOIL<br />

László Szegedi (1) – Lajos Szabó (2.) – Mária Takács Hájos (2.)<br />

(1.) Károly Róbert College Department of Envir<strong>on</strong>mental Management and Agr<strong>on</strong>omy,<br />

(2.) Tessedik Sámuel College, Institute of Envir<strong>on</strong>mental Sciences<br />

ABSTRACT<br />

A l<strong>on</strong>g <strong>term</strong> field experiment was established with different doses of some heavy metals<br />

(As, Cr, Cd, Cu, Hg, Pb, Zn) to study their behaviour in the soil-plant system. The soil<br />

of the experimental site was characterized by pH (H2O) 6.2, pH (KCI) 5.4, soil organic<br />

matter c<strong>on</strong>tent 3%, and clay mineral c<strong>on</strong>tent 30-35%. To check the vertical movement<br />

of the studied elements, two years after applicati<strong>on</strong> soil samples were taken from the 0-<br />

30, 30-60 and 60-90 cm layers of plots treated with the highest heavy metal load (270<br />

kg element/ha). Both total (cc.HNO3+H2O2 extractable) and available (NH4 – acetate +<br />

EDTA extractable) element c<strong>on</strong>tent was de<strong>term</strong>ined using the ICP-MS technique.<br />

Vertical movement of Cr (VI) was detected int he full soil profile. Therefore Cr<br />

c<strong>on</strong>taminati<strong>on</strong> of the soil profile suggest a significant risk for the quality of groundwater.<br />

As and Pb remained mostly int he 0-30 cm layer. There was <strong>on</strong>ly a slight<br />

c<strong>on</strong>taminati<strong>on</strong> int he 30-60 cm layer. Cd, Hg, Cu and Zn were fixed in the plough layer.<br />

Both total c<strong>on</strong>tent and available fracti<strong>on</strong> of these elements were detected in the upper 0-<br />

30 cm layer. These c<strong>on</strong>taminants seem to be resistant to leaching.<br />

INTRODUCTION<br />

Envir<strong>on</strong>mental polluti<strong>on</strong> is placing an ever-increasing load <strong>on</strong> the various resources of<br />

our envir<strong>on</strong>ment, including soil. Tests and experiments involving heavy metals and<br />

other toxic elements play a very important role in our envir<strong>on</strong>mental research programs.<br />

Soils polluted with heavy metals can be found near industrial areas, metropolises, al<strong>on</strong>g<br />

major transportati<strong>on</strong> routes, roads, and areas treated with waste-water sludge, but soils<br />

can also be ”polluted” geologically (1). Soils are able to accumulate heavy metals for<br />

many years without the obvious signs of their acute toxic effect. However, the<br />

filtering/buffering capacity of soils is finite and above a certain level soils are no l<strong>on</strong>ger<br />

able to absorb these elements and become sources of polluti<strong>on</strong> themselves. Toxic<br />

elements are released into water, absorbed by cultivated crops and plants; they are<br />

assimilated into vegetative and generative organs, and enter the food-chain where they<br />

cause l<strong>on</strong>g-<strong>term</strong> harm (2,3).<br />

The system of relati<strong>on</strong>s between heavy metals-soils-plants can be accurately and<br />

reliably studied in targeted field experiments. The Ministry of Envir<strong>on</strong>ment and the Soil<br />

Research Institute of the Hungarian Academy of Science launched a research program<br />

in 1991, titled ”Heavy metal loading of the envir<strong>on</strong>ment”. The goal of the research<br />

program is to study the effect of certain heavy metals and other potentially toxic<br />

elements in the soil –plant system and in the food chain. The study is carried out in l<strong>on</strong>g<br />

<strong>term</strong> field experiments in major soil types (carb<strong>on</strong>ate-loam, carb<strong>on</strong>ate-sand, acidicloam,<br />

acidic-sand) (4). The aim of the present scientific paper is to examine the<br />

following:<br />

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