Abstract

The aim of the study was to compare the concentrations of risk elements (As, Cu, Mn, Ni, Pb, Zn) in alluvial soil, which were measured by a portable X-ray fluorescence analyser (pXRF) in situ (FIELD) and in the laboratory (LABORATORY). Subsequently, regression equations were developed for individual elements through the method of construction of the regression model, which compare the results of pXRF with classical laboratory analysis (ICP-OES). The accuracy of the measurement, expressed by the coefficient of determination (R2), was as follows in the case of FIELD–ICP-OES: Pb (0.96), Zn (0.92), As (0.72), Mn (0.63), Cu (0.31) and Ni (0.01). In the case of LABORATORY–ICP-OES, the coefficients had values: Pb (0.99), Zn (0.98), Cu and Mn (0.89), As (0.88), Ni (0.81). A higher dependence of the relationship was recorded between LABORATORY–ICP-OES than between FIELD–ICP-OES. An excellent relationship was recorded for the elements Pb and Zn, both for FIELD and LABORATORY (R2 higher than 0.90). The elements Cu, Mn and As have a worse tightness in the relationship; however, the results of the model have shown its applicability for common use, e.g., in agricultural practice or in monitoring the quality of the environment. Based on our results, we can say that pXRF instruments can provide highly accurate results for the concentration of risk elements in the soil in real time for some elements and meet the principle of precision agriculture: an efficient, accurate and fast method of analysis.

Highlights

  • (3) a standard laboratory method using the aqua regia followed by inductively coupled plasma optical emission spectrometry (ICP-OES) spectroscopy

  • PXRF was used to analyse an area of 60 km2, with a soil depth of 20 cm, achieving a correlation coefficient of R2 = 0.95 for Pb compared to the laboratory method

  • Using the method of construction of the regression model by regression triplet, we compared the concentrations of risk elements in alluvial soils in the basin of two rivers (Mže and Otava)

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Summary

Introduction

A large number of published studies analysing the risk elements in alluvial soils in the vicinity of rivers, or even in entire flood areas, can be found [1,4,5,6,7,8,9,10,11,12] because the alluvial soils are specific. Their level of pollution can change relatively quickly, depending on the periodicity and extent of the floods

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