119ACTA FACULTATIS ECOLOGIAE, 16: Suppl. 1, 119–123 Z<strong>vo</strong>len (Slovakia), 2007MAGNETIC SUSCEPTIBILITY MAPPING OF ROADSIDEPOLLUTIONDenisa Kľučiarová – D. GregorováGeofyzikálny ústav, Slovenská akadémia vied, Dúbravská cesta 9, 845 28 Bratislava, e-mail: geofdeni@savba.skABSTRACTKľučiarová D. & Gregorová D. Magnetic Susceptibility Mapping of Roadside PollutionIn the last years, several proxy methods have been used to outline increased levels of pollution. Oneof them is based on measurements of the concentration of (ferri)magnetic minerals of antropogenic origin.This approach was successfully applied in several European cities and has shown that magnetic parameters(mainly magnetic susceptibility) can be used as a proxy for heavy metals pollution in topsoils.The aim of our study was to trace the distribution and concentration of contaminants (heavy metals) inthe soil along the road carrying appreciable traffic by using magnetic proxies. The area of this study wasthe part of the main road between Pezinok and Pezinská Baba. We tested how far magnetic measurement ofsoil samples can give information about road soil pollution. The soil samples (very close to the road, 0.5 mand 2m from the road) were collected each 50 m on the 3km long way, air-dried, sieved and measured forthe bulk magnetic susceptibility on the Kappabridge (KLY–2).The results show that the soil samples near the road are characterized by enhanced magnetic susceptibility,with highest values and that the magnetic susceptibility decreases with increasing distance fromthe road. The geochemical analyses revealed the high positive correlation. Therefore the measurement ofmagnetic susceptibility of soils can be – in this case – used as a supplemental method to the geochemicalmapping; method, which allows to assess, in a simple, cheap and rapid way, the level of soil pollution insites, where the geochemical data are missing.Key words: magnetic susceptibility, heavy metals, magnetic screening, pollution of roadside soilsINTRODUCTIONPollution of soils and sediments significantlyreduce environmental quality and affect humanhealth. As a condition for effective protection andremediation actions, the screening and detection ofsoils and sediment pollution has become increasinglyimportant. The pollutants of most concern areheavy metals and organic contaminants.Magnetic techniques were shown to be highlyuseful in investigating industrial pollutants and otheratmospheric aerosols. The intention of magneticstudies of aerosols has been the discrimination offly–ash from other aerosols based on the characteristicmagnetic properties of anthropogenic dusts.Recent studies (Strzyszcz, 1993; Strzyszcz andMagiera, 1998; Petrovský et al,. 1999) demonstratehow a combination of simple magnetic susceptibilitymeasurements can help identify regions wheresoils contain higher than average concentrations offly-ash and other anthropogenic dusts. In additionto fly-ash, there are other numerous atmosphericpollutants such as vehicle and aircraft emissionsor dust from cement production, open pit mining,and steel production. Vehicle emissions have beensuggested to be a significant source of magneticpollutants (Hunt, 1986). However, details about theorigin and the composition of these particles arepresently unknown.Preliminary studies indicate a possible correlationbetween magnetic susceptibility measurementsand atmospheric contaminants. Particles below the
120PM 10 limit (10µm) can significantly affect humanhealth as they can easily be transported into deeperparts of the respiratory tract and accumulated inthe alveoli (LfU – Landesanstalt für Umweltschutz,1998). It is well known that due to their specificsurface, such particles are excellent absorbers andcarriers of pollutants such as heavy metals. Magneticmethods provide an inexpensive and quick diagnosticalternative to other techniques for (direct)analyzing pollutants and are extremely sensitive tomagnetic particles of the above mentioned grainsizes (Hoffmann et al,; 1998, Leven et al., 1998).Sediments and soils can act as natural storagefor many types of pollution. Magnetic proxies representpowerful means for routine screening anddetecting contamination due to heavy metals.Here, we report results of our investigationsfocused on pollution screening using magnetic susceptibilityon roadsides. The main aim of this studyis to test the applicability of the magnetic mappingmethod.ENVIRONMENTAL MAGNETISM– MAGNETO-SCREENINGOF POLLUTIONOverviewA description of the method of environmentalmagnetism including a few results demonstratingthe capabilities of this technique are presented below(more detailed reviews are found, e.g. in (Oldfield,1991; King and Chanell, 1991; Strzyszcz, 1993,Dearing, 1994; Heller and Evans, 1995; Verosub andRoberts, 1995; Reynolds and King, 1995; Petrovskýand Elwood, 1999).In environmental magnetism, magnetic propertiesof materials such as soils, sediments and dustsare investigated. Such measurements provide powerfultools for approaching environmental problemsof concern such as climate and environmentalchanges and, more recently, environmental pollution.The high sensitivity of magnetic measurementsallows the detection of very low quantitiesof magnetic material which often act as proxies forthe underlying environmental processes. Anthropogenicpollution can also have a strong magnetic signatureand magnetic techniques have proven to becapable of discriminating between different sourcesof pollution. Magnetic techniques have beenapplied successfully in studies of climate changes,soil erosion, analyzing of atmospheric (e.g. bydetecting high fly-ash) and pollution produced byhistorical or active mining and other anthropogenicactivities. The sensitivity of magnetic techniques issuited for rapid measuring of very small quantitiesof magnetic particles in bulk samples (in generalequivalent to ppb in chemical analyses). Magneticparameters are capable of discriminating the ferromagneticcomponent of atmospheric dust derivedfrom soil-sizes particles from different source areasas well as fly-ash from different industrial sources(e.g. Hunt et al,. 1984; Chester et al., 1984; Oldfieldand Robinson, 1985; Hunt, 1986).Although magnetic studies have been successfulin providing proxies for environmentalprocesses, the fact that many of the environmentalmagnetic results rely on bulk techniques meansthat only average magnetic parameters are obtainedfrom many measurements.MethodsThe principle of the method of environmentalmagnetism, namely of the magnetic-proxies techniquewhich is used in this study for the screeningand detection of pollution can be summarized asfollows:(1) All rocks, sediments and soils contain a certain,mostly accessory portion of ferri(o)magneticminerals.(2) These phases are: Fe-oxides (magnetite, Fe 3O 4,;maghemite, γ-Fe 2O 3;hematite, α-Fe 2O 3), Fe--hydroxides (goethite, a-FeOOH), Fe-sulfides(pyrrhotite, Fe 7S 8; greigite, Fe 3S 4) or similarphases.(3) In addition, aerosols and dust of anthropogenicorigin containing different ferri(o)magneticphases with Fe partly substituted by other cationslike Ni, Co, Cr, Ti, Al, Mg are depositedand accumulated in soils and sediments.(4) With the help of magnetic proxies such as susceptibility,potentially polluted areas can bemapped in the field (so-called magnetometry):2D-mapping.(5) Only the magnetic signal related to the secondaryferri(o)magnetic phases of anthropogenicorigin is of interest.(6) A series processes are known to result in an enhancementof the magnetic signal in soils or sediments(Maher, 1998). Therefore, the anthropogenicmagnetic signal must be discriminated
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35DISCUSSIONThe ionising radiation
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41180160140this reason we also pick
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435001450400350hKz0,8h [m]300250200
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46deposit is that stripped in off-l
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48TruenessTrueness was determined i
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50MATERIAL AND METHODSChloroform (p
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52absorbance [a.u.]1,000,750,500,25
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65Ai - Ai-1 [Bq.m -3 ]86420-2-4-6-8
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- Page 132 and 133: 131RESULTS AND DISCUSSIONTable 2 gi
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