Further studies show that SIRM and χarm in the urban topsoil are also much higher and both are extremely significantly correlated with χlf, implying the dominance of stable single domain (SSD) and multidomain (MD) magnetic grains. Low χarm/SIRM and χarm/χlf ratios in the urban topsoil also imply its coarse grain size. SOFT(%) in the urban topsoil is 33.5% on average, but HIRM(%) only 2.0%, indicating magnetic soft fraction, ferri(o)magnetic minerals, are the main contributor to the soil magnetism. All the magnetic properties mentioned above imply the extra magnetic minerals accumulated in the urban topsoil originate from anthropogenic activities.
Average values of Cu, Zn, Pb, Cd, Cr, Ni, Mn and Fe in the urban topsoil are 93.4, 794.4, 139.0, 0.30, 243.7, 60.0, 1110.1 and 44.9x103 mg/kg, respectively, compared with 41.7, 238.6, 64.6, 0.080, 111.1, 52.2, 477.8 and 36.1x103 mg/kg, respectively, in the suburban soil. Moreover, Zn, Pb, Cd, Cr, Ni, Mn and Fe in the urban topsoil are significantly correlated with χlf values, indicating that the magnetic enhancement in the urban soil is closely related to heavy metal accumulation.
Affected by industrial activities and heavy traffic, magnetic values and heavy metal contents in the urban topsoil in Shanghai are significantly higher than those in the suburban soil. Magnetic methods reflect not only the content of magnetic minerals, but also their grain size and types, by which, we can distinguish anthropogenic magnetic particles from pedogenic ones. Hence, it is promising to use magnetic techniques for monitoring urban soil pollution.
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