Research Article
Long-Term Dynamics of Urban Soil Pollution with Heavy Metals in Moscow
Table 2
Mean content of HMs (mg/kg) in topsoils of natural background and various land-use zones in the Eastern district of Moscow in 1989, 2005, and 2010.
| Year (number of samples) | Pb | Zn | Cu | Cd | Co | Cr | Ni | Mn | Cs |
| Natural background of the Meshchera lowland | 1989 (10) | 9.04 | 37.5 | 27.9 | 0.34 | 6.60 | 32.0 | 15.2 | 585 | 5.40 |
| Highways (А) and industrial zones (P) | 1989 (12) | 60.5 | 224 | 80.7 | 0.65 | 3.85 | 34.0 | 17.6 | 442 | 5.58 | 2005 (14) | 174 | 305 | 130 | 0.81 | 5.82 | 51.7 | 26.9 | 518 | 8.08 | 2010 (13), А | 59.5 | 183 | 67.5 | 1.23 | 8.48 | 89.9 | 32.2 | 412 | 1.90 | 2010 (5), Р | 114 | 286 | 88.0 | 1.37 | 9.3 | 92.2 | 35.4 | 513 | 1.88 |
| Residential zone with low-rise buildings (L) | 1989 (5) | 72.4 | 138 | 39.4 | 0.64 | 2.67 | 32.1 | 16.2 | 463 | 4.53 | 2005 (5) | 159 | 180 | 65.7 | 0.81 | 3.84 | 47.9 | 22.6 | 549 | 6.34 | 2010 (5) | 68.8 | 163 | 60.6 | 1.33 | 8.12 | 95.6 | 33.6 | 544 | 1.64 |
| Residential zone with medium-rise buildings (M) | 1989 (16) | 23.4 | 130 | 40.1 | 0.35 | 2.48 | 20.5 | 12.1 | 340 | 4.65 | 2005 (17) | 39.9 | 165 | 58.8 | 0.48 | 3.76 | 29.2 | 17.8 | 414 | 6.47 | 2010 (10) | 66.7 | 223 | 62.3 | 1.43 | 8.6 | 106 | 30.0 | 493 | 2.09 |
| Residential zone with high-rise buildings (H) | 1989 (5) | 16.4 | 76.5 | 24.6 | 0.14 | 1.61 | 16.3 | 9.14 | 260 | 2.43 | 2005 (5) | 20.2 | 88.3 | 28.1 | 0.15 | 1.82 | 18.2 | 10.6 | 309 | 2.91 | 2010 (7) | 44.1 | 162 | 54.0 | 1.45 | 8.57 | 104 | 26.1 | 389 | 1.99 |
| Recreational zone (R) | 1989 (6) | 21.1 | 76.7 | 24.3 | 0.17 | 2.44 | 9.24 | 7.58 | 512 | 4.04 | 2005 (6) | 32.9 | 82.7 | 28.9 | 0.20 | 2.87 | 11.6 | 9.20 | 538 | 4.44 | 2010 (9) | 49.4 | 147 | 50.4 | 2.05 | 8.8 | 101 | 29.0 | 482 | 1.87 |
| Agricultural landscapes (AG) | 1989 (5) | 45.6 | 96.3 | 57.7 | 1.07 | 3.20 | 34.0 | 18.0 | 535 | 3.74 | 2005 (5) | 84.7 | 122 | 71.2 | 1.44 | 4.09 | 37.9 | 21.5 | 640 | 5.19 | 2010 (3) | 34.0 | 173 | 67.0 | 3.70 | 7.7 | 137 | 27.3 | 492 | 1.47 |
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