Geological Survey of Finland, Special Paper 46 - arkisto.gsf.fi
Geological Survey of Finland, Special Paper 46 - arkisto.gsf.fi
Geological Survey of Finland, Special Paper 46 - arkisto.gsf.fi
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<strong>Geological</strong> <strong>Survey</strong> <strong>of</strong> <strong>Finland</strong>, <strong>Special</strong> <strong>Paper</strong> <strong>46</strong><br />
Volli Kalm<br />
Fig. 3. Heavy metals<br />
distribution in the section<br />
through cultural layer<br />
in the centre (corner <strong>of</strong><br />
Küüni and Vanemuise<br />
streets) <strong>of</strong> the City <strong>of</strong><br />
Tartu.<br />
144<br />
HEAVY METALS IN THE CULTURAL LAYER<br />
Chemical analyses <strong>of</strong> the samples from the cultural<br />
layer exposed in an excavation at the city centre revealed<br />
that the soil contamination from heavy metals<br />
is very high (Fig. 3). The highest concentrations<br />
<strong>of</strong> Pb were found below the layer <strong>of</strong> debris from<br />
the Second World War (WW2), although this probably<br />
represents the extensive use <strong>of</strong> leaded gas after<br />
WW2. The maximum estimated concentration <strong>of</strong> Pb<br />
(240 mg/kg; Nõges 2006) in the section is 14.6 times<br />
higher than the average amount <strong>of</strong> Pb in Estonian<br />
humic soils (16.4 mg/kg; Petersell et al. 1997). Zinc<br />
and Cu reach their maximums (150 mg/kg and 96<br />
mg/kg respectively) in the lower half <strong>of</strong> the cultural<br />
Undesirable urban geological phenomena – subsidence<br />
<strong>of</strong> buildings, groundwater level fl uctuations,<br />
soil pollution – are mostly restricted to the city<br />
quarters located on the fl oodplain area. Lowering <strong>of</strong><br />
the groundwater level in the fl oodplain deposits lead<br />
into soil compaction, decay <strong>of</strong> timber rafts under the<br />
foundations <strong>of</strong> buildings and subsidence <strong>of</strong> buildings.<br />
The highest rate <strong>of</strong> subsidence (4.9 mm/yr in<br />
CONCLUSIONS<br />
layer, some 1.8-2.6 m below the surface. Concentration<br />
values <strong>of</strong> Zn and Cu have a good correlation<br />
(r = 0.77 and 0.82 respectively) with the content <strong>of</strong><br />
Ca, supporting the conclusion that in Ca-rich soils<br />
Cu and Zn may be sorbed on the surface <strong>of</strong> CaCO 3<br />
(Dudley et al. 1991). Concentration <strong>of</strong> Cd in the cultural<br />
layer (average 0.13 mg/kg) remains below the<br />
average Cd content in Estonian humic soils (0.4 mg/<br />
kg; Petersell et al. 1997). In the peat deposits below<br />
the cultural layer, the concentration <strong>of</strong> heavy metals<br />
decreases rather strongly (Fig. 3) and remains close<br />
to the average values in Estonian soils.<br />
1973) was recorded at the time <strong>of</strong> the most intensive<br />
groundwater consumption from the Quaternary aquifer.<br />
Since 1974, the groundwater level has risen<br />
and the subsidence decreased to 1.5-2 mm/yr over<br />
a 20 year period. Initial analyses showed that the<br />
cultural layer in the centre <strong>of</strong> the city is heavily contaminated<br />
with Pb, Zn and Cu, but not with Cd.