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matters happens more intense than in the furthest sampling plots, where just the<br />

horizon O of organic matter was found (Table 3.5) (Laiviņš et al., 1993, Vaivara,<br />

2006).<br />

Table 3.4<br />

The distance of te sample plots from the source of pollution and the hight above sea level<br />

(Laiviņš et al., 1993)<br />

Observation site Distance, m Height above sea level, m<br />

Dolomite processing<br />

plant<br />

0 27,2<br />

Saulkalne 1 300 28<br />

Saulkalne 2 370 28<br />

Saulkalne 3 1270 25<br />

Saulkalne 4 4370 20,2<br />

Saulkalne 5 6270 16,5<br />

In the two sampling plots closest to the processing plant, the bush storey is well<br />

developed. The vegetation according to the Elenberg scale corresponds to a<br />

moderately rich, neutral soil. Also the bush storey of Saulkalne 3 is well developed.<br />

The vegetation corresponds to a moderately rich, moderately acidic up to a neutral<br />

soil. Saulkalne 4 and 5 correspond to an acidic, poor soil. The furthest sampling plot<br />

was chosen as a control plot, as according to the vegetation it corresponded to a<br />

Vaccinio myrtilli – Pinetum forest type. Other sampling plots correspond to a same<br />

forest type of different stages of degradation (or europhication) (Laiviņš et al., 1993;<br />

Laiviņš, 1998; Vaivara, 2006).<br />

Soil samples were taken in the period of maximum earthworm activity, in<br />

spring and autumn, in each plot digging five 50 x 50 cm (0.25 m 2 ) soil holes up to<br />

the upper border of horizon B. The found earthworms were fixed and till<br />

identification kept in a 70% ethyl alcohol.<br />

30

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