The greatest sources of atmospheric emissions of alkaline dust and SO2 in Estonia are the soil shale based power plants and the cement production. In the vicinity of oil sale processing and chemical plants the organic pollutants, as well asammonia, H2S etc. are also found in the ambient air. Temporal changes in emission amounts and in atmospheric air pollution levels in North-East Estonia since 1960 until today (1997-98) are discussed. During the period of 1989-98 the emissions from power plants decreased about 2.5 times and those from cement production up to 40 times. In 1960-89 oil shale fly ash was the prevalent factor of air pollution, most notably in north-eastern and northern parts of the region. Since 1990-91 the proportion of SO2 has increased in the balance of alkaline and acidic components in some industrial areas. Zonation of landscapes on the basis of air pollution and the critical loads of pollutants for forest trees and Sphagnum are discussed

A needle trace method was used to reveal the chronology of needle retention and growth rates on Scots pine in a stand near a power plant operating on oil shale. During the period of 1964-97, the height increment varied between 31 and 64 cm yr (-1), and the radial increment ranged from 1.06 to 3.71 mm yr (-1). The average needle density on the newly sprouted shoots of the main stem was 5.9 needles cm (-1) and the mean needle production on the same shoots was 266. The average number of needle sets along the main stem ranged from 2.2 to 3.1, the mean age of needles varied between 1.3 and 2.3 years. The short-term maximum concentrations of oil shale fly ash and SO2 ranged from 55 to 2510, and from 75 to 270 micro g m (-3), respectively. The annual average concentrations of fly ash varied between 6 and 95 micro g m (-3), and of SO2 between 2.5 and 10 micro g m (-3). Changes in neither the concentrations of fly ash nor SO2 were associated with the variation in needle retention of Scots pine. In the case of height increment, however, the correlation with the annual average concentration of oil shale fly ash was significant (r=0.83; p0.05)