The accumulation of calcium (Ca), copper (Cu) and cadmium (Cd) in roots and stem of Norway spruce (Picea abies [L.] Karst) was examined. Two-year-old Norway spruce seedlings were treated with elevated concentrations of Ca, Cd or Cu, or as combinations of Ca with Cu or Cd in nutrient solutions for three months. The stem was divided into bark, wood formed during the treatment period (new wood), and wood formed before the treatment period (old wood). The accumulation of the metals in stem and roots increased with addition of the respective metal into nutrient solution. Addition of Cu decreased the accumulation of Ca in roots and wood, and Ca addition decreased the accumulation of Cu in the new wood. By adding Ca in combination with Cu the accumulation of Cu in the stem was decreased even more by Ca and the negative effect of Cu on the Ca content in the stem was diminished. Addition of Cd decreased the accumulation of Ca in wood, especially the old wood, and Ca addition decreased the accumulation of Cd in roots, bark and new wood. By adding Ca in combination with Cd the Ca content was reduced in the bark, instead of in the old wood.

Spreading of wood ashes from the pulp and paper industry will change the content and proportions of calcium (Ca), copper (Cu), cadmium (Cd), and zinc (Zn) in forest soils and thus also in the forest trees. The accumulation and distributions of, and interaction between, Ca and heavy metals in wood and bark of two‐year‐old Norway spruce (Picea abies [L.] Karst.) were investigated in this study. The treatment was carried out for 3 months in nutrient solutions, and there was a low or a high addition of Ca, Cd, Cu or Zn. The metal accumulation in, and distribution between, the bark, the wood formed during the treatment period (new wood), and the wood formed before the treatment period (old wood) was analyzed with AAS. The contents of the metals in the stems (i.e., bark, new wood, old wood) increased with elevated addition of the metal in question, also at the low addition of Ca, Cu, and Zn. Interactions between Ca and the heavy metals were found. Elevated Ca additions decreased the Cd content of the bark and the Zn content of the old wood, and tended to decrease the Cu content of the bark and the Cd content of the old wood. The Ca content decreased in both, wood and bark after Cu addition and the high Cd addition. Thus, even small changes in metal availability and proportions in forest soil, such as after spreading of wood ashes in the forest, will be reflected in the content of the metals in the wood and bark of forest trees.

This study compared the sensitivity to, and uptake and distribution of, cadmium (Cd) in three tree species, Norway spruce (Picea abies (L.) Karst.), Scots pine (Pinus sylvestris L.), and European white birch (Betula pendula Roth), as well as different populations of these species. Seedlings of each species from three regions (southern, central, and northern parts of Sweden) were cultivated in nutrient solution and treated with varying concentrations of Cd. Sensitivity was determined by using the Weibull function on root and shoot dry weight and root length measurements. Cd uptake and translocation were analysed. The results on root sensitivity revealed that birch and spruce were the least and most sensitive species, respectively, to both the external and tissue levels of Cd. In terms of shoot sensitivity, however, birch was the only species affected by Cd, i.e., the most sensitive species. Pine and birch had similar Cd uptake, while spruce had lower uptake and translocation of Cd compared with the others. There were also differences in sensitivity within the species. The central ecotype of all species tended to be the most Cd resistant. The central ecotype of spruce and birch had the lowest Cd uptake, whereas the central ecotype of spruce and pine had the lowest translocation of Cd to the shoot.Key words: birch, cadmium, pine, sensitivity, spruce, uptake.

To counteract nutrient depletion and acidification of forest soils, recycling of waste products from the forest industry has been suggested. Spreading of these waste products will probably change the concentration and availability of Ca and heavy metals in forest soils and thereby the contents of these metals in trees. This field study aimed at examining the influence of pellets of wood ash (ash) or a mixture of wood ash and green liquor dregs (ash+GLD) on the contents of Ca, Cd, Cu and Zn in wood and bark of Norway spruce [Picea abies (L.) Karst.]. The waste products were spread in an amount of 3000 kg ha −1 in 1996 at a felling site in Sweden and in 1999 and 2002 young spruce trees, planted in 1995, were collected and wood and bark were analysed for Ca, Cd, Cu and Zn with AAS. Changes in the metal content of wood and bark of young spruce trees were found 3 and 6 years after spreading pellets of ash or ash+GLD compared with the control. The effect of the treatments on the metal contents of bark and wood differed and was larger after 3 years than after 6 years. Treatment with ash+GLD tended to have less effect on the metal contents of bark and wood than treatment with only ash. An increase in the contents of Cu and Zn in bark or wood, compared with the control, was only found for the ash treatment and only 3 years after application. Both the ash and ash+GLD treatment decreased the Cd content of the wood and/or bark after 3 years, and after 6 years it still was, or tended to be, lower than the control.

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