EFFECT OF ARTIFICIAL SOIL ACIDIFICATION AND LIMING ON GROWTH AND NUTRIENT STATUS OF MYCORRHIZAL ROOTS OF NORWAY SPRUCE (PICEA-ABIES [L.] KARST.)

Effects of soil acidification and liming on biomass responses and ''fr ee'' Al, Ca, K, Mg, Mn and P contents of mycorrhizal roots of mature N orway spruce (Picea abies [L.] Karst.) were studied at Hoglwald Forest in Southern Germany. At the untreated site, mycorrhizal root biomass was lower in the acid humus (pH = 3.3) than in the less acid upper (0- 5 cm) mineral soil (pH 4.1). Mycorrhizal roots from the humus containe d 10% of the level ''free'' Al in mycorrhizal roots from the upper min eral soil. During seven years of soil acidification the quantity of my corrhizal roots remained unaffected in the humus and the upper mineral soil, perhaps due to the high buffering capacity of the humus which p revented a significant alteration of the nutrient status of the roots. However, two years after soil acidification had been terminated, the percentage of mycorrhizal roots in the humus decreased, possibly becau se the ''free'' root concentrations of K had decreased. On the other h and, six years after liming, there was a two-fold increase of the annu al mean quantity of mycorrhizal roots in the humus. Compensatory limin g (acid irrigation after liming) had a similar effect on mycorrhizal r oot production in the humus. However, two years after acid irrigation had been terminated a decrease of mycorrhizal roots in the upper miner al soil (0-5 cm) was observed. Since the total amount of mycorrhizal r oots in the humus and upper mineral soil remained constant, compensato ry liming produced a shift in fine roots to the humus layer. The highe r mass of living mycorrhizal roots in the upper mineral soil (0-5 cm) as compared to the humus of the untreated plot as well as the increase d mass of mycorrhizal roots in the humus after liming or compensatory liming are both attributed to an increase in pH to 4.5 rather than all eviation of Al toxicity.