AHONEN-JONNARTH, ULLA1, ANDERS GÖRANSSON2 & ROGER FINLAY1.
1Department of Forest Mycology & Pathology, SLU, Box 7026, S-750 07 Uppsala, SWEDEN. 2Department of Production Ecology, SLU, Box 7042, S-750 07 Uppsala, SWEDEN.
There is disagreement in Sweden about the severity of forest
damage caused by acidification and the need for remedial actions such as liming.
Use of the molar ratio of base cations to aluminium (Ca+Mg+K)/Al) as a tool
for determining critical loads of acidic deposition has been criticised for
ignoring rhizosphere complexity. The aim of our study is to investigate the
response of Pinus sylvestris seedlings to variations in BC/Al ratio and
the extent to which these responses are modified by the presence of symbiotic
ectomycorrhizal fungi. Seedlings were grown in silver sand in a semi-hydroponic
system allowing steady state growth and received nutrient solution containing
N, K, Ca and Mg in the proportions 100:35:3:4. Plants were either colonised
by Laccaria bicolor or left uninfected. The seedlings were harvested
47, 59, 69, 80, 91 and 102 days after planting. All seedlings initially received
the same nutrient solution without aluminium. After 69 days the remaining seedlings
received either a solution with the molar ratio [Ca+Mg+K]/[Al] = 1.0 or [Ca+Mg+K]/[Al]
= 0.6 ([Ca+Mg]/[Al]=0.1)
The seedlings had the same relative growth rate (about 4 %) both before and
after introduction of the Al-treatment and at both BC/Al -levels. Biomass of
the seedlings was not decreased due to aluminium treatments either in mycorrhizal
or non-mycorrhizal seedlings. The biomass of non-mycorrhizal seedlings was slightly
higher in all treatments. Further experiments, using natural substrates, are
in progress to investigate the possible role of organic acid production and
mineral weathering by the mycorrhizal mycelium.