Aluminum (Al) toxicity may limit the growth and nutrient acquisition of sen
sitive tree species in regions receiving acidic deposition. Symbioses betwe
en tree roots and mycorrhizal fungi may offset the negative impacts of Al i
n the root zone. Liriodendron tulipifera L. (tulip-poplar) is an important
tree species in the Appalachian Mountains of the southeastern United States
and may be at risk from the high levels of acidic deposition in that area.
Mycorrhizal and non-mycorrhizal tulip-poplar seedlings were exposed to Al
levels of 0, 50, 100, and 200 muM in sand culture for 6 weeks. Mycorrhizal
plants accumulated two to seven times the shoot and root biomass of non-myc
orrhizal plants and demonstrated no decreases in biomass with Al exposure.
Non-mycorrhizal plants exhibited significant reductions in biomass at and a
bove 100 muM Al. Aluminum toxicity in non-mycorrhizal plants appears to be
the result of the disruption of P translocation to leaves and Ca, Mg, P, Cu
, and Zn uptake in roots. Mycorrhizal plants accumulated 2 and 1.5 times th
e concentration of Al in shoots and roots, respectively, indicating that Al
resistance was not associated with the exclusion of Al from the plant. Pat
terns of labile Al in solution, nutrients, and Al accumulation in tissues s
uggest that arbuscular mycorrhizal fungal ecotypes may alter the form or co
mpartmentation of Al within the rhizosphere and plant, thus protecting seed
lings from the effects of exposure to Al in the soil solution.