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Actually, probably because roots are considered as the main site of metal toxicity exposure, the cellular and molecular bases of Cd tolerance of mycorrhizal plants have been essentially grasped at the belowground level [ 16- 22].
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Plants were then washed and dried (at 60°C) aboveground and the belowground biomass was measured.
There were differences in the N content of the belowground biomass at the two levels of soil nitrogen content studied between the particular clones.
However, the increase in the belowground biomass at the higher soil N level also brought about an increase in stilbene production (i.e., the amount of stilbenes in the belowground biomass of one plant).
In any case, introduced species have an ever-increasing presence in the aboveground community and now dominate each year's standing vegetation, yet they do not appear to be infiltrating the belowground community at similar rates and proportions.
We expect the belowground estimates of root biomass and C provided here will be helpful in this regard and for developing a more thorough understanding of belowground C stores at the landscape level.
With the contribution of this study, the magnitude of the belowground reservoir can now be updated.
One possibility is that weaker diversity stability relationships at the ecosystem level are due to the presence of soil compensatory mechanisms, such as inherited carbon pools from previous land management and time-lag responses of the belowground communities.
and warn the belowground dweller not to approach the opening too closely.
Fewer studies have considered the belowground biomass.
The belowground biomass of knotweed was only measured in 2007.
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