Soluble soil aluminum alters the relative uptake of mineral nitrogen forms by six mature temperate broadleaf tree species: possible implications for watershed nitrate retention
Soluble soil aluminum alters the relative uptake of mineral nitrogen forms by six mature temperate broadleaf tree species: possible implications for watershed nitrate retention
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DOI:
10.1007/s00442-017-3955-8
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发表时间:
2017-11-01
期刊:
影响因子:
2.7
通讯作者:
Peterjohn, William T.
中科院分区:
文献类型:
--
作者:
Burnham, Mark B.;Cumming, Jonathan R.;Peterjohn, William T.
Increased availability of monomeric aluminum (Al3+) in forest soils is an important adverse effect of acidic deposition that reduces root growth and inhibits nutrient uptake. There is evidence that Al3+ exposure interferes with NO3 (-) uptake. If true for overstory trees, the reduction in stand demand for NO3 (-) could increase NO3 (-) discharge in stream water. These effects may also differ between species that tolerate different levels of soil acidity. To examine these ideas, we measured changes in relative uptake of NO3 (-) and NH4 (+) by six tree species in situ under increased soil Al3+ using a N-15-labeling technique, and measured soluble soil Al levels in a separate whole-watershed acidification experiment in the Fernow Experimental Forest (WV). When exposed to added Al3+, the proportion of inorganic N acquired as NO3 (-) dropped 14% across species, but we did not detect a reduction in overall N uptake, nor did tree species differ in this response. In the long-term acidification experiment, we found that soluble soil Al was mostly in the free Al3+ form, and the concentration of Al3+ was similar to 65 mu M higher (similar to 250%) in the mineral soil of the acidified watershed vs. an untreated watershed. Thus, increased levels of soil Al3+ under acidic deposition cause a reduction in uptake of NO3 (-) by mature trees. When our N-15 uptake results were applied to the watershed acidification experiment, they suggest that increased Al3+ exposure could reduce tree uptake of NO3 (-) by 7.73 kg N ha(-1) year(-1), and thus increase watershed NO3 (-) discharge.