The influence of N pulses in the form of experimental additions of HNO3 at two times ambient and (NH4)2SO4 at two and four times ambient on the herbaceous and woody understory plants in three Adirondack Mountain hardwood forests was evaluated. Addition of (NH4)2SO4 decreased cover of dominant herbs and woody seedlings at Woods Lake, a site in the western Adirondacks. Tissue N concentrations of combined herbs and ferns at Woods Lake increased with addition of roman NH sub 4 sup + at both levels (9% at two times ambient; 13% at four times ambient) and increased with all three N treatments at Huntington Forest, a central Adirondack site (14% with roman NO sub 3 sup - and roman NH sub 4 sup + at two times ambient; 22% with roman NH sub 4 sup + at four times ambient). Seedlings of American beech (Fagus grandifolia Ehrh.) increased foliar N concentration 7-8% with addition of roman NH sub 4 sup + treatments at Huntington Forest, but did not respond to N addition at Woods Lake and Pancake Hall Creek, a western Adirondack site. In general, greatest plant nutrient response to N addition occurred at Huntington Forest, where atmospheric inputs of N are lower than at Woods Lake and Pancake Hall Creek.
Surface waters in forested watersheds in the Adirondack Mountains and northern New York State are susceptible to nitrogen (N) saturation. Atmospheric deposition of N to watersheds in this region has been measured but the extent of internal N inputs from symbiotic N fixation in alder-dominated wetlands is not known. We estimated N fixation by speckled alder in these wetlands by the N natural abundance method and by acetylene reduction using a flow-through system. Foliar N derived from fixation (%N) was estimated for five wetlands. The δN of speckled alder foliage from four of the five sites did not differ significantly (P≤0.05) from that of nodulated speckled alders grown in N-free water culture (-1.2±0.1‰). Estimates from the N natural abundance method indicated that alders at these sites derive 85-100% of their foliar N from N fixation. At one of the sites, we also measured biomass and N content and estimated that the alder foliage contained 43 kg N ha of fixed N in 1997. This estimate was based on a foliar N content of 55.4±7 kg N ha (mean±SE), 86±4%N, and an assumption that 10% of foliar N was derived from reserves in woody tissues. At this site, we further estimated via acetylene reduction that 37±10 kg N ha was fixed by speckled alders in 1998. This estimate used the theoretical 4:1 CH reduction to N fixation ratio and assumed no night-time fixation late in the season. Nitrogen inputs in wet and dry deposition at this site are approximately 8 kg N ha year. We conclude that speckled alder in wetlands of northern New York State relies heavily on N fixation to meet N demands, and symbiotic N fixation in speckled alders adds substantial amounts of N to alder-dominated wetlands in the Adirondack Mountains. These additions may be important for watershed N budgets, where alder-dominated wetlands occupy a large proportion of watershed area.
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