Jen Minnick1, Helga Van Miegroet2, and Jenny Wolfgram1. (1) Utah State University, Dept Wildland Resources, 5230 Old Main, Logan, UT 84322-5230, (2) 5230 Old Main Hill, Utah State University, Utah State University, Department of Wildland Resources, Logan, UT 84322-5230
Atmospheric N deposition is becoming a stressor on
ecosystems in the western U.S.
There are few NADP monitoring sites and little is known about N deposition
impacts on terrestrial ecosystems. High elevation ecosystems (i.e. above 2895
m) may be particularly sensitive to N-induced changes due to shallow soils,
short growing seasons, and sparse plant cover. This study focuses on N deposition
effects on a high elevation ecosystem along a modeled deposition gradient and
across contrasting edaphic conditions in the Grand Teton National Park. For 3 locations, we
measured N input (snow pack surveys, and summer deposition via through fall resin
collectors set out for 40-90 days), soil parameters (total and extractable N,
microbial biomass, and nitrification potential), and plant community
characteristics (species richness, species composition, percent cover, plant
and root biomass, and N in plants) to test whether soils or plants are effected
by N deposition first. Preliminary results show that inorganic N input via snow
ranged from 1-2 kg N ha-¹ with slightly more entering into the
system as NH4-N. Summer deposition (~0.5 kg N ha-¹) did
not differ among sites. Total and extractable N ranged from 0-10 µg g-¹
and failed to follow the modeled deposition regime. However, nitrification
potential followed the modeled regime. For low N deposition sites, wet
conditions favored nitrification potential, while for high N deposition sites,
nitrification potential occurred in drier sites. Regression analysis suggested
that species richness was not affected by either N input, or N already in the
system.