2017 ESA Annual Meeting (August 6 -- 11)

COS 99-8 - Stable nitrogen isotopes in tree rings are an integrator of historical changes in nitrogen cycling dynamics in red spruce (Picea rubens Sarg.) forests in West Virginia

Wednesday, August 9, 2017: 4:00 PM
B117, Oregon Convention Center
Justin M. Mathias and Richard B. Thomas, Department of Biology, West Virginia University, Morgantown, WV
Background/Question/Methods

The availability of soil nitrogen (N) constrains the ability of temperate forests to sequester carbon (C) and mitigate future climate warming. While there are many ways to characterize the N status of an ecosystem’s present state (i.e., mineralization, soil and foliar δ15N), there remain roadblocks to extending N status records back in time. As such, we have a limited understanding of how N deposition altered C sequestration prior to regional forest inventory efforts. To fill this knowledge gap, we investigated the extent to which tree ring δ15N integrates N cycling dynamics and its relationship with carbon isotope discrimination (∆13C). We analyzed tree ring δ15N and δ13C from fifteen red spruce trees (Picea rubens Sarg.) across three sites spanning a latitudinal transect in West Virginia, USA. We first examined whether tree ring δ15N from 2011-2013 tracked present indices of site N availability. From 1940-2013, we analyzed the relationships between tree ring δ15N with time and historical N loading. Further, we investigated the relationship between tree ring δ15N and growth, as well as changes in physiology derived from ∆13C.

Results/Conclusions

Across all red spruce sites, tree ring δ15N for 2011-2013 was positively related to foliar δ15N (R2 = 0.59, p < 0.05), and was marginally related to potential rates of N mineralization (R2 = 0.51, p = 0.07). Averaged across all sites from 1940-1990, tree ring δ15N did not change significantly from a mean of 0.404 ‰. After 1990, tree ring δ15N progressively declined, on average, by 0.082 ‰ each year. The reduction in tree ring δ15N after 1990 was positively related to the decline in national emissions of NOx (R2 = 0.85, p < 0.01) and local wet deposition of NO3- (R2 = 0.74, p < 0.01). Further, reductions in tree ring δ15N after 1990 were synchronous with increases in tree ring ∆13C (R2 > 0.92, p < 0.05), and occurred alongside increased growth of the red spruce trees. Together, these data suggest a tighter, more closed N cycle after 1990 which likely resulted from decreases in exogenous inputs of N coupled with increased red spruce growth and may have broad implications for forest ecosystem recovery to pollution, including increased water quality and fewer occurrences of eutrophication as pollution declines.