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      Nitrogen Cycling Responses to Mountain Pine Beetle Disturbance in a High Elevation Whitebark Pine Ecosystem

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          Abstract

          Ecological disturbances can significantly affect biogeochemical cycles in terrestrial ecosystems, but the biogeochemical consequences of the extensive mountain pine beetle outbreak in high elevation whitebark pine (WbP) ( Pinus albicaulis) ecosystems of western North America have not been previously investigated. Mountain pine beetle attack has driven widespread WbP mortality, which could drive shifts in both the pools and fluxes of nitrogen (N) within these ecosystems. Because N availability can limit forest regrowth, understanding how beetle-induced mortality affects N cycling in WbP stands may be critical to understanding the trajectory of ecosystem recovery. Thus, we measured above- and belowground N pools and fluxes for trees representing three different times since beetle attack, including unattacked trees. Litterfall N inputs were more than ten times higher under recently attacked trees compared to unattacked trees. Soil inorganic N concentrations also increased following beetle attack, potentially driven by a more than two-fold increase in ammonium (NH 4 +) concentrations in the surface soil organic horizon. However, there were no significant differences in mineral soil inorganic N or soil microbial biomass N concentrations between attacked and unattacked trees, implying that short-term changes in N cycling in response to the initial stages of WbP attack were restricted to the organic horizon. Our results suggest that while mountain pine beetle attack drives a pulse of N from the canopy to the forest floor, changes in litterfall quality and quantity do not have profound effects on soil biogeochemical cycling, at least in the short-term. However, continuous observation of these important ecosystems will be crucial to determining the long-term biogeochemical effects of mountain pine beetle outbreaks.

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          Nitrate losses from disturbed ecosystems.

          A systematic examination of nitrogen cycling in disturbed forest ecosystems demonstrates that eight processes, operating at three stages in the nitrogen cycle, could delay or prevent solution losses of nitrate from disturbed forests. An experimental and comparative study of nitrate losses from trenched plots in 19 forest sites throughout the United States suggests that four of these processes (nitrogen uptake by regrowing vegetation, nitrogen immobilization, lags in nitrification, and a lack of water for nitrate transport) are the most important in practice. The net effect of all of these processes except uptake by regrowing vegetation is insufficient to prevent or delay losses from relatively fertile sites, and hence such sites have the potential for very high nitrate losses following disturbance.
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            Long lasting nitrate leaching after bark beetle attack in the highlands of the Bavarian Forest National Park.

            During the past decade bark beetle (Ips typographus) attacks killed nearly all of the Norway spruce [Picea abies (L.) Karst.] stands in the unmanaged zone in the highlands of the Bavarian Forest National Park. This study was conducted to predict if and how long the catastrophic event might cause elevated nitrate NO3(-) concentration in seepage water, and if the presence of ground vegetation may reduce NO3(-) leaching. A chronosequence approach was used to investigate NO3(-) leaching before and after the death of trees. Additionally, the impact of ground vegetation coverage on NO3(-) leaching was determined. Flux weighted yearly NO3(-) concentrations were significantly elevated in the first 5 yr after the dieback compared with intact stands (27 micromol(c) L(-1)), with highest concentrations in the fifth year after the dieback (579 micromol(c) L(-1)). Lowest NO3(-) concentrations were observed 17 yr after the dieback (10 micromol(c) L(-1)). Suction cups in places without ground vegetation showed significantly higher NO3(-) concentrations of 163 to 727 micromol(c) L(-1) (Year 2-5 after the dieback) than suction cups without vegetation. However, net uptake of N by ground vegetation observed during the first 7 yr after the dieback was low on a plot scale. Compared with other severe disturbances in forests, NO3(-) concentrations were elevated for a longer period. Due to high rates of precipitation, NO3(-) dilution occurred and concentrations remained mostly below the European critical level for drinking water. Part of the observed heterogeneity in NO3(-) concentrations could be attributed to different patterns of ground vegetation coverage.
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              Environmental Parameters Regulating Gaseous Nitrogen Losses from Two Forested Ecosystems via Nitrification and Denitrification.

              Gaseous N losses from disturbed and reference forested watersheds at the Coweeta Hydrologic Laboratory in western North Carolina were studied by in situ N(2)O diffusion measurements and laboratory incubations throughout a 10-month period. Soil temperature, percent base saturation, and water-filled pore space accounted for 43% of the variation in in situ N(2)O diffusion measurements. Laboratory incubations distinguished the gaseous N products of nitrification and denitrification. Nitrifying activity, ambient NO(3), and nitrification N(2)O were positively correlated with percent base saturation. However, differences between watersheds in soil N substrate caused by presence of leguminous black locust in the disturbed watershed were confounded with differences in soil acidity. Denitrification was most strongly affected by soil moisture, which in turn was determined by precipitation events and slope position. Gaseous N losses from well-drained midslope and toeslope landscape positions appeared to be minor relative to other N transformations. Favorable conditions for denitrification occurred at a poorly drained site near the stream of the disturbed watershed. Laboratory incubations revealed high rates of NO(3) reduction in these soils. We speculate that the riparian zone is a major site of depletion of NO(3) from the soil solution via denitrification.
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                Author and article information

                Contributors
                Role: Editor
                Journal
                PLoS One
                PLoS ONE
                plos
                plosone
                PLoS ONE
                Public Library of Science (San Francisco, USA )
                1932-6203
                2013
                5 June 2013
                : 8
                : 6
                : e65004
                Affiliations
                [1 ]Department of Ecosystem and Conservation Sciences, University of Montana, Missoula, Montana, United States of America
                [2 ]U.S. Geological Survey, Southwest Biological Science Center, Moab, Utah, United States of America
                DOE Pacific Northwest National Laboratory, United States of America
                Author notes

                Competing Interests: The authors have declared that no competing interests exist.

                Conceived and designed the experiments: MPK SCR CCC. Performed the experiments: MPK CCC. Analyzed the data: MPK CCC. Contributed reagents/materials/analysis tools: CCC. Wrote the paper: MPK SCR CCC.

                Article
                PONE-D-12-32092
                10.1371/journal.pone.0065004
                3673984
                23755166
                12c429a5-85cb-4bb0-ae0b-41fdc4ea57aa
                Copyright @ 2013

                This is an open-access article, free of all copyright, and may be freely reproduced, distributed, transmitted, modified, built upon, or otherwise used by anyone for any lawful purpose. The work is made available under the Creative Commons CC0 public domain dedication.

                History
                : 17 October 2012
                : 23 April 2013
                Page count
                Pages: 8
                Funding
                Funding sources include a United States Department of Agriculture National Needs Fellowship (USDA-CSREES 2008-38420-19524)( http://www.csrees.usda.gov/fo/nationalneedsgraduatefellowships.cfm) and a grant from the McIntire-Stennis Cooperative Forestry Research Program. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
                Categories
                Research Article
                Biology
                Biochemistry
                Metabolism
                Nitrogen Metabolism
                Ecology
                Ecosystems
                Ecosystem Functioning
                Plant Ecology
                Plant-Environment Interactions
                Biogeochemistry
                Ecophysiology
                Global Change Ecology
                Microbial Ecology
                Soil Ecology
                Terrestrial Ecology
                Microbiology
                Microbial Ecology
                Plant Science
                Plant Biochemistry

                Uncategorized
                Uncategorized

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