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  • Hubbard Brook Nitrogen Oligotrophication (HBNO): Microbial Biomass, 2022-2023
  • Groffman, Peter M; Cary Insitute of Ecosystem Studies
    Martel, Lisa D; Cary Institute of Ecosystem Studies
  • 2024-12-05
  • Groffman, P.M. and L.D. Martel. 2024. Hubbard Brook Nitrogen Oligotrophication (HBNO): Microbial Biomass, 2022-2023 ver 1. Environmental Data Initiative. https://doi.org/DOI_PLACE_HOLDER (Accessed 2024-12-27).
  • The goal of this project is to test the overarching hypothesis that positive feedback mechanisms involving changes in seasonal cycles that diminish N availability to plants such that plant N demand is not met by soil N availability in northern forests. Specifically, we hypothesize that increasing N demand by plants (induced by increasing temperatures, longer growing seasons, and other environmental changes) leads to greater N resorption by trees in autumn, increased C:N in litter, and greater net immobilization of N by soil microbes in the following spring. However, the timing of snowmelt and soil freezing in spring may further affect net mineralization and N availability for plants. These hypotheses are being tested with a combination of observational, experimental, and modeling approaches at Hubbard Brook Experimental Forest in New Hampshire: 1) measurements at 14 previously established sites along an elevation/aspect climate gradient; 2) litter and snow manipulation experiments at six sites along the climate gradient to create variation in soil climate conditions and microbial N immobilization during spring. We leveraged 14 sites previously established along an elevation and aspect-driven climate gradient at Hubbard Brook as a “natural climate experiment to test our hypothesis that a positive feedback between N cycling during fall senescence and spring contributes to declining N availability in northern forests. This elevation gradient encompasses variation in mean annual air temperature of ~2.5 °C that is similar to the change projected to occur with climate change over the next 50–100 years in the northeastern U.S. There is relatively little variation in soils along the gradient. We are utilizing three sites at higher elevation (~550-660 m, north facing) and three sites at lower elevation (~375-500 m, south facing) for the litter and snow manipulation experiments to maximize the differences in temperature among the 14 sites.

    Litterbox manipulation:

    The objective of the litterfall manipulation experiment is to determine whether increases in autumn litter C:N ratios contribute to greater N immobilization by microbes and reductions in net mineralization and plant N uptake in spring, and ultimately, N oligotrophication in northern forest ecosystems. We applied early (low C:N litter that is lost from from hardwood foliage in the first two weeks of autumn) and late (high C:N litter that falls in the last two weeks of autumn) season litter in October 2022 that was collected in fall 2021 at rates equal to standing mass of litter (300 g m2). We also applied native litter that was collected from the forest floor of each intensive site to represent background levels of C:N in litter samples. This litter was applied to one litterbox at each of the six intensive sites. Following application of litter, we installed deer netting around and on top of each of the litterboxes to eliminate litter loss from wind. Soil samples were collected from these plots in November 2021, April 2022, May 2022, June 2022, November 2022, April 2023, May 2023, June 2023 and anlalysed for microbial biomass and activity, as described in the methods section.

    Snow manipulation:

    The objective of the snow manipulation experiment is to determine whether the timing of spring snowmelt, length of the spring, and soil freezing in spring affect microbial N immobilization, hydrologic losses, net mineralization, and plant N uptake. The snow manipulation treatment was conducted in the spring of 2022 and 2023. We manually halved (Removal treatment) or doubled (Addition treatment) snow water equivalent (SWE) in experimental plots in March of 2022 and 2023 to accelerate or delay by an average of one week, respectively, the onset of spring snowmelt. Soil Samples were collected from these plots in November 2021, April 2022, May 2022, June 2022, November 2022, April 2023, May 2023, June 2023 and anlalysed for microbial biomass and activity, as described in the methods section.

    These data were gathered as part of the Hubbard Brook Ecosystem Study (HBES). The HBES is a collaborative effort at the Hubbard Brook Experimental Forest, which is operated and maintained by the USDA Forest Service, Northern Research Station.

  • Geographic Coordinates
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    • N: 43.95019236, S: 43.95019236, E: -71.73064174, W: -71.73064174
    • N: 43.93415543, S: 43.93415543, E: -71.7684914, W: -71.7684914
    • N: 43.93218854, S: 43.93218854, E: -71.76717913, W: -71.76717913
    • N: 43.93077007, S: 43.93077007, E: -71.76180633, W: -71.76180633
    • N: 43.92738579, S: 43.92738579, E: -71.77291084, W: -71.77291084
    • N: 43.92305067, S: 43.92305067, E: -71.77643367, W: -71.77643367
    • N: 43.91985666, S: 43.91985666, E: -71.77745584, W: -71.77745584
    • N: 43.95490408, S: 43.95490408, E: -71.71862125, W: -71.71862125
    • N: 43.95885229, S: 43.95885229, E: -71.71984434, W: -71.71984434
    • N: 43.96068944, S: 43.96068944, E: -71.72161276, W: -71.72161276
    • N: 43.95552778, S: 43.95552778, E: -71.74247222, W: -71.74247222
    • N: 43.95311111, S: 43.95311111, E: -71.74066667, W: -71.74066667
  • knb-lter-hbr.419.1  (Uploaded 2024-12-05)  
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  • DOI PLACE HOLDER
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