What’s New

June 2026

New release of THIS BOOK!!

. This book has moved to a new platform to add new features and to make future updates easier. It is now published through GitHub Pages. There have been updates to content, this new ‘What’s New’ section for quick reference, improvements in the user interface, addition of more interactive figures, and more. A special shout-out to a team from the Virginia Tech Environmental Data Science Capstone class (Samantha Libor and Maryann Nwude under the guidance of JP Gannon) for creating more graphs for the book that are directly tied to our published data in the Environmental Data Intiative Repository.

Co-limitation of tree growth by nitrogen and phosphorus in thirteen northern hardwood stands across the White Mountains

Current theory suggests that forest production should trend towards coincident limitation by multiple environmental factors. Based on a long-term, factorial N and P addition experiment at Hubbard Brook and other regional forests, we demonstrated additive co-limitation of tree growth by N and P. These results have important implications in light of rapidly changing environmental drivers in the region. See the Phosphorus Cycling chapter in this volume for details Nitrogen deposition and colimitation.

Blumenthal, N. M., Stevens, M. H. H., Goswami, S., Yanai, R. D., Fahey, T. J., & Fisk, M. C. (2025). Nitrogen and phosphorus co‐limitation of tree growth in northern hardwood forests. Ecology, 106(10), e70217.

Response to environmental change of soil carbon cycling in northern hardwood forest

Radiocarbon measurements of archived soil samples, together with mathematical models and field sampling at Hubbard Brook indicated that surface organic horizons (Oie) have been losing carbon at the site level at the rate of about 15 gC/ m2 yr since 1998. Additional details can be found in the chapter in this volume on Decomposition and soil carbon.

von Fromm, S.F., Olson, C.I., Monroe, M.D., Sierra, C.A., Driscoll, C.T., Groffman, P.M., Johnson, C.E., Raymond, P.A. and Pries, C.H., 2025. Temporal and Spatial Dynamics of Soil Carbon Cycling and Its Response to Environmental Change in a Northern Hardwood Forest. Global Change Biology, 31(5), p.e70250.

Effect of tree species and hydropedological soil type on surface organic horizon properties

Several features of the surface organic horizon, including thickness, CEC, C:N ratio and microbial communities, differed significantly beneath white ash trees in comparison to other hardwood species. Effects of hydropedological soil type also were observed, with thicker organic horizons in Bh podzols. Details about soil types can be found in this volume in the Introduction chapter.

Studer, E. A., Bailey, S. W., von Hoyningen Huene, B. L., Pries, C. E. H., & Ayres, M. P. (2025). Relations of the O-horizon with canopy tree species and hydropedologic soil types. Biogeochemistry.

February 2026

Recent declines of foliar N in northern hardwood forest at HBEF

Based on 32 years of sampling of the three dominant tree species in the northern hardwood forest at the HBEF (Lany et al. 2026), a temporal pattern of increasing foliar N to a peak in the early 2000s was followed by significant declines suggestive of recent N oligotrophication. See chapter on Nitrogen Cycling in this volume for details.

  • Lany, N, L Pardo, NL Cleavitt, T Fahey, and C Goodale. 2026. Long-term declines in nitrogen and other nutrients in foliage of three northern hardwood species at the Hubbard Brook Experimental Forest. Canadian Journal of Forest Research. https://doi.org/10.1139/cjfr-2025-0105

Recent increases of soil respiration in northern hardwood forests

Emission of carbon dioxide from the soil in northern hardwood forests in and around HBEF increased abruptly beginning around 2012-2013. Field measurements indicated roughly doubled CO2 emission during the warm season by 2020 (Mann et al. 2024, Possinger et al. 2024), signaling a profound alteration of the carbon cycle accompanying increasing atmospheric CO2 concentrations. See chapter on Soil Biology in this volume (Figure 7.5)

  • Mann, T. A., R. D. Yanai, T. J. Fahey, and A. B. Reinmann. “Nitrogen and Phosphorus Addition Affect Soil Respiration in Northern Hardwood Forests.” Ecosystems 27, no. 6 (2024): 765–78. https://doi.org/10.1007/s10021-024-00912-1.

  • Possinger, Angela R., Charles T. Driscoll, Mark B. Green, et al. “Increasing Soil Respiration in a Northern Hardwood Forest Indicates Symptoms of a Changing Carbon Cycle.” Communications Earth & Environment 6, no. 1 (2025): 418. https://doi.org/10.1038/s43247-025-02405-ytarget=“_blank” rel=“noopener”}.

Decline of sugar maple abundance following whole-tree harvest of W5 at HBEF The thirty-year trajectory of forest regrowth on W5 at the HBEF following whole-tree harvest indicated a dramatic decline in sugar maple abundance (Cleavitt et al. 2018). The decline has been most severe in upper slope positions where severe base-cation depletion, especially calcium, has been observed as a result of acid deposition and tree removals. For details see chapter on Forest Composition and Dynamics in this volume.

  • CCleavitt, Natalie L., John J. Battles, Chris E. Johnson, and Timothy J. Fahey. “Long-Term Decline of Sugar Maple Following Forest Harvest, Hubbard Brook Experimental Forest, New Hampshire.” Canadian Journal of Forest Research 48, no. 1 (2017): 23–31. HBR.2017-35. https://doi.org/10.1139/cjfr-2017-0233.

Increased evapotranspiration from the HBEF watersheds

Long-term measurements of the hydrologic balance of four small watersheds at the HBEF indicate a significant increase (about 30%) in evapotranspiration from the forest beginning around 2010 and continuing into the 2020s (Green et al. 2021). Although the cause of this increase remains uncertain, ongoing measurements suggest a role of increased transpiration perhaps accompanied by increased canopy GPP. For details see chapter on Hydrology in this volume.

  • Green, Mark B., Scott W. Bailey, John L. Campbell, et al. “A Catchment Water Balance Assessment of an Abrupt Shift in Evapotranspiration at the Hubbard Brook Experimental Forest, New Hampshire, USA.” Hydrological Processes n/a, no. n/a (2021): e14300. https://doi.org/10.1002/hyp.14300.

Enhanced biotic weathering of P from soils on W5 following whole-tree harvest

Long-term measurements of stream chemistry for W5 after the whole-tree harvest in 1984 indicate significant increases in dissolved Si that can only be explained as a result of increased weathering of silicate minerals in the soil profile (Berhardt et al. 2025). Perhaps the depletion of soil P by the forest harvest has promoted biotically driven weathering by ectomycorrhizal fungal networks of the now-dominant birches and beech on the watershed. For details see chapter on Phosphorus Cycling cycling in this volume.

  • Bernhardt, Emily S., Emma J. Rosi, Christopher T. Solomon, et al. “Forest Recovery after Deforestation Is Fueled by Mineral Weathering at the Expense of Ecosystem Buffering Capacity.” Proceedings of the National Academy of Sciences 122, no. 42 (2025): e2419123122. https://doi.org/10.1073/pnas.2419123122.