Methods:
Fertilization
Fertilizer additions of NH4NO3 and Na2SO4 began in 1988 as six equal applications over the growing season (May - Sept). Fertilizer is weighed, mixed with 20 liters of water (equivalent to 0.002 cm rainfall) and applied using a backpack sprayer. Na2SO4 applications were discontinued after the 1998 growing season. The hardwood and pine stands each contain four plots, with application rates as follows: Control, Low = 5gN/m^2 per year, High = 15gN/m^2 per year, N+S = 5gN/m^2 + 7.4gS/m^2 per year. Plot designations are P or H followed by C,L,H,NS for control, low, high N+S, respectively. Upon request, more detailed information is available on the exact applications rates based on fertilizer sample analysis.
Species Codes
ACPE = striped maple (Acer pensylvanicum L.). ACRU = red maple (Acer rubrum L.). ACSA3 = sugar maple (Acer saccharum Marsh.). BELE = black birch (Betula lenta L.). BEPA = white birch (Betula papyrifera Marsh.). CADE12 = American chestnut (Castanea dentata (Marsh.) Borkh.). FAGR = American beech (Fagus grandifolia Ehrh.). NYSY = black tupelo (Nyssa sylvatica Marsh.). PIAB = Norway spruce (Picea abies (L.) Karst.). PIRE = red pine (Pinus resinosa Aiton). PIRU = red spruce (Picea rubens Sarg.). PIST = white pine (Pinus strobus L.). PRSE2 = black cherry (Prunus serotina Ehrh.). QUAL = white oak (Quercus alba L.). QURU = red oak (Quercus rubra L.). QUVE = black oak (Quercus velutina Lam.). TSCA = Eastern hemlock (Tsuga canadensis (L.) Carr.).
HF008-01: Foliar Chemistry
Fresh leaf samples were collected during the first week of August. Needle samples from 20 different red pines in each pine plot were pooled into 5 samples for analysis. Oak, red maple and black birch were sampled in the hardwood plots. A total of four composite samples per species were collected in each plot, with each sample including leaves from the upper canopy, mid-level and understory. Red oak and black oak were combined and labeled as black oak. Samples were dried, ground and scanned for percent nitrogen, lignin and cellulose using an NIRSystems near infrared spectrometer. In selected years, samples were digested and digestate measured for base cations using either ICP (1999, 2002) or DCP (1997 and earlier). This dataset includes percent nitrogen, lignin and cellulose, means and standard deviations for 1988-1999, 2002 and 2005-8.
Data is described in detail in: Magill, A.H., J.D. Aber, W.S. Currie, K.J. Nadelhoffer, M.E. Martin, W.H. McDowell,
J.M. Melillo, P. Steudler. 2004. Ecosystem response to 15 years of chronic nitrogen additions at the Harvard Forest LTER, Massachusetts, USA. Forest Ecology and Management, 196(1):7-28.
HF008-02: Litter Chemistry
Aboveground litterfall was collected three times per year on or near June 1, September 1 and November 15 from each of nine litter collection baskets per plot (2.345 x 10-4 m2 in size). Litter samples were sorted by species (red and black oak combined), dried for 48 hours at 70 C, weighed and ground using a Wiley mill with a 1 mm mesh screen. Ground samples were dried overnight at 70 C and analyzed for nitrogen, lignin, and cellulose content using near-infrared (NIR) spectroscopy.
Data is described in detail in: Magill, A.H., J.D. Aber, W.S. Currie, K.J. Nadelhoffer, M.E. Martin, W.H. McDowell,
J.M. Melillo, P. Steudler. 2004. Ecosystem response to 15 years of chronic nitrogen additions at the Harvard Forest LTER, Massachusetts, USA. Forest Ecology and Management, 196(1):7-28.
HF008-03: Litterfall Biomass
Total litter mass was measured by collecting annual litterfall in baskets (9 baskets per plot, collected several times per season). Data from some years is available at the species level; data posted here are foliar biomass for all species combined,
scaled to g/m^2 for each plot. Currently posted data may be a slight underestimate, since it is based on the species-level collection, and does not unclude unidentified leaf fragments. Data will be updated to make this correction soon (June 2009). Samples were also ground and scanned for percent nitrogen, lignin and cellulose using an NIRSystems near infrared spectrometer (see HF008-02).
HF008-04: Tree Inventory
All trees above 5cm Diameter Breast Height (DBH) were numbered and measured in 1988. In subsequent years,
trees previously too small were tagged and measured. In this dataset, we report tree-level DBH measurements. Tree data is reported by subplot - numbered [a-f][[1-6], for a total of 36 5x5m subplots per plot. Note that in some years, some subplots were not sampled (HC-F1, PL-F[1-6]). This is important when scaling tree-level DBH to biomass per unit area. Also note that DBH is listed as 0 for trees not yet large enough for the inventory. DBH is also listed as 0 after the death of a tree.
For more information on calculating biomass, with suggested sources of allometry, see: Magill, A. H., Aber, J. D., Hendricks, J. J., Bowden, R. D., Melillo, J. M., Steudler, P. A. 1997. Biogeochemical response of forest ecosystems to simulated
chronic nitrogen deposition. Ecological Applications 7: 402-415.
HF008-05: Tension Lysimeters
In 1988, 5 porous-cup lysimeters were installed in each plot at 60cm depth. Tension of 50psi was drawn for 24 hours prior to collection. Samples were filtered and frozen prior to analysis for NH4 and NO3. Samples were also analyzed for TDN using the TOC-5000 with an Antek chemiluminecent detector. Base cations were measured using either ICP (1998 and later) or DCP (1997 and earlier).
Data is described in detail in: Magill, A. H., Aber, J. D., Hendricks, J. J., Bowden, R. D., Melillo, J. M.,
Steudler, P. A. 1997. Biogeochemical response of forest ecosystems to simulated chronic nitrogen deposition. Ecological Applications 7: 402-415.
HF008-06: Soil CN and Mineralization
Net nitrification and net mieralization were measured using the in-situ buried bag technique. Three sets of paired cors were taken in each of the 3 designated subplots of each plot (total of 9 paired samples per treatment). Initial samples were analyzed immediately, while in-situ samples were incubated for a period of 4-6 weeks during the growing season, in addition to an overwinter incubation (Nov-Apr). Samples were analyzed for extractable NH4 and NO3 concentrations using a 1N KCl extraction.
Details on sampling and analysis can be found at: Aber, J. D., Magill, A., Boone, R. D., Melillo, J. M., Steudler, P. A.,
Bowden, R. D. 1993. Plant and soil responses to three years of chronic nitrogen additions at the Harvard Forest, Petersham, MA. Ecological
Applications 3: 156-166.
HF008-07: Litter Decomposition
Decomposition rates and N dynamics of foliar litter from 4 tree species were measured over a 72 month period on the Chronic Nitrogen Addition plots at the Harvard Forest, beginning in November 1988. Fresh litterfall was collected in the fall of 1988 on
nylon mesh screens which were placed in the experimental stands but outside of the treated plots. Litter was air dried and sorted into red
pine, red maple, yellow birch and black oak and approximately 9.5 to 10.0 g placed into 20x20 cm bags made of 1 mm mesh nylon window
screening. Litter bags containing red pine and red maple foliage were placed in plots of both the hardwood and pine stands, black oak bags
were placed in the hardwood plots only and yellow birch bags in the pine plots only.
One string of bags (12 bags with 4 replicates of 3 species) was collected from each plot in mid-August and mid-November beginning in 1989 and continuing through 1993. In 1994, two strings were pulled up
on each collection date, completing the experiment in November 1994. Mass loss was recorded for individual litterbag samples. Samples were then combined, ground and analyzed for percent nitrogen, lignin, and cellulose using near-infrared spectroscopy.
For more details see: Magill, AH, and JD Aber. 1998. Long-term effects of experimental nitrogen additions on foliar litter decay and humus formation in forest ecosystems. Plant and Soil 203:301-311.
HF008-08: Zero Tension Lysimeters
ZTL's are gravity fed gravel and glass bead filled collection units (0.3 to 1.5cm) located beneath the organic horizon with a tube draining approximately 154 cm2 into a 1 liter bottle. Samples were collected within 1 week following a rain event, weighed, filtered through a 0.7um filter and frozen prior to analysis. N and C were measured in the same manner as tension lysimeters (HF08-05). Base cations were measured using either ICP (1998 and later) or DCP (1997 and earlier).