Source: UNIVERSITY OF NEW HAMPSHIRE submitted to NRP
CONTROLS ON FOREST SOIL SOLUTION CHEMISTRY
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
0198140
Grant No.
(N/A)
Cumulative Award Amt.
(N/A)
Proposal No.
(N/A)
Multistate No.
(N/A)
Project Start Date
Oct 1, 2003
Project End Date
Sep 30, 2006
Grant Year
(N/A)
Program Code
[(N/A)]- (N/A)
Recipient Organization
UNIVERSITY OF NEW HAMPSHIRE
51 COLLEGE RD SERVICE BLDG 107
DURHAM,NH 03824
Performing Department
NATURAL RESOURCES
Non Technical Summary
Forest soil solution chemistry is an indicator of overall ecosystem function and a driver of stream water quality in forested watersheds. This project examines the effects of experimental manipulations of nitrogen and organic matter inputs on the nitrogen and organic matter found dissolved in soil solution.
Animal Health Component
(N/A)
Research Effort Categories
Basic
100%
Applied
(N/A)
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
10201991070100%
Knowledge Area
102 - Soil, Plant, Water, Nutrient Relationships;

Subject Of Investigation
0199 - Soil and land, general;

Field Of Science
1070 - Ecology;
Goals / Objectives
1. Determine the long-term effects of organic matter supply on concentrations of dissolved organic C and N (DOC and DON) in soil solution. 2. Determine the long-term effects of inorganic N addition on DOC and DON in soil solution of temperate and tropical forests
Project Methods
Objective 1. Soil solution from the Harvard Forest DIRT plots will be sampled on an event basis at least 12 times during the growing season (April to November) and analyzed for dissoled organic carbon, dissolved organic nitrogen, nitrate, and ammonium. Statistical analysis will be with repeated-measures ANOVA. The organic matter manipulation represents the treatment (5 treatment categories and a control), and repeated measures of soil solution organic chemistry are taken over time. If the ANOVA shows significant treatment effects, Duncan's multiple range test will be used to compare the magnitude of responses to different treatments. In addition to a statistical comparison of concentrations, fluxes will be estimated for each treatment using PNET to develop a hydrologic budget for the plots. Objective 2. Soil solution from both the Harvard Forest Chronic N and Luquillo Chronic N plots will be sampled on an event basis at least 12 times during the growing season (April to November for Harvard Forest; year-round for Luquillo). Chemistry and statistical analysis will be as described for Objective 1. Timetable and Frequency of Sampling: Samples will be collected every third year for each experiment, with a staggered schedule. Thus, soil solution from one of the experiments will be collected during each year. The Harvard Forest chronic N plots will be sampled the first year, followed by the Harvard Forest DIRT plots and the Luquillo chronic N plots. Methods of Chemical analysis: Samples of soil solution will be filtered within 4 hours of collection with a pre-combusted Whatman GF/F glass fiber filter (nominal pore size 0.7 micron), and frozen prior to analysis. Dissolved organic carbon will be measured using automated high temperature platinum-catalyzed combustion (Shimadzu TOC analyzer with autosampler). Total dissolved N will be measured using high temperature platinum-catalyzed combustion followed by chemiluminescent analysis of total NO in the combustion gas (Shimadzu TOC and TDN analyzer). Nitrate and ammonium will be analyzed using standard colorimetric techniques. Dissolved organic N will be estimated as the difference between total N and the inorganic fraction.

Progress 10/01/03 to 09/30/06

Outputs
The effects of organic matter and nutrient supply on the solution chemistry of forest soils were determined by sampling soil solution from lysimeters at three long-term experimental manipulations. At the Harvard Forest (HF), soil solution was sampled at the DIRT plots and the chronic N plots; in the Luquillo Experimental Forest (LEF), soil solution was sampled at the chronic N plots. The DIRT plots at HF involve manipulations of soil organic matter inputs, including 2 times litter input, no litter input, no OA horizon, trenched (no root input), trenched/no litter, and control. The chronic N plots at HF have additions of 50 and 150 kg N per ha per year; at the LEF, two different forest sites are fertilized with 50 kg N per ha per year. Results pooled across all the sites and experiments show that production of dissolved organic carbon (DOC) is remarkably insensitive to N additions and the changes in ecosystem structure (primary productivity, soil microflora) that accompany N fertilization. Nor is DOC production strongly related to organic matter supply; only litter doubling significantly affects DOC concentrations. Dissolved organic nitrogen (DON), in contrast, is very sensitive to inorganic N application, with concentrations doubling or tripling with fertilization. This suggests a fundamental decoupling of the C and N cycles with changes in N inputs, as production of DOC and DON appear to be regulated by different mechanisms.

Impacts
Dissolved organic carbon (DOC), an important contaminant in water supplies, changes its character but not its overall concentration when forests are amended with nitrogen. In contrast, concentrations of DOC increase when organic matter is added to forest soils, such as with increased leaf litter inputs. Better understanding of how forest nutrient cycles affect the DOC in groundwater will improve forest management, and result in better predictions of the impacts that changing forest conditions will have on water quality.

Publications

  • McDowell, W.H., A. Zsolnay, J. A. Aitkenhead-Peterson, E.G. Gregorich, D. L. Jones, D. Jodemann, K. Kalbitz, B. Marschner, and D. Schwesig. 2006. A comparison of methods to determine the biodegradable dissolved organic carbon from different terrestrial sources. Soil Biology and Biochemistry 38:1933-1942.


Progress 10/01/04 to 09/30/05

Outputs
The effects of organic matter and nutrient supply on the solution chemistry of forest soils were determined by sampling soil solution from lysimeters at three long-term experimental manipulations. At the Harvard Forest (HF), soil solution was sampled at the DIRT plots and the chronic N plots; in the Luquillo Experimental Forest (LEF), soil solution was sampled at the chronic N plots. The DIRT plots at HF involve manipulations of soil organic matter inputs, including 2 times litter input, no litter input, no OA horizon, trenched (no root input), trenched/no litter, and control. The chronic N plots at HF have additions of 50 and 150 kg N per ha per year; at the LEF, two different forest sites are fertilized with 50 kg N per ha per year. Results pooled across all the sites and experiments show that production of dissolved organic carbon (DOC) is remarkably insensitive to N additions and the changes in ecosystem structure (primary productivity, soil microflora) that accompany N fertilization. Nor is DOC production strongly related to organic matter supply; only litter doubling significantly affects DOC concentrations. Dissolved organic nitrogen (DON), in contrast, is very sensitive to inorganic N application, with concentrations doubling or tripling with fertilization. This suggests a fundamental decoupling of the C and N cycles with changes in N inputs, as production of DOC and DON appear to be regulated by different mechanisms.

Impacts
This project provides fundamental information about controls on soil solution chemistry in forest ecosystems, with an emphasis on factors controlling the production and delivery of dissolved organic carbon and nitrogen (DOC and DON) to surface waters. DOC and DON are important in aquatic nutrient cycles and as contaminants in drinking water supplies. Better understanding of forest nutrient cycles will improve forest management and facilitate predictions of changes in forests with changing climate.

Publications

  • Macy, Jordan. 2005. Initial effects of N additions in two rain forest ecosystems of Puerto Rico. M.S. thesis, University of New Hampshire, Durham, 66 pps.


Progress 10/01/03 to 09/30/04

Outputs
The effects of organic matter and nutrient supply on the solution chemistry of forest soils were determined by sampling soil solution from lysimeters at three long-term experimental manipulations. At the Harvard Forest (HF), soil solution was sampled at the DIRT plots and the chronic N plots; in the Luquillo Experimental Forest (LEF), soil solution was sampled at the chronic N plots. The DIRT plots at HF involve manipulations of soil organic matter inputs, including 2 times litter input, no litter input, no OA horizon, trenched (no root input), trenched/no litter, and control. The chronic N plots at HF have additions of 50 and 150 kg N per ha per year; at the LEF, two different forest sites are fertilized with 50 kg N per ha per year. Results pooled across all the sites and experiments show that production of dissolved organic carbon (DOC) is remarkably insensitive to N additions and the changes in ecosystem structure (primary productivity, soil microflora) that accompany N fertilization. Nor is DOC production strongly related to organic matter supply; only litter doubling significantly affects DOC concentrations. Dissolved organic nitrogen (DON), in contrast, is very sensitive to inorganic N application, with concentrations doubling or tripling with fertilization. This suggests a fundamental decoupling of the C and N cycles with changes in N inputs, as production of DOC and DON appear to be regulated by different mechanisms.

Impacts
This project provides fundamental information about controls on soil solution chemistry in forest ecosystems, with an emphasis on factors controlling the production and delivery of dissolved organic carbon and nitrogen (DOC and DON) to surface waters. DOC and DON are important in aquatic nutrient cycles and as contaminants in drinking water supplies. Better understanding of forest nutrient cycles will improve forest management and facilitate predictions of changes in forests with changing climate.

Publications

  • Aitkenhead-Peterson J.A., W.H. McDowell and J.C. Neff. 2003. Sources, production and regulation of allochthonous dissolved organic matter In S.E.G. Findlay and R.L. Sinsabaugh (Eds). Aquatic Ecosystems: Interactivity of Dissolved Organic matter. Academic Press, San Diego.
  • McDowell, W.H. 2003. Dissolved organic matter in soils-future directions and unanswered questions. Geoderma 113:179-186.
  • Nadelhoffer, K., R. Boone, R. Bowden, J. Canary, J. Kaye, P. Micks, A. Ricca, W. McDowell, and J. Aitkenhead. 2004. The DIRT experiment: litter and root influences on forest soil organic matter stocks and function. pp. 300-315 In: D. Foster and J. Aber (eds.), Forests in Time: The environmental consequences of 1,000 years of change in New England. Yale University Press.
  • Aber, J., A. Magill, K. Nadelhoffer, J. Melillo, P. Steudler, P. Micks, J. Hendricks, R. Bowden, W. Currie, W. McDowell, and G. Berntson. 2004. Exploring the process of nitrogen saturation. pp. 259-279 In: D. Foster and J. Aber (eds.), Forests in Time: The environmental consequences of 1,000 years of change in New England. Yale University Press.
  • McDowell, W.H., A.H. Magill, J. A. Aitkenhead-Peterson, J.D. Aber, J.L. Merriam, S.S. Kaushal. 2004. Effects of chronic nitrogen amendment on dissolved organic matter and inorganic nitrogen in soil solution. Forest Ecology and Management 196:29-41.
  • Magill, A.H., J.D. Aber, W.S. Currie, K.J. Nadelhoffer, M.E. Martin, W.H. McDowell, J.M. Mellillo, and P. Steudler. 2004. Ecosystem response to 15 years of chronic nitrogen additions at the Harvard Forest LTER, Massachusetts, USA. Forest Ecology and Management 196:7-28.