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Evaluation and Improvement of Model Algorithms for Predicting Belowground Carbon Allocation in Forests. Kathryn A. Berger Master of Science, Candidate Dept. of Natural Resources University of New Hampshire. Research & Discover Student Presentations August 2008.
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Evaluation and Improvement of Model Algorithms for Predicting Belowground Carbon Allocation in Forests Kathryn A. Berger Master of Science, Candidate Dept. of Natural Resources University of New Hampshire Research & Discover Student Presentations August 2008
Total Belowground Carbon Allocation • Forests allocate C belowground to: • Roots, root respiration, exudates & mycorrhizae • Termed Total Belowground Carbon Allocation (TBCA) • Why study TBCA? • A large component of global C cycle • Considerable potential for future C sequestration • Connects belowground soil processes to forest canopy • The mechanism is still poorly understood • Difficulty in directly measuring TBCA restricts our understanding of belowground C cycling • Ecosystem models have proven useful to study effects of forest response to global climate change, but TBCA measurement challenges limit model development and simulation
The PnET-CN Model PnET-CN: Daily-to-monthly time step model of C, N, and H2O forest ecosystem fluxes Relies on relatively few input parameters Minimal reliance on calibration Carbon allocation: Central Plant C pool allocates to: foliage, wood, and fine root pools Fine roots predicted using Raich and Nadelhoffer (1989) mass-balance approach for estimation of TBCA (Aber et al. 1997)
Raich and Nadelhoffer (1989) Approach Fine Root Carbon (g C) = 130 + 1.92 * Leaf Carbon (g C) PnET-CN model: RootAllocA: Intercept of relationship between foliar and root allocation RootAllocB: Slope of relationship between foliar and root allocation RootCAdd = RootAllocA * (DaySpan / 365) + RootAllocB * FolProdCMo RootAllocB RootAllocA (Raich and Nadelhoffer 1989)
Objectives • To evaluate the performance of the current PnET-CN model in predicting TBCA under e[CO2] • If necessary, develop a more realistic simulation to capture TBCA dynamics
Methods • Validation performed using data from 3 U.S. Free-Air CO2 Enrichment (FACE) experimental forests • FACE site objectives: • Quantify CO2 effect on NPP in a manner that will inform ecosystem and global models • Three U.S. forest FACE experiments • Stand treatment plots exposed to ~550 ppm CO2 for 3 to 8 years • NPP from all plots and years post closed canopy
FACE Site Results Duke FACE ORNL FACE wood CO2 on fine root (Norby 2005)
PnET-CN Model Simulation • Model simulation of FACE experiments • Single-step increase in CO2 • Disturbance history as identified by each site • Site-specific vegetation parameters • Site-specific climate records
PnET-CN Simulations:Elevated CO2 Initial evaluation of the PnET-CN model found: NPP (g C m-2 y-1) is predicted by the PnET-CN model into 3 biomass pools: foliage, wood & fine roots Under elevated CO2 additional C is allocated predominantly to wood Experimental evidence suggests otherwise... Example: Aspen FACE, Rhinelander, WI
Development of Modified TBCA Mechanism • “The use of constant partitioning coefficients in static models is unlikely to provide a realistic picture of carbon cycling.” (Litton et al. 2007) • Resource availability always caused shifts in C partitioning between TBCA and Wood C pools • Fertilization increased partitioning to wood and decreased partitioning TBCA for all forests • Based on concept that variability around the Raich and Nadelhoffer (1989) relationship is due to availability of belowground nutrients (N) suggested by: • Functional Carbon Allocation Theory (Root:Shoot Ratio) • Haynes and Gower 1995; Gower et al. 1996; Nadelhoffer et al. 1998; Giardina and Ryan 2002; Palmroth et al. 2006; Franklin 2007
Functional Equilibrium Models Hi CO2 Carbon is allocated to the shoot when C supply is reduced Plant shifts C allocation to roots when water or nutrient supply (predominantly N) is reduced C allocation shifts in such a way that relative growth rate is maximized. (Thornley and Johnson 1990) High Nutrients High Nitrogen (Adapted from: http://ecology.botany.ufl.edu/ecologyf02/homeostasis.html)
Modified TBCA mechanism Dataset: Mature forests ≥ 45 years old (Raich and Nadelhoffer et al. 1989; Davidson et al. 2002) Y-intercept of zero 95% confidence interval Upper slope 3.2 Lower slope 2 R&N (1989)derived slope= 2.59 r2 = 0.3449
Development of Modified TBCA Mechanism • Introduction of internal PnET-CN variable: NStatus • NStatus a function of internal model variable (NRatio) and input parameter (FolNConRange) • Removal of static TBCA mechanism • No longer dependent on RootAllocA and RootAllocB input parameters • Result: A fluctuating TBCA mechanism based upon N availability
Results FACE Site validation Application of the Modified model to future climate scenarios
PnET-CN NStatus : UnderElevated CO2 Predicted PnET- CN NPP (g C m2 y-1) versus published FACE site values under elevated CO2 conditions for each of the three simulated biomass pools: foliage, wood and fine roots
PnET-CN NStatus : UnderElevated CO2 Largest increase in % fine root stimulation at ORNL FACE Enhanced model nearly doubles fine root estimates
Application of the Modified TBCA Mechanism • Model simulations at 5 northeastern forests under a variety of projected climate scenarios (originally performed by Ollinger et al. 2008) • Climate projections for 1990-2099 using the PCM (Parallel Climate Model) and HadCM3 (Hadley Centre Coupled Model version 3) models • Generated using CO2 (and other greenhouse gas emissions) scenarios: higher [A1] and lower [B1] projections • Greatest warming: HADA1 projections 6.3°C warming • Least warming: PCMB1 projections 1.5°C warming
PnET Predictions of Total NPP PCMA1 NPP (g C m-2 y-1) at Howland Forest , ME under Parallel Climate Model (PCM) future climate scenarios Total NPP estimates between models are very similar PCMB1
PnET Predictions of ANPP NPP (g C m-2 y-1) at Howland Forest , ME under Parallel Climate Model (PCM) future climate scenarios Estimates of ANPP decrease with PnET-CN: NStatus model
PnET Predictions of BNPP NPP (g C m-2 y-1) at Howland Forest , ME under Parallel Climate Model (PCM) future climate scenarios Estimates of BNPP increase with PnET-CN: NStatus model
Effect on C Storage • How does the modified TBCA mechanism influence estimates of net ecosystem production (NEP)? • NEP = NPP – Rh • Difference between NPP and heterotrophic respiration (Rh) • Determines the amount of carbon lost or gained by an ecosystem • PnET-CN output can also be used to produce predictions of future NEP • Does increased allocation to fine roots (with faster turnover times) result in decreased carbon storage in the future?
Results • Modified TBCA mechanism suggests increased NEP over long-term (1990-2099) • Additional C allocated to fine roots resulted in more long-term C storage than wood C pool
Discussion • Increased carbon flow belowground has increased intensity of roots foraging for soil nutrients • C allocation shift of fine root and mycorrhizal fungi into deeper soils may allow forests to acquire additional N to offset increased nutrient limitations (Pritchard et al. 2008) • Root foraging concept provides evidence to indicate e[CO2] will stimulate productivity (and carbon storage) in N-limited ecosystems more than previously expected • Unlikely that that ecosystem productivity will be stimulated by e[CO2] fertilization indefinitely
Acknowledgments • Special thanks to: • My committee: Scott Ollinger, Mary Martin, Andrew Richardson, & Christy Goodale • UNH-NASA Research and Discover Fellowship • Rita Freuder and Julian Jenkins • My colleagues in Rm 251 • And most importantly my friends and family for their support • Thanks very much for listening, any questions?