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Reducing uncertainty in NEE estimates from flux measurements

Reducing uncertainty in NEE estimates from flux measurements. D. Hollinger, L. Mahrt, J. Sun, and G.G. Katul. Ameriflux Meeting, Boulder CO., October 20, 2005. Organizing Framework.

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Reducing uncertainty in NEE estimates from flux measurements

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  1. Reducing uncertainty in NEE estimates from flux measurements D. Hollinger, L. Mahrt, J. Sun, and G.G. Katul Ameriflux Meeting, Boulder CO., October 20, 2005

  2. Organizing Framework • Uncertainty in flux measurements (random and systematic errors) over sampling intervals needed to average out turbulence. • Gap-filling missing data when averaging over extended time scales (relevant to impact of carbon allocation on ecosystem properties). • Linking measured fluxes to biological sources and sinks (main issues – stable flows; topography).

  3. Background All recent reviews concerning measurements and modeling of surface-atmosphere mass, energy, and momentum exchange expressed the need to confront the problem of turbulent flows within plant canopies on non-flat terrain.

  4. Previous Studies Field Studies [Mainly forests, stable flows, mild topography] Aubinet et al. (2003; 2005); Yi et al. (2004); Staebler and Fitzjarrald, (2004); Feigenwinter et al., (2004); Fokken et al., (2005); Laboratory Studies: [steep topography] Finnigan and Brunet (1995)

  5. Results from Recent Field Experiments • CO2 advection study at the Niwot Ridge AmeriFlux site by Yi et al. (2004) suggested that: • Both longitudinal and vertical advective fluxes are important and often larger than the turbulent flux. • They often act in opposite direction

  6. Feigenwinter et al1. (2004) • “The opposite sign of horizontal and vertical advection supports the idea that the two fluxes will cancel out each other in the long-term carbon balance”. • “The mean advective fluxes at night have magnitudes comparable to the daily NEE”. 1Feigenwinter et al., 2004, Boundary-Layer Meteorology.

  7. Aubinet et al1. (2005) • “The advective fluxes strongly influence the nocturnal CO2 balance, with the exception of almost flat and highly homogeneous sites”. • Storage - significant “only during periods of both low turbulence and low advection”. • “All sites where advection occurs show the onset of a boundary layer characterized by a downslope flow, negative vertical velocities and negative vertical CO2 concentration gradients during nighttime”. 1Aubinet et al., 2004, Boundary-Layer Meteorology.

  8. Polytechnic of Turin (IT) Flume Experiments Hill Properties: Four hill modules Hill Height (H) = 0.08 m Hill Half Length (L) = 0.8 m Canopy Properties Canopy Height = 0.1 m Rod diameter = 0.004 m Rod density = 1000 rods/m2 Flow Properties: Water Depth = 0.6 m Bulk Re > 1.5 x 105

  9. Velocity Measurements Sampling Frequency = 300 Hz Sampling Period = 300 s Laser Doppler Anemometer

  10. Coordinate Systems Displaced Coordinates

  11. Mean Velocity (m/s) Turbulent Stress (m2/s2)

  12. Model Formulation: 2-D Mean Flow Fluid Continuity: Produced by the Hill Mean Momentum Equation: Two equations with two unknowns – after appropriate parameterization Canopy Drag

  13. Finnigan and Belcher (2004)Analytical Model Closure for Reynolds Stress Constant mixing length inside canopy: Closure for Linearized Drag: Linearized Adv.:

  14. Mixing Length Model

  15. Linearized Advective Term Deep Inside the Canopy Linearized Drag Force

  16. Mean Momentum Balance Advection Drag Turbulent Stress Pressure Gradient

  17. u SWEEPS w EJECTIONS Ejection-Sweep Cycle

  18. Canopy Surface

  19. Smooth Surface (no canopy)

  20. Advective fluxes are opposite in sign They are often larger than Photosynthesis (Sc)

  21. Conclusions Advective terms are (individually) of the same order of magnitude as photosynthesis, consistent with field experiments to date. Note that the model does not consider atmospheric stability. The effects of advective terms on CO2 fluxes at a particular point can be as large as 100%. Both advective terms must be considered in any flux-correction treatment due to topography.

  22. ~1 km (a): SLICER Data from Duke Forest (c): Eucalyptus vegetation Tumbarumba, AU (b): Tower relief map Tumbarumba, AU

  23. Gap-Filling What new information is being added in the Gap-filling? How much are the distributional and spectral properties altered by gap-filling?

  24. Distributional and Autocorrelation Properties fBm process with Hurst exponent =1/3

  25. Shannon-Entropy Entropy = Information Content (Shannon, 1948) p=Empirical probability density function OR Energy distribution (e.g. from spectral analysis) Maximum Entropy:

  26. Wavelet-Based Spectra Haar wavelet, localized in time domain – can remove gaps from spectral calculations. Schimel & others – use Entropy measures for assessing New information injected by gap-filling.

  27. Duke Forest Ameriflux Sites PP = Pine Plantation OF = Old Field HW = Hardwood Forest

  28. Entropy, Gap filling, ET Probability Spectra

  29. Entropy, Gap filling, Daytime NEE Probability Spectra

  30. Night-time NEE Probability Spectra

  31. If after gap-filling, the Remarks is large (>20%), the ‘long-term’ estimates of NEE are going to be sensitive to gap-filling and are likely to have significant artificial correlation with the gap-filling drivers.

  32. Extra References Katul et al., 2001, Advances in Water Resources , 24, 1119. Katul et al., 2001, Geophysical Research Letters, 28, 3305. Katul et al., 2001, Physics of Fluids, 13, 241. Mahrt et al., 1999, Journal of the Atmospheric Sciences, 48, 472. Wesson et al., 2003, Boundary-Layer Meteorology, 106, 507.

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