Ecosystem‐atmosphere exchange of carbon dioxide over a mixed hardwood forest in northern lower Michigan

[1] We report results from the first 3 years (1999–2001) of long-term measurements of net ecosystem exchange (NEE) at an AmeriFlux site over a mixed hardwood forest in northern lower Michigan. The primary measurement methodology uses eddy covariance systems with closed-path infrared gas analyzers at two heights (46 and 34 m) above the forest (canopy height is ∼22 m). One objective is to contribute to a more firmly established methodology of estimating annual net ecosystem production (NEP), by systematically examining the consequences of several variations of criteria to identify periods of unreliable measurements, and to fill gaps in the data. We compared two methods to fill data gaps (about 30% of time in 1999) due to missing observations or rejected data after quality control; one using short-term ensemble averages of the daily course and the other by semiempirical parametric models based on relationships between ecosystem respiration and soil temperature and between gross ecosystem photosynthetic uptake and photosynthetically active radiation. The modeled estimates were also used to replace eddy covariance fluxes during periods of weak and/or poorly developed turbulence when eddy covariance measurements cannot be expected to represent the ecosystem exchange. Examination of the fractions of eddy covariance fluxes and storage change relative to the expected ecosystem respiration suggested a friction velocity (u*) of 0.35 m s−1 as the lower limit for the acceptance of micrometeorologically determined NEE for this site. The differences in estimated annual NEP due to different criteria of data acceptance, measurement height, or gap-filling strategies turned out to be at least as large as the interannual variations over the 3 years. After discussing various analysis strategies we conclude that the best estimate of annual NEP at our site is achieved by replacing data gaps and measurements in low-u* conditions at all times with site and period-specific parametric models, using the upper measurement level (about 2.1 canopy heights). These “best estimates” of annual NEP for 1999–2001 amounted to 170 (1999), 160 (2000), and 80 (2001) g C m−2. We also discuss some problems of assigning quantitative estimates of uncertainty for annual NEP.

[1]  H. Schmid,et al.  Spectral Characteristics and Correction of Long-Term Eddy-Covariance Measurements Over Two Mixed Hardwood Forests in Non-Flat Terrain , 2004 .

[2]  M. Villani,et al.  Turbulence Statistics Measurements in a Northern Hardwood Forest , 2003 .

[3]  W. Oechel,et al.  Energy balance closure at FLUXNET sites , 2002 .

[4]  Hans Peter Schmid,et al.  Biometric and eddy-covariance based estimates of annual carbon storage in five eastern North American deciduous forests , 2002 .

[5]  K. E. Moore,et al.  Importance of Low-Frequency Contributions to Eddy Fluxes Observed over Rough Surfaces , 2001 .

[6]  B. Lamb,et al.  Measurement of isoprene fluxes at the PROPHET site , 2001 .

[7]  P. Shepson,et al.  Overview of the program for research on oxidants: PHotochemistry, emissions, and transport (PROPHET) summer 1998 measurements intensive , 2001 .

[8]  Ü. Rannik,et al.  Gap filling strategies for defensible annual sums of net ecosystem exchange , 2001 .

[9]  Andrew E. Suyker,et al.  Gap filling strategies for long term energy flux data sets , 2001 .

[10]  T. Meyers,et al.  Correction Of Eddy-Covariance Measurements Incorporating Both Advective Effects And Density Fluxes , 2000, Boundary-Layer Meteorology.

[11]  W. Massman A simple method for estimating frequency response corrections for eddy covariance systems , 2000 .

[12]  F. Cropley Spectral dependence of the correction for path-smoothing by 3-D anemometers , 2000 .

[13]  Dennis Baldocchi,et al.  On Measuring Net Ecosystem Carbon Exchange Over Tall Vegetation on Complex Terrain , 2000, Boundary-Layer Meteorology.

[14]  Hans Peter Schmid,et al.  Measurements of CO2 and energy fluxes over a mixed hardwood forest in the mid-western United States , 2000 .

[15]  J. Finnigan,et al.  A comment on the paper by Lee (1998): “On micrometeorological observations of surface-air exchange over tall vegetation” , 1999 .

[16]  Hans Peter Schmid,et al.  Spatial representativeness and the location bias of flux footprints over inhomogeneous areas , 1999 .

[17]  Xuhui Lee,et al.  On micrometeorological observations of surface-air exchange over tall vegetation , 1998 .

[18]  E. Davidson,et al.  Soil water content and temperature as independent or confounded factors controlling soil respiration in a temperate mixed hardwood forest , 1998 .

[19]  Hans Peter Schmid,et al.  Experimental design for flux measurements: matching scales of observations and fluxes , 1997 .

[20]  Dean Vickers,et al.  Quality Control and Flux Sampling Problems for Tower and Aircraft Data , 1997 .

[21]  T. W. Horst,et al.  A SIMPLE FORMULA FOR ATTENUATION OF EDDY FLUXES MEASURED WITH FIRST-ORDER-RESPONSE SCALAR SENSORS , 1997 .

[22]  J. William Munger,et al.  Measurements of carbon sequestration by long‐term eddy covariance: methods and a critical evaluation of accuracy , 1996 .

[23]  Ray Leuning,et al.  The relative merits of open‐ and closed‐path analysers for measurement of eddy fluxes , 1996 .

[24]  Peter D. Blanken,et al.  Annual cycles of water vapour and carbon dioxide fluxes in and above a boreal aspen forest , 1996 .

[25]  John Moncrieff,et al.  The propagation of errors in long‐term measurements of land‐atmosphere fluxes of carbon and water , 1996 .

[26]  Giorgio Matteucci,et al.  Seasonal net carbon dioxide exchange of a beech forest with the atmosphere , 1996 .

[27]  Walter Senn,et al.  A cospectral correction model for measurement of turbulent NO2 flux , 1995 .

[28]  C. N. Hewitt,et al.  A global model of natural volatile organic compound emissions , 1995 .

[29]  D. Paslier,et al.  Net Exchange of CO2 in a Mid-Latitude Forest , 1993, Science.

[30]  J. Højstrup A statistical data screening procedure , 1993 .

[31]  X. J. Zhang,et al.  Evidence of pressure-forced turbulent flow in a forest , 1992 .

[32]  D. Jacob,et al.  Atmosphere‐biosphere exchange of CO2 and O3 in the central Amazon Forest , 1990 .

[33]  C. J. Moore Frequency response corrections for eddy correlation systems , 1986 .

[34]  D. M. Gates Plants and Microclimate: A Quantitative Approach to Environmental Plant Physiology.Hamlyn G. Jones , 1984 .

[35]  C. Richardson,et al.  Biomass and net annual primary production regressions for Populus grandidentata on three sites in northern lower Michigan. , 1980 .

[36]  J. S. Hunter,et al.  Statistics for experimenters : an introduction to design, data analysis, and model building , 1979 .

[37]  J. Kaimal,et al.  Spectral Characteristics of Surface-Layer Turbulence , 1972 .

[38]  Hans Peter Schmid,et al.  Measurements of CO 2 and energy fluxes over a mixed hardwood forest in the mid-western United States , 2000 .

[39]  D. Perala,et al.  Allometric biomass estimators for aspen-dominated ecosystems in the upper Great Lakes. Forest Service research paper , 1993 .

[40]  A. W. Cooper,et al.  Above-Ground Biomass Accumulation and Net Primary Production During the First 70 Years of Succession in Populus grandidentata Stands on Poor Sites in Northern Lower Michigan , 1981 .

[41]  E. K. Webb,et al.  Correction of flux measurements for density effects due to heat and water vapour transfer , 1980 .