Paired‐tower measurements of carbon and energy fluxes following disturbance in the boreal forest

Disturbances by fire and harvesting are thought to regulate the carbon balance of the Canadian boreal forest over scales of several decades. However, there are few direct measurements of carbon fluxes following disturbances to provide data needed to refine mathematical models. The eddy covariance technique was used with paired towers to measure fluxes simultaneously at disturbed and undisturbed sites over periods of about one week during the growing season in 1998 and 1999. Comparisons were conducted at three sites: a 1-y-old burned jackpine stand subjected to an intense crown fire at the International Crown Fire Modelling Experiment site near Fort Providence, North-west Territories; a 1-y-old clearcut aspen area at the EMEND project near Peace River, Alberta; and a 10-y-old burned, mixed forest near Prince Albert National Park, Saskatchewan. Nearby mature forest stands of the same types were also measured as controls. The harvested site had lower net radiation (Rn), sensible (H) and latent (LE) heat fluxes, and greater ground heat fluxes (G) than the mature forest. Daytime CO2 fluxes were much reduced, but night-time CO2 fluxes were identical to that of the mature aspen forest. It is hypothesized that the aspen roots remained alive following harvesting, and dominated soil respiration. The overall effect was that the harvested site was a carbon source of about 1.6 gC m ‐2 day ‐1 , while the mature site was a sink of about ‐3.8 gC m ‐2 day ‐1 . The one-year-old burn had lower Rn, H and LE than the mature jackpine forest, and had a continuous CO2 efflux of about 0.8 gC m ‐2 day ‐1 compared to the mature forest sink of ‐ 0.5 g C m ‐2 day ‐1 . The carbon source was likely caused by decomposition of fire-killed vegetation. The 10-y-old burned site had similar H, LE, and G to the mature mixed forest site. Although the diurnal amplitude of the CO2 fluxes were slightly lower at the 10-y-old site, there was no significant difference between the daily integrals (‐ 1.3 gC m ‐2 day ‐1 at both sites). It appears that most of the change in carbon flux occurs within the first 10 years following disturbance, but more data are needed on other forest and disturbance types for the first 20 years following the disturbance event.

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

[2]  A. Arneth,et al.  Forest–atmosphere carbon dioxide exchange in eastern Siberia , 1998 .

[3]  E. Kasischke,et al.  Fire, Global Warming, and the Carbon Balance of Boreal Forests , 1995 .

[4]  S. Wofsy,et al.  Physiological responses of a black spruce forest to weather , 1997 .

[5]  David Y. Hollinger,et al.  Carbon dioxide exchange between an undisturbed old-growth temperate forest and the atmosphere , 1994 .

[6]  A. Arneth,et al.  Carbon dioxide efflux density from the floor of a central Siberian pine forest , 1999 .

[7]  M. Harmon,et al.  Ecology of Coarse Woody Debris in Temperate Ecosystems , 1986 .

[8]  T. B. Carter,et al.  Forest wildfires as a recent source of CO2 at northern latitudes , 1993 .

[9]  Werner A. Kurz,et al.  Carbon budget of the Canadian forest product sector , 1999 .

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

[11]  M. Weber Forest soil respiration in eastern Ontario jack pine ecosystems , 1985 .

[12]  Christopher B. Field,et al.  The Terrestrial Carbon Cycle: Implications for the Kyoto Protocol , 1998, Science.

[13]  Inez Y. Fung,et al.  Boreal forests and atmosphere–biosphere exchange of carbon dioxide , 1987, Nature.

[14]  K. M. King,et al.  Comparison of eddy-covariance measurements of CO2 fluxes by open- and closed-path CO2 analysers , 1992 .

[15]  D. Baldocchi,et al.  The carbon balance of tropical, temperate and boreal forests , 1999 .

[16]  P. Mcgee,et al.  Simulated fire reduces the density of arbuscular mycorrhizal fungi at the soil surface , 1999 .

[17]  Gordon B. Bonan,et al.  Atmosphere-biosphere exchange of carbon dioxide in boreal forests , 1991 .

[18]  R. K. Dixon,et al.  Carbon Pools and Flux of Global Forest Ecosystems , 1994, Science.

[19]  Dennis D. Baldocchi,et al.  Seasonal variation of energy and water vapor exchange rates above and below a boreal jack pine forest canopy , 1997 .

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

[21]  R. Striegl,et al.  Effects of a clear-cut harvest on soil respiration in a jack pine - lichen woodland , 1998 .

[22]  M. G. Ryan,et al.  Magnitudes and seasonal patterns of energy, water, and carbon exchanges at a boreal young jack pine forest in the BOREAS northern study area , 1997 .

[23]  R. Voroney,et al.  Carbon dioxide efflux from the floor of a boreal aspen forest. I. Relationship to environmental variables and estimates of C respired , 1998 .

[24]  Reply to comment by Finnigan on “On micrometeorological observations of surface-air exchange over tall vegetation” , 1999 .

[25]  T. W. Horst,et al.  Footprint estimation for scalar flux measurements in the atmospheric surface layer , 1992 .

[26]  T. A. Black,et al.  Effects of climatic variability on the annual carbon sequestration by a boreal aspen forest , 1999 .

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

[28]  B. Amiro,et al.  Comparison of turbulence statistics within three boreal forest canopies , 1990 .

[29]  B. Amiro Footprint climatologies for evapotranspiration in a boreal catchment , 1998 .

[30]  H. Fritze,et al.  Microbial biomass and activity in the humus layer following burning : short-term effects of two different fires , 1993 .

[31]  D. Baldocchi,et al.  Energy and CO(2) flux densities above and below a temperate broad-leaved forest and a boreal pine forest. , 1996, Tree physiology.

[32]  Jing Chen,et al.  Net primary productivity following forest fire for Canadian ecoregions , 2000 .

[33]  M. Weber Forest soil respiration after cutting and burning in immature aspen ecosystems , 1990 .

[34]  R. K. Dixon,et al.  Forest fires in Russia: carbon dioxide emissions to the atmosphere , 1993 .

[35]  B. Stocks,et al.  Some potential carbon budget implications of fire management in the boreal forest , 1996 .

[36]  B. Stocks,et al.  Biomass Consumption and Behavior of Wildland Fires in Boreal, Temperate, and Tropical Ecosystems: Parameters Necessary to Interpret Historic Fire Regimes and Future Fire Scenarios , 1997 .

[37]  B. Amiro BOREAS flight measurements of forest-fire effects on carbon dioxide and energy fluxes , 1999 .

[38]  M. Flannigan,et al.  Future wildfire in circumboreal forests in relation to global warming , 1998 .

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

[40]  D. Middleton,et al.  Analysis of small-scale convective dynamics in a crown fire using infrared video camera imagery , 1999 .

[41]  F. Chapin,et al.  A Comparative Approach to Regional Variation in Surface Fluxes Using Mobile Eddy Correlation Towers , 1997 .

[42]  S. T. Gower,et al.  Environmental variables regulating soil carbon dioxide efflux following clear-cutting of a Pinus radiata D. Don plantation , 1998 .

[43]  S. Wofsy,et al.  Controls on Evaporation in a Boreal Spruce Forest. , 1999 .

[44]  Werner A. Kurz,et al.  A 70-YEAR RETROSPECTIVE ANALYSIS OF CARBON FLUXES IN THE CANADIAN FOREST SECTOR , 1999 .

[45]  C. Ahlgren,et al.  Effects of Prescribed Burning on Soil Microorganisms in a Minnesota Jack Pine Forest , 1965 .

[46]  Corinna Rebmann,et al.  Productivity of forests in the Eurosiberian boreal region and their potential to act as a carbon sink –‐ a synthesis , 1999 .

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

[48]  B. Stocks,et al.  Effect of fire on soil‐atmosphere exchange of methane and carbon dioxide in Canadian boreal forest sites , 1997 .

[49]  J. Mccaughey,et al.  Energy balance storage terms in a mixed forest , 1988 .

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

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

[52]  B. Stocks,et al.  Forest Fires and Sustainability in the Boreal Forests of Canada. , 1998 .

[53]  C. B. Tanner,et al.  Sensible heat flux measurements with a yaw sphere and thermometer , 1970 .

[54]  John Moncrieff,et al.  Seasonal variation of carbon dioxide, water vapor, and energy exchanges of a boreal black spruce forest , 1997 .

[55]  M. G. Ryan,et al.  Comparing nocturnal eddy covariance measurements to estimates of ecosystem respiration made by scaling chamber measurements at six coniferous boreal sites , 1997 .