436
Views
1
Downloads
9
Crossref
N/A
WoS
9
Scopus
0
CSCD
The global network of eddy-covariance (EC) flux-towers has improved the understanding of the terrestrial carbon (C) cycle, however, the network has a relatively limited spatial extent compared to forest inventory data and plots. Developing methods to use inventory-based and EC flux measurements together with modeling approaches is necessary evaluate forest C dynamics across broad spatial extents.
Changes in C stock change (ΔC) were computed based on repeated measurements of forest inventory plots and compared with separate measurements of cumulative net ecosystem productivity (ΣNEP) over four years (2003 – 2006) for Douglas-fir (Pseudotsuga menziesii var menziesii) dominated regeneration (HDF00), juvenile (HDF88 and HDF90) and near-rotation (DF49) aged stands (6, 18, 20, 57 years old in 2006, respectively) in coastal British Columbia. ΔC was determined from forest inventory plot data alone, and in a hybrid approach using inventory data along with litter fall data and published decay equations to determine the change in detrital pools. These ΔC-based estimates were then compared with ΣNEP measured at an eddy-covariance flux-tower (EC-flux) and modelled by the Carbon Budget Model - Canadian Forest Sector (CBM-CFS3) using historic forest inventory and forest disturbance data. Footprint analysis was used with remote sensing, soils and topography data to evaluate how well the inventory plots represented the range of stand conditions within the area of the flux-tower footprint and to spatially scale the plot data to the area of the EC-flux and model based estimates.
The closest convergence among methods was for the juvenile stands while the largest divergences were for the regenerating clearcut, followed by the near-rotation stand. At the regenerating clearcut, footprint weighting of CBM-CFS3 ΣNEP increased convergence with EC flux ΣNEP, but not for ΔC. While spatial scaling and footprint weighting did not increase convergence for ΔC, they did provide confidence that the sample plots represented site conditions as measured by the EC tower.
Methods to use inventory and EC flux measurements together with modeling approaches are necessary to understand forest C dynamics across broad spatial extents. Each approach has advantages and limitations that need to be considered for investigations at varying spatial and temporal scales.
The global network of eddy-covariance (EC) flux-towers has improved the understanding of the terrestrial carbon (C) cycle, however, the network has a relatively limited spatial extent compared to forest inventory data and plots. Developing methods to use inventory-based and EC flux measurements together with modeling approaches is necessary evaluate forest C dynamics across broad spatial extents.
Changes in C stock change (ΔC) were computed based on repeated measurements of forest inventory plots and compared with separate measurements of cumulative net ecosystem productivity (ΣNEP) over four years (2003 – 2006) for Douglas-fir (Pseudotsuga menziesii var menziesii) dominated regeneration (HDF00), juvenile (HDF88 and HDF90) and near-rotation (DF49) aged stands (6, 18, 20, 57 years old in 2006, respectively) in coastal British Columbia. ΔC was determined from forest inventory plot data alone, and in a hybrid approach using inventory data along with litter fall data and published decay equations to determine the change in detrital pools. These ΔC-based estimates were then compared with ΣNEP measured at an eddy-covariance flux-tower (EC-flux) and modelled by the Carbon Budget Model - Canadian Forest Sector (CBM-CFS3) using historic forest inventory and forest disturbance data. Footprint analysis was used with remote sensing, soils and topography data to evaluate how well the inventory plots represented the range of stand conditions within the area of the flux-tower footprint and to spatially scale the plot data to the area of the EC-flux and model based estimates.
The closest convergence among methods was for the juvenile stands while the largest divergences were for the regenerating clearcut, followed by the near-rotation stand. At the regenerating clearcut, footprint weighting of CBM-CFS3 ΣNEP increased convergence with EC flux ΣNEP, but not for ΔC. While spatial scaling and footprint weighting did not increase convergence for ΔC, they did provide confidence that the sample plots represented site conditions as measured by the EC tower.
Methods to use inventory and EC flux measurements together with modeling approaches are necessary to understand forest C dynamics across broad spatial extents. Each approach has advantages and limitations that need to be considered for investigations at varying spatial and temporal scales.
Babst F, Bouriaud O, Papale D, Gielen B, Janssens I, Nikinmaa E, Ibrom A, Wu J, Bernhofer C, Köstner B, Grünwald T, Seufert G, Ciais P, Frank D (2014) Above-ground woody carbon sequestration measured from tree rings is coherent with net ecosystem productivity at five eddy-covariance sites. New Phytol 201:1289-1303, doi: 10.1111/nph.12589
Bailey JD, Mayrsohn C, Doescher PS, St Pierre E, Tappeiner JC (1998) Understory vegetation in old and young Douglas-fir forests of western Oregon. For Ecol Manage 112:289-302
Barford CC, Wofsy SC, Goulden ML, Munger JW, Pyle EH, Urbanski SP, Hutyra L, Saleska SR, Fitzjarrald D, Moore K (2001) Factors controlling long- and short-term sequestration of atmospheric CO2 in a mid-latitude forest. Science 294:1688-1691, doi:10.1126/science.1062962
Black K, Bolger T, Davis P, Nieuwenhuis M, Reidy B, Saiz G, Tobin B, Osborne B (2005) Inventory and eddy covariance-based estimates of annual carbon sequestration in a Sitka spruce (Picea sitchensis (Bong.) Carr.) forest ecosystem. Eur J For Res 126:167-178, doi:10.1007/s10342-005-0092-4
Brown JK (1971) A planar intersect method for sampling fuel volume and surface area. For Sci 17:96-102
Chen BB, Black TA, Coops NC, Hilker T, Trofymow JA, Morgenstern K, Black AT (2009) Assessing tower flux footprint climatology and scaling between remotely sensed and eddy covariance measurements. Boundary-Layer Meteorol 130:137-167, doi:10.1007/s10546-008-9339-1
Clark D, Brown S (2001) Measuring net primary production in forests: concepts and field methods. Ecol Appl 11:356-370
Coops NC, Hilker T, Wulder MA, St-Onge B, Newnham GJ, Siggins A, Trofymow JA (2007) Estimating canopy structure of Douglas-fir forest stands from discrete-return LiDAR. Trees-Structure Funct 21:295-310. doi:10.1007/s00468-006-0119-6
Crookston NL, Finley AO (2008) yaImpute: an R package for kNN imputation. J Stat Softw 23(10):1-16
Curtis P, Hanson P, Bolstad P, Barford C, Randolph J, Schmid H, Wilson K (2002) Biometric and eddy-covariance based estimates of annual carbon storage in five eastern North American deciduous forests. Agric For Meteorol 113:3-19, doi:10.1016/S0168-1923(02)00099-0
Dixon RK, Solomon AM, Brown S, Houghton RA, Trexier MC, Wisniewski J (1994) Carbon pools and flux of global forest ecosystems. Science 263:185-190, doi:10.1126/science.263.5144.185
Ehman JL, Schmid HP, Grimmond CSB, Randolph JC, Hanson PJ, Wayson CA, Cropley FD (2002) An initial intercomparison of micrometeorological and ecological inventory estimates of carbon exchange in a mid-latitude deciduous forest. Glob Chang Biol 8:575-589, doi:10.1046/j.1365-2486.2002.00492.x
Ferster CJ, Trofymow JA, Coops NC, Chen B, Black TA, Gougeon FA (2011) Determination of ecosystem carbonstock distributions in the flux footprint of an eddy-covariance tower in a coastal forest in British Columbia. Can J For Res 41:1380-1393, doi:10.1139/X11-055
Gillis M, Omule A, Brierley T (2005) Monitoring Canada's forests: the national forest inventory. For Chron 81:214-221
Göckede M, Rebmann C, Foken T (2004) A combination of quality assessment tools for eddy covariance measurements with footprint modelling for the characterisation of complex sites. Agric For Meteorol 127:175-188, doi:10.1016/j.agrformet.2004.07.012
Gougeon F (1995) A crown-following approach to the automatic delineation of individual tree crowns in high spatial resolution aerial images. Can J Remote Sens 21:274-284
Gough C, Vogel C, Schmid H, Su H, Curtis P (2008) Multi-year convergence of biometric and meteorological estimates of forest carbon storage. Agric For Meteorol 148:158-170, doi:10.1016/j.agrformet.2007.08.004
Granier A, Ceschia E, Damesin C, Dufrene E, Epron D, Gross P, Lebaube S, Le Dantec V, Le Goff N, Lemoine D, Lucot E, Ottorini JM, Pontailler JY, Saugier B (2000) The carbon balance of a young Beech forest. Funct Ecol 14:312-325, doi:10.1046/j.1365-2435.2000.00434.x
Granier A, Bréda N, Longdoz B, Gross P, Ngao J (2008) Ten years of fluxes and stand growth in a young beech forest at Hesse, North-eastern France. Ann For Sci 65:704-704, doi:10.1051/forest
Grant RF, Black TA, Humphreys ER, Morgenstern K (2007) Changes in net ecosystem productivity with forest age following clearcutting of a coastal Douglas-fir forest: testing a mathematical model with eddy covariance measurements along a forest chronosequence. Tree Physiol 27:115-131
Humphreys ER, Black TA, Morgenstern K, Cai T, Drewitt GB, Nesic Z, Trofymow JA (2006) Carbon dioxide fluxes in coastal Douglas-fir stands at different stages of development after clearcut harvesting. Agric For Meteorol 140:6-22, doi:10.1016/j.agrformet.2006.03.018
Jassal RS, Black TA, Trofymow JA, Roy R, Nesic Z (2010) Soil CO2 and N2O flux dynamics in a nitrogen-fertilized Pacific Northwest Douglas-fir stand. Geoderma 157:118-125, doi:10.1016/j.geoderma.2010.04.002
Kolari P, Jukka P, Rannik U, Hannu I, Pertti H, Berninger F (2004) Carbon balance of different aged Scots pine forests in Southern Finland. Glob Chang Biol 10:1106-1119, doi:10.1111/j.1365-2486.2004.00797.x
Kominami Y, Jomura M, Dannoura M, Goto Y, Tamai K, Miyama T, Kanazawa Y, Kaneko S, Okumura M, Misawa N, Hamada S, Sasaki T, Kimura H, Ohtani Y (2008) Biometric and eddy-covariance-based estimates of carbon balance for a warm-temperate mixed forest in Japan. Agric For Meteorol 148:723-737, doi:10.1016/j.agrformet.2008.01.017
Kurz W, Apps M, Banfield E, Stinson G (2002) Forest carbon accounting at the operational scale. For Chron 78:672-679
Kurz WA, Dymond CC, White TM, Stinson G, Shaw CH, Rampley GJ, Smyth C, Simpson BN, Neilson ET, Trofymow JA, Metsaranta J, Apps MJ (2009) CBM-CFS3: a model of carbon-dynamics in forestry and land-use change implementing IPCC standards. Ecol Modell 220:480-504, doi:10.1016/j.ecolmodel.2008.10.018
Lambert M-C, Ung C-H, Raulier F (2005) Canadian national tree aboveground biomass equations. Can J For Res 35:1996-2018, doi:10.1139/x05-112
Landsberg JJ, Waring RH (1997) A generalised model of forest productivity using simplified concepts of radiation-use efficiency, carbon balance and partitioning. For Ecol Manage 95:209-228, doi:10.1016/S0378-1127(97)00026-1
Law B, Thornton P, Irvine J (2001) Carbon storage and fluxes in ponderosa pine forests at different developmental stages. Glob Chang Biol 7:755-777
Law BE, Turner D, Campbell J, Sun OJ, Van Tuyl S, Ritts WD, Cohen WB (2004) Disturbance and climate effects on carbon stocks and fluxes across Western Oregon USA. Glob Chang Biol 10:1429-1444, doi:10.1111/j.1365-2486.2004.00822.x
Leclerc M, Thurtell G (1990) Footprint prediction of scalar fluxes using a Markovian analysis. Boundary-Layer Meteorol 52(3):247-258
Li Z, Kurz WA, Apps MJ, Beukema SJ (2003) Belowground biomass dynamics in the Carbon Budget Model of the Canadian Forest Sector: recent improvements and implications for the estimation of NPP and NEP. Can J For Res 33:126-136, doi:10.1139/x02-165
Mahalanobis P (1936) On the generalized distance in statistics. Proc Natl Inst Sci 12:49-55
Miller SD, Goulden ML, Menton MC, da Rocha HR, de Freitas HC, Figueira AMES, de Sousa CA D (2004) Biometric and micrometeorological measurements of tropical forest carbon balance. Ecol Appl 14:114-126, doi:10.1890/02-6005
Morgenstern K, Andrew Black T, Humphreys ER, Griffis TJ, Drewitt GB, Cai T, Nesic Z, Spittlehouse DL, Livingston NJ (2004) Sensitivity and uncertainty of the carbon balance of a Pacific Northwest Douglas-fir forest during an El Niño/La Niña cycle. Agric For Meteorol 123:201-219, doi:10.1016/j.agrformet.2003.12.003
Ohtsuka T, Mo W, Satomura T, Inatomi M, Koizumi H (2007) Biometric based carbon flux measurements and net ecosystem production (NEP) in a temperate deciduous broad-leaved forest beneath a flux tower. Ecosystems 10:324-334, doi:10.1007/s10021-007-9017-z
Schmid H (2002) Footprint modeling for vegetation atmosphere exchange studies: a review and perspective. Agric For Meteorol 113:159-183, doi:10.1016/S0168-1923(02)00107-7
Schmid HP, Lloyd CR (1999) Spatial representativeness and the location bias of flux footprints over inhomogeneous areas. Agric For Meteorol 93: 195-209, doi: 10.1016/S0168-1923(98)00119-1
Stage AR, Crookston NL (2007) Partitioning error components for accuracy-assessment of near-neighbor methods of imputation. For Sci 53:62-72
Ter-Mikaelian M (1997) Biomass equations for sixty-five North American tree species. For Ecol Manage 97: 1-24, doi: 10.1016/S0378-1127(97)00019-4
Trofymow JA, Stinson G, Kurz WA (2008) Derivation of a spatially explicit 86-year retrospective carbon budget for a landscape undergoing conversion from old-growth to managed forests on Vancouver Island, BC. For Ecol Manage 256:1677-1691, doi:10.1016/j.foreco.2008.02.056
Wang Z, Grant RF, Arain MA, Chen BN, Coops N, Hember R, Kurz WA, Price DT, Stinson G, Trofymow JA, Yeluripati J, Chen Z (2011) Evaluating weather effects on interannual variation in net ecosystem productivity of a coastal temperate forest landscape: a model intercomparison. Ecol Modell 222:3236-3249, doi:10.1016/j.ecolmodel.2011.06.005
Yashiro Y, Lee N-YM, Ohtsuka T, Shizu Y, Saitoh TM, Koizumi H (2010) Biometricbased estimation of net ecosystem production in a mature Japanese cedar (Cryptomeria japonica) plantation beneath a flux tower. J Plant Res 123:463–472, doi:10.1007/s10265-010-0323-8
We thank Bob Ferris, Frank Eichel, and Glenda Russo of the Canadian Forest Service and staff of B.A. Blackwell and Associates for their help processing and collecting National Forest-inventory-style ground plot data. We also thank François Gougeon, CFS, for determining canopy tree density values for the sites and to Graham Stinson, CFS, for the CBM-CFS3 output files used in
This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly credited.