Carbon storage and net primary productivity in Canadian boreal mixedwood stands

Nicholas J. Payne , D. Allan Cameron , Jean-Denis Leblanc , Ian K. Morrison

Journal of Forestry Research ›› 2019, Vol. 30 ›› Issue (5) : 1667 -1678.

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Journal of Forestry Research ›› 2019, Vol. 30 ›› Issue (5) : 1667 -1678. DOI: 10.1007/s11676-019-00886-0
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Carbon storage and net primary productivity in Canadian boreal mixedwood stands

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Abstract

Canadian boreal mixedwood forests are extensive, with large potential for carbon sequestration and storage; thus, knowledge of their carbon stocks at different stand ages is needed to adapt forest management practices to help meet climate-change mitigation goals. Carbon stocks were quantified at three Ontario boreal mixedwood sites. A harvested stand, a juvenile stand replanted with spruce seedlings and a mature stand had total carbon stocks (± SE) of 133 ± 13 at age 2, 130 ± 13 at age 25, and 207 ± 15 Mg C ha−1 at age 81 years. At the clear-cut site, stocks were reduced by about 40% or 90 Mg C ha−1 at harvest. Vegetation held 27, 34 and 62% of stocks, while detritus held 34, 29 and 13% of stocks at age 2, 25 and 81, respectively. Mineral soil carbon stocks averaged 51 Mg C ha−1, and held 38, 37 and 25% of stocks. Aboveground net primary productivity (± SE) in the harvested and juvenile stand was 2.1 ± 0.2 and 3.7 ± 0.3 Mg C ha−1 per annum (p.a.), compared to 2.6 ± 2.5 Mg C ha−1 p.a. in the mature stand. The mature canopies studied had typical boreal mixedwood composition and mean carbon densities of 208 Mg C ha−1, which is above average for managed Canadian boreal forest ecosystems. A comparison of published results from Canadian boreal forest ecosystems showed that carbon stocks in mixedwood stands are typically higher than coniferous stands at all ages, which was also true for stocks in vegetation and detritus. Also, aboveground net primary productivity was typically found to be higher in mixedwood than in coniferous boreal forest stands over a range of ages. Measurements from this study, together with those published from the other boreal forest stands demonstrate the potential for enhanced carbon sequestration through modified forest management practices to take advantage of Canadian boreal mixedwood stand characteristics.

Keywords

Aboveground net primary productivity / Boreal mixedwood forest / Carbon stocks / Mixedwood stand management / Stand age

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Nicholas J. Payne, D. Allan Cameron, Jean-Denis Leblanc, Ian K. Morrison. Carbon storage and net primary productivity in Canadian boreal mixedwood stands. Journal of Forestry Research, 2019, 30(5): 1667-1678 DOI:10.1007/s11676-019-00886-0

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References

[1]

Amiro BD, Todd JB, Wooton BM, Logan KA, Flannigan MD, Stocks BJ, Mason JA, Martell DL, Hirsch KG. Direct carbon emissions from Canadian forest fires, 1959–1999. Can J For Res, 2001, 31(3): 512-525.

[2]

Baldwin KA, MacKenzie WH, Pfalz J, Meades WJ, Meidinger DV, Robataille A, Saucier J-P, Uhlig P (2012) Level 4 map, version 1, Canadian component of the Circumboreal Vegetation Map (CBVM). Canadian regional team of the Circumboreal Vegetation Map Project. Natural Resources Canada, Canadian Forest Service, Great Lakes Forestry Centre, Sault Ste. Marie, ON. Unpublished map

[3]

Bélisle J. Field manual for describing soils, 1980, Ont: Inst. Pedol., Univ. Guelph.

[4]

Bond-Lamberty B, Wang C, Gower S. Net primary production and net ecosystem production of a boreal black spruce wildfire chronosequence. Glob Change Biol, 2004, 10(4): 473-487.

[5]

Brais S, Harvey BD, Bergeron Y, Messier C, Greene D, Belleau A, Paré D. Testing forest ecosystem management in boreal mixedwoods of northwestern Quebec: initial response of aspen stands to different levels of harvesting. Can J For Res, 2004, 34(2): 431-446.

[6]

Brandt JP. The extent of the North American boreal zone. Environ Rev, 2009, 17: 101-161.

[7]

Brassard BW, Han YH, Bergeron Y, Paré D. Coarse root biomass allometric equations for Abies balsamea, Picea mariana, Pinus banksiana, and Populus tremuloides in the boreal forest of Ontario, Canada. Biomass Bioenergy, 2011, 35(1): 4189-4196.

[8]

Carlton DW, Pickford SG. Fuelbed changes with aging of slash from ponderosa pine thinnings. J For, 1982, 80(2): 91-93.

[9]

Chapman LJ, Thomas MK (1968) The climate of northern Ontario. Can. Dep. Transport, Meteorological Br. Climatological Studies 6. Toronto

[10]

Chen HYH, Popadiouk R. Dynamics of North American boreal mixedwoods. Environ Rev, 2002, 10: 137-166.

[11]

Crow TR, Erdmann GG (1983) Weight and volume equations and tables for red maple in the Lake States. U.S. Dep. Agric. For. Serv., North Cent. For. Exp. Stn., St. Paul, MN. Res. Pap. NC-242

[12]

Dixon RK, Brown S, Houghton RA, Solomon AM, Trexler MC, Wisniewski J. Carbon pools and flux of global forest ecosystems. Science, 1994, 263(5144): 185-189.

[13]

Environment Canada (2013) Canadian climate normals 1971–2000. http://www.climate.weatheroffice.gc.ca/climate_normals/results_1971_2000_e.html. Accessed 10 Nov 2016

[14]

Gower ST, Vogel JG, Norman JM, Kucharik CJ, Steele SJ, Stow TK. Carbon distribution and aboveground net primary production in aspen, jack pine and black spruce stands in Saskatchewan and Manitoba, Canada. J Geophys Res, 1997, 102(D24): 29029-29041.

[15]

Hazlett PW, Gordon AM, Sibly PK, Buttle JM. Stand carbon stocks and soil carbon and nitrogen storage for riparian and upland forests of boreal lakes in northeastern Ontario. For Ecol Manage, 2005, 219(1): 56-68.

[16]

He L, Chen JM, Pan Y, Birdsey R, Kattge J. Relationships between net primary productivity and forest stand age in US forests. Glob Biogeochem Cycles, 2012 26 3 GB3009

[17]

Howard E, Gower S, Foley J, Kucharik C. Effects of logging on carbon dynamics of a jack pine forest in Saskatchewan, Canada. Glob Change Biol, 2004, 10(8): 1267-1284.

[18]

IPCC (2014) Climate change 2014: Synthesis report. Contribution of Working Groups I, II and III to Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing team, R.K. Pachauri and L.A.Mayer, (eds.)]. IPCC, Geneva, Switzerland, p 151

[19]

Kurz WA, Shaw CH, Boisvenue C, Stinson G, Metsaranta J, Leckie D, Dyk A, Smyth C, Neilson ET. Carbon in Canada’s boreal forest—a synthesis. Environ Rev, 2013, 21: 260-292.

[20]

Laganière J, Cavard X, Brassard B, Pare D, Bergeron Y, Chen H. The influence of boreal tree species mixtures on ecosystem carbon storage and fluxes. For Ecol Manage, 2015, 354: 119-129.

[21]

Lal R. Forest soils and carbon sequestration. For Ecol Manage, 2005, 220: 242-258.

[22]

Landsberg JJ, Gowe ST. Applications of physiological ecology to forest management. Physiological Ecology Series, 1997, San Diego: Academic Press Inc..

[23]

Lee J, Morrison IK, Leblanc JD, Dumas MT, Cameron DA. Carbon sequestration in trees and regrowth vegetation as affected by clearcut and partial cut harvesting in a second-growth boreal mixedwood. For Ecol Manage, 2002, 169(1–2): 83-101.

[24]

Légaré S, Paré D, Bergeron Y. The responses of black spruce growth to an increased proportion of aspen in mixed stands. Can J For Res, 2004, 34(2): 405-416.

[25]

Lemprière TC, Kurz WA, Hogg EH, Schmoll C, Rampley GJ, Yemshanov D, McKenney DW, Gilsenan R, Beatch A, Blain D, Bhatti JS, Krcmar E. Canadian boreal forests and climate change mitigation. Environ Rev, 2013, 21: 293-321.

[26]

Li Z, Kurz WA, Apps MA, Beukema SJ. 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, 2002, 33(1): 126-136.

[27]

Liu J, Peng C, Apps M, Dang Q, Banfield E, Kurz W. Historic carbon budgets of Ontario’s forest ecosystems. For Ecol Manage, 2002, 169(1–2): 103-114.

[28]

MacDonald GB. The case for boreal mixedwood management: an Ontario perspective. For Chron, 1995, 71(6): 725-734.

[29]

Martin JL, Gower ST, Plaut J, Holmes B. Carbon pools in a boreal mixedwood logging chronosequence. Glob Change Biol, 2005, 11(11): 1883-1894.

[30]

McRae DJ, Alexander ME, Stocks BJ (1979) Measurement and description of fuels and fire behavior on prescribed burns: a handbook. Dep. Environ., Can. For. Serv., Sault Ste. Marie, Ont. Inf. Rep. O-X-287

[31]

Moroni MT. Disturbance history affects dead wood abundance in Newfoundland boreal forests. Can J For Res, 2006, 36(12): 3194-3208.

[32]

Morrison IK. Addition of organic matter and elements to the forest floor of an old growth Acer saccharum forest in the annual litter fall. Can J For Res, 1991, 21(4): 462-468.

[33]

Morrison IK, Foster NW, Hazlett PW. Carbon reserves, carbon cycling, and harvest effects in three mature forest types in Canada. NZ J For Sci, 1993, 23(3): 403-412.

[34]

Morrison IK, Lee J Jr, Cameron DA, Leblanc JD, Dumas MT (2001) Carbon distribution and above-ground net production as influenced by harvesting in a second-growth boreal mixedwood forest in eastern Canada, in: Richardson, J.; Bjorheden, R.; P. Hakkila, A.T. Lowe, and C.T. Smith, compilers. Bioenergy from Sustainable Forestry: Principles and Practice. Proceedings of IEA Bioenergy Task 18 Workshop, October 16-20, 2000, Coff’s Harbour, New South Wales, Australia. New Zealand Forest Research Institute, Rotorura, New Zealand, Forest Research Bulletin 223. Bottom of Form

[35]

National Forest Inventory (2008) Canada’s National Forest Inventory: Ground Sampling Guidelines [electronic resource]. https://ca.nfis.org/index_e.html Version 5.0. Accessed 10 Nov 2016

[36]

Natural Resources Canada (2012) The state of Canada’s forests 2012: annual report [electronic resource]. http://cfs.nrcan.gc.ca/pubwarehouse/pdfs/34055.pdf. Accessed 10 Nov 2016

[37]

Noormets A, Epron D, Domec JC, McNulty SG, Fox T, Sun G, King JS. Effects of forest management on productivity and caerbon sequestration: A review and hypothesis. For Ecol Manage, 2015, 335: 124-140.

[38]

Ohmann LF, Grigal DF, Rogers LL (1981) Estimating plant biomass for undergrowth species of northeastern Minnesota forest communities. U.S. Dep. Agric. For. Serv., North Cent. For. Exp. Stn., St. Paul, MN. Gen. Tech. Rep. NC-61

[39]

Paré D, Bergeron Y. Above-ground biomass along a 230-year chronosequence in the southern portion of the Canadian boreal forest. J Ecol, 1995, 83(6): 1001-1007.

[40]

Paré D, Boutin R, Larocque GR, Raulier F. Effect of temperature on soil organic matter decomposition in three forest biomes of eastern Canada. Can J Soil Sci, 2006, 86: 247-256.

[41]

Perala DA, Alban DH (1994) Allometric biomass estimators for aspen-dominated ecosystems in the Upper Great Lakes. U.S. Dep. Agric. For. Serv., North Cent. For. Exp. Stn., St. Paul, MN. Res. Pap. NC-314

[42]

Prescott CE, Corbin JP, Parkinson D. Input, accumulation and residence times of carbon, nitrogen and phosphorus in four Rocky Mountain coniferous forests. Can J For Res, 1989, 19(3): 489-498.

[43]

Roussopoulous PJ, Loomis RM (1979) Weights and dimensional properties of shrubs and small trees of the Great Lakes conifer forest. U.S. Dep. Agric. For. Serv., North Cent. For. Exp. Stn., St. Paul, MN. Res. Pap. NC-178

[44]

Seedre M, Taylor AR, Brassard BW, Chen HY, Jõgiste K. Recovery of ecosystem carbon stocks in young boreal forests: a comparison of harvesting and wildfire disturbance. Ecosystems, 2014, 17: 851-863.

[45]

Smith WB, Brand GJ (1983) Allometric biomass equations for 98 species of herbs, shrubs, and small trees. U.S. Dep. Agric. For. Serv., N. Central For. Exp. Sta., St. Paul, MN. Res. Note NC-299

[46]

Soil Classification Working Group (1998) The Canadian system of soil classification. Agric Agri-Food Can. Publ. 1646 (revised)

[47]

Strukelj M, Brais S, Paré D. Nine-year changes in carbon dynamics following different intensities of harvesting in boreal aspen stands. Eur J Forest Res, 2015, 134(5): 737-754.

[48]

Ter-Mikaelian MT, Korzukhin MD. Biomass equations for sixty-five North American tree species. For Ecol Manage, 1997, 97(1): 1-24.

[49]

Towill WD (1996) Ontario’s boreal mixed forest: distribution, extent, and importance, p. 21 in: Smith, C. R.; Crook, G. W. (compilers). Advancing Boreal Mixedwood Management in Ontario. Proceedings of a Workshop, 17–19 Oct. 1995, Sault Sainte Marie, ON. Can. For. Serv., Sault Sainte Marie, ON

[50]

Van Wagner CE. The line intersect method in forest fuel sampling. For Sci, 1968, 14(1): 20-26.

[51]

Woodall CW, Liknes GC. Relationships between forest fine and coarse woody debris carbon stocks across latitudinal gradients in the United States as an indicator of climate change effects. Ecol Ind, 2008, 8(5): 686-690.

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