Abstract
C4 plants are rare in cool climates, an ecological pattern attributable to their poor photosynthetic performance at low temperatures relative to C3 species. However, some C4 species are able to persist at high latitudes and high elevations, possibly due to the characteristics of the particular microsites they inhabit in these otherwise unfavourable environments. One such species is Muhlenbergia glomerata, which occurs above 60°N in Canada and is found in the atypical C4 habitat of boreal fens. In this study, we evaluate how microsite features affect the success of M. glomerata in boreal fens. We surveyed 19 populations across northern Ontario during the summers of 1999 and 2000. The ground coverage by woody vegetation was the most important parameter affecting the presence or absence of M. glomerata. Woody plants covered over 50% of the ground area in plots where M. glomerata is absent, but less than 20% where it is present. The minimum light intensity threshold for the presence of the C4 species was about 32% of full-sunlight at plant height. Surprisingly, in boreal fens M. glomerata was largely restricted to the wetter moss hollows, rather than occurring on the dry hummocks where its greater water use efficiency might have been advantageous. Woody species dominated the hummocks, but were uncommon in the hollows. In these cool northern climates M. glomerata apparently persists because sufficient periods of temperatures favourable to C4 photosynthesis occur, but this persistence likely requires some factor that suppresses the woody vegetation.
Similar content being viewed by others
References
Akaike H (1974) A new look at the statistical model identification. IEEE Trans Auto Cont AC 19:716–723
Bray JR (1958) The distribution of savanna species in relation to light intensity. Can J Bot 36:671–681
Bridgham SD, Updegraff K, Pastor J (1998) Carbon, nitrogen, and phosphorus mineralization in northern wetlands. Ecology 79:1545–1561
Ehleringer JR, Monson RK (1993) Evolutionary and ecological aspects of photosynthetic pathway variation. Annu Rev Ecol Syst 24:411–439
Environment Canada (2002) Canadian climate normals 1971–2000. Meteorological Service of Canada. http://www.msc.ec.gc.ca/climate/climate_normals/results_e.cfm.
Farquhar GD, Ehleringer JR, Hubick KT (1989) Carbon isotope discrimination and photosynthesis. Annu Rev Plant Physiol Plant Mol Biol 40:503–537
Johnson D, Kershaw L, MacKinnon A, Pojar J (1995) Plants of the western boreal forest and aspen parkland. Lone Pine, Edmonton, Canada
Ko LJ, Reich PB (1993) Oak tree effects on soil and herbaceous vegetation in savannas and pastures in Wisconsin. Am Midl Nat 130:31–42
Kubien DS (1996) Regulation of transpiration in naturally occurring Picea mariana (Mill.) B.S.P. MSc Thesis, Carleton University, Ottawa, Canada
Kubien DS (2003) On the performance of C4 photosynthesis at low temperatures and its relationship to the ecology of C4 plants in cool climates. PhD Thesis, University of Toronto
Kubien DS, von Caemmerer S, Furbank RT, Sage RF (2003) C4 photosynthesis at low temperature: a study using transgenic plants with reduced amounts of Rubisco. Plant Physiol 132:1577–1585
Lieffers VJ, Rothwell RL (1987) Rooting of peatland black spruce and tamarack in relation to depth of water table. Can J Bot 65:817–821
Long SP (1983) C4 Photosynthesis at low temperatures. Plant Cell Environ 6:345–363
Long SP (1999) Environmental responses. In: Sage RF, Monson RK (eds) C4 plant biology. Academic Press, Toronto, pp 215–249
Long SP, Incoll LD, Woolhouse HW (1975) C4 photosynthesis in plants from cool temperate regions, with particular reference to Spartina townsendii. Nature 257:622–624
MathSoft (1994) S-Plus 4 Guide to Statistics. Seattle, USA
McCullagh P, Nelder JA (1989) Generalized linear models, 2nd edn. Chapman and Hall, New York
Natural Resources Canada (1999). Maps of the National Topographic System of Canada, Index 3. NRC, Canada
Newman JA, Bergelson J, Grafen A (1997) Blocking factors and hypothesis tests in ecology: is your statistics text wrong? Ecology 78:1312–1320
Osmond CB, Winter K, Ziegler H (1982) Functional significance of different pathways of CO2 fixation in photosynthesis. In: Lange OL, Nobel PS, Osmond CB, Ziegler H (eds) Physiological plant ecology. II. (Encyclopedia of plant physiology, vol 12B) Springer, Berlin Heidelberg New York, pp 480–547
Pittermann J, Sage RF (2000) Photosynthetic performance at low temperature of Bouteloua gracilis Lag., a high-altitude C4 grass from the Rocky Mountains, USA. Plant Cell Environ 23:811–823
Pittermann J, Sage RF (2001) The response of the high altitude C4 grass Muhlenbergia montana (Nutt.) A.S. Hitchc. to long- and short-term chilling. J Exp Bot 52:829–838
Pohl RW (1969) Muhlenbergia, subgenus Muhlenbergia (Gramineae) in North America. Am Midl Nat 82:512–542
Sage RF (1996) Modification of fire disturbance by elevated CO2. In: Körner C, Bazzaz FA (eds) Carbon dioxide, populations and communities. Academic Press, San Diego, pp 231–249
Sage RF, Sage TL (2002) Microsite characteristics of Muhlenbergia richardsonis (Trib.) Rydb., an alpine C4 grass from the White Mountains, California. Oecologia 132:501–508
Sage RF, Wedin DA, Li M (1999) The biogeography of C4 photosynthesis: patterns and controlling factors. In: Sage RF, Monson RK (eds) C4 Plant biology. Academic Press, Toronto, pp 313–373
Schwarz AG, Redmann RE (1988) C4 grasses from the boreal forest region of northwestern Canada. Can J Bot 66:2424–2430
Skene KR, Sprent JI, Raven JA, Herdman L (2000) Myrica gale L. J Ecol 88:1079–1094
Smith M, Martin CE (1987) Photosynthetic responses to irradiance in three forest understory species of the C4 grass genus Muhlenbergia. Bot Gaz 148:275–282
Taylor SW, Pike RG, Alexander ME (1997) Field guide to the Canadian forest fire behaviour predication (FBP) system. Canadian Forest Service, Ottawa
Teeri JA, Stowe LG (1976) Climatic patterns and the distribution of C4 grasses in North America. Oecologia 23:1–12
Thormann MN, Bayley SE (1997a) Aboveground plant production and nutrient content of the vegetation in six peatlands in Alberta, Canada. Plant Ecol 131:1–16
Tieszen LL, Senyimba MM, Imbamba SK, Troughton JH (1979) The distribution of C3 and C4 grasses and carbon isotope discrimination along an altitudinal and moisture gradient in Kenya. Oecologia 37:337–350
Van Cleve K, Dyrness CT, Viereck LA, Fox J, Chapin FS III, Oechel W (1983) Taiga ecosystems in interior Alaska. Bioscience 33:39–44
Verry ES (1997) Hydrological processes of natural, northern forested woodlands. In: Trettin CC, Jurgensen MF, Grigal DF, Gale MR, Jeglum JK (eds) Northern forested wetlands: ecology and management. CRC, Boca Raton, pp 163–188
Weltzin JF, Pastor J, Harth C, Bridgham SD, Updegraff K, Chapin CT (2000) Response of bog and fen plant communities to warming and water-table manipulations. Ecology 81:3464–3478
Weltzin JF, Harth C, Bridgham SD, Pastor J, Vonderharr M (2001) Production and microtopography of bog bryophytes: response to warming and water-table manipulations. Oecologia 128:557–565
Yefremova TT, Yefremov SP (1996) Ecological effects of peat fire on forested bog ecosystems. In: Goldammer JG, Furyaev VV (eds) Fire in ecosystems of boreal Eurasia. Kluwer, The Netherlands, pp 350–357
Acknowledgements
The authors wish to thank Deb Metsger (TRT), Erika North (LKHD), Lada Malek (Lakehead) and Dan Paju (Thunder Bay) for access to herbarium collections, and to Barb and Garnie Sproule for access to the Mosque field site. We appreciate the helpful comments of two anonymous reviewers. This work was funded by an NSERC grant (OGP0154273) to R.F.S.
Author information
Authors and Affiliations
Corresponding author
Appendix
Appendix
Details of the sites used to quantify the characteristics of the microsites which support populations of Muhlenbergia glomerata in Ontario
Populations were considered distinct when a hydrological discontinuity was apparent. Sites are typically named by the township in which they occur. Grid references follow the Universal Transverse Mercator (UTM) system, as indicated on the National Topographic System (NTS) of Canada map series (Natural Resources Canada 1999). Note that the populations on this list represent 19 out of over 200 fens examined for the presence of M. glomerata.
Year | Site | Latitude | Longitude | NTS map (1:50,000) | UTM grid reference | Day of year |
---|---|---|---|---|---|---|
1999 | Batchawana | 46 57 | 84 33 | 41 K/15 | 865 022 | 196 |
Pancake Bay | 46 58 | 84 45 | 41 K/15 | 739 041 | 209 | |
Pardee | 48 08 | 89 35 | 52 A/4 | 070 358 | 201 | |
Prairie River | 48 48 | 86 47 | 42 D/15 | 157 055 | 206 | |
T-Bay NW | 48 24 | 89 18 | 52 A/6 | 265 644 | 202 | |
T-Bay SW | 48 23 | 89 20 | 52 A/6 | 271 640 | 203 | |
Mosque | 44 58 | 76 54 | 31 C/15 | 506 846 | 189 | |
Clarendon | 45 00 | 76 53 | 31 F/2 | 507 848 | 190 | |
2000 | Carmichael | 49 05 | 82 00 | 42 G/1 | 267 371 | 185 |
Ford | 49 02 | 82 02 | 42 G/1 | 248 323 | 186 | |
McMillan | 49 46 | 84 40 | 42 F/15 | 682 159 | 191 | |
McCoig | 49 45 | 84 49 | 42 F/15 | 572 146 | 192 | |
Lindwest | 49 43 | 87 08 | 42 E/11 | 904 063 | 193 | |
Wildgoose | 49 43 | 87 09 | 42 E/11 | 895 062 | 194 | |
Errington | 49 41 | 87 03 | 42 E/11 | 966 041 | 195 | |
Stedman | 49 05 | 90 41 | 52 G/2 | 690 389 | 197 | |
Colliver | 49 06 | 90 42 | 52 G/2 | 678 403 | 201 | |
Fisher | 46 56 | 84 33 | 41 K/15 | 862 051 | 208 | |
Herrick | 46 57 | 84 38 | 41 K/15 | 798 029 | 210 |
Rights and permissions
About this article
Cite this article
Kubien, D.S., Sage, R.F. C4 grasses in boreal fens: their occurrence in relation to microsite characteristics. Oecologia 137, 330–337 (2003). https://doi.org/10.1007/s00442-003-1369-2
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s00442-003-1369-2