Potential effects of climate change on the growth of lodgepole pine across diameter size classes and ecological regions
Introduction
Climate models forecast a warming trend of 1.4–5.8 °C under an approximate doubling of atmospheric CO2 concentrations by 2071–2100 (IPCC, 2001). Climate is expected to change most in northern regions and in mountainous areas including the Cordilleran forest of western Canada (Luckman, 1998). Examining past relationships between tree growth and climate in Cordilleran forests will help provide insight into how the productivity of these forests might be affected by future climatic change.
Most tree-ring studies (dendrochronology) involve examining the largest diameter trees to minimize the effect of competition and to simplify cross-dating due to fewer instances of missing rings (Fritts, 1976). Trees of smaller diameter classes are typically aged in demographic studies (i.e., dendroecology), but there have been few attempts to examine how interannual variations in radial growth–climate relationships may differ between trees of different diameter size classes (Piutti and Cescatti, 1997, Cescatti and Piutti, 1998, Meyer and Bräker, 2001). Previous studies have examined diameter growth patterns across elevational ecoregions in the Rocky Mountains but did not directly examine growth–climate relationships (Berg et al., 2007). Past studies examining the influences of climate on the radial growth of lodgepole pine (Pinus contorta Dougl. ex Loud. var. latifolia Engelm.) have been carried out at specific locations (1–4 sites) in the United States (Villalba et al., 1994, Sauchyn et al., 2003). Sauchyn et al. (2003) examined lodgepole pine in the Cypress Hills reporting on radial growth in relation to precipitation. In contrast, the current study describes the relationships between growth and climate for trees of different diameter size classes and for a broad network of 65 lodgepole pine sites that spans a range of elevational ecoregions.
Lodgepole pine forms even-aged, pure stands over broad areas of western North America due to its wide ecological amplitude (Lotan and Critchfield, 1990). In the western Canadian province of Alberta, lodgepole pine is found in every forested region (Natural Regions Committee, 2006) but is the predominant forest type along the eastern slopes of the Rocky Mountains (Huang et al., 2001) and in Cypress Hills of South-eastern Alberta (Henderson et al., 2002) (Fig. 1). Lodgepole pine accounts for approximately 40% of the annual harvest in Alberta (Huang et al., 2001). There is growing concern of the potential vulnerability of Alberta's forests to future climate change (Alberta Environment, 2007). To help address these concerns, the objective of this study was to examine radial growth–climate relationships of lodgepole pine in the Cordilleran forests of Alberta over an 80-year period (1924–2003). Other specific objectives included examining whether the growth response to climate in lodgepole pine varied between diameter size classes and between elevational ecoregions. The other specific objective was to make projections of growth under different climate change scenarios in the 21st century.
Section snippets
Site selection and field sampling
The 4 elevational ecoregions (ER) sampled in the Cordilleran forests included the Boreal Highlands (BH), Foothills (FH), a grouping of the montane and subalpine zones of the Rocky Mountains (RM), and the montane zone of the Cypress Hills (CH) (Table 1; Fig. 1). The elevation region with the lowest average elevation was BH, followed by progressively higher average elevations in FH, CH, and RM. Within each region, the elevation generally declined with a corresponding increase in latitude (Natural
Growth characteristics
The BAI chronologies (based on all DC combined) for each ER and for all ER combined are presented in Fig. 2. The BAI chronology of all ER combined (Fig. 2e) consisted of periods of reduced growth in the late 1950s, early 1970s, early 1980s, and late 1990s, and increased growth in the late 1970s. Within each ER, growth of T trees showed strong and significant correlations with the other 3 DCs (all had r > 0.78 and P < 0.0001), although the strength of the relationship was generally greatest with L
Growth–climate relationships
For all ERs combined, lodgepole pine in Alberta responded to heat and drought stress in late summer of the prior growing season. This lagged climatic response was also found in each ER individually although in BH the response to moisture stress was for the entire summer of the previous year. Lags in response to climatic stress in pines occur partly because climatic conditions in late summer in the year of bud formation generally affects the size of the buds and the number of leaf primordia
Conclusion
Basal area growth of lodgepole pine was generally sensitive to a lag in response to heat and moisture stress, the degree of winter harshness, and the timing of the start of the growing season. Growth–climate relationships varied by ER since growth was inhibited by low temperature in all winter months at the most northern BH sites which had the coldest winters. However, this effect was interrupted in some of the midwinter months in the more southerly sites in the RM, and we postulate this is due
Acknowledgements
This study was partly funded through a research grant from the Forest Resource Improvement Association of Alberta (FRIAA). This study was also supported through a number of doctoral scholarships to S. Chhin: Natural Sciences and Engineering Research Council of Canada (NSERC) Canada Graduate Scholarship (CGS); Alberta Ingenuity Scholarship; Killam Trust Scholarship; and Prairie Adaptation Research Collaborative (PARC) Graduate Scholarship. We thank K. Stadt for his help in the site selection; O.
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