Effects of red alder on growth of Douglas-fir and western redcedar in southwestern British Columbia
Introduction
Red alder (Alnus rubra [Bong.]) is a deciduous tree species that grows both in pure and mixed stands in the Pacific Northwest region of North America. It is commonly found as a component of mixed stands with conifer species such as Douglas-fir (Pseudotsuga menziessi (Mirb.) Franco), Sitka spruce (Picea sitchensis [Bong.] Carr), western hemlock (Tsuga heterophylla [Raf.] Sarg.) and western redcedar (Thuja plicata Donn.) (Eyre, 1980, Deal and Harrington, 2006). In Canada, red alder occurs primarily in the Coastal Western Hemlock zone as a lowland species and generally grows within 200 km of the seacoast at elevations below 750 m. Red alder grows best on deep alluvial soils in river and stream flood plains and is limited by drought and low winter temperatures. Red alder has gained particular interest due to its various uses (furniture, cabinets and pallets), increasing commercial value, and special properties including nitrogen fixation capacity and tolerance of wet soil conditions (Harrington, 1984, Deal and Harrington, 2006).
Admixing red alder into conifer stands can contribute to long-term productivity (fixing nitrogen) (Binkley, 1983, Comeau and Sachs, 1992), enhanced complexity (Piccolo and Wipfli, 2002, Deal and Wipfli, 2004, Deal, 2007), mitigation of pest and pathogen infections of conifer species (McLean et al., 1989, Harrington et al., 1994, Hibbs and DeBell, 1994, McComb, 1994), as well as adaptation to climate change (Cortini et al., 2012). However, red alder is also a strong competitor in young conifer stands due to its rapid juvenile height growth, and detrimental effects on light availability to understory conifers. An understanding of both competitive and beneficial effects of red alder in mixture with conifers is fundamental to making decisions for sustainable management of complex forests in the Pacific Northwest.
A range of competition indices have been used for evaluating levels of competition and for examining the effects of competition on tree growth. For red alder at low densities, the distance to associated conifers would be expected to be important in accounting for competition, which suggests that we should use distance-dependent indices for better prediction of competitive effects. On the other hand, results vary depending on both the broadleaf and conifer species. Previous studies show that two distance-independent indices (Diameter’s Sum and Crown Surface Area) had the highest correlations with Douglas-fir stem volume growth, while for western redcedar the best indices were distance-dependent (Cortini and Comeau, 2008). In addition, Cortini and Comeau (2008) found simple indices such as height factor, total number of competitors, and competitor basal area performed well in their study. Selection of the ideal competition index is complicated due to the simultaneous beneficial and negative effects of red alder with both effects being dependent on site, soil and other factors. Therefore, it is necessary to evaluate a range of competition indices and select the most effective one for predicting radial growth of conifers growing in mixture with low to moderate densities of red alder.
In order to improve our understanding of the competitive effects of different amounts and spatial arrangements of red alder, and how these effects are influenced by factors such as site quality, conifer species, and stand-age, long-term studies of mixed alder-conifer plantings were established in 1992, 1994 and 1999 using both additive and replacement series designs as described by Thomas et al. (2005). The main objectives of the study presented herein are to use data from these experiments to: (1) examine the competitive effects of red alder on the growth of Douglas-fir and western redcedar; (2) evaluate the effectiveness of various distance-dependent and distance-independent competition indices; (3) explore the relationship between light level and alder density; (4) analyze the effects of alder density on soil and foliage nitrogen content, and (5) make recommendations for the management of alder in mixture with conifers.
Section snippets
Site description
This study is part of the long-term Experimental Project 1121.01 which was initiated in 1992 with five installation sites located in southwestern British Columbia (Fig. 1) (Thomas et al., 2005). All sites are located in the Coastal Western Hemlock (CWH) biogeoclimatic zone but vary from dry maritime to very wet maritime subzones (Table 1). The CWH zone has a cool mesothermal climate with cool summers (although hot dry spells can be frequent) and mild winters. Mean annual temperature is about
Soil and Douglas-fir foliar nitrogen
A non-linear mixed effects model with site variations as random terms was used to analyze soil N and Douglas-fir foliar N. Preliminary analysis showed red alder density was a better predictor than its basal area. In general, higher amounts of red alder in the stand were associated with higher soil N availability and the most N deficient site (e.g. Gough Creek, as indicated by this site having the lowest levels of mineralizable N in the 0 alder treatment) shows larger effects of red alder
Soil and foliar nitrogen
Studies have shown that red alder stands can fix large amount of nitrogen (N, 100–200 kg−1 ha−1 year−1 in pure stands and 50–100 kg−1 ha−1 year−1 in mixed species stands) (Binkley et al., 1992, Binkley et al., 1994, Swanston and Myrold, 1997). These N additions would be expected to improve site productivity and tree growth due to the high mobility and amounts of nitrates () in the soil that were significantly related to red alder density. Our study showed that there was a trend of
Conclusions
Our results indicate red alder density of 100 tph has positive effects on the size of western redcedar and, 400 tph red alder resulted in a significant increase in Douglas-fir height growth. Increasing alder density increased nitrogen availability for the associated treatment plots. For predicting conifer growth, initial subject tree basal area (the first year of the growth period) was a highly significant explanatory variable. No single competition index performed consistently better than the
Acknowledgments
This experimental project (EP 1121.01) was funded by B.C. Forest Science Program Projects Y051209 and Y062209. Support has also been provided in part by Forest Renewal BC Project HQ96400-RE (1996–2001), the Canada-British Columbia Partnership Agreement on Forest Resource Development (FRDA II) (1991–1996), and the B.C. Ministry of Forests and Range. We are grateful to Peter Fielder, Balvinder Biring, and other staff from the B.C. Ministry of Forests, Lands, Natural Resource Operations and Rural
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