The Date Creek Silvicultural Systems Research Project

Site Location and Description

The Date Creek silvicultural systems study is located in the transitional coast-interior forests (Interior Cedar-Hemlock zone) of northwestern British Columbia, approximately 20 km north of Hazelton (55o 22’ N, 127o 50’ W). In this mountainous region of B.C., climatic conditions can vary over relatively short distances. The moderate to steep lower slopes of the Kispiox Range make up one half of the study area. The rest of the area is a rolling morainal landscape, dissected by many glacial meltwater channels. Morainal parent materials dominate the area, ranging in texture from loamy sand to clay loam. Eluviated Dystric Brunisols, Orthic Dystric Brunisols, and Orthic Humo-Ferric Podzols are the most common soils; Hemimors and Mormoders are typical humus forms. Forests in the research area are dominated by a mixture of conifer and deciduous tree species. Mature forests (130-140 years since fire) are dominated by western hemlock (Tsuga heterophylla), but are intimately mixed with western redcedar (Thuja plicata), subalpine fir (Abies lasiocarpa), lodgepole pine (Pinus contorta var. latifolia), hybrid spruce [the complex of white spruce (Picea glauca), Sitka spruce (P. sitchensis) and occasionally Engelmann spruce (P. engelmannii)], paper birch (Betula papyrifera), trembling aspen (Populus tremuloides) and black cottonwood (Populus balsamifera ssp. trichocarpa). Subalpine fir is commonly replaced by amabilis fir (Abies amabilis) at higher elevations. In the old-growth stands (300 yrs+ since fire), western hemlock dominates with minor components of western redcedar, subalpine fir and amabilis fir.
 

Mature ICH forest Oldgrowth ICH forest
Mature (135 yrs) ICH forest.
Old-growth (350+ yrs) ICH forest

Background

The silvicultural systems experiment was established in 1992. The treatments represent differing amounts and patterns of tree removal. Two levels of partial cutting were used and compared with both undisturbed forests and clearcuts. In the light partial cutting treatment, approximately 30% of the stand volume was removed by cutting either single stems or small gaps (3 - 10 trees). In the heavy partial cutting treatment, approximately 60% of stand volume was removed. The cutting pattern utilized both large gaps (0.1–0.5 ha in size), evenly distributed across the treatment units and either single tree or small gaps in the forest matrix between the large openings. With the exception of scattered residual deciduous trees (mostly trembling aspen and paper birch), all stems were removed in the clearcut treatment units. There were four replicates of each of the four treatments, organized in a randomized block design; treatment units were approximately 20 hectares in size. The intent was to create four differently structured stands that would provide a wide variety of environmental conditions both between and within treatments. In addition to creating four distinct levels of tree removal (at the treatment unit scale), we wanted to establish a range of canopy opening sizes. These ranged from the removal of single trees to approximately 0.5 ha openings in the partially-cut treatment units, to single large openings in the clearcut treatment units.
 
30% removal treatment 60% removal treatment
Light partial cut - 30% removal treatment.
Heavy partial cut - 60% removal treatment.

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