Post-harvest wood debris
March 28, 2016 - Woody debris in forests of temperate and boreal ecological zones is created by natural (wildfire and insect outbreaks) and harvesting (logging) disturbances. Salvage logging and clearcutting often leave much woody debris after the processing of trees. A major “perception” of our utilitarian outlook is to define excess woody debris as “wood waste,” particularly the residue (slash) occurring after conventional and salvage harvesting of forests.
March 28, 2016 By Thomas Sullivan
Down wood provides many ecological functions essential to the maintenance of forest biodiversity and long-term productivity. Sufficient down wood is usually dispersed over harvested sites during the logging operation, thereby leaving piles of post-harvest debris as “excess” material at landings. These wood residues are typically burned in B.C. and most other provinces to reduce a perceived fire hazard. However, use of woody debris for bio-energy is an alternative management scenario and a potential major contributor to a reduction in use of fossil fuels – a desirable environmental goal. In terms of perceived fire hazard, there is no scientific evidence showing that piles and/or windrows of woody debris are ignition points for forest fires, other than those caused by humans.
The intentional burning of excess woody debris creates much smoke that releases greenhouse gas (GHG) emissions and may also create a potential human health concern in nearby communities. The relationship of wildfire smoke to human health problems is well-documented. There seems to be no reason to consider the smoke arising from the burning of debris piles as a different issue.
Woody debris structures may provide foraging, perching, nesting, and denning sites for a variety of mammals, birds, amphibians, and lizards, as well as space for plants and fungi as these structures become part of the new forest growing on the harvested site. A windrow or series of piles may connect patches of mature forest and riparian areas to allow small mammals and some of their predators to access and traverse clear-cut openings. This practice is particularly relevant on large openings (>10 ha) in conventional, but also larger (>100 ha) salvage harvesting operations.
Some important questions are: Do woody debris structures help conserve biodiversity in managed forests? Are we able to measure this biodiversity and estimate its monetary value compared with that generated by using woody debris for bioenergy? 3.) Is there a monetary value lost by burning debris? To address economic-based objections to the wise use of excess woody debris, we compared the monetary value of mammalian biodiversity associated with constructed windrows with those estimated for woody debris used for bioenergy purposes or simply burned.
Two study areas (Elkhart and Golden) were located in south-central British Columbia. Three windrows of woody debris were installed in clear-cuts (harvested in 2011), connecting uncut forest reserves or patches at each study area. Populations of forest-floor small mammals and incidence of mustelid (weasel family) predators were measured in conventionally dispersed CWD, windrow, and adjacent uncut forest sites from 2012 to 2015. A total of nine species of forest-floor small mammals were captured. At Elkhart, mean total abundance of voles and small mammals were higher in the windrow sites than the dispersed or forest sites. At Golden, mean total abundance of voles was similar, but mean total abundance of small mammals was higher in the dispersed and windrow sites than the forest sites.
The windrow sites had 5.8 times more activity by marten and small weasels than the forest sites, and 3.9 times higher levels of activity than the dispersed sites at Elkhart. This difference was 3.3 times higher in windrow than dispersed sites at Golden.
In terms of mammalian biodiversity, diversity of small mammals was highest in the windrow sites at both study areas. A valuation of mammalian biodiversity has indicated at least five components that may potentially generate some monetary revenue by constructing windrow habitats on clear-cuts. These components include: commercial fur harvest of marten, small weasels, and other fur-bearers; enhancement of predators to help lower vole numbers and protect plantation trees from vole feeding damage; small mammals disseminate mycorrhizal fungi that are essential components for tree and plant growth; consumption of invertebrates by small mammals (including rodents and shrews) may help control some insect populations such as spruce beetle; and dissemination and caching of seeds in safe sites by small mammals may be important for forest regeneration. Windrow construction will be site- and cutblock-specific with windrows connecting patches of uncut forest to forest reserves and riparian areas. They are not required on every cutblock, and generally use only 10 to 15 per cent of excess post-harvest woody debris.
Production of wood pellets is, indeed, a worthwhile endeavour and likely dependent on size of pellet production plant and distance to haul wood chips from the various harvested sites to the plant. Bioenergy is a renewable enterprise that results in reduced use of fossil fuels. This can result in a reduction in carbon emissions – a widely supported environmental goal. In addition, biomass sources in this study were from harvest residues rather than removal of whole trees. Perhaps the most cost-revealing part of our analysis was the negative human and environmental costs of burning piles of wood waste.
Policies regulating “utilization and disposal of waste wood piles” need to be revised as soon as possible to:
- Allocate waste wood resources to the biofuels sector in a cost-effective manner;
- Implement windrow habitats where necessary to maintain mammalian biodiversity on clearcuts;
- Limit burning of waste wood to those sites near human activity (potential fire hazard) that do not have an opportunity for bioenergy purposes.
We thank the Wood Pellet Association of Canada, Natural Sciences and Engineering Research Council of Canada, Aspen Planers Ltd., Louisiana-Pacific Corporation, the British Columbia Habitat Conservation Trust Foundation, the Westbank First Nation, Jaeden Resources Ltd., Gold Mountain Mining Corp., and the Applied Mammal Research Institute for financial and logistical support.
Thomas Sullivan is a professor of wildlife ecology and conservation, food and environment – Faculty of Land and Food Systems, Dept. of Forest and Conservation Sciences – Faculty of Forestry at the University of British Columbia. He can be reached at firstname.lastname@example.org.
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