The Natural
Disturbance Model of Forest Harvesting: An Overview
Fact Sheet by the
Alberta Centre for Boreal Studies (August, 2000)
Concept:
- Through natural selection the
species inhabiting the boreal forest have developed adaptations for
maintaining viability in the face of catastrophic disturbances such as fire.
- Based on the above observation, it
has been hypothesized that that biodiversity can be maintained in the
presence of industrial use if industrial practices are made to approximate
natural disturbances. This hypothesis forms the basis of the Natural
Disturbance Model (NDM) of forest harvesting.
- In practice, it is not the actual
disturbance process that the NDM seeks to approximate, but the forest
structure and pattern resulting from disturbance and subsequent forest
regeneration. The operational goal is to maintain forest structure and
pattern, along with ecological processes, within the typical range of
natural variation.
- The assumption (and hope) is that
the key to maintaining biodiversity is not necessarily the strict emulation
of fire (or other disturbances) but the maintenance of habitat diversity,
however that may be achieved.
NDM targets:
- The ability of forestry companies to
replicate the forest structures and patterns produced by natural
disturbances is dependent on how well these structures and patterns can be
described.
- Because historical landscapes cannot
be adequately characterized, using the current landscape for primary
guidance is the only realistic option available.
- For companies to implement the NDM
they must first develop a series of targets, appropriate for their
management area, that can be incorporated into the planning process. To do
this, key attributes that characterize forest structure and pattern are
selected (see below), and estimates are made of their average level and
range of variation under natural conditions. Economic and logistic
constraints may influence the definition of the actual operational targets
in some cases.
Attributes related to stand
structure:
- Quantity and distribution of
residual live trees after harvest
- Quantity and distribution of
standing dead trees after harvest
- Quantity and distribution of downed
woody material after harvest
- Soil nutrient levels
- Amount of disturbance and compaction
of the forest floor
Attributes related to landscape
pattern:
- Distribution of stand age (including
the proportion of old-growth)
- Distribution of stand type
(including the proportion of mixedwood stands)
- Distribution of stand size
(including the proportion of large unfragmented stands)
- Patch shape and spatial arrangement
of patches on the landscape (Fig.)
Implementation:
- Implementation of the NDM involves
the integration of NDM targets into forest management planning. This
generally involves changes in harvest planning procedures and in operational
practices. The future landscape should resemble the reference landscape at
all points in time and at no time should the value of structure or pattern
attributes exceed the range of natural variation.
- The target distributions for size,
shape, and spatial arrangement of forest stands can best be achieved by
defining harvest blocks on the basis of existing stand boundaries (Fig.).
- In order to maintain mixedwood
stands the current dual land base system (coniferous and deciduous) must be
abandoned and mixedwood management techniques need to be employed in place
of clear-cut harvesting and plantation management.
- The maintenance of old-growth stands
will require a change in the current policy of preferentially targeting
older stands, and a reduction in the overall rate of harvest.
Sustained-yield management:
- The government of Alberta continues
to use sustained-yield management (SYM) as its approach to forest
management; the NDM has not yet been adopted.
- Under SYM the rate of harvest cannot
exceed the rate of tree growth; however, there are no requirements for
maintaining the ecological integrity of the system.
- Under SYM older age classes are
preferentially targeted for harvest. The intent is to liquidate all age
classes older than the optimal harvest age (generally ~ 80 years for aspen
and ~110 years for spruce).
- Under SYM in Alberta the general
approach is to clear-cut stands and then force regeneration to either pure
spruce or aspen as quickly as possible (using plantation techniques for
spruce). Mixedwood stands are lost from the system in the process, and
non-merchantable vegetation is actively targeted for elimination. There are
no targets for maintaining structural attributes on stands after harvest.
- Harvest blocks under SYM in Alberta
are generally of uniform size and shape, and hence the natural variation in
stand size and shape is lost over time. In particular, large contiguous
patches, required by "interior" wildlife species, are lost from
the system.
- The overall effect of SYM is to
reduce habitat diversity by producing a forest that is younger and simpler
than natural-origin forests. Reduced habitat diversity will in turn result
in decreased species diversity.