1 Lecture 11 Implementation of Ecosystem Management: Case Studies Kevin Crowe FORE 4212 25 November,...
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Transcript of 1 Lecture 11 Implementation of Ecosystem Management: Case Studies Kevin Crowe FORE 4212 25 November,...
1
Lecture 11Implementation of Ecosystem
Management: Case Studies
Kevin Crowe
FORE 4212
25 November, 2004
2
Objectives
Review 2 working examples of ecosystem management
Demonstrate how ecosystem management initiatives have sprung from diverse origins– i.e., outside of Ontario
Illustrate innovation in managing all forest values
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Case #1: The Lac Duparquet Forest
Northwestern Quebec Great variety of soil conditions and a forest
mosaic characteristic of eastern boreal mixed-wood forest– Pine, spruce, birch, aspen, balsam fir, tamarack
Allocated to Tembec (sawmills) and Nexfor (OSB mill)
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Case #1: The Lac Duparquet Forest
1996 Tembec and Nexfor gave up 8,000 ha to allow creation of Lac Duparquet Research and Teaching Forest
– University of Quebec at Montreal and University of Quebec in Abitibi took over management of the forest
– Yves Bergeron– Quebec govt. gave 25-year tenure, renewable every 5 years
Universities manage and harvest the forest, selling wood to Tembec and Nexfor
No stumpage fees charged by govt. Revenues are to pay for planning, silviculture, and graduate
student research
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Case #1: The Lac Duparquet Forest
Management Planning– University researchers, and foresters from
Tembec and Nexfor form the management team– First management plan presented in 1998– Plan aimed to manage the forest through
“emulation of natural disturbance” paradigm
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Case #1: The Lac Duparquet Forest
Steps involved in developing and implementing the plan
– 1. Characterization of the historic natural disturbance regime
– 2. Use forest ecosystem classification and fire cycle modeling
– 3. Associate forest types with cohorts– 4. Develop a forest level management model– 5. Use silvicultural treatments to attain landscape level
objectives
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Step #1. Characterization of the historic natural disturbance regime
Using soil pits, researchers reconstructed fire history and mapped it:
– Completed a detailed study of frequency, severity and burn patterns
– In this region, the regime was characterized by large crown fires
– Great variation in severity– Return interval 140 years on avg.
Used this as a benchmark on which to target forest age structure
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Step # 2. Use forest ecosystem classification and fire cycle modeling
First: regional scale ecosystem classification provided information of relative proportion of site types found in the area
Using this, plus fire cycle information and knowledge of stand dynamics, they deduced:– Natural forest age structure and composition
targets
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Step # 3. Associate forest types with cohorts
Stand development was partitioned into three development stages, or, cohorts
12 forest types, based on 3 different cohort types and ecosystem classification
First cohort forest types (even-aged)– tend to have an even aged structure and are composed of pioneer
species– These dominate first 100 years following fire
Second cohort forest types (uneven-aged)– consist of surviving canopy stems from the first cohort and either
1) tolerant softwoods that were present in the understory of the first cohort, or 2) trees recruited in the understory
– Uneven-aged structure
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Step # 3. Associate forest types with cohorts
– Second cohort represents a mid-successional phase– From 75 to 175 years after disturbance– Mixed species, irregular structure
Third cohort type (irregular stand structure)– the late successional phase– First cohort canopy trees have died– Balsam fir, eastern white cedar dominate in irregular stand
structure– Assumption is that wildfire and clearcut revert most forest
types to first cohort type
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Step # 4. Develop a forest level management model
Developed an area-based forest simulation model that controls fluxes within and between forest types
Partial cutting of first and second cohort types creates second and third types respectively
Clearcutting in any cohort type creates first cohort type
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Step # 4. Develop a forest level management model
Non spatial forest level model indicates at what period harvesting and recruitment should occur in each forest type, and over how much area in order to….?– Move from the present age structure and area to
the target condition…which was based on? 1. proportion of each ecosite type 2 fire history 3. stand dynamics
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Step # 4. Develop a forest level management model
This is not unlike our approach using SFMM How does it differ?
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How Does it Differ
1. Fire history data. 2. Emphasis on maintaining cohorts (stand
structures) through partial cutting.
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Step#5. Use silvicultural treatments to attain landscape level objectives
Given a target forest, with an inverse-J age-class distribution (or cohort distribution), there is likely to be a drop in AAC
Especially in the Boreal, where short-lived species die before you can harvest them on extended rotations
Therefore use silvicultural practices to minimize impact on AAC while still:
– Maintaining structural and compositional targets of over mature stands
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First, second, and third cohorts attained using silvicultural treatments
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Step#5. Use silvicultural treatments to attain landscape level objectives
Note: Little experience in partial cutting in the region– Therefore outcomes of treatments were uncertain– Therefore designed and implemented
harvesting experiments– Silvicultural trials were established in 1998
Larger operational trials on Tembec and Norbord’s areas
Adaptive management approach
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Case #1: The Lac Duparquet Forest
They also established a control area– 2,000 ha zoned for conservation to serve as a
natural benchmark for environmental monitoring
Used for fundamental studies in natural forest dynamics and ecosystem processes
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Case #1: The Lac Duparquet Forest
Testing the Triad Zoning Approach Quebec Govt. has been slow to create
network of reserves Consensus is emerging that creation of such
a network will require compensatory increase in intensive silviculture
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Case #1: The Lac Duparquet Forest
Recall triad approach, AKA, balanced forestry?
Divide forest into zones– 1. Majority is in ecosystem management zone– 2. Certain areas on productive sites, close to
mills, are managed intensively– 3. Ecologically significant or rare critical habitats
are put into reserves
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Case #1: The Lac Duparquet Forest
The division in this forest is– 70% ecosystem management– 25% reserve (half of which is non-productive)– 5% intensive (all highly productive)
Therefore, intensive must increase yield per ha 2 and half times over normal silviculture to “break even”, i.e., sustain timber supply
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This is where the lecture ended. Students may ignore material beyond this
point.
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
1994 FMA granted to LP: 2.6 million ha, with productive land base of 584,000 ha
LP must build OSB mill in Swan Valley and develop a 10-year management plan
Plan was to be approved by Forestry Branch of Manitoba Natural Resources and Licensing Branch of Manitoba Environment
And reviewed by Canadian Wildlife Service, Department of Fisheries and Oceans,
In addition, LP had to produce an environmental impact assessment
LP chose to embrace an ecosystem management approach to managing the forest
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
Following the review period, a public environmental hearing process was conducted, by the Clean Environment Commission
– This allows interested parties to question the forest management plan and the environmental impact statement
– The hearings were well attended and lively– Concerns expressed over annual harvest volumes, mill
emissions, and LP’s track record of environmental violations in Colorado
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
Public and Community Involvement LP responded by developing a “Stakeholders
Advisory Committee”, 1995– The SAC provides a forum for expression of values from
various interest groups– LP wished to identify any resources and land uses that may
be “impacted” by the implementation of their plan– LP also held annual open houses and met individually with
environmental organizations
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
Operational Practices and Training Standard Operation Practices were developed in
consultation with Stakeholders Advisory Committee.– LP committed to train staff and operators in both operational
and ecological aspects of forest management to minimize environmental impacts. E.g.,
– New operational practices on stream crossing installation, road construction, erosion control
– Staff attended courses on natural disturbance based approaches to forest management, riparian management, and role of public participation
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
Applied Management Clearcut harvest followed by natural regeneration
was LP’s most common practice– They implemented variable retention practices, i.e.,
clearcuts with residual forest left in patches, to emulate natural disturbance
– LP operation supervisors were trained and audited (by third party) annually on correct implementation
– Blocks were rated on adherence to work permit instructions
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
Inventory and Monitoring Pre-harvest survey program was developed
to determine distribution and abundance of wildlife habitat of every potential harvest site– These data were used with short and long term
planning– 18,000 plots have been completed (vegetation,
soil, timber, non-timber attributes measured) + 450 permanent plots (to act as controls)
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
LP also developed a new Forest Lands Inventory Program– Three components
1. forest lands inventory 2. ecosite inventory 3. terrain and landform inventory
This will provide the basis for planning on an ecosystem basis
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
LP also committed (1997) to funding a bird monitoring program, to evaluate the effectiveness of variable retention– I.e., adaptive management– 2,200 point count stations across the forest– 218 species
LP has reduced harvesting in May, June, and July– bird nesting season
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
Aquatic Ecosystems The potential for harvest effects related to
water quality and peak flows were difficult to estimate without baseline data– DFO allowed LP to operate on not more than 30%
of a watershed (5 year delay for hardwood, 15 for conifer) until watershed impact analysis is completed by LP
32
Case #2: Louisiana-Pacific in Swan Valley, Manitoba
Research Program– Priority is to understand natural disturbance
regime of their region– Collect historical data on
fire frequency, size, and severity Insect and disease dynamics
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Case #2: Louisiana-Pacific in Swan Valley, Manitoba
Understand stand dynamics and successional pathways
Develop reliable targets for long term plans aimed at emulating natural disturbance
In addition, scientific advisory committee is developing forestry effects monitoring program to provide adaptive management framework