Lincoln National Forest Land Management Plan Revision and Environmental Impact Statement
Vegetation and Habitat
What we heard from the public
Support for the use of mechanical thinning and prescribed burning to encourage growth of grasses, forbs, young shrubs, and trees which provide critical forage and cover for elk and other species.
Forest needs thinning.
Preserve old or large trees while maintaining structural diversity and resilience. Large and old trees, especially those established before ecosystem disruption by Euromerican settlement, are important forest components and critical to functionality of ecosystem processes.
Please don't change the beautiful forest much with intentional, artificial, prescribed burning. Plants feel fear and pain of fire and burning. Dead sticks and logs can also be used for building things and firewood for wood stoves, fireplaces, and camp fires.
Draft EIS Alternatives
Alternatives A, B, D and E: Mechanically thin 900-1400 forest acres annually
Alternative C: Mechanically thin 500-800 forest acres annually.
Alternatives A, B, D and E: Mechanically thin 200-450 woodland acres annually
Alternative C: Mechanically thin 50-150 woodland acres annually.
Alternatives: Prescribed/Managed Wildfire 20,000 acres annually
Draft Land Management Components
Desired Conditions for All Vegetation Types
Ecosystems maintain all of their essential components (plant density, species composition, structure, coarse woody debris, and snags), processes (disturbance and regeneration), and functions (nutrient cycling, water infiltration, and carbon sequestration). Overall plant composition similarity to site potential (FSH 2090.11) averages greater than 66 percent, but can vary considerably at the fine- and mid-scales owing to a diversity of seral conditions.
Ecosystems contain a mosaic of diverse native plants (composition and genetic diversity) with vegetative structural diversity that encourages vigor, connectivity, and persistence at a variety of scales across the landscape, reflecting their natural disturbance regimes.
Native plant communities dominate the landscape, while invasive species are nonexistent or low in abundance (less than 5 percent) and do not disrupt ecological functioning.
Natural ecological cycles (energy, hydrologic, nutrient, etc.) facilitate the shifting of plant communities, structure, and ages over time due to natural ecological processes (such as climate fluctuations and fire) affecting site conditions.
Native insects and diseases affect forest communities within their range of natural variability. Nonnative insects and diseases are nonexistent or low in abundance (less than 5 percent) and do not disrupt ecological functioning.
Vegetation cover and litter are distributed across the soil surface in adequate amounts to limit erosion and contribute to soil deposition and development. Soil cover and herbaceous vegetation protect soil, facilitate moisture infiltration, and contribute to plant and animal diversity and ecosystem function.
Ecosystems are resilient or adaptive to the frequency, extent, and severity of disturbances, such as fire in fire-adapted systems, flooding in riparian systems, insects, pathogens, and climate variability.
The composition, structure, and function of vegetation conditions are resilient to the frequency, extent, and severity of disturbances, and to climate variability.
Vegetation communities reflect their natural physical, chemical, and biophysical processes with carefully managed human influence.
Non-climate ecosystem stressors (air and water pollution, high road densities, water depletions, etc.) do not negate the resilience and resistance of an ecosystem’s ability to adapt to a changing climate.
Natural disturbance regimes, including fire, function in their natural ecological role. Uncharacteristic fire (frequency and severity outside historical range for associated vegetation type) is less than 10 percent or absent on the landscape.
Native insects and diseases affect forest communities within their range of natural variability. Nonnative insects and diseases are nonexistent or low in abundance (less than 5 percent) and do not disrupt ecological functioning.
Landscape vegetation structure and patterns create a mosaic that disrupts large continuous areas of uncharacteristic high-severity fire effects.
Healthy, resilient vegetation contribute to the forest’s ability to store carbon and function as a sustainable carbon sink.
The ecological attributes and processes that provide habitat for native animal and plant life and/or historic and cultural values are fully functioning.
A diversity of vegetation exists with a mosaic of cover types and stand structures forming a healthy, resilient landscape that provide for genetic exchange, daily and seasonal movements of animals, including inter-specific interaction at all trophic levels (producer-consumer and predator-prey interactions) across multiple spatial scales, and consistent with existing landforms and topography.
Vegetation provides a sustainable supply of forest and botanical products, such as timber products, firewood, piñon nuts, and forage, consistent with desired conditions for other resources.
All Vegetation Types Objectives
(Objectives for all vegetation types are based on previous Lincoln National Forest accomplishments, anticipated need, and estimated future accomplishment based on capacity).
Over a 10-year period, complete at least the following treatments to move vegetation resources toward desired conditions.
Mixed conifer with aspen: mechanically treat 1,000-3,000 acres along with prescribed fire or naturally ignited wildfire on 40,000 acres
Mixed conifer with frequent fire: mechanically treat 6,000-8,000 acres along with prescribed fire or naturally ignited wildfire on 40,000 acres
Ponderosa pine forest: mechanically treat 2,000-3,000 acres along with prescribed fire and naturally ignited wildfire on 40,000 acres
Piñon-juniper woodland: mechanically treat 1,000-3,000 acres along with prescribed fire and naturally ignited wildfire on 40,000 acres
Piñon-juniper grassland: mechanically treat 1,000-2,500 acres along with prescribed fire and naturally ignited wildfire on 20,000 acres
Piñon-juniper evergreen shrub: prescribed fire and naturally ignited wildfire on 20,000 acres
Over a 10-year period, complete 400 to 1,000 acres of combined vegetation treatments (such as restoration) non-forested areas that are highly departed from historical conditions to move vegetation toward desired conditions. Treatments may include mechanical treatments, prescribed fire or naturally ignited wildfires, seeding, or other techniques still to be determined by best available science depending on the specific ecological response unit.
All Vegetation Types Guidelines
Management activities should favor the retention of species that naturally occurred in those ecosystems in characteristic proportions.
In areas with reasonable assurance of successful regeneration, aspen sprouting should be stimulated in areas that have or previously had aspen, by clearcutting, conifer removal, or fire where desired conditions indicate a need for early seral structures (see individual forested ecological response units).
Slash piles should be burned in locations and at times that will facilitate managing forest vegetation towards desired conditions.
Lincoln national forest vegetation management projects should not remove large diameter trees, snags, and shrubs.
Activities should provide resiliency against potential climate changes by promoting early seral tree species regeneration and identifying and maintaining refugia in cooler moister microsites.
Chemical application techniques (such as chemical-free buffers or spot treatments) should be applied to minimize negative effects.
Note: Individual vegetation types have additional plan components
Next Station: At-risk Species
For more information on the project or to be added to the mailing list, please contact Diane Prather at (575-649-9405) or diane.prather@usda.gov.