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San Bernardino National Forest Land Management Plan - Part 2

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<strong>Land</strong> <strong>Management</strong> <strong>Plan</strong> <strong>Part</strong> 2<br />

<strong>San</strong> <strong>Bernardino</strong> <strong>National</strong> <strong>Forest</strong> Strategy<br />

September 2005<br />

wildlife habitat, increasing vegetation cover to reduce post-fire soil erosion, maintaining mixed<br />

conifer forests in a condition less susceptible to stand replacement fire, or maintaining reduced<br />

fuel loads adjacent to communities to decrease the threat of losing homes in wildland fires.<br />

The Vegetation <strong>Management</strong> Program emphasizes restoring forest health and community<br />

protection, (FH 2 - Prevent Type Conversion), (FH 3 - Restoration of <strong>Forest</strong> Health), and (Fire 2<br />

- Direct Community Protection). Other forest restoration projects will be located further into the<br />

national forest, away from structures, but they will still have the goal of community protection<br />

(Fire 5 - Fuelbreaks and Indirect Community Protection). Over the next three to five years, these<br />

vegetation treatments will be strategically integrated to maximize community protection efforts<br />

and minimize wildland fire size, while considering habitat needs. Mortality removal will be<br />

integrated with thinning within community defense and threat zones. Program goals include<br />

completing approximately 20 percent of identified treatment needs. <strong>Plan</strong>s are expected to include<br />

strategically locating fuels treatments in order to take advantage of burned areas. The mix of<br />

these activities will vary through time and across sites, but the national forest anticipates an<br />

average annual need of 10,000 acres of fuels and vegetation reduction activities, and up to 1,000<br />

acres per year of reforestation activities (FH 1 - Vegetation Restoration). The<br />

location and prioritization will be determined using site-specific prescriptions<br />

developed to guide appropriate implementation for the various objectives<br />

described above.<br />

• Mortality Removal - Annual Need: Included below. This includes<br />

the removal of dead vegetation to reduce fire hazard. This category<br />

includes the use of timber sales to remove merchantable trees, and the<br />

contract removal of non-merchantable trees and shrubs. These<br />

projects include treatment of all slash and are expected to move<br />

forested areas from Condition Class 3 towards Condition Class 1. In<br />

chaparral areas, mortality removal is planned in order to reduce the<br />

fire hazard from high to low.<br />

• Thinning - Annual Need: Included below. This includes the<br />

removal of living trees from overstocked stands, in most cases trees<br />

Barton Flats,<br />

using a<br />

helicopter to<br />

remove dead<br />

trees<br />

of 24 inches in diameter or less. These projects include the treatment of all slash and are<br />

expected to move forested areas from Condition Class 2 or 3 toward Condition Class 1.<br />

Thinning is required prior to the reintroduction of fire in most cases.<br />

• Reforestation And Restoration Of <strong>Forest</strong> Vegetation - Annual Need: 1,000 acres.<br />

Restoration projects are either designed to facilitate natural recovery following<br />

disturbance (fire, drought related mortality, insect and disease) or to implement planting<br />

projects as needed when natural processes are not likely to achieve desired results.<br />

• Fuelbreak Maintenance - Annual Need: 1,000 acres. Existing fuelbreaks are generally<br />

maintained using prescribed fire or mechanical treatments, such as the use of chainsaws<br />

or masticators. Most of the fuelbreaks are in high hazard chaparral areas and are<br />

designed to limit wildland fire size by providing for firefighter access and improved<br />

firefighter safety. A few of the fuelbreaks are in coniferous forest and serve to limit fire<br />

spread from or towards communities or timber stands in poor condition. Most of the<br />

existing fuelbreaks are on ridgetops or along roads.<br />

Page 26

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