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Decision Notice and Finding of No Significant Impact South Fowl ...

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soils. Where located on the bench area, there is expected to be no overl<strong>and</strong> flow<br />

<strong>of</strong> water to cause erosion.<br />

Where the parent material <strong>and</strong> soils change toward the east end <strong>of</strong> the route, the<br />

topography is flatter <strong>and</strong> more similar to that on which we have currently several<br />

trails located. Experience shows erosion is not significant.<br />

Similarly, water quality will not be significantly affected by either Alternative.<br />

Potentially minor amounts <strong>of</strong> sediments may be produced by this action.<br />

However, it is highly unlikely sediments will move from the trail surface, let<br />

alone reach the slopes down toward Royal Lake (see Appendix A). There will be<br />

no heavy equipment in the riparian areas. Each Alternative will have an approach<br />

to <strong>South</strong> <strong>Fowl</strong> Lake for access to <strong>and</strong> from the lake. The riparian impacts <strong>of</strong><br />

clearing brush will not affect ecological function, will not be intensive <strong>and</strong> will<br />

meet water quality st<strong>and</strong>ards found in the Forest Plan on page 2-13 through 15.<br />

There will not be a loss <strong>of</strong> wetl<strong>and</strong>s, nor a significant change to wetl<strong>and</strong>s <strong>and</strong><br />

hydrologic function. Alternative 2 crosses roughly 100 feet <strong>of</strong> lowl<strong>and</strong> cedar on<br />

State l<strong>and</strong> as the route descends from the bench. Alternative 4 crosses a similar<br />

stretch near McFarl<strong>and</strong> Lake. Snowmobile trails are not uncommon in wetl<strong>and</strong><br />

areas <strong>and</strong> experience has shown me that there are effects to the vegetation upon<br />

which the trail is located but, minimal if any, indirect effects to surrounding<br />

vegetation <strong>and</strong> normal water flows are maintained.<br />

My approach to approving two alternatives is different than normal, but I am<br />

confident the effects have been displayed for each <strong>of</strong> these alternatives. One or<br />

the other will be implemented, not both at the same time. It could be that<br />

Alternative 2 is put in place <strong>and</strong> through use <strong>of</strong> the criteria in this decision, it is<br />

later determined that Alternative 4 should be constructed. In that event<br />

Alternative 2 will be obliterated prior to construction <strong>of</strong> Alternative 4. The only<br />

impacts between the two that might be cumulative are soil related. Cumulative<br />

impacts between the two, similar to a 100 foot driveway (EA pg 41), are so very<br />

minor that together, they wouldn’t be significant.<br />

3. Social impacts are <strong>and</strong> will be present. It has been interesting attempting to<br />

determine exactly what the social impacts are. Some folks talk about the<br />

economics from construction. In the context <strong>of</strong> typical budgets for the Superior<br />

National Forest, those are not significant for any Alternative, even if the accuracy<br />

was <strong>of</strong>f by 100%. Wilderness impacts from the perspective <strong>of</strong> sights <strong>and</strong> sounds<br />

are primarily social impacts. These impacts are generally what the debate has<br />

been about over the past two years. It is the same, at times very heated, debate<br />

that has been going on for the last few decades as to what is the proper<br />

management for both the Superior National Forest <strong>and</strong> the BWCAW. CEQ<br />

1508.14 “Human environment” provides guidance on social impacts.<br />

35

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