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<br />Page 4 <br />April 23, 1991 <br />Snyder Tree Planting <br />Corrective Action Plan <br />Dan Hernandez <br />ROAD DISTURBANCE AREA /{3: This site has the deepest soils, the <br />most gradual planting area, and the potential for a tree density on the <br />upper two thirds that exceeds the average in surrounding areas. The <br />lower third is somewhat like area #2, although somewhat less severe. <br />Invasion rates on the lower third will probably be higher than it is on <br />the upper two thirds. Competition for the first two years will be l~~w, <br />but in years three through perhaps eight competition between trees and <br />grass for nutrients, light, and moisture will be intense. During th~it <br />time, the trees should gain functional dominance in the community <br />structure and begin to force out much of the ground cover and/or alter <br />its composition. Thus years three through about eight will largely <br />determine the vegetation character of the site for the next several <br />hundred years. <br />ROAD DISTURBANCE AREA /{4: This site is steeper than J{3, exhibii:s <br />good soil cover, and should produce a tree density that is close to or <br />possibly above the average for this side of the canyon. In many <br />respects it is a smaller version of #1 without the dense grass cover. <br />Invasion should not be significant on this site and should be easily <br />distinguished from the planted vegetation. Like area $3, years three <br />through about eight will largely determine the character of the <br />vegetation on this site for the next few hundred years. <br />MONITORING: It is recommended that monitoring be done twice a year. <br />Replacement of tree markers could be done as needed, except on Road <br />Disturbance #2 where no entry on to the slope should be allowed except <br />for replanting. Spring saseasments (late May or early June) can provide <br />a clear measure of winter kill. Eall assessments (September or Octot~er) <br />can measure survival rates, vegetative condition, and growth rates. <br />Actual counts, condition assessments, and tree height measurements cen <br />be made on road disturbance areas 1, 3, and Q. A scaling monocular in <br />combination with a rangefinder would be useful for examining Area #2 <br />from the roadside until after 1993. <br />Williams Canyon should be examined by standard sampling techniques. <br />It is recommended that a circular or a rectangular quadrat oriented <br />parallel to the contours be used in sampling the vegetation in Williams <br />Canyon. These shapes or orientations will help reduce bias in the data <br />due to linear vegetation patterns parallel to the slope. It is likely <br />that such a pattern will exist for the next several years and could <br />cause severe statistical distortion in the sampling. This pattern, <br />although not extreme, is the result of the type of disturbing agent that <br />caused the damage. Each small tree included in the samples should be <br />examined in an attempt to distinguish between planted trees and invader <br />