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manufacturer's safety recommendations is critical, including the use of appropriate <br />protective equipment such as chemical resistant gloves and eye protection. <br />If cut brush is piled, it should be in areas where the least amount of native cover exists. <br />Potential sites for stacking cut material are on top of larger stumps, rock outcrops, bare <br />soil, and the adjacent crop fields. Brush piles for burning should ideally be constructed <br />in layers with alternating limb directions. Keeping these piles small in basal area but tall <br />makes burning them easier and minimizes soil sterilization. Piles can be burned during <br />most times of the year after the material has had a chance to dry out, but winter is often <br />the best. Snow cover greatly reduces the threat of soil sterilization and unintentional <br />burning of adjacent areas. <br />Other Invasive Species Control <br />Although an inventory was conducted for the area and no significant nonnative species <br />problems noted beyond buckthorn and similar species, there is still a possibility that new <br />problem species will show up or was missed during the inventory process. Detailed <br />inspections should be made at least annually for early detection of problem species on <br />the site, particularly garlic mustard. <br />An integrated resource management activity approach should be used that minimizes <br />the presence of these species, with as little impact on native species as possible. <br />Potential methods for management of problem species include cutting, mowing, spot <br />herbicide application, hand removal, introduction of native species that provide <br />competition, burning, and biological controls. For additional information, see the <br />problem species management section. <br />Oak Recruitment and Release <br />During this phase of restoration, the earlier control of nonnative shrubs and invasive <br />trees, as well as prescribed burning should begin to show results for oak seedling and <br />sapling recruitment. If oak saplings are .found in areas where the canopy above them is <br />dominated by weedy species of trees, selective cutting should be used to release the <br />oaks and provide the opportunity for them to graduate into the canopy. Cutting of <br />boxelder, cottonwood, or aspen to create canopy gaps that enable oak saplings to <br />mature is most preferable. Less preferable is the cutting of other native hardwoods <br />including black cherry, hackberry and other similar species. Although young elm are <br />common in some areas of the forest and may currently hinder the development of some <br />oak saplings into mature trees, the elms will likely fall victim to Dutch elm disease and <br />may not need to be cut to release oaks in their shade. <br />Prescribed (Rx) Fire <br />This activity will be important for maintaining the oak component of this forest and <br />should be considered for application to any given area approximately once every 5-15 <br />years. A few of the positive aspects of well-timed prescribed burning include the <br />Top of fhe World Park Addition Natural Area Management Plan 12 <br />