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Groundcover Restoration in Forests of the Southeastern United States

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Chapter 3: Tailor<strong>in</strong>g <strong>Restoration</strong> Strategies to Initial Site Conditions(Sch<strong>in</strong>us tereb<strong>in</strong>thifolius). A p<strong>in</strong>e rockland restorationundertaken by <strong>the</strong> Miami-Dade Natural Areas Management,<strong>the</strong> Florida Department <strong>of</strong> Transportation, and FairchildTropical Garden required <strong>the</strong> chipp<strong>in</strong>g <strong>of</strong> a monoculture<strong>of</strong> Brazilian pepper, leav<strong>in</strong>g only a sparse canopy <strong>of</strong> southFlorida slash p<strong>in</strong>e and a mulch layer 10-30 cm deep(Wendelberger et al. 2008). In this study, 68 native speciesrecruited from <strong>the</strong> seed bank although 5 non-native specieswere also present (Wendelberger et al. 2008). In contrast,m<strong>in</strong>e restoration sites are usually completely devoid <strong>of</strong>vegetation and <strong>the</strong> high degree <strong>of</strong> soil disturbance precludes<strong>the</strong> germ<strong>in</strong>ation <strong>of</strong> seed bank species. In some m<strong>in</strong>ereclamation sites, topsoil from sites that will be m<strong>in</strong>ed isplaced on <strong>the</strong> disturbed m<strong>in</strong>e sandtail<strong>in</strong>gs and overburdento provide propagules for revegetation (Roth, <strong>in</strong> prep.). Ino<strong>the</strong>r sites, sandtail<strong>in</strong>gs and overburden are directly seededwith bulk green silage (Pfaff and Gonter 2000; Roncoby2004).Monitor<strong>in</strong>g: The sites are cont<strong>in</strong>uously monitored for<strong>in</strong>vasive species establishment. Herbaceous groundcover is monitored by species us<strong>in</strong>g percent coverage<strong>in</strong> random quadrats. In addition, photopo<strong>in</strong>t data arecollected.EXAMPLE 4. Disney Wilderness Preserverestoration <strong>of</strong> improved pasture to longleaf p<strong>in</strong>esandhill habitat (canopy lack<strong>in</strong>g, groundcoverlack<strong>in</strong>g).Goal: Restore longleaf p<strong>in</strong>e sandhill communities onsodgrass pasture lands<strong>Groundcover</strong> restoration at The Nature Conservancy’s DisneyWilderness Preserve <strong>in</strong> Kissimmee, FL. Credits: TNC/Chris Matson.Fuels Present: NoInvasives Present: Yes<strong>Restoration</strong> Activities: Invasive control. Herbicideapplication by tractor or helicopter mountedbroadcast sprayers a m<strong>in</strong>imum <strong>of</strong> twice dur<strong>in</strong>g <strong>the</strong>grow<strong>in</strong>g season. Prescribed fire. All sites are burnedpre-seed<strong>in</strong>g to remove biomass. Prescribed fire isre-<strong>in</strong>itiated 3 years post-seed<strong>in</strong>g but prior to treeand shrub plant<strong>in</strong>g. Seed<strong>in</strong>g. The sites are seededwith wiregrass and bulk collected seeds collectedon site with a flail-vac harvester us<strong>in</strong>g a grasslander.Hand collected seeds <strong>of</strong> small smooth-seeded speciessuch as panic grasses (Panicum spp.) and yelloweyedgrasses (Xyris spp.) are seeded by hand withhome-made shaker bottles. Mow<strong>in</strong>g. Sites are mowed<strong>the</strong> first year to reduce cover and seed<strong>in</strong>g <strong>of</strong> earlysuccessionalspecies such as dogfennel. Plant<strong>in</strong>g.Longleaf p<strong>in</strong>e trees are planted at 5 trees per acre andupland shrubs at 20 plants per acre after groundcoverspecies are established.| 34 |

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