Prior Prevalence of Shortleaf Pine-Oak-Hickory Woodlands in the Tallahassee Red Hills Author(S): Andre F

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Prior Prevalence of Shortleaf Pine-Oak-Hickory Woodlands in the Tallahassee Red Hills Author(S): Andre F Prior Prevalence of Shortleaf Pine-Oak-Hickory Woodlands in the Tallahassee Red Hills Author(s): Andre F. Clewell Source: Castanea, 78(4):266-276. 2013. Published By: Southern Appalachian Botanical Society DOI: http://dx.doi.org/10.2179/13-022 URL: http://www.bioone.org/doi/full/10.2179/13-022 BioOne (www.bioone.org) is a nonprofit, online aggregation of core research in the biological, ecological, and environmental sciences. BioOne provides a sustainable online platform for over 170 journals and books published by nonprofit societies, associations, museums, institutions, and presses. Your use of this PDF, the BioOne Web site, and all posted and associated content indicates your acceptance of BioOne’s Terms of Use, available at www.bioone.org/page/ terms_of_use. Usage of BioOne content is strictly limited to personal, educational, and non-commercial use. Commercial inquiries or rights and permissions requests should be directed to the individual publisher as copyright holder. BioOne sees sustainable scholarly publishing as an inherently collaborative enterprise connecting authors, nonprofit publishers, academic institutions, research libraries, and research funders in the common goal of maximizing access to critical research. CASTANEA 78(4): 266–276. DECEMBER Copyright 2013 Southern Appalachian Botanical Society Prior Prevalence of Shortleaf Pine-Oak-Hickory Woodlands in the Tallahassee Red Hills Andre F. Clewell* Tall Timbers Research Station, 13093 Henry Beadle Drive, Tallahassee, Florida 32312 ABSTRACT Shortleaf pine-oak-hickory woodlands provided the principal vegetation cover in the Tallahassee Red Hills prior to land clearing for plantation agriculture in the 19th century. Ample historical documentation and extant remnants of that community, including old-growth, support this conclusion. This woodland was maintained by surface fires and consisted principally of open stands of shortleaf pine, post oak, Spanish oak, black oak, mockernut hickory, and dogwood. The species- diverse and predominantly herbaceous ground cover was dominated by grasses, legumes, and composites. Coppice sprouting of trees and shrubs after fires was common. In the absence of fire, shortleaf pine-oak-hickory woodlands convert to oak-hickory forest with similar tree species composition and loss of herbaceous species. Within the past 130 years, nearly all stands of shortleaf pine-oak-hickory woodlands and oak-hickory forests have been extirpated or compromised beyond recognition by intrusions of offsite tree species that are typical of moist soils at less elevated landscape positions. Key words: Apalachee, climax, ecotone, longleaf pine, magnolia-beech, mesophication, Tallahassee Red Hills, Tall Timbers. INTRODUCTION The Tallahassee Red other regions in their scarcity or absence of Hills region was mapped by Roland Harper saw-palmetto and wire-grass among the (1914) as an 880 km2 physiographic unit of undergrowth. Both short-leaf and long-leaf northern Leon County, Florida, lying north of the pine forests are subject to occasional fires. Cody scarp and extending a short distance into On some of the hillsides and richer uplands adjacent Grady and Thomas counties, Georgia dense hardwood forests with considerable (Figure 1). Harper characterized the Tallahassee humus can be seen, and the branches and Red Hills (TRH) by their deep deposits of red creeks are bordered by wet woods or sandy clay and rather hilly topography in which swamps. (p. 271) streams were scarce and lakes and ponds common. Harper (1914) described upland vege- Species listed by Harper (1914, with updated tation in the TRH: nomenclature) that occur in ‘‘uplands’’ or ‘‘dry woods’’ included P. echinata (Chapm. ex En- The drier uplands seem to have been gelm.) Vasey ex Sarg. (shortleaf pine), Cornus covered originally with comparatively open florida L. (flowering dogwood), Quercus falcata forests of short-leaf pine (Pinus echinata), Michx. (Spanish or southern red oak), Carya red oak, hickory, dogwood, etc. Consider- tomentosa Nutt. (mockernut hickory), Carya able areas of this forest still remain, though glabra (Mill.) Sweet (pignut hickory), Q. stellata a good deal of it may be second growth. On Wangenh. (post oak), Q. velutina Lam. (black sandier soils near the center of the region oak), Nyssa sylvatica Marshall (blackgum), and there are limited areas (perhaps several Oxydendrum arboreum (L.) DC. (sourwood). In hundred acres) of long-leaf pine forest, this paper, I call this vegetation the shortleaf differing from the typical piney woods of pine-oak-hickory (SPOH) woodland community. Shortleaf pine-oak-hickory woodland is a pyro- *email address: [email protected] Received May 24, 2013; Accepted September 6, 2013. genic community, which, in the absence of fire, DOI: 10.2179/13-022 will convert to a closed canopy oak-hickory 266 2013 CLEWELL: SHORTLEAF PINE-OAK-HICKORY WOODLANDS 267 vegetation that occur elsewhere in the South- east, principally inland towards the continental interior. Beginning in the late 19th century in response to land usage, offsite tree species from less elevated positions in the landscape invaded the remaining original open woods described by Harper (1914) and eventually compromised the species composition of nearly all of them beyond recognition. Most offsite species were typical of flood plains and other sites that approach wetland status. They included Acer rubrum L. (red maple), Liquidambar styraciflua L. (sweet- gum), Pinus taeda L. (loblolly pine), Quercus laurifolia Michx. (diamond-leaf oak), Q. nigra L. (water oak), and Q. virginiana Mill. (live oak). Other offsite species were typical of magnolia-beech forest (Fagus grandifolia Ehrh., Figure 1. The Tallahassee Red Hills according to Harper Magnolia grandiflora L.), particularly Prunus (1914) superimposed on a map by Griffith et al. (2001) showing the western end of Level IV ecoregion 65o. The serotina Ehrh. (black cherry) and Magnolia location of Tall Timbers Research Station is indicated by grandiflora. I call this spontaneously occurring ‘‘TT.’’ secondary forest the water oak-sweetgum-lob- lolly pine community, after three of its most forest. The inclusion of Oxydendrum arboreum abundant and characteristic species. Several in the SPOH woodland community, as intimated upland species contributed to this community by Harper (1914), is disputable; sourwood on upland sites, particularly P. echinata, C. occurs on relatively steep gradients leading from florida, and Quercus hemisphaerica W. Bartram SPOH woodlands to the heads of springs and ex Willd. (laurel oak), which either persisted seeps, and it is better considered an ecotonal after offsite colonization began or established species at the upland border with forested seedlings concurrently with offsite species. wetlands. Quercus hemisphaerica is becoming increasing- The TRH region lies within the western one- ly abundant in the TRH on unburned sites with third of the Tallahassee Hills/Valdosta Limesink well drained soils. Level IV ecoregion (Griffith et al. 2001, mapping Trees that contributed to the water oak- unit 65o). The TRH are commonly conceived to sweetgum-loblolly pine community were spared extend northward at least to Thomasville and from land clearing in the 19th century, because eastward to the Aucilla River, but soils in these the land where they grew was too moist for outlying areas are not as consistently clayey. The agricultural purposes or was protected from TRH form part of a larger physiographic unit lethal fires. Their establishment on abandoned called the Tallahassee Hills Northern Highlands agricultural land was facilitated by the absence consisting of the dissected sedimentary remains of competing trees (Clewell 2011). Upland tree of Neogene fluvial, and delta plain, deposits species were at a disadvantage in colonizing (Schmidt 1997). Upland soils belong to the abandoned agricultural fields, because land Norfolk-Ruston-Orangeburg association (Beck- clearing for agriculture had substantially re- enbach and Hammett 1962). A preponderance of duced the cover of SPOH woodlands that could broadleaved hardwood tree growth distinguishes serve as seed sources. Once established on the TRH from vegetation in surrounding regions, upland sites, water oak-sweetgum-loblolly pine which are, or were formerly typified by, longleaf forests persist indefinitely (Van Lear 2004) by pine-wiregrass savannas (Pinus palustris Mill., means of mesophication (Nowacki and Abrams Aristida stricta Michx.) (Harper 1914, Clewell 2008). Mesophication occurs when fire-main- 1986). Broad regions covered by these savannas tained open SPOH woodlands become closed- isolate the TRH and its predominant SPOH canopied in the absence of fire, which favors vegetation from lands with similar soils and colonization by shade-tolerant and fire-sensitive 268 CASTANEA VOL.78 plant species that produce a less flammable fuel Southeast, collectively called Seminoles, assem- bed. This process promotes rapid compositional bled in the area in small numbers but were and structural changes without ecological ante- driven out by General Andrew Jackson in 1818. cedent. By the latter half of the 20th century, Spain ceded Florida to the United States in 1821 Harper’s descriptions of original vegetation were (Tebeau 1971). forgotten, and ecological opinion accepted for- The TRH were essentially unoccupied from ests dominated by offsite species as natural 1704 until the U.S. Territory of Florida was stages of succession leading towards a climax established in 1824 with Tallahassee as its
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