Overview

Comprehensive Description

Description

General: Slash pine (Pinus elliottii) is one of the hard yellow pines indigenous to southeastern United States. The slash pine is a medium to large tree that reaches heights of 80' to 100' tall. It has a round top and "brooms" of needles at the ends of the branches. Its’ needles may be 5" to 11" long and are borne 2 to 3 to a fascicle. The orange-brown bark is scaly with plates. It is durable and hard, nearly equivalent to that of longleaf pine (Pinus palustrus). It has thick, plate-like bark with an extensive root system, and a moderate taproot. Its cones measure 8-16 cm (3 – 6 inches) long, and are a glossy brown color. And the cone scales are thin with fine prickles

Pinus elliottii var. elliottii is found in the Coastal Plain of north and Central Florida. Whereas, the Southern slash pine or Pinus elliottii var,. densa is found in South Florida, West Indies, Guatemala, and Honduras in Central America.

The slash pine is commonly associated with the loblolly pine (Pinus taeda); however, the length and number of needles per fascicle, cones, and bark can be used to differentiate them.

Distribution: The slash pine can be found on coastal plains throughout the Indian River Lagoon area, and in freshwater upland areas. It occurs on coastal plains from South Carolina to Central Florida, and west to Louisiana. The Pinus elliottii occurs from Central Florida through South Florida and the Florida Keys. Slash pine was introduced in Kentucky, Virginia and eastern Texas in the 1900's, and now reproduces naturally within these states.

Habitat: The climate within the natural range of slash pine is warm and humid, and it likes wet summers, drier falls and springs. It grows well with rainfall averages about 1270 mm (50 in) per year, and summer rains of 13 mm (0.5 in) or more occur about four times per month. The mean annual temperature in the slash pine region is 17° C (63° F), with extremes of 41° C (106° F) and -18° C (0° F), and a growing season of 250 days. The slash Pine grows well on a variety of acidic soils in full sun or partial shade. It does poorly in basic soil (high pH) and is not recommended for irrigation water has a high pH. Once established, it is more tolerant of wet sites than most other pines and is moderately salt-tolerant. It is not highly drought-tolerant, but more so than most other pines. The horizontal branches break easily in ice storms. It is not recommended to plant the tree too close to high traffic areas, since shaded lower branches, die and drop, as the tree grows taller. This is dangerous because branches could fall on people or vehicles, unless there is a regular maintenance plan to remove them.

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Source: USDA NRCS PLANTS Database

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Distribution

Pinus elliottii Engelm.:
United States (North America)
South Africa (Africa & Madagascar)
China (Asia)
Brazil (South America)
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National Distribution

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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P. elliottii var elliottii occurs on coastal plains from South Carolina to Central Florida, and west to Louisiana. P. elliottii var densa occurs from Central Florida through South Florida and the Florida Keys. Slash pine has also been introduced into Kentucky, Virginia and eastern Texas, and now reproduces naturally in these locations. Slash pine occurs on coastal plains throughout the Indian River Lagoon area, most commonly in freshwater upland areas.
  • Abrahamson, W.G. 1984. Species response to fire on the Florida Lake WalesRidge. American Journal of Botany. 71(1): 35-43.
  • Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: Myers, R.L. and J.J. Ewel, eds. Ecosystems of Florida. University of Central Florida Press, Orlando, FL. pp. 103-149.
  • Anderson, R. 1988. Guide to Florida trees. Winner Enterprises, USA. 68 pp. ISBN 0-932855-20-2.
  • Breininger, D.R. and R.B. Smith. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2):223-240.
  • Duncan, W.H. and M.B. Duncan. 1988. Trees of the southeastern United States. University of Georgia Press, Athens, GA. 322 pp.
  • Eyre, F.H., ed. 1980. Forest cover types of the united States and Canada. Society of American Foresters, Washington, D.C. 148 pp.
  • Harlow, W.M., E.S. Harrar, S. Ellwood, F.M. White. 1979. Textbook of dendrology. 6th edition. McGraw-Hill, Inc. New York, NY. 510 pp.
  • Hebb, E.A. and A.F. Clewell. 1976. A remnant stand of old-growth slash pine in the Florida panhandle. Bulletin of the Torrey Botanical Club. 103(1):1-9.
  • Jackson, J.A. 1971. The evolution, taxonomy, distribution, past populations and current status of the red-cockaded woodpecker. In: Thompson, R.L., ed. The ecology and management of the red-cockaded woodpecker: Proceedings of a symposium. May 26-27, 1971, Folkston, GA. Tall Timbers Research Station, Tallahassee, FL. pp. 4-29.
  • Landers, J.L. 1991. Disturbance influences on pine traits in the southeastern United States. In: Proceedings, 17th Tall Timbers fire ecology conference; May 18-21, 1989, Tallahassee, FL. Tall Timbers Research Station, Tallahassee, FL. pp. 61-95.
  • Langdon, O.G. and F. Bennett. 1976. Management of natural stands of slash pine. Res. Pap. SE-147. U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, Ashville, NC. 12 pp.Lohrey, R.E. and S.V. Kossuth. 1990. Pinus elliottii Englem. slash pine. In: Burns, R.M. and B.H. Honkala, technical coordinators. Silvics of north America. Volume 1. Conifers. Agricultural Handb. 654. U.S. Department of Agriculture, Forest Service, Washington, D.C. pp. 338-347.
  • McCune, B. 1988. Ecological diversity in North American pines. American journal of Botany. 75(3):353-368.
  • McCulley, R.D. 1950. Management of natural slash pine stands in the flatwoods of south Florida and north Florida. circular No. 845. U.S. Department of Agriculture, Washington, D.C. 57 pp.
  • Monk, C.D. 1968. Successional and environmental relationships of the forest vegetation of north central Florida. American Midland Naturalist. 79(2): 441-457.
  • Wade, D.D. 1983. Fire management in the slash pine ecosystem. In: Proceedings of the managed slash pine ecosystem, 1981, Gainesville, FL. University of Florida, School of Forest Resources and Conservation, Gainesville, FL. pp. 203-227; 290-294; 301.
  • Wright, H.A. and A.W. Bailey. 1982. Fire ecology: United States and southern Canada. John Wiley and Sons, Inc. New York, NY. 501 pp.
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© Smithsonian Marine Station at Fort Pierce

Source: Indian River Lagoon Species Inventory

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Adaptation

The slash pine grows in the infertile soils of sandhills, flatwoods, and near wet lowlands, such as swamps and ponds. Soils within its range are mostly Spodosols, Ultisols, and Entisols. Spodosols, Entisols are common along the coasts of Florida while the Ultisols are in the northern part of the range. Originally, slash pines were found in moist, well-drained aerated soils, of the southeastern United States, particularly along pond, stream, and lake margins. This habitat preference is a reflection of the susceptibility of the seedlings to fire, with the advent of fire protection, slash pine has spread to drier soils in the southeast and Texas. Although slash pine is adaptable to a variety of site and topographic conditions, it grows best on pond margins and in drainages where soil moisture is ample but not excessive and the soil is well aerated.

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Source: USDA NRCS PLANTS Database

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Physical Description

Morphology

Description

Trees to 30m; trunk to 0.8m diam., straight to contorted; crown conic, becoming rounded or flattened. Bark orange- to purple-brown, irregularly furrowed and cross-checked into large, irregularly rectangular, papery-scaly plates. Branches spreading to ascending; twigs stout (to ca. 1cm thick), orange-brown, aging darker brown, rough-scaly. Buds cylindric, silvery brown, 1.5--2cm; scale margins fringed. Leaves 2 or 3 per fascicle, spreading or ascending, persisting ca. 2 years, 15--20(--23)cm ´ 1.2--1.5mm, straight, slightly twisted, pliant, yellow- to blue-green, all surfaces with stomatal lines, margins finely serrulate, apex abruptly acute to acuminate; sheath 1--2cm, base persistent. Pollen cones cylindric, 30--40mm, purplish. Seed cones maturing in 2 years, falling the year after seed-shed, single or in pairs, symmetric, lance-ovoid before opening, ovoid or ovoid-cylindric when open, (7--)9--18(--20)cm, light chocolate brown, on stalks to 3cm; apophyses lustrous (as if varnished), slightly raised, strongly cross-keeled; umbo central, depressed-pyramidal, with short, stout prickle. Seeds ellipsoid, oblique-tipped; body 6--7mm, dark brown; wing to 20mm.
  • Flora of North America @ eFloras.org
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Physical Description

Tree, Evergreen, Monoecious, Habit erect, Trees without or rarely having knees, Tree with bark rough or scaly, Young shoots 3-dimensional, Buds not resinous, Leaves needle-like, Leaves alternate, Needle-like leaf margins finely serrulate (use magnification or slide your finger along the leaf), Leaf apex acute, Leaves > 5 cm long, Leaves > 10 cm long, Leaves blue-green, Needle-like leaves triangular, Needle-like leaves somewhat rounded, Needle-like leaves twisted, Needle-like leaf habit erect, Needle-like leaves per fascicle mostly 2, Needle-like leaves per fascicle mostly 3, Needle-like leaf sheath persistent, Twigs glabrous, Twigs viscid, Twigs not viscid, Twigs without peg-like projections or large fascicles after needles fall, Berry-like cones orange, Woody seed cones > 5 cm long, Seed cones bearing a scarlike umbo, Umbo with obvious prickle, Bracts of seed cone included, Seeds brown, Seeds winged, Seeds unequally winged, Seed wings prominent, Seed wings equal to or broader than body.
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Stephen C. Meyers

Source: USDA NRCS PLANTS Database

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Description

Trees to 30 m tall; trunk to 0.8 m d.b.h. in native range; bark orange- or purple-brown, furrowed into irregularly oblong, large, papery, scaly plates; crown conical, becoming rounded or flat topped; branchlets orange-brown, aging darker brown, stout, roughly scaly, producing 3 or 4 nodes each year; winter buds silvery brown, cylindric, scales fringed at margin. Needles 2 or 3 per bundle, slightly twisted, yellow- or blue-green, 15-20 (-24) cm × 0.2-1.5 mm, stomatal lines present on all surfaces, base with persistent sheath 1-2 cm, margin finely serrulate. Seed cones solitary or paired, pedunculate (peduncle to 3 cm), pale brown, ovoid or ovoid-cylindric when open, (7-)9-18(-20) cm, maturing in 2 years, then falling the year after seeds shed. Apophyses lustrous, slightly raised, strongly cross keeled; umbo depressed-pyramidal, with a short, stout prickle. Seeds dark brown, ellipsoid, 6-7 mm, apex oblique; wing to 2 cm.
  • Flora of China @ eFloras.org
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Size

Slash pines may live as long as 200 years. The typical variety grows to 18 - 30.5 m (60-100 feet), while the south Florida slash pine grows to only 17 m (56 feet) in height. trunk width in both varieties generally measures 61 cm (24 inches) (Harlow et al. 1979; Wright and Bailey 1982; Lohrey and Kossuth 1990).
  • Abrahamson, W.G. 1984. Species response to fire on the Florida Lake WalesRidge. American Journal of Botany. 71(1): 35-43.
  • Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: Myers, R.L. and J.J. Ewel, eds. Ecosystems of Florida. University of Central Florida Press, Orlando, FL. pp. 103-149.
  • Anderson, R. 1988. Guide to Florida trees. Winner Enterprises, USA. 68 pp. ISBN 0-932855-20-2.
  • Breininger, D.R. and R.B. Smith. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2):223-240.
  • Duncan, W.H. and M.B. Duncan. 1988. Trees of the southeastern United States. University of Georgia Press, Athens, GA. 322 pp.
  • Eyre, F.H., ed. 1980. Forest cover types of the united States and Canada. Society of American Foresters, Washington, D.C. 148 pp.
  • Harlow, W.M., E.S. Harrar, S. Ellwood, F.M. White. 1979. Textbook of dendrology. 6th edition. McGraw-Hill, Inc. New York, NY. 510 pp.
  • Hebb, E.A. and A.F. Clewell. 1976. A remnant stand of old-growth slash pine in the Florida panhandle. Bulletin of the Torrey Botanical Club. 103(1):1-9.
  • Jackson, J.A. 1971. The evolution, taxonomy, distribution, past populations and current status of the red-cockaded woodpecker. In: Thompson, R.L., ed. The ecology and management of the red-cockaded woodpecker: Proceedings of a symposium. May 26-27, 1971, Folkston, GA. Tall Timbers Research Station, Tallahassee, FL. pp. 4-29.
  • Landers, J.L. 1991. Disturbance influences on pine traits in the southeastern United States. In: Proceedings, 17th Tall Timbers fire ecology conference; May 18-21, 1989, Tallahassee, FL. Tall Timbers Research Station, Tallahassee, FL. pp. 61-95.
  • Langdon, O.G. and F. Bennett. 1976. Management of natural stands of slash pine. Res. Pap. SE-147. U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, Ashville, NC. 12 pp.Lohrey, R.E. and S.V. Kossuth. 1990. Pinus elliottii Englem. slash pine. In: Burns, R.M. and B.H. Honkala, technical coordinators. Silvics of north America. Volume 1. Conifers. Agricultural Handb. 654. U.S. Department of Agriculture, Forest Service, Washington, D.C. pp. 338-347.
  • McCune, B. 1988. Ecological diversity in North American pines. American journal of Botany. 75(3):353-368.
  • McCulley, R.D. 1950. Management of natural slash pine stands in the flatwoods of south Florida and north Florida. circular No. 845. U.S. Department of Agriculture, Washington, D.C. 57 pp.
  • Monk, C.D. 1968. Successional and environmental relationships of the forest vegetation of north central Florida. American Midland Naturalist. 79(2): 441-457.
  • Wade, D.D. 1983. Fire management in the slash pine ecosystem. In: Proceedings of the managed slash pine ecosystem, 1981, Gainesville, FL. University of Florida, School of Forest Resources and Conservation, Gainesville, FL. pp. 203-227; 290-294; 301.
  • Wright, H.A. and A.W. Bailey. 1982. Fire ecology: United States and southern Canada. John Wiley and Sons, Inc. New York, NY. 501 pp.
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Source: Indian River Lagoon Species Inventory

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Diagnostic Description

Synonym

Pinus heterophylla (Elliott) Sudworth, 1893, not K. Koch, 1849; P. taeda Linnaeus var. heterophylla Elliott
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Ecology

Habitat

Habitat and Ecology

Systems
  • Terrestrial
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Comments: Restricted to low elevations and normally occurs on wet flatlands along borders of ponds, streams, rivers, and bays (Elias, 1980).

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Habitat & Distribution

Cultivated. Anhui (Jing Xian), Fujian (Minhou Xian), Guangdong, Guangxi, Hubei (Wuhan Shi), Hunan, Jiangsu, Jiangxi (Ji’an Xian), Taiwan, Yunnan (Kunming Shi), Zhejiang [native to SE United States]
  • Flora of China @ eFloras.org
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Dispersal

Establishment

The slash pines are monoecious, and often hybridize with other pines such as loblolly pine (P. taeda), sand pine (P. clausa) and longleaf pine (P. palustris). They begin producing cones at approximately 10-15 years of age. The typical variety produces good cone crops every 3 years, while the south Florida variety produce good cone crops every 4 years. It has been estimated that 90% of the winged seeds from slash pines fall within 46 m (150 feet) of the parent tree.

The male strobili begin to develop in June, and grow for several weeks. It enters a dormant state until midwinter. Pollen is shed from January through February. The female strobili develop in late August and cones mature in September, approximately 20 months after being pollinated. Natural seed fall occurs from October to March.

The germination occurs within two weeks following seedfall. The slash pine seedlings in their first year are grass-like in appearance. Seedlings can have a year grass stage similar to that of longleaf pines (P. palustris). Grass-stage seedlings develop extensive root systems and root collars (Harlow et al. 1979). Root development in influenced by soil texture and structure, clay and clay loam soils produce larger roots than does sandy soil. Soils with a high presence of mycorrhizae have a positive influence on seedling root development and survival. Growth is rapid in the first year, with seedlings reaching heights of approximately 41 cm (16 inches).

Slash pine grown for commercial production is generally established in plantations using genetically improved planting stock. Sites selected for planting are usually site prepared by flat disking, chopping, or bedding. Disking and chopping are effective on dry sandy soils where control of competing vegetation is a problem and one is trying to reduce the use of chemical application for competition control. However, on sites with a shallow water table bedding will increase rooting space, aeration and increase seedling survival and growth. On droughty sites, bedding can be used if the site is irrigated and vegetation is controlled. These treatments are the standard for contemporary slash pine plantation management. Control of weeds, woody shrub, and herbaceous species is a vital part of increased slash pine plantation productivity.

Plantation establishment from seedling is usually with 1-2 year old bare root seedlings or container seedlings. When out planting seedling by hand or machine care must be taken to insure that the roots are planted straight down to, avoid seedling mortality. Because many slash pine site are low in available phosphorus and nitrogen each site should be soil tested to determine the amount of nitrogen and phosphorus needed to ensure seedling survival and volume growth

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Source: USDA NRCS PLANTS Database

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Trophic Strategy

Autotrophic.Competitors: Slash pines are relatively intolerant of shading and competitors, showing decreased growth rates under shaded and crowded conditions (Langdon and Bennett 1976).Habitats: Slash pines are common on pine flatwoods throughout its range. Common community types include oak-pine, longleaf-slash pine, southern mixed forests, and southern floodplain forests. It grows best on mesic (dry) flatwoods and near pod or stream margins, but also grows well in poorly drained soils, or in areas that are flooded from time to time (Lohrey and Kossuth 1990). However, seeds will become established in flooded areas (Hebb and Clewell 1976).
  • Abrahamson, W.G. 1984. Species response to fire on the Florida Lake WalesRidge. American Journal of Botany. 71(1): 35-43.
  • Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: Myers, R.L. and J.J. Ewel, eds. Ecosystems of Florida. University of Central Florida Press, Orlando, FL. pp. 103-149.
  • Anderson, R. 1988. Guide to Florida trees. Winner Enterprises, USA. 68 pp. ISBN 0-932855-20-2.
  • Breininger, D.R. and R.B. Smith. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2):223-240.
  • Duncan, W.H. and M.B. Duncan. 1988. Trees of the southeastern United States. University of Georgia Press, Athens, GA. 322 pp.
  • Eyre, F.H., ed. 1980. Forest cover types of the united States and Canada. Society of American Foresters, Washington, D.C. 148 pp.
  • Harlow, W.M., E.S. Harrar, S. Ellwood, F.M. White. 1979. Textbook of dendrology. 6th edition. McGraw-Hill, Inc. New York, NY. 510 pp.
  • Hebb, E.A. and A.F. Clewell. 1976. A remnant stand of old-growth slash pine in the Florida panhandle. Bulletin of the Torrey Botanical Club. 103(1):1-9.
  • Jackson, J.A. 1971. The evolution, taxonomy, distribution, past populations and current status of the red-cockaded woodpecker. In: Thompson, R.L., ed. The ecology and management of the red-cockaded woodpecker: Proceedings of a symposium. May 26-27, 1971, Folkston, GA. Tall Timbers Research Station, Tallahassee, FL. pp. 4-29.
  • Landers, J.L. 1991. Disturbance influences on pine traits in the southeastern United States. In: Proceedings, 17th Tall Timbers fire ecology conference; May 18-21, 1989, Tallahassee, FL. Tall Timbers Research Station, Tallahassee, FL. pp. 61-95.
  • Langdon, O.G. and F. Bennett. 1976. Management of natural stands of slash pine. Res. Pap. SE-147. U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, Ashville, NC. 12 pp.Lohrey, R.E. and S.V. Kossuth. 1990. Pinus elliottii Englem. slash pine. In: Burns, R.M. and B.H. Honkala, technical coordinators. Silvics of north America. Volume 1. Conifers. Agricultural Handb. 654. U.S. Department of Agriculture, Forest Service, Washington, D.C. pp. 338-347.
  • McCune, B. 1988. Ecological diversity in North American pines. American journal of Botany. 75(3):353-368.
  • McCulley, R.D. 1950. Management of natural slash pine stands in the flatwoods of south Florida and north Florida. circular No. 845. U.S. Department of Agriculture, Washington, D.C. 57 pp.
  • Monk, C.D. 1968. Successional and environmental relationships of the forest vegetation of north central Florida. American Midland Naturalist. 79(2): 441-457.
  • Wade, D.D. 1983. Fire management in the slash pine ecosystem. In: Proceedings of the managed slash pine ecosystem, 1981, Gainesville, FL. University of Florida, School of Forest Resources and Conservation, Gainesville, FL. pp. 203-227; 290-294; 301.
  • Wright, H.A. and A.W. Bailey. 1982. Fire ecology: United States and southern Canada. John Wiley and Sons, Inc. New York, NY. 501 pp.
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Source: Indian River Lagoon Species Inventory

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Associations

Slash pine associates are varied. Plant associates include other canopy trees such as live oak (Quercus virginiana), and cabbage palm (Sabal palmetto); and understory plants such as bluestems (Andropogon spp.), saw palmetto (Serenoa repens) and gallbery (Ilex glabra).Animals associated with slash pines include species that utilize it for protection and cover, as well as those that consume it. Seeds of this tree are eaten by birds and small mammals. Cattle and deer browse its seedlings (Lohrey and Kossuth 1990). Some birds such as the bald eagle and the endangered red-cockaded woodpecker nest in slash pines, though the latter species tends to prefer other trees as nesting habitat (Jackson 1971).
  • Abrahamson, W.G. 1984. Species response to fire on the Florida Lake WalesRidge. American Journal of Botany. 71(1): 35-43.
  • Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: Myers, R.L. and J.J. Ewel, eds. Ecosystems of Florida. University of Central Florida Press, Orlando, FL. pp. 103-149.
  • Anderson, R. 1988. Guide to Florida trees. Winner Enterprises, USA. 68 pp. ISBN 0-932855-20-2.
  • Breininger, D.R. and R.B. Smith. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2):223-240.
  • Duncan, W.H. and M.B. Duncan. 1988. Trees of the southeastern United States. University of Georgia Press, Athens, GA. 322 pp.
  • Eyre, F.H., ed. 1980. Forest cover types of the united States and Canada. Society of American Foresters, Washington, D.C. 148 pp.
  • Harlow, W.M., E.S. Harrar, S. Ellwood, F.M. White. 1979. Textbook of dendrology. 6th edition. McGraw-Hill, Inc. New York, NY. 510 pp.
  • Hebb, E.A. and A.F. Clewell. 1976. A remnant stand of old-growth slash pine in the Florida panhandle. Bulletin of the Torrey Botanical Club. 103(1):1-9.
  • Jackson, J.A. 1971. The evolution, taxonomy, distribution, past populations and current status of the red-cockaded woodpecker. In: Thompson, R.L., ed. The ecology and management of the red-cockaded woodpecker: Proceedings of a symposium. May 26-27, 1971, Folkston, GA. Tall Timbers Research Station, Tallahassee, FL. pp. 4-29.
  • Landers, J.L. 1991. Disturbance influences on pine traits in the southeastern United States. In: Proceedings, 17th Tall Timbers fire ecology conference; May 18-21, 1989, Tallahassee, FL. Tall Timbers Research Station, Tallahassee, FL. pp. 61-95.
  • Langdon, O.G. and F. Bennett. 1976. Management of natural stands of slash pine. Res. Pap. SE-147. U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, Ashville, NC. 12 pp.Lohrey, R.E. and S.V. Kossuth. 1990. Pinus elliottii Englem. slash pine. In: Burns, R.M. and B.H. Honkala, technical coordinators. Silvics of north America. Volume 1. Conifers. Agricultural Handb. 654. U.S. Department of Agriculture, Forest Service, Washington, D.C. pp. 338-347.
  • McCune, B. 1988. Ecological diversity in North American pines. American journal of Botany. 75(3):353-368.
  • McCulley, R.D. 1950. Management of natural slash pine stands in the flatwoods of south Florida and north Florida. circular No. 845. U.S. Department of Agriculture, Washington, D.C. 57 pp.
  • Monk, C.D. 1968. Successional and environmental relationships of the forest vegetation of north central Florida. American Midland Naturalist. 79(2): 441-457.
  • Wade, D.D. 1983. Fire management in the slash pine ecosystem. In: Proceedings of the managed slash pine ecosystem, 1981, Gainesville, FL. University of Florida, School of Forest Resources and Conservation, Gainesville, FL. pp. 203-227; 290-294; 301.
  • Wright, H.A. and A.W. Bailey. 1982. Fire ecology: United States and southern Canada. John Wiley and Sons, Inc. New York, NY. 501 pp.
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Source: Indian River Lagoon Species Inventory

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Population Biology

Slash pines are common throughout the Indian River Lagoon system.Locomotion: Sessile.
  • Abrahamson, W.G. 1984. Species response to fire on the Florida Lake WalesRidge. American Journal of Botany. 71(1): 35-43.
  • Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: Myers, R.L. and J.J. Ewel, eds. Ecosystems of Florida. University of Central Florida Press, Orlando, FL. pp. 103-149.
  • Anderson, R. 1988. Guide to Florida trees. Winner Enterprises, USA. 68 pp. ISBN 0-932855-20-2.
  • Breininger, D.R. and R.B. Smith. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2):223-240.
  • Duncan, W.H. and M.B. Duncan. 1988. Trees of the southeastern United States. University of Georgia Press, Athens, GA. 322 pp.
  • Eyre, F.H., ed. 1980. Forest cover types of the united States and Canada. Society of American Foresters, Washington, D.C. 148 pp.
  • Harlow, W.M., E.S. Harrar, S. Ellwood, F.M. White. 1979. Textbook of dendrology. 6th edition. McGraw-Hill, Inc. New York, NY. 510 pp.
  • Hebb, E.A. and A.F. Clewell. 1976. A remnant stand of old-growth slash pine in the Florida panhandle. Bulletin of the Torrey Botanical Club. 103(1):1-9.
  • Jackson, J.A. 1971. The evolution, taxonomy, distribution, past populations and current status of the red-cockaded woodpecker. In: Thompson, R.L., ed. The ecology and management of the red-cockaded woodpecker: Proceedings of a symposium. May 26-27, 1971, Folkston, GA. Tall Timbers Research Station, Tallahassee, FL. pp. 4-29.
  • Landers, J.L. 1991. Disturbance influences on pine traits in the southeastern United States. In: Proceedings, 17th Tall Timbers fire ecology conference; May 18-21, 1989, Tallahassee, FL. Tall Timbers Research Station, Tallahassee, FL. pp. 61-95.
  • Langdon, O.G. and F. Bennett. 1976. Management of natural stands of slash pine. Res. Pap. SE-147. U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, Ashville, NC. 12 pp.Lohrey, R.E. and S.V. Kossuth. 1990. Pinus elliottii Englem. slash pine. In: Burns, R.M. and B.H. Honkala, technical coordinators. Silvics of north America. Volume 1. Conifers. Agricultural Handb. 654. U.S. Department of Agriculture, Forest Service, Washington, D.C. pp. 338-347.
  • McCune, B. 1988. Ecological diversity in North American pines. American journal of Botany. 75(3):353-368.
  • McCulley, R.D. 1950. Management of natural slash pine stands in the flatwoods of south Florida and north Florida. circular No. 845. U.S. Department of Agriculture, Washington, D.C. 57 pp.
  • Monk, C.D. 1968. Successional and environmental relationships of the forest vegetation of north central Florida. American Midland Naturalist. 79(2): 441-457.
  • Wade, D.D. 1983. Fire management in the slash pine ecosystem. In: Proceedings of the managed slash pine ecosystem, 1981, Gainesville, FL. University of Florida, School of Forest Resources and Conservation, Gainesville, FL. pp. 203-227; 290-294; 301.
  • Wright, H.A. and A.W. Bailey. 1982. Fire ecology: United States and southern Canada. John Wiley and Sons, Inc. New York, NY. 501 pp.
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Life History and Behavior

Reproduction

Slash pines are monoecious. They often hybridize with other pines such as loblolly pine (P. taeda), sand pine (P. clausa) and longleaf pine (P. palustris). The begin producing cones at approximately 10-15 years of age. The typical variety produces good cone crops every 3 years, while the south Florida variety produce good cone crops every 4 years. It has been estimated that 90% of the winged seeds from slash pines fall within 46 m (150 feet) of the parent tree (Lohrey and Kossuth 1990).Male strobili begin to develop in June. These grow for several weeks, but then enter a dormant state until midwinter. Pollen is shed from January through February. Female strobili develop in late August and become fully developed. Cones mature in September, approximately 20 months after being pollinated. Seedfall occurs in October (Lohrey and Kossuth 1990).
  • Abrahamson, W.G. 1984. Species response to fire on the Florida Lake WalesRidge. American Journal of Botany. 71(1): 35-43.
  • Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: Myers, R.L. and J.J. Ewel, eds. Ecosystems of Florida. University of Central Florida Press, Orlando, FL. pp. 103-149.
  • Anderson, R. 1988. Guide to Florida trees. Winner Enterprises, USA. 68 pp. ISBN 0-932855-20-2.
  • Breininger, D.R. and R.B. Smith. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2):223-240.
  • Duncan, W.H. and M.B. Duncan. 1988. Trees of the southeastern United States. University of Georgia Press, Athens, GA. 322 pp.
  • Eyre, F.H., ed. 1980. Forest cover types of the united States and Canada. Society of American Foresters, Washington, D.C. 148 pp.
  • Harlow, W.M., E.S. Harrar, S. Ellwood, F.M. White. 1979. Textbook of dendrology. 6th edition. McGraw-Hill, Inc. New York, NY. 510 pp.
  • Hebb, E.A. and A.F. Clewell. 1976. A remnant stand of old-growth slash pine in the Florida panhandle. Bulletin of the Torrey Botanical Club. 103(1):1-9.
  • Jackson, J.A. 1971. The evolution, taxonomy, distribution, past populations and current status of the red-cockaded woodpecker. In: Thompson, R.L., ed. The ecology and management of the red-cockaded woodpecker: Proceedings of a symposium. May 26-27, 1971, Folkston, GA. Tall Timbers Research Station, Tallahassee, FL. pp. 4-29.
  • Landers, J.L. 1991. Disturbance influences on pine traits in the southeastern United States. In: Proceedings, 17th Tall Timbers fire ecology conference; May 18-21, 1989, Tallahassee, FL. Tall Timbers Research Station, Tallahassee, FL. pp. 61-95.
  • Langdon, O.G. and F. Bennett. 1976. Management of natural stands of slash pine. Res. Pap. SE-147. U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, Ashville, NC. 12 pp.Lohrey, R.E. and S.V. Kossuth. 1990. Pinus elliottii Englem. slash pine. In: Burns, R.M. and B.H. Honkala, technical coordinators. Silvics of north America. Volume 1. Conifers. Agricultural Handb. 654. U.S. Department of Agriculture, Forest Service, Washington, D.C. pp. 338-347.
  • McCune, B. 1988. Ecological diversity in North American pines. American journal of Botany. 75(3):353-368.
  • McCulley, R.D. 1950. Management of natural slash pine stands in the flatwoods of south Florida and north Florida. circular No. 845. U.S. Department of Agriculture, Washington, D.C. 57 pp.
  • Monk, C.D. 1968. Successional and environmental relationships of the forest vegetation of north central Florida. American Midland Naturalist. 79(2): 441-457.
  • Wade, D.D. 1983. Fire management in the slash pine ecosystem. In: Proceedings of the managed slash pine ecosystem, 1981, Gainesville, FL. University of Florida, School of Forest Resources and Conservation, Gainesville, FL. pp. 203-227; 290-294; 301.
  • Wright, H.A. and A.W. Bailey. 1982. Fire ecology: United States and southern Canada. John Wiley and Sons, Inc. New York, NY. 501 pp.
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Growth

Germination occurs within two weeks following seedfall. Slash pine seedlings in their first year are grass-like in appearance. Seedlings of south Florida slash pine have a 2 - 6 year grass stage similar to that of longleaf pines (P. palustris). Grass-stage seedlings develop extensive root systems and root collars (Harlow et al. 1979). Growth is rapid in the first year, with seedlings reaching heights of approximately 41 cm (16 inches).
  • Abrahamson, W.G. 1984. Species response to fire on the Florida Lake WalesRidge. American Journal of Botany. 71(1): 35-43.
  • Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: Myers, R.L. and J.J. Ewel, eds. Ecosystems of Florida. University of Central Florida Press, Orlando, FL. pp. 103-149.
  • Anderson, R. 1988. Guide to Florida trees. Winner Enterprises, USA. 68 pp. ISBN 0-932855-20-2.
  • Breininger, D.R. and R.B. Smith. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2):223-240.
  • Duncan, W.H. and M.B. Duncan. 1988. Trees of the southeastern United States. University of Georgia Press, Athens, GA. 322 pp.
  • Eyre, F.H., ed. 1980. Forest cover types of the united States and Canada. Society of American Foresters, Washington, D.C. 148 pp.
  • Harlow, W.M., E.S. Harrar, S. Ellwood, F.M. White. 1979. Textbook of dendrology. 6th edition. McGraw-Hill, Inc. New York, NY. 510 pp.
  • Hebb, E.A. and A.F. Clewell. 1976. A remnant stand of old-growth slash pine in the Florida panhandle. Bulletin of the Torrey Botanical Club. 103(1):1-9.
  • Jackson, J.A. 1971. The evolution, taxonomy, distribution, past populations and current status of the red-cockaded woodpecker. In: Thompson, R.L., ed. The ecology and management of the red-cockaded woodpecker: Proceedings of a symposium. May 26-27, 1971, Folkston, GA. Tall Timbers Research Station, Tallahassee, FL. pp. 4-29.
  • Landers, J.L. 1991. Disturbance influences on pine traits in the southeastern United States. In: Proceedings, 17th Tall Timbers fire ecology conference; May 18-21, 1989, Tallahassee, FL. Tall Timbers Research Station, Tallahassee, FL. pp. 61-95.
  • Langdon, O.G. and F. Bennett. 1976. Management of natural stands of slash pine. Res. Pap. SE-147. U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, Ashville, NC. 12 pp.Lohrey, R.E. and S.V. Kossuth. 1990. Pinus elliottii Englem. slash pine. In: Burns, R.M. and B.H. Honkala, technical coordinators. Silvics of north America. Volume 1. Conifers. Agricultural Handb. 654. U.S. Department of Agriculture, Forest Service, Washington, D.C. pp. 338-347.
  • McCune, B. 1988. Ecological diversity in North American pines. American journal of Botany. 75(3):353-368.
  • McCulley, R.D. 1950. Management of natural slash pine stands in the flatwoods of south Florida and north Florida. circular No. 845. U.S. Department of Agriculture, Washington, D.C. 57 pp.
  • Monk, C.D. 1968. Successional and environmental relationships of the forest vegetation of north central Florida. American Midland Naturalist. 79(2): 441-457.
  • Wade, D.D. 1983. Fire management in the slash pine ecosystem. In: Proceedings of the managed slash pine ecosystem, 1981, Gainesville, FL. University of Florida, School of Forest Resources and Conservation, Gainesville, FL. pp. 203-227; 290-294; 301.
  • Wright, H.A. and A.W. Bailey. 1982. Fire ecology: United States and southern Canada. John Wiley and Sons, Inc. New York, NY. 501 pp.
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Molecular Biology and Genetics

Molecular Biology

Statistics of barcoding coverage: Pinus elliottii

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 5
Species: 7
Species With Barcodes: 1

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
LR/lc
Lower Risk/least concern

Red List Criteria

Version
2.3

Year Assessed
1998
  • Needs updating

Assessor/s
Conifer Specialist Group

Reviewer/s
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National NatureServe Conservation Status

United States

Rounded National Status Rank: N5 - Secure

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NatureServe Conservation Status

Rounded Global Status Rank: G5 - Secure

Reasons: Common tree in Florida and in coastal regions of Louisiana, Alabama, Georgia, and the southern part of South Carolina.

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Status

Please consult the PLANTS Web site and your State Department of Natural Resources for this plant’s current status (e.g. threatened or endangered species, state noxious status, and wetland indicator values).

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Threats

Pests and potential problems

Fusiform rust (Cronartium quercuum f. sp. fusiforme), annosus root rot (Heterobasidion annosum), and Fusarium moniliforme var subglutinans are the most serious pest of slash pines Fusiform rust, an obligate parasite requiring two living host trees pine and oak leaves to complete its life cycle. The fungus cannot spread from pine to pine, but must return to the oak leaves to produce the spores that in turn infect pine. The disease which develops at or near the point of infection, result in tapered, spindle-shaped swells, called galls, on branches and stems of pines.

Annosus root rot is a fungal disease that infects freshly cut stumps of slash pine, and spreads to other trees by root contact. Diseased or dead and dying trees are usually found in groups.

The slash pines can be damaged by insects pests such as the pales weevil (Hylobius pales), that invades logging areas and feeds on the bark of young seedling, girdling the stem and causing wilting and death. Blockheaded pine sawfly (Tetralopha rosbustella) or several different needle feeders may defoliate young trees. The black turpentine beetle (Dendroctonus terebrans), engraver beetles (Ips spp.), can become major problems especially in naval store plantations. The southern pine beetle (Dendroctonus frontalis), is not a major of slash pine except in areas where the growing environment has placed the trees under stress.

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Management

Cultivars, improved and selected materials (and area of origin)

These materials are readily available from commercial plant sources. Contact your local Natural Resources Conservation Service (formerly Soil Conservation Service) office for more information. Look in the phone book under ”United States Government.” The Natural Resources Conservation Service will be listed under the subheading “Department of Agriculture.”

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Relevance to Humans and Ecosystems

Benefits

Benefit in IRL: Slash pines provide habitat and food for birds and small mammals, and are an important component of many natural communities. Slash pines are an important source of timber in the U.S. Its strong, heavy wood is used for construction. Due to its high resin content, it is useful for producing poles, railroad ties, pilings, turpentine, and rosin (McCulley 1950; Wade 1983; Duncan and Duncan 1988; McCune 1988; Lohrey and Kossuth 1990).
  • Abrahamson, W.G. 1984. Species response to fire on the Florida Lake WalesRidge. American Journal of Botany. 71(1): 35-43.
  • Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: Myers, R.L. and J.J. Ewel, eds. Ecosystems of Florida. University of Central Florida Press, Orlando, FL. pp. 103-149.
  • Anderson, R. 1988. Guide to Florida trees. Winner Enterprises, USA. 68 pp. ISBN 0-932855-20-2.
  • Breininger, D.R. and R.B. Smith. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2):223-240.
  • Duncan, W.H. and M.B. Duncan. 1988. Trees of the southeastern United States. University of Georgia Press, Athens, GA. 322 pp.
  • Eyre, F.H., ed. 1980. Forest cover types of the united States and Canada. Society of American Foresters, Washington, D.C. 148 pp.
  • Harlow, W.M., E.S. Harrar, S. Ellwood, F.M. White. 1979. Textbook of dendrology. 6th edition. McGraw-Hill, Inc. New York, NY. 510 pp.
  • Hebb, E.A. and A.F. Clewell. 1976. A remnant stand of old-growth slash pine in the Florida panhandle. Bulletin of the Torrey Botanical Club. 103(1):1-9.
  • Jackson, J.A. 1971. The evolution, taxonomy, distribution, past populations and current status of the red-cockaded woodpecker. In: Thompson, R.L., ed. The ecology and management of the red-cockaded woodpecker: Proceedings of a symposium. May 26-27, 1971, Folkston, GA. Tall Timbers Research Station, Tallahassee, FL. pp. 4-29.
  • Landers, J.L. 1991. Disturbance influences on pine traits in the southeastern United States. In: Proceedings, 17th Tall Timbers fire ecology conference; May 18-21, 1989, Tallahassee, FL. Tall Timbers Research Station, Tallahassee, FL. pp. 61-95.
  • Langdon, O.G. and F. Bennett. 1976. Management of natural stands of slash pine. Res. Pap. SE-147. U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, Ashville, NC. 12 pp.Lohrey, R.E. and S.V. Kossuth. 1990. Pinus elliottii Englem. slash pine. In: Burns, R.M. and B.H. Honkala, technical coordinators. Silvics of north America. Volume 1. Conifers. Agricultural Handb. 654. U.S. Department of Agriculture, Forest Service, Washington, D.C. pp. 338-347.
  • McCune, B. 1988. Ecological diversity in North American pines. American journal of Botany. 75(3):353-368.
  • McCulley, R.D. 1950. Management of natural slash pine stands in the flatwoods of south Florida and north Florida. circular No. 845. U.S. Department of Agriculture, Washington, D.C. 57 pp.
  • Monk, C.D. 1968. Successional and environmental relationships of the forest vegetation of north central Florida. American Midland Naturalist. 79(2): 441-457.
  • Wade, D.D. 1983. Fire management in the slash pine ecosystem. In: Proceedings of the managed slash pine ecosystem, 1981, Gainesville, FL. University of Florida, School of Forest Resources and Conservation, Gainesville, FL. pp. 203-227; 290-294; 301.
  • Wright, H.A. and A.W. Bailey. 1982. Fire ecology: United States and southern Canada. John Wiley and Sons, Inc. New York, NY. 501 pp.
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Uses

Commercial uses: Slash pine is used for reforestation projects and timber plantations throughout the southeastern United States. Its pines produced turpentine and crude rosins used for a variety of purpose (i.e., poles, railroad ties, pilings, turpentine, and rosin).

Wildlife uses: The slash pine seeds are an excellent food source for gray and fox squirrels and wild turkey.

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Wikipedia

Pinus elliottii

Pinus elliottii, commonly known as the slash pine, is a pine native to the southeastern United States, from southern South Carolina west to southeastern Louisiana, and south to the Florida Keys.[2]

It is fast-growing, but not very long-lived by pine standards (to 200 years), and prefers humid climates and moist soils.

Slash pine is named after the "slashes" – swampy ground overgrown with trees and bushes – that constitute its habitat.

This tree reaches heights of 18–30 m (59–98 ft) with a trunk diameter of 0.6–0.8 m (2.0–2.6 ft). The leaves are needle-like, very slender, in clusters of two or three, and are 18–24 cm (7.1–9.4 in) long.

Grand Bay National Estuarine Research Reserve - maritime slash pine Pinus elliottii savanna on the Mississippi and Alabama state line near Bayou Heron (1998)

The cones are glossy red-brown, 5–15 cm (2.0–5.9 in) in length with a short (2–3 mm/0.079–0.12 in), thick prickle on each scale. It is known for its conical shape.

It may be distinguished from the related loblolly pine by the somewhat longer, glossier needles and larger red-brown cones, and from longleaf pine by the shorter, more slender needles and smaller cones with less broad scales.

The two varieties are:

  • P. elliottii var. elliotti (typical slash pine) ranges from South Carolina to Louisiana, and south to central Florida. Its leaves are in bundles (fascicles) of twos and threes, mostly threes, and the cones are larger, 7–15 cm (2.8–5.9 in).
  • P. elliotti var. densa (South Florida slash pine or Dade County pine) is found in the pine rocklands of southern Florida and Florida Keys, including the Everglades.[3][4] Leaves nearly all in bundles of two. Cones smaller, 5–12 cm (2.0–4.7 in).

Unlike the typical variety of slash pine, seedlings of P. elliotti var. densa pass through a "grass stage", in a manner similar to longleaf pine.

The slash pine also is known as the yellow slash pine, swamp pine, or pitch pine, although it should not be confused with the tree more usually called the pitch pine, Pinus rigida.

This tree is widely grown in plantations, and also is used in horticulture.

References

  1. ^ Conifer Specialist Group (1998). Pinus elliottii. 2006. IUCN Red List of Threatened Species. IUCN 2006. www.iucnredlist.org. Retrieved on 10 May 2006.
  2. ^ Moore, Gerry; Kershner, Bruce; Craig Tufts; Daniel Mathews; Gil Nelson; Spellenberg, Richard; Thieret, John W.; Terry Purinton; Block, Andrew (2008). National Wildlife Federation Field Guide to Trees of North America. New York: Sterling. p. 74. ISBN 1-4027-3875-7. 
  3. ^ "Pine Rocklands" (PDF). United States Fish and Wildlife Service. http://www.fws.gov/southeast/vbpdfs/commun/pr.pdf. Retrieved 2009-06-17. 
  4. ^ Gilman, Edward F.; Dennis G. Watson (2006). "Pinus elliotti: Slash Pine". University of Florida, Institute of Food and Agricultural Sciences. http://edis.ifas.ufl.edu/st463. Retrieved 12 April 2011. 
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