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Publication #CIR1194

Eucalyptus and Corymbia Species for Pulpwood, Mulchwood, Energywood, Windbreaks, and/or Phytoremediation1

D. L. Rockwood and G. F. Peter2

Introduction

In Florida, Eucalyptus species grow faster than our native tree species. E. grandis (EG) and E. amplifolia (EA), in particular, are fast-growing trees that, when planted on suitable sites and managed properly, can produce commercial products such as pulpwood, mulchwood, and energywood. Eucalyptus can also phytoremediate, i.e., remediate environmental problems (Table 1). Eucalyptus species are not invasive, having been planted commercially in Florida for more than 45 years without spreading from managed plantations. EG and EA, along with Corymbia torelliana (CT), also may be used as windbreaks for citrus and vegetables. This circular describes potential applications and presents planting guidelines for these three species.

Applications

Applications for EG, EA, and CT in Florida ranging from traditional forest products to innovative phytoremediation systems and windbreaks are demonstrated in various locations (Table 1).

Forest Products. Commercial markets for Eucalyptus wood currently exist for landscape mulch and pulpwood and may be developed for oriented strand board, specialty pulp, and medium-density fiberboard. The color, texture, and durability of mulch produced from EG and EA compare very favorably to those of cypress mulch. EG in southern Florida and EA in northern Florida presently are harvested for landscape mulch. Assuming that mulch-manufacturing plants in Florida need some 20 million cubic feet of mulchwood each year and using typical growth rates for Eucalyptus in Florida, about 50,000 acres of Eucalyptus plantations would perpetually supply the feedstock needs of the Florida mulch industry.

Considerable Eucalyptus pulp is imported into the United States. Florida-grown EG and EA have very acceptable properties for pulp and paper making, and hardwood pulpwood demand and price are strong in the Southeast. Still, Eucalyptus plantations grown for pulpwood need to be in close proximity to existing pulpmills in northern Florida. EG used for specialty pulp could be greater distances from the high yield pulpmills that could be built in the Southeast.

Energy. Trees can be bioenergy feedstocks. Energywood may be utilized for electricity generation by many utilities in Florida by cofiring with coal, for example. Some utilities in southern Florida are now using woody biomass to produce electricity and steam. Woody biomass also has numerous other energy-related applications including direct combustion, thermo-chemical gasification, methane production, and, potentially, alcohol production. Trees grown for energy applications may qualify for tax credits worth as much as $30 per dry ton.

Windbreaks. The rapid growth and evergreen nature of EG, EA, and CT make them ideal for quickly establishing effective windbreaks around citrus and vegetables. With a wind-slowing effect extending approximately 10 times tree height, after six years these species can easily provide wind and disease protection for crops up to 600 feet downwind from the windbreak. EA and EG windbreaks tend to open at the bottom as the trees grow and lower branches self-prune; CT windbreaks typically stay full as the trees grow. Mixed species windbreaks and use of coppicing afford ways to maximize early and continuous windbreak effectiveness.

Phytoremediation Systems. The rapid year-round growth of EG and EA is advantageous for phytoremediation applications such as a) effluent from sewage treatment facilities, b) stormwater in urban and industrial areas, and c) agricultural irrigation water. Water and nutrient uptakes by EG and EA depend on climatic limits, tree age and vigor, and the timing and extent of the wastewater applications. The upper limit on annual water uptake is approximately 65 inches. Annual nutrient accumulations by vigorous EG may reach 190, 35, 95, 80, and 25 pounds/acre of nitrogen, phosphorus, potassium, calcium, and magnesium, respectively. In phytoremediation systems, Eucalyptus should be managed to reach full canopy development as rapidly as possible and to maintain active growth. They should be harvested as soon as productivity diminishes; they regenerate through vigorous coppicing (sprouting from the stump). At the accelerated growth rates EA and EG can achieve in phytoremediation applications, plantings as small as two acres could be commercially harvested in three to four years. Eucalyptus production combined with wastewater recycling thus has many mutual advantages, such as increasing tree growth, recycling nutrients, and renovating wastewater while at the same time producing mulch, pulpwood, or energywood.

Planting Guidelines

Successful establishment and management of EG, EA, and CT have several aspects (Table 2):

Growing Region. No single species is the most productive in all regions of Florida nor most suitable for all applications. Species choice by region (Figure 1) reflects freeze hardiness differences, particularly in northern Florida. Improved EA is freeze hardy enough for all of Florida. The limited hardiness of EG restricts use of improved seedlings to southern and central Florida, but EG cultivars may also be used in northern Florida. CT has freeze tolerance appropriate for central and southern Florida.

Site Requirements. EA, EG, and CT all grow best on agricultural lands. Lands recently in agricultural use or marginal for agricultural production are typically ideal. EA requires high quality land with relatively high pH. EG and CT have a wide site tolerance. EG grows very well on sandy or organic soils and grows more rapidly than EA and CT on most sites.

All species may be grown on poorer sites if amendments are added to raise nutrient levels and/or pH. EG, for example, grows well on low-phosphorus sites when ground rock phosphate is applied. All three are very responsive to fertilizer amendment. Some EG cultivars have acceptable flood tolerance.

Cultural Practices. On poorly drained flatwood sites or in phytoremediation applications involving flooding, bedding is essential. Beds should be at least one foot high and allowed to settle for about three months before the trees are planted.

All three species survive and grow best when competing vegetation is well controlled during the first two years. The initial site preparation, if bedding is involved, is usually sufficient for vegetation control during the first growing season. Preemergent herbicides provide good first season wood control. With good tree growth during the first year, the trees typically dominate other vegetation for the rest of the rotation. Without adequate vegetation control during the first year, eucalypts will grow very slowly and are likely to fail.

Planting Stock. Superior genotypes have been identified within each species through one (CT), two (EA), and five (EG) generations of genetic testing and selection. These superior genotypes have far better growth and frost resilience than untested trees of the same species.

EA, EG, and CT can all be propagated as containerized seedlings. Superior EG seed is readily available, and EA and CT seed is increasingly available. EG is also currently available as vegetatively propagated cultivars G1, G2, G3, and G4. While the cultivars cost ~$.60 each compared to ~$.45 per seedling, their numerous attributes typically justify their higher cost.

EA, EG, and CT should be planted at the onset of the summer rainy season when soil moisture is ample. Use of water-absorbing gel can initiate or extend the planting season by about a month. Eucalypts planted too late in the year will not reach a size that conveys some resistance to freeze damage.

Management. Management intensity and rotation length vary with species, site, and application. For example, through the 1980s, culture of EG for pulpwood on up to 15,000 acres of flatwoods sites in southern Florida had low intensity and consisted of 1) planting about 600 trees per acre, 2) basic application of ground rock phosphate and minimal weed control through bedding, 3) 8–10 year rotation, and 4) two to three rotations.

For the fastest-growing species grown for energywood, the time from planting to harvest may be two years or less if planted on a high-quality site at close spacing (for instance, EG planted on muck soils at 4,000 trees/acre). To maximize production, management may include intensive culture (environmentally safe site amendment, irrigation, and weed control practices).

For mulchwood production, an intermediate planting density of about 1,000 trees/acre with a rotation of some six years could produce trees of suitable size. However, EG grown for mulchwood at Palmdale (Table 1) is managed with relatively low intensity, but superior planting stock is used.

EA, EG, and CT all coppice (sprout from the stump) after harvest. In the coppice rotation, tree growth may exceed first rotation growth by some 20% and shorten the time to the second harvest by at least one year, but the time of harvest is critical to coppicing success. EA coppices well throughout the year, while EG and CT harvests must be done during the winter to ensure good coppicing. Coppice cycles may be repeated up to six times.

References

Andreu, M. G., B. Tamang, M..H. Friedman, and D. L. Rockwood. 2008. The benefits of windbreaks for Florida growers. Florida Cooperative Extension Service Circular FOR192. 5p. http://edis.ifas.ufl.edu/FR253. http://edis.ifas.ufl.edu/pdffiles/FR/FR25300.pdf

Andreu, M. G., B. Tamang, D. L. Rockwood, and M. H. Friedman. 2009. Potential woody species and species attributes for windbreaks in Florida. Florida Cooperative Extension Service Circular FOR224. 6p. http://edis.ifas.ufl.edu/fr286.

Geary, T. F., G. F. Meskimen, and E. C. Franklin. 1983. Growing eucalyptus in Florida for industrial wood production. USDA Forest Service Gen Tech. Rpt. SE-23, 43p.

Langholtz, M., D. Carter, J. Alavalapati, and D. Rockwood. 2007. The economic feasibility of reclaiming phosphate mined lands with short-rotation woody crops in Florida. J For Econ. 12(4): 237–249.

Langholtz, M., D. R. Carter, and D. L. Rockwood. 2007. Assessing the Economic Feasibility of Short-Rotation Woody Crops in Florida. Florida Cooperative Extension Service Circular 1516. 5p. http://edis.ifas.ufl.edu/FR169.

Langholtz, M., D. R. Carter, D. L. Rockwood, J. R. R. Alavalapati, and AES Green. 2005. Effect of dendroremediation incentives on the profitability of short-rotation woody cropping of Eucalyptus grandis. Forest Policy and Economics 7(5): 806–817.

Meskimen, G. F., D. L. Rockwood, and K. V. Reddy. 1987. Development of Eucalyptus clones for a summer rainfall environment with periodic severe frosts. New Forests 3: 197–205.

Pisano, S. M., and D. L. Rockwood. 1997. Stormwater phytoremediation potential of Eucalyptus. In: Proceedings 5th. Biennial Stormwater Research Conference, Nov. 5–7, 1997, Tampa, FL. Southwest Florida Water Management District, Brooksville, FL. p. 32–42.

Rockwood D. L., D. R. Carter, M. H. Langholtz, and J. A. Stricker. 2006. Eucalyptus and Populus short rotation woody SEQ CHAPTER 1 crops for phosphate mined lands in Florida USA. Biomass & Bioenergy 30 (8,9): 728–734.

Rockwood D. L., D. R. Carter, and J. A. Stricker. 2008. Commercial tree crops on phosphate mined lands. Florida Institute of Phosphate Research. FIPR Publication #03-141-225.

Rockwood, D. L., C. W. Comer, D. R. Dippon, and J. B. Huffman. 1985. Woody biomass production options for Florida. Fla. Agr. Exp. Sta. Tech. Bull. 856. 29p.

Rockwood, D. L., R. J. Dinus, J. M. Kramer, T. J. McDonough, C. A. Raymond, J. V. Owen, and J. T. Devalerio. 1993. Genetic variation for rooting, growth, frost hardiness, and wood, fiber, and pulping properties in Florida-grown Eucalyptus amplifolia. In: Proc. 22nd. Southern For. Tree Improvement Conf., June 14–17, 1993, Atlanta, GA. p. 81–88.

Rockwood, D. L., R. J. Dinus, J. M. Kramer, and T. J. McDonough. 1995. Genetic variation in wood, pulping, and paper properties of Eucalyptus amplifolia and E grandis grown in Florida USA. In: Proc. CRC-IUFRO Conf. Eucalypt Plantations: Improvement of Fibre Yield and Quality, Feb 19–24, 1995, Hobart, Tasmania, Australia. p. 53–59.

Rockwood, D. L., and D. R. Dippon. 1989. Biological and economic potential of Eucalyptus grandis and slash pine as biomass energy crops. Biomass 20(3&4): 155–166.

Rockwood, D. L., L. Q. Ma, G. R. Alker, C. Tu, and R. W. Cardellino. 2001. Phytoremediation of contaminated sites using wood biomass. Final Report to the Florida Center for Solid and Hazardous Waste Management, June 2001. 95p. http://www.floridacenter.org/publications/01_03Rockwood.pdf

Rockwood D. L., C. V. Naidu, D. R. Carter, M. Rahmani, T. Spriggs, C. Lin, G. R. Alker, J. G. Isebrands, and S. A. Segrest. 2004. Short-rotation woody crops and phytoremediation: Opportunities for agroforestry? In: New Vistas in Agroforestry, A Compendium for the 1st World Congress of Agroforestry 2004, P. K. R. Nair, M. R. Rao, and L. E. Buck (Editors), Kluwer Academic Publishers, Dordrecht, The Netherlands. p. 51–63.

Rockwood, D. L., N. N. Pathak, and P. C. Satapathy. 1993. Woody biomass production systems for Florida. Biomass & Bioenergy 5(1): 23–34.

Rockwood, D. L., G. F. Peter, M. H. Langholtz, B. Becker, A. Clark III, and J. Bryan. 2005. Genetically improved eucalypts for novel applications and sites in Florida. In: Proc. 28th South. For. Tree Improvement Conf., June 21–23, 2005, Raleigh, NC. p. 64–75. http://www.ces.ncsu.edu/nreos/forest/feop/Agenda2005/SFTIC/proceedings.pdf

Rockwood, D. L., S. M. Pisano, and W. V. McConnell. 1996. Superior cottonwood and Eucalyptus clones for biomass production in wastewater bioremediation systems. Proc. Bioenergy 96, 7th National Bioenergy Conference, September 15–20, 1996, Nashville, TN. p. 254–261.

Rockwood, D. L., A. W. Rudie, S. A. Ralph, J. Zhu, and J. E. Winandy. 2008. Energy product options for Eucalyptus species grown as short rotation woody crops. Int. J. Mol. Sci. 9:1361–1378. http://www.mdpi.org/ijms/papers/i9081361.pdf

Rockwood, D. L., G. H. Snyder, and R. R. Sprinkle. 1994. Woody biomass production in waste recycling systems. Proc. Bioenergy 94, 6th National Bioenergy Conference, October 2–6, 1994, Reno/Sparks, NV. p. 351–358.

Rockwood D. L., and B. Tamang.2010.Description and performance of four Eucalyptus grandis cultivars released by IFAS/UF in 2009. Proceedings Florida State Horticultural Society 123. (in press)

Rockwood, D. L., E. E. Warrag, K. Javanshir, and K. Kratz. 1989. Genetic improvement of Eucalyptus grandis for southern Florida. In: Proceedings 20th. Southern Forest Tree Improvement Conference, June 27–29, 1989, Charleston, SC. p. 403–410.

Segrest, S. A., D. L. Rockwood, J. A. Stricker, and A. E. S. Green. 1998. Biomass cofiring with coal at Lakeland Utilities. Southeastern Regional Biomass Energy Program Publication No. 219287-1, TVA, Muscle Shoals, AL. 50p.

Stricker, J. A., J. W. Mishoe, G. M. Prine, M. Rahmani, and D. L. Rockwood. 1995. Economic development through biomass systems integration in central Florida. In: Proc. 2nd. Biomass Conf. of the Americas, Aug. 21–24, Portland, OR. p. 1608–1617.

Tamang, B, D. Rockwood, M. Langholtz, E. Maehr, B. Becker, and S. Segrest. 2008. Fast-growing trees for cogongrass (Imperata cylindrica) suppression and enhanced colonization of understory plant species on a phosphate-mine clay settling area. Ecological Engineering 32:329–336.

Tamang B., M. G. Andreu, M. H. Friedman, D. L. Rockwood. 2009. Windbreak designs and planting for Florida agricultural fields. Florida Cooperative Extension Service Circular FOR227. 6p.

Tamang B., M. G. Andreu, M. H. Friedman, D. L. Rockwood. 2009. Management of field windbreaks. Florida Cooperative Extension Service Circular FOR288. 6p.

Figure 1. 

Climate-defined growing regions in Florida for EA, EG, and CT.


[Click thumbnail to enlarge.]

Tables

Table 1. 

Location and description of EG, EA, and CT applications in Florida

Application

Species

Location

Description

Phytoremediation

EA

Tallahassee

Trees planted on landfill cap

Phytoremediation

EG, EA

Tampa

Trees in 1.5-acre stormwater pond

Energywood

EA

Gainesville

Clones in seed orchard/clone bank

Energywood

EA, EG

Perry

Progenies and clones on sandy loam at various spacings

Energywood

EG

Indiantown

Cultivars on sandy muck at various spacings

Energywood

EG, EA

Bowling Green

Cultivars and progenies on clay settling area at various spacings

Mulchwood

EG

Palmdale

Trees planted at 12 x 7 ft on bedded flatwoods

Mulchwood

EA, EG

Old Town

Trees planted at 10 x 4 ft on pasture

Windbreak

EA, EG, CT

Balm

Trees planted around strawberry fields

Windbreak

CT

Clewiston

Trees planted around vegetable fields

Windbreak

EA

Citra

Trees planted around citrus grove

Windbreak

EG

Winter Garden

Trees planted around citrus grove

Table 2. 

Guidelines on the establishment and management of EG, EA, and CT in Florida.

Species

EG

EA

CT

Applications1

E, M, P, R, W

E, M, P, R, W

W

Growing Region

Southern, central, and possibly northern FL

Northern and central FL

Southern and central FL

Site Requirements

Ag land or

flatwoods

Ag or forest land SI2≥65; pH>5.5

Ag land or

flatwoods

Culture

Disk on muck; chop, burn, ½-ton ground rock phosphate/acre, and bed on flatwoods; add N up to 270 lbs/acre on flatwoods; plant in summer

Disk and herbicide; add 15–20 tons/acre of compost or N and P up to 250 lbs/acre; Plant in spring or summer

Disk and herbicide;

add N and P up to 250 lbs/acre;

plant in spring or summer

Planting Stock

Improved seedlings or commercial cultivars3

Improved seedlings or tested clones

Improved seedlings or tested clones

Growth

46 ft tall in 2.5 yrs on muck; 33 ft in 2 yrs and 55 ft in 5 yrs on flatwoods

46 ft in 3 yrs on ag lands

30 ft in 2 yrs on ag lands

Rotation

2 yrs on muck;

5 yrs on flatwoods

2–5 yrs

Coppicing

(sprout from the stump)

Good in winter, poor in summer; 33 ft. in 1.75 yrs on muck, 66 ft in 5 yrs on flatwoods

Excellent in winter and summer; 16 ft. in 6 mos on ag lands

Good in winter and spring; 10 ft. in 6 mos on ag lands

Productivity

(dry tons/acre/yr)

Up to 16

Up to 11

1 E = energywood, M = Mulch, P = Pulpwood, R = Remediation, W = Windbreak

2 Site Index (base age 25 years) for slash pine

3 UF cultivars G1, G2, G3, or G4, as appropriate for site and climate

Footnotes

1.

This document is Circular 1194, one of a series of the School of Forest Resources and Conservation, UF/IFAS Extension. Publication date April 1997. Reviewed April 2014. Please visit the FAIRS website at http://hammock.ifas.ufl.edu. Please visit the EDIS website at http://edis.ifas.ufl.edu.

2.

D. L. Rockwood, Ph.D., professor emeritus, School of Forest Resources and Conservation; and G. F. Peter, associate professor, School of Forest Resources and Conservation;UF/IFAS Extension, Gainesville, FL 32611.


The Institute of Food and Agricultural Sciences (IFAS) is an Equal Opportunity Institution authorized to provide research, educational information and other services only to individuals and institutions that function with non-discrimination with respect to race, creed, color, religion, age, disability, sex, sexual orientation, marital status, national origin, political opinions or affiliations. For more information on obtaining other UF/IFAS Extension publications, contact your county's UF/IFAS Extension office.

U.S. Department of Agriculture, UF/IFAS Extension Service, University of Florida, IFAS, Florida A & M University Cooperative Extension Program, and Boards of County Commissioners Cooperating. Nick T. Place, dean for UF/IFAS Extension.