V Gets Worse! - fnps.org · Chinese Tallo\V Gets Worse! ",j~ //~) ... Holm, L., J.V. Pancho, J.P....

Post on 18-Aug-2018

214 views 0 download

Transcript of V Gets Worse! - fnps.org · Chinese Tallo\V Gets Worse! ",j~ //~) ... Holm, L., J.V. Pancho, J.P....

The PALMEITO, Fall 1993, Page 3

yellow to red in the fall. It flowersand fruits from the time it is aboutthree feet (l m) tall. Inflorescence onsome plants are solitary terminatingbranchlets, each narrowly cylindrical,two to eight inches (5-20 cm) long.On other plants, the inflorescence isbranched. The fruit is usually three­lobed with one seed in each lobe.Each fruit is about 0.4 of an inch (lcm) long and broad; it dehisces toleave three dull white, roundishseeds covered with a white, waxycoating that stay attached to the plantfor a period of time, and superficiallyresemble popcorn.

It is commonplace to find trees 15to 20 feet tall (4.5-6 m), with someolder sites having plants at heights of30 to 40 feet (9-12 m). The nationalchampion, located in Travis County,Texas, is 10 feet (3m) in circumfer­ence, 52 feet (l6m) in height, with an86-foot (26m) spread.Biology

Chinese tallow possesses the classi­cal characteristics of most exotic pestspecies: it grows quickly, fruits whenyoung, produces abundant seeds, isresistant to native pests, grows in awide range of soils, invades undis­turbed habitats, and has traits thatpeople find attractive and are there­fore promoted and distributed. Inmany cases, Chinese tallow has in­vaded Florida's ecosystems as a re-

by Greg Jubinsky

Since the initial introductions, it hasspread into coastal prairie habitats,and is now naturalized in the south­ern coastal plain from South Carolinasouth to Florida and west to Texas. InFlorida, it is distributed from theAlabama border eastward to Jack­sonville and south as far as Tampa.According to the most recent surveyconducted by the Department of Nat­ural Resources, the plant can pres­ently be found in 38 of the 67 Floridacounties and is rapidly invading wildareas where it has not been seenbefore, as evidenced by the fact thatthirteen of these counties have nu­merous populations, numbering atleast 50 trees per cluster, outside theornamental landscape. These clustersare found adjacent to wetlands and indisturbed sites. This is understand­able since Chinese tallow typicallythrives in upland, well-drained areasnear human habitation, as well asnatural, undisturbed areas such asclosed canopy forests, in bottomlandhardwood forests, on shores of waterbodies and sometimes on floatingislands.

DescriptionS. sebiferum is a small to medium­

sized tree with a milky sap that iscommonly thought to be poisonous.It is a popular ornamental because ofits fast growth, resistance to pests,and attractive foliage that becomes

Chinese Tallo\V Gets Worse!",j~

//~ )", \~ ~\//I~,-~J/ ," J' ',' ,/

/' .

/ /',' I', C"\'"' I

i., ." I .f,' / i ~

( /' Ii ~" 'I I \,' '\ ( r;"- '

1 ,i~

"",",/

In 1988,an article entitled "AnotherExotic Nuisance - the Chinese Tal­low Tree" by Steve Farnsworth, pub­lished in The Palmetto, Winter, 1988­89, referred to Chinese tallow tree(Sapium sebiferum) as the "north Flori­da melaleuca", in reference to "chill­ing" similarities to the south andcentral Florida pest: its potential forrapid expansion; its promotion bybeekeepers as a honey plant; and itsability to spread widely from a singleparent tree, especially in moist areas.

Chinese tallow tree - Sapiumsebiferum (L.)Roxb. - is a member ofthe Euphorbiaceae, a family of morethan 1,000species and varieties, manyof which are classified as poisonous.Thegenus Sapium consists of approxi­mately 100 species. Common namesfor S. sebiferum in the United Statesinclude popcorn-tree, Florida aspen,Chinese tallow and Chinese tallow­tree. The latter names arise from thefact that the outer layer of the seedcan be used to obtain solid vegetabletallow. The plant is known as thepopcorn-tree because of the appear­ance of white seeds when the cap­sules split open.Distribution

The tree is a native of China, whereit has been cultivated for at least 14centuries as a seed-oil crop. It hasbeen introduced to various subtrop­ical parts of the world, including theAmerican sunbelt, as an ornamentalplant. Earliest accounts reported thatit was brought to Charleston, SouthCarolina, in the late 17oos. In theearly 1900s the Foreign Plant Intro­duction Division of the U.S. Depart­ment of Agriculture's Bureau of PlantIndustry introduced it to the U.s.Gulf coast in significant numberswith the intent of establishing localsoap industries based upon the largeamounts of vegetable tallow foundaround the seed.

Additionally, an oil, known asstillingia oil, can be extracted fromthe seed, and has been thoroughlyinvestigated as an ingredient forvarnishes and paints. The oil is con­sidered poisonous and has beenproven to be toxic to cattle. The treeproduces heavy seed crops, and theoil in the seed averages 20% byweight.

Page 4, The PALMETTO, Fall 1993

sult of human introductions.The plant is deciduous, losing

leaves in autumn. Fruits ripen fromAugust to November. Maximum lifespan is probably less than 100 years,though root stocks may live muchlonger. Typical trees live only 15 to25 years.

The primary vectors for seed dis­persal are birds and moving waters.Preliminary studies indicate that theseeds can float for several weeks andstill maintain their viability. Thespecies also regenerates from stumpsprouts and is easily propagated bycuttings. It spreads over the land­scape at a high rate. Seedlings quick­ly produce a taproot system and areable to withstand extended periods ofdrought.

A high percentage of plants survivewhen inundated with fresh water,and when raised in soil wetted, butnot inundated, with brackish water,giving them the potential for invad­ing freshwater lakes and rivers, aswell as tidal estuarine and coastalwetlands.

Part of the flood tolerance in seed­lings may be due to heavy growth oflenticels and adventitious roots andthe production of thicker feeder roots.These traits are related to an abilityto oxidize root regions and are typi­cal of woody plants capable of sur­viving prolonged flooding and lowsoil redox potentials.

The plant is restricted by climateonly if temperatures drop belowabout O°F(-18°C).

S. sebifemm can have significanteffects on surrounding ecosystems.They may increase eutrophica tion byadding (actually recycling) nutrientsthrough decay of their leaves, whichis more rapid than that of native Salixnigra (black willow) and other decid­uous leaves. Furthermore, the plantproduces tannins, which are knownto inhibit the feeding of isopod andamaphipod invertebrates of aquaticsystems and which are also toxic tovertebrates.

Additionally, the plant producestoxic organic chemicals capable ofstupefying fish. It also produces skin­irritating and tumor-promoting esters.The latex is acrid and induces blister­ing. Florida biota are not adapted tothese powerful chemical defenses andwould, in many cases, be repressedby them.Management

In appropriate habitats, herbicidessuch as Garlon (triclopyr) and Banvel720 (dicamba plus 2,4-D) should be at

least partly effective for removing S.sebifer1l1n. Preliminary Department ofNatural Resources' test results sug­gest an 11% triclopyr solution withJLB Oil Plus controls trees with dbhless than 6 inches (15 cm); while a20% solution appears to work onlarger trees.

Cutting of horizontal shoots resultsin the immediate production of smallindependent plants, making mechani­cal control impractical.

Habitat manipulation may help tocontrol the plant. Controlled burningof Sapill1n is proposed to evaluatewhether this would work in Floridaecosystems.

The plant apparently lacks seriousinsect biocontrols or pathogens in theUnited States, though the bagworm,E1I1nefa, from Japan appears to be apest.Summary

Chinese tallow has been spreadingacross the southern coastal plain ofthe United States, including Florida.It is tolerant of shade, bright sun, andvarious soil conditions. It producesseeds after only three years ofgrowth, but it can also reproducevegetatively. The seeds are used asfood by wildlife, further disseminat­ing the plant. It monopolizes spaceand colonizes in greater density thannative flora. It competes with nativeplants that provide preferred coverand food for native fauna.

In short, it is bad news.

A copy of the complete 15-page report,titled "Snpium sebiferum, Literature Reviewand Status in Florida", is available fromTechnical Services Section, 3919 Common­

wealth Blvd., Mail Station 710, Tallahas­see, FL 32399-3000.

Greg Jubinsky is environmental adminis­trator for the Technical Services Sectionfor Aquatic Plant Management (formerlypart of the Department of Natural Re­sources; as of July 1, 1993, Departmentof Environmental Protection).

BIBLIOGRAPHY

Ansari, A.A., and G. Nand. 1987. Little known eco­nomic plants of Pauri Garhwal. Ind. J. Forest.10:316-317.

Aziz, P. 1987. Agro-botany of Sapium sebiferum,a rich source of tallow and stillingia oil. Biologia33:367-371.

Bailey, H.S. 1938. Vegetable tallow and stillingiaoil. Cotton Oil Press 4(1920):50.

Bonner, F.T. 1974. Sapium sebiferum (L.) Roxb. p.760. In C.S. Schopmeyer, Seeds of WoodyPlants in the United States. Ag. Handb. 450,Forest Serv., USDA, Washington, D.C.

Bradley, C.E. 1956. Yerba de la f1eche - Arrowand fish poison of the American Southwest.Econ. Bot. 10:362-366.

Brower, J.E., J.H. Zar, and C.N. von Ende. 1990.Field and Laboratory Methods for GeneralEcology. 3rd Ed. Wm. C. Brown Publ.,Dubuque, Iowa.

Cameron, G.N., and T.W. LaPoint. 1978. Effectsof tannins on the decomposition of Chinesetallow leaves by terrestrial and aquatic inverte­brates. Oecologia (Berl.) 32:349-366.

Cameron, G.N., and S.R Spencer. 1989. Rapidleaf decay and nutrient release in a Chinesetallow forest. Oecologia (Berl.) 80:222-228.

Davies, F.T. Jr., and C.A. Call. 1990. Mycorrhizaesurvival and growth of selected woody plantspecies in lignite overburden in Texas, USA.Agric. Ecosyst. Environ. 31 :243-252.

Farnsworth, S. 1988. Another exotic nuisance ­the Chinese tallow tree. The Palmetto, Winter1988-89.

Godfrey, RK., and JW. Wooten. 1981. Aquaticand Wetland Plants of Southeastern UnitedStates: Dicotyledons. Univ. Georgia Press,Athens.

Holm, L., J.V. Pancho, J.P. Herberger and D.L.Plucknett. 1979. A Geographical Atlas of WorldWeeds. Wiley-Interscience, New York.

Hook, D.D. 1984. Adaptations to flooding withfresh water. pp. 265-294. InT.T. Kozlowski, Ed.,Flooding and Plant Growth. Academic Press,New York.

Jones, RH., and KW. McLeod. 1989. Shadetolerance in seedlings of Chinese tallow tree,American sycamore, and cherrybark oak. Bull.Torrey Bot. Club 116:371-377.

Jones, R.H., and RR Sharitz. 1990. Effects ofroot competition and flooding on growth ofChinese tallow tree seedlings. Can. J. For. Res.20:573-578.

Jubinsky, G., and J.D. Oliver. 1992. Suppressionand survival of carrotwood and Chinese tallow

in varying salinity, temperature, light and inun­dation conditions. Fla. Dept. Nat. Res., Bur. Aq.Plant Manage., Tallahassee.

Lieux, M.H. 1975. Dominant pollen types recov­ered from commercial Louisiana USA honeys.Econ. Bot. 29:87-96.

Liu, S.-Q., J.M. Pezzuto and A.D. Kinghorn. 1988.Additionally biologically active constituents ofthe Chinese tallow tree (Sapium sebiferum). J.Natur. Prod. 51 :619-620.

MacGowan, J.D. 1851. Uses of Stil/ingia sebiferaor tallow tree, with a notice of the pe-Ia, aninsect-wax of China. Am. J. Sci.12:17-22.

McDonald, D.L. 1989. A survey of public plantingsin the front yards of residences in Galveston,Texas, USA. J. Ethnobiol. 9:31-46.

Miller, RH., and G.N. Cameron. 1983.Intraspecific variation of life history parametersin the terrestrial isopod Armadillidium vulgare.Oecologia (Berl.) 57:216-226.

Munroe, C. 1981. Restoration and management ofthe Armand Bayou Prairie, Ohio BioI. Surv. BioI.Notes 15:Abstracts.

Nishida, E. 1983. Biologies and parasite complex­

es of two bagworms, Eumeta japonica andEumeta minuscula (Lepidoptera, Psychidae), inJapan. Kontyu (Tokyo) 51 :394-411.

Presnell, R 1992. Pers. comm. to J.D. Oliver,Northwest Fla. Water Management District.

Rielly, F.J. 1947. An investigation of the oil fromthe seed of Sapium sebiferum. Master's Thesis,Texas A&M Univ.

Russell, L.H., W.L. Schwartz and J.W. Dollahite.1969. Toxicity of Chinese tallow tree (Sapiumsebiferum) for ruminants. Am. J. Vet. Res.30:1233-1238.

Scheid, HW., and J.R. Cowles. 1981. Woodybiomass potential of the Chinese tallow treeSapium sebiferum. Econ. Bot. 35:391-397.

Seibert, M., G. Williams, G. Folger and T. Milne.1986. Fuel and chemical co-production fromtree crops. Biomass 9:49-66.

Seip, E.H., H.H. Ott and E. Hecker. 1983. Skinirritant and tumor promoting diterpene esters ofthe tigliane txpe from the Chinese tallow tree(Sapium sebiferum). Planta Med. 49:199-203.

Singh, R.PI, and A. Pal. 1990. Development andstructure of seeds in Chinese tallow-treeSapium sebiferum Roxb. (Euphorbiaceae). Flora184:15-20.

Weimer, J.E. 1992. Pers. comm. to G. Jubinsky,Paynes Prairie Preserve, Florida Dept. of Nat.Res.

Whitcomb, C.E. Undated. Know it and grow it, II.A guide to the identification and use of land­scape plants. Dept. of Horticulture, OklahomaState Univ.

Zar, J.H. 1984. Biostatistical Analysis. 2nd Ed.Prentice-Hall, Inc. Englewood Cliffs, N.J.