Research Cactoblastis cactorum (Lepidoptera: Pyralidae) in the United States: An Immigrant Biological Control Agent or an Introduction of the Nursery Industry? Robert w: Pemberton ABSTRACT Miami APHIS-Plant Protection & Quarantine records showed 13 Cactoblastis cactont11t Bergroth interceptions in commercial nursery imports of Opulltia from the Dominican Republic between 1981 and 1986. These interceptions and the large volume of underinspected cacti that have been imported from the Dominican Republic and other countries with C. cactont11t suggest that the moth may have entered Florida as an unintended commercial introduction. The present problem with C. cactontm relates the difficulty of preventing pest introductions with commercial plant imports and, to a lesser degree, the historical introduction of the moth to the Caribbean and habitat destruction that has contributed to the rarity of some American Opulltia. T HERE IS NO EVIDENCE THAT AGENTS INTRODUCED FOR THE BIOLOG- ical control of weeds have reduced populations of native nontarget plants, although there are a few reports of t::1eiruse of native plants as hosts (Center 1982, Andres 1985, Turner 1985, Turner et al. 1987). The recent advent of Caetobias tis cactorum Bergroth in Florida, however, appears to alter this perception (Simberloff 1992). Although not deliberately introduced to Florida, the moth was purposely introduced to the Caribbean for the control of weedy Oplllttia cacti (Habeck and Bennett 1990). It has been assumed that the moth spread naturally to Florida from the Caribbean (Habeck and Bennett 1990, SimberloH 1992). It may be an immigrant, reaching the U.S. mainland on its own, but it is also possible that it was brought in accidently through commerce. Caetoblastis eaetorum was found established in the Florida Keys in October 1989 (Habeck and Bennett 1990). This moth, a native of Argentina, Uruguay, and Paraguay, was used successfully to control seven species of pest Opulltia cacti in Australia, Hawaii, and elsewhere (Dodd 1940, Fullaway 1954, Julien 1992). Within its native range, C. eactorum is known to breed in 1 species of CleistDcactlls and all but one Opulltia (at least 15 species); the species not used is the usual host of Cactoblastis doddi Heinrich (Mann 1969). Because C. caetomm attacks most all Opulltia species, its recent introduction into the United States is a cause for concern. Indeed, i: is currently threatening three rare or restricted Florida cacti: Opulltia spillosissima (Martyn), O. triaeantha (Willdenow), and O. cubensis Britton and Rose, whose populations have been reduced by habitat destruction (Bennett and Habeck, in press). Comparisons of the mean low temperatures of some of the known South American localities of the moth with various North American localities suggest that C. caetortlm has the potential to spread throughout the warmer areas of the United States and Mexico. In the United States, it should be able to reach Charleston, SC; San Antonino, TX; and the lower altitude areas of New Mexico, Arizona, and California nortt to Sacramento. The degree of the moth's use of, and impact on, Opulltia species varies in its native area and the places where it has been employed as a biological control agent (Mann 1969, McFadyen 1985, Moran 1984; Pemberton, unpublished data). Although specific interactions cannot be predicted, the moth appears to have the ability to reduce significantly the populations of some rare and common North American Opuntia species. Two of the species, O. illermis Candolle and O. strieta (Haworth), successfully controlled in Australia, are native to North America (Dodd 1940). One of these, O. stricta, C. eactorum's most common host in Florida, grows around the Gulf of Mexico (Long and Lakela 1971) and could assist the moth's spread to Texas and Mexico. There are noCleistoeaetus species in the Unit- 230 ed States but there are 46 species of native Opuntia (USDA 1982), one of which (Opl/Iltia treleasei [Coulter]) is a federally protected endangered species (U.S. Dep. Interior 1993a); 12 other taxa (6 subspecies and 6 species) are under review for protected status (U.S. Department of the Interior 1993b). Following successful introductions elsewhere in the world, C. cactorum was introduced to Nevis Island in 1957 where it dramatically controlled the target cacti, O. dillel1ii (Ker-Gawler), O.lindheimeri Englemann, and O. triacal1tha (Willdenow) (Simmonds and Bennett 1966). Because of its success, it subsequently was introduced to other islands with cactus problems: to nearby Montserrat and Antigua in 1962 and to Grand Cayman, below Cuba, in 1970 (Bennett et a!. 1985). It also established on these islands and, additionally, was found in Puerto Rico in 1963, presumably moving on its own from the Lesser Antilles (Garcia-Tuduri et al. 1971). Subsequently, the moth was found in Haiti, the Dominican Republic, and the Bahamas (William Starmer, personal communication). In 1989, it was detected in the Florida Keys by Carol Lippencott, of the Fairchild Tropical Garden, Miami (Simberloff 1992). She searched for the moth because it was predicted to spread to Florida (Starmer et al. 1987), based on its occurrence in the Bahamas, Cuba, and elsewhere in the West Indies (SimberloH 1992). After learning that cacti are imported to Florida from other countries by the state's nursery industry, I contacted the USDA-APHIS, Plant Protection & Quarantine (PPQ), Hyattsville, MD, to learn of possible interceptions of C. cactorum at U.S. ports of entry, and the status of cactus introductions before 1989 when the moth was first detected in Florida. Three PPQ data sources were used: (1) the Hyattsville computer base of pest insect interceptions; (2) individual interception records (PPQ 309 forms) on file at the Plant Inspection Station in Miami, FL; and (3) the Miami station's monthly reports of importation of regulated articles (PPQ 280 forms), in which summary statistics of cactus imports are noted. The computer database covering the years 1985-1992 contained 4 records of C. eaetorum interceptions. Three interceptions occurred in Miami and involved commercial imports of O'Jtmtia pads from the Dominican Republic. The other interception was of 01J1mtia fruit detected in personal airline baggage brought to Dallas from Cancun in Mexico. C. caetorum is not known to be established in Mexico, although this interception from Cancun suggests that it may now occur there. Table 1 shows the 17 interceptions of C. cactorum made at the Miami station, including the 3 Hyattsville computer records for Miami. All of the Opwltia in which the moth was detected were commercial imports of vegetative material intended for propagation. All of the detected C. eactorum were alive, half of the intercepAMERICAN ENTOMOI.()(;IST • Winter 1995 Table 1. Interceptions of C. cacto",m at the USDA-APHIS-PPQ inspection station in Miami, FL Date found Aug.lnl Sept. 19112 Aprilln3 June 1983July 1983 Mar. 19115 April 19116 .June In6" Oct. Oct. Nov. Nov. Nov. Sept. Sept. Sept. Sept. 1986 19116 19116 19116 19116 1991' 1993 1993 1993 Origin Dominican Dominican Dominican Dominican Dominican Dominican Dominican Dominican Dominican Dominican Dominican Dominican Dominican Dominican Haiti Haiti Haiti No. found Republic Republic Republic Republic Republic Republic Republic Republic Republic Republic Republic Republic Republic Republic 39 5 2 8 2 I3 1 1 1 1 1 1 10 1 10 2 1 adults larvae larvae larvae larvae larvae larvae larvae larvae larvae larvae larvae larvae larvae larvae larvae larvae Shipment sIze 3,850 1,200 1,000 1,000 1,490 80 5 4 5 2,400 1 1 1,650 8 4 10 7 cuttings cuttings cuttings plants cuttings plants crates crates era res cuttings crate crate plants boxes boxes boxes boxes plant % inspected 20 5 10 2 10 1.3 20 25 20 10 100 100 10 12.5 25 10 14.2 Host cacti in which C. cactomm were found were reported only as species, except in the tbree cases indicated by footnotes. -Of/III/tia Maverick. {'Of/lllltia Espina. 'Of/III/tia ita/ica Tenore. O/JIII/ita tions had more than one individual, and, other than the adults found in 1981, all of the interceptions were of larvae. The interceptions of C. cactomt11, except 3 from Haiti entering with cacti sent by ship, were in cacti arriving by air. All shipments in which the moths were detected were fumigated with methyl bromide. The insects intercepted in 1981 and 1982 were identified only as members of the Phycitinae the subfamilv to which Cactoblastis and most other cactus mo~hs belong. Gi~en the large number of C. cactomm subsequently intercepted from the Dominican Republic, it seems probable that these too were C. cactorllt11. Because 7 of the 17 C. cactorzml interceptions were made in ] 986, the monthly summaries of cactus imports for that year were examined. Unfortunately, these summaries lump all cacti genera and species together, and the inspection work sheets from which the information was compiled no longer exist. Those imports from countries known to have C. cactomm are listed in Table 2. Although the quantity of Opllntia imported from countries in 1986 cannot be known precisely, some of the inspectors (such as Gordon Muraoka) who worked in the APHIS-PPQ Miami station during that time remember the nature of cactus imports for that period. Imports from Brazil were grafted cacti that were not Oplmtia. Most of the shipments from the Dominican Republic and Haiti contained species of Opt/lltia and other cacti genera. Most of the Oplmtia imports consisted of single pads packed in layers of newspaper in banana-type boxes (2 by 2 by 4 ft). Dominican Republic shipments were fumigated during 6 of the 12 mo in 1986. It is, and was in the 1980s, APHIS-PPQ policy to inspect from 1-25% of each commercial horticultural import shipment (internal operational guidelines for inspection). Usually ",2% of each shipment is examined (G. Muraoka, personal communication). After reading a shipment manifest, the inspector requests that a certain number of boxes, representing samples of different plant species or varieties and sizes, be removed from the shipping container or taken off the pallet. The samples are selected by the customs broker, the owner, or his designee. Air shipments are more accessible (boxes sitting on a pallet) and are much smaller, usually <30 boxes. Shipments in marine truck trailer shipping containers often contain hundreds of boxes. Sampling representative types of air and sea shipments results in a higher percentage of air shipments being inspected. The AMFRICAN ENTml010GIST • Winter 1995 long spines of many of the Opuntia species also inhibit their inspection because specimens are difficult to handle and repack after inspection. Cactoblastis cactorllm has been detected at some of Florida's commercial nurseries since 1991 (Florida Department of Agriculture and Consummer Services, Division of Plant Industry, Entomology Section detection records). Costa Nurseries in Dade County, Florida, have had C. cactorum problems for several years (Tony Costa, Costa Nursery, personal communication). These nurseries are the largest importers of cacti entering the United States through Miami. Most of the cacti that they import are grown at their nursery in the Dominican Republic. That nursery also has had problems with C. cactorum; the moth infests up to 10% of the cactus plants despite control efforts. The 13 C. cactorum interceptions in Miami prior to 1989 (Table 1) were all in air freight from the Dominican Republic. Most of the larger volume shipments were, however, marine (Gordon Muraoka, personal communication). This suggests that the moth may have evaded detection in the less thoroughly inspected marine shipments. It also may have gone undetected in air freight because only a small percentage of this material was inspected and the larvae, which feed internally in the pads, are less obvious than many external feeders. Given the large numbers of cacti entering the United States from the Dominican Republic, >350,000 specimens in 108 shipments in 1986 alone, this is not unlikely. The moth could have been introduced from anywhere in its current range, but the chance of its entering undetected increases with the large commercial shipments. Because the moth was detected first in the Keys based on a prediction of its natural spread to Florida, the assumption has been that it became established there and then spread rapidly northward (Bennett and Habeck 1996). The information that I have assembled suggests that C. cactorum could have been introduced by the nursery industry, become established somewhere in the southern counties of Florida, and then spread rapidly northward and southward. The likely introduction of C. cactorum into the United States through commercial plant introductions points to the difficulty in the detection and exclusion of pests associated with plant imports. During 1993,,,,456 million exotic plants were imported through the 16 USDA-APHIS-PPQ plant introduction facilities (Center et al. 1995). Regardless of whether C. cactorum is an immigrant or an introduction, problems associated with the moth would probably not exist if the moth had not been introduced into the Caribbean. This introduction was, in my opinion, unwise because the Caribbean and other warm areas in the Western Hemisphere are rich in OfJulttia species that could have (and have) become nontarget hosts for the moth. Australia, South Africa, Mauritius, and Hawaii, where the moth was previously used, have no native cacti that could have become hosts. Another problem is that the cactus species (0. triacantha) for which the moth was introduced into Nevis is native to Nevis and other parts of the West Indies and Florida. It is now considered a Table 2. Imports Miami in 1986 Country of origin with C. cactorum, entering of cacti, from countries No. shipments No. imported No. fumigated 719,139 356,394 11,991 200 13,985 217 Brazil Dominican Republic Haiti Jamaica St. Barthelemy 29 108 4 2 1 7 1 Argentina Total 1 145 24 1,087,556 24 killed 231 valued rare plant in Florida (U.S. Department of the Interior 1993b). The moth's introduction into Nevis and its usc in the Caribbean was during a different era, before the increased development, spread, and legal codification of native plant conservation values. Relatively few biological control introductions have been made against native plants that arc weeds (Julien 1992). The practice has been advocated by some (Deloach 1980, Johnson 1985) and questioned by others (Andres 1980, Pemberton 1985a, Turner 1985). The issue is complex but relates primarily to differing perspectives and attitudes about the worth and uniqueness of native plants that are weeds and the appropriateness of using biological control to reduce them. Introduced weeds with close native relatives are routinely targeted, but more attention is given to the safety of nontarget plants in this era than in earlier times, when the safety concerns were focused on economic plants (Pemberton 1985b, Soper 1992). Acknowledgments I thank the following individuals for sharing data and information essential to this story: Susan Broda-Hydorn and Gordon Muraoka (Miami), Joe Cavey (Hyattsville, MD), and Richard Elliot (Dallas), all ofUSDA-APHIS-PPQ; Debra Chalot and Harlo von Wald (Miami), and Michael Thomas (Gainesville), all of the Florida Department of Agriculture and CO::Jsummer Services, Division of Plant Industry; Tony Costa of (Costa Nurseries, Homestead, FL); William Starmer (Department of Biology, Syracuse University); Maria Solis (USDA-ARS Systematic Entomology Laboratory, Beltsville, MD); and Dale Habeck (Department of Entomology and Nematology, University of Florida, Gainesville). Ted Center (Aquatic Plant Management Laboratory, USDA-ARS, Ft. Lauderdale, FL); William Kemp (Rangeland Insect Laboratory, USDA-ARS, Bozeman, MT); and William Starmer and Peter Stilling (Department of Biology, University of South Florida, Tampa) kindly reviewed the manuscript. References Cited Andres, L. 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The waterhyacinth weevils. Aquatics 4: 8, 16, 18-19. Center, T. D., J. D. Frank, and F. A. Dray. 1995. Biological invasions: stemming the tide in Florida. Fla. Entomo!. 78: 45-55. Deloach, C. J. 1980. Prognosis for biological control of weeds of southwestern U.S. rangelands, pp. 175-199. [/1 E. S. Delfosse [ed.], Proceedings, 5th International Symposium Biological Control of Weeds, Brisbane, Australia. CSIRO, Australia. Dodd, A. P. 1940. The biological campaign agail}st prickly pear. Commonwealth Prickly Pear Board, Brisbane, Australia. Fullaway, D. T. 1954. Biological control of cactus in Hawaii. J. Econ. Entomo!. 47: 696-700. Garcia-Turduri, J. c., L. F. Marrorell, and S. M. Gaud. 1971. Geographical distribution and host plants of the cactus moth, Cactoblastis cactomm (Berg) in Puerto Rico and the United States Virgin Islands. J. Agric. Univ. P.R. 55: 130-135. Habeck, D. H., and F. D. Bennett. 1990. Cactoblastis caetorum Berg (Lepidoptera: Pyralidae), a Phycitine new to Florida. Fla. Dep. Agric. Con- 232 sum .. ServoDiv. Plant Ind. Entomo\. Circ. 333. Johnson, H. B. 1985. Consequences of species introductions and removals on ecosystem function-implications for applied ecology, pp. 27-56. 111 E. S. Delfosse [ed.], Proceedings, 6th International Symposium Biological Control of Weeds, Vancouver, BC Canada. Agriculture Canada. Julien, M. H. [ed.]. 1992. Biological control of weeds, a world catalogue of agents and their target weeds. 3rd. ed. Commonwealth Agric. Bur. Int., Wallingford, UK. Long, R. \V., and O. Lakela. 1971. A flora of tropical Florida. University of Miami Press, Coral Gables, FL. Mann, J. 1969. Cactus-feeding insects and mites. U.S. Nat\. Museum Bul!. 256. McFadyen, R. E. 1985. Larval characteristics of Cactoblastis spp. (Lepidoptera: Pyralidae) and the selection of species for biological control of prickly pears (Opumia spp.). Bul!. Enromo!. Res. 75: 159-168. Moran, V. C. 1984. The biological control of cactus weeds: achievements and prospects. Biocontrol News Information 5: 297-320. Pemberton, R. W. 1985a. Native weeds as candidates for biological control research, pp. 869-877. [liE. S. Delfosse [ed.], Proceedings, 6th International Symposium Biological Control of Weeds, Vancouver, BC Canada. Agriculture Canada. 198<;b. Native plant considerations in the biological control of leafy spurge, pp. 360-390. [11 E. S. Delfosse [ed.], Proceedings, 6th International Symposium Biological Control of Weeds, Vancouver, BC Canada. Agriculture Canada. Simberloff, D. 1992. Conservation of pristine habitats and unintended effects of biological control, pp. 102-117. !II W. C. Kauffman and J. E. Nechols [eds.], Selection criteria and ecological consequences of importing natural enemies. Thomas Say Publications in Enromo!. Entomological Society of Amer., Lanham, MD. Simmonds, F.J., and F.D. Bennett. 1966. Biological control of Oplll/tia spp. by Cactoblastis cactortlm in the Leeward Islands (West Indies). Entomophaga 11: 183-189. Soper, R. S. 1992. USDA, Agricultural Research Service National Biological Control Program: program, policy, and constraints, pp. 49-52. [II R. Charudattan and H. W. Browning [eds.], Regulations and Guidelines: Critical Issues in Biological Control, Proceedings of a USDA! CSRS national workshop, Gainesville, FL. Institute of Food and Agricultural Sciences, University of Florida, Gainesville. Starmer, W. T., V. Aberdeen, and M. Lachance. 1987. The yeast community associated with decaying Oprll/tia stricta (Haworth) in Florida with regard to the moth Cactoblastis cactortlm (Bergl. Fla. Sci. 51: 7-11. Turner, C. E. 1985. Conflicting interests in biological control of weeds, pp. 203-225. [II E. S. Delfosse [ed.], Proceedings, 6th International Symposium Biological Control of Weeds, Vancouver, BC Canada. Agriculture Canada. Turner, C. E., R. \V. Pemberton, and S. S. Rosenthal. 1987. Host utilization of native Cirsium thistles (Asteraceae) by the introduced weevil Rhil10cyllus cOllicus (Coleoptera: Curculionidae) in California. Environ. Entomo!. 16: 111-115. U.S. Department of Agriculture, Soil Conservation Service. 1982. National list of plant names. U.S. Dep. Agric.Tech. Pub!. 159. U.S. Department of the Interior, Fish and Wildlife Service. 1993a. Endangered and threatened wildlife and plants. Title 50 Code of Federal Regulations 17.11 and 17.12. 1993b. Endangered and threatened wildlife and plants; review of plant taxa for listing as endangered or threatened species. Fed. Reg. 58: 51144-51190. Received for publicatioll 27 December 1994; accepted 3 August 1995. • Robert Pemberton is a research entomologist with USDAARS Aquatic Plant Management Laboratory, 3205 College Avenue, Ft. Lauderdale, FL 33314. He does research on biological control of insect and weeds. and on arthropod-plant mutual isms (involving extrafloral nectaries and leaf domatia), which result in plant protection. He recently contributed to the American Entomologist on ethnoentomology, an interest stimulated by many years of work in Asia. AMERICAN ENTOMOLOGIST • Willter 1995
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