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Biology, History, Threat,Surveillance and Controlof the Cactus Moth,Cactoblastis cactorum

Biology, History, Threat,Surveillance and Controlof the Cactus Moth,Cactoblastis cactorumH. ZimmermannS. BloemH. KleinFAOJoint FAO/IAEA Programme ofNuclear Techniques in Food and Agriculture

BIOLOGY, HISTORY, THREAT,SURVEILLANCE AND CONTROLOF THE CACTUS MOTH,Cactoblastis cactorumIAEA, VIENNA, 2004IAEA/FAO-BSC/CMPrinted by the IAEA in AustriaJune 2004ISBN 92-0-108304-1

FOREWORDAlien invasive insect pests are increasinglythreatening agriculture and the environment. In thecontext of the rapidly growing international traveland trade, the potential for moving dangerous pestspecies to new geographic regions and locations hasbeen drastically increasing. The United StatesDepartment of Agriculture (USDA), Animal andPlant Health Inspection Service (APHIS) reportsthat the expanding flow of passengers and cargo isfar outpacing the inspection capabilities despiteincreases in funding, staffing and use of technology.The potential threat of bio-terrorism also adds tothe complexities of excluding major foreign pestspecies.Under the Convention of Biodiversity, theInternational Plant Protection Convention (IPPC)and other binding international treaties that alsoaddress alien invasive species, prevention of entry isrecommended as a far more cost effective andenvironmentally desirable measure than othermeasures that have to be taken once introduction ofan alien invasive species has occurred. As such,offshore pest risk mitigation at the point of origin isrecommended as the most viable approach to pestprevention and exclusion. In this approach,identifying potential invasive pests that are high riskso that appropriate preventive and preparednessstrategies can be developed is of paramountimportance.Unfortunately, safeguarding systems are oftenbreached and major alien invasive pests continue toenter and spread, even in countries such asAustralia, Chile, Japan, New Zealand and the USA,which are purported to have state-of-the-artquarantine systems in operation. Once theestablishment of an alien invasive species has beendetected, the above mentioned internationalconventions urge countries to give priority toeradication over containment or managementmeasures. Of course the best opportunity foreradicating introductions of alien invasive species isin the early stages of invasion, when populations aresmall and localized.However, appropriateresponse strategies and tools are in many cases notavailable to eradicate outbreaks of invasive pestintroductions, thus forcing countries to only employcontainment or mitigation measures. Moreover,some of the existing eradication methods aresomewhat controversial or at risk of being phasedout as a result of laws like the Food ProtectionQuality Act (FQPA) in the USA.The Sterile Insect Technique (SIT), beingenvironment-friendly and acting inversely densitydependent and therefore optimally suited to dealwith invasive pest populations up to the lastindividuals, is the ideal tool to complement effortsto eliminate beach-heads of alien insect invasions.Examples of successful integrated application ofSIT in such a context include the eradication of theNew World Screwworm from the Libyan ArabJamahiriya, and of medfly in California and Florida.Australia has invested considerable efforts indeveloping the SIT for the Old World Screwwormto be able to address potential outbreaks of this pestinsect, which would cause major economic damageto its livestock industry in case it becameestablished. California has stand-by contracts inplace for the provision of sterile flies of variousAnastrepha fruit fly species, and New Zealand,being fruit fly-free, has considered a similarapproach to be able to procure sterile flies in thecase of fruit fly outbreaks.Unfortunately, however, SIT methodologieshave not been developed for many of the majorpotential invasive pest species for which it couldplay an important role in eradicating incipientoutbreaks. Among the USDA-APHIS Exotic PestArthropod List for the USA, which highlights 100high-risk pests, ca. fifty percent of this “worst of theworst” list are from the order Lepidoptera. Many ofthese Lepidoptera are a threat not only to the USAbut also to many other regions of the world.Nevertheless, research to develop SIT for these highrisk, exotic lepidopteran pests is lacking in mostcases (gypsy moth and false codling moth being anexception). Cooperative efforts are needed todevelop appropriate response strategies that wouldinclude eradication technologies in advance ofinvasive lepidopteran pest introductions.One is the cactus moth, Cactoblastis cactorum(Pyralidae). Known as the best example ofsuccessful biological control of weeds in Australiaand elsewhere, it was detected in Florida in 1989and has been rapidly expanding its range along theAtlantic coast and the Gulf of Mexico. C. cactorumis now considered a serious threat to the highdiversity of Opuntia species throughout the world,both native and cultivated. Its presence in the

Caribbean and its rapidly expanding range in thesoutheastern USA represents an imminent threat toareas in the southwestern USA, Mexico, andCentral/South America where Opuntia cacti areregarded as extremely important plants, especiallyin arid and semi-arid regions. These plants play arole in subsistence and commercial agriculture, inmaintaining ecological balance in these uniqueecosystems, and in soil conservation. As a result ofworldwide increases in Opuntia cultivation andincreased reliance on Opuntia as a source of foodand income from its products, the invasion byC. cactorum has the potential to impact thousandsof subsistence farmers in Central and SouthAmerica, the Mediterranean, North Africa andother countries. Furthermore, impacts onbiodiversity and ecosystems where Opuntia aredominant components of the vegetation, includingthe centre of Opuntia radiation, Mexico, also loomlarge. The critical nature of this threat, and thetiming and scale of the likely responses needed,require immediate action. Although the emphasisof an intervention campaign may initially focus onMexico, Cuba, other Caribbean islands and theUSA, this does not mean that the threat is lessimportant in other countries. Any effectivecontingency/control programme will need to beapproached on a regional or even interregionalscale.To raise awareness of this major environmental threat and of the potential effectiveness of SIT tohelp address the control of alien species, the FAOand IAEA hosted a planning and co-ordinationmeeting, that included representatives of some environmental organizations. The meeting participantsassessed the role that SIT/F1 Sterility could play inaddressing the cactus moth invasion as a model forthe invasive pests affecting not only agriculture butthe environment. We foresee an increased role inthe use of SIT for suppression of alien invasivespecies that will help FAO and IAEA MemberStates deal with the threat of outbreaks of suchpests.This publication on Cactoblastis was fundedby the IAEA and summarizes the currentknowledge on history, biology, threats, surveillanceand control of this insect. It is part of a widerpublicity campaign to draw attention to the threatof Cactoblastis to the Opuntiae of North Americawith emphasis on Mexico and the USA. This threatshould not only be the concern of countries forwhich the risk is imminent but should constitute aglobal concern, as the social, environmental andeconomic effects of C. cactorum would bedevastating in any country where Opuntia cacti area significant resource.The IAEA is grateful to H.G. etoria, South Africa), S. Bloem (Centre forBiological Control, Florida A&M University,Tallahassee, Florida, USA) and H. Klein (ARCPlant Protection Research Institute, Pretoria, SouthAfrica) for drafting this publication. This work isunique and represents a major contribution to thecactus moth problem worldwide.The IAEA also wishes to thank those whocontributed to the preparation and review of thispublication as follows: K. Bloem and S. Hight(USDA-ARSTallahassee,Florida,USA),J. Carpenter (USDA-ARS Tifton, Georgia, USA),J. Hosking (Dept. Agriculture, NSW, Australia),J. Perea and M. Perez-Sandi y Cuen (SAGARPASENASICA-DGSV, Mexico), and A.L. Alfaro(Mexico), as well as A. Madero for photographs ofnative Mexican cacti, B. Brobbelaar and F. ria, South Africa), J. Hoffmann (University ofCape Town, South Africa) and H. Robertson (SouthAfrican Museum) for photographs of cactoblasticsand its predators, and P. Stiling (University of SouthFlorida, Tampa, Florida, USA) for a photograph ofthe semaphore cactus.The IAEA officer responsible for thepublication was W. Enkerlin of the Joint FAO/IAEA Programme of Nuclear Techniques in Foodand Agriculture.EDITORIAL NOTEThe use of particular designations of countries or territories does not imply any judgement by the publisher, theIAEA, as to the legal status of such countries or territories, of their authorities and institutions or of the delimitation of their boundaries.The mention of names of specific companies or products (whether or not indicated as registered) does not implyany intention to infringe proprietary rights, nor should it be construed as an endorsement or recommendation onthe part of the IAEA.

CONTENTSINTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .1CHAPTER 1: Taxonomic status of Cactoblastis cactorum . . . . . . . . . . . . . . . . . .3The cactus-feeding Pyralidae . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .3The genus Cactoblastis . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .3Cactoblastis cactorum (cactoblastis) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .3CHAPTER 2: The biology of Cactoblastis cactorum . . . . . . . . . . . . . . . . . . . . . . .7Life cycle . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .7Duration of life stages . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .8Fecundity . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .9Damage to host plants . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .9Oviposition behaviour . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .10Dispersal ability and spread . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .10CHAPTER 3: Host plants of Cactoblastis cactorum . . . . . . . . . . . . . . . . . . . . . . .11Natural hosts in South America . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .11Extended host ranges outside its natural distribution . . . . . . . . . . . . . . . . .11Basis for host preference of Cactoblastis . . . . . . . . . . . . . . . . . . . . . . . . . . . .12CHAPTER 4: The history of Cactoblastis cactorum as abiological control agent . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .17Deliberate distribution of Cactoblastis cactorum (cactoblastis)as a biological control agent . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .17The inadvertent dispersal of C. cactorum to additionalCaribbean Islands and North America . . . . . . . . . . . . . . . . . . . . . . . . . . . . .21

CHAPTER 5: Cactoblastis cactorum as a threat . . . . . . . . . . . . . . . . . . . . . . . . . . .24Potential dispersal routes to Texas, adjacent States and Mexico . . . . . . . .24Threat to the United States and Mexico . . . . . . . . . . . . . . . . . . . . . . . . . . . .24Threat to other countries . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .26CHAPTER 6: The surveillance and control of Cactoblastis cactorum . . . . . . . .29Prevention (inspections, phytosanitary methods, early detection,public vigilance) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .29Surveillance . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .29Control . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .30Research . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .35CONCLUSIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .36REFERENCES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .37

INTRODUCTIONCactoblastis cactorum (cactoblastis) has becomefamous for its contribution to the spectacularcontrol of various invasive Opuntia species, notablyin Australia where it has cleared 25 million hectaresof land invaded by Opuntia stricta. Today, the“Cactoblastis Memorial Hall” (Fig. 1) and the“Cactoblastis Cairn” in Queensland are amongstthe memorabilia celebrating these remarkableevents. This success was replicated, to a lesserextent, in South Africa and more so in the LeewardIsland group of the Caribbean Islands. What wasnot foreseen at that time was the natural, accidentaland possibly deliberate spread of the insectthroughout the Caribbean Islands, which wouldlead to its unexpected arrival in Florida around1989.The first alarm signals announcing this event camefrom Habeck & Bennett (1990) and Dickle (1991),and from Pemberton (1995). But it was not until thepublications by Johnson & Stiling in 1996 and 1998,and of Zimmermann & Perez-Sandi in 1999, thatthe authorities recognized the imminent disaster inthe event of the cactus moth’s arrival in Mexico(Fig. 2). A recurrence of the Australian experiencein Mexico was unthinkable. Furthermore, theextremely rapid dispersal of C. cactorum along theFlorida coast over the past ten years also broughthome the necessity of halting the continueddispersal of the moth (Hight et al. 2002).The first initiative came from concerned entomologists from the USDA-APHIS National BiologicalControl Institute and the Cactus and SucculentFIG. 1. Boonarga Memorial Hall in Australia, in honourof cactoblastis.FIG. 2. Native Mexican cacti.1

Society of America, who co-funded the firstworkshop on cactoblastis in Tampa, Florida, inSeptember 2000. Several specialists on cactoblastisand on the Cactaceae were invited, and their contributions were published in volume 84 no. 4 ofFlorida Entomologist, 2001. The questions that wereraised and which were only partially answered were:sanitary officers in Mexico to the dangers of thecactus moth and to the importance of earlydetection and control. These activities are mostcommendable and encouraging and it is hoped thatfurther international support, co-funded by theUSDA-APHISandSAGARPA,willbeforthcoming to carry this project forward.How far is cactoblastis likely to expand itsrange? How will it affect natural stands of Opuntiaspp. and other species of plants and animalsthat depend on this resource? How will it affect the agricultural and horticultural uses of prickly pear? How can it be controlled? How will this situation affect the science andapplication of classical biological control,particularly of weeds?Urgent research is needed to address gaps in ourknowledge on cactoblastis, including the refinementof the application of the F1 sterility technique, moreaccurate predictions of its potential impact oncultivated and native Opuntia species in Mexico andthe USA, and of its expected rate of dispersal inNorth America. To this end, all knowledgeconcerning cactoblastis that is available elsewhere,e.g. in Australia, Argentina and South Africa, has tobe drawn upon.The first international involvement came when theInternational Atomic Energy Agency (IAEA)recognized the potential of the inherited (or F1)sterility technique (Carpenter et al. 2001a) in haltingthe further spread of cactoblastis. They supportedresearch, an international consultants meeting andseveral activities aimed at evaluating the feasibilityof the F1 sterility technique for this purpose. TheMexican Government (through SAGARPA andCONABIO), in collaboration with, and withsupport from IAEA and FAO, initiated a rigorouscampaign to alert all stakeholders and phyto-Currently, the sex pheromone of cactoblastis isbeing identified and will be used as a monitoringtool. In addition mass rearing methods are beingrefined in the USA and in South Africa. Lastly, theradiation biology for the cactus moth has beendetermined (Carpenter et al. 2001b). An SIT/F1sterility programme is being considered to preventfurther geographical expansion of this moth, but theuse of F1 sterility is also being assessed as a tool todetermine the eventual host and geographical rangeand to study the rate of spread of this invadinginsect. 2

CHAPTER 1Taxonomic status of Cactoblastis cactorumThe cactus-feeding PyralidaeThe genus CactoblastisThe sub-family Phycitinae of the family Pyralidaehas about twenty genera with no fewer than 58species, which are associated exclusively with theCactaceae. Cactoblastis is one of these genera.Except for the genus Ozamia, which is found inboth Americas, all genera are geographicallyisolated, either in the north or in the south. Cactoblastis is a genus found only in South America andits equivalents in the north are the genera Melitaraand Olycella, with similar feeding patterns andbiologies except that the colour of their larvae isalways grey-blue to blue (Fig. 3) in contrast toCactoblastis, all of whose species have orangecoloured larvae with black transverse bands (Fig. 4)(Mann 1970; Zimmermann & Granata 2002).There are five described species in the genus Cactoblastis: C. cactorum, C. bucyrus, C. mundelli,C. doddi and C. ronnai. All of these are confined tothe southern part of South America, from southernPeru to Bolivia, Paraguay, Uruguay, Argentina andsouthern Brazil. The taxonomic status of C. ronnaiis doubtful. The species can be distinguished bytheir genitalia, wing patterns and wing colouration(Heinrich 1939). With the exception of C. cactorum,which has a wide hostrange within the Opuntioidea,all the species have very restricted host ranges andlimited distributions. Hosts include species in thegenera Cylindropuntia, (for C. mundelli), Cereus(for C. bucyrus) and Eriocereus (for C. cactorumtype F) (McFadyen 1985), a few species in Opuntia(for C. doddi) and many species of Opuntia (for C.cactorum).Cactoblastis cactorum (cactoblastis)Sub-specific differencesFIG. 3. Larvae of Olycella sp.Recent surveys for cactus-feeding insects revealedthe possible existence of five host-adapted biotypes,sub-species or even separate, independent specieswithin C. cactorum (McFadyen 1985). Thesedifferences are based on host ranges and colourpatterns of the mature larvae. DNA sequencing anddetailed host range studies of all the taxa will beneeded to determine the true status andrelationship of all the described and proposedentities in the genus Cactoblastis.Origin of the exportedCactoblastis cactorum stockFIG. 4. Cactoblastis cactorum larva.Cactoblastis cactorum occurs naturally in thenorthern parts of Argentina, in Uruguay andParaguay and in the southern parts of Brazil (Fig. 5)(Mann 1969). The cactoblastis stock introduced intoAustralia and South Africa, and from there to theCaribbean Islands (see Chapter 4), was collectedfrom Opuntia delaetiana (now known asO. paraguayensis) (R. Kiesling pers. comm.) andfrom an Opuntia species of the “monacantha” group(Fig. 6) (McFadyen 1985). This specific entity is3

Argentina to Australia and South Africa failed toestablish (McFadyen 1985).The mothThe adult moths (Fig. 7) are inconspicuous, theirforewings are brownish-grey with two wavytransverse bands. The wings are somewhat whitertowards the costal margin. The hind wings are palegrey with a dark band along the margin. In contrast,moths of Melitara show considerably more whitecolouration in the forewing (Heinrich 1939). Mothshave a wingspan of 27–40 mm when reared fromoptimal hosts but can be considerably smaller whenreared from sub-optimal hosts or from small hostplants constituting a limited food supply.Females are generally larger than males, their wingsare slightly darker and their palpi are moreprominent than those of the males (Fig. 8).Microscope preparation of the genitalia can providepositive identification (Heinrich 1939).The eggFIG. 5. The native distribution of C. cactorum in SouthAmerica.FIG. 6. Cactoblastis on Opuntia monacantha, nearPeriapolis, Uruguay. All Cactoblastis populations outsideArgentina originated from this region.restricted to the genus Opuntia but has a wide hostrange within this genus in its native geographicalrange. It also readily accepts many Opuntia speciesfrom North America and was responsible for thespectacular control of several invading Opuntiaspecies in different countries (Moran &Zimmermann 1984; Julien & Griffiths 1998). Allpopulations outside Argentina originated from thisone introduction to Australia in 1925, whichcomprised about 3,000 eggs. Previous andsubsequent introductions of Cactoblastis spp. from4The individual egg is cylindrical and flattened,about 0.9 mm wide and 0.4 mm long. It is initiallycream coloured, and darkens to brown and lateralmost black, shortly before the larva emerges. Thefemale stacks its eggs coin-like to form a chain orsmall stick (Fig. 9), resembling a cactus spine. Thefirst egg in the egg stick is glued to a spine ordirectly on the cactus pad (cladode) with an ambercoloured substance presumably derived from theaccessory glands. The positioning of eggs on top ofone another is guided by setae that surround theovipositor. The egg stick contains on average 70 to90 eggs but seldom more than 105. An egg stick of70 eggs has a length of about 2.4 cm. Short egg sticksFIG. 7. Female (left) and male (right) adults ofCactoblastis cactorum.

FIG. 10. First instar Cactoblastis larvae.FIG. 8. Wing pattern of Cactoblastis cactorum male(above) and female (below).FIG. 11. Final instar Cactoblastis larvae.blastis by their shorter length. The egg stick ofMelitara contains between 30 and 40 eggs whilethose of Olycella are even shorter, with only 10 to 12eggs or fewer.The larvaFIG. 9. An egg stick of C. cactorum being deposited.are straight but the normal egg stick is slightlycurved. It is pliable at first but becomes brittle whendry. Several environmental conditions and hostplant characteristics also affect ovipositionbehaviour (Myers et al. 1981; Robertson 1987;Hoffmann & Zimmermann 1989; Stange et al. 1995).The habit of ovipositing eggs in the form of a stick isalso observed in the cactus-feeding genera Melitaraand Olycella, both from North America. Their eggsticks can be distinguished from those of Cacto-First instar larvae (neonates) of C. cactorum(Fig. 10) are 2.5 mm long and are greenish-grey incolour. Later instars have a rich salmon, orange tored colour with blackish spots forming transversebands (Fig. 11). These transverse bands in the final(sixth) instar are nearly always divided into fourseparate blocks or spots and are never fused in themid-line, thus distinguishing it from other, relatedtaxa in the genus (McFadyen 1985). Full-grownlarvae are about 33 mm long before they pupate,but they can be considerably smaller when rearedfrom small or sub-optimal hosts.The pupaMature larvae spin a silky white cocoon in whichthey pupate, usually under debris, e.g. dry cladodes,5

FIG. 12. Pupae: with soil particles adhering to cocoon,with clean cocoon, and without cocoon.leaf litter, near or on the host plant. The cocoons areoften covered with soil or plant particles, whichmakes them difficult to detect (Fig. 12).To distinguish between the sexes, the pupae have tobe studied from the venter (underside) (Fig. 13).Locate the first five visible spiracles on the side of6FIG. 13. Abdominal tip of female (left) and male pupa(right).the abdomen. These are followed by a smaller nonfunctional spiracle on the next segment. In thefemale the segment with the non-functional spiraclehas a slit-like genital scar. In the male the genitalscar is located in the next segment between tworaised bullae. The genital scars should not beconfused with the anal scar, which is near the tip ofthe abdomen.

CHAPTER 2The biology of Cactoblastis cactorumLife cycleThe life cycle of Cactoblastis cactorum (cactoblastis)(Fig. 14) was described in detail by Dodd (1940),Pettey (1948) and Mann (1969). The moths emergefrom their pupae in the early evening. There areusually slightly more males than females in a normalpopulation, and the difference is more pronouncedif the amount or quality of available food isunsuitable for the larvae. They mate early in themorning of the first or second day after emergence,and during the following night the females startlaying eggs. The adult moths live about 9 days anddo not feed. They rest during the day on the lowerparts of plants and are reluctant to fly, even whendisturbed. At night, the moths become active andthe females are occasionally attracted to light.Most eggs are deposited during the early evening.Female moths do not attach any eggs to spines thatare too long for their ovipositors to reach. They laytheir eggs mainly on the succulent segments on thelower parts of suitable host plants, but when suitablehosts are not available they will occasionally depositegg sticks on unsuitable host plants or even objectsinside houses near prickly pear infestations. No eggsare deposited in the presence of artificial light.The eggs usually hatch during the day, but will evenhatch at night if it is warm enough. Larvae from thesame egg stick are gregarious after hatching, sittingin a circle at the base of the spine to which their eggstick was attached while chewing a communalentrance hole into the cactus segment (Fig. 10,Chapter 1). This communal behaviour enables thetiny larvae to penetrate the tough epidermis of thecactus, and possibly overcome the mucilaginous sapexuded by the cladode. Larvae are often repelled bythe sticky exudates and are forced to make anotherentrance elsewhere.The larvae feed as a colony (Fig. 15) while tunnelingthrough a cactus pad (cladode), consuming theinterior except for the fibrous vascular tissues(Fig. 16). Faeces are discharged through the originalentrance hole, and slimy green ooze is oftennoticeable on affected segments as well as on theground. The larvae occasionally cluster on theoutside of a segment to bask in the sun on cold days,or to shelter in the shade on hot days. Havingconsumed the contents of one cladode, the larvaeeither tunnel into an adjacent cladode, or the entirecolony leaves the cladode, crawling over the plantsurface before entering another pad.When mature, the larvae vacate the cladode individually, drop to the ground and spin cocoons of whitesilk under or in rotting cactus pads on the ground, increvices in the cactus stems, in the leaf litter or inFIG. 14. Life cycle of Cactoblastis cactorum.FIG. 15. Larvae feeding gregariously internally in cladodes.7

Emergence of adults of Cactoblastis cactorum in South Africa(after Pettey lAugSepOctNovDecFIG. 17. Graph of Cactoblastis phenology in SouthAfrica.FIG. 16. Cladode hollowed-out by larvae.loose soil. They pupate inside these cocoons, andeventually emerge as adult moths.Duration of life stagesDodd (1940) described the duration of life stages inAustralia, Pettey (1948) in South Africa, and Mann(1969) worldwide. In temperate regions, such as themoth’s natural distribution in Argentina as well asmost parts of South Africa and Australia where themoths have become established, cactoblastis hastwo distinct generations per year. In the warmerregions of South Africa, (e.g. Kruger NationalPark), Australia and Florida, a full or partial thirdgeneration occurs in autumn (J.E. Carpenter & S.D.Hight, unpublished data), and it is expected that ineven warmer regions (e.g. Mexico) the generationsmight overlap and have no clear peaks. In thecoolest parts of New South Wales, the life cycleoccasionally occupies a full year.In Australia and South Africa, the summer generation (Fig. 17) takes 4–5 months, with adults flyingand laying eggs during September–November,8FIG. 18. Graph of Cactoblastis phenology in Florida andGeorgia.larvae hatching after about 40 days, developing for50–60 days before pupating, and moths emergingafter about 28 days during January–March. Thewinter generation takes about 8 months, with mothslaying eggs during January–March, larvae hatchingafter about 50 days, developing for 130–180 daysbefore pupating, and moths emerging after about40–70 days during September–November. Theaverage length of the cactoblastis life cycle in SouthAfrica is 113–132 days in the summer generation,and 234–256 days in the winter generation. InAustralia, it is 100–120 days in summer and 235–265days in winter.Two populations of cactoblastis that were studied atcoastal locations in south Georgia and northFlorida, USA, during 2002–2003, completed threenon-overlapping generations per year (Fig. 18), withthe spring adult flight lasting for about two monthsfrom early April to the end of May (#1, Fig. 18), thesummer flight occurring between early July and

mid-August (#2, Fig. 18) and the fall flight occurringfrom mid-September to mid-November. (#3,Fig. 18) (J.E. Carpenter & S.D. Hight, unpublisheddata). Observations of laboratory colonies initiatedfrom field collections in Georgia and Florida showthe life cycle to be approximately 90 days from eggto adult (J.E. Carpenter, unpublished data).FecundityThe average number of eggs laid per female isaround 88–97 (South Africa) or 99–125 (Australia)for the September–November moths (winter generation), and around 161–188 (South Africa) or 75–120 (

BIOLOGY, HISTORY, THREAT, SURVEILLANCE AND CONTROL OF THE CACTUS MOTH, Cactoblastis cactorum IAEA, VIENNA, 2004 IAEA/FAO-BSC/CM Printed by the IAEA in Austria

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