Translator Disclaimer
1 December 2018 A Study of Cactoblastis cactorum (Lepidoptera: Pyralidae) in its Native Range: Further Insights into Life Cycle, Larval Identification, Developmental Parameters, Natural Enemies, and Damage to the Host Plant Opuntia ficus-indica (Caryophyllales: Cactaceae)
Author Affiliations +
Abstract

Cactoblastis cactorum Berg (Lepidoptera: Pyralidae) has been extensively studied since its initial use as a biological control agent for invasive populations of Opuntia Mill. The moth is native to several South American countries including Argentina where the exotic Opuntia ficus-indica (L.) Mill. (Cactaceae) is grown as a commercial crop. Recently C. cactorum has attracted considerable attention following its non-intentional establishment in Florida, because it now threatens the highly diverse and economically important Opuntia taxa of the southern USA and Mexico. To elucidate several aspects of this system, we recorded phenological data and parasitoid activity from Argentina across an annual cycle. We reared several generations of moths to better document the life cycle, described several formerly unpublished larval stages and morphological characters, and compared developmental parameters from samples collected from different sites. We found that C. cactorum has 3 overlapping generations across a 9 mo growth period with winter quiescence at the larval VI instar or pupal stage. The most common natural enemy of larvae was the parasitoid Apanteles opuntiarum (Martínez and Berta) (Hymenoptera: Braconidae). Information is given on its development and percentages of parasitism throughout the year. No egg parasitoids were found in field-collected eggsticks or on experimental eggsticks. There were no significant differences between developmental stages and times of C. cactorum from Tucumán and Córdoba in Argentina. We found intermediate C. cactorum damage on low-density cultivated Opuntia, but much lower damage in commercial plantations with high densities of plants. Surprisingly, we found that a “black spot” fungal infection (Alternaria Nees) (Pleosporaceae) produced a higher level of damage in commercial plantations in Córdoba, as well as in natural settings in Tucumán

Cactoblastis cactorum Berg (Lepidoptera: Pyralidae) is in the Pyralidae snout moth family, a large group that includes agriculture and forestry pests. Fifteen genera of the subfamily Phycitinae are cactus feeders (Simonsen 2008). Cactoblastis cactorum is 1 of 5 species in this genus native to South America, occurring in Argentina, Uruguay, Paraguay, and southern Brazil (Mann 1969). Individuals of this species were introduced originally from Argentina into Australia (Dodd 1927) and to South Africa (Pettey 1948) in successful biological control programs (Dodd 1940; Annecke & Moran 1978) in the absence of natural enemies and lack of induction of plant defenses by exotic species (Woodard et al. 2012). Cactoblastis cactorum was first observed in Florida in 1989 (Habeck & Bennett 1990), possibly due to accidental introductions and natural spread from Caribbean islands (Pemberton 1995), and its current range includes locations from South Carolina to Louisiana (Hight et al. 2002; Simonsen et al. 2008; Hight &Carpenter 2009; Marsico et al. 2011).

Opuntia is a keystone resource in many new world arid ecoregions. A dramatic loss of Opuntia is likely to have major effects on the structure and biodiversity of native and agro-ecosystems in these regions (Soberón et al. 2001; Zimmerman et al. 2004). The threat of C. cactorum to native and cultivated Opuntia is greatest in habitats where the moth is an exotic and, thus, does not face a full complement of natural parasitoids, predators, and pathogens, as well as lack of induction of host plant defenses. But the threat of introduced C. cactorum is most dire in regions like the southern USA and parts of México where Opuntia species diversity increases sharply (Jezorek et al. 2010). There are 46 native species of Opuntia in USA, of which 1 is federally protected, and 12 others are under review (Zimmermann et al. 2004). In its native range, C. cactorum is considered to negatively affect Opuntia fruit production, plant structure, and longevity (Lobos 2006). However, the level of damage to these cultivated plants in Argentina is not well documented apart from a brief report by Lobos and Ochoa de Cornelli (1997). In fact, several farmers experienced severe outbreaks of black spot fungal damage on the cladodes (Ayala-Escobar et al. 2006) to the point that they have burned their plantations (several farmers, personal communications). Fungal damage to O. ficus-indica has not been reported in Argentina to our knowledge, and there is a possibility of interactions between moth and fungal damage. Black spot is a symptom produced by several fungal infections that has been identified in Mexico (Ochoa 2013; Ochoa et al. 2015) but not in Argentina.

Much of the basic biology of C. cactorum is known from data gathered from its introduced ranges (Dodd 1940; Mann 1969; Zimmermann et al. 2000, 2004), whereas recent studies of C. cactorum in its native range describe its distribution and performance on different native and exotic Opuntia species (Briano et al. 2012; Varone et al. 2012; Brooks et al. 2014). However, few details of the life cycle of C. cactorum are known from the field in its native range other than preliminary accounts (Lobos & Ochoa de Cornelli 1997; Lobos et al. 2013). Early surveys in Argentina reported parasitoids on Cactoblastis (De Santis 1967; Mann 1969; Pemberton & Cordo 2001b), but most of these findings were incidental to the principal survey goals of documenting insect herbivores of Opuntia and refer to generalist parasitoids, precluding their use for biocontrol in the moth's introduced range (Hawkins & Marino 1997; Pemberton & Cordo 2001a; Louda et al. 2003). More recently Goñalons et al. (2014) conducted a more thorough survey for parasitoids of C. cactorum and reported the distribution of the braconid larval parasitoid Apanteles opuntiarum (Martínez & Berta) (Hymenoptera: Braconidae) in Argentina and proposed it to be specific to C. cactorum (Goñalons et al. 2014) or to C. cactorum and Cactoblastis doddi (Heinrich) (Lepidoptera: Pyralidae) (Gomez et al. 2015; Varone et al. 2015). Most probably, A. opuntiarum is part of a group of cryptic species with specialized hosts (Martínez et al. 2012), as was found for the Apanteles leucostigmus (Ashmead) (Hymenoptera: Braconidae) complex, which includes 36 cryptic species (Smith et al. 2008).

The morphological distinction of juvenile forms of C. cactorum classically relies on information given by McFadyen (1985) based on colored spots and their pattern on the VI instar larvae. That work clearly differentiates the larvae among Cactoblastis species. However, several variant morphs were assigned to C. cactorum. Later, these morphological types were assigned to genetic haplotypes (Marsico et al. 2011) by Brooks et al. (2014), although the assignment of the 12 morphological characters used were not published in that work and were referred again to McFadyen's work. In addition, no morphological information is found for C. cactorum in the literature regarding larval stages other than instar VI. However, less variable characters, as well as information from other larval instars, are needed to help confirm the identity of larval stages of this species based on morphological traits.

In the context of planning biological control strategies for invasive C. cactorum in North America, there are several fundamental areas of knowledge that require further study. A detailed knowledge of the life cycle of C. cactorum from its native range is needed to facilitate a search for its natural enemies in various life stages. In addition, there are no long-term surveys of C. cactorum phenology from the native area. Most work done so far in the native habitat was comprised of samples gathered during limited sampling periods. The addition of systematic surveys with continuous data from the same site is needed to quantify the number of generations per yr, and the role of natural enemies across seasons and developmental stages. Furthermore, the description of larval instars other than stage VI, and additional traits beyond those given by McFadyen, is necessary to confirm the identification of C. cactorum. Finally, there is little quantification of damage to O. ficus-indica by C. cactorum in the native range of the moth. We have little understanding of the impacts by C. cactorum where its home range includes the presence of natural enemies.

Accordingly, the goals of this study were:

  • 1) To study in the laboratory the life cycle of C. cactorum from its native range, and describe life stages that lack descriptions using characters besides patterns of spot markings.

  • 2) To study C. cactorum in field populations across 12 mo to determine the phenology of developmental stages, the number of generations, and to assess the presence of potential biological control candidates throughout the life cycle.

  • 3) To follow laboratory generations to evaluate developmental timing differences from samples gathered from different geographical regions.

  • 4) To assess damage by C. cactorum and by black spot fungi on introduced O. ficus-indica within the native range of the moth.

Materials and Methods

FIELD SAMPLING

Field Sites and Survey Methods

Eight field sites (Tala Muyo, Los Arroyos, Paso del Molino, Dique Escaba, Graneros, Taco Rodeo, Lamadrid, and Taco Ralo) within a 90 km range from Alberdi, Tucumán, Argentina (between 27.5886°S, 65.6200°W and 27.6652°S, 65.7530°W) were sampled monthly from Sep 2013 to Sep 2014, except for 2 mo that were not sampled due to logistical problems. Instead, those mo (Feb and Apr 2014) were sampled n 2015; the stages found during 2015 were intermediate between the previous and the following months of 2014, suggesting that the phenology did not change qualitatively between years.

At each site, from 2 to 12 (winter and summer, respectively) samples of Opuntia ficus-indica cladodes infested with Cactoblastis eggs or larvae were collected monthly and brought to the laboratory within 2 to 3 d of collection. Cactoblastis cactorum life stages in these samples were recorded and then placed with fresh O. ficus-indica pads for their further development. Naturally occurring eggsticks of C. cactorum were recovered for laboratory rearing. We searched for pupae by looking at the base of each plant within the litter. In an effort to broaden the survey for natural enemies, we also sampled more opportunistically at other provinces with O. ficus-indica, including Santiago del Estero (28.0980°S, 64.7375°W) where 3 sites were visited in 6 different mo, Córdoba (30.2116°S, 64.4769°W) where 7 sites were visited in 8 different mo, and Salta (25.8000°S, 64.9666°W) where 4 sites were visited in 3 different mo. Voucher specimens of larvae and adults were retained in the Ant Laboratory at the Universidad Nacional de Quilmes.

All of our studies were conducted on the globally cultivated species O. ficus-indica, a polyphyletic taxon originating in Central Mexico (Griffith 2004), because it is the most widely introduced species common to Argentina and USA.

Rearing of Field Collected Samples

Eggsticks and larval stages found in the field were placed on healthy O. ficus-indica pads brought from the same field site. In the field, eggsticks were removed manually, and when possible, with the piece of pad to which they were attached. Infested pads were easily recognized in the field by the presence of larval entry holes surrounded by larval frass. The rearing protocol was based on that of Marti et al. (2008) but modified as described here. Pads with eggs or larvae were placed in a plastic box (32 ×21 × 10 cm) on a wire mesh above a layer of commercial, absorbent cat litter to absorb the larval feces and reduce humidity. Samples were checked every other d. Pupae found in the field or those developed in the laboratory were placed in similar plastic boxes, but without absorbent cat litter and with a segment of host plant fixed high enough for emergent adults to fly and mate. Inside these boxes, we hung paper strips from the cover and mounted thin wooden sticks across the container to provide perches for emerging moths. All the pupae obtained from larvae emerging from the same pad were held together in the same container, and the males and females that emerged were left there to mate without additional handling. The only aspect we controlled was to maintain a limit of 2 eggsticks within each box. This ensured that the first instar larvae had sufficient food within the single entire pad that was placed in each rearing box. Individuals were maintained in controlled rooms at 26 °C, 70% RH, and 12:12 h (L:D) photoperiod following Marti et al. (2008). For tracking purposes, we defined a new generation for each set of new numerous eggsticks collected in the field or obtained in the laboratory.

Characterization of Life Stages

We identified the moth as Cactoblastis cactorum by using literature by Heinrich (1956), McFadyen (1985), and Zimmermann et al. (2004). Voucher specimens of larvae and adults were kept for reference in the Universidad Nacional de Quilmes collection. We recorded size-related and morphological features using a binocular microscope (Nikon SMZ 745, 20×, 30×) (Nikon, Tokyo, Japan) to clearly define each larval stage because they have not been described before except for larval instars I and VI (McFadyen 1985; Zimmermann et al. 2004). The number of larval instars was determined based on Dyar's rule (Gaines & Campell 1935). We also described occurrence of setae on the thorax and abdo men, and the number of crochets on prolegs from each larval instar following Hinton (1946) and Stehr (1987), respectively. Larvae used for taxonomic descriptions belonged to samples from Tucumán. Pupae were readily recognized in their pink-white cocoons. Sex of adults was determined by size, with females being larger and having longer labial palps than males (Heinrich 1956).

Life Stage Development Times

From 36 pupae simultaneously collected in Graneros, Tucumán, in Sep 2013, we reared adults that mated and provided a complete generation that was tracked in the laboratory. We also collected eggsticks in Sep 2014 from the Tucumán and Córdoba sites, and reared them for 2 generations.

During the rearing of these cultures, we recorded the numbers at each life stage on alternate d. For larval stages we opened the pad minimally (to avoid mortality from handling) to score the larval instar and then generalized the result for all larvae inside that pad. However, change of instar was registered as soon as it was noticed in the first individual.

Collection of Parasitoids

All field-collected samples (eggsticks, larvae within pads, and pupae) from all sites and provinces were examined for parasitoids. Such specimens were isolated and the parasitoids were reared in the laboratory at 26 °C, 70% RH, and 12:12 h (L:D) photoperiod.

To survey for egg parasitoids, eggsticks from the field were isolated in the laboratory to document parasitoid emergence. Likewise, eggsticks generated from laboratory stocks were taken to the field and mounted on O. ficus-indica pads and left for 15 to 20 d to attract potential egg parasitoids. At Tucumán, we set out 48 eggsticks in Mar 2013, 1 eggstick per plant, distributed at 6 different sites. On a following visit to Tucumán in May 2013, we placed 30 eggsticks across 10 different sites. At Córdoba, we set out 10 eggsticks at each of the 2 sites (a total of 20). After field exposure these were recovered for further inspection in the laboratory.

In order to assess which larval instars were infected by A. opuntiarum, we recorded which larval instars collected from the field later yielded A. opuntiarum pupae. We also offered different immature stages (eggsticks, each larval instar, and pupae) of C. cactorum to Apanteles adults in the laboratory. For each trial, we placed a number of individuals of C. cactorum on a cladode inside a container (35 × 28 × 20 cm) where we added from 6 to 10 Apanteles females, and a similar number of males, so they could mate and the females oviposit. We repeated this 3 times for each life stage, except for eggsticks where we ran 6 trials. We considered that the tested stage and instar was used as a host by the parasitoid if we obtained C. cactorum instar VI parasitized after rearing them.

Documenting Vegetative Damage in Wild and Cultivated Opuntia

In Tucumán and Córdoba provinces, we documented damage due to C. cactorum and black spot fungus in Jul and Aug of 2014. At Tucumán, of the 9 sites visited, 3 sites had plants cultivated for feeding pigs, and we sampled on average 36 plants per site. At the other 6 sites, O. ficus-indica occurred in the wild at low densities, and we sampled on average 4 plants per site. In Córdoba, all 6 sites were commercial plantations with numerous plants, ranging from 400 to 4,400 plants per site, and we searched an average of 633.3 plants per site. Plants were scored as infected by C. cactorum if 1 or more cladodes were damaged per plant. Similarly, cacti were scored as having fungal dam age if we saw 1 or more cladodes with black spot infections (Fig. 7). The fungi obtained from 20 infected cladodes were placed on water-agar, then isolates were cultured on potato dextrose agar, and later on potato carrot agar or cornmeal when necessary. The isolated fungi were identified using the Barnett and Hunter (1998) and Simmons (2007) morphological keys.

STATISTICAL ANALYSES

When 2 groups of samples were compared, we used Mann-Whitney tests. When more than 2 groups were analyzed, we used Kruskall-Wallis tests with a posteriori contrasts with alpha values adjusted by using the Bonferroni correction (Siegel 1979). We used non-parametric analyses because data did not show normality or homoscedasticity.

Results

DESCRIPTIONS OF CACTOBLASTIS CACTORUM LIFE STAGES

Adults

As described earlier, females are larger and have conspicuous longer and darker palpi than males. Females from Tucumán had a body length of 38 mm (± 0.03) and wing span of 40.4 mm (± 2.55), whereas males measured 28 mm (± 0.02) body length and 29.2 mm (± 1.2) wing span (n = 25). In the laboratory, adults emerged in the afternoon (Fig. 1 i, j, k, l). Mating was seldom observed and assumed to occur mainly at night.

Eggs

In the laboratory, females either deposited eggs onto a pad as an eggstick (Fig. 1a) or directly onto the boxes in which they were housed. Eggsticks resemble spines (Zimmermann et al. 2004). In the field, eggsticks had 12 to 78 eggs (n = 176), whereas in the laboratory eggsticks comprised 15 to 50 eggs (n = 1,608). Eggsticks had a length of 7 to 20 mm depending on the number of eggs per eggstick. Eggs were cylindrical and flattened, changing from a whitish color to brownish as the embryos matured. Egg size was on average 0.32 mm width (± 0.03) and 0.84 mm length (± 0.03) (n = 202). The micropylar region and sculpturing of the egg have been previously described by Baker et al. (2012).

The number of larval instars was confirmed by obtaining a geometric progression of the width of the head capsule according to Dyar's rule (Gaines & Campell 1935). All larvae were gregarious (Mann 1969).

Instar I

First instar larvae are greenish-grey in color, 3.04 mm (± 0.06) long with a fresh weight of 0.60 mg (± 0.03) (n = 45). The head (hypognathous) is dark brown with light-brown antennae and mouthparts (Fig. 1b). The width of the head capsule is 0.49 ± 0.02 mm. The following setae were found: a pair of posterior setae P1 and P2 alongside the epicranial sulcus; a pair of F1 setae on the forehead; 2 pairs of setae AF1 and AF2 on the adfrontal sclerite; a pair of setae C1 and C2 on the clipeus; anterior setae A1, A2, and A3 on the lower side of the head, along with a lateral seta L1 and 3 ocellar setae. The thorax is well differentiated into 3 segments with 1 pair of legs on each. Setae D1 and D2, SD1 and SD2, XD1 and XD2 were found in the dorsal and subdorsal part of the prothorax, L1 and L2 on the side, and SV1 and SV2 subventrally. In the mesothorax D1, D2, SD1, and SD2 setae occur dorsally, L1, L2, and L3 setae laterally, and SV1 subventrally (see Fig. 2 for position of setae). The abdomen has 10 segments, with a pair of prolegs on segments 3, 4, 5, 6, and 10. Setae on the seventh abdominal segment includes D1 and D2 dorsally, L1 and L2 laterally, and SV1 subventrally. The anal segment has setae D1, D2, SD1, SD2, PPI, SV1, and SV4 (Fig. 2). Prolegs of the abdominal segments with crochets arranged in a circle, uniserial, and incipiently biordinal with 16 to 30 crochets. The proleg of the anal segment with crochets penellipse, uniserial, and ordinal with 18 to 20 crochets. The first instar larva has a light prothoracic shield (Fig. 1b, Fig. 2). This instar burrows a small hole to enter the cladode, then spins a silk web to occlude the hole, which is surrounded by ejected frass (feces).

Fig. 1.

(a) An eggstick oviposited on a pad of Opuntia ficus indica; (b) Anterior part of the larva exhibiting the cephalic capsule and prothorax starting to sclerotize; (c) Larva II has a dark shield on the prothorax and small macula at the base of each setae in the abdomen; (d) Larva III with bigger maculae with alternating color intensity on successive segments; (e) Larva IV with a white line between the head capsule and prothorax shield; (f) Larva V characterized by almost continuous black rings on the abdomen on an orange-brownish background; (g) Typical bright orange larval VI with the prothorax shield fractured in 2 and apparently continuous black rings; (h) pupa within silk cocoon and naked pupa; Cactoblastis cactorum females (left) and males (right); females have longer palps (i) than males (j). Both genders are characterized by a transverse line in the distal part of the wings (k, l).

f01_559.jpg

Instar II

Second instar larvae are greenish-creamy in color and are 5.2 mm (± 0.08) long with a fresh weight of 1.12 mg (± 0.4) (n = 43). Head capsule width is 0.71 ± 0.02 mm. Larvae II begin to show spot “k” on the prothorax (surrounding setae L1 and L2) and spot “a” (between D1 and SD1) on abdominal segments (Fig. 1c). Other markings are similar to the previous instar (Fig. 2). Prolegs of the abdominal segments have crochets arranged in a circle, uniserial, and incipiently biordinal with 22 to 34 crochets. Proleg crochets of the anal segment are arranged penellipse, ordinal, and uniserial with 22 to 26 crochets.

Instar III

This instar was light orange-brown (Fig. 1d), 9.0 mm (± 0.2) long, and weighed 8.42 mg (± 0.08) (n = 43). Head capsule width 0.94 ± 0.03 mm. Compared to larvae II markings, spot “k” on the prothorax is darker, spot “a” on the abdominal segments is of greater size, with the lower part (where SD1 is placed) starting to surround the spiracles on the sides, and spot “c” (from L1 and L2) starts to appear (Fig. 2). The L1 seta occurs on the anal segment. The anal shield is clearly seen (Fig. 1d). Prolegs of the abdominal segments with crochets arranged in a circle, uniserial, and biordinal, with 32 to 44 crochets. Proleg of the anal segment has crochets penellipse, uniserial, and biordinal, with 28 to 30 crochets. Crochet arrangements remain consistent from instar III through to the final instar.

Instar IV

Instar IV larvae were of a color similar to LIII, a bit darker, but proportionately wider than the previous instar. Larval length was on average 10.7 mm (± 0.75) with a fresh weight of 32.0 mg (± 9.4) (n = 43). They had a white line between the head capsule and prothoracic shield (Fig. 1e). Head capsule width was 1.08 ± 0.04 mm. A small and light spot (“h”) appears from SD1 setae. All spots were greater and darker than those in the previous instar (Fig. 2). Prolegs of the abdominal segments with 42 to 46 crochets, and of anal segment with 38 to 40 crochets.

Instar V

Each abdominal segment of this instar was orange with black interrupted spots (Fig. 1f). Larval length was 12.7 mm (± 1.7) with a fresh weight of 55.6 mg (± 14.6) on average (n = 36). Head capsule width 1.22 ± 0.03 mm. This instar was of much greater size than the previous one, and in particular broader due to the great voracity that characterized the last 3 instars. At this stage, a fracture appeared on the posterior part of the prothorax shield (Fig. 1g). All the spots mentioned in the fourth instar were very evident in the fifth instar (except “h”), all dark in coloration and larger according to the greater size of this larva (Fig. 2). Prolegs of the abdominal segments with 46 to 56 crochets, and of the anal segment with 38 to 40 crochets.

Instar VI

Sixth instar larvae were intensely orange with apparently continuous black rings on the abdominal segments, although spots did not touch laterally and barely touched in the midline (Fig. 2). This last instar had a length of 21.8 mm (± 2.5) and a fresh weight of 118.6 mg (± 28.7) (n = 36). Cephalic capsule width was 1.57 ± 0.11 mm. The fracture of the prothorax divided the shield clearly into 2 parts (Fig. 1g). All spots mentioned for instar V were very evident, dark, and of greater size in this instar, except “h” (Fig. 2). Prolegs of the abdominal segments with 54 to 62 crochets, and of the anal segment with 42 to 52 crochets.

Fig. 2.

Description of spots and setae from larval I to VI, shown in the pro- and meso-thoracic segment, and the seventh and anal abdominal segments: D1–2: dorsal setae; SD1–2: subdorsal setae; XD1–2: prothoracic setae; L1–3: lateral setae; SV1–2: subventral setae; PP1: posterior setae; spot “k” in prothorax, “h” in mesothorax, “a” and “c” in the seventh abdominal segment, and anal shield in the tenth and last abdominal segment.

f02_559.jpg

Pupa

Cactoblastis cactorum has an obtect pupa, reddish brown in color, usually within a white silk cocoon, and covered partially or completely by small particles of debris (Fig. 1h). Plain silk cocoons were found either on the lid or corner of the container, whereas particle-covered cocoons were found on the base of the box among the cat litter. The size of the pupa appeared to depend on the size attained by the sixth instar, with an average weight of 70.0 mg (± 16.7) (n = 36). As described by Zimmermann et al. (2004), the anal scar was found near the tip of the abdomen at the tenth segment. In female pupae, the genitalia scar was localized ventrally on the eighth and ninth segments, whereas in males the scar was placed on the ninth segment between 2 raised bullae.

Table 1.

Time in days for each developmental form of Cactoblastis cactorum reared in the laboratory from 36 pupae collected in Tucumán. Data shown as medians, quartiles (Q25%–Q75%), and sample sizes (N).

t01_559.gif

PHENOLOGY OF CACTOBLASTIS CACTORUM LIFE STAGES

The complete life cycle of C. cactorum from Tucumán lasted 96.5 d for a first generation reared in the laboratory at 26 °C, 70% RH, and 12:12 h (L:D) photoperiod. The longest developmental stage was the time for eggs to hatch (30 d and 98% of all eggs from the same eggstick hatched simultaneously), whereas the shortest was the adult's lifespan (2.5 d) (Table 1.

From the monthly surveys of C. cactorum at Tucumán we estimated that the life cycle may include 3 generations between early spring (Sep) and late fall (May) followed by quiescence of late instar VI larvae, or pupae (Fig. 3). This is based on 2 lines of evidence; first, the generation time of about 100 d allows for 3 generations during the active months, if indeed the field populations have similar generation times. Second, the presence of eggsticks with (decreasing) peaks in Sep, Dec, and Mar occur at about 90 to 100 d intervals (Figs. 3, 4). Results of the opportunistic surveys in other provinces very distant from each other showed similar patterns. At Córdoba, we found eggsticks in Sep and Nov, and instar VI was found from May to Aug, whereas instars III and IV were found in Apr, and instar 1 in Sep. In Mar at Salta we found instars II, III, VI plus eggsticks, and in Jun instar VI. At Santiago del Estero we found eggsticks in Mar, instar VI in Jun, instar VI and pupae in Oct, and instars V, VI, and pupae in Nov.

Fig. 3.

Proportion of individuals of different developmental stages of Cactoblastis cactorum in Tucumán throughout the year. Inside the bars: E = eggsticks, L = larvae, P = pupae.

f03_559.jpg

Fig. 4.

Number of eggs across months for all sampling sites from Tucumán.

f04_559.jpg

For the laboratory cultures of lineages from Tucumán and Córdoba, we compared the duration of developmental stages and found no significant differences between sites (all P > 0.05) (Table 2). Lifespan for females was, on average, 1 d longer than for males for moths from both provinces. The total development times for material from Córdoba was longer than for Tucumán and almost significant for G1 (KW = 3.19, P = 0.07; Table 2).

Parasitoids Associated with Cactoblastis cactorum

During the year-round field surveys in Tucumán, plus 14 locations in other provinces within the same period of time, we found very few natural enemies. We found A. opuntiarum parasitizing C. cactorum at all sites (Fig. 6), but Apanteles alexanderi Brèthes (Hymenoptera: Braconidae) was found parasitizing C. cactorum only at Tucumán in Feb and Nov. Although no systematic surveys on other lepidopteran larvae were done, we found that A. alexanderi also parasitized Laetilia coccidivora (Comstock) (Lepidoptera: Pyralidae) larvae at Santiago del Estero in Mar, Oct, and Nov. Other parasitoids found in Tucumán samples parasitizing C. cactorum pupae were a species of Ichneumonidae (Hymenoptera), a species of Chalcididae (Hymenoptera), and a species of Tachinidae (Diptera). We also found the fungus Beauveria sp. on eggsticks and larvae in the field. Due to their extremely low abundance, these specimens were not identified to the species level.

There was no clear relationship between the abundance of A. opuntiarum and that of the host in absolute values or percentages of parasitism. The parasitism of A. opuntiarum in Tucumán, calculated from the overall number of C. cactorum larvae collected in that mo was low, ranging from 0% to 7.9% across the yr (Fig. 5). On average, 39.2% of cladodes collected in Tucumán (34% across all sites and provinces) with apparent C. cactorum damage did not contain living C. cactorum larvae. However, from those cladodes that were positive for C. cactorum we calculated that 67% of them at Tucumán (64% across all sites and provinces) were also positive for Apanteles (Fig. 6). On average, from 5 to 18.4 parasitoid pupae were found per infected larvae VI of C. cactorum (Fig. 6). Despite the much higher density of plants on Córdoba sites, the percentages of infection and parasitism were similar to those found at Tucumán, and only a slightly higher number of pupae of Apanteles (13.2 ± 2.5) were found per cocoon at the first site in comparison to Tucumán (10.7 ± 3.3) (Fig. 6).

Apanteles opuntiarum pupated in the same cocoon, and there was 1 cocoon per instar VI host. Adults emerged in 13.6 d ± 7.2 (n = 30). All parasitoid pupae emerged simultaneously and usually generated both females and males (n = 30), except in 8 cases where all adults that emerged from the same cocoon were males (probably due to Wolbachia infection, see Goñalons et al. 2014). The average number of pupae of Apanteles per cocoon (or instar VI) was 11.6 (± 3.1) (Fig. 6). The emergence rate was 87.1% (969 adults from 1113 pupae) with a female to male sex ratio of 1.78:1. Adult wasps did not live for more than 4 d when used in parasitism assays. We encountered parasitized larvae in all mo except from samples collected during Mar, Aug, and Sep.

Table 2.

Developmental times in days for Cactoblastis cactorum eggsticks collected from Córdoba and Tucumán and reared in the laboratory. Data shows median value, sample size and quartiles (25% and 75%).

t02_559.gif

Fig. 5.

Number of larvae of Cactoblastis cactorum per mo from all sites of Tucumán and the proportion of those that were parasitized by Apanteles.

f05_559.jpg

Fig. 6.

Proportion of Cactoblastis cactorum infected cladodes parasitized by Apanteles opuntiarum and proportion per cladode of C. cactorum larvae parasitized by A. opuntiarum throughout the yr for sites from Santiago del Estero, Córdoba, and Tucumán provinces. The average and standard deviation of the number of pupae of A. opuntiarum per C. cactorum larvae also is shown.

f06_559.jpg

In our effort to determine the life stages infected by A. opuntiarum, we obtained A. opuntiarum from instar VI in the laboratory from instars I, III, and VI collected from the field. Furthermore, the only laboratory induced oviposition occurred when instar I were exposed to Apanteles, from which we obtained only 1 instar VI parasitized with 6 Apanteles pupae.

Many of the eggsticks taken from the lab and placed in the field were recovered. In the first experiment at Tucumán, rains delayed recovery by about 1 mo and we recovered only 11 of 48 eggsticks or the emerged larvae. Among the larvae, there were 26 third instars, of which 16 survived to pupal stage, whereas 7 larvae were parasitized by A. opuntiarum. During the second experiment at Tucumán, 23 of 30 eggsticks were recovered after 15 d. All recovered eggsticks were dark colored indicating that they were ready to hatch, and none were parasitized. At Córdoba we recovered all 20 eggsticks close to hatching but none were parasitized.

Sources of Opuntia Damage

Damage to Opuntia pads by C. cactorum and various fungi was easy to distinguish (Fig. 7) and did not differ much in time of occurrence. We documented 2 forms of black spot fungal damage, namely circular and map-shaped, with distinctive shapes of fungal growth. Between 60 to 70% of the plants showed some damage by either Cactoblastis or black spot fungus, with a maximum level of 46% damage by C. cactorum in low density plots and 68% damage by the ‘circular spot' fungus in high density plots (Table 3). The percentage of plants with C. cactorum damage was inversely proportional to plant density, whereas the ‘mapspot' fungus was represented more frequently in low density plots (60%) and the ‘circular spot' fungus in high density plots (68%). There was greater damage by C. cactorum in plants from Tucumán (approximately 40%) than in those from Córdoba (10%), although the effect of site and density cannot be isolated from each other. The proportion of plants with both C. cactorum and fungal infection simultaneously was similar to that of plants with C. cactorum alone, and the proportion of damaged plants decreased as plant density increased.

Fig. 7.

Comparison of 3 characteristic forms of damage: (a) hole and feces coming from inside the pad, useful to distinguish pads with Cactoblastis cactorum; (b) typical damage observed in plants that were attacked by C. cactorum; (c) circular black spot fungal damage; (d) map black spot fungal damage.

f07_559.jpg

We recovered several fungi from the black spot injuries including Fusarium, Cercosporella, Alternaria, and Micelia sterilia. Several species of Alternaria (see section on Alternaria) seemed to produce both circular and map-spot symptoms in the laboratory (Folgarait et al., unpublished results).

Discussion

In our broad study of C. cactorum life history, we have elucidated previously undescribed life stages and morphological larval characters, documented the phenology of field populations, quantified the developmental stages of C. cactorum from 2 sites in Argentina, and conducted surveys of natural enemies of C. cactorum and sources of damage and infections in the O. ficus-indica host plant.

DESCRIPTIONS OF CACTOBLASTIS CACTORUM LIFE STAGES

Our specimens agree mostly with the larvae description of C. cactorum by McFadyen (1985). We disagree only in a potentially variable character, i.e. if spot “a” from the abdominal segments is fused in the midline or not. In some cases we found a slight fusion of spot “a” at the midline instead of being clearly divided, as in McFadyen's species A, whereas in other cases the fusion was absent, matching McFadyen's species B and C, but in all cases the adults consistently matched C. cactorum. However, Zimmermann et al. (2004) mentioned that the spots do not fuse at the midline. We also found a light and small spot “h” in the mesothorax that was not reported by McFadyen. The rest of the characters including spot “k” in the prothorax, spot “c” in the mesothorax, as well as shields in the prothorax and anal segment were quite stable in all descriptions. We also documented other traits that are very characteristic of lepidopteran larvae, in particular the body chaetotaxy and the number and arrangement of the crochets found in the prolegs. It will be interesting to further study the variation of these characters across the haplotypes described by Marsico et al. (2011).

A table of diagnostic characters of C. cactorum, C. doddi, and Cactoblastis bucyrus Dyar (Lepidoptera: Pyralidae) is given to show traits that can be used to confirm species identification (Table 4). Cactoblastis bucyrus is mainly found on Opuntia from the subgenus Cereaneae whereas the other 2 species are found on the Platyopuntia subgenus (McFadyen 1985). Generally, C. cactorum does not develop on O. sulfurea in the field, whereas C. doddi uses it as its preferred host (Mann 1969; Varone et al. 2014; Gomez et al. 2015). The final instar of C. bucyrus may reach twice the size of the other 2 species (Table 4). Accordingly, it has many more larval instars and only 1 generation per year. Although the size of the spots given by McFadyen (1985) may vary among individuals and populations, the presence of certain spots (“I” and “f”) in the final instar can be compared to distinguish the 3 species mentioned (Table 4). Similarly, the arrangements and number of crochets, as well as the number of mesothorax setae, can be used to tease apart the 3 species (Table 4).

PHENOLOGY OF CACTOBLASTIS CACTORUM LIFE STAGES

We found that similar developmental stages are present in the same mo in most of our study provinces. Mann (1969) proposed that C. cactorum in Australia had 2 annual generations, a summer cycle (100–120 d), and a winter cycle (235–265 d), with total development times of 71 to 78 d and 85 to 92 d for each generation, respectively. Up to 3 generations were found in Florida, Georgia, and South Carolina in the US (Hight & Carpenter 2009). Lobos and Cornelli (1997) described 2 generations in populations from Santiago del Estero, 1 during winter–spring (Aug–Sep) and the other during summer–autumn (Mar–Apr). Lobos et al. (2013) mentioned 3 generations for northern Argentina. Our systematic survey at Tucumán demonstrated that the life cycle may include up to 3 overlapping generations (Fig. 4) between early spring (Sep) and late fall (May) followed by a quiescence at the late instar VI or pupal stages. This observation is supported by the 3 pulses of eggstick production (as demonstrated by Hight & Carpenter 2009), at intervals corresponding to approximate laboratory generation times, and the presence of multiple life stages through most monthly surveys.

For laboratory-reared populations, Varone et al. (2012) reported a 30-d larval development time at 25 °C of C. cactorum on O. ficus-indica, whereas our observations of larvae development on O. ficus-indica at 26 °C ranged from 40 to 45 d. Total development times from our data varied from 87 to 98 d at 26 °C compared to 84 d reported from O. ficus-indica in a laboratory under unknown temperature conditions (Varone et al. 2014). In contrast, development times of C. cactorum from Australia and South Africa were longer even for their summer generations (100–120 d and 113–132 d, respectively) (Robertson 1988; Zimmermann et al. 2004). Prolonged development may be a response to sub-optimal abiotic conditions, or biotic factors such as host plant mismatches or microbial interactions.

PARASITOIDS ASSOCIATED WITH CACTOBLASTIS CACTORUM

The principal parasitoid encountered across all sites was A. opuntiarum, in agreement with previous surveys (Goñalons et al. 2014). Apanteles opuntiarum seemed to be well adapted to a variety of climates as we found it at all sites surveyed across Argentina (Gomez et al. 2015; Varone et al. 2015).

Despite finding low levels of natural parasitism by this parasitoid, the low level of damage quantified in Opuntia by C. cactorum suggested an important regulatory effect of the moth population by natural enemies such as parasitoids, ants (Robertson 1988), or pathogens such as microsporidia (Pemberton & Cordo 2001b).

An intriguing feature of the life cycle of C. cactorum was its long time for egg development before hatching, during which time the eggs are exposed to desiccation, predation, and parasitism. Given this, one would expect that parasitoids may take advantage of resources exposed for long periods, and we anticipated finding egg parasitoids. Egg parasitoids (Trichogramma sp.) (Hymenoptera) are found occasionally (Lobos 2006; Goñalons et al. 2014), but they are likely to be generalist parasitoids (Paraiso et al. 2012). However, throughout continuous sampling in 1 province plus non-systematic sampling done at many other times and sites, we found no evidence of egg parasitism. We assume that discovery of eggsticks by egg parasitoids is likely due to odor cues, not visual (Peñaflor et al. 2011), and may occur soon after oviposition when odors are fresh and before the egg shells harden. In South Africa, over 50% of eggs were lost to ant predation (Robertson 1988), and discovery by ants is also likely to be odor based. To further elucidate this issue, studies such as those of Robertson and Hoffman (1989) should be continued.

Table 3.

Damage by Cactoblastis cactorum and black spot on Opuntia ficus-indica discriminated by location and density. Data show counts and proportions. Low density is defined as 4 plants per ha, medium density is 36 plants per ha, high density is 633 plants per ha.

t03_559.gif

Table 4.

Comparison of biological and morphological characteristics among larvae of Cactoblastis cactorum, Cactoblastis doddi, and Cactoblastis.

t04_559.gif

SOURCES OF OPUNTIA DAMAGE

A previous study of damage and pests on Opuntia in Argentina (Lobos 2006) indicated that C. cactorum was the principal pest; however, we found that the major source of cladode damage seemed to be from fungal infections, although we did not measure impacts on fruit production. Our study was focused on the introduced and widely cultivated O. ficus-indica and we consider our findings to reflect an overall intermediate to low level of plant damage by C. cactorum, even where host plants occurred at high densities, implying some population regulation by native parasitoids, predators, or pathogens.

There was small variation (approximately 50 to 60%) in the extent of damage to plants by fungal infections between sites in different provinces, despite being at substantially different plant densities. In addition, only at low densities of host plants in Tucumán, we found a suggestive pattern of intermediate co-occurrence (46%) between the moth and the black spot fungus. Possibly females of C. cactorum have limited choices under low host plant densities and may be able to respond to differences in host plant quality at higher host densities where females may discriminate plants with substantial black spot damage from those that are not affected. If true, then our results contrast to a previous suggestion that C. cactorum may be a vector of fungal pathogens (Martin & Dale 2001). Furthermore, we did not find reports of black spot fungal damage to cactus in introduced ranges where C. cactorum is now present, implying either an absence of infective fungi, or a lack of vectoring by C. cactorum. The dominant fungi we encountered were identified as Alternaria, and not one of the fungal species previously reported as black spot in Mexico (i.e., Pseudocercospora) (Ochoa 2013). Further studies of fungal infections are needed to confirm if this result holds elsewhere in Argentina, and attention should be given to commercial plantations where this fungal disease is prevalent and causes economic costs.

So far, the single candidate for introducing a biological control of C. cactorum to the US seems to be Apanteles opuntiarum. However, 2 important pieces of information still are lacking. On the one hand, it is necessary to confirm that instar I is used by this parasitoid to oviposit and, if so, then introductions of mated females of A. opuntiarum should be made 30 d after eggstick pulses, when instar I would have emerged in the field. On the other hand, it is necessary also to document the effect on non-target individuals, such as experiments of possible parasitism of this wasp on other US native larvae species, as well as the presence and action of pathogens that may be transmitted by the wasp.

Acknowledgments

We would like to thank Cecilia Cabrera, Rocío Souto, and Mario Maldonado for their invaluable help in the field and in the laboratory. We thank Ariel Marfetán for his help with the identification of the black spot disease. We also thank each of the province authorities in Argentina for giving us the necessary permits for collecting the samples within their jurisdiction. This research was funded principally by the Lee and Ramona Bass Foundation through the Brackenridge Field Laboratory of the University of Texas at Austin, and occasionally by the National University of Quilmes.

References Cited

1.

Annecke DP, Moran VC. 1978. Critical reviews of biological pest control in South Africa. 2. The prickly pear, Opuntia ficus-indica (L.) Miller.Journal of the Entomological Society of South Africa41: 161–188. Google Scholar

2.

Arce de Hamity MG, Neder de Román LE. 1999. Bioecología de Cactoblastis bucyrus (Lepidoptera: Phycitidae), especie dañina al cardón Trichocereus pasacana en la prepuna jujeña (Argentina).Revista de la Sociedad Argentina de Entomología58: 23–32. Google Scholar

3.

Ayala-Escobar VM, Yañez-Morales J, Braun U, Groenewald JZ, Crous PW. 2006. Pseudocercospora opuntiae sp. nov., the causal organism of cactus leaf spot in Mexico.Fungal Diversity21: 1–9. Google Scholar

4.

Baker GT, Hight SD, Brown RL. 2012. External morphology of the egg of the native (Melitara prodenialis) and exotic (Cactoblastis cactorum) cactus moths (Lepidoptera: Pyralidae).Proceedings of the Entomological Society of Washington114: 433–438. Google Scholar

5.

Barnett HL, Hunter BB. 1998. Descriptions and Illustrations of Genera. Illustrated Genera of Imperfect Fungi, 4th edition. American Phytopathological Society, St. Paul, Minnesota, USA. Google Scholar

6.

Briano J, Varone L, Logarzo G, Villamil C. 2012. Extended geographical distribution and host range of the cactus moth, Cactoblastis cactorum (Lepidoptera: Pyralidae), in Argentina.Florida Entomologist1: 233–237. Google Scholar

7.

Brooks CP, Lambert BH, Sauby KE, Ervin GN, Varone L, Logarzo GA. 2014. Larval morphology and host use confirm ecotypic variation in Cactoblastis cactorum (Berg).Biological Invasions16: 13–22. Google Scholar

8.

De Santis L. 1967. Catálogo de los Himenópteros Argentinos de la Serie Parasítica, incluyendo Bethyloidea.Publicación de la Comisión de Investigaciones Científicas de la Provincia de Buenos Aires, La Plata, Buenos Aires, Argentina. Google Scholar

9.

Dodd AP. 1927. The Biological Control of Prickly Pear in Australia. Commonwealth Council for Scientific and Industrial Research Bulletin 34.Melbourne, Victoria, Australia. Google Scholar

10.

Dodd AP. 1940. The Biological Campaign Against Prickly Pear.Commonwealth Prickly Pear Board Bulletin, Brisbane, Queensland, Australia. Google Scholar

11.

Gaines J, Campell F. 1935. Dyar's rule as related to the number of instars of the corn ear worm Heliothis obsoleta (Fab.) collected in the field.Annals of the Entomological Society of America28: 445–461. Google Scholar

12.

Gomez GC, Román LE, Linares MA, Zamar MI. 2015. Morphology of the immature stages and biology of Cactoblastis doddi (Lepidoptera: Pyralidae) in Prepuna in Jujuy (Northwestern Argentina).International Journal of Tropical Biology and Conservation63: 971–980. Google Scholar

13.

Goñalons C, Varone L, Logarzo G, Guala M, Rodriguero M, Hight S, Carpenter J. 2014. Geographical range and laboratory studies on Apanteles opuntiarum (Hymenoptera: Braconidae) in Argentina, a candidate for biological control of Cactoblastis cactorum (Lepidoptera: Pyralidae) in North America.Florida Entomologist97: 1458–1468. Google Scholar

14.

Griffith MP. 2004. The origins of an important cactus crop, Opuntia ficus-indica (Cactaceae): new molecular evidence.American Journal of Botany91: 1915–1921. Google Scholar

15.

Habeck DH, Bennett FD. 1990. Cactoblastis cactorum Berg (Lepidoptera: Pyralidae), a phycitine new to Florida. Florida Department of Agriculture and Consumer Services.Division of Plant Industry (circular)333: 1–4. Google Scholar

16.

Hawkins BA, Marino PC. 1997. The colonization of native phytophagous insects in North America by exotic parasitoids.Oecologia112: 566–571. Google Scholar

17.

Heinrich C. 1956. American moths of the subfamily Phyticinae. Bulletin of the United States National Museum207. Google Scholar

18.

Hight SD, Carpenter JE. 2009. Flight phenology of male Cactoblastis cactorum (Lepidoptera: Pyralidae) at different latitudes in the southeastern United States.Florida Entomologist92: 208–216. Google Scholar

19.

Hight SD, Carpenter JE, Bloem KA, Bloem S, Pemberton RW, Stiling P. 2002. Expanding geographical range of Cactoblastis cactorum (Lepidoptera: Pyralidae) in North America.Florida Entomologist85: 527–529. Google Scholar

20.

Hinton HE. 1946. On the homology and nomenclature of the setae of lepidopterous larvae, with some notes on the phylogeny of the Lepidoptera.Transactions of the Royal Entomological Society ofLondon97: 1–37. Google Scholar

21.

Jezorek HA, Stiling PD, Carpenter JE. 2010Targets of an invasive species: oviposition preference and larval performance of Cactoblastis cactorum (Lepidoptera: Pyralidae) on 14 North American opuntioid cacti.Environmental Entomology39: 1884–1892. Google Scholar

22.

Lobos E. 2006. Control de Cactoblastis cactorum Berg, principal plaga de la tuna en Argentina. In Aprovechamiento integral de la tuna.CactusNet1: 26–32. Google Scholar

23.

Lobos E, Ochoa de Cornelli J. 1997. Observations on Cactoblastis cactorum (Berg) as a pest of cactus pear (Opuntia ficus-indica) in Argentina with suggestions on possible control methods.Journal of the Professional Association for Cactus Development2: 97–102. Google Scholar

24.

Lobos E, Passos de Silva DM, Mena-Covarrubias J, Lagarzo G, Varone L. 2013. Principales insectos plaga de las Opuntias en Argentina, México y Brasil.CactusNet Newsletter13: 137–158. Google Scholar

25.

Louda SM, Pemberton RW, Johnson MT, Follett PA. 2003. Nontarget effects – the Achilles' heel of biological control? Retrospective analyses to reduce risk associated with biocontrol introductions.Annual Review of Entomology48: 365–396. Google Scholar

26.

Mann J. 1969. Cactus Feeding Insects and Mites.US Natural Museum Bulletin256.  Google Scholar

27.

Marsico TD, Wallace LE, Ervin GN, Brooks CP, Mclure JE, Welch ME. 2011. Geographic patterns of genetic diversity from the native range of Cactoblastis cactorum (Berg) support the documented history of invasion and multiple introductions for invasive populations.Biological Invasions13: 857–868. Google Scholar

28.

Marti OG, Myers RE, Carpenter JE. 2008. Rearing Cactoblastis cactorum (Lepidoptera: Pyralidae) on artificial diet and Opuntia cladodes.Journal of Entomological Science43: 95–106. Google Scholar

29.

Martin HL, Dale ML. 2001. Potential of Cactoblastis cactorum as a vector for fungi pathogenic to prickly pear, Opuntia inermis.Biological Control21: 258–263. Google Scholar

30.

Martínez JJ, Berta C, Varone L, Logarzo G, Zamudio P, Zaldívar-Riverón A, Aguilar- Velasco G. 2012. DNA barcoding and morphological identification of Argentine species of Apanteles (Hymenoptera: Braconidae), parasitoids of cactus-feeding moths (Lepidoptera: Pyralidae: Phycitinae), with description of a new species.Invertebrates Systematics26: 435–444. Google Scholar

31.

McFadyen REC. 1985. Larval characteristics of Cactoblastis spp. (Lepidoptera: Pyralidae) and the selection of species for biological control of prickly pears (Opuntia spp.).Bulletin of Entomological Research75: 159–168. Google Scholar

32.

Ochoa MJ. 2013. Black spot: an important disease for fodder, fruit, nopalitos cactus plantation.CactusNet Newsletter13: 63–72. Google Scholar

33.

Ochoa MJ, Rivera LA, Arteaga-Garibay RI. 2015. Black spot caused by Pseudocercospora opuntiae in cactus pear productive systems of Jalisco, Mexico.Journal of the Professional Association of the Cactus Development17: 1–12. Google Scholar

34.

Paraiso O, Hight SD, Kairo MTK, Bloem S, Carpenter JE, Reitz S. 2012. Laboratory biological parameters of Trichogramma fuentesi (Hymenoptera: Trichogrammatidae) an egg parasitoid of Cactoblastis cactorum (Lepidoptera: Pyralidae).Florida Entomologist95: 1–7. Google Scholar

35.

Pemberton RW. 1995. Cactoblastis cactorum (Lepidoptera: Pyralidae) in the United States: an immigrant biological control agent or an introduction of the nursery industry?American Entomologist41: 230–232. Google Scholar

36.

Pemberton RW, Cordo H. 2001a. Potential and risks of biological control of Cactoblastis cactorum (Lepidoptera: Pyralidae) in North America.Florida Entomologist84: 513–526. Google Scholar

37.

Pemberton RW, Cordo HA. 2001b. Nosema (Microsporida: Nosematidae) species as potential biological control agents of Cactoblastis cactorum (Lepidoptera: Pyralidae): surveys for the microsporidia in Argentina and South Africa.Florida Entomologist84: 527–530. Google Scholar

38.

Pettey RW. 1948. The biological control of prickly pears in South Africa.Science Bulletin of the Department of Agriculture and Forestry, Arcadia, Pretoria, Union of South Africa 271. Google Scholar

39.

Peñaflor MF, Erb M, Miranda LA, Werneburg AG, Bento JMS. 2011. Herbivoreinduced plant volatiles can serve as host location cues for a generalist and a specialist egg parasitoid.Journal of Chemical Ecology37: 1304–1313. Google Scholar

40.

Robertson HG. 1988. Spatial and temporal patterns of predation by ants on eggs of Cactoblastis cactorum.Ecological Entomology13: 207–214. Google Scholar

41.

Robertson HG, Hoffmann JH. 1989. Mortality and life-tables of Cactoblastis cactorum (Berg) (Lepidoptera: Pyralidae) compared on two host-plant species.Bulletin of Entomological Research79: 7–17. Google Scholar

42.

Siegel S. 1979. Estadísitica No Paramétrica Aplicada a las Ciencias de la Conducta.McGraw Hill, Trillas, México. Google Scholar

43.

Simmons EG. 2007. Alternaria: An Identification Manual.CBS Biodiversity Series 6.  Google Scholar

44.

Simonsen TJ. 2008. Phylogeny of the cactus-feeding phycitines and their relatives (Lepidoptera, Pyralidae) based on adult morphology: evaluation of adult character-systems in phycitine systematics and evidence for a single origin of Cactaceae-feeding larvae.Insect Systematics & Evolution39: 303– 325. Google Scholar

45.

Simonsen TJ, Brown RL, Sperling FAH. 2008. Tracing an invasion: phylogeography of Cactoblastis cactorum (Lepidoptera: Pyralidae) in the United States based on mitochondrial DNA.Annals of the Entomological Society of America101: 899–905. Google Scholar

46.

Smith MA, Rodriguez JJ, Whitifield JB, Deans AR, Janzen DH, Wallwachs W, Herbert PD. 2008. Extreme diversity of tropical parasitoid wasps exposed by iterative integration of natural history, DNA barcoding, morphology, and collections.Proceedings of the National Academy of Sciences105: 12359– 12364. Google Scholar

47.

Soberón J, Golubov J, Sarukhán J. 2001. The importance of Opuntia in México and routes of invasion and impact of Cactoblastis cactorum (Lepidoptera: Pyralidae).Florida Entomologist84: 486–492. Google Scholar

48.

Stehr FW. 1987. Inmature Insects.Kendall/Hunt Publishing Company, Dubuque, Iowa, USA. Google Scholar

49.

Varone L, Logarzo GA, Briano JA, Hight SD, Carpenter JE. 2014. Cactoblastis cactorum (Berg) (Lepidoptera: Pyralidae) use of Opuntia host species in Argentina.Biological Invasions16: 2367–2380. Google Scholar

50.

Varone L, Logarzo G, Martinez JJ, Navarro F, Carpenter JE, Hight SD. 2015. Field host range of Apanteles opuntiarum (Hymenoptera: Braconidae) in Argentina, a potential biocontrol agent of Cactoblastis cactorum (Lepidoptera: Pyralidae) in North America.Florida Entomologist98: 803–806. Google Scholar

51.

Varone L, Manteca Acosta M, Logarzo GA, Briano JA, Hight SD, Carpenter JE. 2012. Laboratory performance of Cactoblastis cactorum (Lepidoptera: Pyralidae) on South and North American Opuntia species occurring in Argentina.Florida Entomologist95: 1163–1173. Google Scholar

52.

Woodard AM, Ervin GN, Marsico TD. 2012. Host plant defense signaling in response to a coevolved herbivore combats introduced herbivore attack.Ecology and Evolution2: 1056–1064. Google Scholar

53.

Zimmermann HG, Bloem S, Klein H. 2004. Biology, History, Threat, Surveillance and Control of the Cactus Moth, Catoblastis cactorum. Joint FAO/IAEA Programme of Nuclear Techniques in Food and Agriculture.IAEA, Vienna, Austria. Google Scholar

54.

Zimmermann HG, Pérez-Sandi M, Goluvob J, Soberón J, Sarukhán J. 2000. Cactoblastis cactorum, una nueva plaga de muy alto riesgo para las opuntias de México.Biodiversitas33: 2–13. Google Scholar
Patricia J. Folgarait and Gloria Albioni Montenegro "A Study of Cactoblastis cactorum (Lepidoptera: Pyralidae) in its Native Range: Further Insights into Life Cycle, Larval Identification, Developmental Parameters, Natural Enemies, and Damage to the Host Plant Opuntia ficus-indica (Caryophyllales: Cactaceae)," Florida Entomologist 101(4), 559-572, (1 December 2018). https://doi.org/10.1653/024.101.0416
Published: 1 December 2018
JOURNAL ARTICLE
14 PAGES


SHARE
ARTICLE IMPACT
Back to Top