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Vicente Hernández-Ortiz, Hugo Delfín-González, Andrés Escalante-Tio, Pablo Manrique-Saide
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In order to carry on the detection and species inventory of hymenopteran parasitoids associated with fruit flies, we examined various tropical fruits growing at the Southern region of Yucatan. During a yearly cycle (Jun 2000 to Jun 2001), 9 host fruit species (including some varieties) were collected by 2 different methods. The first method involved weekly collection of ripened fruits that were transported to the laboratory (“Fruit-Lab”); and the second method was collection of fruits placed on the ground below the tree canopy (“Fruit-Beds”), and which remained in the field for two weeks, after which they were transported to the laboratory. Fruits obtained were counted and weighed, and the recovered pupae were quantified for each sample. As a whole, we sampled 4,470 fruits (850.8 Kg) from the 9 host plant species and varieties, which were infested by 5 fruit fly species: Anastrepha ludens (Loew), A. obliqua (Macquart), A. serpentina (Wiedemann), A. striata Schiner, and A. fraterculus (Wiedemann). The average parasitism in all samples was 3.69% represented by 11 hymenopteran species as follows: Braconidae, Doryctobracon areolatus (Szépligeti), and Opius bellus (Gahan); Figitidae, Aganaspis pelleranoi (Brethes), Aganaspis sp., Odontosema anastrephae Borgmeier and Odontosema sp.; Diapriidae, Coptera haywardi (Oglobin); Chalcididae, Dirhinus sp.; Pteromalidae, Spalangia endius Walker; Eurytomidae, Sycophila sp.; and Perilampidae, Euperilampus sp. On the basis of results in differences among samples for parasitism rates, fruit fly parasitoid, and fruit fly host plant, parasitoid assemblages are analyzed and discussed.

Diverse regional studies in Latin America have addressed the incidence of native parasitoids of the genus Anastrepha in countries such as Guatemala (Eskafi 1990), Costa Rica (Jirón & Mexzon 1989), Colombia (Yepes & Vélez 1989; Carrejo & González 1999), Venezuela (Katiyar et al. 1995; Boscán & Godoy 1996; García & Montilla 2001), Brazil (Canal et al. 1995; Leonel et al. 1995; Guimarâes et al. 1999; Aguiar-Menezes et al. 2001), and Argentina (Ovruski 1995; Ovruski et al. 2004, 2005).

Previous studies have stated that as many as 18 parasitoid species of Anastrepha have been recorded in Mexico, including the exotic species Diachasmimorpha longicaudata (Ashmead) and Aceratoneuromyia indica (Silvestri), both of which have been considered as established (Ovruski et al. 2000). However, at least 6 other exotic species have been introduced into Mexico for control of A. ludens and A. obliqua (Jiménez-Jiménez 1955, 1956, 1963).

Inventories of native parasitoids of Anastrepha fruit flies have been conducted in commercial orchards at Morelos and Chiapas (McPhail & Bliss 1933; Baker et al. 1944; Aluja et al. 1990), but also in wild environments associated with native fruit fly hosts in Nuevo León (Plummer & McPhail 1941; González-Hernández & Tejada 1979), Veracruz (Hernández-Ortiz et al. 1994; López et al. 1999), and Chiapas (Aluja et al. 2003). Inventories have not been done in many other fruit growing regions of Mexico.

Anastrepha ludens (Loew), A. obliqua (Macquart), A. serpentina (Wiedemann), A. striata Schiner, A. fraterculus (Wiedemann), A. ampliata Hernández-Ortiz, and A. pallens (Coquillett) have been recorded from the state of Yucatan (Hernández-Ortiz et al. 2002). The first 4 species are significant pests in fruit crops in Mexico and most of the Neotropics (Hernández-Ortiz & Aluja 1993). Fruit fly control in Yucatan has generally involved use of pesticides (CESVY 2000), and very little is known of the native hymenopteran parasitoid communities. An earlier regional study showed the presence in Yucatan of certain Opiinae (Braconidae) that potentially parasitize Anastrepha species, including Doryctobracon Ender, Utetes Foerster, and Opius Wesmael (Delfín-González & León 1997), although sampling methods in that study were not focused on host collection. Thus, specific relationships between Anastrepha and braconid species remain unknown.

The present study focuses on the search for and inventory of parasitoids that attack Anastrepha species, as well as determination of the relationships between fruit flies, host plants, and parasitoids in the fruit growing region of southern Yucatan, which mainly consists of mixed orchards of citrus, mango, sapodilla, guava, and red mombin.

Materials and Methods

The study was carried out in mixed commercial orchards in the Yaax-Hom Fruit Unit, 5 km from the Lol-Tun archaeological site, Oxkutzcab municipality, in southern Yucatan (20°18’N, 89°42’W). Surrounding native vegetation is semi-evergreen tropical forest (Flores & Espejel 1994). Collection of fruit samples occurred from Jun 2000 to Jun 2001, and included 9 host plant species during their fruit-growing seasons: sour orange, Citrus aurantium L. (Aug 2000 to Jan 2001); Valencia orange, C. sinensis (L.) Osbeck var. valenciana (Oct 2000 to Mar 2001); Ruby grapefruit, C. paradisi MacFad (Jul 2000 to Jan 2001); star apple, Chrysophyllum cainito L. (Jan to Mar 2001); mango, Mangifera indica L. c.v. cordoba, criollo, pico de loro, and manglova (Mar to Jul 2001); sapodilla, Manilkara zapota (L.) P. Royen (Sept to Dec 2000); mamey sapote, Pouteria sapota (Jacq.) H. Moore & Stearn (Apr to Jul 2001); guava, Psidium guajava L. (Jun to Sep 2000; Febr , April to Jun 2001); and red mombin, Spondias purpurea L. c.v. San Juan, tuxpana, and chi-abal (Apr to May 2001).

Fruits were sampled during the fruiting season of each host plant, according to availability of mature fallen fruits under the trees by means of 2 different methods as follows:

  1. Fruit-Lab Samples. Fruits were weekly sampled, placed in 20-liter containers with a substrate of soil from the collection site, covered with wire mesh and topped with a fine-mesh screen to prevent contamination. Samples were taken to the laboratory where they were counted, weighed, and reviewed daily. The recovered pupae were separated in small plastic containers for adult fly and parasitoid emergence.

  2. Fruit-Bed samples. This method was implemented once a sufficient amount of fruits were available. Collected fruits were arranged in “fruit-beds” under the tree canopy, consisting of a plastic tarp covered with soil, containing a known number of fruits previously weighed. “Fruit-beds” remained in the field for 2 weeks and were observed. All pupae recovered were taken to the laboratory in small plastic containers for adult fly and parasitoid emergence.

Percent of parasitism (PP) was recorded as PP = a/(a + b) 100, where a = Number of recovered parasitoids; and b = Number of emerged adult flies in each sample (Steck et al. 1986). Correlation analysis (Statistica 1999) was used to compare mean fruit weight of host sampled (calculated as the Log(10) of fruit weight), infestation index (calculated as the number of larvae/Kg fruit), and percentage of parasitoids recovered in each sample.

Specimens of fruit flies and parasitoids were determined by VHO and HDG, respectively. Voucher specimens are deposited in the Insect Collections (IEXA) of the Instituto de Ecologia (Xalapa, Veracruz), and in the Regional Entomological Collections (CERUY) of the Universidad Autónoma de Yucatán (Mérida, Yucatán). Botanical samples were identified by personnel of the Botanical Department of the UADY and deposited in the Herbarium of this institution. Botanical nomenclature is based on Terrel et al. (1986), and parasitoid nomenclature follows Ovruski et al. (2000).


Altogether, 4,470 fruits (850.8 kg) from 9 host species (including 4 mango varieties and 3 red mombin varieties) were examined and found to be infested by 5 Anastrepha species. All the citrus hosts (C. aurantium, C. sinensis, and C. paradisi) were infested by A. ludens, and 1 specimen of A. serpentina was recovered from ruby grapefruit and 2 from sour orange. A single specimen of A. fraterculus was found in sour orange. The hosts of the family Sapotaceae (C. cainito, P. sapota and M. zapota) were only infested by A. serpentina, and all S. purpurea varieties were infested by A. obliqua. The mango varieties (M. indica) were infested by A. ludens (53.4%) and A. obliqua (45.9%), and 2 specimens of A. serpentina were recovered. The guava fruits (Psidium guajava) were infested by A. fraterculus (84.2%) and A. striata (15.8%).

In total, 12,929 larvae and pupae were recovered from the sampled fruits. Although the number of fruits collected by each sampling method were equivalent, the “Fruit-Lab” samples exhibited a higher degree of infestation (2,227 fruits, with 8,511 recovered pupae), than that left in the “Fruit-Bed” samples (2,243 fruits, with 4,418 recovered pupae). The highest infestation indices per host were observed in P. guajava (103.2 larvae/Kg), S. pupurea (all varieties with 83.3 to 44 larvae/Kg), C. cainito (40.4 larvae/Kg), P. sapota (29.6 larvae/Kg), and C. aurantium (22.5 larvae/Kg). The lowest infestation rates occurred in M. indica (all varieties with 15.9 to 0.3 larvae/Kg), M. zapota (15.7 larvae/Kg), C. sinensis (4.2 larvae/Kg), and C. paradisi (3.1 larvae/Kg). Sample sizes in some of these low-infestation hosts were relatively small. In total, 9,223 fruit fly viable pupae were recovered during the study, which produced 8,883 adult flies and 340 parasitoid specimens. Average parasitism of all fruit flies was 3.69% (Table 1).

The recovered parasitoids included the following 11 species: the larval-pupal parasitoids D. areolatus (Szépligeti) and Opius bellus (Gahan) (Braconidae); Aganaspis pelleranoi (Brethes), Aganaspis sp., Odontosema anastrephae Borgmeier and Odontosema sp. (Figitidae); and the pupal parasitoids Coptera haywardi (Oglobin) (Diapriidae), Dirhinus sp. (Chalcididae), and Spalangia endius Walker (Pteromalidae). In addition, 2 other parasitoid species in the genera Sycophila sp. (Eurytomidae) and Euperilampus sp. (Perilampidae) were recorded for the first time in Anastrepha.

Relationships between fruit fly-parasitoids among samples showed that A. ludens was attacked in Citrus spp. by 5 parasitoids, which accounted for 29.3% of overall species, while in M. indica only 2 parasitoid species were recorded with 0.6%. In this sense, A. obliqua was parasitized in Spondias purpurea by 5 parasitoid species (16.7%); A. serpentina was attacked by 5 parasitoids (25.6%) infesting 3 hosts of the family Sapotaceae; and the Psidium guajava fruits infested by A. striata/A. fraterculus were parasitized by 8 species (27.8%).

Odontosema anastrephae was found in 7 host plant species representing 43.2% of all recovered parasitoids with highest proportions in Psidium guajava and Citrus aurantium. Coptera haywardi represented by 16.2% of parasitoids was found in 6 hosts; Doryctobracon areolatus (14.2%) was present in 4 hosts, particularly in C. cainito; and Spalangia endius only accounted for 6.5% of the overall recorded parasitism, but it was found in 4 different fruit hosts (Table 2).

Parasitism observed between 2 sampled collections revealed that specimens recovered from “Fruit-Bed” samples were higher than those recovered from the “Fruit-Lab” samples with 68.5% and 31.5%, respectively. In this sense, species as C. haywardi, O. anastrephae, S. endius, and Dirhinus sp. were dominant in “Fruit-Beds” accounting for 65% of all parasitoid specimens. On the contrary, the dominant species observed in “Fruit-Lab” samples were D. areolatus, Sycophila sp. and Euperilampus sp., which accounted for 21.2%. Table 3 shows the proportions of parasitoids by hosts obtained from each sampling method.

Correlation analysis between average fruit weight (Log Fruit Weight) and the infestation index (Mean Larvae/kg Fruit) were significant (r = −0.695; P = 0.005), indicating that as average weight increased in the different fruit species, the degree of infestation in the sample decreased. In contrast, there was not a significant correlation between the average fruit weight and the percentage of parasitism (r = -0.090; P = 0.758), and no correlation between infestation index and the percentage of parasitism among samples (r = 0.270; P = 0.350).


All parasitoid species reported here are first records for Anastrepha in Yucatan. No previous published records exist in literature of the genera Sycophila sp. (Eurytomidae) and Euperilampus sp. (Perilampidae) as parasitoids in Anastrepha (Ovruski et al. 2000). In this sense, Eurytoma sivinskii Gates & Grissell (Eurytomidae) was recently described attacking field populations of A. obliqua in Mexico (Gates & Grissell 2004). The eurytomids also occur as parasites in Cynipidae, Pteromalidae, Eurytomidae, Tanaostigmatidae, and Agaonidae (Grisell & Schauff 1990; DiGiulio 1997), and members of the family Perilampidae are hyperparasitoids of Ichneumonidae (Darling 1997). However, since the tephritid pupae were separated from the fruit and counted before adult emergence, these may be cases of hyperparasitism. These results should be further investigated.

The genus Dirhinus (Chalcididae) has been reported as a pupal parasite in Brachycerous Diptera widely distributed throughout the world tropics, with 3 known species in the USA (Burks 1947), and about 15 native species yet to be studied in regions ranging from Indiana (USA) to central Argentina (Boucek 1992). Unpublished data for Mexico indicate the presence of at least D. buscki (Crawford), D. schwarzi (Crawford), D. texanus (Ashmead), and D. giffardii (Silvestri) (data provided by Alejandro González-Hernández and Serguei Triapitsyn), although there are probably 1 or 2 more species with cosmopolitan distribution (Robert A. Wharton, Texas A & M University, personal communication).

Dirhinus giffardi is the unique species reported attacking fruit flies in the Neotropics, a native western African species introduced in Israel around 1950 (Podoler & Mazor 1981), and in Latin American countries of Puerto Rico (1935-1937), Costa Rica (1955), Peru (1960), Colombia (1970), and Bolivia (1971), and in Florida, USA (1977-1979) (Ovruski et al. 2000). In Mexico, it has been introduced in the states of Morelos and Oaxaca (Jiménez-Jiménez 1956), however there is no evidence that it is established in these regions. The Dirhinus species reported in this paper is very similar to D. schwarzi and D. giffardii, representing an undescribed species, and a new record of a native parasitoid for A. obliqua and A. serpentina.

The exotic species Diachasmimorpha longicaudata and Aceratoneuromyia indica were not recorded during the present study, but both have been documented as established and as having significant parasitism indices in Costa Rica (Wharton et al. 1981) and Mexico (Aluja et al. 1990) respectively, though both these studies were only concerned with coffee and mango orchards. Spalangia endius is a remarkable record, since it has been recorded from Anastrepha in Florida, though rarely reared from tephritids (Ovruski et al. 2000).

The majority of the published papers on Anastrepha parasitoids indicate that D. areolatus (Braconidae) is the most important native parasitoid species, having the highest parasitism indices in the Neotropical region in countries such as Mexico (Hernández-Ortiz et al. 1994; López et al. 1999), Guatemala (Eskafi 1990), Costa Rica (Jirón & Mexzon 1989), Colombia (Yepes & Velez 1989; Carrejo & González 1999), Venezuela (Katiyar et al. 1995), Brazil (Canal et al. 1995; Leonel et al. 1995; Aguiar-Menezes & Menezes 1997; Aguiar-Menezes et al. 2001), and Argentina (Ovruski et al. 2004, 2005).

On the basis of our results, O. anastrephae (Figitidae) is the dominant species occurring in 7 host plants attacked by 5 Anastrepha species. This species is considered a koinobiont parasitoid of Anastrepha larvae (Ovruski et al. 2000), though most of the recovered specimens were found in the Fruit-Bed samples, particularly from Citrus species and guava accounting for 87.7%. Such differences in the parasitism indices may be related to parasitoid biological factors, such as the ability of O. anastrephae to reach their host larvae by entering wounds in fruit located on the ground (Sivinski et al. 1997, 2000).

Comparisons between fruit weight and infestation rates among different hosts showed that the number of larvae was larger in small fruits but decreased as fruit size increased. This coincides with results observed for A. suspensa in Florida (USA), when fruit sizes and infestation indices were compared for 6 host species (Sivinski 1991).

Previous hypothesis on parasitism levels have been attributed in part to physical difficulties in locating immature stages within large fruits (Sivinski 1991). However, our comparisons between fruit weight of 14 hosts and the parasitism rates of the 11 parasitoid species showed no correlation. This may be due to the fact that more sample sizes are needed in order to test this hypothesis, or that the native parasitoid community has only become recently adapted to certain exotic fruit species included in our analysis, such as Citrus spp. and M. indica.

The low level of parasitism (3.69%) observed in this study is probably due to orchard management practices, in which destruction of fallen fruit and periodic pesticide use (CESVY 2000), could have a negative impact on parasitoid populations. Similar studies carried out in Brazil reported similar species diversity and levels of parasitism (Uchôa-Fernandes et al. 2003). Based on the parasitoid species diversity that attack the Anastrepha fruit flies in Yucatan, further studies need to be focused on the biology and ecology of certain native parasitoids such as O. anastrephae, C. haywardi, and D. areolatus as promising biological control agents.


The authors thank Luis Hernández Puch for allowing access to his family’s orchard for this research. Thanks are due to 2 anonymous reviewers for helpful suggestions on the earlier version of the manuscript. This study was partially supported by the project “Relaciones huésped-parasitoide y caracterización de la comunidad de bracónidos (Hymenoptera: Parasitica) en el estado de Yucatán” funded by the CONACYT, Mexico (Ref: 25016-N), and by the project “Ecología y sistemática de insectos fitófagos y saprófagos”, funded by the Instituto de Ecología, A.C. (Ref: 902-08/128).

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Table 1. Host plant sampled and recovered fruit fly pupae and parasitoids of Anastrepha species in Yucatan Mexico. Mangifera indica: 1 = var. cordoba; 2 = var. criollo; 3 = var. pico de loro; 4 = var. manglova; Spondias purpurea: 1 = var. San Juan; 2 = var. tuxpana, 3 = var. chi-abal.


Table 2. Parasitoid species emerged by host fruit species under 2 different systems of collection. M. indica; 1 = var. cordoba; S. purpurea; 1 = var. San Juan; 2 = var. tuxpana; 3 = var. chi−abal. Acronyms for parasitoid species are as follows: Dar = D. areolatus; Obel = O. bellus; Chay = C. haywardi; Apell = A. pelleranoi; Asp = Aganaspis sp.; Oanas = O. anastrephae; Osp = Odontoserna sp.; Spend = S. endius; Dsp = Dirhinus sp.; Sysp = Sycophila sp.; Esp = Euperilampus sp.


Table 3.

Relationship fruit fly-parasitoid species recovered from all sampled hosts expressed in percentages.

Vicente Hernández-Ortiz, Hugo Delfín-González, Andrés Escalante-Tio, and Pablo Manrique-Saide "HYMENOPTERAN PARASITOIDS OF ANASTREPHA FRUIT FLIES (DIPTERA: TEPHRITIDAE) REARED FROM DIFFERENT HOSTS IN YUCATAN, MEXICO," Florida Entomologist 89(4), 508-515, (1 December 2006).[508:HPOAFF]2.0.CO;2
Published: 1 December 2006
fruit flies
host plants
natural enemies
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