Short communication. Toxicity of abamectin, acetamiprid, imidacloprid, mineral oil and an industrial detergent with respect to Encarsia formosa



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Short communication. Toxicity of abamectin, acetamiprid, imidacloprid, mineral oil and an industrial detergent with respect to Encarsia formosa (Gahan) parasitizing Trialeurodes vaporariorum Westwood nymphs J. E. Araya 1 *, P. Estay 2 and M. H. Araya 1 1 Departamento de Sanidad Vegetal. Facultad de Ciencias Agronómicas. Universidad de Chile. Casilla 1004. Santiago. Chile 2 Instituto de Investigaciones Agropecuarias. Estación Experimental La Platina. Casilla 439-3. Santiago. Chile Abstract The control of Trialeurodes vaporariorum on tomato with Encarsia formosa is influenced by the use of insecticides. Nine days after allowing E. formosa adults to lay their eggs in T. vaporariorum nymphs on tomato plants, insecticide solutions (abamectin, mineral oil, acetamiprid, an industrial detergent and imadacloprid) were applied at the highest recommended dosages to tomato leaflets in Petri dishes using a Potter tower (four replicates, each involving 20 parasitized nymphs). Adult parasitoids began to emerge on day 7 post-application; this lasted 3-4 days, peaking on day 9 post-application. All the tested products killed the E. formosa pupae (an effect significantly different [P 0.05] to that achieved with the water control). The products with the greatest toxicity were the detergent (62.99% mortality) and mineral oil (49.55% mortality; no significant difference). The effect of abamectin, the third most toxic agent (33.05% mortality), was not statistically different to that of the mineral oil. Imidacloprid (20.17% mortality) and acetamiprid (20.71% mortality) were the least toxic treatments and could be used (along with abamectin to a lesser extent) in integrated whitefly management programmes involving E. formosa pupae. At the concentrations used, the mineral oil and industrial detergent are not recommended for use in such programmes given their high toxicity to E. formosa pupae. Additional key words: control, greenhouse whitefly, IPM, parasitoids, tomato. Resumen Nota corta. Toxicidad de abamectina, acetamiprid, imidacloprid, aceite mineral y un detergente en Encarsia formosa (Gahan) parasitando ninfas de Trialeurodes vaporariorum Westwood Los insecticidas influyen sobre el control de Trialeurodes vaporariorum en tomate mediante Encarsia formosa. Se estudió el efecto en laboratorio de las mayores dosis recomendadas comercialmente de abamectina, aceite mineral, acetamiprid, detergente e imidacloprid, más un control con agua, sobre cuatro repeticiones de 20 ninfas parasitadas de la mosca blanca. Se aplicaron soluciones de dosis calculadas para una placa Petri estándar sobre folíolos de tomate en una torre Potter, 9 días después de introducir parasitoides adultos en las placas Petri (cuando las ninfas parasitadas se veían oscuras). Los parasitoides adultos comenzaron a emerger el día 7 desde las aplicaciones; la emergencia duró 3-4 días, tuvo un máximo el día 2 y decreció luego gradualmente. Todos los productos mataron las pupas de E. formosa y fueron diferentes (P 0,05) del control. Los productos con mayor mortalidad fueron el detergente (62,99%) y el aceite mineral (49,55%), que no difirió estadísticamente del primero, y tampoco con abamectina (33,05%), el siguiente tratamiento en mortalidad. Imidacloprid (20,17%) y acetamiprid (20,71%) fueron los tratamientos menos tóxicos, y podrían ser utilizados (y en menor grado por abamectina) en programas de control integrado de plagas para la mosca blanca que incluyan E. formosa, principalmente como pupas. A las concentraciones aplicadas, el aceite mineral y el detergente industrial no son recomendables es estos programas, debido a su alta toxicidad sobre pupas de E. formosa. Palabras clave adicionales: control integrado de plagas, mosca blanca de los invernaderos, parasitoides, tomate. * Corresponding author: jearaya@uchile.cl jaimearaya@yahoo.com

Toxicity of insecticides on Encarsia formosa parasitizing Trialeurodes vaporariorum nymphs The whitefly Trialeurodes vaporariorum Westwood is a primary pest of greenhouse tomato plants in the Quillota Commune (5 th Region of Chile). The major problem it causes is indirect damage due to the accumulation of honeydew, the removal of which increases production costs (Araya et al., 2005a). This species is normally controlled preventively using anti-aphid nets, weed handling, and the elimination of post-harvest crop remains, etc. However, these controls are commonly insufficient and alternative methods are required (Estay and Bruna, 2002). Of the six parasitoids that directly affect T. vaporariorum on tomato crops in Chile, Encarsia formosa (Gahan) is the most effective in the Quillota area (Estay and Bruna, 2002) (information on the biology of E. formosa can be found in Araya et al. [2005b]). In severe infestations, however, even E. formosa is unable to control the pest effectively, and insecticides have to be used. Unfortunately, this also reduces the effectiveness of the parasitoid. Araya et al. (2005a) reported that 24 h after application, the insecticides imidacloprid, acetamiprid and abamectin were toxic to E. formosa adults. In other studies, the toxicity of a number of pesticides was reported to be lower when the parasitoids were protected inside the body of the host; this has been indicated for E. formosa by Viggiani et al. (1998), for Aphidius ervi Haliday by Zuazúa et al. (2003), and for Apanteles glomeratus (L.) by Araya et al. (2005c). With the aim of selecting the best pesticides for use in integrated pest management (IPM) systems involving E. formosa, the objective of this work was to evaluate the toxicity of a number of treatments (imidacloprid, acetamiprid, abamectin, mineral oil and an industrial detergent) on the pupae of this parasitoid while inside the bodies of T. vaporariorum nymphs. All the agents tested are commonly used to control this whitefly on greenhouse tomato crops in the Quillota area. To provide a secure and permanent supply of specimens for the experiment, Trialeurodes vaporariorum and E. formosa were reared on tomato plants as described by Estay (1993) and Araya et al. (2005b). Nine days after the nymphs had been parasitized, medium size tomato leaflets with at least 20 parasitized nymphs were collected and placed on Petri dishes with wet filter paper to immobilize the leaflets during insecticide application. The insecticides described in Table 1 (0.63 ml) were applied (at the highest dosage recommended for application in the field) to the lower side of the leaflet over an 8 s period using a Potter tower. The treated leaflets were left to dry for 15-20 min at room temperature and then placed in other Petri dishes containing moistened paper. The lids had a window covered with a cloth screen to prevent a lethal chamber effect. These Petri dishes were kept at 25 C and a relative humidity of 55 5% under a 16:8 h light-dark cycle. Petri dishes containing water were used as controls. Each treatment was replicated four times. The toxicity of the insecticides with respect to E. formosa pupae was assessed based on the methodology described by Oomen (1988). The adults that emerged 10 days after the applications were counted. Emergence was examined under binocular magnification. Pupae with exit holes were deemed to have produced live wasps; those with no holes and which appeared dry and dorsally flattened were considered not to have Table 1. formosa Products applied on pupae of Trialeurodes vaporariorum parasitized by Encarsia Treatments Commercial products Commercial product (hl -1 ) Active ingredient (mg L -1 ) Abamectin Fast 1,8 EC 100 ml 18 Mineral oil Citroliv 1500 ml 14250 Acetamiprid Mospilan SP 35 g 70 Detergent Quix 500 ml Imidacloprid Confidor Supra 40 ml 204 Control Water The concentration of the active ingredient of the detergent Quix is not provided because of its high variability.

J. E. Araya et al. produced live adults. Percentage mortality was corrected for the emergence seen in the controls according to Abbott s (1925) formula; the insecticides were then classified using Hassan s toxicity scale (Hassan, 1992). Pesticides causing >30% mortality were considered toxic to E. formosa; no further evaluations were deemed necessary. Those causing <30% mortality were considered potentially toxic and subjected to toxicity tests under semi-field conditions (see Oomen, 1988). Their toxicity with respect to the adult parasitoids was also investigated (see Araya et al., 2005a). The results were normalized by transformation with the function arcsine (% mortality /100), and then analysed by ANOVA. Significant differences (P 0.05) were detected using Duncan s multiple range test (Duncan, 1955). The emergence of adult parasitoids from the pupae began on day 7 after the application of insecticides, and lasted 3-4 days, peaking on day 9 post-application. Table 2 shows the E. formosa pupal mortality rate at 10 days post-application. All the treatments caused some mortality, and all caused significantly (P 0.05) more than the control. The most toxic treatments were the detergent and the mineral oil (no significant difference [NSD]). The third most lethal insecticide was abamectin (NSD compared to the mineral oil). Imidacloprid and acetamiprid were the least toxic. Because of its capacity to form a film on the insects (Chapman et al., 1963; Metcalf and Flint, 1980; Matta and López, 1986; Sazo, 1989; Sazo and Piña, 1989), the mineral oil may have caused the asphyxia and death of the E. formosa pupae inside the T. vaporariorum nymphs. The oil also enters the spiracles and corrodes the tracheae, affects the muscles and nerves (Davidson et al., 1991), and impedes the establishment of the juvenile stages in any scales that might emerge shortly after treatment (Chapman et al., 1963). The E. formosa pupae affected by the detergent looked dehydrated and shrunken; dissection confirmed that they were dead. According to Álvarez (1988), detergents kill pests by dissolving the waxes and other lipids of the epicuticle, leading to dehydration. The 33.05% mortality caused by abamectin applied at 18 mg L -1 was less than the 47% obtained by Zchori-Frein et al. (1994) with 11.24 mg L -1 under the same conditions of temperature and humidity. This discrepancy is probably due to the different application and evaluation methodologies used. In the above-mentioned study, E. formosa pupae were submerged for 5sintheinsecticide; this generally leads to greater mortality than spraying. The lower E. formosa pupal mortality caused by imidacloprid and acetamiprid agrees with that indicated by Viggiani et al. (1998), who reported high emergence rates (NSD) for the parasitoid after treating pupae with these insecticides. A low imidacloprid-induced mortality rate has been reported for Aphidius ervi Haliday when the parasitoid is protected by the body of its host. Zuazúa et al. (2003) observed that imidacloprid caused low mortality and allowed high adult emergence in mummies of parasitized Acyrthosiphon pisum (Harris) aphids. The affording of protection by the host body has also been reported in mummified aphids, in which Aphidius rhopalosiphi De Stefani Perez appeared to be safe from the action of a number of insecticides (Borgemeister et al., 1993). Table 2. Effect of the insecticides on the mortality of Encarsia formosa pupae on tomato leaflets and their toxicity category Treatments Mortality (%) 1 Corrected mortality (%) 2 Categories of toxicity 3 Detergent 63.32 a 62.99 2 Mineral oil 50.00 ab 49.55 2 Abamectin 33.65 bc 33.05 2 Acetamiprid 21.42 c 20.71 1 Imidacloprid 20.89 c 20.17 1 Control 0.89 d 0.00 1 Means in the same column with different letters are significantly different (P 0.05) according to Duncan s (1955) multiple range test. 2 Mortality corrected by Abbott (1925). 3 According to the Hassan scale (Hassan, 1992).

Toxicity of insecticides on Encarsia formosa parasitizing Trialeurodes vaporariorum nymphs Although in this experiment the imidacloprid and acetamiprid treatments were innocuous to E. formosa pupae, their relatively rapid action on the adults of this parasitoid (Araya et al., 2005a) casts doubts about their usefulness in IPM. After evaluating the effects of 18 insecticides on E. formosa pupae and adults in the laboratory, Hayashi (1996) concluded that imidacloprid and acetamiprid should not be used in programs that involve this parasitoid. Tzeng and Kao (1999) also evaluated the effect of imidacloprid and acetamiprid on Eretmocerus orientalis Silvestri, a parasitoid of Bemisia argentifolii Bellows & Perring, and obtained results that warned against the use of either against this whitefly. However, their toxicity classification scale was different since they considered 80-99% mortality to be indicative of «moderate toxicity». The less intense effect of these insecticides on E. formosa pupae in the present study indicates, however, that they could be used in such programs. Abamectin showed a similar trend. The comparison of different studies therefore needs to be performed carefully, taking into account the methodologies and toxicity classification scales used. These results complement those obtained with E. formosa adults by Araya et al. (2005a), and corroborate that parasitoids inside the body of their hosts are less affected by a number of insecticides. In conclusion, imidacloprid and acetamiprid (and to a lesser extent abamectin) could be used in IPM programmes involving E. formosa pupae designed to control whiteflies on tomato. At the concentrations used in this experiment, the mineral oil and the industrial detergent are not recommended for any such programme given their toxicity with respect to the parasitoid pupae. It would not be correct, however, to assume that the same results might be obtained for other mineral oils or detergent-based products. References ABBOTT W.S., 1925. A method of computing the effectiveness of an insecticide. J Econ Entomol 18, 265-267. ÁLVAREZ C., 1988. Insecticidas que inhiben la función de la cutícula. In: Insecticidas biorracionales (Bellés X., ed). Consejo Superior de Investigaciones Científicas, Madrid, Spain. pp. 251-267. ARAYA M.H., ESTAY P., ARAYA J.E., 2005a. Toxicidad de imidacloprid, acetamiprid y abamectina sobre adultos de Encarsia formosa (Gahan). Bol Soc Entomologica Aragonesa 37, 369-371. ARAYA J.E., ESTAY P., ARAYA M.H., 2005b. Observaciones sobre biología y crianza de Encarsia formosa Gahan, parasitoide de Trialeurodes vaporariorum Westwood. Phytoma (Spain) 169 (May), 58-60. ARAYA J.E., SANHUEZA A., GUERRERO M.A., 2005c. Efecto de varios insecticidas sobre adultos de Apanteles glomeratus (L.), parasitoide de larvas de la mariposa blanca de la col, Pieris brassicae L. Bol Sanidad Veg, Plagas (Spain) 31(4), 617-623. BORGEMEISTER C., POEHLING H.M., DINTER A., HÖLLER C., 1993. Effects of insecticides on life story parameters of the aphid parasitoid Aphidius rhopalosiphi (Hym.: Aphidiidae). Entomophaga 38(2), 245-255. CHAPMAN P.J., RIEHL L.A., PEARCE G.W., 1963. Las pulverizaciones de aceite para los árboles frutales. In: Insectos: plagas de la agricultura y sistemas para combatirlos. Centro Regional de Ayuda Técnica, Mexico. pp. 256-268. DAVIDSON N.A., DIBBLE J.E., FLINT M.L., MARER P.J., GUYYE A., 1991. Managing insects and mites with spray oils. University of California, Division of Agriculture and Natural Resources, Publication 3347. 47 pp. DUNCAN D.B., 1955. Multiple F and multiple range tests. Biometrics 11, 1-41. ESTAY P., 1993. Mosquita blanca de los invernaderos. Investigación y Progreso Agropecuario La Platina 78, 30-36. ESTAY P., BRUNA A., 2002. Insectos, ácaros y enfermedades asociados al tomate en Chile. INIA, Santiago, Chile. 111 pp. HASSAN S.A., 1992. Guideline for the evaluation of side effects of plant protection product on Trichogramma cacoeciae. IOBC/WPRS Working Group: Pesticides and Beneficial Organisms Bulletin 14(3), 18-39. HAYASHI H., 1996. Side effects of pesticides on Encarsia formosa Gahan. Bulletin of the Hiroshima Prefectural Agriculture Research Center 64, 33-43. MATTA A., LÓPEZ E., 1986. Bioantagonista de plantas cultivadas y fundamentos de su control: Insectos y ácaros. Unidad III. Control de insectos y ácaros plaga, Facultad de Agronomía, Universidad Católica de Valparaíso. Quillota, Chile. 44 p. METCALF C., FLINT W., 1980. Insectos destructivos e insectos útiles, sus costumbres y su control. Continental, México. 1176 pp. OOMEN P.A., 1988. Guideline for the evaluation of side-effects of pesticides on Encarsia formosa. IOB/WPRS Working Group on Pesticides and Beneficial Organisms Bulletin 11(4), 19-28. SAZO L., 1989. Control de arañita roja en pomáceas y carozos mediante aceites minerales. In: Manejo de plagas y enfermedades en frutales y uva de mesa. Universidad de Chile, Facultad de Ciencias Agrarias Forestales, Departamento de Sanidad Vegetal, Santiago, Chile. pp. 1-167.

J. E. Araya et al. SAZO L., PIÑA P., 1989. Usos y perspectivas de los aceites minerales en el control de ácaros fitófagos en frutales de hoja caduca. Aconex 25, 5-8. TZENG C., KAO S., 1999. Toxicity of some insecticides to Eretmocerus orientalis adults a parasitoid of silverleaf whitefly (Bemisia argentifolii). Plant Protection Bulletin Taipei 41(1), 83-86. VIGGIANI G., BERNARDO U., GIORGINI M., 1998. Effetti di contatto di fitofarmaci su alcuni insetti entomofagi. Informatore-Fitopatologico 48(10), 76-78. ZCHORI-FREIN E., ROUSH R., SANDERSON J., 1994. Potential for integration of biological and chemical control of greenhouse whitefly (Homoptera: Aleyrodidae) using Encarsia formosa (Hymenoptera: Aphelinidae) and abamectin. Environ Entomol 23(5), 1277-1282. ZUAZÚA F., ARAYA J.E., GUERRERO M.A., 2003. Efectos letales de insecticidas sobre Aphidius ervi Haliday (Hymenoptera: Aphidiidae), parasitoide de Acyrthosiphon pisum (Harris) (Homoptera: Aphididae). Bol San Veg, Plagas 29(2), 299-307.