Repellent and Lethal Activities of Extracts From Fruits of Chinaberry (Melia azedarach L., Meliaceae) Against Triatoma infestans

ORIGINAL RESEARCH ARTICLE Front. Vet. Sci., 26 July 2018 | https://doi.org/10.3389/fvets.2018.00158 Martín Dadé, Pedro Zeinsteger, Facundo Bozzolo and Nora Mestorino* Laboratory of Pharmacological and Toxicological Studies (LEFyT), Faculty of Veterinary Science, Universidad Nacional de La Plata, La Plata, Argentina Triatoma infestans is the principal vector of Trypanosoma cruzi, parasite responsible of Chagas's Disease transmission in Argentina. Pyrethroids have become common pesticides for the control of T. infestans but increasing resistance encourages the search of new alternatives and the use of natural products for biological control arises as a new strategy. Melia azedarach L. is originated from the Himalaya's region and several compounds are part of its rich phytochemistry. Folk medicine of the plant is due to its repellent and insecticidal activities. Aims of this work were to evaluate the repellent activity of methanolic and acetonic extracts from fruits of M. azedarach by means of the area preference method of fifth and first nymph stages as well as to test the acute lethal effect of the more repellent extract by means of direct application on cuticle on both stages. For repellence, qualitative filter papers were divided into two halves, one treated with methanolic (ME) or acetonic (AC) extract and the other without treatment. Controls were impregnated half with methanol or acetone and half without the solvents. One nymph was located in each Petri or well and repellence percentage was determined. For the lethal effect, fasted and fed to repletion 5th stage nymphs were topically administered with different concentrations of AC and deaths were registered after 24, 48, 72, 96, and 120 h. Phytochemical analysis of extracts was performed as well. AC demonstrated high repellent activity (100%, both stages), whereas ME extract activity was slight (10–21%). AC extract was selected for lethal assays due to early repellent activity. Fed to repletion nymphs were more sensitive to the lethal activity of the extract when compared to fasted nymphs (LD50: 11.5 vs. 23.1 μg/insect, respectively). Phytochemistry assays of extracts showed a higher concentration of flavonoids, alkaloids and triterpenes for AC. Considering these results, next assays will include the test of Melia azedarach extract on T. infestans that are resistant to pyrethroids for a possible synergism between AC and the pesticides. Introduction Chagas's Disease, also known as American Trypanosomiasis, is a zoonosis caused by the protozoan parasite Trypanosoma cruzi which needs a host body and a vector to complete its life cycle, being the latter the hematophagous insect Triatoma infestans (“kissing bug”) distributed from Southern United States (1) to Argentina (2). The disease is endemic to Latin America and has been reported from Southern Argentina to Northern Mexico. It has also been diagnosed in people from non-endemic countries because of the increment of international migration during recent years (USA and countries from Europe, Asia and Oceania). According to the World Health Organization, up to 10 million humans are infected worldwide with more than 10,000 deaths in 2008 (3). Transmission of T. cruzi is not only due to T. infestans hematophagous activity but also a consequence of the ingestion of contaminated food with vector stools (4), congenital infection (5, 6), blood transfusion (7, 8) and organ transplantation (9, 10). Triatomines live in dark and warm cracks of poorly-constructed homes in both rural and suburban areas. They become active during the night when they feed on hot blooded species including man. An insect usually bites an exposed area of the skin and defecates while feeding close to the bite, this situation enhances infection as the bitten person smears the feces into the bite or into the eyes, mouth or any skin lesion (3). The evolution of the disease is characterized by two phases: acute, which may last 2 months and can be asymptomatic or with symptoms appearing shortly after the infection, they include fever, headache, enlarged lymph nodes, pallor, muscle pain, labored breathing, swelling and abdominal or chest pain (3); and a chronic phase which may last for the entire life with symptoms appearing after a silent period which may take several years. During the chronic phase, up to 30% of infected people develop lesions that compromise the heart, and up to 10% develop digestive, neurological or mixed alterations (3). Two medications are commonly used for the treatment of the acute phase of trypanosomiasis, including nifurtimox and benznidazole, with 75–100% healing with prompt administration, particularly in cases of congenital infection (11). Both medications are effective during the acute phase but not in the chronic phase and this is one of the reasons why many strategies are developed to avoid vector's transmission. Despite these pharmacological alternatives, therapeutic management of the disease is complex as adverse effects may develop during the treatment. Many alternatives have been implemented for the interruption of disease spreading including early detection of seropositive patients and pharmacological treatment during the acute phase to avoid irreversible lesions in target organs, health campaigns and vectors surveillance by means of synthetic pesticides (e.g., pyrethroids) with residual properties (12). Pesticides are extensively used in many countries of Latin America with strong impact on non-target insects, animals and human health as well. Besides these issues, resistance to pesticide develops fast in some species of insects (13, 14) including T. infestans (15). Moreover, the exposition of pyrethroids to sunlight and water determines a substantial reduction of residual power (16), a common situation in rural areas. To minimize these factors new technologies and management strategies are necessary to obtain less hazardous and more resistant chemical or biological compounds. Regarding the latter, the use of plant extracts arises as a promising alternative nowadays, something that it is not necessarily new because botanical insecticides have been used for at least 2000 years in Asia and Middle East (17). Interest in these compounds relies on their low cost, efficacy, degradability and pharmacological activity on insects (18, 19). Melia azedarach L. (MA) also known as “chinaberry tree” is an ornamental species of the Meliaceae family considered to be native from Asia which grows from North to South America as well as Northern Australia, Africa and Southern Europe (20). It is a deciduous and evergreen 3–10 m tree with sweet-scented lilac flowers during autumn and spring, dark green leaves and a round-shaped fruit initially green and yellowish when mature (21). Trees are cultivated in countries with template to warm climates and in Argentina they are easily found in houses and parks as ornamental trees for protection against sunlight and winds. Melia azedarach has demonstrated to have both pharmacological and toxicological properties. Fruits have been studied for their phytochemical composition which includes melianoninol, melianol, melianone, meliandiol, vanillin, and vanillic acid (22). Toxic compounds are tetranortriterpens, known as meliatoxins, present in all the parts of the plants but specially concentrated in the ripe fruits (21). Aqueous and alcohol extracts prepared from different parts of MA have antibacterial (23), antiparasitic (24), antifungal (25), antiviral (26), and antioxidant properties (27) while the ingestion of foliage or fruit by cattle (28), pigs (29), dogs (30), and other species has caused intoxication with fatal outcomes in some cases. MA has also been tested for insecticide activity. Vergara et al. (31) and Carpinella et al. (25) state that this capability is due to the anti-feeding effect of tri-terpenoids that inhibit food intake capacity, which has been demonstrated in phytophagous insects, thus leading to death and malformations in next generations. Plant extracts prepared from leaves or fruits have been tested on bean weevil (32), mosquitoes (33, 34) and moths (35). Some information exists regarding repellent and insecticidal properties on T. infestans (36) but no up-to-date data are available. Purpose of this work is to present the results of tests performed with acetonic and methanolic extracts prepared from fruits of MA considering repellent and insecticidal capabilities on different evolutionary stages of T. infestans for a possible economic and easy to implement complement of traditional pesticides used for the control of the vector of Chagas disease. Materials and Methods Plant Material Ripe fruits of MA (1 kg) were collected in August 2017 from trees located close to the School of Veterinary Science, National University of La Plata (UNLP). Voucher specimens were deposited after botanical identification at the Laboratory of Pharmacological and Toxicological Studies (“LEFyT,” from Spanish), School of Veterinary Sciences, UNLP. Plant material was put inside an Erlenmeyer (2 L) and was shaken, after this 10 g of fruits were separated for the assays. Fruits were washed with distilled water and excess of moisture was removed on adsorbent paper. Covers were separated from the seeds for a better extraction and all the plant material was placed in a Soxhlet cartridge. Melia Azedarach Extracts For the extraction, acetone or methanol (200 mL) was used as solvent for the preparation of the acetonic extract and methanolic extract, respectively. Ten grams of fruits were used to obtain each extract. The extraction temperature of the Soxhlet equipment ranged from 60 to 70°C and the process was carried out during 10 h under dim light to avoid possible inactivation of photosensitive compounds. The acetonic (AC) or methanolic (ME) extract was separated into two parts, 50 mL for phytochemical assay and 150 mL for biological assay in triatomines. The solvent of the 150 mL fraction (AC or ME extracts) was rotaevaporated at 60°C (Senko Ltd.) and a dark red residue was obtained which was resuspended in the same solvent (50 mL). This process was carried out as three consecutive extractions using 10 g of M. azedarach fruits each in order to standardize the amount of residue in the rotaevaporator flask and for each in vivo assay, obtaining in average 342 ± 50 mg/50 mL AC extract and 2,524 ± 150 mg/50 mL ME extract. These stock solutions were used to prepare a series of dilutions (1:1, 1:5, and 1:10). Qualitative chemical determinations were performed with the 50 mL of AC and ME extracts to determine the presence of compounds with potential repellent and insecticide activities. AC and ME total extracts were fractioned in three parts and chemical reactions were used for each fraction as follows: Fraction A: Shinoda for flavonoids, FeCl3 for tannins and phenolic OH, Iodine for lipids, Phenol 5% + concentrated H2SO4 for carbohydrates; fraction B: Liebermann-Burchard for steroids, Bornträger for antraquinones; fraction C: Dragendorff for alkaloids, Kedde for cardenolides and Rosenheim for leucoanthocyanins (37, 38). Only qualitative analysis of the extracts was performed to guarantee the presence of compounds with repellence and lethal activities (considering previous works by other researchers). Quantitative determinations considering chromatographic techniques will be part of future assays in order to determine exact ingredients of AC extract of Melia azedarach in our laboratory. Experimental Insects Nymphs of 1st and 5th stages of T. infestans susceptible to pyrethroids were from an insect colony grown at LEFyT-UNLP insectary. This colony was originated from triatomines provided by the Centro de Referencia de Vectores (CeReVe), Santa María de Punilla, Córdoba, Argentina. All the insects were free of T. cruzi infection. Colonies were fed with chicken blood once a week, kept at 26 ± 2°C, 60–70% relative humidity and a light cycle of 12:12. Repellent Activity of AC and ME Extracts on 1st and 5th T. infestans Stages For the evaluation of the repellent activity of AC and ME extracts the preference area method was used. Fifth stage nymphs were placed on a 9 cm diameter filter paper divided into two areas and then into Petri dishes (Figure 1). For 1st stage nymphs 3.5 cm filter papers were located in multiple-well plates (6 wells, Figure 2), purpose of this was to offer the insect the half of the contact surface treated with different concentrations of extract and the remaining without treatment. In case of positive repellent activity, the insect moves to the area of the paper free of extract. For controls, one half of the paper was treated with acetone o methanol. Treated halves were left to evaporate during 24 h before placement of insects and joined to the correspondent non-treated half using adhesive tape. Both nymph stages were tested using three dilutions of AC or ME extracts (1:1, 1:5, and 1:10), each concentration tested on ten insects. Volume for each dilution was 500 μL for 5th stage nymphs and 77 μL for 1st stage nymphs. Each insect was placed in the center of the paper and observation was performed after 1, 12, 24, and 48 h. Repellent activity (RA) was calculated using the following equation: RA=Nc −NtNc +Nt x 100 Nc: number of insects in the control area; Nt: number of insects in the treated area. FIGURE 1 www.frontiersin.org Figure 1. Fifth stage nymphs located into Petri dishes. FIGURE 2 www.frontiersin.org Figure 2. First stage nymphs located in multiple-well plates (6 wells). Values of RA may be negative or positive. In the case that most of the insects stay in the untreated area (Nc > Nt) RA value will be positive and the assayed substance is considered to have repellent activity. Negative RA values (Nt > Nc) means that most of the insects stay in the treated area, thus considering the assayed extract to have attracting activity (37). Insecticidal Capabilities Assays were performed only with AC extract as it showed rapid onset of repellent activity, a characteristic that was absent in ME extract. Insecticidal capability of AC extract was determined on 5th stage nymphs by means of the calculation of the LD50, comparing fed to repletion vs. fasted triatomines. From the stock solution of the AC extract (342 ± 50 mg/50 mL), different work solutions to be assayed were prepared by means of dilution/concentration procedures in order to obtain a concentrations range between 1.37 and 30.52 μg/μL. Briefly, the stock solution was diluted with acetone (1:5) to obtain a secondary solution (1.37 μg/μL). Afterwards aliquots were taken from the stock or secondary solution, which were concentrated to dryness (SpeedDry Vacuum Concentrators Christ CD Plus, Germany) and then dissolved in different volumes of acetone to reach the final concentrations/μL to be tested on the triatomines. Calculation of LD50 in 5th Stage T. infestans Fasted Nymphs For the determination of the LD50 of AC extract, 5th stage T. infestans susceptible to pyrethroids was used according to the WHO protocol (38). Nymphs were fasted during 12–15 days after ecdysis and prior to their use. The assay considered a binary response—dead or alive—with an independent variable (dose). AC extract was applied topically on the dorsal of nymphs' abdomen (1 μL). For the dose-response curves, increasing doses of the extract were evaluated (1.37–30.52 μg/μL or 1.37–30.52 μg/insect). The same procedure was used for controls with the application of 1 μL acetone. Assay was replicated during three different days under similar conditions and all the extracts were recently prepared for each repetition. Ten nymphs were used for each dose and repetition (30 insects for each dose) and only 10 nymphs as controls. After topication insects were located in labeled flasks and observed after 24, 48, 72, and 168 h. An insect was considered dead when it was not able to move from the center of the filter paper by its own or by means of stimulation with tweezers. Dead insects were removed and placed in labeled containers and observed again after 24 h to corroborate death. Calculation of LD50 in 5th Stage T. infestans Fed to Repletion Nymphs For this experiment, 5th stage T. infestans nymphs fed to repletion with chicken blood were used in groups of 10 insects. Prior to this, nymphs were fasted for a period of 12–15 days after ecdysis. Each triatomine was individualized with different acrylic paint color marks (AD acrílico, Argentina) and weight before and after feeding with a precision scale (Denver Instruments, USA). After a feeding period of 30 min the quotient between weight after and before was calculated and only those insects with a 4-fold relation or more were used. For the determination of the LD50 the same procedure for fasted nymphs was used. Statistical Analysis To verify the relation among different doses of AC extract regarding mortality of nymphs the Probit method was used, which allows to associate mortality with a dose necessary to cause it. Mortality data for the treated nymphs were corrected taking into account the mortality of control nymphs by means of Abbott's Equation (39): Corrected % mortality=(% NT mortality−% NC mortality)(100%−% NC mortality) x 100 Where: NT: nymphs treated with different doses of AC extract diluted in acetone NC: control nymphs, only received acetone. From corrected mortality data of AC extract different dose-response curves were obtained using the POLO-PLUS software (LeOra Software Company, Petaluma, CA 2005). LD50 with its respective confidence interval 95% (CI 95%) was calculated as well. To determine differences in susceptibility between T. infestans nymph populations the ratio calculation between LD50 (RLD50) was calculated with confidence interval (CI) of 95%. LD50's are considered statistically different when 95% CI of RLD50 does not include number one (p < 0.05) (40). Results Phytochemistry of AC and ME Extracts Table 1 shows the results of the phytochemical analysis of the AC extract while Table 2 those for ME extract. TABLE 1 www.frontiersin.org Table 1. Qualitative analysis of AC extract. TABLE 2 www.frontiersin.org Table 2. Qualitative analysis of ME extract. Repellent Activities of AC and ME Extracts In Tables 3, 4 it can be observed that only AC extract showed repellent activity for both stages of T. infestans. Repellent activity was directly proportional to the concentration of the extract. Dilution 1:10 did not cause repellence or it was negligible in any stage. In the case of 1st nymph stage, 1:1 dilution showed weak repellent activity as early as 1 h of the initiation of the assay (Table 3), while 1:5 dilution demonstrated this activity at 24 h. Highest repellent activity (100%) was observed after 24 h and remained constant until 48 h. TABLE 3 www.frontiersin.org Table 3. Repellent activity of AC extract on 1st stage T. infestans nymphs. TABLE 4 www.frontiersin.org Table 4. Repellent activity of AC extract on 5th stage T. infestans nymphs. For the 5th stage repellent activity was lower compared to 1st stage. Again, only 1:1 dilution was effective and its activity started at 12 h after initiation of the experiment. This dilution reached 100% of repellence at 24 h and remained constant until 48 h. LD50 of AC Extract Table 5 shows the influence of nutritional state of nymphs on the lethal activity of AC extract. Fed to repletion nymphs were more sensitive to the lethal activity of the extract when compared to fasted nymphs. Both RLD50 were close to 2, this means that twice the dose was needed for fasted nymphs compared with fed to repletion nymphs. TABLE 5 www.frontiersin.org Table 5. Relation between nymph nutritional state and lethal activity of AC extract. Discussion Under our working conditions we found that AC extract showed efficacy in susceptible to pyrethroid nymphs regarding repellent and lethal activities, such situation was influenced by the feeding state of insects. A possible explanation of the higher lethal efficacy of AC extract in T. infestans nymphs fed to repletion could be associated to the ability of some insects to modify the mechanical properties of cuticle. This process, known as plasticization (41), involves modifications in the aqueous phase of cuticle due to changes in pH, leading to rupture of soft bonds among proteins and chitin microfibers. These reversible modifications allow procuticle to have a better elongation capacity. Plasticization has been largely studied in Rhodnius proxilus (42, 43), researchers found this process to be important during ecdysis and feeding, particularly in 5th stage nymphs when plasticization allows triatomines to considerably increase their original size. Moreover, in 5th stage nymphs of T. infestans it has been demonstrated that a feeding time as short as 1 min using an artificial feeding system is enough to start plasticization. During this process epicuticle folds are expanded and procuticle is more flexible, thus enhancing the penetration of different molecules from outside, such as pesticides (44). From our results it can be stated that in nymphs fed to repletion plasticization allowed an increased penetration of the active compounds present in AC extract resulting in a higher toxic response (LD50 fed to repletion insects < LD50 fasted insects). In 2nd stage T. infestans submitted to 14C-DDT, Fontán and Zerba (45) reported an increased penetration rate of the organochlorine in fed to repletion vs. fasted insects; this result is similar to the topication assay we performed with AC extract. Regarding repellent activity our results were similar to those of Valladares et al. (36) although our extract was acetonic, compared to the ethanolic extract of the researchers. They also determined that the ethanolic extract did not affect the survival of triatomines when they were submitted to papers impregnated with extracts. The latter could be a possible explanation to the differences with our results, because in the case of topication each insect receives a determined volume (dose) while with the contact method the amount of extract on insects depends on the locomotive activity of each individual. Besides, there are some similarities and differences in the chemical composition of extracts. The ethanolic extract from Valladares et al. (36) had limonoids, a group of insecticidal triterpenes. In AC extract, although we did not determine the chemical identity of triterpenes, they were abundant. As a difference, the ethanolic extract did not have alkaloids, compounds that were present in AC extract and are probably responsible for the lethal activity, as these secondary metabolites are used as defense mechanism against insects and herbivores (46). Such compounds, acting as protective agents for plants, are known as allelochemics (47). Acetone is the recommended solvent for experimental use in T. infestans according to the World Health Organization (38). We found that repellent activity of AC extract was slightly greater in 1st stage compared to 5th stage nymphs, this could be related to anatomical and physiological differences between both stages, such as penetration rate of substances through cuticle, presence of sensory organs specific to each stage and augmentation of metabolic activity (48). Repellent activity of ME extract was considerably low when compared to AC extract, this could be due to the higher concentration of some compounds in AC extract such as triterpenes, as previously demonstrated for similar compounds by other researchers (49, 50). Although health campaigns have been implemented in developing countries the infected human population in Latin America is still high and there is concern about international immigration in countries where the disease is non-endemic. Synthetic insecticides are useful tools for the control of pests, but their excessive use has led to negative consequences such as toxicity against farmers, consumers and both wild and domestic animals as well as interruption of natural control and pollination, water pollution and development of resistance (50–53). Moreover, some populations of T. infestans have developed resistance to these pesticides (52, 54) Melia azedarach is present in many countries of Latin America where it is usually used in folk medicine by means of maceration of fruits and leaves to prepare extracts due to their repellent and insecticide properties against many crop pests and human disease vectors. Such conditions together with our findings could justify the use of plant preparations as an accessible complement together with the traditional use of pesticides for the control of T. infestans with probable synergism or potentiation of actions between molecules in susceptible nymphs. Next step in our research will be the assay of MA extracts on T. infestans that are resistant to pyrethroids for a possible synergism between AC extract and the pesticides. Such situation, if successful, may allow to use less concentrations of synthetic insecticides during aspersion, which in turn may cause less impact on environment as well as human population. Part of this work has already started. Author Contributions MD, PZ, and NM conceived and designed the experiments. PZ performed the Melia azedarach Extracts. FB Managed and maintained the triatomines. All authors contributed to the redaction, revision and approved the final manuscript. Conflict of Interest Statement The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest. Acknowledgments The authors thank to the Centro de Referencia de Vectores (CeReVe), Santa María de Punilla, Córdoba, Argentina, for providing the first triatomines to perform our colony. This work was financed by the Laboratory of Pharmacological and Toxicological Studies –LEFyT-, UNLP. References 1. Bern C, Kjos S, Yabsley MJ, Montgomery SP. Trypanosoma cruzi and Chagas' disease in the United States. Clin Microbiol Rev. (2011) 24:655–81. doi: 10.1128/CMR.00005-11 PubMed Abstract | CrossRef Full Text | Google Scholar 2. Gürtler RE, Kitron U, Cecere MC, Segura EL, Cohen JE. Sustainable vector control and management of Chagas disease in the Gran Chaco, Argentina. Proc Natl Acad Sci USA. (2007) 104:16194–99. doi: 10.1073/pnas.0700863104 PubMed Abstract | CrossRef Full Text | Google Scholar 3. World Health Organization (WHO). Chagas Disease (American Trypanosomiasis). Fact Sheet N°340 (2010). Available online at: http://www.who.int/mediacentre/factsheets/fs340/ 4. Carlier Y, Pinto DJC, Luquetti AO, Hontebeyrie M, Torrico F, Truyens C. Trypanosomiase americaine ou maladie de Chagas. Editions Scientifiques et Medicales. Paris: Elsevier SAS (2002). 505 p. 5. Zulantay I, Corral C, Guzman MC, Aldunate F, Guerra W, Cruz I et al. The investigation of congenital infection by Trypanozoma cruzi in an endemic area of Chile: three protocols explored in a pilot project. Ann Trop Med Parasitol. (2011) 105:123–8. doi: 10.1179/136485911X12899838413583 PubMed Abstract | CrossRef Full Text | Google Scholar 6. Howard EJ, Xiong X, Carlier Y, Sosa-Estani S, Buekens P. Frequency of the congenital transmission of Trypanosoma cruzi: a systematic review and meta-analysis. BJOG (2013) 121:22–33. doi: 10.1111/1471-0528.12396 PubMed Abstract | CrossRef Full Text | Google Scholar 7. Angheben A, Boix L, Buonfrate D, Gobbi F, Bisoffi Z, Pupella S et al. Chagas disease and transfusion medicine: a perspective from non-endemic countries. Blood Transfus. (2015) 13:540–50. doi: 10.2450/2015.0040-15 PubMed Abstract | CrossRef Full Text | Google Scholar 8. Blumental S, Lambermont M, Heijmans C, Rodenbach MP, El Kenz H, Sondag D et al. First documented transmission of Trypanosoma cruzi infection through blood transfusion in a child with Sickle-Cell disease in Belgium. PLoS Negl Trop Dis. (2015) 9:e0003986. doi: 10.1371/journal.pntd.0003986 PubMed Abstract | CrossRef Full Text | Google Scholar 9. Huprikar S, Bosserman E, Patel G, Moore A, Pinney S, Anyanwu A et al. Donor-Derived Trypanosoma cruzi Infection in Solid Organ Recipients in the United States, 2001-2011. Am J Transplant. (2013) XX:1–8. doi: 10.1111/ajt.12340 CrossRef Full Text | Google Scholar 10. Kun H, Moore A, Mascola L, Steurer F, Lawrence G, Kubak B et al. Transmission of Trypanosoma cruzi by heart transplantation. Clin Infect Dis. (2009) 48:1534–40. doi: 10.1086/598931 PubMed Abstract | CrossRef Full Text | Google Scholar 11. Muñoz Casas del Valle P. Tratamiento y seguimiento de la enfermedad de Chagas en pacientes inmunocomprometidos. Rev Chilena Infectol. (2017) 34:67–8. doi: 10.4067/S0716-10182017000100010 CrossRef Full Text | Google Scholar 12. Yoshioka K. Impact of a community-based bug-hunting campaign on Chagas disease control: a case study in the department of Jalapa, Guatemala. Mem Inst Oswaldo Cruz. (2013) 108:205–11. doi: 10.1590/0074-0276108022013013 PubMed Abstract | CrossRef Full Text | Google Scholar 13. Zerba EN. Past and present of Chagas vector control and future needs: position paper In: WHO Pesticide Evaluation Shceme & Global Collaboration for Development of Pesticides for Public Health Geneva: World Health Organization (1999). Google Scholar 14. World Health Organization (WHO). Expert Committee on vector biology and control. Vector Resistance to pesticides: fifteenth report of the Expert committee on vector Biology and Control. WHO Organ. Tech. Rep. Ser. (1992) 818:1–62. 15. Lardeux F, Depickère S, Duchon S, Chavez T. Insecticide resistance of Triatoma infestans (Hemiptera, Reduviidae) vector of Chagas disease in Bolivia. Trop Med Int Health. (2010) 15:1037–48. doi: 10.1111/j.1365-3156.2010.02573.x PubMed Abstract | CrossRef Full Text | Google Scholar 16. González Audino P, Vassena C, Barrios S, Zerba E, Picollo MI. Role of enhaced detoxification in a deltamethrin-resistant population of Triatoma infestans (Hemiptera, Reduviidae) from Argentina. Mem Inst Oswaldo Cruz. (2004) 99:335–9. doi: 10.1590/S0074-02762004000300018 CrossRef Full Text | Google Scholar 17. Thacker JRM. An Introduction to Arthropods Pest Control. Cambridge: Cambridge University Press (2002). Google Scholar 18. Rodríguez H. Determinación de toxicidad y bioactividad de cuatro insecticidas orgánicos recomendados para el control de plagas en cultivos hortícolas. Rev Latin Agric Nutr. (1998) 1:32–41. 19. Isman MB, Machial CM. Pesticides based on plant essential oils: from traditional practice to commercialization. In: Rai and Carpinella Editors, Naturally Ocurring Bioactive Compounds. Elsevier B.V. (2006). p. 29–44. Google Scholar 20. Phua DH, Tsai WJ, Ger J, Deng JF, Yang CC. Human Melia azedarach poisoning. Clin Toxicol. (2008) 46:1067–70. doi: 10.1080/15563650802310929 PubMed Abstract | CrossRef Full Text | Google Scholar 21. Botha CJ, Penrith ML. Potential plant poisoning in dogs and cat in Southern Africa. J S Afr Vet Ass. (2009) 80:63–74. Google Scholar 22. Han J, Lin WH, Xu RS, Wang WL, Zhao SH. Studies on the chemical constituents of Melia azedarach Linn. Yao XueXue Bao (1991) 26:426–29. Google Scholar 23. Sen A, Batra A. Evaluation of antimicrobial activity of different solvent extracts of medicinal plant: Melia azedarach. Int J Curr Pharm R (2012) 4:67–73. Google Scholar 24. Szewczuk VD, Mongelli ER, Pomilio AB. Antiparasitic activity of Melia azedarach growing in Argentina. Mol Med Chem. (2003) 1:54–7. Google Scholar 25. Carpinella C, Defagó T, Valladares G, Palacios M. Antifeedant and insecticide properties of a limonoid from Melia azedarach (Meliaceae) with potential use for pest management. J Agric Food Chem (2003) 51:369–74. doi: 10.1021/jf025811w PubMed Abstract | CrossRef Full Text | Google Scholar 26. Alche LE, Assad FK, Meo M, Coto CE, Maier MS. An antiviral meliacarpin from leaves of Melia azedarach. Naturforsch. (2003) 58:215–19. PubMed Abstract | Google Scholar 27. Marimuthu S, Balakrishnan P, Nair S. Phytochemial investigation and radical scavenging activities of Melia azedarach and its DNA protective effect in cultured lymphocytes. Pharm Biol. (2013) 51:1331–40. doi: 10.3109/13880209.2013.791323 PubMed Abstract | CrossRef Full Text | Google Scholar 28. Fazzio LE, Costa EF, Streitenberger N, Pintos ME, Quiroga MA. Intoxicación accidental por paraíso (Melia azedarach) en bovinos. Rev Vet. (2015) 26:54–8. 29. Méndez MC, Elias F, Riet-Correa F, Gimeno EJ, Portiansky EL. (2006). Intoxicaçao experimental com frutos de Melia azedarach (Meliaceae) em suínos. Pesq Vet Bras. 26, 26–30. doi: 10.1590/S0100-736X2006000100006 CrossRef Full Text | Google Scholar 30. Ferreiro D, Orozco JP, Mirón C, Real T, Hernández-Moreno D, Soler F et al. Chinaberry tree (Melia azedarach) poisoning in dog: a case report. Top Companion Anim Med. (2010) 25:64–7. doi: 10.1053/j.tcam.2009.07.001 PubMed Abstract | CrossRef Full Text | Google Scholar 31. Vergara R, Escobar C, Galeno P. (1997). Potencial insecticida de extractos de Melia azedarach L. (Meliaceae). Actividad biológica y efectos. Rev Facultad Nacional de Agronomía (Colombia) 50:186. 32. Mazzonetto F, Vendramim J. Effect of powders from vegetal species on Acanthoscelides obtectus (Say) (Coleoptera: Bruchidae) in stored bean. Neotrop Entomol. (2003) 32:145–9. doi: 10.1590/S1519-566X2003000100022 CrossRef Full Text | Google Scholar 33. Pérez-Pacheco R, Rodríguez C, Lara-Reyna J, Montes R, Ramírez G. Toxicidad de aceites, esencias y extractos vegetales en larvas del mosquito Culex quinquefasciatus (Say.) (Diptera: Culicidae). Acta Zool. Mex. Nueva Serie (2004) 20:141–52. 34. Parra Henao GJ, García Pajón CM, Cotes Torres JM. Actividad insecticida de extractos vegetales sobre Aedes aegypti (Diptera: Culicidae) vector del Dengue en Colombia. Ces Medicina (2007) 21:47–54. Google Scholar 35. Rossetti MR, Defagó MT, Carpinella MC, Palacios SM, Valladares C. (2008). Actividad biológica de extractos de Melia azedarach sobre larvas de Spodoptera eridania (Lepidoptera: Noctuidae). Rev Soc Entomol Argent. 67:115–25. Google Scholar 36. Valladares GR, Ferreyra D, Defago MT, Carpinella MC, Palacios S. Effects of Melia azedarach on Triatoma infestans. Fitoterapia (1999) 70:421–4. Google Scholar 37. Bruneton J. Farmacognosia, 2nd Edn. Zaragoza: Editorial Acribia (2001). p. 1099. 38. Harborne JB. Phytochemical Methods, 3rd Edn. London: Chapman and Hall (1998). 39. Sendi JJ, Ebadollahi A. Biological Activities of Essential Oils on Insects. In: Govil JN, Bhattacharya S, Editors, Recent Progress in Medicinal Plants (RPMP): Essential Oils, 2nd Edn., Vol. 37. Houston, TX: Studium Press LLC. (2013). Google Scholar 40. World Health Organization (WHO). Protocolo de evaluación de efecto insecticida sobre triatominos. Acta Toxicol Argent (1994) 2:29–32. 41. Abbott WS. A method of computing the effectiveness of an insecticide. J Econ Entomol. (1925) 18:265–7. doi: 10.1093/jee/18.2.265a CrossRef Full Text | Google Scholar 42. Robertson JL, Russell RM, Preisler HK, Savin NE. Bioassays With Arthropods, 2nd Edn. CRC Press (2007). Google Scholar 43. Reynolds SE. A post-ecdisial plasticization of the abdominal cuticle in Rhodnius. J. Insect Physiol. (1974) 20:1957–62. PubMed Abstract | Google Scholar 44. Núñez J. Central nervous control of the mechanical properties of the cuticle in Rhodnius prolixus. Nature (1963) 199:621–2. Google Scholar 45. Reynolds S. The mechanism of plasticization of the abdominal cuticle in Rhodnius. J Exp Biol. (1975) 62:81–98. PubMed Abstract | Google Scholar 46. Melcón ML. Dinámica de la Extensibilidad Cuticular en el Contexto de la Alimentación de la Vinchuca Triatoma infestans (Heteroptera: Reduviidae). Master's Degree Thesis (2004). doi: 10.13140/RG.2.1.1783.9847 CrossRef Full Text 47. Fontán A, Zerba EN. Influence of the nutritional state of Triatoma infestans over the insecticidal activity of DDT. Comp Biochem Physiol C. (1992) 101:589–91. PubMed Abstract | Google Scholar 48. Hartmann T, Ober D. Defense by pyrrolizidine alkaloids: developed by plants and recruited by insects. In: Schaller A. editor. Induced Plant Resistance to Herbivory. (Dordrecht: Springer), 213–31. 49. Boppré M. Insects pharmacophagously utilizing defensive plant chemicals (Pyrrolizidine alkaloids). Naturwissenschaften (1986) 73:17–26. doi: 10.1007/BF01168801 CrossRef Full Text | Google Scholar 50. Khan A, Islam Md S, Rahman M, Zaman T, Ekramul Haque Md. Pesticidal and pest repellency activities of a plant derived triterpenoid 2α,3β,21β,23,28-penta hydroxyl 12-oleanene against Tribolium castaneum. Biol Res. (2014) 47:68. doi: 10.1186/0717-6287-47-68 PubMed Abstract | CrossRef Full Text | Google Scholar 51. Busvine JR. A Critical Review of the Techniques for Testing Insecticides, 2nd Edn. London: Commonwealth Agricultural Bureaux (1971). Google Scholar 52. Perry AS, Yamamoto I, Ishaaya I, Perry RY. Insecticides in Agriculture and Environment: Retrospects and Prospects. Berlin: Springer-Verlag (1998). Google Scholar 53. Akhtar Y, Isman MB. Comparative growth, inhibitory and antifeedant effects of plant extracts and pure allelochemicals on four phytophagous insect species. J. Appl. Ent. (2004) 128:32–8. doi: 10.1007/s11101-006-9048-7 CrossRef Full Text | Google Scholar 54. Mougabure-Cueto G, Picollo MI. Insecticide resistance in vector Chagas disease: evolution, mechanisms and management. Acta Trop. (2015) 149:70–85. doi: 10.1016/j.actatropica.2015.05.014 PubMed Abstract | CrossRef Full Text | Google Scholar Keywords: Melia azedarach, extracts, Triatoma infestans, repellent activities, lethal activities Citation: Dadé M, Zeinsteger P, Bozzolo F and Mestorino N (2018) Repellent and Lethal Activities of Extracts From Fruits of Chinaberry (Melia azedarach L., Meliaceae) Against Triatoma infestans. Front. Vet. Sci. 5:158. doi: 10.3389/fvets.2018.00158 Received: 16 April 2018; Accepted: 22 June 2018; Published: 26 July 2018. Edited by: Ramesh Chandra Gupta, Murray State University, United States Reviewed by: Oguzhan Yavuz, Ondokuz Mayis University, Turkey Francisco Soler Rodríguez, Universidad de Extremadura, Spain Copyright © 2018 Dadé, Zeinsteger, Bozzolo and Mestorino. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms. *Correspondence: Nora Mestorino, noram@fcv.unlp.edu.ar