Determinação de carbaril utilizando testes ELISA (Enzyme-linked immunosorbent assay) e CLAE com detecção por arranjo de diodos

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Sintese e caracterização do compósito TixOy- MWCNT para fotodegradação de carbaril

In this study, a composite of titanium oxide (TixOy) and carbon nanotubes multi-walled (MWCNT) was synthesized on a titanium substrate using the sol-gel method. The electrode obtained (TixOy-MWCNT/Ti) was used to the photodegradation of Carbaryl. The morphology and structure of the TixOy-MWCNT composite were characterized by scanning electron microscopy (SEM), scanning electron microscopy by field emission (FEG-SEM) and X-ray diffraction (XRD). The electrode was evaluated for degradation of Carbaryl (0.9 mmol L-1) in phosphate buffer pH 6, and using chronoamperometry by applying a potential of +1,5 V for 1 h. Using the Ultraviolet-Visible test, the absorbance at 220 nm was collected every 15 min to calculate the percentage of Cabaryl´s degradation. Can be evaluated that the Carbaryl degradation using the TixOy-MWCNT/Ti electrode was 22% more efficient when compared with the electrode without the presence of titanium oxides (MWCNT / Ti)

Influência da temperatura nas respostas aos biocidas diazinon e carbaril em Dilocarcinus pagei Stimpson, 1861

Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

Biodegradación de Carbufuran y Carbaril por Sphingomonas sp., S8-M3-13

p.45-52

Ocorrência e controle da vaquinha em seringais em formação.

O controle da vaquinha é difícil por ser um inseto que se alimenta de muitas plantas e apresenta grande mobilidade. No entanto, a aplicação de produtos a base de Tricloform ou Carbaril, principalmente nos foliolos jovens, diminui os prejuízos causados pelo ataque da praga.

Combined effects of chemical and natural stressors to soil organisms and plants

Nas últimas décadas, a Terra tem experimentado um aquecimento global e mudanças nos padrões de precipitação. Muitos estudos sobre a avaliação de risco de agrotóxicos em organismos não-alvo foram realizados com base em protocolos padronizados, com condições abióticas controladas. Mas, em campo, os organismos são expostos a flutuações de vários fatores ambientais, bem como a poluentes, que podem alterar os limites de tolerância dos organismos aos stressores naturais, bem como alterar a toxicidade ou biodisponibilidade do químico em causa. Considerando isso, o principal objetivo deste trabalho foi o de avaliar de que modo e em que medida os fatores ambientais (temperatura, humidade do solo e radiação UV) podem interagir uns com os outros ou afetar a toxicidade do carbaril para invertebrados do solo e plantas. Para isso, foram utilizadas quatro espécies padrão: Folsomia candida, Eisenia andrei, Triticum aestivum e Brassica rapa, e simulados diferentes cenários climáticos, com vários parâmetros letais e subletais analisados. A exposição combinada foi analisada utilizando, quando possível, a ferramenta MIXTOX, com base no modelo de referência de acção independente (IA) e possíveis desvios, assim como rácios sinergísticos/antagonísticos (a partir de valores de EC50/LC50), quando a dose-resposta de um dos stressores não foi obtida. Todos os fatores de stress aplicados isoladamente causaram efeitos significativos sobre as espécies testadas e sua exposição combinada com carbaril, apresentaram respostas diferenciadas: para as minhocas, a seca e temperaturas elevadas aumentaram os efeitos deletérios do carbaril (sinergismo), enquanto o alagamento e temperaturas baixas diminuíram sua toxicidade (antagonismo). Para os colêmbolos, o modelo IA mostrou ser uma boa ferramenta para prever a toxicidade do carbaril tanto para temperaturas altas como para as baixas. Para as duas espécies de plantas foram encontradas diferenças significativas entre elas: em termos gerais, as interações entre carbaril e os stressores naturais foram observadas, com sinergismo aparecendo como o padrão principal relacionado com a radiação UV, solos secos e temperaturas elevadas, enquanto o padrão principal relacionado com temperaturas baixas e stress de alagamento foi o antagonismo. Quando os efeitos de dois stressores naturais (radiação UV e humidade do solo) em plantas foram avaliados, uma interação significativa foi encontrada: a seca aliviou o efeito deletério da radiação UV em T. aestivum e o alagamento aumentou os seus efeitos, mas para B. rapa a adição de ambos os stresses de água causou um aumento (sinergismo) dos efeitos deletérios da radiação UV para todos os parâmetros avaliados. Portanto é necessário que as diferenças sazonais e latitudinais, bem como as mudanças climáticas globais, sejam integradas na avaliação de risco de contaminantes do solo.

Effects of environmental factors on the toxicity of pesticides to zebrafish embryos

During the last century mean global temperatures have been increasing. According to the predictions, the temperature change is expected to exceed 1.5ºC in this century and the warming is likely to continue. Freshwater ecosystems are among the most sensitive mainly due to changes in the hydrologic cycle and consequently changes in several physico-chemical parameters (e.g. pH, dissolved oxygen). Alterations in environmental parameters of freshwater systems are likely to affect distribution, morphology, physiology and richness of a wide range of species leading to important changes in ecosystem biodiversity and function. Moreover, they can also work as co-stressors in environments where organisms have already to cope with chemical contamination (such as pesticides), increasing the environmental risk due to potential interactions. Therefore, the objective of this work was to evaluate the effects of climate change related environmental parameters on the toxicity of pesticides to zebrafish embryos. The following environmental factors were studied: pH (3.0-12.0), dissolved oxygen level (0-8 mg/L) and UV radiation (0-500 mW/m2). The pesticides studied were the carbamate insecticide carbaryl and the benzimidazole fungicide carbendazim. Stressors were firstly tested separately in order to derive concentration- or intensity-response curves to further study the effects of binary combinations (environmental factors x pesticides) by applying mixture models. Characterization of zebrafish embryos response to environmental stress revealed that pH effects were fully established after 24 h of exposure and survival was only affected at pH values below 5 and above 10. Low oxygen levels also affected embryos development at concentrations below 4 mg/L (delay, heart rate decrease and edema), and at concentrations below 0.5 mg/L the survival was drastically reduced. Continuous exposure to UV radiation showed a strong time-dependent impact on embryos survival leading to 100% of mortality after 72 hours of exposure. The toxicity of pesticides carbaryl and carbendazim was characterized at several levels of biological organization including developmental, biochemical and behavioural allowing a mechanistic understanding of the effects and highlighting the usefulness of behavioural responses (locomotion) as a sensitive endpoint in ecotoxicology. Once the individual concentration response relationship of each stressor was established, a combined toxicity study was conducted to evaluate the effects of pH on the toxicity of carbaryl. We have shown that pH can modify the toxicity of the pesticide carbaryl. The conceptual model concentration addition allowed a precise prediction of the toxicity of the jointeffects of acid pH and carbaryl. Nevertheless, for alkaline condition both concepts failed in predicting the effects. Deviations to the model were however easy to explain as high pH values favour the hydrolysis of carbaryl with the consequent formation of the more toxic degradation product 1- naphtol. Although in the present study such explanatory process was easy to establish, for many other combinations the “interactive” nature is not so evident. In the context of the climate change few scenarios predict such increase in the pH of aquatic systems, however this was a first approach focused in the lethal effects only. In a second tier assessment effects at sublethal level would be sought and it is expectable that more subtle pH changes (more realistic in terms of climate changes scenarios) may have an effect at physiological and biochemical levels with possible long term consequences for the population fitness.

Estudo de variações bioquímicas e morfológicas induzidas por peticidas orgnofosforado e carbamato em tilápia (oreochromis niloticus) e cascudo (Pterygoplichthys anisitsi), como biomarcadores de contamincação ambiental

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Análise da variabilidade genética e do padrão de atividade esterásica no hepatopâncreas de camarões palemonídeos expostos a diferentes pesticidas

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Mortalidade de Neoseiulus californicus (Acari: Phytoseiidae) em testes de toxicidade residual e dinâmica populacional de ácaros (Acari) em pomares de macieira com diferentes manejos fitossanitários na Argentina

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Toxicidade de inseticidas para abelhas Apis mellifera L

Pós-graduação em Zootecnia - FMVZ

Bases moleculares de la resistencia a insecticidas en la mosca mediterránea de la fruta Ceratitis Capitata (Wiedemann)

La mosca mediterránea de la fruta Ceratitis capitata (Wiedemann, 1824) está considerada una de las plagas clave para la fruticultura. El malatión es un insecticida organofosforado que fue empleado mayoritariamente en España para el control de C. capitata hasta 2009, año en el que dejó de utilizarse por no estar incluido en el anexo I de la Directiva Europea 91/414/ECC. El incremento del uso del malatión, debido a las graves pérdidas económicas causadas por C. capitata, provocó la aparición de poblaciones de campo resistentes. El estudio de una población resistente a malatión, recogida en Castelló en 2004, permitió la identificación de dos mecanismos de resistencia: una mutación puntual (G328A) en la acetilcolinesterasa (AChE) y un mecanismo de resistencia metabólica, probablemente mediado por carboxilesterasas. Teniendo en cuenta estos antecedentes, nos propusimos estudiar los mecanismos implicados en la resistencia a malatión en C. capitata. Además, durante el desarrollo de esta Tesis, el malatión fue sustituido por otros insecticidas como el espinosad y la lambda-cialotrina para el control de la plaga. En este nuevo contexto, es extremadamente importante analizar la susceptibilidad de poblaciones de campo frente a espinosad y estudiar la posible existencia de resistencia cruzada a estos insecticidas, así como sentar las bases para el estudio de futuros mecanismos de resistencia. En primer lugar, analizamos mediante bioensayos con dosis discriminante la susceptibilidad a malatión y espinosad en doce poblaciones de C. capitata de Andalucía, Aragón, Cataluña, Comunidad Valenciana e Islas Baleares; y nuestros resultados sugirieron la presencia de individuos resistentes a malatión en la mayoría de las poblaciones analizadas. En el caso del espinosad, observamos que la susceptibilidad a este insecticida de origen biológico fue elevada en la mayoría de las poblaciones, sin embargo, la población recogida en Xàbia (Alicante) mostró un nivel de susceptibilidad unas dos veces menor al resto de poblaciones. Mediante la selección en laboratorio, obtuvimos dos líneas resistentes a malatión, W-4Km y W-10Km, con unos niveles de resistencia con respeto a la línea susceptible C de 178 y 400 veces, respectivamente. Además, se seleccionó por primera vez en C. capitata una línea altamente resistente a espinosad (Xàbia-W-100s), que actualmente es unas 500 veces más resistente que la línea de laboratorio C. Con el objetivo de escoger la estrategia más adecuada para el manejo de la plaga, estudiamos la susceptibilidad a diferentes tipos de insecticidas en la línea resistente a malatión W- 4Km. En esta línea detectamos resistencia cruzada moderada a los organofosforados fentión, diazinón, fosmet, triclorfón y metil-clorpirifos (de 7 a 16 veces) y frente al carbamato carbaril, al piretroide lambda-cialotrina y al quimioesterilizante lufenurón (de 4 a 6 veces). Por otra parte, la resistencia cruzada frente a espinosad fue baja (1,5 veces). Es importante destacar que los niveles de resistencia estimados frente a todos los insecticidas fueron de uno o dos órdenes de magnitud inferiores al observado en la línea W-4Km frente a malatión (178 veces), hecho que podría deberse, al menos, a dos posibles hipótesis: que la mutación AChE G328A confiera mayor insensibilidad al malaoxón (forma activa del malatión) que a otros insecticidas que tienen como diana la AChE y/o, en segundo lugar, que el mecanismo de resistencia mediado por carboxilesterasas hidrolice el malatión de manera más eficiente que los otros insecticidas analizados. En el estudio de nuevos mecanismos de resistencia en C. capitata, por un lado, analizamos la diversidad de enzimas citocromo P450, asociadas con resistencia metabólica en otras especies, y por otro lado, desarrollamos un sistema para la detección de nuevas mutaciones puntuales que pudiesen aparecer en los genes que codifican la AChE (Ccace2) y la aliesterasa (Ccae7). Mediante el empleo de cebadores degenerados obtuvimos 37 genes CYP, que codifican enzimas P450, pertenecientes a cinco familias. Posteriormente, en un estudio de inducción con fenobarbital, observamos que la expresión de cuatro de los seis genes analizados era susceptible de ser inducida. Por otro lado, se puso a punto un sistema que permite amplificar y secuenciar, a partir de DNA genómico, los exones de los genes Ccace2 y Ccae7 en los que se han encontrado mutaciones relacionadas con resistencia a insecticidas en otras especies. Los resultados obtenidos facilitarán el estudio de nuevos mecanismos de resistencia mediados por estas enzimas en C. capitata. Se diseñó un método PCR-RFLP para identificar los individuos portadores de la mutación AChE G328A (alelo de resistencia Ccace2R) sin la necesidad de realizar bioensayos y que, además, permite detectar resistencia cuando ésta se encuentra a baja frecuencia. Según el análisis realizado, el alelo Ccace2R se observó en 25 de las 27 localidades españolas muestreadas en el territorio español, incluyendo las Islas Baleares y Canarias. Sin embargo, este alelo no se detectó en poblaciones procedentes de once países y de cinco continentes. El análisis de la presencia del alelo Ccace2R en las líneas resistentes a malatión durante el proceso de selección en el laboratorio mostró una rápida disminución de los homocigotos, tanto para el alelo susceptible como para el alelo de resistencia, en favor de los individuos heterocigotos. Así, después de 52 generaciones de selección, se observó que la totalidad de los individuos analizados de la línea W-10Km presentaban un genotipo heterocigoto para la mutación AChE G328A. Este desequilibrio contradice la segregación mendeliana esperada para un gen con dos alelos pero podría ser explicado por la existencia de una duplicación del gen Ccace2. La demostración de la presencia de esta duplicación se realizó mediante: i) el cruzamiento de individuos heterocigotos de la línea W-10Km con homocigotos susceptibles de la línea C, que dio lugar a una descendencia en la que el 100% de los individuos eran heterocigotos; ii) la evaluación del número de copias del gen Ccace2 por PCR cuantitativa en tiempo real (qPCR), que resultó dos veces mayor en individuos de la línea W-10Km en comparación con los de la línea C; iii) el análisis del nivel de expresión de Ccace2, que fue el doble en la línea W-10Km con respecto a la línea C, y iv) el estudio de la actividad AChE, que resultó mayor en los individuos de la línea W-10Km. Según los resultados obtenidos, una duplicación del gen Ccace2 provoca la coexistencia en un mismo cromosoma del alelo silvestre y del alelo mutado y, además, las dos copias del gen Ccace2, al estar ligadas, producen una heterocigosis permanente (Ccace2RS). De esta manera se explica que el hecho de que 100% de los individuos de la línea W-10Km mostrasen un perfil de restricción correspondiente a un individuo heterocigoto ya que, en realidad, eran homocigotos estructurales para la duplicación (genotipo CCace2RS/RS). Se ha detectado un coste biológico asociado a la duplicación que consiste en un incremento en la mortalidad acumulada de los adultos a partir del séptimo día después de la emergencia. La descripción de la duplicación Ccace2RS supone la identificación de un nuevo mecanismo de resistencia a malatión en C. capitata. Finalmente, mediante el diseño de un método de doble PCR-RFLP se determinó la presencia de la duplicación Ccace2RS en la mayoría de las poblaciones españolas. La proporción de individuos portadores de la duplicación osciló entre el 5% y el 35%, observándose los mayores valores de frecuencia en las poblaciones de C. capitata recogidas en la cuenca mediterránea. Podemos por lo tanto concluir que la resistencia a malatión asociada a la mutación AChE G328A y a la duplicación Ccace2RS está ampliamente establecida en las poblaciones españolas de C. capitata. Nuestros resultados desaconsejan la utilización del malatión (si fuera de nuevo autorizado) o de otros organofosforados para el control de esta plaga. Además, una de las líneas resistentes a malatión mostró resistencia cruzada frente a insecticidas con diferentes modos de acción y que se utilizan actualmente para el control de C. capitata, tales como lambda-cialotrina y lufenurón. La alta susceptibilidad a espinosad observada en las poblaciones españolas, así como la reducida resistencia cruzada estimada para este insecticida, sugieren que su utilización es adecuada para el control de la plaga. Sin embargo, la utilización de un sólo insecticida puede entrañar riesgos por favorecer la selección de resistencia, de hecho, mediante selección en laboratorio se obtuvo una población altamente resistente a espinosad. Por tanto, es recomendable implementar programas de control integrado y de manejo de la resistencia en C. capitata utilizando distintos sistemas de control e insecticidas con diferentes mecanismos de acción que permitan su sostenibilidad en el tiempo. Los sistemas de detección de alelos de resistencia desarrollados en este trabajo permitirán la detección precoz de resistencia en campo, facilitando la decisión sobre el sistema de control más adecuado. Además, los conocimientos generados podrán contribuir al desarrollo de nuevos sistemas de detección para otros mecanismos de resistencia. Abstract. The Mediterranean fruit fly, Ceratitis capitata (Wiedemann, 1824), is considered one of the most harmful pests in fruit crops. Until 2009, when malathion use was banned due to its not inclusion in the Annex I of Directive 91/414/EEC, the application of this organophosphate (OP) insecticide in Spain increased gradually due to the large economic losses caused by C. capitata. The increase in the frequency of treatments resulted in the development of resistant field populations. The study of a malathion-resistant population, collected in 2004 in Castelló (Comunidad Valenciana), allowed the identification of two resistance mechanisms: a single point mutation (G328A) in the target acetylcholinesterase (AChE), as well as a metabolic resistance mechanism, most likely carboxylesterase-mediated. Taking all the preceding into account, we studied the malathion resistance mechanisms in C. capitata. During the development of this PhD Thesis malathion use was banned by the European Union, being replaced by other insecticides, such as spinosad and lambda-cyhalotrin. Within this new working frame, the need to analyse the possible existence of cross-resistance to these insecticides and the susceptibility to spinosad in field populations was raised. This would define the baseline for future studies on resistance mechanisms. Firstly, through discriminant dose bioassays, we analysed malathion and spinosad susceptibility in twelve C. capitata populations from Andalucia, Aragon, Cataluña, C. Valenciana and the Baleares Islands. Our results suggest the presence of malathion-resistant individuals in most of the populations analysed. Regarding spinosad, we noticed a high susceptibility to this biologically derived insecticide in most of the populations, but in the one collected in Xabia (Alicante), which had a susceptibility level two times lower than the rest of populations. Through laboratory selection, we obtained two malathion-resistant strains, W-4Km and W-10Km, with resistance levels 178- and 400-fold, respectively, compared to the control susceptible C strain. Besides, a strain highly-resistant to spinosad (Xabia-W-100s), 500-times more resistant than control C strain, was selected. In order to decide the most appropriate management strategy for the pest, we studied the susceptibility to different insecticides in the malathion-resistant W-4Km strain. We detected a moderated cross-resistance to the OPs fenthion, diazinon, phosmet, trichlorphon and methylchlorpyrifos (7- to 16-fold), and to the carbamate carbaryl, the pyretroid lambda-cyhalotrin and the chemosterilizer lufenuron (4- to 6-fold). On the other hand, cross-resistance to spinosad was low (1.5-fold). It is important to note that resistance levels to all insecticides were one or two orders of magnitude less than that observed against malathion in W-4Km strain (178-fold), a fact that might be due to, at least, two possible causes: mutation AChE G328A may provide a higher insensitivity to malaoxon (the active form of malathion) than to other insecticides having AChE as target, and/or, secondly, the carboxylesterase-mediated resistance mechanism hydrolyzes malathion more efficiently than all other analysed insecticides. To investigate new resistance mechanisms in C. capitata we analysed the diversity of the cytochrome P450 enzymes, which have been associated to metabolic resistance in insects, and we developed a new method to detect single point mutations in acetylcholinesterase (Ccace2) and aliesterase (Ccae7) genes that could appear. Using degenerate primers we obtained 37 CYP genes, coding P450 enzymes, included in five families. Afterwards, in a phenobarbital-induction study, we observed that the expression of 4 out of the 6 analysed genes could be induced. On the other hand, a system was set up to amplify and to sequence from genomic DNA the exons of genes Ccace2 and Ccae7 where mutations related to insecticide resistance have been found in other species. The results obtained could facilitate the study of new resistance mechanisms in C. capitata mediated by these enzymes. A PCR-RFLP method was designed to detect the presence of the mutation AChE G328A (resistance allele Ccace2R), with no need to perform bioassays and allowing detecting resistance at low frequency. According to the analysis, the resistance allele was found in 25 out of 27 sampled locations in Spain, including the Balearic and the Canary Islands. However, this allele was not detected in other populations collected in 11 countries from 5 continents. The follow-up of the presence of the allele Ccace2R in the malathion-resistant strains during the selection process in the laboratory showed a quick decrease in homozygous individuals, for both the susceptible and the resistant alleles, favouring heterozygous. Thus, after 52 generations of selection, all the individuals analysed from W-10Km strain showed a heterozygous genotype for mutation AChE G328A, contradicting mendelian segregation as expected for a gene with two alleles. Afterwards, we were able to demonstrate that this was caused by the presence of a duplication of the gene coding acetylcholinesterase by: i) crossing heterozygous individuals from W-10Km strain with susceptible homozygous from C strain, originating a F1 population in which 100% of individuals were heterozygous; ii) evaluating the number of copies of gen Ccace2 by quantitative PCR in real time (qPCR), that happened to be twice higher in individuals from W-10Km VII strain when compared with C strain; iii) analysing the level of expression of Ccace2, twice in W- 10Km strain when compared to C strain; iv) studying the acetylcholinesterase activity, that was higher in individuals from W-10Km strain. According to these results, duplication of gen Ccace2 originates the coexistence of the susceptible and the resistant allele in the same chromosome. The two linked copies of the gene Ccace2 provoke the existence of permanent heterozygosis (Ccace2RS). This explains why the 100% of individuals from W-10Km strain showed an heterozygous restriction pattern since, in fact, they were structural homozygotes for the duplication (genotype Ccace2RS/RS). A biological cost has been detected associated to this duplication, consisting in a rise in accumulated adult mortality from the seventh day after emergence. The Ccace2RS duplication described in this study represents a new resistance mechanism to malathion in C. capitata. Finally, by the design of a double PCR-RFLP method, the presence of Ccace2RS duplication was confirmed in most of the Spanish populations. We observed that the proportion of individuals carrying the duplication oscillated between 5 and 35%, the frequency being higher in those C. capitata populations collected in the area of the Mediterranean basin. Therefore, we can conclude that malathion resistance associated to mutation AChE G328A and to Ccace2RS duplication are widely distributed in Spanish populations of C. capitata. Our results advice against the use of malathion (if it came to be newly authorized for use) or other OPs for the control of this pest. Besides, one of the malathion-resistant strains showed cross-resistance against insecticides with diverse action modes that are currently used for pest control, such as lambdacyhalotrin and lufenuron. High susceptibility to spinosad in the Spanish populations, as well as the reduced cross-resistance estimated for this insecticide suggests its adequacy for Medfly control. However, the use of a single insecticide is a risky strategy since it favours the selection of resistance. In fact, a population highly resistant to spinosad was obtained through laboratory selection. Therefore, it is advisable to implement integrated pest management (IPM) and resistance management programs for C. capitata control. Using insecticides with different modes of action and diverse control systems would contribute to the sustainability of the pest control. The resistance allele detection systems developed through this work will allow the early detection of resistance in the field, making possible the selection of the most appropriate method for pest control. Besides, the generated knowledge may also contribute to the development of new detection systems for other resistance mechanisms.