45 resultados para Carbaryl


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Biosensors for determination of carbamates in vegetables based on five different cholinesterases as biorecognition elements and a screen-printed electrode system as an amperometric transducer were developed. Measurements were simply performed by dropping solutions (either sample or substrate) directly on the biosensor. The response of biosensors to selected carbamates (aldicarb, carbaryl, carbofuran, methomyl and propoxur) was characterized. The performance was evaluated on extracts of potatoes and carrots, the results from the AChE biosensor and a standard HPLC procedure were compared. Finally, the biosensor was used for the direct analysis of vegetable juices without any pretreatment steps. In this case, 10 mu g/L levels of added carbofuran and propoxur were reliably identified. The whole procedure takes less than 20 min including 10 min incubation with samples. The concentrations of carbamates determined with biosensor agreed well for carbofuran. Lower response was observed for propoxur.

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Several clean-up procedures which included the use of glass chromatography columns (silica gel, alumina, Florisil, silanized Celite-charcoal), Sep-Pak cartridges and standard solutions were compared for the determination of the following N-methylcarbamate (NMC) insecticides: aldicarb, carbaryl, carbofuran, methomyl and propoxur. According to recovery results of the compounds after elution in a glass column, the most efficient systems employed 4.6% deactivated alumina and a silanized Celite-charcoal (4:1) as adsorbents, using dichloromethane-methanol (99:1) and toluene-acetonitrile (75:25) mixtures, respectively, as binary eluents. The recoveries of the compounds studied varied from 84 to 120%. Comparable recoveries (75-100%) for Sep-Pak cartridges in normal phase (NH2, CN) and reversed phase (C-8) were observed. Different temperatures were tested during the concentration step in a rotary evaporator, and we verified a strong influence of this parameter on the stability of some compounds, such as carbofuran and carbaryl. Recovery studies employing the best clean up procedures were performed at the Brazilian agricultural level in potato and carrot samples; Validation methodology of the US Food and Drug Administration was adapted for the N-methylcarbamate analysis. Their recoveries ranged between 79 and 93% with coefficients of variation of 2.3-8%. (C) 1998 Elsevier B.V. B.V.

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An amperometric biosensor based on cholinesterase (ChE) has been used for the determination of selected carbamate insecticides in vegetable samples. The linear range of the biosensor for the N-methylcarbamates (aldicarb, carbaryl, carbofuran, methomyl and propoxur) varied from 5 x 10(-5) to 50 mg kg(-1). Limits of detection were calculated on the basis that the ChE enzymes were 10% inhibited and varied, depending of the combination ChE (as acetyl- or butyrylcholinesterase) vs. inhibitor (pesticide), from 1 x 10(-4) to 3.5 mg kg(-1). The biosensor-based carbamate determination was compared to liquid chromatography/UV methods. Three vegetable samples were spiked with carbofuran and propoxur at 125 mu g kg(-1) followed by conventional procedures. Good correlations were observed for carbofuran in the vegetable extracts (79, 96 and 91% recoveries for potato, carrot and sweet pepper, respectively), whereas for propoxur unsatisfactory results were obtained. Potato and carrot samples were spiked with 10, 50 and 125 mu g kg(-1) carbofuran, followed by direct determination by the amperometric biosensor. The fortified sampler; resulted in very high inhibition values, and recoveries were: 28, 34 and 99% for potato, and 140, 90 and 101% for carrot, respectively, at these three fortification levels. (C) 1998 Elsevier B.V. B.V.

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In this work the interaction of the pesticide carbaryl with two groups of biomimetic ligands, peptides and MIPs was screened by multiple minima hypersurfaces (MMH) procedures, through the AM1 semiempirical method. Data related to the properties of the molecular association of the complex biomimetic ligand-pesticide were obtained and compared with another molecular modeling algorithm named Leapfrog, as included in the Sybyl software package, and experimental results from the literature, remarking good correlation between them. All important MMH program parameters (cells number, box size, conformers) were studied and optimized with the aim of getting the minimum computation time without losing the correlation with experimental data. The data demonstrated that MMH approach can be used as a fast biomimetic ligand screening tool for MIPs. In the case of peptides the computation time was not comparable with the molecular dynamics methods conventionally used for this approach. © 2011 Springer Science+Business Media B.V.

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Pós-graduação em Zootecnia - FMVZ

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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)

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Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

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A sensitive electrochemical acetylcholinesterase (AChE) biosensor was successfully developed on polyaniline (PANI) and multi-walled carbon nanotubes (MWCNTs) core-shell modified glassy carbon electrode (GC), and used to detect carbamate pesticides in fruit and vegetables (apple, broccoli and cabbage). The pesticide biosensors were applied in the detection of carbaryl and methomyl pesticides in food samples using chronoamperometry (CA). The GC/MWCNT/PANI/AChE biosensor exhibited detection limits of 1.4 and 0.95 mu mol L-1, respectively, for carbaryl and methomyl. These detection limits were below the allowable concentrations set by Brazilian regulation standards for the samples in which these pesticides were analysed. Reproducibility and repeatability values of 2.6% and 3.2%, respectively, were obtained in the conventional procedure. The proposed biosensor was successfully applied in the determination of carbamate pesticides in cabbage, broccoli and apple samples without any spiking procedure. The obtained results were in full agreement with those from the HPLC procedure. (C) 2012 Elsevier Ltd. All rights reserved.

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In this work, the reduction reaction of paraquat herbicide was used to obtain analytical signals using electrochemical techniques of differential pulse voltammetry, square wave voltammetry and multiple square wave voltammetry. Analytes were prepared with laboratory purified water and natural water samples (from Mogi-Guacu River, SP). The electrochemical techniques were applied to 1.0 mol L-1 Na2SO4 solutions, at pH 5.5, and containing different concentrations of paraquat, in the range of 1 to 10 mu mol L-1, using a gold ultramicroelectrode. 5 replicate experiments were conducted and in each the mean value for peak currents obtained -0.70 V vs. Ag/AgCl yielded excellent linear relationships with pesticide concentrations. The slope values for the calibration plots (method sensitivity) were 4.06 x 10(-3), 1.07 x 10(-2) and 2.95 x 10(-2) A mol(-1) L for purified water by differential pulse voltammetry, square wave voltammetry and multiple square wave voltammetry, respectively. For river water samples, the slope values were 2.60 x 10(-3), 1.06 x 10(-2) and 3.35 x 10(-2) A mol(-1) L, respectively, showing a small interference from the natural matrix components in paraquat determinations. The detection limits for paraquat determinations were calculated by two distinct methodologies, i.e., as proposed by IUPAC and a statistical method. The values obtained with multiple square waves voltammetry were 0.002 and 0.12 mu mol L-1, respectively, for pure water electrolytes. The detection limit from IUPAC recommendations, when inserted in the calibration curve equation, an analytical signal (oxidation current) is smaller than the one experimentally observed for the blank solution under the same experimental conditions. This is inconsistent with the definition of detection limit, thus the IUPAC methodology requires further discussion. The same conclusion can be drawn by the analyses of detection limits obtained with the other techniques studied.

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A cross-sectional study on the use of three pesticides and their presence in drinking water sources was conducted in Githunguri/Kiaria community between January 1994-March 1995. The main objective of the study was to determine the extent to which some of the pesticides used by the Githunguri/Kiaria agricultural community were polluting their drinking water sources. Due to monetary and physical limitations, only DDT, its isomers and metabolites, carbofuran and carbaryl pesticides were identified and used as surrogates of pollution for the other pesticides.^ The study area was divided into high and low lying geographic surface areas. Thirty-four and 38 water sampling sites were randomly selected respectively. During wet and dry seasons, a total of 144 water samples were collected and analyzed at the Kenya Bureau of Standards Laboratory in Nairobi. Gas chromatography was used to analyze samples for possible presence of DDT, its isomers and metabolites, while high pressure liquid chromatography was used to analyze samples for carbofuran and carbaryl pesticides.^ Six sites testing positively for DDT, its isomers and metabolites represented 19.4% of the total sampled sites, with a mean concentration of 0.00310 ppb in the dry season and 0.0130 ppb in the wet season. All the six sites testing positively for the same pesticide exceeded the European maximum contaminant limit (MCL) in the wet season, and only one site exceeded the European MCL in the dry season.^ Those sites testing positively for carbofuran and carbaryl represented 5.6% of the total sampled sites. The mean concentration for the carbofuran at the sites was 2.500 ppb and 1.590 ppb in the dry and wet seasons respectively. Similarly, the mean concentration for carbaryl at the sites was 0.281 ppb in the dry season and 0.326 ppb in the wet season.^ One site testing positively for carbofuran exceeded the European MCL and WHO set limit in the wet season, while one site testing positively for the same pesticide exceeded the USA, Canada, European and WHO MCLs in the dry season. Similarly, one site which tested positively for carbaryl pesticide exceeded the European MCL in both seasons.^ Out of the 2,587 community members in the study area, 333 (13%) were exposed through their drinking water sources to the three pesticides investigated by this study. As a public health measure, integrated pest management approaches (IPM), protection of the wells and education of the community is necessary to minimize the pollution of the environment and safeguard the drinking water sources from pollution by the pesticides. ^

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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.

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The preparation of a certified reference material of polar pesticides in freeze-dried water is described. The pesticides selected were atrazine, simazine, carbaryl, propanil, linuron, fenamiphos and permethrin which were added to 6000 litres of tap water at 50–80 μg · L–1 (200–320 μg · L–1 for permethrin) level in presence of NaCl (2.5 g · L–1) prior lyophilization. After the freeze-drying process the residue was rehomogenized, filled into amber glass bottles and stored at –20 °C, +4 °C and +20 °C. All pesticides were determined by HPLC/diode array detector, except permethrin which was determined by GC/ECD. The results obtained for atrazine, simazine, carbaryl, propanil, linuron and fenamiphos showed no within- or between-bottle inhomogeneity, however the material was non-homogeneous for permethrin and therefore this was withdrawn from further studies. With respect to the stability for over one year, all pesticides were stable at –20 °C. At +4 °C all pesticides were stable for at least 9 months and at +20 °C the stability was demonstrated only during the first month of storage. The content (mass fractions) of atrazine, simazine, carbaryl, propanil and linuron in freeze-dried water (CRM 606) was certified by an interlaboratory testing and a certification campaign.

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Apresentamos um modelo que estima o fator de bioconcentracão (BCF) de pesticidas em batatas supondo que o pesticida na solução do solo é absorvido pela batata por difusão passiva,seguindo a segunda lei de Fick.Os pesticidas do modelo são compostos orgânicos não-iônicos, tradicionalmente utilizados no cultivo de batatas que degradam no solo de acordo com uma equação cinética de primeira ordem. Este trabalho apresenta uma expressão que relaciona o BCF com a taxa de eliminação do pesticida pela batata, com a taxa de acumulação do pesticida na batata, com a taxa de crescimento da batata, e com a taxa de degradação do pesticida no solo. O BCF foi estimado supondo-se estado de equilíbrio estacionário do quociente entre a concentração do pesticida na batata e a concentração do pesticida na solução do solo. O modelo foi construído baseado no trabalho de Trapp et al. (2007), [Diffusion of PAH in Potato and Carrrot Slices and Applications for a Potato Model] no qual é apresentada uma expressão para calcular a difusividade de substâncias orgânicas persistentes em batatas. A modelagem consistiu em adicionar ao modelo de Trapp et al. (2007) a hipótese de que o pesticida degrada no solo. O valor do BCF sugere um conjunto de pesticidas que devem ser prioritariamente monitorados em cultivos de batatas. Foi estimado o BCF dos pesticidas methamidophos, cymoxanil, carbofuran, aldicarb, metalaxyl, fenamiphos, carbaryl, triazophos, tebuconazole, propiconazole, chlorothalonil e cypermethrin.