728 resultados para Herbicides.


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The Thames Estuary, UK, and the Brisbane River, Australia, are comparable in size and catchment area. Both are representative of the large and growing number of the world's estuaries associated with major cities. Principle differences between the two systems relate to climate and human population pressures. In order to assess the potential phytotoxic impact of herbicide residues in the estuaries, surface waters were analysed with a PAM fluorometry-based bioassay that employs the photosynthetic efficiency (photosystem II quantum yield) of laboratory cultured microalgae, as an endpoint measure of phytotoxicity. In addition, surface waters were chemically analysed for a limited number of herbicides. Diuron atrazine and simazine were detected in both systems at comparable concentrations. In contrast, bioassay results revealed that whilst detected herbicides accounted for the observed phytotoxicity of Brisbane River extracts with great accuracy, they consistently explained only around 50% of the phytotoxicity induced by Thames Estuary extracts. Unaccounted for phytotoxicity in Thames surface waters is indicative of unidentified phytotoxins. The greatest phytotoxic response was measured at Charing Cross, Thames Estuary, and corresponded to a diuron equivalent concentration of 180 ng L-1. The study employs relative potencies (REP) of PSII impacting herbicides and demonstrates that chemical analysis alone is prone to omission of valuable information. Results of the study provide support for the incorporation of bioassays into routine monitoring programs where bioassay data may be used to predict and verify chemical contamination data, alert to unidentified compounds and provide the user with information regarding cumulative toxicity of complex mixtures. (c) 2005 Elsevier B.V. All rights reserved.

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Pesticides and herbicides including organochlorine compounds have had extensive current and past application by Queensland's intensive coastal agriculture industry as web as for a wide range of domestic, public health and agricultural purposes in urban areas, The persistent nature of these types of compounds together with possible continued illegal use of banned organochlorine compounds raises the potential for continued long-term chronic exposure to plants and animals of the Great Barrier Reef. Sediment and seagrass samples were collected from 16 intertidal and 25 subtidal sampling sites between Torres Strait and Townsville, near Mackay and Gladstone, and in Hervey and Moreton Bays in 1997 and 1998 and analysed for pesticide and herbicide residues. Low levels of atrazine (0.1-0.3 mug kg(-1)), diuron (0.2-10.1 mug kg(-1)), lindane (0.08-0.19 mug kg(-1)), dieldrin (0.05-0.37 mug kg(-1)), DDT (0.05-0.26 mug kg(-1)), and DDE (0.05-0.26 mug kg(-1)) were detected in sediments and/or seagrasses. Contaminants were mainly detected in samples collected along the high rainfall, tropical coast between Townsville and Port Douglas and in Moreton Bay. Of the contaminants detected, the herbicide diuron is of most concern as the concentrations detected have some potential to impact local seagrass communities, (C) 2000 Elsevier Science Ltd. All rights reserved.

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Nuisance growths of Cladophora have been associated with eutrophication. A review of the literature, however, reveals a scarcity of relevant experimental growth studies. Sampling experimental streams reveals that the addition of sewage effluent to good quality water alters the flora from that dominated by Potamogetan crispus to one dominated by CLadophora. Spatial and temporal differences in biomass of taxa present are discussed in the context of accompanying physicochemical data. In laboratory batch culture, growth of unialgal C. glomerata was accompanied by elevation of medium pH - considered largely responsible for the poor growth in such culture. However, appropriate experimental conditions and indices of growth were selected and the effects of various herbicides assessed. Diquat and terbutryne were shown to possess algicidal activity towards Cladophora. A closed continuous culture apparatus was developed: growth proceeded through lag, logarithmic and linear phases. Inoculum size and medium flow rate had significant effects on growth, and were standardized. In continuous culture, specific growth rate increased linearly with increased duration of light per day, up to 24 hours, and increased light intensity, up to 6000 lux - the highest intensity tested. Comparison of field and laboratory results suggests that ammonia toxicity is attributable to the undissociated form. In the laboratory, 185 µg/1 undissociated ammoniacal nitrogen reduced specific growth rate to 50% of that at 10 µg/1 undissociated ammcniacal nitrogen. 0.077-1.057 mg/1 NO2-N had no significant effect on growth. 7.2-15.2 mg/1 NO3-N had no significant effect on specific growth rate. Neither was any nitrate/phosphate interaction significant. At 4.9 mg/1 PO4-1, specific growth rate was only 48% of that at 1.9 g/1 P04-P. The critical medium PO4-P concentration was <0.1 mg/i. Specific growth rate was reduced to 50% of that in natural water by 0.036 mgCu/l, 0.070 mgzn/1 and 1.03 mgPb/l. Metal uptake was evaluated.

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Grape is one of the world's largest fruit crops with approximately 67.5 million tonnes produced each year and energy is an important element in modern grape productions as it heavily depends on fossil and other energy resources. Efficient use of these energies is a necessary step toward reducing environmental hazards, preventing destruction of natural resources and ensuring agricultural sustainability. Hence, identifying excessive use of energy as well as reducing energy resources is the main focus of this paper to optimize energy consumption in grape production.In this study we use a two-stage methodology to find the association of energy efficiency and performance explained by farmers' specific characteristics. In the first stage a non-parametric Data Envelopment Analysis is used to model efficiencies as an explicit function of human labor, machinery, chemicals, FYM (farmyard manure), diesel fuel, electricity and water for irrigation energies. In the second step, farm specific variables such as farmers' age, gender, level of education and agricultural experience are used in a Tobit regression framework to explain how these factors influence efficiency of grape farming.The result of the first stage shows substantial inefficiency between the grape producers in the studied area while the second stage shows that the main difference between efficient and inefficient farmers was in the use of chemicals, diesel fuel and water for irrigation. The use of chemicals such as insecticides, herbicides and fungicides were considerably less than inefficient ones. The results revealed that the more educated farmers are more energy efficient in comparison with their less educated counterparts. © 2013.

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The aim of this article is to draw attention to calculations on the environmental effects of agriculture and to the definition of marginal agricultural yield. When calculating the environmental impacts of agricultural activities, the real environmental load generated by agriculture is not revealed properly through ecological footprint indicators, as the type of agricultural farming (thus the nature of the pollution it creates) is not incorporated in the calculation. It is commonly known that extensive farming uses relatively small amounts of labor and capital. It produces a lower yield per unit of land and thus requires more land than intensive farming practices to produce similar yields, so it has a larger crop and grazing footprint. However, intensive farms, to achieve higher yields, apply fertilizers, insecticides, herbicides, etc., and cultivation and harvesting are often mechanized. In this study, the focus is on highlighting the differences in the environmental impacts of extensive and intensive farming practices through a statistical analysis of the factors determining agricultural yield. A marginal function is constructed for the relation between chemical fertilizer use and yield per unit fertilizer input. Furthermore, a proposal is presented for how calculation of the yield factor could possibly be improved. The yield factor used in the calculation of biocapacity is not the marginal yield for a given area, but is calculated from the real and actual yields, and this way biocapacity and the ecological footprint for cropland are equivalent. Calculations for cropland biocapacity do not show the area needed for sustainable production, but rather the actual land area used for agricultural production. The proposal the authors present is a modification of the yield factor and also the changed biocapacity is calculated. The results of statistical analyses reveal the need for a clarification of the methodology for calculating marginal yield, which could clearly contribute to assessing the real environmental impacts of agriculture.

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The aim of this article is to draw attention to calculations on the environmental effects of agriculture and to the definition of marginal agricultural yield. When calculating the environmental impacts of agricultural activities, the real environmental load generated by agriculture is not revealed properly through ecological footprint indicators, as the type of agricultural farming (thus the nature of the pollution it creates) is not incorporated in the calculation. It is commonly known that extensive farming uses relatively small amounts of labor and capital. It produces a lower yield per unit of land and thus requires more land than intensive farming practices to produce similar yields, so it has a larger crop and grazing footprint. However, intensive farms, to achieve higher yields, apply fertilizers, insecticides, herbicides, etc., and cultivation and harvesting are often mechanized. In this study, the focus is on highlighting the differences in the environmental impacts of extensive and intensive farming practices through a statistical analysis of the factors determining agricultural yield. A marginal function is constructed for the relation between chemical fertilizer use and yield per unit fertilizer input. Furthermore, a proposal is presented for how calculation of the yield factor could possibly be improved. The yield factor used in the calculation of biocapacity is not the marginal yield for a given area, but is calculated from the real and actual yields, and this way biocapacity and the ecological footprint for cropland are equivalent. Calculations for cropland biocapacity do not show the area needed for sustainable production, but rather the actual land area used for agricultural production. The proposal the authors present is a modification of the yield factor and also the changed biocapacity is calculated. The results of statistical analyses reveal the need for a clarification of the methodology for calculating marginal yield, which could clearly contribute to assessing the real environmental impacts of agriculture.

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It is well established that secondary metabolites play an important role in plant chemical defense. In an effort to find natural herbicides research on plant growth regulatory activity of secondary metabolites has received more and more attention recently. The genus Piper has been an important source for useful secondary metabolites.^ Crude extracts from Piper species inhibited gram-positive bacteria and higher plant growth under laboratory conditions. Bioassay-guided isolation and purification lead to the identification of safrole, a phenylpropene, as the responsible agent for the inhibitory activity. Safrole was found to leach from naturally fallen leaves with water. Mechanisms of plant growth inhibition by safrole were investigated. Disassociation of cell membrane from cell walls was determined to be a major cause.^ Phenylpropenes structurally similar to safrole had similar phytogrowth inhibitory activity. It is postulated that phenylpropanoids are an important group of naturally occurring secondary metabolites in plant-plant interactions. ^

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A comprehensive investigation of sensitive ecosystems in South Florida with the main goal of determining the identity, spatial distribution, and sources of both organic biocides and trace elements in different environmental compartments is reported. This study presents the development and validation of a fractionation and isolation method of twelve polar acidic herbicides commonly applied in the vicinity of the study areas, including e.g. 2,4-D, MCPA, dichlorprop, mecroprop, picloram in surface water. Solid phase extraction (SPE) was used to isolate the analytes from abiotic matrices containing large amounts of dissolved organic material. Atmospheric-pressure ionization (API) with electrospray ionization in negative mode (ESP-) in a Quadrupole Ion Trap mass spectrometer was used to perform the characterization of the herbicides of interest. ^ The application of Laser Ablation-ICP-MS methodology in the analysis of soils and sediments is reported in this study. The analytical performance of the method was evaluated on certified standards and real soil and sediment samples. Residential soils were analyzed to evaluate feasibility of using the powerful technique as a routine and rapid method to monitor potential contaminated sites. Forty eight sediments were also collected from semi pristine areas in South Florida to conduct screening of baseline levels of bioavailable elements in support of risk evaluation. The LA-ICP-MS data were used to perform a statistical evaluation of the elemental composition as a tool for environmental forensics. ^ A LA-ICP-MS protocol was also developed and optimized for the elemental analysis of a wide range of elements in polymeric filters containing atmospheric dust. A quantitative strategy based on internal and external standards allowed for a rapid determination of airborne trace elements in filters containing both contemporary African dust and local dust emissions. These distributions were used to qualitative and quantitative assess differences of composition and to establish provenance and fluxes to protected regional ecosystems such as coral reefs and national parks. ^

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Arsenic is a human carcinogen that has been found in various waters and wines throughout the world. Therefore, close examination of these liquids is necessary to prevent the intoxication of animals and humans. Wines and waters often contain significant amounts of toxic arsenic species. The source of arsenic in wines and waters is generally believed to be the result of arsenic-based pesticides and herbicides. Recent studies have also shown that toxic arsenic may be used in the cultivation and acceleration of the ripening process of fruit, ultimately contaminating fruit-based beverages. The determination of total arsenic can be found by using several methods, including AFS or ICP/MS. No pretreatment of water is necessary, except for filtering by means of a Fisherbrand PTFE 0.45 connected to a Becton-Dickinson 10 mL syringe to filter particles from water. The pretreatment of the wine includes ethanol evaporation and an addition of 0.1% nitric acid. A number of commercial drinking waters and regional lake water were analyzed. Since we have confirmed the presence of arsenic in a variety of waters and wines from different countries, we decided to test a number of commercially available beverages for the presence of arsenic. The focus ofthis project is to establish the presence of arsenic in various commercially available beverages. ICP-MS was used to determine total arsenic using certified standards. Internal standards Indium and Yttrium were also used to verify the concentration readings, which varied from 0- 20 ppb.

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A comprehensive investigation of sensitive ecosystems in South Florida with the main goal of determining the identity, spatial distribution, and sources of both organic biocides and trace elements in different environmental compartments is reported. This study presents the development and validation of a fractionation and isolation method of twelve polar acidic herbicides commonly applied in the vicinity of the study areas, including e.g. 2,4-D, MCPA, dichlorprop, mecroprop, picloram in surface water. Solid phase extraction (SPE) was used to isolate the analytes from abiotic matrices containing large amounts of dissolved organic material. Atmospheric-pressure ionization (API) with electrospray ionization in negative mode (ESP-) in a Quadrupole Ion Trap mass spectrometer was used to perform the characterization of the herbicides of interest. The application of Laser Ablation-ICP-MS methodology in the analysis of soils and sediments is reported in this study. The analytical performance of the method was evaluated on certified standards and real soil and sediment samples. Residential soils were analyzed to evaluate feasibility of using the powerful technique as a routine and rapid method to monitor potential contaminated sites. Forty eight sediments were also collected from semi pristine areas in South Florida to conduct screening of baseline levels of bioavailable elements in support of risk evaluation. The LA-ICP-MS data were used to perform a statistical evaluation of the elemental composition as a tool for environmental forensics. A LA-ICP-MS protocol was also developed and optimized for the elemental analysis of a wide range of elements in polymeric filters containing atmospheric dust. A quantitative strategy based on internal and external standards allowed for a rapid determination of airborne trace elements in filters containing both contemporary African dust and local dust emissions. These distributions were used to qualitative and quantitative assess differences of composition and to establish provenance and fluxes to protected regional ecosystems such as coral reefs and national parks.

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A batata está sujeita a stresses bióticos (doenças, pragas, infestantes) e abióticos (condições climáticas, secura, excesso de água, ou fitotoxicidade provocada por herbicidas, entre outros). Os adubos foliares contendo nutrientes (macro e micronutrientes) poderão contribuir para uma melhor nutrição da planta, para além de exercer uma ação benéfica ao nível do potencial hídrico da folha e sua proteção contra os diversos inimigos bióticos. Instalou-se um ensaio em Marinhais na variedade de batata de indústria Lady Rosetta, para avaliar o efeito da adubação foliar de uma gama de adubos foliares “Humigel”, contendo, entre outros nutrientes, o enxofre e o potássio, numa situação de fitotoxidade causada pela aplicação de um herbicida. O ensaio foi instalado com um dispositivo experimental de parcelas totalmente aleatórias, com 4 repetições. Os tratamentos foram a aplicação de “Humigel” e sem aplicação (testemunha). A produção comercial nas parcelas com “Humigel” foi significativamente mais elevada (48 192 kg/ha) do que nas parcelas testemunha (43 458 kg/ha). Não se registaram diferenças significativas ao nível do número de tubérculos (comercial e total) por planta, nem ao nível dos parâmetros de qualidade (peso específico e teste de fritura).

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In this study, our goal was develop and describe a molecular model of the enzyme-inhibiting interaction which can be used for an optimized projection of a Microscope Force Atomic nanobiosensor to detect pesticides molecules, used in agriculture, to evaluate its accordance with limit levels stipulated in valid legislation for its use. The studied herbicide (imazaquin) is a typical member of imidazolinone family and is an inhibitor of the enzymatic activity of Acetohydroxiacid Synthase (AHAS) enzyme that is responsible for the first step of pathway for the synthesis of side-chains in amino acids. The analysis of this enzyme property in the presence of its cofactors was made to obtain structural information and charge distribution of the molecular surface to evaluate its capacity of became immobilized on the Microscopy Atomic Force tip. The computational simulation of the system, using Molecular Dynamics, was possible with the force-field parameters for the cofactor and the herbicides obtained by the online tool SwissParam and it was implemented in force-field CHARMM27, used by software GROMACS; then appropriated simulations were made to validate the new parameters. The molecular orientation of the AHAS was defined based on electrostatic map and the availability of the herbicide in the active site. Steered Molecular Dynamics (SMD) Simulations, followed by quantum mechanics calculations for more representative frames, according to the sequential QM/MM methodology, in a specific direction of extraction of the herbicide from the active site. Therefore, external harmonic forces were applied with similar force constants of AFM cantilever for to simulate herbicide detection experiments by the proposed nanobiosensor. Force value of 1391 pN and binding energy of -14048.52 kJ mol-1 were calculated.

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The soybean is the grain in which greater food dependency has Mexico, reason why as of 2008, the government has promoted his culture, granting excellent subsidies, as much to producers as to buyers of the grain, thus contributing to a recent process of expansion in certain states, as it happens in Campeche. The objetive of this article is the analysis of the characteristics and effects of those supports, as well as of the rest of factors that until today they have taken to the producers of the mentioned state to initiate or to expand the cultivation of the soybean. The findings of the investigation reveal that although the producers have improved their levels of income, the process is vulnerable, as it depends on variables like the governmental supports, the international prices of the soybean and exchange rate. Although the study of the negative effects of genetically modified soybeans (GM) in other areas (environment, biodiversity, deforestation, human and animal health) is not the purpose of this investigation, some information will be provided, as on the conflict between soybean producers and beekeepers in the state of Campeche.

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Les services écologiques sont essentiels au maintien de la vie humaine sur terre, puisqu’entre autres, ils participent à la production d’oxygène, de nourriture et de matériaux divers, régulent les cycles de l’eau et des nutriments et contribuent au bien-être humain ; ces services nous sont fournis depuis toujours, gratuitement et continuellement. Toutefois, les activités humaines compromettent de plus en plus ces services écologiques en déréglant les processus écologiques qui en sont à l’origine. Dans les paysages agricoles, les perturbations anthropiques sont connues pour affecter grandement la biodiversité et les services écologiques. L’intensification agricole ainsi que la perte et la fragmentation des habitats naturels menacent notamment les services de pollinisation, lesquels permettent la production de fruits et de graines, pour la reproduction des plantes et la consommation humaine. Cet essai évalue la perspective du service de pollinisation dans le cas précis du café en Mésoamérique. Le premier objectif de cet essai est de déterminer les enjeux écologiques, économiques et sociaux auxquels sont liés les pollinisateurs et la production durable et rentable de café. Le deuxième objectif de cet essai est d’identifier les mécanismes expliquant comment certains facteurs clés de la biodiversité et de l’aménagement peuvent augmenter les rendements du café à travers sa pollinisation par les abeilles. Le troisième objectif de cet essai est de proposer des mesures d’aménagement qui permettent d’intégrer davantage les pollinisateurs aux exploitations de café. Le quatrième et dernier objectif consiste à développer et prioriser des stratégies locales et régionales, qui puissent concilier l’application de ces mesures d’aménagement avec les réalités économiques et sociales. La revue de la littérature a permis de constater qu’en Mésoamérique, ce sont à la fois les populations d’abeilles sauvages et domestiques qui assurent la pollinisation du café. Ces insectes sont sensibles à la perturbation de leurs habitats, bien que certains soient plus tolérants que d’autres. De fait, l’aménagement local et l’aménagement régional peuvent soit bénéficier, soit nuire à la biodiversité d’abeilles et au service de pollinisation du café. Au niveau local, les systèmes agroforestiers de café, malgré de plus faibles rendements en comparaison à des monocultures intensives, sont plus résilients et maintiennent un service de pollinisation de qualité. Ils doivent donc être encouragés pour ne pas accentuer la dépendance des exploitations agricoles à des intrants externes (engrais, pesticides, herbicides, main d’œuvre supplémentaire ou mécanisation de l’agriculture) qui deviennent nécessaires pour compenser la perte des services écologiques et maintenir de hauts rendements. Au niveau régional, la forêt est essentielle au maintien de communautés de pollinisateurs abondants et riches en espèces. À l’échelle du paysage, des efforts doivent donc être investis pour préserver des habitats naturels de qualité et limiter l’isolement des exploitations de café. Cela est particulièrement vrai dans les paysages tropicaux où, contrairement aux paysages tempérés, il reste une proportion importante d’habitats naturels encore préservés. Ces habitats naturels et les terres destinées à d’autres usages (agriculture, élevage, etc.) forment une mosaïque complexe, si bien que l’aménagement du territoire soulève des enjeux majeurs aux niveaux politiques et institutionnels. Des efforts diversifiés sont donc nécessaires pour développer des solutions efficaces qui bénéficient durablement aux petits producteurs de café. Pour cela, il est essentiel que tous les membres de la chaîne de valeur du café soient des parties prenantes actives dans ces efforts. De l’échelle locale à l’échelle régionale, les producteurs, les coopératives, les gouvernements et les consommateurs ont tous une influence sur l’aménagement des paysages agricoles de café et sur les modes de vie ruraux. Bien que le rôle des insectes pollinisateurs dans l’augmentation des rendements soit reconnu, leur conservation requiert de meilleurs prix pour le café quand il est cultivé de façon respectueuse de la biodiversité, ainsi que des subventions directes pour préserver les forêts aux abords des exploitations et empêcher leur conversion en terres agricoles. À condition d’être ciblée et concertée, l’application de ces stratégies d’aménagement devrait permettre de maintenir le service de pollinisation du café en Mésoamérique.

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Avec l’ère industrielle sont venus les polluants environnementaux. Ils sont de plus en plus pointés du doigt pour une variété d’effets indésirables en particulier pour leur potentiel à affecter la santé humaine. Les pesticides font partie de ces polluants et leurs usages ne font que croître depuis une vingtaine d’années. Ces produits qui servent à améliorer la production agricole en éliminant les pestes qui ravagent les récoltes sont souvent peu étudiés à long terme avant d’être homologués. L’effet perturbateur au niveau cellulaire et les effets à long terme de ces pesticides sont peu connus. Pour ce projet de maîtrise, nous avons observé l’effet de deux pesticides, l’imidaclopride et l’acide 2-methyl-4-chlorophenoxyacetic (MCPA), sur les voies de signalisation du récepteur à la dioxine (AhR) et du récepteur aux androgènes (AR). L’imidaclopride est un insecticide de la famille des néonicotinoïdes, une classe de plus en plus utilisée. Ce pesticide est surtout connu pour être en lien avec le déclin des colonies d’abeilles depuis une décennie. Le MCPA est un des herbicides les plus utilisés au Québec, il est persistant et souvent retrouvé dans les eaux de la province. Nous avons traité des cellules du cancer du sein et des cellules du cancer de la prostate avec ces pesticides et nous avons vérifié si leur présence perturbait les deux voies de signalisation cellulaire à l’étude. Le récepteur AhR est un facteur de transcription activé par un ligand. Le TCDD, une dioxine, est le meilleur ligand exogène connu à ce jour de ce récepteur. Par contre, ses ligands naturels, des dérivés du tryptophane ou des facteurs de virulence de bactéries, l’activent de façon beaucoup moins forte. Lors de l’activation de la voie AhR, les gènes CYP1A1 et CYP1B1 sont transcrits et codent pour des enzymes du cytochrome P450 qui transforment les ligands en produits plus facilement éliminables. Dans un contexte où de l’œstradiol (E2) est présent dans les cellules, il y a une interaction croisée entre le récepteur à l’œstrogène (ER) et le récepteur AhR, qui fait en sorte que l’expression de CYP1A1 est réprimée. Cela se traduit en un ratio d’enzyme CYP1A1 à CYP1B1 différent qui pourrait augmenter la possibilité d’une accumulation de métabolites génotoxiques. En effet, CYP1B1 hydroxyle le ligand d’AhR mais aussi l’œstradiol en 4-hydroxyœstradiol (4-OHE), dont l’accumulation peut amener des mutations dans l’ADN alors que l’enzyme CYP1A1 l’hydroxyle en 2-hydroxyœstradiol (2-OHE), qui n’as aucun effet néfaste répertorié sur la cellule. Dans les cellules du cancer du sein, le MCPA appliqué en champs induisait fortement l’expression de CYP1B1 comparable à l’échantillon traité au témoin positif (TCDD), alors que CYP1A1 l’était que très légèrement par rapport au témoin non-traité. Au niveau protéique, CYP1A1 n’était qu’exprimée dans le témoin positif (TCDD) et ce, en quantité moindre lorsqu’il y avait présence d’œstradiol. CYP1B1 était fortement exprimée dans l’échantillon de TCDD, ce qui était attendu, mais aussi dans tous les échantillons traités au MCPA de NuFarm. Ces effets ne sont pas notés avec l’ingrédient actif du MCPA. La présence d’un ou plusieurs autres produits ajoutés dans le MCPA de la compagnie NuFarm en combinaison avec l’ingrédient actif pourrait activer la voie de signalisation d’AhR et causer ce débalancement dans l’expression des gènes CYP1A1 et CYP1B1. Nos résultats indiquent que plusieurs concentrations de l’ingrédient actif de l’imidaclopride ne perturbe pas les voies cellulaires d’AhR ni AR, alors que, le MCPA perturbe ces deux voies cellulaires. Par contre, c’est seulement celui produit par la compagnie NuFarm qui est utilisé en champs. Cette formulation appliquée en terrain agricole inclut l’ingrédient actif ainsi que les antigels, les surfactants et les adjuvants qui permettent au produit d’être plus efficace. L’ingrédient actif du MCPA seul n’affectait pas les deux voies. Le récepteur aux androgènes (AR) est aussi un facteur de transcription qui se lie à l’ADN afin de réguler l’expression des gènes et il est particulièrement important pour le développement et le maintien du phénotype masculin. Depuis une vingtaine d’années, des problèmes de baisse de libido et de fertilité s’accentuent dans notre société et semblent être reliés à la baisse de testostérone des hommes (Travison et al. 2007). Cette molécule est d’ailleurs un des deux ligands du récepteur AR, le deuxième étant la 5-dihydrotestostérone (DHT). Le facteur environnemental plutôt que le mode de vie semble être un facteur déterminant dans l’étude qui portait sur ce déclin. Les pesticides ont déjà été soupçonnés pour avoir un potentiel anti-androgénique, mais aucune étude ne fait un lien de causalité direct. Dans le projet de maitrise présenté dans ce document, l’expression des gènes marqueurs PSA (antigène spécifique de la prostate) et PCA3 (antigène du cancer de la prostate) a été quantifiée pour savoir si les pesticides ont un effet perturbateur sur la voie du récepteur AR. Dans les cellules du cancer de la prostate, l’expression de PSA et PCA3 était semblable au non-traité dans l’échantillon traité au MCPA (NuFarm), et ce, même après l’ajout de DHT, qui active l’expression de ces deux gènes. Cette fois-ci, l’ingrédient actif seul faisait en sorte que les deux gènes marqueurs étaient moins exprimés lors de l’ajout de la DHT, par rapport au témoin. Il semblerait que l’ingrédient actif est à la base de ce changement d’expression de nos gènes marqueurs. Donc, le MCPA pourrait avoir un effet anti-androgénique dans les cellules du cancer de la prostate. Donc, le MCPA est un pesticide qui affecte les voies de signalisation cellulaires AhR et AR. Il est particulier de noter que le pesticide appliqué en champ perturbe nettement plus les voies cellulaires. Il sera important de continuer à étudier les effets des pesticides sur l’homme au niveau cellulaire et de comprendre comment ils pourraient contribuer au développement du cancer.