Aboveground plant community and species-specific vegetation cover from the Jena Experiment (Main Experiment, year 2004)

This data set contains information on vegetation cover, i.e. the proportion of soil surface area that is covered by different categories of plants per estimated plot area. Data was collected on the plant community level (sown plant community, weed plant community, dead plant material, and bare ground) and on the level of individual plant species in case of the sown species. Data presented here is from the Main Experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. In 2004, vegetation cover was estimated twice in May and August just prior to mowing (during peak standing biomass) on all experimental plots of the Main Experiment. Cover was visually estimated in a central area of each plot 3 by 3 m in size (approximately 9 m²) using a decimal scale (Londo). Cover estimates for the individual species (and for target species + weeds + bare ground) can add up to more than 100% because the estimated categories represented a structure with potentially overlapping multiple layers. In 2004, cover on the community level was only estimated for the sown plant community, weed plant community and bare soil. In contrast to later years, cover of dead plant material was not estimated.

Duration of a flood along a plant diversity gradient in the Jena Experiment (Main Experiment, June 2013)

The Jena Biodiversity Experiment is located on a Central European mesophilic floodplain on the banks of the Saale River (see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown in the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, or 4 functional groups). Plots were maintained by bi-annual weeding and mowing. In June 2013, a natural 200-year flood event occurred at the field site. Rainfall in May 2013 in Jena was ~150mm, constituting >25% of annual precipitation at the site that year. Overall the flood affected the entire Elbe River Basin and much of Europe and was one of the largest natural flooding events in the past two centuries. The flood lasted for a total of 24 days at the site (30 May-24 June) and led to anaerobic soil conditions. Due to small topographical differences among the plots in the experiment (<1m), there was variation in the duration of flooding and the proportion of each plot that was flooded. This variation was well-distributed across the diversity gradient. To assess the importance of flood severity, the proportion of each plot that was flooded was estimated by eye (using five classes: 0 completely dry, 0.25 up to a quarter under water, 0.5 half, 0.75 up to three quarters under water, and 1 more than three quarters under water up to completely submerged). These values, for each of the 24 days that the flood lasted, were summed up to calculate a flooding index. The resulting flooding index is given for each plot of the Main Experiment.

Collection of measurements on environmental conditions in plots of the Jena Experiment (time series since 2002)

This collection contains measurements of environmental conditions measured on the plots of the different sub-experiments at the field site of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. The following series of datasets are contained in this collection: 1.Soil temperature measurements on plots of the Main Experiment; 2. Quantification of the duration that individual plots of the Main Experiment were submerged during a flooding event occurring in June 2013

Physico-geochemical and mineral composition of neem tree soils and relation to organic properties

The Neem tree, the oil of which has a long history of pesticide, fertilizer and medicinal use in India, has been studied extensively for its organic compounds. Here we present a physical, mineralogical and geochemical database resulting from the analyses of two Neem soil profiles (epipedons) in India. Neem tree derivatives are used in the manufacture of a variety of products, from anti-bacterial drugs and insecticides to fertilizers and animal feeds. A preliminary geochemical and mineralogical analysis of Neem soils is made to explore the potential for chemical links between Neem tree derivatives and soils. Physical soil characteristics, including colour, texture and clay mineralogy, suggest the two pedons formed under different hydrological regimes, and hence, are products of different leaching environments, one well-drained site, the other poorly drained. Geochemically, the two Neem soils exhibit similarities, with elevated concentrations of Th and rare earth elements. These elements are of interest because of their association with phosphates, especially monazite and apatite, and the potential link to fertilizer derivatives. Higher concentrations of trace elements in the soils may be linked to nutritional derivatives and to cell growth in the Neem tree.

The Use of Multi-Criteria Decision Analysis in Performing Alternatives Assessment and Comparative Risk Analysis: The Case Study of Codling Moth Pesticides

Thesis (Ph.D.)--University of Washington, 2016-08

Effet des pesticides MCPA et imidaclopride sur la régulation des voies de signalisation du récepteur à la dioxine (AhR) et au récepteur aux androgènes (AR)

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.

Synthèse et caractérisation des matériaux nanostructurés et leur mise en oeuvre comme photocatalyseurs pour la dégradation du glyphosate en milieux aqueux

L’utilisation des pesticides n’a cessé d’augmenter en particulier le glyphosate, herbicide utilisé principalement dans l’agriculture. Ses effets ont été démontrés néfastes sur l’environnement et sur la santé humaine. Bien que la plupart du glyphosate résiduel soit adsorbé par les constituants du sol, une partie peut être désorbée ou atteindre les eaux de surface par érosion. Le renforcement des normes de qualité de l’eau en milieu agricole et urbain entraîne le développement de nouveaux procédés. Les photocatalyseurs à base de TiO2 peuvent procurer une solution attrayante pour l’élimination de cet herbicide. Actif uniquement dans le domaine de l’UV qui représente 4% du rayonnement solaire, étendre cette réactivité photocatalytique dans le domaine du visible est un enjeu majeur. Le dopage du TiO2 à l’azote et au graphène a permis une élimination totale du glyphosate au bout de 30 minutes. Après sa synthèse, le photocatalyseur GR-N/TiO2 a été caractérisé par différentes techniques à savoir la diffraction des rayons X (DRX), l’infrarouge à transformée de Fourier (FTIR), la spectroscopie de photoélectrons X (XPS) et la microscopie électronique par transmission (TEM). L’activité photocatalytique est testée sur la dégradation du glyphosate sous irradiation de la lumière visible. Les résultats montrent que le composite GR-N/TiO2 peut effectivement photodégrader le glyphosate grâce à une amélioration impressionnante de l’activité photocatalytique due à une grande adsorption du glyphosate sur le nanomatériau synthétisé et à l’extension de l’absorption au domaine du visible.

A Mobile High Sensitivity On-field Organophosphorous Compounds Detecting System for IoT Based Food Safety Tracking

Food safety has always been a social issue that draws great public attention. With the rapid development of wireless communication technologies and intelligent devices, more and more Internet of Things (IoT) systems are applied in the food safety tracking field. However, connection between things and information system is usually established by pre-storing information of things into RFID Tag, which is inapplicable for on-field food safety detection. Therefore, considering pesticide residue is one of the severe threaten to food safety, a new portable, high-sensitivity, low-power, on-field organophosphorus (OP) compounds detection system is proposed in this thesis to realize the on-field food safety detection. The system is designed based on optical detection method by using a customized photo-detection sensor. A Micro Controller Unit (MCU) and a Bluetooth Low Energy (BLE) module are used to quantize and transmit detection result. An Android Application (APP) is also developed for the system to processing and display detection result as well as control the detection process. Besides, a quartzose sample container and black system box are also designed and made for the system demonstration. Several optimizations are made in wireless communication, circuit layout, Android APP and industrial design to realize the mobility, low power and intelligence.

Decision making models embedded into a web-based tool for assessing pest infestation risk

Current practices in agricultural management involve the application of rules and techniques to ensure high quality and environmentally friendly production. Based on their experience, agricultural technicians and farmers make critical decisions affecting crop growth while considering several interwoven agricultural, technological, environmental, legal and economic factors. In this context, decision support systems and the knowledge models that support them, enable the incorporation of valuable experience into software systems providing support to agricultural technicians to make rapid and effective decisions for efficient crop growth. Pest control is an important issue in agricultural management due to crop yield reductions caused by pests and it involves expert knowledge. This paper presents a formalisation of the pest control problem and the workflow followed by agricultural technicians and farmers in integrated pest management, the crop production strategy that combines different practices for growing healthy crops whilst minimising pesticide use. A generic decision schema for estimating infestation risk of a given pest on a given crop is defined and it acts as a metamodel for the maintenance and extension of the knowledge embedded in a pest management decision support system which is also presented. This software tool has been implemented by integrating a rule-based tool into web-based architecture. Evaluation from validity and usability perspectives concluded that both agricultural technicians and farmers considered it a useful tool in pest control, particularly for training new technicians and inexperienced farmers.

Relations entre apports terrigènes et conchyliculture dans les Pertuis Charentais

This work presents interactions between quantitative and qualitative river freshwater inputs and the shellfish farming (oyster and mussel) in the Pertuis Charentais. The quantity of freshwater (i.e. salinity) seems to have a weak influence on the shellfish farming contrarily to its quality determined by particulate and dissolved matters contained in the water. In autumn and winter, large precipitations have a "globally positive" effect amending the coastal ecosystem. Associated dissolved nutriments and the organic matter largely determine the quality of the coming spring growth for bred shellfish, itself controlling in turn the annual yield efficiencies. However, in winter their effects are postponed because of strong mineral load, low luminosity and temperature, then limiting the primary production. The spring contributions, directly linked to territorial practices, agriculture and tourism are more variable in quantity and quality from one year to another. They often correspond to high-risk inflows since numerous substances from anthropogenic watersheds can be found diluted in the coastal zone as in the Pertuis Charentais. Their impacts on in situ estuarine ecosystems are still poorly known since these substances are mainly studied and estimated in laboratory in controlled conditions. Several studies showed anthropogenic contaminations (i.e. cadmium, pesticides) could have significant direct or indirect effects on shellfish farming. For instance, the "summer" mortalities between 1990 and 2000 in the South of the Marennes-Oléron bay (MOB), that induced environmental and physiological oyster disorders, could be linked to pesticide effects, measured during consecutive years on the oyster bed of Ronce Perquis in the South of the MOB. The weak results from the spring larval rearing of the IFREMER experimental hatchery in the South of the bay, and chromosomal abnormalities measured on the stocks of wild oysters of the Pertuis could confirm a high-risk spring environment for the shellfish farming. In summer terrestrial inputs are reduced by low precipitations, anthropogenic water removals (drinking water, irrigation) and by plant evapotranspiration. Consequently certain years, a significant salinity increase in water masses of the Pertuis Charentais is observed. However, based on long-term observations, the significant interannual variability noticed in freshwater contributions constitutes one of the most important facts of these last years. When contributions are weak (i.e. 1991 and 2011), the mean annual salinity is 34.5 in the MOB. To the contrary, other years (i.e. 1977, 1981, 1983 and 1988), the mean salinity reduced to 30.5 shows the significant freshwater contributions to the bay. Elsewhere, particularly in the mediterranean region, oyster breeding water conditions characterized by high salinity values show the freshwater does not seem to be necessary for biological functions of the Pacific oyster Crassostrea gigas. Indeed, the oyster embryonic life in particular is well adapted to high salinity values as long as trophic resources are substantial and temperatures remain high. These two factors firstly condition the embryonic survival before the water salinity. Besides, in the Pertuis Charentais, wind conditions and the geographical bloodstock position rather determine the success of the larvae capture than seawater physic-chemical conditions. Finally, a misunderstanding still remains on summer freshwater contributions to the oyster larvae food supply.

Citotoxicidade da associação de agrotóxicos da rizicultura em hepatócitos de Zebrafish

No plantio do arroz parte de um corpo d’água (rio, lago, lagoa) é desviado para a irrigação da plantação, e, posteriormente, a água utilizada nas lavouras é devolvida ao rio/lago/lagoa de origem. Assim, seja por lixiviação ou por qualquer outro fator, a água entra em contato com os agrotóxicos que, anteriormente, foram utilizados na plantação, podendo causar danos à qualidade do recurso hídrico e à fauna lacustre, devido à exposição a estes poluentes. O presente trabalho teve por objetivo verificar a citotoxicidade de agrotóxicos (herbicida e inseticida), utilizados na rizicultura no estado do Rio Grande do Sul, em células hepáticas da linhagem ZF-L. A partir da análise de funcionalidade de três alvos celulares diferentes, integridade da membrana celular, estabilidade lisossomal e atividade mitocondrial frente à exposição ao Roundup Transorb® , ao Furadan 350 SC® e à associação destes produtos. Foi analisada ainda, a capacidade de defesa das células, expostas aos poluentes escolhidos, no que diz respeito à atividade de proteínas extrusoras de xenobióticos, assim como à expressão de tais proteínas. A partir dos resultados obtidos foi verificado efeito citotóxico de ambos os agrotóxicos, bem como a mistura destes para todos os alvos verificados, apresentando ainda efeito inibitório à atividade de extrusão de xenobióticos pelas glicoproteínas P (P-gps). Apenas quando expostas ao inseticida e à mistura as células apresentaram um aumento na expressão de glicoproteínas (P-gp). Verificou-se a existência de correlação negativa entre a citotoxicidade apresentada, principalmente na atividade mitocondrial e na integridade lisossomo e a atividade das P-gps. Em conclusão, percebeu-se que as concentrações abaixo do permitido pela legislação brasileira, para os princípios ativos dos agrotóxicos testados, mostraram-se tóxicas para todos os alvos de citotoxicidade testados neste estudo, com exceção da mitocôndria, sugerindo que esta toxicidade apresentada pode ser devido aos surfactantes presentes nas formulações comerciais.

Vegetables production in NW Portugal, agriculture practices and groundwater quality

In NW of Portugal, the region between Esposende and Vila do Conde was established into a unique system called masseiras; masseiras are small fields that were created at the beginning of XX century by removing sand from dunes. Since the 80’s sand between closed masseiras has been removed giving way for larger fields, the “enlarged masseira with greenhouses”. This region is part of vulnerable zone nº1 (VZ1). Nowadays, the masseiras have almost disappeared; they had been replaced by “enlarged masseiras with plastic greenhouses” exploited by a new generation of growers. As water quality is an indicator of agriculture practices, 8 wells were selected and water samples were collected on four dates from September 2009 to May 2010. Laboratorial analysis was performed on nitrates and 28 pesticides. The results confirm that water in VZ1 is contaminated with nitrates (as it was expected) and also with pesticides. The water was contaminated in both dug wells and drilled wells all year round. Masseiras’ wells have more nitrates than greenhouses’ wells, probably due to poor agricultural practices used by growers who still employ high quantities of fertilizers and water. Pesticides detected in water samples include some that have been sprayed in the field and others that have not. Some forbidden substances were found. Our results confirm that, in VZ1, there is a diffusion contamination, which origin is unknown. In this communication, we put in picture the history of masseiras fields: how masseiras fields have been created and how they have disappeared; what trends exist in pest management strategies and the use of fertilizers, pesticides and water resources. These results reinforce the need to change the agricultural system in this region of traditional vegetable production.

Multi-residue analysis of 39 pesticides in surface waters of Ria de Aveiro

A multi-residue gas chromatography-mass spectrometry method was developed in order to evaluate the presence of 39 pesticides of different chemical families (organophosphorus, triazines, imidazole, organochlorine), as well as some of their transformation products, in surface water samples from Ria de Aveiro. Ria de Aveiro is an estuarine coastal lagoon, located in the northern west region of Portugal, which receives inputs from agriculture, urban and industrial activities. The analytical method was developed and validated according international guidelines and showed good linearity, with correlation coefficients higher than 0.9949 for all compounds, adequate precision and accuracy, and high sensitivity. Pesticides were chosen from the priority pollutants list of the Directive 2008/105/EC of the European Parliament and of the Council (on environmental quality standards in the field of water policy), or were selected due their common use in agricultural practices. Some of these 39 pesticides are, or are suspected to be, endocrine disruptor compounds (EDCs), being capable of altering the endocrine system of wildlife and humans, causing form malfunction and ultimately health problems. Even those pesticides which are not EDCs, are known to be awfully toxic and have a recognised impact in human health. The aquatic environment is particularly susceptible to pollution due to intentional and accidental release of chemicals to water [3]. Pesticide contamination of surface water is a national issue as it is often used as drinking water. This concern is especially important in rural agricultural areas where population uses small private water supplies, regularly without any laboratory surveillance. The study was performed in seven sampling points and the results showed a considerable concern pesticide contamination of all samples.

Development of gene expression-based biomarkers of exposure to metals and pesticides in the freshwater amphipod Hyalella azteca

Ecological risk assessment (ERA) is a framework for monitoring risks of exposure and adverse effects of environmental stressors to populations or communities of interest. One tool of ERA is the biomarker, which is a characteristic of an organism that reliably indicates exposure to or effects of a stressor like chemical pollution. Traditional biomarkers which rely on characteristics at the tissue level and higher often detect only acute exposures to stressors. Sensitive molecular biomarkers may detect lower stressor levels than traditional biomarkers, which helps inform risk mitigation and restoration efforts before populations and communities are irreversibly affected. In this study I developed gene expression-based molecular biomarkers of exposure to metals and insecticides in the model toxicological freshwater amphipod Hyalella azteca. My goals were to not only create sensitive molecular biomarkers for these chemicals, but also to show the utility and versatility of H. azteca in molecular studies for toxicology and risk assessment. I sequenced and assembled the H. azteca transcriptome to identify reference and stress-response gene transcripts suitable for expression monitoring. I exposed H. azteca to sub-lethal concentrations of metals (cadmium and copper) and insecticides (DDT, permethrin, and imidacloprid). Reference genes used to create normalization factors were determined for each exposure using the programs BestKeeper, GeNorm, and NormFinder. Both metals increased expression of a nuclear transcription factor (Cnc), an ABC transporter (Mrp4), and a heat shock protein (Hsp90), giving evidence of general metal exposure signature. Cadmium uniquely increased expression of a DNA repair protein (Rad51) and increased Mrp4 expression more than copper (7-fold increase compared to 2-fold increase). Together these may be unique biomarkers distinguishing cadmium and copper exposures. DDT increased expression of Hsp90, Mrp4, and the immune response gene Lgbp. Permethrin increased expression of a cytochrome P450 (Cyp2j2) and decreased expression of the immune response gene Lectin-1. Imidacloprid did not affect gene expression. Unique biomarkers were seen for DDT and permethrin, but the genes studied were not sensitive enough to detect imidacloprid at the levels used here. I demonstrated that gene expression in H. azteca detects specific chemical exposures at sub-lethal concentrations, making expression monitoring using this amphipod a useful and sensitive biomarker for risk assessment of chemical exposure.

Processos Oxidativos Avançados para Remediação de Águas Contaminadas por Pesticidas

Este trabalho teve como objectivo inicial o estudo de processos oxidativos avançados de forma a remediar e tratar águas contaminadas por pesticidas. No entanto, ao longo do trabalho experimental, constatou-se que os produtos resultantes da degradação de pesticidas são muitas vezes mais tóxicos do que os compostos que lhes deram origem e que, por isso, degradar um composto nem sempre é o melhor para o ambiente. Assim, neste trabalho, procurou-se estudar o processo de degradação com o objectivo de minimizar o impacto ambiental dos pesticidas na água e no ambiente em geral. A parte experimental deste trabalho foi dividida em duas etapas, sendo que, em ambas, a voltametria de onda quadrada e a espectrofotometria de UV/Vis foram os métodos de análise utilizados, para acompanhar o processo de fotodegradação. Na primeira etapa estudou-se a relação entre a estrutura química dos pesticidas MCPA, MCPP, 2.4-D e Dicloroprop e a sua fotodegradação. Soluções aquosas dos pesticidas enunciados foram submetidas a irradiação UV/vis, com incrementos variáveis de tempo de irradiação. Os resultados obtidos, nesta etapa, permitiram constatar diferenças na percentagem de degradação dos diferentes pesticidas. Dos pesticidas estudados verificou-se uma maior fotodegradação para o MCPA e MCPP seguido do Dicloroprop e finalmente o 2.4-D que se degradou menos. Os dados obtidos sugerem que a fotodegradação destes pesticidas está intimamente ligada com a estrutura das moléculas. A presença de um maior número de grupos cloro ligados ao anel aromático nos pesticidas 2,4-D e Dicloroprop faz com que estes sejam mais estáveis e por isso se degradam menos que o MCPA e o MCPP. Por outro lado, o facto de o 2,4-D apresentar um potencial de oxidação mais elevado do que o Dicloroprop, faz com que este seja mais difícil de degradar, o que justifica a diferença entre os dois. Desta forma, foi possível concluir que a estrutura dos pesticidas condiciona o processo de degradação, como esperado. Na segunda etapa, estudou-se a estabilização dos pesticidas MCPA e MCPP após encapsulação, com 2-hidroxipropil-β-ciclodextrina (HP-β-CD), em água desionizada e em água do rio. Para tal, submeteram-se as soluções aquosas dos pesticidas com e sem ciclodextrina, a irradiação UV/vis, também com incrementos variáveis de tempo. No caso do MCPA verificou-se que, tanto para água desionizada como para água do rio, que este herbicida encapsulado se degrada bastante menos do que o MCPA livre. O encapsulamento permitiu reduzir quase para metade a taxa de fotodegradação. Assim, confirmou-se que a HP-β-CD permite estabilizar este pesticida, tornando-o mais resistente à fotodegradação. Desta forma, originam-se menos produtos de degradação, os quais podem ser mais tóxicos, e reduz-se de o impacto ambiental deste herbicida. Verificou-se também que o MCPA livre se degrada mais em água do rio do que em água desionizada, provavelmente devido à matéria orgânica presente nesta água, que promove o processo de degradação. No que respeita ao MCPP também se constatou que este herbicida se degrada menos encapsulado do que livre, em água desionizada e em água do rio. Neste caso, conseguiu-se reduzir pouco a taxa de fotodegradação, mas, ainda assim se verifica uma estabilização deste pesticida através do encapsulamento. No entanto, tornou-se mais evidente a estabilização do MCPP após encapsulação em água do rio, já que apresenta uma taxa de fotodegradação menor. Este facto demonstra que a HP-β-CD permite estabilizar também este pesticida, tornando-o mais resistente à fotodegradação, e reduzindo seu impacto ambiental.