L’utilisation du chlordécone (CLD) pour éradiquer les populations de charançon noir dans les bananeraies des Antilles françaises (Guadeloupe et Martinique) entre 1972 et 1993 a conduit à la contamination des sols et de l’environnement. Cet insecticide organochloré très hydrophobe persiste dans les sols d’où il transfère lentement vers les ressources en eau et vers les biotes terrestre et aquatique (plantes, animaux, poissons, crustacées). Réputé « indégradable », le CLD résiste à la photolyse, à l’hydrolyse et à la biodégradation. A ce jour, il n’existe pas de méthode pour remédier les 20 000 hectares de sols pollués avec cet insecticide. Compte-tenu de l’étendue de la pollution avec le CLD, les procédés biologiques de décontamination paraissent appropriés au contexte antillais. Les objectifs de mon travail de thèse étaient d’explorer les possibilités de transformation microbienne du CLD et l’impact écotoxicologique du CLD sur la communauté microbienne des sols. Mes travaux reposent sur l’hypothèse selon laquelle des populations microbiennes exposées de manière chronique au CLD se seraient adaptées à sa dégradation pour détoxifier leur environnement ou éventuellement pour l’utiliser comme source d’énergie pour leur croissance. Pour cela, j’ai développé une méthode d’analyse du CLD dans les sols et les cultures microbiennes basée sur l’isotopie stable. J’ai conduit des expériences d’enrichissement à partir de sols de Guadeloupe pollués avec le CLD. Une centaine de souches fongiques et près de 200 souches bactériennes ont été isolées. Aucunes souches bactériennes dégradantes n’ont pu être mises en évidence bien que certaines formaient un halo de dissolution du CLD sur milieu gélosé. Parmi les isolats fongiques, seul F. oxysporum sp. MIAE01197 se développait sur un milieu minéral contenant le CLD comme seul source de carbone et dissipait 40% du CLD. Cet isolat était deux fois plus tolérant au CLD qu’un isolat de référence jamais exposé au CLD. Cet isolat minéralisait très peu le 14C-CLD, formait très peu de 14C-métabolites, mais le 14C-CLD s’adsorbait sur les parois fongiques, suggérant que l’adsorption était le principal mécanisme impliqué dans la dissipation du CLD. L’analyse de trois autres isolats appartenant au genre Aspergillus a confirmé que l’exposition au CLD était un des paramètres améliorant la tolérance des souches fongiques au CLD et que la biomasse fongique était capable d’adsorber le CLD dans des proportions proches de celles obtenues avec du charbon actif utilisé pour traiter l’eau potable aux Antilles. L’évaluation de l’impact écotoxicologique du CLD sur la communauté microbienne et les fonctions qu’elle supporte a été menée sur deux sols aux propriétés physicochimiques contrastées n’ayant jamais été exposés au CLD. L’analyse de la structure globale (évaluée par RISA), de l’abondance et de l’activité de la communauté microbienne du sol argilo-limoneux n’étaient pas affectées par le CLD. En revanche, la composition taxonomique (qPCR) et l’activité respiratoire de la communauté microbienne étaient affectées par le CLD dans le sol sableux. Ces résultats montrent que la toxicité du CLD pour la communauté microbienne dépend des propriétés physicochimiques du sol qui conditionne sa biodisponibilité. Des études complémentaires devront être menées pour évaluer la toxicité possible du CLD sur des fonctions écosystémiques des sols des Antilles. / The use of chlordecone (CLD) to eradicate the weevil populations in the banana plantations in the French West Indies (Guadeloupe and Martinique) between 1972 and 1993 led to the contamination of the soil and the environment. This very hydrophobic organochlorine insecticide persists in the soil where it slowly transfers not only to the water resources but also to terrestrial and aquatic biota (plants, animals, fishes, shellfishes). Deemed “non-degradable”, CLD is resistant to photolysis, hydrolysis and biodegradation. To date, there is no method to remediate the 20,000 hectares of polluted soil with this insecticide. Given the extent of CLD pollution, biological decontamination processes appear appropriate to the Caribbean context. The objectives of my thesis were to explore the possibilities of microbial transformation of CLD and to assess the ecotoxicological impact of CLD on the soil microbial community. My work is based on the hypothesis that microbial populations chronically exposed to CLD would be adapted to its degradation to detoxify their environment or possibly for use as an energy source for growth.To do so, I developed an analysis method in soils and microbial cultures based on the use of stable isotope to trace CLD. I conducted enrichment experiments with CLD polluted soils from Guadeloupe yielding in the isolation of one hundred fungal strains and nearly two hundred bacterial strains. No degrading bacterial strains have been identified although few of them formed dissolution halo of CLD on solid media. Among the fungal isolates, only F. oxysporum sp. MIAE01197 grew on a mineral medium containing CLD as sole carbon source and dissipated 40% of the CLD. This isolate was twice more tolerant than the reference isolate which had never been exposed to CLD. This isolate mineralizes 14C-CLD very lowly, formed very few 14C-metabolites, but the 14C-CLD was adsorbed on the fungal cell walls, suggesting that the adsorption was the main mechanism involved in the dissipation of the CLD. Analysis of three other isolates belonging to the genus Aspergillus confirmed that exposure to CLD was one of the parameters improving the tolerance of fungal strains to CLD and fungal biomass was capable of adsorbing the CLD in proportions close to those obtained with activated carbon used to treat drinking water in the French West Indies.The assessment of the CLD ecotoxicological impact on the microbial community and functions it supports was carried out on two soils never exposed to CLD showing contrasting physicochemical properties. The analysis of the overall structure (evaluated by RISA), the abundance and the activity of the microbial community of the silty-clay soil were not affected by the CLD. However, the taxonomic composition (evaluated by group specific qPCR) and respiratory activity of the microbial community were affected by the CLD in the sandy soil. These results showed that the toxicity of CLD for microbial community depends on the physicochemical properties of the soil which may determine its bioavailability. Further studies are needed to evaluate the possible toxicity of the CLD on Caribbean soil ecosystemic functions.

The city of Falun has a rich history of mining with the open mine, Stora Stöten, centrally located in the city and nowadays a well-known world heritage tourist attraction. The mine is the main reason that Falun even exists. During its glory days, Falun was one of Sweden’s largest cities, at that time considered to be world-leading in mine engineering and Europe’s main supplier of copper.  A less flattering effect of the mining era was that the city became poisonous and almost unhabitable. Both waters from the mine and from piles of mining waste ended up in rivers and lakes around Falun. Over the years several successful actions have been taken to improve and restore the environment which has decreased the amount of heavy metals leaked into Faluån and lake Tisken. Though, the water is still polluted, and Tisken has in practice for a long period of time worked as a deposit with an increasing amount of poisonous sediments.  This has unfortunately made Falun central waterbodies disabled for human use and made humans no longer have a relationship to the water despite its central location, importance, and potential for the city.  This thesis project seeks to unlock the lost potential of water in Falun by reviving it as a living and interweaved spine in the city in a systematic and schematic approach. The project aims to address the polluted water and sediment challenges while promoting sustainable stormwater and flooding management. A connected green structure linked with a movement network for pedestrians and bicyclists promotes sustainable transport to the spine and existing nodes in the city. The different layers in the project enable new nodes with new potentials for Falun

Two plant species including Polygonum hydropiper L. and Hymenachne acutigluma (Steud.) Gilliland were investigated in their resistance to lead (Pb) and cadmium (Cd) pollution in the soil. Lead-contaminated soil samples were collected from the lead recycling village Dong Mai, Chi Dao commune, Van Lam district, Hung Yen province, Vietnam that had Pb level up to 192,185 mg.kg-1, dry weight (DW). Cadmium-contaminated soil samples were due to supplement of CdCl2.21/2H2O to alluvial soil. Results showed that both species were highly resistant to Pb, however P.hydropiper was better. Similarly, the Cd resistance was higher for P.hydropiper than for H.acutigluma. No morpho-abnormalities of P.hydropiper regarding the impact of lead were recorded, whereas for H.acutigluma, the young leaves had white colour after two months of planting in soil containing lead levels of 192,185 mg.kg-1. The response of both species with Cd in soils included yellowing leaves, withering branches and even dying after 5-15 days exposed to Cd. Lead contents accumulated in above-ground parts of both plants were up to 4,650 and 3,161 mg.kg-1, DW, corresponding to P.hydropiper and H.acutigluma. From the research results on lead resistance and accumulation of two plant species studied, it is suggested that the two species are lead hyperaccumulators can be used for phytoremediation technology to clean contaminated soil. / Hai loài thực vật gồm nghể răm Polygonum hydropiper L. và bấc nhọn Hymenachne acutigluma (Steud.) Gilliland được nghiên cứu về khả năng chống chịu ô nhiễm chì (Pb) và cadmi (Cd) trong đất. Mẫu đất ô nhiễm chì được thu từ làng nghề tái chế chì Đông Mai, xã Chỉ Đạo, huyện Văn Lâm, tỉnh Hưng Yên, Việt Nam có hàm lượng chì lên đến 192.185 mg.kg-1, tính theo trọng lượng khô (DW). Mẫu đất ô nhiễm Cd là do được bổ sung CdCl2.21/2H2O vào đất phù sa. Kết quả cho thấy cả hai loài đều có sức chống chịu chì rất cao, tuy nhiên nghể răm có khả năng tốt hơn. Tương tự như vậy, sức chống chịu Cd của nghể răm cũng cao hơn của bấc nhọn. Không có dấu hiệu bất thường nào của nghể răm đối với tác động của chì được ghi nhận, trong khi ở bấc nhọn thì lá non có màu trắng sau hai tháng trồng trên đất có hàm lượng chì 192.185 mg.kg-1. Phản ứng của cả hai loài thực vật với Cd trong đất gồm có hiện tượng vàng lá, héo ngọn và thậm chí chết sau 5-15 ngày phơi nhiễm với Cd. Hàm lượng chì được tích lũy cao trong phần trên mặt đất của cả hai loài thực vật lên tới 4.650 và 3.161 mg.kg-1, DW, tương ứng cho loài P.hydropiper và H.acutigluma. Từ kết quả nghiên cứu về khả năng chống chịu và tích lũy chì của hai loài thực vật nghiên cứu, có thể đề xuất đây là hai loài siêu tích lũy chì có thể sử dụng trong công nghệ làm sạch đất ô nhiễm.

L’attività di ricerca ha previsto il confronto fra due siti inquinati da metalli pesanti e due siti controllo naturali. Contrariamente ai parametri chimico-fisici e ai contenuti in metallo dei suoli, le analisi vegetazionali non hanno evidenziato differenze significative tra i siti. E’ stata necessaria la messa a punto strumentale di tecniche ICP-OES, ED(P)XRF per la calibrazione empirica di un XRF portatile, per le osservazioni puntiformi in situ di suoli e flora ed è stata modificata la metodica ufficiale per le stime della biodisponibilità dei metalli pesanti nei suoli inquinati. 6 specie comuni ai 4 siti sono state valutate per i loro TF e BAF. Viene confermata la specie-specificità del TF e del BAF per il quale è stato elaborato un inedito algoritmo per un corretto confronto tra le specie. Tra le sei specie, Silene Alba ha i migliori TF e BAF. Successivamente, sono state valutate alcune caratteristiche del Pennisetum clandestinum, candidato per la fitodepurazione: tollera le concentrazioni di arseniato tipiche dei suoli inquinati, l’arseniato è un inibitore competitivo del trasporto del fosfato, possiede un’elevata velocità di assorbimento dell’arseniato che accumula nella radice, ma non lo trasloca nella frazione epigea, parte dell’As(V) viene ridotto ad As(III) che viene efflusso dalla radice / The research has provided a comparison between two heavy metals polluted sites and two natural control sites. Unlike physical-chemical parameters and metal content in the soils, vegetation analysis showed no significant differences between sites. The development and optimization of instrumental techniques ICP-OES and ED(P)XRF was necessary to calibrate empirically a portable XRF for soil and flora point observations in situ and the official method for estimation of bioavailability of heavy metals in polluted soil was changed. Six species, common to the four sites, were evaluated for their TF and BAF. Were confirmed the TF and the BAF species-specificity for which it was developed a novel algorithm to obtain a correct comparison among species. Among the six species, Silene Alba has the best TF and BAF. In the second stage, some characteristics of Pennisetum clandestinum, candidate for the phytoremediation, were assessed: it tolerates arsenate concentrations typical of polluted soil, arsenate is a competitive inhibitor of phosphate transport, it has a high uptake rate of arsenic that accumulates in the root, but it doesn’t move in the aboveground fraction and part of As(V) is reduced to As(III), which is efflux from roots.

Este trabajo tiene como objetivo el desarrollo de la metodología de diseño óptimo de procesos de separación con membranas líquidas selectivas en su aplicación a la separación de mezclas multicomponentes con recuperación selectiva del componente de interés. Para ello se ha investigado la separación selectiva y concentración de cromo(VI) presente inicialmente en un acuífero subterráneo contaminado por acción de la actividad industrial desarrollada a nivel superficial y donde a su vez, coexisten otras especies aniónicas competitivas (sulfato y cloruro mayoritariamente) presentes por las propias características del acuífero y por su localización en una zona litoral. Tras la selección de Alamine 336 (amina terciaria) y NaOH como agentes de extracción y reextracción respectivamente, se caracterizaron experimentalmente las reacciones químicas responsables de la etapa de extracción, así como la cinética del proceso de separación-concentración cuando se emplea la tecnología de pertracción en emulsión (EPT) en contactores de fibra hueca. Finalmente, se desarrolló un modelo matemático multicomponente y se determinaron los parámetros característicos del mismo con el fin de llevar a cabo el diseño óptimo del proceso mediante técnicas de optimización matemática. / This work aims at the development of the methodology for the optimal design of selective liquid membrane processes as efficient alternatives for the separation and selective recovery of raw materials and valuable compounds from multicomponent systems. For this purpose, the proposed methodology has been applied to the remediation of polluted groundwater containing hexavalent chromium as a consequence of effluent leaking from surface deposition of industrial wastes. Furthermore, other competitive anionic species (mainly sulphate and chloride anions) were also present in the groundwaters due to the specific location being close to the shore.After selecting Alamine 336 (tertiary amine) and NaOH as the best extraction and back-extraction agents respectively, a careful experimental design was performed in order to analyse the chemical equilibria involved in the extraction step. Once the emulsion pertraction technology (EPT) was selected as the most suitable separation-concentration process configuration, the experimental kinetic analysis and mathematical modeling of EPT were carried calculating the values of the design parameters. Finally, the proposed multicomponent model was employed to carry out the optimal process design by means of mathematical optimization techniques.

The chemical contamination of natural waters is a global problem with a worldwide impact. Considering the relevance of this problem, this thesis is intended, on one hand, to develop different separation/preconcentration techniques based on membranes ability to permeate anions for the transport of toxic oxyanions of chromium(VI) and arsenic contained in aqueous matrices. In particular, we have investigated supported liquid membranes and polymer inclusion membranes, both of which contain the commercial quaternary ammonium salt Aliquat 336 as a carrier, as well as commercial anion exchange membranes. On the other hand, we have focused on the development of chemical sensors to facilitate the monitoring of several metals from different aqueous matrices. Thus, a selective optical sensor for Cr(VI) based on polymeric membranes containing Aliquat 336 as an ionophore has been designed. Additionally, mercury-based screen-printed electrodes have been evaluated for for cadmium, lead, copper and zinc detection. / La contaminació química de les aigües naturals és un problema global amb repercussió a nivell mundial. Donada la rellevància que té aquesta problemàtica, en la present tesi s’han desenvolupat d’una banda tècniques de separació/preconcentració basades en diferents sistemes de membrana en què el mecanisme de transport proposat és un bescanvi aniònic per als oxoanions tòxics de crom(VI) i arsènic presents en matrius aquoses. Concretament, s’ha treballat amb membranes líquides suportades que contenien el portador comercial Aliquat 336, membranes d’inclusió polimèriques amb el mateix portador i membranes de bescanvi aniònic comercials. D’altra banda, s’ha treballat en el desenvolupament de diferents sensors químics per monitoritzar diversos metalls presents en matrius aquoses. Així, s’ha dissenyat un sistema de sensor òptic selectiu a Cr(VI) basat en membranes polimèriques utilitzant també el portador Aliquat 336 i s’ha desenvolupat un sistema de monitorització per plom, coure, cadmi i zinc basat en microelèctrodes serigrafiats modificats amb mercuri.

Until recently, organic particulate material was simply classified as either primary or secondary with the primary component being treated in models as nonvolatile and inert. This framework is used to simulate the organic aerosol formation, growth and composition in the eastern United States during the four seasons of the year. The model predictions are evaluated against daily average PM2.5 (particulate matter smaller than 2.5 μm) measurements taken throughout the eastern United States by the Interagency Monitoring of Protected Visual Environments (IMPROVE) and the Speciation Trends Network (STN) monitoring networks. The performance of the model in reproducing organic mass concentrations is average during all four seasons of the year. The agreement between the predicted and observed temporal profiles suggests a reasonable understanding and depiction in the model of the corresponding processes. However, this oversimplified view fails to explain the observed highly oxygenated nature of ambient organic aerosols (OA), the relatively small OA concentration gradients between large urban areas and their surroundings, and the concentrations of OA during periods of high photochemical activity. To address the above issues new primary and secondary organic aerosol modules have been added to a three dimensional chemical transport model (PMCAMx) based on recent smog chamber studies. The new modeling framework is based on the volatility basis-set approach: both primary and secondary organic components are assumed to be semivolatile and photochemically reactive and are distributed in logarithmically spaced volatility bins. The resulting PMCAMx-2008 was applied in Mexico City Metropolitan Area (MCMA) for approximately a week during April of 2003. The model predictions are compared with Aerosol Mass Spectrometry (AMS) observations and their Positive Matrix Factorization (PMF) analysis. The final goal of this work is to provide information to the policy makers regarding the response of fine PM to emission controls. PMCAMx is used to investigate changes in PM2.5 concentrations in response to 50% emissions changes of oxides of nitrogen and anthropogenic volatile organic compounds during July 2001 and January 2002 in the Eastern United States. / Τα ατμοσφαιρικά οργανικά σωματίδια συνηθίζεται να χωρίζονται σε δυο κατηγορίες: πρωτογενή και δευτερογενή. Τα πρώτα εκπέμπονται κατευθείαν στην ατμόσφαιρα ενώ τα δευτερογενή δημιουργούνται με την μεταφορά μάζας αερίων χαμηλής πτητικότητας, που προκύπτουν από την οξείδωση πρωτογενών οργανικών αερίων, στα ατμοσφαιρικά σωματίδια. Ένα τρισδιάστατο χημικό μοντέλο (PMCAMx), βασιζόμενο σε αυτό το διαχωρισμό, χρησιμοποιήθηκε για την προσομοίωση της σύνθεσης και της μάζας των οργανικών σωματιδίων της ατμόσφαιρας, στις ανατολικές Ηνωμένες Πολιτείες της Αμερικής κατά τη διάρκεια των τεσσάρων εποχών του χρόνου. Οι προβλέψεις του μοντέλου αξιολογήθηκαν έναντι μετρήσεων που πραγματοποιήθηκαν από τα δίκτυα παρακολούθησης IMPROVE και STN στις ανατολικές ΗΠΑ. Η απόδοση του μοντέλου, όσον αφορά τον προσδιορισμό της συγκέντρωσης των οργανικών ενώσεων κατά τη διάρκεια όλων των εποχών είναι ιδιαίτερα ικανοποιητική. Ωστόσο, αν και οι προβλέψεις του μοντέλου για τη συγκέντρωση της οργανικής μάζας είναι ενθαρρυντικές, δεν είναι ξεκάθαρο εάν το μοντέλο προβλέπει τις σωστές τιμές για τους σωστούς λόγους. Συγκεκριμένα το μοντέλο δεν μπορεί να εξηγήσει την πολύ οξυγονωμένη χημική μορφή των ατμοσφαιρικών οργανικών σωματιδίων όπως αυτή αποτυπώθηκε σε μετρήσεις πεδίου. Για να αντιμετωπιστούν τα ανωτέρω ζητήματα αναπτύσσουμε μια νέα μέθοδο προσομοίωσης των διεργασιών σχηματισμού και χημικής γήρανσης των πρωτογενών και δευτερογενών οργανικών σωματιδίων της ατμόσφαιρας, στο τρισδιάστατο χημικό μοντέλο PMCAMx βασιζόμενοι σε πρόσφατα πειραματικά δεδομένα. Στο νέο αυτό πλαίσιο μοντελοποίησης τόσο τα πρωτογενή, όσο και τα δευτερογενή οργανικά συστατικά θεωρούνται ότι είναι ημιπτητικά και φωτοχημικά ενεργά και κατανέμονται λογαριθμικά σε ομάδες ενώσεων διαφορετικής πτητικότητας. Το βελτιωμένο PMCAMx (PMCAMx-2008) έχει εφαρμοστεί στην ευρύτερη περιοχή της πόλης του Μεξικού για περίπου μια βδομάδα τον Απρίλιο του 2003. Οι προβλέψεις του μοντέλου συγκρίνονται με μετρήσεις φασματογράφου μάζας αεροζόλ και άλλες μετρήσεις που πραγματοποιήθηκαν κατά τη διάρκεια της καμπάνιας MCMA-2003. Τέλος το PMCAMx έχει χρησιμοποιηθεί για να μελετηθούν διεξοδικά οι αλλαγές στη συγκέντρωση των οργανικών σωματιδίων διαμέτρου έως 2.5 μm που προκύπτουν από αλλαγές των εκπομπών NOx και VOCs κατά τη διάρκεια των μηνών του Ιουλίου 2001 και του Ιανουαρίου 2002 στις ανατολικές Ηνωμένες Πολιτείες της Αμερικής.

A relação existente entre os habitantes e a cidade em que vivem está intimamente ligada à forma de utilização do espaço urbano. Atualmente, nas grandes metrópoles, estamos assistindo uma situação bastante preocupante, onde esta utilização do espaço urbano vendo sendo traduzida em poluição visual. Neste contexto, a problemática da poluição visual é muito nova e ainda muito vinculada às leis de zoneamento e leis de aplicação da publicidade no espaço urbano, que são específicas para cada localidade e não levam em consideração a complexidade das relações inerentes ao fenômeno. A poluição visual carece até de uma definição precisa. O que é poluição visual? A tônica desta dissertação de mestrado é analisar um ambiente poluído através de seu levantamento histórico e iconográfico. O local utilizado como exemplo será uma rua da capital paulista, a 25 de março, onde encontraremos realidade dinâmica rica em detalhes históricos, culturais, sociais, econômicos e políticos. / The relation between the citizens and the city they live is inner connected with the way they use the urban space. Nowadays, in the big cities, we are experiencing a very worried situation, when the urban space is being translated in visual pollution. In this context, the visual pollution problematic is very new and it is connected with city laws and advertising application policies in public spaces, which are specific to each place and do not consider the complexity relations that surround the phenomena. The visual pollution don\'t have a precise definition. What is visual pollution? This dissertation tonic is to analyze a polluted environment through your historic and iconographic development. The site used as an example will be a street located in São Paulo capital, 25 de março street, where we will find a dynamic reality, rich in historic, cultural, economic and politic details.

Dans un contexte où les préoccupations environnement-santé sont croissantes à l’échelle globale. Améliorer la compréhension des mécanismes de biodisponibilité et d’(éco)toxicité des polluants métalliques persistants est un enjeu prioritaire, notamment en raison de leur omniprésence observée dans les écosystèmes en relation avec leur compartimentation et spéciation . Le ver de terre est utilisé pour évaluer la qualité des sols ; de plus cet organisme du sol de par ses activités de bioturbation a une influence sur les cycles biogéochimiques. Des tests d’écotoxicité en conditions contrôlées sur vers de terre ont donc été réalisés avec différents sols et espèces de vers. Puis une étude d’impact sur les communautés de vers a été effectuée sur un site pollué présentant un gradient de concentration. L’influence de la bioturbation du ver sur la phytodisponibilité des polluants a été étudiée grâce à des expériences en mésocosmes. Finalement, des mesures de bioaccessibilité des polluants ont été réalisées in vitro sur des sols et végétaux pollués dans différents contextes : friches industrielles, jardins potagers, terrain de sport. L’objectif étant d’étudier le lien entre biodisponibilité pour l’homme, caractéristiques des sols et contexte de pollution. Deux approches complémentaires ont été développées : recherche scientifique liés aux mécanismes et développement d’outils, de procédures pratiques utilisables par les gestionnaires et évaluateurs de risques. L’écotoxicité des métaux et métalloïdes (notés ETM) sur les vers de terre n’est pas simplement régie par leurs concentrations totales, mais dépend fortement des caractéristiques physico-chimiques des sols. Par ailleurs, l’analyse des communautés de ver de terre présentes sur un site contaminé permet d’évaluer la qualité des sols puisqu’on constate un impact sur les l’abondance, la diversité et le taux de juvénile des vers. De plus, la bioturbation du ver de terre augmente significativement la biodisponibilité des ETM pour les plantes potagères telles que la laitue. Finalement, la bioaccessibilité humaine des ETM est régi par de nombreux facteurs liés en particulier au contexte de pollution. Cette fraction bioaccessible des ETM est directement responsable de leur cytotoxicité sur les cellules intestinales. Ces différents résultats ont été complétés par des études mécanistiques (IR, EXAFS, XANES, µ-XRF). / In a context where environmental health concerns are globally increasing. Improve understanding of the mechanisms and bioavailability (eco) toxicity of persistent metals pollutants is a priority, especially because of their observed omnipresence in ecosystems in relation to their compartmentation and speciation. The earthworm is used to assess soil quality; moreover this soil organism through its bioturbation activities affects biogeochemical cycles. Ecotoxicity tests under controlled circumstances on earthworms have been conducted with different soils and worms’ species. Then an impact study on earthworms’ communities was conducted on a polluted site showing a concentration gradient. The influence of earthworms’ bioturbation on phytoavailability of pollutants was studied through experiments in mesocosms and Rhizotest. Finally, in vitro measures of pollutants bioavailability were performed on polluted soils and plants in different contexts: brownfields, gardens, sports field. The objective is to study the link between bioavailability for humans, soil characteristics, context of pollution and toxicity. Two complementary approaches have been developed: scientific research related to the mechanisms and development of tools, practical procedures which could be used by managers and risk assessors. Ecotoxicity of metals and metalloid (denoted ETM) on earthworms is not simply governed by their total concentrations, but strongly depends on the physico-chemical characteristics of soils. Furthermore, analysis of earthworm communities from a contaminated site can evaluate the quality of soil since seen an impact on the abundance, diversity and rate of juvenile worms. In addition, earthworms’ bioturbation significantly increases the bioavailability of ETM for vegetable plants such as lettuce. Finally, the human bioaccessibility of ETM is governed by many factors, in particular the context of pollution. The bioaccessible fraction of ETM is directly responsible for their cytotoxicity on intestinal cells. These results were complemented by mechanistic studies (IR, EXAFS, XANES, μ-XRF).

A relação existente entre os habitantes e a cidade em que vivem está intimamente ligada à forma de utilização do espaço urbano. Atualmente, nas grandes metrópoles, estamos assistindo uma situação bastante preocupante, onde esta utilização do espaço urbano vendo sendo traduzida em poluição visual. Neste contexto, a problemática da poluição visual é muito nova e ainda muito vinculada às leis de zoneamento e leis de aplicação da publicidade no espaço urbano, que são específicas para cada localidade e não levam em consideração a complexidade das relações inerentes ao fenômeno. A poluição visual carece até de uma definição precisa. O que é poluição visual? A tônica desta dissertação de mestrado é analisar um ambiente poluído através de seu levantamento histórico e iconográfico. O local utilizado como exemplo será uma rua da capital paulista, a 25 de março, onde encontraremos realidade dinâmica rica em detalhes históricos, culturais, sociais, econômicos e políticos. / The relation between the citizens and the city they live is inner connected with the way they use the urban space. Nowadays, in the big cities, we are experiencing a very worried situation, when the urban space is being translated in visual pollution. In this context, the visual pollution problematic is very new and it is connected with city laws and advertising application policies in public spaces, which are specific to each place and do not consider the complexity relations that surround the phenomena. The visual pollution don\'t have a precise definition. What is visual pollution? This dissertation tonic is to analyze a polluted environment through your historic and iconographic development. The site used as an example will be a street located in São Paulo capital, 25 de março street, where we will find a dynamic reality, rich in historic, cultural, economic and politic details.