Depuis le début de l'industrialisation, de nombreux déchets contaminés en éléments métalliques et métalloïdes sont rejetés dans l'environnement sans aucune gestion. L’activité minière a généré des quantités colossales de déchets, fins et non consolidés, riches en EMM stockés sous forme de terrils ou entreposés dans des bassins de décantation puis laissés à l’abandon à l’air libre sans aucun aménagement ni protection. Ces déchets restent sur place exposés à une forte érosion éolienne et hydriques induisant une dissémination des particules contaminées dans les différents compartiments de l’environnement (sols/sédiments/eau/atmosphère). Dans un premier temps, l’étude du devenir des éléments métalliques et métalloïdes dans les sols contaminés relatif à l’activité minière ont mis en évidence la présence de risques environnementaux et sanitaires associés. Les résultats soulignent que (i) le comportement géochimique des trois éléments (cadmium, zinc et plomb) est différent, (ii) la spéciation de ces éléments change clairement entre les déchets miniers et les sols, (iii) le Pb plomb peut causer des effets néfastes sur la santé pour les enfants. Dans un second temps, deux techniques de réhabilitation des sites contaminés ont été appréhendées: i) dans le cadre de la refonctionnalisation des sols, la potentialité d’une phytostabilisation assistée par des amendements organique et inorganique de parcelles contaminées avec le sapin de Douglas, ainsi que ii) la valorisation ex-situ par attaque des déchets miniers par voie alcaline qui mets en jeu la réduction de la source de pollution. / Since the beginning of industrialization, many wastes contaminated with metal(loid)shave been released into the environment without any management. Mining has generated huge quantities of fine, unconsolidated waste, rich in metal(loid)s, stored in tailing or in settling ponds and then left to be abandoned in the open air without any development or protection. This waste remains on site exposed to strong wind and water erosion leading to the spread of contaminated particles in the various environmental compartments (soil/sediment/water/atmosphere). First, the study of the fate of metal(loid)s in contaminated soils related to mining activity revealed the presence of associated environmental and health risks. The results highlight that (i) the geochemical behaviour of the three elements (cadmium, zinc and lead) is different, (ii) the speciation of these elements clearly changes between tailings and soils, (iii) Pb lead can cause adverse health effects for children. In a second step, two techniques for the rehabilitation of contaminated sites were apprehended: (i) in the context of soil refunctionalization, the potential for phytostabilization assisted by organic and inorganic amendments of plots contaminated with Douglas fir, as well as (ii) ex-situ recovery by attacking mining waste by alkaline way, which involves reducing the pollution source.

<p>U radu je analiziran&nbsp; uticaj limunske kiseline na morfolo&scaron;ke, fiziolo&scaron;ke i&nbsp; biohemijske<br />karakteristike&nbsp; odabranih&nbsp; klonova&nbsp; vrba&nbsp; (Salix&nbsp; spp.)&nbsp; gajenih&nbsp; u&nbsp; zemlji&scaron;tu&nbsp; umereno zagađenom&nbsp; kadmijumom&nbsp; (Cd).&nbsp; Definisanjem&nbsp; parametara&nbsp; akumulacije,&nbsp; otpornosti&nbsp; i tolerantnosti različitih klonova vrba na prisustvo kadmijuma u podlozi, kao i uspe&scaron;nosti primene&nbsp; limunske&nbsp; kiseline&nbsp; kao&nbsp; helatora&nbsp; u&nbsp; procesu&nbsp; asistirane&nbsp; fitoremedijacije,&nbsp; mogao&nbsp; bi se&nbsp; identifikovati&nbsp; klon&nbsp; (ili&nbsp; klonovi)&nbsp; pogodan&nbsp; za&nbsp; dekontaminaciju&nbsp; zemlji&scaron;ta&nbsp; zagađenog kadmijumom. Da&nbsp; bi&nbsp; se&nbsp; postigao&nbsp; cilj&nbsp; istraživanja biljke su gajene u polu-kontrolisanim uslovima tokom 3 meseca. Eksperiment je podeljen u dve faze (dve godine istraživanja),zasnovane&nbsp; na&nbsp; razlikama&nbsp; u&nbsp; metodolo&scaron;kom&nbsp; pristupu.&nbsp; Tokom&nbsp; prve&nbsp; godine&nbsp; limunska kiselina je dodata jednom, dok je tokom druge druge godine aplikacija ovog helatora vr&scaron;ena&nbsp; u&nbsp; tri&nbsp; ponavljanja.&nbsp; U&nbsp; radu&nbsp; je&nbsp; analizaran&nbsp; sadržaj&nbsp; i&nbsp; distribucija&nbsp; Cd&nbsp; u&nbsp; zemlji&scaron;tu&nbsp; i<br />različitim&nbsp; biljnim&nbsp; organima&nbsp; (koren,&nbsp; izdanak,&nbsp; mladi&nbsp; i&nbsp; stari&nbsp; listovi);&nbsp; uticaj&nbsp; Cd i&nbsp; limunske kiseline na morfometrijske parametre: visina i prečnik izdanka, masa i povr&scaron;ina listova, broj&nbsp; listova,&nbsp; masa&nbsp; i&nbsp; zapremina&nbsp; korena;&nbsp; na&nbsp; fotosintetičke&nbsp; karakteristike:&nbsp; intenzitet fotosinteze,&nbsp; intenzitet&nbsp; transpiracije,&nbsp; stomatalnu&nbsp; provodljivost,&nbsp; intercelularnu koncentraciju&nbsp; CO2,&nbsp; efikasnost&nbsp; kori&scaron;ćenja&nbsp; vode,&nbsp; koncentraciju&nbsp; fotosintetičkih&nbsp; pigmenata; na mineralnu ishranu i distribuciju makronutrijenata u biljkama (sadržaj azota, fosfora i kalijuma);&nbsp; na&nbsp; sadržaj&nbsp; aminokiseline&nbsp; prolina&nbsp; i&nbsp; cisteina;&nbsp; na&nbsp; aktivnost&nbsp; antioksidativnih enzima&nbsp; (katalaza,&nbsp; askorbat-peroksidaza,&nbsp; gvajakol-peroksidaza),&nbsp; kao&nbsp; neezmiskih antioksidanata poput sadržaja redukovanog glutationa i tiola. Dobijeni&nbsp; rezultati&nbsp; su&nbsp; ukazali&nbsp; na&nbsp; genotipsku&nbsp; specifičnost&nbsp; analiziranih&nbsp; klonova&nbsp; vrba&nbsp; u procesu&nbsp; fitoremedijacije&nbsp; u&nbsp; zavisnosti&nbsp; od&nbsp; primenjenog&nbsp; tretmana,&nbsp; doze&nbsp; Cd&nbsp; i&nbsp; prisustva limunske kiseline. Toksično dejstvo nije bilo jasno uočljivo na morfolo&scaron;kom nivou, dok su&nbsp; primenjeni&nbsp; tretmani&nbsp; signifikantno&nbsp; uticali&nbsp; na&nbsp; fiziolo&scaron;ko-biohemijske&nbsp; procese&nbsp; u biljkama.&nbsp; Sa&nbsp; povećanjem&nbsp; sadržaja&nbsp; Cd&nbsp; u&nbsp; biljkama&nbsp; je&nbsp; utvrđena&nbsp; tendencija&nbsp; smanjenja intenziteta fotosinteze, transpiracije, kao i efikasnosti&nbsp; kor&scaron;ćenja vode, dok je primena limunske&nbsp; kiseline&nbsp; ublažila&nbsp; &scaron;tetan&nbsp; efekat&nbsp; ovog&nbsp; te&scaron;kog&nbsp; metala,&nbsp; &scaron;to&nbsp; je&nbsp; registrovano&nbsp; na<br />kombinovanim tretmanima.&nbsp; Kao odgovor na akumulaciju Cd u biljnom tkivu utvrđena<br />je&nbsp; promena&nbsp; aktivnosti&nbsp; antioksidativnih&nbsp; enzima,&nbsp; kao&nbsp; i&nbsp; neezimskih&nbsp; komponenti<br />odbrambenog&nbsp; sistema&nbsp; za&scaron;tite.&nbsp; Pored&nbsp; toga,&nbsp; u&nbsp; radu&nbsp; je&nbsp; utvrđeno&nbsp; da&nbsp; primena&nbsp; limunske kiseline&nbsp; utiče&nbsp; na&nbsp; usvajanje,&nbsp; akumulaciju&nbsp; i&nbsp; toleranciju vrba na prisustvo Cd,&nbsp; te&nbsp; rezultati ove&nbsp; studije&nbsp; imaju&nbsp; praktičan&nbsp; značaj&nbsp; u&nbsp; usavr&scaron;avanju&nbsp; tehnika&nbsp; fitoremedijacije&nbsp; i dekontaminacije zagađenih područja.</p> / <p>The role of citric acid on morphological, physiological and biochemical characteristics of selected willow clones (Salix spp.) grown in soil with moderately polluted cadmium (Cd)&nbsp; was&nbsp; presented.&nbsp; The&nbsp; aim&nbsp; of&nbsp; this&nbsp; study&nbsp; was&nbsp; to&nbsp; determine&nbsp; the&nbsp; Cd&nbsp; accumulation, translocation&nbsp; and tolerance of different willow clones, as well as the influence of citric acid as a chelator in the assisted phytoremediation process.&nbsp; In order to achieve this goal, plants&nbsp; were&nbsp; grown&nbsp; in&nbsp; semi-controlled&nbsp; conditions&nbsp; for&nbsp; 3&nbsp; months.&nbsp; The&nbsp; experiment&nbsp; was divided&nbsp; into&nbsp; two&nbsp; phases&nbsp; (two&nbsp; years&nbsp; of&nbsp; research),&nbsp; based&nbsp; on&nbsp; differences&nbsp; in&nbsp; the methodological approach, regarding the application of citric acid. During the first-year experiment, citric acid was added once, while in the second year the application of this chelator was performed in three repetitions.&nbsp; The analyses included:&nbsp; the accumulation and distribution of Cd in soil and various plant organs (root, stem, young and old leaves); influence of Cd and citric&nbsp; acid on morphometric parameters: stem hight and diameter, number&nbsp; of&nbsp; leaves,&nbsp; biomass&nbsp; and&nbsp; area&nbsp; of&nbsp; leaves,&nbsp; biomass&nbsp; and&nbsp; volume&nbsp; of&nbsp; the&nbsp; root;&nbsp; on&nbsp; photosynthetic&nbsp; characteristics:&nbsp; net&nbsp; photosynthetic&nbsp; and&nbsp; transpiration&nbsp; rate,&nbsp; water&nbsp; use efficiency, stomatal conductance, intercellular concentration of CO2, concentration of photosynthetic&nbsp; pigments;&nbsp; on&nbsp; mineral&nbsp; nutrition&nbsp; and&nbsp; distribution&nbsp; of&nbsp; macronutrients&nbsp; in plants (nitrogen, phosphorus and potassium content); on the content of the amino acid proline&nbsp; and&nbsp; cysteine;&nbsp; on&nbsp; the&nbsp; activity&nbsp; of&nbsp; antioxidant&nbsp; enzymes&nbsp; (catalase,&nbsp; ascorbate peroxidase,&nbsp; guaiacol&nbsp; peroxidase),&nbsp; as&nbsp; non- enzymatic&nbsp; components&nbsp; such&nbsp; as&nbsp; reduced glutathione and thiol content.<br />The obtained results indicated the genotypic specificity of the analyzed willow clones in the phytoremediation process, depending on the treatment applied, the Cd dose, and the presence of&nbsp; citric acid.&nbsp; The toxic effect was not evident on the morphological&nbsp; level, while&nbsp; the&nbsp; applied&nbsp; treatments&nbsp; showed&nbsp; a&nbsp; significant&nbsp; influence&nbsp; on&nbsp; the&nbsp; physiologicalbiochemical processes in the willows. The net photosynthetic rate, transpiration rate, as well as,&nbsp; water use eficiency&nbsp; showed decreasing with increasing Cd concentration in plant tissue,&nbsp; while&nbsp; the&nbsp; application&nbsp; of&nbsp; citric&nbsp; acid&nbsp; mitigated&nbsp; the&nbsp; harmful&nbsp; effect&nbsp; of&nbsp; this&nbsp; heavy metal, which was registered on combined treatments. In response to the accumulation of Cd in plant tissue, a&nbsp; change in the&nbsp; activity&nbsp; of&nbsp; anti-oxidant enzymes,&nbsp; as&nbsp; well as nonenzymatic&nbsp; components&nbsp; of&nbsp; the&nbsp; defense&nbsp; system&nbsp; has&nbsp; been&nbsp; established.&nbsp; In&nbsp; addition,&nbsp; the<br />application of citric acid showed the promotion role on the&nbsp; absorption, accumulation and tolerance of willows grown in moderately polluted soil cadmium, which has a practical significance in the improvement of phytoremediation techniques and decontamination of polluted soil.</p>

Célèbres depuis l'accident de Seveso en 1976, les dioxines/furanes (PCCD/F) restent, malgré une forte baisse de leurs émissions, un sujet de préoccupation permanent en France et dans le monde. Le rémanence de ces composés organochlorés dans le sol et le risque toxique qu'ils représentent pour l'homme et l'environnement font que la gestion et la remédiation des sols contaminés par les PCDD/F sont devenues une priorité des industriels, législateurs et scientifiques. La phytoremédiation compte parmi les méthodes émergentes de dépollution des sols contaminés en raison de son adéquation avec le développement durable. Elle combine les capacités naturelles des plantes et de leur microbiote rhizosphérique à biodégrader les polluants organiques. Cependant, l'efficacité de cette phytotechnologie est encore souvent limitée, en particulier lorsqu'il s'agit de composés chlorés, à cause de leur récalcitrance, de leur phytotoxicité et leur faible biodisponibilité dans le sol. Ainsi, l'objectif de ce travail de thèse a consisté à étudier les performances de la phytoremédition assistée, en particulier par les champignons mycorhiziens arbusculaires, d'un sol agricole historiquement pollué par les PCDD/F prélevé sur une parcelle expérimentale située à proximité d'un ancien incinérateur. L'ensemble des résultats obtenus mettent en évidence, en particulier, le potentiel de deux espèces végétales, la luzerne et la fétuque, dans la rhizodégradation des PCCDD/F. La végétalisation du sol permet de moduler les communautés microbiennes du sol (bactéries, Archées et champignons) et notamment celles qui semblent impliquées dans la dissipation des PCCDD/F. En revanche, bien que la mycorhization agisse sur les communautés microbiennes du sol, celle-ci n'a pas eu d'impact, dans nos conditions expérimentales, sur la dissipation des PCCDD/F quelles que soit l'origine de l'inoculum utilisé et les espèces mycorhiziennes qui le compose. La dégradation de ces composés organochlorés est plus marquée dans un sol préalablement stérilisé, puis recolonisé par certaines communautés microbiennes spécifiques, impliquées dans la dissipation des PCCDD/F. L'utilisation combinée d'un mélange de rhamnolipides avec l'introduction dans le sol d'une bactérie Sphingomonas wittichii RWI, décrite pour ses capacités de dégradation des PCCDD/F, permet d'accroitre l'efficience de la rhizodégradation des PCDD/F qui se traduit par une baisse significative de la cytotoxicité du sol après phytoremédiation. / Famous since the Seveso accident in 1976, dioxins/furans (PCCD/F) remain, despite a sharp decline in emissions, a subject of permanent concern in France and in the world. The remanence of these organochlored compounds in soil and the toxic risk they represent for humans and the environment mean that the management and remediation of PCDD/F contaminated soil has become a priority for industrialists, legislators and scientists. Phytoremediation is one of the emerging depollution methods of contaminated soils due to Its suitability for sustainable development. It combines the natural capacities of plants and their rhizospheric microbiota to biodegrade organic pollutants. However, the effectiveness of this phytotechnology is still often limited, especially in the case of chlorinated compounds, due to their recalcitrance, phytotoxicity and low bioavailability in the soil. Thus, the thesis aims to study the performance of assisted phytoremission, in particular by mycorrhizal fungi, of an agricultural PCDD / F based-polluted soil from an experimental plot near an old incinerator. The results obtained show the potential of two plant species, alfalfa and tall fescue, in the rhizodegradation of PCCDD/F. Soil vegetation shows to modulate soil microbial communities (bacteria, archaea and fungi) includind those that appear to involved in the dissipation of the PCCDD/F. On the other hand, although mycorrhization affects soil microbial communities, it has not had any impact on the dissipation of PCCDD/F in our experimental conditions, whatever the inoculums origin and the mycorrhizal species which compose it. The degradation of these organochlorined compounds is more significant in a previously sterilized soil and then recolonized by specific microbial communities involved in the PCCDD/Fdissipation. The combined use of rhamnolipids mixture and Sphingomonas wittichii RWI bactrerium described for its degradation capabilities of PCCDD/F makes it possible to increase the efficiency of PCDD/F rhizodegradation which results in a significant decrease in soil cytotoxicity after phytoremediation.