Dissertationen zum Thema „Metal tolerant“
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Mullins, M. „Subcellular localization of metals in metal tolerant higher plants“. Thesis, University of Liverpool, 1987. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.384378.
Der volle Inhalt der QuelleLees, Fiona M. „Studies on metal-tolerant estuarine algae“. Thesis, Heriot-Watt University, 1985. http://hdl.handle.net/10399/1620.
Der volle Inhalt der QuelleDuggan, Sam B. „Complex metal mixture reduces apparent protein carbonylation in a tolerant aquatic macroinvertebrate, Arctopsyche grandis“. Thesis, Colorado State University, 2016. http://pqdtopen.proquest.com/#viewpdf?dispub=1606539.
Der volle Inhalt der QuelleMining is widespread and an economically important industry. Unfortunately, acid mine drainage (AMD) can pollute ecosystems with a cocktail of contaminants too complex for accurately forecasting its health consequences. However, through quantification of fundamental toxic events, the effects of complex mixtures can be observed. This project explored two potentially insightful and convenient endpoints. First, oxygen consumption (MO2), a well-established and sensitive indicator of respiratory impairment was utilized. Second, protein carbonyl content (PCC), an experimental ecological biomarker widely lauded in biomedical circles as a highly conserved indicator of health status was assessed for its utility in a metal tolerant aquatic macroinvertebrate, Arctopsyche grandis. A. grandis were exposed to eight environmentally relevant target concentrations (in duplicate) of AMD for eight days at a temperature controlled greenhouse containing artificial flow-through streams. As expected, MO2 was inversely related to treatment concentration (R 2=0.35, p=0.015). Protein carbonyl content, however, diverged from predictions. Protein carbonyl content analysis detected significantly more oxidative protein injury in control treatments than in metal-rich AMD treatments (p<0.001). Moreover, there was not a significant difference in PCC between different AMD concentrations. Protein carbonyl content’s departure from anticipated results likely is the consequence of dynamic interactions between direct and indirect effects at the chemical, biochemical, physiologic and behavioral levels. The results of this project illustrate flaws of utilizing a single biochemical marker to observe effects of a toxic mixture. Rather, a broad suite of biomarkers should be assayed to determine sublethal toxicity. These results also illustrates how multiple stressors can yield unanticipated outcomes.
Yadav, Krishna Kant. „Studies on the molecular physiology of bio-film formation in metal tolerant bacteria- Acinetobacter junii BB1A (Acc.no.LMG 22734)“. Thesis, University of North Bengal, 2013. http://ir.nbu.ac.in/hdl.handle.net/123456789/1515.
Der volle Inhalt der QuelleGokul, Arun. „Impact of vanadium stress on physiological and biochemical characteristics in heavy metal susceptible and tolerant Brassicaceae“. University of the Western Cape, 2013. http://hdl.handle.net/11394/3582.
Der volle Inhalt der QuelleMagister Scientiae - MSc
Choudhary, Aarti. „A process variation tolerant self compensation sense amplifier design“. Connect to this title, 2008. http://scholarworks.umass.edu/theses/166/.
Der volle Inhalt der QuelleMahlatsi, Tladi Abram. „Characterization of heavy metal tolerant bacterial plasmids isolated from a platinum mine tailings dam / by Tladi Abram Mahlatsi“. Thesis, North-West University, 2012. http://hdl.handle.net/10394/9780.
Der volle Inhalt der QuelleThesis (Master of Environmental Sciences)--North-West University, Potchefstroom Campus, 2013.
Hannemann, Benedikt [Verfasser], Ulf Paul [Akademischer Betreuer] Breuer, Gerhard [Akademischer Betreuer] Scharr und Frank [Akademischer Betreuer] Balle. „Multifunctional metal-carbon-fibre composites for damage tolerant and electrically conductive lightweight structures / Benedikt Hannemann ; Ulf Paul Breuer, Gerhard Scharr, Frank Balle“. Kaiserslautern : Technische Universität Kaiserslautern, 2017. http://d-nb.info/1159569517/34.
Der volle Inhalt der QuelleJeffery, Casey Miles. „Performance analysis of dynamic sparing and error correction techniques for fault tolerance in nanoscale memory structures“. [Gainesville, Fla.] : University of Florida, 2004. http://purl.fcla.edu/fcla/etd/UFE0007163.
Der volle Inhalt der QuelleKraemer, Ute. „Nickel hyperaccumulation in the genus Alyssum L“. Thesis, University of Oxford, 1996. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.318487.
Der volle Inhalt der QuelleLakzian, Amir. „Diversity and metal tolerance of Rhizobium leguminosarum bv. viciae in soils contaminated with heavy metals“. Thesis, Imperial College London, 1998. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.287779.
Der volle Inhalt der QuelleLazkian, Amir. „Diversity and metal tolerance of Rhizobium Leguminosarum BV. Viciae in soil contaminated with heavy metals“. Thesis, Imperial College London, 1998. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.300781.
Der volle Inhalt der QuellePhilipson, Andrew Neil. „Metal binding properties of bacteria from metal polluted soils“. Thesis, University of Newcastle Upon Tyne, 2000. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.327323.
Der volle Inhalt der QuelleDan, Tereza Violeta. „Phytoremediation of metal contaminated soils, metal tolerance and metal accumulation in Pelargonium sp“. Thesis, National Library of Canada = Bibliothèque nationale du Canada, 2001. http://www.collectionscanada.ca/obj/s4/f2/dsk3/ftp04/NQ58302.pdf.
Der volle Inhalt der QuellePhelan, Anne. „Heavy metal tolerance in Aspergillus nidulans“. Thesis, University of Liverpool, 1991. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.333642.
Der volle Inhalt der QuelleKumar, S. „Studies on metal tolerance in plants“. Thesis(Ph.D.), CSIR-National Chemical Laboratory, Pune, 2008. http://dspace.ncl.res.in:8080/xmlui/handle/20.500.12252/2711.
Der volle Inhalt der QuelleMahmood, Shafaat. „An investigation of the sensitivity of cyanobacterial lichens to heavy metals and the induction of metal tolerance“. Thesis, University of Bristol, 1997. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.389336.
Der volle Inhalt der QuelleDragana, Tamindžija. „Isolation and characterization of Cr(VI) tolerant soil bacteria“. Phd thesis, Univerzitet u Novom Sadu, Prirodno-matematički fakultet u Novom Sadu, 2019. https://www.cris.uns.ac.rs/record.jsf?recordId=110336&source=NDLTD&language=en.
Der volle Inhalt der QuelleU ovom radu ispitana je tolerantnost zemljišnih bakterija na šestovalentni hrom (Cr(VI)). Prvo, ispitan je uticaj visokog nivoa hroma antropogenog i geogenog porekla na kultivabilnu bakterijsku zajednicu zemljišta. Dalje, izolovani su bakterijski sojevi sa visokom tolerancijom na Cr(VI) iz različitih sredinskih uzoraka kao što su zemljište, sediment, voda i otpadni materijal. Sojevi su identifikovani i određen je nivo njihove Cr(VI) tolerancije i sposobnost redukcije toksičnog Cr(VI) u manje toksični Cr(III). Odabrani sojevi Bacillus cereus grupe su dalje karakterisani – određene su njihove morfološke i biohemijske karakteristike, 16S rDNK i pycA sekvence, potencijal formiranja biofilma i otpornost na druge teške metale. Takođe, sprovedeno je detaljnije ispitivanje njihove tolerancije i redukcije Cr(VI). Soj sa najvišom otpornošću je uporedo sa kontrolnim osetljivim sojem analiziran pomoću STEM EDS na sadržaj hroma u ćelijama I endosporama u različitim uslovima. Rezultati ukazuju da su bakterije tolerantne na Cr(VI) prisutne i u sredinama sa niskim i sa visokim koncentracijama hroma. Većina izolata pripadala je B. cereus grupi što ukazuje na njenu uopšteno visoku otpornost na Cr(VI). Pojedini sojevi su pokazali visoku otpornost i sposobnost redukcije Cr(VI), što ukazuje na mogućnost njihove praktične primene u bioremedijaciji. STEM EDS analiza osetljivog B. subtilis PY79 soja i Cr(VI)- rezistentnog soja B. cereus grupe NCr1a otkrila je značajne razlike u njihovom odgovoru na Cr(VI) i sadržaju Cr u njihovim ćelijama i endosporama.
MacDonald, Hazel. „Heavy metal tolerance in filamentous green algae“. Thesis, University of the West of Scotland, 1989. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.329824.
Der volle Inhalt der QuelleTurner, Andrew Paul. „The tolerance of trees to metal pollution“. Thesis, Liverpool John Moores University, 1991. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.304542.
Der volle Inhalt der QuelleAelst, Sébastien van. „Etude fonctionnelle des gènes plasmidiques de résistance au cuivre de Cupriavidus metallidurans: aspects physiologique, biochimique et écologique“. Doctoral thesis, Universite Libre de Bruxelles, 2008. http://hdl.handle.net/2013/ULB-DIPOT:oai:dipot.ulb.ac.be:2013/210529.
Der volle Inhalt der QuelleOn distingue dans l’îlot cop des gènes codant pour des fonctions de résistance proprement dite (essentiellement par détoxication active du cytoplasme et du périplasme). En effet, les mutants de copSRABCD, copF, et dans une moindre mesure copJ et copE deviennent sensibles. Les phénotypes des mutants divergent toutefois suivant que la mutation soit sur un cosmide qui ne porte que l’îlot (pMOL1024) ou dans son plasmide d’origine (pMOL30). Un second groupe de mutants (copVTMK, copG, copL, copQ) se distingue par un phénotype plus résistant ou identique à la souche parente, sauf autour de la CMI. Ces gènes interviendraient donc à la CMI pour assurer la résistance la plus élevée et le maintien d'un état viable latent.
La présence de l’îlot cop permet de contenir le taux d’oxygène radicalaire qui reste à un taux basal lorsque les cellules sont adaptées au cuivre environnent. Après un choc de Cu (ou stress aigu), l’îlot cop répond de façon « explosive » au stress, en consommant l’énergie du potentiel membranaire et en augmentant fortement l’activité de la chaîne respiratoire.
La résistance au cuivre est inductible, mais de façon différenciée pour la souche sauvage (CH34) et celle qui ne porte qu l’îlot cop (AE1744) :la CMI de CH34 triple après adaptation au cuivre, alors que celle d’AE1744 est inchangée. Après un choc de Cu, la résistance au cuivre est plus fortement induite pour AE1744 que pour CH34. Ces observations suggèrent que l’îlot cop ait été sélectionné pour sa capacité à répondre à un stress aigu puis intégré dans un ensemble de gènes plus vaste qui répond à des impératifs de stress chronique.
L’analyse biochimique de CopI, une petite protéine bleue à cuivre, montre qu’elle porte un site analogue à celui des oxydases multicuivre. Son rôle pourrait dès lors être celui d’une réductase multicuivre. La protéine CopK lie de façon très spécifique le Cu(I) et il semble que la liaison du cuivre modifie sa structure. L’analyse écologique a montré que des homologues de copK pourraient être présents dans l’ADN extrait de la terre de biotopes chargés en cuivre, et dans les souches cuprorésistantes qu’on y trouve.
La contribution majeure de cette thèse est de montrer que l’effet d’un stress métallique ne se résume pas à deux états physiologiques « mort ou vif ». Il y a lieu de considérer des états transitoires (choc de Cu, adaptation au métal, survie autour de la CMI, persistance) où interviennent des gènes spécifiques dans un ou plusieurs états donnés. Les résultats biochimiques et physiologiques ne nous éclairent pas encore assez sur les interconversions Cu(I)/Cu(II) ni sur les flux de cations notamment vers l'espace extracellulaire. Cette thèse ouvre des perspectives sur des mécanismes (protection à la CMI, phénotype persistant) assurant la survie des bactéries ou leur potentiel de recolonisation lors d'une diminution de la pression toxique :les gènes copT, copV, copK, copM, copB, copG, copL et copQ semblent impliqués dans ces fonctions.
Doctorat en Sciences agronomiques et ingénierie biologique
info:eu-repo/semantics/nonPublished
Pati, Nishikanta Guturu Parthasarathy. „Occlusion tolerant object recognition methods for video surveillance and tracking of moving civilian vehicles“. [Denton, Tex.] : University of North Texas, 2007. http://digital.library.unt.edu/permalink/meta-dc-5133.
Der volle Inhalt der QuelleBleackley, Mark Robert. „Transition metal tolerance and the Saccharomyces cerevisiae genome“. Thesis, University of British Columbia, 2011. http://hdl.handle.net/2429/30821.
Der volle Inhalt der QuelleLowell, Christina, und Christina Lowell. „Thermo-acidophilic Algae: pH and Metal Tolerances“. Thesis, University of Oregon, 2012. http://hdl.handle.net/1794/12361.
Der volle Inhalt der QuelleWatmough, Shaun A. „Adaptation to pollution stress in trees : metal tolerance traits“. Thesis, Liverpool John Moores University, 1994. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.260825.
Der volle Inhalt der QuelleSewell, Andrew Kelvin. „The mechanism of heavy metal tolerance in higher plants“. Thesis, University of Liverpool, 1990. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.333676.
Der volle Inhalt der QuelleAnderson, Craig. „Mechanistic bases of metal tolerance : linking phenotype to genotype“. Thesis, Cardiff University, 2012. http://orca.cf.ac.uk/43776/.
Der volle Inhalt der QuelleJobling, M. G. „Physical and genetic analysis of heavy metal resistance plasmids“. Thesis, University of Liverpool, 1985. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.372683.
Der volle Inhalt der QuelleIvorra, i. Castellà Núria. „Metal induced succession in benthic diatom consortia“. [S.l. : Amsterdam : s.n.] ; Universiteit van Amsterdam [Host], 2000. http://dare.uva.nl/document/56237.
Der volle Inhalt der QuelleAl-Hiyaly, Sedik A. K. „Evolution of zinc tolerance under electricity pylons“. Thesis, University of Liverpool, 1989. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.257133.
Der volle Inhalt der QuelleHughes, Ruth. „Serpentine tolerance in the Mimulus guttatus complex“. Thesis, University of Exeter, 1999. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.286489.
Der volle Inhalt der QuelleFiore, Marli de Fatima. „Isolation of Brazilian Amazon cyanobacteria and further characterization for metal tolerance“. Thesis, National Library of Canada = Bibliothèque nationale du Canada, 2000. http://www.collectionscanada.ca/obj/s4/f2/dsk1/tape2/PQDD_0017/NQ55624.pdf.
Der volle Inhalt der QuelleWalker, Paul L. „Genotypic and phenotypic aspects of metal tolerance in Holcus lanatus L“. Thesis, University of Sheffield, 1990. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.284588.
Der volle Inhalt der QuelleCooley, R. N. „Studies of nitrate assimilation and heavy metal tolerance in Aspergillus nidulans“. Thesis, University of Liverpool, 1986. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.372691.
Der volle Inhalt der QuelleSiriwardena, P. P. G. S. N. „Tolerance and early life stages of Tilapia (Cichlidae:Tilapiini) to metal stress“. Thesis, University of Stirling, 1993. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.384838.
Der volle Inhalt der QuelleHarper, Frances Anne. „The cost of copper tolerance in Mimulus guttatus“. Thesis, University of Exeter, 1996. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.307278.
Der volle Inhalt der QuelleDechamps, Caroline. „Biologie des populations de Thlaspi caerulescens: étendue et structuration de la variation génétique et de la plasticité phénotypique de populations métallicoles et non métallicoles“. Doctoral thesis, Universite Libre de Bruxelles, 2008. http://hdl.handle.net/2013/ULB-DIPOT:oai:dipot.ulb.ac.be:2013/210522.
Der volle Inhalt der QuelleTrois expériences ont étudié les variations des traits d’histoire de vie des populations M et NM: (1) une culture en conditions contrôlées des populations sur un gradient de concentrations en Zn, (2) une expérience de transplantation réciproque in situ de populations M et NM et (3) un suivi démographique dans les populations M et NM. Enfin, une quatrième expérience (4) visait à évaluer les variations entre populations M et NM d’un trait particulier :la plasticité du système racinaire en réponse à une distribution hétérogène des métaux dans le sol.
Nos résultats montrent que les plantes M ont, en moyenne, des cycles de vie plus courts que les plantes NM (exp. 1, 3). Par ailleurs, les populations M sont capables de modifier leur stratégie de reproduction en fonction des teneurs en métaux dans le sol ou du site de transplantation (métallifère vs. non métallifère). Que ce soit sur des substrats non contaminés en Zn (exp. 1) ou sur des sites non métallifères (exp. 2), les plantes M produisent autant de graines au cours de leur vie que les plantes NM. Ces résultats suggèrent l’absence d’un coût adaptatif fort chez les plantes M. In situ (exp. 3), nous avons mis en évidence un effet structurant de l’hétérogénéité spatiale des sites métallifères sur les stratégies de vie des plantes M. Enfin, les plantes M ont exprimé une plasticité plus élevée du comportement d’exploration racinaire que les plantes NM (exp. 4).
L’existence de stratégies de vie plastiques, l’homéostasie de la fitness sur une large gamme de concentrations en Zn, ainsi que le faible coût adaptatif mis en évidence chez les populations M suggèrent que ces populations sont plus aptes à fonder de nouvelles populations que les populations NM. Nos résultats ont également clairement démontré que les populations M sont caractérisées par une plasticité plus élevée que les populations NM (génotype généraliste). Cette plasticité concerne à la fois les stratégies de vie et les mécanismes d’exploration racinaire. Cette plasticité élevée des plantes M a très probablement évolué en réponse à l’hétérogénéité spatiale des sites métallifères La sélection de génotypes généralistes sur les sites métallifères est une piste de recherche qui mérite, à présent, d’être approfondie chez les autres espèces colonisant les sites métallifères.
Doctorat en Sciences
info:eu-repo/semantics/nonPublished
Thompson, Jill. „Population biology of Anthoxanthum odoratum, Plantago lanceolata and Rumex acetosa on zinc and lead mine spoil“. Thesis, University of Liverpool, 1987. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.329462.
Der volle Inhalt der QuelleWhitebrook, J. „Heavy metal tolerance and the distribution in SW Britain of the diploid and tetraploid cytotypes of Leucanthemum vulgare Lam. (Compositae)“. Thesis, University of Bristol, 1986. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.372036.
Der volle Inhalt der QuellePiola, Richard Fabio Biological Earth & Environmental Sciences Faculty of Science UNSW. „Differential tolerance of introduced & native marine invertebrates to heavy metal pollution“. Publisher:University of New South Wales. Biological, Earth & Environmental Sciences, 2007. http://handle.unsw.edu.au/1959.4/40673.
Der volle Inhalt der QuellePires, Carlos. „Bacteria in heavy metal contaminated soil : diversity, tolerance and use in remediation“. Thesis, Cranfield University, 2010. http://dspace.lib.cranfield.ac.uk/handle/1826/5581.
Der volle Inhalt der QuelleTilstone, Gavin H. „The significance of multiple metal tolerance in Mimulus guttatus Fischer ex DC“. Thesis, University of Exeter, 1996. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.337730.
Der volle Inhalt der QuelleChang, Po-Yu. „Modeling of fatigue behavior and damage tolerance/durability in fiber metal laminates“. Diss., Restricted to subscribing institutions, 2008. http://proquest.umi.com/pqdweb?did=1608577901&sid=1&Fmt=2&clientId=1564&RQT=309&VName=PQD.
Der volle Inhalt der QuelleFasola, Emanuele. „Acquisition and inheritance of tolerance to metals in anurans“. Doctoral thesis, Universidade de Aveiro, 2017. http://hdl.handle.net/10773/22226.
Der volle Inhalt der QuelleOs anfíbios encontram-se em declínio a nível global, sendo a contaminação química um dos principais fatores associados a este declínio. De facto, a exposição de populações de anfíbios a este tipo de perturbações ambientais pode provocar a perda de diversidade genética, devido à diminuição de: 1) aptidão, 2) plasticidade ambiental e 3) eficácia dos mecanismos de tolerância. A contaminação por metais é uma das causas de poluição mais comum no mundo, estando presente em larga escala na Península Ibérica, nomeadamente na Faixa Piritosa Ibérica. Deste modo o estudo dos mecanismos de tolerância a metais, em anfíbios, é relevante, assim como a investigação sobre os mecanismos de hereditariedade desta tolerância. Um dos objetivos do presente trabalho centrou-se no estudo da hereditariedade de tolerância a metais em ovos de Pelophylax perezi. Os resultados obtidos sugerem uma dominância genética incompleta como sendo o mecanismo mais provável de hereditariedade de tolerância a contaminação por metais, em ovos de P. perezi. Estes resultados suportam a hipótese de hereditariedade de tolerância recessiva (ou dominância incompleta). Neste contexto, uma perda de diversidade genética em populações de anfíbios, expostas a contaminação por metais pode ocorrer, mesmo que a fixação de alelos na população seja excluída. De modo a estudar a possibilidade de girinos adquirirem maior tolerância a contaminação por metais, devido à sua exposição histórica a este tipo de contaminação, foram recolhidos girinos de P. perezi em locais contaminados por metais e em locais de referência. Posteriormente, os girinos foram expostos, em laboratório, a um pulso de contaminação intensa por metais. Os girinos oriundos de locais contaminados não mostraram maior tolerância à toxicidade letal de metais comparativamente aos girinos recolhidos em locais de referência. Mais ainda, não revelaram estar sujeitos a um maior stress oxidativo. No entanto, a quantidade de metais no corpo provou a contaminação por metais nos locais historicamente impactados e mostrou que os iões de mercúrio e chumbo são prontamente biodisponíveis para os girinos de P. perezi. Os girinos de locais contaminados apresentaram níveis constitutivos de metalotioneínas, superiores aos medidos nos girinos recolhido os nos locais de referência, o que pode indicar adaptação a contaminação por metais. Por fim, o último objetivo consistiu em avaliar a influência de contaminação química na composição e diversidade do microbioma da pele de populações de P. perezi bem como, identificar a sua sensibilidade a contaminação por efluentes de drenagem ácida. O microbioma da pele dos anfíbios apresenta um papel fundamental na proteção destes organismos a agentes perturbadores ambientais. Os resultados obtidos revelaram que os metais podem influenciar a composição da comunidade microbiana de anfíbios que habitam locais contaminados. Mais ainda, uma concentração elevada de efluente de drenagem mineira inibiu o crescimento da maioria dos isolados de bactérias da pele dos anfíbios. Esta inibição pode sugerir que os anfíbios perdem uma fração importante do seu microbioma e consequentemente, afetar a proteção da sua pele, quando expostos a contaminação por metais, o que pode determinar um aumento da sensibilidade a este tipo de contaminação.
Amphibians are declining globally, chemical contamination being one of the major factors driving this process. As a consequence of exposure to such environmental perturbation, natural population of amphibians may lose their genetic diversity, which may occur due to a decrease in: 1) fitness, 2) environmental plasticity capabilities and 3) tolerance mechanisms efficiency. Metal contamination is one of the most worldwide distributed contamination source, having a great impact in the Iberian Peninsula habitats, especially in the Iberian pyrite belt region. Therefore, is important to explore how tolerance mechanism, toward metal contamination, work in amphibians and how genetically determined tolerance mechanisms are inherited. In this work, these topics were addressed by assessing the inheritance to lethal tolerance to acid mine drainage and copper contamination in eggs of the Perez's frog Pelophylax perezi. Incomplete dominance was found to be the most likely inheritance mechanism of tolerance toward these two chemical stressors in the eggs of P. perezi. The results support the recessive (or incompletely dominant) tolerance inheritance (working-) hypothesis. Thus, the amphibians’ populations impacted by metal contamination can considerably lower their genetic diversity, even if allele fixation was excluded. The possibility of tadpoles, historically exposed to metal contamination, being able to acquire an increased tolerance to metal contamination, comparatively to tadpoles inhabiting reference sites, was also studied. Pelophylax perezi tadpoles, sampled at historically metal impacted mining sites, did not show higher oxidative stress or lethal tolerance comparatively to tadpoles inhabiting reference sites. However, the metal body burden proved metal contamination at the historically metal impacted sites and showed that mercury and lead ions are readily bioavailable for P. perezi tadpoles. Furthermore, tadpoles from metal contaminated sites seem to show higher constitutive levels of metallothioneins, which may suggest adaptation to metal contamination The last objective of this work, was to evaluate the influence, of metal contamination, on the composition and diversity of the P. perezi skin microbiome, and to explore its tolerance to acid mine drainage contamination. Amphibians’ skin microbial community has been shown to help its hosts tolerating infections. Because the increasing research on the important protective role of amphibians’ skin microbiome, its diversity and capacity to tolerate metal contamination was as well investigated. Obtained results showed that metal contamination influences the skin microbial community composition in frogs living at metal impacted sites; furthermore, an intense acid mine drainage concentration can inhibit the growth of almost all the isolated strains. This inhibition suggests that amphibians may lose an important part of their skin microbiome, affecting the protection of their skin, when exposed to metal contamination; which, in turn may lead to an increased sensitivity to metal contamination.
Johnson, Dallas W. „Metal tolerance, survival characteristics and nodulating abilities of isolates of Rhizobium leguminosarum biovar trifolii from Sudbury reclaimed, metal-contaminated soils“. Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1997. http://www.collectionscanada.ca/obj/s4/f2/dsk2/tape16/PQDD_0004/MQ31441.pdf.
Der volle Inhalt der QuelleRibeiro, Manuella Nóbrega Dourado. „Burkholderia sp. cadmium tolerance mechanism and its influence in phytoremediation“. Universidade de São Paulo, 2013. http://www.teses.usp.br/teses/disponiveis/11/11151/tde-17122013-144639/.
Der volle Inhalt der QuelleO cádmio (Cd) tem contaminado solos pelo uso de fertilizantes, calcário, agrotóxicos e resíduos industriais e/ou domésticos. Podendo ser lixiviado ao lençol freático ou absorvido pelas plantas,resultando na redução do crescimento e da produtividade. Esse metal afeta todos os organismos vivos e causa diferentes danos às células. A tolerância a esse metal se deve principalmente ao balanço do estado redox da célula para manter a integridade celular e metabolismo.Assim, foram isoladas bactérias de solo contaminado e não contaminado com Cd, selecionando isolados tolerantes a altas concentrações de diferentes metais (Cd, Ni e Zn), em seguida, foi observado a resposta do sistema antioxidante da bactéria na presença do Cd, a fim de auxiliar no desenvolvimento de metodologias para biorremediar solos contaminados. Foi quantificado MDA e peróxido de hidrogênio e a atividade de diferentes enzimas do sistema antioxidante (SOD, CAT, GR e GST) de duas estirpes do gênero Burkholderia tolerantes a todos os metais testados, uma isolada do solo contaminado com altas concentrações de Cd (estirpe SCMS54) e a outra do solo sem Cd (estirpe SNMS32) em dois tempos de exposição (5 e 12 h). Na estirpe SCMS54, as medidas de estresse (peroxidação lipídica e peróxido de hidrogênio) e a atividade das enzimas antioxidantes (SOD, CAT, GR e GST) da maioria dos tratamento com cádmio aumentaram, esta estirpe também expressa mais isoformas de SOD, CAT e GR, além de acumular 50% mais Cd. Esses resultados mostram que a estirpe SCMS54 (isolada do solo contaminado com Cd) apresenta uma maior diversidade metabólica e plasticidade. Foram analisadas também a resposta dessas duas estirpes ao Ni, observando uma resposta semelhante ao Cd, exceto na expressão da enzima GST, que no estirpe SCMS54 foi induzida na presença do Ni, indicando que essa enzima pode ser essencial na tolerância ao Ni. Portanto, a estirpe isoladado solo contaminado com Cd (SCMS54) foi selecionada para prosseguir os estudos e avaliar os benefícios da interação entre microrganismos tolerantes-plantas de tomate na fitorremediação. Essa técnica é usada remover para metais pesados do solo com um menor impacto e baixos custos. Os microrganismos do solo podem solubilizar e mobilizar metais do solo, atuando como biorremediador. Além da alta tolerância ao Cd, a estirpe SCMS54 produz ácido indol acético (AIA), solubiliza fosfato inorgânico e produz sideroforo, mostrando seu potencial na interação benéfica planta-microorganismo. Quando interagindo com as plantas de tomate expostas ao Cd, essa bactéria diminui a concentração de peróxido da planta e a clorose ocasionado pelo Cd,e reduz a absorção de Cd pela raiz resultando em um aumento da tolerância da planta ao metal pesado altamente tóxico. Assim, a inoculação de plantas de tomate com Burkholderia sp. SCMS54 promove crescimento da planta na presença de Cd, desencadeando um mecanismo que diminui a concentração de Cd nas raízes devido a essa interação benéfica bactéria-raiz da planta.
Lock, S. J. „Water-tolerant organometallic reactions : nucleophilic additions to carbonyl compounds using allyl metals in aqueous solution“. Thesis, Swansea University, 2003. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.637942.
Der volle Inhalt der QuelleNyberg, Berglund Anna-Britt. „Postglacial colonization and parallel evolution of metal tolerance in the polyploid Cerastium alpinum /“. Uppsala : Dept. of Plant Biology and Forest Genetics, Swedish University of Agricultural Sciences, 2005. http://epsilon.slu.se/200565.pdf.
Der volle Inhalt der QuelleKachenko, Anthony. „Ecophysiology and phytoremediation potential of heavy metal(Loid) accumulating plants“. Thesis, The University of Sydney, 2008. http://hdl.handle.net/2123/6348.
Der volle Inhalt der QuelleKachenko, Anthony. „Ecophysiology and phytoremediation potential of heavy metal(Loid) accumulating plants“. University of Sydney, 2008. http://hdl.handle.net/2123/6348.
Der volle Inhalt der QuelleSoil contamination with heavy metal(loid)s is a major environmental problem that requires effective and affordable remediation technologies. The utilisation of plants to remediate heavy metal(loid)s contaminated soils has attracted considerable interest as a low cost green remediation technology. The process is referred to as phytoremediation, and this versatile technology utilises plants to phytostabilise and/or phytoextract heavy metal(loid)s from contaminated soils, thereby effectively minimising their threat to ecosystem, human and animal health. Plants that can accumulate exceptionally high concentrations of heavy metal(loid)s into above-ground biomass are referred to as hyperaccumulators, and may be exploited in phytoremediation, geobotanical prospecting and/or phytomining of low-grade ore bodies. Despite the apparent tangible benefits of utilising phytoremediation techniques, a greater understanding is required to comprehend the ecophysiological aspects of species suitable for phytoremediation purposes. A screening study was instigated to assess phytoremediation potential of several fern species for soils contaminated with cadmium (Cd), chromium (Cr), copper (Cu), nickel (Ni), lead (Pb) and zinc (Zn). Hyperaccumulation was not observed in any of the studied species, and in general, species excluded heavy metal uptake by restricting their translocation into aboveground biomass. Nephrolepis cordifolia and Hypolepis muelleri were identified as possible candidates in phytostabilisation of Cu-, Pb-, Ni- or Zn-contaminated soils and Dennstaedtia davallioides appeared favourable for use in phytostabilisation of Cu- and Zn-contaminated soils. Conversely, Blechnum nudum, B. cartilagineum, Doodia aspera and Calochlaena dubia were least tolerant to most heavy metals and were classified as being least suitable for phytoremediation purposes Ensuing studies addressed the physiology of arsenic (As) hyperaccumulation in a lesser known hyperaccumulator, Pityrogramma calomelanos var. austroamericana. The phytoremediation potential of this species was compared with that of the well known As hyperaccumulator Pteris vittata. Arsenic concentration of 3,008 mg kg–1 dry weight (DW) occurred in P. calomelanos var. austroamericana fronds when exposed to 50 mg kg–1 As without visual symptoms of phytotoxicities. Conversely, P. vittata was able to hyperaccumulate 10,753 mg As kg–1 DW when exposed to 100 mg kg–1 As without the onset of phytotoxicities. In P. calomelanos var. austroamericana, As was readily translocated to fronds with concentrations 75 times greater in fronds than in roots. This species has the potential for use in phytoremediation of soils with As levels up to 50 mg kg–1. Localisation and spatial distribution of As in P. calomelanos var. austroamericana pinnule and stipe tissues was investigated using micro-proton induced X-ray emission spectrometry (µ-PIXE). Freeze-drying and freeze-substitution protocols (using tetrahydrofuran [THF] as a freeze-substitution medium) were compared to ascertain their usefulness in tissue preservation. Micro-PIXE results indicated that pinnule sections prepared by freeze-drying adequately preserved the spatial elemental distribution and tissue structure of pinnule samples. In pinnules, µ-PIXE results indicated higher As concentration than in stipe tissues, with concentrations of 3,700 and 1,600 mg As kg–1 DW, respectively. In pinnules, a clear pattern of cellular localisation was not resolved whereas vascular bundles in stipe tissues contained the highest As concentration (2,000 mg As kg–1 DW). Building on these µ-PIXE results, the chemical speciation of As in P. calomelanos var. austroamericana was determined using micro-focused X-ray fluorescence (µ-XRF) spectroscopy in conjunction with micro-focused X-ray absorption near edge structure (µ-XANES) spectroscopy. The results suggested that arsenate (AsV) absorbed by roots was reduced to arsenite (AsIII) in roots prior to transport through vascular tissues as AsV and AsIII. In pinnules, AsIII was the predominant species, presumably as aqueous-oxygen coordinated compounds. Linear least-squares combination fits of µ-XANES spectra showed AsIII as the predominant component in all tissues sampled. The results also revealed that sulphur containing thiolates may, in part sequester accumulated As. The final aspect of this thesis examined several ecophysiological strategies of Ni hyperaccumulation in Hybanthus floribundus subsp. floribundus, a native Australian perennial shrub species and promising candidate in phytoremediation of Ni-contaminated soils. Micro-PIXE analysis revealed that cellular structure in leaf tissues prepared by freeze-drying was adequately preserved as compared to THF freeze-substituted tissues. Elemental distribution maps of leaves showed that Ni was preferentially localised in the adaxial epidermal tissues and leaf margin, with concentration of 10,000 kg–1 DW in both regions. Nickel concentrations in stem tissues obtained by µ-PIXE analysis were lower than in the leaf tissues (1,800 mg kg–1 vs. 7,800 mg kg–1 DW, respectively), and there was no clear pattern of compartmentalisation across different anatomical regions. It is possible that storage of accumulated Ni in epidermal tissues may provide Ni tolerance to this species, and may further act as a deterrent against herbivory and pathogenic attack. In H. floribundus subsp. floribundus seeds, µ-PIXE analysis did not resolve a clear pattern of Ni compartmentalisation and suggests that Ni was able to move apoplastically within the seed tissues. The role of organic acids and free amino acids (low molecular weight ligands [LMW]) in Ni detoxification in H. floribundus subsp. floribundus were quantified using high performance liquid chromatography (HPLC) and ultra performance liquid chromatography (UPLC). Nickel accumulation stimulated a significant increase in citric acid concentration in leaf extracts, and based on the molar ratios of Ni to citric acid (1.3:1–1.7:1), citric acid was sufficient to account for approximately 50% of the accumulated Ni. Glutamine, alanine and aspartic acid concentrations were also stimulated in response to Ni hyperaccumulation and accounted for up to 75% of the total free amino acid concentration in leaf extracts. Together, these LMW ligands may complex with accumulated Ni and contribute to its detoxification and storage in this hyperaccumulator species. Lastly, the hypothesis that hyperaccumulation of Ni in certain plants may act as an osmoticum under water stress (drought) was tested in context of H. floribundus subsp. floribundus. A 38% decline in water potential and a 68% decline in osmotic potential occurred between water stressed and unstressed plants, however, this was not matched by an increase in accumulated Ni. The results suggested that Ni was unlikely to play a role in osmotic adjustment in this species. Drought stressed plants exhibited a low water use efficiency which might be a conservative ecophysiological strategy enabling survival of this species in competitive water-limited environments.