P. Des, G. , and P. , 50 TABLEAU 7 : CONSTANTES D'AFFINITES (LOG?) DES COMPLEXES 1 : 1 DE 3, pp.3-50

D. Zamora, M. L. Tracy, B. L. Zielinski, J. M. Meyerhof, D. P. Moss et al., Changes in sleep?wake cycle after chronic exposure to uranium in rats Evaluation of the oral toxicity of uranium in a 4-week drinking-water study in rats Chronic ingestion of uranium in drinking water: a study of kidney bioeffects in humans, TABLEAU 19 : BIODISTRIBUTION ET T 1 ) ET (23) Lestaevel, pp.835-840, 1989.

S. Kurttio, P. Auvinen, A. Salonen, L. Saha, H. Pekkanen et al., Renal effects of uranium in drinking water Grand rounds : nephrotoxicity in a young child exposed to uranium from contaminated well water. Environ. health perspect Reversible uranyl fluoride nephrotoxicity in the Long Evans rat Relation of Distal Nephron Changes to Proximal Tubular Damage in Uranyl Acetate-Induced Acute Renal Failure in Rats, Environ. Health Perspect Fundam. Appl. Toxicol. Am. J. Nephrol, vol.43, issue.2230, pp.68-77, 1989.

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J. Hébert, E. Tissandie, Y. Guéguen, J. M. Lobaccaro, F. Paquet et al., Effects of depleted uranium after short-term exposure on vitamin D metabolism in rat Bone as target organ for metals: the case of felements Mechanisms of Uranium Interactions with Hydroxyapatite: Implications for Groundwater Remediation Molecular-Scale Characterization of Uranium Sorption by Bone Apatite Materials for a Permeable Reactive Barrier Demonstration The crystal structure of synthetic autunite, Ca O) 11 Monovalent cations in structires of meta-autunite group Vibrational spectroscopy of synthetic analogues of ankoleite, chernikovite and intermediate solid solution, Bone as a Possible Target of Chemical Toxicity of Natural Uranium in Drinking Water. Environ. health perspect, pp.786-797, 2002.

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DOI : 10.1097/00004032-198909000-00001

A. Iv, I. Spectroscopie, I. Mesures, and P. Du-complexe, Les spectres infrarouge des solutions de PEI-MC (10 mg.mL -1 ), dont le pH a été fixé à 5,0 ou à 7,0 par ajout d'hydroxyde de sodium (0,1 M) ont été enregistrés sur un diamant ATR 1 réflexion entre 4000 et 600 cm -1 alors qu'un film humide se formait

L. Spectres-infrarouge-du-complexe and P. , U ont été enregistrés à partir de solutions de complexes PEI-MC-U préparées par ajout de 5 µL d'une solution de nitrate d'uranyle (0,1 M) ou par ajout de 20

L. Spectres-infrarouge-du-complexe and P. , ont été enregistrés à partir de solutions de complexe PEI-MP-U préparées par ajout de 10 µL d'une solution de nitrate d'uranyle (0,1 M) à 100 µL de solution de PEI-MP (10 mg.mL -1 ), ce qui correspond à 0,4 équivalent U : PEI-MP. Le pH a été fixé à 7,0 par ajout d'hydroxyde de sodium (1 M). Les mesures ont été faites par déposition de gouttes de solutions PEI-MP-U, p.64

H. Les and P. Sur-lesquelles-ont-Été-déposées-le, PEI-MP-HAP plq ) et les HAP plq natives ont été plongées pendant 4h dans une solution tamponnée de nitrate d'uranyle (TBS, pp.2-10

M. , L. Surface, P. Plq-a-Été-déterminé-indépendamment-pour-chaque, P. Plq-par, and I. , La quantité moyenne, établie sur quatre plaques, d'uranium retenu par plaque est égale à 2,50 ± 0,39 x10 -8 mol pour PEI-MP-HAP plq et 2,33 ± 0,54 x10 -8 mol pour les HAP plq . Cela représente environ 53% de la quantité d'uranium initiale dans la solution de trempage pour le PEI-MP-HAP, p.pour

U. Les-quatre-plaques, HAP plq et les quatre plaques U-HAP plq ont été grattées pour récupérer les poudres correspondantes. Ces poudres ont été séchées sous vide en présence de P 2 0 5 puis conditionnées en pastille de polyéthylene pour être analysées en EXAFS, Ajustement EXAFS : U-PEI-MP-HAP plq et U-HAP plq