IRSN, Institut de radioprotection et de sûreté nucléaire

Search our site :


Contact us :

En Fr

All our expertise to protect you



Uranium speciation and mobility in soils and sediments downstream from former U mines

​Lucie Stetten has defended her thesis on 12th October 2018 in Paris.

Document type > *Mémoire/HDR/Thesis

Keywords >

Research Unit > PSE-ENV/SEDRE/LELI

Authors > STETTEN Lucie

Publication Date > 12/10/2018


Uranium scavenging in soils and sediments located downstream from former U mines is expected to naturally limit uranium dispersion in downstream waterways. However, uranium mobility in such contaminated sites may depend on the identity of U traps as well as the geochemical conditions. The aim of this thesis was to improve our knowledge on the geochemical behavior and the mobility of uranium in U contaminated lacustrine sediments and wetland soils, whose reducing conditions is expected to mitigate uranium mobility because U(IV) species are less soluble than U(VI) ones. X-ray absorption spectroscopy and scanning electron microscopy analyzes combined with geochemical
analyzes were carried out.

In U contaminated lake sediments, we show that indirect reduction of U(VI) by Fe(II) associated to clay minerals may be a major diagenetic process responsible for the scavenging of uranium. For organic-rich weltand soils, we show a sharp uranium redox boundary mainly controlled by the watertable. For both sites, U(IV) mononuclear species and U(IV)-phosphate minerals were identified as the major species controlling uranium solubility, while uraninite is virtually absent. For the highly Ucontaminated wetland soil, we suggest a major uranium redistribution via the oxidative dissolution of U(IV)-minerals followed by U(VI) organic matter complexation. Soil incubation experiments have confirmed these redistribution mechanisms and suggest different geochemical behaviors for lermontovite (U(PO4)(OH)•H2O) and ningyoite (CaU(PO4)2•2H2O). These experiments also highlight the role of organic matter in the control of uranium mobility, favoring the remobilization of U(IV) organic complexes under reducing conditions. Altogether, our results call for the need to consider both non-uraninite U(IV) minerals and mononuclear U(IV) complexes in such anoxic environments as major species controlling uranium solubility.


Send to a friend

The information you provide in this page are single use only and will not be saved.
* Required fields

Recipient's email:*  

Sign with your name:* 

Type your email address:*   

Add a message :

Do you want to receive a copy of this email?