Bn. Noller et al., THE ROLE OF BIOGEOCHEMICAL PROCESSES IN MINIMIZING URANIUM DISPERSIONFROM A MINE SITE, Journal of geochemical exploration, 58(1), 1997, pp. 37-50
The Ranger Uranium Mine located in the Alligator Rivers Region of the
Northern Territory lies in the tropical zone and has an annual wet-dry
monsoonal climate. Following the commencement of the wet season, runo
ff from the waste rock dump accumulates in a retention pond (RP4). Thi
s water is permitted to discharge to the nearby Magela Creek once mini
mum flow of 5 m(3)/sec is reached and following filling of the pond. T
he discharge proceeds via a channel, experimental wetland and a backfl
ow billabong (Djalkmarra Billabong) which acts as a natural wetland fi
lter and flows out to Magela Creek. This study examines monitoring dat
a for water releases over 3 wet seasons, 1 wet season with no release
and 4 dry seasons. The monitoring data comprised electrical conductivi
ty (EC), pH, Na, K, Ca, Mg, HCO3-, SO42-, Cl- and U (total or filtered
, < 0.45 mu m). Some ICP-MS scans of trace elements were also undertak
en with particular reference being made to Re and U. Specific features
of the sequence of water accumulation, release and reconstitution of
Djalkmarra Billabong are able to show that U is effectively removed fr
om solution, from about 50 ppb down to < 1 ppb. Soluble salts may rema
in in the water column and are removed by dilution following discharge
to Magela Creek. Sediment levels show no increase in U concentration
with time. The pH of the billabong water during releases (6.0-6.6) sug
gests that cationic forms of U, such as (UO2)(3) (OH)(5+) predominate,
favouring adsorption on to the humic-rich sediments of the natural we
tland. The application of this principle enables U to be removed effic
iently from waste water and to be contained within the mine lease.