THE TRANSPORT AND FATE OF FE, MN, CU, ZN, CD, PH AND SO4 IN A GROUNDWATER PLUME AND IN DOWNSTREAM SURFACE WATERS IN THE COEUR-DALENE MININGDISTRICT, IDAHO, USA
Aj. Paulson, THE TRANSPORT AND FATE OF FE, MN, CU, ZN, CD, PH AND SO4 IN A GROUNDWATER PLUME AND IN DOWNSTREAM SURFACE WATERS IN THE COEUR-DALENE MININGDISTRICT, IDAHO, USA, Applied geochemistry, 12(4), 1997, pp. 447-464
The controls on metal concentrations in a plume of acidic (pH 3.29-5.5
5) groundwater in the Moon Creek watershed in Idaho, U.S.A., were inve
stigated with the use of property-property plots. A plot of Ca vs S de
monstrated that a plume of contaminated groundwater was being diluted
by infiltration of rain and creek water at shallow depths and by ambie
nt groundwater near bedrock. The small amount of dissolved Fe (2.1 mg/
l) was removed while dissolved Pb was added, reaching a maximum concen
tration of 0.37 mg/l. The other metals (Zn less than or equal to 16, A
l less than or equal to 6.2, Cu less than or equal to 2.1 and Cd less
than or equal to 0.077 mg/l) in the shallow groundwater were essential
ly conserved until they emerged as a seep along the creek bank. Upon m
ixing with the creek water, groundwater was diluted by factors between
11 and 50, and the pH of the mixture became neutral. Metals originati
ng from the contaminated groundwater were removed in the creek in the
following order: Fe > Al > Pb >> Cu > Mn > Zn = Cd. Pb and Cu continue
d to be removed from solution even as the creek passed adjacent to a t
ailings pile. In contrast, Zn concentrations in the creek increased ad
jacent to the tailings area, presumably as a result of the reemergence
of the upgradient plume as the creek lost elevation. Below the tailin
gs dam, contaminated creek water (400-800 mu g Zn/l) was diluted by bo
th smaller side streams and a creek of equal flow. The presence of 3 d
istinctive water masses required the use of two tracers (dissolved Si
and S) to distinguish between mixing and geochemical reactions. The re
moval of metals was greater during low flow conditions. Pb was removed
to the greatest extent, falling below detection limits (0.5 mu g/l) a
t the first sampling location. Copper and Mn were removed to a lesser
extent during low flow conditions and approached conservative behavior
during high dow conditions. During a 5-km journey through two hydrolo
gical regimes, less than 10% of the dissolved Zn and Cd was lost. (C)
1997 Elsevier Science Ltd.