Between 1968 and 1983, the North pit at the Getchell Mine, Humboldt County,
NV, filled with water to form a lake. In 1983, water quality data were col
lected with the following results: As concentrations of 0.29 to 0.59 mg/L,
pH of 7.1 to 7.9, SO4- concentrations of 1490 to 1640 mg/L, and TDS of 2394
to 2500 mg/L. Using geochemical modeling techniques presented here, pit la
ke waters have been theoretically allowed to react for 8.5 a, the approxima
te time that the North pit had been completely full by 1983. Modeling resul
ts predict pH of 7.9 to 8.2, SO4 concentrations of 1503 to 1644 mg/L, TDS o
f 2054 to 2365 mg/L, and As concentrations ranging from 0.57 in the hypolim
nion to 96 mg/L in the epilimnion. In the epilimnion, model results do not
match observed As concentrations, suggesting that mechanisms, such as preci
pitation of arsenate salts or adsorption to mineral surfaces, may control A
s levels in an actual pit lake system. Adsorption to Fe oxyhydroxide surfac
es is questioned by the authors because of the low Fe content in the Getche
ll system, but adsorption to Al(OH)(3) (gibbsite) and clay mineral surfaces
may be important in controlling natural As concentrations. (C) 2000 Elsevi
er Science Ltd. All rights reserved.