doi:10.1016/j.apgeochem.2005.11.004
Copyright © 2006 Elsevier Ltd All rights reserved.
The influence of hydrous Mn–Zn oxides on diel cycling of Zn in an alkaline stream draining abandoned mine lands
Christopher L. Shope1, Ying Xie2 and Christopher H. Gammons
, 
Department of Geological Engineering, Montana Tech of The University of Montana, Butte, MT 59701, USA
Received 24 January 2005;
accepted 4 November 2005.
Editorial handling by B.A. Kimball.
Available online 17 February 2006.
References and further reading may be available for this article. To view references and further reading you must
purchase this article.
Abstract
Many mining-impacted streams in western Montana with pH near or above neutrality display large (up to 500%) diel cycles in dissolved Zn concentrations. The streams in question typically contain boulders coated with a thin biofilm, as well as black mineral crusts composed of hydrous Mn–Zn oxides. Laboratory mesocosm experiments simulating diel behavior in High Ore Creek (one of the Montana streams with particularly high Zn concentrations) show that the Zn cycles are not caused by 24-h changes in streamflow or hyporheic exchange, but rather to reversible in-stream processes that are driven by the solar cycle and its attendant influence on pH and water temperature (T). Laboratory experiments using natural Mn–Zn precipitates from the creek show that the mobilities of Zn and Mn increase nearly an order of magnitude for each unit decrease in pH, and decrease 2.4-fold for an increase in T from 5 to 20 °C. The response of dissolved metal concentration to small changes in either pH or T was rapid and reversible, and dissolved Zn concentrations were roughly an order of magnitude higher than Mn. These observations are best explained by sorption of Zn2+ and Mn2+ onto the secondary Mn–Zn oxide surfaces. From the T-dependence of residual metal concentrations in solution, approximate adsorption enthalpies of +50 kJ/mol (Zn) and +46 kJ/mol (Mn) were obtained, which are within the range of enthalpy values reported in the literature for sorption of divalent metal cations onto hydrous metal oxides. Using the derived pH- and T-dependencies from the experiments, good agreement is shown between predicted and observed diel Zn cycles for several historical data sets collected from High Ore Creek.
Fig. 1. Diel variations in dissolved Zn concentration from several streams in SW Montana: HOC, High Ore Creek; PPC, Prickly Pear Creek; IC, Indian Creek; CFR, Clark Fork River; SR, Stillwater River. All data are from Nimick et al. (2003) with the exception of CFR-1994 (Brick and Moore, 1996), CFR-2003 and IC-2003 (C. Gammons, unpublished data). Shaded regions denote approximate nighttime hours. All of the data were collected under baseflow conditions in late June, July, August, or early September.
Fig. 2. (a) XRD pattern of three samples of HMZO crust from High Ore Creek (all three scans are superimposed on the same scale); (b) SEM-EDX spectrum of HMZO crust.
Fig. 3. (a) Scanning electron image of an HMZO crust from High Ore Creek; (b) a closeup image, showing diatom fustules imbedded in HMZO matrix.
Fig. 4. Results of the Series 1 mesocosm experiments: (a) complete mesocosm, including water, boulders, and biofilms from High Ore Creek; (b) HOC water with filamentous green algae; (c) control tank with HOC water only. Shaded regions denote times when the artificial lights in the laboratory were off.
Fig. 5. Results of the Series 2 mesocosm experiments: (a) complete mesocosm, including water, boulders, and biofilms from High Ore Creek; (b) HOC water with filamentous green algae. The shaded regions denote times when the artificial lights in the laboratory were off.
Fig. 6. Comparison of pH and dissolved Zn concentrations from the Series 2a experiment of this study vs. field data from High Ore Creek. The latter were collected by the US Geological Survey in July, 2000, and were reported in Nimick et al. (2003).
Fig. 7. Results of the Series 3 mesocosm experiments with artificial pH control. Arrows show the sequence in which the samples were collected.
Fig. 8. Results of the Series 4 and 5 experiments with HMZO crusts and pH control.
Fig. 9. The dependence of dissolved Zn and Mn concentration on pH from the Series 4 and Series 5 experiments with HMZO crusts.
Fig. 10. Results of the Series 6 experiments with HMZO crusts and temperature control.
Fig. 11. The dependence of dissolved Zn and Mn concentration on temperature (1000 × reciprocal T, in Kelvin) from the Series 6 and Series 7 experiments with HMZO crusts.
Fig. 12. Results of the Series 8 experiments with HMZO crusts and artificial Eh control. Dashed lines separate periods of time in which either O2 gas or H2 gas was bubbled through the reaction vessel.
Fig. 13. The dependence of dissolved Zn and Mn concentration on temperature (1000 × reciprocal T, in Kelvin) from all experiments with HMZO crusts. The data were adjusted for minor differences in pH between samples. The slopes of the linear regressions were used to derive enthalpies for the adsorption of Zn2+ and Mn2+ onto HMZO.
Fig. 14. A comparison of observed and predicted Zn concentrations for six different diel investigations conducted at High Ore Creek by the US Geological Survey (Nimick et al., 2003, and unpublished data). Streamflow (Q, ft3 s−1 = 0.0283 m3 s−1) is shown on the right y-axis for Fig. 14e and f. The predictions are based on a model that takes into account pH changes only, or a combination of pH and temperature changes (see text).
Table 1.
Composition (acid-available metals) of HMZO crusts from High Ore creek

wt%, weight%; at%, atomic%, normalized to 100.