Source and fate of inorganic solutes in the Gibbon River, Yellowstone National Park, Wyoming, USA. II. Trace element chemistry

https://doi.org/10.1016/j.jvolgeores.2010.05.004Get rights and content

Abstract

The Gibbon River in Yellowstone National Park receives inflows from several geothermal areas, and consequently the concentrations of many trace elements are elevated compared to rivers in non-geothermal watersheds. Water samples and discharge measurements were obtained from the Gibbon River and its major tributaries near Norris Geyser Basin under the low-flow conditions of September 2006 allowing for the identification of solute sources and their downstream fate. Norris Geyser Basin, and in particular Tantalus Creek, is the largest source of many trace elements (Al, As, B, Ba, Br, Cs, Hg, Li, Sb, Tl, W, and REEs) to the Gibbon River. The Chocolate Pots area is a major source of Fe and Mn, and the lower Gibbon River near Terrace Spring is the major source of Be and Mo. Some of the elevated trace elements are aquatic health concerns (As, Sb, and Hg) and knowing their fate is important. Most solutes in the Gibbon River, including As and Sb, behave conservatively or are minimally attenuated over 29 km of fluvial transport. Some small attenuation of Al, Fe, Hg, and REEs occurs but primarily there is a transformation from the dissolved state to suspended particles, with most of these elements still being transported to the Madison River. Dissolved Hg and REEs loads decrease where the particulate Fe increases, suggesting sorption onto suspended particulate material. Attenuation from the water column is substantial for Mn, with little formation of Mn as suspended particulates.

Introduction

The Gibbon River originates at Grebe Lake and flows nearly 40 km to the Firehole River where they combine to form the Madison River. The Madison River is one of four major rivers leaving Yellowstone National Park (YNP). The Gibbon River receives water and solutes from several geothermal sources including Norris Geyser Basin, Chocolate Pots, Gibbon Geyser Basin, Beryl Spring, and Terrace Spring. Knowing the source and fate of geothermal solutes is important because their concentrations are often elevated in rivers receiving geothermal inputs. In Part I of this series (McCleskey et al., 2010), the discharge, concentrations, loads, and geochemical behavior of major solutes in the Gibbon River were described and interpreted. Part I (McCleskey et al., 2010) also contains many details of the study including sampling locations and methods. This paper covers the trace element concentrations, loads, and geochemical interpretations.

Numerous studies on the water and major ion loads in the Madison River exist (e.g., Norton and Friedman, 1985, Friedman and Norton, 1990, Hurwitz et al., 2007); however, there are no comprehensive chemical surveys that include discharge measurements allowing for the identification of sources, loads, and attenuation of trace elements in the Gibbon River. Several trace elements of ecologic importance have elevated concentrations in the Gibbon River, including As and Hg. Geothermal As from YNP causes high As concentrations in the Madison and Missouri Rivers in Montana and Wyoming (Nimick et al., 1998). This is of concern to water managers because some of this water is used for domestic and municipal water supply. Geothermal As in the Gibbon River has been studied previously (Thompson, 1979, Stauffer et al., 1980). Thompson (1979) studied As and F in the Upper Madison River System, including the Gibbon River, and found that Norris Geyser Basin is the primary source of As in the Gibbon River. Working with a small dataset and no discharge measurements, Stauffer et al. (1980) reported that most of the As flux in the Gibbon River drainage basin was precipitated or sorbed prior to the Gibbon River's confluence with the Firehole River at Madison Junction. The diel behavior of Hg has been studied in the Madison River (Nimick et al., 2007), but this study did not identify Hg sources or attenuation within the watershed. The source and fate of other trace metals, including Al, Fe, Mn, Hg, Zn, REEs, Ba, Be, Mo, Sb, Tl, and W, in the Gibbon River have not been previously studied. The purpose of this study was to quantify trace element loads, identify their sources, and identify processes of attenuation and transformation in the Gibbon River. This objective was accomplished by collecting water samples and discharge measurements from the Gibbon River and its major tributaries around Norris Geyser Basin under low-flow conditions in September 2006.

Section snippets

Study area and sample locations

A detailed map and a description of the sample locations and geology are found in Part I (McCleskey et al., 2010). Nineteen water samples were collected along a 28.7 km reach of the Gibbon River beginning upstream from Norris Geyser Basin and ending at the U.S. Geological Survey streamflow-gaging station (06037100) at Madison Junction. Eleven samples (G2–G12) were collected from the Gibbon River and eight samples (I1–I8) were collected from inflows. Seven of the inflow samples were collected

Methods

A complete description of the discharge measurements, water-quality sampling, and quantification of loads can be found in Part I (McCleskey et al., 2010). Water temperature, pH, and specific conductance were measured at each sampling site. Water-quality samples were collected from the Gibbon River using a DH-81 depth-integrating sampler in approximately equal-width increments across the river. The water was composited on-site in a 4-L high-density polyethylene (HDPE) bottle, and dissolved

Results and discussion

Table 1 contains the discharge, pH, specific conductance, and trace element concentrations for the Gibbon River and inflows samples. For nearly all trace elements, the minimum concentrations are upstream from Norris Geyser Basin and the maximum concentrations are found just downstream from one of the geyser basin sources. Part I (McCleskey et al., 2010) contains collection date, discharge, pH, specific conductance, temperature, and results for the major ion water analyses for the same samples.

Conclusion

Even though the Gibbon River contains elevated trace element concentrations (e.g., As, Sb, Be, Tl, Mn, Mo, W) compared to most major rivers, it is an important natural resource and habitat for fisheries and wildlife in YNP. Consequently, knowledge of the source, speciation, redox state, and form (dissolved or particulate) of trace elements is central to understanding their fate and ecological effects. Geothermal inflows are the major source of trace elements in the Gibbon River. Even though

Acknowledgements

We thank David Roth and Dale Peart for providing chemical analyses for the REEs and Hg. P.L. Verpanck, D.A. Nimick, W.C. Evans, B.A. Kimball, and K. Walton-Day are thanked for their thoughtful comments and reviews.

The use of trade, product, industry, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. Government.

References (95)

  • S.A. King et al.

    Mercury in water and biomass of microbial communities in hot springs of Yellowstone National Park, USA; Mercury; distribution, transport, and geochemical and microbial transformations from natural and anthropogenic sources

    Applied Geochemistry

    (2006)
  • A.J. Lewis et al.

    The rare earth element geochemistry of acid-sulphate and acid-sulphate-chloride geothermal systems from Yellowstone National Park, Wyoming, USA

    Geochimica et Cosmochimica Acta

    (1997)
  • A.J. Lewis et al.

    Rare earth element speciation in geothermal fluids from Yellowstone National Park, Wyoming, USA

    Geochimica et Cosmochimica Acta

    (1998)
  • R.B. McCleskey et al.

    Source and fate of inorganic solutes in the Gibbon River, Yellowstone National Park, Wyoming, USA

    Journal of Volcanology and Geothermal Research

    (2010)
  • E.J. McKenzie et al.

    Trace metal chemistry and silicification of microorganisms in geothermal sinter, Taupo Volcanic Zone, New Zealand

    Geothermics

    (2001)
  • J.W. Moffett

    A radiotracer study of cerium and manganese uptake onto suspended particles in Chesapeake Bay

    Geochimica et Cosmochimica Acta

    (1994)
  • K.H. Nealson et al.

    Occurrence and mechanisms of microbial oxidation of manganese

  • D.A. Nimick et al.

    Diel mercury-concentration variations in streams affected by mining and geothermal discharge

    Science of the Total Environment

    (2007)
  • D.R. Norton et al.

    Chloride flux out of Yellowstone National Park

    Journal of Volcanology and Geothermal Research

    (1985)
  • B.K. Pierson et al.

    Phototrophs in high iron microbial mats: microstructure of mats in iron-depositing hot springs

    FEMS Microbiology Ecology

    (2000)
  • R.L. Seiler et al.

    Factors controlling tungsten concentrations in ground water, Carson Desert, Nevada

    Applied Geochemistry

    (2005)
  • N. Strigul et al.

    Effects of tungsten on environmental systems

    Chemosphere

    (2005)
  • P.L. Verplanck et al.

    Rare earth element partitioning between hydrous ferric oxides and acid mine water during iron oxidation

    Applied Geochemistry

    (2004)
  • D.E. Wilson

    Surface and complexation effects on the rate of Mn(II) oxidation in natural waters

    Geochimica et Cosmochimica Acta

    (1980)
  • S.A. Wood

    Theoretical predictions of the speciation of beryllium in hydrothermal solutions and the solubility of bertrandite/phenakite

    Ore Geology Reviews

    (1992)
  • Allen, E.T., and Day, A.L., 1935. Hot springs of the Yellowstone National Park. Carnegie Institution of Washington...
  • S. Arnórsson et al.

    Molybdenum in Icelandic geothermal waters

    Contributions to Mineralogy and Petrology

    (1985)
  • P.M. Ashley et al.

    Magnitudes, spatial scales and processes of environmental antimony mobility from orogenic gold–antimony mineral deposits, Australasia

    Environmental Geology

    (2006)
  • J.W. Ball et al.

    User's manual for WATEQ4F, with revised thermodynamic data base and test cases for calculating speciation of major, trace, and redox elements in natural waters

  • J.W. Ball et al.

    Water-chemistry and on-site sulfur-speciation data for selected springs in Yellowstone National Park, Wyoming, 1994–1995

  • J.W. Ball et al.

    Water-chemistry and on-site sulfur-speciation data for selected springs in Yellowstone National Park, Wyoming, 1996–1998

  • J.W. Ball et al.

    Water-chemistry data for selected springs, geysers, and streams in Yellowstone National Park, Wyoming, 1999–2000

  • J.W. Ball et al.

    Water-chemistry data for selected springs, geysers, and streams in Yellowstone National Park, Wyoming, 2003–2005

  • H.L. Barnes et al.

    Geothermal systems and mercury deposits

  • K. Camponelli et al.

    Determining the chemical and biological availability of zinc in urban stormwater retention ponds

    (2005)
  • D. Craw et al.

    Geochemical controls on the environmental mobility of Sb and As at mesothermal antimony and gold deposits, Applied Earth Science

    Trans. Inst. Min. Metall. B

    (2004)
  • F. David et al.

    Photoredox chemistry of iron (III) chloride and iron (III) perchlorate in aqueous media, a comparative study

    Journal of Physical Chemistry

    (1976)
  • A.P. Davis et al.

    Loading estimates of lead, copper, cadmium, and zinc in urban runoff from specific sources

    Chemosphere

    (2007)
  • S. D'Imperio et al.

    Autoecology of an arsenite chemolithotroph: sulfide constraints on function and distribution in a geothermal spring

    Applied and Environmental Microbiology

    (2007)
  • D.A. Dzombak et al.

    Surface compexation modeling—hydrous ferric oxide

    (1990)
  • J. Gaillardet et al.

    Trace elements in river waters

  • J.R. Garbarino et al.

    An inductive-coupled plasma atomic-emission spectrometric method for routine water quality testing

    Applied Spectroscopy

    (1979)
  • J.R. Garbarino et al.

    Inductively coupled plasma-mass spectrometric method for the determination of dissolved trace elements in natural water

  • T.M. Gihring et al.

    Rapid arsenite oxidation by Thermus aquaticus and Thermus thermophilus: field and laboratory investigations

    Environmental Science & Technology

    (2001)
  • F.A. Gooch et al.

    Analyses of waters of the Yellowstone National Park with an account of the methods of analysis employed

  • N.N. Greenwood et al.

    Chemistry of the Elements

    (1989)
  • L.A. Haskin et al.

    Relative and absolute terrestrial abundances of rare earths

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