Toxic
Trace-Elements in Natural and Contaminated Environments
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One of the important long-term environmental
issues that
our society faces is the management of toxic trace metals and other
harmful
inorganic constituents in the environment. Elevated
levels of these substances are often the result
of human
activities but can also be naturally occurring. My
main research interests are to elucidate the processes
that control
the mobility and fate of harmful inorganic constituents such as heavy
metals in
aquatic and soil environments. These
processes include the formation of metal-containing solid phases, the
formation
of aqueous metal complexes, the adsorption of metals to soils and
sediments and
to aquatic particles, and reduction and oxidation reactions. |
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Understanding these processes is crucial for
the
evaluation of human health risks and ecosystem effects of inorganic
contaminants and for the development of rational and cost-effective
remediation
strategies for contaminated sites. The
scope of these research efforts ranges from spectroscopic
investigations at the
molecular level to bench scale experiments with natural materials and
model
systems to field investigations and numerical modeling.
Two specific areas of research in this field
are described below: |
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| Although
the
groundwater in the southern San Joaquin Valley is generally of high
quality,
there are isolated pockets where the concentration of the toxic element
arsenic
exceeds the drinking water standard. In
this study we examine water and sediments from two nearby wells, one
with low
arsenic, the other with elevated arsenic concentrations. Analyses include sequential sediment extraction, examination of sediments by electron microscopy, and depth-resolved water sampling. Groundwater has a mixed redox state with arsenic occurring as both As(III) and As(V). Arsenic in the sediments is associated with pyrite grains which start to dissolve when the come in contact with oxygenated groundwater. (Boockoff et al., 2005; Negrini et al., in press) This work has been funded by the USDA and several grants from the state of ![]() |
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Chromium-containing precipitates can affect
the
mobility of toxic Cr(VI) in the subsurface, control its concentration
in
groundwater, limit its bioavailability, and impede remediation of
chromium
contaminated sites. These precipitates
can be pure phases such as KFe3(CrO4)2(OH)6,
the chromate-analog of the common sulfate mineral jarosite, or
solid-solutions
where chromate partially substitutes for another ion such as sulfate
(e.g. Ba(SxCr1-xO4)).
In my research, we are measuring the
thermodynamic properties of these solids. These
thermodynamic properties are the basis for
determining the
conditions under which these solids form and remain stable, as well as
the
chromium concentrations in water equilibrated with them. In addition to
the
practical applications, the thermodynamics of inorganic solid solutions
is also
one of the remaining theoretical frontiers in inorganic geochemistry.
(e.g.
Baron and Palmer, 2002; Drouet et al., 2003; Drouet et al., 2004). |
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Central
California Climate History
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We
recently acquired 45 m of core from the This work has been funded by the
National Science Foundation. |
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| Geologic materials such as obsidian, volcanic ash, and chert from different sources can be distinguished based on their trace-element composition. We use ICP/MS and Laser Ablation ICP/MS to analyze various geological materials for stratigraphic and archaeological studies. (e.g. Baron et al., in press; Draucker et al., 2007) | ![]() |
Baron D., Negrini R.M, Golob E.M.*,
Miller D.,
Sarna-Wojcicki A, Fleck R., Hacker B., Erendi A. (in press)
Geochemical
correlation and 40Ar/39Ar dating of the Kern River Ash and related
tephra: Implications for the
stratigraphy of
petroleum-bearing formations in the San Joaquin Valley, California. Quaternary
International.
Baron D. and Palmer C.D. (2002) Solid
solution/aqueous
solution interactions between jarosite
and its chromate analog. Geochimica et
Cosmochimica Acta, 66,
2841-2853.
Baron D., Palmer C.D. and Stanley J.T.
(1996)
Identification of two Fe-chromate precipitates in
a Cr(VI)-contaminated soil.
Environmental Science & Technology,
30, 964-968.
Draucker A., Baron D., Yohe R., and
Horton R. (2007)
Geochemical characterization of obsidian subsources from
the Coso Range,
California, USA. 2007 Goldschmidt
Conference, Cologne, Germany, August 19-24, 2007.
Drouet C., Pass K.L., Baron D., Draucker
S., and
Navrotsky A. (2004) On the thermochemistry of solid solutions
between jarosite,
natrojarosite, and alunite. Geochimica
et Cosmochimica Acta, 58,
2197-2205.
Drouet C., Navrotsky A., and Baron D.
(2003) On the
thermochemistry of solid solutions between jarosite and its
chromate
analog. American
Mineralogist, 88,
1949-1954.
Negrini R., Rhodes D, Stephenson R.,
Noriega-Carlos G.,
Grant L., Baron D, Wigand P, and Rich F.(2007)
Evidence of a long-lived
Pleistocence lake, Carrizo Plain, California.
Annual Meeting of the Geological Society of
America, Denver, CO, October
28-31, 2007, GSA Abstracts with Programs Vol. 39, No.6.
Negrini R., Baron D., Gillespie J.,
Horton R., Draucker
A., Durham N., Huff J., Philley P., Register C., Parker J.,
and Haslebacher T.
(in press) A middle-Pleistocene
lacustrine delta in the Kern River depositional system:
structural
control, regional stratigraphic
context, and impact on groundwater quality.
Invited paper for Pacific Section of the
American Association of
Petroleum Geologists Special Publication.