Geoenvironmental impacts of using high carbon fly ash in structural fill applications.
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2013-03-01
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Abstract:Fly ash produced by power plants in the United States occasionally contains significant amounts of unburned carbon due to the
use of the increased prevalence of low nitrogen-oxide and sulphur-oxide burners in recent years. This ash cannot be reused in
concrete production due to its reactivity with air entrainment admixtures, so it is largely placed in landfills. Highway structures
have high potential for large volume use of high carbon fly ashes (HCFAs). However, in such applications, even though
mechanical properties of the fly ash-amended highway base layers and embankments are deemed satisfactory, a key issue that
precludes such highway embankments built with fly ash is the potential for negative groundwater effects caused by metals in the
fly ash. This study evaluated the leaching potential of metals from highway base layers stabilized with HCFA and highway
embankment structures amended with HCFA. Three different laboratory tests were conducted: (1) batch water leach tests, (2)
toxicity characteristics leaching procedure tests, (3) column leach test. Additionally, two numerical modeling analyses were
conducted: (1) WiscLEACH and (2) MINTEQA2. Analyses were conducted on eight fly ashes and two locally available sandy
soil materials that are mainly used in highway base layer and highway embankment structures. Laboratory test results indicated
that an increase in fly ash content in the soil-fly ash mixtures yielded an increase in leached metal concentrations with the
exception of zinc (Zn). The pHs had significant and different effects on the leaching of metals. The leaching of chromium (Cr),
zinc, (Zn), aluminum (Al), arsenic (As) and selenium (Se) increased with increased pH levels, while leaching of barium (Ba),
boron (B), cooper (Cu), iron (Fe), magnesium (Mn), silver (Sb), vanadium (V) decreased with increased pH levels.. Numerical
model WiscLEACH was used to simulate the leaching behavior of leached metals from HCFA-stabilized highway base layers
and HCFA-amended highway embankment structures. WiscLEACH predicted field metal concentrations were significantly
lower than the metal concentrations obtained in laboratory leaching tests, and field concentrations decreased with time and
distance due to dispersion in soil vadose zone. Numerical model MINTEQA2 predicted that leaching of metals were solubility
controlled except As, Se and Sb. Speciation analyses indicated that leached metals were present at their less or non-toxic forms.
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