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1 n and the magnitude of its mobilization from coal ash.
2 opic fingerprints that are characteristic of coal ash at all but one site.
3 d estimates of the relative contributions of coal ash, Clinch River, and Emory River sediments for a
4 gions where native sediments were mixed with coal ash (e.g., less than 28% as coal ash in the Emory R
5 ith the Emory River are affected by Kingston coal ash; however, the relative contribution of the coal
6                    Given the large number of coal ash impoundments throughout the United States, the
7  mixed with coal ash (e.g., less than 28% as coal ash in the Emory River).
8              The risk of the mobilization of coal ash into the environment has highlighted the need f
9                               Overall, As in coal ash is not environmentally stable and can participa
10                                         This coal ash may have provided substrates (such as sulfate)
11  assessment of the environmental behavior of coal ash, particularly with respect to toxic trace eleme
12 ates, the systematic evidence for leaking of coal ash ponds shown in this study highlights potential
13 , provide strong evidence for the leaking of coal ash ponds to adjacent surface water and shallow gro
14  Carolina) to evaluate possible leaking from coal ash ponds.
15 s potential environmental risks from unlined coal ash ponds.
16 ms and is also promising for waste glass and coal ash recycling.
17             delta(202)Hg values for Kingston coal ash released into the Emory River in 2008 are signi
18                         At the natural pH of coal ash samples (from pH 7.6 to 9.5), the leachable Se
19                                      We used coal ash samples from the Tennessee Valley Authority (TV
20 ion spectroscopic analyses showed that Se in coal ash samples was a mixture of elemental Se(0) and Se
21  states, we aimed to define Se speciation in coal ash solids and examine the relationships between Se
22 1) the 2008 Tennessee Valley Authority (TVA) coal ash spill affected waters; (2) CCR effluents from p
23 ansport of Hg-impacted river sediment near a coal ash spill at Harriman, Tennessee, USA.
24      The Tennessee Valley Authority Kingston coal ash spill in December 2008 deposited approximately
25 TVA)-Kingston fossil plant and the site of a coal ash spill that occurred in 2008 in Tennessee.
26 in the sediments of the Emory River near the coal ash spill, total mercury concentrations were 3- to
27 ta bicolor) from a site impacted by a recent coal ash spill.
28                             Selenium (Se) in coal ash spills poses a threat to adjacent ecosystems be
29                   Future risk assessments of coal ash spills should consider not only the leaching po
30 l power plants are producing huge amounts of coal ash that may be applied to a variety of secondary u
31 h; however, the relative contribution of the coal ash varies among sampling sites.
32 of the total mercury in sediments containing coal ash was present as methylmercury.

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