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1 n and the magnitude of its mobilization from coal ash.
2 ressures also present opportunities to reuse coal ash.
3 wever, the quality and quantity of discarded coal ash across the U.S. are not well known, even though
6 d estimates of the relative contributions of coal ash, Clinch River, and Emory River sediments for a
7 tations from 1973 to 2022 and was trained on coal ash composition data, showing that coal ash element
9 pills and chronic leaking of coal ash ponds, coal ash disposal has only been partially regulated, and
11 gions where native sediments were mixed with coal ash (e.g., less than 28% as coal ash in the Emory R
12 d on coal ash composition data, showing that coal ash elemental composition is strongly associated wi
13 earth elements (REEs) extraction from legacy coal ash enables simultaneous waste valorization and rem
15 ther material innovations that would utilize coal ash harvested from disposal sites across the U.S. S
16 ith the Emory River are affected by Kingston coal ash; however, the relative contribution of the coal
18 mandate the closure or retrofitting of most coal ash impoundments, presenting significant challenges
19 e model for the major element composition of coal ash in reserve at disposal sites of major U.S. coal
24 assessment of the environmental behavior of coal ash, particularly with respect to toxic trace eleme
25 ates, the systematic evidence for leaking of coal ash ponds shown in this study highlights potential
26 , provide strong evidence for the leaking of coal ash ponds to adjacent surface water and shallow gro
27 ophic coal ash spills and chronic leaking of coal ash ponds, coal ash disposal has only been partiall
30 Elevated concentrations of toxic elements in coal ash pose human and ecological health risks upon rel
33 Sr isotopic analyses, revealing unmonitored coal ash releases over the past 40 to 70 years preserved
36 ion spectroscopic analyses showed that Se in coal ash samples was a mixture of elemental Se(0) and Se
37 states, we aimed to define Se speciation in coal ash solids and examine the relationships between Se
38 currence of hundreds of thousands of tons of coal ash solids mainly resulting from high-magnitude sto
39 1) the 2008 Tennessee Valley Authority (TVA) coal ash spill affected waters; (2) CCR effluents from p
43 in the sediments of the Emory River near the coal ash spill, total mercury concentrations were 3- to
45 ity and human health risks from catastrophic coal ash spills and chronic leaking of coal ash ponds, c
48 from 263 children living within 10 miles of coal ash storage facilities in Jefferson and Bullitt Cou
50 l power plants are producing huge amounts of coal ash that may be applied to a variety of secondary u