A framework for understanding Mo isotope records of Archean and Paleoproterozoic Fe- and Mn-rich sedimentary rocks: Insights from modern marine hydrothermal Fe-Mn oxides

2020 ◽  
Vol 280 ◽  
pp. 221-236
Author(s):  
Kosuke T. Goto ◽  
Yasuhito Sekine ◽  
Gen Shimoda ◽  
James R. Hein ◽  
Shogo Aoki ◽  
...  
2021 ◽  
Vol 616 ◽  
pp. 118100
Author(s):  
Narasimharao Katabathini ◽  
Islam Hamdy Abd El Maksod ◽  
Mohamed Mokhtar
Keyword(s):  

Minerals ◽  
2020 ◽  
Vol 10 (10) ◽  
pp. 900
Author(s):  
Taehyoung Kim ◽  
Seonhee Kim ◽  
Hyunji Tak ◽  
Kyeongtae Kim ◽  
Chul-Woo Chung ◽  
...  

The mechanisms at different pH for the stabilization of arsenic (As) in mine tailings (MTs) using steelmaking slag were investigated using laboratory experiments. Two types of steelmaking slag were used in the experiments. Ca-slag has high pH and high calcium oxide content due to its short period of aging. In contrast, Fe-slag is oxidized for a long time and is richer in Fe than in Ca. The As-contaminated MTs were taken from a tailing-storage dam around an abandoned gold mine in Korea. The tailings had an average As concentration of 2225.3 mg/kg. The As-removal batch experiment was performed to investigate the As-removal characteristics of the steelmaking slag. From SEM/EDS analyses after each batch experiment, Ca-As bearing precipitates were broadly found on the surface of Ca-slag particles and the final pH of the solution increased to 12.3. However, for Fe-slag, the As was locally found as forms adsorbed to the surface of Fe and Mn oxides contained in the Fe-slag particles. The final pH of this solution was 8.4. The efficiency of removal of As from water using the Ca-slag was >97% and that with Fe-slag was 79%. This suggests that As ions in solution were removed by Ca-(co-)precipitation (which occurs comprehensively on the Ca-slag surface), or by restrictive adsorption of Fe- and Mn-oxides (on limited parts of the Fe-slag). To determine the efficiency of As-extraction reduction from MTs using steel slags, arsenic-extraction batch experiments with two slags were performed under acidic conditions, simulating the leaching environment formed around a mine tailing storage dam. The As concentration in the extracted solution was decreased by 69.9% (even at pH 2) after the addition of 5% Fe-slag. However, when 5% Ca-slag was added, the As concentration decreased by 42.3% at pH 2. These results suggest that Fe-rich steel slag can be more effective than Ca-rich steel slag as a stabilizer for As in contaminated mine tailings at low pH.


2001 ◽  
Vol 35 (9) ◽  
pp. 1779-1784 ◽  
Author(s):  
Paras Trivedi ◽  
Lisa Axe

2015 ◽  
Vol 33 (5) ◽  
pp. 357-366 ◽  
Author(s):  
Laiby Paul ◽  
Rasmus Jakobsen ◽  
Erik Smolders ◽  
Hans-Jørgen Albrechtsen ◽  
Poul L. Bjerg

Geosciences ◽  
2018 ◽  
Vol 8 (12) ◽  
pp. 495
Author(s):  
Eleanora Robbins ◽  
Shannon Quigley-Raymond ◽  
Ming Lai ◽  
Janae Fried

Microbial populations involved in forming the distinctive precipitates of S, Fe, Mn, and Ca in the San Diego River watershed reflect an interplay between the mineralogy of the rocks in the watershed, sparse rainfall, ground- and surface-water anoxia, and runoff of high sulfate, treated imported water. In the sparsely developed headwaters, the Temescal Creek tributary emerges from pyrite-bearing metamorphic rocks, and thus exhibits both an oxidized Fe and reduced S. In the middle reaches, the river moves through developed land where treated, imported high sulfate Colorado River water enters from urban runoff. Mast Park surrounded by caliche-bearing sedimentary rocks is a site where marl is precipitating. Cobbles in riffles along the river are coated black with Mn oxide. When the river encounters deep-seated volcanic bedrock, it wells up to precipitate both Fe and Mn oxides at the Old Mission Dam. Then, directly flowing through caliche-laced sedimentary rocks, Birchcreek tributary precipitates tufa. Further downstream at a site under a bridge that blocks sunlight, a sulfuretum sets up when the river is deoxygenated. Such a rich geochemistry results in activity of iron and manganese oxidizing bacteria, sulfur oxidizers and reducers, and cyanobacteria precipitating calcareous marl and tufa.


RSC Advances ◽  
2015 ◽  
Vol 5 (52) ◽  
pp. 41877-41886 ◽  
Author(s):  
Shuxin Ye ◽  
Weiping Jin ◽  
Qing Huang ◽  
Ying Hu ◽  
Bakht Ramin Shah ◽  
...  

Hybrid materials were obtained by immobilizing Fe and Mn oxides (FMBO) into a konjac glucomannan (KGM) based aerogel matrix to remove arsenite from water.


2005 ◽  
Vol 69 (5) ◽  
pp. 887-896 ◽  
Author(s):  
W. G. Burgess ◽  
L. Pinto

AbstractDegradation of contaminant hydrocarbons in groundwater by microbially mediated oxidation, linked to the reduction of electron acceptors, is fundamental to the strategy of ‘monitored natural attenuation’ (MNA) for oxidizable hydrocarbons, which is increasingly being adopted at polluted aquifer sites throughout Europe and North America. Commonly, oxygen is depleted and following the reduction of nitrate, solid-phase Fe oxides become the dominant electron acceptors. Arsenic, associated with Fe and Mn oxides in soils and sediments, may therefore be mobilized to groundwater and pose an additional threat to environmental receptors. In a pilot study of three aquifers in England, we have examined the extent to which arsenic is released to groundwater under Fe(III)-reducing conditions imposed by contaminant hydrocarbons. Results show that arsenic is locally mobilized in the Chalk to <10 μg/1, in Quaternary gravels to 70 μg/1 and in the Triassic sandstones to 160 μg/1. At the Chalk and Quaternary gravels sites arsenic mobilization is demonstrably linked to reduction of Fe- and Mn-oxides. This is not so at the Triassic sandstone site, where release of arsenic is related to elevated bicarbonate alkalinity. Redox-driven arsenic mobilization at other Triassic sandstone locations is possible. Further work is required on the solid-phase sources of arsenic in the aquifers, and to relate the hydrochemical observations to groundwater hydraulic conditions.


2011 ◽  
Vol 237 (3-4) ◽  
pp. 179-188 ◽  
Author(s):  
A. Préat ◽  
B. Mamet ◽  
P. Di Stefano ◽  
L. Martire ◽  
K. Kolo

1984 ◽  
Vol 14 (1) ◽  
pp. 33-90 ◽  
Author(s):  
Shailendra K. Singh ◽  
V. Subramanian ◽  
Ronald J. Gibbs

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