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These 41 OREs were present in seven to 119 copies in the BES database and their sizes ranged from 80 bp to 224 bp (Additional file 4).
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In order to gain insight into these interactions, a qualitative and quantitative assay of the microorganisms that colonise the ore surface or are present in the liquid phase between the ore clusters at different levels within a heap has been developed.
When toxic components, e.g., arsenic from refractory gold ore, are present, encapsulation will be required.
The D R isotherm constants are presented in Table 1 and the plot of the D R isotherm for fluoride adsorption onto iron ore is presented in Fig. 2d.
Arsenic is always associated with gold ores and is present in mining areas, probably due to sulfide oxidation and the high pH range where arsenic is soluble.
Similarly, four other OREs may be present more than 4,000 times.
Furthermore, although BLLs ≥ 45 µg/dL and soil-lead levels > 400 ppm were reported exclusively in ore-processing villages, children with BLLs ≥ 10 µg/dL were present in half of the non-ore-processing villages.
Substantial amounts of iron ore also are present in this area.
Even with remediation efforts and medical treatment, recontamination and recurrent lead poisoning can occur if the source of lead exposure (e.g., ore processing) continues to be present or is reintroduced in villages.
Quantitative results regarding detection limits and accuracy for dilute ore concentrations are presented.
In this paper a dynamic model of ore flotation is presented.
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