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School of Engineering and Science - Jacobs University

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sample preparation methods are employed which isolate <strong>and</strong> concentrate the elements<br />

<strong>of</strong> interest from undesirable matrix elements.<br />

Table 2 contains interferences commonly observed in ICPMS analyses<br />

performed within the JUB Geochemistry Lab. The inability <strong>of</strong> the low-resolution<br />

DRC-e ICPMS to resolve interferences from the isotopes <strong>of</strong> interest does not<br />

significantly inhibit the accurate determination <strong>of</strong> the 32 elements routinely analyzed,<br />

as correcting for these interferences is possible through careful characterization <strong>and</strong><br />

quantification <strong>of</strong> the interfering polyatomic species. The majority <strong>of</strong> these corrected<br />

interferences are for the REE (Table 2), as the REE can form significant amounts <strong>of</strong><br />

oxide <strong>and</strong> hydroxide species during ionization. For example, at typical instrument<br />

settings as much as 3% <strong>of</strong> the Ce present in the sample solution will be ionized to<br />

140 Ce 16 O + , <strong>and</strong> the<br />

140 Ce 16 O + ion will consequently contribute to any Gd<br />

determinations that utilize the<br />

156 Gd isotope. The isotopes monitored for<br />

quantification <strong>of</strong> the REE are therefore carefully selected to minimize these effects<br />

<strong>and</strong> maximize analytical accuracy, though as seen in Table 2 a significant number <strong>of</strong><br />

corrections are necessary. While implementing such corrections is not trivial,<br />

uncorrected values may result in reported concentrations for REE elements that are<br />

erroneously high by as much as several percent, as illustrated by the example with<br />

CeO + .<br />

Corrections for polyatomic interferences are performed mathematically,<br />

typically <strong>of</strong>fline using commercially available spreadsheet s<strong>of</strong>tware such as Micros<strong>of</strong>t<br />

Excel (the approach followed at JUB). Interferences are identified <strong>and</strong> quantified by<br />

analyzing solutions that contain relatively high concentrations (50-1000 μg/kg) <strong>of</strong> a<br />

single element, <strong>and</strong> surveying the range <strong>of</strong> masses that might be affected by<br />

interferences produced by oxide, hydroxide, chloride, or nitrogen species <strong>of</strong> that<br />

particular element. For the REE, the most significant interferences are generated by<br />

REE-oxides or -hydroxides, <strong>and</strong> therefore are found at 16 <strong>and</strong> 17 amu above the<br />

interfering element (i.e., REE 16 O + <strong>and</strong> REE 16 O 1 H + ). The measured intensities <strong>of</strong> the<br />

interfering element, <strong>and</strong> the various interferences it produces, allow calculation <strong>of</strong><br />

ratios expressing the relative amount <strong>of</strong> interfering species generated as a function <strong>of</strong><br />

the concentration <strong>of</strong> the interfering element. For example, if as mentioned above, 3%<br />

<strong>of</strong> 140 Ce in the sample is ionized to 140 Ce 16 O + (i.e., 140 Ce 16 O + / 140 Ce equals 0.03), <strong>and</strong> if<br />

the Ce concentration in the sample corresponds to a measured intensity <strong>of</strong> 100,000<br />

8

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