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. Author manuscript; available in PMC: 2020 Oct 1.
Published in final edited form as: J Anal At Spectrom. 2019 Oct 1;34(10):2094–2104. doi: 10.1039/C9JA00086K

Table 2.

An evaluation of M2+ interference-correction approaches on m/z 78 in reagent and regional tap water matrices fortified with Gd

Reagent Water Fortified with Low and High Rare Earth Spikes m/z 78, No Correction1,2 m/z 78, No Correction1,3 m/z 78, External Correction1,3,4 m/z 78, In-Sample Correction5 m/z 94, 8800 ICP-MS6 High Resolution7
4.5mL He ([ppb] ± 2σ) 2.5mL He ([ppb] ± 2σ) 2.5mL He ([ppb] ± 2σ) 2.5mL He ([ppb] ± 2σ) 78→94 Se [O2] ([ppb] ± 2σ) 78Se ([ppb] ± 2σ)
2 ppb Gd 2.3 ± 0.7 0.7 ± 0.6 −0.1 ± 0.6 0.0 ± 0.8 0.01 ± 0.04 −0.03 ± 0.02
2 ppb Gd + spike8 3.1 ± 1.3 1.6 ± 0.9 0.8 ± 0.9 1.5 ± 1.3 1.0 ± 0.1 0.924 ± 0.004
50 ppb Gd 53.0 ± 5.7 19.1 ± 1.9 −1.0 ± 2.0 −0.1 ± 1.2 −0.04 ± 0.03 −0.01 ± 0.12
50 ppb Gd+ spike8 54.0 ± 7.0 20.3 ± 1.8 0.0 ± 1.8 0.6 ± 2.3 1.1 ± 0.1 0.94 ± 0.06
Regional tap waters9
Water A + 50 ppb Gd, Nd, Sm 51.2 ± 7.3 15.5 ± 2.9 −9.6 ± 3.2 −1.0 ± 2.6 0.18 ± 0.10 0.36 ± 0.03
Water B + 50 ppb Gd, Nd, Sm 51.1 ± 7.8 16.2 ± 2.0 −9.3 ± 1.8 −1.0 ± 3.9 1.35 ± 0.24 1.33 ± 0.12
Water C + 50 ppb Gd, Nd, Sm 51.8 ± 4.2 17.9 ± 4.3 −7.3 ± 4.6 1.2 ± 4.2 2.29 ± 0.23 2.17 ± 0.26
Water D + 50 ppb Gd, Nd, Sm 53.3 ± 5.8 15.8 ± 2.5 −9.6 ± 2.9 −2.4 ± 3.5 −0.03 ± 0.05 0.15 ± 0.02
Water E + 50 ppb Gd, Nd, Sm 53.2 ± 6.3 15.8 ± 3.6 −10.3 ± 4.3 −2.8 ± 4.2 −0.01 ± 0.09 0.21 ± 0.01
Water F + 50 ppb Gd, Nd, Sm 52.5 ± 6.7 16.3 ± 3.8 −9.6 ± 3.9 −2.1 ± 1.9 0.33 ± 0.07 0.46 ± 0.05
1.

Data were collected in normal resolution mode (0.8 amu at 10% peak height) using In as an internal standard with a 0.3-sec/amu integration time in selective ion monitoring mode. All estimates are based on 10 instrument replicates.

2.

The calibration blank and 1 ppb standard associated with the analysis of reagent water (4.5 mL He) produced 9 cps and 67 cps, respectively. The calibration blank and 5 ppb standard associated with the analysis of regional waters (4.5 mL He) produced 12 cps and 169 cps, respectively.

3.

The calibration blank and 1 ppb standard associated with the analysis of reagent waters (2.5 mL He) produced 23 cps and 87 cps, respectively. The calibration blank and 5 ppb standard associated with the analysis of regional waters (2.5 mL He) produced 31 cps and 279 cps, respectively.

4.

The M2+ correction factors were estimated in narrow resolution mode (0.4 amu at 10% peak height) in an external rare earth standard and applied as a fixed correction factor to all samples. This correction also incorporated a narrow to normal conversion factor (see Figure 5).

5.

Data were collected in narrow resolution mode (0.4 amu at 10% peak height) using In as an internal standard with a 0.3-sec/amu integration time in selective ion monitoring mode. All estimates are based on 10 instrument replicates. The M2+ correction factors were estimated in each sample. The solutions fortified with 2 ppb rare earth produced about 30 cps at the corresponding half-mass with %RSD across the 10 replicates of about 25%. The solutions fortified with 50 ppb rare earth produced about 300–500 cps at the corresponding half-mass with %RSD across the 10 replicates of 12%. A 1 ppb Se standard in narrow resolution mode using 2.5 mL He produces 51 cps with a 19 cps blank. All in-sample M2+ estimates required manual abundance-sensitivity evaluations at the adjacent masses to the M2+ ion.

6.

Data were collected using m/z 94 in oxygen mode at 0.5 mL/min with a 0.99-sec/amu integration time in selective ion monitoring mode. All estimates are based on n = 5 using Y as an internal standard (YO+, 89→105). The calibration blank and 1 ppb Se standard produced 7 cps and 351 cps, respectively.

7.

Selenium data were collected with an EScan over the mass range of 77.912–77.922 amu with a sampling time of 0.200 sec, 40 samples per peak, and 30% search and 60% integration windows over 3 runs and 2 passes (n = 6). All data were collected in high-resolution mode, and concentrations were determined relative to the 115In internal standard. The Auto Lock Mass feature was active during analysis.

8.

This sample was fortified with 0.050 ppb As and 1 ppb Se.

9.

All regional waters were prepared to reflect the 0.4% HCl concentration that results from an acid digestion according to Method 200.8.