Bufi Poster March 2011

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    XENON INTERFERENCE

    Since ICP-MS differetiates by m/z of ions, 129I + is indistinguishable from 129Xe +, acontaminant in the carrier gas. Without correction for 129Xe, responses such as Figure 2ahave been obtained: peaks occur which look similar to 129I but are actually due to 129Xe. Inthis case the 129Xe peaks did not interfere with the iodide/iodate regions, but did have thesame shape and size as genuine iodine peaks and so could give misleading results.

    By measuring a second isotope of Xe (131Xe), a correction factor (CF) can be applied withinthe ICP-MS software, based on the expected ratio of129Xe/ 131Xe. However this approach

    has been shown to over-correct for 129Xe interference. Instead the CF is now determinedfor each run, based simply on reducing the background 129-signal to zero as shown inFigure 2b. If possible, it would be preferable to reduce 129Xe interference within the ICP-MSrather than correcting the data afterwards. This was attempted by using reaction gasesintroduced into the hexapole chamber between the cones and quadrupole (Figure 1).

    OPTIMISING IODINE ANALYSIS BY ICP-MSSmith, H. E.1,2*, Ander, E. L.2, Bailey, E. H.1, Crout, N. M. J.1, Watts, M. J.2, Young, S. D.1

    1 Division of Agricultural and Environmental Sciences, Biology Building, University of Nottingham, University Park, Nottingham, NG7 2RD.2British Geological Survey, Kingsley Dunham Centre, Keyworth, Nottingham NG12 5GG. HES: [email protected]

    Figure 3: Proposed charge transfer mechanism forremoval of xenon interference

    USING A REACTION GAS

    It has been reported that using ICP-MS in collision/reaction cell mode can improveiodine signal-to-noise ratios. Some authors have used hydrogen and/or helium[1,2],which are commonly used reaction gases, but more success has been reported whenusing oxygen[3-6]. The suggested mechanism[4] by which oxygen could remove xenoninterference from 129I analysis may be by charge transfer to reduce Xe+ to Xe0,illustrated in Figure 3. Only charged particles are transferred through the quadrupole tothe detector, and reportedly xenon reacts much faster with oxygen than iodine does.

    H2 and He were tested as reaction gases for this project, but neither removed the129

    Xeinterference. Oxygen is being considered for future work but there are important safetyfactors to be assessed before it is used. Therefore the xenon CF based on removingbackground 129 counts will continue to be applied to iodide/iodate chromatograms of129I tracer in soil extracts as investigation into iodine behaviour in soil continues.

    REFERENCES

    [1] St Remy, R. R. D. et al. (2004). Journal of Analytical Atomic Spectrometry 19(9): 1104-1110[2] Becker, J. S. (2002). Journal of Analytical Atomic Spectrometry 17(9): 1172-1185[3] Brown, C. F. et al. (2007). Applied Geochemistry 22(3): 648-655

    [4] Reid, H. J. et al. (2008). Talanta 75(1): 189-197[5] Izmer, A. V. et al. (2004). Journal of Analytical Atomic Spectrometry 19: 1278 - 1280[6] Wang, K. E. and S. J. Jiang (2008). Analytical Sciences 24(4): 509-514

    Figure 2a: Effect of xenon interference

    INTRODUCTION

    Iodine is essential for healthy human life, and insufficient intake can result in reduced mental and physicalwell-being, with social and economic impacts for affected communities. Iodine presence in foods relies uponsufficient uptake from the soil. In some circumstances however, even when there is plenty of iodine presentin soil, deficiency in food, crops and grazed pasture may occur.

    This PhD project focuses on understanding how soil properties affect availability of iodine to plants, inparticular pasture grazed by livestock. Thus the adsorption and transformation of iodine in response to soilcharacteristics including composition and pH are being studied in soils from Northern Ireland.

    In order to model the behaviour of iodine in soil, the long-lived radioisotope 129I (t0.5 = 15.7 million years) isbeing added to soils and followed as a proxy for natural iodine. Therefore accurate analysis of iodine species(e.g. iodide, I-, and iodate, IO3

    -) in soil extracts is required. This has involved development of analysis usingHPLC-ICP-MS: high pressure liquid chromatography separates iodine species before detection of specificisotopes by ICP-MS. This poster concentrates on one aspect of analysis, and the challenges investigated.

    Figure 2b: Xenon correction factor applied

    Iodine in soil

    Iodine essential

    in human diet

    ICP-MS

    Inductively coupled plasma mass spectrometry (ICP-MS)separates and detects ions according to their mass to chargeratio, m/z. This allows differentiation between naturally occurringiodine, 127I, and 129I which is added to samples as a tracer.

    Samples are introduced to the ICP-MS as liquids via a nebuliser,which creates an aerosol that is mixed with argon as a carriergas. The fine mist is separated from larger liquid droplets in thespray chamber before moving into the torch, where it is ionisedin plasma at extremely high temperatures. The cones direct andfocus the ion beam into the mass spectrometer, where ions areseparated on the basis of their m/z ratio and finally detected asnumber of counts per second.

    Figure 1: Schematic diagram of inductively coupled plasma mass spectrometer

    Direction of sample flow

    IodideIodate

    NebuliserSpraychamber

    Torch

    ConesQuadrupole:massseparator

    Detector

    IodideIodate

    129Xe+ 129Xe

    O2

    O2+

    129I+

    129I+