&OAE- 9b I 0 IS& - - I Determination of Plutonium in Urine: Evaluation of Electrothermal Vaporization Inductively Coupled Plasma Mass Spectroscopy.

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BNL-6 34 70 &OAE- 9b I 0 IS& - - I Determination of Plutonium in Urine: Evaluation of Electrothermal Vaporization Inductively Coupled Plasma Mass Spectroscopy., t Richard Pietrzak and Edward Kaplan Brookhaven National Laboratory ABSTRACT Mass spectroscopy has the distinct advantage of detecting atoms rather than radioactive decay products for nuclides of low specific activity. Electrothermal vaporization (ETV)is an efficient means of introducing small volumes of prepared samples (<100 ul) into an inductively coupled mass spectrometer (ICPMS) to achieve the lowest absolute detection limits. The operational characteristics and capabilities of ETVhCPMS were evaluated. We describe its application as a detection method for determining Pu in urine, in conjunction with a preliminary separation technique to avoid matrix suppression of the signal. Introduction Urine and water samples have been analyzed for isotopic plutonium by alpha spectroscopy (1-3) and later by Moorthy et al., by fission track analysis (4). Detection limits of 170 pbq and 4 pbq were reported, respectively. In the less familiar fission track procedure, Pu-239 is detected by subjecting the sample, prepared on a quartz slide, to thermal neutron-induced fission. Fission fragments are observed by optical microscopy as tracks on the quartz slide. The fission track method requires a two-step anion-exchange separation with highly purified reagent acids in a dust-free environment and is s m c for detecting any fissionable isotope. Recent improvements to the fission track methodology appear to have lowered its detection limit below about 1 pbq (5). a This work was performed under the auspices of the U.S. Department of Energy under Contract DEAC0276CH00016

Mass spectroscopy as a detection method offersthe possibiity of multi-element determination and Simplified chemical preparation, with a sensitivity between that of alpha spectroscopy and fission track analysis. Several types of commercial mass spectrometers are available. Thermal ionization mass spectroscopy has been used extensively but preparation of the sample is difficult; ICPMS is much more convenient for rapid analysis. Wyse and Fisher (6) reported detecting plutonium by mass spectroscopy, using an ultrasonic nebulizer system for introducing the sample in a peak jumping mode for multi-element determination. A detection limit (3u) of 50 fg (1 10 pbq) for Pu-239 was observed. Hall and others (7) earlier reported a detection limit of 2 fg Pu-244 and 0.8 fg U-235 by ETVDCPMS using the single ion monitoring (SIM) mode to demonstrate the capability of the technique, using acidified standards. The ETV/ICP/MS technique was reviewed recently by Carey and Caruso (8). Experimental An ICP/MSbwas used in conjunction with an ETV unit for introducing the sample. Plutonium was initially co-precipitated with calcium rhodizonate from urine (3). The dried precipitate was wetashed in an open-vessel automated microwave digester" with nitric acid and hydrogen peroxide to remove organic residues and solubilize the inorganic materials (1-4). The sample's matrix elements were removed by an anion-exchange separation based on the methods described for alpha spectroscopy and fission track analysis (43). The use of ETV to introduce the sample and the SIM mode maximized the sensitivity of detection by minimizing the volume of the final sample, eliminating the introduction of solvent into the plasma, and focusing on a single isotope. A standard solution containing 50 ppb uranium was used initially to tune the mass spectrometer and maximize the detection signal. The heating profile and the carrier gas-flow in the ETV unit was then adjusted to obtain a signal for Pu-239. Plasmaquad 11+ and Microtherm 111, Fison Instrument Company, MerrimaC, MA 01860 e Prolabo A301, Questron Corp., Mercerville, NJ 08619 2

i DISCLAIMER This report was prepared as an account of work sponsored by an agency of the United States Government. Neither the United States Government nor any agency thereof, nor any of their employees, makes any warranty, express or implied, or assumes any legal liability or responsibility for the accuracy, completeness, or usefulness of any information, apparatus, product, or process disclosed, or represents that its use would not infringe privately owned rights. Reference herein to any specific commercial product, process, or service by trade name, trademark, manufacturer, or otherwise does not necessarily constitute or imply its endorsement, recommendation, or favoring by the United States Govcmment or any agency thereof. The views and opinions of authors expressed herein do not noccssarily state or reflect thosc of the United States Government or any agency thereof.

DISCLAIMER Portions of this document may be illegible in electronic image products. Images are produced from the best available original document..

Results and Discussion Pu-239, prepared f?om the National Institute of Standards and Technology W S T ) traceable standard solutions in nitric acid, was used to calibrate the ETV/ICP/MS detection system. Current results give a detection limit of 2 fg, (4 @q) based on 3a of the background for Pu-239 with artificial urine blanks. Artificial urine samples containing known amounts of Pu-239 were used to determine the chemical recovery during the separation process. Future analyses will be performed on synthetic urine used in fission track detection of Pu-239, with a long-term goal of using ICP/MS/ETV for routine bioassays of activities in humans and the environment. References 1. Fisenne, I.M., Plutonium in Urine PU-06, EML Procedure Manual, G. de Planque, P. W. Krey, N. A. Chieco, D. C. Bogen and E. 0. Knutson, editors, 27 edition, pp 4.5-108, Environmental Measurements Laboratory, NY, NY (1990). 2. Standard Test Method for Plutonium in Water, D 3865-90, pp 380-383, 1991 Annual Book of ASTM Standards, vol. 11.02 Water (II). 3. Weiss, H. V. and W. H. Shipman, Radiochemical Determination of Plutonium in Urine, Analytical Chemistry, Vol. 33, No. 1, pp 37-39 (1961). 4. Moorthy, A. R.,Schopfer, C. J. and S. Banejee, Plutonium fiom Atmospheric Weapons Testing: Fission Track Analysis of Urine Samples, Analytical Chemistry, 60, 857A (1988). 5. Moorthy, AR and Doty, RM., Procedure for HPLCETA Pu-239 Separations, Unpublished (1 996). 3

A 6. Wyse, E. J. and Fisher, D. R., Radionuclide Bioassay by Inductively Coupled Plasma Mass Spectrometry (ICPMS), Radiation Protection Doshetry, Vol. 55, No. 3, pp 199-206 (1994). 7. Hall, R. J. B., James, M. R., Wayman, T. and Hulmston, P., The Feasibility of the Use of Electrothermal Vaporization Inductively Coupled Plasma Mass Spectrometry for the Determination of Femtogramme Levels of Plutonium and Uranium, Plasma Source Mass Spectrometry, The Proceedings of the Third Surrey Conference on Plasma Source Mass Spectrometry, Royal Society of Chemistry, London England, pp 145-154 (1989). 8. Carey, J. M. and Caruso, J. A., Electrothermal Vaporization for Sample Introduction in Plasma Source Spectrometry, Critical Reviews in Analytical Chemistry, 23(5): 397-439 (1992). 4