Optimizing Peak Separation for Simultaneous Pu and U Measurements Shane Knockemus US EPA / NAREL May 3, 2005.

Slides:



Advertisements
Similar presentations
NUCP 2371 Radiation Measurements II
Advertisements

Introduction to Chromatography
Lecture 8b Gas Chromatography.
Error Characterization of the Alpha Residuals Emissivity Extraction Technique Michael C. Baglivio, Dr. John Schott, Scott Brown Center for Imaging Science.
Study of plastic scintillators for fast neutron measurements
Physics Results of the NA49 exp. on Nucleus – Nucleus Collisions at SPS Energies P. Christakoglou, A. Petridis, M. Vassiliou Athens University HEP2006,
Phytoplankton absorption from ac-9 measurements Julia Uitz Ocean Optics 2004.
Rapid Actinide Analysis for Large Soil Samples
Resolve™ Filters for alpha source preparation Charleston, SC May 4, 2004.
Uranium and Thorium Distributions in the Sediments Collected from the Western South Okinawa Trough and the Northern South China Sea Chun-Yen Wang, Li-Wen.
Spectrum Identification & Artifacts Peak Identification.
Chem. 31 – 4/15 Lecture. Announcements I Exam 2 – Hope to have graded by next Monday Lab Reports –AA report now due Monday, 4/20 (best to try to complete.
Adding electronic noise and pedestals to the CALICE simulation LCWS 19 – 23 rd April Catherine Fry (working with D Bowerman) Imperial College London.
Chapter 14 Applications of Ultraviolet-Visible Molecular Absorption Spectrometry.
Optimizing Radiochemical Methods at SRS
RHESSI/GOES Xray Analysis using Multitemeprature plus Power law Spectra. J.McTiernan (SSL/UCB)
RHESSI/GOES Xray Analysis using Multitemeprature plus Power law Spectra. J.McTiernan (SSL/UCB) ABSTRACT: We present spectral fits for RHESSI and GOES solar.
Qualitative, quantitative analysis and “standardless” analysis NON DESTRUCTIVE CHEMICAL ANALYSIS Notes by: Dr Ivan Gržetić, professor University of Belgrade.
Rapid Separation Methods for Bioassay Samples S. L. Maxwell, III and D. J. Fauth Westinghouse Savannah River Site.
FMS review, Sep FPD/FMS: calibrations and offline reconstruction Measurements of inclusive  0 production Reconstruction algorithm - clustering.
MnO 2 Resin: Concentration of Radium Isotopes Deok-Soo Moon Bill Burnett Department of Oceanography Florida State University Tallahassee, Florida.
The Determination of 226 Ra in Water Samples Anil H. Thakkar Eichrom Technologies, Inc. eichrom TECHNOLOGIES INC.
MultiSimplex and experimental design as chemometric tools to optimize a SPE-HPLC-UV method for the determination of eprosartan in human plasma samples.
The Determination Of 226 Ra In Soil Samples Lawrence D. Morris General Engineering Laboratories, Inc. Anil H. Thakkar Eichrom Technologies, Inc.
Cube Measurements Tent Crew. Scintillation BNL 241 Am Semi- collimated  Spectralon Diffuse UV Reflector SBD  -Trigger Scint. Light Poisson.

SuperNEMO Simulations Darren Price University of Manchester July, 2005.
Rapid Actinide Analysis for Large Soil Samples-Update Sherrod L. Maxwell, III Westinghouse Savannah River Company.
MnO 2 Resin: Concentration of Radium Isotopes Deok-Soo Moon Bill Burnett Department of Oceanography Florida State University Tallahassee, Florida.
Simultaneous determination of inorganic anions and cations by capillary electrophoresis with indirect UV detection I. Haumann, J. Boden, A. Mainka, U.
MS Calibration for Protein Profiles We need calibration for –Accurate mass value Mass error: (Measured Mass – Theoretical Mass) X 10 6 ppm Theoretical.
General Engineering Laboratories Use of Eichrom Resins for Bioassay Pa-231 Bob Timm - GEL Tim Chandler - GEL Bill Burnett - FSU Mike Schultz - PerkinElmer.
Developments in Environmental Radiochemistry* Environmental Radioactivity Measurement Facility Department of Oceanography Florida State University Tallahassee,
Working Through Mistakes, Miscues, and Mishaps in Actinide Separations Shane Knockemus US EPA / NAREL Montgomery, AL May 4, 2004.
New Extraction Methods for Actinides in Urine at SRS Sherrod L. Maxwell III and David Fauth Savannah River Site.
DEVELOPMENT OF BETA SPECTROMETRY USING CRYOGENIC DETECTORS M. Loidl, C. Le-Bret, M. Rodrigues, X. Mougeot CEA Saclay – LIST / LNE, Laboratoire National.
COSIRES 2004 © Matej Mayer Bayesian Reconstruction of Surface Roughness and Depth Profiles M. Mayer 1, R. Fischer 1, S. Lindig 1, U. von Toussaint 1, R.
Th, Pu & U Separation Using TEVA and UTEVA Resin
Recent Improvements in Rapid Column Separation Methods at SRS
e- beam 2D sample e- beam 3D
Optimization of Analysis Cuts for Oscillation Parameters Andrew Culling, Cambridge University HEP Group.
Compensation for Radon Decay Products in Air Monitoring Applications Using Alpha Peak-Shape Fitting David K. Baltz Chief Technologist Bladewerx LLC Rio.
Peterson xBSM Optics, Beam Size Calibration1 xBSM Beam Size Calibration Dan Peterson CesrTA general meeting introduction to the optics.
Optimizing Radiochemical Methods at SRS (Ni-63, I-129, Actinides) Sherrod L. Maxwell, III Westinghouse Savannah River Company.
Kinetic Methods. Rates In order to use a reaction for analytical purposes, the reaction must have a rate slow enough to measure but fast enough to get.
1 Chapter No. 17 Radiation Detection and Measurements, Glenn T. Knoll, Third edition (2000), John Willey. Measurement of Timing Properties.
Pyrosulfate fusion vs. TEVA / TRU forcing the issue Shane Knockemus U.S. EPA / NAREL Montgomery, AL November 11, 2002.
Lecture 8 Peak Parameters and Quantitative chromatography
 A) Pulse Height Spectroscopy  Identify the equipment such as detector, electronics modules and NIM.
Downloaded from کروماتوگرافی CHROMATOGRAPHY Downloaded from
1 Chapter No. 9 Measurements and Detection of Radiation, Nicholas Tsolfanadis, 2010, McGRAW-HILL BOOK INTRODUCTION TO SPECTROSCOPY.
Status of ULE-HPGe Experiment for WIMP Search in YangYang
A Paradigm Shift in nuclear spectrum analysis
Chem. 133 – 5/11 Lecture.
An Introduction to Chromatographic Separations
The Determination of 226Ra in Water Samples
Tracking results from Au+Au test Beam
Chem. 133 – 2/16 Lecture.
General Properties of Radiation
Box and Whisker Plots.
Technical Updates on TRU and TEVA Resins
EMCal Recalibration Check
Rapid Emergency Methods for Actinides and Sr-89/90
An-Najah National University Research Day in Theoretical and Applied Physics    "Measurement of Natural Radioactivity in Some Granite Samples : Prelimenary.
EMCal Recalibration Check
Monoenergetic Neutrino Beam for Long Baseline Experiments
Problems with the Run4 Preliminary Phi->KK Analysis
Psychological Measurement: Reliability and the Properties of Random Errors The last two lectures were concerned with some basics of psychological measurement:
National Air and Radiation Environmental Lab
Graphing.
Presentation transcript:

Optimizing Peak Separation for Simultaneous Pu and U Measurements Shane Knockemus US EPA / NAREL May 3, 2005

Why would anyone be interested in simultaneous determination of Pu and U?  Increased laboratory efficiency due to a higher degree of sample throughput.  Laboratory production would be increased. Twice as many alpha spec detectors would be available for use.  Why do something twice when once is enough?

Goal  I hope to show that a simultaneous determination of Pu and U is possible through manipulating important variables. Such variables include:  mass of carrier used during fluoride precipitation  counting the sample at different shelf heights in the alpha spec chamber  type of filter employed.

Pu and U measured simultaneously?  First noticed the possibility after a mistake during sample separation.

 Studies have been concentrated on source preparation involving a cerium fluoride coprecipitation.  No testing of source preparation with respect to electrodeposition was included in the study.

Experiment parameters  TEVA / TRU separation scheme was used. There are many possible scenarios that could enable simultaneous Pu and U elution.  Pu and U eluted together with ammonium oxalate from TRU.  Pu and U precipitated together in the presence of TiCl 3.  0.2 um filters used during filtration, later Resolve filters were used.  Varying amounts of Ce +3 used.  Varying shelf height in alpha spec chambers.

Full Width Half Maximum (FWHM)  FWHM simply refers to peak width. It is defined as “the width of the distribution at a level that is just half the maximum ordinate (centroid) of the peak.” FWHM is measured in terms of energy (keV) or channel numbers.  Good resolution is a necessity to measurement by alpha spec, and is highly dependent on source preparation and deposition.

FWHM Diagram centroid y y/2 Width of peak in keV at y/2

Carrier mass and FWHM  FWHM values increase with the amount of carrier mass added during fluoride precipitation

Finding the optimum mass of carrier to use  How much does the mass of carrier used during precipitation affect the tracer recovery? –Experiments involving ug of Ce all showed consistently high yields, usually 90+%. –Experiments involving 25 ug had yields that were consistent, but were less than yields of those precipitated with ug of Ce, usually 75-85% –Some experiments involving 10 ug of Ce were also done. These provided yields that were inconsistent and often very low.

Spectra comparison 200 ug Ce 100 ug Ce

Regions of concern  Listed are nuclides whose energies could possibly overlap without optimum peak separation U keV Pu keV Pu keV U keV U-232 Pu keV

Zoom 100 ug Ce high shelf

Spectrum from 25 ug Ce 25 ug zoom Peak separation is better But still needs improvement

FWHM and peak separation  Good FWHM values do not always translate into adequate peak separation. All FWHM values from this spectrum are less than 80 keV, but peak separation is an obvious problem. Without any peak fitting manipulations, the measured analyte activities would be questionable.

How to improve peak separation?  All of the previous samples were counted on the top shelf in alpha spec chamber. If the shelf height of the sample were lowered, the resolution and peak separation should improve. Doing this would decrease the efficiency. If you can sacrifice some efficiency in exchange for improved peak separation, this may be advantageous.

Bottom shelf spectra 200 ug Ce 100 ug Ce

Spectrum of 25 ug Ce on bottom shelf

Zoom of 25 ug Ce on bottom shelf

More spectra with 25 ug Ce on low shelf

Does the type of filter used make a difference in peak separation and resolution? Does the type of filter used make a difference in peak separation and resolution?

Progression of improvements 100ugCe-high 100ugCe-low25ugCe-low 25ugCe-low-Resolve

Experiment results  The samples used for the experiments were 1 liter tap water samples and were spiked ‘in house’ with known amounts of activity.  The recoveries of the spiked analytes were very good and in acceptable ranges when the peak separation was adequate.  Experiment scenarios that produced incomplete peak separation of analyte and tracer peaks were a problem to quantify accurately. The use of peak fitting may be a useful tool.

Discussion and conclusion  There are many factors to consider if simultaneous measurement of Pu and U were to become a reality. Experiments showed a noticeable improvement in peak separation. The combination of minimizing the mass of carrier used and counting the sample on a lower shelf was effective, but both of those adjustments also have their drawbacks. Such drawbacks include a decreased counting efficiency and a slightly lower yield.