Analysis of High Enriched Uranyl Nitrate Solution Containing Cadmium

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INL/CON-05-01002 PREPRINT Analysis of High Enriched Uranyl Nitrate Solution Containing Cadmium PHYSOR-2006 Topical Meeting Soon Sam Kim September 2006 This is a preprint of a paper intended for publication in a journal or proceedings. Since changes may not be made before publication, this preprint should not be cited or reproduced without permission of the author. This document 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, or any of their employees, makes any warranty, expressed or implied, or assumes any legal liability or responsibility for any third party s use, or the results of such use, of any information, apparatus, product or process disclosed in this report, or represents that its use by such third party would not infringe privately owned rights. The views expressed in this paper are not necessarily those of the United States Government or the sponsoring agency.

Analysis of High Enriched Uranyl Nitrate Solution Containing Cadmium Soon Sam Kim * Idaho National Laboratory P. O. Box 1625, Idaho Falls, ID 83415-3458, U.S.A. Abstract A benchmark evaluation has been performed for a set of twenty-one critical experiments involving high enriched uranyl nitrate solution with and without cadmium nitrate as a soluble neutron absorber. The critical experiments analyzed include two types of cylindrical vessels with 24.18 and 29.16 cm in diameters. The vessels were reflected with water and in some cases with water containing dissolved cadmium nitrate. The uranium concentration ranged from 482 to 529 g/l, and cadmium concentration in the uranyl nitrate solution ranged from 0.0 to 11.31 g/l. The cadmium concentration in the reflector solution ranged from 0.0 to 15.16 g/l. Using MCNP and KENO-V.a, complete three-dimensional models were created for the two vessels filled with the uranyl nitrate solution and reflector solution. A series of criticality calculations was performed with KENO-V.a, MCNP4b (with ENDF/B-V data), and MCNP5 (with ENDF/B-VI data). In general, good agreement between KENO-V.a and MCNP4b was observed. However, MCNP5 results show consistently lower values compared with MCNP4b results with the maximum difference of 1.2 %. This ICSBEP supported evaluation provides valuable data for the effect of soluble neutron absorber (cadmium nitrate) on the criticality safety of high-enriched uranyl nitrate solution. These data can also be used in determining critical controls and for validation of the calculation methods. KEYWORDS: Criticality Safety, High-Enriched Uranium, Uranyl Nitrate Solution, Cadmium Nitrate 1. Introduction Twenty-one critical experiments involving high-enriched (~85 wt% 235 U) uranyl nitrate solution containing soluble cadmium nitrate absorber were performed [1] in 1978 and 1979 at the Pacific Northwest Laboratory. The experiments were conducted to validate criticality safety calculations by Allied Chemical Corporation (later known as Westinghouse Idaho Nuclear Company) in the design of proposed fluorinel process dissolver. The critical experiments consisted of a cylindrical experimental vessel filled with high-enriched uranyl nitrate solution with and without cadmium nitrate as a soluble neutron absorber. Water with and without cadmium nitrate was used as the reflector. Evaluation of this set of experiments was accepted by the International Criticality Safety Benchmark Evaluation Project (ICSBEP), as a benchmark [2]. * Corresponding author, Tel. 208-526-7634, Fax. 208-526-0518, E-mail: soon.kim@inl.gov

2. Critical Experiments The critical experiments were conducted inside the Critical Mass Laboratory at the Pacific Northwest Laboratory. A simplified diagram of the experiment is shown in Fig. 1. Figure 1: A simplified diagram of experiments. The experiments were performed using two cylindrical vessels. Experiments 001 through 008 were performed using a 24.18-cm-ID vessel (see Fig. 2). Experiments 009 to 021 were performed using a 29.16-cm-ID vessel (Fig. 3).

Figure 2: Experimental diagram with 24.18-cm ID vessel.

Figure 3: Experimental diagram with 29.16-cm ID vessel. The solution was pumped from a slab storage tank to the experimental vessel. Cadmium nitrate was added in measured amounts to the uranyl nitrate in the slab tank, and the solution was thoroughly mixed prior to use in each of the experiments. Neutron absorbing safety and control blades or rods (not shown in the figures) were provided. In the case of the 24.18-cm-ID vessel, curved safety and control blades (304L stainless steel clad cadmium sheet) were positioned in the reflector region at the interface of the vessel wall. For the larger (29.16-cm-ID) vessel, Zircaloy clad cadmium-lucite rods were used for control and safety rods. These rods were placed directly in the uranyl nitrate solution for increased effectiveness [1]. With the control rod fully inserted, uranyl nitrate solution was pumped to the experimental vessel to a desired height, then the control rod was withdrawn until it no longer influenced the reactivity of the experiment. The process of adding solution to the cylinder, then withdrawing

the control rod was repeated until the critical height was determined. The neutron count rate from three neutron detectors was recorded following each solution addition. As the solution level was raised, the inverse count rate as a function of solution height was plotted. The inverse count rate plot was then extrapolated to determine the critical height. The size of the extrapolation was less than a half-inch, which corresponds to less than 0.028 in reactivity. The system was secured by inserting both rods and draining the solution to the slab tank. Table 1 summarizes the experimental data from the twenty-one critical configurations. The uranium concentration ranged from 481.99 to 528.76 g/l of uranium as uranyl nitrate. The cadmium concentration in the uranyl nitrate solution ranged from 0.0 to 11.33 g/l. The cadmium concentration in the reflector solution ranged from 0.0 to 15.18 g/l. Experiment 018 was the same as Experiment 017, and therefore, not considered as separate experiment. For all of the experiments, the reflector solution was maintained at the lower level of the upper end cap of the experimental vessel. The uranium isotope composition of the solution is shown in Table 2. The uranyl nitrate solution used in the experiments came from six reserved product canisters. The enrichments of the six canisters ranged from 83.90 to 85.96 wt.% U-235. Table 1: Composition of twenty-one critical configurations. Expr. Date Expr. No. Solution Sample No. Specific Gravity Uranyl Nitrate Solution Excess Nitric Acid Uranium (mg/g) Cadmium (mg/g) Solution Sample No. Reflector Solution Specific Gravity Cadmium (mg/g) Solution Height Critical Height (cm) 24.18-cm-ID Vessel 9/26/78 001 830 1.65919 0.22773 293.845 0.0-1.0 0.0 22.3520 9/27/78 002 831 1.66006 0.21369 294.175 0.0 854 1.02257 14.848 31.2674 9/28/78 003 832 1.66092 0.23976 292.98 1.208-1.0 0.0 28.1940 9/29/78 004 833 1.66092 0.23374 291.34 2.393-1.0 0.0 37.8460 9/29/78 005 834 1.66284 0.30312 290.38 3.897-1.0 0.0 76.3524 1/29/79 006 837 1.72322 0.23575 306.435 4.069-1.0 0.0 82.2198 1/30/79 007 838 1.72532 0.23374 306.79 4.196-1.0 0.0 92.4814 2/2/79 008 839 1.72606 0.32660 306.935 4.279-1.0 0.0 98.6282 839 (a) 1.72597 0.23374 306.86 4.262 29.16-cm-ID Vessel 2/16/79 009 842 1.68007 0.30393 298.38 0.0-1.0 0.0 17.8308 2/22/79 010 843 1.68041 0.30192 298.76 0.0 855 1.0151 10.596 21.4884 855 (a) - 10.600 2/23/79 011 844 1.69471 0.27385 301.175 1.240 855 1.0151 10.598 26.5938 2/26/79 012 845 1.70589 0.26583 303.38 2.250 855 1.0151 10.598 32.7406 2/27/79 013 846 1.70729 0.25781 302.03 3.362 855 1.0151 10.598 42.9006 2/28/79 014 847 1.70781 0.25380 301.84 4.189 855 1.0151 10.598 57.9374 3/1/79 015 848 1.70869 0.24778 300.945 4.577 855 1.0151 10.598 71.6280 3/2/79 016 849 1.70851 0.24979 300.775 4.897 855 1.0151 10.598 87.0204 3/5/79 017 850 1.70921 0.25380 301.065 5.049 856 1.01175 9.519 98.1456 3/7/79 018 850 (a) 1.70848 0.35621 301.095 5.044 856 (a) - 9.511 98.0948 3/12/79 019 851 1.71041 0.35621 301.555 5.032-1.0 0.0 46.4312 3/13/79 020 852 1.70956 0.26583 300.33 5.937-1.0 0.0 64.2874 3/13/79 021 853 1.71021 0.36744 302.06 6.626-1.0 0.0 102.362 (a) Second Analysis of the Sample.

Table 2: Uranium isotopic composition (wt%). Expr. No. Sample No. 234 U 235 U 236 U 238 U 24.18 cm-id Vessel 001 830 0.94 85.27 3.47 10.32 002 831 0.94 85.27 3.47 10.32 003 832 0.94 85.24 3.48 10.34 004 833 0.93 85.28 3.47 10.32 005 834 0.94 85.26 3.47 10.33 006 837 0.94 85.21 3.47 10.38 007 838 0.94 85.16 3.47 10.43 008 839 0.93 85.19 3.47 10.41 008 839(b) 0.94 85.17 3.47 10.42 29.16-cm-ID Vessel 009 842 0.85 84.29 1.40 13.46 010 843 0.86 84.28 1.39 13.47 011 844 0.87 84.55 2.00 12.58 012 845 0.89 84.76 2.49 11.86 013 846 0.89 84.74 2.49 11.88 014 847 0.89 84.74 2.49 11.88 015 848 0.90 84.77 2.49 11.84 016 849 0.89 84.72 2.50 11.89 017 850 0.89 84.77 2.50 11.84 018 850 (a) 0.90 84.75 2.49 11.86 019 851 0.90 84.78 2.49 11.83 020 852 0.90 84.76 2.49 11.85 021 853 0.90 84.72 2.49 11.89 (a) Second analysis of the sample. 3. Experiment Modeling Using MCNP [3, 4] and KENO-V.a from SCALE [5], a complete model of the experimental system was created for the 24.18-cm-ID vessel (see Fig. 4). A similar model was created for the 29.16-cm-ID vessel (see Fig. 5). The top flange, Plexiglas cap, and seal plate were explicitly modeled. Twenty individual critical solution heights with different solution densities were modeled. For all of the experiments, the top of the reflector solution level was positioned at 107.315 cm from the bottom of the experimental vessel.

Figure 4: XZ view showing the 24.18-cm-ID experimental vessel.

Figure 5: XZ view showing the 29.16-cm-ID experimental vessel.

4. Results A series of criticality calculations was performed for the 20 experiments with KENO-V.a, MCNP4b, and MCNP5. The 44-group ENDF/B-V cross-section data used in the KENO-V.a runs were based on 20 C. The continuous-energy ENDF/B-V cross-section data of the MCNP4b, and the ENDF/B-VI cross-section data of MCNP5 runs were based on 27 C. Table 3 summarizes these results, showing good agreement between KENO and MCNP4b. MCNP5 results show consistently lower values compared with MCNP4b results, with the maximum difference of 1.2 %. Table 3: KENO-V.a, MCNP4b and MCNP5 results. Expr No. Critical Solution Height (cm) H/ 235 U Uranyl Nitrate Solution Cd/ 235 U Cadmium (mg/g) Cadmium in Reflector (mg/g) KENO-V.a (44-Group ENDF/B-V) MCNP4b (Continuous Energy ENDF/B-V) MCNP5 (Continuous Energy ENDF/B-VI) 01 22.3520 52.5 0.0 0.0 0.0 1.0043 0.0004 1.0023 0.0004 0.9972 0.0004 02 31.2674 52.4 0.0 0.0 14.848 0.9972 0.0004 1.0008 0.0004 0.9948 0.0004 03 28.1940 52.5 0.0101 1.208 0.0 1.0025 0.0004 1.0005 0.0004 0.9928 0.0004 04 37.8460 52.8 0.0201 2.393 0.0 1.0044 0.0005 1.0003 0.0004 0.9917 0.0004 05 76.3524 52.6 0.0329 3.897 0.0 1.0059 0.0004 1.0024 0.0004 0.9922 0.0004 06 82.2198 47.4 0.0326 4.069 0.0 1.0101 0.0004 1.0066 0.0004 0.9956 0.0004 07 92.4814 47.3 0.0336 4.196 0.0 1.0097 0.0005 1.0064 0.0004 0.9958 0.0004 08 98.6282 47.1 0.0342 4.2705 0.0 1.0089 0.0003 1.0054 0.0004 0.9943 0.0004 09 17.8308 51.3 0.0 0.0 0.0 1.0027 0.0004 1.0006 0.0004 0.9960 0.0004 10 21.4884 51.2 0.0 0.0 10.598 0.9949 0.0004 0.9942 0.0004 0.9881 0.0004 11 26.5938 50.0 0.0102 1.24 10.598 0.9999 0.0004 0.9974 0.0004 0.9893 0.0004 12 32.7406 49.0 0.0183 2.25 10.598 1.0022 0.0004 0.9997 0.0004 0.9896 0.0004 13 42.9006 49.2 0.0275 3.362 10.598 1.0032 0.0003 1.0006 0.0004 0.9894 0.0004 14 57.9374 49.1 0.0342 4.189 10.598 1.0041 0.0003 1.0007 0.0004 0.9890 0.0004 15 71.6280 49.3 0.0375 4.577 10.598 1.0054 0.0003 1.0022 0.0004 0.9908 0.0004 16 87.0204 49.3 0.0402 4.897 10.598 1.0046 0.0003 1.0014 0.0004 0.9894 0.0004 17 98.1202 49.0 0.0413 5.0465 9.515 1.0037 0.0003 1.0011 0.0004 0.9883 0.0004 19 46.4312 48.7 0.0412 5.032 0.0 1.0048 0.0005 1.0009 0.0004 0.9895 0.0004 20 64.2874 49.2 0.0488 5.937 0.0 1.0045 0.0003 1.0018 0.0004 0.9905 0.0004 21 102.362 48.2 0.0541 6.626 0.0 1.0034 0.0004 0.9994 0.0004 0.9876 0.0004 KENO-V.a calculations were also performed for the 24.18-cm-ID and the 29.16-cm-ID vessels to calculate the worth of cadmium in the uranyl nitrate solution. Table 4 summarizes results for Experiments 03, 08, 11, and 21. Table 4: KENO-V.a cadmium worth results.. Experiment No. Cd (mg/cm 3 ) With Cd Without Cd k eff 03 2.003 1.0025 0.0004 1.0633 0.0006 6.08 08 7.358 1.0089 0.0003 1.2024 0.0006 19.35 11 2.098 0.9999 0.0004 1.0604 0.0004 6.05 21 11.312 1.0034 0.0003 1.2968 0.0004 29.34

This ICSBEP supported evaluation provides valuable data for the effect of soluble neutron absorber (cadmium nitrate) on the criticality of high-enriched uranyl nitrate solution. These data can also be used in determining criticality controls and for validation of the calculation methods. Acknowledgements The author would like to thank Linda Sandoval of Los Alamos National Laboratory for help in retrieving experimental logbook. He is grateful to Blair Briggs and Todd Taylor of Idaho National Laboratory for providing notes and letter files that contain valuable information about analysis of the experiments. Special acknowledgment is given to B. M. Durst who provided answers for some key questions about the experiments. References 1) R. C. Lloyd, et. al., Critical Experiments Using High-Enriched Uranyl Nitrate with Cadmium Absorber, Nuclear Technology, 79, 82 (1987). 2) S. S. Kim, Highly Enriched Uranyl Nitrate Solution Containing Cadmium, HEU-SOL-THERM-049, International Handbook of Evaluated Criticality Safety Benchmark Experiments, September 2004 Edition, NEA/NSC/DOC(95)03/II, OECD-NEA (2004). 3) MCNP4B Monte Carlo N-Particle Transport Code System, LA-12625-M, Version 4B, Los Alamos National Laboratory (1993). 4) MCNP Monte Carlo N-Particle Transport Code System, Version 5, LA-UR-03-1987, Los Alamos National Laboratory (2005). 5) SCALE: A Modular Code System for Performing Standardized Computer Analyses for Licensing Evaluation, NUREG/CR-200, Rev. 4, Oak Ridge National Laboratory (1995).