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Influence of the decontamination of a high radioactive solution from Cesium on analytical performances

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HAL Id: cea-02509782

https://hal-cea.archives-ouvertes.fr/cea-02509782

Submitted on 17 Mar 2020

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Influence of the decontamination of a high radioactive solution from Cesium on analytical performances

C. Maillard, V. Boyerdeslys, J.-L. Dautheribes, E. Esbelin, A. Beres, C. Rivier

To cite this version:

C. Maillard, V. Boyerdeslys, J.-L. Dautheribes, E. Esbelin, A. Beres, et al.. Influence of the de-contamination of a high radioactive solution from Cesium on analytical performances. RANC 2016 - International conference on radioanalytical and nuclear chemistry, Apr 2016, Budapest, Hungary. �cea-02509782�

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Analyses of gamma emitters

Influence of the decontamination of a high radioactive solution from Cesium

on analytical performances

Ch. Maillard, V. Boyer-Deslys, J-L. Dautheribes, E. Esbelin, A. Bères, C. Rivier

CEA, Nuclear Energy Division, Radiochemistry and Process Department, SERA/LAMM, F-30207 Bagnols sur Cèze, France

Introduction :

In the ATALANTE facility dedicated to the back end nuclear fuel cycle R&D, the high rate of irradiation of certain

samples is essentially due to the presence of

137

Cs. It results several advantages to decontaminate them from this isotope: 1- a decrease

of the irradiation rate, 2- a smaller dilution to make possible the samples manipulation in glove boxes, 3- lower detection limits of

analyzed elements. According to the literature, a separation by chromatography using AMP-PAN is a good method to achieve our

goals: a high decontamination factor of

137

Cs, a high recovery yield for other elements, a small dilution factor of the sample.

137

Cs separation scheme

sample Adjustement of acidity at [HNO3]final = 2 M (2) Washing solution ([HNO3] = 2 M) (3) Conditionning of the column ([HNO3] = 2 M) (1) (2 + 3) Decontaminated 137Cs Solution Effluents (1) AMP-PAN column Sample tested : A(137Cs) = 2.1010 Bq/L

(dissolution solution of residues from a storage tank of fission products

Analysis performed in a glove box laboratory

Consequences of separation:

 Elimination of the Compton effect

 Detection limit improvement (*): 20-50 137Cs decontamination factor > 5.104

241Am recovey yield: 80-100%

(*) measured elements: 54Mn, 60Co, 65Zn, 95Zr, 95Nb, 106(Ru + Rh), 110Ag, 144(Ce + Pr),

152Eu

Compton 137 Cs

(662 KeV)

Initial solution (dilution : 500)

Solution after separation (dilution : 4)

Literature data:

AMP-PAN: inorganic powder of Ammonium Phosphomolybdate embedded in an organic matrix based on PolyAcrylnitrile

Kd(Cs) > 1000 mL/g ([HNO3] = 1-2M) AMP-PAN capacity: 30 mg de Cs/g

Density: 0.27 g/mL

Radiation resistance: 106 Gray

Cationic exchange:

(NH4)3PMo12O40 + 3CsNO3  Cs3PMo12O40 + 3NH4NO3

Alpha emitters Analysis

Sample tested: dissolution solution of residues from a storage tank of fission products

Analysis performed in a glove box laboratory

 High recovery yield of plutonium

 The detection limit (DL) is decreased by a

factor > 100 thanks to a smaller dilution

of the decontaminated sample (dilution = 4) (Initial solution with Cs: dilution 500).

 This high DL enhancement is also due to a

weak salt concentration (Na+ < 4 g/L) and a

weak total alpha activity (5.107 Bq/L) of

the decontaminated sample.

Multi-elementary analyses by ICP-AES and ICP-MS

Sample tested: dissolution solution of residues from a storage tank of fission products

Analysis performed in a glove box laboratory

 High recovery yield of Mo, Zr and B

 ICP-MS: The detection limit (DL) is decreased by a factor > 10 thanks

to a smaller dilution of the decontaminated sample (dilution = 4) (Initial solution: 50-fold dilution).

 ICP-AES: Same DL between the initial solution measured by ICP-AES

in a hot cell and the decontaminated sample measured by ICP-AES in a glove box laboratory.

Behavior of some cations with AMP-PAN

 Goal : confirmation of the selectivity of Cs in presence of some cations

(initial inactive solution : each cation = 50 mg/L, [HNO3] = 2M)

 High recovery yields are obtained except for Ag and Pd

 Recovery yield of Mo > 160 % : release of Mo by AMP-PAN ?

Elements Recovery yield (%) Analytical techniques Al, As B, Ba, Be, Ca, Cd,

Ce, Co, Cr, Cu, Fe, Gd, Hg, K, Mg, Mn, Na, Nd,

Ni, Pb, Rh, Ru, Sb, Se, Si, Sr, Y, Te, Zn, Zr > 98 Ag, Pd < 5% Cs < 0,04 ICP-MS ICPAES

Conclusions

 Very good selectivity of AMP-PAN

. Cs decontamination factor > 5.10

4

 decrease of the irradiation rate of the sample

. High recovery yield for most cations (except Pd and Ag) (behavior of Mo to be confirmed)

 Consequences of the separation using AMP-PAN on sample analyses

. Decrease of Detection Limits in gamma spectrometry (because of the minimization of the Compton effect)

. Decrease of Detection Limits in ICP-MS and alpha spectrometry (because of a smaller dilution of the decontaminated sample))

 Possible applications

. Samples from processes of hydrometallurgical extraction, from dissolution of hulls and spent fuels, radioactive effluent

Sample dilution by this separation = 4

Influence of Chlorides, Fluorides and Sulfates on Cs behavior

Element Initial solution (mg/L) Recovery yield (%) Mo 355 96 Zr 404 97 B 555 90

 AMP-PAN feeding inactive solution: Cs = 25 mg/L, [HNO3] = 2 M, [NaX] = 1 to 1.5 M

 Conclusion: Cesium is strongly fixed by AMP-PAN.

Anions like Cl-, F-, SO

42- have no influence on Cesium behavior

[X] feeding solution Cesium (µg/L)

effluents (feeding + washing) Cesium recovery yield (%) Analytical technique [F-] = 1 M < 10 (DL) < 0.08 [SO42-] = 1.5 M < 10 (DL) < 0.08 [Cl-] = 1.5 M < 10 (DL) < 0.08 no added anion < 10 (DL) < 0.08 ICP-MS Element Initial solution Recovery yield (%) Pu total 2.5 mg/L 94 +/- 10

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