Fluoride Complexation of Rutherfordium (Rf, element 104)
E. Strub 1 , W. Brüchle 2 B. Eichler 4 , H.W. Gäggeler 4,6, J.P. Glatz 7 , A. Grund 4 , M. Gärtner 6 , E. Jäger 2 , D. Jost 4 , U. Kirbach 3 , J.V. Kratz 1 , A. Kronenberg 1 , Y. Nagame 5 , M. Schädel 2 , B. Schausten 2 , E. Schimpf 2 , D. Schumann 3 , P. Thörle 1 , K. Tsukada 5 , A. Türler 4 , S. Zauner 1
1 Institut für Kernchemie,Universität Mainz, 2 Gesellschaft für Schwerionenforschung, Darmstadt, 3 TU Dresden, 4 PSI Villigen, 5 JAERI, Tokai, Japan, 6 Universität Bern, 7 Transuraninstitut KarlsruheThe first aqueous chemistry study of seaborgium (Sg, element 106)[1,2] was performed recently with the Automated Rapid Chemistry Apparatus ARCA II. 265Sg ( T1/2 =7.4+3.3-2.7 s [3]) was eluted from a cation exchange column (Aminex A6) in 0.1 M HNO 3/5·10-4 M HF which is typical for a group-6 element. Due to the half-minute time span needed to prepare samples and to start counting[2], 265 Sg itself was not detected but correlated mother-daughter decays of its descendant 261 Rf. Therefore, it was important that a HF concentration was selected[2] that was insufficient to elute group-4 elements. This had been demonstrated for Zr and Hf and was assumed for Rf. Due to the HSAB concept, Sg 6+ shows a higher affinity to F - ions than any 4+ ion. Thus, the tendency to form anionic fluoride complexes should increase from Rf to Sg. So even if Rf fluoride complexing is different from that of Zr and Hf and is more similar to that of the pseudo-homolog Th than to group 4 elements, it should stick to the column even at higher HF concentrations than Sg.
Nevertheless,
it was of interest to verify experimentally that 261Rf,
under the condition of the seaborgium experiments,
is not eluted from the cation exchange column and can only
appear in the seaborgium sample as a result of the
decay
of 265Sg.
Therefore,
261 Rf was produced directly in the
248 Cm(18 O,5n) reaction at the Philips Cyclotron of
the Paul Scherrer Institute.
A 730
g/cm2
248Cm target
was bombarded with a 0.5 p
A 18O5+ beam.
The target contained 10 % Gd thus producing
simultaneously short-lived Hf isotopes
use to monitor on-line the behaviour of Hf and to perform yield checks.
Rf and Hf were transported by a He/KCl gas jet and collected on the for 90 s by impaction on a slider in ARCA II. The residue was dissolved in 200
For 0.1 M HNO 3/5·10-4 M HF, all 261 Rf events were detected in sample 2. From this one can calculate a lower limit for the distribution coefficient Kd(5·10-4 M HF )>148 . This proves unambiguously that the 261 Rf decays detected in the Sg experiments[1,2] were originating with 265 Sg which had passed the cation exchange column.
There is evidence by D. Schumann et al.[4] that Rf shows a distinctly higher Kd in 0.1 M HCl/10-2 M than Zr and Hf whereby Rf shows similarities to the pseudo homologue Th. Therefore, the Rf experiments were extended to 0.1 M HNO 3 /10 -2 M HF. Also at this HF concentration, all 261 Rf events were detected in sample 2, which defines a lower limit for the distribution coefficient Kd(10-2 M HF )>312 (the higher limit with respect to 5·10-4 M HF results from a higher number of detected events). The Kd values of Rf at 5 cdot10-4 M HF and 10-2 M HF (and an estimate at 10-1 M HF) are shown in Fig. 1 together with the behaviour of Zr, Hf and Th in off-line experiments. Two observations can be made: i)the 261 Rf results show similarities to the behaviour of Th and a sorption behaviour different from that of Zr and Hf, and ii)the behaviour of Hf produced on-line is in good agreement with data from off-line experiments.
Sorption of Zr, Hf, Th and Rf on a cation exchange resin (Aminex A6) at various HF concentrations. The on-line data for Hf and Th are compared to off-line data for Zr, Hf and Th. The aqueous solutions contained 0.1 M HNO3.
References
[1] M. Schädel et al., Nature 388, 55 (1997)
[2] M. Schädel et al., Radiochim. Acta 77 , 149 (1997)
[3] H.W. Gäggeler, Proc. Int. Conf. on Actinides, Baden-Baden, 21-26 September 1997, J. of Alloys and Compounds, in press
[4] D. Schumann et al., Labor für Radio- und Umweltchemie der Universität Bern und des Paul-Scherrer-Instituts, Annual Report 1996, p.37