Radiochemical determination of plutonium in sea water, sediments and marine organisms
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Cited by (103)
Separation of anthropogenic radionuclides from aqueous environment using raw and modified biosorbents
2022, Journal of Environmental RadioactivityCitation Excerpt :This is usually achieved using co-precipitation [Qiao et al., 2009], ion-exchange, or solvent extraction procedures in combination with α-spectrometry [Eroglu et al., 1998; Hirose, 2009]. Co-precipitation can be carried out using various chemical compounds, such as Mn compounds [Becker et al., 2004; Benkrid and Noureddine, 2007; Sidhu, 2003; Wong et al., 1978], Fe compounds [Becker et al., 2004; Chen et al., 1993; Eroglu et al., 1998; Kwong et al., 2004; Wong, 1971], as well as water-soluble metal-binding polymers [Smith et al., 1998], and TiSi [Lujanienė et al., 2009]. The use of sorbents can also be a convenient method of preliminary concentration.
On the use of MnO<inf>2</inf> cartridges for the plutonium determination in seawater
2019, Journal of Environmental RadioactivityCitation Excerpt :The solution was allowed to cool and then transferred to 7–8 M HNO3. In the next step the solution was poured directly over a preconditioned (8 HNO3) anion exchange column (Bio-Rad AG 1 × 8) (Wong, 1971; La Rosa et al., 2001). The column was than washed with 8 M HNO3, eluting interfering elements like e.g. U, Am and rare earths, followed by a 10 M HCl wash to remove Th.
Plutonium determination in seawater by inductively coupled plasma mass spectrometry: A review
2016, TalantaCitation Excerpt :Overall, various and effective approaches of Pu determination in seawater have been developed, and these designed protocols have been widely applied to enhance understanding of ocean processes. For an analytical methodology, although the iron hydroxide co-precipitation method has been widely applied for total Pu determination and speciation of reduced and oxidized Pu in seawater samples [97–98], it can be further optimized because it functions not only for pre-concentration of Pu, but also for separation of Pu from seawater matrix and interfering elements, especially U. The pH is a key parameter for Pu separation during the co-precipitation step, but almost no work has been carried out to clarify in detail the effect of pH on precipitation efficiency of Pu, and there is also no detailed information on the relationship between pH and precipitation efficiency of U. For emergency preparedness in radiological incidents, timely evaluating the radioactivity status of seawater is strongly required.
Monte Carlo uncertainty calculation of <sup>210</sup>Pb chronologies and accumulation rates of sediments and peat bogs
2014, Quaternary GeochronologyCitation Excerpt :In order to validate the 210Pb chronology, the weapons fallout tracer 239,240Pu was analyzed in a nearby core (C2), which shows an identical magnetic susceptibility signal, notably a peak in the 69–70 cm section (Ontiveros-Cuadras et al., 2014). 239,240Pu was purified by using ion interchange resins and electroplating (Wong, 1971; Puphal and Olsen, 1972; Merino et al., 2000). Analytical quality was achieved through the analysis of Certified Reference Materials IAEA-300 (Ballestra et al., 1994), IAEA-384 (Povinec et al., 2007) and IAEA-385 (Pham et al., 2008).
Plutonium as a chronomarker in Australian and New Zealand sediments: A comparison with 137Cs
2011, Journal of Environmental Radioactivity
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Present address: Scripps Institution of Oceanography, La Jolla, Calif. 92037, U.S.A.