The original work of Strobl and Hagedorn suggesting the presence of a third intermediate phase in semicrystalline polyethylene was revisited. The current study, involving the collection of Raman spectroscopic data on a set of 16 polyethylene samples recorded on two different types of instruments in two different laboratories and employing two different methods of curve fitting to both sets of experimental data, has revealed that the claims in the original paper cannot be asserted. The most important reason leading to this conclusion is a problem in correctly describing the complicated overlapping spectral structure in the 1000-1200 and 1400-1500 cm-l spectral ranges. It is noted that the contribution of the melt in the 1000-1150 cm-l range cannot be described by a single line centered around 1080 cm-l. The present results indicate that the quantification of a third, intermediate, phase in polyethylene is not possible when based on standard Raman spectra.
Post-Chernobyl experience has demonstrated that persistently high plant transfer of 137 Cs occurs from organic soils in upland and seminatural ecosystems. The soil properties influencing this transfer have been known for some time but have not been quantified. A pot experiment was conducted using 23 soils collected from selected areas of Great Britain, which were spiked with 134 Cs, and Agrostis capillaris grown for 19-45 days. The plant-tosoil 134 Cs concentration ratio (CR) varied from 0.06 to 44; log CR positively correlated to soil organic matter content (R 2 ) 0.84), and CR values were highest for soils with low distribution coefficients (K d ) of 134 Cs. Soils with high organic matter contents and high concentrations of NH 4 + in solution showed high 134 Cs mobility (low K d ). The plantto-soil solution 134 Cs ratio decreased sharply with increasing soil solution K + . A two parameter linear model, used to predict log CR from soil solution K + and K d , explained 94% of the variability in CR values. In conclusion, the high transfer of 134 Cs in organic soils is related to both the high 134 Cs mobility (low clay content and high NH 4 + concentrations) and low K availability.
During the years after a nuclear accident, the bioavailability
and environmental mobility of radiocesium declines
markedly, resulting in large changes in contamination of
foodstuffs, vegetation, and surface waters. Predicting such
changes is crucial to the determination of potential
doses to affected populations and therefore to the
implementation of radiological countermeasures. We
have analyzed 77 data sets of radiocesium (137Cs) activity
concentrations in milk, vegetation, and surface waters
after the Chernobyl accident. Our results show that the
rate of decline in 137Cs during the years after Chernobyl is
remarkably consistent in all three ecosystem components,
having a mean effective half-life, T
eff ≈ 2 years. By comparing
changes in 137Cs availability with rates of diffusion of 40K
(a close analogue) into the lattice of an illitic clay () we have,
for the first time, directly linked changes in the environmental
availability of 137Cs to fixation processes at a mechanistic
level. These changes are consistent with declines in the
exchangeable fraction of 137Cs in soils (2,
3).
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