Fixation of Cs to marine sediments estimated by a stochastic modelling approach

Dumping of nuclear waste in the Kara Sea represents a potential source of radioactive contamination to the Arctic Seas in the future. The mobility of Cs-137 ions leached from the waste will depend on the interactions with sediment particles. Whether sediments will act as a continuous permanent sink for released Cs-137 or contaminated sediments will serve as a diffuse Source of Cs-137 in the future. depends on the interaction kinetics and binding mechanisms involved. The main purpose of this paper is to study the performance of different stochastic models using kinetic information to estimate the time needed for Cs ions to become irreversibly fixed within the sediments. The kinetic information, as obtained from Cs-134 tracer sorption and desorption (sequential extractions) experiments, conducted over time. using sediments from the Stepovogo Fjord waste dumping site, on the east coast of Novaya Zemlya. Results show that Cs-134 ions interact rapidly with the surfaces of the Stepovogo sediment, with an estimated distribution coefficient K-d(eq) of 300 ml/g (or 13 m(2)/g), and the Cs-134 ions are increasingly irreversible, fixed to the sediment over time. For the first time, stochastic theory has been utilised for sediment-seawater systems to estimate the mean residence times (MRTS) of Cs ions in operationally defined sediment phases described by compartment models. In the present work. two different stochastic models (i) a Markov process model (MP) being analogous to deterministic compartment models and (ii) a semi-Markov process model (SMP) which should be physically more relevant for inhomogeneous systems, have been compared. As similar results were obtained using the two models. the less complicated MP model was utilised to predict the time needed for an average Cs ion to become irreversibly fixed in the Stepovogo sediments. According the model. approximately 1100 days of contact time between Cs ions and sediments is needed before 50% of the Cs-134 ion becomes fixed in the irreversible sediment phase. while about 12.5 years are needed before 99.7% of the Cs ions are fixed. Thus, according to the model estimates the contact time between Cs-137 ions leached from dumped waste and the Stepovogo Fjord sediment should be about 3 years before the sediment will act as an efficient permanent sink. Until then a significant fraction of Cs-137 should be considered mobile, The stochastic modelling approach provides useful tools when assessing sediment-seawater interactions over time, and should be easily applicable to all sediment-seawater systems including a sink term. (C) 2002 Elsevier Science Ltd. All rights reserved.