title: Distribution coefficients (Kd's) for use in risk assessment models of the Kara Sea.
abstract: As a prerequisite for most evaluations of radionuclide transport pathways in marine systems, it is necessary to obtain basic information on the sorption potential of contaminants onto particulate matter. Kd values for use in modeling radionuclide dispersion in the Kara Sea have been determined as part of several international programs addressing the problem of radioactive debris residing in Arctic Seas. Field and laboratory Kd experiments were conducted for the following radionuclides associated with nuclear waste: americium, europium, plutonium, cobalt, cesium and strontium. Emphasis has been placed on two regions in the Kara Sea: (i) the Novaya Zemlya Trough (NZT) and (ii) the mixing zones of the Ob and Yenisey Rivers (RMZ). Short-term batch Kd experiments were performed at-sea on ambient water column samples and on samples prepared both at-sea and in the laboratory by mixing filtered bottom water with small amounts of surficial bottom sediments (particle concentrations in samples = 1-30 mg/l). Within both regions, Kd values for individual radionuclides vary over two to three orders of magnitude. The relative particle affinities for radionuclides in the two regions are americium approximately equal to europium > plutonium > cobalt > cesium > strontium. The values determined in this study agree with minimum values given in the IAEA Technical Report [IAEA, 1985. Sediment Kd's and Concentration Factors for Radionuclides in the Marine Environment. Technical Report No. 247. International Atomic Energy Agency, Vienna.]. Given the importance of Kd's in assessments of critical transport pathways for radionuclide contaminants, we recommend that Kd ranges of values for specific elements rather than single mean values be incorporated into model simulations of radionuclide dispersion.
authors.affiliation: IAEA Marine Environment Laboratory, Monaco. jolynn.carroll@akvaplan.niva.no
authors.forename: J
authors.initials: J
authors.lastname: Carroll
authors.forename: F
authors.initials: F
authors.lastname: Boisson
authors.forename: J L
authors.initials: JL
authors.lastname: Teyssie
authors.forename: S E
authors.initials: SE
authors.lastname: King
authors.forename: M
authors.initials: M
authors.lastname: Krosshavn
authors.forename: M L
authors.initials: ML
authors.lastname: Carroll
authors.forename: S W
authors.initials: SW
authors.lastname: Fowler
authors.forename: P P
authors.initials: PP
authors.lastname: Povinec
authors.forename: M S
authors.initials: MS
authors.lastname: Baxter
mesh_terms: D000576:Americium / Q000032:analysis / Q000633:toxicity; D002588:Cesium Radioisotopes / Q000032:analysis / Q000633:toxicity; D003035:Cobalt / Q000032:analysis / Q000633:toxicity; D005063:Europium / Q000032:analysis / Q000633:toxicity; D019015:Geologic Sediments; D008956:Models, Chemical; D011005:Plutonium / Q000032:analysis / Q000633:toxicity; D011868:Radioisotopes / Q000032:analysis* / Q000633:toxicity; D018570:Risk Assessment; D012623:Seawater; D013326:Strontium Radioisotopes / Q000032:analysis / Q000633:toxicity; D014875:Water Pollutants, Radioactive / Q000032:analysis* / Q000633:toxicity
chemical_list: D002588:Cesium Radioisotopes; D011868:Radioisotopes; D013326:Strontium Radioisotopes; D014875:Water Pollutants, Radioactive; D003035:Cobalt; D005063:Europium; D011005:Plutonium; D000576:Americium