eyeno wrote:But if this contamination is to persist for perhaps years as is suspected, which would mean chronic exposure, would that not constitute a means for accumulation?
Forget my guess earlier, somebody smarter has done the legwork, and the news is not good. Am posting full text but follow link for more links:
Iaato on TOD wrote:I was not going to comment on this thread after Euan's statement about irrational fears of radiation, but I feel I must correct some very serious misinformation about "bioaccumulation of radioactive fallout" in general, especially the slower varieties, which is the real danger that we are talking about and dancing around in these discussions. Try Google Scholar.
http://www.ukmarinesac.org.uk/activitie ... wq8_49.htm
The principal diffuse source of radioactivity to the aquatic environment is from atmospheric fall-out and the main point source is from the nuclear reprocessing industry. Estuarine systems, in particular, are sinks for organic matter from both freshwater and marine origins and, as such, accumulate radionuclides that are associated with organic matter. They are also very productive and act as a nursery and feeding area for fish, birds and macro-crustaceans. As such, there is a pathway for accumulated radionuclides to enter the food web where potential impacts may occur and possibly result in the exposure of Mankind to this source of radioactivity. . . .
Radionuclides are found in measurable quantities in the water column, suspended sediments, sea-bed sediments and the biota (Kershaw et al 1992). . . .
Radionuclide accumulation in saltmarshes is controlled principally by the physical processes associated with tidal flow and sediment deposition (Horrill 1983), but the type of vegetation present also has an effect on accumulation rates - vegetated areas accumulate radionuclides, such as americium, caesium and plutonium at faster rates than unvegetated areas. A large number of other factors can also affect accumulation rates, to the extent that variability within and between different saltmarshes can be wide. However, the relative stability and high biological productivity of saltmarsh sediments (away from tidal channels) favours the accumulation of plutonium and caesium isotopes, with highest activities often being associated with fine-grained mud flats, such as those in the Solway Firth (Kennedy et al 1988)
Some radionuclides have been found to accumulate in the biota. In particular, benthic algae, molluscs (mussels, winkles, limpets, whelks, scallops, queens), crustacea (crab, lobster, Nephrops, shrimps) and fish (including plaice, cod, flounder, herring) have been found to accumulate some radionuclides based on monitoring information collected by MAFF in the Irish Sea (Kershaw et al 1992). The principal concern has been to determine the risk to the human population and so the fish and shellfish species selected for monitoring have been commercially important ones. These species have been found to accumulate a number of radionuclides but the most important appear to be 106Ru and 137Cs. Both have been found to accumulate in fish muscle (plaice) and in crab Cancer pagurus hepatopancreas and muscle tissue. Crabs were found to accumulate 144Ce and 95Zr/95Nb in addition to 106Ru and 137 Cs. The most significant uptake route for these species is believed to be via the diet. . . .
The fate and behaviour of radionuclides in the marine environment is determined by the fate and behaviour of the element concerned. For example, if an element is adsorbed to sediment particles, then the radionuclide of that element will behave in the same way.
The radioactive elements will not be destroyed in the environment and radioactivity will be emitted from whatever compounds are formed with the element. The duration that the energy will be emitted is governed by the half-life of the radionuclide which can range from hours to hundreds of years. . . .
http://74.125.155.132/scholar?q=cache:Q ... e.com/+b...
In studying the effects of radioactive substances on food chains, the concepts of bioaccumulation and biological magnification were established—later to become intimately identified with Carson’s Silent Spring. Bioaccumulation refers to a process whereby a toxic substance is absorbed by the body at a rate faster than it is lost. For instance, strontium-90 is a radioactive isotope that is chemically similar to calcium and can accumulate in the bones, where it can cause genetic mutations and cancer. Biological magnification occurs when a substance increases in concentration along the food chain. An example of this occurred when radionuclides discharged into the Columbia River in trace amounts from the Hanford nuclear facility in Washington State were discovered to increase in order of magnitude as they were pa! ssed along in the food chain. A number of variables influence such biological magnification, such as the length of the food chain, the rate of bioaccumulation within an organism, the half-life of the nuclide (in the case of radioactive substances), and the concentration of the toxic substance in the immediate environment. Ecologist Eugene Odum noted that due to biological magnification it was possible to release an “innocuous amount of radioactivity and have her [nature] give it back to us in a lethal package!” Carson herself pointed to how biological magnification resulted in dangerously high burdens of strontium-90 and cesium-137 in the bodies of Alaskan Eskimos and Scandinavian Lapps at the terminal end of a food chain that included lichens and caribou.
In the 1961 edition of The Sea Around Us, Carson, who was deeply involved in protesting the dumping of radioactive wastes in the oceans, raised the pregnant question, “What happens then to the careful calculation of a ‘maximum permissible level’ [of radioactivity]? For the tiny organisms are eaten by larger ones and so on up the food chain to man. By such a process tuna over an area of a million square miles surrounding the Bikini bomb test developed a degree of radioactivity enormously higher than that of the sea water.”
http://www.springerlink.com/content/1dc6bdvbhwqbdcfh/
The paucity of investigations on the presence of artificial radionuclides and their bioaccumulation in Antarctic fauna is due to the erroneous belief that this area is pristine. We report evidence that significant levels of the artificial radionuclides Sr-90, Cs-137, Am-241 and plutonium isotopes can be found in sponges, bivalves, krill and demersal fish fauna of Terra Nova Bay (Ross Sea), sometimes with a seasonal pattern. Increasing concentrations of Cs-137 were detected in the bivalve Adamussium colbecki (Antarctic scallop) during austral summer months, as a result of major trophic activity and changes in metabolic rates. Bioconcentration factors for artificial radionuclides in different Antarctic species are presented and discussed in relation to their different trophic strategies. Unexpectedly high radiocesium bioconcentration factors determined in bivalves suggested the particular role played by filter feeding in bioaccumulation, particularly in summer when radionuclide bioavailability is enhanced. The feeding preference of the trematomiid fish Trematomus bernacchii for the scallop A. colbecki is confirmed, not only by fish gut content analyses, but also through radiometric results. Transuranics bioaccumulation by sensitive species allowed some interesting comparisons on the different plutonium contamination of the southern hemisphere with respect to the northern one.
http://www.sciencedirect.com/science?_o ... VCHHBC-5...
Radionuclide tracers of heavy metals (59Fe, 60Co, 65Zn, 75Se 85Sr, 134Cs and 203Hg) representing potential contamination from nuclear power plants, industry and agriculture were added to separate basins of Lake 226, Experimental Lakes Area, northwestern Ontario. The two basins were part of a eutrophication experiment and differed in their trophic status; the north basin (L226N) was eutrophic whereas the south basin (L226S) was mesotrophic. Our objective was to determine the uptake of the radionuclides by biota and the effect of lake trophic status on their bioaccumulation. The trophic status of the lakes did not appear to have a marked effect on the accumulation of radionuclides by the biota. This may have been because of a mid-summer leakage of nutrients between the basins which enhanced primary production in L226S, because there is a time lag between primary production and the availability of the radionuclides to the fishes or because trophic status does not affect the uptake of at least some of these radionuclides. However, there was a tendency for faster uptake of the radionuclides in L226N by fish than L226S, but the differences were not significant. Concentrations in the biota generally decreased in the order: fathead minnow>pearl dace>tadpoles>slimy sculpin>leeches. Concentrations in biota generally decreased in the order: 65Zn>203Hg>75Se>134Cs>60Co>85Sr=59Fe. Cobalt-60 concentrations in tadpoles were greater than in the other biota. Radionuclide concentrations in the tissues of lake whitefish indicated that uptake was predominantly from food. Radionuclide concentrations were usually higher in the posterior gut, liver and kidney than in other tissues, whereas body burdens were generally high in the muscle for 75Se, 134Cs and 203Hg; kidney and gut for 60Co; and bone for 65Zn and 75Se. Mercury-203 burdens were also high in the bone and gut.
As we lower the bar on how much our environment can tolerate, and as isotopes continue to bioaccumulate in our bodies, how much is too much for species as a whole?