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[Ecological consequences of radioactive pollution for soil bacteria within the 10-km region around the Chernobyl Atomic Energy Station].

The diversity of aerobic chemoorganotrophic (capable of growing on nutrient agar) bacteria in radioactive soil (0.3-17.0 microCi/kg soil) sampled in the 10-km zone around the Chernobyl Nuclear Power Plant (CNPP) was found to be lower than that observed in control, uncontaminated soil with a radioactivity of 0.002-0.006 microCi/kg soil. All the radioactive soil samples contained the bacteria Bacillus cereus and Methylobacterium extorquens or M. mesophillicum, which exhibited a high tolerance to 0.3-1.0 M hydrogen peroxide, whose action can to a certain extent simulate the effect of ionizing radiation. Some of the contaminated soil samples contained other species of chemoorganotrophic bacteria with a low tolerance to H2O2. The survival of bacteria in the Chernobyl accident zone is probably due to the functioning of mechanisms efficiently neutralizing peroxide compounds and repairing radiation-damaged DNA. The population of cellulolytic, nitrifying, and sulfate-reducing bacteria in contaminated soil was found to be 1-2 orders of magnitude less than in control soil, indicating the unfavorable effect of anthropogenic radiation on the abundance and diversity of soil bacteria.

Bacillus cereus↗

The Allium cepa chromosome aberration test reliably measures genotoxicity of soils of inhabited areas in the Ukraine contaminated by the Chernobyl accident.

The accident on the Chernobyl Nuclear Power Plant reactor IV in April 1986 led to the release of an enormous amount of radioactive material into the biosphere and to the formation of a complex pattern of nuclear contamination over a large area. As a consequence more than 5 million km2 of the soil in the Ukraine became contaminated with more than 1 Ci/km2 [1,2]. An assessment of the genetic consequences of the nuclear pollution is one of the most important problems. We applied the Allium cepa test to estimate the impact on plant chromosomes of nuclear pollution in the inhabited zones of the Ukraine. We tested soil from the obligatory resettlement zone (zone 2), where the mean density of pollution is 15-40 Ci/km2; zones of enhanced radiological control-zone 3, 5-15 Ci/km2 and zone 4, 1-5 Ci/km2. We found a dose-dependent increase in the fraction of aberrant mitoses from control values of 1.6 +/- 0.9% up to 23.8 +/- 5.0%, and a corresponding monotonous decrease of the mitotic index from 49.4 +/- 4.8% to a limiting value of 22.5 +/- 4.0% at pollution levels exceeding 35 Ci/km2 (activity of the soil samples exceeding 6000 Bq/kg, respectively). We observed a strong, significant correlation of 137Cs activity of soil samples with the percentage of chromosomal abnormalities, r = 0.97 (P < 0.05), and with the mitotic index, r = -0.93 (P < 0.05), in the roots of A. cepa, respectively. The results showed high toxicity and genotoxicity of radioactively polluted soils and confirmed the efficiency of the A. cepa test as a quick and inexpensive biological test for ecological and genetic risk assessment in the 'Chernobyl' zones.

Chromosome Aberrations↗

Environmental tritium transport from an atmospheric release of tritiated water.

Elevated tritium levels were found in samples of pine needles and surface leaf litter taken along the path of an atmospheric tritiated water release from the Savannah River Plant, Aiken, South Carolina. After the initial exposure period, tritium levels declined to background within 3 days. The equilibration half-time for tritium in terrestrial ecosystems is much shorter after exposure to tritiated water than after an exposure to molecular tritium. This difference is due to preferential deposition of molecular tritium in soil.

Air Pollution, Radioactive↗

Natural radioactivity of Miami soils.

An important part of man's radioactive environment is the natural radioactivity of soils. This radioactivity varies with soil type and withdepth in the soil profile. The relation between gross gamma activity and soil depth for a particular soil (Miami silt loam) is presented, together with a discussion of the contribution of K(40) and the uranium and thorium series and of the effects of fallout from bomb tests in increasing the radioactivity of a thin layer of surface soil.

Gamma Rays↗

[Effect of separate radioactive and chemical pollutants on the yield of cytogenetic disruptions in the intercalary meristem in spring barley].

Dependencies of the yield of cytogenetic disturbances within intercalary meristem cells of spring barley on the soil level of 137Cs (1.48-14.8 MBq/m2), Cd, Pb (2-50 and 30-300 mg per kilogram of the soil) and 2.4-D herbicide (1 or 2 kg/ha) had a non-linear character in the studied range. At low concentrations the yield of cytogenetic disturbances grew faster than at higher ones. Concentrations of lead in soil (at the level of maximum concentration limit) and doses of 2.4-D recommended for agricultural use resulted in the increase in the rate of aberrant cells. The observed rate of cytogenetic disturbances was comparable with the effect of the maximum studied level or the radioactive soil pollution. The heaviest damage to aberrant cells was found in the presence of 137Cs.

2,4-Dichlorophenoxyacetic Acid↗

Comparative uptake of U and Th by native plants at a U production site.

During a 3- to 4-year period, concentrations of 238U, 234U, 230Th, 232Th and 228Th were determined in soils and native vegetation at various sites around a typical U mining and milling operation in Wyoming. Plant/soil concentration ratios (CR) for U and Th isotopes were estimated for (1) exposed, weathered tailings, (2) the edge of a tailings impoundment, (3) an area downwind from exposed tailings, (4) a reclamation area and (5) several background, native range locations. The 238U/234U concentration ratio of 0.9 to 1.1 in soil and vegetation indicated near-radioactive equilibrium of both radionuclides at all locations. Mean concentrations of the U and Th isotopes in background soil ranged from 44 to 52 mBq g-1. Concentrations of 238U and 230Th in soil and vegetation were elevated above background at all sites disturbed by mining and milling activities. Uranium concentrations in tailings and invading vegetation were an order of magnitude greater than in the background locations, whereas 230Th concentrations were elevated above background by some two orders of magnitude. No demonstrable differences in radionuclide concentrations between plant groups and collection years were found. The observed CR values for 238U and 230Th of 0.81 and 0.69 for vegetation growing on exposed tailings were elevated above native range by factors of 9.0 and 3.6, respectively, and generally higher than other published values. Exceptionally high CR values for 230Th (1.9-2.9) observed near the tailings impoundment demonstrate that under certain conditions, vegetation can accumulate 230Th to a much greater extent than previously reported. Vegetation concentrations were lower for 232Th relative to 230Th and 228Th at locations where they are present at similar soil concentrations.

Colorado↗

Accumulation of radionuclides by plants as a monitor system.

The accumulation of radionuclides by plants acting as a monitoring system in the environment may occur by two modes; foliar absorption by the leaves and shoot of the plant, or by root uptake from the soil. Data on plant accumulation of radionuclides may be obtained from studies of fission product radionuclides deposited as worldwide fallout, and from tracer studies of plant physiology. The epidermal features of plant foliage may exert an effect upon particle retention by leaves, and subsequent uptake of radionuclides from the surface. The transport of radionuclides across the cuticle and epidermis of plant leaves is determined in part by the anatomy of the leaf, and by physiological factors. The foliar uptake of fallout radionuclides, 99Sr, 131I, and 137Cs, is described with examples from the scientific literature. The environmental half-life of 131I, for example, is considerably shorter than its physical half-life because of physical and biological factors which may produce a half-life as short as 0.23/day. 99Sr and 137Cs are readily taken up by the leaf, but 137Cs undergoes more translocation into fruit and seeds than 99Sr which tends to remain in the plant part in which it was initially absorbed. Soil-root uptake is conditioned primarily by soil chemical and physical factors which may selectively retain a radionuclide, such as 137Cs. The presence of organic matter, inorganic colloids (clay), and competing elements will strongly affect the uptake of 99Sr and 137Cs by plants from the soil. The role of plants as monitors of radionuclides is twofold: as monitors of recent atmospheric releases of radionuclides; and as indicators of the long-term behavior of aged deposits of radionuclides in the soil.

Absorption↗

[The protein-synthesizing activity of a number of strains of Cladosporium cladosporioides (Fres.) de Vries grown under conditions of continuous low-intensity gamma irradiation].

Phenomena of melanization of radioactively polluted soils, due to prevalence of melanin-containing species and positive radiotropism of some micromycetes have been found during monitoring of mycobiota of the 30-km alienation zone of the Chernobyl NPP for 10 years. To elucidate the contribution of the melanin system to the cell protection against irradiation, the influence of gamma-irradiation on the activity of protein synthesis in four Cladosporium cladosporioides (Fres.) de Vries strains has been investigated. Two strains isolated from radioactively polluted substrates were characterised by the presence of positive radiotropism. Laboratory strain 396 and its alb-mutant (with blocked melanin synthesis), did not possess this feature. The protein synthesizing activity was assayed by incorporation of 14C-leucine in the protein fraction of mycelium, grown during 7 days under continuous gamma-irradiation of low intensity and without it. The protein synthesis was activated in the radioactively treated mycelium of dark-pigmented C. cladosporioides strains and it was suppressed in similarly treated mycelium of alb-mutant of C. cladosporioides. The rate of 14C-leucine incorporation into biomass of investigated strains correlated with positive radiotropism. The dependence between protein synthesis intensity and the availability of melanin protection system in micromycetes is assumed.

Carbon Radioisotopes↗

Radiocesium-137 movement in a southern coastal plain ecosystem.

The movement of radiocesium (137Cs) in an open ecosystem under natural conditions was investigated at the Louisiana State University Radioecology Field Laboratory. Approximately 80 mCi of 137Cs were transferred to an experimental plot in September 1979. Observations over a six-month period beginning February 1981 indicated that the 137Cs content of plants growing naturally in the plot was low (0.98 Bq/g of plant tissue, dry wt). The vertical mobility of 137Cs to more than 10 cm was also found to be low (up to 1.32 Bq/g of soil, dry wt). The horizontal migration of 137Cs along water drainage directions from the plot was limited to the area of a small ditch that surrounds the experimental plot. No 137Cs above background was found in the fields beyond the 10 m X 10 m plot boundary. The overall results demonstrated that greater than 99.9% of the 137Cs remained within the top 10 cm of the soil profile of the experimental plot under natural field conditions.

Cesium Radioisotopes↗

Dynamics of 137Cs in the forests of the 30-km zone around the Chernobyl nuclear power plant.

Dynamics of the 137Cs content in the components of the forests in the 30-km zone around the Chernobyl nuclear power plant (NPP) in 1986-1994 are associated mainly with such factors as the size of radioactive particles in the fallout, ecosystem humidification and soil type, tree age. The influence of particle size was especially noticeable between 1986-1987 and was displayed by low biological availability of radionuclides in the near part of the zone (within the 10-km radius circle around the NPP) in comparison with more distant regions (within the 30-km radius circle). Later, the expression of this influence decreased and transfer factor (the ratio of 137Cs content in overground phytomass to the soil contamination density) became approximately the same for all plots with similar ecological and fallout characteristics. Humidity of landscape and soil type determined the velocity of radionuclide vertical migration in the soil and 137Cs biological availability. These parameters were maximum for the hydromorphic soils of wet landscapes enriched in organic substance and poor clayey minerals. Differences of 137Cs accumulation in overground phytomass of trees caused by tree age are displayed in the higher 137Cs concentration in structural parts of young trees as compared with old ones.

Cesium Radioisotopes↗

Technical basis for EPA's proposed regulation on the cleanup of sites contaminated with radioactivity.

The U.S. Environmental Protection Agency is proposing a regulation for the protection of the public from radioactive contamination at sites that are to be cleaned up and released for public use. The rule will apply to sites under the control of Federal agencies, and will impose limits on radiation doses to individuals living or working on a site following cleanup; it will thereby provide site owners and managers with uniform, consistent cleanup criteria for planning and carrying out remediation. This paper presents an overview of EPA's approach to assessing some of the beneficial and adverse effects associated with various possible values for the annual dose limit. In particular, it discusses the method developed to determine how the choice of cleanup criterion affects (1) the time-integrated potential numbers of non-fatal and fatal radiogenic cancers averted among future populations, (2) the occurrence of radiogenic cancers among remediation workers and the public caused by the cleanup process itself, and (3) the volumes of contaminated soil that may require remediation. The analytic methods described here were used to provide input data and assumptions for the Regulatory Impact Analysis (RIA) that supports the proposed regulation; the RIA also considered non-radiological benefits and costs (i.e., public health, economic, and ecological) of the standards.

Radiation Injuries↗

Modeling the outdoor environment--new perspectives and challenges.

Assessing risk from manmade and naturally occurring radionuclides in the environment has long been of primary interest in radiation protection. Early investigations and decisions relied on direct measurements of radiation in environmental media; however, these techniques were inadequate for determining exposure to humans and biota from very low levels of radiation and in predicting exposures from future releases. The Plowshare Program in 1957 investigated the use of nuclear explosives for peaceful purposes and created an immediate need for predicting the dispersion and ultimate fate of radionuclides that might be vented to the atmosphere or enter groundwater and expose man. As a result, modeling the behavior of radionuclides in the outdoor environment became a field of vigorous interest, merging disciplines of mathematics, biology and physics, among others. Environmental models and, more specifically, models predicting radiation dose from radionuclides in the environment have evolved rapidly and have increased significantly in sophistication, complexity and scope. Application of these models is commonly known as radiological assessment. This presentation examines the current status, future direction and weaknesses of radiological assessment models used in making decisions about radiation. The trend in recent years has been toward more complex models, which has not necessarily improved the accuracy of dose estimates and, in certain cases, has had the opposite effect. The presentation also discusses the future of model development, with particular emphasis on simple techniques and the expanded use of microcomputers, which will make radiological assessment models widely available for risk assessment and for practical applications such as the design of efficient monitoring programs and engineering calculations on the clean-up of contaminated soils. The screening models developed by the National Council on Radiation Protection and Measurements are offered as an example of a powerful yet simple method for demonstrating compliance with standards. Finally, the paper reviews two major areas of challenge for the future--defining uncertainty associated with radiological assessment models and the potential for converting radiological assessment models for use with nonradioactive environmental pollutants such as chemicals. Modeling radionuclides in the environment is adopting a new perspective. Future models will be less complex than their predecessors and will be adaptable to a much broader range of users. Key challenges remain in applying the techniques used for radionuclides to nonradioactive pollutants.

Air Pollutants, Radioactive↗

Radiocesium contamination in a submediterranean semi-natural ecosystem following the Chernobyl accident: measurements and models.

Radiocesium dynamics in a Quercus conferta Kit ecosystem in Northern Greece have been extensively studied over the years 1993-1995. Radiocesium distribution in the different parts of the ecosystem was measured. A total 137Cs inventory of 243+/-66 MBq ha(-1) due to the Chernobyl accident was measured in all parts of the ecosystem. Almost 90% of this inventory is still in the upper layers of the soil and the forest floor. In particular 13.4% is in the forest floor, 52.6% in the Ah horizon, and 23.4% in the upper 5 cm of the soil. Only 2.2% of this inventory is in the above ground biomass. The mean total 137Cs deposited on the forest floor from the above ground biomass is 0.18 MBq ha(-1) y(-1). Cesium leaching from the forest floor is negligible. The radiocesium distribution in soil is fixed and in equilibrium, at least since 1993. Most of radiocesium is not available for migration. Cesium migration in soil was modeled by a) an "equivalent diffusion" model with different initial conditions and b) a "compartment" model derived from a diffusion-advection model. A compartment model for the contamination of living biomass is proposed. The total absorbed dose rate in air as well as the contribution due to 137Cs from the Chernobyl accident was determined inside the forest, by in-situ gamma spectrometry.

Biomass↗

Radioactive contamination of forests in Poland.

Partial results of a large survey of radioactive contamination in Polish forests are presented. All measurements were performed with low-background gamma spectrometers. The measurement method is briefly described. Activities of 137Cs, 134Cs, 125Sb, 106Ru, 144Ce, 154Eu, 155Eu, and 60Co in A0 and A1 layers of forest litter from all over Poland are determined. The geographical distribution of contamination as well as its origin is discussed. Nonuniform composition of the Chernobyl fallout over Poland is confirmed and documented.

Agaricales↗

In-vivo estimates for the uptake of caesium-137 by cattle grazing contaminated pasture around the ESK and IRT estuaries, Cumbria, U.K.

Sea water contaminated with diluted radioactive effluent from the Windscale nuclear complex in Cumbria periodically floods low-lying grazing pasture around the estuaries of the rivers Esk, Irt and Mite near Ravenglass. During 1979, an experiment was carried out to measure the transfer of caesium-137 from grass to muscle in cows grazing these pastures. Grass samples were taken in a vivo external gamma-ray measurements were made on cattle. A very low transfer coefficient was found, less than 9 X 10-4 days kg-1 with a best estimate of 4 X 10-4 days kg-1, compared with a more usual value of around 3 X 10-2 days kg-1. The low transfer seems to occur because the bulk of the caesium-137 on the grass is bound to resuspended estuarine surface sediment deposited during flooding. In this form, the caesium-137 is only poorly absorbed across the gut of the grazing cattle.

Animals↗

Chemical speciation and bioavailability of elements in the environment and their relevance to radioecology.

The commonly used terms 'chemical speciation' and 'bioavailability' are discussed and an attempt made to produce both qualitative and quantitative descriptions of their influence on the transfer of elements in the environment. The importance of considering the presence of the many different species of radionuclides which may occur in the environment is emphasized. The limitations of using concentration ratios, which take no account of the differing bioavailability of various chemical species of radionuclides, are discussed.

Accidents↗

Radioactivity distribution in some Permian sediments from the Iratí and Corumbataí Formations of the Paraná Basin, Southeastern Brazil.

In the city of Limeira, southeastern Brazil, an important exposure of Permian sediments of the Paraná basin was revealed by an open pit mine that exploits limestone for production of soil correction compounds and raw materials for the ceramic industry. The radioactivity of these sediments was investigated in some detail and the results provided a general view of the vertical distributions of uranium, thorium and potassium concentrations and of the element ratios U/K, U/Th and Th/K. In general, the concentrations of the main natural radioactive elements are low, with uranium being enriched in some limestone and shale levels. In addition the results showed that the 238U series is in radioactive disequilibrium in many of the analyzed samples. Although the origin of the observed disequilibrium has not been investigated, the results suggest that it is due to weathering processes and water interaction with the rock matrix.

Brazil↗