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Environmental fallout

Apart from the environmental fallout (elimination of emissions of greenhouse gases) this process allows one to obtain industrially useful energy in the form of medium-pressure steam (0.16 toristeaxn per ton A)- All this occurs in the absence of fuel consumption (e.g., methane) and with a negligible use of power for the movement of process fluids. [Pg.382]

In this section only the bioburden determination of a parenteral product solution for aerobic isolates is discussed and details regarding bioburden testing of facility or equipment surfaces are not included. For parenteral products, bioburden is usually estimated on the unfiltered bulk product solution (UBPS). In this way the test will indicate the total microbial load culminating in the batch solution as a result of the various contributing factors such as all batch ingredients, manual manipulations, and environmental fallout. Testing of filtered bulk parenteral solution either before or after filling into the final container may be done for comparison to the previously tested unfiltered bulk solution or to comply with the directives from European inspectors. All isolates should be identified to the species level whenever possible. The... [Pg.294]

Lntts, R. H. (1985). Chemical Fallout Rachel Carson s Silent Spring, Radioactive Fallout and the Environmental Movement. Environmental Histoiy Review 9 210—225. [Pg.223]

The plutonium concentration in marine samples is principally due to environmental pollution caused by fallout from nuclear explosions and is generally at very low levels [75]. Environmental samples also contain microtraces of natural a emitters (uranium, thorium, and their decay products) which complicate the plutonium determinations [76]. Methods for the determination of plutonium in marine samples must therefore be very sensitive and selective. The methods reported for the chemical separation of plutonium are based on ion exchange resins [76-80] or liquid-liquid extraction with tertiary amines [81], organophosphorus compounds [82,83], and ketones [84,85]. [Pg.354]

The 239j240pu can (je accounted for as being from nuclear weapons-produced fallout over the past 30 years, and not from the waste disposal canisters. The mechanism must be by transport and redistribution of the fine floculent sediment at the sediment-water interface. Because of the significant amount of sediment which is being transported down-canyon, any leakage from the canisters would probably be scavenged locally by the environmental sediment material. [Pg.357]

Clooth, G. and D.C. Aumann. 1990. Environmental transfer parameters and radiological impact of the Chernobyl fallout in and around Bonn (FRG). Jour. Environ. Radioactivity 12 97-119. [Pg.1739]

Melin J. and Wallberg L. Distribution and retention of cesium in Swedish boreal forest ecosystems, in The Chernobyl fallout in Sweden, results from a research program on environmental radiology, ed. J. Moberg, Stockholm, Swedish Radiat. Protect. Inst., 1991, pp. 467-475. [Pg.43]

Bunzl, K Flessa, H., Krackf, W. Schimmack, W. 1995. Association of fallout 239+240pu and 241 Am with various soil components in successive layers of grassland soil. Environmental Science Technology. 29. 2513-2518. [Pg.150]

Michel, H., Barci-Funel, G., Dalmasso, J., Ardisson, G., Appleby, P. G Haworth, E. El-Daoushy, F. 2002. Plutonium and americium inventories in atmospheric fallout and sedimentary coves from Blelham Tarn, Cumbria, UK. Journal of Environmental Radioactivity, 59, 127-137. [Pg.151]

Montero, P. R. Sanchez, A. M. 2001. Plutonium contamination from accidental release or simply fallout study of soils at Palomares (Spain). Journal of Environmental Radioactivity, 55, 157-165. [Pg.151]

Environmental impact. Contamination by fallout from downwind transport of emitted particulate matter from the oil-shale power stations has been demonstrated throughout northeastern Estonia, as far as c. 140 km northwards to Finland and as far as 100 km to the southwest within Estonia (Jalkanen et aL 2000). Indeed, Teinemaa et al. (2002) and Jalkanen et aL (2000) examined the morphology of particles in power station fly ash (see Fig. 9) and found similarities in structure, size and chemical composition of particles collected from moss surfaces in northeastern Estonia and southeastern Finland. Although the emissions of SO2 and NOx from the BPP and EPP are generally similar to, or lower than, those from conventional... [Pg.278]


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