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Nuclear waste, discharges

Plutonium (Pu) is an artificial element of atomic number 94 that has its main radioactive isotopes at 2 °Pu and Pu. The major sources of this element arise from the manufacture and detonation of nuclear weapons and from nuclear reactors. The fallout from detonations and discharges of nuclear waste are the major sources of plutonium contamination of the environment, where it is trapped in soils and plant or animal life. Since the contamination levels are generally very low, a sensitive technique is needed to estimate its concentration. However, not only the total amount can be estimated. Measurement of the isotope ratio provides information about its likely... [Pg.369]

Sekimoto H, Nakamura H, Takagi N. 1996. Toxicity of radioactive wastes discharged from nuclear energy center in the future equilibrium state. Ann Nucl Energy 23(8) 663-668. [Pg.260]

The scope and scale of pollution from radionuclides has been greatly reduced due to (1) the cessation of aboveground nuclear bomb testing, (2) an international ban on the dumping of nuclear wastes at sea, and (3) better control of discharges from power and fuel reprocessing plants. [Pg.807]

Radioactive substances The principal sources of radionuclides released into the environment include nuclear weapon testing fallout from accidents such as the Chernobyl accident in 1986 or from foundering of nuclear submarines from the dumping of nuclear waste into the deep ocean and from discharges from nuclear power plants and nuclear reprocessing plants. [Pg.10]

The following section provides detailed information concerning the transport of radionuclides associated with two very different field analogues the Chernobyl reactor accident and the Oklo Natural Reactor. These examples span wide temporal and spatial scales and include the rapid geochemical and physical processes important to nuclear reactor accidents or industrial discharges as well as the slower processes important to the geologic disposal of nuclear waste. [Pg.4783]

The characteristics of permeate and retentate streams in terms of upper limits at the exit of RO plant were presented in Table 30.2. The concentration of salt in permeate is lower than 0.1 g/dm. The concentration of some specific elements as heavy metals has to be in conformity with the limits of impurities for wastes discharged to the inland waters. Total specific activity for (3 and y emitters is lower than 10 kBq/m, while for a emitters it is lower than 1 kBq/m (the limits for liquid waste). The total salt concentration in retentate is limited by ability of binding the solution with the concrete, the specific radioactivity by nuclear... [Pg.852]

Radioactive transuraiuc elements with atomic numbers that are greater than 92 have been introduced into the environment since the 1940s from atmospheric testing of nuclear weapons, discharges of nuclear wastes, and nuclear fuel reprocessing. Transuranic isotopes with half-lives of more than 10,000 years (i.e., 24Vcm, " Pa,... [Pg.686]

An interesting application of emissions control catalysts occurs in management and inmiobilization of spent radioactive fuels and wastes in the nuclear industry. During nuclear waste processing (NWP) at the Idaho Chemical Processing Plant (ICPP) NOx (NO and NO2) and CO pollutants are typically discharged at levels of 1-3% to a waste gas stream. It is necessary to control both NOx CO emissions in order to comply with current and anticipated regulatory requirements. [Pg.56]

The civilian nuclear icebreaker facility, RTP ATOMFLOT, is located in Kola Bay, Northwest Russia, where several nuclear installations are operated by the Russian Northern Fleet. The Atomfiot facility discharges purified nuclear waste into the bay at an annual rate of 500 m. The mean Cs activity concentration of seawater at the mouth of the Kola Bay was (8.0 0.8) Bq/m at 1994, showing no indication of contamination. In 1986, Cs levels in seaweed were increased by the Chernobyl release, but in the 1990s, Cs levels decreased to less than 2 Bq/kg from 8 Bq/kg earlier in the 1980s. However, one exceptional seaweed sample, which shows Cs level of (46 5) Bq/kg wet wt. and additional radioactivities of Cs, Ru, Co, and Eu, is found in the Atomfiot area (Matishov et al. 2000). [Pg.2522]

The narrow spectral line of a DL enables isotope selective analysis. For light and heavy elements (such as Li and U) the isotope shifts in spectral lines are often larger than the Doppler widths of the lines, in this case isotopically selective measurements are possible using simple Doppler-limited spectroseopy - DLAAS or laser induced fluorescence (LIF). For example, and ratios have been measured by Doppler-limited optogalvanic. spectroscopy in a hollow cathode discharge. DLAAS and LIF techniques have been combined with laser ablation for the selective detection of uranium isotopes in solid samples. This approach can be fruitful for development of a compact analytical instrument for rapid monitoring of nuclear wastes. [Pg.743]

Other practical issues which derive from the lack of effective demarcation include the problem of spacecraft using nuclear fuels which discharge nuclear waste. It may be the case that states can prohibit the unauthorized discharge of nuclear waste onto their territory, but the question then to be answered is at what altitude spacecraft are able to discharge nuclear waste, without such discharge being an attack on a nation s territory. [Pg.2167]

The principal sources of radioactive waste discharges, containing artificial radionuclides, to the Irish Sea and all UK coastal waters, are mostly related to power generation and the nuclear fuel cycle. The locations of these sources are shown in Figure 1. [Pg.145]

Transuranic Waste. It has been proposed that in the future the transuranic (plutonium-containing) wastes be placed in deep mined vaults. This includes the high-level nuclear wastes. The vaults are expected to be about 1000 meters below the earth s surface and will be backfilled and sealed as they are filled. It appears that the repository capacity for high-level wastes will be heat-limited to one kilowatt/acre. This is equivalent to one ton of fuel after storage for ten years. The spent fuel discharged by the year 2000 will require about 2700 subterranean acres. This would... [Pg.1262]


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