Abstract
Types, amounts and activity concentrations of the radioactive wastes arising from the different sections of the fuel cycle are described as well as the methods of their treatment and final disposal. By conversion to glass products, highly active fission product solutions can be transferred into a form well suited for final disposal. Low and medium level waste waters are purified so far that safe discharge or reuse is possible. The concentrates thus produced are incorporated into concrete or bitumen. Baling lends itself for treatment of non-combustible solid wastes. Combustible wastes can be incinerated, the residues are incorporated into concrete. For final storage of the conditioned wastes, salt formations in the deep underground are chosen in the Federal Republic of Germany. They offer a series of favourable preconditions for this purpose and guarantee the isolation of the radionuclides from the biocycle over secular periods of time.
Krause, H
[1]
- Kernforschungszentrum Karlsruhe (Germany, F.R.)
Citation Formats
Krause, H.
Treatment and final storage of radioactive wastes from the nuclear fuel cycle.
Germany: N. p.,
1977.
Web.
Krause, H.
Treatment and final storage of radioactive wastes from the nuclear fuel cycle.
Germany.
Krause, H.
1977.
"Treatment and final storage of radioactive wastes from the nuclear fuel cycle."
Germany.
@misc{etde_5386452,
title = {Treatment and final storage of radioactive wastes from the nuclear fuel cycle}
author = {Krause, H}
abstractNote = {Types, amounts and activity concentrations of the radioactive wastes arising from the different sections of the fuel cycle are described as well as the methods of their treatment and final disposal. By conversion to glass products, highly active fission product solutions can be transferred into a form well suited for final disposal. Low and medium level waste waters are purified so far that safe discharge or reuse is possible. The concentrates thus produced are incorporated into concrete or bitumen. Baling lends itself for treatment of non-combustible solid wastes. Combustible wastes can be incinerated, the residues are incorporated into concrete. For final storage of the conditioned wastes, salt formations in the deep underground are chosen in the Federal Republic of Germany. They offer a series of favourable preconditions for this purpose and guarantee the isolation of the radionuclides from the biocycle over secular periods of time.}
journal = []
volume = {101:5}
journal type = {AC}
place = {Germany}
year = {1977}
month = {May}
}
title = {Treatment and final storage of radioactive wastes from the nuclear fuel cycle}
author = {Krause, H}
abstractNote = {Types, amounts and activity concentrations of the radioactive wastes arising from the different sections of the fuel cycle are described as well as the methods of their treatment and final disposal. By conversion to glass products, highly active fission product solutions can be transferred into a form well suited for final disposal. Low and medium level waste waters are purified so far that safe discharge or reuse is possible. The concentrates thus produced are incorporated into concrete or bitumen. Baling lends itself for treatment of non-combustible solid wastes. Combustible wastes can be incinerated, the residues are incorporated into concrete. For final storage of the conditioned wastes, salt formations in the deep underground are chosen in the Federal Republic of Germany. They offer a series of favourable preconditions for this purpose and guarantee the isolation of the radionuclides from the biocycle over secular periods of time.}
journal = []
volume = {101:5}
journal type = {AC}
place = {Germany}
year = {1977}
month = {May}
}