The cement solidification systems at LANL
Conference
·
OSTI ID:6161985
There are two major cement solidification systems at Los Alamos National Laboratory. Both are focused primarily around treating waste from the evaporator at TA-55, the Plutonium Processing Facility. The evaporator receives the liquid waste stream from TA-55's nitric acid-based, aqueous-processing operations and concentrates the majority of the radionuclides in the evaporator bottoms solution. This is sent to the TA-55 cementation system. The evaporator distillate is sent to the TA-50 facility, where the radionuclides are precipitated and then cemented. Both systems treat TRU-level waste, and so are operated according to the criteria for WIPP-destined waste, but they differ in both cement type and mixing method. The TA-55 systems uses Envirostone, a gypsum-based cement and in-drum prop mixing; the TA-50 systems uses Portland cement and drum tumbling for mixing.
- Research Organization:
- Los Alamos National Lab., NM (USA)
- Sponsoring Organization:
- DOE/DP
- DOE Contract Number:
- W-7405-ENG-36
- OSTI ID:
- 6161985
- Report Number(s):
- LA-UR-90-4161; CONF-901264--1; ON: DE91005897
- Country of Publication:
- United States
- Language:
- English
Similar Records
Immobilization of Rocky Flats Plant liquid organic wastes
Waste-form development for conversion to portland cement at Los Alamos National Laboratory (LANL) Technical Area 55 (TA-55)
Designing a solidification/stabilization process for a fine powder mixed radioactive waste
Technical Report
·
Mon Oct 17 00:00:00 EDT 1983
·
OSTI ID:6320993
Waste-form development for conversion to portland cement at Los Alamos National Laboratory (LANL) Technical Area 55 (TA-55)
Technical Report
·
Tue Oct 01 00:00:00 EDT 1996
·
OSTI ID:392776
Designing a solidification/stabilization process for a fine powder mixed radioactive waste
Journal Article
·
Fri Dec 30 23:00:00 EST 1994
· Transactions of the American Nuclear Society
·
OSTI ID:89454
Related Subjects
052001* -- Nuclear Fuels-- Waste Processing
12 MANAGEMENT OF RADIOACTIVE AND NON-RADIOACTIVE WASTES FROM NUCLEAR FACILITIES
ALKALI METAL COMPOUNDS
ALKALINE EARTH
ALKALINE EARTH METAL COMPOUNDS
ALPHA-BEARING WASTES
ALUMINIUM COMPOUNDS
ALUMINIUM SILICATES
BUILDING MATERIALS
CALCIUM COMPOUNDS
CALCIUM SULFATES
CEMENTS
GYPSUM
INORGANIC ION EXCHANGERS
ION EXCHANGE MATERIALS
IRON COMPOUNDS
IRON SILICATES
LANL
LIQUID WASTES
MAGNESIUM COMPOUNDS
MAGNESIUM SILICATES
MANAGEMENT
MATERIALS
MINERALS
NATIONAL ORGANIZATIONS
OXYGEN COMPOUNDS
PHASE TRANSFORMATIONS
PORTLAND CEMENT
PROCESSING
RADIOACTIVE MATERIALS
RADIOACTIVE WASTE MANAGEMENT
RADIOACTIVE WASTE PROCESSING
RADIOACTIVE WASTES
SILICATES
SILICON COMPOUNDS
SLUDGES
SODIUM COMPOUNDS
SODIUM SILICATES
SOLIDIFICATION
SULFATE MINERALS
SULFATES
SULFUR COMPOUNDS
TRANSITION ELEMENT COMPOUNDS
US DOE
US ORGANIZATIONS
VERMICULITE
WASTE MANAGEMENT
WASTE PROCESSING
WASTES
12 MANAGEMENT OF RADIOACTIVE AND NON-RADIOACTIVE WASTES FROM NUCLEAR FACILITIES
ALKALI METAL COMPOUNDS
ALKALINE EARTH
ALKALINE EARTH METAL COMPOUNDS
ALPHA-BEARING WASTES
ALUMINIUM COMPOUNDS
ALUMINIUM SILICATES
BUILDING MATERIALS
CALCIUM COMPOUNDS
CALCIUM SULFATES
CEMENTS
GYPSUM
INORGANIC ION EXCHANGERS
ION EXCHANGE MATERIALS
IRON COMPOUNDS
IRON SILICATES
LANL
LIQUID WASTES
MAGNESIUM COMPOUNDS
MAGNESIUM SILICATES
MANAGEMENT
MATERIALS
MINERALS
NATIONAL ORGANIZATIONS
OXYGEN COMPOUNDS
PHASE TRANSFORMATIONS
PORTLAND CEMENT
PROCESSING
RADIOACTIVE MATERIALS
RADIOACTIVE WASTE MANAGEMENT
RADIOACTIVE WASTE PROCESSING
RADIOACTIVE WASTES
SILICATES
SILICON COMPOUNDS
SLUDGES
SODIUM COMPOUNDS
SODIUM SILICATES
SOLIDIFICATION
SULFATE MINERALS
SULFATES
SULFUR COMPOUNDS
TRANSITION ELEMENT COMPOUNDS
US DOE
US ORGANIZATIONS
VERMICULITE
WASTE MANAGEMENT
WASTE PROCESSING
WASTES