DWPF GC FILTER ASSEMBLY SAMPLING AND ANALYSIS | |
Bannochie, C. ; Imrich, K. | |
Savannah River Site (S.C.) | |
关键词: Radioactive Waste Facilities; Flow Blockage; Off-Gas Systems; Sampling; 12 Management Of Radioactive Wastes, And Non-Radioactive Wastes From Nuclear Facilities; | |
DOI : 10.2172/969039 RP-ID : SRNL-STI-2009-00602 RP-ID : DE-AC09-08SR22470 RP-ID : 969039 |
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美国|英语 | |
来源: UNT Digital Library | |
【 摘 要 】
On March 18, 2009 a Defense Waste Processing Facility (DWPF) GC Line Filter Assembly was received at the Savannah River National Laboratory (SRNL). This filter assembly was removed from operation following the completion of Sludge Batch 4 processing in the DWPF. Work on this sample was requested in a Technical Assistance Request. This document reports the pictures, observations, samples collected, and analytical results for the assembly. The assembly arrived at SRNL separated into its three component filters: high efficiency particulate air (HEPA)-1, HEPA-2, and a high efficiency mist evaporator (HEME). Each stage of the assembly's media was sampled and examined visually and by scanning electron microscopy (SEM). Solids built up in the filter housing following the first stage HEME, were dissolved in dilute nitric acid and analyzed by ICP-AES and the undissolved white solids were analyzed by x-ray diffraction (XRD). The vast majority of the material in each of the three stages of the DWPF GC Line Filter Assembly appears to be contaminated with a Hg compound that is {approx}59 wt% Hg on a total solids basis. The Hg species was identified by XRD analysis to contain a mixture of Hg{sub 4}(OH)(NO{sub 3}){sub 3} and Hg{sub 10}(OH){sub 4}(NO{sub 3}){sub 6}. Only in the core sample of the second stage HEPA, did this material appear to be completely covering portions of the filter media, possibly explaining the pressure drops observed by DWPF. The fact that the material migrates through the HEME filter and both HEPA filters, and that it was seen collecting on the outlet side of the HEME filter, would seem to indicate that these filters are not efficient at removing this material. Further SRAT off-gas system modeling should help determine the extent of Hg breakthrough past the Mercury Water Wash Tank (MWWT). The SRAT off-gas system has not been modeled since startup of the facility. Improvements to the efficiency of Hg stripping prior to the ammonia scrubber would seem to be the only way to prevent/mitigate the formation of the compounds found in the GC Line Filter Assembly filters and therefore prevent pluggage of this filter assembly.
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