The long-range objective of this study was to develop chemically assisted technologies for removing heels from tanks. In FY 01, the first two steps toward this objective were taken: (1) catalogue the occurrence and nature of tank heels and assess which materials are available for study and (2) develop methods for synthesizing non-radioactive surrogate heel materials for use in testing potential removal technologies.The chief finding of Task 1 was the existence of "heels", depending on the definition used. Hard materials that would be almost impossible to remove by sluicing are all but absent from the records ofboth Savannah River and Hanford. Historical usage suggests that the term "heel" may also apply to chunky, granular, or semi-solid pasty accumulations. These materials are documented and may also be difficult to remove by conventional sluicing technologies. Such heels may be comprised of normal sludge components, dominantly iron and aluminum hydroxides, or they may result from added materials which were not part of the normal fuel reprocessing operations: Portland cement, diatomaceous earth, sand and soil and spent zeolite ion exchange "resins". The occurrence and chemistry of the most notable "heel", that of the zeolite mass in Tank 19F at Savannah River, is reviewed in some detail. Secondly, no clear correlation was found between high tank temperatures and difficulties encountered in removing materials fiom a tank at a later date; nor did the sludges fiom these tanks give any indication of being particularly solid.Experimental studies to develop synthetic heel materials were caned out using a number of different approaches. For normal sludge materials settling, even when assisted by a centrihge, it proved ineffective. The same result was obtained from drylng sludge samples. Even exposing sludges to a molten salt melt at 233' C, only produced a fine powder, rather than a resilient ceramic which resisted disaggregation. A cohesive material, however, was produced by wicking the pore fluid out of a sludge gel (into packed diatomaceous earth), while simultaneously applying pressure to compact the sludge as it dehydrated. Osmotic gradients could provide the same fimction as the capillary forces provided by the diatomaceous earth sorbant placed in contact with the sludge. Tests on the anomalous materials added to the tanks all indicated potential problems. Hard granules, and maybe chunks, may be encountered where Portland cement was added to a tank. Sand, spent zeolite resin, and diatomaceous earth, will all react with the tank fluids to produce a sodalite/cancrinite material. The degree of reaction determines whether the grains become cemented together. SRS activities showed that heels formed when spent zeolites were added to 3 tanks can be readily dislodged and it is expected that heels from sand would possess equal or less cohesion. Diatomaceous earth may f o m more resilient crusts or masses.To summarize, the existence of "hard" heels has yet to be documented. A broader definition suggests inclusion ...