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18 <br /> of a fine water spray, described earlier, provides another technique which may <br /> be effective for controlling excess acidity. <br /> Tailings samples from several locations would not support vegetation <br /> without neutralization. Among these were uranium tailings from Wyoming and <br /> Colorado which had respective pH values of 2.3 and 4.5. Addition of 70 and <br /> 7 pounds of lime per acre, respectively, added to the top 2 inches of tailings <br /> raised the pH to a level high enough to sustain plant life. The tailings pile <br /> at the site of the former Vitro Minerals & Chemical Co. , Salt Lake City, Utah, <br /> contains both acidic uranium tailings (pH 3.6) and basic vanadium tailings <br /> (pH 8.5). These were mixed in the laboratory in equal portions to produce a <br /> material of pH 6.3 in which seeds readily germinated. Fertilization, however, <br /> was necessary to sustain adequate plant growth. <br /> Altering the Structure and Organic Composition of Tailings <br /> As previously noted, fine mineral wastes lack nutrients, humus, and micro <br /> bial populations all of which militate against the growth of vegetation. They <br /> may also lack the proper surface structure for air and water access and resist <br /> ance to being blown or washed away. Coarse grains and mineral aggregates are <br /> of importance on the surface of beach and pond areas of tailings accumulations <br /> because they resist movement by wind and water. Coarse grains and aggregates <br /> are of even greater benefit to stability,on the sloping dikes of the tailings <br /> ponds. Fertile soil in which vegetation grows most abundantly, unlike mill <br /> tailings, usually contains a small but important percentage of organic matter <br /> and micro-organisms. Plants can be grown well in pure sand cultures to which <br /> have been added a proper balance of all the necessary mineral compounds needE� <br /> by the plant, but if a little appropriate organic matter, such as leaf mold, <br /> is added, the plants grow much better. To prepare synthetic soils from barren <br /> tailings, research was conducted using additions of chemicals, sewage sludge, <br /> and compost. <br /> Structural and Organic Modifications of Tailings <br /> Several methods were tried for increasing particle aggregation of tail- <br /> ings to provide better root environment and soil aeration, thereby improving <br /> vegetative growth. Effective pelletizing and agglomerating procedures were <br /> developed. One of these procedures consisted of pelletizing tailings to <br /> minus-8-plus-35-mesh size with 2.5 percent asphalt, hardening the pellets by <br /> baking at 250° C, and spreading the pellets over the surface of the tailings <br /> to a depth of 1/2 inch, or mixing the pellets with an equal quantity of tail- <br /> ings to form a 1-inch-deep covering over normal tailings. A similar pellet <br /> was prepared, without the baking step, by pelletizing with 3 to 4 percent <br /> Peneprime (a commercial asphaltic bitumen product cut with white kerosine) or <br /> with 1 to 2 percent Coherex. Another procedure not requiring pelletization <br /> encompassed (1) seeding, (2) watering, (3) raking the wet tailings to form <br /> small-size agglomerates , and (4) spraying the agglomerates with Coherex and/or <br /> Soil Gard to preserve the pelletized form. Plant growth was improved in all <br /> instances where a granular, soillike texture was achieved by these methods. <br /> Additionally, two types of municipal wastes were tested as additives to <br /> x tailings. One was a commercial compost made from municipal refuse , and the <br />