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14 <br /> Breaking the dormancy of Indian ricegrass seeds offers substantial prom- <br /> ise for initiating this type of growth on adverse tailing materials, thus <br /> offering the potential of reducing nitrogen fertilizer requirements and <br /> related maintenance costs. Stands of Indian ricegrass are normally short- <br /> lived, but should prepare the way for accession of other plants. Tests are <br /> underway to determine if properly treated seeds can be germinated and growth <br /> sustained in adverse tailing materials. <br /> Vegetating Adverse Tailings <br /> Practically all mill tailings contain deleterious inorganic salts, lack <br /> organic components and essential nutrients, and do not have the physical <br /> nature required for sustaining vegetative growth. For many tailings these <br /> adverse conditions can be overcome in time by fertilization, gradual buildup <br /> of organic and microbial populations by encouraging plant growth, and use of <br /> chemicals for binding of the surface to prevent blowing of loose sands that <br /> cut off or bury established vegetation. However, excessive salinity or acid- <br /> ity presents more difficult problems. Combination problems can exist in which <br /> tailings may be excessively saline, because of the recycling of processing <br /> waters, and simultaneously contain sulfide materials such as pyrite that upon <br /> oxidation would drop the pH of the tailings to a low level in a- relatively <br /> short time. Such a tailing is Kennecott's Utah Copper Division milling waste. <br /> This material with a pH of 7.8, when fresh, contains salinity equivalent to <br /> 2.4 atmospheres osmotic concentration plus approximately 1.3 percent pyrite. <br /> The salts in the tailings cause an osmotic gradient that transfers fluid from <br /> the plants and thus vegetation dies of dehydration shortly after sprouting. <br /> Another problem is that , if vegetation is planted on these tailings and irri- <br /> gation of the plants leaches away the salts, the pyrite oxidizes and the pH <br /> may drop from 7.8 to less than 3.0 within a month's time. Therefore, this <br /> material was considered as a typical adverse waste and was used for laboratory <br /> and small field testing. <br /> Salinity and Heavy Metal Salt Problems <br /> Salts present in the wastes or mill waters impede plant growth. Consid- <br /> erable difficulty was encountered in growing vegetation in milling wastes from <br /> Kennecott's Utah Copper Division. To determine the reasons, duplicate plant- <br /> ings were made in (1) the normal flotation tailings, containing considerable <br /> water-soluble salts,but assaying only 0.05 percent copper, and (2) a simulated <br /> tailing containing few soluble salts but almost 0.25 percent copper. In both <br /> materials the copper was present mainly as the sulfide mineral, chalcopyrite. <br /> Seeded test plots were watered'with tapwater and tailings effluent water. <br /> Both germination and growth were adversely affected when effluent water was <br /> used. For samples watered with tapwater, germination and growth were much <br /> better in the simulated tailing material despite the higher content of copper. <br /> These tests indicated that the toxicity was due primarily to the high salt con- <br /> tent of the water and tailings. <br /> Supplementary tests were made to determine which salts or organic <br /> reagents in the copper mill tailings solutions most affected plant growth. <br /> The tailings water was compared with a prepared solution simulating saline but <br />