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Salar

Brine Sources. Lithium occurs naturally in brines from salars, saline lakes and seawater, od-fteld waters, and geothermal brines. Of these sources, lithium is produced only from brines of two salars. [Pg.221]

Sa.Ia.rs and Lakes. Brines having high lithium concentration are found in salars of northern Chile, southwestern Bohvia, and northwestern Argentina. Brines of lower lithium concentration are found in salars in the western United States and the Tibetan Plateau. Brines pumped from beneath the surface of the Salar de Atacama (Chile) and Silver Peak (Clayton Valley, Nevada) are used for commercial production of lithium uti1i2ing solar evaporation (see Chemicals frombrines). The concentration of selected ions in brines from salars and lakes of potential commercial interest worldwide are shown in Table 1. [Pg.221]

Occurrence. Brine found in Seades Lake, California is the only brine source where boron is produced commercially. Other brine bodies such as the Great Salt Lake or brine from thermal weUs at the Salton Sea have been considered but have not been exploited. Brines at the Salar de Atacama in Chile also contain boron, but it is not presently extracted. [Pg.409]

Occurrence. Numerous brines contain lithium in minor concentrations. Commercially valuable natural brines are located at Silver Peak, Nevada (400 ppm) (40,41), and at Seades Lake, California (50 ppm) (42,43). Great Salt Lake brine contains 40 ppm and is a source not yet exploited. Seawater contains less than 0.2 ppm. Lithium production started at Silver Peak in the 1970s. The concentration of lithium in the brine is diminishing, and now the principal production occurs from brine in the Salar de Atacama, Chile. [Pg.411]

Recovery Process. Lithium is extracted from brine at Silver Peak Marsh, Nevada, and at the Salar de Atacama, Chile. Both processes were developed by Foote Mineral Corp. The process at Silver Peak consists of pumping shallow underground wells to solar ponds where brines are concentrated to over 5000 ppm. Lithium ion is then removed by precipitation with soda ash to form a high purity lithium carbonate [554-13-2]. At the Atacama, virgin brine with nearly 3000 ppm lithium is concentrated to near saturation in lithium chloride [7447-41 -8]. This brine is then shipped to Antofagasta, Chile where it is combined with soda ash to form lithium carbonate. [Pg.411]

Economic Aspects and Uses. In 1976, one-third of the lithium produced in the United States was extracted from brines of Seades Lake and Silver Peak (44,45). Since then, lithium production at Seades Lake has been discontinued and the lithium concentration at Silver Peak is decreasing. During the 1980s lithium extraction was started at the Salar de Atacama, Chile. This is the largest lithium production plant in the wodd using brine as its raw material. [Pg.411]

Besides the oceans, there are vast reserves of magnesium chloride in the Dead Sea Qaidam Basin, China and many salars of South America. [Pg.411]

New technology and development of brine reserves are increasing each year in the United States and abroad. This affects the uses and price of brine chemicals. For example, development of the Salar de Atacama in Chile in the 1980s as the largest producer of brine lithium in the world has affected lithium production and prices worldwide. Lithium production from Seades Lake brine has been discontinued, and the Silver Peak operation in Nevada is in a slow production decline caused by weaker brine grades. [Pg.414]

Bangsgaard, K., Madsen, S.S., and Korsgaard, B. (2006). Effect of waterhome exposnre to 4-tert-octylphenol and 17(beta)-estradiol on smoltification and downstream migration in Atlantic salmon, Salmo salar. Aquatic Toxicology 80, 23-32. [Pg.338]

Morgan, M.J., Fancey, L.L., and Kiceniuk, J.W. (1990). Response and Recovery of Brain Acetylcholinesterase Activity in Atlantic Salmon (Sahno-Salar). Exposed to Fenitrothion. Canadian Journal of Fisheries and Aquatic Sciences 47, 1652-1654. [Pg.361]

NORDRUM S, BAKKE-MCKELLEP A M, KROGDAHL A, BUDDINGTON R K (2000) Effects of Soybean meal and salinity on intestinal transport of nutrients in Atlantic salmon (Salmo salar L.) and rainbow trout Oncorhynchus mykiss). Comp Biochem Physiol B Biochem Mol Biol. 125 317-35. [Pg.182]

Christiansen, R., Lie, O., and Torrissen, O.J., Growth and survival of Atlantic salmon, Salmo salar L, fed different dietary levels of astaxanthin first-feeding fry, Aquacult. Nutr., 1, 189, 1995. [Pg.424]

Robst AL, Lowenstein TK, Jordan TE, Godfrey LV, Ku T-L, Luo S (2001) A 106 ka paleoclimate record from drill core of the Salar de Atacama, northern Chile. Paleogeo Paleoclim Paleoecol 173 21-42 Rosholt JN (1957) Quantitative radiochemical methods for determination of the sources of natural radioactivity. Anal Chem 29 1398-1408... [Pg.404]

Salares VR, Young NM, Carey PR, and Bernstein HJ. 1977. Excited-state (exciton) interactions in polyene aggregates—Resonance Raman and absorption spectroscopic evidence. Journal of Raman Spectroscopy 6(6) 282-288. [Pg.57]

Rombough, P.J. and E.T. Garside. 1982. Cadmium toxicity and accumulation in eggs and alevins of Atlantic salmon, Salmo salar. Canad. Jour Zool. 60 2006-2014. [Pg.76]

Winberg, S., R. Bjerselius, E. Baatrup, and K.J. Doving. 1992. The effect of Cu(II) on the electro-olfactogram (EOG) of the Atlantic salmon (Salmo salar L) in artificial freshwater of varying inorganic carbon concentrations. Ecotoxicol. Environ. Safety 24 167-178. [Pg.234]

Baatrup, E. and K.B. Doving. 1990. Flistochemical demonstration of mercury in the olfactory system of salmon (Salmo salar L.) following treatments with dietary methylmercuric chloride and dissolved mercuric chloride. Ecotoxicol. Environ. Safety 20 277-289. [Pg.425]

Hodson, P.V. and J.B. Sprague. 1975. Temperature-induced changes in acute toxicity of zinc to Atlantic salmon (Salmo salar). Jour. Fish. Res. Bd. Canada 32 1-10. [Pg.733]

Atlantic salmon, Salmo salar, east coast of Canada, 1976, egg ... [Pg.847]

Zitko, V. and R.L. Saunders. 1979. Effect of PCB s and other organochlorine compounds on the hatchability of Atlantic salmon (Salmo salar) eggs. Bull. Environ. Contam. Toxicol. 21 125-130. [Pg.886]

Alabaster, J.S., D.G. Shurben, and M.J. Mallett. 1983. The acute lethal toxicity of mixtures of cyanide and ammonia to smolts of salmon, Salmo salar L. at low concentrations of dissolved oxygen. Jour. Fish Biol. 22 215-222. [Pg.956]


See other pages where Salar is mentioned: [Pg.866]    [Pg.13]    [Pg.221]    [Pg.221]    [Pg.221]    [Pg.221]    [Pg.221]    [Pg.221]    [Pg.222]    [Pg.223]    [Pg.399]    [Pg.32]    [Pg.495]    [Pg.56]    [Pg.56]    [Pg.169]    [Pg.193]    [Pg.598]    [Pg.602]    [Pg.654]    [Pg.663]    [Pg.697]    [Pg.704]    [Pg.718]    [Pg.918]    [Pg.934]    [Pg.973]    [Pg.1004]   
See also in sourсe #XX -- [ Pg.333 , Pg.392 , Pg.402 ]




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Salmo salar

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