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Mineral Tolerance of Domestic Animals (1980)
Board on Agriculture (BOA)

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510
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510

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Titanium Titanium (Ti) is a dark, gray metal that ranks eighth in abundance in igneous rocks. The concentration in the earth's crust is estimated to be 0.43 percent. The most important titanium ores are ilmenite (PeTiO3) and rutile (TROD. Titanium is also found as a silicate (sphere), as calcium titanate (CaTiO3), and in association with hematite deposits (Browning, 19691. Titanium forms compounds in which it has an oxida- tion state of +2, +3, or +4. It is used as a constituent of aluminum, tin, and vanadium alloys and is particularly important as ferrotitanium in the steel industry. Titanium oxide is used as a white pigment in paint and as a constituent of the coating of welding rods. Titanium dioxide is used as an ingredient marker in comminuted meats. Titanium com- pounds are used as a mordant in the dyeing industry, as a constituent of glass and ceramics, in surgical devices for properties of lightness and tensile strength, and with carbon and tungsten in the manufacture of electrodes and lamp f~larnents. Cobalt cemented carbides (Carbaloy) used in cutting tools contain titanium, and the military uses titanium chloride as a smoke screen. ESSENTIALITY No essential metabolic function for titanium has been established in either plants or animals. 510

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Titanium METABOLISM 511 Published evidence on absorption of titanium from the alimentary tract is contradictory. Lehmann and Herget (1927) found no evidence of absorption when titanium oxide was fed. However, when Lloyd et al. (1955) attempted to use titanium oxide as an indigestible marker for digestion studies, they were unable to completely recover the element In the feces. They suggested that prolonged retention in some portion of the digestive tract (such as the cecum) may provide the explanation. However, Tipton et al. (1966) found significant urinary excretion of titanium in two humans consuming 0.37 and 0.41 mg per day in their diet. Both individuals were in negative titanium balance, and about equal amounts were found in feces and urine. It was not established whether urinary titanium was derived from titanium absorbed during the study or whether it came from previously established tissue stores. SOURCES The titanium concentration of herbage can be used as an index of soil contamination (Barlow e' al., 1960), because soil concentrations of titanium are about 10,000 times greater than those in uncontaminated herbage (Swaine, 19551. A variety of plants were assayed by Bertrand and Varonca-Sp~rt (1929a,b), who found titanium levels ranged from 0.1 to 5 ppm (dry basis) with a majority near 1 ppm. Mitchell (1957) found a mean of 1.8 ppm (range 0.7-3.8) on a dry basis in red clover and a mean of 2.0 ppm (range 0.9- 4.6) In ryegrass. Titanium concentrations of individual human foods have not been reported, but Tipton et al. (1966) reported the Away mean total diet titanium intakes of two individuals were 0.37 and 0.41 mg per day. The primary titanium exposures In industry are to the metal, the dioxide, and the chloride. There seems to be general agreement that titanium and its compounds are low In toxicity (Browning, 1969~. However, since the powders of titanium are pyrophor~c and its liquid form burns in air, several explosions have resulted from careless handling. Hydrolysis of titanium chloride will result in release of hydrochloric acid and a consequent hazard from exposure to that chemical. It has been proposed that air titanium concentrations be limited to 15 mg/m3 (Hamilton and Hardy, 1974~.

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512 MINERAL TOLERANCE OF DOMESTIC ANIMALS TOXICOSIS It is questionable whether a specific toxicity of titanium has been demonstrated. Ereaux (1955) stated that oral administration of large amounts of titanium salts in the diet of experimental animals had no adverse effect. Vernetti-Blina (1928) administered titanium oxide by mouth, by subcutaneous injection, and by inhalation in varying dosages over periods of 1 to 2 months. He concluded this compound was basic- ally inert and innocuous. Even inhalation of the dust for ~ hours a day for 30 days produced no significant clinical illness. At necropsy the peribronchial glands showed some hyperplasia, and the lungs had an increased amount of connective tissue in the stroma, with an exudate in the large and medium bronchi (evidence only of the irritating effect of the dust). Christie et al. (1963) exposed rats to titanium dioxide by inhalation for up to 13 months. There was little tissue reaction, but lung ash contained more than 10 percent titanium. Stokinger (1963) reported that inhalation exposure to high levels of titanium chloride produced severe respiratory distress, while lower levels (mean of 8.4 ppm) pro- duced silicosislike lesions. When Bloom and Swensson (1958) injected titanium dioxide intravenously, there was a decrease in circulating thrombocytes. Implantation of small titanium discs into the abdominal muscle of dogs for several months caused no irritation (Beder and Eade, 1956~. Titanium plates and screws have also been used in fixation of fractures in dogs and have proved inert (Beder et al., 1957; Gross and Gold, 1957). Ereaux (1955) has found topical application of titanium salicylate, peroxide, tannate, and oxides beneficial for skin disorders. Kato and Gozsy (1955) suggested that the therapeutic value of organic salts is due to their stimulation of phagocytic activity of capillary endothelial cells, thus increasing defense mechanisms of the skin without causing irrita- tion. Deribere (1941) found titanium oxides were harmless when used in cosmetics. Industrial exposure of humans to titanium dust is generally believed not to induce lung fibrosis (Vernetti-Blina, 1928; Lundgren and Ohman, 1954; Moschinski et al., 1959~. Inhalation of fumes of titanic acid and titanic oxychloride resulted in marked congestion of the mucous membranes of the pharynx, vocal cords, and trachea; followed by cicatrization and stenosis of the larynx, trachea, and upper bronchi (Heimendinger and Klotz, 1956~.

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Titanium TISSUE LEVELS 513 Tipton and Cook (1963) reported that most of the soft tissues of the adult human body contain 0.1 to 0.2 ppm titanium (on a wet basis). However, lungs averaged over 4 ppm, with some samples over 50 ppm. Hamilton et al. (1972/1973) found the following mean titanium concen- trations (parts per million, wet weight) in human tissues: muscle, 0.2; brain, 0.8; kidney cortex, 1.3; kidney medulla, 1.2; liver, 1.3; and lung, 3.7. Losee et al. (1973) also found considerable variability in titanium concentration of 29' samples of human dental enamel. Levels ranged from 0.1 to 4.8 ppm (dry basis), with a mean of 0.46. MAXIMUM TOLERABLE LEVEL No evidence of oral toxicosis has been found. SUMMARY Titanium is a dark, gray metal that is found in the earth's crust at a concentration of about 0.43 percent. It is used in alloys with aluminum, tin, and vanadium and as ferrotitanium in steel. Its compounds are useful as ingredient markers in comminuted meat, as pigments in paint, in the coating of welding rods, in glass and ceramics, in implantable surgical devices, and in electrodes and lamp filaments. Titanium has no known metabolic function in plants or animals, and the metal and its compounds appear to have low toxicity. Implantation of titanium metal during the surgical repair of tissues produces no tissue reaction, and for this reason (plus properties of lightness and tensile strength) titanium has found considerable application in medicine.

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1 S14 MINERAL TOLERANCE OF DOMESTIC ANIMALS REFERENCES Barlow, R. M., D. Purves, E. J. Butler, and I. J. McIntyre. 1960. Swayback in south-east Scotland. I. Field aspects. J. Comp. Pathol. Ther. 70:396. Beder, D. E., and G. Eade. 1956. Tissue tolerance to titanium metal implants in dogs. Surgery 39:470. Beder, D. E., J. K. Stevenson, and T. W. Jones. 1957. Further investigations of the surgical application of titanium metal in dogs. Surgery 41:1012. Bertrand, G., and C. Varonca-Spirt. 1929a. Le titane dans les plantes phanerogames. C. R. Hebd. Seances Acad. Sci. 188:1199. Bertrand, G., and C. Varonca-Spirt. 1929b. Le titane dans les plantes cryptogames. C. R. Hebd. Seances Acad. Sci. 189:73. Bloom, G., and A. Swensson. 1958. The reaction of thrombocytes to intravenously injected suspensions of submicroscopic particles. Acta Med. Scand. 162:423. Browning, E. 1969. Toxicity of Industrial Metals, 2nd ed. Butterworth & Co., London. 383 pp. Christie, H., R. J. MacKay, and A. M. Fisher. 1963. Pulmonary effects of inhalation of titanium dioxide by rats. Am. Ind. Hyg. Assoc. J. 24:42. Deribere, M. 1941. Les Composes du Titane et ['Hygiene. Ann. Hyg. Publ. 18:133. Ereaux, L. P. 1955. Clinical observations on the use of titanium salts in the treatment of dermatitis. Can. Med. Assoc. J. 73:47. Gross, P. P., and L. Gold. 1957. Compatibility of vitallium and austenium in completely buried implants in dogs. Oral Surg. 10:769. Hamilton, A., and H. L. Hardy. 1974. Industrial Toxicology, 3rd ed. Publishing Sciences Group, Inc., Acton, Mass. 575 pp. Hamilton, E. I., M. J. Minski, and J. J. Cleary. 1972/1973. The concentration and distribution of some stable elements in healthy human tissues from the United King- dom (an environmental study). Sci. Total Environ. 1:341. Heimendinger, E., and G. Klotz. 1956. Stenose laryago-tracheo-bronchique consecutive a une brulure par chlorure de titane. Arch. Otolaryng. 73:645. Kato, L., and B. Gozsy. 1955. Stimulation of the cell-linked defense forces of the skin. Can. Med. Assoc. J. 73:31. Lehmann, K. B., and L. Herget. 1927. Studien uber die hygienischen Eigenschaften des Titanoxyds und des Titanweiss. Chemiker-ztg. 82:793. Lloyd, L. E., B. E. Rutherford, and E. W. Crampton. 1955. Ti oxide and Cr oxide as index materials for determining apparent digestibility. J. Nutr. 56:265. Losee, F., T. W. Cutress, and R. Brown. 1973. Trace elements in human dental enamel. Trace Substances in Environmental Health—VII. University of Missouri, Columbia. Lundgren' K. D., and H. Ohman. 1954. Pneumokoniose in der Hartmetall-industrie. Virchows Arch. Pathol. Anat. 325:284. Mitchell, R. L. 1957. The trace element content of plants. Research (London) 10:357. Moschinski, G., A. Jurisch' and W. Reinl. 1959. Die Lungenversanderungen bei Sinter- hartmetall Arbeitern. Arch. Gewerbepath. Gewerbehyg. 16:697. Stokinger, H. E. 1963. The metals (excluding lead). ln F. A. Patty, ed. Industrial Hygiene and Toxicology, vol 2, 2nd ed. John Wiley ~ Sons, New York. Swaine, D. 1. 1955. The Trace Element Content of Soils. Commonw. Burl Soils Tech. Commun. No. 48. Tipton, I. H., and M. J. Cook. 1963. Trace elements in human tissue. Part II. Adult subjects from the United States. Health Phys. 9:103. Tipton, I. H., P. L. Stewart, and P. G. Martin. 1966. Trace elements in diet and excrete. Health Phys. 12:1683. Vernetti-Blina, L. 1928. Ricerche clinica e sperimentale sull' Assido di Titanio. Riform. med. 47:1516.

Representative terms from entire chapter:

titanium oxide