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78-30-8

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78-30-8 Usage

Description

TRI-O-CRESYL PHOSPHATE (TOCP) is an organophosphate compound that has a wide range of applications across various industries due to its versatile properties, such as its ability to act as a plasticizer, flame retardant, and synthetic lubricant.

Uses

Used in the Paint and Coating Industry:
TRI-O-CRESYL PHOSPHATE is used as a plasticizer in lacquers and varnishes, enhancing their flexibility and durability.
Used in the Plastics Industry:
TRI-O-CRESYL PHOSPHATE is used as a plasticizer to increase the flexibility and workability of plastics, making them easier to process and use in various applications.
Used in the Textile Industry:
TRI-O-CRESYL PHOSPHATE is used as a waterproofing agent, providing water-resistant properties to fabrics and improving their performance in outdoor and wet conditions.
Used in the Automotive Industry:
TRI-O-CRESYL PHOSPHATE is used as a gasoline additive to control preignition, ensuring a smoother and more efficient combustion process in engines.
Used in the Lubricant Industry:
TRI-O-CRESYL PHOSPHATE is used as a synthetic lubricant, providing reduced friction and wear in various mechanical systems.
Used in the Chemical Industry:
TRI-O-CRESYL PHOSPHATE is used as an extreme pressure additive, enhancing the performance of lubricants under high stress conditions.
Used in the Pharmaceutical Industry:
TRI-O-CRESYL PHOSPHATE is used as an intermediate in pharmaceutical manufacturing, contributing to the production of various drugs and medications.
Used in the Construction Industry:
TRI-O-CRESYL PHOSPHATE is used as a heat exchange medium, facilitating the transfer of heat in various systems and processes.
Used in the Petroleum Industry:
TRI-O-CRESYL PHOSPHATE is used as a lead scavenger in gasoline, helping to reduce the harmful effects of lead on engines and the environment.

Production Methods

Prepared from cresol and phosphorus oxychloride, phosphoric acid, or phosphorus pentachloride. The grades of cresol commonly used are the isomeric (o-, m-, /p-), and meta-para mixtures from coal tar and cresylic acid from petroleum. Purification of the product is based on the intended use; the commercial product is generally obtained as a mixture. A 'refined grade' of tricresyl phosphate is prepared by vacuum distillation, or alternatively by washing with 2% NaOH and water (Lowenheim and Moran 1975).

Hazard

Toxic by ingestion and skin absorption. The oisomer is highly toxic. TLV: 0.1 mg/m3 (skin); not classifiable as a Human Carcinogen.

Health Hazard

Non-industrial: During the prohibition era in the United States in the 1920s and 1930s, Jamaican ginger extract was used as an additive to beverages for popular consumption. An outbreak of polyneuritis, an estimated 20,000 to 30,000 cases, led to the discovery that the ginger extract, used because of its alcohol content, was contaminated with TOCP, leading to the polyneuritis. This syndrome thus came to be known as 'jake', 'ginger jake', and 'jake leg' (Baron 1981; Morgan 1982). The discovery of the polyneuritis associated with tri-o-cresyl phosphate led to much research on this compound (Lillie and Smith 1932; Smith and Elvove 1930; Smith and Lillie 1931; Smith et al 1930, 1932) and related materials, particularly the organophosphorus insecticides, in which polyneuritis was associated with a delayed neuropathy characterized by degeneration of axons with subsequent secondary degeneration of myelin (Abou-Donia 1981). Man may very well be the most sensitive species. The best known and most studied incidences of poisoning by TOCP, therefore, are associated with the contamination of Jamaican ginger extract with 0.5 to 3% tri-o-cresyl phosphate during the 1930s in the United States (Abou-Donia 1981; Baron 1981; Calabrese 1971; Morgan 1982; Morgan and Penovich 1978). However, other cases of poisoning have been reported in connection with the use of contaminated cooking oil in Japan (Yuasa et al 1970) and Morocco (Smith and Spalding 1959), gingili oil in Sri Lanka (Senanayake and Jeyaratnam 1981), and in other situations as summarized by Morgan (1982). Industrial: Cases of poisoning associated with the use of TOCP have been reported in workers in the shoe industries of Italy (Capellini et al 1968; Cosi et al 1973; Desantis 1979; Faggi et al 1971) and Spain (Bermejillo 1971a,b). The glues and adhesives used, apparently contaminated with TOCP, are associated with symptoms characteristic of TOCP poisoning. However, Morgan (1981) suggests caution in assigning causation in such situations because of the possibility of the presence of other chemicals which may cause similar symptomology.

Health Hazard

TOCP is a highly poisonous compound. Its toxicity is greater than that of the meta- or para-isomer. The toxic routes are inhalation, ingestion, and absorption through the skin; and the symptoms varied with the species and the route of admission. Ingestion of 40–60 mL of the liquid can be fatal to humans. An oral dose of 6–7 mg/kg has produced serious paralysis in humans (Patty 1949). The toxic symptoms from oral intake can be gastrointestinal pain, diarrhea, weakness, muscle pain, kidney damage, and paralysis. The target organs are the gastrointestinal tract, kidney, central nervous system, and neuromuscular system.LD50 value, oral (rabbits): 100 mg/kgSomkuti et al. (1987) reported testicular toxicity of TOCP in adult leghorn roosters. Birds dosed with 100 mg/kg/day exhibited limb paralysis in 7–10 days. Such symptoms are characteristics of delayed neurotoxicity caused by organophosphorus compounds. Analysis at the termination of 18 days indicated a significant inhibition of neurotoxic esterase activity in both brain and testes, and a decrease in sperm motility and brain acetylcholinesterase activity. TOCP caused adverse reproductive effects in mice, such as increased maternal mortality and a decreased number of viable litters. An LD50 value of 515 mg/kg/day is reported (Environmental Health Research and Testing 1987)..

Fire Hazard

Noncumbustible solid; vapor pressure 0.02 torr at 150°C (302°F); fire retardant.

Safety Profile

Poison by subcutaneous, intramuscular, intravenous, and intraperitoneal routes. Moderately toxic by ingestion. Most of the cases of tri-o-cresyl phosphate poisoning have followed its ingestion. In 1930, some 15,000 persons were affected in the United States, and of these, 10 died. The responsible material was found to be an alcoholic drink known as Jamaica ginger, or "jake." This beverage had been adulterated with about 2% of tri-o-cresyl phosphate. The affected persons developed a polyneuritis, which progressed, in many cases, with degeneration of the peripheral motor nerves, the anterior horn cells, and the pyramidal tracts. Sensory changes were absent. Since 1930 there have been several other outbreaks of poisoning following ingestion of the material. Tri-ocresyl phosphate is more toxic than the mform, and much more so than tri-p-cresyl phosphate or triphenyl phosphate. Experimental reproductive effects. flame. Can react with oxidizing materials. To fight fire, use CO2, dry chemical. When heated to decomposition it emits highly toxic fumes of POx. See also PHOSPHATES. Combustible when exposed to heat or

Potential Exposure

Tricresyl phosphate is used as an additive in hydraulic fluids; as a plasticizer; pigment dispersant; flame retardant; as a plasticizer for chlorinated rubber; vinyl plastics; polystyrene, polyacrylic, and polymethacrylic esters; as an adjuvant in milling of pigment pastes; as a solvent and as a binder in nitrocellulose and various natural resins, and as an additive to synthetic lubricants and gasoline. It is also used in the recovery of phenol in coke-oven wastewaters.

Environmental fate

Biological. A commercial mixture containing tricresyl phosphates was completely degraded by indigenous microbes in Mississippi River water to carbon dioxide. After 4 wk, 82.1% of the theoretical carbon dioxide had evolved (Saeger et al., 1979). Chemical/Physical. Tri-o-cresyl phosphate hydrolyzed rapidly in Lake Ontario water, presumably to di-o-cresyl phosphate (Howard and Doe, 1979). When an aqueous solution containing a mixture of isomers (0.1 mg/L) and chlorine (3 to 1,000 mg/L) was stirred in the dark at 20 °C for 24 h, the benzene ring was substituted with one to three chlorine atoms (Ishikawa and Baba, 1988). Decomposes at temperatures greater than 424 °C (Dobry and Keller, 1957).

Metabolism

The skin penetrating ability of a series of phosphorus esters, including tri-o-cresyl phosphate, was studied by Marzulli et al (1965). They found a relationship between the solubility of the compounds studied in benzene and water, the molecular weight, and the volatility and their skin-penetrating capacity. Tri-ocresyl phosphate was one of the least penetrating of the compounds studied in a series of related phosphorus esters. However, Ahmed and Glees (1971) showed that the application of 0.2 cm3/kg body weight of tricresyl phosphate daily for 10 d on the skin of the neck of simian primates produced general symptoms of intoxication. This observation has been confirmed in mice (Litau 1975). Following dermal application of tri-o-cresyl phosphate to a preclipped area on the back of the neck of male cats (Nomeir and Abou-Donia 1984), the compound reached its maximum concentration in plasma at 12 h, while its metabolites reached their maximum concentrations between 24 and 48 h. The subsequent disappearance of TOCP from the plasma followed monoexponential kinetics with a half-life of 1.2 d. Di-o-cresyl phosphate and o-cresyl phosphate were the major metabolites in the plasma, while dihydroxymethyl TOCP was present in trace amounts. Appreciable amounts of saligenin cyclic-o-tolyl phosphate were detected in the plasma at all time points. TOCP was the predominant compound in the brain, spinal cord, and sciatic nerve, while the liver, kidneys, and lungs contained mostly metabolites. The major metabolite identified in these tissues was ohydroxybenzoic acid, followed by di-o-cresyl phosphate. Di-o-cresyl phosphate and o-cresyl phosphate were the predominant metabolites in the brain, spinal cord, and sciatic nerve. Other metabolites identified in the tissues were ocresol, dihydroxymethyl TOCP, as well as the stepwise oxidation products of the methyl group of o-cresol. In chickens, after oral administration of radiolabeled tri-o-cresyl phosphate (Sharma and Watanabe 1974; Watanabe and Sharma 1973), nerve tissues accumulated the compound over a period of two weeks. Other tissues examined showed an increase over a period of 3-7 d, followed by a decline. During that period the principal metabolite, 2-(2-methylphenoxy)-4H-l,3,2-benzodioxaphosphorin- 2-oxide (CBDP), represented 71 and 74% of the total in the liver at 12 and 24 h. The concentration of TOCP and metabolites in the plasma at 24 h was only about 5% that of the liver. These workers suggest that CBDP is bound to tissues to a greater extent than TOCP, since low concentrations of the metabolite were found in plasma; TOCP was the major circulating compound. However, the total recovery of the administered radiolabeled compound over the first 3 d was relatively low, emphasizing the extended period of time this chemical remains in the body. Only 26.5% of the administered dose was excreted in 3 d. Eto (1969) has reviewed the pathways of metabolism of tri-o-cresyl phosphate.

Shipping

UN2574 Tricresyl phosphate with >3% ortho (o-) isomer, Hazard Class: 6.1; Labels: 6.1-Poisonous materials.

Incompatibilities

Incompatible with oxidizers (chlorates, nitrates, peroxides, permanganates, perchlorates, chlorine, bromine, fluorine, etc.); contact may cause fires or explosions. Keep away from alkaline materials, strong bases, strong acids, oxoacids, epoxides. Contact with magnesium may cause explosion. Organophosphates, such as tricresyl phosphate, are susceptible to formation of highly toxic and flammable phosphine gas in the presence of strong reducing agents such as hydrideds and active metals. Partial oxidation by oxidizing agents may result in the release of toxic phosphorus oxides.

Waste Disposal

TOCP is dissolved in a combustible solvent and burned in a chemical incinerator equipped with an afterburner and scrubber.

Check Digit Verification of cas no

The CAS Registry Mumber 78-30-8 includes 5 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 2 digits, 7 and 8 respectively; the second part has 2 digits, 3 and 0 respectively.
Calculate Digit Verification of CAS Registry Number 78-30:
(4*7)+(3*8)+(2*3)+(1*0)=58
58 % 10 = 8
So 78-30-8 is a valid CAS Registry Number.
InChI:InChI=1/C21H21O4P/c1-16-10-4-7-13-19(16)23-26(22,24-20-14-8-5-11-17(20)2)25-21-15-9-6-12-18(21)3/h4-15H,1-3H3

78-30-8 Well-known Company Product Price

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  • (51885)  Tri-o-tolyl phosphate  analytical standard

  • 78-30-8

  • 51885-250MG

  • 600.21CNY

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78-30-8SDS

SAFETY DATA SHEETS

According to Globally Harmonized System of Classification and Labelling of Chemicals (GHS) - Sixth revised edition

Version: 1.0

Creation Date: Aug 12, 2017

Revision Date: Aug 12, 2017

1.Identification

1.1 GHS Product identifier

Product name Tri-o-tolyl phosphate

1.2 Other means of identification

Product number -
Other names tris(2-methylphenyl) phosphate

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only.
Uses advised against no data available

1.4 Supplier's details

1.5 Emergency phone number

Emergency phone number -
Service hours Monday to Friday, 9am-5pm (Standard time zone: UTC/GMT +8 hours).

More Details:78-30-8 SDS

78-30-8Relevant articles and documents

Method for preparing phosphate ester derivatives from white phosphorus

-

Paragraph 0062-0064, (2021/06/23)

A method for preparing phosphate ester derivatives from white phosphorus relates to the field of chemical engineering, and comprises the following steps: adding alkali, a catalyst, a white phosphorus solution, ROH or RSH (R represents alkyl or aromatic group) into a reaction container in an inert atmosphere, and heating and stirring the mixture in a mixed solvent of toluene and DMSO (dimethyl sulfoxide) to react for a certain time, so as to obtain three-coordinated phosphate ester derivatives; and 2) continuing to add H2O2, air or sulfur powder until the oxidation is completed, thereby obtaining the tetra-coordinated phosphate ester derivative. According to the method, chlorine, phosphorus trichloride and halogen are not needed, phosphite ester is directly prepared from elementary white phosphorus in an efficient, green and environment-friendly manner, and phosphate and thiophosphate can be directly prepared after oxidation. High pollution and high corrosivity of a traditional method are avoided in the whole process; meanwhile, white phosphorus is completely converted in the whole process, white phosphorus residues are avoided, and the post-reaction treatment process is safe.

Aerobic Oxidation of Phosphite Esters to Phosphate Esters by Using an Ionic-Liquid-Supported Organotelluride Reusable Catalyst

Mihoya, Aya,Shibuya, Yuga,Ito, Akane,Toyoda, Anna,Oba, Makoto,Koguchi, Shinichi

supporting information, p. 2043 - 2045 (2020/11/10)

We describe the synthesis of an ionic-liquid (IL)-supported organotelluride catalyst and its application as a recyclable catalyst for the aerobic oxidation of phosphite esters to phosphate esters. This method shows high conversion rates, allows the ready isolation and purification of the resulting products, and exhibits good reusability of the catalyst.

Nickel-catalyzed amination of aryl phosphates through cleaving aryl C-O bonds

Huang, Jin-Hua,Yang, Lian-Ming

supporting information; experimental part, p. 3750 - 3753 (2011/09/14)

The amination of triaryl phosphates was achieved using a Ni(II)-(σ-Aryl) complex/NHC catalyst system in dioxane at 110 °C in the presence of NaH as base. Electron-neutral, -rich, and -deficient triaryl phosphates were coupled with a wider range of amine partners including cyclic and acyclic secondary amines, aliphatic primary amines, and anilines in good to excellent yields.

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