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HCID 8289생성일: 2026년 10월 27일

트리페닐포스페이트

인산트리페닐 · 트리페닐포스페이트 · 인산,트리페닐에스테르 · 트리페녹시포스핀산화물 · 셀루플렉스TPP · 디스플 · 트라이페닐포스페이트 · 트라이페닐 포스페이트

https://huagongshe.com/ko/chemical/8289

트리페닐포스페이트 분자 구조식

식별자 및 물리적 특성

CAS No.115-86-6
분자식C18H15O4P
평균 분자량326.3 g/mol
단동위원소 질량326.07079559 g/mol
SMILESO=P(Oc1ccccc1)(Oc1ccccc1)Oc1ccccc1
InChIKeyXZZNDPSIHUTMOC-UHFFFAOYSA-N
PubChem CID8289
ChEMBLCHEMBL454511
ChEBICHEBI:35033
EC No.204-112-2
DTXSIDDTXSID1021952
현지명트리페닐포스페이트

화학 및 물리적 성질

XLogP4.6
극성 표면적44.8
수소 결합 공여자 수0
수소 결합 수용자 수4
회전 가능 결합 수6
무거운 원자 수23
형식 전하0
복잡도325
물질 분류Other Classes -> Organophosphates, OtherWaste-water effluent contaminant
PolymersPlastics -> ABSPlastics -> Other functions -> Flame retardantPlastics -> Plasticisers
화장품Cosmetic ingredients (Triphenyl Phosphate) -> CIR (Cosmetic Ingredient Review)
SpringerMaterials Properties13C nuclear magnetic resonance spectrum
LogP(분배 계수)log Kow = 4.593.9
냄새OdorlessPhenol-like odor냄새 없는
PlasticizersPlasticizer
밀도1.2055 (NTP, 1992) - Denser than waterwill sinkDensity: 1.2055 g/cu cm at 50 °CBulk density: 10.5 lb/galRelative density (water = 1): 1.271.268 @ 60°C
Flame RetardantsFlame retardantsFlame Retardants -> Organophosphorus flame retardant (OP)
Color/FormCrystals from ligroinprisms from alcoholneedles from diethyl etherColorless, crystalline powder
용해도Insoluble (NTP, 1992)In water, 1.9 mg/L at 25 °CInsoluble in waterSoluble in ethanolvery soluble in ether, benzene, carbon tetrachloride, chloroformSoluble in benzene, chloroform, ether, acetonemoderately soluble in alcoholFor more Solubility (Complete) data for Triphenyl phosphate (7 total), please visit the HSDB record page.H2O: 20°C에서 용해성0.0019g/L
인화점428 °F (NTP, 1992)220 °C428 °F (220 °C) (Closed cup)220 °C c.c.435 °F
녹는점48-50 °C (lit.)
끓는 점244 °C/10 mmHg (lit.)
증기 밀도11.3 (vs air)
증기압1.3 mm Hg ( 200 °C)
굴절률1.563
저장 조건Store below +30°C.
물리적 상태플레이크 크리스탈
색상하얀색
용해도불용성
비열Cp(crystal): 1.09 J/(g·K), at 25℃
Merck14,9742
BRN1888236
헨리 상수5.88 at 20 °C (approximate - calculated from water solubility and vapor pressure)
안정성안정적인.
화장품 원료 기능가소제
InChI1S/C18H15O4P/c19-23(20-16-10-4-1-5-11-16,21-17-12-6-2-7-13-17)22-18-14-8-3-9-15-18/h1-15H
InChIKeyXZZNDPSIHUTMOC-UHFFFAOYSA-N
SMILESO=P(Oc1ccccc1)(Oc2ccccc2)Oc3ccccc3
LogP(분배 계수)4.6 at 20℃
NISTTriphenylphosphate(115-86-6)
EPATriphenyl phosphate (115-86-6)

화학적 성질

Triphenyl phosphate (TPP) is a colorless crystalline powder with a faint, phenol-like odor. Triphenyl phosphate is practically insoluble in water at 1.9 × 10 7 mg/l at 24 °C (Yalkowsky et al., 2010). It is very soluble in carbon tetrachloride (Haynes, 2010) and is soluble in most lacquers, solvents, thinners, and oils, as well as in alcohol, benzene, ether, chloroform, and acetone (Lewis, 1996). It begins to decompose at about 600 °C in inert gas, and in a large excess of air, complete combustion to carbon dioxide occurs in the range 800–900 °C (Lhomme et al., 1984). Hydrolysis of TPP occurs very slowly in acidic or neutral solutions, but occurs rapidly in alkaline solutions (Barnard et al., 1966).

안전 및 규제

GHS 분류This chemical does not meet GHS hazard criteria for 0.6% (9 of 1488) of reports.WarningH400 (83.4%): Very toxic to aquatic life [Warning Hazardous to the aquatic environment, acute hazard]P273, P391, and P501 (click each P-code to see the statement)Aggregated GHS information provided per 1488 reports by companies from 25 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies.
규제 정보Chemical: Phosphoric acid, triphenyl esterHazard Traits - Endocrine ToxicityNeurotoxicityReproductive ToxicityPhosphoric acid, triphenyl ester is listed on the EPA's Chemical Data Reporting (CDR) system. Manufacturers and importers of Phosphoric acid, triphenyl ester are required to report information about their production and use of this chemical to the EPA under the Toxic Substances Control Act (TSCA). (40 eCFR Part 711)T - indicates a substance that is the subject of a final TSCA section 4 test rule.Status: Active Update: 21-07-2022 https://echa.europa.eu/registration-dossier/-/registered-dossier/15972Substance: Triphenyl phosphate
기타 안전 정보Evaluation - Triphenyl phosphate and diphenyl phosphate
화재 위험Combustible.
화재 가능성Combustible when exposed to heat or flame.
건강 유해성Excerpt from NIOSH Pocket Guide for Triphenyl phosphate:
유해성 요약Cholinesterase inhibition, but no cumulative toxicity, was observed in animal studies. A study of 33 workers (employed for an average of 7.4 years) in a plant manufacturing TPP found no adverse health effects. A slight reduction in erythrocyte cholinesterase activity was found in six workers. One case of occupational allergic contact dermatitis has been documented. [ACGIH] In high-dose animal studies, adverse effects include delayed paralysis similar to that seen with tri-o-cresyl phosphate. [HSDB]
FDA 요건Triphenylphosphate is an indirect food additive for use only as a component of adhesives.
반응성 그룹Esters, Sulfate Esters, Phosphate Esters, Thiophosphate Esters, and Borate Esters

용도

용도

Triphenyl phosphate is known as a product with manifold fields of applications regarding its qualities in particular as a flame retardant. One primary use is as a flame retardant in phenolic- and phenylene oxide-based resins for the manufacture of electrical and automobile components, for auto upholstery, and as a nonflammable plasticizer in cellulose acetate for photographic films. It has also been used to impregnate roofing paper. Triphenyl phosphate occurs as a plasticizer in various lacquers and varnishes (O'Neil, 2006), and as a component of lubricating oil and hydraulic fluids (ACGIH, 2012).

제조 및 합성 방법

제조 방법

Triphenyl phosphate is prepared by reacting phosphorus pentoxide and phenol (Budavari, 2001), or by reacting phosphorus oxychloride and phenol (Snyder, 1990). On a larger scale phosphorus oxychloride and phenol are reacted in an esterification tank with heating. The HCL formed is trapped and condensed, while the crude triphenyl phosphate runs into a large tank where it is purified.

TSCA 요건Pursuant to section 8(d) of TSCA, EPA promulgated a model Health and Safety Data Reporting Rule. The section 8(d) model rule requires manufacturers, importers, and processors of listed chemical substances and mixtures to submit to EPA copies and lists of unpublished health and safety studies. Phosphoric acid, triphenyl ester is included on this list. Effective date: 10/4/82Sunset date: 10/4/92.
OSHA StandardsPermissible Exposure Limit: Table Z-1 8-hr Time Weighted Avg: 3 mg/cu m.
Reactivity ProfileOrganophosphates, such as TRIPHENYL PHOSPHATE, are susceptible to formation of highly toxic and flammable phosphine gas in the presence of strong reducing agents such as hydrides. Partial oxidation by oxidizing agents may result in the release of toxic phosphorus oxides.
Chemical DangersDecomposes on heating. This produces toxic fumes.
소화This compound is not very flammable but any fire involving this compound may produce dangerous vapors. You should evacuate the area. All firefighters should wear full-body protective clothing and use self-contained breathing apparatuses. You should extinguish any fires involving this chemical with a dry chemical, carbon dioxide, foam, or halon extinguisher. (NTP, 1992)Use water spray, powder, foam, carbon dioxide.
응급 조치Fresh air, rest. Refer for medical attention.Remove contaminated clothes. Rinse and then wash skin with water and soap.First rinse with plenty of water for several minutes (remove contact lenses if easily possible), then refer for medical attention.Rinse mouth. Refer for medical attention .
응급 처치EYES: First check the victim for contact lenses and remove if present. Flush victim's eyes with water or normal saline solution for 20 to 30 minutes while simultaneously calling a hospital or poison control center. Do not put any ointments, oils, or medication in the victim's eyes without specific instructions from a physician. IMMEDIATELY transport the victim after flushing eyes to a hospital even if no symptoms (such as redness or irritation) develop.(General first aid procedures)
안전 보관Store in an area without drain or sewer access. Provision to contain effluent from fire extinguishing.
Firefighting HazardsHazardous decomposition products formed under fire conditions: Carbon oxides, Oxides of phosphorus.
노출 관리 및 개인 보호10.0 [mg/m3], inhalable fraction[German Research Foundation (DFG)]
소화 절차Suitable extinguishing media: Use water spray, alcohol-resistant foam, dry chemical or carbon dioxide.Advice for firefighters: Wear self contained breathing apparatus for fire fighting if necessary.
보관 조건Keep container tightly closed in a dry and well-ventilated place.Store in an area without drain or sewer access. Provision to contain effluent from fire extinguishing.
정리 방법ACCIDENTAL RELEASE MEASURES: Personal precautions, protective equipment and emergency procedures: Avoid dust formation. Avoid breathing vapors, mist or gas. Ensure adequate ventilation. Environmental precautions: Prevent further leakage or spillage if safe to do so. Do not let product enter drains. Discharge into the environment must be avoided. Methods and materials for containment and cleaning up: Pick up and arrange disposal without creating dust. Sweep up and shovel. Keep in suitable, closed containers for disposal.Sweep spilled substance into covered containers. If appropriate, moisten first to prevent dusting. Carefully collect remainder. Then store and dispose of according to local regulations. Personal protection: particulate filter respirator adapted to the airborne concentration of the substance. Do NOT let this chemical enter the environment.If triphenyl phosphate is spilled ... : ventilate area of spill. For small quantities, sweep onto paper or other suitable material, place in appropriate container and burn in a safe place (such as a fume hood). Large quantities may be reclaimedhowever, if this is not practical, dissolve in a flammable solvent (such as alcohol) and atomize in a suitable combustion chamber equipped with an appropriate effluent gas cleaning device.
비화재 누출 대응SMALL SPILLS AND LEAKAGE: Should a spill occur while you are handling this chemical, you should dampen the solid spill material with alcohol, then transfer the dampened material to a suitable container. Use absorbent paper dampened with alcohol to pick up any remaining material. Seal the absorbent paper, and any of your clothes, which may be contaminated, in a vapor-tight plastic bag for eventual disposal. Solvent wash all contaminated surfaces with alcohol followed by washing with a strong soap and water solution. Do not reenter the contaminate area until the Safety Officer (or other responsible person) has verified that the area has been properly cleaned.
처리 방법SRP: Recycle any unused portion of the material for its approved use or return it to the manufacturer or supplier. Ultimate disposal of the chemical must consider: the material's impact on air qualitypotential migration in air, soil or watereffects on animal, aquatic and plant lifeand conformance with environmental and public health regulations. If it is possible or reasonable use an alternative chemical product with less inherent propensity for occupational harm/injury/toxicity or environmental contamination.Product: Product: Offer surplus and non-recyclable solutions to a licensed disposal company. Contaminated packaging: Dispose of as unused product.1. By making packages of triphenyl phosphate in paper or other flammable material and burning in a suitable combustion chamber... with an appropriate effluent gas cleaning device. 2. By dissolving... in a flammable solvent... and atomizing in a suitable combustion chamber... with an... effluent gas cleaning device.
누출 처리Personal protection: particulate filter respirator adapted to the airborne concentration of the substance. Do NOT let this chemical enter the environment. Sweep spilled substance into covered containers. If appropriate, moisten first to prevent dusting. Carefully collect remainder. Then store and dispose of according to local regulations.
체내 부담Concentration of triphenyl phosphate at five work environments in Kuopio, Finland(1).Concentration of triphenyl phosphate at two work environments in Kuopio, Finland(1).Triphenyl phosphate concentrations were reported in hair, fingernail, toenail and blood samples in 50 individuals from Indiana University's Bloomingdale campus, sampled in July-August, 2014, the compound was not detected in blood samples.(1).During a study of the level of triaryl/alkyl phosphates in human adipose tissue, no conclusions for triphenyl phosphate were drawn because trace levels of triphenyl phosphate were identified in the method blankshowever, triphenyl phosphate was detected in two human adipose tissue samples (13.6 and 11.2 ng/g) at levels significantly above the method blanks(1). Triphenyl phosphate concentrations were hair, fingernail, toenail and blood samples, respectively, in 50 individuals from Indiana University's Bloomingdale campus, sampled in July-August, 2014(2).
상호 작용A series of symmetrical trisubstituted phosphorus esters was tested as synergists for malathion and other organophosphorus insecticides against resistant and normal strains of Chrysomya putoria and Musca domestica. Triphenyl phosphate synergized the insecticides more effectively against insecticide-resistant than normal insect strains.
표적 장기Blood, peripheral nervous system
생태독성 수치LC50Species: Menidia beryllina /(Inland silverside)/Conditions: static bioassayConcentration: 95 mg/L for 96 hrSpecies: Carassius auratus (Goldfish) weight 0.8-2.8 gConcentration: 0.70 mg/L for 96 hrSpecies: Ictalurus punctatus (Channel catfish) weight 0.23 gConditions: static bioassay, 22 °C, pH 7.5, hardness 38 mg/LConcentration: 0.42 mg/L for 96 hrSpecies: Gammarus pseudolimnaeus (Scud) age 60-90 day mid-instar larvaeConditions: freshwater, static, 17 °CConcentration: 250 ug/L for 96 hr (95% confidence interval: 160-390 ug/L) /99% purity formulation/For more Ecotoxicity Values (Complete) data for Triphenyl phosphate (24 total), please visit the HSDB record page.
환경 거동TERRESTRIAL FATE: Based on a classification scheme(1), a Koc range of 2,514 to 3,561(2) indicates that triphenyl phosphate is expected to have slight mobility in soil(SRC). Volatilization of triphenyl phosphate from moist soil surfaces is expected to be an important fate process(SRC) given an estimated Henry's Law constant of 3.3X10-6 atm-cu m/mole(SRC), based upon its vapor pressure, 2.00X10-6 mm Hg(3), and water solubility, 1.9 mg/L(4). However, adsorption to soil is expected to attenuate volatilization(SRC). Triphenyl phosphate is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(3). Mineralization half-lives of 37 and 32 days under aerobic and anaerobic conditions, respectively, using a loamy sand(2) suggest that biodegradation may be an important environmental fate process in soil(SRC).AQUATIC FATE: Based on a classification scheme(1), a Koc range of 2,514 to 3,561(2) indicates that triphenyl phosphate is expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(3) based upon an estimated Henry's Law constant of 3.3X10-6 atm-cu m/mole(SRC), derived from its vapor pressure, 2.00X10-6 mm Hg(4), and water solubility, 1.9 mg/L(5). Estimated volatilization half-lives for a model river and model lake are 20 and 152 days, respectively. However, volatilization from water surfaces is expected to be attenuated by adsorption to suspended solids and sediment in the water column. The estimated volatilization half-life from a model pond is 400 days if adsorption is considered(6). According to a classification scheme(7), bioconcentration factors ranging from 132(8) to 573(9) suggest that bioconcentration in aquatic organisms is high(SRC). Biodegradation half-lives of 2-4 days in river die-away tests(10) suggest that biodegradation may be an important environmental fate process in water(SRC).ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), triphenyl phosphate, which has a vapor pressure of 2.00X10-6 mm Hg at 25 °C(2), will exist in both the vapor and particulate phases in the ambient atmosphere. Vapor-phase triphenyl phosphate is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC)the half-life for this reaction in air is estimated to be 12 hours(SRC), calculated from its rate constant of 1.1X10-11 cu cm/molecule-sec at 25 °C(SRC) that was derived using a structure estimation method(3). Particulate-phase triphenyl phosphate may be removed from the air by wet and dry deposition(SRC). Triphenyl phosphate does not absorb light at wavelengths >290 nm(4) and, therefore, is not expected to be susceptible to direct photolysis by sunlight(SRC).
식품 조사 수치Triphenyl phosphate has been detected in a composite grain product sample (flours, breads, and cereals)however, this food sample may have been contaminated during analysis through laboratory reagents that contain triphenyl phosphate(1). Triphenyl phosphate was detected in 8 out of 230 ready to eat foods in the US at an average concentration of 0.2803 ug/g(2). The compound was tested for but not detected in 228 fresh potato samples sold at 34 farm markets in Alberta, Canada(3).
유해 작용Neurotoxin - Predominantly motor
노출 경로The substance can be absorbed into the body by inhalation.inhalation, ingestion
독성 요약Safe in the present practices of use and concentration. Ingredient, concentration, and use information are available in documents discoverable at https://cir-reports.cir-safety.orgIDENTIFICATION AND USE: Triphenyl phosphate (TPP) is a solid. It is used as fire-retarding agent, and a plasticizer for cellulose acetate and nitrocellulose. Triphenyl phosphate also has been found as one component of lubricating oil and hydraulic fluids. HUMAN STUDIES: It causes a delayed peripheral neuritis involving motor neurons, resulting in a flaccid paralysis, particularly of the distal muscles. No sensory disturbances. Potential symptoms of overexposure are minor changes in blood enzymes. In workers engaged in the manufacture of TPP there was some inhibition of plasma cholinesterase but no correlation of this effect with degree of exposure or with minor gastrointestinal or neuromuscular symptoms. A case of TPP allergy from spectacle frames was reported. TPP increased both 17beta-estradiol (E2) and testosterone concentrations in human H295R cells in vitro. In addition, transcription of four major steroidogenic genes was up-regulated and that of two sulfotransferase genes was down-regulated. Increase of TPP concentration in house dust was associated with a 10% increase in prolactin and a 19% decrease in sperm concentration in exposed men. ANIMAL STUDIES: Topical application of TPP to rats and mice caused no skin irritation. Because cholinesterase was not inhibited after topical application of TPP, it was concluded that percutaneous absorption was limited. TPP caused generalized delayed illness and paralysis in cats and primates. Administration of 0.2 g/kg of TPP s.c. caused paralysis in cats and fatal doses ranged between 0.3-1.0 g/kg. In mice choline esterase activity was reduced after doses of 10 to 500 mg/kg bw to 87.1 to 30.4% of control. No cholinergic or other symptoms were reported. TPP acted in vitro as antagonist of estrogen receptor inhibiting binding of E2 to estrogen receptor. Zebrafish retinoic acid receptor (RAR) may be involved in mediating TPP-induced developmental toxicity. Perinatal exposure to TPP exacerbates the development of obesity in male and female rats. TPP mutagenicity was negative at doses of 0, 100, 333, 1000, 3333, and 10,000 ug/plate in four Salmonella typhimurium strains (TA98, TA100, TA1535, and TA1537) in the presence and absence of metabolic activation. In vitro TPP was found to cause significant direct inhibition of monocyte antigen presentation at non-cytotoxic concentrations as low as 1 umol/L. ECOTOXICITY STUDIES: Vertebral damage and spinal curvature were observed in rainbow trout exposed to TPP for 96 hr. The growth of green algae was completely inhibited at concentrations of 1 mg/L or more but stimulated at lower concentrations (0.1 and 0.05 mg/L). TPP could increase the thyroid hormone concentrations in the early life stages of zebrafish by disrupting the central regulation and hormone synthesis pathways.
Average Daily IntakeThe average daily intake (AVDI) of triphenyl phosphate in 8 population groups in 1982-1984 was determined according to the FDA's monitoring program for chemical contaminants in the U.S. food supply (Total Diet Study or Market Basket Study). In 6-11 month old infants, the AVDI was 0.3 ng/kg-body weight-per day. In 2 yr old toddlers, the AVDI was 4.4 ng/kg-body weight-per day. In 14-16 year old females, the AVDI was 1.6 ng/kg-body weight-per day. In 14-16 year old males, the AVDI was 1.2 ng/kg-body weight-per day. In 25-30 year old females, the AVDI was 0.8 ng/kg-body weight-per day. In 25-30 year old males, the AVDI was 1.6 ng/kg-body weight-per day. In 60-65 year old females, the AVDI was 0.5 ng/kg-body weight-per day. In 60-65 year old males, the AVDI was 0.5 ng/kg-body weight-per day(1).
생태독성 발췌/AQUATIC SPECIES/ 1 ppm ... in water caused death of all six exposed goldfish within 8 hr. At concentration of 3 ppm or 5 ppm, all fish died within 5 hr and 1 hr, respectively. /Histological changes similar to mice and rats TPP poisoning/ congestion, degeneration, and hemorrhage from smaller blood vessels, pronounced mostly in liver, kidney, and brain./AQUATIC SPECIES/ Vertebral damage and spinal curvature were observed in rainbow trout exposed to triphenyl phosphate for 96 hr./AQUATIC SPECIES/ ...The growth of green algae was completely inhibited at concentrations of 1 mg/L or more but stimulated at lower concentrations (0.1 and 0.05 mg/L). The nitrogenase activity, measured by the acetylene reduction technique, of a cyanobacterium (blue-green alga: Anabaena flosaquae) was affected by TPP. Additions of 0.1, 1.0, and 5.0 mg/L reduced the nitrogenase activity to 84, 77, and 68% of the control value, respectively./AQUATIC SPECIES/ The toxicities of five phosphate ester compounds - Fyrquel GT, Kronitex 200, Phosflex 31P, Pydraul 50E and Santicizer 148-were evaluated in acute toxicity tests with rainbow trout (Salmo gairdneri), fathead minnows (Pimephales promelas), channel catfish (Ictalurus punctatus) and bluegills (Lepomis macrochirus) and in 90 day partial life-cycle tests with fathead minnows. Nominal exposure concentrations were 0, 0.06, 0.12, 0.25, 0.5 and 1.0 mg/L in the partial life-cycle tests with Fyrquel GT, Kronitex 200, Phosflex 31P and Pydraul 50E, and 0, 0.05, 0.09, 0.19, 0.38 and 0.75 mg/L in the test with Santicizer 148. The 96 hr LC50 values for rainbow trout, fathead minnows, channel catfish and bluegills exposed to the five phosphate esters ranged from <0.3 to >72 mg/L. The LC50 values may be directly related to the percentage of triphenyl phosphate contained in each of the compounds. The phosphate esters generally showed similar chronic toxicities to fathead minnows, and adverse toxic effects occurred at nominal exposure concentrations of 0.38 to 1.0 mg/L. Comparison of available environmental concentration data for phosphate esters with the effect concentrations obtained for fish in the present study indicated that phosphate ester compounds may not now pose a threat to fish populations. /SRP: Formulated products/For more Ecotoxicity Excerpts (Complete) data for Triphenyl phosphate (6 total), please visit the HSDB record page.
Animal ConcentrationsTriphenyl phosphate was reported at median concentrations of 4.3 and 0.22 ng/g in plasma and feathers, respectively, of White-tailed Eagle (Haliaeetus albicilla) nestlings in Trondelag, Norwaysampling was conducted in 2011 just prior to fledging at between 6 to 9 weeks of age(1).
직업 노출 등급(OEB)B
직업 노출 한계(OEL)TWA: 3 mg/m3
수질 위해 등급(WGK)2
즉시 생명 위험 농도1,000 mg/m3
TSCA 등재 상태TSCA listed
RTECS 번호TC8400000
운송 번호(UN)UN 3077 9/PG 3
독성LD50 orally in Rabbit: 3500 mg/kg LD50 dermal Rabbit > 7900 mg/kg
관세 코드29190010
위험 문구(R)22-38-40-48/20/22-50/53-52/53-36/37/38-67-66-36-11-51/53
위험 표시Xn,N,F,Xi
안전 문구(S)36/37-61-60-24/25-22-36-26-16-24-9
포장분류III
위험 등급9Aquatic Acute 1Aquatic Chronic 1
기존화학 물질KE-34739
자연 발화 온도>500 °C
저장 분류11 - Combustible Solids
유해 물질 데이터115-86-6(Hazardous Substances Data)
함량 및 규제정보물질구분: 유독물질혼합물(제품)함량정보: 트리페닐인산 및 이를 25% 이상 함유한 혼합물
유해화학물질 필터링2001-1-517