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HCID 29307Erstellt: 4. November 2026

O,O-Diethyl-O-5-phenylisoxazol-3-ylthiophosphat

e-48 · si-6711 · KARPHOS · HSDB6692 · HSDB 6692 · HSDB-6692 · Isoxathion · Isoxathion 0.1

https://huagongshe.com/de/chemical/29307

Molekülstruktur von O,O-Diethyl-O-5-phenylisoxazol-3-ylthiophosphat

Identifikatoren & physikalische Daten

CAS No.18854-01-8
SummenformelC13H16NO4PS
Durchschnittliche Molmasse313,31 g/mol
Monoisotopische Masse313,05376616 g/mol
SMILESCCOP(=S)(OCC)Oc1cc(-c2ccccc2)on1
InChIKeySDMSCIWHRZJSRN-UHFFFAOYSA-N
PubChem CID29307
ChEMBLCHEMBL3182191
ChEBICHEBI:34801
EC No.242-624-8
DTXSIDDTXSID0042080
Lokaler NameO,O-Diethyl-O-5-phenylisoxazol-3-ylthiophosphat

Chemische & physikalische Eigenschaften

XLogP4,2
Polarare Oberfläche (TPSA)85,8
H-Brücken-Donoren0
H-Brücken-Akzeptoren6
Frei drehbare Bindungen7
Schwere Atome20
Formalladung0
Komplexität328
PestizideInsecticidesActive substance -> EU Pesticides database: Not approvedPesticides -> Organophosphate Insecticides
LogP (Verteilungskoeffizient)log Kow = 3.734.58
Geruch...An ester-like odor.
Color/FormYellowish liquid
LöslichkeitReadily soluble in organic solvents.In water, 1.9 mg/l @ 25 °CChloroform (Slightly), Methanol (Slightly)1.9 mg l-1 (25 °C)
Siedepunkt160 °C/0.15 mmHg160°C (rough estimate)
DecompositionDecomposes at 160 °C.When heated to decomposition it emits very toxic fumes of /nitrogen, phosphorous and sulfur oxides/.
Dampfdruck0.00000222 [mmHg]-4 Pa (25 °C)
Physical DescriptionYellowish liquid[HSDB]
Stability/Shelf LifeUnstable to alkalis.
Collision Cross Section180.8 Ų [M+Na]+ [CCS Type: DTBuffer gas: N2Ionization: ESI+Dataset: TOXCASTSource Identifier: DTXSID0042080]
Other Experimental PropertiesDecomposes at 160 °CWhen heated to decomposition it emits very toxic fumes of NOx, POx, and SOx.
Schmelzpunkt<25℃
Dichte1.48 g/ml
Lagerbedingungen0-6°C
pKa (Säurekonstante)-6.17±0.28(Predicted)
Aggregatzustandliquid
FarbeColourless to Pale Yellow
Wichte1.48
BRN1222135
Henry-Konstante1.6×102 mol/(m3Pa) at 25℃, HSDB (2015)
EPA chemische InformationenIsoxathion (18854-01-8)

Sicherheit & Vorschriften

GHS-EinstufungDangerH301: Toxic if swallowed [Danger Acute toxicity, oral]P262, P264, P270, P273, P280, P301+P316, P302+P352, P316, P321, P330, P361+P364, P391, P405, and P501 (click each P-code to see the statement)H301+H311 (100%): Toxic if swallowed or in contact with skin [Danger Acute toxicity, oralacute toxicity, dermal]
Regulatorische Informationen2002/2076
GefahrenübersichtThe average of two baseline respective cholinesterase activity determinations three days apart, with no exposures to enzyme inhibiting pesticides for at least 30 days, is recommended for each worker prior to exposure to cholinesterase inhibitors because of large inter-individual differences in published baseline values. To be established at least once a year. Removal from workplace exposures is recommended until the cholinesterase activity returns to within 20% of baseline. [TLVs and BEIs]
DOT Emergency Guidelines/GUIDE 131: FLAMMABLE LIQUIDS-TOXIC/ Health: TOXICmay be fatal if inhaled, ingested or absorbed through skin. Inhalation or contact with some of these materials will irritate or burn skin and eyes. Fire will produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control or dilution water may cause pollution. /Organophosphorus pesticide, liquid, flammable, poisonousOrganophosphorus pesticide, liquid, flammable, toxicOrganophosphorus pesticide, liquid, poisonous, flammableOrganophosphorus pesticide, liquid, toxic, flammable//GUIDE 131: FLAMMABLE LIQUIDS-TOXIC/ Fire or Explosion: HIGHLY FLAMMABLE: Will be easily ignited by heat, sparks or flames. Vapors may form explosive mixtures with air. Vapors may travel to source of ignition and flash back. Most vapors are heavier than air. They will spread along ground and collect in low or confined areas (sewers, basements, tanks). Vapor explosion and poison hazard indoors, outdoors or in sewers. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Runoff to sewer may create fire or explosion hazard. Containers may explode when heated. Many liquids are lighter than water. /Organophosphorus pesticide, liquid, flammable, poisonous/GUIDE 131: FLAMMABLE LIQUIDS-TOXIC/ Public Safety: CALL Emergency Response Telephone Number ... . As an immediate precautionary measure, isolate spill or leak area for at least 50 meters (150 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate closed spaces before entering. /Organophosphorus pesticide, liquid, flammable, poisonous

Anwendungen & Verwendung

Beschreibung

Isoxathion is a pale yellow liquid, bp 160 C/0.15 mm Hg, vp

Verwenden

Isoxathion is used to control sucking pests, leaf miners and some chewing pests in a variety of fruit, vegetables and ornamental plants.

/GUIDE 131: FLAMMABLE LIQUIDS-TOXIC/ Protective Clothing: Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY
it is not effective in spill situations where direct contact with the substance is possible. /Organophosphorus pesticide, liquid, flammable, poisonous
For more DOT Emergency Guidelines (Complete) data for ISOXATHION (16 total), please visit the HSDB record page.
DOT Hazard ClassificationIsoxathionSevere marine pollutant
Hazard Classes and CategoriesAcute Tox. 3 (100%)Acute toxicity - category 3Acute toxicity (Oral) - Category 3Acute Tox. 3 *
Standard Transportation Number49 216 74Organophosphorus pesticide, liquid, not otherwise specified (compounds and preparations) (insecticides, other than agricultural, NEC)49 216 75Organophosphorus pesticide, liquid, not otherwise specified (compounds and preparations) (agricultural insecticides, NEC, liquid)49 105 4449 105 4549 216 76Organophosphorus pesticide, solid, not otherwise specified (compounds and preparations) (insecticides, other than agricultural, NEC)49 216 77Organophosphorus pesticide, solid, not otherwise specified (compounds and preparations) (agricultural insecticides, NEC, other than liquid)
Shipment Methods and RegulationsSevere marine pollutantNo person may /transport,/ offer or accept a hazardous material for transportation in commerce unless that person is registered in conformance ... and the hazardous material is properly classed, described, packaged, marked, labeled, and in condition for shipment as required or authorized by ... /the hazardous materials regulations (49 CFR 171-177)./The International Air Transport Association (IATA) Dangerous Goods Regulations are published by the IATA Dangerous Goods Board pursuant to IATA Resolutions 618 and 619 and constitute a manual of industry carrier regulations to be followed by all IATA Member airlines when transporting hazardous materials.The International Maritime Dangerous Goods Code lays down basic principles for transporting hazardous chemicals. Detailed recommendations for individual substances and a number of recommendations for good practice are included in the classes dealing with such substances. A general index of technical names has also been compiled. This index should always be consulted when attempting to locate the appropriate procedures to be used when shipping any substance or article.
Shipping Name/ Number DOT/UN/NA/IMOUN 3018Organophosphorus pesticides, liquid, toxic, not otherwise specifiedUN 3017Organophosphorus pesticides, liquid, toxic, flammable, not otherwise specified, flashpoint between 23 °C and 61 °CUN 2783Organophosphorus pesticides, solid, toxic, not otherwise specifiedUN 2784Organophosphorus pesticides, liquid, flammable, toxic, not otherwise specified, flashpoint less than 23 °CFor more Shipping Name/ Number DOT/UN/NA/IMO (Complete) data for ISOXATHION (6 total), please visit the HSDB record page.
Expositionsschutz und Persönliche SchutzausrüstungBiological Exposure Indices (BEI) [ACGIH] - Acetylcholinesterase activity in red blood cells = 70% of individual's baselineButylcholinesterase activity in serum or plasma = 60% of individual's baselineSample at end of shift[TLVs and BEIs]
BrandbekämpfungsverfahrenIf material on fire or involved in fire: Do not extinguish fire unless flow can be stopped. Use water in flooding quantities as fog. Solid streams of water may be ineffective. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. Use "alcohol" foam, dry chemical or carbon dioxide. /Organophosphorus pesticides, liquid, flammable, toxicOrganophosphorus pesticides, liquid, toxic/If material on fire or involved in fire: Use water in flooding quantities as fog. Extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) /Organophosphorus pesticides, solid, toxic/
ReinigungsverfahrenEnvironmental considerations: Air spill: Apply water spray or mist to knock down vapors. /Organophosphorus pesticides, liquid, flammable, toxicOrganophosphorus pesticides, liquid, toxicOrganophosphorus pesticides, solid, toxic/Environmental considerations: Water spill: Use natural barriers or oil spill control booms to limit spill travel. Remove trapped material with suction hoses. /Organophosphorus pesticides, liquid, flammable, toxicEnvironmental considerations: Land spill: Dig a pit, pond, lagoon, holding area to contain liquid or solid material. /SRP: If time permits, pits, ponds, lagoons, soak holes, or holding areas should be sealed with an impermeable flexible membrane liner./ Dike surface flow using soil, sand bags, foamed polyurethane, or foamed concrete. Absorb bulk liquid with fly ash, cement powder, or commercial sorbents. /Organophosphorus pesticides, liquid, flammable, toxic
EntsorgungsverfahrenSRP: The most favorable course of action is to use an alternative chemical product with less inherent propensity for occupational exposure or environmental contamination. 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 soil or watereffects on animal, aquatic, and plant lifeand conformance with environmental and public health regulations.
Preventive MeasuresIf material not on fire and not involved in fire: Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers. /Organophosphorus pesticides, solid, toxicIf material not on fire and not involved in fire: Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers. Build dikes to contain flow as necessary. Attempt to stop leak if without undue personnel hazard. Use water spray to knock-down vapors. /Organophosphorus pesticides, liquid, toxic/If material not on fire and not involved in fire: Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers. Build dikes to contain flow as necessary. Use water spray to knock-down vapors. /Organophosphorus pesticides, liquid, flammable, toxic/Personnel protection: Avoid breathing dusts, and fumes from burning material. Keep upwind. Avoid bodily contact with the material. Do not handle broken packages unless wearing appropriate personal protective equipment. Wash away any material which may have contacted the body with copious amounts of water or soap and water. /Organophosphorus pesticides, solid, toxic/For more Preventive Measures (Complete) data for ISOXATHION (8 total), please visit the HSDB record page.
WechselwirkungenBecause different classes of enzymes may be inhibited, the effects of organophosphorus pesticide poisoning may be complex and potentially at least could involve interactions with drugs as well as with other pesticides or chemicals. Potentiation may also involve solvents or other components of formulated pesticides. Certain drugs such a phenothiazines, antihistamines, CNS depressants, barbiturates, xanthines (theophylline), aminoglycosides and parasympathomimetic agents are to be avoided because of increased toxicity. /Organophosphorus pesticides/
ÖkotoxizitätswerteLC50 Cyprinus carpio 2.1 mg/l/48 hr /Conditions of bioassay not specified/LD50 Chicken oral 21,600 ug/kgLC50 Daphnia pulex 0.0052 mg/L/3 hr /Conditions of bioassay not specified/LC50 Bufo bufo japonicus (Toad25-35 days, 0.34 g tadpole) 5,100 ug/L/72 hr12,000 ug/L/24 hr5,300 ug/L/48 hr5,100 ug/L/96 hrstatic /Formulated product/For more Ecotoxicity Values (Complete) data for ISOXATHION (6 total), please visit the HSDB record page.
UmweltverhaltenTERRESTRIAL FATE: Based on a classification scheme(1), a Koc value of 14,568(2) indicates that isoxathion is expected to be immobile in soil(SRC). Volatilization of isoxathion from moist soil surfaces is not expected to be an important fate process(SRC) given an estimated Henry's Law constant of 6.1X10-8 atm-cu m/mole(SRC), using a fragment constant estimation method(3). Isoxathion is not expected to volatilize from dry soil surfaces(SRC) based upon an estimated vapor pressure of 2.2X10-6 mm Hg(SRC), determined from a fragment constant method(4). Isoxathion has been shown to biodegrade in soil with the major metabolic pathway being via the formation of 3-hydroxy-5-phenylisoxazole to 5-phenyl-4-oxazolin-2-one, benzoylacetamide and benzoic acid(5).AQUATIC FATE: Based on a classification scheme(1), a Koc value of 14,568(2) indicates that isoxathion is expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is not expected(3) based upon an estimated Henry's Law constant of 6.1X10-8 atm-cu m/mole(SRC), developed using a fragment constant estimation method(4). According to a classification scheme(5), an estimated BCF of 150(SRC), from its log Kow of 3.73(6) and a regression-derived equation(7), suggests the potential for bioconcentration in aquatic organisms is high(SRC). However, aquatic organisms readily metabolize this class of compounds(8) and organophosphates can be altered chemically(9) once released into the environment. Aqueous photolytic half-lives of 12-18 days have been reported, with the addition of humic acids increasing the rate of photolysis by up to 25%(10). Percent biodegradation of isoxathion from three ponds near Nagoya City, Japan ranged from 0-31% after four days of incubationcompared to aniline (biodegradation rate as high as 86%), this compound was classified as not expected to biodegrade rapidly(11).ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), isoxathion, which has an estimated vapor pressure of 2.2X10-6 mm Hg at 25 °C(SRC), determined from a fragment constant method(2), will exist in both the vapor and particulate phases in the ambient atmosphere. Vapor-phase isoxathion 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 3 hrs(SRC), calculated from its rate constant of 1.2X10-10 cu cm/molecule-sec at 25 °C(SRC) that was derived using a structure estimation method(3). Particulate-phase isoxathion may be removed from the air by wet and dry deposition(SRC).
Unerwünschte WirkungenOther Poison - Organophosphate
Milk ConcentrationsMany of the organophosphorus insecticides are excreted in the milk ... /Organophosphorus insecticides/
Effluent ConcentrationsIsoxathion, 200-4,300 g applied at a rate of 0.50 g/sq m, was not detected in drainage samples from 24 Japanese golf courses, monitored from 1994 to 1996detection limit less than 0.001 mg/l(1).
Medical SurveillanceMeasurement of whole blood-AChE is the most widely adopted method for monitoring the effects of occupational exposure to organophosphorus insecticides. Physiological variations in blood ChE levels occur in a healthy person and are seen among a population. It has been estimated that the coefficient of variation for AChE activity in samples from an individual is 8-11%, and that a decrease of 23% below pre-exposure level may, therefore, be considered significant. If the average of several pre-exposure values were available, then a decrease of 17% would be significant. It has been recommended that, if measured activity is reduced by 30% or more of the pre-exposure value, AChE measurements should be repeated at appropriate intervals to confirm the results. Depressions of AChE or ChE in excess of 20-25% are considered diagnostic of exposure but not, necessarily, indicative of hazard. Depressions of 30-50% or more are considered indicators for removal of an exposed individual from further contact with pesticides until levels return to normal. /Organophosphorus Pesticides/...Organophosphorus pesticides may undergo hydrolysis in vivo to yield substituted phosphoric acids that are subsequently excreted in urine. Advances in gas chromatography and combined gas chromatography/mass spectrometry (GC/MS) have made it possible to analyse the urine of exposed persons for the presence of appropriate metabolites. It is usually necessary to preserve the sample by the addition of chloroform, to concentrate or extract the metabolite(s), and to convert them to suitably-volatile derivatives that can be detected by GC. Obviously, access to a well-equipped analytical laboratory, capable of the quick processing of samples, is a necessary factor if monitoring by urine analysis is proposed. However, in some cases, simpler and sensitive colorimetric tests are available for screening the urine of exposed persons. Thus, 4-nitrophenol can be measured directly in the urine of workers exposed to parathion. Consideration of the concentration of metabolite(s) in the urine can be helpful in determining patterns of exposure, and these concentrations can be calibrated against the effects on AChE for a particular pesticide. However, the time-course and peak of excretion of metabolites appears to vary according to dose, so that serial sampling and analyses of urine are desirable. Levels of metabolite alone cannot be considered a guide to hazard. This is obvious when it is realized that pesticides that have very different toxicities may yield identical acidic metabolites. Thus, the level of metabolites in urine, after exposure to sufficient amounts of the very toxic parathion-methyl to depress blood-AChE to 50%, will be much lower than that of the identical metabolites, following exposure to the related fenitrothion, which is about 40 times less toxic. /Organophosphorus Pesticides/SRP: Workers should undergo an annual medical exam. Contraindications for work with organophosporous pesticides are organic diseases of the CNS, mental disorders and epilepsy, and pronounced endocrine disorders. Blood cholinesterase, both plasma and RBC, must be determined before work starts. In the event of prolonged work periods, this activity should be determined at intervals of 3-4 days. Persons exhibiting a fall in cholinesterase activity of 25% or more must be transferred to other work where they are not exposed until cholinesterase activity is restored. /Organophosphorous pesticides/
Soil Adsorption/MobilityThe Koc of isoxathion in turf grass soil is 14,568(1). According to a classification scheme(2), this estimated Koc value suggests that isoxathion is expected to be immobile in soil. Rf (retention factor) values for isoxathion were reported as 0.63, 0.50, and 0.62, using three Japanese soils - Hiratsuka (sandy loam, 69.8% sand, 19.6% silt, 10.6% clay, 3.2% organic matter, pH 5.9), Tanashi (loam, 60.5% sand, 30.2% silt, 9.3% clay, 8.4% organic matter, pH 6.0), and Yasu (sandy loam, 56.6% sand, 29.9% silt, 1.56% clay, 1.8% organic matter, pH 4.9), respectively(3).
Atmospheric ConcentrationsURBAN/SUBURBAN: Air samples from Kitayushu City, Japan during 21-22 July 1991 and 23-24 April, 1992 were tested for isoxathionconcentrations of 0.63 ng/cu m and not detected (detection limit = 0.2 ng/cu m), respectively, were reported(1).SOURCE DOMINATED: Isoxathion was detected, not quantified in air samples collected from golf courses in the Kanagawa Prefecture, Japanlevels were higher in daytime(1).
Human Toxicity Excerpts/SIGNS AND SYMPTOMS/ Signs and symptoms of acute intoxication by organophosphorus insecticides include muscarinic, nicotinic, and central nervous system (CNS) manifestations. Symptoms may develop rapidly, or there may be a delay of several hours after exposure before they become evident. The delay tends to be longer in the case of more lipophilic compounds, which also require metabolic activation. Symptoms may increase in severity for more than one day and may last for several days. In severe cases, respiratory failure is a dominant effect. /Organophosphorus Pesticides//SIGNS AND SYMPTOMS/ Although many epidemiological studies have been carried out, few controlled studies on man have been reported. It is generally recognized that there are behavioural and psychic changes during overt clinical poisoning by organophosphorus insecticides and that these may take several months to regress. However, there is no information to suggest that effects occur at exposure levels that do not either alter ChE levels or produce physical symptoms. ...Much /of the work on different aspects of behavior as affected by organophasphates/ was based on generalized complaints from workers occupationally exposed to many agricultural chemicals (and probably also to automobile fuels and lubricants and to alcohol). In summary, ...in human subjects sufficiently exposed to organophosphates to depress plasma- or erythrocyte-ChEs, some or all of the following behavioral variables might be impaired. In cognition: vigilance, information processing and psychomotor speed, and memoryin speech: both performance and perceptionin psychic state: increased tendencies to depression, anxiety, and irritabilityand in EEG records: a tendency to faster frequencies and higher voltages. /Organophosphorus Pesticides//SIGNS AND SYMPTOMS/ Respiratory and ocular symptoms are expected to appear first after exposure to airborne organophosphorus pesticides. /Organophosphorus pesticides//SIGNS AND SYMPTOMS/ The clinical picture of organophosphorus intoxication results from accumulation of ACh at nerve endings. ...The symptoms can be summarized in three groups as follows: (a) Muscarinic manifestations- increased bronchial secretion, excessive sweating, salivation, and lachrymationpinpoint pupils, bronchoconstriction, abdominal cramps (vomiting and diarrhea)and bradycardia. (b) Nicotinic manifestations- fasciculation of fine muscles and, in more severe cases, of diaphragm and respiratory musclesand tachycardia. (c) Central nervous system manifestations- headache, dizziness, restlessness, and anxietymental confusion, convulsions, and comaand depression of the respiratory centre. All these symptoms can occur in different combinations and can vary in time of onset, sequence, and duration, depending on the chemical, dose, and route of exposure. Mild poisoning might include muscarinic and nicotinic signs only. Severe cases always show central nervous system involvementthe clinical picture is dominated by respiratory failure, sometimes leading to pulmonary edema, due to the combination of the above-mentioned symptoms. /Organophosphorus Pesticides/For more Human Toxicity Excerpts (Complete) data for ISOXATHION (8 total), please visit the HSDB record page.
Artificial Pollution SourcesIsoxathion's former production may have resulted in its release to the environment through various waste streamsit's use as an insecticide(1) may have resulted in its direct release to the environment(SRC).
Environmental BiodegradationAEROBIC: Half-lives in turf grass soil and other soils of 5 and 15-40 days, respectively, have been reported for isoxathion(1). Isoxathion was added to fresh water inoculums from three ponds near Nagoya City, Japan and using the Handai biodegradation test method(2). Biodegradation rates were measured at different times over the years were as follows: Ara-ike (irrigation reservoir), June 1991 thru October 1992, 6-23% after 4-day incubationMakinoga-oke (located in a park near a residential area and a golf course), July 1990 thru April 1991, 0-31% after 4-day incubationTatsuga-ike (boating pond in a park), July 1989-March 1992, 14-22% after 4-day incubation(2). In comparison to aniline which exhibited a biodegradation rate as high as 86%, this compound is not expected to biodegrade rapidly(2).30 ppm of 14C-labeled isoxathion was incubated in 50 g of three Japanese soils - Hiratsuka (sandy loam, 69.8% sand, 19.6% silt, 10.6% clay, 3.2% organic matter, pH 5.9), Tanashi (loam, 60.5% sand, 30.2% silt, 9.3% clay, 8.4% organic matter, pH 6.0), and Yasu (sandy loam, 56.6% sand, 29.9% silt, 1.56% clay, 1.8% organic matter, pH 4.9). Soils were maintained at 60% field capacity for non-flooded conditions and at 150% field capacity for flooded conditions. %14C-isoxathion recovered from non-flooded Hiratsuka soil was 75, 51, and 32 after 20, 40, and 60 days, respectively, initial half-life = 44 days% recovered from flooded Hiratsuka soil - 46, 14, and 5, respectively, initial half-life = 18 days. %14C-isoxathion recovered from non-flooded Tanashi soil was 69, 17, and 10 after 10, 30, and 45 days, respectively, initial half-life = 19 days). %14C-isoxathion recovered from non-flooded Yasu soil was 80 and 47 after 10 and 20 days, respectively, initial half-life = 31 days(1). The major metabolic pathway is via the formation of 3-hydroxy-5-phenylisoxazole to 5-phenyl-4-oxazolin-2-one, benzoylacetamide and benzoic acid(1).
Wassergefährdungsklasse (WGK)3
UN-Transportnummer3018
Zollcode29349990
R-Sätze (R)24/25-50/53
GefahrensymboleT,N
Sicherheitshinweise (S)28-36/37-45-60-61
Gefahrenklasse6.1(b)
VerpackungsgruppeIII
Gefahrstoffdaten18854-01-8(Hazardous Substances Data)