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Nonan
NONANE · 1-NONANE · n-Nonane, 99% 500ML · Nonane( 99%, HyDry, with molecular sieves, Water≤50 ppm (by K.F.)) · n-C9H20 · nonanes · n-Nonane · ALKANE C9
Identifikatoren & physikalische Daten
| CAS No. | 111-84-2 |
|---|---|
| Summenformel | C9H20 |
| Durchschnittliche Molmasse | 128,25 g/mol |
| Monoisotopische Masse | 128,15650064 g/mol |
| SMILES | CCCCCCCCC |
| InChIKey | BKIMMITUMNQMOS-UHFFFAOYSA-N |
| PubChem CID | 8141 |
| ChEMBL | CHEMBL335900 |
| ChEBI | CHEBI:32892 |
| EC No. | 203-913-4 |
| DTXSID | DTXSID9025796 |
| Lokaler Name | Nonan |
Chemische & physikalische Eigenschaften
| XLogP | 4,5 |
|---|---|
| Polarare Oberfläche (TPSA) | 0 |
| H-Brücken-Donoren | 0 |
| H-Brücken-Akzeptoren | 0 |
| Frei drehbare Bindungen | 6 |
| Schwere Atome | 9 |
| Formalladung | 0 |
| Komplexität | 33,3 |
| Stoffklassen | Flammable agents - 3rd degree |
| Lipide | Fatty Acyls [FA] -> Hydrocarbons [FA11] |
| Solvents | Solvents -> Aliphatics, Saturated (<C12) |
| SpringerMaterials Properties | Gibbs energy |
| Duftstoffe | Fragrance Ingredient (Nonane) -> IFRA transparency List |
| LogP (Verteilungskoeffizient) | log Kow = 5.65 |
| Geruch | Gasoline-like odor |
| Dichte | 0.718 at 68 °F (USCG, 1999) - Less dense than waterwill float0.7176 g/cu cm at 20 °CRelative density (water = 1): 0.70.7192 @ 20°C0.720.72 g/mL at 20 °C |
| Viscosity | 0.6696 cP at 25 °C |
| Color/Form | Colorless liquid |
| Löslichkeit | less than 1 mg/mL at 70 °F (NTP, 1992)In water, 0.220 mg/L at 25 °CVery soluble in ethanol and ethermiscible with acetone, benzene, chloroform, hydrogen peroxide0.00022 mg/mL at 25 °CSolubility in water, g/100ml at 25 °C: 0.00002 (very poor)InsolubleIn methanol, g/L: 84 at 5 °C, 95 at 10 °C, 105 at 15 °C, 116 at 20 °C, 129 at 25 °C, 142 at 30 °C, 155 at 35 °C, 170 at 40 °C (Kiser et al., 1961). Miscible with many aliphatic hydrocarbons.Miscible with ethanol, ether, acetone, benzene, chloroform and hydrogen peroxide. Immiscible with water. |
| Flammpunkt | 88 °F (NTP, 1992)31 °C88 °F (31 °C) (Closed Cup)31 °C c.c. |
| Schmelzpunkt | -53 °C |
| Siedepunkt | 151 °C(lit.) |
| Dampfdichte | 4.41 (vs air) |
| Dampfdruck | 0.18 psi ( 37.7 °C) |
| Brechungsindex | n20/D 1.407 |
| Lagerbedingungen | Store below +30°C. |
| pKa (Säurekonstante) | >14 (Schwarzenbach et al., 1993) |
| Aggregatzustand | Liquid |
| Wichte | 0.72 (20/4℃) |
| Farbe | Clear colorless |
| Geruch | gasoline |
| Geruchsschwelle | 2.2ppm |
| Explosionsgrenze | 0.7-5.6%(V) |
| Spezifische Wärmekapazität | Cp(liquid): 2.22 J/(g·K), at 25℃ |
| BRN | 1696917 |
| Henry-Konstante | 2.32 at 25 °C (Jnsson et al., 1982) |
| Dielektrizitätskonstante | 2.0(20℃) |
| Stabilität | Stable. Highly flammable. Incompatible with strong oxidizing agents. |
| Kosmetik-Inhaltsstoffe Funktionen | SKIN CONDITIONING - MISCELLANEOUSSOLVENT |
| InChI | 1S/C9H20/c1-3-5-7-9-8-6-4-2/h3-9H2,1-2H3 |
| InChIKey | BKIMMITUMNQMOS-UHFFFAOYSA-N |
| SMILES | CCCCCCCCC |
| LogP (Verteilungskoeffizient) | 5.293 (est) |
| Oberflächenspannung | 23.04mN/m at 293.15K |
| CAS Datenbank | 111-84-2(CAS DataBase Reference) |
| EPA chemische Informationen | Nonane (111-84-2) |
Sicherheit & Vorschriften
| GHS-Einstufung | This chemical does not meet GHS hazard criteria for 0.2% (3 of 1344) of reports.DangerH226 (65.8%): Flammable liquid and vapor [Warning Flammable liquids]P210, P233, P240, P241, P242, P243, P261, P264, P264+P265, P271, P273, P280, P301+P316, P302+P352, P303+P361+P353, P304+P340, P305+P351+P338, P317, P319, P321, P331, P332+P317, P337+P317, P362+P364, P370+P378, P391, P403+P233, P403+P235, P405, and P501 (click each P-code to see the statement)Aggregated GHS information provided per 1344 reports by companies from 39 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies. |
|---|---|
| Regulatorische Informationen | Chemical: NonaneNonane is listed on the EPA's Chemical Data Reporting (CDR) system. Manufacturers and importers of Nonane 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: 01-11-2022 https://echa.europa.eu/registration-dossier/-/registered-dossier/11446Nonane: HSNO Approval: HSR001208 Approved with controlsThe New Jersey Worker and Community Right to Know Act requires public and private employers to provide information about hazardous substances at their workplaces. (N.J.S.A. 34:5A-1 et. seq.) |
| DOT-Kennzeichnung | Flammable Liquid |
| Brandgefahren | Excerpt from ERG Guide 128 [Flammable Liquids (Water-Immiscible)]:Flammable. Above 31 °C explosive vapour/air mixtures may be formed. |
| Brandpotenzial | A very dangerous fire hazard when exposed to heat or flame. |
| Gesundheitsgefahren | Inhalation of concentrated vapor causes depression, irritation of respiratory tract, and pulmonary edema. Liquid can irritate eyes and (on prolonged contact) skin. Ingestion causes irritation of mouth and stomach. Aspiration causes severe lung irritation, rapidly developing pulmonary edema, and central nervous system excitement followed by depression. (USCG, 1999) |
| Gefahrenübersicht | A skin, eye, and respiratory tract irritantInhalation of high concentrations can cause CNS depression[ICSC] TLV Basis = CNS impairmentIn animals, inhalation causes reversible CNS effects at >2500 ppmIn a 13-week inhalation study of rats, NOAEL = 590 ppm, and LOAEL = 1600 ppm[ACGIH] |
| DOT-Nummer und Handbuch | 1920 128 |
| Reaktive Gruppe | Hydrocarbons, Aliphatic Saturated |
| UN-Einstufung | UN Hazard Class: 3UN Pack Group: III |
| TSCA-Anforderungen | Section 8(a) of TSCA requires manufacturers of this chemical substance to report preliminary assessment information concerned with production, exposure, and use to EPA as cited in the preamble in 51 FR 41329. Effective date: 1/26/94Reporting date: 3/28/94.Pursuant 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. Nonane is included on this list. Effective date: 1/26/94Sunset date: 6/30/98. |
| Reactivity Alerts | Highly Flammable |
| Reactivity Profile | N-NONANE is incompatible with oxidizing materials. It is also incompatible with oxygen. (NTP, 1992). |
| Brandbekämpfung | Excerpt from ERG Guide 128 [Flammable Liquids (Water-Immiscible)]:Use foam, powder, carbon dioxide. In case of fire: keep drums, etc., cool by spraying with water. |
| Erste-Hilfe-Maßnahmen | Fresh air, rest. Refer for medical attention.Rinse and then wash skin with water and soap. Refer for medical attention if skin irritation occurs.Rinse with plenty of water (remove contact lenses if easily possible).Rinse mouth. Do NOT induce vomiting. Refer for medical attention . |
| Erste Hilfe | EYES: 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) |
| Sichere Lagerung | Fireproof. Separated from strong oxidants. Store in an area without drain or sewer access. |
| Brandbekämpfungsverfahren | For small (incipient) fires, use media such as "alcohol" foam, dry chemical, or carbon dioxide. For large fires, apply water from as far as possible. Use very larg quantities (flooding) of water applied as a mist or spraysolid streams of water may be ineffective. Cool all affected containers with flooding quantities of water.Wear self contained breathing apparatus for fire fighting if necessary. |
| Lagerbedingungen | Store in cool place. Keep container tightly closed in a dry and well-ventilated place. Containers which are opened must be carefully resealed and kept upright to prevent leakage. Moisture sensitive.Fireproof. Separated from strong oxidants. Store in an area without drain or sewer access. |
| Reinigungsverfahren | Personal protection: filter respirator for organic gases and vapors adapted to the airborne concentration of the substance. Ventilation. Absorb remaining liquid in dry sand or inert absorbent. Then store and dispose of according to local regulations.Contain spillage, and then collect with an electrically protected vacuum cleaner or by wet-brushing and place in container for disposal according to local regulations...Prevent further leakage or spillage if safe to do so. Do not let product enter drains. Discharge into the environment must be avoided. |
| Freisetung ohne Brand | Excerpt from ERG Guide 128 [Flammable Liquids (Water-Immiscible)]: |
| Entsorgungsverfahren | Burn in a chemical incinerator equipped with an afterburner and scrubber but exert extra care in igniting as this material is highly flammable. Offer surplus and non-recyclable solutions to a licensed disposal company. Contact a licensed professional waste disposal service to dispose of this material.SRP: Wastewater from contaminant suppression, cleaning of protective clothing/equipment, or contaminated sites should be contained and evaluated for subject chemical or decomposition product concentrations. Concentrations shall be lower than applicable environmental discharge or disposal criteria. Alternatively, pretreatment and/or discharge to a permitted wastewater treatment facility is acceptable only after review by the governing authority and assurance that "pass through" violations will not occur. Due consideration shall be given to remediation worker exposure (inhalation, dermal and ingestion) as well as fate during treatment, transfer and disposal. If it is not practicable to manage the chemical in this fashion, it must be evaluated in accordance with EPA 40 CFR Part 261, specifically Subpart B, in order to determine the appropriate local, state and federal requirements for disposal. |
| Verschüttetes entsorgen | Personal protection: filter respirator for organic gases and vapours adapted to the airborne concentration of the substance. Ventilation. Absorb remaining liquid in dry sand or inert absorbent. Then store and dispose of according to local regulations. |
| Preventive Measures | SRP: The scientific literature for the use of contact lenses by industrial workers is inconsistent. The benefits or detrimental effects of wearing contact lenses depend not only upon the substance, but also on factors including the form of the substance, characteristics and duration of the exposure, the uses of other eye protection equipment, and the hygiene of the lenses. However, there may be individual substances whose irritating or corrosive properties are such that the wearing of contact lenses would be harmful to the eye. In those specific cases, contact lenses should not be worn. In any event, the usual eye protection equipment should be worn even when contact lenses are in place.SRP: Contaminated protective clothing should be segregated in such a manner so that there is no direct personal contact by personnel who handle, dispose, or clean the clothing. The completeness of the cleaning procedures should be considered before the decontaminated protective clothing is returned for reuse by the workers. Contaminated clothing should not be taken home at the end of shift, but should remain at employee's place of work for cleaning.The worker should wash daily at the end of each work shift, and prior to eating, drinking, smoking, etc.Work clothing that becomes wet should be immediately removed due to its flammability hazard (i.e., for liquids with a flash point <100 °F).Use protective equipment. Avoid breathing vapors, mist or gas. Ensure adequate ventilation. Remove all sources of ignition. Evacuate personnel to safe areas. Beware of vapors accumulation to form explosive concentrations. Vapors can accumulate in low areas. |
| Isolation and Evacuation | Excerpt from ERG Guide 128 [Flammable Liquids (Water-Immiscible)]: |
| Körperbelastung | n-Nonane was detected in 8 of 12 samples of mothers breast milk from the cities of Bayonne NJ, Jersey City NJ, Bridgeville PA and Baton Rouge LA(1). The air expired from humans contained n-nonane in 36.7% of the 387 samples collected from 54 subjects(2). The average n-nonane concentration of 0.308 ng/L was expressed as the geometric mean with upper and lower limits of 1.37 and 0.069 ng/L, respectively(2).The median concentration of n-nonane in personal air and breath samples were 3.2 and 0.3 ug/cu m, respectively, for 50 individuals in Los Angeles during the winter of 1987, 2.3 and not detected (<0.1-0.3) ug/cu m, respectively, for 40 individuals in Los Angeles during the summer of 1987, and 2.8 and 0.5 ug/cu m, respectively, for 75 individuals in Baltimore, MD during the spring of 1987(1). The at home median exposure of 26 individuals living in smoking homes to n-nonane was reported to be 0.82-0.89 ug-day/cu m(2). The at-home median exposure of 51 individuals living in nonsmoking homes to n-nonane was reported to be 0.76 ug-day/cu m(2). Median concentrations of n-nonane were 3.16, 2.71, 3.05, and 1.08 ug/cu m in personal, kitchen, living area, and outdoor air samples, respectively, collected from 50 individuals in Los Angeles, CA during the Total Exposure Assessment Methodology (TEAM) study(4). During the second German Environmental Survey, n-nonane was detected above 1 ug/cu m in 109 out of 113 personal exposure samples collected from individuals in the Western part of Germany(3). The 95th percentile and geometric mean concentrations in these samples were 26 and 3.3 ug/cu m, respectively(4).[ |
| Wechselwirkungen | The penetration enhancing effects of nonane on the in vivo penetration of 1 mg propranolol hydrochloride applied under topical occlusive conditions with and without the presence of 4% nonane to 12 human volunteers are described. Propranolol penetration increased from 0.705 to 1.402% of the applied dose in the presence of nonane. All 7 subjects receiving the enhancer sustained moderate to severe erythema with slight edema at the application site, with slight eschar formation observed in 2 subjects after 24 hr exposure. In in vitro studies propranolol bioavailability was increased from 1.03 to 2.28% of the applied dose.Alkaline phosphatase activity in liver, spleen, and bone marrow were increased in female rats exposed to n-octane or n-nonane for 2 and 7 days. The increase in splenic alkaline phosphatase activity persisted for up to 42 days after a single dose of either solvent. Pretreatment with protein formation inhibitors, cycloheximide or ethionine, removed this observed increase of alkaline phosphatase activity in liver and spleen. |
| Zielorgane | Eyes, skin, respiratory system, central nervous system |
| Umweltverhalten | TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 8.0X10+4(SRC), determined from a log Kow of 5.65(2) and a regression-derived equation(3), indicates that n-nonane is expected to be immobile in soil(SRC). Volatilization of n-nonane from moist soil surfaces is expected to be an important fate process(SRC) given an estimated Henry's Law constant of 3.4 atm-cu m/mole(SRC), derived from its vapor pressure, 4.45 mm Hg(4), and water solubility, 22 mg/L)(5). n-Nonane is expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(4). Evaporation was considered to be the primary removal mechanism during a study where n-nonane was completely removed from both sterile and non-sterile soils after 5 days(6). Under conditions where volatilization is hindered, biodegradation of n-nonane is expected to be an important fate process based on 100% degradation after 5 and 25 days in screening tests using seawater sediment and activated sewage sludge inocula, respectively(7,8), suggesting that biodegradation may be an important environmental fate process in soil(SRC).AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 8.0X10+4(SRC), determined from a log Kow of 5.65(2) and a regression-derived equation(3), indicates that n-nonane is expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(4) based upon an estimated Henry's Law constant of 3.4 atm-cu m/mole(SRC), derived from its vapor pressure, 4.45 mm Hg(5), and water solubility, 22 mg/L)(6). Using this Henry's Law constant and an estimation method(4), volatilization half-lives for a model river and model lake are 3.3 hours and 4.5 days, respectively(SRC). 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 155 days if adsorption is considered(7). According to a classification scheme(8), an estimated BCF of 100(SRC), from its log Kow(2) and a regression-derived equation(3), suggests the potential for bioconcentration in aquatic organisms is moderate(SRC). Based on 100% degradation after 5 days in water inoculated with seawater sediment(9) and 100% degradation after 25 days in water inoculated with activated sewage sludge(10), biodegradation is expected to be an important fate process for n-nonane in water(SRC).ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), n-nonane, which has a vapor pressure of 4.45 mm Hg at 25 °C(2), is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase n-nonane 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 1.7 days(SRC), calculated from its rate constant of 1.02X10-11 cu cm/molecule-sec at 25 °C(3). n-Nonane does not contain chromophores that absorb at wavelengths >290 nm(4) and, therefore, is not expected to be susceptible to direct photolysis by sunlight(SRC). |
| Lebensmitteluntersuchungswerte | n-Nonane has been detected in dry-cured hams at different stages of the manufacturing processhowever, the concentrations were not specified(1). n-Nonane was identified as a volatile component of roasted filberts(2), and beaufort cheese(3). n-Nonane has been identified in headspace samples of heated peanut oil(4). n-Nonane has been detected in the headspace of floured chickpea seed(5). |
| Unerwünschte Wirkungen | Neurotoxin - Acute solvent syndrome |
| Expositionspfade | The substance can be absorbed into the body by inhalation of its vapour and by ingestion.inhalation, ingestion, skin and/or eye contact |
| Milk Concentrations | n-Nonane was detected in 8 of 12 samples of mothers breast milk from the cities of Bayonne NJ, Jersey City NJ, Bridgeville PA and Baton Rouge LA(1). n-Nonane has also been detected in samples of mother's milk collected from Pittsburgh, PA(2). The concentrations of n-nonane in the samples from these studies were not reported. |
| Plant Concentrations | n-Nonane was identified as a volatile constituent in kiwi fruit flowers collected in Kawanishishi, Hyogo, Japan(1). The compound has also been reported in the essential oil of Common St Johnswort (Hyericum perfortum), ginger (Zingiber officale), and in the fruit of black pepper (Piper nigrum)(2). n-Nonane has been identified in the volatile fractions obtained from the edible Korean chamchwi plant (Aster scber Thunb)(3). |
| Signs and Symptoms | Cough. Sore throat. Drowsiness. Dizziness. Ataxia Convulsions. Unconsciousness.Dry skin. Redness.Nausea. Vomiting. Aspiration hazard! Further see Inhalation.irritation eyes, skin, nose, throatheadache, drowsiness, dizziness, confusion, nausea, tremor, incoordinationchemical pneumonitis (aspiration liquid) |
| Effluent Concentrations | n-Nonane has been detected in 4 of 63 industrial wastewater effluents at concentrations less than 10 ug/L(1). Underwater hydrocarbon vents and formation water discharges from offshore oil production platforms were found to contain n-nonane concentration in the vapor phase at 1 umol/L and in the liquid state at 50 ng/L(2). Formation water contained n-nonane at a concentration of 520 ug/L(2). n-Nonane was detected in influent samples collected at the Jones Island, Akron, OH, Gary, IN, and Wadottee public-owned treatment works at concentrations ranging from <1-9 ppb(3). It was detected in only one effluent sample (Jones Island) at a concentration of <1 ppb(3).n-Nonane has been identified as a trace component (0.064% vol) of landfill gas from a municiple landfill in Palos Verdes, CA(1). The average concentration of n-nonane measured in landfill gas samples from the Fresh Kills Municipal Solid-Waste Landfill in New York City has been reported as 3.57 ppmv(2). The concentration of n-nonane in the active compost blower exhaust from the Peninsula Composting Facility in Virginia has been measured to be 19 ug/cu m(3). n-Nonane was detected in greater than 25% of air samples collected at three sites at a municipal landfill in Dupont-Alpha Oxon, UK(4). The actual concentrations were not specified(4). n-Nonane has been detected in waste disposal site landfill gas in the UKhowever, concentrations were not provided(5). A clay pit landfill in England that received municipal, industrial and liquid wastes emitted n-nonane gas at a concentration of 116 mg/L(4). The percentage of n-nonane in the emissions of volatile organic compounds in the UK during 1990 has been reported as 1.1%(6). The concentrations of n-nonane in the biogas released from a waste disposal site in Augsburg, Germany, a waste disposal site in Munich, Germany, and two sewage treatment plants in Munich, Germany were 14.9-18.3, 15.8-17.8, 0.8-1.3 mg/cu m, respectively(7). The concentration of n-nonane in the emissions of a municipal waste incineration plant located in Germany was 0.57 ug/cu m(8). The annual emission rate of n-nonane from the city of Athens, Greece has been calculated to be 1.396 kt/yr(9).n-Nonane is emitted during the combustion of plastics(1). Building materials such as petroleum based solvents such as floor adhesives and waxes, wood stains, polyurethane finish and air fresheners emit n-nonane to indoor air(2). The concentrations of n-nonane released from tufted textile floor covering with styrene-butadiene rubber backing at 23 and 30 °C were 14.6 and 14.0 g/L, respectively(3). The average gaseous concentration of n-nonane in emissions from simulated asphalt roofing kettle tests ranged from not detected to 0.0854 mg/cu m(4). The emissions of n-nonane per area ranged from 36-1311 mg/sq m-hr for the tests in which n-nonane was detected(4).Data collected from Aug 25 to Sept 7, 1979 showed that for a speed of 80 km/hr on straight and level highway, gasoline powered vehicles emitted n-nonane at an average rate of 3.6 mg/km, and diesel trucks emitted n-nonane at an average of 5.1 mg/km(1). The average exhaust from 67 gasoline fueled vehicles was found to contain n-nonane at a concentration 0.2% by weight(2). The concentrations of n-nonane measured in the tailpipe emissions of catalyst-equipped and noncatalyst-equipped gasoline-powered motor vehicles were 430 and 45,300 ug/km, respectively(3). The concentration of n-nonane measured in the emissions of diesel-powered medium duty trucks was reported to be 160 ug/km(4). The mean concentration of n-nonane in six car exhaust samples collected in the UK was 262 ppbV(5). n-Nonane concentrations measured in the emissions of diesel engines and petrol vehicles have been reported as 17 and 520 ug/cu m, respectively(6). The concentrations of n-nonane in samples of exhaust air from the Elbtunnel in Hamburg, Germany ranged from 2.04-2.44 ug/cu m(7). Motorboats emitted n-nonane to canal water with resultant concentration ranging from 1 to 14 ng/L with an average of 6 ng/L in 8 samples(8). The average mass emission rate of n-nonane from ten four-stroke lawnmower engines was 0.50-0.58% of total organic gases(9).For more Effluent Concentrations (Complete) data for N-NONANE (6 total), please visit the HSDB record page. |
| ICSC Environmental Data | Bioaccumulation of this chemical may occur in soil. |
| Berufliche Expositionsstufe (OEB) | A |
| Arbeitsplatzgrenzwert (OEL) | TWA: 200 ppm (1050 mg/m3) |
| Wassergefährdungsklasse (WGK) | 3 |
| TSCA-Inventar-Status | TSCA listed |
| UN-Transportnummer | UN 1920 |
| Zollcode | 2901 10 00 |
| RTECS-Nr. | RA6115000 |
| R-Sätze (R) | 10-67-65-53-20-36-36/38 |
| Toxizität | LC50 (inhalation) for rats 3,200 ppm/4-h (quoted, RTECS, 1985). |
| Gefahrensymbole | Xn |
| Sicherheitshinweise (S) | 62-24/25-23-26 |
| Gefahrenklasse | 3Aquatic Acute 1Aquatic Chronic 1Asp. Tox. 1Flam. Liq. 3Skin Irrit. 2STOT SE 3 |
| Verpackungsgruppe | III |
| Lagerklasse | 3 - Flammable liquids |
| Gefahrstoffdaten | 111-84-2(Hazardous Substances Data) |
| Selbstentzündungstemperatur | 401 °F |
Anwendungen & Verwendung
Verwenden
Organic synthesis, biodegradable detergents, distillation chaser.