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HCID 10943Erstellt: 27. Oktober 2026

1,3-Dichlorbenzol

MDCB · M-DICHLOROBENZENE · Benzene, m-dichloro- · meta-dichlorobenzene · 1.3-Dichlorobe · 1,3-Dichlorbenzol · 1,3-dichlorbenzene · Metadichlorobenzene

https://huagongshe.com/de/chemical/10943

Molekülstruktur von 1,3-Dichlorbenzol

Identifikatoren & physikalische Daten

CAS No.541-73-1
SummenformelC6H4Cl2
Durchschnittliche Molmasse147 g/mol
Monoisotopische Masse145,96900549 g/mol
SMILESClc1cccc(Cl)c1
InChIKeyZPQOPVIELGIULI-UHFFFAOYSA-N
PubChem CID10943
ChEMBLCHEMBL45235
ChEBICHEBI:36693
EC No.208-792-1
DTXSIDDTXSID6022056
Lokaler Name1,3-Dichlorbenzol

Chemische & physikalische Eigenschaften

XLogP3,5
Polarare Oberfläche (TPSA)0
H-Brücken-Donoren0
H-Brücken-Akzeptoren0
Frei drehbare Bindungen0
Schwere Atome8
Formalladung0
Komplexität64,9
StoffklassenFlammable agents - 2nd degreeVolatile Organic Compound (VOC) (Volatile Organic Compound (VOC)/Semi-Volatile Organic Compound (SVOC))
SolventsSolvents -> Chlorinated Aromatics
SpringerMaterials Properties13C nuclear magnetic resonance spectrum
PestizidePesticide -> EPA IRIS
LogP (Verteilungskoeffizient)log Kow = 3.533.44
Dichte1.2884 at 68 °F (USCG, 1999) - Denser than waterwill sink1.2884 at 20 °C/4 °CRelative density (water = 1): 1.2881.2884 @ 20°C1.288 g/mL at 25 °C (lit.)
Viscosity1.044 mPa.s at 25 °C
Color/FormColorless liquid
Löslichkeitless than 1 mg/mL at 70 °F (NTP, 1992)Sol in ethanol, ethervery soluble in acetoneIn water, 125 mg/L at 25 °CSolubility in water: noneDifficult to mix.0.0123 g/100 mL (25 ºC)
Flammpunkt146 °F (NTP, 1992)63 °C
Endocrine DisruptorsPotential endocrine disrupting compound
Siedepunkt343 °F at 760 mmHg (NTP, 1992)173 °C173 °C @760 [mm Hg]172-173 °C (lit.)
Schmelzpunkt-25--22 °C (lit.)
Dampfdruck5 mm Hg ( 38.8 °C)
Brechungsindexn20/D 1.546(lit.)
Lagerbedingungen2-8°C
AggregatzustandLiquid
FarbeClear colorless to slightly yellow
GeruchPleasant odor
Merck14,3055
BRN956618
Henry-Konstante2.14 at 20.00 °C (inert gas stripping, Hovorka and Dohnal, 1997)
Dielektrizitätskonstante5.0
StabilitätStability Combustible. Incompatible with strong oxidizing agents, aluminium, aluminium alloys. Moisture-sensitive.
InChI1S/C6H4Cl2/c7-5-2-1-3-6(8)4-5/h1-4H
InChIKeyZPQOPVIELGIULI-UHFFFAOYSA-N
SMILESClc1cccc(Cl)c1
LogP (Verteilungskoeffizient)3.53 at 22℃
CAS Datenbank541-73-1(CAS DataBase Reference)
NIST chemische InformationenBenzene, 1,3-dichloro-(541-73-1)
EPA chemische Informationenm-Dichlorobenzene (541-73-1)

Sicherheit & Vorschriften

GHS-EinstufungWarningH302: Harmful if swallowed [Warning Acute toxicity, oral]P264, P270, P273, P301+P317, P330, P391, and P501 (click each P-code to see the statement)H302 (100%): Harmful if swallowed [Warning Acute toxicity, oral]P261, P264, P270, P271, P272, P273, P280, P301+P317, P302+P352, P304+P340, P319, P321, P330, P332+P317, P333+P317, P362+P364, P391, P403+P233, P405, and P501 (click each P-code to see the statement)
Regulatorische InformationenChemical: Benzene, 1,3-dichloro-Hazard Traits - Endocrine ToxicityHepatotoxicity and Digestive System ToxicityNephrotoxicity and Other Toxicity to the Urinary SystemStatus: Active Update: 13-03-2023 https://echa.europa.eu/registration-dossier/-/registered-dossier/180761,3-Dichlorobenzene: Does not have an individual approval but may be used under an appropriate group standardThe 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.)
Weitere SicherheitsinformationenIMAP assessments - Benzene, 1,3-dichloro-: Human health tier I assessment
DOT-KennzeichnungPoison
BrandgefahrenSpecial Hazards of Combustion Products: Irritating vapors including hydrogen chloride are produced. (USCG, 1999)Combustible. Gives off irritating or toxic fumes (or gases) in a fire. Above 63 °C explosive vapour/air mixtures may be formed.
BrandpotenzialCombustiblem-Dichlorobenzene is ignitable only with difficulty.
GesundheitsgefahrenINHALATION: Causes headache, drousiness, unsteadiness. Irritating to mucous membranes. EYES: Severe irritation. SKIN: Severe irritation. INGESTION: Irritation of gastric mucosa, nausea, vomiting, diarrhea, abdominal cramps and cyanosis. (USCG, 1999)
GefahrenübersichtAn eye, nose, and throat irritant[HSDB] Severely irritating to eyes and skin

Anwendungen & Verwendung

Verwenden

1,3-Dichlorobenzene is used in organic synthesis that can synthesize fungicides imazalil, propiconazole, epiconazole, and insecticides insectaphos. It is also used in the synthesis of 1,2-diaminobenzene, in addition, it is also used as a solvent in the fields of dyes, medicine, resin, rubber and so on.

Verwenden

1,3-Dichlorobenzene is used in medicine, and dyes. And it is also used to study the effect of solvent vapor pressure on the vertical nanowire of C60 molecules1. 1,3-Dichlorobenzene, a chlorinated aromatic hydrocarbon, can be detected in environmental samples using an advanced Fourier transform infrared spectroscopy-attenuated total reflectance (FTIR-ATR) sensor.

Herstellung & Synthese

synthetische

1,3-Dichlorobenzene is prepared from o-chloroaniline through diazotization and displacement reaction. Add o-chloroaniline and hydrochloric acid into the reaction pot, mix evenly below 25°C, cool to 0°C, drop in sodium nitrite solution, control the temperature at 0-5°C, stop adding when the potassium iodide starch indicator turns blue, and obtain diazonium salt solution. Then add the diazonium salt solution into the hydrochloric acid solution of cuprous chloride at 0～5℃, stir well, heat up to 60～70℃ and react for 1h, after cooling, let stand for stratification, and use 5% sodium hydroxide for the oil layer. Repeated washing with water, dehydration with anhydrous calcium chloride, fractional distillation, and collection of fractions at 177-183 °C to obtain the product 1,3-dichlorobenzene.

A mucous membrane irritant
Can cause drowsiness and unsteadiness after inhalation
[CAMEO] A skin, eye, and respiratory tract irritant
May cause liver and kidney injury
[ICSC] An irritant
[MSDSonline]
Reaktive GruppeAryl Halides
EG-EinstufungSymbol: Xn, NR: 22-51/53S: (2)-61
UN-EinstufungUN Hazard Class: 6.1UN Pack Group: III
Special ReportsUSEPAAmbient Water Quality Criteria Doc: Dichlorobenzenes (1980) EPA 440/5-80-039Dangerous Prop Ind Mater Rept 5 (1): 56-63 (1985). Review of 1,3-dichlorobenzene toxicology, health hazards, and safety measures.Dichlorobenzenes, Dangerous Prop Ind Mater Rpt 6 (2): 50-7 (1986). Review of dichlorobenzene toxicology, health hazards and safety measures.Drinking Water Criteria Doc: ortho-Dichlorobenzene, meta-Dichlorobenzene, para-Dichlorobenzene (Draft) 174p (1986)For more Special Reports (Complete) data for 1,3-DICHLOROBENZENE (6 total), please visit the HSDB record page.
RCRA-AnforderungenU071As stipulated in 40 CFR 261.33, when 1,3-dichlorobenzene, as a commercial chemical product or manufacturing chemical intermediate or an off-specification commercial chemical product or a manufacturing chemical intermediate, becomes a waste, it must be managed according to Federal and/or State hazardous waste regulations. Also defined as a hazardous waste is any residue, contaminated soil, water, or other debris resulting from the cleanup of a spill, into water or on dry land, of this waste. Generators of small quantities of this waste may qualify for partial exclusion from hazardous waste regulations (40 CFR 261.5).
BrandbekämpfungFire Extinguishing Agents: Water, foam, carbon dioxide or dry or dry chemical. (USCG, 1999)Use water spray, powder, foam, carbon dioxide. In case of fire: keep drums, etc., cool by spraying with water.
Erste-Hilfe-MaßnahmenFresh air, rest. Refer for medical attention.Remove contaminated clothes. Rinse skin with plenty of water or shower. Refer for medical attention .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 .
Erste HilfeEYES: 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.
Sichere LagerungProvision to contain effluent from fire extinguishing. Separated from strong oxidants, aluminium and food and feedstuffs. Well closed. Store in an area without drain or sewer access.
Expositionsschutz und Persönliche Schutzausrüstung2.0 [ppm]
BrandbekämpfungsverfahrenWATER, FOAM, CARBON DIOXIDE, DRY CHEM ...If material on fire or involved in fire: Extinguish fire using agent suitable for type of surrounding fire (Material itself does not burn or burns with difficulty.). Use water in flooding quantities as fog. Use foam, dry chemical, or carbon dioxide. /o-Dichlorobenzene/
ReinigungsverfahrenEnvironmental considerations: Land spill: Dig a pit, pond, lagoon, holding area to contain liquid or solid material. Dike surface flow using soil, sand bags, foamed polyurethane, or foamed concrete. Absorb bulk liquid with fly ash or cement powder. Apply "universal" gelling agent to immobilize spill. /SRP: If time permits, pits, ponds, lagoons, soak holes, or holding areas should be sealed with an impermeable flexible membrane liner./ /o-Dichlorobenzene/ Cover solids with a plastic sheet to prevent dissolving in rain or fire fighting water. /p-Dichlorobenzene/Environmental considerations: Water spill: Use natural deep water pockets, excavated lagoons, or sand bag barriers to trap material at bottom. If dissolved in region of 10 ppm or greater concn, apply activated carbon at ten times the spilled amount. Remove trapped material with suction hoses. Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates. /o-Dichlorobenzenep-Dichlorobenzene/Evacuate and restrict persons not wearing protective equipment for the area of spill or leak until cleanup is complete. Remove all ignition sources. Establish forced ventilation to keep levels below explosive limit. Absorb liquids in vermiculite, dry sand,earth, peat, carbon, or a similar material and deposit in sealed containers. Keep this chemical out of a confined space, such as a sewer, because of the possibility of an explosion, unless the sewer is designed to prevent the build-up of explosive concentrations. It may be necessary to contain and dispose of this chemical as a hazardous waste. If material or contaminated runoff enters waterways, notify downstream users of potentially contaminated waters. Contact your Department of Environmental Protection or your regional office of the federal EPA for specific recommendations. If employees are required to clean-up spills, they must be properly trained and equipped.
Freisetung ohne BrandExcerpt from ERG Guide 153 [Substances - Toxic and/or Corrosive (Combustible)]:
Entsorgungsverfahren[40 CFR 240-280, 300-306, 702-799 (7/1/2006)] Generators of waste (equal to or greater than 100 kg/mo) containing this contaminant, EPA hazardous waste number U071, must conform with USEPA regulations in storage, transportation, treatment and disposal of waste.Generators of waste (equal to or greater than 100 kg/mo) containing this contaminant, EPA hazardous waste number U071, must conform with USEPA regulations in storage, transportation, treatment and disposal of waste.... Halogenated compounds may be disposed of by incineration provided they are blended with other compatible wastes or fuels so that the composite contains less than 30% halogens and the heating value is from 7000 to 9000 BTU/lb. Liquid injection, rotary kiln, and fluidized bed incinerators are typically used to destroy liquid halogenated wastes. ... Temperatures of at least 2000-2200 °F and residence times /of more than 2 sec/ ... are required for the destruction of halogenated aromatic hydrocarbons. /Halogenated aromatic hydrocarbons/Potential candidate for rotary kiln incineration, with a temperature range of 820 to 1,600 °C, and a residence time of seconds. Also a potential candidate for liquid injection incineration, with a temperature range of 650 to 1,600 °C, and a residence time of 0.1 to 2 seconds.For more Disposal Methods (Complete) data for 1,3-DICHLOROBENZENE (6 total), please visit the HSDB record page.
Verschüttetes entsorgenPersonal protection: filter respirator for organic gases and particulates adapted to the airborne concentration of the substance. Collect leaking and spilled liquid in sealable containers as far as possible. Absorb remaining liquid in sand or inert absorbent. Then store and dispose of according to local regulations. Do NOT let this chemical enter the environment.
Preventive MeasuresSRP: The scientific literature for the use of contact lenses in industry is conflicting. The benefit 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.Contact lenses should not be worn when working with this chemical.If material not on fire and not involved in fire: Keep material out of water sources and sewers. Build dikes to contain flow as necessary. /o-Dichlorobenzene/Personnel protection: Avoid breathing vapors. Keep upwind. ... Avoid breathing vapors or dusts. Wash away any material which may have contacted the body with copious amounts of water or soap and water. /o-Dichlorobenzene/
Isolation and EvacuationExcerpt from ERG Guide 153 [Substances - Toxic and/or Corrosive (Combustible)]:
KörperbelastungDichlorobenzene isomers were detected in human blood samples taken from residents of Love Canal, NY at concns of 1-68 ng/L(1). The combined 1,3-, 1,4-dichlorobenzene concn in the breath of Los Angeles, CA residents was 3.5 and 2.8 ug/cu m and residents of Contra Costa, CA had a concn of 2.5 ug/cu m(2).A survey of human milk from the general population of Canada found 1,3-dichlorobenzene residues in 17 percent of the samples at an avg concn of 2 ppb(1). 1,3-Dichlorobenzene was detected in human milk at less than 5 ug/kg(2).
Gesundheitliche AuswirkungenAcute (short-term) exposure to 1,4-dichlorobenzene, via inhalation in humans, results in irritation of the skin, throat, and eyes. Chronic (long-term) 1,4-dichlorobenzene inhalation exposure in humans results in effects on the liver, skin, and central nervous system (CNS). No information is available on the reproductive, developmental, or carcinogenic effects of 1,4-dichlorobenzene in humans. A National Toxicology Program (NTP) study reported that 1,4-dichlorobenzene caused kidney tumors in male rats and liver tumors in both sexes of mice by gavage (experimentally placing the chemical in their stomachs).
ÖkotoxizitätswerteEC50Species: Scenedesmus subspicatus (Green algae, log growth phase)Conditions: freshwater, static, 24 °C, pH 8.0-9.3Concentration: 19000 ug/L for 48 hrEffect: population biomassConcentration: 30000 ug/L for 48 hrEffect: general population changesSpecies: Daphnia magna (Water flea)Conditions: freshwater, renewal, 25 °C, pH >7Concentration: 7 mg/L for 24 hrEffect: behavior, equilibriumSpecies: Daphnia magna (Water flea, age <24 hr)Conditions: freshwater, static, 25 °C, pH > or =7.0, dissolved oxygen > or = 58%Concentration: 7000 ug/L for 24 hrEffect: intoxication, immobilizationFor more Ecotoxicity Values (Complete) data for 1,3-DICHLOROBENZENE (33 total), please visit the HSDB record page.
UmweltverhaltenTERRESTRIAL FATE: Based on a recommended classification scheme(1), a Koc value of 300(2) indicates 1,3-dichlorobenzene is expected to have moderate mobility in soil(SRC). Volatilization of 1,3-dichlorobenzene is expected from moist soil surfaces given its Henry's Law constant of 2.8X10-3 atm-cu m/mole at 20 °C(3). Volatilization of 1,3-dichlorobenzene from dry soil surfaces is expected based on a vapor pressure of 2.15 mm Hg at 25 °C(4). A 0% theoretical BOD in sludge over a 4 week incubation period(5) suggests that biodegradation is expected to be slow in soil(SRC).AQUATIC FATE: Based on a recommended classification scheme(1), a Koc value of 300(2) indicates that 1,3-dichlorobenzene is expected to adsorb to suspended solids and sediment in water(SRC). 1,3-Dichlorobenzene is expected to volatilize from water surfaces(3) given its Henry's Law constant of 2.8X10-3 atm-cu m/mole at 20 °C(4). Using this Henry's Law constant and an estimation method(3), volatilization half-lives for a model river and model lake are 4 and 120 hours, respectively(SRC). According to a classification scheme(5), BCF values in the range of 60 to 740, measured in carp(6) and trout(7), suggest that bioconcentration in aquatic organisms is moderate to high. A theoretical BOD of 0% in sludge over a 4 week incubation period(6) suggests that biodegradation is expected to be slow in water under aerobic conditions. 1,3-Dichlorobenzene was slowly biodegraded by an acclimated anaerobic sediment slurry obtained from the Tsurumi River, Japan(8). The first-order biodegradation rate constant was 0.0016 days-1, corresponding to a half-life of about 433 days(8).ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), 1,3-dichlorobenzene, which has a vapor pressure of 2.15 mm Hg at 25 °C(2), is expected to exist in the vapor phase in the ambient atmosphere. Vapor-phase 1,3-dichlorobenzene 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 about 22 days(SRC), calculated from its rate constant of 7.2X10-13 cu cm/molecule-sec at 25 °C(3). 1,3-Dichlorobenzene does not contain chromophores that absorb at wavelengths >290 nm and therefore is not expected to undergo direct photolysis by sunlight(4).
Lebensmitteluntersuchungswerte1,3-Dichlorobenzene was identified, not quantified in 6 of 234 table ready foods in the US at an avg concn of 7.36 ppb(1). 1,3-Dichlorobenzene was detected in fruits (0.0044 ug/g) and vegetables and potatoes (0.0011 ug/g)(2). 1,3-Dichlorobenzene was detected in potato core at a concn of 0.096 ug/kg and pea seeds at a concn of 0.087 ug/kg(3).
Unerwünschte WirkungenNeurotoxin - Acute solvent syndrome
ExpositionspfadeThe substance can be absorbed into the body by inhalation and by ingestion.
Milk ConcentrationsTrace concn (less than 5 ug/kg) of 1,3-dichlorobenzene were detected in Yugoslavian human milk.ENVIRONMENTAL: A survey of human milk from the general population of Canada found 1,3-dichlorobenzene residues in 17 percent of the samples at an avg concn of 2 ppb(1). 1,3-Dichlorobenzene was detected in human milk at less than 5 ug/kg(2).1,3- and 1,4-DCB were detected together in whole human milk with mean and maximum concentrations of 6 and 75 ppb, respectively. These isomers were detected in milkfat samples at a mean concentration of 161 ppb and a maximum concentration of 4,180 ppb. 1,2-, 1,3-, and 1,4-DCB measured separately in whole human milk samples had concentrations of 9, <5, and 25 ppb, respectively, while the milk fat of these samples contained 230 ppb of 1,2-DCB and 640 ppb of 1,4-DCB.
ToxizitätsübersichtThe liver damage caused in rats by 1,3-dichlorobenzene is accompanied by induction of xenobiotic metabolizing enzymes of the phenobarbital type. In rats, a disturbance in thyroid homoeostasis can develop by hepatic enzyme induction: 1,3-dichlorobenzene induces glucuronosyl transferases. The conjugation of the thyroid hormones thyroxine (T4) and triiodothyronine (T3) is increased by the induction of glucuronosyl transferases. This leads to an increased release of T4 and T3 in the thyroid follicles.
Average Daily IntakeBased on monitoring data at three USA urban sites (Los Angeles, Phoenix, Oakland), the AVDI for 1,3-dichlorobenzene has been estimated to be 0.8-1.1 ug/day(1). The AVDI (via inhalation exposure only) of combined 1,2-, 1,3- and 1,4-dichlorobenzene isomers in the Netherlands is 7.0 ug/day(2).
Ökotoxizitätsauszüge/AQUATIC SPECIES/ ... For fathead minnows, chronic toxicities were estimated from 32-33 day embryo through early juvenile development exposures. The ranges between the highest no observable effect concentrations and lowest observed effect concentrations were 1000-2300, 570-1000, and 240-410 ug/L for 1,3-dichlorobenzene, 1,4-dichlorobenzene, 1,2,3,4-tetrachlorobenzene, respectively. The tissue concentrations associated with the no observable effect concentration and lowest observed effect concentration for 1,3-dichlorobenzene, 1,4-dichlorobenzene, and 1,2,3,4-tetrachlorobenzene were 120-160, 70-100, and 640-1000 ug/g, respectively. Mean bioconcentration factors obtained in these tests were 97, 10, 2400, 8400, and 22,000 for 1,3-dichlorobenzene, 1,4-dichlorobenzene, 1,2,3,4-tetrachlorobenzene, pentachlorobenzene, and hexachlorobenzene, respectively. 96 hr median lethal concentration values, obtained for juvenile fish, for 1,3-dichlorobenzene, 1,4-dichlorobenzene, and 1,2,3,4-tetrachlorobenzene were 7800, 4200, and 1100 ug/L, respectively./AQUATIC SPECIES/ A test was developed using Tetrahymena pyriformis in order to determine the toxicity of various chemicals. Precultured Tetrahymena pyriformis was exposed for 24 hr at 30 °C to various concentrations of chemicals. The concentration of the chemical, at which the proliferation of Tetrahymena pyriformis was restricted to one-half of the blank test (EC50), was determined. The method, applied to 57 chemicals, demonstrated that it could be used to detect the chemicals at low concentrations rapidly and with ease. The EC50 values showed a good relationship with 48 hr LC50 values for Himedaka (Oryzias latipes), and could be explained on the basis of the partition coefficient between water and n-octanol. EC50 for m-dichlorobenzene was 130 mg/L (880 umol/L)./AQUATIC SPECIES/ Developmental, genetic, and reproductive toxicities of benzene, chlorobenzene, and o-, m-, and p-dichlorobenzenes were investigated in sea urchin, Paracentrotus lividus. Toxicity order depended on whether the target organ was embryo or sperm. Benzene was active in sea urchin sperm causing developmental and mitotic abnormalities in offspring. Benzene also showed a significant increase in developmental defects following embryo exposure. For chlorobenzene, developmental defects were seen when the concentration was increased to 10(-4). M-Dichlorobenzene caused a strong increase in developmental defects and also in mitotic abnormalities.
Plant Concentrations1,3-Dichlorobenzene was identified, not quantified, in plant material grown in an Illinois coal refuse reclamation site(1).
TSCA-AnforderungenPursuant to section 8(d) of TSCA, EPA promulagated 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. Benzene, 1,3-dichloro- is included on this list. Effective date 10/4/82Sunset date 10/4/92.
LuftstandardsThis action promulgates standards of performance for equipment leaks of Volatile Organic Compounds (VOC) in the Synthetic Organic Chemical Manufacturing Industry (SOCMI). The intended effect of these standards is to require all newly constructed, modified, and reconstructed SOCMI process units to use the best demonstrated system of continuous emission reduction for equipment leaks of VOC, considering costs, non air quality health and environmental impact and energy requirements. m-Dichlorobenzene is produced, as an intermediate or a final product, by process units covered under this subpart.
CERCLA-MeldepflichtmengenPersons in charge of vessels or facilities are required to notify the National Response Center (NRC) immediately, when there is a release of this designated hazardous substance, in an amount equal to or greater than its reportable quantity of 100 lb or 45.4 kg. The toll free number of the NRC is (800) 424-8802. The rule for determining when notification is required is stated in 40 CFR 302.4 (section IV. D.3.b).
Clean Water Act AnforderungenToxic pollutant designated pursuant to section 307(a)(1) of the Federal Water Pollution Control Act and is subject to effluent limitations. /Dichlorobenznes (1,2-, 1,3- and 1,4-dichlorobenzenes)/
State Drinking Water Standards(NJ) NEW JERSEY 600 ug/l
Landesrichtlinien für Trinkwasser(AZ) ARIZONA 620 ug/l(CT) CONNECTICUT 210 ug/l(ME) MAINE 60 ug/l(WI) WISCONSIN 1250 ug/l
Federal Drinking Water StandardsEPA 600 ug/l
Bundesrichtlinien für TrinkwasserEPA 600 ug/l
Wassergefährdungsklasse (WGK)2
TSCA-Inventar-StatusTSCA listed
UN-TransportnummerUN 3082 9/PG 3
Zollcode29036990
RTECS-Nr.CZ4499000
R-Sätze (R)22-51/53-39/23/24/25-23/24/25-11
ToxizitätLD50 orally in Rabbit: 580 mg/kg
GefahrensymboleXn,N,T,F
Sicherheitshinweise (S)61-45-36/37-16-7
Gefahrenklasse6.1(b)Acute Tox. 4 OralAquatic Chronic 2
VerpackungsgruppeIII
Lagerklasse10 - Combustible liquids
Gefahrstoffdaten541-73-1(Hazardous Substances Data)
Selbstentzündungstemperatur>500 °C