106-46-7 Hazards Identification
Pictogram(s):


Signal:
Warning
GHS Hazard Statements:
H319: Causes serious eye irritation [Warning Serious eye damage/eye irritation]
H351: Suspected of causing cancer [Warning Carcinogenicity]
H400: Very toxic to aquatic life [Warning Hazardous to the aquatic environment, acute hazard]
H410: Very toxic to aquatic life with long lasting effects [Warning Hazardous to the aquatic environment, long-term hazard]
Precautionary Statement Codes:
P203, P264+P265, P273, P280, P305+P351+P338, P318, P337+P317, P391, P405, and P501
Hazard Classes and Categories:
Carc. 2
Eye Irrit. 2
Aquatic Acute 1
Aquatic Chronic 1
Eye Irrit. 2 (100%)
Carc. 2 (100%)
Aquatic Acute 1 (93.06%)
Aquatic Chronic 1 (100%)
Carcinogenicity - category 2
Eye irritation - category 2
Hazardous to the aquatic environment (acute) - category 1
Hazardous to the aquatic environment (chronic) - category 1
Serious eye damage/eye irritation - Category 2
Skin sensitization - Category 1
Carcinogenicity - Category 2
Reproductive toxicity - Category 2
Specific target organ toxicity - Single exposure - Category 1 (central nervous system, blood system, liver),
Category 3 (respiratory tract irritation)
Specific target organ toxicity - Repeated exposure - Category 1 (nervous system, liver, blood system),
Category 2 (respiratory system, kidney)
Hazardous to the aquatic environment (Acute) - Category 1
Hazardous to the aquatic environment (Long-term) - Category 1
Reproductive toxicity - Category 1B
Specific target organ toxicity - Single exposure - Category 1 (blood, liver),
Category 3 (respiratory tract irritation)
Specific target organ toxicity - Repeated exposure - Category 1 (respiratory system, liver, nervous system, blood),
Category 2 (kidney)
Acute toxicity (Oral) - Category 5
Skin corrosion/irritation - Category 3
Serious eye damage/eye irritation - Category 2B
Germ cell mutagenicity - Category 2
Specific target organ toxicity - Single exposure - Category 1 (blood system, liver)
Specific target organ toxicity - Repeated exposure - Category 1 (respiratory system, liver, nervous system),
Category 2 (kidney)
Carcinogens, Flammable - 2nd degree
Hazards Summary:
The primary exposure to 1,4-dichlorobenzene is from breathing contaminated indoor air. Acute (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). EPA has classified 1,4- dichlorobenzene as a Group C, possible human carcinogen.
106-46-7 Usage
Uses
1,4-Dichlorobenzene is used in various applications across different industries due to its properties and characteristics. Some of its primary uses include:
Used in Pest Control:
1,4-Dichlorobenzene is used as a moth repellent, making it a common ingredient in mothballs and deodorant cakes. It is used to protect stored clothes, fabrics, and other materials from damage caused by moths and other insects.
Used in Deodorization:
1,4-Dichlorobenzene is used as a space deodorant in various products, such as room deodorizers, toilet bowl blocks, and diaper pail deodorizers. Its strong odor helps to mask and neutralize unpleasant smells in these environments.
Used in Agriculture:
1,4-Dichlorobenzene is used as an insecticide on fruit, helping to protect crops from damage caused by insects. It is also used to control mold and mildew growth on tobacco seeds, leather, and certain fabrics.
Used in Beekeeping:
1,4-Dichlorobenzene is approved for controlling wax moths in empty, stored beehives, helping to protect the hives from infestation and damage.
Used in Chemical Production:
1,4-Dichlorobenzene serves as an intermediate in the production of various chemicals, including those used in the manufacturing of plastics for electronic components.
Used in Fumigation:
As a fumigant, 1,4-dichlorobenzene is used to control pests in various settings, such as agricultural storage facilities and other areas where pests may be a problem.
Preparation
1,4-Dichlorobenzene was first produced commercially in the United States in 1915 (IARC 1982). It is produced by reacting liquid benzene with gaseous chlorine in the presence of a catalyst at moderate temperature and atmospheric pressure. 1,4-Dichlorobenzene is used mainly as a fumigant for the control of moths, molds, and mildews, and as a space deodorant for toilets and refuse containers.
Synthesis Reference(s)
Chemistry Letters, 8, p. 939, 1979The Journal of Organic Chemistry, 48, p. 250, 1983 DOI: 10.1021/jo00150a020Tetrahedron Letters, 23, p. 371, 1982 DOI: 10.1016/S0040-4039(00)86833-1
Air & Water Reactions
Insoluble in water.
Reactivity Profile
1,4-Dichlorobenzene is incompatible with oxidizing agents. 1,4-Dichlorobenzene is also incompatible with aluminum and its alloys. 1,4-Dichlorobenzene liquefies when mixed with camphor, phenol and salol. 1,4-Dichlorobenzene will attack some forms of plastics, rubber and coatings. .
Health Hazard
Toxic symptoms are headache, weakness,dizziness, nausea, vomiting, diarrhea, loss ofweight, and injury to liver and kidney. Thesesymptoms occur from repeated inhalationof high concentrations of vapors or fromingestion. The vapors are an irritant to theeyes, throat, and skin. Chronic exposure maycause jaundice and cirrhosis. The oral LD50value in mice is in the range 3000 mg/kg.The fatal oral dose in humans is estimated tobe 40–50 g. Carcinogenic studies on animalshave not produced adequate evidence of anycancer-causing action.
Fire Hazard
Special Hazards of Combustion Products: Vapors are irritating. Toxic chlorine, hydrogen chloride, and phosgene gases may be generated in fires.
Trade name
DowTHERM?; EVOLA; PARACIDE?;
PARA CRYSTALS?; PARADI?; PARADOW?;
PARAMOTH?; PARANUGGETS?; PARAZENE?;
PERSIA-PERAZOL?; SANTOCHLOR?; Mixed isomers:
DILATIN DBI?; MOTTENSCHUTZMITTEL
EVAU P?; MOTT-EX?; TOTAMOTT?
Safety Profile
There is limited evidence that 1,4-dichlorobenzene can damage a developing fetus. Exposure can damage the lungs, liver, kidneys, and blood cells, causing anemia; it can also cause swelling of the eyes, hands, and feet. It can damage the nervous system, causing weakness, trembling, and numbness in the arms and legs. It may cause a skin allergy, which when developed can cause itching and a skin rash. Higher levels of the chemical in air, such as the levels that are sometimes associated with industrial exposure, can cause headaches, nausea, clumsiness, slurred speech, and dizziness. Levels that would result in death would be associated with an odor so intense that it would be very unpleasant, if not intolerable, and would serve as a danger warning. In industrial situations, workers exposed to 1,4-dichlorobenzene at high levels are usually directed to wear respirators. Workers involved in the production of the chemical may be exposed to concentrations significantly higher than those encountered by the general population. High exposure levels may result from some consumer products of moth repellents and room deodorizers. Approximately 95% of the environmental release of 1,4-dichlorobenzene occurs during its use, rather than during its manufacture or processing.
Potential Exposure
The major uses of o-DCB are as
a process solvent in the manufacturing of toluene diisocyanate and as an intermediate in the synthesis of dyestuffs,
herbicides, and degreasers. p-Dichlorbenzene is used
primarily as a moth repellant, a mildew control agent;
space deodorant; and in insecticides, which accounts for
90% of the total production of this isomer. Information is
not available concerning the production and use of m-DCB.
However, it may occur as a contaminant of o-or p-DCB
formulations. Both o-and p-isomers are produced almost
entirely as by-products during the production of
monochlorobenzene
Carcinogenicity
1,4-Dichlorobenzene is reasonably anticipated to be a human carcinogen based on sufficient evidence of carcinogenicity from studies in experimental animals.
Metabolic pathway
1,4-Dichlorobenzene undergoes degradation by the
Xanthobacter flavus 14p1 isolated from river sludge by
selective enrichment with 1,4-dichlorobenzene,
resulting in the degradation products 3,6-dichloro-cis-
1,2-dihydroxycyclohexa-3,5-diene and 3,6-
dichlorocatechol. 2,5-Dichloromuconic acid and 2-
chloromaleylacetic acid, as well as the decarboxylation
product 2-chloroacetoacrylic acid, are identified after
enzymatic conversion of 3,6-dichlorocatechol.
Shipping
m-DCB: UN2810 Toxic liquids, organic, n.o.s.,
Hazard Class: 6.1; Labels: 6.1-Poisonous materials,
Technical Name Required. United States DOT Regulated
Marine Pollutant. UN3077 Environmentally hazardous
substances, solis, n.o.s., Hazard class: 9; Labels:
9-Miscellaneous hazardous material, Technical NameRequired. UN3082 Environmentally hazardous substances,
liquid, n.o.s., Hazard class: 9; Labels: 9-Miscellaneous hazardous material, Technical Name Required
Purification Methods
o-Dichlorobenzene is a common impurity. The p-isomer has been purified by steam distillation, crystallisation from EtOH or boiling MeOH, air-dried and dried in the dark under vacuum. It has also been purified by zone refining. [Beilstein 5 IV 658.]
Incompatibilities
For o-DCB and m-DCB: acid fumes,
chlorides, strong oxidizers; hot aluminum, or aluminum
alloys. For p-DCB: Strong oxidizers; although, incompatibilities for this chemical may also include other materials
listed for o-DCB.
Waste Disposal
Incineration, preferably
after mixing with another combustible fuel. Care must be
exercised to assure complete combustion to prevent
the formation of phosgene. An acid scrubber is necessary
to remove the halo acids produced. Consult with
environmental regulatory agencies for guidance on
acceptable disposal practices. Generators of waste containing
this contaminant (≥100 kg/mo) must conform with EPA
regulations governing storage, transportation, treatment, and
waste disposal
Check Digit Verification of cas no
The CAS Registry Mumber 106-46-7 includes 6 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 3 digits, 1,0 and 6 respectively; the second part has 2 digits, 4 and 6 respectively.
Calculate Digit Verification of CAS Registry Number 106-46:
(5*1)+(4*0)+(3*6)+(2*4)+(1*6)=37
37 % 10 = 7
So 106-46-7 is a valid CAS Registry Number.
106-46-7Relevant academic research and scientific papers
Marques, Carlos Alberto,Selva, Maurizio,Tundo, Pietro
, p. 5256 - 5260 (1993)
A multiphase system consisting of a hydrocarbon solvent, a strong alkaline solution, and a quaternary onium salt, in the presence of a Pd/C catalyst with hydrogen at atmospheric pressure, allows the rapid and progressive displacement of the chlorine atoms from polyhalogenated benzenes.The onium salt in this case constitutes a third liquid phase in which the reaction takes place.At 50 deg C, 1,2,4,5-tetrachlorobenzene is reduced to benzene in 30 min using a Pd/Cl molar ratio of 1/130.Halogenated compounds are partitioned between the hydrocarbon solution and the liquid phase of the phase-transfer agent; rapid removal of HCl adsorbed on Pd/C is effected by neutralization with the alkaline solution.The enhancement of the reaction rate compared with the known methods might be attributed to the facile adsorption of H2 by the catalyst under the reaction conditions.Different reaction rates result in the reduction of the three isomeric chlorotoluenes, whether the reaction is carried out in the presence or absence of the onium salt.
Freeman, Peter K.,Srinivasa, Ramanujan,Campbell, J.-A.,Deinzer, Max L.
, p. 5531 - 5536 (1986)
Negative chemical ionization mass spectroscopy of polychlorobenzenes reveals that parent radical anion undergoes fission by two pathways--(a) cleavage to aryl radical plus Cl- (kCl-) and (b) fission to aryl carbanion plus chlorine atom (kCl*)--and that there is a Hammett relationship between log(kCl*/kCl-) and Σ?.The dependence of the reciprocal of the quantum yield for photochemical dechlorination of trichlorobenzenes through pentachlorobenzene upon the reciprocal of the concentration of the electron donor, triethylamine, was analyzed in order to establish the optimum concentration for radical anion formation.The regiochemistries for the photodechlorination of trichlorobenzenes through pentachlorobenzene in the presence of triethylamine, with and without acetophenone sensitizer, were determined and found to be very similar and quite different from those observed for the direct photolysis in the absence of triethylamine for the comparison cases of 1,2,3,5-tetrachloro- and pentachlorobenzene.The regiochemistry of the fragmentation of polychlorobenzene radical anion to aryl radical plus chloride ion is rationalized in terms of a bent transition state.
Hirota, Minoru,Nakada, Masahiro
, p. 2926 - 2933 (1992)
Polychloro- and polybromobenzenes were photolyzed in acetonitrile and perfluorohexane.Photolyses of polychlorobenzenes in acetonitrile gave isomerized products in addition to dechlorinated products, which appeared exclusively in the photolyses in hexane and other solvents carrying hydrogen atoms active to hydrogen abstraction.The photolyses in perfluorohexane gave isomerized products to a lesser extent.The reaction in this solvent gave predominantly polyhalobiphenyls which are assumed to be produced through coupling.Without exception the isomerized products have the structure which can be expected to be formed via 1,3-migration of chlorine atom, though it is not sure at present whether it takes place actually.The isomerization was shown to proceed intramolecularly.Some evidence and theoretical rationalization in favor of the 1.3-chlorine migration mechanism are given.
Huizinga,Scholten,Wortel,van Bekkum
, p. 3809 - 3812 (1980)
ZSM-5 type zeolites and related high siliceous materials induce addition of chlorine to benzene yielding hexachlorocyclohexanes, whereas Y-type zeolites favour substitution to yield chlorobenzenes.
Morisaki, Kenji,Miura, Yasuki,Abe, Kazuhisa,Hirota, Minoru,Nakada, Masahiro
, p. 1589 - 1592 (1987)
Several polychlorobenzenes were irradiated by ultraviolet light (254 nm) in acetonitrile and the products were determined by gas chromatography.In addition to the abstraction of hydrogen atom from the solvent, photo-isomerization was shown to proceed giving isomeric polychlorobenzenes one of which chlorine atoms migrated to meta to the original position.The meta-rearrangement was rationalized by an MNDO calculation on o-chlorophenyl free radical.
Nakamura, Tadashi,Shinoda, Kiyonori,Yasuda, Kensei
, p. 1881 - 1882 (1992)
Benzene was chlorinated by using L type zeolite into p-dichlorobenzene (p-DCB) in a high yield in the presence of 1,2-dichloroethane (EDC) and oxygen.
Hao, Cui Xiang,Nakada, Masahiro,Yamaguchi, Tatsuaki,Fukushi, Sachio,Hirota, Minoru
, p. 1707 - 1710 (1985)
Dechlorination of polychlorobenzenes over Fe3O4 was investigated by a pulse micro-reactor technique.Dechlorinations of various polychlorobenzenes in hexane and cyclohexane were carried out in the gas phase at the temperatures ranging from 498 to 623 K.In the presence of such hydrogen donating solvents, dechlorination was shown to proceed almost exclusively.The relative rates of dechlorination were measured by gas chromatography.It was found that the solvents used to dissolve polychlorobenzenes plays a role of a hydrogen donor in this reaction.The different rates among unequivalent chlorine atoms in a molecule were interpreted by the effect of steric acceleration caused by the neighboring chlorine atom(s).The reaction will probably proceed via hydrogenolytic cleavage of C-Cl bonds.
Kimura, Masaru,Okamoto, Hideki,Kura, Hisatoshi,Okazaki, Ayumi,Nagayasu, Eiji,et al.
, p. 3908 - 3911 (1988)
Electronic oxidative bisdecarboxylation of photoadducts of 2,5-dihalo-1,2-dihydrophthalic anhydride and anthracene gave the corresponding energy-rich heterodimers 12 and 13.The quantum yields of the formation of the excited anthracene from 12 and 13 by the irradiation of 280-nm light were 0.65 and 0.25, respectively.We assumed that the heterodimers of 12 and 13 form biradicaloid intermediates during thermal retro cycloaddition and consumed their stored energy without any visible light.However, we observed emission light from 340 to 460 nm through a glass filter and the formation of anthracene using Nd-YAG laser IR light (1.06 μm) by the multiphoton absorption, when fine powders of 12 and 13 were used.
Kubatova, Alena,Lagadec, Arnaud J. M.,Hawthorne, Steven B.
, p. 1337 - 1343 (2002)
Pure water has been used to dechlorinate aliphatic organics without the need for catalysts or other additives. Dehydrohalogenation (loss of HCl with the formation of a double bond) occurred at temperatures as low as 105-200 °C for 1,1,2,2-tetrachloroethane, lindane (1,2,3,4,5,6-hexachlorocyclohexane, γ-isomer), and dieldrin (1,2,3,4,10,10-hexachloro-6,7-epoxy-1,4,4a,5,6,7,8,8a-octahydro-endo, exo-1,4:5,8-dimethanonaphthalene). Complete loss of the parent compounds was achieved in less than 1 h at 150, 200, and 300 °C for 1,1,2,2-tetrachloroethane, lindane, and dieldrin, respectively. The initial dechlorination of lindane had an activation energy of 84 kJ mol-1 with an Arrhenius pre-exponential factor of 1.5 x 106 s-1. Dehydrohalogenation of lindane formed trichlorobenzenes, followed by subsequent hydrolysis and hydride/chloride exchange to form chlorophenols, lower chlorobenzenes, and phenol as the major final product. Reaction of poly(vinyl chloride) at 300 °C for 1 h formed aromatic hydrocarbons ranging from benzene to anthracene and a char residue with a ca. 1:1 carbon-to-hydrogen ratio (mol/mol). The residue contained 1 wt % of chlorine compared to 57 wt % chlorine in the original polymer. All compounds tested yielded chloride ion as the major product (at higher temperatures), indicating that complete dechlorination of some aliphatic organochlorines may be feasible.
Stiles Martin
, p. 5381 - 5385 (1994)
Nickel(II) complexes 1 and 2 are soluble catalysts for reductive dehalogenation of aromatic bromides and polychlorobenzenes by sodium borohydride at 25-45 deg C in aqueous ethanol, aqueous acetonitrile, or ethanol-acetonitrile.Deuterium incorporation experiments, and rate retardation by added cumene, point to a radical-chain mechanism.Hydrazine can replace borohydride as a source of reducing power.Reactivity toward this reducing system increases with increasing halogen content of the substrate, a finding that parallels prior observations of dechlorination in natural sediments.