ChemicalBook > Product Catalog > Organic Chemistry > Amides > Naphthenic amines derivatives > 3,3'-Dichlorobenzidine
3,3'-Dichlorobenzidine Chemical Properties
- Melting point:132.5°C
- Boiling point:398.89°C (rough estimate)
- Density 1.3171 (rough estimate)
- vapor pressure 4.2 x 10-7 at 25 °C (estimated, Howard, 1989)
- refractive index 1.6400 (estimate)
- Flash point:10 °C
- storage temp. 2-8°C
- solubility Soluble in ethanol, benzene, and glacial acetic acid (Windholz et al., 1983)
- form neat
- Water Solubility 3.114mg/L(25 ºC)
- Henry's Law Constant4.5 x 10-8 atm?m3/mol at 25 °C (estimated, Howard, 1989)
- Stability:Stable. Incompatible with strong oxidizing agents.
- CAS DataBase Reference91-94-1(CAS DataBase Reference)
- IARC2B (Vol. 29, Sup 7) 1987
- NIST Chemistry Reference[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dichloro-(91-94-1)
- EPA Substance Registry System3,3'-Dichlorobenzidine (91-94-1)
- Hazard Codes T,N,F
- Risk Statements 45-21-43-50/53-52/53-39/23/24/25-23/24/25-11-51/53
- Safety Statements 53-45-60-61-36/37-16-7
- RIDADR UN 3077 9/PG 3
- WGK Germany 3
- RTECS DD0550000
- HazardClass IRRITANT
- HS Code 29215900
- Hazardous Substances Data91-94-1(Hazardous Substances Data)
- ToxicityAcute oral LD50 for rats as free base or dihydrochloride are 7,070 and 3,820, respectively (Gerade and Gerade, 1974).
3,3'-Dichlorobenzidine Usage And Synthesis
- Chemical Propertiescolourless to white crystalline solid
- Chemical Properties3,3’-Dichlorobenzidine is a gray or purple crystalline solid.
- Physical propertiesColorless to grayish-purple needles or crystals with a mild or pungent odor
- UsesIntermediate in the manufacture of azo dyes and pigments for printing inks, textiles, paints, plastics, and crayons; curing agent for isocyanate-terminated polymers and resins; rubber compounding ingredient; analytical determination of gold; formerly used as chemical intermediate for direct red 61 dye.
- UsesUsed in the production of yellow and red pigments for the printing ink, textile, paper, paint, rubber, plastic, and related industries
- General DescriptionGray to purple crystalline powder. Insoluble in water. Very toxic. Used in the dye industry, curing agent for isocyanate terminated resins.
- Air & Water ReactionsInsoluble in water.
- Reactivity ProfileA halogenated amine. Amines are chemical bases. They neutralize acids to form salts plus water. These acid-base reactions are exothermic. The amount of heat that is evolved per mole of amine in a neutralization is largely independent of the strength of the amine as a base. Amines may be incompatible with isocyanates, halogenated organics, peroxides, phenols (acidic), epoxides, anhydrides, and acid halides. Flammable gaseous hydrogen is generated by amines in combination with strong reducing agents, such as hydrides.
- Health Hazard3,3'-Dichlorobenzidine (DCB) is carcinogenic in several animal species.
- Fire HazardCombustible.
- Safety ProfileConfirmed carcinogen with experimental carcinogenic and tumorigenic data. Human mutation data reported. When heated to decomposition it emits very toxic fumes of Cl and NOx.
- Potential ExposureA halide-and amine-substituted aromatic compound used in the dye industry, curing agent for isocyanate terminated resins. The major uses of dichlorobenzidine are in the manufacture of pigments for printing ink, textiles, plastics, and crayons and as a curing agent for solid urethane plastics. There are no substitutes for many of its uses. Additional groups that may be at risk include workers in the printing or graphic arts professions handling the 3,3’-DCB-based azo pigments. 3,3’-DCB may be present as an impurity in the pigments, and there is some evidence that 3,3’-DCB may be metabolically liberated from the azo pigment
- CarcinogenicityStudies in several test systems have shown
DCB to be genotoxic in vitro and in vivo and
suggest that this effect most likely mediates the
carcinogenicity of the chemical. In vitro, DCB
has induced sister chromatid exchanges,
unscheduled DNA synthesis, and positive
responses in bacterial Salmonella assays; in vivo
DCB induced micronuclei in polychromatic
erythrocytes in male mice and fetuses.
Because of demonstrated potent carcinogenicity in multiple animal species, evidence of genotoxicity, and structural relationship to the known bladder carcinogen benzidine, DCB should be regarded as a probable human carcinogen and exposure by any route should be avoided.
3,3￠-Dichlorobenzidene has no threshold limit value (TLV) exposure limit and is classified as an A3, confirmed animal carcinogen with unknown relevance to humans, and a notation for skin absorption.
- SourceSynthesized from o-chloronitrobenzene in the presence of NaOH and zinc dust (Shriner et al., 1978).
- Environmental FateBiological. In activated sludge, 2.7% mineralized to carbon dioxide after 5 d (Freitag et al.,
1985). Sikka et al. (1978) reported 3,3′-dichlorobenzidine is resistant to degradation by indigenous
aquatic microbial communities in a 4-wk period. Under aerobic and anaerobic conditions,
3,3′-dichlorobenzidine is mineralized very slowly (Boyd et al., 1984; Chung and Boyd, 1987).
Nyman et al. (1997a) studied the transformation of 3,3′-dichlorobenzidine under laboratory
controlled conditions at 20 °C. Wet sediment (50 g) and water (150 mL) from Lake Macatawa,
Holland, MI were placed in glass serum bottles and purged with nitrogen to ensure anaerobic
conditions to which 3,3′-dichlorobenzidine was added. The bottles were incubated in the dark at
20 °C for 12 months. Soil and water samples were retrieved periodically for transformation
product identification using HPLC. The investigators identified 3-chlorobenzidine as a transient
metabolite from the biological transformation of 3,3′-dichlorobenzidine. 3-Chlorobenzidine
rapidly dechlorinated forming the end product benzidine.
Photolytic. An aqueous solution subjected to UV radiation caused a rapid degradation (half-life <10 min) to monochlorobenzidine, benzidine, and several unidentified, brightly-colored, waterinsoluble chromophores (Banerjee et al., 1978). In a similar experiment, 3,3′-dichlorobenzidine in an aqueous solution was subjected to radiation at λ=310 nm for approximately 15 min. During the period of irradiation, concentrations of 3,3′-dichlorobenzidine decreased rapidly. 3-Chlorobenzidine formed as a transient intermediate which underwent dechlorination forming a benzidine, a stable photoproduct. Depending upon the wavelength used, the benzidine yields ranged from 8 to 12% of the total 3-chlorobenzidine transformed (Nyman et al., 1997). A carbon dioxide yield of 41.2% was achieved when 3,3′-dichlorobenzidine adsorbed on silica gel was irradiated with light (λ >290 nm) for 17 h (Freitag et al., 1985).
Chemical/Physical. 3,3′-Dichlorobenzidine will not hydrolyze to any reasonable extent (Kollig, 1993).
At influent concentrations of 1.0, 0.1, 0.01, and 0.001 mg/L, the GAC adsorption capacities at were 300, 190, 120, and 73 mg/g, respectively (Dobbs and Cohen, 1980).
- ShippingUN2811 Toxic solids, organic, n.o.s., Hazard Class: 6.1; Labels: 6.1-Poisonous materials, Technical Name Required
- Purification MethodsCrystallise the benzidine from EtOH, pet ether (m 133o) or *benzene. [Beilstein 13 H 234, 13 I 67, 13 II 106, 13 III 477, 13 IV 384.] CARCINOGEN.
- IncompatibilitiesIncompatible with oxidizers (chlorates, nitrates, peroxides, permanganates, perchlorates, chlorine, bromine, fluorine, etc.); contact may cause fires or explosions. Keep away from alkaline materials, strong bases, strong acids, oxoacids, and epoxides. Achemical base: neutralize acids to form salts plus water with an exothermic reaction. May be incompatible with isocyanates, halogenated organics, peroxides, phenols (acidic), epoxides, anhydrides, and acid halides. Flammable gaseous hydrogen is generatedby amines in combination with strong reducing agents such as hydrides, nitrides, alkali metals, and sulfides.
- Waste DisposalIncineration (816C, 0.5 second for primary combustion; 1204C, 1.0 second for secondary combustion). The formation of elemental chlorine can be prevented through injection of steam ormethane into the combustion process. nitrogen oxides may be abated through the use of thermal or catalytic devices. 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
3,3'-Dichlorobenzidine Preparation Products And Raw materials
- Pigment Yellow 12 MIXTURE NO 7-BENZIDINES 3,3'-dichlorobenzidine sulphate 3,3'-DICHLOROBENZIDINE (RING-D6),3,3'-DICHLOROBENZIDINE-D6 (RINGS-D6) Biphenyl-4,4'-dicarboxylic acid Ethylenediamine Amines, N-tallow alkyltrimethylenedi- HYDRAZINE 4,4'-Ethylenedianiline 3,3'-Dichlorobenzidine 4,4'-Dimethylbiphenyl 3,3',5,5'-Tetramethylbenzidine dihydrochloride Benzidine dihydrochloride 2,3-Dichloroaniline Dichlormid DICHLORO BENZIDINE DI HYDROCHLORIDE (DCB) Benzidine 4,4'-Bis(chloromethyl)-1,1'-biphenyl
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