ChemicalBook
Chinese English Japanese Germany Korea

나이트로벤젠

나이트로벤젠
나이트로벤젠 구조식 이미지
카스 번호:
98-95-3
한글명:
나이트로벤젠
동의어(한글):
나이트로벤젠(니트로벤젠);니트로벤젠;니트로벤젠,액체;니트로벤졸;미르반기름;미르반의기름;미르반의정제물;벤젠,니트로-;나이트로벤젠
상품명:
Nitrobenzene
동의어(영문):
NCI-C60082;NITROBENZOL;MYRBANE OIL;MIRBANE OIL;Nitrobenzen;oilofmyrbane;NITROBENZENE;Nitrobenzeen;nitro-benzen;Mitrobenzole
CBNumber:
CB7854756
분자식:
C6H5NO2
포뮬러 무게:
123.11
MOL 파일:
98-95-3.mol

나이트로벤젠 속성

녹는점
5-6 °C(lit.)
끓는 점
210-211 °C(lit.)
밀도
1.205
증기 밀도
4.2 (vs air)
증기압
0.15 mm Hg ( 20 °C)
굴절률
n20/D 1.551(lit.)
인화점
190 °F
저장 조건
2-8°C
용해도
1.90g/l
산도 계수 (pKa)
3.98(at 0℃)
물리적 상태
Liquid
색상
Clear yellow
수소이온지수(pH)
8.1 (1g/l, H2O, 20℃)
상대극성
4.5
폭발한계
1.8-40%(V)
수용성
slightly soluble
Merck
14,6588
BRN
507540
Henry's Law Constant
9.86 at 25 °C (thermodynamic method-GC/UV spectrophotometry, Altschuh et al., 1999)
노출 한도
TLV-TWA 1 ppm (~5 mg/m3) (ACGIH, MSHA, and OSHA); IDLH 200 ppm (NIOSH).
안정성
Stable. Incompatible with strong oxidizing agents, strong reducing agents, strong bases. Flammable. Note wide explosion limits.
CAS 데이터베이스
98-95-3(CAS DataBase Reference)
NIST
Benzene, nitro-(98-95-3)
EPA
Benzene, nitro-(98-95-3)
안전
  • 위험 및 안전 성명
  • 위험 및 사전주의 사항 (GHS)
위험품 표기 T,N,F,Xn
위험 카페고리 넘버 23/24/25-40-48/23/24-51/53-62-39/23/24/25-11-36/37/38-60-52/53-48/23/24/25-36-20/21/22
안전지침서 28-36/37-45-61-28A-16-7-27-53-26
유엔번호(UN No.) UN 1662 6.1/PG 2
WGK 독일 2
RTECS 번호 DA6475000
자연 발화 온도 899 °F
TSCA Yes
위험 등급 6.1
포장분류 II
HS 번호 29042010
유해 물질 데이터 98-95-3(Hazardous Substances Data)
독성 LD50 orally in rats: 600 mg/kg (PB91-108398)
그림문자(GHS):
신호 어: Danger
유해·위험 문구:
암호 유해·위험 문구 위험 등급 범주 신호 어 그림 문자 P- 코드
H225 고인화성 액체 및 증기 인화성 액체 구분 2 위험 P210,P233, P240, P241, P242, P243,P280, P303+ P361+P353, P370+P378,P403+P235, P501
H227 가연성 액체 인화성 액체 구분 4 경고 P210, P280, P370+P378, P403+P235,P501
H300 삼키면 치명적임 급성 독성 물질 - 경구 구분 1,2 위험 P264, P270, P301+P310, P321, P330,P405, P501
H310 피부와 접촉하면 치명적임 급성 독성 물질 - 경피 구분 1,2 위험 P262, P264, P270, P280, P302+P350,P310, P322, P361, P363, P405, P501
H330 흡입하면 치명적임 급성 독성 물질 흡입 구분 1, 2 위험 P260, P271, P284, P304+P340, P310,P320, P403+P233, P405, P501
H351 암을 일으킬 것으로 의심됨 (노출되어도 암을 일으키지 않는다는 결정적인 증거가 있는 노출경로가 있다면 노출경로 기재) 발암성 물질 구분 2 경고 P201, P202, P281, P308+P313, P405,P501
H361 태아 또는 생식능력에 손상을 일으킬 것으로 의심됨 생식독성 물질 구분 2 경고 P201, P202, P281, P308+P313, P405,P501
H370 장기(또는, 영향을 받은 알려진 모든 장기를 명시)에 손상을 일으킴(노출되어도 특정 표적장기 독성을 일으키지 않는다는 결정적인 노출경로가 있다면 노출경로를 기재) 특정 표적장기 독성 - 1회 노출 구분 1 위험 P260, P264, P270, P307+P311, P321,P405, P501
H372 장기간 또는 반복 노출되면 장기(또는, 영향을 받은 알려진 모든 장기를 명시)에 손상을 일으킴 특정 표적장기 독성 - 반복 노출 구분 1 위험 P260, P264, P270, P314, P501
H401 수생생물에 유독함 수생 환경유해성 물질 - 급성 구분 2 P273, P501
H411 장기적 영향에 의해 수생생물에 유독함 수생 환경유해성 물질 - 만성 구분 2
H412 장기적 영향에 의해 수생생물에 유해함 수생 환경유해성 물질 - 만성 구분 3 P273, P501
예방조치문구:
P201 사용 전 취급 설명서를 확보하시오.
P210 열·스파크·화염·고열로부터 멀리하시오 - 금연 하시오.
P280 보호장갑/보호의/보안경/안면보호구를 착용하시오.
P320 긴급히 (…) 처치를 하시오.
P330 입을 씻어내시오.
P304+P340 흡입하면 신선한 공기가 있는 곳으로 옮기고 호흡하기 쉬운 자세로 안정을 취하시오.
P308+P313 노출 또는 접촉이 우려되면 의학적인 조치· 조언를 구하시오.
P370+P378 화재 시 불을 끄기 위해 (Section 5. 폭발, 화재시 대처방법의 적절한 소화제)을(를) 사용하시오.
P405 밀봉하여 저장하시오.
P403+P235 환기가 잘 되는 곳에 보관하고 저온으로 유지하시오.

나이트로벤젠 C화학적 특성, 용도, 생산

화학적 성질

yellow liquid

화학적 성질

Nitrobenzene is a pale yellow to dark brown oily liquid whose odor resembles bitter almonds (or black paste shoe polish).

화학적 성질

Aromatic nitro compounds mixed with nitrobenzene are explosives of high sensitivity and detonation velocities and are spark detonatable).

물리적 성질

Clear, light yellow to brown, oily liquid with an almond-like or shoe polish odor. May darken on exposure to air. An experimentally determined odor threshold concentration of 4.7 ppbv was reported by Leonardos et al. (1969). A detection odor threshold concentration of 9.6 mg/m3 (1.9 ppmv) was determined by Katz and Talbert (1930).

용도

Most nitrobenzene (97%) is used in the manufacture of aniline (IARC 1996, HSDB 2009). Miscellaneous uses include the manufacture of benzidine, quinoline, azobenzene, pyroxylin compounds, isocyanates, pesticides, rubber chemicals, pharmaceuticals, and dyes such as nigrosines and magenta. Nitrobenzene is found in soaps and shoe and metal polishes and is used as a solvent for cellulose ester, in modifying esterification of cellulose acetate, and in refining lubricating oils (HSDB 2009). Nitrobenzene also is used as a solvent in petroleum refining and the synthesis of other organic compounds, such as acetaminophen (ATSDR 1990).

용도

The primary use of nitrobenzene is in the captive production of aniline, with about 97.5% of nitrobenzene production consumed in this process. The major use of aniline is in the manufacture of polyurethanes. Nitrobenzene is also used as a solvent in petroleum refining, in the manufacture of cellulose ethers and acetate, and in Friedel-Crafts reactions to hold the catalyst in solution. It is also used in the synthesis of other organic compounds including acetaminophen, which is an over-the-counter analgesic commonly known as Tylenol?.
Nitrobenzene is used as a flavoring agent, a perfume for soaps and as a solvent for shoe dyes.

용도

Nitrobenzene is an organic compound used a standard for detection and analyses as well as its removal from the environment. The compound’s cytotoxic effects have been studied in a hepatocarcinoma cell line.

용도

For the manufacture of aniline; in soaps, shoe polishes; for refining lubricating oils; manufacture of pyroxylin Compounds.

생산 방법

Nitrobenzene is produced by the direct nitration of benzene with a mixture of sulfuric and nitric acids. U.S. capacity for nitrobenzene production is approximately 1.5 billion pounds . The most important use for nitrobenzene is in the production of aniline. Nearly 98% of the nitrobenzene produced in the U.S. is converted to aniline.

정의

ChEBI: A nitroarene consisting of benzene carrying a single nitro substituent. An industrial chemical used widely in the production of aniline.

제조 방법

Nitrobenzene is produced commercially by the exothermic nitration of benzene with fuming nitric acid in the presence of a sulfuric acid catalyst at 50 to 65℃. The crude nitrobenzene is passed through washer-separators to remove residual acid and is then distilled to remove benzene and water.

정의

A yellow organic oil obtained by refluxing benzene with a mixture of concentrated nitric and sulfuric acids. The reaction is a typical electrophilic substitution on the benzene ring by the nitryl cation (NO2+).

정의

nitrobenzene: A yellow oily liquid,C6H5NO2; r.d. 1.2; m.p. 6°C; b.p.211°C. It is made by the nitration ofbenzene using a mixture of nitricand sulphuric acids.

일반 설명

A pale yellow to dark brown liquid. Flash point 190°F. Very slightly soluble in water. Toxic by inhalation and by skin absorption. Combustion give toxic oxides of nitrogen. Density 10.0 lb /gal.

공기와 물의 반응

Very slightly soluble in water.

반응 프로필

Aluminum chloride added to Nitrobenzene containing about 5% phenol caused a violent explosion [Chem. Eng. News 31:4915. 1953]. Heating a mixture of Nitrobenzene, flake sodium hydroxide and a little water led to an explosion, discussed in [Bretherick's 5th ed. 1995]. Mixed with oxidants, i.e. dinitrogen tetraoxide, fluorodinitromethane, nitric acid, peroxodisulfuric acid, sodium chlorate, tetranitromethane, uranium perchlorate, etc., forms highly sensitive explosive, [Bretherick 5th ed, 1995]. Heated mixtures of Nitrobenzene and tin(IV) chloride produce exothermic decomposition with gas production [Bretherick, 5th Ed., 1995].

위험도

Toxic by ingestion, inhalation, and skin absorption. Methemoglobinemia. Possible carcinogen.

건강위험

Can cause death due to respiratory failure. Classified as extremely toxic. The mean lethal oral dose is probably between 1 and 5 grams. Systemic effects may be delayed for a few hours. Nitrobenzene is rapidly absorbed through the skin. It is a powerful methemoglobin former. Ethyl alcohol aggravates intoxication caused by Nitrobenzene exposure.

건강위험

The routes of entry of nitrobenzene intothe body are the inhalation of its vaporsor absorption of the liquid or the vaporthrough the skin and, to a much lesserextent, ingestion. The target organs are theblood, liver, kidneys, and cardiovascular system. Piotrowski (1967) estimated that in anexposure period of 6 hours to a concentration of 5 mg/m3, 18 mg of nitrobenzene wasabsorbed through the lungs and 7 mg throughthe skin in humans. Furthermore, about 80%of inhaled vapor is retained in the respiratorytract. The dermal absorption rate at this concentration level is reported as 1 mg/h, whilethe subcutaneous absorption of the liquidis between 0.2 and 0.3 mg/cm3/h (ACGIH1986).
The symptoms of acute toxicity are headache, dizziness, nausea, vomiting, and dyspnea. Subacute and chronic exposure cancause anemia. Nitrobenzene effects the conversion of hemoglobin to methemoglobin. Itis metabolized to aminophenols and nitrophenols to about 30%, which are excreted.

건강위험

The most consistently reported toxic effect in humans exposed to nitrobenzene is methemoglobinemia. Numerous case reports have appeared in the literature, and there is no clear-cut correlation between suspected dose and severity of the methemoglobinemia. Infants are apparently particularly sensitive to nitrobenzeneinduced methemoglobinemia. A number of case histories relate neurologic symptoms to nitrobenzene exposure. The signs and symptoms include headache, confusion, vertigo, nausea, loss of cognition, hyperalgesia, paresthesia, and polyneuritis . Hepatotoxic effects have also been reported to occur in humans exposed to nitrobenzene. A female patient who had been exposed to high concentrations of nitrobenzene for 17 months developed an enlarged and tender liver, icterus, and an increased retention of bromosulfophthalein.

화재위험

Moderate explosion hazard when exposed to heat or flame. Reacts violently with nitric acid, aluminum trichloride plus phenol, aniline plus glycerine, silver perchlorate and nitrogen tetroxide. Avoid aluminum trichloride; aniline; gycerol; sulfuric acid; oxidants; phosphorus pentachloride; potassium; potassium hydroxide. Avoid sunlight, physical damage to container, freezing, and intense heat.

공업 용도

Nitrobenzene is mainly utilized for aniline production. The aniline is used primarily for the manufacture of 4,4'-methylenebis (phenyl isocyanate) and polymers thereof (50%). The second largest use of aniline is in the manufacture of chemicals for rubber production (30%). Dyes and dye intermediates, hydroquinone and drugs account for about 8% of the aniline produced, while 10% of the aniline is converted to agricultural products such as pesticides and defoliants (Northcott 1978). It also is used as a solvent for cellulose ethers and an ingredient in polishes for metals and shoes (HSDB 1988).

Safety Profile

Confirmed carcinogen. Human poison by an unspecified route. Poison experimentally by subcutaneous and intravenous routes. Moderately toxic by ingestion, skin contact, and intraperitoneal routes. Human systemic effects by ingestion: general anesthetic, respiratory stimulation, and vascular changes. An experimental teratogen. Experimental reproductive effects. Mutation data reported. An eye and skin irritant. Can cause cyanosis due to formation of methemoglobin. It is absorbed rapidly through the skin. The vapors are hazardous. to heat and flame. Moderate explosion hazard when exposed to heat or flame. Explosive reaction with solid or concentrated alkali + heat (e.g., sodium hydroxide or potassium hydroxide), aluminum chloride + phenol (at 12O°C), aniline + glycerol + sulfuric acid, nitric + sulfuric acid + heat. Forms explosive mixtures with aluminum chloride, oxidants (e.g., fluorodinitromethane, uranium perchlorate, tetranitromethane, sodium chlorate, nitric acid, nitric acid + water, peroxodsulfuric acid, dinitrogen tetraoxide), phosphorus pentachloride, potassium, sulfuric acid. Reacts violently with aniline + glycerin, N20, AgCLO4. To fight fne, use water, foam, CO2, dry chemical. Incompatible with potassium hydroxide. When heated to decomposition it emits toxic fumes of NOx. See also NITRO COMPOUNDS OF AROMATIC HYDROCARBONS.

잠재적 노출

Nitrobenzene is used in the manufacture of explosives and aniline dyes and as solvent and intermediate. It is also used in floor polishes; leather dressings and polished; and paint solvents, and to mask other unpleasant odors. Substitution reactions with nitrobenzene are used to form m-derivatives. Pregnant women may be especially at risk with respect to nitrobenzene as with many other chemical compounds, due to transplacental passage of the agent. Individuals with glucose-6-phosphate dehydrogenase deficiency may also be special risk groups. Additionally, because alcohol ingestion or chronic alcoholism can lower the lethal or toxic dose of nitrobenzene, individuals consuming alcoholic beverages may be at risk.

Carcinogenicity

Nitrobenzene is reasonably anticipated to be a human carcinogenbased on sufficient evidence of carcinogenicity from studies in experimental animals.

환경귀착

Biological. In activated sludge, 0.4% of the applied nitrobenzene mineralized to carbon dioxide after 5 d (Freitag et al., 1985). Under anaerobic conditions using a sewage inoculum, nitrobenzene degraded to aniline (Hallas and Alexander, 1983). When nitrobenzene (5 and 10 mg/L) was statically incubated in the dark at 25 °C with yeast extract and settled domestic wastewater inoculum, complete biodegradation with rapid acclimation was observed after 7 to 14 d (Tabak et al., 1981). In activated sludge inoculum, 98.0% COD removal was achieved in 5 d. The average rate of biodegradation was 14.0 mg COD/g?h (Pitter, 1976).
Razo-Flores et al. (1999) studied the fate of nitrobenzene (50 mg/L) in an upward-flow anaerobic sludge bed reactor containing a mixture of volatile fatty acids and/or glucose as electron donors. The nitrobenzene loading rate and hydraulic retention time for this experiment were 43 mg/L?d and 28 h, respectively. Nitrobenzene was effectively reduced (>99.9%) to aniline (92% molar yield) in stoichiometric amounts for the 100-d experiment.
Photolytic. Irradiation of nitrobenzene in the vapor phase produced nitrosobenzene and 4- nitrophenol (HSDB, 1989). Titanium dioxide suspended in an aqueous solution and irradiated with UV light (λ = 365 nm) converted nitrobenzene to carbon dioxide at a significant rate (Matthews, 1986). A carbon dioxide yield of 6.7% was achieved when nitrobenzene adsorbed on silica gel was irradiated with light (λ >290 nm) for 17 h (Freitag et al., 1985).
Chemical/Physical. In an aqueous solution, nitrobenzene (100 μM) reacted with Fenton’s reagent (35 μM). After 15 min, 2-, 3-, and 4-nitrophenol were identified as products. After 6 h, about 50% of the nitrobenzene was destroyed. The pH of the solution decreased due to the formation of nitric acid (Lipczynska-Kochany, 1991). Augusti et al. (1998) conducted kinetic studies for the reaction of nitrobenzene (0.2 mM) and other monocyclic aromatics with Fenton’s reagent (8 mM hydrogen peroxide; [Fe+2] = 0.1 mM) at 25 °C. They reported a reaction rate constant of 0.0260/min.

신진 대사

Nitrobenzene vapor is readily absorbed through the skin and lungs. At an airborne nitrobenzene concentration of 10 mg/m3 humans may absorb 18 to 25 mg in 6 h through the lungs and from 8 to 19 mg through the skin in the same length of time .
Urine is the major route of excretion of nitrobenzene metabolites in rabbits , rats and mice . The most abundant metabolite in earlier studies in rabbits and rats was p-aminophenol. This compound, or its glucuronide or sulfate conjugates, accounted for 19% to 31% of the dose. In a later study in rats in which the acid hydrolysis step employed by earlier workers to cleave conjugates was replaced by enzyme hydrolysis, no p-aminophenol was found in the urine of male Fischer-344 or CD rats .
About 9% of a nitrobenzene dose was excreted by B6C3F1 mice as the sulfate conjugate. The major metabolites found in Fischer-344 rat urine were p-hydroxyacetanilide sulfate (19% of the dose), p-nitrophenol sulfate (20% of the dose) and m-nitrophenol sulfate (10% of the dose) .
In addition, an unidentified metabolite accounted for about 10% of the dose .
Male CD rats excreted the same metabolites after an oral dose of nitrobenzene, but in slightly different proportions. They excreted about half as much of the dose as the glucuronide or sulfate conjugates of P-hydroxyacetanilide (9% of the dose) and P-nitrophenol (13% of the dose), approximately the same amount of m-nitrophenol (8% of the dose), and about twice as much as the unidentified metabolite. Interestingly, whereas Fischer-344 rats excreted the phenolic metabolites of nitrobenzene exclusively as sulfates, CD rats excreted the same metabolites in the free form (15-17% of the total metabolite) and as glucuronides (4-20% of the total metabolite).
Approximately 4% of the dose also was excreted as p-hydroxyacetanilide by B6C3F1 mice and as p- and m-nitrophenol (7% and 6% of the dose, respectively) sulfates, glucuronides and free metabolites .
Clearly, ring hydroxylation and reduction are important metabolic steps in the biotransformation of nitrobenzene in rabbits, rats, mice and humans . Since no significant isotope effect was found in the metabolism of deuterated nitrobenzene to these products in rats in vivo , the o- and p-nitrophenols may be formed through an arene oxide intermediate. A significant isotope effect was noted in the formation of m-nitrophenol from deuterated nitrobenzene in the same rats, leading to the conclusion that m-nitrophenol is formed by a direct oxygen insertion mechanism or by some other mechanism which does not involve an arene oxide intermediate. The reduction of nitrobenzene in vivo is largely, if not exclusively, due to the action of anaerobic intestinal microflora. Treatment with antibiotics totally eliminated the ability of cecal contents of Fischer-344 rats to reduce nitrobenzene in vitro, and rats treated with antibiotics eliminated p-hydroxyacetanilide as 0.9% of an oral dose of nitro-benzene. Normal rats excreted 16.2% of an oral dose of nitrobenzene as that metabolite .
The reduction of most nitro compounds by hepatic microsomes is not detectable under aerobic conditions, but is readily observable under anaerobic conditions. Mason and Holtzman proposed that the first intermediate in the microsomal reduction of nitroaromatic compounds is the nitro anion radical, the product of a one electron transfer to nitrobenzene or other nitroaromatic compound. Oxygen would rapidly oxidize the radical to yield the parent nitro compound and Superoxide anion. Both the nitro anion radical and Superoxide anion are potentially toxic compounds.
Both P-nitrophenol and P-aminophenol have been detected in human urine after exposure to nitrobenzene. p-Aminophenol has been found only after large accidental exposures and acid hydrolysis of urine. Since acid conditions convert p-acetamidophenol to P-aminophenol, the identity of the metabolite actually excreted is in doubt. P-Nitrophenol has been found in the urine of volunteers exposed to low inhalation doses of nitrobenzene, and Kuzelova and Popler have suggested that urinary P-nitrophenol be used to monitor exposure to nitrobenzene.

운송 방법

UN1662 Nitrobenzene, Hazard Class: 6.1; Labels: 6.1-Poisonous materials.

Purification Methods

Common impurities include nitrotoluene, dinitrothiophene, dinitrobenzene and aniline. Most impurities can be removed by steam distillation in the presence of dilute H2SO4, followed by drying with CaCl2, and shaking with, then distilling at low pressure from BaO, P2O5, AlCl3 or activated alumina. It can also be purified by fractional crystallisation from absolute EtOH (by refrigeration). Another purification process includes extraction with aqueous 2M NaOH, then water, dilute HCl, and water, followed by drying (CaCl2, MgSO4 or CaSO4) and fractional distillation under reduced pressure. The pure material is stored in a brown bottle, in contact with silica gel or CaH2. It is very hygroscopic. [Beilstein 5 H 233, 5 I 124, 5 II 171, 5 III 591, 5 IV 708.]

비 호환성

Concentrated nitric acid, nitrogen tetroxide; caustics; phosphorus pentachloride; chemically-active metals, such as tin or zinc. Violent reaction with strong oxidizers and reducing agents. Attacks many plastics. Forms thermally unstable compounds with many organic and inorganic compounds.

폐기물 처리

Incineration (982℃, 2.0 seconds minimum) with scrubbing for nitrogen oxides abatement . 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.

법규

Coast Guard, Department of Homeland Security
Minimum requirements have been established for safe transport of nitrobenzene on ships and barges.
Department of Transportation (DOT)
Nitrobenzene is considered a hazardous material and marine pollutant, and special requirements have been set for marking, labeling, and transporting this material.
Environmental Protection Agency (EPA)
Clean Air Act
National Emissions Standards for Hazardous Air Pollutants: Listed as a hazardous air pollutant. New Source Performance Standards: Manufacture of nitrobenzene is subject to certain provisions for the control of volatile organic compound emissions.
Clean Water Act
Effluent Guidelines: Listed as a toxic pollutant. Water Quality Criteria: Based on fish or shellfish and water consumption = 17 μg/L; based on fish or shellfish consumption only = 690 μg/L.

나이트로벤젠 준비 용품 및 원자재

원자재

준비 용품


나이트로벤젠 공급 업체

글로벌( 0)공급 업체
공급자 전화 팩스 이메일 국가 제품 수 이점

나이트로벤젠 관련 검색:

Copyright 2019 © ChemicalBook. All rights reserved