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| 融点 | 227-229 °C(lit.) | | 沸点 | 323-326 °C(lit.) | | 比重(密度) | 1.5691 | | 蒸気圧 | 1.45 x l0-3 Pa (20 °C) | | 屈折率 | 1.5691 (estimate) | | 闪点 | 11 °C | | 貯蔵温度 | APPROX 4°C | | 溶解性 | Chloroform, Hexanes (Slightly) | | 水溶解度 | Practically insoluble in water | | Merck | 13,4696 | | BRN | 1912585 | | Henry's Law Constant | 6.11 at 25 °C (continuous flow sparger, Sproule et al., 1991) | | 暴露限界値 | No exposure limit has been set for this com pound. Carcinogenicity: Animal Sufficient
Evidence, Human Limited Evidence (IARC). | | 安定性： | Stable. Incompatible with strong oxidizing agents. | | InChIKey | CKAPSXZOOQJIBF-UHFFFAOYSA-N | | CAS データベース | 118-74-1(CAS DataBase Reference) | | IARC | 2B (Vol. Sup 7, 79) 2001 | | EPAの化学物質情報 | Hexachlorobenzene (118-74-1) |
| | ヘキサクロロベンゼン Usage And Synthesis |
| 解説 | ヘキサクロロベンゼン．塩化アルミニウムと塩化硫黄とを触媒にして，クロロベンゼンを塩化スルフリルで塩素化すると得られる．針状晶．融点229 ℃，沸点326 ℃．昇華性がある．有機溶媒に可溶，冷エタノールに微溶，水に不溶．毒性は比較的低いが，長期間さらされると関節炎，甲状腺肥大などを起こす．有機合成用試薬，農薬(殺菌剤)に用いられる． | | 用途 | 殺菌剤、防かび剤、防汚剤、合成中間体。EUでは使われておらず塩ビに含まれる非意図的副生成物。日本では71年製造?使用?輸入禁止 | | 農薬用途 | 殺菌剤 | | 説明 | Hexachlorobenzene is a white crystalline solid. This compound does not occur naturally.
It is formed as a by-product during the manufacture of chemicals used as solvents
(substances used to dissolve other substances), other chlorine-containing compounds,
and pesticides. Small amounts of hexachlorobenzene can also be produced during combustion
processes such as burning of city wastes. It may also be produced as a by-product
in waste streams of chlor-alkali and wood-preserving plants. Hexachlorobenzene
was widely used as a pesticide until 1965. It was also used to make fireworks, ammunition,
and synthetic rubber. | | 化学的特性 | Hexachlorobenzene is a solid, crystallizing in nee dles. | | 化学的特性 | white powder | | 使用 | Seed fungicide | | 使用 | No commercial uses of hexachlorobenzene as an end product in the United States were identified (ATSDR 2002). Previously, it was used as a seed-treatment fungicide for onions, sorghum, wheat, and other grains (IARC 1979). All registered pesticide uses in the United States were voluntarily cancelled in 1984 (ATSDR 2002). Hexachlorobenzene was also used as a chemical intermediate in dye manufacturing, in the synthesis of other organic chemicals, and in the production of pyrotechnic compositions for the military. It was used as a raw material for synthetic rubber, as a plasticizer for polyvinyl chloride, as a porosity controller in the manufacture of electrodes, and as a wood preservative (IARC 1979, ATSDR 2002). | | 使用 | In organic syntheses. Formerly as agricultural fungicide. | | 使用 | Hexachlorobenzene is used as a fungicideand as an intermediate in organic synthesis. | | 定義 | hexachlorobenzene: A colourlesscrystalline compound, C6Cl6; m.p.227°C. It is made by the chlorinationof benzene with an iron(III) chloridecatalyst or by treating hexachlorocyclohexanewith chlorine in hexachloroethane.It is used to preservewood and dress seeds, and in themanufacture of hexafluorobenzene. | | 定義 | ChEBI: A member of the class of chlorobenzenes that is benzene in which all of the hydrogens are replaced by chlorines. An agricultural fungicide introduced in the mid-1940s and formerly used as a seed treatment, its use has been banned since 1984 under the Stock
olm Convention on Persistent Organic Pollutants. | | Synthesis Reference(s) | Journal of the American Chemical Society, 69, p. 3146, 1947 DOI: 10.1021/ja01204a507 | | 一般的な説明 | A white crystalline substance. Insoluble in water and denser than water. Contact may irritate skin, eyes and mucous membranes. May be toxic by ingestion. Used to make other chemicals. | | 空気と水の反応 | HEXACHLOROBENZENE is sensitive to moisture. Insoluble in water. | | 反応プロフィール | HEXACHLOROBENZENE reacts violently with dimethylformamide. . | | 危険性 | Possible carcinogen. Toxic by ingestion.
Combustible. | | 健康ハザード | The acute oral and inhalation toxicity ofhexachlorobenzene is low in test animals.Repeated ingestion of this compound mayproduce porphyria hepatica (increased for mation and excretion of porphyrin) causedby disturbances in liver metabolism. The oralLD50 value in rabbits is 2600 mg/kg; theinhalation LC50 value from a single exposureis 1800 mg/m3 (NIOSH 1986). The occupa tional health hazard from inhalation shouldbe very low because of its very low vaporpressure (0.00001 torr).
Hexachlorobenzene causes cancer in ani mals. Oral administration of this compoundfor 18 weeks to 2 years caused tumors inthe liver, kidney, thyroid, and blood in rats,mice, and hamsters. It is a suspected humancarcinogen, evidence of which occurs to alimited extent. | | 健康ハザード | Harmful by dust inhalation or if swallowed. Irritating to eyes, skin and mucous membranes. Prolonged periods of ingestion may cause cutaneous porphyria. | | 火災危険 | Noncombustible solid; very low reactiv ity. Reaction with dimethyl formamide is
reported to be violent at temperatures above
65°C (149°F) (NFPA 1997). | | 職業ばく露 | Hexachlorobenzene was used as a fun gicide; an additive for pyrotechnic compositions; and as
wood preservative. It was used widely as a pesticide to pro tect seeds of onions and sorghum, wheat, and other grains
against fungus until 1965. This material was used to make
fireworks; ammunition for military uses; synthetic rubber;
as a porosity controller in the manufacture of electrodes; as
an intermediate in dye manufacture; in organic synthesis. It
is formed as a by-product of making other chemicals; in
the waste streams of chloralkali and wood-preserving
plants; and when burning municipal waste. Currently, there
are no commercial uses of hexachlorobenzene in the United
States. | | 応急処置 | If this chemical gets into the eyes, remove anycontact lenses at once and irrigate immediately for at least15 min, occasionally lifting upper and lower lids. Seekmedical attention immediately. If this chemical contacts theskin, remove contaminated clothing and wash immediatelywith soap and water. Seek medical attention immediately. Ifthis chemical has been inhaled, remove from exposure,begin rescue breathing (using universal precautions, includ-ing resuscitation mask) if breathing has stopped and CPR ifheart action has stopped. Transfer promptly to a medicalfacility. When this chemical has been swallowed, get medi-cal attention. Give large quantities of water and inducevomiting. Do not make an unconscious person vomit.Note to physician: For ingestions of less than 10 mg/kg bodyweight occurring less than an hour before treatment, induceemesis. For ingestions of more than 10 mg/kg body weightoccurring less than an hour before treatment, use gastriclavage. For ingestion occurring more than an hour beforetreatment, use activated charcoal. There is no specific anti-dote, and supervision for at least 72 h is recommended. | | 発がん性 | Hexachlorobenzene is reasonably anticipated to be a human carcinogen based on sufficient evidence of carcinogenicity from studies in experimental animals. | | Source | Hexachlorobenzene may enter the environment from incomplete combustion of
chlorinated compounds including mirex, kepone, chlorobenzenes, pentachlorophenol, PVC,
polychlorinated biphenyls, and chlorinated solvents (Ahling et al., 1978; Dellinger et al., 1991). In
addition, hexachlorobenzene may enter the environment as a reaction by-product in the production
of carbon tetrachloride, dichloroethylene, hexachlorobutadiene, trichloroethylene, tetrachloroethylene,
pentachloronitrobenzene, and vinyl chloride monomer (quoted, Verschueren, 1983). | | 環境運命予測 | Biological. Reductive monodechlorination occurred in an anaerobic sewage sludge yielding principally 1,3,5-trichlorobenzene. Other compounds identified included pentachlorobenzene, 1,2,3,5-tetrachlorobenzene and dichlorobenzenes (Fathepure et al., 1988). In activated sludge, only 1.5% of the applied hexachlorobenzene mineralized to carbon dioxide after 5 days (Freitag et al., 1985). In a 5-day experiment, 14C-labeled hexachlorobenzene applied to soil-water suspensions under aerobic and anaerobic conditions gave 14CO2 yields of 0.4 and 0.2%, respectively (Scheunert et al., 1987).
When hexachlorobenzene was statically incubated in the dark at 25°C with yeast extract and settled domestic wastewater inoculum, no signi?cant biodegradation was observed. At a concentration of 5 mg/L, percent losses after 7, 14, 21 and 28-day incubation
Groundwater. According to the U.S. EPA (1986) hexachlorobenzene has a high potential to leach to groundwater.
Photolytic. Solid hexachlorobenzene exposed to arti?cial sunlight for 5 months photolyzed at a very slow rate with no decomposition products identified (Plimmer and Klingebiel, 1976). The sunlight irradiation of hexachlorobenzene (20 g) in a 100 mL borosilicate glass-stoppered Erlenmeyer ?ask for 56 days yielded 64 ppm pentachlorobiphenyl (Uyeta et al., 1976). A carbon dioxide yield <0.1% was observed when hexachlorobenzene adsorbed on silica gel was irradiated with light (λ >290 nm) for 17 hours (Freitag et al., 1985).
Irradiation (λ ≥285 nm) of hexachlorobenzene (1.1–1.2 mM/L) in an acetonitrile-water mixture containing acetone (concentration = 0.553 mM/L) as a sensitizer gave the following products (% yield): pentachlorobenzene (71.0), 1,2,3,4-tetrachlorobenzene (0.6) | | 代謝経路 | With the incubation of rat liver microsomes,
hexachlorobenzene is metabolized to give
pentachlorophenol and tetrachlorohydroquinone, and,
in addition, a considerable amount of covalent binding
to protein is detected (250 pM pentachlorophenol,
17 pM tetrachlorohydroquinone, and 11 pM
tetrachlorobenzoquinone covalent binding in an
incubation containing 50 μM hexachlorobenzene). | | 代謝 | Sensitized photolysis of HCB at wavelengths greater
than 285 nm in acetonitrile/water containing acetone gave
dechlorinated products: pentachlorobenzene (78) (71%),
1,2,3,4-tetrachlorobenzene (79) (0.6%), 1,2,3,5-tetrachlorobenzene
(80) (2.2%), and 1,2,4,5- tetrachlorobenzene
(81) (3.7%). Without acetone, products included
pentachlorobenzene (78) (76.8%), 1,2,3,5-tetrachlorobenzene
(80) (1.2%), 1,2,4,5- tetrachlorobenzene (81) (1.7%),
and 1,2,4-trichlorobenzene (82) (0.2%) (105).
Irradiation of hexachlorobenzene in methanol solution
at wavelengths greater than 260 nm gave a
mixture of reductively dechlorinated products (pentachlorobenzene
and a tetrachlorobenzene, probably 80)
and pentachlorobenzyl alcohol 83, and also a tetrachlorodi(
hydroxymethyl)benzene (106). A similar product
mixture was obtained by exposing a methanolic solution of
hexachlorobenzene inmethanol to sunlight outdoors. After
15 days, only 30% of hexachlorobenzene was recovered.
Photolysis rates were enhanced by the addition of sensitizers
(diphenylamine, tryptophane, and naturally occurring
organic substances), but no products were identified.
In an anaerobic sewage sludge, hexachlorobenzene was
reductively dechlorinated and the principal product was
1,3,5-trichlorobenzene (84). Pentachlorobenzene, 1,2,3,5-
tetrachlorobenzene, and dichlorobenzenes were also identified
(107). In activated sludge, 1.5% of hexachlorobenzene
was mineralized as carbon dioxide after 5 days. | | Solubility in organics | In millimole fraction at 25 °C: 2.62 in n-hexane, 3.14 in n-heptane, 3.71 in n-octane, 4.10 in nnonane,
4.60 in n-decane, 6.81 in n-hexadecane, 2.95 in cyclohexane, 3.87 in methylcyclohexane,
2.52 in 2,2,4-trimethylpentane, 4.71 in tert-butylcyclohexane, 4.40 in dibutyl ether, 3.20
in methyl tert-butyl ether, 5.92 in tetrahydrofuran, 3.97 in 1,4-dioxane, 0.0902 in methanol,
0.236 in ethanol, 0.398 in 1-propanol, 0.298 in 2-propanol, 0.667 in 1-butanol, 0.521 in 2-
butanol, 0.533 in 2-methyl-1-propanol, 0.517 in 2-methyl-2-propanol, 1.03 in 1-pentanol, 0.860
in 2-propanol, 0.770 in 3-methyl-1-butanol, 1.20 on 2-methyl-2-butanol, 1.44 in 1-hexanol, 1.40
in 2-methyl-1-pentanol, 1.43 in 4-methyl-2-pentanol, 1.90 in 1-heptanol, 2.38 in 1-octanol, 1.74
in 2-ethyl-1-hexanol, 3.80 in 1-decanol, 0.920 in cyclopentanol, 3.65 in butyl acetate, 2.11 in
ethyl acetate, 1.48 in methyl acetate, 2.86 in 1,2-dichloroethane, 3.83 in 1-chlorobutane, 5.08 in
1-chlorohexane, 6.06 in 1-chlorooctane, 6.10 in chlorocyclohexane (De Fina et al., 2000) | | Solubility in water | In millimole fraction at 25 °C: 2.62 in n-hexane, 3.14 in n-heptane, 3.71 in n-octane, 4.10 in nnonane,
4.60 in n-decane, 6.81 in n-hexadecane, 2.95 in cyclohexane, 3.87 in methylcyclohexane,
2.52 in 2,2,4-trimethylpentane, 4.71 in tert-butylcyclohexane, 4.40 in dibutyl ether, 3.20
in methyl tert-butyl ether, 5.92 in tetrahydrofuran, 3.97 in 1,4-dioxane, 0.0902 in methanol,
0.236 in ethanol, 0.398 in 1-propanol, 0.298 in 2-propanol, 0.667 in 1-butanol, 0.521 in 2-
butanol, 0.533 in 2-methyl-1-propanol, 0.517 in 2-methyl-2-propanol, 1.03 in 1-pentanol, 0.860
in 2-propanol, 0.770 in 3-methyl-1-butanol, 1.20 on 2-methyl-2-butanol, 1.44 in 1-hexanol, 1.40
in 2-methyl-1-pentanol, 1.43 in 4-methyl-2-pentanol, 1.90 in 1-heptanol, 2.38 in 1-octanol, 1.74
in 2-ethyl-1-hexanol, 3.80 in 1-decanol, 0.920 in cyclopentanol, 3.65 in butyl acetate, 2.11 in
ethyl acetate, 1.48 in methyl acetate, 2.86 in 1,2-dichloroethane, 3.83 in 1-chlorobutane, 5.08 in
1-chlorohexane, 6.06 in 1-chlorooctane, 6.10 in chlorocyclohexane (De Fina et al., 2000) | | 貯蔵 | Color Code- Blue: Health Hazard/Poison: Storeinia securepoison location. Prior to working with thischemical you should be trained on its proper handling andstorage. Store in tightly closed containers in a cool, well-ventilated area away from oxidizers, dimethyl formamide,and heat. Where possible, automatically pump liquid fromdrums or other storage containers to process containers. Aregulated, marked area should be established where thischemical is handled, used, or stored in compliance withOSHA Standard 1910.1045. | | 輸送方法 | UN2729 Hexachlorobenzene, Hazard Class: 6.1;
Labels: 6.1-Poisonous materials. | | 純化方法 | Crystallise hexachlorobenzene repeatedly from *benzene. Dry it under vacuum over P2O5. [Beilstein 5 H 205, 5 IV 670.] | | Degradation | Hexachlorobenzene is very stable and is unreactive toward acids and
bases.
Photolysis is very slow and in artificial sunlight, solid HCB photodecomposed
after 5 months. In sunlight, 20 g of HCB contained in a borosilicate flask gave a concentration of 64 mg kg-1 of pentachlorobiphenyl
after 56 days (Uyeta et al., 1976).
Sensitised photolysis of HCB in an acetonitrile/water mixture containing
acetone at wavelengths greater than 285 nm gave the following products:
pentachlorobenzene (2) (71%), 1,2,3,4-tetrachlorobenzene (3)
(0.6%), 1,2,3,5-tetrachlorobenzene (4) (2.2%) and 1,2,4,5-tetrachlorobenzene
(5) (3.7%). In the absence of acetone, products identified included
2 (76.8%), 4 (1.2%), 5 (1.7%) and 1,2,4-trichlorobenzene (6) (0.2%)
(Choudhry and Hutzinger, 1984) (see Scheme 1). | | Toxicity evaluation | There are no reports of avian casualties, although raptors
found dead in The Netherlands had substantial levels
of HCB in their livers along with cyclodiene and DDE
residues (33). The same authors reported porphyria in
quail following a 3-month dosing period with 20-ppm
HCB. Product registrations in Canada at the time allowed
up to 1000 ppm on various cereal seeds. In the early
1970s, levels in the range of 3–4 ppm (fresh weight
basis) were seen in eggs of fish-eating birds of the
Great Lakes and likely contributed to the high levels
of embryonic mortality seen (34). However, because HCB
is also an intermediate in the manufacture of several
chemicals, industrial pollution rather than use of the
chemical on farm fields could have been the source of
the contamination. | | 不和合性 | Reacts violently with oxidizers; dimethyl
formamide above 65 ℃. | | 廃棄物の処理 | Incineration is most effective
@ 1300 ℃ and 0.25 seconds. Consult with environmental
regulatory agencies for guidance on acceptable disposal
practices. Generators of waste containing this contaminant
(≥100 kg/mo) must conform to EPA regulations governing
storage, transportation, treatment, and waste disposal. |
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