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化工社化工社 化学情報印刷レポート · 研究参考用
HCID 12867作成日：2026年10月27日

2,6-ジ-tert-ブチル-1,4-ベンゾキノン

2,6-ジ-tert-ブチル-1,4-ベンゾキノン · 2,6-ジ-tert-ブチル-2,5-シクロヘキサジエン-1,4-ジオン · 2,6-ジtert-ブチル-2,5-シクロヘキサジエン-1,4-ジオン · 2,6-ジtert-ブチル-1,4-ベンゾキノン · 2,6-ジ(1,1-ジメチルエチル)-1,4-ベンゾキノン · BHT-キノン · 2,6-ジ-tert-ブチル-p-ベンゾキノン · 2,6-ジ(tert-ブチル)-p-ベンゾキノン

https://huagongshe.com/ja/chemical/12867

2,6-ジ-tert-ブチル-1,4-ベンゾキノン の分子構造式

識別子と物理属性

CAS No.719-22-2
分子式C14H20O2
平均分子量220.31 g/mol
単同位体質量220.14632988 g/mol
SMILESCC(C)(C)C1=CC(=O)C=C(C(C)(C)C)C1=O
InChIKeyRDQSIADLBQFVMY-UHFFFAOYSA-N
PubChem CID12867
ChEMBLCHEMBL3185121
ChEBICHEBI:89187
EC No.211-946-0
DTXSIDDTXSID7021493
現地名2,6-ジ-tert-ブチル-1,4-ベンゾキノン

化学・物理的性質

XLogP3.4
極性表面積34.1
水素結合供与体数0
水素結合受容体数2
回転可能結合数2
重原子数16
形式電荷0
複雑度359
物質分類Other Classes -> Aromatic KetonesAntioxidant
SpringerMaterials PropertiesChemical shift
LogP（分配係数）log Kow = 4.42
Color/FormYellow crystals
融点65-67 °C65-67 °C(lit.)
蒸気圧0.000411 [mmHg]
Physical DescriptionYellow solid[HSDB] Orange crystalline powder[MSDSonline]
沸点75-80 °C (0.7 mmHg)
密度1.0106 (rough estimate)
屈折率1.4970 (estimate)
引火点>110°(230°F)
貯蔵条件Amber Vial, -20°C Freezer, Under inert atmosphere
溶解度クロロホルム（微量）、メタノール（微量）水に不溶。
外観・状態結晶または結晶性粉末
色オレンジからブラウン
BRN1911512
ヘンリー定数6.2×102 mol/(m3Pa) at 25℃, HSDB (2015)
安定性Light sensitive
InChI1S/C14H20O2/c1-13(2,3)10-7-9(15)8-11(12(10)16)14(4,5)6/h7-8H,1-6H3
InChIKeyRDQSIADLBQFVMY-UHFFFAOYSA-N
SMILESCC(C)(C)C1=CC(=O)C=C(C1=O)C(C)(C)C
CAS データベース719-22-2(CAS DataBase Reference)
NISTの化学物質情報2,5-Cyclohexadiene-1,4-dione, 2,6-bis(1,1-dimethylethyl)-(719-22-2)
EPAの化学物質情報2,6-Di-tert-butylbenzoquinone (719-22-2)

化学的特性

ORANGE TO BROWN CRYSTALS OR CRYSTALLINE POWDER

安全性と法規制

GHS 分類WarningH315 (100%): Causes skin irritation [Warning Skin corrosion/irritation]P261, P264, P264+P265, P271, P280, P302+P352, P304+P340, P305+P351+P338, P319, P321, P332+P317, P337+P317, P362+P364, P403+P233, P405, and P501 (click each P-code to see the statement)Aggregated GHS information provided per 47 reports by companies from 5 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies.
有害性の概要An irritantEffects in high-dose animal studies include ulceration of the nasal septum and hemorrhage[MSDSonline] See Quinone.
Hazard Classes and CategoriesSkin Irrit. 2 (100%)
処分方法SRP: At the time of review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices.
環境中動態TERRESTRIAL FATE: Based on a recommended classification scheme(3), an estimated Koc value of 6000(SRC), determined from a measured log Kow(2) and a recommended regression-derived equation(1), indicates that suggests that 2,6-di-t-butyl-p-benzoquinone will be essentially immobile in soil(3). In an unconfined aquifer, however, 2,6-di-t-butyl-p-benzoquinone was transported an estimated 2710 meters over a 43 year period(2,4). 2,6-Di-t-butyl-p-benzoquinone is not expected to volatilize from moist soil surfaces based on an estimated Henry's Law constant of 1.6X10-8 atm-cu m/mole(5,SRC). It may, however, volatilize from the surface of dry soils given an estimated vapor pressure of 4.1X10-4 mm Hg(6,SRC). Incomplete information is available regarding the biodegradation potential of 2,6-di-t-butyl-p-benzoquinoneRhine River water which was subjected to bank filtration had lower concentrations of 2,6-di-t-butyl-p-benzoquinone than the original water(7). Adsorption to soil however, was not measured(7,SRC)).AQUATIC FATE: 2,6-Di-t-butyl-p-benzoquinone should adsorb to suspended solids and organic matter in the water column based on an estimated Koc of 6100(1,SRC) from an experimental log Kow(2) and a suggested classification scheme(3). 2,6-Di-t-butyl-p-benzoquinone (at 0.3 ug/L) had a half-life in Rhine River water of 3.4 daysmeasurements were made at Lobith and 24.5 hours later at Gorinchem(4). Loss of this compound during this stretch of river may have been due to adsorption to particulates or to biodegradation(4,SRC). An estimated BCF value of 1400(1,SRC), from an experimental log Kow(2), suggests that 2,6-di-t-butyl-p-benzoquinone will bioconcentrate in aquatic organisms. This compound has been detected in fish from the Great Lakes(5). 2,6-Di-t-butyl-p-benzoquinone is not expected to volatilize from water surfaces based on an estimated Henry's Law constant of 1.6X10-8 atm-cu m/mole(SRC) using a fragment constant estimation method(6).

用途

使用

2.6-Di-tert-butyl-p-benzoquinone was used as a treatment agent to improve germination, plant health and yield.

製法・合成法

純化方法

It can be recrystallised from MeOH and sublimes in a vacuum. [Beilstein 7 IV 2116.]

ATMOSPHERIC FATE: Based on an estimated vapor pressure of 4.1X10-4 mm Hg at 25 °C(1,SRC), 2,6-di-t-butyl-p-benzoquinone should exist in both the vapor phase and particulate phase in the ambient atmosphere(2,SRC). 2,6-Di-t-butyl-p-benzoquinone should degrade in the vapor phase by reaction with photochemically produced hydroxyl radicals with an estimated half-life of about 17 hours(3,SRC). Particulate-phase 2,6-di-t-butyl-p-benzoquinone may be physically removed from the air by wet and dry deposition(SRC).
Effluent Concentrations1 of 21 samples of wastewater from the photographic industry contained unreported concentrations of 2,6-di-t-butyl-p-benzoquinone(1). 1 of 10 POTW plants sampled contained 2,6-di-t-butyl-p-benzoquinone in the final effluent(2).
Soil Adsorption/MobilityBased on an experimental log Kow of 4.42(1), the Koc of 2,6-di-t-butyl-p-benzoquinone is estimated as approximately 6100 using a regression-derived equation(2,SRC). According to a suggested classification scheme(3), this estimated Koc value suggests that 2,6-di-t-butyl-p-benzoquinone will be immobile in soil(SRC). Sewage which had been through secondary treatment was subjected to rapid infiltrationthe concentration of 2,6-di-t-butyl-p-benzoquinone in the initial sewage was from 0.022-0.037 ug/L and ranged from barely detected to 0.005 ug/L in the groundwater below the rapid infiltration beds(4). It was believed that the loss of this compound was due to adsorption as the sewage had already been through secondary treatment(4). In an unconfined aquifer, however, 2,6-di-t-butyl-p-benzoquinone was shown to have been transported for a considerable distance(between 1940-1983, estimated 2710 m)(1,5).
Atmospheric ConcentrationsURBAN/SUBURBAN: 2,6-Di-t-butyl-p-benzoquinone was detected in the personal air (1 of 8 samples total) of 12 people located either in New Jersey or North Carolina(1).
Human Toxicity ExcerptsChronic neurotoxic effects include vision disturbances. /From table/ /Quinones/
Fish/Seafood ConcentrationsComposite fish samples (lake trout, walleye) were found to contain 2,6-di-t-butyl-p-benzoquinone in 3 of 8 locations in the Great Lakes (two sites in Lake Erie, one site in Lake Michigan)(1).
Artificial Pollution SourcesVOLATILE POLLUTANTS, INCLUDING 2,6-DI-T-BUTYL-P-BENZOQUINONE, WERE PRODUCED FROM SEVERAL RUBBER GOODS MANUFACTURING PROCESSES & ANALYZED BY GAS CHROMATOGRAPHY/MASS SPECTROMETRY. THEIR CUMULATIVE CONCN RANGED FROM 25-27,000 UG/CU M.2,6-Di-t-butyl-p-benzoquinone's production and subsequent use as an oxidant and polymerization catalyst(1), may result in its release to the environment through various waste streams(SRC). 2,6-Di-t-butyl-p-benzoquinone is also an environmental product of the oxidation of 2,6-di-t-butyl phenol, a common antioxidant additive(2,3).
Environmental Biodegradation2,6-Di-t-butyl-p-benzoquinone (at 0.3 ug/l) had a half-life in Rhine River water of 3.4 daysmeasurements were made at Lobith and 24.5 hours later at Gorinchem(1). Degradation of this compound was believed due to aerobic and anaerobic biodegradation(1)however, adsorption to suspended solids and organic matter in the water column was not measured(1,SRC). 2,6-di-t-butyl-p-benzoquinone (at 2 ug/L) initially present in Rhine River water was not detected once the water was passed through a bank filtration process(2). It was not specified whether the loss of this compound was due to biodegradation or adsorption(2,SRC).
Sediment/Soil Concentrations2,6-Di-t-butyl-p-benzoquinone was present in Pawtuxet River sediment located downstream of a plant which produced antioxidants (at concentrations of 1 ppm to 80 ppm(1). 2,6-Di-t-butyl-p-benzoquinone was present in sediment (0.1-40 ppm) located downstream from a specialty chemicals manufacturing plant(2).
Environmental BioconcentrationAn estimated BCF value of 1400 was calculated for 2,6-di-t-butyl-p-benzoquinone, using a measured log Kow of 4.42(1) and a recommended regression-derived equation(2,SRC). This BCF value suggests that 2,6-di-t-butyl-p-benzoquinone will bioconcentrate in aquatic organisms(2,SRC).This compound was detected in fish in the Great Lakes(3) suggesting that bioconcentration may occur(SRC).
Volatilization from Water/SoilThe Henry's Law constant for 2,6-di-t-butyl-p-benzoquinone is estimated as 1.6X10-8 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This indicates that 2,6-di-t-butyl-p-benzoquinone will essentially not volatilize from water surfaces(2,SRC).
Non-Human Toxicity ExcerptsAcute neurotoxic effects reported in animals include convulsionsmedullary paralysis. /From table/ /Quinones/
水環境危害等級（WGK）3
TSCA 収載状態TSCA listed
RTECS 番号DK3970000
税関コード29146990
危険文句（R）36/37/38
危険表示Xi
安全措置（S）26-36-36/37/39-22
危険等級Eye Irrit. 2Skin Irrit. 2STOT SE 3
貯蔵分類11 - Combustible Solids
有害物質データ719-22-2(Hazardous Substances Data)