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苯并[k]荧蒽 | 207-08-9

中文名称
苯并[k]荧蒽
中文别名
苯并(k)荧;苯并(k)萤蒽;苯并(k)荧蒽;苯并(K)荧蒽
英文名称
Benzo[k]fluoranthene
英文别名
——
苯并[k]荧蒽化学式
CAS
207-08-9
化学式
C20H12
mdl
——
分子量
252.315
InChiKey
HAXBIWFMXWRORI-UHFFFAOYSA-N
BEILSTEIN
——
EINECS
——
  • 物化性质
  • 计算性质
  • ADMET
  • 安全信息
  • SDS
  • 制备方法与用途
  • 上下游信息
  • 反应信息
  • 文献信息
  • 表征谱图
  • 同类化合物
  • 相关功能分类
  • 相关结构分类

物化性质

  • 熔点:
    215-217 °C(lit.)
  • 沸点:
    480 °C
  • 密度:
    1.286
  • 闪点:
    100 °C
  • 溶解度:
    95% 乙醇:20°C 时溶解度 <1mg/mL
  • 物理描述:
    Benzo(k)fluoranthene appears as pale yellow needles or yellow crystalline solid. (NTP, 1992)
  • 颜色/状态:
    Yellow prisms from hexane or acetic acid
  • 蒸汽压力:
    9.65X10-10 mm Hg at 25 °C
  • 亨利常数:
    5.84e-07 atm-m3/mole
  • 稳定性/保质期:
    - 存在于主流烟气中。 - 根据IARC的致癌性评估,证据充分,具有引发活性。
  • 分解:
    Hazardous decomposition products formed under fire conditions - Carbon oxides.[Sigma-Aldrich; Safety Data Sheet for Benzo
  • 碰撞截面:
    154.36 Ų [M+H]+ [CCS Type: DT, Method: stepped-field]
  • 保留指数:
    2722;2761;2708;2734.3;2751.2;442.6;442.8;443.6;442.8;444.2;442.6;443.4

计算性质

  • 辛醇/水分配系数(LogP):
    6.4
  • 重原子数:
    20
  • 可旋转键数:
    0
  • 环数:
    5.0
  • sp3杂化的碳原子比例:
    0.0
  • 拓扑面积:
    0
  • 氢给体数:
    0
  • 氢受体数:
    0

ADMET

代谢
环境广泛分布的多环芳烃(PAH)苯并[k]芘是一种有效的芳香烃羟化酶(AHH)诱导剂。这一点已经通过记录大鼠肝脏中苯并[a]蒽代谢物谱得以证实,方法是使用气相色谱/质谱(GC/MS)技术。即使是总共3次50微克/千克体重的剂量,也能将苯并[a]蒽的代谢提高2倍。8,9-以及5,6-二氢二醇的形成被同等程度地刺激,而10,11-二氢二醇的形成则被抑制。在相对较低的诱导剂量下,形成了一种代谢物,其所有参数都与假设的终极致癌物3,4-二羟基-1,2-环氧-1,2,3,4-四氢苯并[a]蒽相对应。这种代谢物以及许多其他初级和次级氧化产物可以在诱导后的微粒体中但不在正常微粒体中通过孵化得以识别。因此,应该强调,为了评估诱导效果,必须记录代谢物谱,而不是测量PAH底物的总转化率。
The environmentally widespread polycyclic aromatic hydrocarbon (PAH) benzo[k]fluoranthene is a potent AHH inducer. This has been proven by recording the benz[a]anthracene metabolite profile in the rat liver by means of gas chromatography/mass spectrometry (GC/MS) technique. Even a total dose of 3 times 50 micrograms/kg body wt increases the metabolism of benz[a]anthracene by a factor of 2. The formation of the 8,9- as well as the 5,6-dihydrodiol is stimulated to about the same extent, whereas the formation of the 10,11-dihydrodiol is suppressed. After comparatively low doses of the inducer, a metabolite is formed which corresponds in all parameters with the postulated ultimate carcinogen 3,4-dihydroxy-1,2-epoxy-1,2,3,4-tetrahydrobenz[a]anthracene. This metabolite and a number of other primary and secondary oxidation products could be identified after incubation with induced but not with normal microsomes. Therefore, it should be emphasised that metabolite profiles have to be recorded instead of measuring brutto conversions of PAH substrates to evaluate inducing effects.
来源:Hazardous Substances Data Bank (HSDB)
代谢
环境因素苯并(j)-荧蒽和苯并(k)荧蒽的代谢被研究了,使用的是Aroclor 1254预处理的大鼠肝脏上清液,这些上清液能有效激活苯并(j)荧蒽和苯并(k)荧蒽,转化为对鼠伤寒沙门氏菌TA 100具有诱变性的代谢物。通过高压液相色谱分离出苯并(j)荧蒽的六种代谢物带,并测试了每个带有激活作用的代谢物对S. typhimurium TA 100的诱变性。主要的诱变带包含两种二氢二醇,其中一种通过与其合成参照标准比较被鉴定为9,10-二氢-9,10-二羟基苯并(j)荧蒽。9,10-二氢-9,10-二羟基苯并(j)荧蒽在激活后对S. typhimurium TA 100具有诱变性,可能是由于转化为了相应的二氢二醇环氧化合物。苯并(k)荧蒽的主要二氢二醇代谢物通过与合成标准比较被鉴定为8,9-二氢-8,9-二羟基苯并(k)荧蒽。这种二氢二醇也可以转化为二氢二醇环氧化合物,对S. typhimurium TA 100具有激活后的诱变性。这项研究的结果表明,代谢成二氢二醇是苯并(j)荧蒽和苯并(k)荧蒽激活为S. typhimurium TA 100最终诱变剂的一条途径。
The metabolism of the environmental agents benzo(j)-fluoranthene and benzo(k)fluoranthene was investigated using supernatants from the livers of Aroclor 1254-pretreated rats, which are effective in activating benzo(j)fluoranthene and benzo(k)fluoranthene to metabolites mutagenic toward Salmonella typhimurium TA 100. Six bands of metabolites of benzo(j)fluoranthene were separated by high-pressure liquid chromatography, and each band was tested for mutagenicity toward S. typhimurium TA 100 with activation. The major mutagenic band contained two dihydrodiols, one of which was identified as 9,10-dihydro-9, 10-dihydroxybenzo(j)fluoranthene by comparison to a synthetic reference standard. 9,10-Dihydro-9,10-dihydroxybenzo(j)fluoranthene was mutagenic toward S. typhimurium TA 100 with activation, presumably as a result of conversion to the corresponding dihydrodiol-epoxide. The major dihydrodiol metabolite of benzo(k)fluoranthene was identified, by comparison to a synthetic standard, as 8,9-dihydro-8,9-dihydroxybenzo(k)fluoranthene. This dihydrodiol, which could also be converted to a dihydrodiol-epoxide, was mutagenic toward S. typhimurium TA 100 with activation. The results of this study indicate that metabolism to dihydrodiols is one pathway in the activation of benzo(j)fluoranthene and benzo(k)fluoranthene to ultimate mutagens for S. typhimurium TA 100.
来源:Hazardous Substances Data Bank (HSDB)
代谢
研究了3-, 8-和9-氟代苯并[k]荧蒽(B[k]F)相对于B[k]F的新陈代谢。使用大鼠肝脏S-9代谢系统体外形成的B[k]F的主要代谢产物是8,9-二氢-8,9-二羟基B[k]F,B[k]F的2,3-醌和3-, 8-和9-羟基B[k]F。B[k]F结构中的氟代取代显著改变了体外形成的代谢产物类型。9-氟代B[k]F的效应最为显著。与B[k]F不同,8,9-二氢-8,9-二羟基-、9-羟基-和10,11-二氢-10,11-二羟基衍生物并未作为9-氟代B[k]F的代谢产物被检测到。然而,检测到了9-氟代B[k]F的2,3-或4,5-二氢二醇。在8-氟代B[k]F的情况下,既没有检测到8-羟基-也没有检测到11-羟基-衍生物。从8-氟代B[k]F形成的主要二氢二醇是10,11-二氢二醇和2,3-或4,5-二氢二醇。3-氟代B[k]F形成的代谢产物模式与B[k]F观察到的相似,除了没有形成3-或4-羟基衍生物。质谱数据表明,在3-, 8-和9-氟代B[k]F的代谢过程中,氟代取代并未显著丢失。在鼠伤寒沙门氏菌TA100和大鼠肝脏S-9代谢系统存在下,评估了这些B[k]F氟代衍生物以及B[k]F、2,3-二氢-2,3-二羟基B[k]F、B[k]F的2,3-醌和8,9-二氢-8,9-二羟基B[k]F的致突变活性。3-氟代B[k]F比B[k]F更具致突变性,而8-和9-氟代B[k]F的活性较低。虽然2,3-二氢二醇和2,3-醌的活性较弱,但8,9-二氢二醇的致突变潜力与B[k]F相似。
The metabolism of 3-, 8- and 9-fluorobenzo[k]fluoranthene (B[k]F) relative to B[k]F was investigated. The major metabolites of B[k]F formed in vitro using rat liver S-9 metabolism systems were 8,9-dihydro-8,9-dihydroxyB[k]F, the 2,3-quinone of B[k]F and 3-, 8- and 9-hydroxyB[k]F. Fluorine substitution within the structure of B[k]F substantially altered the types of metabolites formed in vitro. The most pronounced effect was observed with 9-fluoroB[k]F. In contrast to B[k]F, the 8,9-dihydro-8,9-dihydroxy-, 9-hydroxy- and 10,11-dihydro-10,11-dihydroxy derivatives were not detected as metabolites of 9-fluoroB[k]F. However, either the 2,3- or 4,5-dihydrodiol of 9-fluoroB[k]F was detected. In the case of 8-fluoroB[k]F, neither the 8- nor 11-hydroxy- derivatives were detected. The principle dihydrodiols formed from 8-fluoroB[k]F were the 10,11-dihydrodiol and either the 2,3-or 4,5-dihydrodiol. The pattern of metabolites formed with 3-fluoroB[k]F was similar to that observed with B[k]F with the exception that neither the 3- nor 4-hydroxy derivatives were formed. Mass spectral data indicated that fluoro substitution is not lost to any appreciable extent during the metabolism of 3-, 8- and 9-fluoroB[k]F. The mutagenic activity of these B[k]F fluoro derivatives along with B[k]F, 2,3-dihydro-2,3-dihydroxyB[k]F, the 2,3-quinone of B[k]F and 8,9-dihydro-8,9-dihydroxyB[k]F were evaluated in Salmonella typhimurium TA100 in the presence of rat liver S-9 metabolism systems. 3-FluoroB[k]F was more mutagenic than B[k]F, while both 8- and 9-fluoroB[k]F were less active. While the 2,3-dihydrodiol and 2,3-quinone were weakly active, the 8,9-dihydrodiol had similar mutagenic potency to B[k]F.
来源:Hazardous Substances Data Bank (HSDB)
代谢
8,9-二氢二醇已被检测为苯并(k)荧蒽的代谢物。
The 8,9-dihydrodiol has been detected as a metabolite of benzo(k)fluoranthene.
来源:Hazardous Substances Data Bank (HSDB)
代谢
多环芳烃(PAHs)的代谢发生在所有组织中,通常通过细胞色素P-450及其相关酶进行。多环芳烃被代谢成反应性中间体,其中包括环氧中间体、二氢二醇、酚、醌以及它们的各种组合。酚、醌和二氢二醇都可以与葡萄糖苷酸和硫酸酯结合;醌还可以形成谷胱甘肽结合物。
PAH metabolism occurs in all tissues, usually by cytochrome P-450 and its associated enzymes. PAHs are metabolized into reactive intermediates, which include epoxide intermediates, dihydrodiols, phenols, quinones, and their various combinations. The phenols, quinones, and dihydrodiols can all be conjugated to glucuronides and sulfate esters; the quinones also form glutathione conjugates. (L10)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 毒性总结
识别和使用:苯并(k)荧蒽(B(k)F)是一种固体。目前没有这种化合物的商业生产或已知用途。苯并(k)荧蒽普遍存在于不完全燃烧的产物中。它也存在于化石燃料中。多环芳烃是一组化学物质,它们在煤炭、石油、天然气、木材、垃圾或其他有机物质(如烟草和炭烤肉)的不完全燃烧过程中形成。人类暴露和毒性:预计可能是一种人类致癌物。在人类乳腺癌细胞中,暴露于0.1至1微摩尔B(k)F会诱导CYP1A1/1B1催化的17 beta-雌二醇(E(2))代谢,而B(k)F水平大于1微摩尔则抑制E(2)代谢。动物研究:将2.1微摩尔苯并(k)荧蒽注入新生小鼠腹腔内,分别在6.3%和16.7%的雄性和雌性小鼠中诱导肺腺瘤,在18.8%的雄性小鼠中诱导肝细胞瘤和腺瘤。苯并(k)荧蒽在经肺植入的小鼠中产生肿瘤,并且在皮肤涂布生物测定中与促癌剂一起使用时也产生肿瘤。将苯并(k)荧蒽注入肺内导致雌性大鼠肺癌(鳞状细胞癌),而将苯并(k)荧蒽皮下注射导致注射部位(肉瘤)的癌症,这种情况在雌雄小鼠中均有发生。据报道,苯并(k)荧蒽在浓度为10微克/板的Salmonella typhimurium TA100(his-/his+)菌株和浓度为5微克/板的TA98菌株中诱导突变,前提是有外源代谢系统存在。生态毒性研究:苯并(k)荧蒽不具有光毒性,在测试的三种生物中,浓度高达300毫克/千克(在Daphnia magna、Hyalella azteca和Chironomus riparius中测试)时未表现出毒性,这种浓度在环境中很少见。
IDENTIFICATION AND USE: Benzo(k)fluoranthene (B(k)F) is a solid. There is no commercial production or known use of this compound. Benzo(k)fluoranthene occurs ubiquitously as a product of incomplete combustion. It also occurs in fossil fuels. Polycyclic aromatic hydrocarbons are a group of chemicals that are formed during the incomplete burning of coal, oil, gas, wood, garbage, or other organic substances, such as tobacco and charbroiled meat. HUMAN EXPOSURE AND TOXICITY: It is reasonably anticipated to be a human carcinogen. In human breast cancer cells, exposure to 0.1 to 1 uM B(k)F induced CYP1A1/1B1-catalyzed 17 beta-estradiol (E(2)) metabolism, whereas B(k)F levels greater than 1 uM inhibited E(2) metabolism. ANIMAL STUDIES: Intraperitoneal injection of 2.1 umol benzo[k]fluoranthene into newborn mice induced lung adenomas in 6.3% and 16.7% of males and females, respectively, and liver hepatomas and adenomas in 18.8% of males. Benzo(k)fluoranthene produced tumors after lung implantation in mice and when administered with a promoting agent in skin painting bioassays. Intrapulmonary injection of benzo[k]fluoranthene caused lung cancer (squamous-cell carcinoma) in female rats, and subcutaneous injection of benzo[k]fluoranthene caused cancer at the injection site (sarcoma) in mice of both sexes. Benzo(k)fluoranthene was reported to induce mutations in Salmonella typhimurium strain TA100 (his-/his+) at a concentration of 10 ug/plate and in strain TA98 at a concentration of 5 ug/plate in the presence of an exogenous metabolic system. ECOTOXICITY STUDIES: Benzo(k)fluoranthene was not phototoxic and presented no toxicity for the three organisms tested up to 300 mg/kg, concentration rarely found in the environment (tested in Daphnia magna, Hyalella azteca, and Chironomus riparius).
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 毒性总结
多环芳烃(PAHs)能够与血液中的蛋白质,如白蛋白结合,从而在体内进行传输。许多多环芳烃通过与芳烃受体或甘氨酸N-甲基转移酶蛋白结合,诱导细胞色素P450酶的表达,尤其是CYP1A1、CYP1A2和CYP1B1。这些酶将多环芳烃代谢成其有毒的中间产物。多环芳烃的反应性代谢物(环氧化物中间体、二氢二醇、酚、醌及其各种组合)与DNA和其他细胞大分子共价结合,启动突变和致癌过程。
The ability of PAH's to bind to blood proteins such as albumin allows them to be transported throughout the body. Many PAH's induce the expression of cytochrome P450 enzymes, especially CYP1A1, CYP1A2, and CYP1B1, by binding to the aryl hydrocarbon receptor or glycine N-methyltransferase protein. These enzymes metabolize PAH's into their toxic intermediates. The reactive metabolites of PAHs (epoxide intermediates, dihydrodiols, phenols, quinones, and their various combinations) covalently bind to DNA and other cellular macromolecules, initiating mutagenesis and carcinogenesis. (L10, L23, A27, A32)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 致癌性证据
分类:B2;可能的人类致癌物。分类依据:基于无人类数据和充足的动物生物测试数据。在肺植入实验中,小鼠接触了苯并[k]荧蒽后产生了肿瘤,并且在皮肤涂敷研究中,与促癌剂共同使用时也产生了肿瘤。在小鼠肺腺瘤实验中发现了不确定的结果。苯并[k]荧蒽在细菌中具有诱变性。人类致癌性数据:无。动物致癌性数据:充足。
CLASSIFICATION: B2; probable human carcinogen. BASIS FOR CLASSIFICATION: Based on no human data and sufficient data from animal bioassays. Benzo[k]fluoranthene produced tumors after lung implantation in mice and when administered with a promoting agent in skin-painting studies. Equivocal results have been found in a lung adenoma assay in mice. Benzo[k]fluoranthene is mutagenic in bacteria. HUMAN CARCINOGENICITY DATA: None. ANIMAL CARCINOGENICITY DATA: Sufficient.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
没有关于人类的数据。有充分的证据表明对动物具有致癌性。总体评估:2B组:该物质可能对人类具有致癌性。
No data are available in humans. Sufficient evidence of carcinogenicity in animals. OVERALL EVALUATION: Group 2B: The agent is possibly carcinogenic to humans.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
芘(k):有充分理由预期对人类是一种致癌物。/多环芳烃/
Benzo(k)fluoranthene: reasonably anticipated to be a human carcinogen. /Polycyclic Aromatic Hydrocarbons/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
荧蒽(Benzo(k)fluoranthene)在9名屋顶工人的皮肤油中检出,中位浓度为0.2 ng/mg(范围:0.02-2.2);从额头36平方厘米面积的样品中总ng数为0.8中位数(范围:0.5至4.3)。
Benzo(k)fluoranthene was detected in skin oil of 9 roofers at median concentration of 0.2 ng/mg (range: 0.02-2.2); total ng in sample from 36 sq cm area of forehead, 0.8 median (range: 0.5 to 4.3).
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
芘(k)被胃肠道和肺部迅速吸收。一般来说,多环芳烃类化合物具有很高的脂溶性,能够通过上皮膜。
Benzo(k)fluoranthene is absorbed readily from the gastrointestinal tract and lung. In general, polycyclic aromatic hydrocarbons are highly lipid soluble and can pass across epithelial membranes.
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • 危险等级:
    6.1(b)
  • 危险品标志:
    Xn,F,T,N
  • 安全说明:
    S26,S36/37,S45,S53,S60,S61,S62
  • 危险类别码:
    R45
  • WGK Germany:
    3
  • 海关编码:
    2902909090
  • RTECS号:
    DF6350000
  • 包装等级:
    III
  • 危险类别:
    6.1(b)
  • 危险品运输编号:
    UN 2811 6.1/PG 3
  • 危险标志:
    GHS02,GHS07,GHS08
  • 危险性描述:
    H315,H319,H335,H336,H351,H373
  • 危险性防范说明:
    P201,P210,P273,P280,P304 + P340 + P312,P308 + P313

SDS

SDS:d0d65482b8270d3908250d224bc127d2
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国标编号:
CAS: 207-08-9
中文名称: 苯并[k]荧蒽
英文名称: Benzo[k]fluorathene;BaF
别 名: 多环芳烃(PAH);稠环芳烃
分子式: C 20 H 12
分子量: 252
熔 点: 217℃ 沸点:480℃
密 度: 比重1.32
蒸汽压: 20℃(蒸汽压 1.32×10-13kPa )
溶解性: 不溶于水
稳定性:
外观与性状: 晶体
危险标记:
用 途: 本品在工业上无生产和使用价值,一般只作为生产过程中形成的副产物随废气排放

2.对环境的影响:
毒性毒理:人们对环境中多环芳烃的毒性的全面研究还比较少。在环境中很少遇到单一的多环芳烃(PAH),而PAH混合物中可能发生很多相互作用。PAH化合物中有不少是致癌物质,但并非直接致癌物,必须经细胞微粒中的混合功能氧化酶激活后才具有致癌性。第一步为氧化和羟化作用,产生的环氧化物或酚类可能再以解毒反应生成葡萄糖苷、硫酸盐或谷胱甘肽结合物,但某些环氧化物可能代谢成二氢二醇,它依次通过结合而生成可溶性的解毒产物或氧化成二醇-环氧化物,这后一类化合物被认为是引起癌症的终致癌物。PAH的化学结构与致癌活性有关,分子结构的改变,常引起致癌活性显著变化。在苯环骈合类的多环芳烃中有致癌活性的只是4至6环的环芳烃中的一部分。苯并[k]荧蒽的相对致癌性较弱。

代谢、降解、蓄积:PAH具有高度的脂溶性,易于经哺乳动物的内脏和肺吸收,能迅速地从血液和肝脏中被清除,并广泛分布于各种组织中,特别倾向于分布在体脂中。虽然PAG有高度的脂溶性,但是在动物或人的脂肪中几乎无生物蓄积作用的倾向,主要因为PAH能迅速和广泛地被代谢,代谢产物主要以水溶性化合物从尿和粪中排泄。在环境大气和水体中的PAH受到足够能量的阳光中紫外线的照射时会发生光解作用,土壤中的某些微生物可以使PAH降解,但分子量较大的苯并[k]荧蒽的光解、水解和生物降解是很微弱的。

迁移、转化:环境中的PAH主要来源于煤和石油的燃烧,也可来自垃圾焚烧或森林大火。其生成量同燃烧设备和燃烧温度等因素有关,如大型锅炉生成量很低,家用煤炉生成量很高。柴油和汽油机的排气中,以及炼油厂、煤焦油加工厂和沥青加工厂等排出的废气和废水中都含有PAH。PAH还存在于熏制的食物和香烟烟雾中。PAH大多吸附在大气和水中的微小颗粒物上,大气中的PAH为通过沉降和降水而污染土壤和地面水,研究表明,除了工业排污外,大气降水是径流排水中PAH的主要来源。由于PAH的水中溶解度低和亲脂性较强,因此该类化合物易于从不中分配到沉积物、有机质及生物体内,其结果使水中PAH的浓度较低,而在沉积物中残留浓度较高。


3.现场应急监测方法:



4.实验室监测方法:
高效液相色谱法(GB13198-91,水质)
气相色谱法《空气中有害物质的测定方法》(第二版),杭士平编
气相色谱法《固体废弃物试验分析评价手册》中国环境监测总站等译


5.环境标准:
欧洲共同体(1975)饮用水 0.0001mg/L(PAH)


6.应急处理处置方法:
处置:由于PAH与悬浮固体紧密结合,所以可以通过采用水处理措施降低浊度来保证PAH含量降至最低水平。

预防措施:由于PAH污染人类环境的范围很广,产生污染的具体原因很多,所以预防措施涉及的工艺操作过程,废水废气的综合利用和处理,自来水的净化和消毒,改进汽油燃烧过程,改良食品烟熏剂,提供间接烘烤,养成个人卫生习惯(不吸烟或少吸烟)等。






制备方法与用途

类别:有毒物品

可燃性危险特性:

  • 可燃;燃烧时会产生刺激性烟雾

储运特性:

  • 保持通风、低温和干燥环境

灭火剂:

  • 干粉、泡沫、沙土、二氧化碳、雾状水

上下游信息

  • 上游原料
    中文名称 英文名称 CAS号 化学式 分子量
  • 下游产品
    中文名称 英文名称 CAS号 化学式 分子量

反应信息

  • 作为反应物:
    参考文献:
    名称:
    Moureu; Chovin; Rivoal, Bulletin de la Societe Chimique de France, 1948, p. 99,103
    摘要:
    DOI:
  • 作为产物:
    描述:
    (E)-triisopropyl((8-styrylnaphthalen-1-yl)ethynyl)silane 在 四丁基氟化铵 作用下, 以 四氢呋喃甲苯 为溶剂, 反应 24.5h, 生成 苯并[k]荧蒽
    参考文献:
    名称:
    Ruthenium-Catalyzed Peri- and Ortho-Alkynylation with Bromoalkynes via Insertion and Elimination
    摘要:
    The alkynylation of naphthols takes place with total regiocontrol at the peri position of the hydroxyl group in the presence of [RuCl2(p-cymene)](2) as the catalyst. This reaction features high functional group tolerance. The related ortho-alkynylation of benzoic acids proceeds under similar conditions and also shows wide functional group tolerance. Both reactions proceed through metalation, insertion of the alkyne, and bromide elimination.
    DOI:
    10.1021/acs.orglett.7b02655
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文献信息

  • Scholl Cyclizations of Aryl Naphthalenes: Rearrangement Precedes Cyclization
    作者:Sarah L. Skraba-Joiner、Erin C. McLaughlin、Aida Ajaz、Rajesh Thamatam、Richard P. Johnson
    DOI:10.1021/acs.joc.5b01559
    日期:2015.10.2
    We provide evidence that this classic organic name reaction proceeds through sequential and reversible formation of 1,2′- and 2,2′-binaphthyl isomers. Acid-catalyzed isomerization of 1,1′-binaphthyl to 2,2′-binaphthyl has been noted previously. The superacid trifluoromethanesulfonic acid (TfOH), 1 M in dichloroethane, catalyzes these rearrangements, with slower cyclization to perylene. Minor cyclization
    在1910年,Scholl,Seer和Weitzenbock报告了AlCl 3催化的1,1'-联萘基环化为per。我们提供的证据表明,这种经典的有机名称反应是通过顺序地和可逆地形成1,2'-和2,2'-联萘异构体而进行的。先前已经注意到酸催化的1,1′-联萘基异构化为2,2′-联萘基。在二氯乙烷中1 M的超强酸三氟甲磺酸(TfOH)催化这些重排,但环化成to的速度较慢。次要环化产物为苯并[ k ]荧蒽和苯并[ j]荧蒽。在环境温度下,观察到的1,1'-联萘,1,2'-联萘和2,2'-联萘的平衡比<1:3:97。DFT计算与包含溶剂化的支持,其中一个机械方案本位-arenium离子是负责重排; 但是,对于环化步骤,我们无法区分芳族离子机理和自由基阳离子机理。在相似的反应条件下,1-苯基萘与2-苯基萘相互转化,后者以平衡状态(5:95的比例)受青睐,并且也缓慢转化为荧蒽。计算再次支持用于重排的芳烃离子机制。
  • Emission Factors and Importance of PCDD/Fs, PCBs, PCNs, PAHs and PM<sub>10</sub> from the Domestic Burning of Coal and Wood in the U.K.
    作者:Robert G. M. Lee、Peter Coleman、Joanne L. Jones、Kevin C. Jones、Rainer Lohmann
    DOI:10.1021/es048745i
    日期:2005.3.1
    fuels. However, their combined emissions from the domestic burning of coal and wood would contribute only a few percent to annual U.K. emission estimates. Emissions of PAHs and PM10 were major contributors to U.K. national emission inventories. Major emissions were found from the domestic burning for Cl1,2,3DFs, while the contribution of PCDD/F-sigmaTEQ to total U.K. emissions was minor.
    本文介绍了当煤和木材经过受控燃烧实验时针对一系列持久性有机污染物(POPs)得出的排放因子(EFs),旨在模拟空间供暖的家庭燃烧。排放了各种各样的持久性有机污染物,煤炭的排放量高于木材的排放量。对于颗粒物,PM10(大约10 g / kg燃料)和多环芳烃(对于sigmaPAHs大约100 mg / kg燃料)获得了最高的EF。对于氯化物,多氯联苯(PCB)的EF最高,而多氯萘(PCN),二苯并-对-二恶英(PCDD)和二苯并呋喃(PCDF)的丰度较低。对于sigmaPCB,EF大约为1000 ng / kg燃料,对于sigmaPCNs大约为100s ng / kg燃料,对于sigmaPCDD / Fs大约为100 ng / kg燃料。该研究证实,一氯化至三氯化二苯并呋喃Cl1,2,3DFs是低温燃烧过程(如煤炭和木材的国内燃烧)的有力指标。结论是,在固体燃料燃烧期间通常形成许多PCB和PC
  • Three-Step Synthesis of Fluoranthenes through Pd-Catalyzed Inter- and Intramolecular C–H Arylation
    作者:Miyuki Yamaguchi、Mayu Higuchi、Kanae Tazawa、Kei Manabe
    DOI:10.1021/acs.joc.6b00553
    日期:2016.5.6
    the preparation of fluoranthenes, involving Miura’s intermolecular C–H arylation, nonaflation, and intramolecular C–H arylation, has been developed. Various 1-naphthols and haloarenes were successfully used as substrates. Reaction conditions that afford high site selectivity have been developed for the intramolecular C–H arylation step.
    已经开发了一种三步合成的荧光素合成方法,涉及Miura的分子间C–H芳基化,非消融和分子内C–H芳基化。各种1-萘酚和卤代芳烃已成功用作底物。已经为分子内CH芳基化步骤开发了具有高位点选择性的反应条件。
  • NMR and DFT Study on Onium Ions Derived from Substituted Fluoranthenes and Benzo[<i>k</i>]fluoranthenes
    作者:Takao Okazaki、Taisuke Adachi、Toshikazu Kitagawa
    DOI:10.1246/bcsj.20120308
    日期:2013.4.15
    Fluoranthene and benzo[k]fluoranthene (3) are nonalternant polyaromatic hydrocarbons. Their derivatives, 3-acetyl, 8-acetyl, 3-nitro, and 3-aminofluoranthenes (4, 5, 7, and 8) were reacted in FSO3H...
    荧蒽和苯并[k]荧蒽 (3) 是非交替多环芳烃。它们的衍生物 3-乙酰基、8-乙酰基、3-硝基和 3-氨基荧蒽(4、5、7 和 8)在 FSO3H...
  • Efficient Routes to Acenaphthylene-Fused Polycyclic Arenes/Heteroarenes and Heterocyclic Fluoranthene Analogues
    作者:Kausik Panda、Chelvam Venkatesh、Hiriyakkanavar Ila、Hiriyakkanavar Junjappa
    DOI:10.1002/ejoc.200400735
    日期:2005.5
    α-oxoketene dithioacetal 2 has been subjected to various [3 + 3] aromatic and heteroaromatic annulation and other heterocyclization reactions previously developed in our laboratory, providing short and efficient routes to a diverse range of known and unknown acenaphtho-annulated linear and angular PAHs, heteroaromatics and five-membered heterocycles in good yields. Thus, benzo- and naphthoannulation of 2 with
    苊酮衍生的 α-氧代烯酮二硫缩醛 2 已经进行了各种 [3 + 3] 芳族和杂芳族环化以及我们实验室先前开发的其他杂环化反应,为各种已知和未知的苊环化线性提供了短而有效的途径和角多环芳烃、杂芳烃和五元杂环的收率良好。因此,2 与各种烯丙基和苄基格氏试剂的苯并环和萘环化分别以良好的产率得到取代的荧蒽 4a-c 和苯并 [k] 荧蒽 8。类似地,母体苯并[j]荧蒽 15a 及其取代衍生物 16b 已通过芳基乙腈与 2 的碱诱导共轭 1,4-加成合成,接着是酸诱导的共轭加合物 12a-b 环化得到 13a-b 并随后进一步转化。由苯乙酮和苊酮衍生的阴离子的 1,4-加成得到的加合物在乙酸铵存在下进行杂环化,得到 8-芳基苊[1,2-b]吡啶 18a-b 和双(苊)-环化吡啶 20 . 2 与双功能亲核试剂(如 2-吡啶甲基锂和硝酸胍)的杂环化分别以高产率得到相应的苊并 [1,2-b] 喹啉鎓盐 23
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表征谱图

  • 氢谱
    1HNMR
  • 质谱
    MS
  • 碳谱
    13CNMR
  • 红外
    IR
  • 拉曼
    Raman
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mass
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ir
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  • 峰位数据
  • 峰位匹配
  • 表征信息
Shift(ppm)
Intensity
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Assign
Shift(ppm)
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测试频率
样品用量
溶剂
溶剂用量
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