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荧蒽 | 206-44-0

中文名称
荧蒽
中文别名
1,2-苯并苊;苯并[j,k]芴;苯并苊,萤蒽,二苯(a)并;萤蒽;苯并苊
英文名称
fluoranthene
英文别名
benzo[j,k]fluorene
荧蒽化学式
CAS
206-44-0
化学式
C16H10
mdl
MFCD00001184
分子量
202.255
InChiKey
GVEPBJHOBDJJJI-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:
    105-110 °C (lit.)
  • 沸点:
    384 °C (lit.)
  • 密度:
    1.252
  • 闪点:
    -18 °C
  • 溶解度:
    氯仿(可溶)、DMSO(少量溶解)、乙酸乙酯(少量溶解)、甲醇(少量溶解)
  • 物理描述:
    Fluoranthene appears as light yellow fine crystals. (NTP, 1992)
  • 颜色/状态:
    Colored needles
  • 蒸汽压力:
    9.22X10-6 mm Hg at 25 °C
  • 亨利常数:
    8.86e-06 atm-m3/mole
  • 大气OH速率常数:
    5.00e-11 cm3/molecule*sec
  • 稳定性/保质期:
    1. 本品有毒,且有腐蚀性,大鼠经口LD₅₀为2000毫克/公斤。操作人员应佩戴防护用具。 2. 它存在于烟叶和主流烟气中。
  • 分解:
    Hazardous decomposition products formed under fire conditions. - Carbon oxides.
  • 碰撞截面:
    136.7 Ų [M*]+; 137.2 Ų [M+H]+
  • 保留指数:
    2020.45;2038.9;2062.3;2015;2091;2091;2051;2091;2028;2031;2006;2041.4;2030;2091;2086.3;338.5;344;344.6;340.66;340.99;341.94;342.27;343.15;343.16;343.44;344.01;344;349.3

计算性质

  • 辛醇/水分配系数(LogP):
    5.2
  • 重原子数:
    16
  • 可旋转键数:
    0
  • 环数:
    4.0
  • 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
白地霉ATCC 36112在培养的72小时内代谢了大约80%添加的(3-14)C标记的芴(FA)。白地霉将芴代谢为反式-2,3-二羟基-2,3-二氢芴(反式-2,3-二氢二醇)、8-和9-羟基芴反式-2,3-二氢二醇、3-芴-β-葡萄糖苷和3-(8-羟基芴)-β-葡萄糖苷。这些代谢物通过薄层和反相高效液相色谱分离,并通过1H核磁共振、紫外光谱和质谱技术鉴定。主要途径涉及羟基化形成3-羟基芴的葡萄糖苷共轭物和3,8-二羟基芴的葡萄糖苷共轭物,这两者共同占可溶于乙酸乙酯的代谢物总量的52%。白地霉最初在2,3位置代谢芴形成芴反式-2,3-二氢二醇,该化合物在哺乳动物和细菌基因毒性试验中已被证明是一种具有生物活性的化合物。然而,白地霉主要形成芴酚衍生物的葡萄糖苷共轭物,这表明这种真菌具有解毒芴的潜力。
The fungus Cunninghamella elegans ATCC 36112 metabolized approximately 80% of the (3-14)C-labeled fluoranthene (FA) added within 72 hr of incubation. C. elegans metabolized FA to trans-2,3-dihydroxy-2,3-dihydrofluoranthene (trans-2,3-dihydrodiol), 8- and 9-hydroxyfluoranthene trans-2,3-dihydrodiol, 3-fluoranthene-beta-glucopyranoside, and 3-(8-hydroxyfluoranthene)-beta-glucopyranoside. These metabolites were separated by thin-layer and reversed-phase high-performance liquid chromatography and identified by 1H nuclear magnetic resonance, UV, and mass spectral techniques. The major pathway involved hydroxylation to form a glucoside conjugate of 3-hydroxyfluoranthene and a glucoside conjugate of 3,8-dihydroxyfluoranthene which together accounted for 52% of the total ethyl acetate-soluble metabolites. C. elegans initially metabolized FA in the 2,3 position to form fluoranthene trans-2,3-dihydrodiol, which has previously been shown to be a biologically active compound in mammalian and bacterial genotoxicity tests. However, C. elegans formed predominantly glucoside conjugates of the phenolic derivatives of FA, which suggests that this fungus has the potential to detoxify FA.
来源:Hazardous Substances Data Bank (HSDB)
代谢
二氢二醇作为荧蒽的代谢物,在大鼠肝脏制剂孵化后已被检测到。研究发现,在代谢活化系统的存在下,二氢二醇对细菌具有诱变性。
The 2,3-dihydrodiol has been detected as a metabolite of fluoranthene following incubation of this compound with a rat-liver preparation. The 2,3-dihydriol was found to be mutagenic to bacteria in the presence of a metabolic activation system.
来源:Hazardous Substances Data Bank (HSDB)
代谢
荧蒽的代谢物...通过用Aroclor预处理的大鼠肝脏匀浆进行孵化得到...2,3-二氢-2,3-二羟基荧蒽。
The metabolite of fluoranthene ... obtained upon incubation with liver homogenate from Aroclor pretreated rats ... 2,3-dihydro-2,3-dihydroxyfluoranthene.
来源:Hazardous Substances Data Bank (HSDB)
代谢
化学污染食品富含有脂肪,可能会导致癌症和毒性等健康问题。脂肪摄入量的增加和脂肪中毒性化学物质的滞留,会加大人体健康风险。本研究的目的是探讨饮食脂肪对多环芳香族化合物氟罗烷(FLA)的处置和代谢的影响。将FLA以单不饱和(花生油)、多不饱和(玉米油)和饱和(椰子油)脂肪的形式,以50和100微克/千克的剂量,通过口服给药的方式给予F-344大鼠。在FLA暴露后的不同时间点收集血液、小肠、肝脏、肺、睾丸、脂肪组织、尿液和粪便。通过反相高效液相色谱法分析FLA母体化合物及其代谢物。从组织中提取DNA,并采用(32)P-后标记法检测FLA-DNA加合物。与单不饱和和多不饱和脂肪组相比,饱和脂肪处理组的未改变FLA (FLA母体化合物)及其代谢物的浓度有所增加。通过饱和脂肪接受FLA的大鼠组织中FLA-DNA加合物的浓度较高。毒物动力学参数、FLA代谢物浓度和FLA-DNA加合物浓度呈剂量依赖性增加,且这种增加在饱和脂肪中具有统计学意义(P<0.05)。这些发现清楚地表明,饱和脂肪中FLA母体化合物的长时间滞留,使得FLA的活性代谢物与DNA结合,导致长期暴露下的明显损伤。
Adverse health effects such as cancer and toxicity may be attributed to consumption of chemically contaminated food rich in fat. This leads to a larger intake and retention of lipophilic toxic chemicals in the body with an increase in risks to human health. The objective of this study was to characterize the effect of dietary fat on disposition and metabolism of fluoranthene (FLA), a polycyclic aromatic hydrocarbon compound. FLA was administered to F-344 rats in monounsaturated (peanut oil), polyunsaturated (corn oil) and saturated (coconut oil) fats at doses of 50 and 100 ug/kg via oral gavage. Blood, small intestine, liver, lung, testis, adipose tissue, urine and feces were collected at various time points' post-FLA exposure. Samples were analyzed by reverse-phase high-performance liquid chromatography for FLA parent compound and metabolites. DNA was isolated from the tissues and subjected to (32)P-post labeling to measure FLA-DNA adducts. The concentrations of unchanged FLA (FLA parent compound) and its metabolites showed an increase for the saturated fat treatment group compared with mono- and polyunsaturated fat groups. The FLA-DNA adduct concentrations were high in tissues of rats that received FLA through saturated fat. The toxicokinetic parameters, concentrations of FLA metabolites and FLA-DNA adduct showed a dose-dependent increase, and this increase was statistically significant (P<.05) for saturated fat. These findings clearly demonstrate that the high residence time of FLA parent compound in saturated fat allows extensive metabolism, contributing reactive metabolites of FLA that bind with DNA and causing marked damage in a long-term exposure scenario.
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
鉴定和使用:芴是一种固体。目前,还没有已知的这种化合物的生产或使用。多环芳烃是一组在煤炭、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的化学物质。人类暴露和毒性:芴在存在外源代谢系统的情况下,对培养的人淋巴母细胞系具有诱变性。它被确认为人类致癌物。动物研究:使用新生小鼠进行了为期24周的肺腺瘤生物测定,以确定芴的致瘤性。在最高剂量(每只小鼠3.5毫克)处理的小鼠中观察到肺肿瘤发生率增加了6.5倍(58%),肿瘤数量增加了12倍(每只小鼠1.08个肿瘤),但每只小鼠700微克的剂量并未诱导肿瘤发生率的增加。在另一项实验中,将芴通过腹腔注射入断乳前的小鼠体内,剂量为0.7、1.75和3.5毫克,6-9个月后诱导了肺和肝肿瘤。尽管芴在细菌和哺乳动物体外细胞系统中经过代谢激活后具有诱变性,但关于体内诱变性的信息缺乏,关于小鼠肿瘤启动活性的研究结果是模棱两可的。芴可以在大鼠中产生行为毒性。芴还可能损害B淋巴细胞的生成。进行了一项发育研究,其中在妊娠第6、7、8或9天通过腹腔注射一次给C57/B6小鼠注射芴。观察到胚胎吸收率增加。生态毒性研究:在标准实验室荧光灯和紫外光测试条件下,对一组多样的淡水和海水物种进行了芴的急性毒性和慢性毒性研究。21种物种的急性测试表明,在荧光灯下,芴在其水溶性极限内对大多数测试物种并不致命,但在紫外光下,远低于这一极限时对几乎所有测试物种都是致命的。总体而言,紫外光将急性芴毒性提高了大约一到三个数量级。
IDENTIFICATION AND USE: Fluoranthene is a solid. Currently, there is no known production of or use of this compound. 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: Fluoranthene was mutagenic to cultured human Iymphoblastoid cells in the presence of an exogenous metabolic system. It is confirmed human carcinogen. ANIMAL STUDIES: A 24 week lung adenoma bioassay using newborn mice was employed to determine the tumorigenicity of fluoranthene. A 6.5-fold elevation of lung tumor incidence (58%) and a 12-fold increase in numbers (1.08 tumors/mouse) was observed in animals treated with the highest dose (3.5 mg/mouse), but no increase in tumor incidence was induced by 700 micrograms/mouse. In other experiment, fluoranthene induced lung and liver tumors 6-9 months after intraperitoneal injection of 0.7, 1.75 and 3.5 mg into preweanling mice. Although fluoranthene is mutagenic in bacterial and mammalian in vitro cell systems following metabolic activation, information on in vivo mutagenicity is lacking and studies on tumor initiating activity in mice are equivocal. Fluoranthene can produce behavioral toxicity in rats. Fluoranthene could also compromise B lymphopoiesis. A developmental study was performed in which fluoranthene was administered once via intraperitoneal injection to pregnant C57/B6 mice on gestational day 6, 7, 8 or 9. An increased rate of embryo resorption was observed. ECOTOXICITY STUDIES: The acute and chronic toxicity of fluoranthene was determined for a diverse group of freshwater and saltwater species under both standard laboratory fluorescent light and ultraviolet (UV) light test conditions. Acute tests with 21 species demonstrated that fluoranthene was not lethal within its water solubility limit to most species tested under fluorescent light, but was lethal well below this limit to nearly all of the species tested under UV light. Overall, UV light increased acute fluoranthene toxicity approximately one to three orders of magnitude.
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。许多多环芳烃通过结合芳烃受体或甘氨酸N-甲基转移酶蛋白,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:D;无法归类为人类致癌性。分类依据:基于没有人类数据和动物生物试验的不充分数据。人类致癌性数据:无。动物致癌性数据:不充分。
CLASSIFICATION: D; not classifiable as to human carcinogenicity. BASIS FOR CLASSIFICATION: Based on no human data and inadequate data from animal bioassays. HUMAN CARCINOGENICITY DATA: None. ANIMAL CARCINOGENICITY DATA: Inadequate.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
没有关于人类的数据。动物致癌性证据不足。总体评估:第3组:该物质对人类致癌性无法分类。
No data are available in humans. Inadequate evidence of carcinogenicity in animals. OVERALL EVALUATION: Group 3: The agent is not classifiable as to its carcinogenicity to humans.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌物分类
国际癌症研究机构致癌物:荧蒽
IARC Carcinogenic Agent:Fluoranthene
来源:International Agency for Research on Cancer (IARC)
吸收、分配和排泄
雄性大鼠单次腹腔注射(3)H-荧蒽后24小时,研究了血红蛋白结合的剂量依赖性以及荧蒽及其荧蒽-DNA加合物在不同组织中的分布。还研究了饮食中长期给予荧蒽后DNA加合物的形成和分布。单次给药后,荧蒽衍生的放射性物质在动物体内广泛分布,所有剂量水平下,排泄物中含有的放射性物质最多。荧蒽与珠蛋白的结合在2 nmol/kg到177 umol/kg的剂量范围内与剂量成正比,加合物蛋白的清除速率与未修饰的血红蛋白相同,表明这些加合物在体内是稳定的。相比之下,荧蒽-DNA加合物在单次给药后24小时内在肝脏或肾脏中并未达到可检测水平;只有在最高剂量水平下,在肺部发现了低水平的加合物。然而,饮食中长期给予荧蒽导致了大多数被检查的组织中DNA加合物的形成,包括肝脏、肾脏、肺、小肠、心脏、脾脏和淋巴细胞;在睾丸DNA中未检测到加合物。在大鼠组织中发现的主要荧蒽-DNA加合物,通过其色谱相似性被鉴定为使用微体活化的荧蒽和牛胸腺DNA在体外形成的 主要荧蒽加合物,之前被鉴定为反-2,3-二羟基-1,10b-环氧-1,2,3-三氢荧蒽与N2-脱氧鸟苷的反应产物。这种二醇环氧在生理pH下的不寻常稳定性可能允许这种最终DNA结合代谢物几乎运输到所有组织。这些结果表明,HPLC-(32)P后标记程序可用于检测和量化体内形成的荧蒽-DNA加合物,并且建议分析这些加合物在可接触的组织(如淋巴细胞)中可能是评估长期、高水平暴露于荧蒽的一种方法。我们的结果还表明,如果开发出合适的检测方法,荧蒽的血红蛋白加合物可能是有用的剂量计,用于检测短期或长期暴露于该化合物。
The dose-dependence of hemoglobin binding as well as distribution of fluoranthene and fluoranthene-DNA adducts in various tissues was characterized in male rats 24 hr after a single i.p. injection of (3)H-fluoranthene. Formation and distribution of DNA adducts after chronic administration of fluoranthene in the diet was also studied. Fluoranthene-derived radioactivity was widely distributed throughout the animal after a single dose, and excreta contained the greatest amounts of radioactivity at all dose levels. Fluoranthene binding to globin was proportional to dose over the range of 2 nmol/kg to 177 umol/kg, and the adducted protein was cleared at the same rate as unmodified hemoglobin, indicating that the adducts are stable in vivo. In contrast, fluoranthene-DNA adducts were not present at detectable levels in liver or kidney 24 hr after one dose; low levels of adducts were found only in the lung at the highest dose level. Chronic administration of fluoranthene in the diet, however, resulted in DNA adduct formation in most tissues examined, including liver, kidney, lung, small intestine, heart, spleen and lymphocytes; adducts were not detectable in testes DNA. The major fluoranthene-DNA adduct found in rat tissues was identified by its chromatographic similarity to the major fluoranthene adduct formed in vitro using microsomally-activated fluoranthene and calf thymus DNA, previously identified as a reaction product of anti-2,3-dihydroxy-1,10b-epoxy-1,2,3-trihydro-fluoranthene with N2-deoxyguanosine. The unusual stability of this diol epoxide at physiological pH may allow transport of this ultimate DNA-binding metabolite to virtually all tissues. These results demonstrate the applicability of the HPLC-(32)P-postlabelling procedure to detect and quantify fluoranthene-DNA adducts formed in vivo, and suggest that analysis of these adducts in accessible tissues such as lymphocytes may be a means of assessing chronic, high level exposure to fluoranthene. Our results also indicate that hemoglobin adducts of fluoranthene could be useful dosimeters for detecting short-term or chronic exposure to this compound if a suitable method for their detection were developed.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
/MILK/ 多环芳烃(PAHs)在怀孕期间暴露于柴油尾气(DE)的Fischer 344大鼠的母体血液和胎儿中进行了分析,以及在怀孕和哺乳期间暴露于DE的大鼠的母乳中进行了分析,使用高效液相色谱法结合荧光检测。与对照组相比,DE组的母体血液中菲(Phe)、蒽(Ant)和苯并[a]蒽(BaA)的浓度显著较高。DE组胎儿中Phe的浓度显著高于对照组。DE组胎儿中荧蒽、Ant、芴(Flu)、芘(Pyr)、BaA和屈(Chr)的浓度有升高趋势。DE组母乳中Ant、Flu、Pyr和Chr的水平显著高于对照组。这些结果表明,通过吸入DE进入母鼠体内的PAHs可以通过胎盘传递给胎儿,并进入母乳中。...
/MILK/ Polycyclic aromatic hydrocarbons (PAHs) were analyzed in maternal blood and fetuses from Fischer 344 rats exposed to diesel exhaust (DE) during pregnancy, and in breast milk from rats exposed to DE during pregnancy and lactation using high performance liquid chromatography with fluorescence detection. Concentrations of phenanthrene (Phe), anthracene (Ant) and benz[a]anthracene (BaA) were significantly higher in maternal blood of the DE group than those of the control group. Concentration of Phe in fetuses of the DE group was significantly higher than those of the control group. Concentrations of fluorene, Ant, fluoranthene (Flu), pyrene (Pyr), BaA and chrysene (Chr) tended to be higher in fetuses of the DE group. The levels of Ant, Flu, Pyr and Chr in breast milk from the DE group were significantly higher than those of the control group. These results indicate that PAHs taken into mother rat by the inhalation of DE are transferred into fetuses via placenta and into breast milk. ...
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
芴苯已在人类尿液和粪便中被发现。
Fluoranthene has been found in human urine and feces.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
血液中的芴、芘和苯并[a]蒽经口服给药后的水平在大鼠中进行了检测。将芴、芘或苯并[a]蒽溶解在Tween 80/等渗盐水中,以20 mg/kg的剂量口服给予大鼠。给药后的血液水平显示,三种化合物的峰值浓度在给药后1-2小时达到。芴的峰值浓度(大约30 mg/立方厘米)是芘的两倍,是苯并[a]蒽的5倍。
Blood levels of fluoranthene, pyrene, and benz[a]anthracene after oral administration were examined in rats. Fluoranthene, pyrene, or benz[a]anthracene in Tween 80/isotonic saline, was administered orally to rats at a dose of 20 mg/kg. Blood levels after administration indicated that peak concentrations of the three compounds were reached at 1-2 hours after administration. The peak concentration of fluoranthene (approximately 30 mg/cu cm) was twice as high as that of pyrene, and 5 times higher than benz[a]anthracene.
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • 危险品标志:
    Xn
  • 安全说明:
    S26,S37/39
  • 危险类别码:
    R22,R36/37/38
  • WGK Germany:
    2
  • 海关编码:
    2902909090
  • 危险品运输编号:
    UN 3077 9 / PGIII
  • RTECS号:
    LL4025000
  • 储存条件:
    本品应密封保存。它属于有机腐蚀品,危规编号为98018。更多信息可参考苊。

SDS

SDS:61f6875c525c6b13443699b50fb28008
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国标编号: 83510
CAS: 206-44-0
中文名称: 荧蒽
英文名称: Fluoranthene;1,2-Benzacenaphthene
别 名: 多环芳烃(PAH);稠环芳烃
分子式: C 16 H 10
分子量: 202.26
熔 点: 109~110℃
密 度: 相对密度(水=1)1.252(
蒸汽压:
溶解性: 不溶于水,溶于苯、乙醚、乙醇、乙酸
稳定性: 稳定
外观与性状: 黄绿色结晶或无色固体。常温下无臭无味
危险标记: 20(腐蚀品),40(有毒品)
用 途: 用于制造染料、合成树脂和工程塑料等

2.对环境的影响: 一、健康危害 侵入途径:吸入、食入、经皮吸收。 健康危害:吸入、摄入或以皮肤吸收后会中毒。具腐蚀性。资料报道有致突变作用。 二、毒理学资料及环境行为 毒性:低毒类。无致癌作用。 急性毒性:LD502000mg/kg(大鼠经口);3180mg/kg(兔经皮) 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。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。 危险特性:遇明火、高热可燃。与氧化剂能发生强烈反应。有腐蚀性。 燃烧(分解)产物:一氧化碳、二氧化碳。 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: 一、泄漏应急处理 隔离泄漏污染区,周围设警告标志,建议应急处理人员戴好防毒面具,穿化学防护服。不要直接接触泄漏物,用砂土或其它不燃性吸附剂混合吸收,收集于一个密闭的容器中,运至废物处理场所。用水刷洗泄漏污染区,经稀释的污水放入废水系统。如大量泄漏,收集回收或无害处理后废弃。 二、防护措施 呼吸系统防护:作业工人应该佩戴防尘口罩。空气中浓度较高时,佩戴防毒面具。 眼睛防护:戴化学安全防护眼镜。 防护服:穿防腐工作服。 手防护:戴橡胶手套。 其它:工作现场禁止吸烟、进食和饮水。工作后,淋浴更衣。工作服不要带到非作业场所,单独存放被毒物污染的衣服,洗后再用。注意个人清洁卫生。 三、急救措施 皮肤接触:用肥皂水及清水彻底冲洗。就医。 眼睛接触:拉开眼睑,用流动清水冲洗15分钟。就医。 吸入:脱离现场至空气新鲜处。呼吸困难时给输氧。呼吸停止时,立即进行人工呼吸。就医。 食入:误服者,口服牛奶、豆浆或蛋清,就医。 灭火方法:泡沫、砂土。 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

理化性质

荧蒽为白色或淡黄色针状或片状结晶。分子量202.26,熔点111℃,沸点约375℃,相对密度1.202,折射率1.0996 (18.7℃)。它溶于醚、苯、氯仿、二硫化碳、乙酸和热醇中,微溶于冷醇且不溶于水。荧蒽在紫外线照射下会显现出荧光。

主要用途

荧蒽是一种四环芳烃,是煤焦油加工过程中的产物之一。它通常在高温煤焦油中有约2.5%的含量,主要集中在二蒽油馏分中。荧蒽可用于制备染料和医药产品,如紫色还原染料3-氨基-8,9-酞酰荧蒽、黄色染料11,12-酞酰荧蒽以及治疗霍乱和痉挛药物等。

应用

荧蒽可作为非磁性金属表面探伤剂的荧光剂、染料中间体及医药中间体使用。

提取荧蒽的方法

以二蒽油馏分或沥青蒸出油为原料,通过减压精馏分离并切取375~385℃的荧蒽馏分。此过程需多次重结晶。采用30%溶剂油与70%乙醇的混合物作为溶剂,荧蒽与溶剂的比例为1:1。将荧蒽与配好的混合溶剂装入结晶器内边搅拌加热直至完全溶解后冷却结晶、离心分离,反复此过程直到得到合格的产品。

毒性和致癌性

荧蒽被归类于潜在致癌物(多环芳烃)。尽管实验中未表现出致突变或原发致癌特性,但它作为辅致癌物质的作用已经证实。对多种淡水和海水生物有毒性。

接触机会与健康危害

高温热解加工煤、石油等有机原料时可产生荧蒽;自然界中它也是植物生物合成的产物,广泛存在于环境中如饮水、食物原材料及香烟中。特定职业群体如炼焦、炼钢工人以及吸烟者暴露于荧蒽的风险较高。

化学性质

无色或黄绿色针状结晶,不溶于水但稍溶于乙醇,易溶于二硫化碳和醋酸,可溶于乙醚及苯类。在紫外线照射下显现出荧光。

用途

用作非磁性金属表面探伤剂的荧光剂、合成染料以及药物生产等。

生产方法

从煤焦油中回收荧蒽的最佳原料为Ⅱ蒽油和沥青氧化过程中的馏出物。在间歇式直接火加热蒸馏锅中通入少量过热蒸汽,并于0.09MPa真空度下进行蒸馏,将馏出的物质经过精馏塔、分凝器及冷却器处理后,在高于熔点温度下流入受槽收集375-385℃范围内的馏分结晶并离心脱油得到粗荧蒽。用混合溶剂(30%轻溶剂油和70%乙醇)进行重结晶,得到成品,收率可达40%,纯度99%。

类别

腐蚀物品

毒性分级

中毒

急性毒性

口服-大鼠LD50: 2000毫克/公斤

爆炸物危险特性

对皮肤、角膜有腐蚀性

可燃性危险特性

可燃;燃烧产生刺激烟雾

储运特性

库房通风低温干燥,与氧化剂分开存放。

灭火剂

砂土、泡沫、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
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    • 2
    • 3
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    • 6
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反应信息

  • 作为反应物:
    描述:
    荧蒽 在 sodium amide 作用下, 以 N,N-二甲基乙酰胺 为溶剂, 反应 10.0h, 以46.7%的产率得到二茚并
    参考文献:
    名称:
    一种二茚并苝的合成方法
    摘要:
    本发明公开了一种二茚并苝的合成方法,包括如下步骤:将荧蒽、氨基钠和有机溶剂加入反应容器中,向反应容器中充入惰性气体,然后加热以进行合成反应得到含二茚并苝的混合溶液;将含二茚并苝的混合溶液冷却后,滴加无水乙醇,再滴加水,过滤得到二茚并苝粗品。本发明与现有技术相比,具有如下有益效果:本发明的反应路线原料易得,成本低,收率高,工艺要求低,操作简单,反应过程及后处理安全,而且易于纯化,利于工业化生产。
    公开号:
    CN105001037B
  • 作为产物:
    描述:
    1,2-bis(trimethylsilylethynyl)acenaphthylene 在 sodium tetrahydroborate 、 Aliquat 464 sodium hydroxide碲化氢 作用下, 以 为溶剂, 反应 8.0h, 以30%的产率得到荧蒽
    参考文献:
    名称:
    在温和条件下碲介导的无环烯二炔环芳构化
    摘要:
    无环烯二炔的环芳构化通常需要非常高的温度(> 160 摄氏度)和稀释条件才能以合成有用的产率进行。这些条件阻碍了反应产量,抑制了该反应在材料的大规模生产中的应用。碲化钠与无环芳二炔反应生成相应的碲碱,在温和加热下会挤出 Te 度,生成环芳构化产物。我们已经开发出从廉价的碲金属原位形成碲化钠的条件,并在同一过程中对甲硅烷基化芳烃进行脱甲硅烷基化。在我们的条件下,我们能够在低至 40 摄氏度的温度和大至 5 克的标准实验室玻璃器皿中进行脱甲硅烷基化和环芳构化。
    DOI:
    10.1021/ja0389467
  • 作为试剂:
    描述:
    1-(苯氧甲基)萘荧蒽 作用下, 以 乙二醇二甲醚 为溶剂, 生成 甲基萘
    参考文献:
    名称:
    自由基阴离子裂解中的电子分配。2. 萘甲基苯基醚与萘基苄基醚
    摘要:
    Les ethers du titre subissent une scission de la liaison H 2 CO lorsqu'ils sont traites par les radicaux anioniques de l'anthracene ou du fluoranthrene。Dans des conditions 可比 les naphtylmethyl phenyl ethers reagisent plus de 10 4 fois plus vite que lesnaphtylbenzyl ethers。解释
    DOI:
    10.1021/ja00270a022
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文献信息

  • ORGANIC ELECTROLUMINESCENCE DEVICE AND ANTHRACENE DERIVATIVE
    申请人:IKEDA Hidetsugu
    公开号:US20110034744A1
    公开(公告)日:2011-02-10
    An anthracene derivative having a specific asymmetric structure is provided. The asymmetric anthracenes are useful in an organic electroluminescence device and exhibit efficient light emission and a long performance lifetime.
    提供一种具有特定不对称结构的蒽衍生物。这种不对称的蒽衍生物在有机电致发光器件中很有用,表现出高效的光发射和长期的性能寿命。
  • Birch‐Type Photoreduction of Arenes and Heteroarenes by Sensitized Electron Transfer
    作者:Anamitra Chatterjee、Burkhard König
    DOI:10.1002/anie.201905485
    日期:2019.10
    energy-transfer and electron-transfer processes generates an arene radical anion, which is subsequently trapped by hydrogen-atom transfer and finally protonated to form the dearomatized product. The photoreduction converts planar aromatic feedstock compounds into molecular skeletons that are of use in organic synthesis.
    通过可见光照射直接还原芳烃和杂芳烃仍然具有挑战性,因为单个光子的能量不足以破坏芳香族的稳定性。本文显示两个可见光光子的能量积累允许芳烃和杂芳烃的脱芳构化。机理研究证实,能量转移和电子转移过程的结合产生芳烃自由基阴离子,随后被氢原子转移捕获,最后质子化形成脱芳构化产物。光还原将平面芳香族原料化合物转化为可用于有机合成的分子骨架。
  • [EN] NOVEL ORGANIC ELECTROLUMINESCENT COMPOUNDS AND ORGANIC ELECTROLUMINESCENT DEVICE USING THE SAME<br/>[FR] NOUVEAUX COMPOSÉS ÉLECTROLUMINESCENTS ORGANIQUES ET DISPOSITIF ÉLECTROLUMINESCENT ORGANIQUE LES UTILISANT
    申请人:ROHM & HAAS ELECT MAT
    公开号:WO2013032278A1
    公开(公告)日:2013-03-07
    The present invention relates to a novel compound and an organic electroluminescent device containing the same. Since the compounds according to the present invention have high efficiency in transporting electrons, crystallization could be prevented when manufacturing the device, and since they are adaptable in the formation of the layers, the current characteristic of the device is improved, and finally they can manufacture an organic electroluminescent device having lowered driving voltage, advanced power efficiency, and improved light emitting efficiency and lifetime characteristic compared with devices comprising the conventional materials.
    本发明涉及一种新型化合物和包含该化合物的有机电致发光器件。由于本发明的化合物在电子传输方面具有高效率,因此在制造器件时可以防止结晶,而且由于它们适用于层的形成,器件的电流特性得到改善,最终可以制造出与采用传统材料的器件相比,具有降低驱动电压、提高功率效率、改善发光效率和寿命特性的有机电致发光器件。
  • Platinum-catalysed diborylation of arynes: synthesis and reaction of 1,2-diborylarenes
    作者:Hiroto Yoshida、Kengo Okada、Shota Kawashima、Kenji Tanino、Joji Ohshita
    DOI:10.1039/b919407j
    日期:——
    Arynes are found to be facilely inserted into bis(pinacolato)diboron by using a platinum–isocyanide catalyst, affording diverse 1,2-diborylarenes, which can be converted into o-terphenyls via Suzuki–Miyaura coupling reaction.
    研究发现,使用铂-异氰化物催化剂可以轻松将烯插入双(松香酸酯)二硼化合物中,生成多种1,2-二硼基芳烃,这些化合物可以通过铃木-宫浦偶联反应转化为邻三联苯。
  • Preparation of Substituted Phenanthridines from the Coupling of Aryldiazonium Salts with Nitriles: A Metal Free Approach
    作者:Mani Ramanathan、Shiuh-Tzung Liu
    DOI:10.1021/acs.joc.5b00579
    日期:2015.5.15
    A transition metal free approach for the synthesis of substituted phenanthridines from the coupling reaction of aryldiazonium tetrafluoroborates with nitriles has been developed. This operationally simple protocol proceeds through a substitution of aryldiazonium with nitriles followed by an intramolecular arylation to provide the corresponding phenanthridines in moderate to excellent yields.
    已经开发了一种无过渡金属的方法,该方法可通过四氟硼酸芳基重氮与腈的偶联反应来合成取代的菲啶。该操作简单的方案是通过用腈取代芳基重氮,然后进行分子内芳基化,以中等至极好的收率提供相应的菲啶。
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表征谱图

  • 氢谱
    1HNMR
  • 质谱
    MS
  • 碳谱
    13CNMR
  • 红外
    IR
  • 拉曼
    Raman
hnmr
mass
cnmr
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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