摩熵化学
数据库官网
小程序
打开微信扫一扫
首页 分子通 化学资讯 化学百科 反应查询 关于我们
请输入关键词

1-氯-1,1-二氟乙烷 | 75-68-3

中文名称
1-氯-1,1-二氟乙烷
中文别名
二氟一氯乙烷;氢氯氟碳142B;1,1-二氟氯乙烷;一氯二氟乙烷;氟里昂-142;1-氯二氟乙烷;氟里昂-142b
英文名称
1-Chloro-1,1-difluoroethane
英文别名
freon 142b;1,1-difluoro-1-chloroethane;HCFC-142b
1-氯-1,1-二氟乙烷化学式
CAS
75-68-3
化学式
C2H3ClF2
mdl
——
分子量
100.496
InChiKey
BHNZEZWIUMJCGF-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

  • 稳定性/保质期:
    1. 稳定性<sup>[20]</sup>:稳定。 2. 禁配物<sup>[21]</sup>:强氧化剂、镁铜及其合金。 3. 避免接触的条件<sup>[22]</sup>:受热。 4. 聚合危害<sup>[23]</sup>:不聚合。 5. 分解产物<sup>[24]</sup>:氟化氢、氯化氢。

计算性质

  • 辛醇/水分配系数(LogP):
    2
  • 重原子数:
    5
  • 可旋转键数:
    0
  • 环数:
    0.0
  • sp3杂化的碳原子比例:
    1.0
  • 拓扑面积:
    0
  • 氢给体数:
    0
  • 氢受体数:
    2

ADMET

代谢
男性,比格犬,每天吸入6小时,每周5天,持续90天,浓度在1,000 - 10,000 ppm(空气中的体积比)。尿液中氟化物没有显著增加,提示几乎没有代谢。
Male, Beagle dogs, inhalation 6 hr/day, 5 days/wk for 90 days at 1,000 - 10,000 ppm (v/v in air). No significant increase in urinary fluoride suggesting little or no metabolism.
来源:Hazardous Substances Data Bank (HSDB)
代谢
代谢研究是使用Fischer 344和Sprague-Dawley大鼠进行的,这些大鼠在吸入1.0%(体积比)的1-氯-1,1-二氟乙烷(HCFC-142b)空气气氛中暴露了2小时。两种品系的大鼠在结果上没有显著差异。暴露于HCFC-142b的大鼠在尿液中排出了氯二氟乙酸;在组织样本中没有检测到挥发性代谢物...
Metabolism studies were conducted using Fischer 344 and Sprague-Dawley rats following inhalation exposure to 1.0% (v/v) air atmospheres of ... 1-chloro-1,1-difluoroethane (HCFC-142b) ... for 2 hr. There were no remarkable differences in results between the two strains of rats ... Rats exposed to HCFC-142b excreted chlorodifluoroacetic acid in their urine; no volatile metabolites were detected in tissue samples ...
来源:Hazardous Substances Data Bank (HSDB)
代谢
一项体外研究提供了证据,当大鼠肝微粒体与0.6%的HCFC 142b一起孵化时,会发生脱氯反应。
One in vitro study provided evidence for dechlorination when rat hepatic microsomes were incubated with 0.6% HCFC 142b.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 毒性总结
人类健康:1-氯-1,1-二氟乙烷的急性毒性较低(大鼠LC50/6小时>1,640,000毫克/立方米(400,000 ppm))。吸入高浓度可诱导大鼠肺部刺激症状和类似麻醉的中枢神经系统抑制作用,以及狗的心脏敏感化。因此,在密闭空间内,如果空气被1-氯-1,1-二氟乙烷取代,可能导致氧气含量降低,从而对人类造成危害。在重复吸入暴露研究中,大鼠和狗每天暴露6小时,每周5天,连续几个月,1-氯-1,1-二氟乙烷没有引起特定的慢性毒性(没有识别出靶器官;狗在3个月内暴露的无观察到不良效应水平高于41,000毫克/立方米(10,000 ppm),大鼠终身暴露的无观察到不良效应水平高于82,000毫克/立方米(20,000 ppm))。终身暴露的大鼠中没有致癌效应(每天6小时,每周5天,浓度高达82,000毫克/立方米(20,000 ppm))。在遗传毒性研究中,1-氯-1,1-二氟乙烷在细菌(Ames试验)中具有诱变性,并在细胞肿瘤转化试验中给出了不确定的结果。然而,在体内诱变性研究中,它是不活跃的(在大鼠吸入暴露15周和13周的显性致死试验和骨髓细胞遗传学试验中)。总的来说,这些结果表明1-氯-1,1-二氟乙烷对人类不构成显著的遗传毒性危害。在生殖领域,1-氯-1,1-二氟乙烷对雄性小鼠的生育能力没有不良影响,暴露高达82,000毫克/立方米(20,000 ppm)(在显性致死试验中),并且在大鼠和狗暴露几个月后,没有引起雄性和雌性性器官的病变。在两项吸入发育毒性研究中,大鼠在怀孕期间暴露高达41,000毫克/立方米(10,000 ppm),也没有诱导出致畸性或胚胎/胎儿毒性效应,也没有母体毒性。 环境:基于其物理化学性质,空气层是1-氯-1,1-二氟乙烷的首选目标。142b的整体大气寿命为18.5年,对应于半个寿命为12.8年。由于与OH反应而被移除的平流层寿命为19.5年。大气降解产物主要是142b的醛形式,进一步降解形成CF2(=O),在大气水中水解形成HF(也在经合组织高产量化学品计划中)和CO2。1-氯-1,1-二氟乙烷的臭氧消耗潜力是该物质的主要关注点。由于其ODP值为0.065,被认为是一种消耗臭氧的物质。1-氯-1,1-二氟乙烷的全球变暖潜力为1800,积分时间为100年。其对温室效应的贡献很小,即0.00108 W/平方米。在水中,1-氯-1,1-二氟乙烷在好氧条件下不易生物降解(大约28天后有5%的生物降解)。预计不会生物累积(log Kow = 1.64 - 2.05)。1-氯-1,1-二氟乙烷对鱼类和大型蚤的急性毒性较低。最低可用的LC50高于100毫克/升。没有藻类的急性毒性测试。藻类似乎对1-氯-1,1-二氟乙烷比鱼类和大型蚤更敏感,计算出的96小时EC50为45毫克/升。 暴露:预计1-氯-1,1-二氟乙烷在2000年的生产量为欧洲36,000吨,美国42,000吨,全球总量为84,000吨。其主要用作生产氟聚合物的化学中间体和发泡剂。一小部分用作制冷剂流体的组成部分。1-氯-1,1-二氟乙烷的生产和消费受蒙特利尔议定书管制。在发达国家,1-氯-1,1-二氟乙烷和其他氢氯氟烃(HCFCs)的逐步淘汰计划如下:2004年35%,2010年65%,2015年90%,2020年99.5%。2030年计划完全淘汰。对于发展中国家,计划在2016年冻结生产,2040年完全淘汰。在欧洲联盟,臭氧消耗物质的淘汰计划比蒙特利尔议定书要求的更快。要求在2010年1月1日完全禁止氢氯氟烃(HCFCs),从2002年1月1日起禁止用作膨胀聚苯乙烯的发泡剂。
Human Health: Acute toxicity of 1-chloro-l,l-difluoroethane is low (LC50/6hr >1,640,000 mg/cum (400,000 ppm) in rats). Inhalation of high concentrations induced signs of lung irritation and Central Nervous System depressing effects of anesthetic type in rats and cardiac sensitisation in dogs. Consequently, 1-chloro 1,1 -difloroethane may be hazardous to humans in case of accidental exposure to high concentrations occurring in confined area where replacement of air by the gas could at the same time reduce oxygen in the atmosphere. In repeated inhalation exposure studies, 1-chloro -1,1- difluoroethane did not induce specific chronic toxicity in rats and dogs exposed 6 hr/d, 5 d/week during several months (no target organs identified ; the no observed adverse effects were higher than 41,000 mg/cum (10,000 ppm) in dogs exposed during 3 months and higher than 82,000 mg/cum (20,000 ppm) in rats exposed for their lifetime). There was no carcinogenic effect in rats exposed for their life time (6hr/d, 5d/week at concentrations up to 82,000 mg/cum (20,000 ppm)). In genotoxicity studies, 1-chloro-1,1-difluoroethane was mutagenic in vitro on bacteria (Ames test) and gave equivocal results in a cell neoplastic transformation assay. However, in in vivo mutagenicity studies it was inactive (in a Dominant lethal assay and in a Bone Marrow cytogenetic assay in rats exposed by inhalation du ring 15 and 13 weeks respectively). Overall, these results suggest that 1-chloro-1,1-difluoroethane does not pose a significant genotoxic hazard to humans. In the reproduction field, 1-chloro 1,1-difluoroethane did not induce adverse effect on fertility of male mice exposed up to 82,000 mg/cum (20,000 ppm) (in a Dominant lethal assay) and did not induce male and female lesions of sexual organs in rats and dogs exposed for several months. Also the gas did not induce teratogenic or embryo/foetotoxicity effect and no maternal toxicity in two inhalation developmental toxicity studies where rats were exposed during pregnancy up to 41,000 mg/cum (10,000 ppm). Environment: Based on its physico-chemical properties, the air compartment is the preferred target one for 1-chloro -1,1- difluoroethane. The global atmospheric lifetime of 142b is 18.5 years corresponding to a 1/2 -lifetime of 12.8 years. The tropospheric lifetime due to removal by reaction with OH is 19.5 years. Atmospheric degradation products are essentially the aldehyde form of 142b which further degrade to form CF2(=O) which will hydrolyze in atmospheric water to form HF (also in the OECD HPV Chemicals Programme) and CO2. The ozone depletion potential (ODP) of 1-chloro -1,1-difluoroethane is the main concern of this substance. Due to its ODP value of 0.065, it is considered as an ozone depleting substance. The calculated Global Warming Potential of 1-chloro-1,1-difluoroethane is 1800 for an integration horizon of 100 years. Its contribution to the Greenhouse effect is small i.e. 0.00108 W/sq m. In water, 1-chloro-1,1-difluoroethane is not readily biodegradable under aerobic condition (about 5 % of biodegradation after 28 days). It is not expected to bioaccumulate (log Kow = 1.64 - 2.05). 1-chloro-1,1-difluoroethane has a low acute toxicity to fish and daphnia. The lowest available LC50 being higher than 100 mg/L. No acute toxicity tests are available for algae. Algae appear to be more sensitive than fish and daphnids to 1-chloro1,1-difluoroethane with a calculated 96h EC50 of 45 mg/L. Exposure: The expected production volume of 1-chloro-1,1-difluoroethane in year 2000 is 36,000 tonnes in Europe, 42,000 tonnes in the USA and an amount of 84,000 tonnes for the total world. Its main uses are as a chemical intermediate to produce fluoropolymers and as a blowing agent. A small portion is used as a component of refrigerant fluids. The production and consumption of 1-chloro1,1-difluoroethane are covered by the Montreal Protocol. In the case of developed countries, a phase-out of 1-chloro1,1-difluoroethane and other hydrochlorofluorocarbons (HCFCs) is scheduled as follows: 35% in 2004, 65% in 2010, 90% in 2015, 99.5% in 2020. A total phase-out is scheduled in 2030. For developing countries, a freeze of the production is scheduled in 2016 and a total phase-out in 2040. In the European Union, the phase-out of ozone depleting substances is scheduled more rapidly than that required by the Montreal protocol. The total ban of hydrochlorofluorocarbons (HCFCs) is required on January 1, 2010, the use as blowing agent for expended polystyrene being prohibited from January 1, 2002.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 副作用
神经毒素 - 急性溶剂综合征
Neurotoxin - Acute solvent syndrome
来源:Haz-Map, Information on Hazardous Chemicals and Occupational Diseases
毒理性
  • 毒性数据
LC50(小鼠)= 447,000 ppm/2小时;
LC50 (mice) = 447,000 ppm/2h;
来源:Haz-Map, Information on Hazardous Chemicals and Occupational Diseases
毒理性
  • 相互作用
氟碳化合物与拟交感神经支气管扩张剂的组合对于治疗支气管哮喘具有潜在危险性。出于同样的原因,拟交感神经药物在治疗氟碳化合物中毒患者的心脏复苏中是禁忌的。/氟碳化合物中毒/
... The combination of fluorocarbon with a sympathomimetic bronchodilator is potentially dangerous for the treatment of bronchial asthma. For the same reason, sympathomimetic drugs are contraindicated in cardiac resuscitation of patients suffering from fluorocarbon poisoning. /Fluorocarbon poisoning/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 解毒与急救
在氟碳化合物中毒的人员中,可以采取措施减少心律失常的风险。在医院评估前,应建议患者避免剧烈运动。在医院中,患者可以被安置在一个安静、无威胁的环境中,并在必要时进行镇静。如果出现低氧血症,应给予吸氧并纠正代谢异常。应避免使用拟交感神经药物。室性心律失常最好用β受体阻滞剂治疗。/氟碳化合物/
... In persons who are intoxicated with fluorocarbons, steps can be taken to lessen the risk of arrhythmias. ... Before evaluation at the hospital, patients should be advised to avoid strenuous exercise. In the hospital, patients can be placed in a quiet, nonthreatening environment and sedated if necessary. If hypoxic, oxygen should be administered and metabolic abnormalities corrected. Sympathomimetic drugs should be avoided. Ventricular arrhythmias are best treated with beta-blocking agents. /Fluorocarbons/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
影响氟碳化合物命运的主要因素是体脂肪,它们在那里集中并缓慢释放到血液中,浓度不应导致任何心脏敏感化的风险。/氟碳化合物/
... Main factor affecting fate of fluorocarbons is body fat, where they are concentrated and slowly released into blood at a concn that should not cause any risk of cardiac sensitization. /Fluorocarbons/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
氟碳化合物在脑、肝和肺中的积累量显著高于血液水平,表明氟碳化合物在组织中的分布类似于氯仿。/氟碳化合物/
There is a significant accumulation of fluorocarbons in brain, liver, and lung compared to blood levels, signifying a tissue distribution of fluorocarbons similar to that of chloroform. /Fluorocarbons/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
氟碳化合物经口服摄入后的吸收率远低于吸入(35-48倍)。...在尸检时,肺部通常具有最高的氟碳化合物浓度。/氟碳化合物/
Abosrption of fluorocarbons is much lower after oral ingestion (35-48 times) than after inhalation. ... The lung generally have the highest fluorocarbon concentrations on autopsy. /Fluorocarbons/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
尽管氟碳化合物会在某些动物物种中引起心脏敏感化,但是它们的快速消除可以防止气溶胶支气管扩张剂使用时心脏毒性浓度的积累,除非剂量极高(在2分钟内使用12到24剂)。/氟碳化合物/
Although fluorocarbons cause cardiac sensitization in certain animal species, rapid elimination prevents the development of cardiotoxic concentrations from aerosol bronchodilator use except at exceedingly high doses (12 to 24 doses in 2 minutes). /Fluorocarbons/
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • 储存条件:
    储存于阴凉、通风的易燃气体专用库房。库温不宜超过30℃。远离火种、热源,与氧化剂、金属粉末等分开存放,切忌混储。使用防爆型照明和通风设施,并禁止使用可能产生火花的机械设备和工具。储区应配备泄漏应急处理设备。

制备方法与用途

制备方法:

  • 用作制冷剂、溶剂、聚合物发泡剂以及中间体等。
用途简介:

用途:

  • 用作制冷剂、溶剂、聚合物发泡剂以及中间体等。 [26]

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:
    描述:
    参考文献:
    名称:
    The Chlorination of 1,1-Difluoroethane and 1-Chloro-1,1-difluoroethane1
    摘要:
    DOI:
    10.1021/ja01139a502
  • 作为产物:
    描述:
    三氯乙烷 在 antimony dichloride trifluoride 、 三氟化锑 作用下, 生成 1-氯-1,1-二氟乙烷
    参考文献:
    名称:
    Henne; Renoll, Journal of the American Chemical Society, 1936, vol. 58, p. 888
    摘要:
    DOI:
点击查看最新优质反应信息

文献信息

  • Method of making difluoromethane, 1,1,1-trifluoroethane and 1,1-difluoroethane
    申请人:Merkel C. Daniel
    公开号:US20050222472A1
    公开(公告)日:2005-10-06
    A process for the production of difluoromethane (HFC-32), 1,1,1-trifluoroethane (HFC-143a) and 1,1-difluoroethane (HFC-152a). In the process the following steps are employed: (a) providing a reaction vessel, (b) providing in the reaction vessel activated carbon impregnated with a strong Lewis acid fluorination catalys selected from halides of As, Sb, Al, TI, In, V, Nb, Ta, Ti, Zr and Hf, (c) activating the catalyst by passing through the activated carbon impregnated with a strong Lewis acid fluorination catalyst anhydrous hydrogen fluoride gas and chlorine gas, (d) contacting, in a vapor state in the reaction vessel containing the activated catalyst, hydrogen fluoride and one or more halogenated hydrocarbons selected from chlorofluoromethane, dichloromethane, 1,1,1-trichloroethane, vinyl chloride, 1,1-dichloroethylene, 1.2-dichloroethylene, 1,2-dichloroethane, and 1,1-dichloroethane for a time and at a temperature to produce a product stream comprising hydrofluorocarbon product(s) corresponding to the chlorinated hydrocarbon reactant(s), and one or more of hydrogen chloride, unreactacted chlorinated hydrocarbon reactant(s), under-fluorinated intermediates, and unreacted hydrogen fluoride, and (e) separating the hydrofluorocarbon product(s) from the product stream.
    生产二氟甲烷(HFC-32)、1,1,1-三氟乙烷(HFC-143a)和1,1-二氟乙烷(HFC-152a)的工艺。在该工艺中采用以下步骤:(a)提供一个反应容器,(b)在反应容器中提供用强Lewis酸氟化催化剂选择的活性炭,该催化剂选自As、Sb、Al、TI、In、V、Nb、Ta、Ti、Zr和Hf的卤化物,(c)通过经过强Lewis酸氟化催化剂浸渍的活性炭通入无水氟化氢气体和氯气来激活催化剂,(d)在含有活性催化剂的反应容器中以蒸汽状态接触氢氟酸和氯气,并与氯氟烃、二氯甲烷、1,1,1-三氯乙烷、氯乙烯、1,1-二氯乙烯、1,2-二氯乙烯、1,2-二氯乙烷和1,1-二氯乙烷中选择的一个或多个卤代烃反应物在时间和温度下反应,以产生包含与氯化烃反应物相对应的氢氟烃产品的产品流,以及氯化氢、未反应的氯化烃反应物、次氟化中间体和未反应的氢氟酸中的一个或多个,(e)从产品流中分离氢氟烃产品。
  • Porous aluminum fluoride
    申请人:Quan Hengdao
    公开号:US20060025639A1
    公开(公告)日:2006-02-02
    A porous aluminum fluoride on which SbCl x F 5-x (wherein x represents a numeral of 0 to 5) is supported, SbCl x F 5-x being obtainable by supporting SbCl, or the like on a porous aluminum fluoride and treating it with hydrogen fluoride. The resulting porous aluminum fluoride has a high activity as a fluorinating agent, a fluorination catalyst, or the like, is easy to handle, can be used for a flow-type reaction, and also can be used even at a high temperature.
    在多孔氟化铝上支持SbCl x F 5-x (其中x表示0到5的数字),可以得到SbCl x F 5-x ,通过在多孔氟化铝上支持SbCl或类似物质,并用氢氟酸处理。所得的多孔氟化铝具有高活性作为氟化剂、氟化催化剂等,易于处理,可用于流动式反应,甚至可在高温下使用。
  • Estimation of Atmospheric Lifetimes of Hydrofluorocarbons, Hydrofluoroethers, and Olefins by Chlorine Photolysis Using Gas-Phase NMR Spectroscopy
    作者:Alexander A. Marchione、Paul J. Fagan、Eric J. Till、Robert L. Waterland、Concetta LaMarca
    DOI:10.1021/ac800883t
    日期:2008.8.1
    hydrofluoroethers and relative rates of reaction with photolyzed chlorine in excess at ambient temperature. These kinetic systems were studied by nuclear magnetic resonance (NMR) spectroscopy in the gas phase, marking the first application of NMR spectroscopy to this field. The square of the Pearson coefficient R for the linear correlation between observed reaction rates and accepted atmospheric lifetimes was 0.87
    在一组氢氟烃和氢氟醚的公认大气寿命与在环境温度下与过量光解氯的相对反应速率之间存在经验相关性。在气相中通过核磁共振(NMR)光谱研究了这些动力学系统,这标志着NMR光谱在该领域的首次应用。对于观察到的反应速率与可接受的大气寿命之间的线性相关性,皮尔逊系数R的平方对于寿命小于20年的化合物为0.87。该方法扩展到乙烯和丙烯的研究。发现丙烯在23摄氏度下的反应速率是乙烯的1.25倍。
  • Room-temperature catalytic fluorination of C1 and C2 chlorocarbons and chlorohydrocarbons on fluorinated Fe3O4 and Co3O4
    作者:James Thomson
    DOI:10.1039/ft9949003585
    日期:——
    A study of the room-temperature reactions of a series of C1 and C2 chlorohydrocarbon and chlorocarbon substrate molecules with fluorinated iron (II, III) oxide and cobalt (II, III) oxide has been conducted. The results show that fluorinated iron(II, III) oxide exhibits an ability to incorporate fluorine into the following substrates in the order: Cl2CCCl2 > H2CCCl2 > CH3CCl3 > CHCl3 > CH2Cl2 > CH2ClCCl3 > CCI4 > CHCl2CHCl2. The fluorinated cobalt(II,III) oxide gave the reactivity series CHCl3 > CCl4 > H2CCCl2 > CHCl2CHCl2 > CH2CI2 > CH3CCl3 > CCl2CCl2 > CH2ClCl3. Reactions of C1 chlorohydrocarbon or chlorocarbon probe molecules with fluorinated Fe3O4 gave predominately C1 chlorofluorohydrocarbon and chlorofluorocarbon products, respectively, whereas fluorinated cobalt(II, III) oxide produced predominately C2 chlorofluorohydrocarbon and chlorofluorocarbons. For fluorinated Co3O4 the distribution of C2 products obtained from C1 chlorohydrocarbon precursor molecules is consistent with the formation of radical intermediates at strong Lewis acid surfaces. C2 chlorohydrocarbons exhibit a fluorine for chlorine (F-for-Cl) exchange reaction through the catalytic dehydrochlorination of the substrate to the alkenic intermediate. The F-for-Cl exchange process was dependent upon the ability of the substrate material to undergo dehydrochlorination; the inability of a substrate to undergo dehydrochlorination results in the fluorination process proceeding through the formation of chlorocarbon or chlorohydrocarbon radical intermediates.
    对一系列C1和C2氯代烃和氯代碳基底分子室温下与氟化铁(II,III)氧化物和钴(II,III)氧化物的反应进行了研究。结果表明,氟化铁(II,III)氧化物具有将氟引入以下基质的能力,顺序为:Cl2CCCl2 > H2CCCl2 > CH3CCl3 > CHCl3 > CH2Cl2 > CH2ClCCl3 > CCl4 > CHCl2CHCl2。氟化钴(II,III)氧化物给出的反应活性系列为:CHCl3 > CCl4 > H2CCCl2 > CHCl2CHCl2 > CH2Cl2 > CH3CCl3 > CCl2CCl2 > CH2ClCl3。C1氯代烃或氯代碳探针分子与氟化Fe3O4反应分别主要生成C1氯氟烃和氯氟碳产物,而氟化钴(II,III)氧化物主要生成C2氯氟烃和氯氟碳。对于氟化Co3O4,从C1氯代烃前体分子获得的C2产物的分布与在强路易斯酸表面形成自由基中间体一致。C2氯代烃通过催化脱氯化氢生成烯烃中间体,进行氟氯(F-for-Cl)交换反应。F-for-Cl交换过程取决于基质材料进行脱氯化氢的能力;基质不能进行脱氯化氢将导致氟化过程通过形成氯代碳或氯代烃自由基中间体进行。
  • Cobalt/diamine-catalyzed 1,1-difluoroethylation and 2,2,2-trifluoroethylation of aryl Grignard reagents with corresponding fluoroalkyl halides
    作者:Yuhki Ohtsuka、Tetsu Yamakawa
    DOI:10.1016/j.jfluchem.2016.03.007
    日期:2016.5
    Cobalt/diamine-catalyzed 1,1-difluoroethylation and 2,2,2-trifluoroethylation of aryl Grignard reagents with 1,1-difluoroethyl and 2,2,2-trifluoroethyl halides were investigated. With regard to the 1,1-difluoroethylation, 1,2-bis(dimethylamino)-2-methylpropane, which has been rarely used in the cross-coupling reactions, gave the highest yield among the diamine ligands tested. In the 2,2,2-trifluoroethylation
    研究了钴/二胺催化的芳基格氏试剂与1,1-二氟乙基和2,2,2-三氟乙基卤化物的1,1-二氟乙基化和2,2,2-三氟乙基化。关于1,1-二氟乙基化,在交叉偶联反应中很少使用的1,2-双(二甲基氨基)-2-甲基丙烷在所测试的二胺配体中给出了最高的收率。在2,2,2-三氟乙基化反应中,反式-1,2-双(二甲基氨基)环己烷不仅提供2,2,2-三氟乙基碘,而且提供氯化物,以令人满意的收率提供了所需的产物。在合适的二胺配体存在下,该Co /二胺催化剂对于与其他部分氟化的烷基卤化物的偶联也是有效的。
查看更多

表征谱图

  • 氢谱
    1HNMR
  • 质谱
    MS
  • 碳谱
    13CNMR
  • 红外
    IR
  • 拉曼
    Raman
查看更多图谱数据,请前往“摩熵化学”平台
mass
查看更多图谱数据,请前往“摩熵化学”平台
ir
查看更多图谱数据,请前往“摩熵化学”平台
  • 峰位数据
  • 峰位匹配
  • 表征信息
Shift(ppm)
Intensity
查看更多图谱数据,请前往“摩熵化学”平台
Assign
Shift(ppm)
查看更多图谱数据,请前往“摩熵化学”平台
测试频率
样品用量
溶剂
溶剂用量
查看更多图谱数据,请前往“摩熵化学”平台