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六氯苯 | 118-74-1

中文名称
六氯苯
中文别名
六氯苯13C6;灭黑穗药;六氯代苯;全氯代苯;气相色谱/质谱联用仪校准用;过氯苯;六氯苯(HCB)
英文名称
hexachlorobenzene
英文别名
HCB;perchlorobenzene;1,2,3,4,5,6-hexachlorobenzene
六氯苯化学式
CAS
118-74-1
化学式
C6Cl6
mdl
MFCD00000540
分子量
284.784
InChiKey
CKAPSXZOOQJIBF-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:
    227-229 °C(lit.)
  • 沸点:
    323-326 °C(lit.)
  • 密度:
    1.5691
  • 闪点:
    11 °C
  • 溶解度:
    可溶于氯仿、己烷(微溶)
  • 暴露限值:
    No exposure limit has been set for this com pound. Carcinogenicity: Animal Sufficient Evidence, Human Limited Evidence (IARC).
  • 物理描述:
    Hexachlorobenzene appears as 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.
  • 颜色/状态:
    White needles
  • 蒸汽密度:
    9.8 (NTP, 1992) (Relative to Air)
  • 蒸汽压力:
    1.72X10-5 mm Hg at 25 °C
  • 亨利常数:
    0.00 atm-m3/mole
  • 大气OH速率常数:
    2.70e-14 cm3/molecule*sec
  • 稳定性/保质期:
    1. 稳定性<sup>[21]</sup>:稳定。 2. 禁配物<sup>[22]</sup>:强氧化剂。 3. 避免接触的条件<sup>[23]</sup>:受热。 4. 聚合危害<sup>[24]</sup>:不聚合。 5. 分解产物<sup>[25]</sup>:氯化氢。
  • 分解:
    Dangerous; When heated to decomposition, emits toxic fumes of /hydrogen chloride/.
  • 燃烧热:
    -2372 kJ/mol
  • 汽化热:
    49 kJ/mol at 20 °C
  • 保留指数:
    1700;1688;1688;1690;1691;1691;1691;1693;1693;1662;1656;1695;1656;1673;1695;1724;1691;1688;1661;1724;1704.7;1689.3;1683.1;1680;1680;1693.5

计算性质

  • 辛醇/水分配系数(LogP):
    5.7
  • 重原子数:
    12
  • 可旋转键数:
    0
  • 环数:
    1.0
  • 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
在大鼠口服和肠道给药(14)C六氯苯后,代谢物以剂量依赖性方式排出...主要尿代谢物是...五氯酚、四氯对苯二酚和五氯硫酚。其它尿代谢物包括四氯苯、五氯苯、2,4,5-和2,4,6-三氯酚...2,3,4,6-和2,3,5,6-四氯酚;2,3,4-三氯酚和其他四氯酚仅以微量存在。这些代谢物以结合物或自由形式在尿液中排出。未改变的六氯苯在粪便和脂肪中发现。
After ip and oral admin of (14)C hexachlorobenzene in rats was dose-dependent ... major urinary metabolites were ... pentachlorophenol, tetrachlorohydroquinone, and pentachlorothiophenol. Other urinary metabolites were tetrachlorobenzene, pentachlorobenzene, 2,4,5- & 2,4,6-trichlorophenols ... 2,3,4,6- and 2,3,5,6-tetrachlorophenols; 2,3,4-trichlorophenol and other tetrachlorophenols were present in traces. These metabolites were excreted as conjugates or in free form in urine. Unchanged hexachlorobenzene was found in the feces and in fat.
来源:Hazardous Substances Data Bank (HSDB)
代谢
当每天口服给猕狨猴110微克/(14)C-六氯苯,持续11-15个月时,尿液中发现的50%的放射性物质是五氯酚,25%是五氯苯,其余的是未识别的代谢物和未改变的六氯苯。在粪便中,99%的放射性物质是未改变的六氯苯。
When 110 ug/day (14)C-hexachlorobenzene was given orally to macaca mulatta monkeys for 11-15 months, 50% of radioactivity found in urine was pentachlorophenol and 25% pentachlorobenzene, the remainder was unidentified metabolites and unchanged hexachlorobenzene. In feces, 99% of radioactivity was unchanged HCB.
来源:Hazardous Substances Data Bank (HSDB)
代谢
六氯苯(HCB)通过诱导雄性大鼠肝微粒体的苯巴比妥代谢为五氯苯、五氯酚、四氯-1,2-苯二酚和四氯-1,4-苯二酚(1:88:2:9)。代谢物通过电子捕获气相色谱进行鉴定和定量。结构通过选择性离子监测气相色谱/质谱得到确认。五氯酚的形成依赖于NADPH和氧气的存在,并被一氧化碳SKF 525A和甲巯咪唑抑制。用苯巴比妥预处理大鼠可刺激HCB转化为五氯酚,而3-甲基胆蒽或2,3,7,8-四氯二苯并对二英则不能。相比之下,五氯酚转化为四氯-1,4-苯二酚明显被3-甲基胆蒽诱导,而苯巴比妥诱导效果较差。HCB、Aroclor 1254和异补骨脂素均刺激了这两种羟基化反应。细胞色素p450抑制剂9-羟基椭圆icine抑制了HCB将五氯酚转化为四氯苯二酚的过程,而beta-萘黄酮诱导的微粒体促进了这一转化。除了羟基化反应外,还获得了HBC与谷胱甘肽结合的证据,该结合由微粒体谷胱甘肽转移酶催化。在好氧培养过程中,(14)碳标记的HCB的放射性结合到微粒体蛋白上。这种结合被GSH和N-乙酰半胱氨酸抑制。
Hexachlorobenzene (HCB) was metabolized by phenobarbital induced liver microsomes from male rats to pentachlorobenzene, pentachlorophenol, tetrachloro-1,2-benzenediol, and tetrachloro-1,4-benzenediol (1:88:2:9). Metabolites were identified and quantified by electron capture gas-liquid chromatography. Structures were confirmed by selective ion monitoring gas-liquid chromatography/mass spectrometry. The formation of pentachlorophenol was dependent on the presence of NADPH and oxygen and inhibited by carbon monoxide SKF 525A, and metyrapone. Conversion of HCB to pentachlorophenol was stimulated by pretreatment of rats with phenobarbital but not by 3-methylcholanthrene, or 2,3,7,8-tetrachlorodibenzo-p-dioxin. In contrast, the conversion of pentachlorophenol to tetrachloro-1,4-benzenediol was markedly induced by 3-methylcholanthrene but poorly by phenobarbital. HCB, Aroclor 1254, and isosafrole stimulated both hydroxylations. The cytochrome p450 inhibitor 9-hydroxyellipticine inhibited conversion of pentachlorophenol to tetrachlorobenzenediols by HCB and beta-naphthoflavone induced micrsomes. In addition to hydroxylation reactions, evidence was obtained for the conjugaton of HBC with glutathione catalyzed by a microsomal glutathione transferase. Radioactivity from (14)carbon HCB was bound to microsomal protein during aerobic incubations. Binding was inhibited by GSH and N-acetyl-cysteine.
来源:Hazardous Substances Data Bank (HSDB)
代谢
有机氯农药对大鼠肝脏微粒体单加氧酶的诱导作用,这些酶对苯并(a)芘和睾酮进行羟基化,与苯巴比妥的诱导作用进行了比较,以探究它们作为不同细胞色素P450同种酶诱导剂的活动。长期给予朗埃文斯大鼠连续4天腹腔注射400微摩尔/千克苯巴比妥,并在随后的日子处死,或者给予单次剂量的七氯、氯丹、六氯苯、毒杀酚、狄氏剂、林丹或p,p'-DDT,并在4天后处死。对肝脏微粒体组分进行了苯并(a)芘和睾酮代谢的分析。除了林丹外,所有测试的化合物都诱导了苯并(a)芘和睾酮羟化酶。六氯苯诱导了苯并(a)芘9,10-二氢二醇和7,8-二氢二醇代谢物的形成。每种化学物质诱导了睾酮羟化酶的不同组合。苯巴比妥诱导了15-β、16-α和16-β睾酮羟化酶的活性。除了林丹外,所有测试的农药都诱导了16-α和16-β睾酮羟化酶。
The induction by organochloride pesticides of rat hepatic microsomal monooxygenases which hydroxylate benzo(a)pyrene and testosterone was compared with that of phenobarbital, in order to investigate their activity as inducers of different cytochrome p450 isozymes. Long Evans rats were administered intraperitoneal injections of 400 umol/kg phenobarbital for 4 consecutive days and were sacrificed the following day, or were administered single doses of heptachlor, chlordane, hexachlorobenzene, toxaphene, dieldrin, lindane, or p,p'-DDT and were sacrificed 4 days later. Microsomal liver fractions were analyzed for benzo(a)pyrene and testosterone metabolism. All the compounds tested except lindane induced both benzo(a)pyrene and testosterone hydroxylases. Hexachlorobenzene induced formation of benzo(a)pyrene 9,10-dihydrodiol and 7,8-dihydrodiol metabolites. A different combination of testosterone hydroxylases was induced by each of the chemicals. Phenobarbital induced the activities of the 15-beta, 16-alpha, and 16-beta testosterone hydroxylases. With the exception of lindane, all of the pesticides tested induced the 16-alpha and 16-beta testosterone hydroxylases.
来源:Hazardous Substances Data Bank (HSDB)
代谢
六氯苯已知的人类代谢物包括五氯酚。
HEXACHLOROBENZENE has known human metabolites that include Pentachlorophenol.
来源:NORMAN Suspect List Exchange
毒理性
  • 毒性总结
基于空气中、水中和食物中的六氯苯代表性水平,一般人群成年人的六氯苯总摄入量主要是通过饮食摄入的。...六氯苯在实验动物中通过口服途径容易被吸收,而通过皮肤吸收较差。...在动物和人类中,六氯苯会在富含脂质的组织中积累,如脂肪组织、肾上腺皮质、骨髓、皮肤和一些内分泌组织,并且可以通过胎盘和母奶传递给后代。六氯苯的代谢有限,尿液中主要代谢产物为五氯酚、四氯对氢醌和五氯硫酚。...六氯苯对实验动物的急性毒性较低...在动物研究中,六氯苯不是皮肤或眼睛的刺激物...现有的关于六氯苯系统毒性的数据显示,血红素的生物合成途径是六氯苯毒性的主要靶标。在多种实验室哺乳动物的肝脏、其他组织和排泄物中发现了卟啉及其前体水平的升高...在多项对大鼠进行亚慢性或慢性口服暴露的研究中报告了卟啉症...重复暴露于六氯苯也显示出对多种器官系统(包括肝脏、肺、肾脏、甲状腺、皮肤和神经和免疫系统)的影响,尽管这些影响的发生频率低于卟啉症。六氯苯是一种混合型细胞色素P-450诱导化合物,具有苯巴比妥诱导性和3-甲基胆蒽诱导性。已知它能与Ah受体结合。...六氯苯的致癌性已经在多项关于啮齿动物的充分生物实验中进行了评估。...肝脏细胞肿瘤(肝细胞瘤)的发病率有所增加...肝脏的血管内皮瘤...甲状腺的腺瘤...肝脏的肿瘤性结节和肾上腺嗜铬细胞瘤...甲状旁腺腺瘤...肾细胞腺瘤...肝细胞癌、胆管腺瘤/癌...和肾上腺皮质腺瘤。...六氯苯几乎不具有直接诱导基因突变、染色体损伤和DNA修复的能力。它表现出微弱的致突变活性...也有证据表明在体外和体内有低水平的DNA结合,但远低于基因毒性致癌物的预期水平。在生殖研究.../表明/六氯苯在卵巢部位具有特异性。...多项研究的结果表明六氯苯影响免疫系统。...关于六氯苯对人类影响的大多数数据来源于1955-1959年在土耳其发生的意外中毒事件,其中发现了600多例迟发型皮肤卟啉症。在此事件中,观察到卟啉代谢紊乱、皮肤病变、色素沉着过度、多毛症、肝脏肿大、甲状腺和淋巴结肿大,以及(大约一半的病例中)骨质疏松或关节炎,主要发生在儿童身上。食用暴露于六氯苯的母亲母乳的婴儿发展出了一种称为“粉红疮”(pembe yara)的疾病,大多数婴儿在一年内死亡。也有有限证据表明,在工业场所或一般环境中接触较高水平六氯苯的人类会发生迟发型皮肤卟啉症。关于癌症的少数可用流行病学研究...不足以评估六氯苯对人类的致癌性。...关于环境风险评估的实验研究很少。...然而,六氯苯的浓度.../表明/六氯苯可能对敏感鸟类物种的胚胎造成伤害.../并且/对...食用鱼类的哺乳动物产生不利影响。
Based on representative levels of hexachlorobenzene in air, water, and food, the total intake of hexachlorobenzene by adults in the general population ... is predominantly from the diet. ... Hexachlorobenzene is readily absorbed by the oral route in experimental animals and poorly via the skin. ... In animals and humans, hexachlorobenzene accumulates in lipid-rich tissues, such as adipose tissue, adrenal cortex, bone marrow, skin and some endocrine tissues, and can be transferred to offspring both across the placenta and via mothers' milk. Hexachlorobenzene undergoes limited metabolism, yielding pentachlorophenol, tetrachlorohydroquinone and pentachlorothiophenol as the major metabolites in urine.... The acute toxicity of hexachlorobenzene to experimental animals is low ... In animal studies, hexachlorobenzene is not a skin or eye irritant ... The available data on the systemic toxicity of hexachlorobenzene indicate that the pathway for the biosynthesis of heme is a major target of hexachlorobenzene toxicity. Elevated levels of porphyrin and/or porphyrin precursors have been found in the liver, other tissues and excreta of several species of laboratory mammals ... Porphyria has been reported in a number of studies in rats with subchronic or chronic oral exposure ... Repeated exposure to hexachlorobenzene has also been shown to affect a wide range of organ systems (including the liver, lungs, kidneys, thyroid, skin and nervous and immune systems) although these have been reported less frequently than porphyria. Hexachlorobenzene is a mixed-type cytochrome P-450-inducing compound, with phenobarbital-inducible and 3-methylcholanthrene-inducible properties. It is known to bind to the Ah receptor. ... The carcinogenicity of hexachlorobenzene has been assessed in several adequate bioassays on rodents. ... There were increases in the incidence of liver cell tumors (hepatoma) ... hemangioendotheliomas of the liver ... adenomas of the thyroid ... neoplastic liver nodules and adrenal pheochromocytomas ... parathyroid adenomas ... renal cell adenomas ... hepatocellular carcinomas, bile duct adenomas/carcinomas ... and adrenal cortical adenomas. ... Hexachlorobenzene has little capability to induce directly gene mutation, chromosomal damage and DNA repair. It exhibited weak mutagenic activity ... There is also some evidence of low-level binding to DNA in vitro and in vivo, but at levels well below those expected for genotoxic carcinogens. In studies of reproduction .... /suggest/ specificity of hexachlorobenzene within the site of the ovary. ... The results of a number of studies have indicated that hexachlorobenzene affects the immune system .... Most data on the effects of hexachlorobenzene on humans originate from accidental poisonings that took place in Turkey in 1955-1959, in which more than 600 cases of porphyria cutanea tarda were identified. In this incident, disturbances in porphyrin metabolism, dermatological lesions, hyperpigmentation, hypertrichosis, enlarged liver, enlargement of the thyroid gland and lymph nodes, and (in roughly half the cases) osteoporosis or arthritis were observed, primarily in children. Breast-fed infants of mothers exposed to hexachlorobenzene in this incident developed a disorder called pembe yara (pink sore) and most died within a year. There is also limited evidence that porphyria cutanea tarda occurs in humans with relatively high exposure to hexachlorobenzene in the workplace or in the general environment. The few available epidemiological studies of cancer ... are insufficient to assess the carcinogenicity of hexachlorobenzene to humans. ... There are few experimental studies on which an environmental risk assessment can be made. ... However, hexachlorobenzene concentrations ... /suggest/ that hexachlorobenzene has the potential to harm embryos of sensitive bird species ... /and/ to cause adverse effects in ... fish-eating mammals..
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 毒性总结
六氯苯通过改变尿卟啉原脱羧酶的催化或底物结合位点的巯基团,导致卟啉症。这抑制了尿卟啉原脱羧酶,导致尿卟啉原III的脱羧化不足,并在肝脏中积累尿卟啉。此外,六氯苯通过细胞色素P-450酶系统的代谢被认为会产生反应性亲电性代谢物,这些代谢物会与细胞蛋白和DNA共价结合,造成不可逆的损害。暴露于六氯苯还会吸引巨噬细胞到脾脏、肺和皮肤等器官,在那里它们被六氯苯激活。这导致了一系列涉及先天免疫细胞的反应。基因表达谱为巨噬细胞和粒细胞以及这些细胞释放的介质在对抗六氯苯的炎症反应中的重要性提供了证据。通过这种方式,产生了共同刺激或危险信号,可能多克隆激活T细胞。六氯苯是芳烃受体的弱激动剂,可能通过激活该蛋白的基因调节特性表现出一些毒性作用,可能诱导细胞色素P-450酶。它也可能在某些内分泌受体上发挥作用。
Hexachlorobenzene causes porphyria by modifying sulfhydryl groups in the catalytic or substrate-binding sites of uroporphyrinogen decarboxylase. This inhibits uroporphyrinogen decarboxylase, resulting in a deficiency of the decarboxylation of uroporphyrinogen III and accumulation of uroporphyrins in the liver. In addition, metabolism of hexachlorobenzene by the cytochrome P-450 enzymes is believed to produce reactive electrophilic metabolites that covalently bind to cellular proteins and DNA, causing irreversible damage. Exposure to hexochlorobenzene also causes macrophages to be attracted to organs such as the spleen, lungs, and skin, where they become activated by the hexochlorobenzene. This leads to a cascade of reactions involving innate immune cells. The gene expression profiles provide evidence for the importance of macrophages and granulocytes and mediators released by these cells in the adverse inflammatory response against hexochlorobenzene. In this way, co-stimulatory or danger signals are generated that could polyclonally activate T cells. Hexachlorobenzene is a weak agonist for aryl hydrocarbon receptor and may exhibit some of its toxic effects by activating the gene-regulatory properties of this protein, possibly inducing cytochome P-450 enzymes. It may also act at certain endocrine receptors. (A14, L225, A156, A157, A60)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 致癌性证据
评估:对于六氯苯在人类中的致癌性,证据不足。在实验动物中,六氯苯的致癌性证据充分。总体评估:六氯苯可能对人类具有致癌性(2B组)。
Evaluation: There is inadequate evidence in humans for the carcinogenicity of hexachlorobenzene. There is sufficient evidence in experimental animals for the carcinogenicity of hexachlorobenzene. Overall evaluation: Hexachlorobenzene is possibly carcinogenic to humans (Group 2B).
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
分类:B2;可能的人类致癌物。分类依据:六氯苯经口服给药时,已在三种啮齿动物中诱导出肝脏、甲状腺和肾脏肿瘤。人类致癌性数据:不足。动物致癌性数据:充分。
CLASSIFICATION: B2; probable human carcinogen. BASIS FOR CLASSIFICATION: Hexachlorobenzene, when administered orally, has been shown to induce tumors in the liver, thyroid, and kidney in three rodent species. HUMAN CARCINOGENICITY DATA: Inadequate. ANIMAL CARCINOGENICITY DATA: Sufficient.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
A3; 已确认的动物致癌物,对人类的相关性未知。
A3; Confirmed animal carcinogen with unknown relevance to humans.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
在大鼠经过53周的时间里,每隔一天口服... 六氯苯 ...。治疗开始后9周,摄入和排泄该化合物及其代谢物之间达到平衡。
... In rats over a 53 week period ... /hexachlorobenzene/ was given orally every other day ... 9 weeks after start of treatment an equilibrium was reached between intake and elimination of the compound and its metabolites.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
... 雄性威斯大鼠,通过胃管喂食每公斤8毫克/六氯苯/(在葵花籽油中)持续19天。治疗期末的脏器浓度为:体脂肪82 ppm;肌肉17 ppm;全肝脏125微克;全肾脏21微克;全脾9微克;全心脏1.5微克;以及肾上腺每个0.5微克。
... Male wistar rats, fed by stomach tube 8 mg /hexachlorobenzene/ ... per kg (in sunflower oil) for 19 days. Tissue concentration at termination of treatment period were for body fat, 82 ppm; muscle, 17 ppm; total liver, 125 ug; total kidney, 21 ug; total spleen, 9 ug; total heart, 1.5 ug; and adrenal, 0.5 ug each.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
带有标记的六氯苯...给药后四周,7%的放射性物质通过大鼠的肾脏排出,27%通过粪便排出。尿液中的几乎全部都是六氯苯的代谢物,而粪便中的69%...是未改变的药物。
... With labeled hexachlorobenzene ... four weeks after administration, 7% of radioactivity was excreted in rats via kidneys and 27% with feces. Nearly the total in urine was contained in metabolites of hexachlorobenzene, and 69% ... in feces was ... unchanged drug.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
... Cd-1小鼠...通过胃插管用六氯苯进行治疗,剂量为... 10, 50, 或 100 mg/kg/天。胎儿中的浓度范围从0.76 ppm到... 19.09 ppm,并且似乎...与母亲接受的剂量水平有关。在着床前治疗的...小鼠的胎儿水平高于妊娠第6-11天治疗的小鼠。...
... Cd-1 mice ... treated with hexachlorobenzene by gastric intubation at ... 10, 50, or 100 mg/kg/day. Concentration in fetuses ranged from 0.76 ppm to ... 19.09 ppm and appeared ... related to level of dose received by mother. Fetal ... levels were higher in mice treated before implantation than in those treated on days 6-11 of gestation. ...
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • 危险等级:
    6.1(b)
  • 安全说明:
    S16,S26,S29,S33,S36/37,S45,S53,S60,S61,S62,S9
  • 危险品运输编号:
    UN 2729 6.1/PG 3
  • WGK Germany:
    3
  • 海关编码:
    2903920000
  • 危险类别:
    6.1(b)
  • 危险品标志:
    T,N
  • 危险类别码:
    R50/53,R45,R48/25
  • RTECS号:
    DA2975000
  • 包装等级:
    III
  • 储存条件:
    储存注意事项: - 储存于阴凉、通风的库房。 - 远离火种、热源,包装密封。 - 应与氧化剂、食用化学品分开存放,切忌混储。 - 配备相应品种和数量的消防器材。 - 储区应备有合适的材料收容泄漏物。

SDS

SDS:e29e991ec7111e8354792623b3f3a034
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国标编号: 61876
CAS: 118-74-1
中文名称: 六氯苯
英文名称: Hexachlorobenzene;Hexachlorbenzd
别 名: 灭黑穗药
分子式: C 6 Cl 6
分子量: 284.78
熔 点: 226℃ 沸点:323~326
密 度: 相对密度(水=1)2.44;
蒸汽压: 242℃
溶解性: 不溶于水,溶于乙醚、氯仿等多数有机溶剂
稳定性: 稳定
外观与性状: 纯品为无色细针状或小片状晶体,工业品为淡黄色或淡棕色晶体
危险标记: 14(有毒品)
用 途: 用作防治麦类黑穗病,种子和土壤消毒

2.对环境的影响:
一、健康危害

侵入途径:吸入、食入。
健康危害:中毒时能影响肝脏、中枢神经系统和心血管系统。用本品拌种时引起眼刺激、烧灼感、口鼻发干、疲乏、头痛、恶心等。可致皮肤溃疡。接触者尿和粪中有大量紫质排出。
二、毒理学资料及环境行为

急性毒性:LD 50 3500mg/kg(大鼠经口);4000mg/kg(小鼠经口)
亚急性和慢性毒性:动物亚急性和慢性毒性反应有神经毒性症状,肝、肾重量增加,尿中粪卟啉排泄增加等。
致突变性:DNA损伤:鼠伤寒沙门氏菌20umol/L。微粒体致突变:制酒酵母菌100ppm。
生殖毒性:大鼠经口最低中毒剂量(TDL 0 ):40mg/kg(孕后10~13天用药),对胎鼠肌肉、骨骼系统有影响。小鼠经口最低中毒剂量(TDL 0 ):1g/kg,有胚胎毒性,对泌尿生殖系统有影响。
致癌性:IARC致癌性评论:人为可疑性反应,动物为阳性反应。
危险特性:不易燃烧。受高热分解产生有毒腐蚀性烟气。
燃烧(分解)产物:一氧化碳、二氧化碳、氯化氢。

3.现场应急监测方法:


4.实验室监测方法:


气相色谱法《水和废水监测分析方法》(第三版)国家环保局编
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:

前苏联 车间空气中有害物质的最高容许浓度 0.9mg/m 3
前苏联(1977) 居民区大气中有害物最大允许浓度 0.03mg/m 3 (最大值,昼夜均值)
中国(待颁布) 饮用水源中有害物质的最高容许浓度 0.05mg/L
中国(GHZB1-1999) 地表水环境质量标准(I、II、III类水域) 0.05mg/L


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,切断火源。应急处理人员戴好防毒面具,穿一般消防防护服。用洁净的铲子收集于干燥洁净有盖的容器中,用水泥、沥青或适当的热塑性材料固化处理再废弃。如大量泄漏,收集回收或无害处理后废弃。
废弃物处置方法:目前处置方法包括焚烧法、深井灌注法和填埋法。最有效的方法是焚烧法。
二、防护措施

呼吸系统防护:可能接触其粉尘时,应该佩戴防毒口罩。紧急事态抢救或撤离时,建议佩戴自给式呼吸器。
眼睛防护:必要时戴化学安全防护眼镜。
防护服:穿工作服。
手防护:戴防化学品手套。
其它:工作现场禁止吸烟、进食和饮水。工作后,彻底清洗。及时换洗工作服。注意个人清洁卫生。
三、急救措施

皮肤接触:脱去污染的衣着,用大量清水彻底冲洗。
眼睛接触:立即翻开上下眼睑,用流动清水或生理盐水冲洗。就医。
吸入:迅速脱离现场至空气新鲜处。保持呼吸道通畅。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:给饮足量温水,催吐。就医。

灭火方法:雾状水、泡沫、二氧化碳、干粉、砂土。


制备方法与用途

性质

六氯苯标准溶液中的溶质六氯苯具有完全对称的结构,氯取代数多,毒性大且降解困难。

特性

纯六氯苯为无色细长针状结晶,工业用品则呈淡黄色或浅棕色,并有轻微香气。它不溶于水而易溶于乙醚、三氯甲烷、热苯等有机溶剂。此化学药品是可燃物,可能具有致癌性,对眼睛和皮肤有刺激作用。受高热时会分解产生有毒腐蚀性烟气,燃烧后产物包括一氧化碳、二氧化碳及氯化氢。

用途
  • 农业杀菌剂:用于粮食农作物及种子处理,防治麦类黑穗病等疾病。
  • 工业化学品:可用于制造爆竹烟火、弹药和合成橡胶。
  • 拌种杀菌剂:用作小麦腥黑穗病和杆黑穗病的防治。
  • 焰火着色剂及五氯酚及其钠盐的原料。
化学性质

纯六氯苯为无色细长针状结晶,工业品呈淡红色,并有轻微香气。它不溶于水及乙醇,但可溶于乙醚、氯仿、苯、甲苯、二氯甲烷等有机溶剂中。

用途
  • 拌种杀菌剂:用于防治小麦腥黑穗病和杆黑穗病。
  • 焰火着色剂。
  • 生产五氯酚及五氯酚钠的原料。
  • 有机元素微量分析时用做氯的标准,也用于有机合成。
生产方法
  1. 三氯苯氯化法:将三氯苯加热至110℃干燥后,通入氯气氯化。反应温度从100-120℃上升到260-270℃,持续10-14小时后冷却结晶,用水洗涤即得六氯苯。
  2. 六六六无效体直接氯化法:将六六六无效体加热至150-170℃熔融,加入氯化塔中进行氯化。控制反应温度逐渐上升,并通入尾气吸收系统。冷却结晶后得到成品。
类别
  • 农药
  • 毒性分级:中毒
  • 急性毒性:大鼠口服LD50: 10000毫克/公斤;小鼠口服LD50: 4000毫克/公斤
  • 可燃性危险特性:燃烧产生有毒氯化物气体
  • 储运特性:库房通风低温干燥,与食品原料分开储运
灭火剂

雾状水、泡沫、二氧化碳、砂土。

职业标准
  • TWA 0.5 毫克/立方米
  • STEL 0.9 毫克/立方米

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
    • 1
    • 2

反应信息

  • 作为反应物:
    描述:
    六氯苯sodium hydroxide 作用下, 生成 五氯酚
    参考文献:
    名称:
    Preparation of pentachlorophenol
    摘要:
    公开号:
    US02107650A1
  • 作为产物:
    描述:
    参考文献:
    名称:
    Molera; Ariza, Anales de la Real Sociedad Espanola de Fisica y Quimica, Serie B: Quimica, 1958, vol. 54, p. 389,390
    摘要:
    DOI:
  • 作为试剂:
    描述:
    α-Chloro-α-(4-methoxyphenyl)acetonitrile正丁基锂六氯苯 作用下, 以 乙醚 为溶剂, 以28%的产率得到1,2,4,5-四氯苯
    参考文献:
    名称:
    Reaction of Hexachlorobenzene and (Pentachlorophenyl)lithium with .alpha.-Arylacetonitriles
    摘要:
    (Pentachlorophenyl)lithium (2) reacts with alpha-lithio-alpha-arylacetonitriles (4) at -70 degrees C to room temperature to supply alpha-aryl-alpha-(2,3,5,6-tetrachlorophenyl)ace a. Small amounts of 1,2,4,5-tetrachlorobenzene (8) and trans-1,2-dicyano-1,2-diarylethylenes 9 are also obtained; however, no alpha-tetrachloroarylated nitriles 6 from 3,4,5,6-tetrachlorobenzyne were detected. Similar treatment of hexachlorobenzene (1) and 4 afforded alpha-aryl-alpha-(2,3,4,5,6-pentachlorophenyl)acetonitriles 10. The addition of 2 to 4 at tetrachlorobenzyne-generating temperatures (0-20 degrees C) gave a complex mixture containing mainly dimeric and polymeric materials; 6 was not found. A mechanism is proposed for the reaction of 2 and 4 which suggests that nitriles 7 are formed by the condensation of 2 and 4 via a four-centered transition state and that alkenes 9 are supplied by a base-mediated dimerization of alpha-chloro-alpha-arylacetonitriles 13, formed by a lithium-chlorine exchange between 2 and 4. Nitriles 10 most likely are provided from the reaction of 1 and 4 by the usual aromatic nucleophilic substitution pathway.
    DOI:
    10.1021/jo00112a019
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文献信息

  • [EN] ACC INHIBITORS AND USES THEREOF<br/>[FR] INHIBITEURS DE L'ACC ET UTILISATIONS ASSOCIÉES
    申请人:GILEAD APOLLO LLC
    公开号:WO2017075056A1
    公开(公告)日:2017-05-04
    The present invention provides compounds I and II useful as inhibitors of Acetyl CoA Carboxylase (ACC), compositions thereof, and methods of using the same.
    本发明提供了化合物I和II,这些化合物可用作乙酰辅酶A羧化酶(ACC)的抑制剂,以及它们的组合物和使用方法。
  • [EN] BICYCLYL-SUBSTITUTED ISOTHIAZOLINE COMPOUNDS<br/>[FR] COMPOSÉS ISOTHIAZOLINE SUBSTITUÉS PAR UN BICYCLYLE
    申请人:BASF SE
    公开号:WO2014206910A1
    公开(公告)日:2014-12-31
    The present invention relates to bicyclyl-substituted isothiazoline compounds of formula (I) wherein the variables are as defined in the claims and description. The compounds are useful for combating or controlling invertebrate pests, in particular arthropod pests and nematodes. The invention also relates to a method for controlling invertebrate pests by using these compounds and to plant propagation material and to an agricultural and a veterinary composition comprising said compounds.
    本发明涉及公式(I)中变量如索权和说明中所定义的自行车基取代异噻唑啉化合物。这些化合物对抗或控制无脊椎动物害虫,特别是节肢动物害虫和线虫方面具有用途。该发明还涉及一种通过使用这些化合物来控制无脊椎动物害虫的方法,以及包含所述化合物的植物繁殖材料、农业和兽医组合物。
  • [EN] AZOLINE COMPOUNDS<br/>[FR] COMPOSÉS AZOLINE
    申请人:BASF SE
    公开号:WO2015128358A1
    公开(公告)日:2015-09-03
    The present invention relates to azoline compounds of formula (I) wherein A, B1, B2, B3, G1, G2, X1, R1, R3a, R3b, Rg1 and Rg2 are as defined in the claims and the description. The compounds are useful for combating or controlling invertebrate pests, in particular arthropod pests and nematodes. The invention also relates to a method for controlling invertebrate pests by using these compounds and to plant propagation material and to an agricultural and a veterinary composition comprising said compounds.
    本发明涉及式(I)的噁唑啉化合物,其中A、B1、B2、B3、G1、G2、X1、R1、R3a、R3b、Rg1和Rg2如权利要求和描述中所定义。这些化合物对抗或控制无脊椎动物害虫,特别是节肢动物害虫和线虫方面具有用途。该发明还涉及一种利用这些化合物控制无脊椎动物害虫的方法,以及包括所述化合物的植物繁殖材料、农业和兽医组合物。
  • [EN] MICROBIOCIDAL OXADIAZOLE DERIVATIVES<br/>[FR] DÉRIVÉS D'OXADIAZOLE MICROBIOCIDES
    申请人:SYNGENTA PARTICIPATIONS AG
    公开号:WO2017157962A1
    公开(公告)日:2017-09-21
    Compounds of the formula (I) wherein the substituents are as defined in claim 1, useful as a pesticides, especially fungicides.
    式(I)的化合物,其中取代基如权利要求1所定义,作为杀虫剂特别是杀菌剂有用。
  • Thieno-pyrimidine compounds having fungicidal activity
    申请人:Brewster Kirkland William
    公开号:US20070093498A1
    公开(公告)日:2007-04-26
    The present invention relates to thieno[2,3-d]-pyrimidine compounds having fungicidal activity.
    本发明涉及具有杀真菌活性的噻吩[2,3-d]-嘧啶化合物。
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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
cnmr
ir
raman
  • 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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