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2,2',3,4,5,5'-六氯联苯 | 52712-04-6

中文名称
2,2',3,4,5,5'-六氯联苯
中文别名
2,2’,3,4,5,5’-六氯联苯
英文名称
2,2',3,4,5,5'-hexachlorobiphenyl
英文别名
PCB 141;CB 141;1,2,3,4-tetrachloro-5-(2,5-dichlorophenyl)benzene
2,2',3,4,5,5'-六氯联苯化学式
CAS
52712-04-6
化学式
C12H4Cl6
mdl
——
分子量
360.882
InChiKey
UCLKLGIYGBLTSM-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:
    85°C
  • 沸点:
    446.99°C (rough estimate)
  • 密度:
    1.5940 (rough estimate)
  • 溶解度:
    2.09e-08 M
  • 亨利常数:
    2.30e-05 atm-m3/mole
  • 保留指数:
    2291.5;2278.6;2325.9;2324.5;2327;2314;2314;2315

计算性质

  • 辛醇/水分配系数(LogP):
    7.2
  • 重原子数:
    18
  • 可旋转键数:
    1
  • 环数:
    2.0
  • 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
多氯联苯(PCBs)通过吸入、口服和皮肤接触途径被吸收。它们通过血液运输,通常与白蛋白结合。由于它们的亲脂性特性,它们倾向于在富含脂质的组织中积累,如肝脏、脂肪组织和皮肤。多氯联苯的代谢非常缓慢,并且根据氯化的程度和位置而有所不同。多氯联苯通过微粒体单加氧酶系统代谢,该系统由细胞色素P-450酶催化,转化为极性代谢物,这些代谢物可以与谷胱甘肽和葡萄糖醛酸结合。主要的代谢物是羟基化产物,通过胆汁和粪便排出。多氯联苯的缓慢代谢意味着它们倾向于在身体组织中积累。(L4, T6)
PCBs are absorbed via inhalation, oral, and dermal routes of exposure. They are trasported in the blood, often bound to albumin. Due to their lipophilic nature they tend to accumulate in lipid-rich tissues, such as the liver, adipose, and skin. Metabolism of PCBs is very slow and varies based on the degree and position of chlorination. PCBs are metabolized by the microsomal monooxygenase system catalyzed by cytochrome P-450 enzymes to polar metabolites that can undergo conjugation with glutathione and glucuronic acid. The major metabolites are hydroxylated products which are excreted in the bile and faeces. The slow metabolism of PCBs means they tend to accumulate in body tissues. (L4, T6)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 毒性总结
PCB的作用机制因具体类型而异。类二噁烷PCB通过结合芳基烃受体,通过改变基因的转录来扰乱细胞功能,主要是通过诱导肝脏第一阶段和第二阶段酶的表达,特别是细胞色素P450家族。PCB的大多数毒性效应被认为是由Ah受体结合的结果。其他PCB被认为会干扰钙通道和/或改变大脑中的多巴胺水平。PCB还通过改变甲状腺激素的生成和结合到雌激素受体来造成内分泌干扰,这可以刺激某些癌细胞的生长并产生其他雌激素效应,如生殖功能障碍。它们通过结合到如uteroglobin等受体蛋白上而生物富集。(A3, A4, A30, A66)
The mechanism of action varies with the specific PCB. Dioxin-like PCBs bind to the aryl hydrocarbon receptor, which disrupts cell function by altering the transcription of genes, mainly be inducing the expression of hepatic Phase I and Phase II enzymes, especially of the cytochrome P450 family. Most of the toxic effects of PCBs are believed to be results of Ah receptor binding. Other PBCs are believed to interfere with calcium channels and/or change brain dopamine levels. PCBs can also cause endocrine disurption by altering the production of thyroid hormones and binding to estrogen receptors, which can stimulate the growth of certain cancer cells and produce other estrogenic effects, such as reproductive dysfunction. They will bioaccumulate by binding to receptor proteins such as uteroglobin. (A3, A4, A30, A66)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 致癌物分类
1, 对人类致癌。
1, carcinogenic to humans. (L135)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 健康影响
多氯联苯最常见的健康影响是皮肤状况,如氯痤疮和皮疹。长期暴露于多氯联苯还会导致肝脏、胃和肾脏损伤、黄疸、水肿、贫血、免疫系统变化、行为改变以及生殖能力受损。
The most common health effects of PCBs are skin conditions such as chloracne and rashes. Chronic PCB exposure has also been shown to cause liver, stomach and kidney, damage, jaundice, edema, anemia, changes in the immune system, behavioral alterations, and impaired reproduction. (L4)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 暴露途径
口服(L4级);吸入(L4级);皮肤给药(L4级)
Oral (L4) ; inhalation (L4) ; dermal (L4)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 症状
慢性PCB暴露会导致如下症状:腹痛、恶心、呕吐、腹泻、头痛、眩晕、抑郁、紧张、皮肤和眼睛损伤、疲劳、月经周期不规律以及免疫力下降。
Chronic PCB exposure results in symptoms such as abdominal pain, nausea, vomiting, diarrhea, headache, dizziness, depression, nervousness, dermal and ocular lesions, fatigue, irregular menstrual cycles and a lowered immune response. (A3)
来源:Toxin and Toxin Target Database (T3DB)

安全信息

  • 海关编码:
    2903999090

SDS

SDS:48099743fe97c50ee1646cb379d78e95
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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

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文献信息

  • 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
  • Physical, spectral and chromatographic properties of all 209 individual PCB congeners
    作者:Michael Bolgar、James Cunningham、Russell Cooper、Richard Kozloski、Jack Hubball、Don P. Miller、Terry Crone、Harry Kimball、Anita Janooby、Barry Miller、Billy Fairless
    DOI:10.1016/0045-6535(95)00140-4
    日期:1995.7
    Physical, spectral and chromatographic data for all 209 individual PCB congeners is presented. The individual congeners were synthesized and then isolated and purified. Recent emphasis on the source of the toxicity of commercial PCB formulations has increased the need for a complete set of the PCB congeners. Through the use of two capillary GC columns: 40% octadecyl/ 15% phenyl methyl siloxane and 50% phenyl methyl siloxane, it was possible to separate 201 PCB congeners with only four unresolved pairs. The data compiled in this study for all 209 congeners will aid in the identification of selected individual components of these environmental pollutants. The use of this data also presents the opportunity for the improved quantification of the commercial PCB formulations.
  • Erb,F. et al., Bulletin de la Societe Chimique de France, 1976, p. 964 - 968
    作者:Erb,F. et al.
    DOI:——
    日期:——
  • Solvent extraction and tandem dechlorination for decontamination of soil
    作者:Paul Nam、Shubhen Kapila、Qunhui Liu、Wander Tumiatti、Adriana Porciani、Virgil Flanigan
    DOI:10.1016/s0045-6535(00)00398-2
    日期:2001.5
    The United States Environmental Protection Agency (US EPA) guidelines allow removal of polychlorinated biphenyls (PCBs) from soils via solvent extraction. This option holds promise for removal of other recalcitrant organic contaminants as well. A study was undertaken to evaluate the effectiveness of solvent extraction with two tandem degradation techniques. The degradation techniques were chemical dehalogenation with immobilized reagents and gamma -ray irradiation. The integrated approach was evaluated with contaminated soils from wood treatment and electric power substation sites. Evaluations were carried out on a bench scale in the laboratory and on a semi-pilot scale at a contaminated site. Binary solvent mixture of alkanes and alcohols yielded the highest extraction efficiencies. Extraction efficiencies in excess of 90% were obtained for PCBs, polychlorinated dibenzo-p dioxins (PCDDs) and polynuclear aromatic hydrocarbons (PAHs), Extracted PCBs were rapidly degraded through chemical dehalogenation or with high doses of the gamma -ray irradiation. The residual organics in the solvent mixture were removed with activated carbon, and the solvent was recycled for subsequent soil extractions. Contaminants adsorbed on the activated carbon were destroyed with a counter flow oxidation process. (C) 2001 Elsevier Science Ltd. All rights reserved.
  • Synthesis of the 38 tetrachlorodibenzofuran isomers and identification by capillary column gas chromatography mass spectrometry
    作者:Thomas. Mazer、Fred D. Hileman、Roy W. Noble、Joseph J. Brooks
    DOI:10.1021/ac00252a028
    日期:1983.1.1
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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
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  • 峰位数据
  • 峰位匹配
  • 表征信息
Shift(ppm)
Intensity
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Shift(ppm)
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测试频率
样品用量
溶剂
溶剂用量
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同类化合物

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