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Ammonium dichromate | 7789-09-5

中文名称
——
中文别名
——
英文名称
Ammonium dichromate
英文别名
diazanium;oxido-(oxido(dioxo)chromio)oxy-dioxochromium
Ammonium dichromate化学式
CAS
7789-09-5
化学式
[NH4]2Cr2O7
mdl
——
分子量
252.07
InChiKey
JOSWYUNQBRPBDN-UHFFFAOYSA-P
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:
    170 °C (dec.)(lit.)
  • 密度:
    2.150
  • 蒸气密度:
    8.7 (vs air)
  • 溶解度:
    H2O:1 Mat 20 °C,透明,无色
  • 暴露限值:
    ACGIH: TWA 0.0002 mg/m3; STEL 0.0005 mg/m3 (Skin)OSHA: Ceiling 0.1 mg/m3NIOSH: IDLH 15 mg/m3; TWA 0.0002 mg/m3
  • 物理描述:
    Ammonium dichromate is a bright orange red crystalline solid. It is readily ignited and burns producing a voluminous green residue. If heated in a closed container, the container may rupture due to the decomposition of the material. It may also act as a strong oxidizing agent if mixed with or contaminated with combustible material. It is soluble in water.
  • 颜色/状态:
    Solid at 15 °C and 1 atm
  • 气味:
    Odorless
  • 稳定性/保质期:
    Stable under recommended storage conditions.
  • 自燃温度:
    225 °C
  • 分解:
    Thermal decomposition is initiated by locally heating to 190 °C, and flame spreads rapidly through the mass.

计算性质

  • 辛醇/水分配系数(LogP):
    -2.17
  • 重原子数:
    11
  • 可旋转键数:
    0
  • 环数:
    0.0
  • sp3杂化的碳原子比例:
    0.0
  • 拓扑面积:
    126
  • 氢给体数:
    2
  • 氢受体数:
    7

ADMET

代谢
铬通过口腔、吸入或皮肤接触被吸收,并分布到几乎所有组织中,肾脏和肝脏中浓度最高。骨骼也是一个主要的储存场所,并可能对长期保留有所贡献。六价铬与硫酸盐和铬酸盐的相似性使其能够通过硫酸盐转运机制进入细胞。在细胞内,六价铬首先被还原为五价铬,然后通过包括抗坏血酸、谷胱甘肽和烟酸腺嘌呤二核苷酸等多种物质还原为三价铬。铬几乎全部通过尿液排出。(A12, L16)
Chromium is absorbed from oral, inhalation, or dermal exposure and distributes to nearly all tissues, with the highest concentrations found in kidney and liver. Bone is also a major storage site and may contribute to long-term retention. Hexavalent chromium's similarity to sulfate and chromate allow it to be transported into cells via sulfate transport mechanisms. Inside the cell, hexavalent chromium is reduced first to pentavalent chromium, then to trivalent chromium by many substances including ascorbate, glutathione, and nicotinamide adenine dinucleotide. Chromium is almost entirely excreted with the urine. (A12, L16)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 毒性总结
鉴定和使用:重铬酸铵在15°C和1大气压下是固体,形成橙色针状物。它在美国目前没有注册为农药使用,但批准的农药用途可能会定期更改,因此必须咨询联邦、州和地方当局以获取当前批准的用途。它被用作纯氮源(尤其是在实验室中);在烟火制造中(维苏威火山火);在平版印刷和照片雕刻中;在特殊媒染剂、催化剂和瓷器成品中;在颜料制造中的中间体;以及磁性记录材料。它还用作分析化学中的氧化标准。人类暴露和毒性:对皮肤和粘膜有高度腐蚀性。如果摄入,会导致剧烈的胃肠炎,伴有霍乱样粪便、外周血管衰竭、眩晕、肌肉痉挛、昏迷、出血性疾病、发热、肝损伤和急性肾衰竭。高铁血红蛋白血症可能是血管内溶血的次要表现。文献中曾报道,一名儿童摄入重铬酸铵后导致多器官系统衰竭和死亡。交换输血和血液透析未能有效去除大量铬或导致持续的临床改善。在工业环境中,接触重铬酸铵的工人们接受了临床检查,其中18人中有9人的手背和前臂出现了皮炎。其中三名工人的皮炎在调离工作岗位后得到了治愈。动物研究:对大鼠的实验表明,吸入灰尘会导致血管周围和支气管周围组织的水肿。重铬酸铵引起的改变比钠重铬酸更明显。生态毒性研究:强烈刺激物。重铬酸铵的毒性来自未结合的部分。铬通常是两种物质中的过敏原和限制因素;通过摄入或吸入具有高度毒性。对淡水鱼和咸水鱼的阈值浓度:0.05 ppm Cr(VI)。对鱼的自由氨的阈值浓度:0.5 ppm Cr(VI)。对植物有毒。
IDENTIFICATION AND USE: Ammonium dichromate is a solid at 15 °C and 1 atm, forming orange needles. It is not registered for current pesticide use in the U.S., but approved pesticide uses may change periodically and so federal, state and local authorities must be consulted for currently approved uses. It is used as a source of pure nitrogen (especially in the laboratory); in pyrotechnics (Vesuvius fire); in lithography and photo engraving; in special mordant, catalysts, and porcelain finished; intermediate in the manufacturing of pigments; of magnetic recording materials. It is also used as an oxidimentric standard in analytical chemistry. HUMAN EXPOSURE AND TOXICITY: Highly corrosive to skin and mucous membranes. If ingested, violent gastroenteritis with cholera-like stools, peripheral vascular collapse, vertigo, muscle cramps, coma, hemorrhagic diathesis, fever, liver damage & acute renal failure. Methemoglobinemia is probably secondary to intravascular hemolysis. It has been reported in the literature that the ingestion of ammonium dichromate by a child resulted in multiple-organ-system failure and death. Exchange transfusion and hemodialysis were ineffective in removing significant amounts of chromium or causing sustained clinical improvement. In an industrial setting, workers exposed to ammonium dichromate were clinically examined, and 9 of 18 showed dermatitis on the back of the hands and forearms. Three of these workers were transferred and were cured of their dermatitis. ANIMAL STUDIES: Experiments on rats showed inhalation of dust caused edema in perivascular and peribronchial tissue. Ammonium dichromate caused more pronounced changes than did sodium dichromate. ECOTOXICITY STUDIES: Strong irritant. Ammonium toxicity stems from unionized fraction. Chromium will usually be the allergen and limiting factor of the two; Highly toxic by ingestion or inhalation. Threshold concentration for fresh and saltwater fish: 0.05 ppm Cr(VI). Threshold concentration for free ammonia to fish: 0.5 ppm Cr(VI). Toxic to plants.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 毒性总结
六价铬的致癌作用是由其代谢物五价铬和三价铬引起的。DNA损伤可能是由细胞内存在的过氧化氢分子在五价铬再氧化过程中产生的羟基自由基引起的。三价铬还可能形成与肽、蛋白质和DNA的复合物,导致DNA-蛋白质交联、DNA链断裂、DNA-DNA链间交联、铬-DNA加合物、染色体畸变和细胞信号通路改变。已经证明,它通过过度刺激细胞调节通路,并通过激活某些丝裂原活化蛋白激酶增加过氧化氢水平来诱导致癌作用。它还可以通过将组蛋白去乙酰化酶1-DNA甲基转移酶1复合物与CYP1A1启动子染色质交联,抑制组蛋白修饰,引起转录抑制。铬可能通过修饰金属调节转录因子1,导致抑制锌诱导的金属硫蛋白转录,从而增加其自身的毒性。(A12, L16, A34, A35, A36)
Hexavalent chromium's carcinogenic effects are caused by its metabolites, pentavalent and trivalent chromium. The DNA damage may be caused by hydroxyl radicals produced during reoxidation of pentavalent chromium by hydrogen peroxide molecules present in the cell. Trivalent chromium may also form complexes with peptides, proteins, and DNA, resulting in DNA-protein crosslinks, DNA strand breaks, DNA-DNA interstrand crosslinks, chromium-DNA adducts, chromosomal aberrations and alterations in cellular signaling pathways. It has been shown to induce carcinogenesis by overstimulating cellular regulatory pathways and increasing peroxide levels by activating certain mitogen-activated protein kinases. It can also cause transcriptional repression by cross-linking histone deacetylase 1-DNA methyltransferase 1 complexes to CYP1A1 promoter chromatin, inhibiting histone modification. Chromium may increase its own toxicity by modifying metal regulatory transcription factor 1, causing the inhibition of zinc-induced metallothionein transcription. (A12, L16, A34, A35, A36)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 致癌性证据
证据权重特征:根据当前指南(1986年),六价铬被归类为A组——已知的人类通过吸入途径的致癌物。通过口服途径的致癌性无法确定,被归类为D组。在拟议的指南(1996年)下,六价铬将被定性为通过吸入途径的已知人类致癌物,基于以下原因。已知六价铬通过吸入途径对人类具有致癌性。职业流行病学研究的结果一致,研究人群也一致。已经建立了铬暴露与肺癌的剂量反应关系。接触铬的工人会暴露于三价铬和六价铬化合物。然而,只有六价铬在动物研究中被发现在动物研究中具有致癌性,因此只有六价铬被归类为人类致癌物。动物数据与六价铬的人类致癌性数据一致。六价铬化合物在动物生物测定中具有致癌性,产生以下肿瘤类型:大鼠和小鼠的肌肉注射部位肿瘤,各种六价铬化合物的大鼠胸膜植入部位肿瘤,各种六价铬化合物的大鼠支气管内植入部位肿瘤,以及大鼠的皮下注射部位肉瘤。体外数据提示六价铬致癌性的潜在作用模式。六价铬的致癌性可能是由于六价铬在细胞内还原为三价形式后,形成致突变的氧化DNA损伤。六价铬容易通过细胞膜,并在细胞内迅速还原,生成反应性的三价和四价铬中间体和活性氧种。在六价铬还原过程中形成许多潜在的致突变DNA损伤。六价铬在细菌试验、酵母和V79细胞中具有致突变性,六价铬化合物降低了体外DNA合成的准确性,并因DNA损伤产生非计划性DNA合成。铬酸已被证明能转化原代细胞和细胞系。 人类致癌性数据:职业暴露于铬化合物已在铬酸盐生产、镀铬、铬颜料、铁铬生产、金矿开采、皮革鞣制和铬合金生产行业中进行研究。铬酸盐行业的工人暴露于三价和六价的铬化合物。对日本、英国、西德和美国的铬酸盐生产厂进行的流行病学研究揭示了职业暴露于铬与肺癌之间的相关性,但没有确定导致癌症的具体铬形态……对铬颜料工人的研究一致表明,职业铬暴露(主要是六价铬)与肺癌有关。对镀铬行业进行的几项研究已经证明了癌症与铬化合物暴露之间的正相关关系。 动物致癌性数据:动物数据与六价铬的人类流行病学研究结果一致……/六价铬/
WEIGHT OF EVIDENCE CHARACTERIZATION: Under the current guidelines (1986), Cr(VI) is classified as Group A - known human carcinogen by the inhalation route of exposure. Carcinogenicity by the oral route of exposure cannot be determined and is classified as Group D. Under the proposed guidelines (1996), Cr(VI) would be characterized as a known human carcinogen by the inhalation route of exposure on the following basis. Hexavalent chromium is known to be carcinogenic in humans by the inhalation route of exposure. Results of occupational epidemiological studies of chromium-exposed workers are consistent across investigators and study populations. Dose-response relationships have been established for chromium exposure and lung cancer. Chromium-exposed workers are exposed to both Cr(III) and Cr(VI) compounds. Because only Cr(VI) has been found to be carcinogenic in animal studies, however, it was concluded that only Cr(VI) should be classified as a human carcinogen. Animal data are consistent with the human carcinogenicity data on hexavalent chromium. Hexavalent chromium compounds are carcinogenic in animal bioassays, producing the following tumor types: intramuscular injection site tumors in rats and mice, intrapleural implant site tumors for various Cr(VI) compounds in rats, intrabronchial implantation site tumors for various Cr(VI) compounds in rats and subcutaneous injection site sarcomas in rats. In vitro data are suggestive of a potential mode of action for hexavalent chromium carcinogenesis. Hexavalent chromium carcinogenesis may result from the formation of mutagenic oxidatitive DNA lesions following intracellular reduction to the trivalent form. Cr(VI) readily passes through cell membranes and is rapidly reduced intracellularly to generate reactive Cr(V) and Cr(IV) intermediates and reactive oxygen species. A number of potentially mutagenic DNA lesions are formed during the reduction of Cr(VI). Hexavalent chromium is mutagenic in bacterial assays, yeasts and V79 cells, and Cr(VI) compounds decrease the fidelity of DNA synthesis in vitro and produce unscheduled DNA synthesis as a consequence of DNA damage. Chromate has been shown to transform both primary cells and cell lines. HUMAN CARCINOGENICITY DATA: Occupational exposure to chromium compounds has been studied in the chromate production, chromeplating and chrome pigment, ferrochromium production, gold mining, leather tanning and chrome alloy production industries. Workers in the chromate industry are exposed to both trivalent and hexavalent compounds of chromium. Epidemiological studies of chromate production plants in Japan, Great Britain, West Germany, and the United States have revealed a correlation between occupational exposure to chromium and lung cancer, but the specific form of chromium responsible for the induction of cancer was not identified ... Studies of chrome pigment workers have consistently demonstrated an association between occupational chromium exposure (primarily Cr(VI)) and lung cancer. Several studies of the chromeplating industry have demonstrated a positive relationship between cancer and exposure to chromium compounds. ANIMAL CARCINOGENICITY DATA: Animal data are consistent with the findings of human epidemiological studies of hexavalent chromium ... /Chromium (VI)/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
评估:有足够的人类证据证明铬(VI)化合物的致癌性。铬(VI)化合物会导致肺癌。此外,暴露于铬(IV)化合物与鼻咽癌之间也存在正相关关系。有足够的实验动物证据证明铬(VI)化合物的致癌性。铬(VI)化合物对人类具有致癌性(第1组)。/铬(VI)化合物/
Evaluation: There is sufficient evidence in humans for the carcinogenicity of chromium(VI) compounds. Chromium(VI) compounds cause cancer of the lung. Also positive associations have been observed between exposure to Chromium(IV) compounds and cancer of the nose and nasal sinuses. There is sufficient evidence in experimental animals for the carcinogenicity of chromium(VI) compounds. Chromium(VI) compounds are carcinogenic to humans (Group 1). /Chromium(VI) compounds/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
铬 hexavalent 化合物:已知是人类致癌物。/铬 hexavalent 化合物/
Chromium Hexavalent Compounds: known to be human carcinogens. /Chromium hexavalent compound/
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • TSCA:
    Yes
  • 危险等级:
    5.1
  • 危险品标志:
    E
  • 安全说明:
    S45,S53,S60,S61
  • 危险类别码:
    R8,R61,R42/43,R21,R26,R48/23,R45,R2,R50/53,R60,R34,R25,R46
  • WGK Germany:
    3
  • RTECS号:
    HX7650000
  • 包装等级:
    II
  • 危险类别:
    5.1
  • 危险标志:
    GHS03,GHS05,GHS06,GHS08,GHS09
  • 危险品运输编号:
    UN 1439 5.1/PG 2
  • 危险性描述:
    H272,H301,H312,H314,H317,H330,H334,H340,H350,H360FD,H372,H410
  • 危险性防范说明:
    P201,P280,P304 + P340 + P310,P305 + P351 + P338,P308 + P313

SDS

SDS:8fdc8540e680f82fa60271023472609a
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制备方法与用途

水中溶解度(g/100ml)

不同温度(℃)时每100毫升水中溶解的克数如下:

  • 0℃: 18.2g
  • 10℃: 25.5g
  • 20℃: 35.6g
  • 30℃: 46.5g
  • 40℃: 58.5g
  • 60℃: 86g
  • 80℃: 115g
  • 100℃: 156g
毒性

吸入重铬酸铵粉末可导致呼吸器官和鼻腔发炎,严重时甚至可能造成鼻中隔软骨穿孔。当重铬酸铵溅到皮肤上时,应立即用清水冲洗15分钟;如出现湿疹或皮炎,则需局部使用洗液、撒粉及无刺激作用的软膏。不慎入眼后,应立即用清水冲洗15分钟以上,并滴入鱼肝油及30%磺胺乙酰溶液;必要时应及时就医。

铬酸盐和重铬酸盐(按CrO₃计)的最大允许浓度为0.01 mg/m³。

生产过程中须确保设备完全密闭,工作场所通风良好以保持空气中含铬浓度低。员工应穿着工作服、佩戴口罩及使用乳胶手套等劳保用品;如有气溶胶存在时,则需佩戴防毒面具。

化学性质

重铬酸铵是一种橙红色单斜晶体,易溶于水和乙醇而不溶于丙酮。

用途
  • 凹版印刷照相制版、显影液配制
  • 制造陶瓷釉药及烟火
  • 合成香料
  • 印染媒染剂
  • 塑料与橡胶发泡剂

此外,重铬酸铵还可用于分析试剂的制备以及香料合成;在印染行业中用作酸性染料和媒介染料的媒染剂。

生产方法

工业生产方法包括复分解法和中和法。复分解法是将重铬酸钠与氯化铵按理论配比溶解于重铬酸铵母液及洗液混合物中,加热至沸腾以确保反应溶液浓度达37~38°Bé。经澄清分离不溶物后冷却至常温,并析出结晶。经过滤并水洗去除氯化物后再离心脱水干燥,最终制得重铬酸铵成品。反应方程式如下: Na₂Cr₂O₇ + 2NH₄Cl → (NH₄)₂Cr₂O₇ + 2NaCl

类别
  • 氧化剂
  • 高毒物质
  • 急性毒性:皮下注射豚鼠LDL0: 25毫克/公斤
  • 爆炸物危险特性:不稳定氧化剂,遇还原剂、硫磺或磷等混合受热、撞击或摩擦可引发爆炸
可燃性危险特性

较易燃烧,在高温分解时会释放有毒含铬化合物及氮氧化物和氨气。

储运特性

储存于通风低温干燥库房内;轻装轻卸,与有机物、还原剂、硫磺或磷等可燃物质分开存放,不与食品原料混存。

灭火方法

使用雾状水或砂土进行灭火。

职业标准
  • 时间加权平均容许浓度(TWA):0.05毫克/立方米 (铬)

反应信息

  • 作为反应物:
    参考文献:
    名称:
    CIAHOTNY, KAREL;MACHALEK, PAVEL;PICK, PETR;SIMANEK, JIRI, SB. USCHT PARZE D., 56,(1988) C. 145-172
    摘要:
    DOI:
  • 作为产物:
    描述:
    Sodium ammonium chromate 在 solution 、 Ammonium dichromate 作用下, 以 为溶剂, 反应 16.0h, 以20.31 g of ammonium dichromate were obtained的产率得到Ammonium dichromate
    参考文献:
    名称:
    METHOD FOR PRODUCING AMMONIUM DICHROMATE
    摘要:
    制备重铬酸铵的过程,包括以下步骤: c) 在温度高达200℃,尤其是在75至190℃之间,热分解碱金属铵铬酸盐双盐,特别是钠铵铬酸盐双盐或其水合物,以形成重铬酸铵; d) 通过结晶从步骤c)得到的分解产物中去除重铬酸铵。 其特征在于,碱金属铵铬酸盐双盐对应于以下公式: Mx(NH4)yCrO4或其水合物, 其中M为Na或K,特别是Na,x为0.1至0.9,优选为0.4至0.7,y为1.1至1.9,优选为1.3至1.6,x和y的和为2。
    公开号:
    US20130129604A1
  • 作为试剂:
    描述:
    Sodium ammonium chromate 、 在 Ammonium dichromate 作用下, 以 为溶剂, 反应 17.58h, 以15.72 g of ammonium dichromate were obtained的产率得到Ammonium dichromate
    参考文献:
    名称:
    METHOD FOR PRODUCING AMMONIUM DICHROMATE
    摘要:
    制备重铬酸铵的过程,包括以下步骤: c) 在温度高达200℃,尤其是在75至190℃之间,热分解碱金属铵铬酸盐双盐,特别是钠铵铬酸盐双盐或其水合物,以形成重铬酸铵; d) 通过结晶从步骤c)得到的分解产物中去除重铬酸铵。 其特征在于,碱金属铵铬酸盐双盐对应于以下公式: Mx(NH4)yCrO4或其水合物, 其中M为Na或K,特别是Na,x为0.1至0.9,优选为0.4至0.7,y为1.1至1.9,优选为1.3至1.6,x和y的和为2。
    公开号:
    US20130129604A1
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  • METHOD FOR PRODUCING CHROMIUM (III) OXIDE
    申请人:Friedrich Holger
    公开号:US20130108543A1
    公开(公告)日:2013-05-02
    Process for preparing chromium(III) oxide, comprising the steps of: a) Decomposing an alkali metal ammonium chromate double salt at a temperature of 200 to 650° C., especially of 250 to 550° C., b) washing the decomposition product obtained after a) and c) calcining the product obtained after b) at a temperature of 700 to 1400° C., especially of 800 to 1300° C.
    制备三价铬氧化物的过程,包括以下步骤: a) 在200至650°C的温度下分解一种碱金属铵铬酸盐双盐,特别是在250至550°C的温度下进行; b) 洗涤步骤a)得到的分解产物; c) 在700至1400°C的温度下煅烧步骤b)得到的产物,特别是在800至1300°C的温度下进行。
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