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Ammonium chromate | 7788-98-9

中文名称
——
中文别名
——
英文名称
Ammonium chromate
英文别名
diazanium;dioxido(dioxo)chromium
Ammonium chromate化学式
CAS
7788-98-9;52110-72-2
化学式
(NH4)2CrO4
mdl
——
分子量
152.07
InChiKey
MFFLHUNPSHBKRG-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:
    180°C (dec.)
  • 密度:
    1.91 g/mL at 25 °C (lit.)
  • 溶解度:
    在水中的溶解度1 Mat 20 °C,澄清,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 chromate appears as a yellow crystalline solid. Density 1.866 g / cm3. Soluble in water. Toxic by inhalation (of dust). A strong irritant. The primary hazard is the threat to the environment. Immediate steps should be taken to limit its spread to the environment. Used in dyeing, photography, chemical analysis, and as a corrosion inhibitor.
  • 颜色/状态:
    Yellow crystals
  • 气味:
    Smells of ammmonia
  • 稳定性/保质期:
    Stable under recommended storage conditions.
  • 分解:
    When heated to decomposition it emits toxic fumes of /ammonia/.

计算性质

  • 辛醇/水分配系数(LogP):
    -1.87
  • 重原子数:
    7
  • 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:
    82.3
  • 氢给体数:
    2
  • 氢受体数:
    4

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
识别和使用:醋酸铬形成黄色晶体。它用于摄影中感光明胶,在纺织品印花浆料中,用于将铬酸盐染料固定在羊毛上,并作为分析化学中的试剂。人类暴露和毒性:无数据可用。动物研究:在rec分析中使用枯草杆菌H17和M45菌株和大肠杆菌TA1538菌株进行的测试表明,醋酸铬具有诱变性。该化合物在0.05 M下进行了测试,并在两种有机体中呈阳性。醋酸铬使用大肠杆菌WP2、WP67和CM871进行大肠杆菌DNA修复测试,并使用大肠杆菌TA1535、TA100、TA1538、TA98、TA1537和TA97进行Ames反转测试。该测试包括有代谢激活和无代谢激活。该化合物在点测试中呈阳性,在2小时预孵化分析中也呈阳性。在Ames测试中,该化合物在TA100和TA97菌株中呈阳性,在TA1538、TA98和TA1537菌株中呈弱阳性,在TA1535菌株中呈阴性。
IDENTIFICATION AND USE: Ammonium chromate forms yellow crystals. It is used for sensitizing gelatin in photography, in textile printing pastes, in fixing chromate dyes on wool, and as a reagent in analytical chemistry. HUMAN EXPOSURE AND TOXICITY: There is no data available. ANIMAL STUDIES: Ammonium chromate was mutagenic when tested in the rec assay using Bacillus subtilis strains H17 and M45 and Salmonella typhimurium strain TA1538. The compound was tested at 0.05 M and was positive in both organisms. Ammonium chromate was tested using Escherichia coli strains WP2, WP67 and CM871 in the Escherichia coli DNA-repair test and using Salmonella typhimurium strains TA1535, TA100, TA1538, TA98, TA1537 and TA97 in the Ames reversion test. The test was performed both with and without metabolic activation. The compound was positive in the spot test and also in the 2 hr preincubation assay. In the Ames test the compound was positive in strains TA100 and TA97, weakly positive in strains TA1538, TA98, and TA1537 and negative in TA1535.
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在人类中具有致癌性。对接触铬的工人的职业流行病学研究结果在研究者之间和研究人群中是一致的。已经建立了铬暴露与肺癌的剂量-反应关系。接触铬的工人既暴露于三价铬也暴露于六价铬化合物。然而,只有六价铬在动物研究中被发现的具有致癌性,因此得出结论,只有六价铬应该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:大鼠和小鼠的肌内注射部位肿瘤,各种六价铬化合物在大鼠的胸膜内植入部位肿瘤,各种六价铬化合物在大鼠的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了许多潜在的致突变DNA损伤。六价铬在细菌测定、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。铬酸已被证明可以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得到研究。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......铬颜料工人的研究一致表明,职业铬暴露(主要是六价铬)与肺癌之间存在关联。对镀铬行业进行的几项研究已经证明了癌症与接触铬化合物之间的正相关关系。 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:
    O,N,T
  • 安全说明:
    S17,S45,S53,S60,S61
  • 危险类别码:
    R49
  • WGK Germany:
    3
  • 危险品运输编号:
    UN 3087
  • 危险类别:
    5.1
  • RTECS号:
    GB2880000
  • 包装等级:
    III

制备方法与用途

水中溶解度(g/100ml)

不同温度(℃)时每100毫升水中的溶解克数:

  • 25g/0℃;
  • 29.2g/10℃;
  • 34g/20℃;
  • 39.3g/30℃;
  • 45.3g/40℃;
  • 59g/60℃;
  • 76.1g/80℃。
毒性

参见铬酸钠。

化学性质

黄色单斜结晶。相对密度(12)为1.91。加热至180℃开始分解。溶于冷水,微溶于氨、丙酮,不溶于醇。长期放置可分解放出氨,部分转变为重铬酸铵。

用途

主要用作媒染剂、照相涂层增感剂、催化剂、缓蚀剂。 也可用作分析试剂、氧化剂和媒染剂。

生产方法
  • 中和法:将氨水加入盛有重铬酸铵的反应器中进行中和反应,生成铬酸铵溶液,经蒸发浓缩、冷却结晶、固液分离、干燥后制得铬酸铵成品。 [(NH_4)_2Cr_2O_7 + 2NH_4OH → 2(NH_4)_2CrO_4 + H_2O]

  • 复分解法:将铬酸钾加入盛有水的反应器中,在搅拌下缓慢加入硫酸铵溶液,进行复分解反应,生成铬酸铵和硫酸钾溶液。过滤除去硫酸钾后经蒸发浓缩、冷却结晶、固液分离、干燥制得铬酸铵成品。 [K_2CrO_4 + (NH_4)_2SO_4 → (NH_4)_2CrO_4 + K_2SO_4]

类别

氧化剂

毒性分级

高毒

急性毒性

参考值:

  • 腹腔-大鼠 LD50: 57 毫克/公斤;
  • 腹腔-小鼠LD50: 32 毫克/公斤。
爆炸物危险特性

遇热或受震动起爆

可燃性危险特性

高温产生有毒氧化铬、氮氧化物和氨烟雾

储运特性

库房通风低温干燥;与还原剂分开存放

灭火剂

干粉、泡沫、砂土、二氧化碳,雾状水

职业标准

TWA 0.05 毫克 (铬)/立方米

反应信息

  • 作为反应物:
    描述:
    参考文献:
    名称:
    SHULGA, E. A.;VOLXIN, V. V.;SOKOLOVA, T. S.;KLIMOVSKAYA, S. YU., IZV. AN TSSR. CEP. FIZ.-TEXN., XIM. I GEOL. N.,(1989) N, S. 68-70
    摘要:
    DOI:
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文献信息

  • SHULGA, E. A.;VOLXIN, V. V.;SOKOLOVA, T. S.;KLIMOVSKAYA, S. YU., IZV. AN TSSR. CEP. FIZ.-TEXN., XIM. I GEOL. N.,(1989) N, S. 68-70
    作者:SHULGA, E. A.、VOLXIN, V. V.、SOKOLOVA, T. S.、KLIMOVSKAYA, S. YU.
    DOI:——
    日期:——
  • LUCZAK, FRANCIS J.;LANDSMAN, DOUGLAS A.
    作者:LUCZAK, FRANCIS J.、LANDSMAN, DOUGLAS A.
    DOI:——
    日期:——
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