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铬铁矿,亚铬酸盐 | 1308-31-2

中文名称
铬铁矿,亚铬酸盐
中文别名
亚铬酸亚铁
英文名称
ferrous chromate
英文别名
chromate iron;iron chromate;Chromite (Cr2FeO4);dioxido(dioxo)chromium;iron(2+)
铬铁矿,亚铬酸盐化学式
CAS
1308-31-2
化学式
CrO4*Fe
mdl
——
分子量
171.841
InChiKey
HATQFAUMXLAKIU-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

计算性质

  • 辛醇/水分配系数(LogP):
    -2.62
  • 重原子数:
    6
  • 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:
    80.3
  • 氢给体数:
    0
  • 氢受体数:
    4

ADMET

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分析中具有致癌性,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细胞内还原为三价形式后形成的致突变氧化DNA损伤的结果。六价铬容易通过细胞膜并迅速在细胞内还原,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。六价铬在细菌分析、酵母和V79细胞中具有致突变性,六价铬化合物减少了体外DNA合成的准确性,并因DNA损伤产生非计划性DNA合成。铬酸盐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、镀铬和铬颜料、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暴露于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
A1; 确认的人类致癌物。/水溶性铬(VI)无机化合物/
A1; Confirmed human carcinogen. /Water-soluble Cr(VI) inorganic compounds/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
A1; 确认的人类致癌物。/不溶性铬(VI)无机化合物/
A1; Confirmed human carcinogen. /Insoluble Cr(VI) inorganic compounds/
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)
吸收、分配和排泄
... 铬尘很容易从兔或狗的肺部转移到其他器官,并且尿液中的铬含量有所增加。
... Chromite dust is easily translocated from lungs of rabbits or dogs to other organs, & chromium appears in /an/ increased amount in urine.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
老鼠暴露于0、0.2和1毫克/立方米铬矿渣尘埃(平均直径3.3微米)105周,检测器官和血液中铬的浓度。暴露于0.2毫克/立方米铬矿渣尘埃的老鼠肺部、肾脏和脾脏的铬浓度分别为3200、279.2和56.9纳克/克,而暴露于1.0毫克/立方米的老鼠的铬浓度分别为87700、1780和382纳克/克。肝脏、大脑和血液中的浓度大于40纳克/克。
Rats were exposed to 0, 0.2, and 1 mg/cu m of chromite ore residue dust (mean diameter 3.3 mum) for 105 wk, and concn of chromium in organs and blood were det. The chromium concn in the lung, kidney, and spleen of rats exposed to 0.2 mg/cu m were 3200, 279.2, and 56.9 ng/g, resp, and those of rats exposed to 1.0 mg/cu m were 87700, 1780, and 382 ng/g, resp The concn in the liver, brain, and blood were >40 ng/g.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
铬矿加工残留物(COPR)颗粒的偶然摄入构成了潜在的健康风险。本研究的目的是使用体外胃肠道(IVG)程序确定COPR中Cr的生物可及性。在COPR中总共有19490 mg kg(-1) Cr(VI)的情况下,胃相和肠相的生物可及Cr(VI)分别为53.8%和42.9%。食物摄入,包括牛奶、面团和抗坏血酸,导致Cr(VI)生物可及性显著降低。一些有机酸,如乳酸、苹果酸和柠檬酸适度降低了Cr(VI),而醋酸没有显示出降低Cr(VI)的能力。使用IVG提取的浓度-时间曲线下的综合面积(AUC)来计算生物可及性。与使用提取结束时的浓度(CEP)传统估计的生物可及性相比,当提取过程中发生Cr(VI)的还原时,应实施AUC技术以确认IVG方法的准确性。XANES和XRPD分析证实了提取残留物中不存在Cr(VI)相,这证明了食物和抗坏血酸释放和还原Cr(VI)。由于Cr(VI)易于生物可及且人类吸收迅速,Cr(VI)的还原可能并不像最初认为的那样是一种有效的解毒途径。/铬矿加工残留物/
Incidental ingestion of Chromite ore processing residue (COPR) particles poses a potential health risk. The purpose of this study was to determine the Cr bioaccessibility from COPR using the in vitro gastrointestinal (IVG) procedure. The bioaccessible Cr(VI) was 53.8% and 42.9%, respectively, in the gastric and intestinal phases from a total of 19490 mg kg(-1) Cr(VI) in COPR. Food intake including milk, dough, and ascorbic acid resulted in a significant decrease in Cr(VI) bioaccessibility. Some organic acids such as lactic, malic, and citric acid moderately reduced Cr(VI), while acetic acid exhibited no capacity for Cr(VI) reduction. The integrated area under the concentration-time curve (AUC) of the IVG extraction was used to calculate bioaccessibility. Compared with the bioaccessibility conventionally estimated using concentrations at the end of the extraction (CEP), the AUC technique should be implemented to confirm the accuracy of the IVG method when reduction of Cr(VI) occurs during the extraction. The absence of Cr(VI) phases in extracted residues as evidenced by XANES and XRPD analysis confirmed the Cr(VI) release and Cr(VI) reduction by food and ascorbic acid. With readily bioaccessible Cr(VI) and rapid human uptake, reduction of Cr(VI) might not be as effective a detoxification pathway as initially thought. /Chromite ore processing residue/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
铬矿加工残留物(COPR)含有可测量的六价铬和三价铬水平。[分别为Cr(VI)和Cr(III)]已被用于填充新泽西州哈德逊县的低洼地区。虽然已经证明,先前敏感个体与含有Cr(VI)的溶液直接皮肤接触可能会引起过敏性接触性皮炎(ACD),但目前尚不清楚皮肤湿度可能在多大程度上从粘附在皮肤上的COPR中溶解Cr(VI)。为了建立防止敏感个体引发ACD的COPR中Cr(VI)和Cr(III)的浓度,需要准确估计这种提取潜力。本研究的目的是使用人体汗液作为提取剂,测量受COPR影响的土壤中可提取的Cr(VI)和总铬[Cr(III)和Cr(VI)]的份额。从七名男性志愿者那里收集了人体汗液。收集了含有以下Cr(VI)和总铬浓度的COPR样品:Cr(VI),16、136和1240 ppm;总铬,932和6660 ppm。将这些样品筛分以获得均匀的粒径<500微米。然后将样品与人体汗液在30摄氏度下混合12小时,之后过滤汗液并进行分析,以确定溶解的Cr(VI)和总铬的浓度。这些分析的数据显示,在含有16 ppm Cr(VI)的COPR中没有检测到Cr(VI)的浸出(检测限=0.010 ppm)。在Cr(VI)浓度为136和1240 ppm时,COPR样品中存在的Cr(VI)的不到0.1%被提取到汗液中,汗液中的Cr(VI)浓度不超过0.133 ppm。同样,在COPR浓度为6600 ppm Crtotal时,提取的总铬量不超过0.3%,汗液中总铬的浓度不超过2.3 ppm Crtotal。如果铬敏感个体引发ACD反应所需的汗液中Cr(VI)的最低浓度为10 ppm至54 ppm,那么当前的研究结果建议,引发ACD所需的COPR Cr(VI)浓度至少为10,000-54,000 ppm。如果需要500 ppm(或更高)的溶解Cr(III)来引发ACD反应,那么引发过敏反应所需的COPR Cr(III)浓度至少为250,000 ppm。这些结果表明,由于环境暴露于COPR,ACD不太可能发生。/铬矿加工残留物/
Chromite ore processing residue (COPR) containing measurable levels of hexavalent and trivalent chromium. [Cr(VI) and Cr(III), respectively] has been used to fill in low-lying areas in Hudson County, N.J. While it has been demonstrated that direct dermal contact with solutions containing Cr(VI) may elicit allergic contact dermatitis (ACD) in previously sensitized individuals, it is unknown to what degree skin moisture may solubilize Cr(VI) from COPR adhering to skin. An accurate estimate of this extraction potential is necessary to establish COPR concentrations of Cr(VI) and Cr(III) that are protective of eliciting ACD in sensitized individuals. The purpose of this study was to measure the extractable fraction of Cr(VI) and total chromium [Cr(III) and Cr(VI)] in soils impacted by COPR using human sweat as the extractant. Human sweat was collected from seven male volunteers. Samples of COPR material containing the following Cr(VI) and total chromium concentrations were collected: Cr(VI), 16, 136, and 1240 ppm; total chromium, 932 and 6660 ppm. The samples were sieved to obtain a uniform particle size < 500 microns. The samples were then mixed with human sweat at 30 degrees C for 12 hr, after which the sweat was filtered and analyzed to determine the dissolved concentration of Cr(VI) and total chromium. The data from these analyses show that no detectable levels (limit of detection = 0.010 ppm) of Cr(VI) were leached from COPR containing 16 ppm Cr(VI). At Cr(VI) concentrations of 136 and 1240 ppm, less than 0.1% of the Cr(VI) present in the COPR sample was extracted into sweat, and sweat concentrations were 0.133 ppm Cr(VI) or less. Similarly, the amount of Cr total extracted was 0.3% or less at COPR concentrations as high as 6600 ppm Crtotal, and sweat concentrations were 2.3 ppm Crtotal or less. If a minimum concentration of 10 ppm to 54 ppm Cr(VI) in sweat is required to elicit an ACD response in chromium-sensitive individuals, the current study results suggest that a COPR Cr(VI) concentration of at least 10,000-54,000 ppm would be required to elicit ACD. If 500 ppm (or greater) of solubilized Cr(III) is required to elicit an ACD response, then a COPR concentration of 250,000 ppm Cr(III) or greater would be required to elicit an allergic response. These results suggest that ACD is unlikely to occur as a result of environmental exposure to the COPR. /Chromite ore processing residue/
来源:Hazardous Substances Data Bank (HSDB)

反应信息

  • 作为产物:
    描述:
    、 potassium dichromate 、 铁粉 在 air 作用下, 以 为溶剂, 生成 chromium(III) hydroxide 、 chromium(III) oxide铬铁矿,亚铬酸盐 、 iron(III) chromate
    参考文献:
    名称:
    Chemical reactions in electric pulse dispersion of iron in aqueous solutions
    摘要:
    IR spectroscopy, X-ray phase, chemical, kinetic, and thermodynamic analyses were used to determine the nature of chemical reactions occurring in electric pulse dispersion of a metal (Fe) in aqueous solutions of inorganic substances (MnSO4, NaH2AsO4, H3AsO3, K2Cr2O7).
    DOI:
    10.1134/s1070427208050157
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文献信息

  • Chemical reactions in electric pulse dispersion of iron in aqueous solutions
    作者:N. B. Danilenko、G. G. Savel’ev、N. A. Yavorovskii、T. A. Yurmazova
    DOI:10.1134/s1070427208050157
    日期:2008.5
    IR spectroscopy, X-ray phase, chemical, kinetic, and thermodynamic analyses were used to determine the nature of chemical reactions occurring in electric pulse dispersion of a metal (Fe) in aqueous solutions of inorganic substances (MnSO4, NaH2AsO4, H3AsO3, K2Cr2O7).
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