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聚合甲醛 | 50-00-0

中文名称
聚合甲醛
中文别名
蚁醛;福尔马林;多聚甲醛;甲醛水质标样;固体甲醛;甲醛;仲甲醛;聚氧亚甲基
英文名称
formaldehyd
英文别名
paraformaldehyd;formalin;aqueous formaldehyde;formaline;methanal;carbaldehyde;p-formaldehyde;Formaldehyde
聚合甲醛化学式
CAS
50-00-0;30525-89-4
化学式
CH2O
mdl
MFCD00003274
分子量
30.0263
InChiKey
WSFSSNUMVMOOMR-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:
    120-170 °C (lit.)
  • 沸点:
    107.25°C (rough estimate)
  • 密度:
    0.88 g/mL at 25 °C (lit.)
  • 蒸气密度:
    1.03 (vs air)
  • 闪点:
    158 °F
  • 溶解度:
    可溶于70°C 以上的氯酚
  • 介电常数:
    4.0(Ambient)
  • 物理描述:
    Solids containing varying amounts of formaldehyde, probably as paraformaldehyde (polymers of formula HO(CH2O)xH where x averages about 30). A hazard to the environment. Immediate steps should be taken to limit spread to the environment.
  • 颜色/状态:
    Nearly colorless gas [Note: Often used in an aqueous solution]. /Pure formaldehyde/
  • 气味:
    Pungent, suffocating odor
  • 蒸汽密度:
    1.067 (Air = 1)
  • 蒸汽压力:
    3,890 mm Hg at 25 °C /100% formaldehyde/
  • 亨利常数:
    Henry's Law constant = 3.37X10-7 atm-cu m/mol at 25 °C
  • 大气OH速率常数:
    9.37e-12 cm3/molecule*sec
  • 稳定性/保质期:

    On standing, especially in the cold, may become cloudy, and on exposure to very low temperature ppt of trioxymethylene formed; in air it slowly oxidizes to formic acid /40% solution/.

  • 自燃温度:
    795 °F (424 °C)
  • 分解:
    Uncatalyzed decomposition is very slow below 300 °C; extrapolation of kinetic data to 400 °C indicates that the rate of decomposition is about 0.44%/min at 101 kPa (1 atm). The main products are carbon monoxide and hydrogen. Metals such as platinium, copper, chromia, and alumina also catalyze the formation of methanol, methylformate, formic acid, carbon dioxide, and methane.
  • 粘度:
    0.1421 cP at 25 °C
  • 腐蚀性:
    Aqueous formaldehyde is corrosive to carbon steel, but formaldehyde in gas phase is not.
  • 燃烧热:
    570.7 kJ/mol (gas)
  • 汽化热:
    23.3 kJ/mol at 19 °C
  • 表面张力:
    27.3797 dyn/cm at 25 °C
  • 电离电位:
    10.88 eV
  • 聚合:
    Anhydrous, monomeric formaldehyde ... /a dry gas/ is relatively stable at 80-100 °C but slowly polymerizes at lower temp. Traces of polar impurities such as acids, alkalies, and water qreatly accelerate the polymerization. When liquid formaldehyde is warmed to room temp in a sealed ampule, it polymerizes rapidly with the evolution of heat (63 kJ/mol or 15.05 kcal/mol).
  • 气味阈值:
    Odor Threshold Low: 0.02 [ppm]; Odor Threshold High: 1.9 [ppm]; Odor threshold from CHEMINFO; In HSDB: odor threshold = 0.5-1 ppm; Odor threshold estimated at less than 0.5 ppm
  • 折光率:
    Index of refraction: 1.3746 at 20 °C/D /Formaldehyde soln/
  • 解离常数:
    13.3 (at 25 °C)
  • 保留指数:
    229 ;273 ;247 ;247

计算性质

  • 辛醇/水分配系数(LogP):
    1.2
  • 重原子数:
    2
  • 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:
    17.1
  • 氢给体数:
    0
  • 氢受体数:
    1

ADMET

代谢
当雌性大鼠以70毫克/千克的剂量经腹腔注射给予14C-甲醛时,82%的剂量以14二氧化碳的形式呼出,13-14%的剂量以蛋酸、丝氨酸甲醛-半胱酸加合物的形式通过肾脏排出。
When female rats were administered (14)C-formaldehyde ip at dose level of 70 mg/kg, 82% of dose was expired as (14)carbon dioxide and 13-14% was excreted via kidneys in form of methionine, serine, and formaldehyde-cysteine adduct.
来源:Hazardous Substances Data Bank (HSDB)
代谢
注射了0.26毫克/千克(14)C标记的甲醛的老鼠...在5天内通过尿液排出了大约22%的剂量。在尿液中,甲醛的代谢物被鉴定为甲酸噻唑烷-4-羧酸生物
Rats injected ip with 0.26 mg/kg (14)C-labeled formaldehyde ... excreted approx 22% of this dose in the urine over 5 days. Formic acid and a thiazolidine-4-carboxylic acid derivative were identified in urine as formaldehyde metabolites.
来源:Hazardous Substances Data Bank (HSDB)
代谢
在大鼠腹腔注射(14)C-甲醛后,已经鉴定出甲醛的几种尿液排泄产物。在给Wistar大鼠注射0.26毫克/千克体重后,检测到了甲酸和一种含代谢物(认为是噻唑烷-4-羧酸的衍生物)以及假定来源于一碳代谢的产物。通过甲醛与半胱酸的非酶促缩合形成的噻唑烷-4-羧酸酯在尿液中未被检测到。
Several of the urinary excretion products of formaldehyde in rats have been identified after intraperitoneal administration of (14)C-formaldehyde. After injecting Wistar rats with 0.26 mg/kg body weight, ... formate and a sulfur-containing metabolite (thought to be a derivative of thiazolidine-4-carboxylic acid) and products presumed to result from one-carbon metabolism /were detected/. Thiazolidine-4-carboxylate, which is formed via the nonenzymatic condensation of formaldehyde with cysteine, was not detected in urine.
来源:Hazardous Substances Data Bank (HSDB)
代谢
甲醛被吸收进入血液后,会被代谢成甲酸,然后以钠盐的形式通过尿液排出,或者进一步氧化成二氧化碳。这种解毒过程可以有效处理低浓度的甲醛,但高浓度的甲醛会导致酸中毒和组织损伤。
Formaldehyde absorbed into the bloodstream is metabolized to formic acid, which is excreted in the urine as the sodium salt or oxidized further to carbon dioxide and water. This detoxification process can deal efficiently with low concentrations of formaldehyde, but high concentrations cause acidosis and tissue damage.
来源:Hazardous Substances Data Bank (HSDB)
代谢
甲醛可能通过吸入、口服或皮肤接触被吸收。它是所有细胞中的基本代谢中间体,在丝氨酸、甘酸、甲酸和胆碱的正常代谢过程中产生,也通过N-、S-和O-甲基化合物的脱甲基作用产生。外源性甲醛通过酶甲醛脱氢酶在最初接触点转化为甲酸甲醛氧化为甲酸后,碳原子进一步氧化为二氧化碳,或者通过四氢叶酸依赖的一碳生物合成途径并入嘌呤、胸腺嘧啶氨基酸中。甲醛不会在体内储存,而是通过尿液排出(主要是作为甲酸),并入其他细胞分子中,或者作为二氧化碳呼出。
Formaldehyde may be absorbed following inhalation, oral, or dermal exposure. It is an essential metabolic intermediate in all cells and is produced during the normal metabolism of serine, glycine, methionine, and choline and also by the demethylation of N-, S-, and O-methyl compounds. Exogenous formaldehyde is metabolized to formate by the enzyme formaldehyde dehydrogenase at the initial site of contact. After oxidation of formaldehyde to formate, the carbon atom is further oxidized to carbon dioxide or incorporated into purines, thymidine, and amino acids via tetrahydrofolatedependent one-carbon biosynthetic pathways. Formaldehyde is not stored in the body and is excreted in the urine (primarily as formic acid), incorporated into other cellular molecules, or exhaled as carbon dioxide. (L962)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 毒性总结
识别和使用:甲醛是一种无色、白色、微酸性、气体或液体。它在美国注册用于杀虫剂,但批准的杀虫剂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。甲醛主要用于农业场所的熏蒸,如家禽和养猪场及加工厂,以及柑橘包装和蘑菇房。它还用作商业场所、工业场所和兽医诊所的硬表面消毒剂。甲醛还注册为消费品(如洗衣粉、通用清洁剂和壁纸粘合剂)的材料防腐剂。这种化学物质没有不活性成分的用途。它还用作生物制品、外用剂、乙型肝炎疫苗和肾透析膜的消毒剂。医学上甲醛的额外用途包括消毒医院病房、保存标本,以及作为对抗足癣的消毒剂。人类暴露和毒性:空气中甲醛暴露的急性效应:气味检测,0.05-1.0 ppm;眼刺激,0.01-2 ppm;上呼吸道刺激(例如,鼻或喉咙刺激),0.10-11 ppm;下呼吸道刺激(例如,咳嗽、胸闷和喘息),5-30 ppm;肺肿、炎症、肺炎,50-100 ppm;死亡>100 ppm。甲醛能引起敏感个体的皮肤反应,不仅通过接触,还通过吸入。根据国际癌症研究机构(IARC)的数据,有足够的证据表明甲醛对人类具有致癌性。甲醛导致鼻咽癌和白血病。此外,甲醛暴露与鼻咽癌之间存在正相关关系。对服装行业暴露于甲醛的妇女的生殖功能调查发现,月经失调、生殖道炎症疾病、不孕、贫血和后代低出生体重的发生率增加。发表的研究表明,吸入甲醛会导致鼻腔和/或颊粘膜细胞微核频率增加。动物研究:大鼠对低浓度(<1 ppm)或中等浓度(10-50 ppm)蒸汽的急性效应导致呼吸道阻力增加、鼻腭神经敏感性降低、眼睛和呼吸系统刺激以及下丘脑变化。高剂量(>100 ppm)暴露导致流涎、急性呼吸困难、呕吐、抽搐和死亡。在黑色小鼠的sc注射部位观察到100 ug甲醛的毛发脱色。皮肤处理甲醛的小鼠发展为严重肝损伤。将25只交配的雌性大鼠通过吸入暴露于甲醛(0、2、5或10 ppm(2.5、6.2或12.3 mg/cu m),每天6小时,妊娠第6-15天。在10 ppm时,母体食物消耗量和体重增加显著降低。妊娠的各个参数,包括黄体数量、着床点、活胎、死胎和吸收或胎儿体重,均未受到处理的影响。在5和10 ppm时观察到骨质减少的发生率增加,且没有母体毒性(10 ppm)。在大鼠吸入暴露2年后,甲醛引起了鼻鳞状细胞癌。在历史数据库中的16,794只大鼠中,这种肿瘤的发生率为零,表明这是一种罕见的自发性肿瘤。在实验开始时,不同年龄的雄性和雌性大鼠(12天胚胎,以及7周和25周大)通过饮用给予不同剂量的甲醛(2,500或1,500、1,000、500、100、50、10、0 ppm)。在处理甲醛的大鼠中观察到白血病和胃肠肿瘤的发生率增加。胃肠肿瘤在所用大鼠群体中极为罕见。甲醛诱导细菌、真菌、酵母和果蝇幼虫以及培养的啮齿动物和人类细胞的基因突变。这部分突变似乎是DNA损伤的结果。甲醛可能损害基因组的第二种机制是抑制DNA修复。生态毒性研究:研究结论是,将福尔马林以2.5 mL/kg饲料喂给雌性鹌鹑是无害的,然而,更高剂量并非没有健康风险。
IDENTIFICATION AND USE: Formaldehyde is a clear, water-white, very slightly acid, gas or liquid. It is registered for 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. Formaldehyde is used primarily as a fumigant in agricultural premises such as poultry and swine farms and processing plants as well as in citrus packing and mushroom houses. It is used as a hard surface disinfectant in commercial premises, industrial premises and veterinary clinics. Formaldehyde is also registered as a materials preservative for consumer products such as laundry detergents, general purpose cleaners and wall paper adhesives. There are no inert ingredient uses for this chemical. It is also used as an antimicrobial in biologics, topicals, hepatitis B vaccine, sterilizer for kidney dialysis membranes. Additional uses of formaldehyde in medicine include disinfecting hospital wards, preserving specimens, and as a disinfectant against athlete's foot. HUMAN EXPOSURE AND TOXICITY: Acute effects of airborne formaldehyde exposure: Odor detection, 0.05-1.0 ppm; Eye irritation, 0.01-2 ppm; Upper respiratory tract irritation (e.g., irritation of the nose or throat), 0.10-11 ppm; Lower airway irritation (e.g., cough, chest tightness, and wheezing), 5-30 ppm; Pulmonary edema, inflammation, pneumonia, 50-100 ppm; Death >100 ppm. Formaldehyde can provoke skin reactions in sensitized subjects, not only by contact but also by inhalation. According to IARC, there is sufficient evidence in humans for the carcinogenicity of formaldehyde. Formaldehyde causes cancer of the nasopharynx and leukemia. Also, a positive association has been observed between exposure to formaldehyde and sinonasal cancer. An investigation of reproductive function in female workers exposed to formaldehyde in the garment industry revealed increased incidence of menstrual disorders, inflammatory disease of the reproductive tract, sterility, anemia, and low birth weights among offspring. The published studies suggest that inhalation of formaldehyde leads to increased micronuclei frequencies in nasal and/or buccal mucosa cells. ANIMAL STUDIES: Acute effects in rats to low (<1 ppm) or moderate (10-50 ppm) of vapor resulted in increased airway resistance, decreased sensitivity of nasopalatine nerve, irritation of eyes and of respiratory system, and changes in hypothalamus. Exposure to high doses (above 100 ppm) caused salivation, acute dyspnea, vomiting, cramps and death. Hair depigmentation was observed in black mice at site of sc injection of 100 ug formaldehyde. Mice treated with formaldehyde on skin developed severe liver damage. Groups of 25 mated female rats were exposed by inhalation to formaldehyde (0, 2, 5 or 10 ppm (2.5, 6.2 or 12.3 mg/cu m) for 6 hr per day on days 6-15 of gestation. At 10 ppm, there was a significant decrease in maternal food consumption and weight gain. None of the parameters of pregnancy, including numbers of corpora lutea, implantation sites, live fetuses, dead fetuses and resorptions or fetal weights, were affected by treatment. An increased incidence of reduced ossification was observed at 5 and 10 ppm in the absence of maternal toxicity (10 ppm). Formaldehyde caused nasal squamous cell carcinomas in the rat following 2 year inhalation exposure. The incidence of this tumor in a historical data base of 16,794 rats was nil, indicating that it is a rare spontaneous tumor. Male and female rats of different ages at the start of the experiments (12 day embryos, and 7 and 25 weeks old) were administered formaldehyde in drinking water at different doses (2,500 or 1,500, 1,000, 500, 100, 50, 10, 0 ppm). An increased incidence of leukemias and of gastro-intestinal tumors was observed in formaldehyde treated rats. Gastro-intestinal tumors are exceptionally rare in the rats of the colony used. Formaldehyde induces gene mutation in bacteria, fungi, yeast, and Drosophila larvae as well as in cultured rodent and human cells. In part, these mutations appear to be the consequence of DNA damage. A second mechanism by which formaldehyde may damage the genome is inhibition of DNA repair. ECOTOXICITY STUDIES: It was concluded from the study that formalin feeding to female quails at 2.5 mL/kg feed is without harmful effects, however, higher doses are not without health risks.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 毒性总结
当细胞内甲醛平饱和了甲醛脱氢酶活性时,很可能会发生甲醛中毒,使得未经代谢的完整分子得以发挥其作用。甲醛已知能够在蛋白质和DNA之间形成交联,并且代谢整合进入大分子(DNA、RNA和蛋白质)中。
It is likely that formaldehyde toxicity occurs when intracellular levels saturate formaldehyde dehydrogenase activity, allowing the unmetabolized intact molecule to exert its effects. Formaldehyde is known to form cross links between protein and DNA and undergo metabolic incorporation into macromolecules (DNA, RNA, and proteins). (L962)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 致癌性证据
甲醛在人类中有充分的致癌证据。甲醛会导致鼻咽癌和白血病。此外,甲醛暴露与鼻咽癌之间也观察到了正相关。在实验动物中也有充分的证据表明甲醛具有致癌性。工作组对于甲醛是否会在人类中导致白血病的评估并不完全一致,小部分人认为致癌的证据是充分的,而少数人则认为证据有限。特别是在讨论充分证据时,一项最近被接受发表的研究首次报告了暴露工人的血液中存在非整倍体现象,这是骨髓白血病和骨髓增生异常综合症的特征,并提供了支持性信息,表明主要循环血细胞类型和循环造血干细胞数量有所减少。作者和工作组认为这项研究需要被重复验证。甲醛对人类具有致癌性(第1组)。
There is sufficient evidence in humans for the carcinogenicity of formaldehyde. Formaldehyde causes cancer of the nasopharynx and leukaemia. Also, a positive association has been observed between exposure to formaldehyde and sinonasal cancer. There is sufficient evidence in experimental animals for the carcinogenicity of formaldehyde. The Working Group was not in full agreement on the evaluation of formaldehyde causing leukaemias in humans, with a small majority viewing the evidence as sufficient of carcinogenicity and the minority viewing the evidence as limited. Particularly relevant to the discussions regarding sufficient evidence was a recent study accepted for publication which, for the first time, reported aneuploidy in blood of exposed workers characteristic of myeloid leukaemia and myelodysplastic syndromes, with supporting information suggesting a decrease in the major circulating blood-cell types and in circulating haematological precursor cells. The authors and Working Group felt that this study needed to be replicated. Formaldehyde is carcinogenic to humans (Group 1).
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
癌症分类:B1组,可能的人类致癌物
Cancer Classification: Group B1 Probable Human Carcinogen
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
分类:B1;可能的人类致癌物。分类依据:基于有限的人类数据和充分的动物数据。人类数据包括九项研究,这些研究显示了特定部位呼吸道肿瘤与甲醛或含甲醛产品暴露的统计学显著相关性。在大鼠和小鼠的长期吸入研究中观察到了鼻鳞状细胞癌发病率的增加。这一分类得到了体外遗传毒性数据的支持,以及甲醛与其他致癌性醛类乙醛的结构关系。人类致癌性数据:有限。动物致癌性数据:充分。
CLASSIFICATION: B1; probable human carcinogen. BASIS FOR CLASSIFICATION: Based on limited evidence in humans, and sufficient evidence in animals. Human data include nine studies that show statistically significant associations between site-specific respiratory neoplasms and exposure to formaldehyde or formaldehyde-containing products. An increased incidence of nasal squamous cell carcinomas was observed in long-term inhalation studies in rats and in mice. The classification is supported by in vitro genotoxicity data and formaldehyde's structural relationships to other carcinogenic aldehydes such as acetaldehyde. HUMAN CARCINOGENICITY DATA: Limited. ANIMAL CARCINOGENICITY DATA: Sufficient.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
甲醛可以通过呼吸道和口腔途径轻易吸收,通过皮肤吸收的量要少得多。它是简单的醛类化合物,容易与蛋白质和核酸等大分子反应。报告显示,吸入暴露几乎可以完全吸收。由于接触含有甲醛的材料(如纺织品、永久压烫服装、化妆品或其他材料)而导致的皮肤吸收量相对较低。甲醛通常被转化为二氧化碳排出空气中,以甲酸的形式排出尿液中,或作为单碳池代谢的一个或多个分解产物。由于通过口腔和吸入途径的快速吸收以及其快速的代谢,几乎没有未代谢的甲醛被排出。在通过吸入暴露于14C-甲醛的大鼠中,40%的放射性标记物通过空气排出,20%通过尿液和粪便排出,而40%留在尸体中。
Formaldehyde is absorbed readily from the respiratory and oral tracts and, to a much lesser degree, from the skin. It is the simplest aldehyde and reacts readily with macromolecules, such as proteins and nucleic acids. Inhalational exposure has been reported to result in almost complete absorption. Dermal absorption due to contact with formaldehyde-containing materials (e.g., textiles, permanent-press clothing, cosmetics, or other materials) is of low order of magnitude. ... Formaldehyde normally is converted and excreted as carbon dioxide in the air, as formic acid in the urine, or as one of many breakdown products from one-carbon pool metabolism. As a result of rapid absorption by both the oral and inhalational routes and its rapid metabolism, little or no formaldehyde is excreted unmetabolized. In rats exposed to (14)C-formaldehyde by inhalation, 40% of the radiolabel was excreted in the air and 20% in the urine and feces, whereas 40% remained in the carcass.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
在大鼠和小鼠中通过胃管给予14C-甲醛后,12小时内,40%的剂量以二氧化碳形式呼出,10%通过尿液排出,1%通过粪便排出;24小时后尸体中含有20%,4天后含有10%。当以70毫克/千克的剂量平通过腹腔注射给雌性大鼠14C-甲醛时,82%的剂量以14C二氧化碳形式呼出,13-14%通过肾脏排出……。
In rats and mice administered (14)C-formaldehyde intragastrically, 40% of dose... /was/ expired as carbon dioxide, 10% /was/ excreted in urine and 1% in feces after 12 hr; carcasses contained 20% after 24 hr and 10% after 4 days. When female rats were administered (14)C-formaldehyde ip at dose level of 70 mg/kg, 82% of dose was expired as (14)C dioxide and 13-14% was excreted via kidneys... .
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
甲醛在啮齿动物肠道中被迅速且几乎完全吸收。在大鼠中,口服剂量的约40%(14)C-甲醛(7毫克/千克)在12小时内以(14)C-二氧化碳的形式排出,而10%通过尿液排出,1%通过粪便排出。大量的放射性物质以代谢结合产物的形式残留在尸体中。
Formaldehyde is absorbed rapidly and almost completely from the rodent intestinal tract. In rats, about 40% of an oral dose of (14)C-formaldehyde (7 mg/kg) was eliminated as (14)C-carbon dioxide within 12 hours, while 10% was excreted in the urine and 1% in the feces. A substantial portion of the radioactivity remained in the carcass as products of metabolic incorporation.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
有四男两女暴露在1.9 ppm甲醛浓度的大型步入式实验舱中40分钟。在暴露前后不久,从每个人(每个人都是自己的对照)静脉抽取血样,并分析血中的甲醛含量。暴露前人体静脉血中甲醛的平均浓度为2.61 ± 0.41微克/克血。个体间的变异性非常明显。在40分钟暴露后立即,血液中甲醛的平均浓度为2.77 ± 0.28微克/克血。在本次研究中测试的甲醛空气浓度下,暴露前后的血液甲醛浓度没有显著差异。这个结果表明甲醛只被吸收到呼吸道的组织中。血液中甲醛浓度没有增加可能是由于它在这些组织中快速代谢和/或与细胞大分子的快速反应。
Four men and two women were exposed to a 1.9 ppm air concentration of formaldehyde in a large walk-in chamber for 40 minutes. Shortly before and shortly after the exposure, venous blood samples were taken from each person (each person served as his/her own control) and the blood was analyzed for formaldehyde content. Mean venous blood formaldehyde concentrations in humans prior to exposure showed a blood concentration of 2.61 + or - 0.41 ug/g of blood. Individual variability was markedly present. Immediately after a 40-minute exposure, mean blood concentration of formaldehyde was 2.77 + or - 0.28 ug/g of blood. There was no significant difference between pre- and postexposure blood concentrations of formaldehyde at the formaldehyde air concentrations tested in this study. This result suggests that formaldehyde was absorbed only into the tissues of the respiratory tract. The absence of increased formaldehyde concentrations in the blood is likely due to its rapid metabolism in these tissues and/or fast reaction with cellular macromolecules.
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • TSCA:
    Yes
  • 危险等级:
    4.1
  • 危险品标志:
    C,T
  • 安全说明:
    S26,S36/37/39,S45,S51,S53,S60
  • 危险类别码:
    R23/24/25,R34,R45,R43
  • WGK Germany:
    2
  • 海关编码:
    2912110000
  • 危险品运输编号:
    UN 2209 8 / PGIII
  • 危险类别:
    S26;S36/37/39;S45;S51;S53;S60
  • RTECS号:
    LP8925000
  • 包装等级:
    8
  • 危险标志:
    GHS05,GHS06,GHS08
  • 危险性描述:
    H301 + H311 + H331,H314,H317,H335,H341,H350,H370
  • 危险性防范说明:
    P201,P260,P280,P301 + P310 + P330,P303 + P361 + P353,P304 + P340 + P310,P305 + P351 + P338,P308 + P311

SDS

SDS:e0e264c88f8a8be2b7f3b903c52dfe41
查看
国标编号: 83012
CAS: 50-00-0
中文名称: 甲醛
英文名称: Formaldehyde
别 名: 福尔马林蚁醛
分子式: CH 2 O;HCHO
分子量: 30.03
熔 点: -92℃ 沸点:-19.4℃
密 度: 相对密度(=1)0.82;
蒸汽压: 50℃/37%
溶解性: 易溶于,溶于乙醇等多数有机溶剂
稳定性: 稳定
外观与性状: 无色,具有刺激性和窒息性的气体,商品为其溶液
危险标记: 20(腐蚀品)
用 途: 是一种重要的有机原料,也是炸药、染料、医药、农药的原料,也作杀菌剂、消毒剂等

2.对环境的影响:
一、健康危害
侵入途径:吸入、食入、经皮吸收。
健康危害:本品对粘膜、上呼吸道、眼睛和皮肤有强烈刺激性。接触其蒸气,引起结膜炎、角膜炎、鼻炎、支气管炎;重者发生喉痉挛、声门肿和肺炎等。对皮肤有原发性刺激和致敏作用;浓溶液可引起皮肤凝固性坏死。口服灼伤口腔和消化道,可致死。
慢性影响:长期低浓度接触甲醛蒸气,可出现头痛、头晕、乏力、两侧不对称感觉障碍和排汗过盛以及视力障碍。本品能抑制汗腺分泌,长期接触可致皮肤干燥皲裂。
甲醛是一种具强还原性的原生质毒素,进入人体器官后,能与蛋白质中的基结合生成所谓甲酰化蛋白而残留在体内,其反应速度受pH值温度的显著影响。进入人体的甲醛亦可能转化成甲酸强烈地刺激粘膜,并逐渐排出体外。
二、毒理学资料及环境行为
急性毒性:LD 50 800mg/kg(大鼠经口),2700mg/kg(兔经皮);LC 50 590mg/m 3 (大鼠吸入);人吸入60~120mg/m 3 ,发生支气管炎、肺部严重损害;人吸入12~24mg/m 3 ,,鼻、咽粘膜严重灼务、流泪、咳嗽;人经口10~20ml,致死。
亚急性和慢性毒性:大鼠吸入50~70mg/m 3 ,1小时/天,3天/周,35周,发现气管及支气管基底细胞增生及生化改变;人吸入20~70mg/m×长时间,食欲丧失、体重减轻、无力、头痛、失眠;人吸入12mg/m 3 ×长期接触,嗜睡、无力、头痛、手指震颤、视力减退。
致突变性:微生物致突变:鼠伤寒沙门氏菌4mg/L。哺乳动物体细胞突变:人淋巴细胞130umol/L。姊妹染色体交换:人淋巴细胞37pph。
生殖毒性:大鼠经口最低中毒剂量(TDL 0 ):200mg/kg(1天,雄性),对精子生存有影响。大鼠吸入最低中毒浓度(TCL 0 ):12ug/m 3 ,24小时(孕1~22天),引起新生鼠生化和代谢改变。
致癌性:IARC致癌性评论:动物阳性;人类不明确。
代谢和降解:环境中甲醛的主要污染来源是有机合成、化工、合成纤维、染料、木材加工及制漆等行业排放的废、废气等。某些有机化合物在环境中降解也产生甲醛,如氯乙烯的降解产物也包含甲醛。由于甲醛有强的还原性,在有氧化性物质存在条件下,能被氧化为甲酸。例如进入体环境中的甲醛可被腐生菌氧化分解,因而能消耗中的溶解氧。甲酸进一步的分解产物为二氧化碳。进入环境中的甲醛在物理、化学生物等的共同作用下,被逐渐稀释氧化和降解。甲醛的氧化降解过程如下:2HCHO+O 2 ---2HCOOH 2HCOOH+O 2 ---2H 2 O+2CO 2

残留与蓄积:资料记载,工业企业区土壤中吸附的甲醛含量可达180-720mg/kg干土。土壤的污染可导致地下污染,甲醛含量可以比表层土高出10-20倍。
甲醛在环境中颇稳定,当甲醛浓度为5mg/L时(20℃),观察结果表明,5天内可以保持恒定。甲醛浓度为<20mg/L时,可以被曝气池中经驯化的微生物降解消化。而含量为100mg/L时,能抑制微生物对有机物的氧化。当甲醛含量为500mg/L时,生物耗氧过程全部中止,中微生物被杀死。

迁移转化:甲醛由于沸点低又易溶于,所以主要通过大气和排放进入环境。生产甲醛的工厂其未处理的气体,当排放高度为18米时,其距工厂250-500米的大气样品中,甲醛含量均在0.035mg/m 3 以上。1000米远在大气中甲醛浓度在嗅阈以下。以甲醛作鞣剂生产塑料的企业周围大气中的甲醛浓度在嗅阈以下。以甲醛作鞣剂生产塑料的企业周围大气中的甲醛浓度距厂区100米内为0.012mg/m 3 ;200米处36个样品中有15个浓度低于0.012mg/m 3 ;400米处均低于0.012mg/m 3
工业废中排放的甲醛含量由于行业不同有很大差别,其中浓度最高的甲醛是生产树脂的上层焦油废,含甲醛量高达2.5%。
危险特性:其蒸气与空气形成爆炸性混合物,遇明火、高热能引起燃烧爆炸。若遇高热,容器内压增大,有开裂和爆炸的危险。
燃烧(分解)产物:一氧化碳二氧化碳

3.现场应急监测方法:


直接进样气相色谱法;气体检测管法
气体速测管(德国德尔格公司产品)

4.实验室监测方法:

监测方法 来源 类别
乙酰丙酮分光光度法 GB13197-91
乙酰丙酮分光光度法 GB/T15500-95 空气
示波极谱法 WS/T150-1999 作业场所空气
气相色谱法 《空气中有害物质的测定方法》(第二版),杭士平主编 空气
气相色谱法 质分析大全》,张宏陶等主编
变色酸光度法 和废监测分析方法》国家环保局编 和废

5.环境标准:

中国(TJ36-79) 车间空气中有害物质的最高容许浓度 3mg/m 3
中国(TJ36-79) 居住区大气中有害物质的最高容许浓度 0.05mg/m 3 (一次值)
中国(GB16297-1996) 大气污染物综合排放标准 ①最高允许排放浓度(mg/m 3 ):
30(表1);25mg/m 3 (表2)
②最高允许排放速率(kg/h):
二级0.3~6.4;0.26~5.4(表1)
三级0.46~9.8h;0.39~8.3(表2)
③无组织排放监控浓度限值(mg/m 3 ):
0.20(表2);0.25(表1)
中国(待颁布) 饮用源中有害物质的最高允许浓度 0.5mg/L
中国(GB8978-1996) 综合排放标准 一级1.0mg/L
二级2.0mg/L
三级5.0mg/L
嗅觉阈浓度 1ppm

6.应急处理处置方法:
一、泄漏应急处理
疏散泄漏污染区人员至安全区,禁止无关人员进入污染区,切断火源。建议应急处理人员戴自给式呼吸器,穿化学防护服。不要直接接触泄漏物,在确保安全情况下堵漏。喷雾能减少蒸发但不要使进入储存容器内。用沙土或其它不燃性吸附剂混合吸收,然后收集运至集运至废物处理场所处置。也可以用大量冲洗,经稀释的洗放入废系统。
二、防护措施
呼吸系统防护:可能接触其蒸气时,应该佩带防毒面具。紧急事态抢救或逃生时,佩带自给式呼吸器。
眼睛防护:戴化学安全防护眼镜。
防护服:穿相应的防护服。
手防护:戴防化学品手套。
其它:工作现场禁止吸烟、进食和饮。工作后,彻底清洗。注意个人清洁卫生。进行就业前和定期的体检。进入罐或其它高浓度区作业,须有人监护。
三、急救措施
皮肤接触:脱去污染的衣着,用肥皂及清彻底冲洗。或用2%碳酸氢溶液冲洗。
眼睛接触:立即提起眼睑,用流动清或生理盐冲洗至少15分钟。
吸入:迅速脱离现场至空气新鲜处。保持呼吸道通畅。必要时进行人工呼吸。就医。
食入:患者清醒时立即漱口,洗胃。就医。
灭火方法:雾状、泡沫、二氧化碳、砂土。

制备方法与用途

聚甲醛概述

聚甲醛(IUPAC命名Polyoxymethylene,POM)是甲醛的聚合物,分子量较高,一般结构长度在八到一百个单位之间。长链多聚甲醛常用于制作耐热塑料,又称聚甲醛塑胶(POE),杜邦公司出品的商品名为Derlin。多聚甲醛分解较快,会释放出具有轻微臭味的甲醛

应用

聚甲醛主要用于除草剂的生产和使用,还用于合成树脂(如人造角制品或人造象牙)与胶粘剂的制备。此外,在制药工业中,它是避孕乳膏的有效成分之一,并可作为药物熏蒸、消毒之用,亦可用作杀菌和杀虫剂

制备

聚甲醛的制备方法包括将含37%甲醛溶液在65℃下真空浓缩至80%的浓度。随后以1.5%的比例加入氧化镁悬浊液中,该悬浊液由甲醇中的氧化镁细粉末分散而成(氧化镁浓度为50ppm),然后通过挤压机制成2-5mm颗粒,并在干燥机中进行60分钟或120分钟的干燥。这样可分别得到含固体成分80%和92%的多聚甲醛,产量可达400kg/hr。

化学性质

聚甲醛是一种白色、可燃的结晶粉末,具有甲醛特有的气味。它能缓慢溶解于冷,在热中的溶解度较快。在20℃时中溶解度为0.24g/100cm³H₂O,不溶于乙醇乙醚,但可溶于苛性溶液中。

用途

聚甲醛作为有机化工、合成树脂的原料,还用于药物熏蒸剂。它是一种高甲醛含量的固态甲醛,呈固体颗粒状便于储存与运输,在高温下可转化为甲醛气体,有利于参与各种化学反应,尤其适用于无甲醛作原料的合成。

主要用途
  1. 农药:合成乙草胺丁草胺草甘膦等。
  2. 涂料:制备高档汽车用漆。
  3. 树脂:合成树脂树脂、聚缩醛树脂蜜胺树脂、离子交换树脂及其他粘合剂。
  4. 造纸:合成纸张增强剂。
  5. 铸造:作为翻砂脱膜剂和铸造粘合剂。
  6. 养殖业:用作熏蒸消毒剂。
  7. 有机原料:用于制备季戊四醇三羟甲基丙烷甘油丙烯酸及其衍生物等。
  8. 医药与消毒:作为制药工业的原材料和灭菌剂。
生产方法

聚甲醛通过将37%的甲醛在减压下蒸发,经催化缩合得到固体甲醛。此过程中需要过滤并用洗涤,最终通过真空干燥制成成品,含量一般为93-95%,每吨多聚甲醛消耗约3180kg的37%甲醛

安全与储存 性质
  • 较易燃固体
  • 中毒级别:中毒
  • 口服大鼠LD₅₀:800mg/kg
  • 皮肤刺激:兔子500mg/24小时重度刺激
燃烧特性

遇明火、高温或氧化剂可燃;燃烧时会产生刺激性烟雾。

储存与运输

应储存在通风良好、低温干燥的库房内,并与氧化剂分开存放。

灭火方法

可用清、泡沫灭火器、二氧化碳或干粉灭火器进行扑救。

上下游信息

  • 下游产品
    中文名称 英文名称 CAS号 化学式 分子量

反应信息

  • 作为反应物:
    描述:
    参考文献:
    名称:
    Pummerer et al., Chemische Berichte, 1942, vol. 75, p. 880
    摘要:
    DOI:
  • 作为产物:
    描述:
    zinc(II) formate 以 neat (no solvent) 为溶剂, 生成 聚合甲醛
    参考文献:
    名称:
    Hofmann, K. A.; Schibsted, H., Chemische Berichte, 1918, vol. 51, p. 1398 - 1418
    摘要:
    DOI:
  • 作为试剂:
    描述:
    ethyl 1-(1-(6-bromoquinazolin-4-yl)azetidine-3-yl)-2-oxopyrrolidine-3-carboxylate 在 聚合甲醛二甲胺 、 lithium hydroxide 作用下, 以 四氢呋喃甲醇乙酸乙酯 为溶剂, 反应 6.0h, 生成 1-(1-(6-bromoquinazolin-4-yl)azetidin-3-yl)-3-methylenepyrrolidin-2-one
    参考文献:
    名称:
    KR20240069725A
    摘要:
    公开号:
点击查看最新优质反应信息

文献信息

  • Stereoselective Synthesis of Medium-Sized Cyclic Ethers by Sequential Ring-Closing Metathesis and Tsuji–Trost Allylation
    作者:James Skardon-Duncan、Michael Sparenberg、Alexandre Bayle、Sam Alexander、J. Stephen Clark
    DOI:10.1021/acs.orglett.8b01082
    日期:2018.5.4
    Fully functionalized medium-sized cyclic ethers, of the type found in fused polyether natural products, have been prepared by sequential ring-closing diene metathesis, conversion of the resulting cyclic enone into an allylic enol carbonate, and Tsuji–Trost allylation using a chiral palladium complex. Very high levels of diastereocontrol, favoring the diastereomer in which there is a cis relationship
    通过顺序闭环二烯复分解,将所得环状烯酮转化为烯丙基烯醇碳酸酯,以及使用手性进行Tsuji-Trost烯丙基化反应,可以制备在融合的聚醚天然产物中发现的类型的完全功能化的中型环状醚。复杂的。在催化剂控制和催化反应的情况下,可以获得非常高的非对映异构控制平,有利于非对映异构体,其中在中环醚的C-2处的烯丙基与C-7 / C-8处的取代基之间存在顺式关系。底物对照是匹配的。
  • A Facile Synthesis of Hydroxamic Acids of<i>N<sup>α</sup></i>-Protected Amino Acids Employing BDMS, a Study of Their Molecular Docking and Their Antibacterial Activities
    作者:K. Uma、H. S. Lalithamba、V. Chandramohan、K. Lingaraju
    DOI:10.1080/00304948.2019.1579039
    日期:2019.3.4
    Hydroxamic acids have received much attention as biologically active compounds. Synthetic hydroxamic acids enhance the growth of plant sources and improve the soil quality, act as antibiotics, cell...
    异羟酸作为生物活性化合物受到了很多关注。合成异羟酸可促进植物来源的生长并改善土壤质量,作为抗生素、细胞...
  • Ammonia–dimethylchloramine system: Kinetic approach in an aqueous medium and comparison with the mechanism involving liquid ammonia
    作者:J. Stephan、V. Pasquet、M. Elkhatib、V. Goutelle、H. Delalu
    DOI:10.1002/kin.20312
    日期:2008.6
    medium. Dimethylchloramine prepared in a pure state undergoes dehydrohalogenation in an alkaline medium: the principal products formed are N-methylmethanimine, 1,3,5-trimethylhexahydrotriazine, formaldehyde, and methylamine. The kinetics of this reaction was studied by UV, GC, and HPLC as a function of temperature, initial concentrations of sodium hydroxide, and chlorinated derivative. The reaction is of
    在对液中的-二甲基氯胺系统进行了详尽的研究之后,比较该系统在液中的反应性与相同系统在性介质中的反应性是很有趣的。以纯态制备的二甲基氯胺在碱性介质中进行脱卤化氢:形成的主要产物是 N-甲基甲亚胺、1,3,5-三甲基六氢三嗪、甲醛甲胺。该反应的动力学通过 UV、GC 和 HPLC 作为温度、氢氧化钠初始浓度和化衍生物的函数进行了研究。该反应是二级反应,遵循 E2 机理(k1 = 4.2 × 10-5 M-1 s-1,ΔH○# = 82 kJ mol-1,ΔS○# = -59 J mol-1 K-1 )。二甲基氯胺氧化不对称二甲基涉及两个连续的过程。第一步遵循关于卤胺和的一级定律,导致形成基氮烯中间体 (k2 = 150 × 10-5 M-1 s-1)。第二步对应于在 pH 13) 下将基氮烯转化为甲醛二甲腙。该反应遵循一阶定律 (k3 = 23.5 × 10-5 s-1)。二甲基氯胺-相互作用对应于
  • PYRAZOLO[1,5a]PYRIMIDINE DERIVATIVES AS IRAK4 MODULATORS
    申请人:Arora Nidhi
    公开号:US20120015962A1
    公开(公告)日:2012-01-19
    Compounds of the formula I or II: wherein X, m, Ar, R 1 and R 2 are as defined herein. The subject compounds are useful for treatment of IRAK-mediated conditions.
    式I或II的化合物: 其中X,m,Ar,R1和R2如本文所定义。所述化合物对于治疗IRAK介导的疾病是有用的。
  • Compositions for Treatment of Cystic Fibrosis and Other Chronic Diseases
    申请人:Vertex Pharmaceuticals Incorporated
    公开号:US20150231142A1
    公开(公告)日:2015-08-20
    The present invention relates to pharmaceutical compositions comprising an inhibitor of epithelial sodium channel activity in combination with at least one ABC Transporter modulator compound of Formula A, Formula B, Formula C, or Formula D. The invention also relates to pharmaceutical formulations thereof, and to methods of using such compositions in the treatment of CFTR mediated diseases, particularly cystic fibrosis using the pharmaceutical combination compositions.
    本发明涉及含有上皮通道活性抑制剂与至少一种ABC转运蛋白调节剂化合物(A式、B式、C式或D式)的药物组合物。该发明还涉及这些药物配方,以及使用这些组合物治疗CFTR介导的疾病,特别是囊性纤维化的方法。
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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
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ir
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  • 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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