摩熵化学
数据库官网
小程序
打开微信扫一扫
首页 分子通 化学资讯 化学百科 反应查询 关于我们
请输入关键词

苯醚甲环唑 | 119446-68-3

中文名称
苯醚甲环唑
中文别名
恶醚唑;噁醚唑;世高;除虫脲;敌萎丹;顺,反-3-氯-4-[4-甲基-2-(1H-1,2,4-三唑-1-基甲基)-1,3-二噁戊烷-2-基]苯基4-氯苯基醚;顺,反3-氯-4-[4-甲基-2-(1H-1,2,4-三唑-1-基甲基)-1,3-二恶戊烷-2-基]苯基-4-氯苯基醚;二芬恶醚唑;顺,反-3-氯-4-[4-甲基-2-(1H-1,2,4-三唑-1-基甲基)-1,3-二氧戊烷-2-基]苯基4-氯苯基醚
英文名称
difenconazole
英文别名
Difenoconazole;difenoconazol;1-[2-[2-chloro-4-(4-chlorophenoxy)phenyl]-4-methyl-1,3-dioxolan-2-ylmethyl]-1H-1,2,4-triazole;3-chloro-4-[4-methyl-2-(1H-1,2,4-triazol-1-ylmethyl)-1,3-dioxolan-2-yl]phenyl 4-chlorophenyl ether;MMV688943;cis,trans-3-chloro-4-[4-methyl-2-(1H-1,2,4-triazol-1-ylmethyl)-1,3-dioxolan-2-yl]phenyl 4-chlorophenyl ether;(+/-)-4-chloro-4-[4-methyl-2-(1H-1,2,4-triazol-1-ylmethyl)-1,3-dioxolan-2-yl]phenyl 4-chlorophenyl ether;1-[[2-[2-chloro-4-(4-chlorophenoxy)phenyl]-4-methyl-1,3-dioxolan-2-yl]methyl]-1,2,4-triazole;difeconazole;Score
苯醚甲环唑化学式
CAS
119446-68-3
化学式
C19H17Cl2N3O3
mdl
MFCD00144119
分子量
406.268
InChiKey
BQYJATMQXGBDHF-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:
    76°C
  • 沸点:
    220°C
  • 密度:
    1.4916 (rough estimate)
  • 溶解度:
    氯仿:微溶,甲醇:微溶
  • LogP:
    4.300
  • 颜色/状态:
    White crystalline solid
  • 气味:
    Odorless
  • 蒸汽压力:
    2.5X10-10 mm Hg at 25 °C (3.3X10-5 mPa)
  • 分解:
    When heated to decomposition it emits toxic vapors of /nitrogen oxides/ and /chloride/.
  • 粘度:
    529 cP at 25 °C
  • 解离常数:
    pKa = 1.1 at 20 °C
  • 碰撞截面:
    198.48 Ų [M+H]+ [CCS Type: TW]
  • 保留指数:
    3136;3136;3136.2;3017;3019;2941.7;3025;3027;2954.1

计算性质

  • 辛醇/水分配系数(LogP):
    4
  • 重原子数:
    27
  • 可旋转键数:
    5
  • 环数:
    4.0
  • sp3杂化的碳原子比例:
    0.263
  • 拓扑面积:
    58.4
  • 氢给体数:
    0
  • 氢受体数:
    5

ADMET

代谢
代谢物从给予[(14)C-苯基]苯并环唑或[(14)C-三唑]苯并环唑单次口服剂量为0.5或300 mg/kg bw的雄性和雌性大鼠的尿液和粪便中分离出来,或者在预先用未标记的苯并环唑以0.5 mg/kg bw连续口服14剂后再给予0.5 mg/kg bw。苯基和三唑环标签的平衡数据显示,在所有情况下,超过97%的放射性标记物被排出,其中超过78%通过粪便排出。三种主要代谢物A、B和C从粪便中分离出来,平均占给药剂量的68%。代谢物B(羟基-CGA 169374)在外侧苯环上发生羟基化,光谱分析显示它包含两种异构体,其中一种在外侧苯环上的氯原子发生了重排,归因于类似于NIH位移的机制。代谢物C(CGA 205375)是二氧戊环环从苯并环唑分子断裂的羟基产物,仅在给予较高剂量的老鼠粪便中存在。代谢物A(羟基-CGA 205375)是代谢物C的外侧苯环羟基化产物,包含两种对映异构体,与代谢物B的描述相同。尿液代谢物的轮廓更为复杂,并且在两种放射性标记形式之间表现出更多的变异性。自由的1,2,4-三唑在雄性尿液中被发现,占给药剂量的不到10%,表示环系统之间的烷基桥断裂。其他尿液代谢物包括代谢物C,其硫酸结合物,环羟基化代谢物C及其硫酸结合物,以及氯苯氧基-氯苯基部分的羟基醋酸代谢物,它们都以微量存在,每种都代表给药剂量的不到3%。一种代谢物CGA 189138(氯苯氧基-氯苯甲酸)也从肝脏中分离出来。因此,苯并环唑分子被广泛代谢,尽管三唑和二氧戊环环的裂解有限。观察到的广泛胆汁排泄与主要代谢物具有相对较高的分子质量一致。
Metabolites were isolated from the urine and feces of male and female rats given [(14)C-phenyl] difenoconazole or [(14)C-triazole]difenoconazole as single oral dose at 0.5 or 300 mg/kg bw, or 0.5 mg/kg bw after pre-treatment with 14 daily oral doses of unlabelled difenoconazole at 0.5 mg/kg bw. Balance data for the phenyl and triazole ring labels ... showed that > 97% of the radiolabel in all cases was excreted with > 78% in all cases eliminated in the feces. Three main metabolites, A, B and C, were isolated from feces and together accounted for an average of 68% of the administered dose. Metabolite B (hydroxy-CGA 169374) was hydroxylated in the outer phenyl ring and spectral analysis showed that that it comprised two isomers, one with a rearrangement of the chlorine on the outer phenyl ring, attributed to a mechanism analogous to an NIH shift. Metabolite C (CGA 205375) was the hydroxyl product of cleavage of the dioxolane ring from the difenoconazole molecule and was present only in the feces of rats given the higher dose. Metabolite A (hydroxy-CGA 205375) was the outer phenyl-ring hydroxylated product of metabolite C and comprised two diastereoisomers, as described for metabolite B. The profile of urinary metabolites was more complex and showed more variability between the two radiolabelled forms. Free 1,2,4-triazole was identified in male urine, accounting for less than 10% of the administered dose and represented cleavage of the alkyl bridge between the ring systems. Other urinary metabolites included metabolite C, its sulfate conjugate, ring-hydroxylated metabolite C and its sulfate conjugate, as well as an hydroxyacetic acid metabolite of the chlorophenoxy-chlorophenyl moiety, all of which were present in minor quantities, each representing less than 3% of the administered dose. One metabolite CGA 189138 (chlorophenoxy-chlorobenzoic acid) was also isolated from the liver. The difenoconazole molecule was therefore extensively metabolized, although with limited cleavage of the triazole and dioxolane rings. The extensive biliary elimination observed was consistent with the major metabolites being of relatively high molecular mass.
来源:Hazardous Substances Data Bank (HSDB)
代谢
双苯恶唑啉在大鼠体内的主要代谢步骤推测涉及双苯恶唑啉中的缩酮水解,生成CGA 205375(1-[2-氯-4-(4-氯苯氧基)-苯基]-2-(1,2,4-三唑)-1-基-乙醇),以CGA 205374(1-(2-氯-4-(4-氯苯氧基)-苯基)-2-(1,2,4-三唑)-1-基-乙酮)为假设但未识别的中间体,并在母体(羟基-CGA 169374)和CGA 205375(羟基-CGA 205375)的外苯环上发生羟基化。作为一个次要过程,三唑和内苯环之间的烷基链断裂,导致羟基乙酸(NOA 448731)或CGA 189138(2-氯-4-(4-氯苯氧基)-苯甲酸)和自由三唑的形成。CGA 205375和羟基-CGA 205375的硫酸结合物被识别。
The major steps of the metabolism of difenoconazole in the rat were deduced to involve hydrolysis of the ketal in difenoconazole, resulting in CGA 205375 (1-[2-chloro-4-(4-chloro-phenoxy)-phenyl]-2- (1,2,4-triazol)-1-yl-ethanol), with the ketone CGA 205374 (1-(2-chloro-4-(4-chloro-phenoxy)-phenyl)- 2-(1,2,4-triazol)-1-yl-ethanone) as a postulated but not identified intermediate, and hydroxylation on the outer phenyl ring of the parent (hydroxy-CGA 169374) and in CGA 205375 (hydroxy-CGA 205375). As a minor process, cleavage of the alkyl chain between the triazole and the inner phenyl ring occurs, resulting in a hydroxyacetic acid (NOA 448731) or CGA 189138 (2-chloro-4-(4-chlorophenoxy)-benzoic acid) and free triazole. Sulfate conjugates were identified for CGA 205375 and for hydroxy-CGA 205375.
来源:Hazardous Substances Data Bank (HSDB)
代谢
杀真菌剂苯醚甲环唑(3-氯-4-[(2RS,4RS;2RS,4SR)-4-甲基-2-(1H-1,2,4-三唑-1-基甲基)-1,3-二氧戊环-2-基]苯基 4-氯苯基醚)在用于生产婴儿食品的苹果上的消散情况进行了研究。苹果(品种:乔纳金Decosta、嘎啦和Idared)被喷洒了该制剂以控制引起真菌病害的病原体:白粉病(Podosphaera leucotricha ELL et Ev./Salm.)和苹果黑星病(Venturia inaequalis Cooke/Aderh.)。使用了一种经过验证的基于气相色谱的同时电子捕获和氮磷检测(GC-ECD/NPD)的方法进行残留分析。该方法的分析性能非常令人满意,扩展不确定性为19%(覆盖因子k=2,置信水平为95%)。研究了苯醚甲环唑的消散情况,采用伪一级动力学模型(其中决定系数R2介于0.880和0.977之间)。在三种苹果品种的实验中,苯醚甲环唑的半衰期为12-21天。在这些实验中,初始残留水平逐渐下降,并在50-79天内达到0.01 mg/kg的水平。为了使残留水平保持在0.01 mg/kg以下(婴儿食品的最大可接受浓度),苯醚甲环唑必须在收获前大约3个月施用,剂量为0.2 L/ha(每公顷50克活性成分)。
Dissipation of fungicide difenoconazole (3-chloro-4-[(2RS,4RS;2RS,4SR)-4-methyl-2-(1H-1,2,4-triazol-1-ylmethyl)-1,3-dioxolan-2-yl]phenyl 4-chlorophenyl ether) was studied following its application on apples intended for production of baby food. The apples (varieties: Jonagold Decosta, Gala and Idared) were sprayed with the formulation to control pathogens causing fungal diseases: powdery mildew (Podosphaera leucotricha ELL et Ev./Salm.) and apple scab (Venturia inaequalis Cooke/Aderh.). A validated gas chromatography-based method with simultaneous electron capture and nitrogen phosphorus detection (GC-ECD/NPD) was used for the residue analysis. The analytical performance of the method was highly satisfactory, with expanded uncertainties 19% (a coverage factor, k = 2, and a confidence level of 95%). The dissipation of difenoconazole was studied in pseudo-first-order kinetic models (for which the coefficients of determination, R2, ranged between 0.880 and 0.977). The half-life of difenoconazole was 12-21 days in experiments conducted on three apple varieties. In these experiments, the initial residue levels declined gradually and reached the level of 0.01 mg/kg in 50-79 days. For the residue levels to remain below 0.01 mg/kg (the maximum acceptable concentration for baby foods), difenoconazole must be applied approximately 3 months before harvest, at a dose of 0.2 L/ha (50 g of an active ingredient per ha).
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 毒性总结
识别和使用:联苯肼是一种白色结晶固体。它被用作杀真菌剂、杀虫剂、种子处理/保护剂。人类暴露和毒性:如果吸入或通过皮肤吸收,有害。对眼睛有中度刺激作用。在人类淋巴细胞中未引起染色体畸变。报告了一起对配方产品过敏反应的案例。动物研究:联苯肼对家兔眼睛有中度和暂时性刺激作用。对家兔皮肤有非常轻微和暂时性刺激作用。当在闭合条件下应用于完整家兔皮肤时,联苯肼被认为基本上是无毒的。在大鼠连续皮肤给药28天的情况下,雄性和雌性在1000 mg/kg体重剂量下出现了最小中央小叶肝细胞肥大的增加。在大鼠的甲状腺中,1000 mg/kg体重剂量组中的滤泡上皮肥大最小到中度的严重程度略有增加。肝脏似乎是毒性的靶器官。在大鼠中没有致癌性或致癌性的证据。在兔子的剂量达到每天75 mg/kg体重时,没有出现胚胎毒性、胎儿毒性或致畸性的迹象。在大鼠的剂量达到200 mg/kg体重时,也没有出现胚胎毒性或致畸性的迹象。对大鼠的中枢和周围神经系统进行显微镜检查,在雄性或雌性的饮食浓度高达1500 ppm时,没有发现联苯肼处理的效果。联苯肼在细菌细胞或培养的哺乳动物细胞中未诱导基因突变。生态毒性研究:在斑马鱼实验中,不同剂量的联苯肼在胚胎发育期间引起了一大套症状,包括孵化抑制、异常自发运动、心率缓慢、生长退化和形态畸形。暴露于联苯肼可能会改变斑马鱼幼体的甲状腺激素水平和基因转录,表明内分泌干扰。与孵化、维甲酸代谢和脂质稳态相关的基因在斑马鱼胚胎中被联苯肼上调。联苯肼暴露还可能改变海洋青鳉(Oryzias melastigma)的脂质代谢和脂质谱。联苯肼抑制了大黄蜂飞行肌肉线粒体的呼吸。
IDENTIFICATION AND USE: Difenoconazole is a white crystalline solid. It is used as fungicide, insecticide, seed treatment/protectant. HUMAN EXPOSURE AND TOXICITY: Harmful if inhaled or absorbed through skin. Causes moderate eye irritation. It did not cause chromosomal aberrations in human lymphocytes. One case of allergic reaction to a formulated product was reported. ANIMAL STUDIES: Difenoconazole was moderately and transiently irritating to the eyes of rabbits. It was very slightly and transiently irritating to the skin of rabbits. Difenoconazole was considered to be essentially non-toxic when applied topically under occlusion to intact rabbit skin. In rats treated dermally for 28 days there was an increased incidence of minimal centrilobular hepatocellular hypertrophy in males and females at 1000 mg/kg bw. In the thyroid, the incidence of minimal to moderate severity grades of hypertrophy of the follicular epithelium was slightly increased in the group of rats at 1000 mg/kg bw. The liver appeared to be the target organ for toxicity. There was no evidence for carcinogenicity or oncogenicity in rats. There were no indications of embryotoxicity, fetotoxicity or teratogenicity at a dose up to 75 mg/kg bw per day in rabbits. There were no indications of embryotoxicity or teratogenicity at any dose up to 200 mg/kg bw in rats. Microscopic examination of the central and peripheral nervous system of rats showed no effects of treatment with difenoconazole at dietary concentrations of up to 1500 ppm in males or females. Difenoconazole did not induce gene mutations in either bacterial cells or cultured mammalian cells. ECOTOXICITY STUDIES: In zebrafish experiments, a large suite of symptoms was induced in embryonic development by different dosages of difenoconazole, including hatching inhibition, abnormal spontaneous movement, slow heart rate, growth regression and morphological deformities. Exposure to difenoconazole could alter thyroid hormone levels and gene transcription in zebrafish larvae, indicating endocrine disruption. Genes related to hatching, retinoic acid metabolism and lipid homeostasis were up-regulated by difenoconazole in zebrafish embryos. Difenoconazole exposure could also change lipid metabolism and profiles in marine medaka (Oryzias melastigma). Difenoconazole inhibited the respiration of mitochondria of the flight muscles of bumblebee.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌物分类
对人类无致癌性(未列入国际癌症研究机构IARC清单)。
No indication of carcinogenicity to humans (not listed by IARC).
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 解毒与急救
/SRP:/ 立即急救:确保已经进行了充分的中和。如果患者停止呼吸,请开始人工呼吸,最好使用需求阀复苏器、球囊阀面罩设备或口袋面罩,按训练操作。如有必要,执行心肺复苏。立即用缓慢流动的水冲洗受污染的眼睛。不要催吐。如果患者呕吐,让患者向前倾或将其置于左侧(如果可能的话,头部向下),以保持呼吸道畅通,防止吸入。保持患者安静,维持正常体温。寻求医疗帮助。 /毒物A和B/
/SRP:/ Immediate first aid: Ensure that adequate decontamination has been carried out. If patient is not breathing, start artificial respiration, preferably with a demand valve resuscitator, bag-valve-mask device, or pocket mask, as trained. Perform CPR if necessary. Immediately flush contaminated eyes with gently flowing water. Do not induce vomiting. If vomiting occurs, lean patient forward or place on the left side (head-down position, if possible) to maintain an open airway and prevent aspiration. Keep patient quiet and maintain normal body temperature. Obtain medical attention. /Poisons A and B/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 解毒与急救
/SRP:/ 基本治疗:建立专利气道(如有需要,使用口咽或鼻咽气道)。如有必要,进行吸痰。观察呼吸不足的迹象,如有需要,辅助通气。通过非循环呼吸面罩以10至15升/分钟的速度给予氧气。监测肺水肿,如有必要,进行治疗……。监测休克,如有必要,进行治疗……。预防癫痫发作,如有必要,进行治疗……。对于眼睛污染,立即用水冲洗眼睛。在运输过程中,用0.9%的生理盐水(NS)持续冲洗每只眼睛……。不要使用催吐剂。对于摄入,如果患者能吞咽、有强烈的干呕反射且不流口水,则用温水冲洗口腔,并给予5毫升/千克,最多200毫升的水进行稀释……。在去污后,用干燥的无菌敷料覆盖皮肤烧伤……。/毒药A和B/
/SRP:/ Basic treatment: Establish a patent airway (oropharyngeal or nasopharyngeal airway, if needed). Suction if necessary. Watch for signs of respiratory insufficiency and assist ventilations if needed. Administer oxygen by nonrebreather mask at 10 to 15 L/min. Monitor for pulmonary edema and treat if necessary ... . Monitor for shock and treat if necessary ... . Anticipate seizures and treat if necessary ... . For eye contamination, flush eyes immediately with water. Irrigate each eye continuously with 0.9% saline (NS) during transport ... . Do not use emetics. For ingestion, rinse mouth and administer 5 mL/kg up to 200 mL of water for dilution if the patient can swallow, has a strong gag reflex, and does not drool ... . Cover skin burns with dry sterile dressings after decontamination ... . /Poisons A and B/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 解毒与急救
/SRP:/ 高级治疗:对于昏迷、严重肺水肿或严重呼吸困难的病人,考虑进行口咽或鼻咽气管插管以控制气道。使用气囊面罩装置的正压通气技术可能有益。考虑使用药物治疗肺水肿……。对于严重的支气管痉挛,考虑给予β激动剂,如沙丁胺醇……。监测心率和必要时治疗心律失常……。开始静脉输注D5W TKO /SRP: "保持开放",最低流量/。如果出现低血容量的迹象,使用0.9%生理盐水(NS)或乳酸钠林格氏液(LR)。对于伴有低血容量迹象的低血压,谨慎给予液体。注意液体过载的迹象……。用地西泮或劳拉西泮治疗癫痫……。使用丙美卡因氢氯化物协助眼部冲洗……。/毒物A和B/
/SRP:/ Advanced treatment: Consider orotracheal or nasotracheal intubation for airway control in the patient who is unconscious, has severe pulmonary edema, or is in severe respiratory distress. Positive-pressure ventilation techniques with a bag valve mask device may be beneficial. Consider drug therapy for pulmonary edema ... . Consider administering a beta agonist such as albuterol for severe bronchospasm ... . Monitor cardiac rhythm and treat arrhythmias as necessary ... . Start IV administration of D5W TKO /SRP: "To keep open", minimal flow rate/. Use 0.9% saline (NS) or lactated Ringer's (LR) if signs of hypovolemia are present. For hypotension with signs of hypovolemia, administer fluid cautiously. Watch for signs of fluid overload ... . Treat seizures with diazepam or lorazepam ... . Use proparacaine hydrochloride to assist eye irrigation ... . /Poisons A and B/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
单次口服剂量为0.5 mg/kg体重的[(14)C-苯基]戊唑醇在雄性和雌性大鼠中迅速且几乎完全被吸收。单次口服剂量为300 mg/kg体重的[(14)C-苯基]戊唑醇吸收程度较低,因为胆管插管的雄性和雌性大鼠分别有17%和22%的剂量通过粪便排出。最大血药浓度在2小时内达到,随后对于较低剂量迅速下降,而对于较高剂量在大约4小时后,血药浓度先是缓慢下降,直到24小时,此后下降速率与较低剂量相似。在雌性中,较低剂量和较高剂量之间的血药浓度-时间曲线下面积(AUC)测量值的差异与剂量差异相符,而在雄性中AUC的差异是400倍。系统剂量主要通过胆汁消除,其中雄性占给药剂量的73%,雌性占76%。胆管插管的大鼠通过尿液排出的比例在雄性中占14%,在雌性中占9%,粪便排出量不到剂量的4%,从而证实了在较低剂量下几乎完全吸收。当将0.5 mg/kg体重的雄性大鼠胆汁管注入其他胆管插管的大鼠时,80%的剂量通过胆汁再次排出,仅有4%通过尿液,从而证明了肠肝循环。在300 mg/kg体重时,胆汁也是主要的消除途径,在雄性中占给药剂量的56%,在雌性中占39%,而尿液排出的比例仅占剂量的1%。在未插管的雄性和雌性大鼠中单次口服[(14)C-苯基]戊唑醇或[(14)C-三唑]戊唑醇0.5 mg/kg体重,13-22%的给药剂量通过尿液排出,81-87%通过粪便排出。在未插管的雄性和雌性大鼠中单次口服[(14)C-苯基]戊唑醇或[(14)C-三唑]戊唑醇300 mg/kg体重,8-15%的给药剂量通过尿液排出,85-95%通过粪便排出。在两种性别之间或两种放射性标记形式之间在任一剂量下排泄概况没有显著差异。当给予类似剂量的[(14)C-苯基]戊唑醇或[(14)C-三唑]戊唑醇给预先用0.5 mg/kg体重未标记戊唑醇连续口服14天的大鼠时,与没有预处理的大鼠相比,排泄概况在性别上没有差异,也没有明显差异。0.5 mg/kg体重的大鼠排泄数据显示,虽然存在肠肝循环,但胆汁代谢物主要在粪便中排出。在较低剂量下,排泄的半衰期大约为20小时。在300 mg/kg体重时,未插管的大鼠通过尿液排出的给药剂量比胆管插管的大鼠多,这显然是在重新吸收和进一步代谢一些胆汁代谢物之后;然而,胆汁放射性的主要排泄途径再次是在粪便中,如较低剂量时观察到的那样。在较高剂量下,排泄的半衰期大约为33-48小时。因此,在两种剂量下,消除动力学都与性别和放射性标记位置无关。
A single oral dose of [(14)C-phenyl]difenoconazole at 0.5 mg/kg bw was rapidly and almost completely absorbed by male and female rats. A single oral dose of [(14)C-phenyl]difenoconazole at 300 mg/kg bw was less extensively absorbed since bile-duct cannulated male and female rats excreted 17% and 22%, respectively, of the dose in feces. Maximum blood concentrations were reached within 2 hr, followed by a rapid decline for the lower dose and after approximately 4 hr, with an initial slow decline up to 24 hr, for the higher dose, after which the rate of decline was similar to the lower dose. In females the difference in area under the blood concentration-time curve (AUC) measurements between the lower and higher doses matched the dose differential, while in males the AUC differential was 400-fold. The systemic dose was eliminated predominantly via bile where it accounted for 73% of the administered dose (0.5 mg/kg bw) in males and 76% in females. Urinary excretion by bile-duct cannulated rats accounted for 14% of the administered dose in males and 9% in females, with fecal excretion representing less than 4% of the dose and thereby confirming the almost complete absorption at the lower dose. When bile from male rats at 0.5 mg/kg bw was administered intraduodenally to other bile duct cannulated rats, 80% of the dose was re-eliminated via the bile and just 4% in the urine, thereby demonstrating enterohepatic recirculation. Bile was also the major route of elimination at 300 mg/kg bw, accounting for 56% of the administered dose in males and 39% in females, while urinary excretion represented only 1% of the dose. In non-cannulated male and female rats given a single oral dose of [(14)C-phenyl] difenoconazole or [(14)C-triazole]difenoconazole at 0.5 mg/kg bw, 13-22% of the administered dose was excreted in the urine and 81-87% in the feces. In non-cannulated male and female rats given a single oral dose of [(14)C-phenyl]difenoconazole or [(14)C-triazole]difenoconazole at 300 mg/kg bw, 8-15% of the administered dose was excreted in the urine and 85-95% in the feces. There was no pronounced difference in excretion profiles, either between the sexes or between the two radiolabelled forms at either dose. When a similar dose of [(14)C-phenyl]difenoconazole or [(14)C-triazole]difenoconazole was given to rats pre-treated with 14 daily oral doses of unlabelled difenoconazole at 0.5 mg/kg bw, there was neither a sex difference nor any marked difference in excretion profiles from the rats with no pre-treatment. The excretion data for rats at 0.5 mg/kg bw showed that while enterohepatic recirculation was evident, biliary metabolites were largely excreted in the feces. At the lower dose, the half-life of excretion was approximately 20 hr. At 300 mg/kg bw, more of the administered dose was excreted in the urine by noncannulated rats than by bile-duct cannulated rats, apparently after reabsorption and further metabolism of some biliary metabolites; however, the predominant route of excretion of biliary radioactivity was again in feces, as observed at the lower dose. At the higher dose, the half-life of excretion was approximately 33-48 hr. At both doses, elimination kinetics were thus independent of sex and radiolabel position.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
血液中的放射性同位素浓度在大鼠口服0.5 mg/kg bw后2小时达到最大浓度(Cmax),之后迅速下降。给药后168小时内的AUC为6.19 ug等效/小时每毫升。女性的Tmax比男性短,女性的Cmax和AUC仅达到男性的约50%。雌性大鼠中放射性同位素的消失速度略快于雄性大鼠。组织耗竭结果显示,在给予0.5 mg/kg bw的[(14)C-phenyl]difenoconazole后2小时和24小时,只有肝脏和肾脏中的浓度在两性中均持续高于血浆。在类似剂量的雄性大鼠的整体放射性自显影切片中也观察到了一致的结果,因为在给药后2小时和24小时,大部分放射性同位素存在于胃肠道内容和胆汁中,肝脏和肾脏中的浓度较低。最初浓度高于血浆的其他组织包括两性的肾上腺和雌性的哈德氏腺和脂肪组织;然而,这些浓度迅速下降。168小时后,组织中的[(14)C-phenyl]difenoconazole残留物非常低,只有脂肪组织的浓度与血浆中的相当,而所有组织中的[(14)C-triazole]difenoconazole残留物要么低于检测限,要么低于定量限。对于两种放射性标记形式的difenoconazole,女性组织中的残留物也倾向于略低于男性,并且预先用未标记的测试物质处理对组织分布没有影响。
The concentration of radiolabel in the blood reached a maximum concentration (Cmax) at 2 hr after oral administration in male rats at 0.5 mg/kg bw and declined rapidly thereafter. The AUC up to 168 hr after administration was 6.19 ug equivalent/hr per mL. Tmax was shorter in females than in males and Cmax and AUC in females reached only about 50% of the respective values in males. The disappearance of radioactivity in female rats was slightly faster than in male rats. Tissue depletion results showed that at 2 hr and 24 hr after a dose of [(14)C-phenyl]difenoconazole at 0.5 mg/kg bw, only in the liver and kidney were concentrations consistently higher than those in plasma for both sexes. Consistent results were observed in whole-body autoradiography sections of similarly-dosed male rats, since at 2 hr and 24 hr after dosing most of the radioactivity was present in the gastrointestinal tract contents and in bile, with lower concentrations in the liver and kidneys. Other tissues with concentrations initially higher than in plasma were adrenal glands in both sexes and Harderian glands and adipose tissue in females; however, these concentrations declined rapidly. After 168 hr, [(14)C-phenyl]difenoconazole residues in tissue were very low, with only fat showing concentrations comparable to those present in plasma, while all tissue residues of [(14)C-triazole]difenoconazole were either below the limit of detection or below the limit of quantification. For both radiolabelled forms of difenoconazole, residues in female tissues also tended to be slightly lower than those in males and pre-treatment with unlabelled test substance had no effect on tissue distribution.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
组织耗竭结果显示,在给予300 mg/kg bw剂量的[(14)C-苯基]苯并康唑后4小时,大多数组织的浓度与血浆中相似或更高,男女皆然。在男女双方中,脂肪中的组织浓度最高,其次是肝脏、哈德氏腺、肾上腺、肾脏和胰腺的浓度逐渐降低。在所有其他最初浓度高于血浆的组织中,浓度在给药后48小时内迅速下降,到168小时时,所有组织中[(14)C-苯基]苯并康唑的残留物都显著下降,只有脂肪显示的残留物高于血浆。[(14)C-三唑]苯并康唑的组织残留物显著低于[(14)C-苯基]苯并康唑的残留物,到168小时时仅在肝脏中可测量。对胃肠道内容物的测量结果与观察到的吸收和消除轮廓一致。
Tissue depletion results showed that at 4 hr after a dose of [(14)C-phenyl]difenoconazole at 300 mg/kg bw, most tissue concentrations were similar to or higher than those in plasma in both sexes. The highest tissue concentrations were present in fat in both sexes, with progressively lower concentrations in the liver, Harderian glands, adrenal glands, kidney and pancreas. In all other tissues that initially showed concentrations higher than those in plasma concentrations declined rapidly by 48 hr after dosing and by 168 hr all tissue residues of [(14)C-phenyl] difenoconazole had declined markedly, only fat showing residues that were higher than in plasma. Tissue residues of [(14)C-triazole]difenoconazole were significantly lower than those of [(14)C-phenyl]difenoconazole residues and by 168 hr were measurable only in the liver. Measurements in the contents of the gastrointestinal tract were consistent with the observed absorption and elimination profiles.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
在14天内,每天以0.5毫克/公斤体重的剂量给予[4-氯苯氧基-U-(14)C]苯醚甲环唑后,吸收的放射性标记物会迅速且几乎完全排出,主要通过粪便。在最后一次给药后的24小时内,超过90%的总给药放射性标记物被排出,7天内回收了总放射性标记物的98.5%。此时,不到0.5%的给药剂量残留在组织和尸体中。尿液和粪便中的代谢物轮廓在每个时间点在质上相似,尽管在单次和多次口服给药后观察到了小的定量差异。在7天后,大多数组织中的放射性残留物浓度达到稳定水平。随着持续给药,肝脏、肾脏、脂肪和胰腺中的残留物浓度增加,在给药期间没有达到稳定水平;然而,估计残留物浓度将在3周内达到稳定水平。组织中的放射性残留物排出速度适中。假设组织中的放射性标记物排出为一阶动力学和单相排出动力学,半衰期通常在4-6天。在肝脏、肾脏和胰腺中排出更快,半衰期为1-3天,在脂肪中较慢,半衰期为9天。用特定位置放射性标记化合物的实验表明,三唑标记在肝脏中浓度最高,而苯基标记在脂肪和血浆中浓度最高。三唑标记化合物的残留物显著低于苯基标记化合物。雌性动物的组织残留物略低于雄性。用未标记的苯醚甲环唑进行多次预处理对组织分布没有影响。
After 14 days of [4-chloro-phenoxy-U-(14)C]difenoconazole at a dose of at 0.5 mg/kg bw per day, the absorbed radiolabel was rapidly and almost completely excreted, predominantly via the feces. More than 90% of the total administered radiolabel was excreted within 24 hr after the last dose and 98.5% of the total radiolabel was recovered within 7 days. At that time, less than 0.5% of the administered dose remained in the tissues and carcass. Metabolite profiles in the urine and feces were qualitatively similar at each time-point, although small quantitative differences were observed after the administration of single and multiple oral doses. Concentrations of radioactive residues reached a plateau in most tissues after 7 days. Residue concentrations increased with continued dosing in liver, kidneys, fat and pancreas and did not reach a plateau during the dosing period; however, it was estimated that residue concentrations would reach a plateau within 3 weeks. The depletion of radioactive residues from tissues was moderately fast. Assuming first-order kinetics and monophasic depletion kinetics for the depuration of radiolabel from tissues, the half-lives ranged typically from 4-6 days. Depletion was more rapid in the liver, kidneys and pancreas, with half-lives of 1-3 days, and slower in fat, with a half-life of 9 days. Experiments with position-specific radiolabelled compounds demonstrated that the highest tissue concentrations were found in the liver for the triazole label, and in fat and plasma for the phenyl label. Residues from the triazole-labelled compound were significantly less than those from the phenyl-labelled compound. Tissue residues in females were slightly less than in males. Multiple pre-treatment with unlabelled difenoconazole had no effect on tissue distribution.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
对大鼠进行皮肤给药的 difenoconazole 的体内研究和在大鼠及人体皮肤体外进行的研究使用了非放射性标记的 difenoconazole(纯度99.3%)和 [triazole-U-(14)C]difenoconazole。在单次皮肤给药 (14)C-标记的 difenoconazole 混合非标记的 difenoconazole 制成的 SCORE 250 EC 后,研究了雄性 HanBrlWIST(SPF)大鼠体内放射性物质的吸收、分布和排泄。在最高剂量下,特定活性为 54 kBq/mg (1.5 uCi/mg)。对于最高剂量,difenoconazole 在空白制剂中的浓度为 250 g/L,代表未稀释的产品。对于中间和最低剂量,这种配制的材料分别与水按 1:200 (w/v) 和 1:5000 (w/v) 的比例混合。应用的标称剂量分别为 0.5、13 和 2600 ug/sq cm,并保持 6 小时。在另一个实验中,重复了最高剂量的皮肤吸收测定,应用剂量为 2400 ug/sq cm。... 在最低、中间和最高剂量下,6 小时内的系统吸收率分别为 15.3%、7.5% 和 7.1%,渗透率分别为 0.013、0.162 和 30.4 ug/sq cm/小时。这些渗透率的比率,即 1:12:2400,与应用浓度成正比,即 1:26:5100。然而,数据中有很大的变化,这归因于配方载体 SCORE 250 EC 的刺激性;这导致皮肤吸收的个别值范围很广,达到施用剂量的 45%。对于大鼠体内的研究,在最坏的情况下,最低、中间和最高剂量的平均皮肤吸收值分别为 37.6%、14.6% 和 10.6%。尽管如此,血液中的残留物浓度通常非常低:中间和最高剂量在应用后 6-8 小时,最高浓度(以 difenoconazole 当量计)分别为 0.01 ug/mL 和 0.26 ug/mL。在剥离皮肤角质层后,通过体外暴露于浓度为 0.05、1.28 或 250 mg/mL 的 difenoconazole 24 小时,测定了非放射性标记的 difenoconazole(纯度 99.3%)和 [triazole-U-14C]difenoconazole 通过孤立的大鼠和人体表皮膜制备的渗透。... 在 24 小时内,最低、中间和最高浓度下渗透膜的放射性比例分别为大鼠皮肤的 71%、64% 和 23%,人体皮肤的 7.6%、7.0% 和 0.7%。尽管用人皮肤进行的体外研究指出,在最低浓度下皮肤吸收率大约为 8%(7.6%),但如果将皮肤中保留的量视为潜在可吸收的,则增加至 15%。然而,大鼠和人体皮肤体外比较研究的主要目的是评估实际吸收百分比的差异,从而估计适当的物种比率。在最低、中间和最高浓度下,大鼠皮肤的通量(即在稳态条件下的渗透率)分别为 0.020、0.455 和 26.0 ug/sq cm/小时,人体皮肤的通量分别为 0.002、0.037 和 0.82 ug/sq cm/小时。因此,大鼠:人体的通量比率大约为 1:10、1:12 和 1:32。比较不同剂量下的渗透率(浓度比率为 1:25:5000),大鼠表皮膜的渗透率增加了 1:23:1300,而人体表皮膜的渗透率仅显示出 1:24:500 的比率。
Studies of dermal penetration in rats given difenoconazole as an application to the skin in vivo and studies with rat and human skin in vitro were conducted using non-radiolabelled difenoconazole (purity, 99.3%) and [triazole-U-(14)C]difenoconazole. The absorption, distribution and excretion of radioactivity was studied in male HanBrlWIST (SPF) rats after a single dermal administration of (14)C-labelled difenoconazole mixed with the nonlabelled difenoconazole formulated as SCORE 250 EC. At the highest dose, the specific activity was 54 kBq/mg (1.5 uCi/mg). For the highest dose, difenoconazole was dissolved in blank formulation at a concentration of 250 g/L, representing the undiluted product. For the intermediate and lowest dose, this formulated material was mixed with water in a ratio of 1:200 (w/v) and 1:5000 (w/v), respectively. The applied nominal doses were 0.5, 13 and 2600 ug/sq cm and these were left in place for 6 hr. The determination of dermal absorption at the highest dose was repeated in a separate experiment, using an application of 2400 ug/sq cm. ... At the lowest, intermediate and highest doses, respectively, systemic absorption within 6 hr was 15.3%, 7.5% and 7.1% and the penetration rates was 0.013, 0.162 and 30.4 ug/sq cm per hr. The ratios of these penetration rates, i.e. 1:12:2400 were proportional to the application concentrations, i.e. 1:26:5100. There was, however, a substantial variation in the data that was attributed to the irritancy of the formulation vehicle, SCORE 250 EC; this resulted in a broad range of individual values for dermal absorption of up to 45% of the administered dose. For the study in rats in vivo, in a worst-case scenario the mean dermal absorption values at the lowest intermediate and highest doses, respectively, were 37.6%, 14.6% and 10.6%. Nevertheless, concentrations of residues in the blood were generally very low: the highest concentrations (as difenoconazole equivalents) were 0.01 ug/mL and 0.26 ug/mL at the intermediate and highest doses, respectively, 6-8 hr after appliciation. The penetration of non-radiolabelled difenoconazole (purity, 99.3%) and [triazole-U-14C] difenoconazole through isolated rat and human epidermal membrane preparations in vitro after stripping the stratum corneum from skin was determined after an exposure of 24 hr to difenoconazole at a concentration of 0.05, 1.28 or 250 mg/mL, achieving applications of 0.5, 12 or 2345 ug/sq cm. ... Within 24 hr, the proportions of radiolabel penetrating the membranes at the lowest, intermediate and highest concentrations, respectively, were 71%, 64% and 23% for the preparations of rat skin and 7.6%, 7.0% and 0.7% for the preparations of human skin. Although the studies with human skin in vitro indicated that dermal absorption was approximately 8% (7.6%) for the lowest concentration, if the amount retained in skin is considered as potentially absorbable it increases to 15%. However, the main objective of the comparative studies of rat and human skin in vitro was to evaluate the differences in the percentage actually absorbed, permitting the estimation of an appropriate species ratio. The flux (i.e. rate of penetration under steady-state conditions) at the lowest, intermediate and highest concentrations, respectively, was 0.020, 0.455 and 26.0 ug/sq cm/hr for the rat skin and 0.002, 0.037 and 0.82 ug/sq cm/hr for the human skin. The flux ratios rat:human were therefore about 1:10, 1:12 and 1:32 at the lowest, intermediate and highest concentrations, respectively. Comparison of the penetration rates at the different doses (concentration ratio, 1:25:5000), revealed an increase in the penetration rates of 1:23:1300 for rat epidermal membranes, while the penetration rates for human epidermal membranes revealed a ratio of only 1:24:500.
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • 危险品标志:
    Xn
  • 安全说明:
    S26,S36/37/39
  • 危险类别码:
    R22,R41,R43
  • WGK Germany:
    3
  • 危险品运输编号:
    UN 3077 9 / PGIII
  • RTECS号:
    XZ4380000
  • 储存条件:
    0-6°C

SDS

SDS:09346eb69fc7fb863f7e2e3b42a2e1b7
查看

模块 1. 化学品
1.1 产品标识符
: 苯醚甲环唑
产品名称
1.2 鉴别的其他方法
无数据资料
1.3 有关的确定了的物质或混合物的用途和建议不适合的用途
仅用于研发。不作为药品、家庭或其它用途。

模块 2. 危险性概述
2.1 GHS-分类
急性毒性, 经口 (类别 4)
急性毒性, 吸入 (类别 4)
急性毒性, 经皮 (类别 5)
皮肤刺激 (类别 3)
急性水生毒性 (类别 1)
慢性水生毒性 (类别 1)
2.2 GHS 标记要素,包括预防性的陈述
象形图
警示词 警告
危险申明
H302 + H332 如果咽下或吸入是有害的。
H313 接触皮肤可能有害。
H316 引起轻微皮肤刺激。
H410 对水生生物毒性极大并具有长期持续影响.
警告申明
预防措施
P261 避免吸入粉尘/烟/气体/烟雾/蒸气/喷雾.
P264 操作后彻底清洁皮肤。
P270 使用本产品时不要进食、饮水或吸烟。
P271 只能在室外或通风良好之处使用。
P273 避免释放到环境中。
事故响应
P301 + P312 如果吞咽并觉不适: 立即呼叫解毒中心或就医。
P304 + P340 如果吸入:将受害人移至空气新鲜处并保持呼吸舒适的姿势休息。
P312 如感觉不适,呼救中毒控制中心或医生.
P330 漱口。
P391 收集溢出物。
废弃处置
P501 将内容物/ 容器处理到得到批准的废物处理厂。
当心 - 物质尚未完全测试。
2.3 其它危害物 - 无

模块 3. 成分/组成信息
3.1 物 质
: C19H17Cl2N3O3
分子式
: 406.26 g/mol
分子量
组分 浓度或浓度范围
Difenoconazole
<=100%
化学文摘登记号(CAS 119446-68-3
No.)

模块 4. 急救措施
4.1 必要的急救措施描述
一般的建议
请教医生。 向到现场的医生出示此安全技术说明书。
吸入
如果吸入,请将患者移到新鲜空气处。 如呼吸停止,进行人工呼吸。 请教医生。
皮肤接触
用肥皂和大量的水冲洗。 请教医生。
眼睛接触
用水冲洗眼睛作为预防措施。
食入
切勿给失去知觉者通过口喂任何东西。 用水漱口。 请教医生。
4.2 主要症状和影响,急性和迟发效应
4.3 及时的医疗处理和所需的特殊处理的说明和指示
无数据资料

模块 5. 消防措施
5.1 灭火介质
灭火方法及灭火剂
用水雾,抗乙醇泡沫,干粉或二氧化碳灭火。
5.2 源于此物质或混合物的特别的危害
碳氧化物, 氮氧化物, 氯化氢气体
5.3 给消防员的建议
如必要的话,戴自给式呼吸器去救火。
5.4 进一步信息
无数据资料

模块 6. 泄露应急处理
6.1 作业人员防护措施、防护装备和应急处置程序
使用个人防护用品。 避免粉尘生成。 避免吸入蒸气、烟雾或气体。 保证充分的通风。 避免吸入粉尘。
6.2 环境保护措施
如能确保安全,可采取措施防止进一步的泄漏或溢出。 不要让产品进入下水道。
一定要避免排放到周围环境中。
6.3 泄漏化学品的收容、清除方法及所使用的处置材料
收集和处置时不要产生粉尘。 扫掉和铲掉。 放入合适的封闭的容器中待处理。
6.4 参考其他部分
丢弃处理请参阅第13节。

模块 7. 操作处置与储存
7.1 安全操作的注意事项
避免接触皮肤和眼睛。 避免形成粉尘和气溶胶。
在有粉尘生成的地方,提供合适的排风设备。
7.2 安全储存的条件,包括任何不兼容性
贮存在阴凉处。 使容器保持密闭,储存在干燥通风处。
7.3 特定用途
无数据资料

模块 8. 接触控制和个体防护
8.1 容许浓度
最高容许浓度
没有已知的国家规定的暴露极限。
8.2 暴露控制
适当的技术控制
根据良好的工业卫生和安全规范进行操作。 休息前和工作结束时洗手。
个体防护设备
眼/面保护
带有防护边罩的安全眼镜符合 EN166要求请使用经官方标准如NIOSH (美国) 或 EN 166(欧盟)
检测与批准的设备防护眼部。
皮肤保护
戴手套取 手套在使用前必须受检查。
请使用合适的方法脱除手套(不要接触手套外部表面),避免任何皮肤部位接触此产品.
使用后请将被污染过的手套根据相关法律法规和有效的实验室规章程序谨慎处理. 请清洗并吹干双手
所选择的保护手套必须符合EU的89/686/EEC规定和从它衍生出来的EN 376标准。
完全接触
物料: 丁腈橡胶
最小的层厚度 0.11 mm
溶剂渗透时间: 480 min
测试过的物质Dermatril® (KCL 740 / Z677272, 规格 M)
飞溅保护
物料: 丁腈橡胶
最小的层厚度 0.11 mm
溶剂渗透时间: 480 min
测试过的物质Dermatril® (KCL 740 / Z677272, 规格 M)
, 测试方法 EN374
如果以溶剂形式应用或与其它物质混合应用,或在不同于EN
374规定的条件下应用,请与EC批准的手套的供应商联系。
这个推荐只是建议性的,并且务必让熟悉我们客户计划使用的特定情况的工业卫生学专家评估确认才可.
这不应该解释为在提供对任何特定使用情况方法的批准.
身体保护
全套防化学试剂工作服, 防护设备的类型必须根据特定工作场所中的危险物的浓度和数量来选择。
呼吸系统防护
如须暴露于有害环境中,请使用P95型(美国)或P1型(欧盟 英国
143)防微粒呼吸器。如需更高级别防护,请使用OV/AG/P99型(美国)或ABEK-P2型 (欧盟 英国 143)
防毒罐。
呼吸器使用经过测试并通过政府标准如NIOSH(US)或CEN(EU)的呼吸器和零件。

模块 9. 理化特性
9.1 基本的理化特性的信息
a) 外观与性状
形状: 固体
b) 气味
无数据资料
c) 气味阈值
无数据资料
d) pH值
无数据资料
e) 熔点/凝固点
无数据资料
f) 沸点、初沸点和沸程
无数据资料
g) 闪点
无数据资料
h) 蒸发速率
无数据资料
i) 易燃性(固体,气体)
无数据资料
j) 高的/低的燃烧性或爆炸性限度 无数据资料
k) 蒸气压
无数据资料
l) 蒸汽密度
无数据资料
m) 密度/相对密度
无数据资料
n) 水溶性
0.015 g/l 在 25 °C
o) n-辛醇/水分配系数
辛醇--水的分配系数的对数值: 3.975
p) 自燃温度
无数据资料
q) 分解温度
无数据资料
r) 粘度
无数据资料

模块 10. 稳定性和反应活性
10.1 反应性
无数据资料
10.2 稳定性
无数据资料
10.3 危险反应
无数据资料
10.4 应避免的条件
无数据资料
10.5 不相容的物质
强氧化剂
10.6 危险的分解产物

模块 11. 毒理学资料
11.1 毒理学影响的信息
急性毒性
半数致死剂量 (LD50) 经口 - 大鼠 - 1,453 mg/kg
半数致死浓度(LC50) 吸入 - 大鼠 - 4 h - 3,300 mg/m3
半数致死剂量 (LD50) 经皮 - 兔子 - > 2,010 mg/kg
皮肤刺激或腐蚀
皮肤 - 兔子 - 轻度的皮肤刺激
眼睛刺激或腐蚀
眼睛 - 兔子 - 无眼睛刺激
呼吸道或皮肤过敏
长期或反复接触导致个别人过敏反应 前面的数据或数据判读是根据定量结构活性关系(QSAR)确定的。
生殖细胞致突变性
无数据资料
致癌性
IARC:
此产品中没有大于或等于 0。1%含量的组分被 IARC鉴别为可能的或肯定的人类致癌物。
生殖毒性
生殖毒性 - 大鼠 - 经口
母体效应:其他影响。 特定发育异常:肌肉骨骼系统。
特异性靶器官系统毒性(一次接触)
无数据资料
特异性靶器官系统毒性(反复接触)
无数据资料
吸入危险
无数据资料
潜在的健康影响
吸入 吸入有害。 可能引起呼吸道刺激。
摄入 误吞对人体有害。
皮肤 通过皮肤吸收可能有害。 可能引起皮肤刺激。
眼睛 可能引起眼睛刺激。
附加说明
化学物质毒性作用登记: XZ4380000

模块 12. 生态学资料
12.1 生态毒性
对鱼类的毒性 半数致死浓度(LC50) - 虹鳟 (红鳟鱼) - 0.81 mg/l - 96 h
对水蚤和其他水生无脊 半数效应浓度(EC50) - 大型蚤 (水蚤) - 0.77 mg/l - 48 h
椎动物的毒性
12.2 持久性和降解性
无数据资料
12.3 潜在的生物累积性
无数据资料
12.4 土壤中的迁移性
无数据资料
12.5 PBT 和 vPvB的结果评价
无数据资料
12.6 其它不良影响
对水生生物毒性极大并具有长期持续影响.
无数据资料

模块 13. 废弃处置
13.1 废物处理方法
产品
将剩余的和不可回收的溶液交给有许可证的公司处理。
与易燃溶剂相溶或者相混合,在备有燃烧后处理和洗刷作用的化学焚化炉中燃烧
受污染的容器和包装
按未用产品处置。

模块 14. 运输信息
14.1 联合国危险货物编号
欧洲陆运危规: 3077 国际海运危规: 3077 国际空运危规: 3077
14.2 联合国运输名称
欧洲陆运危规: ENVIRONMENTALLY HAZARDOUS SUBSTANCE, SOLID, N.O.S. (Difenoconazole)
国际海运危规: ENVIRONMENTALLY HAZARDOUS SUBSTANCE, SOLID, N.O.S. (Difenoconazole)
国际空运危规: Environmentally hazardous substance, solid, n.o.s. (Difenoconazole)
14.3 运输危险类别
欧洲陆运危规: 9 国际海运危规: 9 国际空运危规: 9
14.4 包裹组
欧洲陆运危规: III 国际海运危规: III 国际空运危规: III
14.5 环境危险
欧洲陆运危规: 是 国际海运危规 国际空运危规: 是
海洋污染物(是/否): 是
14.6 对使用者的特别提醒
进一步信息
危险品独立包装,液体5升以上或固体5公斤以上,每个独立包装外和独立内包装合并后的外包装上都必须有EHS
标识 (根据欧洲 ADR 法规 2.2.9.1.10, IMDG 法规 2.10.3),


模块 15 - 法规信息
N/A


模块16 - 其他信息
N/A

制备方法与用途

苯醚甲环唑简介

苯醚甲环唑,又名噁醚唑,商品名为“世高”,属于三唑类杀菌剂。它是一种甾醇脱甲基化抑制剂,具有高效、广谱、低毒和用量低的特点,是三唑类杀菌剂中的优良品种之一。其内吸性强,通过抑制病菌细胞麦角甾醇的生物合成,破坏病原菌细胞膜结构与功能,用于果树、蔬菜、小麦、马铃薯、豆类、瓜类等作物。它对多种真菌性病害具有很好的保护和治疗作用,并且具有“三不”(不污染环境、不污染农产品、不杀伤天敌)的特点,是目前我国乃至世界各国防治柑橘疮痂病、斑点落叶病等作物抗性病害的理想杀菌剂。

作用机制

苯醚甲环唑水分散粒剂为米黄至棕色细粒。它对植物病原菌的孢子形成具有强烈抑制作用,并能抑制分生孢子成熟,从而控制病情进一步发展。苯醚甲环唑的作用方式是通过干扰病原菌细胞的C14脱甲基化作用,抑制麦角甾醇的生物合成,从而使甾醇滞留于细胞膜内,损坏了膜的生理作用,导致真菌死亡。

特点
  • 内吸传导,杀菌谱广:苯醚甲环唑是一种高效、安全、低毒、广谱性杀菌剂。可被植物内吸,渗透作用强。施药后2小时内即被作物吸收,并有向上传导的特性,能使新生的幼叶、花、果免受病菌为害。能一药多治,对多种真菌性病害都有良好的防治效果。能有效地防治蔬菜的黑星病、叶斑病、白粉病及锈病,兼具预防和治疗作用。

  • 耐雨冲刷、药效持久:黏着在叶面的药剂耐雨水冲刷,从叶片挥发极少,即使在高温条件下也表现较持久的杀菌活性,比一般杀菌剂持效期长3~4天。

  • 剂型先进,作物安全:水分散粒剂由有效成份、分散剂、湿润剂、崩解剂、消泡剂、黏合剂和防结块剂等助剂通过微细化、喷雾干燥等工艺造粒。投入水中可迅速崩解分散,形成高悬浮分散体系,无粉尘影响,对使用者及环境安全。不含有机溶剂,对推荐作物安全。

  • 混配性好:苯醚甲环唑可与丙环唑、嘧菌酯等杀菌剂成分混配,用于生产复配杀菌剂。

合成方法

以间二氯苯为原料,经酰化、醚化、溴化、环化和缩合反应,最终合成苯醚甲环唑。图1为苯醚甲环唑的合成路线。

适宜作物

西红柿、甜菜、香蕉、禾谷类作物、水稻、大豆、园艺作物及各种蔬菜等。对小麦、大麦进行茎叶(小麦株高24~42cm)处理时,有时叶片会出现变色现象,但不会影响产量。

化学性质和用途
  • 化学性质:无色固体,熔点76℃。

  • 用途:苯醚甲环唑属三唑类杀菌剂,具有内吸性,是甾醇脱甲基化抑制剂。用于叶面处理或种子处理。

防治对象

苯醚甲环唑对子囊亚门、担子菌亚门以及包括链格孢属、壳二孢属、尾孢霉属、刺盘孢属、球座菌属、茎点霉属、柱隔孢属、壳针孢属、黑星菌属在内的半知菌,白粉菌科,锈菌目和某些种传病原菌有持久的保护和治疗活性。同时对甜菜褐斑病、小麦颖枯病、叶枯病、锈病以及由几种致病菌引起的霉病,苹果黑星病、白粉病,葡萄白粉病,马铃薯早疫病,花生叶斑病、网斑病等均有较好的治疗效果。

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

  • 作为反应物:
    描述:
    苯醚甲环唑异丙基氯化镁 、 sulfur 、 盐酸 作用下, 以 四氢呋喃 为溶剂, 反应 2.5h, 以59%的产率得到2-[2-chloro-4-(4-chloro-phenoxy)-phenyl]-2-[(5-mercapto-1,2,4-triazol-1-yl)-methyl]-4-methyl-1,3-dioxolan
    参考文献:
    名称:
    [EN] A PROCESS USING GRIGNARD REAGENTS
    [FR] PROCÉDÉ UTILISANT DES RÉACTIFS DE GRIGNARD
    摘要:
    本发明涉及一种利用格氏试剂提供含硫代三唑基团化合物的过程。
    公开号:
    WO2011113820A1
  • 作为产物:
    描述:
    1,3-二氯苯 在 aluminum (III) chloride 、 双氧水对甲苯磺酸咪唑氢溴酸盐(低含水量) 、 potassium hydroxide 作用下, 以 二氯甲烷环己烷N,N-二甲基甲酰胺 为溶剂, 反应 25.0h, 生成 苯醚甲环唑
    参考文献:
    名称:
    一种苯醚甲环唑的制备方法
    摘要:
    本申请涉及杀菌剂技术领域,具体公开了一种苯醚甲环唑的制备方法。一种苯醚甲环唑的制备方法,包括以下步骤:2–氯‑4‑(4‑氯苯氧基)苯乙酮依次经溴化反应、环化反应、缩合反应,得到苯醚甲环唑粗品;苯醚甲环唑粗品再经纯化后得到成品苯醚甲环唑;合成路线用反应方程式表示如下: 。本申请所提供的苯醚甲环唑的生产工艺溴素利用率较高,可以有效改善生产苯醚甲环唑的经济效益和环境效益。
    公开号:
    CN115745973A
点击查看最新优质反应信息

文献信息

  • [EN] ACC INHIBITORS AND USES THEREOF<br/>[FR] INHIBITEURS DE L'ACC ET UTILISATIONS ASSOCIÉES
    申请人:GILEAD APOLLO LLC
    公开号:WO2017075056A1
    公开(公告)日:2017-05-04
    The present invention provides compounds I and II useful as inhibitors of Acetyl CoA Carboxylase (ACC), compositions thereof, and methods of using the same.
    本发明提供了化合物I和II,这些化合物可用作乙酰辅酶A羧化酶(ACC)的抑制剂,以及它们的组合物和使用方法。
  • [EN] BICYCLYL-SUBSTITUTED ISOTHIAZOLINE COMPOUNDS<br/>[FR] COMPOSÉS ISOTHIAZOLINE SUBSTITUÉS PAR UN BICYCLYLE
    申请人:BASF SE
    公开号:WO2014206910A1
    公开(公告)日:2014-12-31
    The present invention relates to bicyclyl-substituted isothiazoline compounds of formula (I) wherein the variables are as defined in the claims and description. The compounds are useful for combating or controlling invertebrate pests, in particular arthropod pests and nematodes. The invention also relates to a method for controlling invertebrate pests by using these compounds and to plant propagation material and to an agricultural and a veterinary composition comprising said compounds.
    本发明涉及公式(I)中变量如索权和说明中所定义的自行车基取代异噻唑啉化合物。这些化合物对抗或控制无脊椎动物害虫,特别是节肢动物害虫和线虫方面具有用途。该发明还涉及一种通过使用这些化合物来控制无脊椎动物害虫的方法,以及包含所述化合物的植物繁殖材料、农业和兽医组合物。
  • [EN] AZOLINE COMPOUNDS<br/>[FR] COMPOSÉS AZOLINE
    申请人:BASF SE
    公开号:WO2015128358A1
    公开(公告)日:2015-09-03
    The present invention relates to azoline compounds of formula (I) wherein A, B1, B2, B3, G1, G2, X1, R1, R3a, R3b, Rg1 and Rg2 are as defined in the claims and the description. The compounds are useful for combating or controlling invertebrate pests, in particular arthropod pests and nematodes. The invention also relates to a method for controlling invertebrate pests by using these compounds and to plant propagation material and to an agricultural and a veterinary composition comprising said compounds.
    本发明涉及式(I)的噁唑啉化合物,其中A、B1、B2、B3、G1、G2、X1、R1、R3a、R3b、Rg1和Rg2如权利要求和描述中所定义。这些化合物对抗或控制无脊椎动物害虫,特别是节肢动物害虫和线虫方面具有用途。该发明还涉及一种利用这些化合物控制无脊椎动物害虫的方法,以及包括所述化合物的植物繁殖材料、农业和兽医组合物。
  • [EN] SUBSTITUTED QUINAZOLINES AS FUNGICIDES<br/>[FR] QUINAZOLINES SUBSTITUÉES, UTILISÉES EN TANT QUE FONGICIDES
    申请人:SYNGENTA PARTICIPATIONS AG
    公开号:WO2010136475A1
    公开(公告)日:2010-12-02
    The present invention relates to a compound of formula (I) wherein wherein the substituents have the definitions as defined in claim 1or a salt or a N-oxide thereof, their use and methods for the control and/or prevention of microbial infection, particularly fungal infection, in plants and to processes for the preparation of these compounds.
    本发明涉及一种具有如下式(I)的化合物,其中取代基具有权利要求1中定义的定义,或其盐或N-氧化物,它们的用途以及用于控制和/或预防植物中微生物感染,特别是真菌感染的方法,以及制备这些化合物的方法。
  • [EN] MICROBIOCIDAL OXADIAZOLE DERIVATIVES<br/>[FR] DÉRIVÉS D'OXADIAZOLE MICROBIOCIDES
    申请人:SYNGENTA PARTICIPATIONS AG
    公开号:WO2017157962A1
    公开(公告)日:2017-09-21
    Compounds of the formula (I) wherein the substituents are as defined in claim 1, useful as a pesticides, especially fungicides.
    式(I)的化合物,其中取代基如权利要求1所定义,作为杀虫剂特别是杀菌剂有用。
查看更多

表征谱图

  • 氢谱
    1HNMR
  • 质谱
    MS
  • 碳谱
    13CNMR
  • 红外
    IR
  • 拉曼
    Raman
查看更多图谱数据,请前往“摩熵化学”平台
mass
查看更多图谱数据,请前往“摩熵化学”平台
ir
查看更多图谱数据,请前往“摩熵化学”平台
  • 峰位数据
  • 峰位匹配
  • 表征信息
Shift(ppm)
Intensity
查看更多图谱数据,请前往“摩熵化学”平台
Assign
Shift(ppm)
查看更多图谱数据,请前往“摩熵化学”平台
测试频率
样品用量
溶剂
溶剂用量
查看更多图谱数据,请前往“摩熵化学”平台

同类化合物

(βS)-β-氨基-4-(4-羟基苯氧基)-3,5-二碘苯甲丙醇 (S)-(-)-7'-〔4(S)-(苄基)恶唑-2-基]-7-二(3,5-二-叔丁基苯基)膦基-2,2',3,3'-四氢-1,1-螺二氢茚 (S)-盐酸沙丁胺醇 (S)-3-(叔丁基)-4-(2,6-二甲氧基苯基)-2,3-二氢苯并[d][1,3]氧磷杂环戊二烯 (S)-2,2'-双[双(3,5-三氟甲基苯基)膦基]-4,4',6,6'-四甲氧基联苯 (S)-1-[3,5-双(三氟甲基)苯基]-3-[1-(二甲基氨基)-3-甲基丁烷-2-基]硫脲 (R)富马酸托特罗定 (R)-(-)-盐酸尼古地平 (R)-(+)-7-双(3,5-二叔丁基苯基)膦基7''-[((6-甲基吡啶-2-基甲基)氨基]-2,2'',3,3''-四氢-1,1''-螺双茚满 (R)-3-(叔丁基)-4-(2,6-二苯氧基苯基)-2,3-二氢苯并[d][1,3]氧杂磷杂环戊烯 (R)-2-[((二苯基膦基)甲基]吡咯烷 (N-(4-甲氧基苯基)-N-甲基-3-(1-哌啶基)丙-2-烯酰胺) (5-溴-2-羟基苯基)-4-氯苯甲酮 (5-溴-2-氯苯基)(4-羟基苯基)甲酮 (5-氧代-3-苯基-2,5-二氢-1,2,3,4-oxatriazol-3-鎓) (4S,5R)-4-甲基-5-苯基-1,2,3-氧代噻唑烷-2,2-二氧化物-3-羧酸叔丁酯 (4-溴苯基)-[2-氟-4-[6-[甲基(丙-2-烯基)氨基]己氧基]苯基]甲酮 (4-丁氧基苯甲基)三苯基溴化磷 (3aR,8aR)-(-)-4,4,8,8-四(3,5-二甲基苯基)四氢-2,2-二甲基-6-苯基-1,3-二氧戊环[4,5-e]二恶唑磷 (2Z)-3-[[(4-氯苯基)氨基]-2-氰基丙烯酸乙酯 (2S,3S,5S)-5-(叔丁氧基甲酰氨基)-2-(N-5-噻唑基-甲氧羰基)氨基-1,6-二苯基-3-羟基己烷 (2S,2''S,3S,3''S)-3,3''-二叔丁基-4,4''-双(2,6-二甲氧基苯基)-2,2'',3,3''-四氢-2,2''-联苯并[d][1,3]氧杂磷杂戊环 (2S)-(-)-2-{[[[[3,5-双(氟代甲基)苯基]氨基]硫代甲基]氨基}-N-(二苯基甲基)-N,3,3-三甲基丁酰胺 (2S)-2-[[[[[[((1R,2R)-2-氨基环己基]氨基]硫代甲基]氨基]-N-(二苯甲基)-N,3,3-三甲基丁酰胺 (2-硝基苯基)磷酸三酰胺 (2,6-二氯苯基)乙酰氯 (2,3-二甲氧基-5-甲基苯基)硼酸 (1S,2S,3S,5S)-5-叠氮基-3-(苯基甲氧基)-2-[(苯基甲氧基)甲基]环戊醇 (1-(4-氟苯基)环丙基)甲胺盐酸盐 (1-(3-溴苯基)环丁基)甲胺盐酸盐 (1-(2-氯苯基)环丁基)甲胺盐酸盐 (1-(2-氟苯基)环丙基)甲胺盐酸盐 (-)-去甲基西布曲明 龙胆酸钠 龙胆酸叔丁酯 龙胆酸 龙胆紫 龙胆紫 齐达帕胺 齐诺康唑 齐洛呋胺 齐墩果-12-烯[2,3-c][1,2,5]恶二唑-28-酸苯甲酯 齐培丙醇 齐咪苯 齐仑太尔 黑染料 黄酮,5-氨基-6-羟基-(5CI) 黄酮,6-氨基-3-羟基-(6CI) 黄蜡,合成物 黄草灵钾盐