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啶虫脒 | 160430-64-8

中文名称
啶虫脒
中文别名
(E)-N-(N-氰基乙亚胺基)-N-甲基-2-氯吡啶-5-甲胺;乙虫脒;N-((6-氯-3-吡啶)甲基)-N'-氰基-N-甲基乙脒
英文名称
acetamiprid
英文别名
N-[(6-chloropyridin-3-yl)methyl]-N'-cyano-N-methylethanimidamide
啶虫脒化学式
CAS
160430-64-8
化学式
C10H11ClN4
mdl
MFCD06201842
分子量
222.677
InChiKey
WCXDHFDTOYPNIE-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:
    100-102°C
  • LogP:
    0.620 (est)
  • 颜色/状态:
    White crystals
  • 气味:
    Odorless
  • 溶解度:
    In water, 4.25X10+3 mg/L at 25 °C
  • 密度:
    1.330 g/cu cm at 20 °C
  • 蒸汽压力:
    4.36X10-5 mm Hg at 25 °C (est)
  • 解离常数:
    pKa = 0.7
  • 碰撞截面:
    150.24 Ų [M+H]+ [CCS Type: TW]
  • 保留指数:
    2452;2458;2435.8

计算性质

  • 辛醇/水分配系数(LogP):
    1.4
  • 重原子数:
    15
  • 可旋转键数:
    3
  • 环数:
    1.0
  • sp3杂化的碳原子比例:
    0.3
  • 拓扑面积:
    52.3
  • 氢给体数:
    0
  • 氢受体数:
    3

ADMET

代谢
乙酰胆碱酯酶抑制剂在蜜蜂体内的代谢研究。将蜜蜂分为六个生物学区室:头部、胸部、腹部、血淋巴、中肠和直肠。蜜蜂口服100微克[(14)C]-乙酰胆碱酯酶抑制剂/千克蜜蜂,此剂量约为半数致死剂量的1500倍。72小时后,只有40%的总放射性被消除,表明乙酰胆碱酯酶抑制剂及其代谢物在蜜蜂体内趋向于持久存在。乙酰胆碱酯酶抑制剂在所有区室内迅速分布并发生代谢。给药后,放射性主要局限于腹部,随后在直肠。72小时后,最大量的放射性(约占总摄入剂量的20%)再次在腹部检测到,而总放射性的最低平在中肠淋巴中检测到。头部的放射性不超过总摄入放射性的7.6%。在30分钟内,超过50%的乙酰胆碱酯酶抑制剂被代谢,表明该化合物的半衰期非常短。在最初几小时,乙酰胆碱酯酶抑制剂主要在富含尼古丁乙酰胆碱受体的组织中检测到:腹部、胸部和头部。在检测到的七种代谢物中,主要的是6-尼古丁酸和一个被称为U1的未知代谢物,它们主要存在于直肠、胸部和头部。我们的结果表明,乙酰胆碱酯酶抑制剂的低毒性可能反映了其迅速的代谢。
The in vivo metabolism of acetamiprid was studied in the honeybee, Apis mellifera L. The distribution of acetamiprid and its metabolites was monitored over a 72-h period in six biological compartments: head, thorax, abdomen, haemolymph, midgut and rectum. Honeybees were treated orally with 100 ug [(14)C]-acetamiprid/kg bee, a dose which is about 1500 times lower than the median lethal dose. After 72 hr, only 40% of the total radioactivity was eliminated, suggesting that acetamiprid and its metabolites tended to persist in the honeybee. Acetamiprid was rapidly distributed in all compartments and metabolized. Just after administration, radioactivity was mainly localized in the abdomen and subsequently in the rectum. After 72 hr, the maximum amount of radioactivity (about 20% of the ingested dose) was detected again in the abdomen, whereas the lowest level of total radioactivity was detected in the hemolymph. Radioactivity in the head did not exceed 7.6% of total ingested radioactivity. More than 50% of acetamiprid was metabolized in less than 30 min, indicating a very short half-life for the compound. During the first hours, acetamiprid was mainly detected in nicotinic acetylcholine receptor-rich tissues: abdomen, thorax and head. Of the seven metabolites detected, the major ones were 6-choronicotinic acid and an unknown metabolite called U1, which was present mainly in the rectum, the thorax and the head. Our results indicate that the low toxicity of acetamiprid may reflect its rapid metabolism.
来源:Hazardous Substances Data Bank (HSDB)
代谢
背景:新烟碱杀虫剂是一种新型杀虫剂,已经在全球范围内使用,因为它们对节肢动物具有选择性毒性,对脊椎动物相对无毒。有研究表明,几种新烟碱杀虫剂会导致哺乳动物的神经发育毒性。本研究旨在建立人类摄入与新烟碱杀虫剂尿排出的关系,以便进行生物监测,并估计日本成年人的膳食新烟碱杀虫剂摄入量。方法/主要结果:九名健康成年人摄入了标记的新烟碱杀虫剂乙螨唑克百威丁氟螨酯吡虫啉)微剂量,并在给药后连续四天收集24小时合并尿液样本。使用一室和二室模型对排泄动力学进行建模,然后在涉及12名健康成年人的非标记新烟碱杀虫剂微剂量研究中进行验证。给药后观察到标记新烟碱杀虫剂尿浓度增加。克百威在3天内未发生变化地回收,大部分丁氟螨酯在1天内未发生变化地回收。大约10%的吡虫啉剂量未发生变化地排出。大部分乙螨唑代谢为去甲基乙螨唑。分析了373名日本成年人的点尿样本中新烟碱杀虫剂,并估计了每日摄入量。估计这些新烟碱杀虫剂的日均摄入量为0.53-3.66微克/天。研究人群中任何一种新烟碱杀虫剂的最高摄入量为64.5微克/天,这低于可接受日摄入量的1%。
BACKGROUND: Neonicotinoids, which are novel pesticides, have entered into usage around the world because they are selectively toxic to arthropods and relatively non-toxic to vertebrates. It has been suggested that several neonicotinoids cause neurodevelopmental toxicity in mammals. The aim was to establish the relationship between oral intake and urinary excretion of neonicotinoids by humans to facilitate biological monitoring, and to estimate dietary neonicotinoid intakes by Japanese adults. METHODOLOGY/PRINCIPAL FINDINGS: Deuterium-labeled neonicotinoid (acetamiprid, clothianidin, dinotefuran, and imidacloprid) microdoses were orally ingested by nine healthy adults, and 24 hr pooled urine samples were collected for 4 consecutive days after dosing. The excretion kinetics were modeled using one- and two-compartment models, then validated in a non-deuterium-labeled neonicotinoid microdose study involving 12 healthy adults. Increased urinary concentrations of labeled neonicotinoids were observed after dosing. Clothianidin was recovered unchanged within 3 days, and most dinotefuran was recovered unchanged within 1 day. Around 10% of the imidacloprid dose was excreted unchanged. Most of the acetamiprid was metabolized to desmethyl-acetamiprid. Spot urine samples from 373 Japanese adults were analyzed for neonicotinoids, and daily intakes were estimated. The estimated average daily intake of these neonicotinoids was 0.53-3.66 ug/day. The highest intake of any of the neonicotinoids in the study population was 64.5 ug/day for dinotefuran, and this was <1% of the acceptable daily intake.
来源:Hazardous Substances Data Bank (HSDB)
代谢
五只雄性和五只雌性大鼠每天口服一剂非标记的乙酰胺,连续给药14天,然后在第15天单次给药放射性标记的乙酰胺。在第14天收集一次尿液和粪便,然后在给予[(14)C]乙酰胺剂量溶液后的24小时间隔内收集,直到处死。通过薄层共色谱法与未标记的参照物质进行代谢物的定性分析。未知的代谢物通过液相色谱-串联质谱法(LC-MS/MS)鉴定为IC-O的甘酸结合物(简称为IC-O-Gly)。大鼠排泄物中的主要放射性化合物是乙酰胺本身(雄性:5.21%;雌性:7.41%)、去甲基化合物IM-2-1(雄性:15.48%;雌性:20.39%)、烟酸生物IC-O(雄性:11.12%;雌性:8.01%)和IC-O甘酸结合物IC-O-Gly(雄性:10.10%;雌性:10.32%)。此外,还检测到了MeS-IC-O、IM-1-4、IM-2-4、IM-O、IM-1-3和IM-2-3,但它们占剂量的不到2%。尿液中还有几个未知化合物,"其他"部分中未知化合物的最大丰度为1.0%。认为大鼠体内乙酰胺的主要代谢途径是N-去甲基化产生IM-2-1,从IM-2-1分离出乙酰胺侧链产生IC-O,以及从乙酰胺和IM-2-1分别分离出乙酰胺侧链产生IS-1-1和IS-2-1。
... Five males and five female /rats/ were orally administered a daily dose of non-labelled acetamiprid for 14 days followed by a single dose of radiolabelled acetamiprid on day 15. The urine and feces were collected once on day 14 and then at 24-hour intervals after administration of the [(14)C]acetamiprid dose solution until sacrifice. Qualitative analysis of metabolites was performed by thin-layer co-chromatography with unlabelled reference substances. The unknown metabolite was identified by liquid chromatography-tandem mass spectrometry (LC-MS/MS) as the glycine conjugate of IC-O (abbreviated as IC-O-Gly). The major radioactive compounds in the excreta of rats were acetamiprid itself (males: 5.21%; females: 7.41%), demethylated compound IM-2-1 (males: 15.48%; females: 20.39%), nicotinic acid derivative IC-O (males: 11.12%; females: 8.01%) and IC-O glycine conjugate IC-O-Gly (males: 10.10%; females: 10.32%). In addition, MeS-IC-O, IM-1-4, IM-2-4, IM-O, IM-1-3 and IM-2-3 were detected, but they accounted for less than 2% of the dose. There were several unknown compounds in urine, and the maximum abundance of an unknown compound in the "others" fraction was 1.0%. It was considered that the major metabolic routes of acetamiprid in rats are the production of IM-2-1 by N-demethylation, the production of IC-O by detachment of the cyanoacetamide side-chain from IM-2-1, and the production of IS-1-1 and IS-2-1 by detachment of the cyanoacetamide sidechain from acetamide and IM-2-1, respectively.
来源:Hazardous Substances Data Bank (HSDB)
代谢
在大鼠排泄物中识别并定量分析了放射性化合物。B组中主要识别出的化合物为乙酰甲胺磷本身(雄性:6.10%;雌性:5.63%)、去甲基化合物IM-2-1(雄性:19.51%;雌性:19.00%)和烟酸生物IC-O(雄性:28.19%;雌性:25.52%);D组中为乙酰甲胺磷(雄性:7.75%;雌性:7.34%)、IM-2-1(雄性:24.48%;雌性:21.37%)和IC-O(雄性:27.11%;雌性:27.63%);A组中为乙酰甲胺磷(雄性:4.16%;雌性:6.12%)、IM-2-l(雄性:13.39%;雌性:18.98%)和IC-O(雄性:28.13%;雌性:24.73%)。CN-B组中的主要化合物为乙酰甲胺磷(雄性:3.98%;雌性:4.51%)、IM-2-1(雄性:16.95%;雌性:16.56%)、IS-1-1(雄性:13.15%;雌性:16.45%)和IS-2-1(雄性:35.61%;雌性:30.23%)。IS-1-1和IS-2-1被认为是通过乙酰甲胺磷和IM-2-1侧链的裂解产生的。此外,IC-O-Gly、MeS-IC-O、IM-1-4、IM-2-4、IM-O、IM-1-3和IM-2-3在A、B和D组中也被检测到,但每组中的含量均低于剂量的4%。大鼠体内乙酰甲胺磷的主要代谢途径是通过去甲基化转变为IM-2-1,然后通过从乙酰甲胺磷和IM-2-1中裂解出IS-1-1和IS-2-1进一步转变为IC-O。
... Radioactive compounds in the excreta of rats were identified and analysed quantitatively. The major compounds identified were acetamiprid itself (males: 6.10%; females: 5.63%), demethylated compound IM-2-1 (males: 19.51%; females: 19.00%) and nicotinic acid derivative IC-O (males: 28.19%; females: 25.52%) in group B; acetamiprid (males: 7.75%; females: 7.34%), IM-2-1 (males: 24.48%; females: 21.37%) and IC-O (males: 27.11%; females: 27.63%) in group D; and acetamiprid (males: 4.16%; females: 6.12%), IM-2-l (males: 13.39%; females: 18.98%) and IC-O (males: 28.13%; females: 24.73%) in group A. Acetamiprid (males: 3.98%; females: 4.51%), IM-2-1 (males: 16.95%; females: 16.56%), IS-1-1 (males: 13.15%; females: 16.45%) and IS-2-1 (males: 35.61%; females: 30.23%) were detected as the main compounds in group CN-B. IS-1-1 and IS-2-1 were thought to be generated by cleavage of the side-chains of acetamiprid and IM-2-1. In addition, IC-O-Gly, MeS-IC-O, IM-1-4, IM-2-4, IM-O, IM-1-3 and IM-2-3 were detected in groups A, B and D, but each at less than 4% of the dose. The main metabolic pathways of acetamiprid in rats were the transformation to IM-2-1 by demethylation and further to IC-O after cleaving IS-1-1 and IS-2-1 from acetamiprid and IM-2-1, respectively
来源:Hazardous Substances Data Bank (HSDB)
代谢
有机腈通过肝脏中的细胞色素P450酶的作用转化为化物离子。化物迅速被吸收并在全身分布。化物主要通过罗丹酶或3-巯基丙酸转移酶代谢为硫氰酸盐。化物代谢物通过尿液排出。
Organic nitriles are converted into cyanide ions through the action of cytochrome P450 enzymes in the liver. Cyanide is rapidly absorbed and distributed throughout the body. Cyanide is mainly metabolized into thiocyanate by either rhodanese or 3-mercaptopyruvate sulfur transferase. Cyanide metabolites are excreted in the urine. (L96)
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 毒性总结
识别和使用:啶虫脒是一种固体。啶虫脒是一种新烟碱杀虫剂,用于控制叶菜、果菜、十字花科作物、柑橘、仁果、葡萄、棉花以及观赏植物和花卉上的吸汁型昆虫。人体研究:有两例因自杀目的服用含有啶虫脒杀虫剂制剂导致的急性中毒病例。两例病例均出现严重恶心和呕吐、肌肉无力、体温过低、抽搐,以及包括心动过速、低血压、心电图改变、低氧血症和口渴的临床表现,其中血清啶虫脒浓度较高的病例症状更为明显。这些症状部分类似于急性有机中毒。一名79岁的男性摄入了啶虫脒,并在摄入后两小时得到医疗注意。到达时,他的血液中啶虫脒浓度为21.1微克/毫升。他出现了意识障碍、低血压、恶心、呕吐和高血糖,但没有出现有机中毒特征性的瞳孔缩小和粘液过度分泌。在体外,啶虫脒能显著诱导人外周血淋巴细胞姐妹染色单体交换和染色体畸变,并在所有浓度和处理时间下显著诱导微核形成,在30、35和40微克/毫升的啶虫脒浓度下尤为明显。动物研究:在兔子的眼和皮肤刺激性研究中,啶虫脒不是刺激物,在豚鼠的马格努森和克里格曼最大化测试中也不是皮肤致敏物。将啶虫脒混合到小鼠的饮食中,剂量平为0、400、800、1600或3200 ppm,并连续喂养13周。在3200 ppm剂量下,有2只雄性和2只雌性小鼠在研究期间死亡。在3200 ppm剂量下的5只雌性小鼠观察到震颤。在800、1600和3200 ppm剂量下,两性小鼠的平均相对肝脏重量增加。显微镜检查显示,在3200 ppm剂量下,两性小鼠均出现中央小叶肝细胞增生和肾上腺皮质的脂肪耗尽。在大鼠(NOEL = 16 mg/kg/天,基于骨骼变异)和家兔(发育NOEL = 15 mg/kg/天,基于2个胎儿胸椎椎弓和融合肋骨)中注意到发育毒性。在大鼠中,啶虫脒通过降低胆固醇转化为睾酮的速率和阻止胆固醇进入莱迪希细胞内的线粒体,从而干扰睾酮生物合成。这些效应造成了大鼠的生殖损伤。啶虫脒在大鼠中具有神经毒性,并在小鼠中诱导神经发育毒性。啶虫脒暴露干扰了雄性小鼠执行社会性行为和焦虑相关行为所需的神经回路的发展。在使用鼠伤寒沙门氏菌TA100、TA1535、TA98和TA1537菌株以及大肠杆菌WP2 uvrA菌株进行反转突变测试时,无论是否进行代谢激活,啶虫脒均为阴性。生态毒性研究:啶虫脒可引起青蛙坐骨神经的神经病性变化。口服摄入啶虫脒后,在1微克/蜜蜂的剂量下增加了蜜蜂对蔗糖溶液触角刺激的敏感性,并在0.1微克/蜜蜂的剂量下损害了嗅觉学习的长期保留。啶虫脒胸廓应用在这些行为测试中没有产生效果,但增加了蜜蜂的活动的活动性(0.1和0.5微克/蜜蜂)和诱导的吻突延伸反射(0.1、0.5和1微克/蜜蜂)。啶虫脒对Amblyseius cucumeri不同发育生活阶段产生了显著的负面影响。啶虫脒暴露引起了蚯蚓的氧化应激和DNA损伤,并改变了抗氧化酶的活性。
IDENTIFICATION AND USE: Acetamiprid is a solid. Acetamiprid is a neonicotinoid insecticide that is used for the control of sucking-type insects on leafy vegetables, fruiting vegetables, cole crops, citrus fruits, pome fruits, grapes, cotton, and ornamental plants and flowers. HUMAN STUDIES: There are two cases of acute poisoning with an insecticide formulation containing acetamiprid for suicidal purposes. Both cases experienced severe nausea and vomiting, muscle weakness, hypothermia, convulsions, and clinical manifestations including tachycardia, hypotension, electrocardiogram changes, hypoxia, and thirst in the case with the higher serum concentration of acetamiprid. The symptoms were partially similar to acute organophosphate intoxication. A 79-year-old man had ingested acetamiprid and got medical attention two hours after ingestion. On arrival, his blood concentration of acetamiprid was 21.1 ug/mL. He had consciousness disturbance, hypotension, nausea, vomiting and hyperglycemia, but had no constricted pupils nor mucous supersecretion which are characteristic in organophosphate poisoning. In human peripheral blood lymphocytes, in vitro acetamiprid induced sister chromatid exchanges and chromosomal aberrations significantly at all concentrations and treatment times and micronucleus formation was significantly induced at 30, 35, and 40 ug/mL of acetamiprid. ANIMAL STUDIES: Acetamiprid was not an irritant in a study of ocular and dermal irritation in rabbits or a dermal sensitizer in the Magnusson and Kligman maximization test in guinea-pigs. Acetamiprid was admixed to the diet of mice at dose levels of 0, 400, 800, 1600, or 3200 ppm and fed to mice for a period of 13 weeks. 2 males and 2 females at 3200 ppm died during the study. Tremor was observed in 5 females at 3200 ppm. A treated-related increase in mean relative liver weight was observed in both sexes at 800, 1600, and 3200 ppm. Microscopic examination revealed centrilobular hepatocellular hypertrophy and depletion of fat from the adrenal cortex in both sexes at 3200 ppm. Developmental toxicity noted in rats (NOEL = 16 mg/kg/day, based on the skeletal variation) and rabbits (developmental NOEL = 15 mg/kg/day, based on fused thoracic vertebral arches and fused ribs in 2 fetuses). In rats, acetamiprid disrupted testosterone biosynthesis by decreasing the rate of conversion of cholesterol to testosterone and by preventing cholesterol from entering the mitochondria within the Leydig cells. These effects caused reproductive damage to the rats. Acetamiprid was neurotoxic in rats and induced neurodevelopmental toxicity in mice. Acetamiprid exposure interfered with the development of the neural circuits required for executing socio-sexual and anxiety-related behaviors in male mice. Acetamiprid was negative when Salmonella typhimurium strains TA100, TA1535, TA98, and TA1537, and Escherichia coli strain WP2 uvrA were used in reverse mutation tests with and without metabolic activation. ECOTOXICITY STUDIES: Acetamiprid can cause neuropathic changes in sciatic nerve of frogs. After oral consumption acetamiprid increased sensitivity of honeybees to antennal stimulation by sucrose solutions at doses of 1 ug/bee and impaired long-term retention of olfactory learning at the dose of 0.1 ug/bee. Acetamiprid thoracic application induced no effect in these behavioral assays but increased locomotor activity (0.1 and 0.5 ug/bee) and water-induced proboscis extension reflex (0.1, 0.5, and 1 ug/bee). Acetamiprid had significant adverse effects on different development life stages of Amblyseius cucumeri. Acetamiprid exposure caused oxidative stress and DNA damage of earthworm and changed the activity of the antioxidant enzyme.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 毒性总结
有机腈在体内和体外都会分解成化物离子。因此,有机腈的主要毒性机制是它们产生有毒的化物离子或氢氰酸化物是电子传递链第四个复合体(存在于真核细胞线粒体膜中)中的细胞色素c氧化酶的抑制剂。它与这种酶中的三价原子形成复合物。化物与这种细胞色素的结合阻止了电子从细胞色素c氧化酶传递到氧气。结果,电子传递链被中断,细胞无法再通过有氧呼吸产生ATP能量。主要依赖有氧呼吸的组织,如中枢神经系统和心脏,受到特别影响。化物也通过与过氧化氢酶谷胱甘肽过氧化物酶、变性血红蛋白、羟胺素、磷酸酶、酪氨酸酶抗坏血酸氧化酶黄嘌呤氧化酶、琥珀酸脱氢酶以及Cu/Zn超氧化物歧化酶结合,产生一些毒性效应。化物与变性血红蛋白中的三价离子结合,形成无活性的化变性血红蛋白。
Organic nitriles decompose into cyanide ions both in vivo and in vitro. Consequently the primary mechanism of toxicity for organic nitriles is their production of toxic cyanide ions or hydrogen cyanide. Cyanide is an inhibitor of cytochrome c oxidase in the fourth complex of the electron transport chain (found in the membrane of the mitochondria of eukaryotic cells). It complexes with the ferric iron atom in this enzyme. The binding of cyanide to this cytochrome prevents transport of electrons from cytochrome c oxidase to oxygen. As a result, the electron transport chain is disrupted and the cell can no longer aerobically produce ATP for energy. Tissues that mainly depend on aerobic respiration, such as the central nervous system and the heart, are particularly affected. Cyanide is also known produce some of its toxic effects by binding to catalase, glutathione peroxidase, methemoglobin, hydroxocobalamin, phosphatase, tyrosinase, ascorbic acid oxidase, xanthine oxidase, succinic dehydrogenase, and Cu/Zn superoxide dismutase. Cyanide binds to the ferric ion of methemoglobin to form inactive cyanmethemoglobin. (L97)
来源:Toxin and Toxin Target Database (T3DB)
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
  • 副作用
神经毒素 - 其他中枢神经系统神经毒素
Neurotoxin - Other CNS neurotoxin
来源:Haz-Map, Information on Hazardous Chemicals and Occupational Diseases
毒理性
  • 毒性数据
LC50 (rat) = 290 mg/m3 大白鼠 LC50 = 290 毫克/立方米
LC50 (rat) = 290 mg/m3
来源:Haz-Map, Information on Hazardous Chemicals and Occupational Diseases
吸收、分配和排泄
为了获取有关啶虫脒的吸收、分布、消除速率和途径、代谢和药代动力学信息,对成年Sprague-Dawley大鼠(雄性体重154-193克,雌性体重134-152克;在开始给药时年龄为5-6周;给药15天)进行了[(14)C]啶虫脒的研究。放射性标记的测试物质(化学纯度>99.9%,放射性化学纯度97.1-97.2%)由赞助商发送给合同研究组织。未标记的测试物质的化学纯度大于99.9%。在口服给药15天后进行了研究。总共使用了五个处理组(I、II、III、IV和V组),前三个组每组6只大鼠(3只雄性和3只雌性),后两个组每组10只大鼠(5只雄性和5只雌性)。使用了一个单一的对照组(VI组),由四只大鼠(两只雄性和两只雌性)组成。I、II和III组口服给予了[(14)C]啶虫脒,剂量为1.0毫克/千克体重,连续15天。IV和V组在14天内口服给予了啶虫脒,然后在第15天口服给予了单一的[(14)C]啶虫脒剂量。所有五个组的大鼠实际剂量率为0.97-1.01毫克/千克体重。通过高效液相色谱法分析,确定[(14)C]啶虫脒在剂量溶液中的放射性化学纯度为97.9%。剂量溶液在冷藏条件下至少15天内是稳定的。确定放射性标记剂量溶液的比活度为1.85 x 10(+3) Bq/ug。VI组仅用0.9%盐给药。在连续15天给予[(14)C]啶虫脒后,I、II和III组的大鼠分别在1、10和96小时后处死。在给予单一[(14)C]啶虫脒剂量后,IV组的大鼠在96小时后处死以收集组织和器官。V组仅用于血液药代动力学分析。在III组的每只大鼠给药后大约1小时,在第1、3、7和15天抽取全血,以确定血液中[(14)C]啶虫脒的浓度。血液中的平均浓度在雄性为0.477-0.747微克/毫升,在雌性为0.465-0.698微克/毫升。观察到动物之间的变异性。这些结果表明,在给药后1小时的血液浓度在整个给药期间是一致的。在V组的每只大鼠给药后大约0.25、0.5、1、2、3、4、5、7、9、12、24和48小时抽取全血,以确定血液中[(14)C]啶虫脒的浓度。雄性大鼠的平均峰值浓度(Cmax)、达到Cmax的时间(Tmax)、吸收半衰期和无限时间下的浓度-时间曲线下面积分别为0.798 +/- 0.111微克/毫升、2.80 +/- 0.637小时、1.35 +/- 0.825小时和8.35 +/- 1.12微克等效*小时/毫升。雌性大鼠的同一参数平均值分别为0.861 +/- 0.132微克/毫升、2.81 +/- 0.894小时、1.18 +/- 0.868小时和10.3 +/- 2.90微克等效*小时/毫升。雄性和雌性大鼠的消除半衰期分别为4.42 +/- 1.10小时和5.56 +/- 1.93小时。两性的药代动力学参数没有显著差异。两性的Tmax值表明,啶虫脒的吸收速率是迅速的,大约在2-3小时内达到可能的饱和最大血液浓度。消除结果表明,大部分啶虫脒(53-65%)通过尿液排出。尿液和笼子冲洗的排出量合计为61-73%。结果还表明,啶虫脒从胃肠道吸收迅速(在1小时内),因为给药后1小时内从胃肠道排出的剂量超过90%。在连续给药14天后再给予一次放射性标记啶虫脒(IV组)与连续15天给予放射性标记啶虫脒(I、II和III组)之间,测试物质的消除没有观察到差异。在雌性(22-29%)中,通过粪便排出的放射性物质量低于雄性(30-35%)。从I、II、III和IV组的每只大鼠收集了全血、肝脏、肾脏、肺、胰腺、脾脏、心脏、大脑、睾丸(雄性)、卵巢(雌性)、骨骼肌、腹股沟脂肪(白色)、带毛的皮肤、甲状腺、骨骼、肾上腺、带有内容的胃肠道和笼子冲洗物以及残留的
To obtain information on the absorption, distribution, rate and route of elimination, metabolism and pharmacokinetics of acetamiprid, a study was performed in adult Sprague-Dawley rats (body weight 154-193 g for males, 134-152 g for females; aged 5-6 weeks at the start of dosing; dosing for 15 days) using [(14)C]acetamiprid. The radiolabelled test substance (chemical purity > 99.9%, radiochemical purity 97.1-97.2%) was sent by the sponsor to the contract research organization. The non-labelled test substance /had/ a chemical purity of greater than 99.9%. The studies were conducted after oral administration of the test substance for 15 days. In total, five treatment groups (groups I, II, III, IV and V), consisting of 6 rats (3 males and 3 females) in each of the first three groups and 10 rats (5 males and 5 females) in each of the two remaining groups, were used. A single control group (group VI), consisting of four rats (two males and two females), was used. Groups I, II and III received oral doses of [(14)C]acetamiprid in 0.9% saline for 15 days at a target dose rate of 1.0 mg/kg body weight (bw). Groups IV and V received oral doses of acetamiprid in 0.9% saline for 14 days followed by a single oral dose of [(14)C]acetamiprid in 0.9% saline on day 15. The actual dose rate was 0.97-1.01 mg/kg bw for the rats in all five groups. The radiochemical purity of [(14)C]acetamiprid in the dose solution was determined to be 97.9% by high-performance liquid chromatographic (HPLC) analysis. The dose solution was stable under refrigerated conditions for at least 15 days. The specific activity of the radiolabelled dose solution was determined to be 1.85 x 10(+3) Bq/ug. Group VI was dosed with 0.9% saline only. Rats of groups I, II and III were sacrificed 1, 10 and 96 hours, respectively, after dosing of [(14)C]acetamiprid for 15 days. Rats of group IV were sacrificed 96 hours after a single dose of [(14)C]acetamiprid for tissue and organ collection. Group V was used only for blood pharmacokinetic analysis. Whole blood was drawn from each rat of group III approximately 1 hour post-dosing on days 1, 3, 7 and 15 to determine the [(14)C]acetamiprid concentration in blood. The average concentration in blood was in the range of 0.477-0.747 ug/mL in the males and 0.465-0.698 ug/mL in the females. Variation between animals was observed. These results indicate that the blood concentration at 1 hour post-dosing was consistent during the entire dosing period. Whole blood was drawn from each rat of group V at approximately 0.25, 0.5, 1, 2, 3, 4, 5, 7, 9, 12, 24 and 48 hours to determine the [(14)C]acetamiprid concentration in blood. The mean values for peak concentration (Cmax), time to Cmax (Tmax), absorption half-life and area under the concentration versus time curve at infinity for the male rats were 0.798 +/- 0.111 ug/mL, 2.80 +/- 0.637 hours, 1.35 +/- 0.825 hours and 8.35 +/- 1.12 ug eq*hr/mL, respectively. Values for the same parameters in female rats averaged 0.861 +/- 0.132 ug/ml, 2.81 +/- 0.894 hours, 1.18 +/- 0.868 hours and 10.3 +/- 2.90 ug eq*hr/mL, respectively. The elimination half-lives for the male and female rats were 4.42 +/- 1.10 hours and 5.56 +/- 1.93 hours, respectively. The pharmacokinetic parameters for both sexes did not differ considerably. The Tmax values in both sexes indicated that the rate of absorption of acetamiprid was rapid, and a maximum blood concentration to possible saturation was achieved in approximately 2-3 hours. The elimination results indicate that most acetamiprid (53-65%) was excreted in the urine. The excretion in urine and cage rinse combined amounted to 61-73%. The results also indicate that acetamiprid was absorbed rapidly (within 1 hour) from the gastrointestinal tract, as greater than 90% of the administered dose was eliminated from the gastrointestinal tract within 1 hour after dosing. No difference was observed in elimination of test substance between chronic administration of acetamiprid for 14 days followed by a single administration of radiolabelled acetamiprid on day 15 (group IV) and chronic administration of radiolabelled acetamiprid for 15 days (groups I, II and III). The amount of administered radioactivity eliminated in feces was lower for females (22-29%) than for males (30-35%). The whole blood, liver, kidney, lung, pancreas, spleen, heart, brain, testes (male), ovary (female), skeletal muscles, inguinal fat (white), skin with hair, thyroid, bone, adrenal glands, gastrointestinal tract with contents, cage rinses and residual carcasses were collected from each rat of groups I, II, III and IV. All collected samples were not composited but kept and analysed separately to account for the material balance for each rat. Radioactivity, after administration of the last chronic dose, was detected at the earliest sampling point (1 hour) in all the tissues collected from each rat. The radioactivity in most tissues was the highest at 1 hour post-dosing and declined rapidly thereafter (groups II and III). The Tmax for [(14)C]acetamiprid in the male and female rats indicated that the rate of absorption was rapid, and a maximum blood concentration (approximately 0.8 ug/mL) to possible saturation was achieved in approximately 2-3 hours. The levels of [(14)C]acetamiprid residue in tissues collected at 1 hour post-dosing confi rm the results obtained from the pharmacokinetic analysis. [(14)C]Acetamiprid residue levels seen in tissues collected 10 hours post-dosing (group II) were found to be substantially lower than residue levels in tissues collected 1 hour post-dosing. The elimination half-life for both sexes indicated that the rate of elimination was rapid. The levels of [(14)C]acetamiprid residues in tissues collected at 10 hours post-dosing confirm the results obtained from the pharmacokinetic studies. [(14)C]Acetamiprid residue levels seen in tissues collected 96 hours post-dosing (group III) were found to be very low compared with the levels observed in the tissues collected at 1 hour and 10 hours post-dosing. The elimination half-life for both sexes was between 4 and 6 hours postdosing, indicating that the rate of elimination was rapid and that retention of residue in tissues after chronic administration was minimal. The highest radioactivity levels were observed in the gastrointestinal tract, liver and kidney in both sexes at all sacrifice times. The lowest concentration was observed in bone and white fat. The residue levels observed were higher in all tissues of rats chronically treated with [(14)C]acetamiprid for 15 days (group III) compared with the rats in group IV, which received a single final dose of [(14)C]acetamiprid following 14 days of non-labelled acetamiprid doses. The residue levels observed in the tissues of rats sacrificed 96 hours after the last dose were very low (0.01-0.1 part per million [ppm]), as most of the administered dose (> 90%) was eliminated through the urine and feces. The total administered radioactivity recovered in groups I, II, III and IV was in the range of 91.7-106%, whereas recovery in group V (the pharmacokinetics group) was 71.7% and 85.6% in males and females, respectively. The loss of urine samples during a series of bleeding procedures is a possible explanation for the low recovery in group V.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
为了确定单次低剂量和高剂量施用啶虫脒的效果,研究了在大鼠体内啶虫脒的吸收、分布、代谢和排泄。将[吡啶-2,6-(14)C]啶虫脒以1.0、1.0和50 mg/kg bw的剂量分别静脉注射或口服给A、B和D组的五只雄性和五只雌性大鼠。在CN-B组中,以1.0 mg/kg bw的剂量进行了[基-(14)C]啶虫脒的代谢研究。A组用于通过排泄率和代谢物分析计算吸收率。B、D和CN-B组用于血液平、组织分布、代谢物分析和排泄率。...总结来说,口服给予大鼠的啶虫脒被迅速吸收并广泛分布到组织中。大部分放射性物质通过肾脏随尿液排出,并通过胆汁随粪便排出。放射性物质从大鼠体内的消失速度很快,没有发现会积累该化合物的组织。在性别之间没有观察到差异。
To ascertain the effect of administration of acetamiprid in single low and high doses, the absorption, distribution, metabolism and excretion of acetamiprid in rats were investigated. [Pyridine- 2,6-(14)C]acetamiprid was intravenously or orally administered to five male and five female rats in groups A, B and D at dose levels of 1.0, 1.0 and 50 mg/kg bw, respectively. In group CN-B, the metabolism study of [cyano-(14)C]acetamiprid was performed at a dose level of 1.0 mg/kg bw. Group A was for the determination of the absorption rate by calculation from the excretion rate and metabolite analysis. Groups B, D and CN-B were for blood levels, tissue distribution, metabolite analysis and excretion rate. ... In summary, acetamiprid orally dosed in rats was rapidly absorbed and widely distributed into the tissues via blood. The majority of the radioactivity was excreted in the urine through the kidney and in the feces via bile. The disappearance of the radioactivity from the body of the rat was rapid, and there were no tissues that are presumed to accumulate the compound. No differences in the sexes were observed.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
使用大约10-12周龄的Sprague-Dawley胆管插管大鼠进行了胆汁排泄研究。四只雄性和四只雌性胆管插管大鼠通过胃插管单次给予含[(14)C]啶虫脒的0.9%盐。雄性和雌性大鼠的平均给药剂量率分别为1.02和1.07 mg/kg体重。通过高效液相色谱分析,确定剂量溶液中[(14)C]啶虫脒的放射化学纯度为97.1%。一只雄性和一只雌性大鼠给予安慰剂(不含测试物质的0.9%盐)。从给药后3小时到12小时,观察到胆汁中[(14)C]啶虫脒残留平稳步上升,在给药后12小时,雄性和雌性大鼠的残留量(占给药剂量的百分比)最高。在48小时内,雄性大鼠胆汁中给药剂量的平均回收率为19.9% +/- 1.47%,雌性大鼠为18.6% +/- 0.62%。在胆汁中排泄的[(14)C]啶虫脒残留物的回收量占给药剂量的不到20%,这表明胆汁在雄性或雌性大鼠中都不是主要的排泄途径。测试物质的吸收和首次通过代谢/系统前消除的程度在性别之间没有显著差异。在48小时内,雄性大鼠粪便中给药剂量的平均回收率为6.72% +/- 3.36%,雌性大鼠为5.84% +/- 0.86%。在48小时内,雄性大鼠尿液中给药剂量的平均回收率为24.3% +/- 5.22%,雌性大鼠为36.9% +/- 3.80%。在雄性和雌性大鼠中,尿液加笼子冲洗的总和,分别为60.2% +/- 5.20%和64.4% +/- 2.86%,占总残留物的大部分,这表明大部分给药剂量通过尿液排泄。在给药后48小时,雄性大鼠肝脏中给药剂量的平均回收率为0.22% +/- 0.13%,雌性大鼠为0.18% +/- 0.18%。在给药后48小时,雄性大鼠胃肠道中给药剂量的平均回收率为0.46% +/- 0.34%,雌性大鼠为0.33% +/- 0.23%。这些结果表明,在雄性和雌性大鼠中,少量的啶虫脒(在收集的组织中<1%)被吸收到肝脏或留在胃肠道中。三只雄性大鼠给药剂量的总回收率分别为93.2%,92.8%和89.6%。三只雌性大鼠给药剂量的总回收率分别为94.9%,93.5%和91.2%。
A biliary excretion study was conducted using Sprague-Dawley bile duct-cannulated rats approximately 10-12 weeks old at dosing. Four male and four female bile duct-cannulated rats received single doses of [(14)C]acetamiprid in 0.9% saline through an intragastric cannula. The average dose rates were 1.02 and 1.07 mg/kg bw for the male and female rats, respectively. The radiochemical purity of [(14)C]acetamiprid in the dose solution was determined to be 97.1% by HPLC analysis. One male and one female rat were dosed with placebo (0.9% saline, containing no test substance). A steady increase in [(14)C]acetamiprid residue level was observed in bile from 3 to 12 hours post-dosing, with the highest amount (percentage of administered dose) at 12 hours post-dosing in both male and female rats. The average recovery of the administered dose in bile over a 48-hour period was 19.9% +/- 1.47% in the male rats and 18.6% +/- 0.62% in the female rats. Recovery of the [(14)C]acetamiprid residues excreted in bile accounted for less than 20% of the total administered dose, suggesting that bile is not a predominant excretory pathway in either the male or the female rats. The absorption of the test substance and the extent of fi rst-pass metabolism/presystemic elimination were not signifi cantly different between the sexes. were not significantly different between the sexes. The average recovery of the administered dose in feces over a 48-hour period was 6.72% 3.36% in the male rats and 5.84% +/- 0.86% in the female rats. The average recovery of the administered dose in urine over a 48-hour period was 24.3% +/- 5.22% in the male rats and 36.9% +/- 3.80% in the female rats. In the male and female rats, the sum of urine plus cage rinses, 60.2% +/- 5.20% and 64.4% +/- 2.86%, respectively, accounted for the major residues, suggesting that most of the administered dose was excreted in urine. The average recovery of the administered dose in liver at 48 hours post-dosing was 0.22% 0.13% in the male rats and 0.18% +/- 0.18% in the female rats. The average recovery of the administered dose in the gastrointestinal tract at 48 hours post-dosing was 0.46% +/- 0.34% in the male rats and 0.33% +/- 0.23% in the female rats. These results indicate that an insignificant amount of acetamiprid (< 1% in the collected tissues) was absorbed into the liver or remained in the gastrointestinal tract in both the male and female rats. the male and female rats. The total recoveries of the administered dose in the three male rats were 93.2%, 92.8% and 89.6%, respectively. The total recoveries of the administered dose in the three female rats were 94.9%, 93.5% and 91.2%, respectively.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
研究了在雄性Crl: CD(SD)BR大鼠皮肤上施用含有[(14)C]乙酰甲胺磷(纯度97.5%)的70%可湿性粉剂后乙酰甲胺磷的吸收程度。动物到达时大约8周大,体重为176-216克(预试验阶段)和143-203克(正式试验阶段)。目标剂量平为1、10和100微克/平方厘米。实际剂量平为0.0136毫克/动物(1.09微克/平方厘米)、0.119毫克/动物(9.53微克/平方厘米)和1.13毫克/动物(90.2微克/平方厘米)。在预试验阶段,由两组各四只雄性大鼠组成,以评估和建立测试材料的应用和皮肤清洗技术。在预试验阶段,雄性大鼠在两个平(0.0128毫克/动物和1.26毫克/动物)上进行皮肤给药。在正式试验阶段,每组24只大鼠的三组大鼠以三个剂量平皮肤给药[(14)C]-乙酰甲胺磷。仅接受载体的两组大鼠作为对照组(1%羧甲基纤维素溶液)。收集每只大鼠的尿液和粪便。在处死前立即清洗施用部位的皮肤。每个剂量组的四只大鼠在0.5、1、2、4、10和24小时处死;对照组大鼠在24小时处死。在处死时,通过心脏穿刺收集血液。在处理组中,放射性物质的总回收率在96.6%至102%之间,大部分放射性物质(63.9-87.5%)在皮肤清洗中。施用部位皮肤的放射性物质占施用放射性物质的10.2-32.2%。血液、排泄物和尸体中的放射性物质占施用放射性物质的不到6.50%。在血液中发现的放射性物质量、在排泄物中消除的量和在尸体中保留的量被认为是直接通过皮肤吸收[(14)C]乙酰甲胺磷的结果。在同一组内,随着暴露时间的增加,皮肤吸收的量也增加。在最长暴露时间,即给药后24小时,检测到最高的吸收,分别占1.09、9.53和90.2微克/平方厘米剂量组的4.27%(0.581微克)、6.34%(7.54微克)和2.82%(31.9微克)。直接吸收和施用部位皮肤中剩余的放射性物质总量被认为是间接吸收。1.09、9.53和90.2微克/平方厘米剂量组的间接吸收量分别为3-5微克、25-37微克和118-197微克。在1.09微克/平方厘米剂量组,血液中放射性物质最高浓度为0.001 ppm,在给药后24小时;在9.53微克/平方厘米剂量组,血液中放射性物质浓度为0.019 ppm和0.010 ppm,分别在给药后10小时和24小时;在90.2微克/平方厘米剂量组,血液中放射性物质浓度为0.041 ppm,在给药后24小时。在大鼠中,乙酰甲胺磷的直接吸收量在两个较低剂量平上呈比例增加,并在最高剂量平上似乎达到饱和。
The extent of absorption of acetamiprid was studied following application of 70% wettable powder containing [(14)C]acetamiprid (purity 97.5%) to the skin of male Crl: CD(SD)BR rats. The animals were approximately 8 weeks old upon arrival and weighed 176-216 g (preliminary phase) and 143-203 g (defi nitive phase). Target dose levels were 1, 10 and 100 ug/sq cm. Actual dose levels were 0.0136 mg/animal (1.09 ug/sq cm), 0.119 mg/animal (9.53 ug/sq cm) and 1.13 mg/animal (90.2 ug/sq cm). A preliminary phase, consisting of two groups of four animals each, was conducted to evaluate and establish test material application and skin washing techniques. In the preliminary phase, male rats were dermally dosed at two levels (0.0128 mg/animal and 1.26 mg/animal). In the definitive phase, three groups of 24 rats per group were dermally dosed with [(14)C]-acetamiprid at three dose levels. A control group of two rats received only the vehicle (1% carboxymethylcellulose aqueous solution). Urine and feces were collected from each rat. Immediately before sacrifice, the skin at the application site was washed. Four rats per time point from each dose group were sacrificed at 0.5, 1, 2, 4, 10 and 24 hours; the control rats were sacrifi ced at 24 hours. At sacrifice, blood was collected by cardiac puncture. Among the treated groups, the mean total recovery of radioactivity ranged from 96.6% to 102%, with most of the radioactivity (63.9-87.5%) in the skin wash. Radioactivity in the skin at the application site accounted for 10.2-32.2% of the applied radioactivity. Radioactivity in blood, excreta and carcasses accounted for less than 6.50% of the applied radioactivity. The amounts of radioactivity found in the blood, eliminated in the excreta and retained in the carcass were considered to result from direct dermal absorption of [(14)C]acetamiprid. Within groups, amounts of dermal absorption increased with increasing exposure time. The highest absorption was detected at the longest exposure time, 24 hours post-dosing, and accounted for 4.27% (0.581 ug), 6.34% (7.54 ug) and 2.82% (31.9 ug) for the 1.09, 9.53 and 90.2 ug/sq cm dose groups, respectively. The sum of direct absorption and amount of radioactivity remaining in the skin at the application site was considered to be indirect absorption. The amounts of indirect absorption were 3-5 ug, 25-37 ug and 118-197 ug for the 1.09, 9.53 and 90.2 ug/sq cm dose groups, respectively. The highest concentration of radioactivity in blood was 0.001 ppm for the 1.09 ug/sq cm dose group at 24 hours post-dosing, 0.019 ppm and 0.010 ppm for the 9.53 ug/sq cm dose group at 10 and 24 hours post-dosing, respectively, and 0.041 ppm for the 90.2 ug/sq cm dose group at 24 hours post-dosing. The amount of direct absorption of acetamiprid in rats was proportional at the two lower dose levels and appeared to reach saturation at the highest dose level.
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • 危险品标志:
    T
  • 安全说明:
    S45
  • 危险类别码:
    R57,R23/25
  • WGK Germany:
    3
  • 危险品运输编号:
    UN 2811
  • RTECS号:
    KJ4235200
  • 海关编码:
    2933399022
  • 包装等级:
    III

SDS

SDS:7fc2871745acec9da9a3824766167de2
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制备方法与用途

概述

啶虫咪是一种90年代问世的新一代超高效、内吸性杀虫剂,属于烟碱类化合物。它不仅具有触杀和胃毒作用,还能有效防治半翅目、鳞翅目、鞘翅目等各类害虫,表现出活性高、用量少、持效期长及速效性好等特点。尤其对有机氨基甲酸酯类以及拟除虫菊酯类杀虫剂产生严重抗性的害虫有特效。

化学性质

纯品为白色结晶状固体,熔点在101~103.3℃之间,蒸气压小于1.0×10^-6Pa(25℃)。啶虫咪易溶于丙酮甲醇乙醇二氯甲烷氯仿乙腈四氢呋喃,其在25℃时的溶解度为4200mg/L。

用途

啶虫脒是一种广谱杀虫剂,具有高效的杀虫效果。它对半翅目害虫(如蚜虫、叶蝉、粉虱等)、鳞翅目害虫(小菜蛾、潜蛾、小食心虫、纵卷叶螟)和鞘翅目害虫(天牛、猿叶虫)均有效,同时也能防治总翅目的害虫。由于其独特的杀虫机制,啶虫脒对有机类、氨基甲酸酯类及拟除虫菊酯类等农药产生抗性的害虫有特效。

此外,啶虫脒吡虫啉同属一类杀虫剂,但其杀虫谱更广,主要适用于防治黄瓜、苹果、柑桔和烟草上的蚜虫。由于其独特的药效机制,对有机氨基甲酸酯以及拟除虫菊酯类等农药品种产生抗性的害虫具有较好效果。

生产方法 2--5-甲基吡啶的制备

将烘干后的六次甲基四胺(23.5g)与乙腈(200mL)、2--5-甲基吡啶(27.4g,90.2%)混合后加热回流8小时。冷却过滤得57.8g白色固体,并进一步处理以获得最终产品。

N-基-N'-(2--5-吡啶甲基)乙脒的制备

在100mL反应瓶中加入2--5-甲基吡啶(15.89g,84.3%)和(52.3mol),室温下滴加N-基乙酰亚胺乙酯(11.64g,95%)。滴毕搅拌30分钟后加入乙醇(18.5mL),加热至78℃使其完全溶解。冷却析出白色固体,过滤干燥后得到最终产品。

啶虫脒的合成

在250mL反应瓶中加入N-基-N'-(2--5-吡啶甲基)乙脒(20.5g,85.27%)、氯仿(54.5mL)和甲丁基溴化铵(0.11g)。冷却至15℃时滴加硫酸二甲酯(11.6g)及50%NaOH溶液(8.4g),搅拌反应3小时。然后加入(33.6mL)与40%二甲胺溶液(0.33g),搅拌1小时后分层,进行氯仿萃取并蒸馏脱去氯仿。冷却至35℃滴加(37mL)以析出固体,并在冷却下过滤得到淡黄色晶体产品。

以上总收率为57%,含量大于85%。其他制备方法包括N-氰基-N'-甲基乙脒与2--5-甲基吡啶反应或由N-基乙亚胺酸酯和N-甲基-2--5-吡啶甲基胺反应制得。

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

反应信息

  • 作为产物:
    描述:
    氰基乙酯1-(6-氯-3-嘧啶基)-N-甲基甲胺 1.4 HCl 反应 9.0h, 以96%的产率得到啶虫脒
    参考文献:
    名称:
    啶虫脒的生产工艺
    摘要:
    本发明公开了啶虫脒的生产工艺。包括以下步骤:(1)胺化:将溶剂加入胺化反应釜,降温,并向溶剂中通入一定量的一甲胺气体,并控制一定的温度条件下,向反应釜内加入2‑氯‑5‑氯甲基吡啶,反应毕,升温排胺,再降温过滤,滤出一甲胺盐酸盐,滤液脱降溶剂后转入下一步,(2)缩合:将上一步物料控制在一定的温度条件下,滴加氰基乙酯,反应毕,降温,过滤,得啶虫脒,干燥,滤液蒸馏回收乙醇。本发明胺化反应收率高,后处理简单,不产生废水,缩合反应简单,产率高,无废水产生。
    公开号:
    CN107501172A
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文献信息

  • 一种啶虫脒的生产工艺
    申请人:青岛恒宁生物科技有限公司
    公开号:CN111808018B
    公开(公告)日:2022-06-14
    本发明涉及一种啶虫脒的生产工艺,具体公开了以一甲胺和2‑‑5‑甲基吡啶为反应物制得胺化反应后再与N‑基乙亚酸酯反应制得啶虫脒的制备路线。本发明的技术方案通过使甲胺溶液第一时间与2‑‑5‑甲基吡啶溶液接触并升温反应能够减少副产物生成,能有效提高反应效率、并能缩短反应时间;实现了在层十次套用的情况下仍有极佳的收率和含量;无需额外加入缚酸剂,产品后处理步骤简化,废盐废产生量少,产品产率高、纯度高,符合绿色环保的要求。
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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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同类化合物

(S)-氨氯地平-d4 (R,S)-可替宁N-氧化物-甲基-d3 (R)-(+)-2,2'',6,6''-四甲氧基-4,4''-双(二苯基膦基)-3,3''-联吡啶(1,5-环辛二烯)铑(I)四氟硼酸盐 (R)-N'-亚硝基尼古丁 (R)-DRF053二盐酸盐 (5E)-5-[(2,5-二甲基-1-吡啶-3-基-吡咯-3-基)亚甲基]-2-亚磺酰基-1,3-噻唑烷-4-酮 (5-溴-3-吡啶基)[4-(1-吡咯烷基)-1-哌啶基]甲酮 (5-氨基-6-氰基-7-甲基[1,2]噻唑并[4,5-b]吡啶-3-甲酰胺) (2S,2'S)-(-)-[N,N'-双(2-吡啶基甲基]-2,2'-联吡咯烷双(乙腈)铁(II)六氟锑酸盐 (2S)-2-[[[9-丙-2-基-6-[(4-吡啶-2-基苯基)甲基氨基]嘌呤-2-基]氨基]丁-1-醇 (2R,2''R)-(+)-[N,N''-双(2-吡啶基甲基)]-2,2''-联吡咯烷四盐酸盐 (1'R,2'S)-尼古丁1,1'-Di-N-氧化物 黄色素-37 麦斯明-D4 麦司明 麝香吡啶 鲁非罗尼 鲁卡他胺 高氯酸N-甲基甲基吡啶正离子 高氯酸,吡啶 高奎宁酸 马来酸溴苯那敏 马来酸氯苯那敏-D6 马来酸左氨氯地平 顺式-双(异硫氰基)(2,2'-联吡啶基-4,4'-二羧基)(4,4'-二-壬基-2'-联吡啶基)钌(II) 顺式-二氯二(4-氯吡啶)铂 顺式-二(2,2'-联吡啶)二氯铬氯化物 顺式-1-(4-甲氧基苄基)-3-羟基-5-(3-吡啶)-2-吡咯烷酮 顺-双(2,2-二吡啶)二氯化钌(II) 水合物 顺-双(2,2'-二吡啶基)二氯化钌(II)二水合物 顺-二氯二(吡啶)铂(II) 顺-二(2,2'-联吡啶)二氯化钌(II)二水合物 韦德伊斯试剂 非那吡啶 非洛地平杂质C 非洛地平 非戈替尼 非布索坦杂质66 非尼拉朵 非尼拉敏 雷索替丁 阿雷地平 阿瑞洛莫 阿扎那韦中间体 阿培利司N-6 阿伐曲波帕杂质40 间硝苯地平 间-硝苯地平 镉,二碘四(4-甲基吡啶)- 锌,二溴二[4-吡啶羧硫代酸(2-吡啶基亚甲基)酰肼]-