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敌草隆 | 330-54-1

中文名称
敌草隆
中文别名
3-(3,4-二氯苯)-1,1-二甲基脲;3-(3,4-二氯苯基)-1,1-二甲基脲;地草净;3-(3,4-二氯苯基)-N,N-二甲基脲;N-(3,4-二氯苯基)-N',N'-二甲基脲;N-(3,4-二氯苯基)-N,N'-二甲基脲;N'-(3,4-二氯苯基)-N,N-二甲基脲
英文名称
DCMU
英文别名
diuron;3-(3,4-dichlorophenyl)-1,1-dimethylurea
敌草隆化学式
CAS
330-54-1
化学式
C9H10Cl2N2O
mdl
MFCD00018136
分子量
233.097
InChiKey
XMTQQYYKAHVGBJ-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:
    158-159°C
  • 沸点:
    180-190°C
  • 密度:
    1.48
  • 闪点:
    180-190°C
  • 溶解度:
    在丙酮中:27 °C 时为 5.3 wt%(Meister,1988)。
  • 暴露限值:
    NIOSH REL: TWA 10 mg/m3.
  • LogP:
    2.84-2.89 at 20℃ and pH4.03-9
  • 物理描述:
    Diuron is a white crystalline solid. It is a wettable powder. The primary hazard is the threat to the environment. Immediate steps should be taken to limit its spread to the environment. It can cause illness by inhalation, skin absorption and/or ingestion. It is used as a herbicide.
  • 颜色/状态:
    White, crystalline solid
  • 气味:
    Odorless
  • 蒸汽压力:
    8.25X10-9 mm Hg (1.1X10-3 mPa) at 25 °C
  • 稳定性/保质期:
    高浓度时,该物质会对眼睛和黏膜产生刺激作用。
  • 分解:
    Diuron, stable under normal conditions, decomposed on heating to 180 to 190 °C giving dimethylamine and 3,4-dichlorophenyl isocyanate.
  • 腐蚀性:
    Non-corrosive
  • 碰撞截面:
    153.32 Ų [M+H]+ [CCS Type: DT, Method: stepped-field]
  • 保留指数:
    1721.3;1718.5

计算性质

  • 辛醇/水分配系数(LogP):
    2.7
  • 重原子数:
    14
  • 可旋转键数:
    1
  • 环数:
    1.0
  • sp3杂化的碳原子比例:
    0.222
  • 拓扑面积:
    32.3
  • 氢给体数:
    1
  • 氢受体数:
    1

ADMET

代谢
迪uron在大鼠高饮食水平下对大鼠膀胱具有致癌性。迪uron的拟议作用模式(MOA)为尿路上皮细胞毒性和坏死,随后是再生的尿路上皮增生。迪uron诱导的尿路上皮细胞毒性不是由于尿液固体。迪uron被广泛代谢,在大鼠中,N-(3,4-二氯苯基)尿素(DCPU)和4,5-二氯-2-羟基苯基尿素(2-OH-DCPU)是主要的尿代谢物;较少的代谢物包括N-(3,4-二氯苯基)-3-甲基尿素(DCPMU)和微量的3,4-二氯苯胺(DCA)。在人类中,DCPMU和DCPU在一例产品滥用后在尿液中被发现。为了帮助阐明迪uron的MOA并评估负责膀胱上皮毒性的代谢物,我们研究了用2500 ppm迪uron处理的雄性Wistar大鼠尿液中代谢物的浓度,代谢物的体外尿路上皮细胞毒性及其基因表达谱。在大鼠尿液中发现的DCPU浓度远高于体外IC50,并且比其他测试的代谢物引起更多的基因表达改变。2-OH-DCPU在尿液中的浓度大约是体外IC50的一半,而DCPMU和DCA在尿液中的浓度远低于IC50。对于大鼠膀胱的迪uron诱导的MOA,我们建议DCPU是主要负责尿路上皮细胞毒性的初级代谢物,2-OH-DCPU也有一定的贡献。本研究支持大鼠膀胱中迪uron诱导的膀胱效应的MOA,包括代谢为DCPU(以及较小程度的2-OH-DCPU),在尿液中浓缩和排泄,尿路上皮细胞毒性和再生性增殖。
Diuron is carcinogenic to the rat urinary bladder at high dietary levels. The proposed mode of action (MOA) for diuron is urothelial cytotoxicity and necrosis followed by regenerative urothelial hyperplasia. Diuron-induced urothelial cytotoxicity is not due to urinary solids. Diuron is extensively metabolized, and in rats, N-(3,4-dichlorophenyl)urea (DCPU) and 4,5-dichloro-2-hydroxyphenyl urea (2-OH-DCPU) were the predominant urinary metabolites; lesser metabolites included N-(3,4-dichlorophenyl)-3-methylurea (DCPMU) and trace levels of 3,4-dichloroaniline (DCA). In humans, DCPMU and DCPU have been found in the urine after a case of product abuse. To aid in elucidating the MOA of diuronand to evaluate the metabolites that are responsible for the diuron toxicity in the bladder epithelium, we investigated the urinary concentrations of metabolites in male Wistar rats treated with 2500 ppm of diuron, the urothelial cytotoxicity in vitro of the metabolites and their gene expression profiles. DCPU was found in rat urine at concentrations substantially greater than the in vitro IC50 and induced more gene expression alterations than the other metabolites tested. 2-OH-DCPU was present in urine at a concentration approximately half of the in vitro IC50, whereas DCPMU and DCA were present in urine at concentrations well below the IC50. For the diuron-induced MOA for the rat bladder, we suggest that DCPU is the primary metabolite responsible for the urothelial cytotoxicity with some contribution also by 2-OH-DCPU. This study supports a MOA for diuron-induced bladder effects in rats consisting of metabolism to DCPU (and 2-OH-DCPU to a lesser extent), concentration and excretion in urine, urothelial cytotoxicity, and regenerative proliferation.
来源:Hazardous Substances Data Bank (HSDB)
代谢
这项研究旨在调查敌草隆的生物转化和处置...。通过液相色谱/质谱法在人肝脏匀浆和包括人在内的七种哺乳动物肝脏微粒体中检测到的唯一代谢途径是末端的氮原子去甲基化。没有观察到其他I相或II相代谢物。基于固有清除率(V(max)/K(m))的肝脏微粒体形成N-去甲基敌草隆的排名顺序是狗>猴子>兔子>小鼠>人类>小型猪>大鼠。所有测试的重组人细胞色素P450(P450s)催化了敌草隆N-去甲基化,活性最高的是CYP1A1、CYP1A2、CYP2C19和CYP2D6。根据人肝脏微粒体中P450酶的平均含量,人CYP1A2、CYP2C19和CYP3A4对肝脏敌草隆N-去甲基化的相对贡献分别约为60%、14%和13%。敌草隆仅对CYP1A1/2(IC(50) 4 uM)有相对较强的抑制作用...
This study was designed to investigate diuron biotransformation and disposition ... . The only metabolic pathway detected by liquid chromatography/mass spectometry in human liver homogenates and seven types of mammalian liver microsomes including human was demethylation at the terminal nitrogen atom. No other phase I or phase II metabolites were observed. The rank order of N-demethyldiuron formation in liver microsomes based on intrinsic clearance (V(max)/K(m)) was dog > monkey > rabbit > mouse > human > minipig > rat. All tested recombinant human cytochrome P450s (P450s) catalyzed diuron N-demethylation and the highest activities were possessed by CYP1A1, CYP1A2, CYP2C19, and CYP2D6. Relative contributions of human CYP1A2, CYP2C19, and CYP3A4 to hepatic diuron N-demethylation, based on average abundances of P450 enzymes in human liver microsomes, were approximately 60, 14, and 13%, respectively. Diuron inhibited relatively potently only CYP1A1/2 (IC(50) 4 uM)...
来源:Hazardous Substances Data Bank (HSDB)
代谢
3,4-二氯苯胺(3,4-DCA)是敌草隆的一种代谢物,也是另外两种农药,利草隆和丙草隆的代谢物。然而,美国环保署的代谢评估审查委员会(MARC)得出结论,不应将3,4-DCA的残留物累积起来进行敌草隆、利草隆和丙草隆的风险评估,因为3,4-DCA是丙草隆的一个重要残留物关注点,但对于敌草隆或利草隆来说,并不是一个本身需要关注的残留物。尽管将敌草隆所有残留物转化为3,4-DCA作为一种便利的分析方法,但在任何代谢或水解研究中,3,4-DCA并不是一个显著的残留物。
3,4-dichloroaniline (3,4-DCA) is a metabolite of diuron as well as two other pesticides, linuron and propanil. However, EPA's Metabolism Assessment Review Committee (MARC) concluded that residues of 3,4-DCA should not be aggregated for the diuron, linuron, and propanil risk assessments because 3,4-DCA is significant residue of concern for propanil, but is not a residue of concern per se for diuron or linuron. Although the analytical method for quantifying residues of concern from diuron converts all residues to 3,4-DCA as a convenience, 3,4-DCA was not a significant residue in any metabolism or hydrolysis study.
来源:Hazardous Substances Data Bank (HSDB)
代谢
在一个案例中,一名女性因敌草隆中毒,从尿液中分离出了1-(3,4-二氯苯基)-3,3-二甲基脲,以及3-氨基-1,2,4-三唑、1-(3,4-二氯苯基)-3-甲基脲和1-(3,4-二氯苯基)脲。尿液中可能还含有少量的3,4-二氯苯胺,但没有未改变的除草剂。
... In ... a woman poisoned with Diuron, 1-(3,4-dichlorophenyl)-3,3-dimethylurea, plus 3-amino-1,2,4-triazole, 1-(3,4-dichlorophenyl)-3-methylurea, and 1-(3,4-dichlorophenyl)urea were isolated from urine. The urine probably contained small amt of 3,4-dichloroaniline, but no unchanged herbicide.
来源:Hazardous Substances Data Bank (HSDB)
代谢
Diuron has known human metabolites that include N-demethyldiuron. 迪uron已知的人类代谢物包括N-去甲基迪uron。
Diuron has known human metabolites that include N-demethyldiuron.
来源:NORMAN Suspect List Exchange
毒理性
  • 毒性总结
尿素是一种固体。尿素是一种光合作用抑制剂,主要用于非作物区域的杂草控制。它还被用于甘蔗、柑橘、菠萝、棉花、芦笋和温带气候的树木和灌木果实中萌发的阔叶和禾本科杂草的选择性控制。它也用作土壤消毒剂。人体研究:它可能会刺激皮肤、眼睛或鼻子。尿素在体外对人类细胞具有细胞毒性,氧化应激有助于其毒性。自杀未遂者服用尿素和氨基嘧啶制剂后没有出现中毒迹象。动物研究:它对兔子的眼睛和粘膜有刺激性,但50%的水糊对豚鼠的完整皮肤无刺激性。在20周接触后,高饮食水平的尿素(2500 ppm)可诱导大鼠膀胱增生。还指出,在大鼠暴露于高剂量尿素(1250和2500 ppm)时,与芳基烃受体信号传导相关的基因上调。在2年的生物分析中,高剂量(2500 ppm)的大鼠接触尿素,膀胱癌的发病率很高,肾盂乳头状瘤和肾癌的发病率很低。这种除草剂在大鼠尿路上皮中的作用机制是由代谢激活产生代谢物,这些代谢物在尿液中排出并浓缩,导致细胞毒性,尿路上皮细胞坏死和剥脱,再生性增生,最终导致肿瘤。在2500 ppm接触2年后,大鼠和狗的生长都受到了抑制,出现了轻微的贫血,异常色素的存在,红细胞生成的增加和脾脏的含铁血黄素沉着。一些大鼠出现脾脏肿大,狗出现肝脏肿大。在雄性后代中,尿素在750 ppm时诱导雄性后代毒性,但这些改变不是永久性的,因为在大鼠成年后没有生殖系统改变。在三代大鼠研究中,125 ppm的饮食浓度对繁殖没有不利影响。在大鼠发育研究中,在500 mg/kg时,平均胎儿体重降低,250 mg/kg时增加了异常胎儿的数量。在斑马鱼研究中,行为的变化,如胚胎的自发卷曲运动的减少和幼虫的趋触性的降低,对尿素来说是非常明显的。在体外试验中,尿素具有干扰内分泌的潜力。在Salmonella菌株TA1535、TA97、TA98和TA100中,有代谢激活和无激活的尿素分别为0、10、25、50、100或250 ug/板和0、0.5、1、2.5、5或10 ug/板。没有报告反转率的增加。TA1535的细胞毒性。生态毒性研究:尿素的代谢物具有潜在的雌激素效应,可能是通过增强雌二醇生物合成和加速尼罗罗非鱼雌性的卵巢发育。进一步的研究表明,尿素转化为活性代谢物改变了中枢神经系统的信号传导途径,这可能会影响鱼类对雄激素和应激反应以及社会优势、生长和繁殖所必需的行为。在牡蛎性腺发生阶段经常遇到的尿素浓度可以影响下一代,并可能导致适应性的干扰。尿素对牡蛎繁殖的负面影响是通过诱导DNA的结构和功能修饰来增强的。在牡蛎中,亲代尿素的暴露对其后代的DNA甲基化模式有影响。利用循环多室藻类、大型蚤、细菌微生态系统对除草剂尿素的效果进行了评估。0.2 ppm的尿素对大型蚤的种群是致命的。尿素对新生动物有影响,因此这些动物没有成熟。尿素与澳大利亚东北部麦凯地区三个相邻河口内优势红树林、Avicennia marina(Forsk.)Vierh. var. eucalyptifolia(Val.)N.C.杜克(Avicenniaceae)的严重和广泛死亡有关,其冠层状况较差,幼苗健康下降。这种死亡的可能后果包括沿海水质下降,浊度增加,营养物和沉积物沉积,以及进一步分散有毒化学品。
IDENTIFICATION AND USE: Diuron is a solid. Diuron is a photosynthesis inhibitor that is used mainly for general weed control on noncrop areas. It has also been used in the selective control of germinating broadleaf and grass weeds in sugarcane, citrus, pineapples, cotton, asparagus, and temperate climate tree and bush fruits. It is also used as a soil sterilant. HUMAN STUDIES: It may irritate the skin, eyes, or nose. Diuron is cytotoxic in vitro in human cells and oxidative stress contributes to its toxicity. The victim of a suicide attempt did not show signs of intoxication after ingesting diuron and amitrole preparation. ANIMAL STUDIES: It caused irritation to eyes and mucous membranes of rabbits but a 50% water paste was not irritating to intact skin of guinea pigs. Diuron at high dietary levels (2500 ppm) induces rat urinary bladder hyperplasia after 20 weeks of exposure. It was also noted that genes related to the aryl hydrocarbon receptor signaling were upregulated in rats exposed to the diuron high dose (1250 and 2500 ppm). Diuron induced high incidences of urinary bladder carcinomas and low incidences of kidney pelvis papillomas and carcinomas in rats exposed to high doses (2500 ppm) in a 2-year bioassay. The proposed rat urothelial mode of action for this herbicide consists of metabolic activation to metabolites that are excreted and concentrated in the urine, leading to cytotoxicity, urothelial cell necrosis and exfoliation, regenerative hyperplasia, and eventually tumors. At 2500 ppm for 2 years, both rats and dogs showed growth retardation, slight anemia, presence of abnormal pigment, increased erythropoiesis, and splenic hemosiderosis. Some rats showed splenic enlargement, and dogs showed liver enlargement. Diuron at 750 ppm induced male offspring toxicity but these alterations were not permanent, as evidenced by absence of reproductive-system alterations in adult rats. A dietary concentration of 125 ppm did not adversely affect reproduction in a three-generation rat study. In rat developmental studies, reduction in mean fetal weight at 500 mg/kg was noted, and 250 mg/kg increased the number of anomalous fetuses. In zebrafish studies, changes in behavior, such as decrease in spontaneous coiling movements of embryos and reduction of thigmotaxis in larvae, were pronounced for diuron. Diuron was active in vitro when tested for endocrine disrupting potential. Diuron was tested in Salmonella strains TA1535, TA97, TA98, and TA100 with metabolic activation at 0, 10, 25, 50, 100, or 250 ug/plate and without activation at 0, 0.5, 1, 2.5, 5, or 10 ug/plate. No increase in reversion rate reported. Cytotoxicity with TA1535. ECOTOXICITY STUDIES: Diuron metabolites had estrogenic effects potentially mediated through enhanced estradiol biosynthesis and accelerated the ovarian development of Nile tilapia females. Further studies indicated that biotransformation of diuron to active metabolites alter signaling pathways of the CNS which may impact androgen and the stress response as well as behavior necessary for social dominance, growth, and reproduction in fish. Exposure to a concentration of diuron that is frequently encountered in the field during the oyster's gametogenesis stage can impact the next generation and may result in fitness disturbance. Negative effect of diuron on oyster reproduction potentiated by inducing both structural and functional modifications of the DNA. Further in oysters, parental diuron exposure has an impact on the DNA methylation pattern of its progeny. The effect of the herbicide diuron was evaluated using a recycling multi compartment algae, Daphnia magna, bacteria microecosystem. A concentration of 0.2 ppm diuron was lethal to the Daphnia magna population. Diuron had an effect on newly born animals, and therefore these did not mature. Diuron was correlated with severe and widespread dieback of the dominant mangrove, Avicennia marina (Forsk.) Vierh. var. eucalyptifolia (Val.) N.C. Duke (Avicenniaceae), its reduced canopy condition, and declines in seedling health within three neighbouring estuaries in the Mackay region of NE Australia. The likely consequences of such dieback included declines in coastal water quality with increased turbidity, nutrients and sediment deposition, as well as further dispersal of the toxic chemicals.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 毒性总结
敌草隆据报道能够与雄激素受体结合。这表明敌草隆可能会阻断这些受体,导致对生殖系统的毒性。
Diuron has been reported to bind to androgen receptors. This suggests that diuron may block the receptors and result in the toxicity on the reproductive system.
来源:Toxin and Toxin Target Database (T3DB)
毒理性
  • 致癌性证据
癌症分类:已知/很可能/对人类致癌/
Cancer Classification: Known/ Likely /to be Carcinogenic to Humans/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌性证据
A4:不能归类为人类致癌物。
A4: Not classifiable as a human carcinogen.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 致癌物分类
未列在IARC(国际癌症研究机构)的名单上。
Not listed by IARC.
来源:Toxin and Toxin Target Database (T3DB)
吸收、分配和排泄
敌草隆在大鼠和狗中通过胃肠道被迅速吸收。组织中敌草隆的水平与剂量呈正相关。没有明显的组织储存敌草隆的迹象...敌草隆也部分以未改变的形式通过粪便和尿液排出。
Diuron is readily absorbed through the gastrointestinal tract in rats and dogs. Tissue level of diuron were positively correlated with dosage. No apparent storage of diuron in tissues was noted ... Diuron is also partially excreted unchanged in feces and urine.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
根对溶液中(14)C-Diuron的吸收进行研究时,发现营养溶液中存在少量的一甲基和去甲基衍生物,这些溶液来自大豆、燕麦和玉米顶部的培养。
Root uptake of (14)C-Diuron from solution was studied. ... small amount of the monomethyl and demethylated derivatives were found in nutrient solution from ... soybeans, ... oat, and corn tops.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
敌草隆主要通过根系吸收;通过叶片和茎部吸收较少。在木质部中,其主要向上转移。
Diuron is most readily absorbed through the root system; less so through foliage & stems. Translocation is primarily upward in xylem.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
敌草隆以0-550 ppm的浓度水平喂养了五头奶牛。大约50%的敌草隆在尿液中检出,10%在粪便中,5%在血液中。牛奶样本中未检测到敌草隆。尿液和血液中敌草隆代谢物浓度之间存在正相关关系,而尿液和粪便之间存在负相关关系。这表明剩余的敌草隆被身体吸收或降解为无法检测到的代谢物。
Diuron was fed to five dairy cows at 0-550 ppm concentration levels. About 50% of the diuron was detected in the urine, 10% in the feces and 5% in the blood. Milk samples did not contain diuron. A positive correlation was noted between the concn of diuron products in urine and blood and a negative correlation between urine and feces. It is suggested that the remaining diuron is absorbed in the body or degraded into undetectable metabolites.
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • 职业暴露等级:
    B
  • 职业暴露限值:
    TWA: 10 mg/m3
  • TSCA:
    Yes
  • 危险等级:
    9
  • 危险品标志:
    O,C
  • 安全说明:
    S13,S2,S22,S23,S26,S36/37,S37,S46,S60,S61
  • 危险类别码:
    R22,R40,R48/22,R50/53
  • WGK Germany:
    3
  • 海关编码:
    2924299032
  • 危险品运输编号:
    UN 3077 9/PG 3
  • 危险类别:
    9
  • RTECS号:
    YS8925000
  • 包装等级:
    III
  • 储存条件:
    库房应保持通风、低温和干燥,并需与其他氧化剂、碱类及食品添加剂分开存放。

SDS

SDS:bc034759fb6a7b9642987401288f49d9
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国标编号: 61904
CAS: 330-54-1
中文名称: 敌草隆
英文名称: Diuron;N-(3,4-Dichlorophenyl)-N',N'-dimethylurea
别 名: N-(3,4-二氯苯基)-N',N'-二甲基脲
分子式: C 9 H 10 Cl 2 N 2 O
分子量: 233.10
熔 点: 158~159℃ 沸点:180
密 度: 相对密度(空气=1)8.04
蒸汽压: 50℃
溶解性: 微溶于水、烃类
稳定性: 稳定
外观与性状: 纯品为白色无臭晶体
危险标记: 15(有害品,远离食品)
用 途: 用于除草


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:本品属低毒除草剂。误服会中毒。对粘膜和上呼吸道有刺激作用。
二、毒理学资料及环境行为
毒性:属低毒类。
急性毒性:LD 50 3400mg/kg(大鼠经口);人经口500mg/kg,最小致死剂量。
亚急性和慢性毒性:大鼠经口5000ppm×90日,未引起死亡,但体重下降,红细胞减少。
危险特性:遇明火、高热可燃。受高热分解,放出有毒的烟气。
燃烧(分解)产物:一氧化碳、二氧化碳、氮氧化物、氯化氢。

3.现场应急监测方法:

4.实验室监测方法:

气相色谱法《现代环境监测方法》(水、粮食和土壤)张晓林等主编

5.环境标准:
前苏联(1975) 车间空气中有害物质的最高容许浓度 5mg/m 3
前苏联(1978) 环境空气中最高容许浓度 0.05mg/m 3
前苏联(1978) 渔业用水中最高容许浓度 1.5μg/L
前苏联(1978) 地面水中有害有机物的最大允许浓度 1.0mg/L
前苏联(1975) 污水中有机物最大允许浓度 10mg/L
联合国规划署(1974) 保护水生生物淡水中农药的最大允许浓度 1.6μg/L

6.应急处理处置方法:
一、泄漏应急处理
隔离泄漏污染区,周围设警告标志,建议应急处理人员戴好口罩、护目镜,穿工作服。小心扫起,置于袋中转移至安全场所。也可以用大量水冲洗,经稀释的洗水放入废水系统。如大量泄漏,收集回收或无害处理后废弃。
二、防护措施
呼吸系统防护:生产操作或农业使用时,佩带防毒口罩。必要时佩戴防毒面具。
眼睛防护:必要时可采用安全面罩。
身体防护:穿紧袖工作服,长筒胶鞋。
手防护:必要时戴防护手套。
其它:工作现场严禁吸烟、进食和饮水。工作后,淋浴更衣。注意个人清洁卫生。
三、急救措施
皮肤接触:用肥皂水及清水彻底冲洗。就医。
眼睛接触:拉开眼睑,用流动清水冲洗15分钟。就医。
吸入:脱离现场至空气新鲜处。就医。
食入:误服者,饮适量温水,催吐。就医。
灭火方法:泡沫、干粉、砂土、水。






制备方法与用途

取代脲类除草剂敌草隆

敌草隆与灭草隆、利谷隆是三种常用的取代脲类除草剂,其中敌草隆属内吸传导型除草剂,具有一定的触杀活性。该药剂可被植物的根和叶吸收,以根系吸收为主,杂草根系吸收后,通过传送到地上叶片中,并沿着叶脉向周围传播,抑制光合作用的希尔反应,导致叶片失绿、叶尖和叶缘褪色,进而发黄枯死。在低剂量情况下,敌草隆可作为选择性除草剂使用;高剂量下则为灭生性除草剂。

适用范围:

  • 适用于水稻、棉花、玉米、甘蔗及果、胶、桑、茶园等作物。
  • 防治稗草、马唐、狗尾草、蓼、藜及眼子菜等杂草。

敌草隆对人畜低毒,大鼠急性口服LD50为3400毫克/公斤。高浓度时会对眼睛和黏膜产生刺激作用。该药剂在种子萌发及根系方面影响不大,但药效期可维持60天以上。

使用注意事项:
  1. 敌草隆对麦苗有毒杀作用,应避免在麦田使用。
  2. 在茶、桑、果园中宜采用毒土法施用,以防产生药害。
  3. 由于敌草隆对棉花选择性较差,应在棉田谨慎使用。
  4. 施用时需注意土壤水分和温度条件。
生产方法:
  1. 氯化:将熔融脱水的对氯硝基苯与适量催化剂无水FeCl₃混合后,在100~105℃下通氯,反应8~9小时制得3,4-二氯硝基苯。
  2. 还原:将上述硝基化合物还原,制得3,4-二氯苯胺。国内还采用电解质中铁粉和水还原的方法生产。
  3. 酯化:将甲苯溶液于0℃通光气饱和后滴加3,4-二氯苯胺,在0~10℃下进行反应。然后加入40%二甲胺水溶液(酯胺比为1:1.05),控制温度在34℃左右,反应2小时。
  4. 加成:将上述产物与溶剂甲苯混合冷却至20℃以下后,加入40%的二甲胺水溶液,反应生成敌草隆。
类别
  • 农药
毒性分级
  • 中毒
急性毒性
  • 口服:大鼠LD₅₀: 1017毫克/公斤;小鼠LD₅₀: 500毫克/公斤
燃烧危险特性
  • 可燃,燃烧时产生有毒氮氧化物和氯化物烟雾。
储运及灭火方法
  • 库房应通风、低温干燥。
  • 避免与氧化剂、碱类、食品添加剂等分开存放。
  • 灭火剂:泡沫、二氧化碳、砂土或水。

职业暴露限值:

  • 时间加权平均容许浓度(TWA):10毫克/立方米
  • 短时间接触容许浓度(STEL):20毫克/立方米

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
    • 1
    • 2

反应信息

  • 作为反应物:
    描述:
    敌草隆氧气 作用下, 生成 硫丙磷
    参考文献:
    名称:
    Estimation of dioxin emission from fires in chemicals
    摘要:
    The formation of the 17 toxic 2,3,7,8-substituted PCDDs and PCDFs during combustion of selected chemicals were measured by high-resolution GC/MS. The 16 chemicals studied were commonly used chlorinated pesticides, industrial chemicals, and PVC. In a series of experiments carried out in a DIN 53,436 furnace, 2.5 g of these compounds were burned at 500 degrees C and 900 degrees C, respectively. The resultant yields ranged from 740 ng ITEQ/g for pentachlorophenol, to below 0.01 ng ITEQ/g for PVC and dichlobenil. The results show that some chemicals generate PCDD/F in very high possibly dangerous - amounts during burning, whereas others generate insignificant amounts. The influence of scale were studied for chlorobenzene and 4-chloro-3-nitro-benzoic acid in additional experiments, carried out in a cone calorimeter burning 20 g substance, and in ISO 9705 room test burning about 50 kg. A good agreement between the results for large and small scale indicated that formation of PCCD/F during a fire may be estimated from laboratory experiments. This suggest laboratory test may be used to screen for chemicals posing a hazard for release of PCDD/F during fires. (C) 1999 Elsevier Science Ltd. All rights reserved.
    DOI:
    10.1016/s0045-6535(99)00231-3
  • 作为产物:
    描述:
    3-(3,4-二氯苯基)-1,1-二甲基硫脲sodium chlorite 作用下, 反应 2.0h, 以72%的产率得到敌草隆
    参考文献:
    名称:
    New Synthetic Strategy for Urea Herbicides
    摘要:
    This work describes an effective and a safe procedure for the preparation of commercially applicable trisubstituted ureas derived from their thio analogues which result from the thiuram disulfides in quantitative yields.
    DOI:
    10.1080/00397919708003392
  • 作为试剂:
    描述:
    2-(trimethylsilyl)ethyl β-D-glucopyranoside 在 potassium fluoride 、 N-碘代丁二酰亚胺偶氮二异丁腈敌草隆三正丁基氢锡silver trifluoromethanesulfonate对甲苯磺酸silver nitrate溶剂黄146三乙胺三氟乙酸2,3-二氯-5,6-二氰基-1,4-苯醌 作用下, 以 二氯甲烷甲苯乙腈 为溶剂, 反应 60.67h, 生成 2-O-benzoyl-3-deoxy-6-O-(p-methoxybenzoyl)-4-O-<6-O-acetyl-2,3-di-O-benzoyl-4-O-(2,3,4,6-tetra-O-acetyl-α-D-galactopyranosyl)-β-D-galactopyranosyl>-β-D-ribo-hexopyranosyl trichloroacetamidate
    参考文献:
    名称:
    Synthesis of Double-Chain Bis-Sulfone Neoglycolipids of the 2-, 3-, and 6-Deoxyglobotrioses
    摘要:
    Partially protected 2-(trimethylsilyl)ethyl 2- and 3-deoxyglucosides and 6-deoxylactoside were synthesised via various routes and glycosylated with galabiosyl and galactosyl donors to give the corresponding deoxytrisaccharides. Removal of the protecting groups gave the 2-(trimethylsilyl)ethyl 2-, 3-, and 6-deoxyglobotriosides. Transformation of the protected trisaccharides into trichloroacetimidates, via the corresponding hemiacetals, proceeded in similar to 80% overall yield. Glycosylation of 3-(hexadecylsulfonyl)-2-[(hexadecylsulfonyl)methyl]propanol with the trisaccharidic trichloroacetimidates, in 72-79% yield, followed by removal of protecting groups, gave the title neoglycolipids.
    DOI:
    10.1021/jo951914k
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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] 3-[(HYDRAZONO)METHYL]-N-(TETRAZOL-5-YL)-BENZAMIDE AND 3-[(HYDRAZONO)METHYL]-N-(1,3,4-OXADIAZOL-2-YL)-BENZAMIDE DERIVATIVES AS HERBICIDES<br/>[FR] DÉRIVÉS DE 3-[(HYDRAZONO))MÉTHYL]-N-(TÉTRAZOL-5-YL)-BENZAMIDE ET DE 3-[(HYDRAZONO)MÉTHYL]-N-(1,3,4-OXADIAZOL-2-YL)-BENZAMIDE UTILISÉS EN TANT QU'HERBICIDES
    申请人:SYNGENTA CROP PROTECTION AG
    公开号:WO2021013969A1
    公开(公告)日:2021-01-28
    The present invention related to compounds of Formula (I): or an agronomically acceptable salt thereof, wherein Q, R2, R3, R4, R5 and R6 are as described herein. The invention further relates to compositions comprising said compounds, to methods of controlling weeds using said compositions, and to the use of compounds of Formula (I) as a herbicide.
    本发明涉及以下式(I)的化合物或其农业上可接受的盐,其中Q、R2、R3、R4、R5和R6如本文所述。该发明还涉及包含所述化合物的组合物,使用这些组合物控制杂草的方法,以及将式(I)的化合物用作除草剂的用途。
  • [EN] INSECTICIDAL TRIAZINONE DERIVATIVES<br/>[FR] DÉRIVÉS DE TRIAZINONE INSECTICIDES
    申请人:SYNGENTA PARTICIPATIONS AG
    公开号:WO2013079350A1
    公开(公告)日:2013-06-06
    Compounds of the formula (I) or (I'), wherein the substituents are as defined in claim 1, are useful as pesticides.
    式(I)或(I')的化合物,其中取代基如权利要求1所定义的那样,可用作杀虫剂。
  • Inhibitors of histone deacetylase
    申请人:——
    公开号:US20020177594A1
    公开(公告)日:2002-11-28
    Compounds having the formula 1 or therapeutically acceptable salts thereof, are histone deacetylase (HDAC) inhibitors. Preparation of the compounds, compositions containing the compounds, and treatment of diseases using the compounds are disclosed.
    具有以下化学式的化合物或其治疗上可接受的盐是组蛋白去乙酰化酶(HDAC)抑制剂。本文揭示了该化合物的制备、含有该化合物的组合物以及使用该化合物治疗疾病的方法。
  • [EN] SQUALENE COMPOUNDS AS MODULATORS OF LDL-RECEPTOR EXPRESSION<br/>[FR] COMPOSÉS DE SQUALÈNE EN TANT QUE MODULATEURS DE L'EXPRESSION DU RÉCEPTEUR LDL
    申请人:ISIS INNOVATION
    公开号:WO2016042318A1
    公开(公告)日:2016-03-24
    The present invention relates to compounds that modify low density lipoprotein receptor (LDLR) expression. The compounds have the structural formula I shown below: wherein m, R1, n, R2 and R3 are each as defined herein. The present invention also relates to processes for the preparation of these compounds, to pharmaceutical compositions comprising them, and to their use in the treatment of diseases or disorders associated with elevated levels of low density lipoprotein cholesterol (LDL-C).
    本发明涉及修改低密度脂蛋白受体(LDLR)表达的化合物。这些化合物具有下面所示的结构式I:其中m、R1、n、R2和R3如本文所定义。本发明还涉及制备这些化合物的方法,包括它们的药物组合物,以及它们在治疗与低密度脂蛋白胆固醇(LDL-C)水平升高相关的疾病或紊乱中的应用。
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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
cnmr
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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