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草甘膦异丙胺盐 | 38641-94-0

中文名称
草甘膦异丙胺盐
中文别名
N-(膦酰基甲基)甘氨酸异丙胺盐
英文名称
isopropyl glyphosate
英文别名
N-(phosphonomethyl)glycine mono-isopropylammonium salt;N-phosphonomethyl glycine monoisopropylamine salt;N-(phosphonomethyl)glycine isopropyl amine salt;N-phosphonomethylglycine isopropylammonium salt;N-(Phosphonomethyl)glycine isopropylamine salt;N-(phosphonomethyl)glycine isopropylamine;(Carboxymethylamino)methyl-hydroxyphosphinate;propan-2-ylazanium
草甘膦异丙胺盐化学式
CAS
38641-94-0
化学式
C3H8NO5P*C3H9N
mdl
——
分子量
228.185
InChiKey
ZEKANFGSDXODPD-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

  • 密度:
    1.218 g/mL at 25 °C
  • 闪点:
    >230 °F
  • 溶解度:
    水基(少量溶解)、甲醇(少量、加热、超声处理)、水(少量溶解)
  • 物理描述:
    Odorless crystalline solid or powder, very soluble in water.
  • 颜色/状态:
    White powder
  • 气味:
    Odorless
  • 熔点:
    Occurs in two steps 143-164 °C and 189-223 °C
  • 蒸汽压力:
    2.1X10-3 mPa at 25 °C /1.58X10-8 mm Hg/ at 25 °C
  • 稳定性/保质期:

    Glyphosate and all its salts are non-volatile, do not photochemically degrade and are stable in air.

  • 分解:
    When heated to decomposition it emits toxic fumes of /nitrogen and phosphorous oxides/.
  • 解离常数:
    pKa1 = 2.18 /monophosphate/; pKa2 = 5.77 /carboxylic acid/, both at 20 °C

计算性质

  • 辛醇/水分配系数(LogP):
    -0.85
  • 重原子数:
    14
  • 可旋转键数:
    4
  • 环数:
    0.0
  • sp3杂化的碳原子比例:
    0.83
  • 拓扑面积:
    133
  • 氢给体数:
    5
  • 氢受体数:
    7

ADMET

毒理性
  • 毒性总结
草甘膦异丙胺盐是一种无色无味的白色粉末,通常用作除草剂,用于控制阔叶杂草和禾本科杂草,在许多食品和非食品作物中都有应用。它是除草剂农达”中的活性成分。人类暴露和毒性:研究人员报告了意外接触或故意摄入农达的患者临床经验。使用产品时皮肤接触导致的症状包括眼周肿和结膜肿、心血管效应(心动过速和血压升高)、接触部位肿胀和感觉异常以及持续的皮肤刺激。故意摄入导致更严重的效应,包括由于明显的呼吸和心脏骤停导致的致命性。在含有草甘膦除草剂中,腹痛伴恶心、呕吐和/或腹泻是急性中毒最常见的表现。这些症状可能是轻微的,可以自行解决,但在严重中毒时可能会出现炎症、溃疡或梗死。严重的腹泻和反复呕吐可能导致脱。高剂量的浓缩配方可能导致胃肠道烧伤和坏死,并可能伴有出血。上消化道广泛糜烂与更严重的系统性中毒和长期住院有关。含有草甘膦除草剂引起的严重中毒表现为低血压、心脏心律失常、肾脏和肝脏功能障碍、高血、胰腺炎、肺肿或肺炎、意识平改变和代谢性酸中毒。这些效应可能是短暂的或严重的,在12到72小时内进展到休克和死亡。低血压的机制可能与血容量减少(液体转移和增加丢失)和直接的心脏毒性有关。仅摄入农达导致的死亡是由于一种综合症,表现为低血压,对静脉输液或血管收缩药物无反应,有时伴有肺肿,而中心静脉压正常。动物研究:将10只雄性家兔分为6组,每周5天,连续21天,每天给予76或114毫克/千克体重的未稀释草甘膦异丙胺盐。仅在皮肤变化上表现出毒性,这种变化在磨损皮肤上更为明显,但在所有情况下,在28天的恢复期结束时都已愈合。在含有表面活性剂的草甘膦异丙胺配方中,急性毒性是由表面活性剂引起的。在一项急性雌性犬研究中,农达配方中草甘膦和表面活性剂的共同作用导致心脏抑制,这主要是由表面活性剂引起的,因为草甘膦本身增加了心肌收缩力。对大鼠进行了一项为期4周的吸入研究,使用1:3稀释的农达配方。将50、160和360毫克/立方米的稀释配方作为气溶胶喷雾,每天6小时,每周5天。仅在最高剂量组的雌性中观察到鼻甲(亚急性炎症)、气管(单核细胞浸润)和肺(血管周围淋巴滤泡/聚集)刺激增加的发病率。没有发现系统性毒性的迹象(参数:存活、生长、有限的血液学和血液生化、器官重量、有限的组织病理学)。研究了除草剂农达草甘膦异丙胺盐的遗传毒性潜力,使用了三种不同的试验。两种剂量的小鼠骨髓微核试验均未发现断裂效应。在沙门氏菌试验中,仅测试了农达。在TA98中浓度为360微克/板(无代谢激活)和TA100中浓度为720微克/板(有代谢激活)时,显示出弱的突变效应。草甘膦异丙胺盐的后期-末期葱试验未显示效果,但在以草甘膦异丙胺盐计算浓度为1.44和2.88毫克/升时,经农达处理后,染色体畸变显著增加。观察到的最常见畸变可以特征化为纺锤体干扰。生态毒性研究:在处理森林一年后,农达对鹿鼠的繁殖、生长或存活没有明显的不利影响。Townsend花栗鼠(EuTAmias townsendii)的种群密度在处理区似乎最初下降,但这种反应是短暂的。在成体虹鳟鱼中,即使处理剂量高达2.0毫克/升的草甘膦异丙胺盐,也未观察到繁殖力或性腺体指数的变化。在回避研究中,虹鳟鱼不回避高达10.0毫克/升的异丙胺盐浓度。对于虹鳟鱼和渠道鲶鱼来说,卵期是最不敏感的早期生活阶段。总体而言,农达配方的毒性是技术级材料的3到42倍。
IDENTIFICATION AND USE: Glyphosate isopropylamine salt is a white odorless powder that is commonly used as a herbicide to control broadleaf weeds and grasses, in many food and non-food crops. It is an active ingredient in the herbicide Roundup. HUMAN EXPOSURE AND TOXICITY: Clinical experiences with patients exposed to Roundup either accidentally or through deliberate ingestion have been reported by investigators. Symptoms resulting from dermal exposure incidental to the use of the product included periorbital edema and chemosis of the eye, cardiovascular effects (tachycardia and elevated blood pressure), swelling and paraesthesia at the site of dermal contact and prolonged skin irritation. Deliberate ingestion resulted in more severe effects, including lethality from apparent respiratory and cardiac arrest. In glyphosate-containing herbicides abdominal pain with nausea, vomiting, and/or diarrhea are the most common manifestations of acute poisoning. These may be mild self-resolving, but in severe poisoning there may be inflammation, ulceration, or infarction. Severe diarrhea and recurrent vomiting may induce dehydration. Gastrointestinal burns and necrosis occurs with high doses of concentrated formulations and may be associated with hemorrhage. Extensive erosions of the upper gastrointestinal tract are associated with more severe systemic poisoning and a prolonged hospitalization. Severe poisonings by glyphosate-containing herbicides manifests as hypotension, cardiac dysrhythmias, renal and hepatic dysfunction, hyperkalemia, pancreatitis, pulmonary edema or pneumonitis, altered level of consciousness, and metabolic acidosis. These effects may be transient or severe, progressing over 12 to 72 hours to shock and death. The mechanism of hypotension may relate to both hypovolemia (fluids shifts and increased losses) and direct cardiotoxicity. Deaths following ingestion of Roundup alone were due to a syndrome that involved hypotension, unresponsive to iv fluids or vasopressor drugs, and sometimes pulmonary edema, in the presence of normal central venous pressure. ANIMAL STUDIES: Six groups of 10 male rabbits were treated with 76 or 114 mg/kg b.w. undiluted glyphosate isopropylamine salt for 5 days/week for 21 days. Toxicity was apparent only as dermal changes, which were more pronounced on abraded skin, but which in all cases had healed by the end of a 28-day recovery period. In glyphosate isopropylamine formulations containing surfactants, acute toxicity was due to the surfactant. In acute female dog study the joint effect of both glyphosate and the surfactant in Roundup formulation resulted in cardiac depression, which was mostly due to the surfactant since glyphosate itself increased myocardial contractility. A 4-week inhalation study was carried out on rats with a 1:3 dilution of Roundup formulation. Test concentrations of 50, 160 and 360 mg/cu m of the diluted formulation were administered as an aerosol spray for 6 hr/day, 5 days/week. An increased incidence of irritation of the nasal turbinates (subacute inflammation), trachea (mononuclear cell infiltration) and lungs (perivascular lymphoid infiltrates/aggregates) was observed among the high-dose females only. No signs of systemic toxicity were found (parameters: survival, growth, limited hematology and blood biochemistry, organ weights, limited histopathology). The genotoxic potential of the herbicide Roundup and glyphosate isopropylamine salt was studied in three different assays. No clastogenic effects were found in the mouse bone marrow micronucleus test for either of the two agents. In the Salmonella assay only Roundup was tested. It showed a weak mutagenic effect for the concn 360 ug/plate in TA98 (without metabolic activation) and 720 ug/plate in TA100 (with metabolic activation). The anaphase-telophase Allium test showed no effect for the glyphosate isopropylamine salt, but a significant increase in chromosome aberrations appeared after treatment with Roundup at concn of 1.44 and 2.88 mg/L when calculated as glyphosate isopropylamine. The most frequent aberrations observed could be characterized as disturbances of the spindle. ECOTOXICITY STUDIES: Roundup had no apparent adverse effects on reproduction, growth, or survival of deer mice 1 year after treatment of forest. The population density of Townsend chipmunks (Eutamias townsendii) appeared to initially decline in the treated area, although this response was short lived. No changes in fecundity or gonadosomatic index were observed in adult rainbow trout treated with up to 2.0 mg/L of glyphosate isopropylamine salt. In avoidance studies, rainbow trout did not avoid concentrations of the isopropylamine salt up to 10.0 mg/L. The egg stage was the least sensitive early life stage for both rainbow trout and channel catfish. Overall, the Roundup formulation was 3 to 42 times more toxic than the technical grade material.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 副作用
职业性肝毒素 - 第二性肝毒素:在职业环境中的毒性效应潜力是基于人类摄入或动物实验的中毒案例。
Occupational hepatotoxin - Secondary hepatotoxins: the potential for toxic effect in the occupational setting is based on cases of poisoning by human ingestion or animal experimentation.
来源:Haz-Map, Information on Hazardous Chemicals and Occupational Diseases
毒理性
  • 毒性数据
LC50 (大鼠) > 0.0013 毫克/立方米/4小时
LC50 (rat) > 0.0013 mg/m3/4h
来源:Haz-Map, Information on Hazardous Chemicals and Occupational Diseases
毒理性
  • 解毒与急救
立即急救:确保已经进行了充分去污。如果患者停止呼吸,开始人工呼吸,最好使用需求阀复苏器、袋阀面罩装置或口袋面罩,按培训操作。根据需要执行心肺复苏。立即用缓慢流动的冲洗受污染的眼睛。不要催吐。如果发生呕吐,让患者前倾或将其置于左侧(如果可能,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。/草甘膦(Roundup)及相关化合物/
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 as necessary. Immediately flush contaminated eyes with gently flowing water. Do not induce vomiting. If vomiting occurs, lean patient forward or place on 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. /Glyphosate (Roundup) and Related Compounds/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
  • 解毒与急救
基本治疗:建立专利气道(如有需要,使用口咽或鼻咽气道)。必要时进行抽吸。观察呼吸不足的迹象,并在必要时协助通气。通过非循环呼吸面罩以10至15升/分钟的速度给予氧气。监测肺肿并视必要进行治疗……。监测休克并视必要进行治疗……。对于眼睛污染,立即用冲洗眼睛。在运输过程中,用0.9%的生理盐持续冲洗每只眼睛……。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,则用冲洗口腔,并给予5毫升/千克,最多200毫升的进行稀释。给予活性炭……。监测体温并在必要时进行治疗。去污染后,用干燥的无菌敷料覆盖皮肤烧伤……。/草甘膦( Roundup )及相关化合物/
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 necessary. 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 ... . For eye contamination, flush eyes immediately with water. Irrigate each eye continuously with 0.9% saline 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. Administer activated charcoal ... . Monitor body temperature and treat if necessary. Cover skin burns with dry sterile dressings after decontamination ... . /Glyphosate (Roundup) and Related Compounds/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
草甘膦及其异丙胺盐口服毒性极低。口服给予大鼠的草甘膦在胃肠道中吸收不完全,尤其是在雄性中。它以原型形式在尿液中排出,尽管有证据表明存在胆汁排泄和肠肝循环。
Glyphosate and its isopropylamine salt have extremely low oral toxicity. Orally administered glyphosate is incompletely absorbed from the gastrointestinal tract of rats, especially in males. It is excreted unchanged in the urine, although there is evidence of biliary excretion and enterohepatic circulation.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
从三种草甘膦制剂中,使用体外技术测量了(14)C标记草甘膦通过切除的人类腹部皮肤的经皮吸收。在这些条件下,草甘膦的吸收非常差,表皮作为主要的屏障。
The percutaneous absorption of (14)C-labelled glyphosate from 3 formulations of glyphosate was measured in excised human abdominal skin using an in vitro technique. Glyphosate was found to be very poorly absorbed under these conditions, with the epidermis acting as the primary barrier /Glyphosate formulations/.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
研究了草甘膦的经皮吸收,包括体内和体外实验。评估了商用草甘膦配方Roundup原液及其1:20至1:32稀释液穿透尸检中取得的人类大腿皮肤样本的能力,使用含有人类血浆作为受体流体的流过细胞进行评估。调查了14C标记的Roundup及其1:20和1:32稀释液与粉末化的人类角质层的结合能力。成年雌性猕猴被涂抹500或5400微克/200平方厘米标记的草甘膦,或者静脉注射9或93微克草甘膦。从给药前24小时开始,至给药后8天,收集血液和尿液样本,并测定碳-14活性。在局部暴露7天后,选取的猴子被处死,以确定草甘膦衍生的碳-14活性的组织分布。其他猴子被局部应用1:20稀释的14C标记草甘膦。在涂抹后0至24小时内,用肥皂和清洗涂抹部位,以评估这些处理去除草甘膦的能力。体外实验中,穿透人类皮肤的草甘膦不到2%。Roundup中的草甘膦或稀释形式的草甘膦并未与粉末化的角质层结合。静脉给药的草甘膦大约有95至99%通过尿液排出,大部分在最初的24小时内排出。局部应用后,在8天内,只有5400微克/200平方厘米剂量的2.2%和500微克/200平方厘米剂量的0.8%通过尿液排出。根据静脉给药数据,估计应用的剂量中有0.8至2.2%被吸收。静脉给药后,在血液中检测到草甘膦,但局部应用后未检测到。局部应用后,在任何内部器官中均未检测到草甘膦衍生的放射性。肥皂和在处理后12小时分别去除了89.6%和83.6%的涂抹剂量,而在暴露后24小时,这两种处理大约去除了50%的涂抹剂量。结论是,猕猴通过皮肤吸收的草甘膦量很低,约为0.8至2.2%。由于猕猴是人类经皮吸收的良好模型,因此草甘膦对人类应具有很低的皮肤毒性。/Roundup/
The percutaneous absorption of glyphosate was studied in vivo and in vitro. The ability of Roundup, a commercial glyphosate formulation, applied neat and in 1:20 to 1:32 dilutions to penetrate human thigh skin samples obtained at autopsy was evaluated using flow through cells containing human plasma as the receptor fluid. The ability of 14C-labeled Roundup and the 1:20 and 1:32 dilutions to bind to powdered human stratum corneum was investigated. Adult female rhesus monkeys were administered 500 or 5400 ug per 200 sq cm labeled glyphosate topically or 9 or 93 ug glyphosate iv. Blood and urine samples were collected starting 24 hr before dosing and up to 8 days post dosing and assayed for carbon-14 activity. Selected monkeys were killed 7 days after topical exposure to determine the tissue distribution of glyphosate derived carbon-14 activity. Other monkeys were topically administered a 1:20 dilution of 14C-labeled glyphosate.The application sites were washed with soap and water or water 0 to 24 hr later to assess the ability of these treatments to remove glyphosate. In vitro, less than 2% of the applied glyphosate penetrated human skin. Glyphosate as Roundup or in diluted form did not bind to powdered stratum corneum. Around 95 to 99% of iv administered glyphosate was excreted in the urine, mostly within the first 24 hr. Following topical application only 2.2% of the 5400 ug/200 sq cm dose and 0.8% of the 500 ug/200 sq cm dose were excreted in the urine over 8 days. Based on the iv data, 0.8 to 2.2% of the applied doses was estimated to have been absorbed. Glyphosate was detected in the blood after iv administration, but not topical application. No glyphosate derived radioactivity was detected in any internal organs after topical application. Soap and water, or water removed 89.6 and 83.6% of the applied dose, respectively, 12 hr after treatment. Both treatments removed about 50% of the applied dose 24 hr after exposure. It was concluded that the amounts of glyphosate absorbed through the skin of rhesus monkeys is low, on the order of 0.8 to 2.2%. Since the rhesus monkey is a good model for percutaneous absorption relevant to humans, glyphosate should have little dermal toxicity for humans. /Roundup/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
草甘膦与皮肤的相互作用以及通过经皮吸收的潜在系统性可用性通过皮肤结合、皮肤吸收、残留组织分布和皮肤去污进行了研究。最终配方(Roundup)中的草甘膦未稀释和用稀释1:20和1:32,不会分配到人类角质层的粉末中(<1%)。在体外,通过人类皮肤进入人类血浆作为受体液的经皮吸收不超过2%,浓度范围为0.5-154微克/平方厘米,涂抹体积范围为0.014-0.14毫升/平方厘米。在恒河猴静脉注射93和9微克剂量的草甘膦后,草甘膦的处置主要是通过尿液排泄,7天内分别达到95 + 或 - 8%和99 + 或 - 4%。在恒河猴体内,低剂量(25微克/平方厘米)的经皮吸收为0.8 + 或 - 0.6%,高剂量(270微克/平方厘米)的经皮吸收为2.2 + 或 - 0.8%。在涂抹后7天处死的猴子器官中没有发现残留的^14C。用肥皂和水清洗皮肤涂抹部位可以去除90 + 或 - 4%的涂抹剂量,只用水清洗可以去除84 + 或 - 3%的涂抹剂量。肥皂和水以及只用水的清洗在24小时皮肤涂抹期间去除草甘膦的能力相同。大约50%的初始涂抹剂量可以在24小时后回收。草甘膦在水中的溶解性非常高,而在大多数有机物中不溶(辛醇/水log P = -1.70),因此与富含脂质的角质层不相容。这与低皮肤结合和皮肤吸收以及用肥皂和水或只用水清洗能高效去除皮肤上的草甘膦是一致的。
Interactions /of glyphosate/ with skin and potential systemic availability through percutaneous absorption was studied by skin binding, skin absorption, residual tissue distribution, and skin decontamination. Glyphosate in a final formulation (Roundup) undiluted and diluted with water 1:20 and 1:32, would not partition into powdered human stratum corneum (<1%). In vitro percutaneous absorption through human skin into human plasma as receptor fluid was no more than 2% over a concentration range of 0.5-154 ug/sq cm and a topical volume range of 0.014-0.14 mL/sq cm. Disposition of glyphosate following iv administration of 93 and 9 ug doses to rhesus monkeys was mainly through urine excretion, 95 + or - 8 and 99 + or - 4% in 7 days, respectively. Percutaneous absorption in vivo in rhesus monkey was 0.8 + or - 0.6% for the low dose (25 ug/sq cm) and 2.2 + or - 0.8% for the high dose (270 ug/sq cm). No residual (14)C was found in organs of the monkeys euthanized 7 days after the topical application. Washing the skin application site with soap and water removed 90 + or - 4% of applied dose, and washing with water only removed 84 + or - 3% of applied dose. Both soap and water and water only were equal in ability to remove glyphosate from skin over a 24 hr skin application period. About 50% of the initially applied dose could be recovered after 24 hr. Glyphosate is very soluble in water and insoluble in most organics (octanol/water log P = -1.70) and therefore not compatible with the lipid-laden stratum corneum. This is consistent with the low skin binding and skin absorption and also consistent with the efficient removal from skin with soap and water or water-only wash. /Roundup/
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
在哺乳期的山羊中,在给予含有9:1混合物(14)C-草甘膦和(14)C-甲基膦酸AMPA)的胶囊,剂量平相当于120 mg/kg饮食(以自由酸形式表示)5天后,测量了牛奶中碳-14标记的浓度。在测试期间,牛奶中的浓度(以每千克全牛奶中草甘膦的毫克当量表示)范围为0.019至0.086 mg/kg;在最后一次给药后的第5天,浓度为0.006 mg/kg。
In lactating goats concentrations of carbon-14 label in milk were measured after giving capsules containing a 9:1 mixture of (14)C-glyphosate and (14)C-aminomethylphosphonic acid (AMPA) to a dose level equivalent to 120 mg/kg diet (expressed as free acid) for 5 days. Concentrations in milk (as mg equivalents glyphosate/kg whole milk) ranged from 0.019 to 0.086 mg/kg during the test period; at day 5 after the last dose the concentration was 0.006 mg/kg.
来源:Hazardous Substances Data Bank (HSDB)

安全信息

  • 危险品标志:
    Xi
  • 安全说明:
    S26
  • 危险类别码:
    R36
  • 海关编码:
    2931900090
  • 储存条件:
    存放温度应为2-8℃,请保持环境干燥。

SDS

SDS:0b566f64e5e9771d09957ae41d97f14a
查看
1.1 产品标识符
: N-(PhOSphonomethyl)glycine, monoisopropylamine
化学品俗名或商品名
salt solution
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
仅供科研用途,不作为药物、家庭备用药或其它用途。

模块 2. 危险性概述
2.1 GHS分类
眼刺激 (类别2A)
急性的体毒性 (类别2)
2.2 GHS 标记要素,包括预防性的陈述
危害类型象形图
信号词 警告
危险申明
H319 造成严重眼刺激。
H401 对生物有毒。
警告申明
预防
P264 操作后彻底清洁皮肤。
P273 避免释放到环境中。
P280 穿戴防护手套/ 眼保护罩/ 面部保护罩。
措施
P305 + P351 + P338 如进入眼睛:用小心清洗几分钟。如戴隐形眼镜并可方便地取出,取出
隐形眼镜。继续冲洗。
P337 + P313 如仍觉眼睛刺激:求医/ 就诊。
处理
P501 将内容物/ 容器处理到得到批准的废物处理厂。
2.3 其它危害物 - 无

模块 3. 成分/组成信息
3.2 混合物
: C6H17N2O5P
分子式
成分 分类 浓度
N-(PhOSphonomethyl)glycine, compound with 2-propylamine (1:1)
Eye Irrit. 2A; Aquatic Acute 2; 40 %
254-056-8 H319, H401
015-184-00-8
Water
60 %
231-791-2
如需在本章节中提及的H类告知和R类描述的全部文字说明,请见第16章节.

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。 出示此安全技术说明书给到现场的医生看。
如果吸入
如果吸入,请将患者移到新鲜空气处。 如果停止了呼吸,给于人工呼吸。 请教医生。
在皮肤接触的情况下
用肥皂和大量的冲洗。 请教医生。
在眼睛接触的情况下
冲洗眼睛作为预防措施。
如果误服
切勿给失去知觉者从嘴里喂食任何东西。 用漱口。 请教医生。
4.2 最重要的症状和影响,急性的和滞后的
据我们所知,此化学,物理和毒性性质尚未经完整的研究。
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
雾,耐醇泡沫,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, 的氧化物
5.3 救火人员的预防
如必要的话,戴自给式呼吸器去救火。
5.4 进一步的信息
无数据资料

模块 6. 泄露应急处理
6.1 人员的预防,防护设备和紧急处理程序
防止吸入蒸汽、气雾或气体。 保证充分的通风。
6.2 环境预防措施
在确保安全的条件下,采取措施防止进一步的泄漏或溢出。 不要让产物进入下道。
防止排放到周围环境中。
6.3 抑制和清除溢出物的方法和材料
存放在合适的封闭的处理容器内。
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
无数据资料
7.2 安全储存的条件,包括任何不兼容性
贮存在阴凉处。 容器保持紧闭,储存在干燥通风处。
打开了的容器必须仔细重新封口并保持竖放位置以防止泄漏。
7.3 特定用途
无数据资料

模块 8. 接触控制/个体防护
8.1 控制参数
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
根据工业卫生和安全使用规则来操作。 休息以前和工作结束时洗手。
人身保护设备
眼/面保护
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。
身体保护
防渗透的衣服, 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含量来选择。
呼吸系统防护
不需要对呼吸系统保护.对少量挥发请采用美国OV/AG (US)标准类型的 或欧洲ABEK (EU EN
14387)标准类型的呼吸器过滤器.
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: 云状, 液体
颜色: 琥珀色
b) 气味
无数据资料
c) 气味临界值
无数据资料
d) pH值
4.4 - 4.8 在 10 g/l 在 25 °C
e) 熔点/凝固点
无数据资料
f) 起始沸点和沸程
无数据资料
g) 闪点
无数据资料
h) 蒸发速率
无数据资料
i) 可燃性(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) 相对蒸气密度
无数据资料
m) 相对密度
1.169 g/cm3
n) 溶性
可溶的
o) 辛醇/分配系数的对数值
无数据资料
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 化学稳定性
无数据资料
10.3 危险反应的可能性
无数据资料
10.4 避免接触的条件
无数据资料
10.5 不兼容的材料
强氧化剂
10.6 危险的分解产物
其它分解产物 - 无数据资料

模块 11. 毒理学资料
11.1 毒理学影响的信息
急性毒性
无数据资料
皮肤腐蚀/刺激
无数据资料
严重眼损伤 / 眼刺激
无数据资料
呼吸道或皮肤过敏
无数据资料
生殖细胞诱变
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
无数据资料
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 吸入可能有害。 可能引起呼吸道刺激。
摄入 如服入是有害的。
皮肤 如果通过皮肤吸收可能是有害的。 可能引起皮肤刺激。
眼睛 可能引起眼睛刺激。
接触后的征兆和症状
据我们所知,此化学,物理和毒性性质尚未经完整的研究。
附加说明
化学物质毒性作用登记: 无数据资料

模块 12. 生态学资料
12.1 毒性
无数据资料
12.2 持久存留性和降解性
无数据资料
12.3 生物积累的潜在可能性
无数据资料
12.4 土壤中的迁移
无数据资料
12.5 PBT 和 vPvB的结果评价
无数据资料
12.6 其它不利的影响
生物有毒。

模块 13. 废弃处置
13.1 废物处理方法
产品
污染了的包装物
作为未用过的产品弃置。

模块 14. 运输信息
欧洲陆运危规: - 国际海运危规: - 国际空运危规: -
14.2 联合国(UN)规定的名称
欧洲陆运危规: 无危险货物
国际海运危规: 无危险货物
国际空运危规: 无危险货物
14.3 运输危险类别
欧洲陆运危规: - 国际海运危规: - 国际空运危规: -
14.4 包裹组
欧洲陆运危规: - 国际海运危规: - 国际空运危规: -
14.5 环境危险
欧洲陆运危规: 否 国际海运危规 海运污染物: 否 国际空运危规: 否
14.6 对使用者的特别预防
无数据资料


模块 15 - 法规信息
N/A


模块16 - 其他信息
N/A

反应信息

  • 作为反应物:
    描述:
    草甘膦异丙胺盐 作用下, 以 为溶剂, 反应 336.0h, 生成 ammonium (isopropylammonium) N-(phospbonomethyl)glycine
    参考文献:
    名称:
    Enhanced glyphosate herbicidal concentrates
    摘要:
    一种含有草甘膦双盐和增效剂的除草浓缩液,通过调整含有草甘膦盐的浓缩液的pH值,直到获得单相浓缩液。添加到浓缩液中的碱的量通常是使浓缩液的pH值达到约7.0至8.5所需的量。
    公开号:
    US20060199737A1
  • 作为产物:
    描述:
    草甘膦异丙胺 为溶剂, 反应 0.5h, 以99%的产率得到草甘膦异丙胺盐
    参考文献:
    名称:
    [EN] METHOD FOR THE SYNTHESIS OF N-(PHOSPHONOMETHYL)GLYCINE
    [FR] PROCÉDÉ DE SYNTHÈSE DE N-(PHOSPHONOMÉTHYL)GLYCINE
    摘要:
    本发明涉及一种合成N-(膦甲基)甘氨酸或其所选衍生物(包括其盐、膦酸酯或膦酸酯盐)的方法,其中包括以下步骤: • a)在酸催化剂的存在下,形成反应混合物,该混合物包括2,5-二酮哌嗪、甲醛和一种包含一个或多个P-O-P酐基团的化合物,该酐基团具有一个P原子在氧化状态(+ III)和另一个P原子在氧化状态(+ III)或(+ V),以形成N,N'-双膦甲基-2,5-二酮哌嗪、其单至四膦酸酯、N,N'-双膦甲基-2,5-二酮哌嗪的脱水形式以及其脱水形式的膦酸酯; • b)水解所述的N,N'-双膦甲基-2,5-二酮哌嗪、其脱水形式或其膦酸酯,以获得N-(膦甲基)甘氨酸或其所选衍生物(包括其盐、膦酸酯和膦酸酯盐)。
    公开号:
    WO2014012991A1
点击查看最新优质反应信息

文献信息

  • [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] ISOXAZOLINE COMPOUNDS AND THEIR USE AS PEST CONTROL AGENTS<br/>[FR] COMPOSÉS ISOXAZOLINE ET LEUR UTILISATION EN TANT QU'AGENTS DE LUTTE CONTRE LES ORGANISMES NUISIBLES
    申请人:PI INDUSTRIES LTD
    公开号:WO2021038501A1
    公开(公告)日:2021-03-04
    The present invention discloses an isoxazoline compound of formula (I), wherein, R1, R2a, R2b, R2c, A, T and Z are as defined in the detailed description. The present invention further discloses methods for preparation of compounds of formula (I) and use of the compounds of formula (I) as a pest control agents.
    本发明公开了一种式(I)的异氧杂环烷化合物,其中,R1、R2a、R2b、R2c、A、T和Z如详细说明中所定义。本发明还公开了制备式(I)化合物的方法以及将式(I)化合物用作杀虫剂的用途。
  • [EN] PLANT GROWTH REGULATION<br/>[FR] REGULATION DE LA CROISSANCE VEGETALE
    申请人:BAYER CROPSCIENCE GMBH
    公开号:WO2005107465A1
    公开(公告)日:2005-11-17
    The present invention relates to the use of a compound for plant growth regulation, preferably by application of the compound to plants, to the seeds from which they grow or to the locus in which they grow, in an effective plant growth regulating, preferably non-phytotoxic amount, which compound is a 3,4-disubstituted maleimide derivative of formula (I) or an agriculturally acceptable salt thereof, wherein: X is aryl or heteroaryl which groups are unsubstituted or substituted; Y is NH or a covalent bond; and Z is aryl or heteroaryl which groups are unsubstituted or substituted and a method for treatment of plants with such compounds in order to induce growth regulating responses.
    本发明涉及一种化合物用于植物生长调节,优选通过将该化合物施用于植物、它们生长的种子或它们生长的位置,以有效的植物生长调节,优选为非植物毒性量,该化合物是式(I)的3,4-二取代马来酰亚胺生物或其农业可接受的盐,其中:X是未取代或取代的芳基或杂环芳基;Y是NH或共价键;Z是未取代或取代的芳基或杂环芳基,以及使用这些化合物处理植物的方法,以诱导生长调节反应。
  • [EN] HERBICIDAL PROPYNYL-PHENYL COMPOUNDS<br/>[FR] COMPOSÉS PROPYNYLE-PHÉNYLE HERBICIDES
    申请人:SYNGENTA PARTICIPATIONS AG
    公开号:WO2015197468A1
    公开(公告)日:2015-12-30
    The present invention relates to a compound of formula (I) wherein: R1 is C1-C3alkoxy, C1-C2alkoxy-C1-C3alkoxy, C1-C2fluoroalkoxy, ethyl, n-propyl, n-butyl, cyclopropyl or ethynyl; R2 is hydrogen, ethyl, n-propyl, cyclopropyl, vinyl, ethynyl, C1-C3alkoxy, C1-C3fluoroalkyl, C1-C2fluoroalkoxy, C1-C2alkoxy-C1-C3alkoxy-, or C1fluoroalkoxy-C1-C3alkoxy-; provided that when R1 is ethyl, n-propyl, n-butyl, cyclopropyl or ethynyl, then R2 is hydrogen, ethyl, n-propyl, cyclopropyl, vinyl or ethynyl; and Y is O, S, S(O), S(O)2, N(C1-C2alkyl), N(C1-C2alkoxy), C(O), CR8R9 or -CR10R11CR12R13-; and and G, R3, R4, R5 and R6 are as defined herein; wherein the compound of formula (I) is optionally present as an agrochemically acceptable salt thereof. These compounds are suitable for use as herbicides. The invention therefore also relates to a method of controlling weeds, especially grassy monocotyledonous weeds, in crops of useful plants, comprising applying a compound of formula (I), or a herbicidal composition comprising such a compound, to the plants or to the locus thereof.
    本发明涉及一种具有以下结构的化合物(I):其中:R1为C1-C3烷氧基,C1-C2烷氧基-C1-C3烷氧基,C1-C2氟烷氧基,乙基,正丙基,正丁基,环丙基或乙炔基;R2为氢,乙基,正丙基,环丙基,乙烯基乙炔基,C1-C3烷氧基,C1-C3氟烷基,C1-C2氟烷氧基,C1-C2烷氧基-C1-C3烷氧基,或C1氟烷氧基-C1-C3烷氧基-;但是当R1为乙基,正丙基,正丁基,环丙基或乙炔基时,R2为氢,乙基,正丙基,环丙基,乙烯基乙炔基;Y为O,S,S(O),S(O)2,N(C1-C2烷基),N(C1-C2烷氧基),C(O),CR8R9或-CR10R11CR12R13-;以及G,R3,R4,R5和R6如本文所定义;其中化合物(I)可作为农药中可接受的盐存在。这些化合物适用于用作除草剂。因此,本发明还涉及一种控制杂草,特别是草本单子叶杂草,在有用植物作物中的方法,包括将化合物(I)或含有这种化合物的除草剂组合物施用于植物或其生长地点。
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