Cinosulfuron 醚磺隆

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醚磺隆

CAS:94593-91-6
英文名: cinosulfuron
化学名称 : 3-(4,6-二甲氧基-1,3,5三嗪-2-基)-1-[2-(2-甲氧基乙氧基)苯基〕磺酰脲;N-[[(4,6-dimethoxy-1,3,5-triazin-2-yl)amino]carbonyl]-2-(2-methoxyethoxy)benzenesulfonamide
其他名称 : 莎多伏(Setoff);CGA 142464;醚黄隆
分子式:C15H19N5O7S
分子量:413.4

理化性质 :纯品为无色晶状粉末,熔点144.6℃,蒸气压<0.01mPa(25℃),密度1.47(20℃),水中 溶解度(25℃)120(pH5.0)、4000mg/L(pH6.7)、1900mg/L(pH8.1)、丙酮36000mg/L 、乙醇1900mg/L、甲苯540mg/L、正辛醇260mg/L、正己烷<1mg/L (25℃),pH3 -pH5水解明显,pH7-9时水解不明显,熔点以上分解。在土壤中半衰期20天,在稻田水中半衰期3~7天,试验室稻田水中半衰期19~48天,光解半衰期80分钟。

毒性: 据中国农药毒性分级标准,醚磺隆属低毒除草剂。原药大鼠急性经口LD50大于5000毫克/千克,急性经皮LD50大于2000毫克/千克,急性吸入LC50大于5000毫克/米3。对免皮肤和眼睛无刺激作用,对豚鼠无致敏作用,在试验条件下,无致畸、致癌、致突变作用。大鼠两年喂养试验无作用剂量22毫克/千克,小鼠两年喂养无作用剂量9毫克/千克,狗一年喂养无作用剂量109毫克/千克, ADl为0.009毫克/千克/天。对鱼类和水生生物低毒,魟鱼、鳟鱼、鲤鱼、蓝腮鱼、鲇鱼的LC50(96小时)均大于100毫克/升。对蜜蜂低毒,急性口服(48小时)LD50大于1000毫升/千克。日本鹌鹑和北京鸭LD50均大于2000毫克/千克。

制剂大鼠急性经口和经皮LD50均大于2000毫克/千克。对皮肤和眼睛无刺激作用。

作用特点及杀草谱:属于磺酰脲类除草剂,抑制支链氨基酸合成,抑制细胞分裂。中毒杂草一般5-10天开始黄化枯萎直至死亡。水稻极易将其降解,因而安全。 醚磺隆主要通过植物根系及茎部吸收,传导至叶部,但植物叶面吸收很少。有效成分进入杂草体内后,由输导组织传递至分生组织,阻碍缬氨酸及异亮氨酸的合成,从而抑制细胞分裂及细胞的长大。用药后,中毒的杂草不会立即死亡,但生长停止,5~10天后植株开始黄化、枯萎,最后死亡。

防治对象 热带:水苋菜、异型莎草、圆齿尖头草、沟酸浆(属)、鸭舌草、慈姑(属)、粗大蕉草、萤蔺、仰卧蕉草、尖瓣花。

温带:绯红水苋菜、水生田繁缕、花简、异型莎草、鳢肠、三蕊沟繁缕、牛毛毡、水虱草、丁香蓼(属)、鸭舌草、眼子菜、浮叶眼于菜、萤蔺、雨久花、花蔺、异型莎草。对泽泻、矮慈姑、野慈姑、毋草、扁秆藨草等有较好的药效。

使用方法 :

1.直播田 水稻2-4叶期,18-30克/公顷(有效成分计)撒毒土或喷雾。保水3-5天。

2.插秧田 插秧后4-7天,方法向上。

3.对禾本科杂草效果不好,可酌情考虑与其他除草剂混配或混用。

剂型 :20%水分散粒剂,16%醚磺隆•异丙甲草胺可湿性粉剂,10%醚磺隆可湿性粉剂,25%醚磺隆•乙草胺可湿性粉剂

生产方法:以 2 -氯苯胺为原料 ,经过重氮化、磺酰化和胺化反应得到 2 -氯苯磺酰胺 ,再和乙二醇单甲醚经取代反应得到 2 -甲氧基乙氧基苯磺酰胺 , 与光气反应制成相应的异氰酸酯,再与2-氨基-4,6-二甲氧基-均三嗪反应,即制得醚磺隆。

生产情况:我国醚磺隆原药生产企业有江苏安邦、安徽省宣城市群业精细化工研究所、杭州大阳化工有限公司、江苏得丰农化公司,南京艾森精细化工有限公司等,瑞士先正达也在我国登记生产。我国醚磺隆原药产能1000吨/年,实际产量约200吨/年,每年内需在100吨左右,并有一定数量的出口。

 

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cinosulfuron
Herbicide
HRAC B WSSA 2; sulfonylurea

  Cinosulfuron

NOMENCLATURE
Common name cinosulfuron (BSI, draft E-ISO)
IUPAC name 1-(4,6-dimethoxy-1,3,5-triazin-2-yl)-3-[2-(2-methoxyethoxy)phenylsulfonyl]urea
Chemical Abstracts name N-[[(4,6-dimethoxy-1,3,5-triazin-2-yl)amino]carbonyl]-2-(2-methoxyethoxy)benzenesulfonamide
CAS RN [94593-91-6] Development codes CGA 142 464 (Ciba-Geigy)

PHYSICAL CHEMISTRY
Mol. wt. 413.4 M.f. C15H19N5O7S Form Colourless crystalline powder. M.p. 127.0-135.2 ºC (pure) V.p. <0.01 mPa (25 ºC) (OECD 104) KOW logP = 2.04 (pH 2.1, 25 ºC) Henry <1 ´ 10-6 Pa m3 mol-1 (pH 6.7, calc.) S.g./density 1.47 (20 ºC). Solubility In water 120 (pH 5.0), 4000 (pH 6.7), 19 000 (pH 8.1) (all in mg/l, 25 ºC). In acetone 36 000, ethanol 1900, toluene 540, n-octanol 260, n-hexane <1 (all in mg/l, 25 ºC). Stability Decomposes above the melting point. No significant hydrolysis at pH 7-10; considerable hydrolysis at pH 3-5. pKa 4.72

COMMERCIALISATION
History Herbicide reported by M. Quadranti et al. (Proc. 11th Conf. Asian Pacific Weed Sci. Soc., 1987, 1, 117). Introduced by Ciba-Geigy AG (now Syngenta AG). Patents US 4479821; EP 44807 Manufacturers Syngenta

APPLICATIONS
Biochemistry Branched chain amino acid synthesis (ALS or AHAS) inhibitor. Acts by inhibiting biosynthesis of the essential amino acids valine and isoleucine, hence stopping cell division and plant growth. Selectivity derives from rapid metabolism in the crop. Metabolic basis of selectivity in sulfonylureas reviewed (M. K. Koeppe & H. M. Brown, Agro-Food-Industry, 6, 9-14 (1995)). Mode of action Absorbed primarily by shoots and roots, and translocated to actively growing meristematic tissue. Uses Applied post-emergence to control many weeds, including Alisma, annual Cyperus, Eleocharis, Marsilea, Potamogeton and Sagittaria spp., Monochoria vaginalis and Sphenoclea zeylanica in transplanted, direct seeded, wet-sown and water-sown, and dry-sown flooded rice crops, at 20-80 g/ha. Also used in tropical plantation crops. For full weed spectrum, may need to be combined with a grass herbicide in tank-mix or sequential treatment. Phytotoxicity No varietal restrictions for rice. Formulation types GR; WG. Selected products: 'Setoff' (Syngenta); mixtures: 'Apiro Ace' (+ pyriftalid) (Syngenta)

OTHER PRODUCTS
Mixtures: 'PIPSET' (+ piperophos) (Syngenta) Discontinued products: 'Sailant' * (Ciba); 'Sofit Super' * (Ciba)

ANALYSIS
Product and residue analysis by hplc. Methods for sulfonylurea residues in crops, soil and water reviewed (A. C. Barefoot et al., Proc. Br. Crop Prot. Conf. - Weeds, 1995, 2, 707). Details available from Syngenta.

MAMMALIAN TOXICOLOGY
Oral Acute oral LD50 for rats and mice >5000 mg/kg. Skin and eye Acute percutaneous LD50 for rats >2000 mg/kg; not irritant to skin or eyes of rabbits. Non-sensitising to skin (guinea pigs). Inhalation LC50 (4 h) for rats >5 mg/l air. NOEL (2 y) for rats 400, mice 60 ppm; (1 y) for dogs 2500 ppm. Toxicity class WHO (a.i.) U

ECOTOXICOLOGY
Birds Acute oral LD50 for Japanese quail >2000 mg/kg. Fish LC50 (96 h) for rainbow trout >100 mg/l. Daphnia LC50 (48 h) 2500 mg/l. Algae EC50 (72 h) for Scenedesmus subspicatus 4.8 mg/l. Bees Non-toxic; LD50 (oral and contact) >100 mg/bee. Worms LC50 (14 d) for Eisenia foetida 1000 mg/kg.

ENVIRONMENTAL FATE
Animals Hydrolysis of methoxy groups and cleavage of the sulfonylurea bridge. It is rapidly excreted (80-100% within 24 h). Plants In plants, rapid degradation by cleavage of the sulfonylurea bridge. Soil/Environment In soil, degrades (a) by O-dealkylation in both ring systems, forming the corresponding phenol, mono- and di- hydroxytriazine and (b) by cleavage of the sulfonylurea bridge; degradation proceeds further to form bound residues and CO2; DT50 in soil (lab.) c. 20 d, in paddy fields c. 3 d. No potential for bioaccumulation. Koc c. 20, indicating that cinosulfuron may leach; column data show however that rapid degradation prevents leaching. In paddy fields under natural conditions, cinosulfuron dissipates rapidly due to photolysis and, to a lesser extent, by adsorption to soil.