Cloransulam-methyl 氯酯磺草胺

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中文通用名称: 氯酯磺草胺
英文通用名称: cloransulam-methyl (BSI,ISO)
商品名称: FirstRate

分子式: C15H13CIFN5O5S
分子量:429.8
化学名称: 3-氯-2-(5-乙氧基-7-氟[1,2,4]三唑[1,5-c]嘧啶- 2 -基磺酰氨基)苯甲酸甲酯
methyl 3-chloro-2-(5-ethoxy-7-fluoro[1,2,4]triazolo[1,5-c]pyrimidine-2-
ylsulfonamido)benzoate 或
3-氯-2-(5-乙氧基-7-氟[1,2,4]三唑[1,5-c]嘧啶- 2 -基磺酰基)氨基苯甲酸甲酯
methyl 3-chloro-2-(5-ethoxy-7-fluoro[1,2,4]triazolo[1,5-c]pyrimidine-2-ylsulfonyl)
anthranilate

CA主题索引名及CAS登录号:
methyl 3-chloro-2-[[(5-ethoxy-7-fluoro[1,2,4]triazolo[1,5-c]pyrimidine-2-yl)
sulfonyl]amino]benzoate
[147150-35-4]

化学结构类型: 三唑并嘧啶磺酰胺类

理化性质: 纯品为灰白固体;熔点216~218℃(分解);密度1.538(20℃)。

毒性:
大(小)鼠急性经口L D50:雌、雄>5000mg/kg;兔急性经皮L D50:>2000mg/kg;大鼠急
性吸入L C50(4小时):>3.77mg/l。对鸟类、鱼类、蜜蜂、蚯蚓等无毒。无致畸、致癌、致
突变作用,对遗传亦无不良影响。

作用机理: 乙酰乳酸合成酶(ALS)的抑制剂。
适宜作物: 大豆

安全性:在推荐剂量下使用对大豆安全。对后茬作物的影响:施药后3个月可种小麦;9个月后可种植苜蓿、燕麦、棉花、花生;30个月后可种植甜菜、向日葵、烟草。
防除对象:防除大多数重要的阔叶杂草如苘麻、豚草、三裂豚草、苍耳、裂叶牵牛、向日葵等。
使用方法:
大豆田中苗前和苗后防除阔叶杂草。使用剂量:17.5~44克有效成分/公顷。

合成方法:
以2-乙氧基-4,6-二氟嘧啶为起始原料,首先与水合肼反应,再与二硫化碳合环,并经重排制得中间体( I );最后中间体( I )经氯磺化后与取代苯胺反应,处理即得目的物。反应式如下:

主要原料与中间体:
2-乙氧基-4,6-二氟嘧啶、2-氯-6-甲氧羰基苯胺、水合肼

分析方法:HPLC
开发公司:美国陶氏农业科学(Dow Agroscience)公司。

 

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cloransulam-methyl
Herbicide
HRAC B WSSA 2; triazolopyrimidine

  cloransulam-methyl

NOMENCLATURE
Common name cloransulam-methyl (BSI, pa ISO, ANSI)
IUPAC name methyl 3-chloro-2-(5-ethoxy-7-fluoro[1,2,4]triazolo[1,5-c]pyrimidin-2-ylsulfonamido)benzoate; methyl 3-chloro-N-(5-ethoxy-7-fluoro[1,2,4]triazolo[1,5-c]pyrimidin-2-ylsulfonyl)anthranilate
Chemical Abstracts name methyl 3-chloro-2-[[(5-ethoxy-7-fluoro[1,2,4]triazolo[1,5-c]pyrimidin-2-yl)sulfonyl]amino]benzoate
CAS RN [147150-35-4]; (acid [159518-97-5]) Development codes XDE-565 (Dow)

PHYSICAL CHEMISTRY
Mol. wt. 429.8; (acid 415.8) M.f. C15H13ClFN5O5S; (acid C14H11ClFN5O5S) Form Off-white powder. M.p. 216-218 °C V.p. 4.0 ´ 10-11 mPa (25 °C) KOW logP = 1.12 (pH 5), -0.365 (pH 7), -1.24 (pH 8.5), 0.268 (distilled water) S.g./density 1.538 (20 °C) Solubility In water 3 ppm (pH 5), 184 ppm (pH 7) (both 25 °C). In acetone 4360, acetonitrile 5500, dichloromethane 6980, ethyl acetate 980, methanol 470, hexane <10, octanol <10, toluene 14 (all in mg/l). Stability Stable to aqueous hydrolysis (pH 5), slowly degraded (pH 7), rapidly hydrolysed (pH 9). DT50 for aqueous photolysis 22 min. pKa 4.81 (20 °C)

COMMERCIALISATION
History First registered in USA in 1997. Manufacturers Dow AgroSciences

APPLICATIONS
Biochemistry Inhibits the acetolactate synthase (ALS) enzyme. The primary site of activity is in plant meristems. Soya beans quickly metabolise cloransulam-methyl into a non-active form; DT50 <5 h. Uses Applied to the soil surface or incorporated pre-emergence or post-emergence in soya beans, to control broad-leaved weeds. Applied by ground only, at 42-53 g/ha. Formulation types WG. Selected products: 'First Rate' (Dow AgroSciences); 'Meta' (Dow AgroSciences); 'Pacto' (Dow AgroSciences)

OTHER PRODUCTS
'Amplify' (Monsanto); 'Gangster' (Valent) mixtures: 'Frontrow' (+ flumetsulam) (Dow AgroSciences); 'Gauntlet' (+ sulfentrazone) (FMC)

MAMMALIAN TOXICOLOGY
Oral Acute oral LD50 for rats >5000 mg/kg. Skin and eye Acute percutaneous LD50 for rabbits >2000 mg/kg. Not a skin irritant (rabbits). Not a skin sensitiser (guinea pigs). Inhalation LC50 (4 h) for rats >3.77 mg/l. NOEL (1 y) for dogs 5 mg/kg daily; (90 d) for male mice 50 mg/kg daily. ADI 0.1 mg/kg. Other Negative in mouse micronucleus and CHO tests. Toxicity class WHO (a.i.) U; EPA (formulation) III

ECOTOXICOLOGY
Birds Acute oral LD50 for bobwhite quail >2250 mg/kg b.w. Dietary LC50 for bobwhite quail and mallard ducks >5620 ppm. Fish LC50 (96 h) for bluegill sunfish >295, rainbow trout >86 ppm. Daphnia LC50 (48 h) >163 mg/l. Algae EC50 for Selenastrum capricornutum 0.00346 ppm Other aquatic spp. LC50 (96 h) for grass shrimp (Palaemonetes pugio) >121 mg/l; LC50 (48 h) for Eastern oyster (Crassostrea virginica) >111 mg/l. Bees LD50 (48 h, contact) for honeybees >25 mg/bee. Worms NOEC (14 d) for earthworms 859 mg/kg soil. Other beneficial spp. Practically non-toxic.

ENVIRONMENTAL FATE
Animals In female rats, administered cloransulam-methyl is excreted mainly via the urine; in male rats, it is excreted in both urine and faeces. After 72 h, <0.1% of the dose was found in any tissue. Soil/Environment Rapidly photolysed in water, DT50 22 min (pH 7). Photolysis on soil surface, DT50 30-70 d (corrected for metabolism). The apparent transformation DT50 in aerobic soils 9-13 d (est.). The transformation DT50 of cloransulam-methyl residues, under anaerobic aquatic conditions, c. 16 d. Although cloransulam-methyl and its transformation products are likely to be only of short persistence on the surface, the chemicals may be mobile in soil and may leach into ground water. Residues are contained in the top 30 to 45 cm.