Tribenuron Methyl 苯磺隆

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苯磺隆

基本信息
苯磺隆是一种除草剂,主要用于麦类(冬小麦、春小麦、大麦等)作物田中防除阔叶杂草。
其它名称:巨星、阔叶净。
英文名称:tribenuron-methyl。
CAS号:101200-48-0。
分子式:C15H17N5O6S。
分子量:395.39。 
化学名:2-[N-(4-甲氧基-6-甲基-1,3,5-三嗪-2-基)-N-甲基氨基甲酰胺基磺酰基]苯甲酸甲酯

理化性质
本品为白色固体。m.p.141℃,蒸气压0.036×10-3Pa (25℃)。在pH值4、pH值5、pH值6时,在水中的溶解度分别为28mg/L、50mg/L、280mg/L;在有机溶剂中溶解度为:丙酮43.8mg/L、乙腈54.2mg/L、四氯化碳3.12mg/L、乙酸乙酯17.5mg/L、己烷0.028mg/L。分配系数(正辛醇/水)0.36 (pH=7)。常温贮存稳定,对光稳定,在45℃时水解,pH值8~10稳定,但在pH<7或>12时迅速水解。土壤中半衰期1~7d。

动物毒性
雌、雄大鼠急性经口LD50>5000mg/kg ;大鼠急性经皮LD50>5000mg/kg,兔>2000mg/kg;大鼠急性吸入LC50>5mg/L (4h)。对眼睛有轻度刺激性,但24h症状消失;对皮肤无刺激反应;对豚鼠皮肤无过敏性。微核试验表明,苯磺隆对体细胞无致突变效应;睾丸染色体畸变试验表明,苯磺隆对生殖细胞无遗传毒效应;未发现大鼠致畸。虹鳟鱼LC50>1000mg/L (96h),水蚤LC50720mg/L (48h)。鹌鹑急性经口LD50>2250mg/kg。蜜蜂LD50>0.1mg/只,蚯蚓LC50>1200mg/kg土壤。

常用剂型
10%苯磺隆可湿性粉剂、75%苯磺隆水分散粒剂(也称为干燥悬浮剂或干悬浮剂)。

适用作物
冬小麦、春小麦、大麦、元麦、燕麦。

防除对象
主要用于防除各种一年生阔叶杂草,对播娘蒿、荠菜、碎米荠菜、麦家公、藜、反枝苋等效果较好,对地肤、繁缕、蓼、猪殃殃等也有一定的防除效果,对田蓟、卷茎蓼、田旋花、泽漆等效果不显著,对野燕麦、看麦娘、雀麦、节节麦等禾本科杂草无效。

作用机理
本品为选择性内吸传导型除草剂,可被杂草的根、叶吸收,并在植株体内传导。通过抑制乙酰乳酸合成酶(ALS)的活性,从而影响支链氨基酸(如:亮氨酸、异亮氨酸、缬氨酸等)的生物合成。植物受害后表现为生长点坏死、叶脉失绿,植物生长受到严重抑制、矮化,最终全株枯死。敏感杂草吸收药剂后立即停止生长,1-3周后死亡。

使用方法
小麦2叶期至拔节期,杂草苗前或苗后早期施药。一般用药量10%苯磺隆可湿性粉剂10-20g/亩,对水量15-30kg,均匀喷雾杂草茎叶。杂草较小时,低剂量即可取得较好的防效,杂草较大时,应用高剂量。

注意事项
1.每季作物只能使用本品1次。
2 .本品活性高,施用时应严格掌握用药量,并注意与水混合均匀。
3.本品只能用于防除已出苗杂草,对未出土杂草防效很差。
4.大风天气应停止喷雾施药,以免药液飘移对邻近阔叶作物产生药害。
5.本品在土壤中的残效期为60天左右。
6.花生对本品敏感,施用过本品的冬小麦田,后茬不得种植花生。


 

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tribenuron-methyl
Herbicide
HRAC B WSSA 2; sulfonylurea

 

NOMENCLATURE
tribenuron-methyl
Common name tribenuron-methyl
IUPAC name methyl 2-[4-methoxy-6-methyl-1,3,5-triazin-2-yl(methyl)carbamoylsulfamoyl]benzoate
Chemical Abstracts name methyl 2-[[[[(4-methoxy-6-methyl-1,3,5-triazin-2-yl)methylamino]carbonyl]amino]sulfonyl]benzoate
CAS RN [101200-48-0] EEC no. 401-190-1 Development codes DPX-L5300 (DuPont); L5300

tribenuron
Common name tribenuron (BSI, ANSI, draft E-ISO)
IUPAC name 2-[4-methoxy-6-methyl-1,3,5-triazin-2-yl(methyl)carbamoylsulfamoyl]benzoic acid
Chemical Abstracts name 2-[[[[(4-methoxy-6-methyl-1,3,5-triazin-2-yl)methylamino]carbonyl]amino]sulfonyl]benzoic acid
CAS RN [106040-48-6]

PHYSICAL CHEMISTRY
tribenuron-methyl
Composition Tech. is >95%. Mol. wt. 395.4 M.f. C15H17N5O6S Form Off-white powder with a slight pungent odour. M.p. 142 ºC V.p. 5.2 ´ 10-5 mPa (25 ºC) KOW logP = 0.78 (pH 7, 25 °C) Henry 1.03 ´ 10-8 Pa m3 mol-1 S.g./density 1.46 (20 °C) Solubility In water 0.05 (pH 5), 2.04 (pH 7), 18.3 (pH 9) (g/l, 20 ºC). In acetone 3.91 ´ 104, acetonitrile 4.64 ´ 104, ethyl acetate 1.63 ´ 104, n-heptane 20.8, methanol 2.59 ´ 103 (mg/l, 20 °C). Stability No significant photolysis occurs over the pH range 5-9 at 25 ºC. Does not ignite nor support combustion. Hydrolysis DT50 <1 d (pH 5), 15.8 d (pH 7), stable (pH 9) (all 25 ºC). pKa 4.7

tribenuron
Mol. wt. 381.4 M.f. C14H15N5O6S

COMMERCIALISATION
History Herbicide reported by D. T. Ferguson et al. (Proc. Br. Crop Prot. Conf. - Weeds, 1985, 1, 43). The methyl ester introduced in Spain (1986) by E. I. du Pont de Nemours and Co. ; first approval in 1987. Manufacturers DuPont; Jiangsu Yangnong; Sharda; Shenyang

APPLICATIONS
tribenuron-methyl
Biochemistry Affects sensitive weeds through inhibition of the enzyme acetolactate synthase (ALS). Inhibition of ALS leads to the rapid cessation of cell division and subsequent growth processes in plants. Mode of action Selective, post-emergence herbicide, acting primarily through foliar uptake, with little or no soil activity. Symptoms of chlorosis appear in affected weeds in days with necrosis and death occuring after 10-25 days under optimal conditions. Uses Post-emergence control of broad-leaved weeds in cereal crops, including wheat, barley, oats, rye and triticale, at 7.5-30 g/ha. Formulation types TB; WG. Selected products: 'Express' (USA) (DuPont); 'Granstar' (Europe) (DuPont); 'Pointer' (Germany) (DuPont); 'Oscar' (Vapco); 'Rapid' (Rotam); mixtures: 'Canvas' (+ metsulfuron-methyl+ thifensulfuron-methyl) (DuPont)

OTHER PRODUCTS
tribenuron-methyl
'Cameo' (DuPont); 'Quantum' (DuPont); 'Sprinter' (DuPont) mixtures: 'Calibre' (+ thifensulfuron-methyl) (DuPont); 'Harmony Extra' (+ thifensulfuron-methyl) (DuPont) Discontinued products mixtures: 'DP 911' * (+ metsulfuron-methyl) (DuPont); 'DUK 110' * (+ thifensulfuron-methyl) (DuPont)

ANALYSIS
Product and residue analysis by hplc/ms/ms (Handbook of Residue Analytical Methods, pp 400-410).

MAMMALIAN TOXICOLOGY
tribenuron-methyl
Oral Acute oral LD50 for rats >5000 mg/kg. Skin and eye Acute percutaneous LD50 for rabbits >5000 mg/kg. Non-irritating to skin and eyes (rabbits). Mildly sensitising to skin (guinea pig maximisation test), but not likely to be a dermal sensitisation risk to humans. Inhalation LC50 (4 h) for rats >5.0 mg/l air. NOEL (2 y) for rats 25 ppm diet; (18 mo) for mice 200 ppm diet (25 mg/kg b.w. daily); (1 y) for dogs 250 ppm diet (8.2 mg/kg b.w. daily); (90 d) for rats 100, for mice 500, for dogs 500 mg/kg diet. ADI 0.01 mg/kg Other Not genotoxic. Toxicity class WHO (a.i.) U; EPA (formulation) III EC classification R43

ECOTOXICOLOGY
tribenuron-methyl
Birds Acute oral LD50 for bobwhite quail >2250 mg/kg. Dietary LC50 (8 d) for bobwhite quail and mallard ducks >5620 mg/kg. Fish LC50 (96 h) for rainbow trout 738 mg/l. Daphnia LC50 (48 h) 894 mg/l. Algae EC50 (120 h) for green algae 20.8 mg/l. Other aquatic spp. EC50 (14 d) for Lemna 4.24 mg/l. Bees LD50 for honeybees (contact) >100 mg/bee; (oral) >9.1 mg/bee. Worms LC50 for earthworms >1000 mg/kg.

ENVIRONMENTAL FATE
Animals Tribenuron-methyl is rapidly and extensively metabolised in animals by N-demethylation, de-esterfication, hydrolysis of the sulfonylurea bridge, hydroxylation of the phenyl ring and/or O-demethylation of the triazine ring. Plants Tribenuron-methyl is rapidly and extensively metabolised in plants. A major metabolic reaction was N-demethylation; further metabolism is primarily through hydroxylation of the phenyl ring and conjugation with glucose. Soil/Environment DT50 of tribenuron-methyl in field soils of intended use 3.5-5.1 days. No significant photodecomposition under field conditions. Degradation in the soil occurs primarily by aqueous hydrolysis and by direct microbial degradation. Hydrolysis is affected by soil pH, being faster in acidic than alkaline soils. Losses due to volatilisation are not significant.