Pyrithiobac sodium 嘧草硫醚

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嘧硫草醚

  英文名: Pyrithiobac-sodium
别名:2-Chloro-6-{(4,6-dimethoxy-2-pyrimidinyl)thio}benzoic acid sodium salt; Sodium 2-chloro-6-((4,6-dimethoxy-2-pyrimidinyl)thio)benzoate; Pyrithiobac sodium salt; DPX-PE350; KIH 2031; Staple
产品名称:嘧草硫醚; 嘧硫草醚; 2-氯-6-(4,6-二甲氧基嘧啶-2-基硫)苯甲酸钠
分子结构: 完整的应该是:
分子式:C13H10ClN2NaO4S
分子量:348.74
CAS 登录号:123343-16-8
分析方法:高效液相色谱,外标法测定
物理化学性质
熔点 233-234°C
DECOMPOSITION 234°C
水溶性 705 g/L (pH7)

  防治对象:嘧硫草醚为侧链氨基酸合成抑制剂,用于防治棉花田一年生和多年生阔叶杂草,稗草,施药量为35-105g/ha
嘧草硫醚是日本组合化学公司研制,组合化学公司,埯原公司和美国杜邦公司共同开发,于94年上市的新一代广谱除草剂。
它可以防除一年生和多年生禾本科杂草和大多数阔叶杂草。对难除杂草如各种牵牛、苍耳、苘麻、刺黄花禾念,田普、阿拉伯高粱等都有很好的防除效果。
它是一种乙酰乳酸合成酶(从S)抑制剂,通过阻止氨基酸的生物合成而达到防除杂草的作用。
化学结构类型:嘧啶水扬酸类。
适用作物:主要用于棉田,苗前苗后均可使用,土地处理和茎叶处理均可。
用量少:茎叶处理,3g(活性物)/亩,土地处理7g(活性物)/亩。
安全性:对棉花高度安全。?因为它可在棉花植株中快速降解。
国外己推广的剂型:水分散颗粒剂。
我们正在研究中的嘧草硫醚除草地膜,对该除草剂的应用推广开劈了另外一个有效途径。

  二、市场前景:
目前市场上除草剂品种中,广谱除草剂较少,防治阔叶杂草除草剂具多,兼有防治阔叶杂草和禾本科杂草,而且对多年杂草和难除杂草效果显著者尚不多。由于嘧草硫醚同时具.备上述特点。而且高效、低毒、用量很小,会使化学除草的水平上一大台阶,也必然有相当大的市场。特别是近几年我国农药品种中,除草剂是销售量增长最快的一类,这类新型除草剂必将占有相当份额。
目前我国化学除草面积1995年为4133万公顷。1999年为6000万公顷,农田化学除草己进入快速发展地区。除草剂,特别是高效、低毒、安全性高的除草剂极待迅速发展。
目前我国棉花种植普遍使用地膜覆盖技术,相应要求要有可以土地处理的高效除草剂相配套。嘧草硫醚从两个方面可以满足棉花地膜覆盖的要求,第一,可以复膜前作土地处理(播种前或播种后);第二,发展嘧草硫醚的除草地膜。(我们研制的嘧草硫醚除草地膜正在实验阶段)这种形式,不用另外施加除草剂,很受棉农欢迎。


 

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pyrithiobac-sodium
Herbicide
HRAC B WSSA 2; pyrimidinyloxybenzoic analogue

  pyrithiobac-sodium

NOMENCLATURE
Common name pyrithiobac-sodium (BSI, pa E-ISO, ANSI)
IUPAC name sodium 2-chloro-6-(4,6-dimethoxypyrimidin-2-ylthio)benzoate
Chemical Abstracts name sodium 2-chloro-6-(4,6-dimethoxypyrimidin-2-ylthio)benzoate
CAS RN [123343-16-8] sodium salt; [123342-93-8] parent acid Development codes KIH-2031 (Kumiai); DPX-PE 350 (DuPont)

PHYSICAL CHEMISTRY
Composition Tech. is >93%. Mol. wt. 348.7 M.f. C13H10ClN2NaO4S Form Off white powder at ambient temperature. M.p. 233.8-234.2 ºC (decomp.) V.p. 4.80 ´ 10-6 mPa (25 °C) KOW logP = 0.6 (pH 5), -0.84 (pH 7) S.g./density 1.609 Solubility In water 264 (pH 5), 705 (pH 7), 690 (pH 9), 728 (unbuffered) (all in g/l, 20 °C). In acetone 812, methanol 270 ´ 103, n-hexane 10, dichloromethane 8.38 (all in mg/l, 20 °C). Stability Stable in water (32 d, pH 5-9, 27 °C) and to heat (15 d at 54 °C). pKa 2.34

COMMERCIALISATION
History Discovered in 1988 by Kumiai Chemical Industry Co., Ltd. Reported by S. Takahashi et al., Proc. Br. Crop Prot. Conf. - Weeds, 1991, 1, 57-62. Developed jointly by Kumiai, Ihara Chemical Industry Co., Ltd and E. I. du Pont de Nemours Co. Introduced by DuPont in USA in 1995. Patents US 4932999; EP 315889 Manufacturers Ihara/Kumiai

APPLICATIONS
Biochemistry Branched chain amino acid synthesis (ALS or AHAS) inhibitor. Selectivity is based on differing rates of metabolism. Mode of action Initial symptoms are cessation of growth and yellowing, followed by necrosis of terminal tissue and death. Uses Control of a wide range of broad-leaved weeds in cotton. Weeds controlled post-emergence, at 40-105 g/ha include Ipomoea spp., Xanthium spp., and Amaranthus spp.; those controlled pre-emergence, at 35-50 g/ha include Amaranthus spp., Sida spinosa, and Abutilon theophrasti. Phytotoxicity Non-phytotoxic to cotton when applied as directed. Formulation types SP; SL. Selected products: 'Staple' (DuPont, Kumiai)

OTHER PRODUCTS
Mixtures: 'Staple Plus' (+ glyphosate-isopropylammonium) (DuPont)

ANALYSIS
Details from DuPont.

MAMMALIAN TOXICOLOGY
Oral Acute oral LD50 for male rats 3300, female rats 3200 mg/kg. Skin and eye Acute percutaneous LD50 for rabbits >2000 mg/kg. Non-irritating to skin; irritating to eyes (rabbits). Inhalation LC50 (4 h) for rats >6.9 mg/l. NOEL (2 y) for male rats 58.7, female rats 278 mg/kg b.w. daily; (78 w) for male mice 217, female mice 319 mg/kg b.w. daily. Other Non-mutagenic. Non-teratogenic (rats and rabbits). Non-oncogenic (rats). Toxicity class WHO (a.i.) U; EPA (formulation) III

ECOTOXICOLOGY
Birds Acute oral LD50 for bobwhite quail >2250 mg/kg b.w. Dietary LC50 (5 d) for mallard ducks and bobwhite quail >5620 mg/kg diet. Fish LC50 (96 h) for bluegill sunfish >930, rainbow trout >1000, sheepshead minnow >145 mg/l. Daphnia LC50 (48 h) >1100 mg/l. Algae EC50 (5 d) for Selenastrum capricornutum 107 mg/l; NOEC for Selenastrum capricornutum 22.8 mg/l. Bees LD50 (48 h, contact) >25 mg/bee.

ENVIRONMENTAL FATE
Animals More than 90% of radiolabelled pyrithiobac-sodium, applied orally and intravenously at 5 mg/kg to rats, was excreted in urine and faeces within 48 h; the major excreted metabolite was the O-desmethyl derivative. Pyrithiobac-sodium applied to hens and goats at 10 ppm diet was also substantially excreted, mostly unchanged, but the O-desmethyl derivative was a significant metabolite; residues in the kidney of both species were £0.06 ppm and were lower in liver, muscle and fat. Plants Amounts of pyrithiobac-sodium in cotton leaves rapidly decreased, following foliar application; at 62 dat, no residues were found; major metabolites found in foliage were the phenol formed by mono-demethylation, and its glucose conjugate. No residues were found in mature cotton seed on lint. Soil/Environment Microbial and photochemical degradation play a major role in degradation in the environment; DT50 in silty soil 60 d. Kd 0.32 (sandy loam), 0.60, 0.38, 0.75 (3 silty loam soils).