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52645-53-1
  • names:

    Permethrin

  • CAS号:

    52645-53-1

    MDL Number: MFCD00041809
  • MF(分子式): C21H20Cl2O3 MW(分子量): 391.29
  • EINECS:258-067-9 Reaxys Number:52645-53-1
  • Pubchem ID:36845 Brand:BIOFOUNT
氯菊酯
氯菊酯(Permethrin,52645-53-1):纯品为固体,原药为棕黄色黏稠液体或半固体。氯菊酯有较强的触杀和胃毒作用,具有击倒力强、杀虫速度快的特点。对光较稳定,在同等使用条件下,对害虫抗性发展也较缓慢,对鳞翅目幼虫高效。
货品编码 规格 纯度 价格 (¥) 现价(¥) 特价(¥) 库存描述 数量 总计 (¥)
YZM000778-500mg 500mg >98.0% ¥ 810.00 ¥ 810.00 2-3天
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¥ 0.00
YZM000778-100mg 100mg >98.0% ¥ 487.50 ¥ 487.50 2-3天
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¥ 0.00
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中文别名 氯菊酯(Permethrin,52645-53-1)
英文别名 PermethrinI(氯菊酯,52645-53-1)
CAS号 52645-53-1
SMILES O=C(C1C(C)(C)C1/C=C(Cl)\Cl)OCC2=CC=CC(OC3=CC=CC=C3)=C2
Inchi InChI=1S/C21H20Cl2O3/c1-21(2)17(12-18(22)23)19(21)20(24)25-13-14-7-6-10-16(11-14)26-15-8-4-3-5-9-15/h3-12,17,19H,13H2,1-2H3
InchiKey RLLPVAHGXHCWKJ-UHFFFAOYSA-N
分子式 Formula C21H20Cl2O3
分子量 Molecular Weight 391.29
闪点 FP 159.4±27.7 °C
熔点 Melting point 34-35°C
沸点 Boiling point 465.9±45.0 °C at 760 mmHg
Polarizability极化度 41.9±0.5 10-24cm3
密度 Density 1.3±0.1 g/cm3
蒸汽压 Vapor Pressure 0.0±1.2 mmHg at 25°C
溶解度Solubility 生物体外In Vitro:DMSO溶解度50 mg/mL(127.78 mM;Need ultrasonic)H2O< 0.1 mg/mL(insoluble)
性状 Solid
储藏条件 Storage conditions Pure form -20°C 3 years年 4°C 2 years年 / In solvent溶液中:-80°C 6 months月 -20°C 1 month月
氯菊酯(Permethrin,52645-53-1)毒性:
生物 测试类型 路线 报告剂量(标准化剂量) 影响 参考
bird - domestic LD50 oral 32gm/kg (32000mg/kg)   Defense des Vegetaux. Vol. 32, Pg. 168, 1978.
chicken LD50 oral 7gm/kg (7000mg/kg) BEHAVIORAL: IRRITABILITY

BEHAVIORAL: TREMOR

GASTROINTESTINAL: CHANGES IN STRUCTURE OR FUNCTION OF SALIVARY GLANDS
JAT, Journal of Applied Toxicology. Vol. 7, Pg. 367, 1987.
duck LD50 oral 11300mg/kg (11300mg/kg)   Defense des Vegetaux. Vol. 32, Pg. 168, 1978.
guinea pig LD50 oral 4gm/kg (4000mg/kg)   "Agrochemicals Handbook," with updates, Hartley, D., and H. Kidd, eds., Nottingham, Royal Soc of Chemistry, 1983-86Vol. A316, Pg. 1984,
man LD50 unreported > 4gm/kg (4000mg/kg)   Defense des Vegetaux. Vol. 32, Pg. 168, 1978.
man TDLo oral 2270mg/kg (2270mg/kg)   Journal of Toxicology, Clinical Toxicology. Vol. 36, Pg. 57, 1998.
man TDLo oral 2270mg/kg (2270mg/kg) GASTROINTESTINAL: "HYPERMOTILITY, DIARRHEA"

BEHAVIORAL: COMA
Journal of Toxicology, Clinical Toxicology. Vol. 36, Pg. 57, 1998.
mouse LC50 inhalation 685mg/m3 (685mg/m3)   Yakkyoku. Pharmacy. Vol. 30, Pg. 1635, 1979.
mouse LD50 intraperitoneal 429mg/kg (429mg/kg)   Ecotoxicology and Environmental Safety. Vol. 18, Pg. 27, 1989.
mouse LD50 intravenous 31mg/kg (31mg/kg)   Toxicology and Applied Pharmacology. Vol. 66, Pg. 153, 1982.
mouse LD50 oral 424mg/kg (424mg/kg)   Ecotoxicology and Environmental Safety. Vol. 18, Pg. 27, 1989.
mouse LD50 skin > 10gm/kg (10000mg/kg)   Yakkyoku. Pharmacy. Vol. 30, Pg. 1635, 1979.
mouse LD50 subcutaneous 10gm/kg (10000mg/kg) BEHAVIORAL: ATAXIA

BEHAVIORAL: TREMOR
Bochu Kagaku. Scientific Pest Control. Vol. 41, Pg. 143, 1976.
mouse LD50 unreported 680mg/kg (680mg/kg) BEHAVIORAL: COMA

BEHAVIORAL: ATAXIA

BEHAVIORAL: CONVULSIONS OR EFFECT ON SEIZURE THRESHOLD
Gigiena i Sanitariya. For English translation, see HYSAAV. Vol. 53(9), Pg. 69, 1988.
mouse LDLo intracrebral 600ug/kg (0.6mg/kg)   Toxicology and Applied Pharmacology. Vol. 66, Pg. 290, 1982.
quail LD50 oral 13500mg/kg (13500mg/kg)   Defense des Vegetaux. Vol. 32, Pg. 168, 1978.
rabbit LD50 oral 4gm/kg (4000mg/kg)   "Agrochemicals Handbook," with updates, Hartley, D., and H. Kidd, eds., Nottingham, Royal Soc of Chemistry, 1983-86Vol. A316, Pg. 1984,
rabbit LD50 skin > 2gm/kg (2000mg/kg)   Farm Chemicals Handbook. Vol. -, Pg. C233, 1991.
rat LC50 inhalation 485mg/m3 (485mg/m3)   Gigiena i Sanitariya. For English translation, see HYSAAV. Vol. 55(12), Pg. 21, 1990.
rat LD intravenous > 270mg/kg (270mg/kg)   Nature. Vol. 246, Pg. 169, 1973.
rat LD50 oral 383mg/kg (383mg/kg)   National Technical Information Service. Vol. AD-A047-284,
rat LD50 skin 1750mg/kg (1750mg/kg)   Gigiena i Sanitariya. For English translation, see HYSAAV. Vol. 53(9), Pg. 69, 1988.
rat LD50 subcutaneous 6600mg/kg (6600mg/kg) BEHAVIORAL: ATAXIA

BEHAVIORAL: TREMOR
Bochu Kagaku. Scientific Pest Control. Vol. 41, Pg. 143, 1976.
rat LD50 unreported 537mg/kg (537mg/kg) BEHAVIORAL: ATAXIA

BEHAVIORAL: CONVULSIONS OR EFFECT ON SEIZURE THRESHOLD

BEHAVIORAL: COMA
Gigiena i Sanitariya. For English translation, see HYSAAV. Vol. 53(9), Pg. 69, 1988.

氯菊酯(Permethrin,52645-53-1)物理性质:
生物 测试类型 路线 报告剂量(标准化剂量) 影响 参考
Melting Point 34 deg C   EXP  
log P (octanol-water) 6.5 (none)   EXP  
Water Solubility 0.006 mg/L 20 EXP  
Vapor Pressure 2.18E-08 mm Hg 25 EXP  
Henry's Law Constant 1.87E-06 atm-m3/mole 25 EST  
Atmospheric OH Rate Constant 3.90E-11 cm3/molecule-sec 25 EST  

氯菊酯(Permethrin,52645-53-1)实验注意事项:
1.实验前需戴好防护眼镜,穿戴防护服和口罩,佩戴手套,避免与皮肤接触。
2.实验过程中如遇到有毒或者刺激性物质及有害物质产生,必要时实验操作需要手套箱内完成以免对实验人员造成伤害
3.实验后产生的废弃物需分类存储,并交于专业生物废气物处理公司处理,以免造成环境污染Experimental considerations:
1. Wear protective glasses, protective clothing and masks, gloves, and avoid contact with the skin during the experiment.
2. The waste generated after the experiment needs to be stored separately, and handed over to a professional biological waste gas treatment company to avoid environmental pollution.
Tag:氯菊酯(MSDS,氯菊酯(蒸汽压,氯菊酯(合成,氯菊酯(标准,氯菊酯(应用,氯菊酯(合成,氯菊酯(沸点,氯菊酯(闪点,氯菊酯(用途,氯菊酯(溶解度,氯菊酯(价格,氯菊酯(作用,氯菊酯(结构式,氯菊酯(用处,氯菊酯(毒理性质,氯菊酯(物理性质
产品说明 氯菊酯(Permethrin,52645-53-1)是一种合成的拟除虫菊酯和神经毒素。
IntroductionPermethrinI(氯菊酯,52645-53-1)Permethrin is a synthetic pyrethroid and neurotoxin
Application1氯菊酯(Permethrin,52645-53-1)有较强的触杀和胃毒作用,具有击倒力强、杀虫速度快的特点。对光较稳定,在同等使用条件下,对害虫抗性发展也较缓慢,对鳞翅目幼虫高效。
Application2氯菊酯(Permethrin,52645-53-1)通过阻止钠离子从外向内移动到神经元细胞膜而影响神经元膜,从而破坏调节膜极化的钠通道电流。
Application3
Reaction of 2,6-dichloroquinone-4-chloroimide (Gibbs reagent) with permethrin – an optical sensor for rapid detection of permethrin in treated wood Chemistry Central Journal 2013/PMID: 23867006
Dermal absorption of permethrin following topical administration European Journal of Clinical Pharmacology 2005/PMID: 15947923
Spermiotoxicity and Embryotoxicity of Permethrin in the Sea Urchin Paracentrotus lividus Bulletin of Environmental Contamination and Toxicology 2015/PMID: 25634326
Persistence of indoor permethrin and estimation of dermal and non-dietary exposure Journal of Exposure Science & Environmental Epidemiology 2019/PMID: 30926895
Bioactivity and laundering resistance of five commercially available, factory-treated permethrin-impregnated fabrics for the prevention of mosquito-borne diseases: the need for a standa/PMID: 26738734

The pharmaceutical use of permethrin: sources and behavior during municipal sewage treatment

Abstract

Permethrin entered use in the 1970s as an insecticide in a wide range of applications, including agriculture, horticultural, and forestry, and has since been restricted. In the 21st century, the presence of permethrin in the aquatic environment has been attributed to its use as a human and veterinary pharmaceutical, in particular as a pedeculicide, in addition to other uses, such as a moth-proofing agent. However, as a consequence of its toxicity to fish, sources of permethrin and its fate and behavior during wastewater treatment are topics of concern. This study has established that high overall removal of permethrin (approximately 90%) was achieved during wastewater treatment and that this was strongly dependent on the extent of biological degradation in secondary treatment, with more limited subsequent removal in tertiary treatment processes. Sources of permethrin in the catchment matched well with measured values in crude sewage and indicated that domestic use accounted for more than half of the load to the treatment works. However, removal may not be consistent enough to achieve the environmental quality standards now being derived in many countries even where tertiary treatment processes are applied.


Spermiotoxicity and embryotoxicity of permethrin in the sea urchin Paracentrotus lividus

Abstract

The toxicity of permethrin on the fertilization and early development of sea urchin Paracentrotus lividus embryos were studied. Spermiotoxicity was evaluated on the basis of fertilization rate. Embryotoxicity was determined by comparing the frequency of normal development and malformations in embryos exposed to permethrin throughout their development. Permethrin inhibited fertilization success, and yielded IC25 and IC50 values of 0.58 (CL = 0.44-0.77) and 0.94 (CL = 0.92-0.95) µg/L, respectively. The embryotoxicity of permethrin was concentration dependent indicating a decreased percentage of normally developed plutei with increasing permethrin concentrations: IC25 = 0.195 µg/L (CL = 0.15-0.26) and IC50 = 0.346 µg/L (CF = 0.29-0.41). Associated with the decrease in normal pluteus frequency was an increase in larval malformations as skeleton deformities. The results suggest that permethrin is more highly toxic to embryos than to sperm, and that this insecticide may present a potential risk for the sea urchin in contaminated marine environments.

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