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52645-53-1
  • names:

    Permethrin

  • CAS號(hào):

    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):純品為固體,原藥為棕黃色黏稠液體或半固體。氯菊酯有較強(qiáng)的觸殺和胃毒作用,具有擊倒力強(qiáng)、殺蟲速度快的特點(diǎn)。對(duì)光較穩(wěn)定,在同等使用條件下,對(duì)害蟲抗性發(fā)展也較緩慢,對(duì)鱗翅目幼蟲高效。
貨品編碼 規(guī)格 純度 價(jià)格 (¥) 現(xiàn)價(jià)(¥) 特價(jià)(¥) 庫存描述 數(shù)量 總計(jì) (¥)
YZM000778-500mg 500mg >98.0% ¥ 810.00 ¥ 810.00 2-3天
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YZM000778-100mg 100mg >98.0% ¥ 487.50 ¥ 487.50 2-3天
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中文別名 氯菊酯(Permethrin,52645-53-1)
英文別名 PermethrinI(氯菊酯,52645-53-1)
CAS號(hào) 52645-53-1
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
溶解度Solubility 生物體外In Vitro:DMSO溶解度50 mg/mL(127.78 mM;Need ultrasonic)H2O< 0.1 mg/mL(insoluble)
性狀 Solid
儲(chǔ)藏條件 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 測(cè)試類型 路線 報(bào)告劑量(標(biāo)準(zhǔn)化劑量) 影響 參考
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)物理性質(zhì):
生物 測(cè)試類型 路線 報(bào)告劑量(標(biāo)準(zhǔn)化劑量) 影響 參考
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)實(shí)驗(yàn)注意事項(xiàng):
1.實(shí)驗(yàn)前需戴好防護(hù)眼鏡,穿戴防護(hù)服和口罩,佩戴手套,避免與皮膚接觸。
2.實(shí)驗(yàn)過程中如遇到有毒或者刺激性物質(zhì)及有害物質(zhì)產(chǎn)生,必要時(shí)實(shí)驗(yàn)操作需要手套箱內(nèi)完成以免對(duì)實(shí)驗(yàn)人員造成傷害
3.實(shí)驗(yàn)后產(chǎn)生的廢棄物需分類存儲(chǔ),并交于專業(yè)生物廢氣物處理公司處理,以免造成環(huán)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(蒸汽壓,氯菊酯(合成,氯菊酯(標(biāo)準(zhǔn),氯菊酯(應(yīng)用,氯菊酯(合成,氯菊酯(沸點(diǎn),氯菊酯(閃點(diǎn),氯菊酯(用途,氯菊酯(溶解度,氯菊酯(價(jià)格,氯菊酯(作用,氯菊酯(結(jié)構(gòu)式,氯菊酯(用處,氯菊酯(毒理性質(zhì),氯菊酯(物理性質(zhì)
產(chǎn)品說明 氯菊酯(Permethrin,52645-53-1)是一種合成的擬除蟲菊酯和神經(jīng)毒素。
IntroductionPermethrinI(氯菊酯,52645-53-1)Permethrin is a synthetic pyrethroid and neurotoxin
Application1氯菊酯(Permethrin,52645-53-1)有較強(qiáng)的觸殺和胃毒作用,具有擊倒力強(qiáng)、殺蟲速度快的特點(diǎn)。對(duì)光較穩(wěn)定,在同等使用條件下,對(duì)害蟲抗性發(fā)展也較緩慢,對(duì)鱗翅目幼蟲高效。
Application2氯菊酯(Permethrin,52645-53-1)通過阻止鈉離子從外向內(nèi)移動(dòng)到神經(jīng)元細(xì)胞膜而影響神經(jīng)元膜,從而破壞調(diào)節(jié)膜極化的鈉通道電流。
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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