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26002-80-2
  • names:

    Phenothrin

  • CAS號:

    26002-80-2

    MDL Number: MFCD00078716
  • MF(分子式): C23H26O3 MW(分子量): 350.45
  • EINECS:247-431-2 Reaxys Number:
  • Pubchem ID:4767 Brand:BIOFOUNT
苯醚菊酯
苯醚菊酯(26002-80-2,Phenothrin)是淡黃色至黃棕色液體,無腐蝕性。苯醚菊酯是環(huán)丙烷羧酸酯。苯醚菊酯具有擬除蟲菊酯殺蟲劑的作用。 苯醚菊酯衍生自菊花酸。
貨品編碼 規(guī)格 純度 價格 (¥) 現(xiàn)價(¥) 特價(¥) 庫存描述 數(shù)量 總計 (¥)
YZM000803-200mg 200mg >95% ¥ 0.00 ¥ 0.00 Backorder
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YZM000803-100mg 100mg >95% ¥ 488.00 ¥ 488.00 Backorder
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中文別名 苯醚菊酯(26002-80-2,Phenothrin);苯氧司林;苯諾茨林;酚丁滅虱;聚醚菊酯
英文別名 Phenothrin(26002-80-2);Sumithrin;Phenoxythrin;Pibutin
CAS號 26002-80-2
Inchi InChI=1S/C23H26O3/c1-16(2)13-20-21(23(20,3)4)22(24)25-15-17-9-8-12-19(14-17)26-18-10-6-5-7-11-18/h5-14,20-21H,15H2,1-4H3
InchiKey SBNFWQZLDJGRLK-UHFFFAOYSA-N
分子式 Formula C23H26O3
分子量 Molecular Weight 350.45
溶解度Solubility
性狀 淺黃色至黃棕色液體
儲藏條件 Storage conditions 存放在陰涼干燥處,短期(數(shù)天至數(shù)周)在0-4℃,長期(數(shù)月至數(shù)年)在-20℃。

苯醚菊酯(26002-80-2,Phenothrin)毒性測試:
生物 測試類型 路線 報告劑量(標(biāo)準化劑量) 影響 參考
    mouse           LD50            intraperitoneal   > 5gm/kg (5000mg/kg)                                   Japan Pesticide Information. Vol. (37), Pg. 30, 1980.               
mouse LD50 intravenous 354mg/kg (354mg/kg)   Japan Pesticide Information. Vol. (37), Pg. 30, 1980.
mouse LD50 oral 10gm/kg (10000mg/kg)   Yakkyoku. Pharmacy. Vol. 32, Pg. 47, 1981.
mouse LD50 skin > 5gm/kg (5000mg/kg)   Japan Pesticide Information. Vol. (37), Pg. 30, 1980.
mouse LD50 subcutaneous > 5gm/kg (5000mg/kg)   Japan Pesticide Information. Vol. (37), Pg. 30, 1980.
quail LD50 oral > 2150mg/kg (2150mg/kg)   Pesticide Manual. Vol. 9, Pg. 667, 1991.
rat LD50 intraperitoneal > 5gm/kg (5000mg/kg)   Japan Pesticide Information. Vol. (37), Pg. 30, 1980.
rat LD50 intravenous 354mg/kg (354mg/kg)   Japan Pesticide Information. Vol. (37), Pg. 30, 1980.
rat LD50 oral > 10gm/kg (10000mg/kg)   Yakkyoku. Pharmacy. Vol. 37, Pg. 1481, 1986.
rat LD50 skin > 5gm/kg (5000mg/kg)   Japan Pesticide Information. Vol. (37), Pg. 30, 1980.
rat LD50 subcutaneous > 5gm/kg (5000mg/kg)   Japan Pesticide Information. Vol. (37), Pg. 30, 1980.

苯醚菊酯(26002-80-2,Phenothrin)實驗注意事項:
1.實驗前需戴好防護眼鏡,穿戴防護服和口罩,佩戴手套,避免與皮膚接觸。
2.實驗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,必要時實驗操作需要手套箱內(nèi)完成以免對實驗人員造成傷害
3.實驗后產(chǎn)生的廢棄物需分類存儲,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

Phenothrin(26002-80-2) 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:苯醚菊酯(26002-80-2,Phenothrin),苯醚菊酯試劑,苯醚菊酯殺蟲劑,苯醚菊酯的純度,苯醚菊酯的作用,苯醚菊酯的生產(chǎn),苯醚菊酯的價格,苯醚菊酯的廠家,苯醚菊酯的外觀,苯醚菊酯的MSDS,苯醚菊酯的溶解度,苯醚菊酯的儲存條件
產(chǎn)品說明 苯醚菊酯(26002-80-2,Phenothrin)是環(huán)丙烷羧酸酯。苯醚菊酯具有擬除蟲菊酯殺蟲劑的作用。
IntroductionPhenothrin (26002-80-2, 苯醚菊酯) is a cyclopropane carboxylate. Phenothrin has the effect of pyrethroid insecticides.
Application1
Application2
Application3
警示圖
危險性 warning
危險性警示 Not available
安全聲明 H303吞入可能有害+H313皮膚接觸可能有害+H2413吸入可能對身體有害
安全防護 P264處理后徹底清洗+P280戴防護手套/穿防護服/戴防護眼罩/戴防護面具+P305如果進入眼睛+P351用水小心沖洗幾分鐘+P338取出隱形眼鏡(如果有)并且易于操作,繼續(xù)沖洗+P337如果眼睛刺激持續(xù)+P2393獲得醫(yī)療建議/護理
備注 實驗過程中防止吸入、食入,做好安全防護
象形圖 Irritant
 
Environmental Hazard
信號警告 Warning
GHS危險說明

Aggregated GHS information provided by 186 companies from 8 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies.

Reported as not meeting GHS hazard criteria by 8 of 186 companies. For more detailed information, please visit ECHA C&L website

Of the 7 notification(s) provided by 178 of 186 companies with hazard statement code(s):

H302 (96.63%): Harmful if swallowed [Warning Acute toxicity, oral]

H312 (96.63%): Harmful in contact with skin [Warning Acute toxicity, dermal]

H332 (96.07%): Harmful if inhaled [Warning Acute toxicity, inhalation]

H400 (99.44%): Very toxic to aquatic life [Warning Hazardous to the aquatic environment, acute hazard]

H410 (100%): Very toxic to aquatic life with long lasting effects [Warning Hazardous to the aquatic environment, long-term hazard]

Information may vary between notifications depending on impurities, additives, and other factors. The percentage value in parenthesis indicates the notified classification ratio from companies that provide hazard codes. Only hazard codes with percentage values above 10% are shown.

防范說明代碼

P261, P264, P270, P271, P273, P280, P301+P312, P302+P352, P304+P312, P304+P340, P312, P322, P330, P363, P391, and P501

(The corresponding statement to each P-code can be found at the GHS Classification page.)

Electrochemical Determination of Phenothrin in Agricultural Formulations, Vegetables, and Storage Bags of Wheat and Rice by Differential Pulse Adsorptive Stripping Voltammetry (DP-AdSV)
A Comparison of the Toxicity of Synergized and Technical Formulations of Permethrin, Sumithrin, and Resmethrin to Trout(Archives of Environmental Contamination and Toxicology,2005)
Pyrethroid Metabolism: Studies on Cis- and Trans-Phenothrins, and Related Epoxide Intermediates(Toxic Interfaces of Neurones, Smoke and Genes,1986)
Kinetics and Photophysical Mechanism of Sunlight Photolysis of Unstable Resmethrin and Phenothrin in Aerosols and Thin Films
The photochemical behaviour of five household pyrethroid insecticides and a synergist as studied by photo-solid-phase microextraction

1.Asymmetric syntheses and bio-evaluation of novel chiral esters derived from substituted tetrafluorobenzyl alcohol.
Xu S1, Li H1, Wang X1, Chen C1, Cao M1, Cao X2. Bioorg Med Chem Lett. 2014 Jun 15;24(12):2734-6. doi: 10.1016/j.bmcl.2014.04.055. Epub 2014 Apr 21.

A series of novel chiral esters derived from tetrafluorobenzyl alcohol were designed and prepared via asymmetric synthesis. The target molecules have been identified on the basis of analytical spectra data. All newly synthesized compounds have been screened their potential insecticidal activity against Plutella xylostella compared with those of fenvalerate and d-trans-phenothrin by standard method, and the respective pairs of enantiomers (3-B1-R/S, 3-C1-R/S, 3-D1-R/S) indicated significantly different activities.

2.Susceptibility of Adult Cat Fleas (Siphonaptera: Pulicidae) to Insecticides and Status of Insecticide Resistance Mutations at the Rdl and Knockdown Resistance Loci.
Rust MK1, Vetter R, Denholm I, Blagburn B, Williamson MS, Kopp S, Coleman G, Hostetler J, Davis W, Mencke N, Rees R, Foit S, Böhm C, Tetzner K. Parasitol Res. 2015 Aug;114 Suppl 1:S7-18. doi: 10.1007/s00436-015-4512-1.

The susceptibility of 12 field-collected isolates and 4 laboratory strains of cat fleas, Ctenocephalides felis was determined by topical application of some of the insecticides used as on-animal therapies to control them. In the tested field-collected flea isolates the LD50 values for fipronil and imidacloprid ranged from 0.09 to 0.35 ng/flea and 0.02 to 0.19 ng/flea, respectively, and were consistent with baseline figures published previously. The extent of variation in response to four pyrethroid insecticides differed between compounds with the LD50 values for deltamethrin ranging from 2.3 to 28.2 ng/flea, etofenprox ranging from 26.7 to 86.7 ng/flea, permethrin ranging from 17.5 to 85.6 ng/flea, and d-phenothrin ranging from 14.5 to 130 ng/flea. A comparison with earlier data for permethrin and deltamethrin implied a level of pyrethroid resistance in all isolates and strains. LD50 values for tetrachlorvinphos ranged from 20.0 to 420.0 ng/flea.

3.Susceptibility of field-collected mosquitoes in central New Jersey to organophosphates and a pyrethroid.
Sun D, Indelicato N, Petersen J, Williges E, Unlu I, Farajollahi A. J Am Mosq Control Assoc. 2014 Jun;30(2):138-42.

Chemical insecticides are the primary means to control mosquitoes, and mosquito control programs must regularly monitor for resistance of mosquito vectors to commonly used insecticides to ensure the efficacy and sustainability of active ingredients. We performed insecticide resistance bioassays to test the susceptibility of field-collected mosquitoes in central New Jersey to 1 larvicide (temephos) and 2 adulticides (malathion and sumithrin). Larval susceptibility of Culex pipiens pipiens to temephos provided median concentration (LC50) and 95% lethal concentration (LC95) values of 1.108 microg/l and 2.02 microg/l, respectively. Bottle bioassays of adult Aedes albopictus showed that 100% mortality was achieved at 35-min exposure to sumithrin and at 40-min to malathion. Baseline values were obtained using both temephos and sumithrin. Our bioassays indicate satisfactory susceptibility to temephos and sumithrin in Ae. albopictus and Cx. p. pipiens field populations in central New Jersey.

4.Comparison of phenothrin mousse, phenothrin lotion, and wet-combing for treatment of head louse infestation in the UK: a pragmatic randomised, controlled, assessor blind trial.
Burgess IF1, Brown CM1, Nair P2. F1000Res. 2014 Jul 10;3:158. doi: 10.12688/f1000research.2026.1. eCollection 2014.

In this investigation of effectiveness of an alternative pediculicide dosage form, we recruited 228 children and 50 adult participants from Bedfordshire, UK, to a randomised, controlled, assessor blind trial comparing two insecticide products with mechanical removal of lice as a control group.  Participants using insecticide were treated with either the investigative 0.5% phenothrin mousse, for 30 minutes, or 0.2% phenothrin lotion, for 2 hours as the reference product.  Both treatments were applied only once, followed by shampoo washing.  Those treated by wet-combing with conditioner were combed 4 times over 12 days.  Parents/carers carried out the treatments to mimic normal consumer use.  The outcome measure was the absence of lice, 14 days after treatment for the insecticides, and up to 14 days after completion of combing.  Intention to treat analysis of the outcomes for 275 participants showed success for phenothrin mousse in 21/105

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