-
氯菊酯
- 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
| 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 | ¥ 0.00 | ||
| YZM000778-100mg | 100mg | >98.0% | ¥ 487.50 | ¥ 487.50 | 2-3天 | ¥ 0.00 |
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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 |
| 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。 |
| Introduction | PermethrinI(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 |
| 警示圖 | |
| 危險(xiǎn)性 | warning |
| 危險(xiǎn)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(duì)身體有害 |
| 安全防護(hù) | P264處理后徹底清洗+P280戴防護(hù)手套/穿防護(hù)服/戴防護(hù)眼罩/戴防護(hù)面具+P305如果進(jìn)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(hù)理 |
| 備注 | 實(shí)驗(yàn)過程中防止吸入、食入,做好安全防護(hù) |
| 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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