-
氯菊酯
- 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
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 | ¥ 0.00 | ||
YZM000778-100mg | 100mg | >98.0% | ¥ 487.50 | ¥ 487.50 | 2-3天 | ¥ 0.00 |
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 |
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。 |
Introduction | PermethrinI(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 |
警示图 | |
危险性 | warning |
危险性警示 | Not available |
安全声明 | H303吞入可能有害+H313皮肤接触可能有害+H2413吸入可能对身体有害 |
安全防护 | P264处理后彻底清洗+P280戴防护手套/穿防护服/戴防护眼罩/戴防护面具+P305如果进入眼睛+P351用水小心冲洗几分钟+P338取出隐形眼镜(如果有)并且易于操作,继续冲洗+P337如果眼睛刺激持续+P2393获得医疗建议/护理 |
备注 | 实验过程中防止吸入、食入,做好安全防护 |
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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