N,N-Diethyl-3-methylbenzamide - CAS 134-62-3
Catalog number:
134-62-3
Category:
Inhibitor
Not Intended for Therapeutic Use. For research use only.
Molecular Formula:
C12H17NO
Molecular Weight:
191.27
COA:
Inquire
Targets:
Antiparasitic
Description:
N,N-Diethyl-3-methylbenzamide, a benzamide derivative, could be a significant additive in vermifuge.
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Purity:
98%
Appearance:
Powder
Synonyms:
N,N-Diethyl-3-methylbenzamide; DEET; N,N-Diethyl-m-toluamide; Diethyltoluamide; Metadelphene
Solubility:
10 mM in DMSO
Storage:
-20ºC Freeze
MSDS:
Inquire
Application:
N,N-Diethyl-3-methylbenzamide could be a significant additive in vermifuge.
Shelf Life:
As supplied, 2 years from the QC date provided on the Certificate of Analysis, when stored properly
Quantity:
Grams-Kilos
Density:
0.9955
InChIKey:
MMOXZBCLCQITDF-UHFFFAOYSA-N
InChI:
InChI=1S/C12H17NO/c1-4-13(5-2)12(14)11-8-6-7-10(3)9-11/h6-9H,4-5H2,1-3H3
Canonical SMILES:
CCN(CC)C(=O)C1=CC(=CC=C1)C
1.Organic contaminants in Great Lakes tributaries: Prevalence and potential aquatic toxicity.
Baldwin AK1, Corsi SR2, De Cicco LA2, Lenaker PL2, Lutz MA2, Sullivan DJ2, Richards KD2. Sci Total Environ. 2016 Jun 1;554-555:42-52. doi: 10.1016/j.scitotenv.2016.02.137. Epub 2016 Mar 4.
Organic compounds used in agriculture, industry, and households make their way into surface waters through runoff, leaking septic-conveyance systems, regulated and unregulated discharges, and combined sewer overflows, among other sources. Concentrations of these organic waste compounds (OWCs) in some Great Lakes tributaries indicate a high potential for adverse impacts on aquatic organisms. During 2010-13, 709 water samples were collected at 57 tributaries, together representing approximately 41% of the total inflow to the lakes. Samples were collected during runoff and low-flow conditions and analyzed for 69 OWCs, including herbicides, insecticides, polycyclic aromatic hydrocarbons, plasticizers, antioxidants, detergent metabolites, fire retardants, non-prescription human drugs, flavors/fragrances, and dyes. Urban-related land cover characteristics were the most important explanatory variables of concentrations of many OWCs. Compared to samples from nonurban watersheds (<15% urban land cover) samples from urban watersheds (>15% urban land cover) had nearly four times the number of detected compounds and four times the total sample concentration, on average.
2.Personal Protection Measures Against Mosquitoes, Ticks, and Other Arthropods.
Alpern JD1, Dunlop SJ2, Dolan BJ3, Stauffer WM4, Boulware DR5. Med Clin North Am. 2016 Mar;100(2):303-16. doi: 10.1016/j.mcna.2015.08.019.
Arthropod-associated diseases are a major cause of morbidity among travelers. Obtaining a detailed travel itinerary and understanding traveler-specific and destination-specific risk factors can help mitigate the risk of vector-borne diseases. DEET, picaridin, PMD, and IR3535 are insect repellents that offer sufficient protection against arthropod bites. IR3535 does not provide adequate protection against Anopheles mosquitoes, and should be avoided in malaria-endemic regions. General protective measures, such as bite avoidance, protective clothing, insecticide-treated bed nets, and insecticide-treated clothing, should be recommended, especially in malaria-endemic areas. Spatial repellents may prevent nuisance biting, but have not been shown to prevent against vector-borne disease.
3.Sources and transport of contaminants of emerging concern: A two-year study of occurrence and spatiotemporal variation in a mixed land use watershed.
Fairbairn DJ1, Karpuzcu ME2, Arnold WA3, Barber BL4, Kaufenberg EF2, Koskinen WC5, Novak PJ3, Rice PJ5, Swackhamer DL2. Sci Total Environ. 2016 May 1;551-552:605-13. doi: 10.1016/j.scitotenv.2016.02.056. Epub 2016 Feb 18.
The occurrence and spatiotemporal variation of 26 contaminants of emerging concern (CECs) were evaluated in 68 water samples in 2011-2012 in the Zumbro River watershed, Minnesota, U.S.A. Samples were collected across a range of seasonal/hydrological conditions from four stream sites that varied in associated land use and presence of an upstream wastewater treatment plant (WWTP). Selected CECs included human/veterinary pharmaceuticals, personal care products, pesticides, phytoestrogens, and commercial/industrial compounds. Detection frequencies and concentrations varied, with atrazine, metolachlor, acetaminophen, caffeine, DEET, and trimethoprim detected in more than 70% of samples, acetochlor, mecoprop, carbamazepine, and daidzein detected in 30%-50% of samples, and 4-nonylphenol, cotinine, sulfamethoxazole, erythromycin, tylosin, and carbaryl detected in 10%-30% of samples. The remaining target CECs were not detected in water samples. Three land use-associated trends were observed for the detected CECs.
4.A national-scale assessment of micro-organic contaminants in groundwater of England and Wales.
Manamsa K1, Crane E1, Stuart M2, Talbot J1, Lapworth D1, Hart A3. Sci Total Environ. 2016 Apr 10. pii: S0048-9697(16)30444-2. doi: 10.1016/j.scitotenv.2016.03.017. [Epub ahead of print]
A large variety of micro-organic (MO) compounds is used in huge quantities for a range of purposes (e.g. manufacturing, food production, healthcare) and is now being frequently detected in the aquatic environment. Interest in the occurrence of MO contaminants in the terrestrial and aquatic environments continues to grow, as well as in their environmental fate and potential toxicity. However, the contamination of groundwater resources by MOs has a limited evidence base compared to other freshwater resources. Of particular concern are newly 'emerging contaminants' such as pharmaceuticals and lifestyle compounds, particularly those with potential endocrine disrupting properties. While groundwater often has a high degree of protection from pollution due to physical, chemical and biological attenuation processes in the subsurface compared to surface aquatic environments, trace concentrations of a large range of compounds are still detected in groundwater and in some cases may persist for decades due to the long residence times of groundwater systems.
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CAS 134-62-3 N,N-Diethyl-3-methylbenzamide

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