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Methyl Bromodichloroacetate, a halogenated organic compound with the chemical formula C3H3BrCl2O2, is a colorless liquid characterized by a pungent odor and a powerful lachrymatory effect, causing intense eye irritation. Its high reactivity and ability to undergo various chemical reactions make it a valuable intermediate in the synthesis of pharmaceuticals, agrochemicals, and other organic compounds.

20428-76-6

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20428-76-6 Usage

Uses

Used in Pharmaceutical and Agrochemical Industries:
Methyl Bromodichloroacetate is used as an intermediate in the manufacturing process for various pharmaceuticals and agrochemicals. Its reactivity allows for the synthesis of a wide range of compounds, contributing to the development of new drugs and agricultural products.
Used as a Pesticide and Herbicide in Agriculture:
In the agricultural sector, Methyl Bromodichloroacetate is utilized as a pesticide and herbicide. Its effectiveness in controlling pests and unwanted plant growth supports crop protection and yield enhancement.
Used in Organic Synthesis:
Due to its high reactivity, Methyl Bromodichloroacetate is employed in organic synthesis for the production of various organic compounds. Its ability to participate in different chemical reactions makes it a versatile building block in the synthesis of complex molecules.
However, it is important to note that Methyl Bromodichloroacetate is considered toxic and environmentally harmful. Therefore, it requires careful handling, use, and disposal to minimize potential risks to human health and the environment.

Check Digit Verification of cas no

The CAS Registry Mumber 20428-76-6 includes 8 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 5 digits, 2,0,4,2 and 8 respectively; the second part has 2 digits, 7 and 6 respectively.
Calculate Digit Verification of CAS Registry Number 20428-76:
(7*2)+(6*0)+(5*4)+(4*2)+(3*8)+(2*7)+(1*6)=86
86 % 10 = 6
So 20428-76-6 is a valid CAS Registry Number.

20428-76-6 Well-known Company Product Price

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  • Supelco

  • (47761)  Methylbromodichloroacetatesolution  1000 μg/mL in methyl tert-butyl ether, analytical standard

  • 20428-76-6

  • 000000000000047761

  • 359.19CNY

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20428-76-6SDS

SAFETY DATA SHEETS

According to Globally Harmonized System of Classification and Labelling of Chemicals (GHS) - Sixth revised edition

Version: 1.0

Creation Date: Aug 20, 2017

Revision Date: Aug 20, 2017

1.Identification

1.1 GHS Product identifier

Product name methyl 2-bromo-2,2-dichloroacetate

1.2 Other means of identification

Product number -
Other names Dichlorbromessigsaeure-methylester

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only.
Uses advised against no data available

1.4 Supplier's details

1.5 Emergency phone number

Emergency phone number -
Service hours Monday to Friday, 9am-5pm (Standard time zone: UTC/GMT +8 hours).

More Details:20428-76-6 SDS

20428-76-6Downstream Products

20428-76-6Relevant articles and documents

Occurrence, synthesis, and mammalian cell cytotoxicity and genotoxicity of haloacetamides: An emerging class of nitrogenous drinking water disinfection byproducts

Plewa, Michael J.,Muellner, Mark G.,Richardson, Susan D.,Fasano, Francesca,Buettner, Katherine M.,Woo, Yin-Tak,Mckague, A. Bruce,Wagner, Elizabeth D.

, p. 955 - 961 (2008/03/31)

The haloacetamides, a class of emerging nitrogenous drinking water disinfection byproduct (DBPs), were analyzed for their chronic cytotoxicity and for the induction of genomic DNA damage in Chinese hamster ovary cells. The rank order for cytotoxicity of 13 haloacetamides was DIAcAm > IAcAm > BAcAm > TBAcAm > BIAcAm > DBCAcAm > CIAcAm > BDCAcAm > DBAcAm > BCAcAm > CAcAm > DCAcAm > TCAcAm. The rank order of their genotoxicity was TBAcAm > DIAcAm ≈ IAcAm > BAcAm > DBCAcAm > BIAcAm > BDCAcAm > CIAcAm > BCAcAm > DBAcAm > CAcAm > TCAcAm. DCAcAm was not genotoxic. Cytotoxicity and genotoxicity were primarily determined by the leaving tendency of the halogens and followed the order I > Br > > Cl. With the exception of brominated trihaloacetamides, most of the toxicity rank order was consistent with structure-activity relationship expectations. For di- and trihaloacetamides, the presence of at least one good leaving halogen group (I or Br but not Cl) appears to be critical for significant toxic activity. Log P was not a factor for monohaloacetamides but may play a role in the genotoxicity of trihaloacetamides and possible activation of dihaloacetamides by intracellular GSH and -SH compounds. With the advent of the U.S. EPA Stage 2 DBP regulations, water utilities are considering the use of disinfectants that are alternatives to chlorine. The use of these alternative disinfectants will shift the distribution of DBP chemical classes. The emergence of new, highly toxic iodinated, nitrogenous DBPs, as illustrated by the discovery of bromoiodoacetamide as a new DBP, underscores the importance of comparative toxicity studies to assist in the overall goal of safer drinking water practice.

In situ derivatization/solid-phase microextraction for the determination of haloacetic acids in water

Sarrion,Santos,Galceran

, p. 4865 - 4873 (2007/10/03)

An in situ derivatization solid-phase microextraction method has been developed for the determination of haloacetic acids (HAAs) in water. The analytical procedure involves derivatization of HAAs to their methyl esters with dimethyl sulfate, headspace sampling using solid-phase microextraction (SPME), and gas chromatography-ion trap mass spectrometry (GC/ITMS) determination. Parameters affecting both derivatization efficiency and headspace SPME procedure, such as the selection of the SPME coating, derivatization-extraction time and temperature, and ionic strength, were optimized. The commercially available Carboxen-poly(dimethylsiloxane) (CAR-PDMS) fiber appears to be the most suitable for the determination of HAAs. Moreover, the formation of HAA methyl esters was dramatically improved (up to 90-fold) by the addition of tetrabutylammonium hydrogen sulfate (4.7 μmol) to the sample as ion-pairing agent in the derivatization step. The precision of the in situ derivatization/HS-SPME/GC/ITMS method evaluated using an internal standard gave relative standard deviations (RSDs) between 6.3 and 11.4%. The method was linear over 2 orders of magnitude, and detection limits were compound-dependent, but ranged from 10 to 450 ng/L. The method was compared with the EPA method 552.2 for the analysis of HAAs in various water samples, and good agreement was obtained. Consequently, in situ derivatization/HS-SPME/GC/ITMS is proposed for the analysis of HAAs in water.

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