1999
DOI: 10.1021/ac990453q
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Analysis of Cationic Surfactants by Microbore High-Performance Liquid Chromatography−Electrospray Mass Spectrometry

Abstract: In the work reported here, a state-of-the-art analytical method for the quantitative analysis of cationic surfactants in environmental matrixes is described. High-performance liquid chromatography on-line coupled via an electrospray interface to a mass spectrometer (HPLC-ESP-MS) is used for the determination of ditallowdimethylammonium chloride (DTDMAC) and two of its most important substitution products, diethylester dimethylammonium chloride (DEEDMAC) and Diesterquaternary (DEQ). Using the analytical method … Show more

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Cited by 52 publications
(33 citation statements)
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References 14 publications
(23 reference statements)
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“…Data for aqueous environments comprise data on surface water, usually river water, as well as one study on marine water, which was included in this data set (Ding and Liao 2001;Ferrer and Furlong 2002;Merino et al 2003b;Ding and Tsai 2003;UBA Wien 2005;Shrivas and Wu 2007;Bassarab et al 2011;Olkowska et al 2013;Radke et al 1999;Merino et al 2003b). The overall mean and median values for QAAC cumulative concentrations for wastewater equal 271 and 11 lg L -1 , respectively, and those for surface water equal 33 and 40 lg L -1 , respectively.…”
Section: Marine and Freshwater Environmentsmentioning
confidence: 99%
“…Data for aqueous environments comprise data on surface water, usually river water, as well as one study on marine water, which was included in this data set (Ding and Liao 2001;Ferrer and Furlong 2002;Merino et al 2003b;Ding and Tsai 2003;UBA Wien 2005;Shrivas and Wu 2007;Bassarab et al 2011;Olkowska et al 2013;Radke et al 1999;Merino et al 2003b). The overall mean and median values for QAAC cumulative concentrations for wastewater equal 271 and 11 lg L -1 , respectively, and those for surface water equal 33 and 40 lg L -1 , respectively.…”
Section: Marine and Freshwater Environmentsmentioning
confidence: 99%
“…In order to effectively monitor CS + pollution, it is necessary to develop a convenient and appropriate fast analytical method for the separation and detection of these quaternary ammonium surfactants. The most common methods to determine CS + in environmental, pharmaceutical, cosmetic, and other samples are spectrophotometry,8, 9 high‐performance liquid chromatography (HPLC),10 gas chromatography (GC),11 high‐performance liquid chromatography‐electrospray ionization mass spectrometry (HPLC‐ESI/MS),12 and capillary electrophoresis (CE) 13, 14. These methods require large quantities of reagents and are time consuming and tedious in the analysis process.…”
Section: Introductionmentioning
confidence: 99%
“…Since these surfactants containing different alkyl chain lengths are added as ingredients to end products such as shampoo and conditioners, it is of importance to develop analytical separation/detection methods in order to monitor the composition that can ultimately affect the performance of these end products. To date, the analysis of ATMA 1 has been accomplished using different methods such as GC-MS requiring conversion to tertiary amine [1][2][3], HPLC utilizing various detection such as chemiluminescent nitrogen [4], ESI-MS [5][6][7], and conductometric detection [8]. In addition, CE methods using indirect photometric detection [9][10][11][12][13] or MS detection [14] have also been employed for the analysis of ATMA As a recent alternative to these traditional methods of analysis, CEC is gaining recognition as a powerful separation technique that combines both electrophoretic separation based on charge-to-mass ratio, along with HPLC retention mechanisms including ion-exchange and hydrophobic/hydrophilic interactions with a stationary phase.…”
Section: Introductionmentioning
confidence: 99%