2022
DOI: 10.1016/j.seppur.2021.120067
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Efficient trap of polar aromatic amines in environmental waters by electroenhanced solid phase microextraction based on porous monolith doped with carboxylic carbon nanotubes

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Cited by 21 publications
(7 citation statements)
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“…Indeed, water solubility of amines is largely due to their capability for hydrogen bonding. [56] Further, we observed a sp 3 -CH stretching peak of CH 2 and CH 3 groups in PHB at 2977.86 cm −1 (Figure S2A, Supporting Information) [57] and an aromatic -NH stretch of secondary amine peak in melanin at 3213.16 cm −1 (Figure S2B, Supporting Information). [58] A carboxylic -C = O stretching peak was observed in PHB and melanin at 1726.15 and 1716.51 cm −1 respectively.…”
Section: Chemical Analysis and Tracing Of Fibers Elemental Compositionmentioning
confidence: 92%
“…Indeed, water solubility of amines is largely due to their capability for hydrogen bonding. [56] Further, we observed a sp 3 -CH stretching peak of CH 2 and CH 3 groups in PHB at 2977.86 cm −1 (Figure S2A, Supporting Information) [57] and an aromatic -NH stretch of secondary amine peak in melanin at 3213.16 cm −1 (Figure S2B, Supporting Information). [58] A carboxylic -C = O stretching peak was observed in PHB and melanin at 1726.15 and 1716.51 cm −1 respectively.…”
Section: Chemical Analysis and Tracing Of Fibers Elemental Compositionmentioning
confidence: 92%
“…The first report of AAs in surface waters came in the 1970s with the detection of 3,4-dichloroaniline and 2-chloroaniline in the Rhine River . Bioanalytical findings have indicated the contribution of AAs to the mutagenic effects observed in surface water samples across the globe, including North America, Europe, ,, Brazil, and Japan. , Despite these findings, chemical/quantification data on AAs in surface waters are limited: primary AAs have been quantified in Turkish river and seawater; Italian, German, and Iranian rivers; and Chinese surface waters. ,,, However, most of these studies are limited to method validation, and extensive screenings have not been done. There is growing literature covering tire rubber-associated AAs in surface waters , given the particular concern about their aquatic toxicity, and increases in surface water concentrations of tire rubber-associated AAs are documented during rain events, which suggests a clear pathway from surface runoff to surface waters …”
Section: Environmental Presence and Fatementioning
confidence: 99%
“…With the aid of an electric or magnetic field, better extraction performance can be achieved. Electric field-enhanced SPME has been used for the fast extraction and desorption of polar aromatic amines (AAs) and phenoxycarboxylic acids herbicides (PCAHs), and their precise quantifications at trace level have been realized. , On the other hand, magnetic nanoparticles (Fe 3 O 4 ) have been composited with other polymers and further in situ polymerized in a capillary for IT-SPME. The fabricated monolithic adsorbents present porous and super paramagnetic properties and possess abundant functional groups, which have exhibited satisfactory performance for the capture of inorganic species (mercury, chromium, and selenium).…”
Section: Spme In Environmental Analysismentioning
confidence: 99%