Aromatic amines in surface waters of The Netherlands
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Cited by (49)
Atlantic cod (Gadus morhua) embryos are highly sensitive to short-term 3,4-dichloroaniline exposure
2021, Toxicology ReportsCitation Excerpt :Due to its tendency to form covalent bonds with the organic fraction of sediments and suspended matter, 3,4-DCA is subjected to vertical transport from the water column to sediments and therefore, constituting a potential risk for marine benthopelagic species [14]. 3,4-DCA has been detected in various fresh-, brackish- and marine aquatic environments at concentrations up to 0.7 μg/L [15–20]. As part of the NORMAN list (http://www.norman-network.net/), it is widely recognized as an emerging aquatic pollutant and has a well-documented toxicity towards many standard test species, including several freshwater fish during their early life stages (ELS) [21,22].
Optimization of a solid-phase microextraction technique for chloro‑ and nitro- substituted aromatic compounds using design of experiments
2020, Journal of Chromatography ACitation Excerpt :However, derivatization methods often have low selectivity and poor reproducibility. The environmental concentrations of these compounds span several orders of magnitude, from the low μg/L (0.02–2 μg/L) range in agricultural runoff [19,20], up to the high mg/L (1–260 mg/L) next to chemical production sites [21–23]. As a result, a sample preconcentration step is sometimes necessary to reach field-relevant concentration levels.
Impregnation of GO with Cu<sup>2+</sup> for enhancement of aniline adsorption and antibacterial activity
2017, Journal of Water Process EngineeringCitation Excerpt :It is also used in pharmaceuticals, pesticides and plastics industries [2,3]. The discharge of wastewaters of these industries is a major source of aromatic amines in the aquatic environment [4–6]. Furthermore, these compounds are formed during decomposition of azo-dyes in the environment and biological treatment of the dye-containing wastewaters [7–12].
Nontargeted detection and identification of (aromatic) amines in environmental samples based on diagnostic derivatization and LC-high resolution mass spectrometry
2017, ChemosphereCitation Excerpt :Concentrations in surface waters are typically lower with, for example, about 10 μg L−1 aniline in the River Rhine (Wegman and De Korte, 1981; Börnick and Schmidt, 2006). Despite the increasing focus of water monitoring on emerging pollutants and despite their hazard potential, there is only limited information on the occurrence of aromatic amines in surface waters, mainly with regard to textile industry emissions (Wegman and De Korte, 1981; Schmidt et al., 2000; Mazzo et al., 2006; Pielesz et al., 2002). Expanding targeted analytical methods for more individual compounds might help to broaden our knowledge, but will not be able to address so far unknown transformation and by-products, for example from the vast number of aromatic amine-based dyes.