2006
DOI: 10.1016/j.watres.2006.02.003
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Sorption of acetaminophen, 17α-ethynyl estradiol, nalidixic acid, and norfloxacin to silica, alumina, and a hydrophobic medium

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Cited by 154 publications
(54 citation statements)
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“…For norfloxacin, at pH below 6.10 the positively charged form of the molecule is dominant, while at pH between 6.2 and 8.5, the zwitterionic form becomes dominant. [32] Soil pH could change the species composition of norfloxacin, resulting in different behavior and effects. The effect of pH value on degradation of norfloxacin should also be considered in future studies.…”
Section: Discussionmentioning
confidence: 99%
“…For norfloxacin, at pH below 6.10 the positively charged form of the molecule is dominant, while at pH between 6.2 and 8.5, the zwitterionic form becomes dominant. [32] Soil pH could change the species composition of norfloxacin, resulting in different behavior and effects. The effect of pH value on degradation of norfloxacin should also be considered in future studies.…”
Section: Discussionmentioning
confidence: 99%
“…Some 254 pharmaceuticals contain nitrogen-containing functional groups which are basic 255 and will therefore be readily protonated to give a cation under certain conditions 256 [19,20]. To evaluate the cation-exchange properties of the HXLPP-WCX 257 sorbent, and establish the scope of its sorption characteristics, we selected a 258 group of acidic and basic pharmaceuticals with variable pK a values (Table 1).…”
Section: Spe Optimisation 252mentioning
confidence: 99%
“…Many techniques have been investigated for NOR decontamination, including adsorption (Lorphensri et al 2006), photodegradation , and chlorine oxidation (Dodd et al 2005), among which adsorption is considered to be a simple and effective method to remove NOR. Previous research on adsorption of fluoroquinolone antimicrobials by different environmental matrices has included silica, alumina (Lorphensri et al 2006), soils (MacKay and Seremet 2008), clay minerals (Figueroa-Diva et al 2010), natural aquifer material (Hari et al 2005), oxide minerals (Gu and Karthikeyan 2005), carbon nanotubes , and activated carbon (Liu et al 2011;Carabineiro et al 2011;Ahmed and Theydan 2011), but few studies about its sorption by biochar have been done.…”
Section: Introductionmentioning
confidence: 99%
“…Previous research on adsorption of fluoroquinolone antimicrobials by different environmental matrices has included silica, alumina (Lorphensri et al 2006), soils (MacKay and Seremet 2008), clay minerals (Figueroa-Diva et al 2010), natural aquifer material (Hari et al 2005), oxide minerals (Gu and Karthikeyan 2005), carbon nanotubes , and activated carbon (Liu et al 2011;Carabineiro et al 2011;Ahmed and Theydan 2011), but few studies about its sorption by biochar have been done. Generally, the adsorption mechanisms of fluoroquinolone antimicrobials with model sorbent phases have been documented to be cation exchange, cation bridging, surface complexation, hydrophobic effect, electrostatic interaction, and electron-donor-acceptor interactions .…”
Section: Introductionmentioning
confidence: 99%