Table 1.
Adsorbent | Micropollutant | Highlights of adsorption behavior | References |
---|---|---|---|
Magnetic CrFe2O4 nanocomposite prepared sonochemically using a nonionic surfactant | Mo6+ | Thermodynamic data indicated that adsorption of Mo6+ ions was spontaneous and endothermic | Gamal et al. (2021) |
The adsorbent could be regenerated through the desorption of more than 98% of Mo6+ with 1.0 mol L−1 sodium hydroxide | |||
Magnetic nanocomposite Co-multiwalled carbon nanotubes | Methylene blue | Maximum adsorption capacity=324.34 mg g−1 | Çalımlı (2021) |
Adsorption was endothermic and followed pseudo-second-order kinetic model | |||
Fe3O4-MnO2-EDTA composite | Cu2+ ions from binary or ternary metal adsorbate system | As-synthesized adsorbents yielded high Cu2+ selective adsorption (both in binary and ternary systems) | Chen and Xie (2020) |
In comparison with Fe3O4-MnO2, the magnetic Fe3O4-MnO2-EDTA nanoparticles resulted in rapid magnetic separation with high selectivity for Cu2+ | |||
Magnetic CoFe2O4/graphene oxide adsorbents | Methylene blue, methyl orange and Rhodamine B | Adsorption of organic dyes for CoFe2O4/graphene oxide composite mainly attributable to contribution of graphene oxide | Chang et al. (2020) |
Superior adsorption capacity qe(max) for methylene blue and Rhodamine B at 355.9 mg g−1 and 284.9 mg g−1, respectively (Langmuir adsorption model). | |||
Selective adsorption with order of adsorption capacity as follows: Methylene blue > Rhodamine B > methyl orange | |||
Hydroxypropyl-β- cyclodextrin-polyurethane/graphene oxide magnetic nanoconjugates | Cr6+ and Pb2+ | Adsorption capacity of adsorbents for Cr6+ and Pb2+ at 987 mg g−1 and 1399 mg g−1, respectively, and adsorption followed pseudo-second-order kinetics | Nasiri and Alizadeh (2021) |
Reusability of adsorbent makes it a promising candidate for Pb2+ removal from aqueous solutions | |||
This magnetic composite was endowed with a high adsorption performance and good reusability for heavy metal ions | |||
Magnetic molecular imprint polymer networks synthesized from vinyl-functionalized magnetic nanoparticles | Antibiotics (ciprofloxacin and erythromycin) | Networks exhibited high binding capacity toward erythromycin and ciprofloxacin at 70 mg g−1 and 32 mg g−1, respectively. | Kuhn et al. (2020) |
Networks were recyclable and retained their binding capacity after 4 cycles | |||
Results demonstrated that the networks developed had high binding capacity, selectivity and recyclability | |||
The networks can be utilized both for monitoring and removal of hazardous antibiotic pollutants potentially present in different samples and food products | |||
Phosphoramide-functionalized magnetic nanoparticles | Uranium | High maximum adsorption capacity=95.2 mg U g−1 sorbent | Singhal et al. (2020) |
80% adsorption achieved for pH 4–8 with maximum adsorption observed at pH 6 | |||
Higher than 90% uranium extraction was recorded during adsorption studies conducted using drinking water, tap water and seawater | |||
Inferences were made in the study as follows: high adsorption capacity, low cost, less equilibration time, easy separation from matrix and non-toxicity of the adsorbent constitute some key merits sought when envisioning the process at an industrial scale | |||
Magnetic tubular carbon nanofibers | Cu2+ | Maximum adsorption capacity of nanofibers for Cu2+=375.93 mg g−1 | Ahmad et al. (2020b) |
Porous morphology, large surface area and tubular structure of the nanofibers contributed to the rapid and highest adsorption of Cu2+ ions | |||
Langmuir adsorption isotherm model best described adsorption data | |||
The nanofibers developed have exhibited excellent regenerability when treated with EDTA | |||
Magnesium–zinc ferrites | Cr6+ and Ni2+ | Mg0·2Zn0·8Fe2O4 yielded best adsorption capacity (30.49 mg g−1) | Tatarchuk et al. (2021) |
Mg0·4Zn0·6Fe2O4 was observed to be the most effective adsorbent for removing Ni2+ (93.2%) | |||
Adjustment of magnesium content to an optimal value can enhance mixed ferrites’ ability to remove heavy metals from aqueous solutions | |||
Sulfur-functionalized polyamidoamine dendrimer/magnetic Fe3O4 hybrid materials | Hg2+ and Ag+ | Maximum adsorption capacity for Hg2+ and Ag+ was 0.8 mmol g−1 and 1.29 mmol g−1, respectively | Luan et al. (2021) |
Good adsorption selectivity (100% selective adsorption of Hg2+ in the presence of Ni2+, Zn2+ and Mn2+) | |||
Excellent regeneration characteristics, and reuse repeatedly over four use cycles | |||
Magnetic sodium alginate (SA)-based Fe3O4@SA-Ca gel beads | Direct Orange 26 in aqueous solutions | Gel had ultrahigh adsorption capacity of 1252 mg g−1 | Li and Lin (2021) |
Dye removal efficiency=96.2 % (298 K, 50 mg polymer dosage, 2.6 g L−1 initial dye concentration, pH 2.0, 90 min adsorption time) | |||
Adsorption was spontaneous and exothermic | |||
Gel was easily separated and recuperated from aqueous solutions without secondary pollution |
EDTA Ethylenediaminetetraacetic acid, SA Sodium alginate