Interfacial Imide Polymerization of Functionalized Filled Microcapsule Templates by the Pickering Emulsion Method for the Rapid Removal of 3,4,5-Trichlorophenol from Wastewater.

["Wei Z", "Ma X", "Wang P", "Pan J"]
Nanomaterials (Basel, Switzerland) 2022
Open on PubMed

In this work, an olive oil-filled composite capsule (C-O/W) adsorbent was prepared for the adsorption of 3,4,5-trichlorophenol (3,4,5-TCP) by the emulsion templating method. Using methylene diisocyanate (HDI) and 1,6-hexanediamine (HMDA) as functional monomers, olive oil was encapsulated in a shell layer composed of graphene oxide and a polymer by interfacial imine polymerization. The contaminant target was efficiently removed by the hydrophobic interaction between olive oil and chlorophenols. The removal of 3,4,5-TCP was remarkable, with an encapsulation rate of 85%. The unique microcapsule structure further enhanced the kinetic performance, which reached 92% of the maximum value within 40 min. The adsorption of different chlorophenols was investigated using 2-chlorophenol (2-CP), 2,6-dichlorophenol (2,6-DCP), and 3,4,5-TCP. The adsorption of 3,4,5-TCP by the C-O/W microcapsules was found to be much higher than that of other chlorophenols. When analyzing a real sample, the content of 3,4,5-TCP was significantly reduced after adsorption by the C-O/W microcapsules, demonstrating that the C-O/W microcapsules were also capable of removing 3,4,5-TCP from a complex environment. This simple and inexpensive preparation strategy provides a new method for the synthesis of functionalized C-O/W microcapsule adsorbents and an effective adsorbent of 3,4,5-TCP.

12 Figures Extracted
Figure 1
Figure 1 PMC
Schematic illustration of the synthesis of C–O/W microcapsules ( a ) and interfacial imine reaction in situ ( b ).
Figure 2
Figure 2 PMC
Fluorescence microscopy of the O/W emulsion in bright field ( a ) and dark field ( b ).
Figure 3
Figure 3 PMC
SEM image of GO ( a ) and C-O/W microcapsules ( b – d ).
Figure 4
Figure 4 PMC
FT-IR spectra of GO, C-O/W microcapsules and olive oil.
Figure 5
Figure 5 PMC
TGA curves of C–O/W microcapsules and olive oil.
Figure 6
Figure 6 PMC
Effects of pH on the adsorption of 3,4,5-TCP by C-O/W microcapsules ( C 0 = 150 mg/L, T = 298 K).
Figure 7
Figure 7 PMC
Non-linear kinetic model fitting curve for 3,4,5-TCP adsorption on C–O/W microcapsules ( a ) and particle diffusion ( b ) model fitting curves of 3,4,...
Figure 8
Figure 8 PMC
Adsorption isotherms of 3,4,5-TCP adsorption onto the C-O/W microcapsules and non-linear fitting curves according to the Langmuir and Freundlich equat...
Figure 9
Figure 9 PMC
Van’t Hoff graph of 3,4,5-TCP adsorption onto C–O/W microcapsules.
Figure 10
Figure 10 PMC
Adsorption capacity of the C–O/W microcapsules towards different PEDs.
Figure 11
Figure 11 PMC
Adsorbed amounts of 3,4,5-TCP (down) and desorption efficiency (up) of the C–O/W microcapsules over 3 cycles.
Figure 12
Figure 12 PMC
HPLC chromatograms of 3,4,5-TCP-spiked water samples.