Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2019 Apr 18;11(4):712.
doi: 10.3390/polym11040712.

Anisotropic Cellulose Nanofibers/Polyvinyl Alcohol/Graphene Aerogels Fabricated by Directional Freeze-drying as Effective Oil Adsorbents

Affiliations

Anisotropic Cellulose Nanofibers/Polyvinyl Alcohol/Graphene Aerogels Fabricated by Directional Freeze-drying as Effective Oil Adsorbents

Lijie Zhou et al. Polymers (Basel). .

Abstract

Under the current situation of frequent oil spills, the development of green and recyclable high-efficiency oil-absorbing aerogel materials has attracted wide attention from researchers. In this study, we report a high-strength, three-dimensional hydrophobic cellulose nanofiber (CNF)/polyvinyl alcohol (PVA)/graphene oxide (GO) composite aerogel with an anisotropic porous structure, which was fabricated by directional freeze-drying technology using anisotropically grown ice crystals as a template, followed by hydrophobic treatment with a simple dip coating process. The prepared composite aerogel presented anisotropic multi-level pore microstructures, low density (17.95 mg/cm3) and high porosity (98.8%), good hydrophobicity (water contact angle of 142°) and great adsorption capacity (oil absorption reaching 96 times its own weight). More importantly, the oriented aerogel had high strength, whose compressive stress at 80% strain reached 0.22 MPa and could bear more than 22,123 times its own weight without deformation. Therefore, the CNF/PVA/GO composite aerogel prepared by a simple and easy-to-operate directional freeze-drying method is a promising absorbent for oil-water separation.

Keywords: cellulose nanofibers; directional freeze-drying; graphene; oil absorption; polyvinyl alcohol.

PubMed Disclaimer

Conflict of interest statement

The authors declare no conflict of interest.

Figures

Figure 1
Figure 1
Schematic representation of (a) the directional freeze-drying method; (b) the non-directional freeze-drying method and (c) the refrigerator freeze-drying method. Cellulose nanofiber (CNF); polyvinyl alcohol (PVA); graphene oxide (GO).
Figure 2
Figure 2
Schematic showing experimental process of the samples.
Figure 3
Figure 3
Macroscopic pictures and microstructures of aerogels formed by different freeze-drying methods. (a), (d) and (g) are macro photographs of d-MCPGA, r-MCPGA, n-MCPGA, respectively; (b) vertical section of d-MCPGA; (c) cross section of d-MCPGA; (ef) internal SEM image of r-MCPGA; (h) vertical section of n-MCPGA; (i) cross section of n-MCPGA.
Figure 4
Figure 4
FTIR spectra of (a) CNFs, (b) GO, (c) PVA, (d) CNF/PVA/GO and (e) TMCS /CNF/PVA/GO aerogels.
Figure 5
Figure 5
XRD patterns of (a) CNFs, (b) PVA, (c) GO, (d) CNF/PVA/GO and (e) TMCS/CNF/PVA/GO aerogels.
Figure 6
Figure 6
Compressive behavior of aerogels (d-MCPGA, r-MCPGA, n-MCPGA) prepared by different freeze-drying methods consisting of CNFs, PVA and GO.
Figure 7
Figure 7
Comparison of the compressive strength of different materials [49,50,51,52,53].
Figure 8
Figure 8
(a) Ultra-light cylindrical d-MCPGA supported by young leaves; (bd) the pre, middle and post processes of the d-MCPGA supporting a 500 g mass load.
Figure 9
Figure 9
Water contact angle of (a) CPGA, (b) d-MCPGA, (c) r-MCPGA and (d) n-MCPGA.
Figure 10
Figure 10
Removal of corn oil (dyed with Sudan red) from the water surface using MCPGA.
Figure 11
Figure 11
Absorption capacity of MCPGA (d-MCPGA, r-MCPGA, n-MCPGA) for different oils and organic liquids.
Figure 12
Figure 12
The absorption capacity of MCPGA (d-MCPGA, r-MCPGA, n-MCPGA) to adsorb (a) pump oil; (b) engine oil and (c) corn oil as a function of time.

References

    1. Al-Majed A.A., Adebayo A.R., Hossain M.E. A sustainable approach to controlling oil spills. J. Environ. Manag. 2012;113:213–227. doi: 10.1016/j.jenvman.2012.07.034. - DOI - PubMed
    1. Shannon M.A., Bohn P.W., Elimelech M., Georgiadis J.G., Marinas B.J., Mayes A.M. Science and technology for water purification in the coming decades. Nature. 2008;452:301–310. doi: 10.1038/nature06599. - DOI - PubMed
    1. Vilcáez J., Li L., Hubbard S.S. A new model for the biodegradation kinetics of oil droplets: Application to the Deepwater Horizon oil spill in the Gulf of Mexico. Geochem. Trans. 2013;14:4. doi: 10.1186/1467-4866-14-4. - DOI - PMC - PubMed
    1. Ge J., Ye Y.D., Yao H.B., Zhu X., Wang X., Wu L., Yu S.H. Pumping through porous hydrophobic/oleophilic materials: An alternative technology for oil spill remediation. Angew. Chem. Int. Ed. 2014;126:3686–3690. doi: 10.1002/ange.201310151. - DOI - PubMed
    1. Liu H., Geng B., Chen Y., Wang H. A review on the aerogel-type oil sorbents derived from nanocellulose. ACS Sustain. Chem. Eng. 2016;5:49–66. doi: 10.1021/acssuschemeng.6b02301. - DOI

LinkOut - more resources