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
. 2021 Jan 17;13(1):66.
doi: 10.3390/toxins13010066.

Enhanced Photocatalytic Removal of Cyanotoxins by Al-Doped ZnO Nanoparticles with Visible-LED Irradiation

Affiliations

Enhanced Photocatalytic Removal of Cyanotoxins by Al-Doped ZnO Nanoparticles with Visible-LED Irradiation

Majdi Benamara et al. Toxins (Basel). .

Abstract

The ZnO-based visible-LED photocatalytic degradation and mineralization of two typical cyanotoxins, microcystin-LR (MC-LR), and anatoxin-A were examined. Al-doped ZnO nanoparticle photocatalysts, in Al:Zn ratios between 0 and 5 at.%, were prepared via sol-gel method and exhaustively characterized by X-ray diffraction, transmission electron microscopy, UV-vis diffuse reflectance spectroscopy, photoluminescence spectroscopy, and nitrogen adsorption-desorption isotherms. With both cyanotoxins, increasing the Al content enhances the degradation kinetics, hence the use of nanoparticles with 5 at.% Al content (A5ZO). The dosage affected both cyanotoxins similarly, and the photocatalytic degradation kinetics improved with photocatalyst concentrations between 0.5 and 1.0 g L-1. Nevertheless, the pH study revealed that the chemical state of a species decisively facilitates the mutual interaction of cyanotoxin and photocatalysts. A5ZO nanoparticles achieved better outcomes than other photocatalysts to date, and after 180 min, the mineralization of anatoxin-A was virtually complete in weak alkaline medium, whereas only 45% of MC-LR was in neutral conditions. Moreover, photocatalyst reusability is clear for anatoxin-A, but it is adversely affected for MC-LR.

Keywords: LEDs; ZnO-doped nanoparticles; anatoxin-(a); cyanotoxins; microcystin-LR; photocatalysis; visible light.

PubMed Disclaimer

Conflict of interest statement

The authors declare no conflict of interest.

Figures

Figure 1
Figure 1
X-ray diffraction patterns of (a) A0ZO, (b) A1ZO, (c) A3ZO, and (d) A5ZO nanopowders with Williamson-Hall plots (inset).
Figure 2
Figure 2
Transmission electron microscopic images and grain sizes distribution of (a) A0ZO, (b) A1ZO, (c) A3ZO, and (d) A5ZO nanopowders. Scale bar: 50 nm.
Figure 3
Figure 3
(a) UV-Vis DRS absorption spectra in diffuse reflectance spectroscopy and (b) photoluminescence spectra of ZnO and Al-doped ZnO nanoparticles at room temperature.
Figure 4
Figure 4
Photocatalytic activity of ZnO and AZO nanoparticle photocatalysts (photocatalyst dosage = 0.5 g L−1) in the photocatalytic degradation of (a) microcystin-LR (MC-LR) and (b) anatoxin-A under visible light-emitting diode (LED) irradiation at pH 7.0 and 20 °C. Effect of A5ZO photocatalyst dosage on the photocatalytic degradation of (c) MC-LR and (d) anatoxin-A under visible LED irradiation at pH 7.0 and 20 °C. Effect of pH of A5ZO photocatalyst (0.5 g L−1) on the photocatalytic degradation of (e) MC-LR and (f) anatoxin-A under visible LED irradiation at 20 °C. Error bars indicate standard deviations of the four replicated experiments.
Figure 5
Figure 5
Mineralization (180 min) as a function of pH for AZO nanoparticle photocatalysts (photocatalyst dosage = 0.5 g L−1) of (a) microcystin-LR and (b) anatoxin-A under visible-light-emitting-diode irradiation at 20 °C. Error bars indicate standard deviations of the four replicated experiments.
Figure 6
Figure 6
(a) Degradation of MC-LR at pH 7.0 and anatoxin-A at pH 9.0, in five consecutive reusability experiments with A5ZO nanoparticle photocatalysts (photocatalyst dosage = 0.5 g L−1), after 80 min of visible light-emitting diode (LED) irradiation at 20 °C. (b) Time-dependent concentration of Zn(II) ions from A5ZO at different pH levels during 40 h of visible-LED irradiation at 20 °C. Error bars indicate standard deviations of the four replicated experiments.
Scheme 1
Scheme 1
Synthesis of AZO nanoparticles by the sol-gel method.

References

    1. Huisman J., Codd G.A., Paerl H.W., Ibelings B.W., Verspagen J.M.H., Visser P.M. Cyanobacterial blooms. Nat. Rev. Microbiol. 2018;16:471–483. doi: 10.1038/s41579-018-0040-1. - DOI - PubMed
    1. Buratti F.M., Manganelli M., Vichi S., Stefanelli M., Scardala S., Testai E., Funari E. Cyanotoxins: Producing organisms, occurrence, toxicity, mechanism of action and human health toxicological risk evaluation. Arch. Toxicol. 2017;91:1049–1130. doi: 10.1007/s00204-016-1913-6. - DOI - PubMed
    1. Dittmann E., Wiegand C. Cyanobacterial toxins—Occurrence, biosynthesis and impact on human affairs. Mol. Nutr. Food Res. 2006;50:7–17. doi: 10.1002/mnfr.200500162. - DOI - PubMed
    1. Meriluoto J., Blaha L., Bojadzija G., Bormans M., Brient L., Codd G.A., Drobac D., Faassen E.J., Fastner J., Hiskia A., et al. Toxic cyanobacteria and cyanotoxins in European waters—Recent progress achieved through the CYANOCOST action and challenges for further research. Adv. Oceanogr. Limnol. 2017;8:161–178. doi: 10.4081/aiol.2017.6429. - DOI
    1. Liu Y., Chen W., Li D., Huang Z., Shen Y., Liu Y. Cyanobacteria-/cyanotoxin-contaminations and eutrophication status before Wuxi Drinking Water Crisis in Lake Taihu, China. J. Environ. Sci. 2011;23:575–581. doi: 10.1016/S1001-0742(10)60450-0. - DOI - PubMed

Publication types