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. 2015 Jan;30(1):109-18.
doi: 10.1002/tox.21917. Epub 2013 Oct 30.

Evaluation of alpha and gamma aluminum oxide nanoparticle accumulation, toxicity, and depuration in Artemia salina larvae

Affiliations

Evaluation of alpha and gamma aluminum oxide nanoparticle accumulation, toxicity, and depuration in Artemia salina larvae

Mehmet Ates et al. Environ Toxicol. 2015 Jan.

Abstract

In this study, Artemia salina (crustacean filter feeders) larvae were used as a test model to investigate the toxicity of aluminum oxide nanoparticles (Al2O3 NPs) on marine microorganisms. The uptake, toxicity, and elimination of α-Al2O3 (50 nm and 3.5 μm) and γ-Al2O3 (5 nm and 0.4 μm) NPs were studied. Twenty-four and ninety-six hour exposures of different concentrations of Al2O3 NPs to Artemia larvae were conducted in a seawater medium. When suspended in water, Al2O3 NPs aggregated substantially with the sizes ranging from 6.3 nm to >0.3 µm for spherical NPs and from 250 to 756 nm for rod-shaped NPs. The phase contrast microscope images showed that NPs deposited inside the guts as aggregates. Inductively coupled plasma mass spectrometry analysis showed that large particles (3.5 μm α-Al2O3) were not taken up by Artemia, whereas fine NPs (0.4 μm γ-Al2O3) and ultra-fine NPs (5 nm γ-Al2O3 and 50 nm α-Al2O3) accumulated substantially. Differences in toxicity were detected as changing with NP size and morphology. The malondialdehyde levels indicated that smaller γ-Al2O3 (5 nm) NPs were more toxic than larger γ-Al2O3 (0.4 µm) particulates in 96 h. The highest mortality was measured as 34% in 96 h for γ-Al2O3 NPs (5 nm) at 100 mg/L (LC50 > 100 mg/L). γ-Al2O3 NPs were more toxic than α-Al2O3 NPs at all conditions.

Keywords: Artemia; accumulation; aluminum oxide; nanoparticles; oxidative stress; toxicity.

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Figures

Figure 1
Figure 1
Powdered XRD spectrum for Al2O3 nanoparticles (A: α-Al2O3 50 nm; B: α-Al2O3 3.5 μm; C: γ-Al2O3 5nm; D: γ-Al2O3 0.4 μm) sample.
Figure 1
Figure 1
Powdered XRD spectrum for Al2O3 nanoparticles (A: α-Al2O3 50 nm; B: α-Al2O3 3.5 μm; C: γ-Al2O3 5nm; D: γ-Al2O3 0.4 μm) sample.
Figure 1
Figure 1
Powdered XRD spectrum for Al2O3 nanoparticles (A: α-Al2O3 50 nm; B: α-Al2O3 3.5 μm; C: γ-Al2O3 5nm; D: γ-Al2O3 0.4 μm) sample.
Figure 1
Figure 1
Powdered XRD spectrum for Al2O3 nanoparticles (A: α-Al2O3 50 nm; B: α-Al2O3 3.5 μm; C: γ-Al2O3 5nm; D: γ-Al2O3 0.4 μm) sample.
Figure 2
Figure 2
The images of α-Al2O3 and γ-Al2O3 nanoparticles (A: α-Al2O3 50 nm; B: α-Al2O3 3.5 μm; C: γ-Al2O3 5nm; D: γ-Al2O3 0.4 μm).
Figure 2
Figure 2
The images of α-Al2O3 and γ-Al2O3 nanoparticles (A: α-Al2O3 50 nm; B: α-Al2O3 3.5 μm; C: γ-Al2O3 5nm; D: γ-Al2O3 0.4 μm).
Figure 2
Figure 2
The images of α-Al2O3 and γ-Al2O3 nanoparticles (A: α-Al2O3 50 nm; B: α-Al2O3 3.5 μm; C: γ-Al2O3 5nm; D: γ-Al2O3 0.4 μm).
Figure 2
Figure 2
The images of α-Al2O3 and γ-Al2O3 nanoparticles (A: α-Al2O3 50 nm; B: α-Al2O3 3.5 μm; C: γ-Al2O3 5nm; D: γ-Al2O3 0.4 μm).
Figure 3
Figure 3
Phase contrast microscope images of the nanoparticles inside Artemia larvae. (A: The guts are empty in controls. B: Nanoparticles are visible as a dark line inside the guts of treatments).
Figure 3
Figure 3
Phase contrast microscope images of the nanoparticles inside Artemia larvae. (A: The guts are empty in controls. B: Nanoparticles are visible as a dark line inside the guts of treatments).
Figure 4
Figure 4
Accumulation and elimination (in 24 h) profiles of α-Al2O3 (a) and γ-Al2O3 (b) nanoparticles by Artemia larvae for 24 h and 96 h exposure (μg/g).
Figure 4
Figure 4
Accumulation and elimination (in 24 h) profiles of α-Al2O3 (a) and γ-Al2O3 (b) nanoparticles by Artemia larvae for 24 h and 96 h exposure (μg/g).
Figure 5
Figure 5
Percent mortality rates for Artemia salina larvae from exposure to α-Al2O3 and γ-Al2O3 particles for 24 h and 96 h.
Figure 6
Figure 6
Malondialdehyde levels measured in Artemia larvae exposed to α-Al2O3 and γ-Al2O3 nanoparticles for 24 h and 96 h exposure (nmol/g)

References

    1. Adams LK, Lyon DY, Alvarez PJJ. Comparative eco-toxicity of nanoscale ZnO and Zn, SiO2, and ZnO water suspensions. Water. Res. 2006;40:3527–3532. - PubMed
    1. Alizadeh-Gheshlaghi E, Shaabani B, Khodayari A, Azizian-Kalandaragh Y, Rahimi R. Investigation of the catalytic activity of nano-sized CuO, Co3O4 and CuCo2O4 powders on thermal decomposition of ammonium perchlorate. Powder Technol. 2012;217:330–339.
    1. Arslan Z, Ates M, McDuffy W, Agachan MS, Farah IO, Yu WW, Bednar AJ. Probing metabolic stability of CdSe nanoparticles: alkaline extraction of free cadmium from liver and kidney samples of rats exposed to CdSe nanoparticles. J. Haz. Mat. 2011;192:192–199. - PMC - PubMed
    1. Ates M, Daniels J, Arslan Z, Farah OI. Effects of aqueous suspensions of titanium dioxide nanoparticles on Artemia salina: assessment of nanoparticle aggregation, accumulation, and toxicity. Environ. Monit. Asses. 2013;185:3339–3348. - PMC - PubMed
    1. Boumaza A, Djelloul A, Guerrab F. Specific signatures of α-alumina powders prepared by calcinations of boehmite or gibbsite. Powder Technol. 2010;201:177–180.

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