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. 2023 Mar 3;13(5):927.
doi: 10.3390/nano13050927.

Ecotoxicological Properties of Titanium Dioxide Nanomorphologies in Daphnia magna

Affiliations

Ecotoxicological Properties of Titanium Dioxide Nanomorphologies in Daphnia magna

Freddy Mendoza-Villa et al. Nanomaterials (Basel). .

Abstract

In this work, the structural, vibrational, morphological, and colloidal properties of commercial 15.1 nm TiO2 nanoparticles (NPs) and nanowires (NWs, 5.6 thickness, 74.6 nm length) were studied with the purpose of determining their ecotoxicological properties. This was achieved by evaluating acute ecotoxicity experiments carried out in the environmental bioindicator Daphnia magna, where their 24-h lethal concentration (LC50) and morphological changes were evaluated using a TiO2 suspension (pH = 7) with point of zero charge at 6.5 for TiO2 NPs (hydrodynamic diameter of 130 nm) and 5.3 for TiO2 NWs (hydrodynamic diameter of 118 nm). Their LC50 values were 157 and 166 mg L-1 for TiO2 NWs and TiO2 NPs, respectively. The reproduction rate of D. magna after fifteen days of exposure to TiO2 nanomorphologies was delayed (0 pups for TiO2 NWs and 45 neonates for TiO2 NPs) in comparison with the negative control (104 pups). From the morphological experiments, we may conclude that the harmful effects of TiO2 NWs are more severe than those of 100% anatase TiO2 NPs, likely associated with brookite (36.5 wt. %) and protonic trititanate (63.5 wt. %) presented in TiO2 NWs according to Rietveld quantitative phase analysis. Specifically, significant change in the heart morphological parameter was observed. In addition, the structural and morphological properties of TiO2 nanomorphologies were investigated using X-ray diffraction and electron microscopy techniques to confirm the physicochemical properties after the ecotoxicological experiments. The results reveal that no alteration in the chemical structure, size (16.5 nm for TiO2 NPs and 6.6 thickness and 79.2 nm length for NWs), and composition occurred. Hence, both TiO2 samples can be stored and reused for future environmental purposes, e.g., water nanoremediation.

Keywords: aquatic biota; biomarkers; metal-oxides; nanoparticles; nanowires.

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Conflict of interest statement

The authors declare no conflict of interest.

Figures

Figure 1
Figure 1
Rietveld refinement of X-ray diffractograms obtained for (A) TiO2 NPs and (B) TiO2 NWs. The black line corresponds to experimental data, red line to calculated diffractogram, and the blue line is the residual data between the experimental and calculated data. Green vertical lines indicate the Bragg’s positions and Miller indices which are given by vertical number in parentheses. Blue numbers between parentheses are assigned to brookite phase.
Figure 2
Figure 2
Fit to experimental µ-Raman spectrum for TiO2 NWs sample. The laser power over the sample was of 8.3 mW. Lorentzian subcomponents were highlighted with different colors and main Raman modes are indicated on the top of each identified active optical mode. B indicates the brookite phase.
Figure 3
Figure 3
Zeta potential measurements as a function of pH for TiO2 samples. (A) First measurement for TiO2 NPs, (B) second measurement for TiO2 NPs, (C) first measurement for TiO2 NWs, (D) second measurement for TiO2 NWs.
Figure 4
Figure 4
(a) TEM image of the TiO2 NPs before the ecotoxicity experiment, (b) 10 nm zoomed TEM image, (c) normal distribution of the measurements of the TiO2 NPs from before the ecotoxicity experiment, (d) TEM image of the TiO2 NPs after the ecotoxicity experiment, (e) 5 nm zoomed TEM image, and (f) normal distribution of the TiO2 NPs measurements after the ecotoxicity experiment.
Figure 5
Figure 5
(a) TEM image of the TiO2 NWs before the ecotoxicity experiment, (b) TEM image of the TiO2 NWs after the ecotoxicity experiment. (c) Log-normal distribution of the TiO2 NWs length measurements before the experiment of ecotoxicity and (d) log-normal distribution of the measurements of the length of the TiO2 NWs after the ecotoxicity experiment. (e) Lorentz distribution of the measurements of the diameter of the TiO2 NWs before the ecotoxicity experiment and (f) normal distribution of the measurements of the diameter of the TiO2 NWs after the ecotoxicity experiment.
Figure 6
Figure 6
(A) Mortality (%) for the TiO2 NP sample vs. concentration and (B) probit of mortality vs. log10 concentration (right) fitted with a non-linear cubic function. Goodness of fit (R2 = 1.0). (C) Mortality (%) for the TiO2 NWs sample against concentration and (D) mortality probit vs. log10 concentration (right) fitted with a nonlinear parabolic function. R2 = 0.859.
Figure 7
Figure 7
Boxplot for all morphological parameters (tail, body, heart, antenna, and eye) measured after TiO2 NPs exposure. Numbers above boxes are their p-values, with those written in bold numbers indicating significance (p-value < 0.05).
Figure 8
Figure 8
Box plot for all morphological parameters (tail, body, heart, antenna, and eye) measured after TiO2 NWs exposure. Numbers above boxes are their p-values, with those written in bold numbers indicating significance (p-value < 0.05).
Figure 9
Figure 9
(A) D. magna individual from the negative control, (B) D. magna individual exposed to 37.5 mg L1 of TiO2 NPs, (C) D. magna individual exposed to 75 mg L1 of TiO2 NPs, (D) D. magna individual exposed to 150 mg L1 of TiO2 NPs, (E) D. magna individual exposed to 300 mg L1 of TiO2 NPs, and (F) D. magna individual exposed to 600 mg L1 of TiO2 NPs.
Figure 10
Figure 10
(A) D. magna individual from the negative control, (B) D. magna individual exposed to 50 mg L1 TiO2 NWs, (C) D. magna individual exposed to 100 mg L1 TiO2 NWs, (D) D. magna exposed to 200 mg L1 TiO2 NWs, (E) D. magna individual exposed to 400 mg L1 TiO2 NWs, and (F) D. magna exposed to 800 mg L1 TiO2 NWs.
Figure 11
Figure 11
SAED pattern for before (a) and after (b) TiO2 NPs. SAED pattern for before (c) and after (d) TiO2 NWs. The inset (bottom-right) in blue indicates the indexed rotational average pattern for the identified crystalline phases before and after ecotoxicological experiments.
Figure 12
Figure 12
(a) SEM image, (b) EDS mapping, (c,d) elemental (Ti,O) EDS images for before TiO2 NPs, (e) SEM image, (f) EDS mapping, (g,h) elemental (Ti,O) EDS images for after TiO2 NPs, (i) SEM image, (j) EDS mapping, (k,l) elemental (Ti,O) EDS images for before TiO2 NWs, (m) SEM image, (n) EDS mapping, and (o,p) elemental (Ti,O) EDS images for after TiO2 NWs.
Figure 13
Figure 13
(a) Ti-L2,3 edge and (b) O-K edge in the EELS spectra for before and after TiO2 NPs. (c) Ti-L2,3 edge and (d) O-K edge in the EELS spectra for before and after TiO2 NWs. The upper letters (A, B, C, and D) indicate the characteristic energy loss positions (eV).

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