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Aggregation and Colloidal Stability of Commercially Available Al₂O₃ Nanoparticles in Aqueous Environments.

作者信息

Mui Julie, Ngo Jennifer, Kim Bojeong

机构信息

Department of Earth and Environmental Science, College of Science and Technology, Temple University, Philadelphia, PA 19122, USA.

出版信息

Nanomaterials (Basel). 2016 May 13;6(5):90. doi: 10.3390/nano6050090.


DOI:10.3390/nano6050090
PMID:28335218
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC5302499/
Abstract

The aggregation and colloidal stability of three, commercially-available, gamma-aluminum oxide nanoparticles (γ-Al₂O₃ NPs) (nominally 5, 10, and 20-30 nm) were systematically examined as a function of pH, ionic strength, humic acid (HA) or clay minerals (e.g., montmorillonite) concentration using dynamic light scattering and transmission electron microscopy techniques. NPs possess pH-dependent surface charges, with a point of zero charge (PZC) of pH 7.5 to 8. When pH < PZC, γ-Al₂O₃ NPs are colloidally stable up to 100 mM NaCl and 30 mM CaCl₂. However, significant aggregation of NPs is pronounced in both electrolytes at high ionic strength. In mixed systems, both HA and montmorillonite enhance NP colloidal stability through electrostatic interactions and steric hindrance when pH ≤ PZC, whereas their surface interactions are quite limited when pH > PZC. Even when pH approximates PZC, NPs became stable at a HA concentration of 1 mg·L. The magnitude of interactions and dominant sites of interaction (basal planes edge sites) are significantly dependent on pH because both NPs and montmorillonite have pH-dependent (conditional) surface charges. Thus, solution pH, ionic strength, and the presence of natural colloids greatly modify the surface conditions of commercial γ-Al₂O₃ NPs, affecting aggregation and colloidal stability significantly in the aqueous environment.

摘要
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/5126f67e6f11/nanomaterials-06-00090-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/03d8e1100260/nanomaterials-06-00090-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/d82e1644de0c/nanomaterials-06-00090-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/8f720237d5b3/nanomaterials-06-00090-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/b59b7af3cff4/nanomaterials-06-00090-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/70661b0a50f1/nanomaterials-06-00090-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/4bc61f6d34c8/nanomaterials-06-00090-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/f4d219f03e55/nanomaterials-06-00090-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/5126f67e6f11/nanomaterials-06-00090-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/03d8e1100260/nanomaterials-06-00090-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/d82e1644de0c/nanomaterials-06-00090-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/8f720237d5b3/nanomaterials-06-00090-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/b59b7af3cff4/nanomaterials-06-00090-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/70661b0a50f1/nanomaterials-06-00090-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/4bc61f6d34c8/nanomaterials-06-00090-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/f4d219f03e55/nanomaterials-06-00090-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/9e9b/5302499/5126f67e6f11/nanomaterials-06-00090-g008.jpg

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本文引用的文献

[1]
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Clay particles destabilize engineered nanoparticles in aqueous environments.

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Environ Sci Technol. 2012-6-14

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J Hazard Mater. 2012-4-6

[10]
Commercial titanium dioxide nanoparticles in both natural and synthetic water: comprehensive multidimensional testing and prediction of aggregation behavior.

Environ Sci Technol. 2011-10-31

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