Abstract
The growing development of nanotechnology has promoted the wide application of engineered nanomaterials, raising immense concern over the toxicological impacts of nanoparticles on the ecological environment during their transport processes. Nanoparticles in aquatic systems may undergo deposition onto environmental surfaces, which affects the corresponding interactions of engineered nanoparticles (ENPs) with other contaminants and their environmental fate to a certain extent. In this review, the most common ENPs, i.e., carbonaceous, metallic, and nonmetallic nanoparticles, and their potential ecotoxicological impacts on the environment are summarized. Colloidal interactions, including Derjaguin-Landau-Verwey-Overbeek (DLVO) and non-DLVO forces, involved in governing the depositional behavior of these nanoparticles in aquatic systems are outlined in this work. Moreover, laboratory approaches for examining the deposition of ENPs on collector surfaces, such as the packed-bed column and quartz crystal microbalance (QCM) method, and the limitations of their applications are outlined. In addition, the deposition kinetics of nanoparticles on different types of surfaces are critically discussed as well, with emphasis on other influencing factors, including particle-specific properties, particle aggregation, ionic strength, pH, and natural organic matter. Finally, the future outlook and challenges of estimating the environmental transport of ENPs are presented. This review will be helpful for better understanding the effects and transport fate of ENPs in aquatic systems.
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Abbreviations
- ENPs :
-
engineered nanoparticles
- DLVO :
-
Derjaguin-Landau-Verwey-Overbeek
- NOM :
-
natural organic matter
- CNTs :
-
carbon nanotubes
- GOs :
-
graphene oxide
- CDs :
-
carbon dots
- ZVI :
-
zero-valent iron
- QDs :
-
quantum dots
- SWNTs :
-
single-walled carbon nanotubes
- MWNTs :
-
multiwalled carbon nanotubes
- OECD :
-
Organization for Economic Cooperation and Development
- ROS :
-
reactive oxygen species
- FSNP :
-
fluorescent core-shell silica nanoparticles
- vdW :
-
van der Waals
- EDL :
-
electrostatic double layer
- LSA :
-
linear superposition approximation
- QCM :
-
quartz crystal microbalance
- CFT :
-
colloid filtration theory
- ADE :
-
advection-dispersion equation
- CSP :
-
constant surface potential, IS ionic strength
- PLL :
-
poly-L-lysine
- QCM-D :
-
quartz crystal microbalance with monitoring
- IEP :
-
isoelectric point
- SAM :
-
self-assembled monolayer
- FeO-GB :
-
hematite-coated glass bead
- pzc :
-
point of zero charge
- PAA :
-
polyacrylic acid
- CCC :
-
critical coagulation concentration
- CDC :
-
critical deposition concentration
- HA :
-
humic acid
- BSA :
-
bovine serum albumin
- SRHA :
-
Suwannee River humic acid
- SRFA :
-
Suwannee River fulvic acid
- ICP-MS :
-
inductively coupled plasma mass spectrometry
- spICP-MS :
-
single-particle inductively coupled plasma mass spectrometry
- GLC-TEM :
-
transmission electron microscopy using graphene liquid cells
- FFF :
-
field-flow fractionation
- NTA :
-
nanoparticle tracking analysis
- PNC :
-
particle number concentration
- PSD :
-
particle size distribution
- A 123 :
-
Hamaker constant of nanoparticle-medium-substrate system
- U vdW :
-
Van der Waals interaction energy
- a p :
-
particle radius
- D :
-
particle to surface separation distance
- λ :
-
characteristic wavelength
- U EDL :
-
electrical double-layer interaction energy
- ε 0 :
-
dielectric permittivity in vacuum, 8.85 × 10−12 F/m
- ε r :
-
relative dielectric permittivity of solution
- k B :
-
Boltzmann constant, 1.3805 × 10-23 J/K
- T :
-
absolute temperature
- e :
-
electron charge, 1.602 × 10−19 C
- \( \mathcal{z} \) :
-
counterion valence
- Γi :
-
dimensionless surface potential for particle or collector, Γi=tanh [(\( \mathcal{z}e \)ψi)/(4kBT)]
- κ:
-
inverse Debye length
- U HD :
-
the hdration interaction energy
- c 0, c :
-
empirical constants
- F ST :
-
the steric force
- S :
-
distance between polymer chains on a surface
- l :
-
the film thickness
- U ST :
-
the steric interaction energy
- F B :
-
the bridging force
- U B :
-
the bridging interaction energy
- L C :
-
units segment length in polymer chain
- L ∗ :
-
critical hydrocarbon chain length
- C :
-
nanoparticle concentration in the liquid phase
- x :
-
the distance traveled in the porous media
- v :
-
the interstitial particle velocity
- k :
-
the particle deposition rate coefficient
- α :
-
the attachment efficiency
- η 0 :
-
single-collector contact efficiency
- d c :
-
the median diameter of the porous media
- ε:
-
the packed-bed porosity
- L :
-
the length of the packed bed
- C 0 :
-
the influent concentration
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Funding
The present work has been financially supported by the National Natural Science Foundation of China (51608067, 51878092); Graduate Research and Innovation Foundation of Chongqing, China (Grant CYS18029); the Scientific and Technological Innovation Special Program of Social Livelihood of Chongqing (cstc2015shmsztzx0053); the Chongqing Postdoctoral Science Foundation (Grant Xm2016059); and the Fundamental Research Funds for the Central Universities (Grant 0903005203276 and Grant 106112016CDJXY210010).
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A summary of research examining the depositional behavior of various nanomaterials on environmentally relevant surfaces.
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Ma, C., Huangfu, X., He, Q. et al. Deposition of engineered nanoparticles (ENPs) on surfaces in aquatic systems: a review of interaction forces, experimental approaches, and influencing factors. Environ Sci Pollut Res 25, 33056–33081 (2018). https://doi.org/10.1007/s11356-018-3225-2
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DOI: https://doi.org/10.1007/s11356-018-3225-2