2022
DOI: 10.1016/j.cej.2021.131191
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Heteroaggregation of nanoplastics with oppositely charged minerals in aquatic environment: Experimental and theoretical calculation study

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Cited by 39 publications
(19 citation statements)
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“…This Feature Article will focus on heteroaggregation in a dispersion of oppositely charged binary colloids, which has been a subject of intense research lately. , The electrostatic attraction between oppositely charged particles, referred to as electrostatic heteroaggregation (EHA), is the fundamental driving mechanism for heteroaggregation in a dispersion of oppositely charged colloids. The kinetic stability of colloidal particles in a dispersion can be quantified by DLVO (Derjaguin–Landau–Verway–Overbeek) theory which states that the overall particle–particle interaction potential is given by the summation of attractive van der Waals (vdW) interactions and repulsive electrical double-layer (EDL) interactions.…”
Section: Electrostatic Heteroaggregation (Eha)mentioning
confidence: 99%
“…This Feature Article will focus on heteroaggregation in a dispersion of oppositely charged binary colloids, which has been a subject of intense research lately. , The electrostatic attraction between oppositely charged particles, referred to as electrostatic heteroaggregation (EHA), is the fundamental driving mechanism for heteroaggregation in a dispersion of oppositely charged colloids. The kinetic stability of colloidal particles in a dispersion can be quantified by DLVO (Derjaguin–Landau–Verway–Overbeek) theory which states that the overall particle–particle interaction potential is given by the summation of attractive van der Waals (vdW) interactions and repulsive electrical double-layer (EDL) interactions.…”
Section: Electrostatic Heteroaggregation (Eha)mentioning
confidence: 99%
“…This will identify interferences and potential false positive or false negative results Test the bioaccumulation of a contaminant in the absence of the NMP By comparing the bioaccumulation of a contaminant in the presence and absence of the NMP, it is possible to assess if there is a vector effect All co-contaminant bioaccumulation studies If biomarkers are also evaluated, it may be helpful to include a NMP only control; it may also be important to confirm uptake of the NMP Zero-hour control 64,92,93 Add the NMPs at a certain step of the assay and then immediately perform the remainder of the assay without modification; this differs from the typical approach in that there is no exposure period after the NMPs are added container, 44 flotation on the air−water interface, 45,46 and sedimentation of the particles out of the suspension after homo-or heteroagglomeration. 47,48 Sedimentation can potentially be accelerated in the presence of test organisms by agglomeration during passage through the organism or by attachment to suspended cells (e.g., algae, bacteria). 40,49,50 For other types of exposure systems, the size of the particles can impact function of the exposure test method.…”
Section: ■ Dosimetry Issues During Toxicity Testsmentioning
confidence: 99%
“…For exposure systems where exposure occurs to organisms with suspended particles in the test media (e.g., algae, fish), potential sources of bias include adsorption to sidewalls of the container, flotation on the air–water interface, , and sedimentation of the particles out of the suspension after homo- or heteroagglomeration. , Sedimentation can potentially be accelerated in the presence of test organisms by agglomeration during passage through the organism or by attachment to suspended cells (e.g., algae, bacteria). ,, For other types of exposure systems, the size of the particles can impact function of the exposure test method. For example, microplastic particles could potentially clog the channels in microphysiological devices, which often have cross-channels smaller than 1 mm, or flow-through systems with aerosolized particles .…”
Section: Dosimetry Issues During Toxicity Testsmentioning
confidence: 99%
“…The concentration of mono-and divalent ions reported for freshwater bodies rarely exceeds ~50 mM for Na + and ~2.5 mM for Ca 2+ . Therefore, it is likely that most NPL suspensions are stable in natural freshwater ecosystems since their CCC values are considerably higher [63] . However, freshwater may contain other substances than those reviewed here that could co-occur with NPLs and modify the stability of their suspensions.…”
Section: Physicochemical Behavior Of Npls In Freshwatermentioning
confidence: 99%