Aggregation and deposition of engineered nanomaterials in aquatic environments: role of physicochemical interactions.

By A. R. Petosa, D. Jaisi, I. R. Quevedo, Menachem Elimelech, N. Tufenkji. Environmental Science and Technology, 2010

1,129 citations recorded by the source corpus.

Subfields: Biomedical Engineering, Materials Chemistry, Water Science and Technology

View Paper: https://www.semanticscholar.org/paper/a0e1586d6c67aa640c0888814cb8163f8366d082

How researchers see this paper

The researchers whose trusted networks rank it highest, strongest advocate first. Every researcher gets a different order.

In Biomedical Engineering

1. S. Tang
2. I. Lo
3. Teresa A. P. Rocha-Santos

In Materials Chemistry

1. S. Tang
2. G. Metreveli
3. K. Hund-Rinke
4. I. Lo
5. Stephan Wagner
6. Moira S. McKee
7. Ralf Schulz
8. M. Bundschuh

In Water Science and Technology

1. S. Tang
2. I. Lo
3. T. Kuhlbusch

Citations in the corpus

• Nanoparticles in the environment: where do we come from, where do we go to? (2018, background): “The IEP varies substantially among commercially available NP [101, 102], suggesting that even at the same pH the fate and thus the interaction of NP with organisms might vary substantially [103].”
• Adsorption of graphene for the removal of inorganic pollutants in water purification: a review (2014, neutral): “…Y. Cao (&) X. Li Institute of Environment and Municipal Engineering, North China University of Water Resources and Electric Power, Zhengzhou 450045, People’s Republic of China e-mail: caoyangel@126.com and Elimelech 2008; Petosa et al. 2010; Tawabini et al. 2010; Pyrzynska and Bystrzejewski 2010).”
• Magnetic nanoparticles: essential factors for sustainable environmental applications. (2013, methodology): “In aquatic environments, aggregation of nanoparticles, controlled by particleeparticle interactions, has been conventionally described by DerjaguineLandaueVerweyeOverbeek (DLVO) theory (Baalousha, 2009; Petosa et al., 2010; Phenrat et al., 2009a; Saleh et al., 2008).”
• Fate and Bioavailability of Engineered Nanoparticles in Soils: A Review (2014, background): “…ec re as ed w ith d is so lv ed p h o sp h at e co n ce n tr at io n (C o rn el is et al ., 20 11 ) 2730 Engineered Nanoparticles in Soils 2731 sites, whereas larger, negatively charged natural colloids only encounter the average surface charge, most often negative in soils (Petosa et al., 2010).”