Organic Matter Role in Illitic Soil Colloids Flocculation: II. Surface Charge

1993 ◽  
Vol 57 (5) ◽  
pp. 1246-1253 ◽  
Author(s):  
Dean Heil ◽  
Garrison Sposito
2019 ◽  
Vol 21 (10) ◽  
pp. 1729-1735 ◽  
Author(s):  
Gabriel Sigmund ◽  
Stephanie Castan ◽  
Christopher Wabnitz ◽  
Rani Bakkour ◽  
Thorsten Hüffer ◽  
...  

Transformation of soot with NO2 and interactions with NOM decreased the soot surface charge, size and sorption affinity for organic contaminants.


2002 ◽  
Vol 36 (17) ◽  
pp. 3864-3871 ◽  
Author(s):  
Yongki Shim ◽  
Hong-Joo Lee ◽  
Sangyoup Lee ◽  
Seung-Hyeon Moon ◽  
Jaeweon Cho

Author(s):  
Mircea MIHALACHE ◽  
Leonard ILIE

Samples from surface and subjacent horizons of main soil types from chernozem to podzol were selected. Both soil colloids and released cations may be retained or deplaced to the depth. The differences of the averages and medians and the histograms of the two horizon properties show the translocation of clay and free sesquioxides and the retention or migration of some nutrient cations. The deplacement to the depth were charactherized by migration level difference of concentration in the two horizons A2-A1, by the migration index namely the concentration ratio A2/A1 and by migration gradient, the angular coefficient m of linear relation between the content of the same component in the two horizons.


Author(s):  
Anthony S. R. Juo ◽  
Kathrin Franzluebbers

Soil chemistry deals with the chemical properties and reactions of soils. It is essentially the application of electrochemistry and colloid chemistry to soil systems. Major topics include surface charge properties of soil colloids, cation and anion sorption and exchange, soil acidity, soil alkalinity, soil salinity, and the effects of these chemical properties and processes on soil biological activity, plant growth, and environmental quality. The ability of the electrically charged surface of soil colloids to retain nutrient cations and anions is an important chemical property affecting the fertility status of the soil. There are two major sources of electrical charges on soil organic and inorganic colloids, namely, permanent or constant charges and variable or pH-dependent charges. Permanent or constant charges are the result of the charge imbalance brought about by isomorphous substitution in a mineral structure of one cation by another of similar size but differing valence (see also section 2.3.2). For example, the substitution of Mg2+ for Al3+ that occurs in Al-dominated octahedral sheets of 2:1 clay minerals results in a negative surface charge in smectite, vermiculite, and chlorite. The excess negative charges are then balanced by adsorbed cations to maintain electrical neutrality. Permanent negative charges of all 2:1 silicate minerals arise from isomorphous substitutions. The l:l-type clay mineral, kaolinite, has only a minor amount of permanent charge due to isomorphic substitution. The negative charges on kaolinite originate from surface hydroxyl groups on the edge of the mineral structure and are pH-dependent. Variable or pH-dependent charges occur on the surfaces of Fe and Al oxides, allophanes, and organic soil colloids. This type of surface charge originates from hydroxyl groups and other functional groups by releasing or accepting H+ ions, resulting in either negative or positive charges. Other functional groups are hydroxyl (OH) groups of Fe and/or Al oxides and allophanes and the COOH and OH groups of soil organic matter. Variable-charge soil colloids bear either a positive or a negative net surface charge depending on the pH of the soil. The magnitude of the charge varies with the electrolyte concentration of the soil solution.


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