Soils 205

Lecture 9 - Cation exchange

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13,14                                                    339-360

 

A. Source of charge on clays-  permanent or variable (pH dependent charge)

1. Permanent or constant charge

(a) isomorphous substitution

for example: Zn+2 for Al+3 in octahedral sheet

no substitution isomorphous substitution
= negative charge

(b) both octahedral and tetrahedral sheets

Mg+2, Zn+2, Cu+2, Fe+2 for Al+3

Al+3 for Si+4

(c) can form + charge

- Al+3 for Mg+2

- negative charge dominates

2. Variable or pH-dependent charge

(a) Dissociation of exposed OH groups

]-OH ¬¾¾® ]-O- + H+

uncharged negative
charge

<-----------(+ H+)---------

-------(- H+)--------->

(b) Occurs with humus, hydrous oxides,

and broken edges of silicate clays

(c) Increased pH values = more negative charge

acid = less negative charge

(d) Protonation of O and OH groups

]-O- + H+ ¬¾® ]-OH + H+ ¬¾® ]-OH2+

negative charge no charge positive charge
high pH intermediate pH low pH

(e) Depends on soil colloids present

Colloid

Negative
charge

Positive
charge

% constant

% variable

Humus

200

0

10

90

Vermiculite

120

0

95

5

Smectite

100

0

95

5

Illite

40

0

80

20

Kaolinite

12

4

5

95

Fe & Al Oxides

5

5

0

100

(f) Positive charge << negative charge in most temperate zone soils

acid tropical soils = net + charge

 

B. Cation Exchange

1. Process of cation replacement

 

 

Example:

Ca+2-colloid + 2 H+ ¬¾® 2 H+-colloid + Ca+2

= H+ replaces Ca+2 adsorbed to soil colloids

or

Ca-x + 2 H+ ¬¾® 2 H-x + Ca+2

x = the soil solid phase

or

Ca(ad) + 2 H+ ¬¾® 2 H(ad) + Ca+2

X(ad) = "adsorbed" cation X

2. Maintain electroneutrality

2 Na+ for 1 Ca+2

1 Mg+2 for 2 K+

3 H+ for 1 Al+3

 

 

C. Cation Exchange Capacity (CEC)

1. Total charge on soil

= sum of adsorbed cations (charge)

- (soil) = + (cations)

2. Determination

 

 

1.

 

 

 

 

 

 

2.

3.

Cation Exchange Capacity =

 

 

3. Units of charge per unit weight

(a) centimoles of charge per kilogram of soil

= cmolc/kg

= old units of milliequivalents per 100 grams of soil

(meq/100 g)

(b) all cations are equal on a charge basis

1 cmolc/kg Na+

= 1 cmolc/kg Ca+2

= 1 cmolc/kg Al+3

(c) conversion of charge to weight

5 cmolc/kg of Ca+2

= ? g Ca+2 (1)

= ? g CaCl2 (2)

= ? lbs/A-ft (3)

molecular weights: Ca+2 = 40 g/mol

Cl- = 35.5 g/mol

(from periodic table)

(1) (5 cmolc/kg soil)(molc/100 cmolc)(mol Ca+2/2 molc)(40 g Ca+2/mol Ca+2)

= 1 g Ca+2/kg soil

(2) (5 cmolc/kg soil)(molc/100 cmolc)(mol CaCl2/2 molc)(111 g CaCl2/mol CaCl2)

= 2.775 g CaCl2/kg soil

(3) (2.775 g CaCl2/kg soil)(kg soil/1000 g soil)(454 g soil/lb soil)(lb CaCl2/454 g CaCl2)

(4 x 106 lb soil/A-ft) = 11,100 lb CaCl2/ A-ft

 

4. Cation exchange capacity of soils

(a) related to components

humus » 200 cmolc/kg
smectites » 100 cmolc/kg
illite » 25 cmolc/kg
kaolinite » 10 cmolc/kg
Fe and Al oxides » 4 cmolc/kg

(b) estimate soil cation exchange capacity from composition:

5 % O.M. & 20 % smectite clay

200 x 0.05 = 10

100 x 0.20 = 20

total = 30 cmolc/kg

vs

2 % O.M. & 30 % kaolinite clay

200 x 0.02 = 4

10 x 0.30 = 3

total = 7 cmolc/kg

5. Cation exchange capacity and pH

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