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Soil Chemistry

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Soil Chemistry Chapter 5 5.1 Introduction basic chemical composition of a soil is less useful than a knowledge of its component minerals and organic materials. – PowerPoint PPT presentation

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Title: Soil Chemistry


1
Soil Chemistry
  • Chapter 5

2
5.1 Introduction
  • basic chemical composition of a soil is less
    useful than a knowledge of its component minerals
    and organic materials.
  • these dictate
  • reactions that occur in the soil
  • availability of nutrients

3
Exercise 5.1
  • Decrease
  • uptake by plants
  • leaching
  • conversion into insoluble forms
  • Increase
  • addition of fertiliser
  • decomposition of plants
  • animal poo
  • dissolving of rock

4
5.2 Clay Minerals
  • naturally occurring inorganic compounds
  • form initially in the crystallisation of molten
    rock material
  • known as primary minerals
  • eg olivine, quartz, feldspar and hornblende
  • not stable when exposed to water, wind and
    extremes of temperature
  • break down physically and chemically
  • reform and crystallise in a different structure

5
Clay minerals
  • called secondary minerals
  • eg vermiculite, montmorillonite and kaolinite
  • tend to be much smaller in particle size than
    primary minerals
  • most commonly found in the clay fraction of soils
  • only the youngest and unweathered of soils will
    not contain mainly secondary minerals

6
The Earths crust
7
  • oxygen is negatively charged
  • the other major elements are positively charged
  • oxygen bonds with one or more of the cations,
    producing a chemistry of oxides
  • silicon oxides (silicates)
  • aluminium oxides (aluminates)
  • generally in combination as aluminosilicates
  • these dominate the minerals
  • low levels of other elements account for the
    differences in minerals

8
  • Si binds to four oxygens in a tetrahedron
  • Al has six oxygens (often as OH) in an octahedron
  • not a matter of individual SiO4 or Al(OH)6 units
  • some Os are shared between the silicate or
    aluminate units
  • most common structure in clay minerals is the
    formation of sheets
  • flat layers of silicate tetrahedra or aluminate
    octahedra
  • these sheets stack on top of each other
  • held together by hydrogen bonding or
    electrostatic attraction

9
Common sheet arrangement in clay minerals
(tetrahedrons in grey)
10
  • real clay crystals are not pure silicates or
    aluminates
  • some Si or Al atoms are substituted during the
    crystallisation process
  • creates spare charges which give the overall
    crystal a charge
  • balanced by loose cations or anions

11
  • these cations generally are held on the surface
    of the clay
  • are not strongly held
  • can be exchanged for other cations in an
    equilibrium process
  • measured as the cation exchange capacity (CEC)
  • soil pH has no effect on the exchange capacity
    from the clay minerals

12
  • as minerals weather, they lose silicon
  • this leads to increasing proportions of aluminate
    in weathered clays
  • Al-OH species are amphiprotic
  • soils dominated by oxides of aluminium (and other
    metals) can have positive sites in acidic soils
  • this allows anion exchange
  • Al-OH H ltgt Al-OH2 X-

13
5.3 Ion exchange in soils
  • when the loosely held cations or anions on the
    mineral surfaces are replaced by ions of the same
    charge (sign and magnitude) in solution
  • cation exchange is by far the most common
  • necessary for soil fertility
  • as soils weather, they lose cation exchange
    capacity and lose fertility

14
Cation Exchange
  • clay minerals have negative charge due to
    substitution of aluminium or silicon in the
    crystal lattice
  • humus also contributes negative charge, due to
    the presence of dissociated organic acids
  • humus-COOH ? humus-COO- H
  • Exercise 5.2
  • What effect would soil pH have on the amount of
    cation sites from humus?
  • low pH, less dissociated acid, less sites

15
  • a cation in solution replaces an adsorbed cation
    on the soil particle
  • eg soil-Na K (aq) ? soil-K Na (aq)
  • charges that are balanced, not number of charged
    species.
  • Class Exercise 5.3
  • Write an equation for the exchange of adsorbed
    sodium with solution calcium.
  • soil-Na soil-Na Ca2 (aq) ? soilCa
    2Na (aq)

16
  • exchange is equilibrium
  • reversible and dependent on the levels of each of
    the species, particularly the solution species
  • eg if a soil solution becomes depleted in
    calcium, then some calcium will desorb from an
    exchange site into solution
  • known as buffering
  • in all but the most leached and infertile of
    soils, there will be a balance between adsorbed
    and dissolved ions

17
Exercise 5.4
  • What do you think would happen to a soil which is
    treated with lime (calcium hydroxide), in
    addition to a pH change?
  • high concentration of Ca in solution
  • this would be partly reduced by exchange with the
    soil cations

18
Cation exchange capacity (CEC)
  • the moles of exchangeable positive charge per
    unit mass 100 g of dry soil
  • usually mmole/100g or cmole/kg (the same value)
  • Ca Mg contribute twice as much to the CEC as an
    equivalent number of sodium and potassium ions
    because of their 2 charges

19
  • Class Exercise 5.5
  • Comment on the trend in CEC in Table 5.1.
  • CEC increases with higher clay levels

20
Significance of CEC
  • uptake of nutrient ions from plant roots occurs
    from solution only
  • as cations are absorbed into the roots, they are
    replaced in the soil solution by H ions
  • when the exchange equilibrium is disturbed, some
    of that ion will desorb from the soil particles
  • replaced by another ion
  • if the nutrient is a weakly adsorbed one, such as
    K, there may not be enough adsorbed to replenish
    the soil, presenting a fertility problem
  • K is the most likely cation to be in short supply

21
Anion exchange
  • the important soil anions, nitrate and phosphate,
    behave very different at exchange sites
  • nitrate and chloride are only weakly held at
    positive sites
  • more likely to be found in soil solution
  • phosphate and sulfate are very strongly bound to
    the exchange sites
  • phosphate can become covalently and irreversibly
    bound

22
Soil pH
  • one of its most important properties
  • it affects so many other soil properties, (eg ion
    exchange and nutrient availability)
  • soil pH comes about from a balance between acidic
    and alkaline species
  • reflects mainly the levels of dissolved H and
    OH-, but also the adsorbed H on cation exchange
    sites
  • normally ranges from 4-9

23
Sources of soil acidity
  • rain - polluted or fresh will be slightly acidic
    due to dissolved gases
  • microbial and root respiration this produces
    CO2, which is slightly acidic in solution
  • oxidation of organic matter this produces
    organic acids known as humic acids, together with
    nitric and sulfuric acids

24
Sources of soil alkalinity
  • carbonate minerals calcium and magnesium
    carbonate are common materials in minerals
  • they are slightly soluble in water, and produce
    OH- as they dissolve
  • these cations and Na K are known as bases
    because of their association with alkaline soils
  • mineral weathering many primary minerals as
    they weather release hydroxide salts of the basic
    cations

25
Trends in soil pH
  • as soils age by weathering and leaching, they
    tend to become more acidic
  • primary minerals that release alkaline materials
    are replaced by neutral or slightly acidic
    secondary minerals
  • leaching removes the carbonate minerals
  • weathering occurs from the surface downwards so
    that the A and B horizons will tend to be more
    acidic than the C horizon

26
Significance of soil pH
  • nutrient availability the ability of plants to
    take up nutrients is very much dependent on the
    soil pH

27
Significance of soil pH
  • effect on soil organisms soil organisms prefer
    different pH levels
  • acid-sulfate soils - soils that are rich in
    inorganic sulfide minerals, such as pyrites,
  • can lead to the formation of excessive levels of
    sulfuric acid through oxidation
  • soil pH dives to very low levels
  • causes solubilisation of toxic levels of
    aluminium, manganese and iron from soil minerals
  • plant preferences most alkaline soils a few
    which need acidic soils

28
Soil pH management
  • soils tend towards lower pH values as they age
  • the main need for pH management is to making the
    soil more alkaline
  • most common method by liming
  • agricultural lime is a mixture dominated by
    CaCO3, but also containing MgCO3 and Ca(OH)2
  • comes from ground limestone,
  • add the nutrients calcium and magnesium to the
    soil
  • dolomite lime has a higher proportion of
    magnesium carbonate
  • to reduce pH , add Fe, S or peat

29
Exercise 5.9
  • What factors will affect the amount of liming
    required?
  • buffering capacity
  • pH

30
Redox potential (Eh)
  • a measure of its ability to produce oxidation or
    reduction of chemical species in it
  • the most important soil property indicated by the
    soil Eh is whether it is aerobic or anaerobic
  • aerobic soils give a positive value
  • the lower the value the more anaerobic the
    conditions
  • a value that is affected by soil pH
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