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assessment of changes in the phosphorus status of forest ...

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upon soil and plant processes and <strong>the</strong> amount <strong>of</strong> P <strong>in</strong>puts. Among <strong>the</strong> several factors<br />

<strong>in</strong>fluenc<strong>in</strong>g <strong>the</strong> <strong>phosphorus</strong> concentrations <strong>in</strong> soil solution, soil pH, organic matter<br />

content, clay content, oxides <strong>of</strong> Fe and Al, carbonate content, uptake patterns <strong>of</strong> roots<br />

and microbes, and organic matter m<strong>in</strong>eralisation are <strong>the</strong> most important ones. To<br />

describe <strong>changes</strong> <strong>in</strong> P concentration <strong>of</strong> <strong>the</strong> soil solution, sorption iso<strong>the</strong>rms are used,<br />

which account for both <strong>in</strong>tensity and capacity factors <strong>of</strong> P equilibrium <strong>in</strong> soils. These<br />

two factors and <strong>the</strong> k<strong>in</strong>etics <strong>of</strong> P release and uptake constitute important parameters<br />

for predict<strong>in</strong>g <strong>the</strong> P supply<strong>in</strong>g characteristics <strong>of</strong> soils for optimum plant growth. Any<br />

soil test that <strong>in</strong>volves sorption iso<strong>the</strong>rms is considered more accurate than<br />

conventional P analysis methods (Klages et al. 1988) as iso<strong>the</strong>rms may <strong>in</strong>clude<br />

several factors mentioned above which <strong>in</strong>fluence <strong>the</strong> <strong>phosphorus</strong> dynamics <strong>in</strong> soil<br />

(Monterroso et al. 1996). P sorption iso<strong>the</strong>rms describe <strong>the</strong> amount <strong>of</strong> P required to<br />

br<strong>in</strong>g <strong>the</strong> concentration <strong>of</strong> P <strong>in</strong> <strong>the</strong> soil solution to an optimum level required for<br />

maximum plant growth.<br />

Concentrations <strong>of</strong> elements <strong>in</strong> soil solution can be used to calculate <strong>the</strong> so called ‘ Ppotentials’<br />

or ‘Sch<strong>of</strong>ield’s potentials’. These P potentials are related to lime potentials<br />

or pH values <strong>in</strong> <strong>the</strong> soil solution to obta<strong>in</strong> solubility diagrams. Such diagrams provide<br />

<strong>in</strong>formation on <strong>the</strong> predom<strong>in</strong>ant form <strong>of</strong> solid P which may be determ<strong>in</strong><strong>in</strong>g P<br />

concentrations <strong>in</strong> <strong>the</strong> soil solutions (Sch<strong>of</strong>ield 1955). One such diagram is given <strong>in</strong><br />

Fig 12 which was taken from Ulrich and Khanna (1968). This figure is based on 230<br />

<strong>forest</strong> soil samples from northwest Germany. All <strong>the</strong> values presented <strong>in</strong> <strong>the</strong> figure<br />

(pH, Ca, Al, P) were obta<strong>in</strong>ed <strong>in</strong> soil solutions by prepar<strong>in</strong>g saturation extracts <strong>of</strong> field<br />

moist soils.<br />

The Fig. 12 shows a number <strong>of</strong> categories, where soils <strong>of</strong> dist<strong>in</strong>ct groups were<br />

comb<strong>in</strong>ed. The groups were based on <strong>the</strong>ir soil pH (lime potential), calcium carbonate<br />

content, organic matter content, and soil depth (water logged soils, and those<br />

receiv<strong>in</strong>g fertilization were excluded). In soils <strong>of</strong> pH >6.8 and calcium carbonate <strong>of</strong><br />

>2% <strong>of</strong> soil weight concentration <strong>of</strong> P <strong>in</strong> <strong>the</strong> soil solution was def<strong>in</strong>ed by Ca-P forms,<br />

which were more soluble than apatite but less than octacalcium phosphates. In<br />

contrast, <strong>in</strong> soils with

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