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Nutrients                                                             123

                   Table 6.2  Typical concentration ranges of phosphorus  species in soil, groundwater, and surface water.
                               Soil 1    Soil solution 2  Groundwater 3  Surface water 4  Wastewater 5
                               g P kg -1  mg P l -1   mg P l -1   mg P l -1    mg P l -1
                   Total P     0.01–5.6  -            -           -            -
                   TP (< 0.45)  -        0.02–7.8     0.005–6.6   0.01–2.1     3–8
                   RP (< 0.45)  -        0.004–7.8    trace–4.2   0.003–1.9    3–6
                   1  Source: Whitehead (2000); Willems et al. (2002)
                   2  Source: Whitehead (2000); Sims et al. (1998)
                   3  Source: Willems et al. (2002); Kedziora et al. (1995)
                   4  Source: EEA (2006a)
                   5  Source: Van der Perk (1996); Corbett et al. (2002)

                    ( Al,  Fe)  OH  +  +  H  PO   ( Al,  Fe)  O  PO( OH)  +  H  O       (6.4)
                               2        2  4                          2       2
                        ( Al,  Fe)  OH                   ( Al,  Fe)  O    O
                                                                                        (6.5)
                    O                +  H 2 PO 4     O                P
                        ( Al,  Fe)  OH                   ( Al,  Fe)  O    OH

                                                       +  OH    +  H  O
                                                                     2
                   In reaction (6.5), a ring structure with two O-bridges is formed, in which the phosphate  is

                   strongly bonded. These type of specific adsorption  can also occur at a pH above the point
                   of zero charge , and so in a wide pH range. As a consequence, phosphate ions are bonded
                   strongly in soils containing sesquioxides . Under reducing conditions, ferric  iron is reduced
                   to ferrous iron , which is much more soluble (see Section 5.6). This reductive dissolution
                   of ferric hydroxides causes phosphate adsorbed to the ferric hydroxides to be released into
                   solution too. Under these conditions, the phosphate concentration is controlled by the
                   solubility of ferrous iron phosphate (vivianite ; Fe (PO ) ⋅8H O). Since the solubility product
                                                         3   4 2  2
                   of vivianite is much higher than that of ferric iron  phosphates, phosphate is much more
                   soluble and is therefore mobile in acid to neutral anaerobic  environments.
                      In the higher pH  range (pH > 7), phosphates also precipitate as calcium  phosphates,
                   mainly in the form of hydroxyapatite  (Ca OH(PO ) ) and fluor apatite (Ca F(PO ) ). The
                                                    5       4 3                 5    4 3
                   interactions of phosphates with iron , aluminium , sesquioxides , and calcium are collectively
                   referred to as  phosphate  fixation . As a result of phosphate fixation, the concentration of
                   dissolved phosphates is often only one-twentieth or less than the concentration of nitrogen
                   or potassium . Table 6.2 shows some typical ranges of concentrations of phosphorus  species
                   in soil, groundwater, and surface water, including variations in space and time in unpolluted
                   and polluted situations.

                   6.3.2  Phosphorus cycle

                   The phosphorus  cycle is roughly similar to the cycle of nitrogen  through the food chain.
                   However, it is much less complex than the nitrogen cycle, because phosphorus occurs in
                   fewer forms and there are no volatile gaseous compounds.
                      Dissolved phosphate  is used by primary producers and some heterotrophic bacteria.
                   These organisms convert inorganic phosphate into organic phosphorus . Subsequently, part
                   of the organic phosphorus is transferred into the food chain and the remains are left behind
                   in detritus  (e.g. phosphorus in plant roots). Ultimately, all living organic materials die and
                   become detritus.  The microbial decomposition  of organic matter  mineralises organically










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