Page 110 - Soil and water contamination, 2nd edition
P. 110

Major dissolved phase constituents                                     97

                      In contrast to the K-containing minerals, potassium  salts are readily soluble in water, so
                   are not subject to precipitation–dissolution  reactions, except when water evaporates under
                   semi-arid and arid conditions and salts are left behind. The major mechanisms that control K
                   concentrations in soil and water are sorption  to clay minerals  and plant uptake . Adsorption
                   of K to organic matter  plays only a minor role in K retention . Due to its strong affinity with
                   illitic clay minerals, K is partly irreversibly retained in sediments (K fixation ). In general,
                   there is equilibrium  between the following pools of K:

                   Dissolved  K  +   Exchangabl e  K +  Fixed  K                        (5.2)

                   The equilibrium  between dissolved and exchangeable (adsorbed) K is reached relatively fast,
                   whereas the equilibrium between K adsorbed to the clay mineral surfaces and the K fixed
                   between the clay lattices is reached much more slowly. The exchangeable K content in soil
                   generally increases with increasing clay content . In acid, sandy soils the exchangeable K
                   content only amounts to a few mg K per 100 g soil; in basic, clayey soils it is up to about
                   100 mg K per 100 g soil (= 0.1 percent). Because of the fixation of K in clay minerals , K
                   seldom occurs in very large concentrations in natural waters and its concentration is usually
                   much lower than the concentration of Na. Because of the relatively strong K sorption  in soil,
                   K generally moves slowly through the soil.
                      The second important factor (after sorption  and fixation of K to clay minerals ) that
                   controls the availability of K for solution in subsurface water is the biological cycling of
                   K. The potassium  taken up by plants comes from the exchangeable and dissolved K pools.
                   The fixed K pools are generally not available for uptake by plants. When exchangeable and
                   dissolved K are available in sufficiently large amounts, luxury consumption by plants may
                   occur, which means that plants take up K in excess amounts. The average K content of
                   living plant material is about 0.3 percent, but concentrations in dry plant material and ash
                   are considerably greater (1.5–4 percent). Potassium assimilated by plants becomes available
                   immediately after the plants die or when leaves and other parts are shed at the end of the
                   growing season. The K present in the litter or detritus  is readily released in dissolved form
                   during the dormant season. The released K leaches into the soil where it is adsorbed to cation
                   exchange sites of clay minerals and recycled during the subsequent growing season. A small
                   part of the K may be lost from the soil due to leaching  to groundwater or runoff to surface
                   water. In agricultural  soils, part of the K is exported by crop harvesting and removal of crop
                   residues.


                   5.4  CALCIUM

                   Calcium (Ca) is the most abundant of the alkaline-earth  metals ; under natural conditions
                   it occurs only in the 2+ oxidation state . Calcium is an essential element for plant and
                   animal life forms: it is needed for the physical integrity and normal functioning of cell
                   membranes and it plays a vital role in cells that are dividing. In animals and humans, Ca is
                   also used to build bones and teeth and to control muscle activity and transmission of nerve
                   signals. In addition, it plays a role in the coagulation  of the blood and the regulation heart
                   activity. Calcium is non-toxic, but large concentrations in drinking water are considered as
                   undesirable, because it causes the formation of boiler scale  (i.e. calcareous deposits) in much
                   household equipment such as boilers, washing machines, and kettles. The sum of the ions
                   which can precipitate as ‘hard particles’ from water is called the hardness . The hardness is
                   usually reported as mg CaCO  per litre or meq/l or in hardness degrees. One German degree
                                          3
                   corresponds to 17.8 mg CaCO /l and 1 French degree corresponds to 10 mg CaCO /l. The
                                            3                                        3
                                                                                    -
                                                2+
                                                        2+
                   temporary hardness is the part of Ca  and Mg  ions which are balanced by HCO  and can
                                                                                    3




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