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Enzymes in Tropical Soils   41


                           immobilization.    Huang  et  al.  (1995)  reported  that  a  complete  adsorption  of
                           enzymes led to the formation of clay-enzyme complexes, that had lower activities
                           than the free enzymes.  They stated that enzyme adsorption by clay was one of the
                           factors that can reduce the enzyme activity other than the amount of clay and the
                           increase in soil pH.  Boyd and Mortland (1985) found that the behavior of the free
                           and bound enzymes were similar with respect to kinetics parameters, optimum pH,
                           and substrate selectivity.    However, in general most researchers agree that the
                           major part of the active enzymes are those that are soluble in the soil water (Huang
                           et  al.,  1995).  The  enzymes  in  soils  can  be  extracted,  among  which  by  0.14  M
                           sodium pyrophosphate pH 7.1 that can extract phosphatase, urease, casein, and
                           proteases (Nannipieri et al., 1980).
                                The soluble forms of enzymes are in equilibrium with those adsorbed by soil
                           solids (Huang et al., 1995).  Therefore, the concentrations of soluble enzymes are
                           also determined by the concentrations of the adsorbed enzymes.  As the soluble
                           enzymes  decrease due to  some other mechanisms such  as leaching through soil
                           body or enzyme decays, the adsorbed enzymes may dissolve to compensate the
                           equilbrium  shifting.    Conversely,  the  concentration  of  the  adsorbed  enzymes
                           increases as the concentration of dissolved enzymes increases.  Dick and Tabatabai
                           (1987)  reported  that  a  part  of  adsorbed  phosphatase  also  participates  in  the
                           organic P transformation. However, part of soil researchers suggest that the biggest
                           part of active phosphatases is those dissolved in soil water (Huang et al., 1995).
                           The activities of enzymes in soil are probably determined by the soluble enzymes.
                           Changes in the soil environment properties, such as pH, soil water, and so on, may
                           probably directly affect this form of enzymes.
                                The soluble enzymes may easily move with water through water percolation
                           and/or  run-off  while  the  adsorbed  enzymes  may  move  only  with  soil  particles
                           through  soil  erosion  or  leaching  (Tabatabai  and  Fu,  1992).  Salam  et  al.    (1998)
                           suggests that some soil enzymes might have moved from topsoils (0 – 30 cm) to
                           subsoils  (30  –  60  cm).    Plant  roots  and  microorganisms  generally  concentrate  in
                           topsoils and, therefore, the soil enzymes must concentrate in topsoils.  However, it
                           was  reported  that  these  soil  enzymes  are  also  found  in  subsoils  at  lower
                           concentrations.  The enzymes in subsoils were probably originated from topsoils
                           and moved to subsoils by leaching.  Huysman et al. (1994) suggested that native
                           bacteria  can  also  migrate  downward  in  soil  body  for  a  considerable  distances  in
                           agricultural  soils.    This  suggestion  indicate  that  the  subsoils  enzymes  are  also
                           possibly produced by the migrated microorganims.




                                                                          Abdul Kadir Salam - 2014
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