Page 106 - Enzymes in Tropical Soils
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94     Enzymes In Tropical Soils


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                           higher  than  30 C  may  be  degradative  and  may  lower  their  populations  and
                           activities in soils.  Curtin et al. (2012) noticed from their experiment in some New
                           Zealand  soils  that  the  microbial  biomass  carbon  was  particularly  sentitive  to
                                                                                           o
                           temperature; the post-incubation biomass C decreased 18-35% between 5 – 25  C.
                                As  the  soil  temperature  is  related  to  soil  cover,  the  forest  conversion  to
                           other land-uses may change the soil temperature (Dash et al., 1981; Moyo et al.,
                           1989;  Neal,  1990)  and  also  the  types  of  vegetation,  plant  roots,  and  soil
                           microorganisms (Duxbury and Tate III,1981; Frankenberger and Dick, 1983; Jha et
                           al., 1992).  For example, in the regions of Northeast India, it was found that the
                           activities of some soil enzymes such as dehydrogenase, urease, and phosphatase
                           were higher in the regions that had not been degraded than those in the degraded
                           regions.    This  phenomenon  was  related  to  the  lower  populations  of  fungi  and
                           bacteria in the degraded regions.



                           6.4  Soil Water and Temperature versus Soil Biochemical
                                Reactions

                                The  rates  of  soil  biochemical  reactions  increase  with  the  increase  in  soil
                           water content and soil temperature below their respective optimum values.  This
                           facts enable the use of these soil properties to manage the rates of organic matter
                           decomposition.  The rates of the soil biochemical reactions can be accelerated or
                           lowered by manipulating these soil properties.
                                As  mentioned  previously,  water  molecule  is  one  of  the  most  important
                           reactants  in  the  decomposition  of  organic  matters.    For  example,  the
                           decomposition of organic P (Eq. 4.1) and organic S (Eq. 4.5) in soils may not occur
                           in the absence of water.  Therefore, the decomposition of organic matters in dry
                           soils  does  not  occur.    The  decomposition  may  start  after  the  air-dry  soil  is
                           moistened and may increase significantly as water is added until an optimum value.
                           The general optimum water content for the biochemical reactions is the soil field
                           water capacity.  The  soil field  water capacity is the water hold by soils at water
                           potential of 10 – 35 kPa, which is different between soils (Singer and Munns, 1987).
                                The rate of a biochemical reaction is expressed by the activity of enzymes,
                           which indicates the amount of products of an enzymatic reaction per unit soil mass
                           per unit time.  For example, the activities of phosphatases are usually expressed in
                                                                             -1 -1
                           mg p-Nitrophenol per gram soil per hour (mg p-Nitrophenol g h ).  Related to the
                           role of water, Balligar et al. (1988) reported that the activities of phosphatases of

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