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PE EIE[R-Rg RESEARCH ON - HJ Andrews Experimental Forest

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The net rate of primary production at any<br />

particular depth depends upon the temperature,<br />

light intensity, essential nutrient concentration,<br />

and zooplankton grazing pressure a t<br />

that depth. The vertical distribution an d<br />

abundance of phytoplankton is thus a functio n<br />

of varying net production, sinking rates of algae<br />

and mixing dynamics of the water column . Th e<br />

total production per unit area of lake surfac e<br />

may be obtained by integrating the concentration<br />

of phytoplankton from top to bottom .<br />

The next step is to incorporate the size selective<br />

feeding of zooplankton and determine it s<br />

effect upon production (since algal cells o f<br />

different sizes possess varying capacities t o<br />

absorb nutrients) .<br />

The effective grazing rate by zooplankto n<br />

is modeled as a function of the phytoplankton<br />

density (at high densities the zooplanktons<br />

feeding structures become saturated) .<br />

The efficiency of assimilation of phytoplankton<br />

by zooplankton is also allowed to depen d<br />

upon algae abundance (efficiency decrease s<br />

with increasing abundance) .<br />

The overall model relating the phytoplankton,<br />

zooplankton, and nutrients is a system o f<br />

partial differential equations (in time and<br />

depth) .<br />

The submodel describing the physical<br />

cycling of nutrients (developed in the botto m<br />

related processes group) is an integral part of<br />

the phytoplankton, zooplankton submodels .<br />

The number and kinds of heterotrophi c<br />

bacteria will be assessed to give some information<br />

on the constancy of community structure<br />

of the decomposers . The utilization an d<br />

ultimate destruction of fixed organic material<br />

for the entire system will be estimated by<br />

respiration studies and verified by substrat e<br />

disappearance . The respiration an d<br />

heterotroph abundance values will also be correlated<br />

with the regeneration of nutrients .<br />

The nutrient budget and effective concentrations<br />

will be assessed . All of the above studie s<br />

will be carried out in units of biomass or wil l<br />

be convertible to biomass and units of carbo n<br />

by calculation of size distribution. Determinations<br />

of the magnitude of nitrogen transformation<br />

within each of the above compartments,<br />

as well as the search for evidence nitrogen<br />

fixation and its opposite process, denitri -<br />

fication, will be made .<br />

The detailed carbon cycle through th e<br />

phytoplankton, zooplankton, bacteria and<br />

pools of dissolved inorganic carbon, dissolved<br />

organic carbon, and detritus are bein g<br />

modeled initially with a varying rate compartment<br />

system. The rates of flow between th e<br />

compartments are to be functions of light ,<br />

temperature, and P0 4 and NO 3 concentrations.<br />

Later the rates will also be modeled a s<br />

functions of 0 2 and Si concentration. Thi s<br />

model will allow an analysis of what paths o f<br />

the cycling process limit the rate of<br />

production .<br />

Bottom Related Process Studie s<br />

The compartments are shown in figure 9 .<br />

The necessary chemical analyses to assess thi s<br />

aspect of the nutrient budget will also be<br />

done. Inputs of detrital materials to the sediments<br />

and their potential incorporation int o<br />

higher food chains via bottom invertebrates t o<br />

the fish will be assessed . The oxidation of<br />

organic material will be assessed by respiration<br />

rates of the sediments. The disappearanc e<br />

of substrates such as cellulose and chitin an d<br />

information on the bacteria associated wit h<br />

Figure 9 . Categories and relationships of sub-syste m<br />

(C)b ; bottom related processes.<br />

30

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