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

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contribute to detrital compartment as a resul t<br />

of their fecal deposits or their death and decomposition.<br />

Ultimately DOC and detrital<br />

carbon are decomposed by bacteria or zoo -<br />

plankton feeding on bacteria/detritus mixtures,<br />

to dissolved inorganic carbon as a result<br />

of respiratory oxidative decompositio n<br />

processes .<br />

In nature the standing stock in each compartment<br />

is the dynamic equilibrium level<br />

attained as a result of input/output rate s<br />

about the compartment . The quality of th e<br />

standing stock will also vary as the input /<br />

output mechanisms change .<br />

With the advent of the carbon-14 tracer<br />

techniques, the transports of carbon to and<br />

from each compartment in an aquatic ecosystem<br />

is possible . For example, Steemann-<br />

Nielsen (1952) initiated such studies with C' 4<br />

bicarbonate to estimate the rate of primar y<br />

production in the ocean . Goldman (1963 )<br />

outlined the use of this method in fres h<br />

water .<br />

Sorokin (1966), Shuskina and Monako v<br />

(1969), and Johannes and Satomi (1967) use d<br />

labeled phytoplankton to determine the rat e<br />

at which zooplankton feed and process thei r<br />

waste . The production of dissolved organic<br />

carbon (DOC) by phytoplankton (Fogg 1965,<br />

Saunders and Storch 1971) and uptake by<br />

zooplankton and bacteria have been success -<br />

fully measured using carbon-14 tracers.<br />

Hobbie and Wright (1965) and Wright an d<br />

Hobbie (1966) refined the enzyme saturatio n<br />

technique of Parson and Strickland (1962) a s<br />

measured by a carbon-14 tracer, to evaluat e<br />

the pool size and potential flux of dissolve d<br />

organics through the bacterial (heterotrophic )<br />

compartment in the aquatic web . With<br />

carbon-14 labeled detritus Sorokin (1966 )<br />

measured assimilation by zooplankton . H e<br />

prepared the detritus by homogenizing radio -<br />

actively labeled algal cultures . Others hav e<br />

used autoclaved, labeled natural and culture d<br />

algal populations 2 (Bell and Ward 1970) .<br />

Labeled detritus may also be prepared, b y<br />

foam separating C-14 labeled dissolve d<br />

organics from the liquid phase (Baylor an d<br />

Sutcliff 1963) . However, there is evidenc e<br />

2 G . W. Saunders, personal communication .<br />

that this method will work only in sea water .<br />

For the first time, Saunders 3 recently combined<br />

the aforementioned methods to measure<br />

simultaneously all of the previously liste d<br />

carbon fractions and their fluxes in a "Compartment<br />

Analysis" scheme (Patten 1968 ,<br />

Atkins 1969). He has made this type of<br />

analysis at one location and one instant in<br />

time at several lakes .<br />

Compartment Analysis, in essence, is performed<br />

by establishing a series of known fractions<br />

or compartments in an experimenta l<br />

confine (e .g., glass carboy or plastic bag) and<br />

following a tracer such as carbon-14 as a func -<br />

tion of time as it proceeds through each compartment<br />

in the confined system . Measurement<br />

of the radioactive carbon as it passe s<br />

through each compartment can be used t o<br />

evaluate the rate of incorporation of carbo n<br />

into each compartment in succession, and b y<br />

isotopic dilution or total carbon conten t<br />

analysis, the pool size estimated . These data<br />

may be used to describe mathematically th e<br />

carbon change in compartments as a functio n<br />

of time, e .g .,<br />

d( q 1) _ - k l q l and<br />

dt<br />

d( q 2 )<br />

dt =k l q 1 -k 2 q 2<br />

where (4 1 and q 2 are the specific activities o f<br />

the first and second compartments and k l<br />

and k2 are the rate constants into each compartment.<br />

The compartments could very wel l<br />

be phytoplankton and zooplankton or DOC ,<br />

bacteria and zooplankton, etc. The specifi c<br />

activities rather than tracer amounts will b e<br />

used in mathematical models .<br />

It must be emphasized that the confinement<br />

of an aliquot of the sampled water during<br />

the compartment analysis will yield value s<br />

prevailing for (1) standing stock at the time o f<br />

sample confinement, and (2) uptake value s<br />

for that particular sample during the incubation<br />

period . Thus, it is very important whe n<br />

and where test water samples are chosen . For<br />

example, if lake water were collected for a<br />

compartment analysis of the carbon fraction s<br />

during maximum expected respiratory and<br />

3 Unpublished data .<br />

291

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