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June 1 - 3 , 1978 - University of Hawaii at Manoa

June 1 - 3 , 1978 - University of Hawaii at Manoa

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We see from the two figures th<strong>at</strong> interactions between trees<br />

introduce an interesting kind <strong>of</strong> stability, with an associ<strong>at</strong>ed<br />

fragility, into the forest system. The stability comes from the<br />

tendency <strong>of</strong> the forest to maintain its st<strong>at</strong>e even for rel<strong>at</strong>ively<br />

small 9. However, once 9 becomes neg<strong>at</strong>ive, there is a tendency<br />

for the whole system to "collapse." Hence a fragility, when<br />

close to critical values <strong>of</strong> the growth factors and stand condi-<br />

tion parameter, is closely connected with the stability <strong>of</strong> the<br />

forest.<br />

DISCUSSION AND CONCLUSIONS<br />

The motiv<strong>at</strong>ion for this work has been to examine the plausi-<br />

bility <strong>of</strong> the hypothesis th<strong>at</strong> n<strong>at</strong>ural mechanisms within the<br />

'ohi'a forest ecosystem can produce an interdependent collapse <strong>of</strong><br />

a forest stand.<br />

As illustr<strong>at</strong>ed in the previous section, the simplified model<br />

discussed here does show such behavior. It has been noted th<strong>at</strong><br />

the modific<strong>at</strong>ions required to make the model realistic do not<br />

change the qualit<strong>at</strong>ive behavior <strong>of</strong> the collapse, which is the<br />

focus <strong>of</strong> our interest. We see th<strong>at</strong> collapse due to a n<strong>at</strong>ural<br />

mechanism is a possible outcome which is an altern<strong>at</strong>ive to random<br />

thinning, or, in a more extreme case, to introduced epidemic.<br />

The reason th<strong>at</strong> collapse occurs r<strong>at</strong>her than random thinning is<br />

rel<strong>at</strong>ed to the way in which 'ohi'a stands are established as<br />

pioneer, uniform-age stands on new lava flows with no regenera-<br />

tion in their own shade.<br />

The fact th<strong>at</strong> dieback in 'ohi'a forests seems to occur only<br />

in fairly m<strong>at</strong>ure forests, perhaps <strong>at</strong> intervals <strong>of</strong> several hundred<br />

years, suggests th<strong>at</strong> the magnitude <strong>of</strong> environmental stress (i-e.,<br />

the reduction in q) required to produce collapse is quite large<br />

and hence unusual. This fact also suggests th<strong>at</strong> the interaction<br />

parameter, which increases as the trees get larger and more able<br />

to affect one another, must be fairly large. In addition, S will<br />

be larger for m<strong>at</strong>ure trees than, for example, for seedlings: So<br />

the requirements for collapse (i.e., th<strong>at</strong> k be large and g go<br />

from a significant positive value to a significant negaeive<br />

value) are associ<strong>at</strong>ed with the long time scale <strong>of</strong> several hundred<br />

years from establishment <strong>of</strong> the stand to dieback. This long time<br />

scale has made the collapse more difficult to recognize as a n<strong>at</strong>ural<br />

phenomenon in the sense addressed here. Similar phenomena<br />

on a shorter time scale have been much easier to recognize.* For<br />

example, one could apply the same type <strong>of</strong> model to the yearly<br />

dieback <strong>of</strong> annual plants. Annual life-forms provide a mechanism<br />

to respond to environmental stress (sharp decrease in - G). This<br />

* The example given here was originally suggested to me by<br />

N. Balakrishnan.

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