Abstract:
This cha pter presents an overview and some specilic concepts and examples
concerning the diverse roles of insects in regulating or inl1uencing platH
populations. Also considered are some conseque nces of these populationcelllered
roles and of o the r, broader roles of inseCls that affect plant community
composition, functioning, and maintenance. These roles are seen
as e ffects on density, age and quality, pauernsof seasonal express ion, spatial
distribution, and stability of specific populations and, to an extent, the ...
communities of which they are a pari (cL Chapters 2, 12). Both short-term
functioning and more distan t evolutio nary processes are considered. T he
spcctrum of these influences embrace ( I) local movemelll, d yna mics, and
natural control and (2) larger-sca le move ment , d ynamics, and evolutionary
change, all commonly affected by various physical and biotic inll uences,
including their heteroge neity in time and space (cl". Cha pters 6-18, 23).
Insects can se rve such roles as exploiters, allies, or competitors of other
species. T heir roles as pollinators are presellled in Chapter 20, and omilted
here. We here emphasize examples where insects are sig nificant in a regulatory
sense (C hapter 12). Some populations of plants (as of a nimals) may
be regulated thro ugh the reciprocal predator-prey interaction in volving
insects, and the structure, fu nctio nin g, and slability of some biotic COIll Illunities
may thus be strongly inl1uenced by insects.
Most terrestrial plants, and also animals and microorganisms, are in some
way closely associated with insects. Coevolution of insects and va riotls associated
organisms has produced some clearly mutual benelits; and for
others roles mainly as food , one for the o ther. For some, a stable predatorprey
(host- parasitoid) relationship at the population interaction level can
be seen, despite the violence of individual to individual interaction. Some
insects mediate interspeci fic competition between ot her o rga nisms, including
plants, affecting their dynamics, resource sharing, and succession
(Chapters 2, 15) . T hrough their exploitation of epidemic po pulatio ns and
mediating roles, some insects contribute to reestablishing a more natural
(primeval) community composition (e.g., through reducing the density of
o ne spl."C ies of plant where <In increased density has been ca used by human
or other distu rbance of balance, or in mediating the species richness of the «
biotic community). Over long periods of lime, it is presumed that individuals'
adaptations associated wilh such activities have undergone a fine tunin
g, cont ributing to ex ist ing community integrity and relative stability.
Epidemics of herbivores resulting from disturbance may cause destruction
of much of certain plant po pulations. Whether this occllrs in patches
or more generally wilt affect the rate of resto ration of the plant S(;l nd. Rate
of resto ration wi ll depend Llpon the type and age distribution of the stand
and the characteristics of the individual plant species. For smail patches of
destruction, compensations (e.g., growth of ncig hboring surviv ing plants
or branc hes) may achieve a rapid adjustment: fo r la rger patches, restoration
could only be achieved by establishment and maturing of recruit plants.
T his would be a 10llg lime for a redwood forest but much less for vegetation
of annllal plants.