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PHYTOCHEMICAL PROTECTION AND NATURAL ENEMIES IN THE<br />

REGULATION OF A ROOT AND STEM BORING INSECT<br />

A.V. WHIPPLE and D.R. STRONG<br />

Bodega Marine Lab<strong>or</strong>at<strong>or</strong>y, University of Calif<strong>or</strong>nia, Box 247, Bodega Bay, Calif<strong>or</strong>nia 94923, USA<br />

INTRODUCTION<br />

Much debate has centered on why herbiv<strong>or</strong>es in natural systems do not m<strong>or</strong>e often have a large negative effect on the<br />

plants on which they feed. Except f<strong>or</strong> some aquatic trophic cascades in which plants are algae, (Carpenter et aL 1987,<br />

Carpenter and Kitchell 1988) and a few large mammalian grazers (McNaughton et al. 1988), herbiv<strong>or</strong>es have rarely been<br />

shown to substantially depress plant populations. Two main ideas why <strong>this</strong> is are top-down suppression by predat<strong>or</strong>s and<br />

bottom-up plant protection (Hunter and Price 1992). The natural enemy hypothesis suggests that populations are generally .<br />

controlled by their predat<strong>or</strong>s and/<strong>or</strong> pathogens (Hairston et al. 1960, Oksanen et al. 1981, Hairston and Hairston 1993). Thus,<br />

the plant feeders are kept too sparse to substantially depress plant populations. The endogenous plant protection hypothesis<br />

proposes that, in terrestrial and some aquatic systems, plant biomass is protected by noxious secondary chemicals (Ehrlich<br />

and Raven 1964, Hawkins 1992, Hay and Steinberg 1992). An adjunct to <strong>this</strong> is that higher plant biomass is also largely<br />

unavailable to most herbiv<strong>or</strong>es (Strong 1992, White 1993). This is because most herbiv<strong>or</strong>es cannot digest cellulose <strong>or</strong> lignin<br />

without the aid of microbial symbionts (Martin 1991). Because cellulose and lignin make up a large p<strong>or</strong>tion of the plant,<br />

many essential nutrients f<strong>or</strong> herbiv<strong>or</strong>es are present only in low concentrations, which may limit the growth of herbiv<strong>or</strong>e<br />

populations so that they are not able to have substantial impact on plant populations.<br />

Of course, these hypotheses are not mutually exclusive, and in the system discussed here both plant defense and<br />

herbiv<strong>or</strong>e natural enemies may play a role in determining the level of herbiv<strong>or</strong>e effect on the plant population (Price 1992).<br />

The system of the bush lupine, Lupinus arb<strong>or</strong>eus, and its stem and root b<strong>or</strong>ing ghost moth <strong>or</strong> "swift," Hepialus caI(f<strong>or</strong>nicus,<br />

is ideal f<strong>or</strong> examining the roles of these different fact<strong>or</strong>s because the level of herbiv<strong>or</strong>e attack varies over space with some<br />

areas exhibiting extensive plant m<strong>or</strong>tality and others with little m<strong>or</strong>tality (Strong et al. in prep.).<br />

Directly <strong>or</strong> indirectly, abiotic fact<strong>or</strong>s are probably involved in the differences between the sites in level of attack. The<br />

effect of an abiotic fact<strong>or</strong> on the level of herbiv<strong>or</strong>y may act directly on the herbiv<strong>or</strong>e <strong>or</strong> be mediated through the herbiv<strong>or</strong>e's<br />

host plant, which would be bottom-up regulation, <strong>or</strong> through predat<strong>or</strong>s and pathogens, which would be top-down suppression.<br />

Herbiv<strong>or</strong>y<br />

and Resistance in the Bush Lupine<br />

The bush lupine is a dominant woody shrub of some coastal headland habitats in central Calif<strong>or</strong>nia. At Point Reyes<br />

and on Bodega Head in Marin and Sonoma Counties, a maj<strong>or</strong> source of m<strong>or</strong>tality to the bush lupine appears to be the swift,<br />

Hepialus calif<strong>or</strong>nicus (Opler 1968, Davidson and Barbour 1977, Wagner 1986). The mid to late instars of the swift caterpillar<br />

b<strong>or</strong>e in the roots and stem of the bush lupine. The early instars are thought to feed on litter and rootlets (Wagner 1986).<br />

The caterpillars reach 40-50 mm, and as many as 60 have been found in one bush. While those numbers are exceptional, it is :<br />

difficult to find a large bush with no evidence of swift caterpillar damage (pets. obs.).<br />

Lupines produce large quantities of quinolizidine alkaloids, which are thought to function in nutrient st<strong>or</strong>age and in<br />

defense against herbiv<strong>or</strong>es and pathogens (Wink 1992). As little as 0.11%fresh weight of these alkaloids can be toxic to<br />

insect herbiv<strong>or</strong>es (Wink 1992). Bush lupine leaves contain high levels of these quinolizidine alkaloids in their foliage _<br />

(Bentley and Johnson 1991). The bush lupine probably also has substantial levels of alkaloids in the stems and roots where<br />

the swift caterpillars feed (Wink and Witte 1984). The alkaloid is probably concentrated in the epidermis of the stem and root<br />

where exceptionally high levels of alkaloid have been found in other lupines (Wink 1992).<br />

Mattson, W.J., Niemel/i, R, and Rousi, M., eds. 1996. Dynamics of f<strong>or</strong>est herbiv<strong>or</strong>y: quest f<strong>or</strong> pattern and principle. <strong>USDA</strong><br />

F<strong>or</strong>. Serv. Gen. Tech. Rep. NC-183, N.C. F<strong>or</strong>. Exp. Sta., St. Paul, MN 55108.<br />

127<br />

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