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Environmental Predisposition to Subc<strong>or</strong>tical Insects and Fungi Associated with Declining Red Pine Stands<br />
Although the above description may partially describe within-stand dynamics, it cannot explain the onset of decline.<br />
To address <strong>this</strong> question, we have conducted a variety of experiments on the effects of environmental stress on host suitability<br />
to insects and pathogens associated with Red Pine Decline. The results suggest that a relatively broad range of biotic and<br />
abiotic fact<strong>or</strong>s can improve host suitability to these <strong>or</strong>ganisms (Table 3). F<strong>or</strong> example, defoliation decreases resin flow,<br />
reduces tree ability to confine O. ips, and increases feeding preference to H. pales (Krause and Raffa 1994). Likewise,<br />
nitrification increases feeding, development, and survival by H. pales (Hunt et al. 1993). Reduced light availability also<br />
decreases host ability to respond to L. terebrantis (Klepzig et al. 1994c). Both defoliation and reduced light availability<br />
reduce the overall pool of photosynthate f<strong>or</strong> carbon-based defenses such as terpenes and phenolics (Wright et al. 1979,<br />
Ericsson et al. 1985, L<strong>or</strong>io and Summers 1986, Miller and Berryman 1986, Peet and Christensen 1987, Waring 1987, Dunn et<br />
al. 1990, Reich et al. 1992, Krause et al. 1993, Krause and Raffa 1994). These stresses can themselves be initiated by biotic<br />
agents. F<strong>or</strong> example, outbreaks by insect (<strong>or</strong> microbial) defoliat<strong>or</strong>s are often followed by m<strong>or</strong>tality due to bark beetles<br />
(Wright et al. 1984, Paine and Baker 1993), densely crowded stands m<strong>or</strong>e commonly experience bark beetle outbreaks<br />
(Nebeker et al. 1993), and suppressed trees are less able to resist attack (Safranyik et al. 1975, Raffa and Berryman 1982b,<br />
Mitchell et al. 1983, Waring and Pitman 1985, Paine and Baker 1993, Preisler and Mitchell 1993).<br />
Our current understanding of the biotic and abiotic interactions contributing to Red Pine Decline is depicted in Figure<br />
4. Each of the maj<strong>or</strong> assumptions underlying <strong>this</strong> model has been supp<strong>or</strong>ted, although some of the mechanisms are only<br />
po<strong>or</strong>ly understood. In particular, our knowledge of the relative imp<strong>or</strong>tance, impact, and tolerance ranges of the various<br />
inciting fact<strong>or</strong>s lags behind our knowledge of within-stand spread. Our current understanding is now sufficient, however, to<br />
test putative natural and anthropogenic stress agents on specific tree physiological, insect behavi<strong>or</strong>al and developmental, and<br />
microbial developmental parameters, and to project these impacts to the stand level. This model can also serve as a framew<strong>or</strong>k<br />
f<strong>or</strong> expanding our basic understanding of interactions among feeding guilds, the interaction of constitutive and inducible<br />
allelochemicals in host plant resistance, and microbial mediation of plant-insect interactions.<br />
.,__,_._ _:_ • ..., _,_...,_...,, :- . :. ..<br />
..... g g g ..... ..... .<br />
Figure 4._Sequence of events in the infection, decline, and m<strong>or</strong>tality of plantation red pines.<br />
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