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Table 3..--Mean spruce budworm performance (female equivalents) on white spruce in 1991 on early, middle, and late phenology trees and flowering and nonflowering trees. Means varying significantly (p < 0.05) due to main effects have different letters. Only mean weight and development time were affected by phenology. There were no flowering effects. Budworm performance Tree phenol0_y class Tree flowering, class variable Early Middle Late Yes No Cohort one Survival (larvae) 0.57 0.57 0.55 0.57 0.57 Weight dwt (rag) 28.61b 30.96a 32.48a 30.13 311.33 Dev. time (days) 41.11 40.93 40.85 40.96 40.95 Growth rate (mg/da) 0.70b 0.76a 0.80a 0.74 0.77 F x P had any significant (p < 0.05) effects on growth, development time, or growth rates. Although, there was a hint (p < 0.08) of a tendency for nonflowering trees to be superior for larval performance than flowering trees (Fig. 2). DISCUSSION and CONCLUSIONS Yearly Differences in Protocol and Weather Weaken the Tests The differences in the effects of flowering and phenology on spruce budworm performance between years is ahnost certainly due to the differences in host tree phenology when the studies were initiated. In 1989, we placed our first cohort of budworms on the trees at 133 degree days (dd), very close to the time native budworm populations would have been emerging (est. at 100 dd). The second cohort was placed out at 204 dd, 71 dd and 7 days later than the first. In 1991 the experiment was begun 10 calendar days earlier than in 1989 but at a phenologically later point, 210 dd, about the time of budbreak on the early flushing trees (Nienstaedt and King 1970). Hence, the first cohort in 1991 was more nearly equivalent to the second cohort in 1989. The second cohort on fir in 1991 was placed on the host plants at 262 dd thereby having no 1989 equivalents. Finally, the single cohort on spruce in 1991 was placed on the trees at 280 degree days, about the time of budbreak for the later flushing spruce trees (Nienstaedt and King 1970). In addition, in 1991, just after placing the first cohort of second instars on the trees, the weather turned cool and wet keeping the young insects in their overwintering hibernaculum until nearly 1 week later when the next cohort was being placed on the trees. Although this study attempted to examine the combined effects of staminate flowering by host phenology on the performance of spruce budworm, we were unable to execute the experiment in perfect phenological duplication that would have allowed the most powerful tests of the hypotheses. Flower by Phenology Effects , The data clearly suggest that the survival of budworms is dependent on the flowering x phenology interaction of its host plants. In the case of fir, abundant flowering probably enhances survival most significantly on the later flushing trees, i.e., late relative to budworm emergence (they inevitably emerge before their hosts break bud). This was apparent especially in 1989. In that year all flowering branches supported higher survival than nonflowering branches regardless of tree phenology class, and regardless of cohort timing. In 1991 there was no apparent flowering effect on survival except for the late flushing trees, especially in the case of the second cohort. Likewise, on spruce there was a strong tendency, though only nearly significant (p
There was practically no evidence to suggest that flowering enhances the growth and development rate of budworms, not on fir, nor on spruce. Likewise, there seems to be no strong evidence that there is any kind of F x P effect on growth processes. To the contrary, the data on spruce, though not quite statistically significant (p
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DYNAMICS OF FOREST HERBIVORY: QUEST
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TABLE OF CONTENTS Seeking The Rules
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32. Companion planting of the nitro
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GRIMALSKY, ¥.I., Research Institut
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POUTTU, ANTTI, Finnish Forest Resea
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persist in mature leaves and affect
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THE SINK-SOURCE HYPOTHESIS: TYPE AN
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late season defoliation decreases t
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BLANCHE, C.A., LORIO, EL., Jr., SOM
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NIEMELA, R, TUOMI, J,, and LOJANDER
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induced reactions have been studied
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summer, but the other sawfly specie
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LARSSON, S., BJ(_RKMAN, C., and GRE
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STAND AND LANDSCAPE DIVERSITY AS A
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not related to resistance to the se
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In contrast to the situation in eas
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ROOT, R.B. 1973. Organization of a
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We tlhus neglect two potential sour
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c__ c__ 1T1 Ill a) a) 0 0 0 e 1 o e
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c_ >l.s S S S m N < DN DN < D c DN
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:hen k > 0 suggest that the cue or
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oth as protective weapons and as po
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DEFENSE THEORIES AND BIRCH RESISTAN
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P 45 A L 40 A T 35 A B 30 I L 25 I
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However, hares showed strong prefer
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DUGLE, J.A. 1966. A taxonomic study
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accommodate findings related to mic
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Table l.--Mean ±S.E. area eaten by
Page 62 and 63: Sulfhydryl-Disulfide Mechanisms In
Page 64 and 65: Iraa prior experimental analysis of
Page 66 and 67: FRAZIER, J.L. and HEITZ, J.R. 1975.
Page 68 and 69: REICHARD, R 1993. From RNA to DNA,
Page 70 and 71: ; trees, and between and within ind
Page 72 and 73: Encapsulated objects are data struc
Page 74 and 75: _re3.--The Lignum model can be cont
Page 76 and 77: SEVERE DEFOLIATION Tree Fine Root +
Page 78 and 79: RUMBAUGH, J., BLAHA, M., PREMERLANI
Page 80 and 81: oo0 a b ol ¢' _achiman_i ()® 1,eA
Page 82 and 83: 1000 Conspicuous Defo i at ion 100
Page 84 and 85: 2.oo 2.oo o t 4 t ¢._ e'- 1.80 1.8
Page 86 and 87: Qualitative Changes in [,eaves and
Page 88 and 89: t00 2 Yr 1 Yr o_ 80 Treatment Treat
Page 90 and 91: Table 2.--Body size of Q. purzctate
Page 92 and 93: 06 b AddedBSA < 04 _ 2rag -'=' i:3
Page 94 and 95: Severe Defol iat ion Site-A 1993 _
Page 96 and 97: KAMATA, N. and IGARASHI, M. 1995b.
Page 98 and 99: enclosure %r 20 post-diapausing sec
Page 100 and 101: 2,500 F 000 F NF NF b _7 a _;_ a _7
Page 102 and 103: 8O D 09 i 4,'.) F AS4L a Z___7 2o !
Page 104 and 105: 2,500 _ st2-st4 El st5 0 st6 [_ pup
Page 106 and 107: 96 SLANSKY, E, Jr. 1990. Insect nut
Page 108 and 109: later, we selected one more floweri
Page 110 and 111: Table 2.---Mean spruce budworm perf
Page 114 and 115: FOLIVORE FEEDING ON MALE CONIFER FL
Page 116 and 117: Table 3.--Lymantria monacha prefere
Page 118 and 119: 500- 400- i 300 v ¢ m a 200- I00 L
Page 120 and 121: From the point of view of trees, th
Page 122 and 123: THE BLACKMARGINED APHID AS A KEYSTO
Page 124 and 125: Wood et al. (1987) report that M. c
Page 126 and 127: MIZELL, R.E 1991. Pesticides and be
Page 128 and 129: METHODS Study Site The study took p
Page 130 and 131: the samples. Fertilization had subs
Page 132 and 133: Table 2.--Percent nutrient content
Page 134 and 135: Some tree responses to fertilizatio
Page 136 and 137: PHYTOCHEMICAL PROTECTION AND NATURA
Page 138 and 139: Indirect effects of abiotic factors
Page 140 and 141: HUNTER, M.D. and PRICE, P.W. 1992.
Page 142 and 143: A° ADDITIVE C. HYBRID SUSCEPTIBILI
Page 144 and 145: Galls, leaf miners, or leaf folds w
Page 146 and 147: Table 2.--Summary of the hypotheses
Page 148 and 149: the inheritance patterns of seconda
Page 150 and 151: FLOATE, K.D. and WHITHAM, T.G. 1993
Page 152 and 153: Elements of the Suitability/Defense
Page 154 and 155: Table l.--Comparing the mean number
Page 156 and 157: ACKNOWLEDGEMENTS The authors sincer
Page 158 and 159: SINGH, D.R 1986_ Breeding for resis
Page 160 and 161: The objectives of this presentation
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Table 1.--Average weevil attack on
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1977, Kline and Mitchell 1979, Wood
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Further research is underway to cla
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A SUGI CLONE HIGHLY PALATABLE TO HA
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RESULTS Seasonal Stability of Palat
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-
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OGAWA, A., NAGATA, Y., and SUKENO,
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MATERIALS AND METHODS Field Work In
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Laboratory Procedures The week afte
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E 120 Nogent-sur-Vernisson Remnings
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Interdependence Between Reaction Zo
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alance hypothesis (Lorio 1986) cann
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SOLHEIM, H., LANGSTROM, B., and HEL
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In a second experiment, three 30-ye
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Considering biochemical pathways, i
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- = 120 N /'_" =40 1/ _ j Days 0 _
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BIGGS, A.R. 1985. Suberized boundar
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DIFFERENTIAL SUSCEPTIBILITY OF WHIT
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Table 2.--Mortality of white fir pr
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Results from the geographic range p
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esulting seedlings were then rooted
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-0.2 0 5 82. _j -0,4 e a a a D4 E I
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1960, Kalkstein 1976). Increased su
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RYAN, B.F., JOtNER, B.L., and RYAN,
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It is seldom feasible to control wa
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15 15 u. 10 |O O N tal 5 5 g ao o 4
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Only recently have we conducted stu
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esistance to beetle attack. Another
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LORIO, EL., Jr'. and HODGES, J.D. 1
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EFFECTS OF ROOT INHABITING INSECT-F
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OCCURRENCE OF ROOT AND STEM SUBCORT
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]Predisposition of Root-infected Tr
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chemistry associated with root colo
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Implications to Natural Resource Ma
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KLEPZIG, K.D., RAFFA, K.F., and SMA
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RAFFA, K.F., PHILLIPS, T., and SALO
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METHODS The study was installed in
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FURNISS, M.M., LIVINGSTON, R.L., an
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METHODS In the spring and summer of
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The importance of a compound as a r
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WERNER, R.A. 1995. Toxicity and rep
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41 40 42 \ 4t 42 41 42 ",,,\ 42 40
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Table 1.--Summary data for the 26 p
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One weakness of using data from gen
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Lower Peninsula (populations 14-26)
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AUCLAIR, A.ND., WORREST, R.C., LACH
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KELLOMAKI, S., HANNINEN, H., and KO
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WARGO, RM. and HAACK, R.A. 1991. Un
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investigation. Sampling was done on
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Figure 2.--Changes in protein preci
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q) J 400 T J ! i i i i o control tr
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attacked trees than in control tree
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ACIDIC DEPOSITION, DROUGHT, AND INS
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Table 1.--Impact of acidic fog upon
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MENGEL, K., BREININGER, T., and LUT
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THE RESISTANCE OF SCOTCH PINE TO DE
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EXPERIMENTAL METHODS Experiments we
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C w Q. 1,200 1,000 o 800 C_ --- 600
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0 .................................
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FONTAtNE, R.G. 1985. Forty years of
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Host Defenses An important componen
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Functional Heterogeneity of Forest
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The Connectivity Index (CI). The CI
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FUNCTIONAL HETEROGENEITYANALYSIS :
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The Modified Hazard Map. The next l
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systems facilitate mapping of fores
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KOLASA, J. and ROLLO, C.D. 1991. In
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) i,i_i)i_)i_i_ U.S. Departme_]t of
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