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1000 Conspicuous Defo i at ion 100 .__. _; Si t e-A _.i Hakkohda t0 _ .... ,, _ i 0.1 o.o_i 100 , i i : , Site-C 10 _ _" Appi i ''_ " i....* >" i...*"! i ,J o3 0.1 o.ol,iii i i ', i I00 i 0.1 Site-B Hachimantai O.Ol i i o.ool ,,.... i ..... i i _ i 198586 87 88 89 90 91 92 93 Year Figure 2._Annual changes in last instar larval densities of Q. punctatella in the three study plots (mean + 90% confidence intervals). Site A (Hakkohda) is where conspicuous defoliation occurred during our study, Site B (Hachimantai) is where conspicuous defoliation had been recorded but did not occur during our study, and Site C (Appi) is where no conspicuous defoliation of this species has been recorded. 71
400 -0 " 350 r'''" = 300 .¢Z: ,_ 250 "='200 E Femal e • : • '. , • "- 150 o 100 ,5 z 50 _.--_ 1600 1400 % 1200 < 1000 _._ % 800 Male ! ! _..===J ." "_ '-,--o600 _" "", , _; 400 -/ z 200 ' I _I I II il ! _I 1985 1986 1987 1988 1989 1990 1991 1992 1993 Year Figure 3.--Number of Q. punctatella adults caught in two light traps in Site B (Hachimantai) 1985-1993. The number of adults of each sex in each trap is shown. Nitrogen content of foliage was measured by a CHNS/O Analyzer (Perkin-Ehner PE2400 Series II) to the nearest 0.01%. Body size of moths gradually increased with larval density, but decreased suddenly in 1991 in Site A where severe defoliation had occurred the previous year (Fig. 4). A quantitative food shortage in 1990 was probably the main factor causing this size reduction. Body size increased a bit but was still small in 1992 and 1993, but larval density decreased and no food shortage occurred after 1991. Thus, factors other than a shortage of food were involved in the size decrease. Because size was ahnost the same in the two sites before the outbreak, the great difference between the two after the outbreak was not genetically determined. 72
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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
Page 32 and 33: STAND AND LANDSCAPE DIVERSITY AS A
Page 34 and 35: not related to resistance to the se
Page 36 and 37: In contrast to the situation in eas
Page 38 and 39: ROOT, R.B. 1973. Organization of a
Page 40 and 41: We tlhus neglect two potential sour
Page 42 and 43: c__ c__ 1T1 Ill a) a) 0 0 0 e 1 o e
Page 44 and 45: c_ >l.s S S S m N < DN DN < D c DN
Page 46 and 47: :hen k > 0 suggest that the cue or
Page 48 and 49: oth as protective weapons and as po
Page 50 and 51: DEFENSE THEORIES AND BIRCH RESISTAN
Page 52 and 53: P 45 A L 40 A T 35 A B 30 I L 25 I
Page 54 and 55: However, hares showed strong prefer
Page 56 and 57: DUGLE, J.A. 1966. A taxonomic study
Page 58 and 59: accommodate findings related to mic
Page 60 and 61: 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 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 112 and 113: Table 3..--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
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Table 2.--Percent nutrient content
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Some tree responses to fertilizatio
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PHYTOCHEMICAL PROTECTION AND NATURA
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Indirect effects of abiotic factors
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HUNTER, M.D. and PRICE, P.W. 1992.
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A° ADDITIVE C. HYBRID SUSCEPTIBILI
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Galls, leaf miners, or leaf folds w
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Table 2.--Summary of the hypotheses
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the inheritance patterns of seconda
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FLOATE, K.D. and WHITHAM, T.G. 1993
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Elements of the Suitability/Defense
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Table l.--Comparing the mean number
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ACKNOWLEDGEMENTS The authors sincer
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SINGH, D.R 1986_ Breeding for resis
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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
Page 242 and 243:
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
Page 270 and 271:
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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