HURRICANE DAMAGE INFLUENCES FOLIAR POLYPHENOLICS AND SUBSEQUENT HERBIVORY ON SURVIVING TREES

Hurricane damage results in tree mortality and variation in both light and nutrient availability for the individuals that remain. In turn, resource availability influences the interactions between plants and insect herbivores. We report effects of Hurricane Opal on the phenolic chemistry and levels of defoliation on surviving trees at the Coweeta Hydrologic Laboratory in North Carolina. We measured foliar astringency, hydrolysable tannins, and condensed tannins in the foliage of red maple and red oak saplings in hurricane- damaged and undamaged sites. We estimated inorganic nitrogen and phosphorus availability in the soil, and the accumulated leaf area removed by insect herbivores. The foliar astrin- gency of both red maple and red oak was higher in sites damaged by the hurricane. Later in the growing season, condensed tannin levels were significantly higher in the foliage of red oak in damaged sites. There were no consistent differences in ammonium, nitrate, or phosphate availability between damaged and undamaged sites. Despite higher foliar as- tringency of trees in sites damaged by Hurricane Opal, levels of defoliation by insect herbivores were higher in damaged than in control sites on both tree species. Apparent increases in putative defensive compounds following hurricane damage did not protect trees from herbivory.

[1]  J. Henry,et al.  RECONSTRUCTING FOREST HISTORY FROM LIVE AND DEAD PLANT MATERIAL AN APPROACH TO THE STUDY OF FOREST SUCCESSION IN SOUTHWEST NEW HAMPSHIRE , 1974 .

[2]  Michael R. Willig,et al.  Introduction: Disturbance and Caribbean Ecosystems , 1996 .

[3]  R. Chazdon,et al.  Light Environments of Tropical Forests , 1984 .

[4]  J. Schultz,et al.  Relationships among defoliation, red oak phenolics, and gypsy moth growth and reproduction , 1988 .

[5]  D. Binkley Ion Exchange Resin Bags: Factors Affecting Estimates of Nitrogen Availability1 , 1984 .

[6]  D. J. Shure,et al.  The influence of light and nutrients on foliar phenolics and insect herbivory , 1994 .

[7]  John H. Loughrin,et al.  Response of Japanese Beetles (Coleoptera: Scarabaeidae) to Leaf Volatiles of Susceptible and Resistant Maple Species , 1997 .

[8]  F. Chapin Nutrient Allocation and Responses to Defoliation in Tundra Plants , 1980 .

[9]  I. Kögel‐Knabner,et al.  Comparison of humus horizons from two ecosystem phases on northern Vancouver Island using 13C CPMAS NMR spectroscopy and CuO oxidation , 1993 .

[10]  D. J. Lodge,et al.  Nitrogen immobilization by decomposing woody debris and the recovery of tropical wet forest from hurricane disturbance , 1995 .

[11]  S. Pickett,et al.  Microsite variation and soil dynamics within newly created treefall pits and mounds. , 1990 .

[12]  J. Schultz,et al.  SEASONAL AND INDIVIDUAL VARIATION IN LEAF QUALITY OF TWO NORTHERN HARDWOODS TREE SPECIES , 1982 .

[13]  J. Schultz,et al.  Fertilization Mitigates Chemical Induction and Herbivore Responses Within Damaged Oak Trees , 1995 .

[14]  D. J. Shure,et al.  PATCH-SIZE EFFECTS ON PLANT PHENOLICS IN SUCCESSIONAL OPENINGS OF THE SOUTHERN APPALACHIANS' , 1993 .

[15]  L. Walker,et al.  Tree damage and recovery from Hurricane Hugo in Luquillo Experimental Forest, Puerto Rico , 1991 .

[16]  Thomas P. Clausen,et al.  Effects of balsam poplar (Populus balsamifera) tannins and low molecular weight phenolics on microbial activity in taiga floodplain soil: implications for changes in N cycling during succession , 1996 .

[17]  M. Hunter Opposing effects of spring defoliation on late season oak caterpillars , 1987 .

[18]  Chadwick Dearing Oliver,et al.  Reconstruction of a Mixed‐Species Forest in Central New England , 1977 .

[19]  F. Stuart Chapin,et al.  Carbon/nutrient balance of boreal plants in relation to vertebrate herbivory , 1983 .

[20]  L. Donovan,et al.  Ecophysiological differences among growth stages of Quercus laevis in a sandhill oak community , 1998 .

[21]  E. C. Bate-smith Astringent tannins of Acer species , 1977 .

[22]  J. Schimel,et al.  Nitrogen turnover and availability during succession from alder to poplar in Alaskan taiga forests , 1995 .

[23]  Steward T. A. Pickett,et al.  The Ecology of Natural Disturbance and Patch Dynamics , 1985 .

[24]  Thomas P. Clausen,et al.  Effects of Mineral Nutrition on Delayed Inducible Resistance in Alaska Paper Birch , 1993 .

[25]  D. Phillips,et al.  Patch-size effects on early succession in southern Appalachian forests. , 1990 .

[26]  P. White,et al.  The Ecology of Natural Disturbance and Patch Dynamics , 1986 .

[27]  D. Binkley,et al.  Ion Exchange Resin Bag Method for Assessing Forest Soil Nitrogen Availability , 1983 .

[28]  J. Schultz,et al.  Oak Leaf Quality Declines in Response to Defoliation by Gypsy Moth Larvae , 1982, Science.

[29]  L. Butler,et al.  Chapter 10 – Tannins and Lignins , 1991 .

[30]  F. Stuart Chapin,et al.  Resource Availability and Plant Antiherbivore Defense , 1985, Science.

[31]  T. Schowalter Invertebrate community structure and herbivory in a tropical rain forest canopy in Puerto Rico following Hurricane Hugo. , 1994 .

[32]  S. Pickett,et al.  Microsite and elevational influences on early forest regeneration after catastrophic windthrow , 1990 .

[33]  R. Lindroth,et al.  EFFECTS OF CO2 AND NO3− AVAILABILITY ON DECIDUOUS TREES: PHYTOCHEMISTRY AND INSECT PERFORMANCE , 1997 .

[34]  S. W. Beatty Influence of Microtopography and Canopy Species on Spatial Patterns of Forest Understory Plants , 1984 .