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Leaf Size and Biomass Allocation in Thelypteris dentata, Woodwardia virginica, and Osmunda regalis in Central Florida PDF

6 Pages·1997·3.2 MB·English
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Leaf and Biomass Size Allocation in Thelypteris Woodwardia Osmunda dentata, and virginica, regalis in Central Florida Bartsch Ingrid Environmental Science and Policy Program University of South Florida, Tampa, FL 33620 Lawrence John Department of Biology and length weight, the greatest specific leaf area (area:we mass and Thelypteris dentata exhibited charac leaflet:stalk. leaf tolerant strategy, whereas W. virginica and O. regalis exhibited a commonly associated with competitive plants. Life-history characteristics of seed plants have been used to identify strategies that have evolved to environmental characteristics. In the three-strategy, fit C-S-R model proposed by Grime (1979), plants exist in particular places at par- ticular times as a result of reaching an equilibrium between the intensities of numerous and disturbance, competition. Autecological studies of plant stress, species have allowed plant ecologists to generate a of morphological, phys- list and with main iological, life-history attributes associated the three, strategies; One competitive, and ruderal (Grime 1988). characteristic stress-tolerant, et al., used to distinguish between these strategies growth, with the most rapid rates is generally found environments with abundant resources and relatively low in may disturbance, although plant species differ widely in their relative rate of biomass production, even when grown as isolated individuals under productive conditions (Garnier, 1991). There are also differences in the grovirth of individual may mechanism whereby plants and of plant populations, which be a species and with more monopolize suppress resources competitive rapidly strategies the growth and regeneration of neighboring plants (Grime et 1988). al., A second used distinguish plant strategies are those suite of characteristics to related to the size and composition of supporting and photosynthetic structures. Biomass allocation typically defined in terms of leaf, stem, and root weight is ratios and allocation leaves and stems of particular importance (Lambers to is and Poorter, 1992). Patterns, as well as shifts in allocation patterns, reflect se- may lective pressures and be a measure of the adaptive significance associated Some even with specific plant structures (Harper, 1977). ratios are plastic, in response small conditions (Dong, 1995). Therefore, leaves to differences in local AMERICAN FERN VOLUME NUMBER JOURNAL: 87 2 may barometer represent a particularly sensitive for assessing plant strategies used to adapt and succeed under, existing environmental conditions. to, Plant strategies have been proposed for a number of herbs, trees and shrubs, and bryophytes, lichens (Grime 1988) but type of analysis has not et this al., been The and among applied to ferns. great variety in leaf sizes textures ferns has been used to qualify species as more primitive or recently evolved (Gifford may and and Foster, 1989) also suggests that leaves provide excellent models determining for life-history strategies appropriate for different environments. and Certainly, the reproductive physiological differences that distinguish ferns make from other plants such an analysis desirable. We examined the sizes of leaves of three fern species that have contrasting We how grow leaf forms but in similar determined biomass was habitats. divid- ed within on which the focusing function photosynthetic leaf, leaflets, as units, and which leaf have both photosynthetic and support Under- stalks, functions. was lying our investigation the question of whether these species exhibit similar under strategies apparently similar environmental conditions in freshwater, for- ested habitats. A clearly defined, monospecific population each was of of the three species selected in the Ecological Research Area, a 220-ha tract of land located in Hills- borough County, west central Florida (28°05' N, 82°20' W) The in July 1994. populations of Thelypteris dentata and Woodwardia (Forssk.) John E. St. virgin- m ica (L.) Sm. were approximately 50 from each wetland other in a forested dominated by elm {Ulmus americana and oak [Quercus L.) Michx.). laurifolia The Osmunda population of was km regalis located approximately away, L. 1 but in a similar Nomenclature habitat. follows Wunderlin that of (1982). The density (number of leaves of leaves per square meter) each species for was calculated in three areas of each population. Twenty over the five leaves, range size represented, were collected between to establish the relationship length and weight during leaf growth. Their length was measured within hours 2 and after collection the weight of and measured leaflets leaf stalks after drying A 60°C at for 2 days. curve-fitting procedure (DeltaGraph was used de- to 3.5) termine the relationship between and length weight. Ten leaves of dentata and T. W. virginica and 10 clumps were of O. regalis randomly by selected throwing marker a The were into the population. leaves clipped at the surface and placed in a labeled plastic bag. The length and area each was of measured leaf within 2 hours of Each was then collection. leaf separated and into leaflets leaf stalks (petioles), placed in individual, labeled aluminum containers, dried 60°C and at for 2 days, weighed. Two were ratios calculated, both reflecting relative contributions of energy invested in photosynthetic versus support were tissue. Leaf length:mass ratios calculated using the and total leaf length dry mass, and were leaflet:stalk ratios calculated using the dry mass of leaflets to the dry mass of The specific stalks. leaf area area/dry was (leaf weight) also determined. BARTSCH AND LAWRENCE: AND LEAF BIOMASS SIZE 72 Table 1. Leaf characteristics (mean and standard deviations with sample size in parentheses) of The lypteris dentata. Wood.vardia and Ostnunda vi,'ginica, regalis in west central Florida. Characteristic T. dentata W. virginica O. regalis Leaves m^ per ± 18 5 16 (3) i Leaf length (cm) 19.6(10) : Dry weight of leaves 0.06 ±0.06 ± (g) (10) 2.06 1.21 (10) 2.22 t 22.4(10) showed All three species considerable variation in leaf characteristics (Table had 1). Thelypteris dentata the densest population of leaves, but the leaves were considerably smaller and lighter than those of the two other species. Thelypteris had dentata also the greatest within species variation in leaf length and weight. The was specific leaf area (area:weight) of dentata twice that of W. virginica. T. Leaf area was not measured in O. regalis, as the instrument used to measure the was areas unavailable. The between and mass was relationship leaf length for a range of leaf sizes not linear (Fig. but was most highly correlated with a parabolic curve. Thus, 1), and more dentata W. virginica devoted energy to increasing leaf length (or T. height) early in their development while continuing to increase in biomass later in their development. The was and more ratio of leaf length:mass significantly higher variable for dentata than were more con- T. for the other species (Fig. Leaflet:stalk ratios 2). between and were sistent populations than length:mass ratios generally highest which showed two for dentata, also greater variation that the other species T. (Fig. 3). Discussion Osmunda The Woodwardia and populations of Thelypteris dentata, virginica, showed could regalis and intraspecific variation in leaf characteristics that inter- had be the result of different adaptive strategies. Thelypteris dentata the greatest variation both terms of being different from the other in leaf characteristics, in two species, as well as having high variability within the population. Thelyp- and teris dentata an introduced species in Florida, whereas W. virginica O. is may due Some be regalis are native differences in characteristics to this area. to this, although we cannot determine whether dentata is different from the T. native plants because introduced, as we have neither other populations nor is it other introduced with which compare our data. species to Although our observation that three species, variation in leaf size exists for all mass expansion plants invest more biomass height than leaf early in leaf in leaf canopy within suggests grow equalize the height of the that these ferns so as to new when growth shading the The canopy impacts population. height of the AMERICAN FERN JOURNAL: VOLUME NUMBER 87 2 { wardia virginica. from standing {dead litter leaves) influences the density, and growth rate size, of emerging shoots (Ekstam, much 1995). Thelypteris dentata does not produce biomass, and decompose leaves quickly once they become brown and Sim- dry. O. grows clumps ilarly, rega/js in that are slightly more elevated and where drier conditions and increased oxidation promote higher decomposition. rates of However, W. virginica has high biomass production, creating dense that litter does decompose not as rapidly and which may emerging affect the size of Thelypteris dentata more allocates energy producing to photosynthetic leaf material than supporting leaf material. This evident not only from the data is on ratios of length:weight and leafletsdeaf stalks but also from the qualitatively nature fragile of these leaves. Thelypteris dentata also has a higher specific leaf may and area capture more by light displaying These leaves horizontally. leaf adaptations are indicative of a stress-tolerant strategy (Grime 1988). Fur- et al., BARTSCH AND LAWRENCE: AND LEAF BIOMASS SIZE Ml O D DE WOV, OSRE V 1600 1400 1200- E 1000- 1 600- t i J jfc :: Fig. 2. Ratios of leaf length to leaf b Tbelypteris dentata (THDE), f we thermore, have not observed spore production in dentata in nearly three T. years of monitoring this population, and lack of investment to reproduction is another measure (Grime of a stress-tolerant strategy et 1988). al., Woodwardia and number virginica O. regalis exhibit a of the characteristics associated with competitive plants including robust and mesophytic leaves, a rapidly ascending monolayer canopy, and high investment in support tissue to provide height growth which increases competitive effectiveness for radiation (Grime et 1988). not possible to quantify competitive interactions in the al., is It absence of shared environmental (Mitchell-Olds, 1987) but likely effects is it due that intraspecific competition for light resources occurs in both populations to the high density of leaves in W. virginica and the clumped growth of O. regalis. Competitive plants also tend to have high turn-over rates for leaves since, in a competitive situation, the ability to redistribute resources from old leaves to new may Some and better placed ones be crucial (Grime 1979). of the leaves measured in study may have been produced different times during the this at season, serving different functions as environmental conditions changed over The and time. value of a leaf varies with developmental age (Harper, 1989), its we cannot assume leaves were necessarily older leaves in the case that larger of these ferns. Although there a growing body of research related to fern populations is (Werth and be need fundamental studies Cousens, 1990) there continues to a for such within as these build our understanding about basic characteristics this to group versus native of plants. In addition to identifying strategies for exotic ferns, future research related to plant strategies should strive to include allo- cation to reproductive as well as vegetative structures since plant strategies re- populations (growth) flect a trade-off between efficiencies in maintaining local VOLUME NUMBER AMERICAN FERN JOURNAL: 87 2 QOSKE thde WOVI {~\ 10-1 ^ 8- «j 7- E 5 6- . .^ :: n« I . te i ™l 'M 1 and expanding Our populations (reproduction). study does not include repro- ductive allocation, because only W. virginica produced although both sori, T. and dentata O. regalis are capable of producing sori and viable spores. This raises interesting questions about the absolute and relative allocation to repro- among duction and between between produce ferns, particularly species that and similar fertile vegetative leaves (where sori are borne on "normal" leaves) versus those that produce modified leaves resembling bearing fertile stalks sori. Literature Cited Morphological 95. responses to conditions in clonal herbs from contrasting Oecologia 101:282-288. . Ramet 1995. size equalisation Phragmites plant, Oecologia ii australis. 104: omass allocation and growth in herbaceous Trends plants. Foster. Morphology and S. evoluti . P. 1979. Plant strategies and vegetation processes. John Wiley & Sons, Ltd. R, G. Hodgson, and R. Hunt. 1988. Comparative plant ecology: a functional approach J. common Unwin, Hyman, British species. London. L. 1977. Population biology of plants. Academic Press, London. J. The 1989. value of a Oecologia 80:53-58. leaf. and H. Porter. H., 1992. Inherent variation in growth rate between higher ;, plants: a search for physiological causes and ecolc Ecol. Res. 23:187-261. Mitchell-Olds, 1987. Analysis T. of Ecology Ic lant size. 68:82-87. Werth, C. R. and M. I. Cousens. 1990. Summary: The contributions of population studies o Amer. Fern 80:183-190. J. Guide 982. to the vascular plants of central Florida. 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