Hydrological and Climatic Responses of Pinus Elliottii Var. Densa in Mesic Pine Flatwoods Florida, USA Chelcy Ford, Jacqueline Brooks

Total Page:16

File Type:pdf, Size:1020Kb

Hydrological and Climatic Responses of Pinus Elliottii Var. Densa in Mesic Pine Flatwoods Florida, USA Chelcy Ford, Jacqueline Brooks Hydrological and climatic responses of Pinus elliottii var. densa in mesic pine flatwoods Florida, USA Chelcy Ford, Jacqueline Brooks To cite this version: Chelcy Ford, Jacqueline Brooks. Hydrological and climatic responses of Pinus elliottii var. densa in mesic pine flatwoods Florida, USA. Annals of Forest Science, Springer Nature (since 2011)/EDP Science (until 2010), 2003, 60 (5), pp.385-392. 10.1051/forest:2003030. hal-00883710 HAL Id: hal-00883710 https://hal.archives-ouvertes.fr/hal-00883710 Submitted on 1 Jan 2003 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Ann. For. Sci. 60 (2003) 385–392 385 © INRA, EDP Sciences, 2003 DOI: 10.1051/forest:2003030 Original article Hydrological and climatic responses of Pinus elliottii var. densa in mesic pine flatwoods Florida, USA Chelcy Rae FORDa,b, Jacqueline Renée BROOKSc* a Department of Biology, University of South Florida, Tampa FL 33620-5150, USA b Present address: Warnell School of Forest Resources, University of Georgia, Athens GA 30602-2152, USA c U.S. EPA/NHEERL Western Ecology Division, Corvallis, OR 97333, USA (Received 4 January 2002; accepted 18 September 2002) Abstract – Pinus elliottii Engelm. var. densa Little & Dorman is the only native sub-tropical pine in the US and is now restricted to an estimated 4.5% of its original area. To understand how this species might respond to changing environments, we examine the relationship between two hydrologic variables and growth of three stands of P. elliottii var. densa occurring along a hydrologic gradient using tree-ring records. The two variables were a short-term indicator of water status, precipitation minus potential evapotranspiration (P-PET), and a long-term indicator of water status, runoff (R). Growth at all sites was positively correlated to current growing season P-PET and R, and strongly, negatively correlated with previous winter R. The positive correlation with spring R was greater in the site with the deepest water table than in sites with shallower water tables. We discuss the potential for root dynamics to explain the relationships between growth and R. south Florida slash pine / Pinus elliottii var. densa / dendrochronology / tree-ring / runoff / potential evapotranspiration Résumé – Réaction de Pinus elliottii var. densa aux conditions hydrologiques et climatiques dans les forêts de plaine mésoïque. Pinus elliottii Engelm. Var densa Little et Dorman est la seule espèce de pin subtropicale des États-Unis. Elle n’occupe plus que 4,5 % de son aire d’origine. Afin de comprendre comment cette essence pourrait réagir face à un changement des conditions de milieu, nous avons examiné les relations entre deux variables hydrologiques et l’accroissement dans 3 peuplements de P. elliottii var. densa situés sur des stations présentant un gradient hydrologique, à partir de mesures de largeur de cernes. Les deux variables étaient d’une part un indicateur à court terme du statut hydrique, à savoir précipitations moins l’évapotranspiration potentielle (P-PET) et d’autre part un indicateur à long terme du niveau de la nappe d’eau dans le sol par mesure de l’écoulement (R). La croissance, dans toutes les stations, était corrélée positivement avec P-PET et R de la saison de végétation en cours ; la liaison est très fortement négative avec le R de l’hiver précédent. La corrélation positive avec le R du printemps est plus grande pour la station dont le niveau de la nappe d’eau dans le sol est plus profond que pour les stations à niveau d’eau plus superficiel. La discussion porte sur le potentiel dynamique des racines pour expliquer les relations entre croissance et R. Slash Pine de Floride du Sud / Pinus elliottii var. densa / dendrochronologie / cernes / écoulement de l’eau / évapotranspiration potentielle 1. INTRODUCTION mesic pine flatwoods in southern peninsular Florida are domi- nated by Pinus elliottii Engelm. var. densa Little & Dorman Recent changes in land-use practices are having a dramatic (south Florida slash pine), the only pine to inhabit the lower effect on ecosystem characteristics [7] and are largely driven third of the Florida peninsula, and the only native subtropical by changes in hydrology. Faced with the impact of rapid envi- pine in the United States [28]. Currently, the P. elliottii var. ronmental changes and limited resources, Myers et al. [34] densa ecosystem type has been reduced in area by 95% from identified 25 global hotspots for conservation priorities. Southern pre-settlement conditions [39]. peninsular Florida was included as the third-ranked hotspot. Managers of parks and other areas within critical biodiver- Land-use changes in Florida are threatening the remaining nat- sity hotspots have begun to preserve and restore P. elliottii var. ural pine forest ecosystems. Among these pine forest ecosys- densa flatwoods throughout south Florida, without specific tems, pine flatwoods are characterized by dry, sandy, nutrient- data on basic long-term abiotic responses of these ecosystems. poor soils and a frequent fire-regime (every 3–10 years). Site Local hydrology has a strong effect on species composition moisture availability largely controls the productivity of these and ecosystem productivity in these flatwood systems; thus, ecosystems [31] and the dominant canopy species [32]. The understanding hydrological influences is critical for restoring * Corresponding author: [email protected] 386 C.R. Ford, J.R. Brooks these ecosystems. Specifically, managers need information on 1895 through 1998 the average annual precipitation of the region was how P. elliottii var. densa responds to hydrologic variables 1314 mm and the average annual temperature for the region was that can change over time due to climate change or land use 22.3 ºC (National Oceanographic and Atmospheric Administration alterations, such as precipitation, potential evapotranspiration, [35, 36]). MRSP is Florida’s largest state park encompassing river discharge or runoff, and groundwater table fluctuations. 11 686 ha of land and 22.5 km of the Myakka River. The park’s land was acquired in 1934 and until 1976 a fire-exclusion and suppression This long-term response information could allow managers to management strategy existed; yet, nearly 85% of the plant communi- assess the impact of potential hydrologic fluctuations and cli- ties in MRSP are fire-dependent [25]. The present management strat- mate change scenarios [44] on the sustainability of the habitat egy is to promote or create conditions under which these plant com- and to develop alternative strategies for conserving habitat if munities will re-establish (Belinda Perry, MRSP biologist, pers. the habitat was potentially vulnerable. comm.). The dominant ecosystems in MRSP are fire-maintained dry Long-term correlations between tree growth and these var- prairies, pine flatwoods (mesic flatwoods), scrubby flatwoods, and iables can be evaluated using tree-ring records [15, 16] when fire-intolerant oak-palm hammocks [25]. records of the hydrologic parameters spanning the length of 2.2. Site selection and sampling the tree-ring records exist. Reliable long-term records of pre- cipitation exist for many sites, and can be used to calculate Sites were selected to (1) span the range of hydrologic conditions potential evapotranspiration when combined with long-term in mesic pine flatwoods within the park, but be relatively close to records of temperature [23]. Subtracting potential evapotran- each other in order to decrease climatic variability between sites, spiration from precipitation provides an estimate of water (2) comprise older trees to maximize the length of the tree-ring chro- demand and deficit. Estimates of water supply are also impor- nology, and (3) comprise at least 10–20 dominant individuals so that the sample depth of the chronology would stabilize variance. In a tant; and although precipitation records exist, soil water table related study, we found five stands that met the second two objec- positions may be a more reliable indicator of water supply than tives. For this study, we eliminated two of those stands – one because precipitation because the water table is influenced by infiltra- of its geographic distance from the other sites, and the other because of tion and soil storage. Recent efforts to model flatwoods a negative shift in growth due to recent hydrological changes (see [12]). groundwater tables have shown that removal of the canopy Within each of the three sites (CG, NP, and SP, Tab. I), average layer raised the water table during dry years but not during wet depth to the water table was recorded in the dry season to provide a years [43]. This suggests that tree growth may be highly relative index of water table depth differences among sites. Using a dependent on access to groundwater in dry years; thus a corre- soil auger, two wells at each site were drilled to the water table (one lation between tree-ring growth and groundwater depth could near the maximum and minimum site elevation). After equilibration, be expected. However, long-term records of ground water lev- water-table depths were recorded and the two values for each site els generally do not exist, but correlations between ground were averaged (Tab. I). For the NP and CG sites, the 2 depth values water and tree growth can be inferred from runoff data because differed by an average of 15 cm; at the SP site, the wells differed by the water table controls runoff in these lowland systems. Run- 1 m (due to slight rise in elevation in the stand).
Recommended publications
  • Contortae, the Fire Pines
    Contortae, The Fire Pines Contortae includes 4 species occuring in the United States and Canada. Leaves are usually 2 per fascicle and short. The seed cones are small, and symmetrical or oblique in shape. These cones are normally serotinous, remaining closed or opening late in the season, and often remaining for years on the tree. Cone scales may or may not be armed with a persistent prickle, depending upon species. Contortae includes 2 species in the southeastern North America: Pinus virginiana Pinus clausa Virginia pine sand pine Glossary Interactive Comparison Tool Back to Pinus - The Pines Pinus virginiana Mill. Virginia pine (Jersey pine, scrub pine, spruce pine) Tree Characteristics: Height at maturity: Typical: 15 to 23 m (56 to 76 ft) Maximum: 37 m (122 ft) Diameter at breast height at maturity: Typical: 30 to 50 cm (12 to 20 in) Maximum: 80 cm (32 in) Crown shape: open, broad, irregular Stem form: excurrent Branching habit: thin, horizontally spreading; dead branches persistent Virginia pine regenerates prolificly, quickly and densely reforesting abandoned fields and cut or burned areas. This pine is a source of pulpwood in the southeastern United States on poor quality sites. Human uses: pulpwood, Christmas trees. Because of its tolerance to acidic soils, Virginia pine has been planted on strip-mine spoil banks and severely eroded soils. Animal uses: Old, partly decayed Virginia pines are a favorite nesting tree of woodpeckers. Serves as habitat for pine siskin (Spinus pinus) and pine grosbeak (Pinicola enucleator). A variety of songbirds and small mammals eat the pine seeds. Deer browse saplings and young trees.
    [Show full text]
  • Volume 27, No. 3 Southeastern Conifer Quarterly September 2020
    S. Horn Volume 27, no. 3 Southeastern Conifer Quarterly September 2020 American Conifer Society Southeast Region Alabama, Florida, Georgia, Kentucky, Louisiana, Mississippi, North Carolina, South Carolina, Tennessee, Virginia, West Virginia From the Southeast Region President Hello, Everyone! Well, we have made it thru 2/3rds of 2020! I hope everyone is doing well and enjoying their garden. It has been a good garden year. With not much else to do, we have spent a lot of time in the yard. Most of it has not looked this good in years. We are planning on moving some plants this fall and relocating others. Sort of a garden spring cleaning. Creating spots for many more conifers. They are much easier to weed around than some perennials, which we all know. We will be looking for some more low-spreading ground covers this fall and winter. We love them for the edges of the garden beds and in between larger specimens. I have spoken to Dr. Alan Solomon, and he is very excited that we will be going to visit his garden and the Knoxville area the first weekend in May. There is plenty of parking and room to socially distance in his garden. Other details of the meeting are still taking shape as to what we can do. In the meantime, this fall, we are going to try to do a few virtual tours of gardens or hold some discussions. We will try a few different things and see what works better. More info will be sent out by email later this month or in early October.
    [Show full text]
  • Flammability of Litter from Southeastern Trees: a Preliminary Assessment
    FLAMMABILITY OF LITTER FROM SOUTHEASTERN TREES: A PRELIMINARY ASSESSMENT J. Morgan Varner, Jeffrey M. Kane, Erin M. Banwell, and Jesse K. Kreye1 Abstract--The southeastern United States possesses a great diversity of woody species and an equally impressive history of wildland fires. Species are known to vary in their flammability, but little is known about southeastern species. We used published data and our own collections to perform standard litter flammability tests on a diverse suite of 25 native overstory trees from the region. Flame heights, duration of flaming and smoldering combustion, and fuel consumption were measured for each species. Species spanned a wide spectrum of flammability, from highly flammable to fire-impeding. The southeast has several flammable species, including several Pinus and Quercus that rank among the most flammable species ever measured. In addition to these species, several species burned with poor flammability, notably eastern hemlock [Tsuga canadensis (L.) Carrière], Ocala sand pine [P. clausa var. clausa (Chapm. ex Engelm.) Vasey ex Sarg.], and eastern white pine (P. strobus L.), dampening local fire intensity and enabling these fire-intolerant species to survive in fire-prone landscapes. INTRODUCTION The focus of flammability in forests is senesced The southeastern United States encompasses a litter, the primary carrier of fire in these wide variety of fire-prone ecosystems. Within ecosystems. Litter flammability can be evaluated this diversity of ecosystems, individual species in a number of ways that quantifies its ignitability have traits that allow them to withstand heating (resistance or delay to ignition), fire intensity (e.g., thick bark), recover damaged above- (energy release rate, as measured by flame ground stems (e.g., via resprouting), or link characteristics), sustainability (the duration of reproduction or establishment to the season or flaming and smoldering phases of combustion), frequency of fires.
    [Show full text]
  • Pinus Virginiana (Virginia Pine) Is a Small to Medium Sized Tree Growing Among the Central Hardwoods of the East-Central United States
    PinusPinus virginianavirginiana VirginiaVirginia pinepine by Dr. Kim D. Coder, Professor of Tree Biology & Health Care Warnell School of Forestry & Natural Resources, University of Georgia Pinus virginiana (Virginia pine) is a small to medium sized tree growing among the central hardwoods of the East-central United States. It was first described as a species in 1768. One other scientific name has been historically used for this tree, Pinus inops. The scientific name means “pine of Virginia.” Other common names include scrub pine, possum pine, shortstraw pine, poverty pine, black pine, spruce pine, and Jersey pine. Pinus virginiana grows from Long Island, New York, South to the Northern tier of counties in Georgia, and West to Western Tennessee. New York lists Pinus virginiana as a state endangered spe- cies. See the Georgia distribution map figure. Pinus virginiana is not a Southern yellow pine, but is more closely akin to more Northern and Western pines. It grows in Hardiness Zone 6a - 7a and Heat Zone 5-8. The lowest number of Hardiness Zone tends to delineate the Northern range limit and the largest Heat Zone number tends to define the Southern edge of the range. This native Georgia pine grows in Coder Tree Grow Zone (CTGZ) A-B (a multiple climatic attribute based map), and in the temperature and precipitation cluster based Coder Tree Planting Zone 1-3. Figure 2. Pinus virginiana is slow growing and short-lived (80 years). Pinus virginiana grows on well drained sites in uplands, sandy and rocky woodlands, ridges, and eroded and heavy soils. It colonizes old infertile lands with open mineral soil and few hardwood competitors.
    [Show full text]
  • Shoot Dieback of Planted Sand Pine Caused by Fusarium Moniliforme Var
    Shoot Dieback of Planted Sand Pine Caused by Fusarium moniliforme var. subglutinans G. M. BLAKESLEE, Assistant Professor of Forest Pathology, School of Forest Resources and Conservation and Department of Plant Pathology, and S. W. OAK, Biologist, and S. H. KRATKA, Assistant in Forest Pathology, School of Forest Resources and Conservation, Institute of Food and Agricultural Sciences, University of Florida, Gainesville 32611 subglutinans, as did cultures derived ABSTRACT BLAKESLEE, G. M., S. W. OAK, and S. H. KRATKA. 1980. Shoot dieback of planted sand pine from conidia transferred from sporo- caused by Fusarium moniliforme var. subglutinans. Plant Disease 64:703-704. dochia. The fungus isolates were morphologically the same (8) as those Fusarium moniliforme var. subglutinans was identified as the cause of shoot dieback in plantation- regularly obtained from slash pine grown Ocala and Choctawhatchee varieties of Pinus clausa in Florida. Isolates cultured from sand cankers as well as from sporodochia of F. pine were pathogenic to seedlings of both slash and sand pine. Sand pine seedlings were also moniliforme var. subglutinans from a susceptible to isolates of F. moniliforme var. subglutinans obtained from pitch cankers on slash variety of hosts and locations. (C. S. pine. Moses [personal communication] has recently isolated F. moniliforme var. subglutinans from a naturally occurring Pitch canker disease, caused by tested (3) by inoculating actively growing stem canker on a young Ocala sand pine Fusarium moniliforme Sheld. var. shoots of 2-yr-old potted slash pine and planted in a research area in Alachua subglutinans Wollenw. and Reink., is 18-mo-old potted Choctawhatchee sand County.) widespread in southern pine plantations pine seedlings.
    [Show full text]
  • Disturbance and Scale Effects on Southern Old- Growth Forests (USA)
    ABSTRACT: Sand pine (Pinus clausa [Chapm. ex Engelm.] Vasey ex Sarg.), often a monotypic dominant of the Florida (USA) scrub assemblage, is an early successional tree CONSERVATION ISSUES species that is small in size, short-lived, and disturbance dependent. It does not conform to traditional images of old-growth forest. Nevertheless, to implement old-growth policy, the U.S. Forest Service has published stand-scale quantitative guidelines for recognizing old-growth sand pine (Outcalt 1997). Although the policy is well intentioned, we question • the conceptual basis and management perspective implicit in developing a stand-scale definition of old-growth sand pine. Our principal concerns involve matters of scale and disturbance suppression. A stand-scale perspective on management of old-growth sand Disturbance and pine is doomed to failure: if fires are allowed to burn, older forests will be consumed; if fires are suppressed, sand pine will likely be replaced by shade-tolerant associates. A Scale Effects on landscape-level management framework is essential to allow for a spatiotemporally shifting pattern of mature sand pine patches embedded within a matrix of younger scrub. Moreover, we caution that modern scrub vegetation in wilderness areas occurs on a small Southern Old- scale and is dramatically altered by fire suppression; therefore, it is imprudent to use wilderness areas as a standard for judging the character of a sand pine scrub landscape Growth Forests in pre-European-contact conditions. (USA): The Sand Index terms: Florida, old growth, Pinus clausa, sand pine scrub, scale effects Pine Example DIFFERING IMAGES OF OLD GROWTH Albert J. Parker windswept, rocky ridges and south-facing Images of old-growth forest in the Amer- slopes characterized by thin, sandy soils Kathleen C.
    [Show full text]
  • Sand Pine Scrub Vegetation Response to Two Burning and Two Non-Burning Treatments
    SAND PINE SCRUB VEGETATION RESPONSE TO TWO BURNING AND TWO NON-BURNING TREATMENTS Richard E. Roberts Florida Department of Environmental Protection, P.O. Box 1246, Hobe Sound, FL 33475 Anne C. COX Florida International University, Miami, FL 33199 ABSTRACT Peninsula Florida's sand pine scrub community tends to burn with a high fire intensity under sometimes extreme weather conditions, thus exhibiting uncontrollable and unpredictable fire behavior. Because of the potential hazards and risks associated with scrub burns, few representative samples of these xeric.pinewoods are being perpetuated by natural or human-induced fires, often with subsequent adverse effects on the community's flora and fauna, including its many endangered and threatened species. To study the effects of burning versus not burning scrub parcels of various sizes, a combination of fire and mechanical alteration treatments was applied in May 1996 to 4.05 hectares of this community at Jonathan Dickinson State Park in southeastern Florida. Effects of the 4 treatments on the canopy, shrub understory, and ground cover were compared with each other and untreated areas. Three permanent 5 X 20-meter nested quadrats were located in 3 replicate research units for: BURN (vegetation left intact and burned), CUT&BURN (shrubs and small trees cut, dried, and burned), MULCHED (all shrubs and trees chopped, mulched, and left unburned), and UNTREATED (natural vegetation left intact). Two replicate units were also established for HAND-CUT (understory vegetation hand-cut, removed, and not burned). Preliminary results (1 year after burn) show a significant difference (F(4,37) = 10.6, P < 0.01) in mean number of trees that died in the treated and untreated units.
    [Show full text]
  • Population Ecology of a Sandhill Endemic Shrub, Ceratiola Ericoides
    POPULATION ECOLOGY OF A SANDHILL ENDEMIC SHRUB, CERATIOLA ERICOIDES (SANDHILL ROSEMARY) by JOHN PAUL SCHMIDT (Under the Direction of C. Ronald Carroll) ABSTRACT Ceratiola ericoides (sandhill rosemary) is a dioecious, wind-pollinated, evergreen shrub adapated to the xeric, fire-adapted communities of the Southeast. 1. Spatial pattern of males and females in C. ericoides was investigated. Ripley’s K was used to analyze the spatial pattern of mapped populations of C. ericoides, and whether they exhibited spatial segregation of sexes (SSS). Results provide little evidence of SSS in this species. 2. Optimal fire frequency for C. ericoides was also investigated. Bayesian methods were employed to derive populations parameters from data collected in the field and from air-photos over a four-year period. Under the Bayesian approach, every parameter has a probability distribution rather than a fixed value. Results of Bayesian analyses of demographic data suggest that that increasing female distance from male significantly reduced realized female fecundity; both mortality and fecundity were higher on burned sites; shrub survivorship significantly increased with distance from longleaf pine on burned sites. These data were used to parameterize a stochastic individual-based model of C. ericoides population dynamics. Results suggest that a 20 year fire return cycle is optimal for C. ericoides, but that stochastic fire return intervals between 3 and 20 years result, on average, in population increases. INDEX WORDS: Plant population ecology, Ceratiola
    [Show full text]
  • May 6, 2021 Aaron Stuckmeyer Pulte Homes
    May 6, 2021 Aaron Stuckmeyer Pulte Homes – North Florida Division 4901 Vineland Road, Suite 500 Orlando, Florida 32811 Proj: Kerina Parkside PD – County, Florida Sections 10 & 15, Township 24 South, Range 28 East Re: 2021 Sand Skink Survey Report (BTC Project #214-102) Dear Mr. Stuckmeyer: During March and April of 2021, Bio-Tech Consulting, Inc. (BTC) conducted a formal sand skink (Neoseps reynoldsi) survey on the Kerina Parkside PD site. This project site is approximately 68.66 acres and is located east of Apopka Vineland Road (CR 435) and south of Buena Vista Woods Boulevard, with Fenton Street bisecting the property east to west; within Sections 10 & 15, Township 24 South, Range 28 East, Orange County, Florida (Figures 1 & 2). The following presents an environmental description of the property, survey methodology, and the results of the sand skink survey. TOPOGRAPHY Based upon review of the USGS Topographic Map Lake Jessamine Quad, (Figure 3), the property elevations range from 110 feet to 125 feet NGVD. The land generally slopes down from the western boundary towards the eastern boundary of the subject site. Aaron Stuckmeyer; Pulte Homes Kerina Parkside PD– Orange County, Florida Sand Skink Survey Report (BTC File #214-102) Page 2 of 11 SOILS According to the Soil Survey of Orange County, Florida, prepared by the U.S. Department of Agriculture (USDA) Natural Resources Conservation Service (NRCS), eight (8) soil types occur within the subject property boundaries (Figure 4). These soils include the following: Immokalee fine sand (#20) Pomello fine sand, 0 to 5 percent slopes (#34) St. Johns fine sand (#37) St.
    [Show full text]
  • Fine-Scale Genetic Structure in Pinus Clausa (Pinaceae) Populations: Effects of Disturbance History
    Heredity 87 (2001) 99±113 Received 22 August 2000, accepted 30 April 2001 Fine-scale genetic structure in Pinus clausa (Pinaceae) populations: effects of disturbance history KATHLEEN C. PARKER* , J. L. HAMRICKà, ALBERT J. PARKER & JOHN D. NASONà Department of Geography, University of Georgia, Athens, GA 30602, àDepartments of Botany and Genetics, University of Georgia, Athens, GA 30602 and §Department of Botany, Iowa State University, Ames, IA 50011, U.S.A. Spatial autocorrelation analyses of 12 allozyme loci were used to compare genetic structure within populations of two varieties of Pinus clausa. P. clausa var. immuginata populations tend to be uneven- aged, with continuous recruitment in small gaps created by wind damage, whereas P. clausa var. clausa populations are more even-aged, with recruitment postdating periodic canopy ®res. Three var. immuginata populations and three matched pairs of var. clausa populations, including both a mature and a nearby recently burned population, were examined. Aggregation of multilocus genotypes at small distances was evident in all young var. clausa populations. Little inbreeding was apparent among juveniles or adults in these populations; their genetic structure is likely to have resulted from limited seed dispersal. Genotypes were not signi®cantly spatially structured in nearby matched mature populations. Genetic structure was less evident in var. immuginata populations. Aggregated genotypes were only apparent in the population where patches included juveniles of similar ages; dense juvenile clumps in the other two var. immuginata populations comprised a variety of ages. Interannual variability in allele frequencies of surviving seedlings may account for the absence of genetic structure in these populations.
    [Show full text]
  • Allelopathic Effects of Ceratiola Ericoides (Empetraceae) on Germination and Survival of Six Florida Scrub Species
    Plant Ecol (2008) 198:47–59 DOI 10.1007/s11258-007-9384-8 Allelopathic effects of Ceratiola ericoides (Empetraceae) on germination and survival of six Florida scrub species Rebecca E. Hewitt Æ Eric S. Menges Received: 14 August 2007 / Accepted: 7 November 2007 / Published online: 23 November 2007 Ó Springer Science+Business Media B.V. 2007 Abstract Allelopathic inhibition of germination by Keywords Gap specialist Á Leachates Á Florida scrub plants has been demonstrated in the Fire Á Seedling survival Á Rosemary scrub Á greenhouse and lab, but not in the field. We studied the Allelopathy allelopathic effects of Florida rosemary (Ceratiola ericoides) roots, leaves, and litter leachates on field germination and three-month survival of six Florida Introduction scrub species, three habitat generalists (Lechea deckertii, Palafoxia feayi, and Polygonella robusta), and three In 300 B.C., Theophrastus made the first known rosemary scrub specialists (Hypericum cumulicola, observation of allelopathy (Rice 1984). Since then Lechea cernua,andPolygonella basiramia). We used allelopathy, the direct or indirect harmful or stimula- AIC and model averaging to evaluate support for a tory effect of one plant on another through the series of non-exclusive hypotheses. Species varied in production and release of chemical compounds, has germination (2.7–24.6%) and survival (39.2–71%) been noted as an important form of plant-to-plant percentages, and in their sensitivity to leachates. interference in natural and agricultural settings (Rice Germination of scrub species was most negatively 1984). Allelochemicals, secondary compounds pro- affected by leaf [ root [ litter leachates, although not duced by plants, occur in leaves and stems, though all species followed the overall trend.
    [Show full text]
  • Rapid Assessment Metrics to Enhance Wildlife Habitat and Biodiversity Within Southern Open Pine Ecosystems
    Rapid Assessment Metrics to Enhance Wildlife Habitat and Biodiversity within Southern Open Pine Ecosystems Carl Nordman, Rickie White, Randy Wilson, Clay Ware, Catherine Rideout, Milo Pyne, Chuck Hunter Version 1.0 Date of current draft: 5-12-2016 Table of Contents Acknowledgements ....................................................................................................................................... 4 Executive summary ....................................................................................................................................... 6 Introduction .................................................................................................................................................. 7 Purpose and Use of this Document .......................................................................................................... 7 Study Area / Scope and Scale of Project ................................................................................................... 8 Priority Species ........................................................................................................................................ 10 Summary information for Priority Wildlife Species ................................................................................ 12 Methods ...................................................................................................................................................... 16 Priority Species .......................................................................................................................................
    [Show full text]