The Quantitative Importance of Stemflow: an Evaluation of Past Research and Results from a Study in Lodgepole Pine (Pinus Contorta Var
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Landscaping and Gardening with Native Plants in Georgia's Coastal
Dry woodlands with scattered canopy trees WHAT ARE NATIVE PLANTS? often support a profusion of fall blooming & Native Plants, species that grew naturally in this wildflowers such as sunflowers, goldenrods, region prior to the colonial era, are uniquely G with and blazing stars. The upland forest with adapted to local conditions. They are suited to both the highest soil moisture occurs on slopes the physical and biological conditions of their native Native Plants where resistance to fire allows a variety of areas. trees such as American beech, white oak, BENEFITS OF NATIVES Georgia’s spruce pine, and southern magnolia to Promote biodiversity grow, as well as shrubs like Carolina Lower landscape & garden maintenance once Coastal buckthorn, needle palm, red buckeye, horse established by reducing the need for fertilizer, sugar, fringe tree, and native azaleas. pesticides and watering. Where soils have higher moisture and Foster appreciation of our natural mineral levels, the ground layer is rich and heritage and the beauty of our native reminiscent of the Southern Appalachians landscape with spring flowering plants like bloodroot, Native flora provide food and shelter tailored May apple, trout lily, doll’s eyes and to wildlife Solomon’s seal. By maintaining natural habitats and mending Coastal Plain of G LOWLANDS AND WETLANDS are areas those that are fragmented, you can make a Climate Zone: 8B Eco-regions 65 - 75 where the soil is inundated or saturated for a difference whether working at the landscape portion of each year, and include both riverine level or planting in containers. THE COASTAL PLAIN OF GEORGIA in this BASICS FOR USING NATIVES and isolated wetlands. -
Meteorological Influences on Stemflow Generation Across Diameter Size Classes of Two Morphologically Distinct Deciduous Species
See discussions, stats, and author profiles for this publication at: https://www.researchgate.net/publication/260683953 Meteorological influences on stemflow generation across diameter size classes of two morphologically distinct deciduous species Article in International Journal of Biometeorology · March 2014 DOI: 10.1007/s00484-014-0807-7 · Source: PubMed CITATIONS READS 13 52 3 authors, including: John Toland Van Stan Jarrad Van Stan Georgia Southern University Harvard Medical School, Massachusetts Gen… 64 PUBLICATIONS 398 CITATIONS 25 PUBLICATIONS 105 CITATIONS SEE PROFILE SEE PROFILE Some of the authors of this publication are also working on these related projects: Canopy influences over microbial processes in forest critical zones View project Effects of Urbanization on Forest Canopy Ecohydrology View project All content following this page was uploaded by John Toland Van Stan on 16 July 2015. The user has requested enhancement of the downloaded file. Int J Biometeorol (2014) 58:2059–2069 DOI 10.1007/s00484-014-0807-7 ORIGINAL PAPER Meteorological influences on stemflow generation across diameter size classes of two morphologically distinct deciduous species John T. Van Stan II & Jarrad H. Van Stan & Delphis F. Levia Jr. Received: 15 November 2013 /Revised: 11 February 2014 /Accepted: 19 February 2014 /Published online: 11 March 2014 # ISB 2014 Abstract Many tree species have been shown to funnel sub- meteorological conditions). Multiple regressions performed on stantial rainfall to their stem base as stemflow flux, given a leafless canopy stemflow resulted in an inverse relationship favorable stand structure and storm conditions. As stemflow is with wind speeds, likely decoupling stemflow sheltered solely a spatially concentrated flux, prior studies have shown its on bark surfaces from VPD influences. -
Nutrient Cycling by Throughfall and Stemflow Precipitation in Three Coastal Oregon Forest Types
NUTRIENT CYCLING BY THROUGHFALL AND STEMFLOW PRECIPITATION IN THREE COASTAL OREGON FOREST TYPES by ROBERT F. TARRANT, K. C. LU, W. B. BOLLEN, and C. S. CHEN PACIFIC NORTHWEST U.SD.A. FOREST SERVICE FOREST AND RANGE EXPERIMENT STATION RESEARCH PAPER PNW-54 U S. DEPARTMENT OF AGRICULTURE • FOREST SERVICE 1968 CONTENTS INTRODUCTION 1 EXPERIMENTAL PROCEDURES 2 RESULTS AND DISCUSSION 3 Nitrogen 3 Total Dissolved Solids 4 Acidity of Precipitation 5 CONCLUSIONS . .... ..... 6 LITERATURE CITED 7 Robert F. Tarrant and K C. Lu are, respect- ively, Principal Soil Scientist and Microbiolo- gist, Forestry Sciences Laboratory, Pacific Northwest Forest and Range Experiment Sta- tion, Corvallis, Oregon. W. B. Bollen and C. S. Chen are, respectively, Professor and Research Assistant, Department of Microbiology, Oregon State University, Corvallis, Oregon. This study was supported, in part, by the National Science Foundation, Grant No. GB- 3214. INTRODUCTION In the Pacific Northwest, where annual pre- cipitation ranges from about 40 to 120 inches per year in commercial forest areas, rainfall washing through the forest canopy returns a part of the nutrient capital of the ecosystem to the soil. Nitrogen is of special interest in this connection because it is the only nutrient ele- ment thus far found to appreciably stimulate growth of Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco) when applied as fertilizer (Gessel et al. 1965). A number of tree species throughout the world have been shown to contribute to the en- richment of throughfall and stemflow. 1 but in most studies of this phenomenon, only nonnitro- genous nutrient ions have been determined. Few investigators have determined N content in throughfall and stemflow (Voigt 1960b; Sviridova 1960; Mina 1965; Maruyama et al. -
Rainfall Input, Throughfall and Stemflow of Nutrients in a Central
Biogeochemistry 67: 73–91, 2004. © 2004 Kluwer Academic Publishers. Printed in the Netherlands. Rainfall input, throughfall and stemflow of nutrients in a central African rain forest dominated by ectomycorrhizal trees G.B. CHUYONG1,2,4, D.M. NEWBERY2,3,* and N.C. SONGWE1 1Institute of Agronomic Research, Forest Research Station Kumba, PMB 29 Kumba, Cameroon; 2De- partment of Biological and Molecular Sciences, University of Stirling, Stirling, FK9 4LA, UK; 3Institute of Plant Sciences, University of Bern, Altenbergrain 21, Bern, CH-3013, Switzerland; 4Current address: Department of Life Sciences, University of Buea, POB 63 Buea, Cameroon; *Author for correspon- dence (e-mail: [email protected]; phone: 0041-31-631-8815; fax: -31-332-2059) Received 5 March 2002; accepted in revised form 14 January 2003 Key words: Atmospheric input, Ectomycorrhizas, Korup, Leaching, Phosphorus, Priming effect Abstract. Incident rainfall is a major source of nutrient input to a forest ecosystem and the consequent throughfall and stemflow contribute to nutrient cycling. These rain-based fluxes were measured over 12 mo in two forest types in Korup National Park, Cameroon, one with low (LEM) and one with high (HEM) ectomycorrhizal abundances of trees. Throughfall was 96.6 and 92.4% of the incident annual rainfall (5370 mm) in LEM and HEM forests respectively; stemflow was correspondingly 1.5 and 2.2%. Architectural analysis showed that ln(funneling ratio) declined linearly with increasing ln(basal area) of trees. Mean annual inputs of N, P, K, Mg and Ca in incident rainfall were 1.50, 1.07, 7.77, 5.25 and 9.27 kg ha−1, and total rain-based inputs to the forest floor were 5.0, 3.2, 123.4, 14.4 and 37.7 kg ha−1 respectively. -
ISTA List of Stabilized Plant Names 7Th Edition
ISTA List of Stabilized Plant Names th 7 Edition ISTA Nomenclature Committee Chair: Dr. M. Schori Published by All rights reserved. No part of this publication may be The Internation Seed Testing Association (ISTA) reproduced, stored in any retrieval system or transmitted Zürichstr. 50, CH-8303 Bassersdorf, Switzerland in any form or by any means, electronic, mechanical, photocopying, recording or otherwise, without prior ©2020 International Seed Testing Association (ISTA) permission in writing from ISTA. ISBN 978-3-906549-77-4 ISTA List of Stabilized Plant Names 1st Edition 1966 ISTA Nomenclature Committee Chair: Prof P. A. Linehan 2nd Edition 1983 ISTA Nomenclature Committee Chair: Dr. H. Pirson 3rd Edition 1988 ISTA Nomenclature Committee Chair: Dr. W. A. Brandenburg 4th Edition 2001 ISTA Nomenclature Committee Chair: Dr. J. H. Wiersema 5th Edition 2007 ISTA Nomenclature Committee Chair: Dr. J. H. Wiersema 6th Edition 2013 ISTA Nomenclature Committee Chair: Dr. J. H. Wiersema 7th Edition 2019 ISTA Nomenclature Committee Chair: Dr. M. Schori 2 7th Edition ISTA List of Stabilized Plant Names Content Preface .......................................................................................................................................................... 4 Acknowledgements ....................................................................................................................................... 6 Symbols and Abbreviations .......................................................................................................................... -
Variability of Throughfall and Stemflow Deposition in Pine and Beech Stands ( Czarne Lake Catchment, Gardno Lake Catchment on Wolin Island )
PrACE GEOGrAfICzNE, zeszyt 143 Instytut Geografii i Gospodarki Przestrzennej UJ Kraków 2015, 85 – 102 doi : 10.4467/20833113PG.15.027.4628 Variability of throughfall and stemflow deposition in pine and beech stands ( Czarne lake catchment, gardno lake catchment on wolin island ) Robert Kruszyk, Andrzej Kostrzewski, Jacek Tylkowski Abstract : The research sought to determine the range of conversion of the chemical composition of precipitation in a beech stand located in the Gardno Lake catchment ( Wolin Island ) and a pine stand in the Czarne Lake catchment ( Upper Parsęta catchment, West Pomerania Province ). The presented results cover three hydrological years : 2012, 2013 and 2014. The research focused on the chemical composition of bulk precipitation ( in the open ), throughfall and stemflow ( in a forest ). The obtained results confirm that after precipitation has had contact with plant surfaces there is an increase in its mineral content. This is due to the process of enrichment of throughfall and stemflow with elements leached out of needles + 2+ + – + 2+ 2– – and leaves ( K , Mg ) and coming from dry deposition ( NH 4, Cl , Na , Mg , SO 4 , NO 3 ) washed out from plant surfaces. The research, based on the canopy budget model, indicates that in the case of potassium, its load leached out of needles and leaves accounted for 75.6 % and 73 %, respectively, of its total deposition on the forest floor. Calcium leaching was not detected in either of the two stands. In comparison with potassium, the range of magnesium leaching was smaller and amounted to 34 % under beech and 26.5 % under pine. As to loads of potassium and magnesium in the beech stand, they were more than twice as large as the ones observed in the pine stand. -
The Interception Process in Tropical Rain Forests: a Literature Review and Critique (*)
THE INTERCEPTION PROCESS IN TROPICAL RAIN FORESTS: A LITERATURE REVIEW AND CRITIQUE (*) . R. T. Clarke (**) SÜMMARY A noviw oi tht tLtQJioJuAn on m&aAuKem&ntò o{ naln mtzn. íntzucdptÁon ptiocçAòzA by ^oheAtis i& madt. ln{)OtwiaXÁ.on on A^nÁca, C2.ntn.0l and South AmztvLca, and A&ia ÃJ> QÒJ&I. A gene.Aal anatgòLt, lò made. and thz me.d to kun.tho.h. tko.. mimuAomuntò undoA ^toXd condÁ. - txonò ÍÁ òtAQAòzd. BACKGROVm In temperate latitudes, interception as a component of the total evaporative loss from forests has been intensívely studíed (see, for example, Helvey & Patrick, 1965; HeJvey, 1967; Lawson, 7967; BJake, 1975; Calder, 1976, 1978) and its importance welj_ established. Field studies of the interception process have given results which, in rnany cases, have been expressed as empirical regression equations of the form I = aP + b G where I is the depth of water intercepted and lost by evaporaiion, P. is the gross rain b — fali incident upon the forest canopy, and a, b are regression coefficrents; see, for example, Penman (1963)- Many authors, however, Blake (1975) being one, expressed the relation in the alternative form (l/P„) = b/P+a expressing the fact that the percen- G G tage interception loss tends to be hyperbolically related to gross rainfall. In con - trast to this empirical approach, Rutter et ai. (1970, Gash & Morton have constructed physically-based computer models using as inputs rainfal? and the meteorológica! varia- bles controlling evaporation to compute a running water balance of a forest canopy with known structure, thereby producing estimates of interception losses. -
Is Stemflow a Vector for the Transport of Small Metazoans from Tree Surfaces
Ptatscheck et al. BMC Ecol (2018) 18:43 https://doi.org/10.1186/s12898-018-0198-4 BMC Ecology RESEARCH ARTICLE Open Access Is stemfow a vector for the transport of small metazoans from tree surfaces down to soil? Christoph Ptatscheck* , Patrick Connor Milne and Walter Traunspurger Abstract Background: Stemfow is an essential hydrologic process shaping the soil of forests by providing a concentrated input of rainwater and solutions. However, the transport of metazoans by stemfow has yet to be investigated. This 8-week study documented the organisms (< 2 mm) present in the stemfow of diferent tree species. Because the texture of the tree bark is a crucial determination of stemfow, trees with smooth bark (Carpinus betulus and Fagus sylvatica) and rough bark (Quercus robur) were examined. Results: Up to 1170 individuals per liter of stemfow were collected. For rotifers and nematodes, a highly positive cor- relation between abundance and stemfow yield was determined. Both taxa were predominant (rotifers: up to 70%, nematodes: up to 13.5%) in the stemfow of smooth-barked trees whereas in that of the oak trees collembolans were the most abundant organisms (77.3%). The mean number of organisms collected per liter of stemfow from the two species of smooth-barked trees was very similar. A higher number of nematode species was found in the stemfow of these trees than in the stemfow of rough-barked oak and all were typical colonizers of soil- and bark-associated habitats. Conclusion: This pilot study showed for the frst time that stemfow is a transport vector for numerous small metazo- ans. -
Viburnum L. Viburnum
VWYZ genera Layout 1/31/08 1:11 PM Page 1154 V Ericaceae—Heath family Vaccinium L. blueberry, cranberry Jason J. Griffin and Frank A. Blazich Dr. Griffin is assistant professor at Kansas State University’s Department of Horticulture, Forestry, and Recreation Resources, Manhatten, Kansas; Dr. Blazich is alumni distinguished graduate professor of plant propagation and tissue culture at North Carolina State University’s Department of Horticultural Science, Raleigh, North Carolina Occurrence, growth habit, and uses. There are about Although cranberry has been introduced successfully 150 to 450 species (the number varies by authority) of into cultivation in British Columbia, Washington, and deciduous or evergreen shrubs (rarely trees or vines) in Oregon, Wisconsin and Massachusetts remain the largest Vaccinium (Huxley 1992b; LHBH 1976; Vander Kloet producers; the crops for 2000 were estimated at 2.95 and 1988). The majority of species are native to North and South 1.64 million barrels, respectively (NASS 2001). America and eastern Asia (LHBH 1976; Vander Kloet Evergreen huckleberry grows along the Pacific Coast 1988). Some of the more commonly cultivated North and is valued for its attractive foliage, which is often used in American species are listed in table 1. Like other members flower arrangements (Everett 1981). Species of Vaccinium of the Ericaceae, Vaccinium species require an acidic (pH also are prized as landscape plants. Lowbush forms are used 4.0 to 5.2) soil that is moist, well drained, and high in organ- to form attractive ground covers or shrubs. Two cultivars of ic matter (3 to 15%). Symptoms of mineral nutrient defi- creeping blueberry (V. -
Florida Exotic Pest Plant Councils 2017 List Of
CATEGORY II (continued) Gov. The 2017 list was prepared by the Scientific Name** Common Name List Zone FLEPPC List Definitions: Exotic – a species FLEPPC Plant List Committee Florida Exotic Pest Plant Tradescantia spathacea oyster plant C, S introduced to Florida, purposefully or accidentally, from a (Rhoeo spathacea, Rhoeo discolor) natural range outside of Florida. Native – a species Patricia L. Howell, Chair 2012-2017, Broward Tribulus cistoides puncture vine, burr-nut N, C, S Council’s 2017 List of whose natural range includes Florida. Naturalized County Parks, Natural Resources and Land Vitex trifolia simple-leaf chaste tree C, S Management Section, [email protected] Washingtonia robusta Washington fan palm C, S exotic – an exotic that sustains itself outside cultivation Invasive Plant Species Wisteria sinensis Chinese wisteria N, C (it is still exotic; it has not “become” native). Invasive Stephen H. Brown, UF / IFAS Lee County Xanthosoma sagittifolium malanga, elephant ear N, C, S exotic – an exotic that not only has naturalized, Extension, Parks and Recreation Division, The mission of the Florida Exotic Pest Plant but is expanding on its own in Florida native plant [email protected] Council is to support the management of invasive Recent changes to plant names exotic plants in Florida’s natural areas by communities. Janice Duquesnel, Florida Park Service, Florida providing a forum for the exchange of scientific, Department of Environmental Protection, educational and technical information. Old Name New Name Abbreviations: Government List (Gov. List): [email protected] www.fleppc.org Possession, propagation, sale, and/or transport of Aleurites fordii Vernicia fordii David W. -
Canopy Interception, Stemflow and Streamflow on a Small Drainage in the Missouri Ozarks
RESEARCH BULLETIN 951 APRIL, 1969 UNIVERSITY OF MISSOURI - COLUMBIA COLLEGE OF AGRICULTURE AGRICULTURAL EXPERIMENT STATION ELMER R. KIEHL, Director Canopy Interception, Stemflow and Streamflow on a Small Drainage in the Missouri Ozarks DAVID R. DEWALLE & LEE K. PAULSELL (Publication authorized April 12, 1969) COLUMBIA, MISSOURI TABLE OF CONTENTS Page Introduction ........ ... ........ ... ... ... .... ... ... .... 3 Canopy Interception .. ........... .. ........... .. ........... 3 Study Areas and Design ........... ..... .......... ... .. ... 4 Results .. .. .. ..... .. .... .... .. ...... .. .. ... .. ..... 5 Stemflow ... .. .. .. .. .. ... .. ... .. .. ... .. .. .... ... ... ... 8 Methods .. .. .... .. .. .. .. ...... ... ..... .......... 9 Results ...... .. .. , .. ......... ... ... .... .... ..... ... 11 Streamflow ... .... .... ..... ... ... .. .. .. ... ... .. ... .. 13 Gaging Installation D escription .. ... ... ....... ........ ..... 14 Results .... .. .... .. ................ .. ..... ..... ........... 14 H ydrologic Budget .. .. ..... ......... ... .. .... .... .. .......... 20 Methods . .. ... ....... ... ............. ..... .... .. .... 21 Results . .............................. .. ... ... ... ... ... 22 Summary ........... ... .. ... .. ...... .. ... .. .. .. .. ..... ... 25 Literature Cited .... .. .. ...... .. ........ ....... .. .. .. ... ...... 26 Canopy Interception, Stemflow and Streamflow on a Small Drainage in the Missouri Ozarks DAVID R. DEWALLE & LEE K. P AULSELL * INTRODUCTION This report presents an analysis -
Appendix 6: Invasive Plant Species
USDA Forest Service Understanding i-Tree – Appendix 6: Invasive Plant Species APPENDIX 6 Invasive Plant Species The following is a list of invasive tree and shrub species by state that are included in i-Tree database (version 6). Each list of invasive species is followed by the reference of the source which were obtained circa 2014. Some of the Web addresses are no longer working; some have been relocated to alternative sites. State-specific invasive species lists will be updated in the future. Alabama Ailanthus altissima Lonicera japonica Poncirus trifoliate Albizia julibrissin Lonicera maackii Pyrus calleryana Ardisia crenata Lonicera morrowii Rosa bracteata Cinnamomum camphora Lonicera x bella Rosa multiflora Elaeagnus pungens Mahonia bealei Triadica sebifera Elaeagnus umbellata Melia azedarach Vernicia fordii Ligustrum japonicum Nandina domestica Wisteria sinensis Ligustrum lucidum Paulownia tomentosa Ligustrum sinense Polygonum cuspidatum Alabama Invasive Plant Council. 2007. 2007 plant list. Athens, GA: Center for Invasive Species and Ecosystem Health, Southeast Exotic Pest Plant Council. http://www.se-eppc.org/ alabama/2007plantlist.pdf Alaska Alnus glutinosa Lonicera tatarica Sorbus aucuparia Caragana arborescens Polygonum cuspidatum Cytisus scoparius Prunus padus Alaska National Heritage Program. 2014. Non-Native plant data. Anchorage, AK: University of Alaska Anchorage. http://aknhp.uaa.alaska.edu/botany/akepic/non-native-plant-species- list/#content Arizona Alhagi maurorum Rhus lancea Tamarix parviflora Elaeagnus angustifolia Tamarix aphylla Tamarix ramosissima Euryops multifidus Tamarix chinensis Ulmus pumila Arizona Wildland Invasive Plant Working Group. 2005. Invasive non-native plants that threaten wildlands in Arizona. Phoenix, AZ: Southwest Vegetation Management Association https:// www.swvma.org/wp-content/uploads/Invasive-Non-Native-Plants-that-Threaten-Wildlands-in- Arizona.pdf (Accessed Sept 3.