Ecology Glossary
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Grassland & Shrubland Vegetation
Grassland & Shrubland Vegetation Missoula Draft Resource Management Plan Handout May 2019 Key Points Approximately 3% of BLM-managed lands in the planning area are non-forested (less than 10% canopy cover); the other 97% are dominated by a forested canopy with limited mountain meadows, shrublands, and grasslands. See table 1 on the following page for a break-down of BLM-managed grassland and shrubland in the planning area classified under the National Vegetation Classification System (NVCS). The overall management goal of grassland and shrubland resources is to maintain diverse upland ecological conditions while providing for a variety of multiple uses that are economically and biologically feasible. Alternatives Alternative A (1986 Garnet RMP, as Amended) Maintain, or where practical enhance, site productivity on all public land available for livestock grazing: (a) maintain current vegetative condition in “maintain” and “custodial” category allotments; (b) improve unsatisfactory vegetative conditions by one condition class in certain “improvement” category allotments; (c) prevent noxious weeds from invading new areas; and, (d) limit utilization levels to provide for plant maintenance. Alternatives B & C (common to all) Proposed objectives: Manage uplands to meet health standards and meet or exceed proper functioning condition within site or ecological capability. Where appropriate, fire would be used as a management agent to achieve/maintain disturbance regimes supporting healthy functioning vegetative conditions. Manage surface-disturbing activities in a manner to minimize degradation to rangelands and soil quality. Mange areas to conserve BLM special status species plants. Ensure consistency with achieving or maintaining Standards of Rangeland Health and Guidelines for Livestock Grazing Management for Montana, North Dakota, and South Dakota. -
Perspectives of Forest Ecophysiological Research in the Context of Mediterranean Basin M
Invest Agrar: Sist Recur For (2005) 14(3), 538-549 Perspectives of forest ecophysiological research in the context of Mediterranean Basin M. Fernández* and R. Tapias Departamento de Ciencias Agroforestales. Escuela Politécnica Superior. Huelva University. 21819 Palos de la Frontera. Huelva. Spain Abstract The mediterranean-climate regions are linked to the presence of the unusual global conditions of cool rainy winters and warm dry summers. Thus, the common drought periods, frost nights, summer heat and fires and soil erosion disturb plants life. These regions have a global significance by their floristic richness. Nevertheless, these areas have been more heavily impacted by human activities than almost any other ecosystem. The foreseeable global change will most likely influence plant life, and the Mediterranean Basin will be specially affected (e.g. a decrease in spring and winter rainfalls, an increase in mean annual temperature), affecting the delicate equilibrium of these ecosystems. Ecophysiology is a powerful tool to examine the controlling mechanisms behind the functioning, distribution, abundance, and productivity of forest tree species and their response to a changing environment. This science discipline can help to the forest management by physiological approaches of the response of plant processes to the biotic and abiotic constraints imposed by the environment. Key words: Tree research, forest ecosystems, plant physiological ecology. Resumen Perspectivas en la investigación ecofisiológica forestal en el contexto de la cuenca mediterránea Las regiones de clima mediterráneo se caracterizan por presentar las precipitaciones concentradas en la época fría y veranos secos y calurosos. Ello conduce a la frecuente aparición de períodos de sequía, heladas, altas temperaturas estivales, fuegos forestales y fenómenos de erosión edáfica que afectan la vida de las plantas. -
Plant Ecophysiology – Biology 2210 (Or ES 2223)
Fall, 2019 Plant Ecophysiology – Biology 2210 (or ES 2223) Young Spruces - Rockwell Kent Professor Barry Logan Laboratory Instructor: Jaret Reblin Lecture: MWF: 10:40 – 11:35AM Laboratory: Tu, W or Th: 1:15 – 4:10PM Roux 207 Druckenmiller 222 Barry Logan Jaret Reblin Druckenmiller 220A Druckenmiller 222A 725-3944 725-3166 [email protected] [email protected] Office Hours: Tu. 9:15-10:25AM & W. 4:15-5:15PM M. 11:40 – 12:40PM & Th. 11:00 – 12:00PM (or by appointment) (or by appointment) Prerequisites: Biology 1102, 1109 or recommendation of the Biology Department Fall, 2019 Plant Ecophysiology – Biology 2210 (or ES 2223) Course Description: Examines the functional attributes of plants and the manner in which they vary across the plant kingdom by the processes of evolution and acclimation. Topics of focus include photosynthesis and protection against high-light stress, the acquisition and distribution of water and mineral nutrients, and environmental and hormonal control of development. Special topics discussed may include plant parasitism, carnivory, the origins and present state of agriculture, plant responses to global climate change, plant life in extreme environments, and the impacts of local land-use history on plant communities. Contemporary research instrumentation is used in weekly laboratories, some conducted in the field, to enable first-hand exploration of phenomena discussed in lecture. Inquiry in the Natural Sciences & Mathematical, Computational and Statistical Reasoning requirements: This course can be completed to satisfy either the INS or MCSR Distribution Requirement. This course is dedicated to understanding plant function, distribution and responses to the environment. We will pursue this through lecture; guided problem solving and critical thinking; reading and discussion of journal articles describing original research, review articles & chapters; field excursions; and field/lab exercises designed to offer you opportunities to pursue authentic research using contemporary instrumentation. -
Understanding the Causes of Bush Encroachment in Africa: the Key to Effective Management of Savanna Grasslands
Tropical Grasslands – Forrajes Tropicales (2013) Volume 1, 215−219 Understanding the causes of bush encroachment in Africa: The key to effective management of savanna grasslands OLAOTSWE E. KGOSIKOMA1 AND KABO MOGOTSI2 1Department of Agricultural Research, Ministry of Agriculture, Gaborone, Botswana. www.moa.gov.bw 2Department of Agricultural Research, Ministry of Agriculture, Francistown, Botswana. www.moa.gov.bw Keywords: Rangeland degradation, fire, indigenous ecological knowledge, livestock grazing, rainfall variability. Abstract The increase in biomass and abundance of woody plant species, often thorny or unpalatable, coupled with the suppres- sion of herbaceous plant cover, is a widely recognized form of rangeland degradation. Bush encroachment therefore has the potential to compromise rural livelihoods in Africa, as many depend on the natural resource base. The causes of bush encroachment are not without debate, but fire, herbivory, nutrient availability and rainfall patterns have been shown to be the key determinants of savanna vegetation structure and composition. In this paper, these determinants are discussed, with particular reference to arid and semi-arid environments of Africa. To improve our current under- standing of causes of bush encroachment, an integrated approach, involving ecological and indigenous knowledge systems, is proposed. Only through our knowledge of causes of bush encroachment, both direct and indirect, can better livelihood adjustments be made, or control measures and restoration of savanna ecosystem functioning be realized. Resumen Una forma ampliamente reconocida de degradación de pasturas es el incremento de la abundancia de especies de plan- tas leñosas, a menudo espinosas y no palatables, y de su biomasa, conjuntamente con la pérdida de plantas herbáceas. En África, la invasión por arbustos puede comprometer el sistema de vida rural ya que muchas personas dependen de los recursos naturales básicos. -
(Vell.) Mart. (Mimosaceae) Seeds Subjected to Hypoxia and Anoxia1
Revta brasil. Bot., São Paulo, V.23, n.1, p.51-57, mar. 2000 Ecophysiology and respiratory metabolism during the germination of Inga sessilis (Vell.) Mart. (Mimosaceae) seeds subjected to hypoxia and anoxia1 JANETE MAYUMI OKAMOTO2 and CARLOS ALFREDO JOLY2,3 (received: May 27, 1999; accepted: November 17, 1999) ABSTRACT - (Ecophysiology and respiratory metabolism during the germination of Inga sessilis (Vell.) Mart. (Mimosaceae) seeds subjected to hypoxia and anoxia). This paper presents a study on the respiratory metabolism of germinating seeds of Inga sessilis subjected to normoxia, hypoxia and anoxia. Although it is typical of environments where waterlogging seldom occurs, 40% of its seeds are able to germinate under hypoxia; yet, anoxia periods over 96 h are lethal to the seeds. Ethanol is the main product of the seeds anaerobic metabolism, but the steep increase in lactate after 24 h anoxia or 48 h hypoxia may explain the drop in seed viability. RESUMO - (Ecofisiologia da germinação e metabolismo respiratório de sementes de Inga sessilis (Vell.) Mart. (Mimosaceae) submetidas à hipoxia e anoxia). Os estudos referentes à germinação e ao metabolismo respiratório de sementes de Inga sessilis (Vell.) Mart. submetidas a normoxia, hipoxia e anoxia, mostraram que apesar de ser uma espécie típica de ambientes com solos bem drenados, 40% das sementes germinam sob hipoxia. A anoxia, por outro lado, é letal para as sementes. O etanol é o principal produto do metabolismo anaeróbico das sementes. A perda de viabilidade das sementes parece estar associada ao rápido aumento na concentração de lactato após 24 h de anoxia ou 48 h de hipoxia. -
Mikaël BILI Préparée À L’UMR 1349 « IGEPP » Institut De Génétique, Environnement Et Protection Des Plantes UFR Sciences De La Vie Et De L’Environnement
ANNÉE 2014 THÈSE / UNIVERSITÉ DE RENNES 1 sous le sceau de l’Université Européenne de Bretagne pour le grade de DOCTEUR DE L’UNIVERSITÉ DE RENNES 1 Mention : Biologie Ecole doctorale Vie – Agro – Santé présentée par Mikaël BILI Préparée à l’UMR 1349 « IGEPP » Institut de Génétique, Environnement et Protection des Plantes UFR Sciences de la Vie et de l’Environnement Eléments de Thèse soutenue à Rennes le18 décembre 2014 différenciation de la devant le jury composé de : Didier BOUCHON niche écologique chez Professeur, Université de Poitiers/rapporteur deux coléoptères Emmanuel DESOUHANT Professeur,Université de Lyon 1 / rapporteur parasitoïdes en Geneviève PREVOST Professeur,Université Picardie Jules Verne / compétition : examinateur Cécile LE LANN Maître de Conférences,Université de Rennes 1/ comportement et examinateur communautés Denis POINSOT Maître de Conférences,Université de Rennes 1/ directeur de thèse bactériennes. Anne Marie CORTESERO Professeur, Université de Rennes 1 / co-directrice de thèse Remerciements Après trois années en thèse, comme tout doctorant, il y a un grand nombre de personnes que j'aimerais remercier tant au sein de l'UMR IGEPP que parmi les gens qui m'épaulent (i. e. "me supportent") depuis plus longtemps. Mais tout d’abord je tiens à remercier sincèrement Didier Bouchon, Emmanuel Desouhant, Geneviève Prevost et Cécile Le Lann pour avoir accepté sans hésiter de prendre le temps et de se déplacer à Rennes (avec plus ou moins de difficultés) afin de juger ce travail. Votre intérêt et vos questions m’ont permis de savourer pleinement la défense de cette thèse. Je n'oublierai pas mes encadrants, Denis Poinsot et Anne Marie Cortesero. -
Human Alteration of the Global Nitrogen Cycle
What is Nitrogen? Human Alteration of the Nitrogen is the most abundant element in Global Nitrogen Cycle the Earth’s atmosphere. Nitrogen makes up 78% of the troposphere. Nitrogen cannot be absorbed directly by the plants and animals until it is converted into compounds they can use. This process is called the Nitrogen Cycle. Heather McGraw, Mandy Williams, Suzanne Heinzel, and Cristen Whorl, Give SIUE Permission to Put Our Presentation on E-reserve at Lovejoy Library. The Nitrogen Cycle How does the nitrogen cycle work? Step 1- Nitrogen Fixation- Special bacteria convert the nitrogen gas (N2 ) to ammonia (NH3) which the plants can use. Step 2- Nitrification- Nitrification is the process which converts the ammonia into nitrite ions which the plants can take in as nutrients. Step 3- Ammonification- After all of the living organisms have used the nitrogen, decomposer bacteria convert the nitrogen-rich waste compounds into simpler ones. Step 4- Denitrification- Denitrification is the final step in which other bacteria convert the simple nitrogen compounds back into nitrogen gas (N2 ), which is then released back into the atmosphere to begin the cycle again. How does human intervention affect the nitrogen cycle? Nitric Oxide (NO) is released into the atmosphere when any type of fuel is burned. This includes byproducts of internal combustion engines. Production and Use of Nitrous Oxide (N2O) is released into the atmosphere through Nitrogen Fertilizers bacteria in livestock waste and commercial fertilizers applied to the soil. Removing nitrogen from the Earth’s crust and soil when we mine nitrogen-rich mineral deposits. Discharge of municipal sewage adds nitrogen compounds to aquatic ecosystems which disrupts the ecosystem and kills fish. -
Nitrogen Removal Training Program
Nitrogen Removal Training Program Module 1 Nitrogen in the Aquatic Environment • Forms of Nitrogen and Nitrogen Transformations • Nitrogen in Surface Waters • Water Quality Impacts of Nitrogen Discharges • Nitrogen in Wastewater Module 1 Transparency 1 Nitrogen Removal Training Program Module 1 Forms of Nitrogen and Nitrogen Transformations Module 1 Transparency 2 Forms of Nitrogen in the Environment Unoxidized Forms Oxidized Forms of Nitrogen of Nitrogen Nitrite (NO -) • Nitrogen Gas (N2) • 2 + Nitrate (NO -) • Ammonia (NH4 , NH3) • 3 • Organic Nitrogen (urea, • Nitrous Oxide (N2O) amino acids, peptides, proteins, etc...) • Nitric Oxide (NO) • Nitrogen Dioxide (NO2) Module 1 Transparency 3 Nitrogen Fixation • Biological Fixation - Use of atmospheric nitrogen by certain photosynthetic blue-green algae and bacteria for growth. Nitrogen Gas Organic Nitrogen (N2) • Lightning Fixation - Conversion of atmospheric nitrogen to nitrate by lightning. lightning Nitrogen Gas + Ozone Nitrate - (N2) (O3)(NO3 ) • Industrial Fixation - Conversion of nitrogen gas to ammonia and nitrate-nitrogen (used in the manufacture of fertilizers and explosives). Module 1 Transparency 4 Biological Nitrogen Fixation Nitrogen Gas (N2) Bacteria Blue-green Algae Organic N Organic N Certain blue-green algae and bacteria use atmospheric nitrogen to produce organic nitrogen compounds. Module 1 Transparency 5 Atmospheric Fixation Lightning converts Nitrogen Gas and Ozone to Nitrate. Nitrogen Gas Nitrate Module 1 Transparency 6 Industrial Fixation N2 Nitrogen gas is converted to ammonia and nitrate in the production of fertilizer and explosives. NH3 - NO3 Module 1 Transparency 7 Ammonification and Assimilation Ammonification - Conversion of organic nitrogen to ammonia-nitrogen resulting from the biological decomposition of dead plant and animal tissue and animal fecal matter. -
Acclimatization of Aquatic Organisms in Culture - Gilles Boeuf
FISHERIES AND AQUACULTURE – Vol. IV – Acclimatization of Aquatic Organisms in Culture - Gilles Boeuf ACCLIMATIZATION OF AQUATIC ORGANISMS IN CULTURE Gilles Bœuf Laboratoire Arago, Université Pierre et Marie Curie, BP 44, 66650 Banyuls-sur-mer and Muséum National d’Histoire Naturelle, 57 rue Cuvier, 75005 Paris, France. Keywords: aquaculture, acclimatization, mollusc, shrimp, fish, environmental factors, temperature, salinity, light, oxygen, intensive culture, extensive culture. Contents 1. Introduction 2. Biological characteristics of aquatic species 2.1. They live and breathe in water 2.1.1. Stabilization and movements 2.1.2. Respiration and excretion 2.1.3. Salinity and light 2.2. They do not control their internal temperature 2.3. They often are "carnivorous" 3. From the wild to domestication 3.1. Rearing based on juvenile or breeder capture from the wild 3.1.1. Capture of juveniles 3.1.2. Capture of wild breeders 3.2. Juvenile releases into the wild 3.3. Entire completion of rearing cycle 4. Conclusions Acknowledgements Glossary Bibliography Biographical Sketch Summary Human introduced many aquatic species in culture for a long time, essentially mollusks, shrimps and fishes. These animals live and breathe in water and face very specific situations,UNESCO compared to terrestrial species –. DifferentEOLSS environmental factors such as salinity, light, very variable oxygen content or presence of ammonia involve particular capabilities of adaptation. SAMPLE CHAPTERS They do not control their internal temperature and this raises very particular questions, compared to "commonly-reared" birds and mammals. Moreover, very often, some of them are "carnivorous". All these facts influence the type of rearing techniques usable to produce them and though, the level of acclimatization in culture. -
Insect Cold-Hardiness: to Freeze Or Not to Freeze Richard E. Lee, Jr. Bioscience, Vol. 39, No. 5
Insect Cold-Hardiness: To Freeze or Not to Freeze Richard E. Lee, Jr. BioScience, Vol. 39, No. 5. (May, 1989), pp. 308-313. Stable URL: http://links.jstor.org/sici?sici=0006-3568%28198905%2939%3A5%3C308%3AICTFON%3E2.0.CO%3B2-8 BioScience is currently published by American Institute of Biological Sciences. Your use of the JSTOR archive indicates your acceptance of JSTOR's Terms and Conditions of Use, available at http://www.jstor.org/about/terms.html. JSTOR's Terms and Conditions of Use provides, in part, that unless you have obtained prior permission, you may not download an entire issue of a journal or multiple copies of articles, and you may use content in the JSTOR archive only for your personal, non-commercial use. Please contact the publisher regarding any further use of this work. Publisher contact information may be obtained at http://www.jstor.org/journals/aibs.html. Each copy of any part of a JSTOR transmission must contain the same copyright notice that appears on the screen or printed page of such transmission. The JSTOR Archive is a trusted digital repository providing for long-term preservation and access to leading academic journals and scholarly literature from around the world. The Archive is supported by libraries, scholarly societies, publishers, and foundations. It is an initiative of JSTOR, a not-for-profit organization with a mission to help the scholarly community take advantage of advances in technology. For more information regarding JSTOR, please contact [email protected]. http://www.jstor.org Tue Jan 8 14:40:48 2008 Insect Cold-hardiness: To Freeze or Not to Freeze How insects survive low temperatures by Richard E. -
1 Behavioral Ecology and the Transition from Hunting and Gathering to Agriculture
GRBQ084-2272G-C01[01-21]. qxd 11/30/05 7:43 PM Page 1 pinnacle Quark11:JOBS:BOOKS:REPRO: 1 Behavioral Ecology and the Transition from Hunting and Gathering to Agriculture Bruce Winterhalder and Douglas J. Kennett he volume before you is the first THE SIGNIFICANCE OF THE TRANSITION T systematic, comparative attempt to use the concepts and models of behavioral ecology There are older transformations of comparable to address the evolutionary transition from so- magnitude in hominid history; bipedalism, en- cieties relying predominantly on hunting and cephalization, early stone tool manufacture, gathering to those dependent on food produc- and the origins of language come to mind (see tion through plant cultivation, animal hus- Klein 1999). The evolution of food production bandry, and the use of domesticated species is on a par with these, and somewhat more ac- embedded in systems of agriculture. Human cessible because it occurred in near prehistory, behavioral ecology (HBE; Winterhalder and the last eight thousand to thirteen thousand Smith 2000) is not new to prehistoric analy- years; agriculture also is inescapable for its im- sis; there is a two-decade tradition of applying mense impact on the human and non-human models and concepts from HBE to research worlds (Dincauze 2000; Redman 1999). Most on prehistoric hunter-gatherer societies (Bird problems of population and environmental and O’Connell 2003). Behavioral ecology degradation are rooted in agricultural origins. models also have been applied in the study of The future of humankind depends on making adaptation among agricultural (Goland 1993b; the agricultural “revolution” sustainable by pre- Keegan 1986) and pastoral (Mace 1993a) pop- serving cultigen diversity and mitigating the ulations. -
Ectomycorrhizal Fungal Communities at Forest Edges 93, 244–255 IAN A
Journal of Blackwell Publishing, Ltd. Ecology 2005 Ectomycorrhizal fungal communities at forest edges 93, 244–255 IAN A. DICKIE and PETER B. REICH Department of Forest Resources, University of Minnesota, St Paul, MN, USA Summary 1 Ectomycorrhizal fungi are spatially associated with established ectomycorrhizal vegetation, but the influence of distance from established vegetation on the presence, abundance, diversity and community composition of fungi is not well understood. 2 We examined mycorrhizal communities in two abandoned agricultural fields in Minnesota, USA, using Quercus macrocarpa seedlings as an in situ bioassay for ecto- mycorrhizal fungi from 0 to 20 m distance from the forest edge. 3 There were marked effects of distance on all aspects of fungal communities. The abundance of mycorrhiza was uniformly high near trees, declined rapidly around 15 m from the base of trees and was uniformly low at 20 m. All seedlings between 0 and 8 m distance from forest edges were ectomycorrhizal, but many seedlings at 16–20 m were uninfected in one of the two years of the study. Species richness of fungi also declined with distance from trees. 4 Different species of fungi were found at different distances from the edge. ‘Rare’ species (found only once or twice) dominated the community at 0 m, Russula spp. were dominants from 4 to 12 m, and Astraeus sp. and a Pezizalean fungus were abundant at 12 m to 20 m. Cenococcum geophilum, the most dominant species found, was abundant both near trees and distant from trees, with lowest relative abundance at intermediate distances. 5 Our data suggest that seedlings germinating at some distance from established ecto- mycorrhizal vegetation (15.5 m in the present study) have low levels of infection, at least in the first year of growth.