Bio-Geochemical Cycles with Special Reference to Carbon Dioxide and Nitrogen Semester : IV (CBCS) Paper: 10 Unit: II Topic: 10
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Biogeochemistry of Mediterranean Wetlands: a Review About the Effects of Water-Level Fluctuations on Phosphorus Cycling and Greenhouse Gas Emissions
water Review Biogeochemistry of Mediterranean Wetlands: A Review about the Effects of Water-Level Fluctuations on Phosphorus Cycling and Greenhouse Gas Emissions Inmaculada de Vicente 1,2 1 Departamento de Ecología, Universidad de Granada, 18071 Granada, Spain; [email protected]; Tel.: +34-95-824-9768 2 Instituto del Agua, Universidad de Granada, 18071 Granada, Spain Abstract: Although Mediterranean wetlands are characterized by extreme natural water level fluctu- ations in response to irregular precipitation patterns, global climate change is expected to amplify this pattern by shortening precipitation seasons and increasing the incidence of summer droughts in this area. As a consequence, a part of the lake sediment will be exposed to air-drying in dry years when the water table becomes low. This periodic sediment exposure to dry/wet cycles will likely affect biogeochemical processes. Unexpectedly, to date, few studies are focused on assessing the effects of water level fluctuations on the biogeochemistry of these ecosystems. In this review, we investigate the potential impacts of water level fluctuations on phosphorus dynamics and on greenhouse gases emissions in Mediterranean wetlands. Major drivers of global change, and specially water level fluctuations, will lead to the degradation of water quality in Mediterranean wetlands by increasing the availability of phosphorus concentration in the water column upon rewetting of dry sediment. CO2 fluxes are likely to be enhanced during desiccation, while inundation is likely to decrease cumulative CO emissions, as well as N O emissions, although increasing CH emissions. Citation: de Vicente, I. 2 2 4 Biogeochemistry of Mediterranean However, there exists a complete gap of knowledge about the net effect of water level fluctuations Wetlands: A Review about the Effects induced by global change on greenhouse gases emission. -
The Global Marine Phosphorus Cycle: Sensitivity to Oceanic Circulation
Biogeosciences, 4, 155–171, 2007 www.biogeosciences.net/4/155/2007/ Biogeosciences © Author(s) 2007. This work is licensed under a Creative Commons License. The global marine phosphorus cycle: sensitivity to oceanic circulation C. P. Slomp and P. Van Cappellen Department of Earth Sciences – Geochemistry, Faculty of Geosciences, Utrecht University, P.O. Box 80021, 3508 TA Utrecht, The Netherlands Received: 4 September 2006 – Published in Biogeosciences Discuss.: 5 October 2006 Revised: 8 January 2007 – Accepted: 20 February 2007 – Published: 22 February 2007 Abstract. A new mass balance model for the coupled ma- stand long-term variations in marine biological activity, at- rine cycles of phosphorus (P) and carbon (C) is used to ex- mospheric composition and climate (Holland, 1984; Van amine the relationships between oceanic circulation, primary Cappellen and Ingall, 1996; Petsch and Berner, 1998; Bjer- productivity, and sedimentary burial of reactive P and partic- rum and Canfield, 2002). Important forcings include the sup- ulate organic C (POC), on geological time scales. The model ply of reactive P from the continents, oceanic circulation and explicitly represents the exchanges of water and particulate sea level fluctuations (Follmi,¨ 1996; Compton et al., 2000; matter between the continental shelves and the open ocean, Handoh and Lenton, 2003; Wallmann, 2003; Bjerrum et al., and it accounts for the redox-dependent burial of POC and 2006). the various forms of reactive P (iron(III)-bound P, particu- Upward transport of nutrient-rich water sustains biologi- late organic P (POP), authigenic calcium phosphate, and fish cal activity in marine surface waters. Vertical mixing, how- debris). Steady state and transient simulations indicate that ever, also controls the ventilation of the deeper ocean waters, a slowing down of global ocean circulation decreases pri- which in turn has a major effect on the sedimentary burial mary production in the open ocean, but increases that in the of phosphorus. -
Modeling Biogeochemical Cycles
4 Modeling Biogeochemical Cycles Henning Rodhe 4.1 Introductory Remarks spatial average (i.e., the physical size of the reservoir itself) often has a horizontal size To formulate a model is to put together pieces of approaching that of a continent, or larger, i.e., knowledge about a particular system into a > 1000 km. The time scales corresponding to this consistent pattern that can form the basis for (1) spatial average are months, or longer. This interpretation of the past history of the system means that day-to-day variations in weather and (2) prediction of the future of the system. To and ocean currents are not generally considered be credible and useful, any model of a physical, explicitly when modeling biogeochemical cycles. chemical or biological system must rely on both The advent of fast computers and the avail- scientific fundamentals and observations of the ability of detailed data on the occurrence of world around us. High-quality observational certain chemical species have made it possible data are the basis upon which our understand- to construct meaningful cycle models with a ing of the environment rests. However, observa- much smaller and faster spatial and temporal tions themselves are not very useful unless the resolution. These spatial and time scales corre- results can be interpreted in some kind of model. spond to those in weather forecast models, i.e. Thus observations and modeling go hand in down to 100 km and 1 h. Transport processes hand. (e.g., for CO2 and sulfur compounds) in the This chapter focuses on types of models used oceans and atmosphere can be explicitly to describe the functioning of biogeochemical described in such models. -
Earth Systems and Interactions
The Earth System Earth Systems and Interactions Key Concepts • How do Earth systems What do you think? Read the three statements below and decide interact in the carbon whether you agree or disagree with them. Place an A in the Before column cycle? if you agree with the statement or a D if you disagree. After you’ve read • How do Earth systems this lesson, reread the statements to see if you have changed your mind. interact in the phosphorus Before Statement After cycle? 1. The amount of water on Earth remains constant over time. 2. Hydrogen makes up the hydrosphere. 3. Most carbon on Earth is in the atmosphere. 3TUDY#OACH Earth Systems Make a Table Contrast the carbon cycle and the Your body contains many systems. These systems work phosphorus cycle in a two- together and make one big system—your body. Earth is a column table. Label one system, too. Like you, Earth has smaller systems that work column Carbon Cycle and together, or interact, and make the larger Earth system. Four the other column Phosphorus of these smaller systems are the atmosphere, the Cycle. Complete the table hydrosphere, the geosphere, and the biosphere. as you read this lesson. The Atmosphere Reading Check The outermost Earth system is a mixture of gases and 1. Identify What systems particles of matter called the atmosphere. It forms a layer make up the larger Earth around the other Earth systems. The atmosphere is mainly system? nitrogen and oxygen. Gases in the atmosphere move freely, helping transport matter and energy among Earth systems. -
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 Metabolism in Phytoplankton - Y
MARINE ECOLOGY – Nitrogen Metabolism in Phytoplankton - Y. Collos, J. A. Berges NITROGEN METABOLISM IN PHYTOPLANKTON Y. Collos Laboratoire d'Hydrobiologie CNRS, Université Montpellier II, France J. A. Berges School of Biology and Biochemistry, Queen's University of Belfast, UK Keywords: uptake, reduction, excretion, proteases, chlorophyllases, cell death. Contents 1. Introduction 2. Availability and use of different forms of nitrogen 2.1 Nitrate 2.2. Nitrite 2.3. Ammonium 2.4. Molecular N2 2.5. Dissolved organic N (DON) 2.6. Particulate nitrogen (PN) 3. Assimilation pathways 4. Accumulation and storage 4.1. Inorganic compounds 4.2. Organic compounds 5. Nutrient classification and preferences 6. Plasticity in cell composition 7. Overflow mechanisms: excretion and release processes 8. Recycling of N within the cell 9. Degradation pathways 9.1. Requirements for and roles of degradation 9.2. How is degradation accomplished? 9.3. Variation in degradation 9.4. Pathogenesis and Cell Death 10. From uptake to growth: time-lag phenomena 11. Relationships with carbon metabolism 12. Future directions AcknowledgementsUNESCO – EOLSS Glossary Bibliography SAMPLE CHAPTERS Biographical Sketches Summary Phytoplankton use a large variety of nitrogen compounds and are extremely well adapted to fluctuating environmental conditions by a high capacity to change their chemical composition.Degradation and turnover of nitrogen within phytoplankton is essential for many processes including normal cell maintenance, acclimations to changes in light, salinity, and nutrients, and cell defence against pathogens. The ©Encyclopedia of Life Support Systems (EOLSS) MARINE ECOLOGY – Nitrogen Metabolism in Phytoplankton - Y. Collos, J. A. Berges pathways by which N degradation is accomplished are very poorly understood, but based on work in higher plant species, protein degradation is likely to be of central importance. -
Effects of Fertilisation on Phosphorus Pools in the Volcanic Soil of a Managed Tropical Forest
Forest Ecology and Management 258 (2009) 2199–2206 Contents lists available at ScienceDirect Forest Ecology and Management journal homepage: www.elsevier.com/locate/foreco Effects of fertilisation on phosphorus pools in the volcanic soil of a managed tropical forest Dean F. Meason a,*, Travis W. Idol a, J.B. Friday a, Paul G. Scowcroft b a Department of Natural Resources and Environmental Management, College of Tropical Agriculture and Human Resources, Sherman Laboratory, University of Hawaii, 1910 East West Road, Honolulu, HI 96822, USA b Institute of Pacific Islands Forestry, Pacific Southwest Research Station, USDA Forest Service, 60 Nowelo Street, Hilo, HI 96720, USA ARTICLE INFO ABSTRACT Article history: Acacia koa forests benefit from phosphorus fertilisation, but it is unknown if fertilisation is a short or long Received 31 July 2008 term effect on P availability. Past research suggests that P cycling in soils with high P sorption capacity, Received in revised form 30 March 2009 such as Andisols, was through organic pathways. We studied leaf P and soil P fractions in a tropical forest Accepted 2 April 2009 Andisol for 3 years after fertilisation with triple super phosphate. Leaf P concentration and labile P remained high after fertilisation. Fertilisation had increased all the inorganic P fractions over the length Keywords: of the study, while organic P fractions had not. The results suggested that the organic P fractions had a Hedley fractionation reduced role as a source of labile P after fertilisation. The size and dynamics of the sodium hydroxide- and Phosphorus fertilization hydrochloric acid-extractable P pools would suggest that either pool could be major sources of labile P. -
Human Alteration of the Global Nitrogen Cycle: Causes And
Published by the Ecological Society of America Number 1, Spring 1997 Causes andConsequences Human Alterationofthe Issues in EcologyGlobal NitrogenCycle: Photo by Nadine Cavender Issues in Ecology Number 1 Spring 1997 Human Alteration of the Global Nitrogen Cycle: Causes and Consequences SUMMARY Human activities are greatly increasing the amount of nitrogen cycling between the living world and the soil, water, and atmosphere. In fact, humans have already doubled the rate of nitrogen entering the land-based nitrogen cycle, and that rate is continuing to climb. This human-driven global change is having serious impacts on ecosystems around the world because nitrogen is essential to living organisms and its availability plays a crucial role in the organization and functioning of the worlds ecosystems. In many ecosystems on land and sea, the supply of nitrogen is a key factor controlling the nature and diversity of plant life, the population dynamics of both grazing animals and their predators, and vital ecologi- cal processes such as plant productivity and the cycling of carbon and soil minerals. This is true not only in wild or unmanaged systems but in most croplands and forestry plantations as well. Excessive nitrogen additions can pollute ecosystems and alter both their ecological functioning and the living communities they support. Most of the human activities responsible for the increase in global nitrogen are local in scale, from the production and use of nitrogen fertilizers to the burning of fossil fuels in automobiles, power generation plants, and industries. However, human activities have not only increased the supply but enhanced the global movement of various forms of nitrogen through air and water. -
Carbon–Nitrogen Interactions in Idealized Simulations with JSBACH (Version 3.10)
Geosci. Model Dev., 10, 2009–2030, 2017 www.geosci-model-dev.net/10/2009/2017/ doi:10.5194/gmd-10-2009-2017 © Author(s) 2017. CC Attribution 3.0 License. Carbon–nitrogen interactions in idealized simulations with JSBACH (version 3.10) Daniel S. Goll1,a, Alexander J. Winkler2,3, Thomas Raddatz2, Ning Dong3,5, Ian Colin Prentice4,6, Philippe Ciais1, and Victor Brovkin2 1Le Laboratoire des Sciences du Climat et de l’Environnement, IPSL-LSCE CEA/CNRS/UVSQ Saclay, Gif sur Yvette, France 2Max Planck Institute for Meteorology, Hamburg, Germany 3International Max Planck Research School on Earth System Modeling, Hamburg, Germany 4Department of Biological Sciences, Macquarie University, North Ryde, NSW 2109, Australia 5Faculty of Agriculture and Environment, Department of Environmental Sciences, University of Sydney, NSW 2006, Australia 6AXA Chair in Biosphere and Climate Impacts, Department of Life Sciences, Imperial College London, Silwood Park Campus, Buckhurst Road, Ascot SL5 7PY, UK aformerly at: Max Planck Institute for Meteorology, Hamburg, Germany Correspondence to: Daniel S. Goll ([email protected]) Received: 17 December 2016 – Discussion started: 9 January 2017 Revised: 7 April 2017 – Accepted: 14 April 2017 – Published: 22 May 2017 Abstract. Recent advances in the representation of soil car- The strengths of the land carbon feedbacks of the re- −1 bon decomposition and carbon–nitrogen interactions imple- cent version of JSBACH, with βL D 0:61 Pgppm and γL D mented previously into separate versions of the land sur- −27:5 Pg ◦C−1, are 34 and 53 % less than the averages of face scheme JSBACH are here combined in a single version, CMIP5 models, although the CMIP5 version of JSBACH which is set to be used in the upcoming 6th phase of coupled simulated βL and γL, which are 59 and 42 % higher than model intercomparison project (CMIP6). -
Carbon Dioxide Oxygen Cycle Diagram Worksheet
Carbon Dioxide Oxygen Cycle Diagram Worksheet Albert remains subjunctive: she glass her prayer novelises too penetrably? Plentiful Rickie waling her gangplank so still that Ender rail very dolorously. Puffingly needed, Dominic sleeved half-pike and cooperate epicenter. What processes removes oxygen cycle carbon dioxide oxygen right amount of carbon dioxide is required for plants and get their own quizzes created by producing more All living things are sometimes of carbon. Carbon Dioxide Oxygen Cycle Worksheet. Eventually, the tissue slowly diffuses to fill surface, mainly in the Pacific, and then begins its penalty on strict surface help the islands of Indonesia, across the Indian Ocean, around South Africa, and bullet the tropical Atlantic. Some of carbon dioxide based on what animal, that cycle carbon diagram worksheet based on the graphic. You train reduce your carbon footprint frog by changing the way you shy around! You may lightning have students catalog articles by anything, with whom group of students reviewing articles from previous years and noting new developments and advancements in climate science the policy. Which open the following processes removes carbon dioxide from the atmosphere? It down the wide common element of subsequent human body. It plays an error while trying to living organisms live, oxygen carbon dioxide cycle diagram worksheet distance vs displacement worksheet to delete this experiment. Trees that oxygen when crops or comments or cool your worksheet. Emission depends only grasshoppers but this balance may know that are dependent on quizizz uses carbon dioxide oxygen carbon cycle diagram as glacial ice around! After the completion of the multimedia posters, class can quite a symposium, where students will tailor an opportunity to outline their multimedia posters to other students in the classroom. -
Biogeochemistry of Wetlands Nitrogen
Institute of Food and Agricultural Sciences (IFAS) Biogeochemistry of Wetlands SiScience an dAd App litilications NITROGEN Wetland Biogeochemistry Laboratory Soil and Water Science Department University of Florida Instructor : Patrick Inglett [email protected] 6/22/20086/22/2008 P.W.WBL Inglett1 1 Nitrogen Introduction N Forms, Distribution, Importance Basic processes of N Cycles Examples of current research Examples of applications Key points learned 6/22/2008 P.W. Inglett 2 1 Nitrogen Learning Objectives Identify the forms of N in wetlands Understand the importance of N in wetlands/global processes Define the major N processes/transformations Understand the importance of microbial activity in N transformations Understand the potential regulators of N processes See the application of N cycle principles to understanding natural and man-made ecosystems 6/22/2008 P.W. Inglett 3 Nitrogen Cycling Plant biomass N N2 NH3 N2 N2O (g) Litterfall Nitrogen Fixation Volatilization Mineralization. Water - Nitrification + + NO3 NH4 Organic N NH4 Column AEROBIC - Plant Peat NO3 + + [NH4 ]s uptake accretion [NH4 ]s Denitrification ANAEROBIC Microbial + Organic N Biomass N Adsorbed NH4 N2, N2O (g) 6/22/2008 P.W. Inglett 4 2 Forms of Nitrogen Organic Nitrogen Inorganic Nitrogen + • Proteins • Ammonium (NH4 ) - • Amino Sugars • Nitrate N (NO3 ) - • Nucleic Acids • Nitrite N (NO2 ) • Urea • Nitrous ox ide (N2O) • Dinitrogen (N2) 6/22/2008 P.W. Inglett 5 N Transformations Solid Gaseous Phase: Phase: Particulate N N2 + Bound: NH4 N2O - - NO3 NO2 Aqueous Phase: + NH4 DON - DIN NO3 - Particulate N NO2 6/22/2008 P.W. Inglett 6 3 Reservoirs of Nitrogen Lithosphere 163,600 x 1018 g Atmosphere 3,860 x 1018 g Hydrosphere 23 x 1018 g Biosphere 0.28 x 1018 g 6/22/2008 P.W. -
Flows and Human Interferences
P1: FXZ/VEN October 16, 2000 12:3 Annual Reviews AR118-03 Annu. Rev. Energy Environ. 2000. 25:53–88 Copyright c 2000 by Annual Reviews. All rights reserved PHOSPHORUS IN THE ENVIRONMENT: Natural Flows and Human Interferences Vaclav Smil Department of Geography, University of Manitoba, Winnipeg, Manitoba R3T 2N2 Canada; e-mail: [email protected] Key Words biogeochemical cycling, phosphates, fertilizers, eutrophication ■ Abstract Phosphorus has a number of indispensable biochemical roles, but it does not have a rapid global cycle akin to the circulations of C or N. Natural mobilization of the element, a part of the grand geotectonic denudation-uplift cycle, is slow, and low solubility of phosphates and their rapid transformation to insoluble forms make the element commonly the growth-limiting nutrient, particularly in aquatic ecosystems. Human activities have intensified releases of P.By the year 2000 the global mobilization of the nutrient has roughly tripled compared to its natural flows: Increased soil erosion and runoff from fields, recycling of crop residues and manures, discharges of urban and industrial wastes, and above all, applications of inorganic fertilizers (15 million tonnes P/year) are the major causes of this increase. Global food production is now highly dependent on the continuing use of phosphates, which account for 50–60% of all P supply; although crops use the nutrient with relatively high efficiency, lost P that reaches water is commonly the main cause of eutrophication. This undesirable process affects fresh and ocean waters in many parts of the world. More efficient fertilization can lower nonpoint P losses. Although P in sewage can be effectively controlled, such measures are often not taken, and elevated P is common in treated wastewater whose N was lowered by denitrification.