The Iron Cycle (Fe), Also Known As the Ferrous Wheel, Is the Biogeochemical Cycle of Iron Through the Atmosphere, Hydrosphere, Biosphere and Lithosphere

Total Page:16

File Type:pdf, Size:1020Kb

The Iron Cycle (Fe), Also Known As the Ferrous Wheel, Is the Biogeochemical Cycle of Iron Through the Atmosphere, Hydrosphere, Biosphere and Lithosphere CLASS NOTES FOR SEMESTER –IV STUDENTS, Date- 6.5.2020 Dr. Harekrishna Jana Assistant Professor Dept. Of Microbiology Raja N.L.Khan Women’s College B.Sc (HONOURS) MICROBIOLOGY (CBCS STRUCTURE) C-9: ENVIRONMENTAL MICROBIOLOGY (THEORY) SEMESTER –IV Unit 3 Biogeochemical Cycling No. of Hours: 12 Elemental cycles: Iron and manganese Q. What is Iron cycle? Write the importance of Iron Cycle. Ans. Defination: The iron cycle (Fe), also known as the Ferrous Wheel, is the biogeochemical cycle of iron through the atmosphere, hydrosphere, biosphere and lithosphere. While Fe is highly abundant in the Earth's crust, it is less common in oxygenated surface waters. Iron is a key micronutrient in primary productivity, and a limiting nutrient for the growth of plants and animal. Importance: 1. Iron (Fe) follows a geochemical cycle like many other nutrients. Iron is typically released into the soil or into the ocean through the weathering of rocks or through volcanic eruptions. Iron is required to produce chlorophyl, and plants require sufficient iron to perform photosynthesis. 2. Iron is the most abundant element on Eaith and the most frequently utilized transition metal in the biosphere. It is a component of many ceIlular compounds and is involved in numerous physiological functions. Hence, iron is an essential micronutrient for all eukaryotes and the majority of prokaryotes. Prokaryotes that need iron for biosynthesis require micromolar concentrations, levels that are often not available in neutral pH oxic environments. Therefore, prokaryotes have evolved specific acquisition molecules, called siderophores, to increase iron bioavailability. Q. Draw the Iron Cycle and briefly describe the Iron Cycle. Fig-1 Fig-2 Description of Iron Cycle: On our planet, iron Is ubiquitousi n the hydrosphere,li thosphere,b iospherea nd atmosphere, either as particulate ferric [Fe(ill)] or ferrous [Fe(ll)] iron-bearing minerals or as dissolved ions. Redox transformations of iron, as weIl as dissolution and precipitation and thus mobilization and redistribution, are caused by chemical and to--a significant extent by microbial processes (Fig. 1). Microorganisms catalyze the oxidation of Fe(ll) under oxic or anoxic conditions as weIl as the reduction of Fe(ill) in anoxic habitats. Microbially infiuenced transformations of iron are orten much raster than the respective chemical reactions. They take place in most soils and sediments, both in freshwater and marine environments,-and play an important role in other (bio ) geochemical cycles, in particular in the carbon cycie. Iron exists in a range of oxidation states from -2 to +7; however, on Earth it is predominantly in its +2 or +3 redox state and is a primary redox-active metal on Earth. The cycling of iron between its +2 and +3 oxidation states is referred to as the iron cycle. This process can be entirely abiotic or facilitated by microorganisms, especially iron-oxidizing bacteria. The abiotic processes include the rusting of iron-bearing metals, where Fe2+ is abiotically oxidized to Fe3+ in the presence of oxygen, and the reduction of Fe3+ to Fe2+ by iron-sulfide minerals. The biological cycling of Fe2+ is done by iron oxidizing and reducing microbes. Iron is an essential micronutrient for almost every life form. It is a key component of hemoglobin, important to nitrogen fixation as part of the Nitrogenase enzyme family, and as part of the iron-sulfur core of ferredoxin it facilitates electron transport in chloroplasts, eukaryotic mitochondria, and bacteria. Due to the high reactivity of Fe2+ with oxygen and low solubility of Fe3+, iron is a limiting nutrient in most regions of the world. The ferrous form of iron, Fe2+, is dominant in the Earth's mantle, core, or deep crust. The ferric form, Fe3+, is more stable in the presence of oxygen gas. Dust is a key component in the Earth's iron cycle. Chemical and biological weathering break down iron-bearing minerals, releasing the nutrient into the atmosphere. Changes in hydrological cycle and vegetative cover impact these patterns and have a large impact on global dust production, with dust deposition estimates ranging between 1000 and 2000 Tg/year. Aeolian dust is a critical part of the iron cycle by transporting iron particulates from the Earth's land via the atmosphere to the ocean. Q. Draw and describe the Manganese cycle. Fig-1 Microorganisms have long been known to mediate manganese (Mn) oxidation in a variety of environments, including caves (fig-1). Microbial Mn oxide minerals are typically dark brown to black in color, nm-scale, and poorly crystalline, with birnessite (layer) or todorokite (tunnel) crystal structures. Both bacteria and fungi produce Mn oxide minerals, although the exact mechanism for Mn oxidation remains elusive. Chemolithoautotrophic Mn oxidation is highly unlikely to be carried out with the enzymes currently known, although indirect oxidation of Mn during heterotrophic growth or reproduction has been observed in both bacteria and fungi. Differences in nutrient availability in caves influence not only the microbial community structure associated with ferromanganese deposits, but also Mn cycling and microbial functions. Q.3. Draw and describe the couple iron- Manganese cycle. Fig-1 Fig.2 Description: Mn can precipitate at high pH, lowering Mn availability so deficiencies are most likely to occur in high pH soils (calcareous soils or over-limed soils). Manganese is most available at soil pH levels of 5 to 6.5. The transformations of iron and manganese in nature and the relationship between the cycling of these and other biologically active elements occurs. Both the oxidation and the reduction of iron and manganese in natural environments is, to a large extent, promoted by microbial catalysis, but abiotic transformations are also important and may compete with the biological processes. In the Earth's crust, iron and manganese are mainly found as minor components of rock-forming silicate minerals such as olivine, pyroxenes, and amphiboles. Iron has a high abundance of 4.3% by mass in the continental crust. At a 50-fold lower crustal abundance than iron, manganese is the second most abundant redox-active metal. There are many similarities between iron and manganese in terms of both geochemistry and microbiology. Microbes play an important role in the oxidation of reduced iron and manganese. Dissimilatory iron- and manganese-reducing microorganisms catalyze the reduction of Fe (III) to Fe (II), and of Mn (III) or Mn (IV) to Mn(II). The microbial manganese and iron reduction also occur in aquatic environments. Three basic conditions—absence of oxygen and presence of electron donors and oxidized manganese or iron in an appropriate form—are required to fulfill for microbial iron or manganese reduction to thrive in normal aquatic environments of near neutral pH. The first is a direct quantification of changes in Fe(III) or Fe(II) pools during sediment incubations. The second approach determines rates of dissimilatory iron and manganese reduction by comparing the depth distribution of total carbon oxidation, based on production of dissolved inorganic carbon, to measured rates of sulfate reduction. Reference 1. Thamdrup 2000; Straub et al. 2001; Comell and Schwertmann 2003. 2. Krishnamurthy, Aparna; Moore, J. Keith; Mahowald, Natalie; Luo, Chao; Doney, Scott C.; Lindsay, Keith; Zender, Charles S. (2009). "Impactsof increasing anthropogenic soluble iron and nitrogen deposition on ocean biogeochemistry". Global Biogeochemical Cycles. 23 (3). doi:10.1029/2008GB003440. ISSN 1944-9224. 3. Fortin D, Langley S. Formation and occurrence of biogenic iron-rich minerals. Earth Sci Rev,2005, 72, 1–19..
Recommended publications
  • Limits of Iron Fertilization
    LIMITS OF IRON FERTILIZATION Anand Gnanadesikan1, John P. Dunne1 and Irina Marinov2 1: NOAA Geophysical Fluid Dynamics Laboratory, PO Box 308, Princeton, NJ 08542 [email protected], [email protected] 2: Department of Earth, Atmosphere and Planetary Sciences, Massachusetts Institute of Technology, Cambridge, MA, [email protected] ABSTRACT Iron fertilization has been proposed as a cheap, controllable, and environmentally benign method for removing carbon dioxide from the atmosphere. While this is in fact the case in simple, 3-box models of the carbon cycle, more realistic models show that these claims fall short of reality. The fact that the efficiency of iron fertilization depends on the long term fate of the added iron and on the carbon associated with it makes tracking the effects of iron fertilization much more difficult and expensive than has been asserted. Additionally, advection of low nutrient water away from iron-rich areas can result in lowering production remotely, with potentially serious consequences. INTRODUCTION The idea of offsetting anthropogenic carbon dioxide emissions by fertilizing the ocean with iron has a number of superficially attractive features. A host of iron fertilization experiments have demonstrated that adding iron to surface waters leads to a local increase in productivity [see for example Coale et al., 1996]. Our own survey of the literature [Dunne et al. subm.] shows that this should be expected to lead to a local increase in particle export. It is claimed however, that this local increase in particle export would necessarily lead to an easily verifiable drawdown in atmospheric carbon dioxide. It is further claimed that the increase in export is controllable and environmentally benign, implying that the effects cease as soon as the fertilization stops.
    [Show full text]
  • An Iron Cycle Cascade Governs the Response of Equatorial Pacific Ecosystems to Climate Change
    Received: 19 June 2020 | Revised: 7 August 2020 | Accepted: 9 August 2020 DOI: 10.1111/gcb.15316 PRIMARY RESEARCH ARTICLE An iron cycle cascade governs the response of equatorial Pacific ecosystems to climate change Alessandro Tagliabue1 | Nicolas Barrier2 | Hubert Du Pontavice3,4 | Lester Kwiatkowski5 | Olivier Aumont5 | Laurent Bopp6 | William W. L. Cheung4 | Didier Gascuel3 | Olivier Maury2 1School of Environmental Sciences, University of Liverpool, Liverpool, UK Abstract 2MARBEC (IRD, Univ. Montpellier, CNRS, Earth System Models project that global climate change will reduce ocean net pri- Ifremer), Sète, France mary production (NPP), upper trophic level biota biomass and potential fisheries 3ESE, Ecology and Ecosystem Health, Institut Agro, Rennes, France catches in the future, especially in the eastern equatorial Pacific. However, projec- 4Nippon Foundation-Nereus Program, tions from Earth System Models are undermined by poorly constrained assumptions Institute for the Oceans and Fisheries, regarding the biological cycling of iron, which is the main limiting resource for NPP University of British Columbia, Vancouver, BC, Canada over large parts of the ocean. In this study, we show that the climate change trends 5LOCEAN, Sorbonne Université-CNRS-IRD- in NPP and the biomass of upper trophic levels are strongly affected by modifying MNHN, Paris, France assumptions associated with phytoplankton iron uptake. Using a suite of model ex- 6ENS-LMD, Paris, France periments, we find 21st century climate change impacts on regional NPP range from Correspondence −12.3% to +2.4% under a high emissions climate change scenario. This wide range Alessandro Tagliabue, School of Environmental Sciences, University of arises from variations in the efficiency of iron retention in the upper ocean in the Liverpool, Liverpool, UK.
    [Show full text]
  • Iron Stable Isotopes Track Pelagic Iron Cycling During a Subtropical Phytoplankton Bloom
    Iron stable isotopes track pelagic iron cycling during PNAS PLUS a subtropical phytoplankton bloom Michael J. Ellwooda,1, David A. Hutchinsb, Maeve C. Lohanc, Angela Milnec, Philipp Nasemannd, Scott D. Noddere, Sylvia G. Sanderd, Robert Strzepeka, Steven W. Wilhelmf, and Philip W. Boydg,2 aResearch School of Earth Sciences, Australian National University, Canberra, ACT 2601, Australia; bMarine and Environmental Biology, Department of Biological Sciences, University of Southern California, Los Angeles, CA 90089; cSchool of Geography, Earth and Environmental Sciences, University of Plymouth, Plymouth PL4 8AA, United Kingdom; dMarine and Freshwater Chemistry, Department of Chemistry, University of Otago, Dunedin 9054, New Zealand; eNational Institute of Water and Atmospheric Research, Wellington 6021, New Zealand; fDepartment of Microbiology, The University of Tennessee, Knoxville, TN 37996; and gNational Institute of Water and Atmospheric Research Centre for Chemical and Physical Oceanography, Department of Chemistry, University of Otago, Dunedin 9012, New Zealand Edited by Edward A. Boyle, Massachusetts Institute of Technology, Cambridge, MA, and approved December 1, 2014 (received for review November 11, 2014) The supply and bioavailability of dissolved iron sets the magnitude (www.geotraces.org) process voyages (2008 and 2012) designed of surface productivity for ∼40% of the global ocean. The redox to study temporal changes in the biogeochemical cycling of Fe at state, organic complexation, and phase (dissolved versus particu- the same locality in subtropical waters (38°S−39°S, 178°W late) of iron are key determinants of iron bioavailability in the −180°W) within the mesoscale eddy field east of New Zealand marine realm, although the mechanisms facilitating exchange be- (3).
    [Show full text]
  • Microbial Iron Metabolism in Natural Environments Marianne Erbs & Jim Spain
    L I Microbial iron metabolism in natural environments Marianne Erbs & Jim Spain Microbial Diversity 2002 Microbial iron metabolism in natural environments Marianne Erbs & Jim Spain [email protected] [email protected] Abstract The aim of this project was to assess the diversity of iron metabolizing bacteria in several ecological niches by culture-dependent and culture-independent methods. In particular, we wanted to determine whether non-phototrophic, anaerobic nitrate-dependent Fe(II)-oxidizers coexist with aerobic Fe(1I)-oxidizers and facultatively anaerobic Fe(III)-reducers in natural habitats. To this end, we sampled iron-rich sites in freshwater, estuarine and marine environments and enriched for non-phototrophic anaerobic and aerobic Fe(II)-oxidizers. The identification of the two environmentally most important facultatively anaerobic Fe(III) reducers and one aerobic heterotrophic Fe(II)-oxidizer in the sediment samples was carried out by means of fluorescent in situ hybridization (FISH). We were able to culture aerobic Fe(II) oxidizers in gradient tubes from each sample site. Nitrate-reducing Fe(TI)-oxidizers were only found in sediments from a Cranberry Bog. Geobacter, S’hewanella and Leptothrix coexist in Salt Pond at the oxic/anoxic interface. Microbial iron metabolism in natural environments Marianne Erbs & Jim Spain Introduction The significance of bacteria in the biogeochemical cycling of iron has been broadly recognized over the past two decades. In Fig. 1 the role of dissimilatory anaerobic Fe(III)-reducers as well as acidophilic and neutrophilic aerobic Fe(II)-oxidizers, anaerobic phototrophic Fe(II)-oxidizers and facultatively anaerobic nitrate-reducing Fe(11)-oxidizers in the microbial cycling of iron is shown.
    [Show full text]
  • DOE Mission: Carbon Cycling and Sequestration
    APPENDIX C Appendix C. DOE Mission: Carbon Cycling and Sequestration C.1.1. The Climate Change Challenge ..............................................................................................................................228 C.1.2. The Role of Microbes ..................................................................................................................................................229 C.1.3. Microbial Ocean Communities ................................................................................................................................231 C.1.3.1. Photosynthetic Capabilities .......................................................................................................................................231 C.1.3.2. Strategies for Increasing Ocean CO2 Pools ................................................................................................................231 C.1.3.3. GTL’s Vision for Ocean Systems .................................................................................................................................233 C.1.3.3.1. Gaps in Scientific Understanding .............................................................................................................................233 C.1.3.3.2. Scientific and Technological Capabilities Required ..................................................................................................233 C.1.4. Terrestrial Microbial Communities ........................................................................................................................235
    [Show full text]
  • Biogeochemical Cycling of Iron and Phosphorus Under Low Oxygen Conditions
    BIOGEOCHEMICAL CYCLING OF IRON AND PHOSPHORUS UNDER LOW OXYGEN CONDITIONS Dissertation Zur Erlangung des Doktorgrades Dr. rer. nat. der Mathematisch- Naturwissenschaftlichen Fakultät der Christian-Albrechts- Universität zu Kiel vorgelegt von Ulrike Lomnitz Kiel, Mai 2017 Referent: Prof. Dr. Klaus Wallmann Koreferent: PD Dr. Mark Schmidt Tag der mündlichen Prüfung: 14.07.2017 zum Druck genehmigt: 14.07.2017 Erklärung Hiermit erkläre ich, dass ich die vorliegende Doktorarbeit selbstständig und ohne Zuhilfenahme unerlaubter Hilfsmittel erstellt habe. Weder diese noch eine ähnliche Arbeit wurde an einer anderen Abteilung oder Hochschule im Rahmen eines Prüfungsverfahrens veröffentlicht oder zur Veröffentlichung vorgelegt. Ferner versichere ich, dass die Arbeit unter Einhaltung der Regeln guter wissenschaftlicher Praxis der Deutschen Forschungsgemeinschaft entstanden ist. 05.05.2017 Ulrike Lomnitz Abstract Benthic release of the key nutrients iron (Fe) and phosphorus (P) is enhanced from sediments that are impinged by oxygen-deficient bottom waters due to its diminished retention capacity for such redox sensitive elements. Suboxic to anoxic and sometimes even euxinic conditions are recently found in open ocean oxygen minimum zones (OMZs, e.g. Eastern Boundary Upwelling Systems) and marginal seas (e.g. the Black Sea and the Baltic Sea). Recent studies showed that OMZs expanded in the last decades and will further spread in the future. Due to the additional release of bioavailable key nutrients from the sediments in such high productivity regions, several feedback mechanisms can evolve. The scenarios range from positive to neutral and negative consequences on the evolution of the ocean’s oxygen levels. This controversial issue makes it crucial to investigate the biogeochemical cycling of Fe and P in OMZs.
    [Show full text]
  • Feedbacks Between the Nitrogen, Carbon and Oxygen Cycles 1513
    Comp. by: RVijayarajProof0000836003 Date:4/6/08 Time:13:20:09 Stage:First Proof File Path://ppdys1108/Womat3/Production/PRODENV/0000000038/0000009008/ 0000000005/0000836003.3D Proof by: QC by: B978-0-12-372522-6.00035-3, 35 CHAPTER 35 Feedbacks Between the Nitrogen, c0035 Carbon and Oxygen Cycles Ilana Berman-Frank, Yi-bu Chen, Yuan Gao, Katja Fennel, Mick Follows, Allen J. Milligan, and Paul Falkowski Contents 1. Evolutionary History of the N, C, and O Cycles 1512 1.1. Nitrogen in the preoxygenated world/oceans 1512 1.2. Oxygenation of the early atmosphere: The influence of shelf area and nitrogen fixation rates 1513 2. Nitrogen-Fixation, Nitrogenase, and Oxygen. Evolutionary Constraints, Adaptations of Cellular Pathways and Organisms, Feedbacks to Global N, C, O Cycles 1515 2.1. Evolutionary constraints for nitrogen fixation and adaptive strategies 1515 2.2. Adaptive strategies. Oxygen consumption—The Mehler reaction 1520 2.3. Biological feedbacks to the global N, C, and O cycles 1523 3. Sensitivity of the Nitrogen, Carbon, and Oxygen Cycles to Climate Change 1524 3.1. Aeolian iron and stratification of the surface mixed layer in the future 1525 3.2. Interactions of the oxygen and nitrogen cycles: Nitrification and denitrification 1527 3.3. Ocean circulation and the global ocean cycles of nitrogen, oxygen and carbon 1527 3.4. Implications for the global carbon cycle 1529 4. Summary and Conclusions 1530 References 1531 Abstract p0090 The global cycles of nitrogen, carbon, and oxygen are inextricably interconnected via biologically mediated, coupled redox reactions. The primary reactions include nitrogen fixation, nitrification, denitrification, oxygenic photosynthesis, and respiration.
    [Show full text]
  • Whole-Cell Response of the Pennate Diatom Phaeodactylum Tricornutum to Iron Starvation
    Whole-cell response of the pennate diatom Phaeodactylum tricornutum to iron starvation Andrew E. Allen*†, Julie LaRoche‡§, Uma Maheswari*, Markus Lommer‡, Nicolas Schauer¶, Pascal J. Lopez*, Giovanni Finazziʈ, Alisdair R. Fernie¶, and Chris Bowler*§** *Centre National de la Recherche Scientifique Unite Mixte de Recherche 8186, Dept of Biology, Ecole Normale Supe´rieure, 46 rue d’Ulm, 75005 Paris, France; ‡Leibniz-Institut fu¨r Meereswissenschaften, 24105 Kiel, Germany; ¶Max Planck Institute of Molecular Plant Physiology, Am Muhlenberg 1, 14476 Potsdam-Golm, Germany; ʈCentre National de la Recherche Scientifique Unite Mixte de Recherche 7141, Universite´Paris 6 Institut de Biologie Physico-Chimique, 13 rue Pierre et Marie Curie, 75005 Paris, France; and **Stazione Zoologica, Villa Comunale, I 80121 Naples, Italy Edited by David M. Karl, University of Hawaii, Honolulu, HI, and approved May 3, 2008 (received for review December 4, 2007) Marine primary productivity is iron (Fe)-limited in vast regions of Table 1. General cellular, physiological, and biochemical the contemporary oceans, most notably the high nutrient low characteristics of Fe-limited P. tricornutum cells and cultures chlorophyll (HNLC) regions. Diatoms often form large blooms upon Fe-limited/ the relief of Fe limitation in HNLC regions despite their prebloom Parameter Fe-limited Fe-replete Fe-replete low cell density. Although Fe plays an important role in controlling Ϯ Ϯ Ϯ diatom distribution, the mechanisms of Fe uptake and adaptation Growth rate 0.18 0.05 0.88 0.01 0.2 0.06 Ferric reductase assay, 0.717 Ϯ 0.03 0.020 Ϯ 0.004 35.9 Ϯ 7.3 to low iron availability are largely unknown.
    [Show full text]
  • Proximity Proteomics in a Marine Diatom Reveals a Putative Cell
    RESEARCH ARTICLE Proximity proteomics in a marine diatom reveals a putative cell surface-to- chloroplast iron trafficking pathway Jernej Turnsˇek1,2,3,4,5,6†, John K Brunson6,7, Maria del Pilar Martinez Viedma8‡, Thomas J Deerinck9, Alesˇ Hora´ k10,11, Miroslav Obornı´k10,11, Vincent A Bielinski12, Andrew Ellis Allen4,6* 1Biological and Biomedical Sciences, The Graduate School of Arts and Sciences, Harvard University, Cambridge, United States; 2Department of Systems Biology, Harvard Medical School, Boston, United States; 3Wyss Institute for Biologically Inspired Engineering, Harvard University, Boston, United States; 4Integrative Oceanography Division, Scripps Institution of Oceanography, University of California San Diego, La Jolla, United States; 5Center for Research in Biological Systems, University of California San Diego, La Jolla, United States; 6Microbial and Environmental Genomics, J. Craig Venter Institute, La Jolla, United States; 7Center for Marine Biotechnology and Biomedicine, Scripps Institution of Oceanography, University of California San Diego, La Jolla, United States; 8Informatics, J. Craig Venter Institute, La Jolla, United States; 9National Center for Microscopy and Imaging Research, University of California San Diego, La Jolla, United States; 10Biology Centre CAS, Institute of Parasitology, Cˇ eske´ Budeˇjovice, Czech Republic; *For correspondence: 11 ˇ [email protected] University of South Bohemia, Faculty of Science, Ceske´ Budeˇjovice, Czech Republic; 12Synthetic Biology and Bioenergy, J. Craig Venter Institute, La Jolla, Present address: †Department of Plant and Microbial Biology, United States University of California, Berkeley, Howard Hughes Medical Institute, University of California, Berkeley, United States; Abstract Iron is a biochemically critical metal cofactor in enzymes involved in photosynthesis, ‡PharmaMar S.A., Madrid, Spain cellular respiration, nitrate assimilation, nitrogen fixation, and reactive oxygen species defense.
    [Show full text]
  • The Biogeochemical Cycle of Iron in the Ocean P
    REVIEW ARTICLE PUBLISHED ONLINE: 26 SEPTEMBER 2010 | DOI: 10.1038/NGEO964 The biogeochemical cycle of iron in the ocean P. W. Boyd1* and M. J. Ellwood2 Advances in iron biogeochemistry have transformed our understanding of the oceanic iron cycle over the past three decades: multiple sources of iron to the ocean were discovered, including dust, coastal and shallow sediments, sea ice and hydrothermal fluids. This new iron is rapidly recycled in the upper ocean by a range of organisms; up to 50% of the total soluble iron pool is turned over weekly in this way in some ocean regions. For example, bacteria dissolve particulate iron and at the same time release compounds — iron-binding ligands — that complex with iron and therefore help to keep it in solution. Sinking particles, on the other hand, also scavenge iron from solution. The balance between these supply and removal processes determines the concentration of dissolved iron in the ocean. Whether this balance, and many other facets of the biogeochemical cycle, will change as the climate warms remains to be seen. ron is undoubtedly the most studied trace element in the ocean, budgets and models. Here, we review the oceanic biogeochemical having received widespread attention since the late 1980s1,2. The cycle of iron and explore the contribution of these sub-themes to Idisproportionate interest in iron stems from the control it was our understanding of this cycle. thought to exert on ocean productivity, the resulting sequestration of carbon into the ocean’s interior, and consequent modulation of Global patterns of ocean iron atmospheric carbon dioxide concentrations in the geological past3.
    [Show full text]
  • The Carbon Cycle and Atmospheric Carbon Dioxide
    3 The Carbon Cycle and Atmospheric Carbon Dioxide Co-ordinating Lead Author I.C. Prentice Lead Authors G.D. Farquhar, M.J.R. Fasham, M.L. Goulden, M. Heimann, V.J. Jaramillo, H.S. Kheshgi, C. Le Quéré, R.J. Scholes, D.W.R. Wallace Contributing Authors D. Archer, M.R. Ashmore, O. Aumont, D. Baker, M. Battle, M. Bender, L.P. Bopp, P. Bousquet, K. Caldeira, P. Ciais, P.M. Cox, W. Cramer, F. Dentener, I.G. Enting, C.B. Field, P. Friedlingstein, E.A. Holland, R.A. Houghton, J.I. House, A. Ishida, A.K. Jain, I.A. Janssens, F. Joos, T. Kaminski, C.D. Keeling, R.F. Keeling, D.W. Kicklighter, K.E. Kohfeld, W. Knorr, R. Law, T. Lenton, K. Lindsay, E. Maier-Reimer, A.C. Manning, R.J. Matear, A.D. McGuire, J.M. Melillo, R. Meyer, M. Mund, J.C. Orr, S. Piper, K. Plattner, P.J. Rayner, S. Sitch, R. Slater, S. Taguchi, P.P. Tans, H.Q. Tian, M.F. Weirig, T. Whorf, A. Yool Review Editors L. Pitelka, A. Ramirez Rojas Contents Executive Summary 185 3.5.2 Interannual Variability in the Rate of Atmospheric CO2 Increase 208 3.1 Introduction 187 3.5.3 Inverse Modelling of Carbon Sources and Sinks 210 3.2 Terrestrial and Ocean Biogeochemistry: 3.5.4 Terrestrial Biomass Inventories 212 Update on Processes 191 3.2.1 Overview of the Carbon Cycle 191 3.6 Carbon Cycle Model Evaluation 213 3.2.2 Terrestrial Carbon Processes 191 3.6.1 Terrestrial and Ocean Biogeochemistry 3.2.2.1 Background 191 Models 213 3.2.2.2 Effects of changes in land use and 3.6.2 Evaluation of Terrestrial Models 214 land management 193 3.6.2.1 Natural carbon cycling on land 214 3.2.2.3 Effects
    [Show full text]
  • An International Study of the Global Marine Biogeochemical Cycles of Trace Elements and Their Isotopes SCOR Working Groupã1
    ARTICLE IN PRESS Chemie der Erde 67 (2007) 85–131 www.elsevier.de/chemer INVITED REVIEW GEOTRACES – An international study of the global marine biogeochemical cycles of trace elements and their isotopes SCOR Working GroupÃ1 Received 28 April 2006; accepted 19 September 2006 Abstract Trace elements serve important roles as regulators of ocean processes including marine ecosystem dynamics and carbon cycling. The role of iron, for instance, is well known as a limiting micronutrient in the surface ocean. Several other trace elements also play crucial roles in ecosystem function and their supply therefore controls the structure, and possibly the productivity, of marine ecosystems. Understanding the biogeochemical cycling of these micronutrients requires knowledge of their diverse sources and sinks, as well as their transport and chemical form in the ocean. Much of what is known about past ocean conditions, and therefore about the processes driving global climate change, is derived from trace-element and isotope patterns recorded in marine deposits. Reading the geochemical information archived in marine sediments informs us about past changes in fundamental ocean conditions such as temperature, salinity, pH, carbon chemistry, ocean circulation and biological productivity. These records provide our principal source of information about the ocean’s role in past climate change. Understanding this role offers unique insights into the future consequences of global change. The cycle of many trace elements and isotopes has been significantly impacted by human activity. Some of these are harmful to the natural and human environment due to their toxicity and/or radioactivity. Understanding the processes that control the transport and fate of these contaminants is an important aspect of protecting the ocean environment.
    [Show full text]