Ocean Acidification and Marine Biogenic Trace Gas Production

Total Page:16

File Type:pdf, Size:1020Kb

Ocean Acidification and Marine Biogenic Trace Gas Production Ocean Acidification and Marine Biogenic Trace Gas Production A thesis submitted to the School of Environmental Sciences of the University of East Anglia in candidature for the degree of Doctor of Philosophy By Frances Elizabeth Hopkins March 2010 © This copy of the thesis has been supplied on condition that anyone who consults it is understood to recognise that its copyright rests with the author and that no quotation from the thesis, nor any information derived therefrom, may be published without the author’s prior consent. i ii Abstract The oceanic uptake of anthropogenic CO2 emissions is leading to an alteration of seawater carbonate chemistry, manifested as increasing [H+], falling [CO32-] and a drop in seawater pH. Over the coming centuries this process, termed “ocean acidification”, is expected to negatively impact marine biota, with implications for marine biological and biogeochemical processes. In this thesis, the impact that such changes may have on the net production of a range of climatically- and atmospherically-important marine biogenic trace gases, including halocarbons and dimethyl sulphide (DMS), is assessed through a mesocosm phytoplankton bloom CO2 perturbation experiment, two laboratory CO2 incubation experiments on natural seawater samples, and at a volcanically-acidified shallow marine fieldsite in Italy. Large and significant reductions in DMS and DMSP concentrations under future high CO2 conditions were observed during the mesocosm experiment (mean decreases of 57 percent and 24 percent, respectively), a finding in strong support of a previous study (Avgoustidi 2007). Furthermore, concentrations of iodocarbons showed large decreases, with mean decreases under high CO2 ranging from 59 to 93 percent. Results for the laboratory incubation experiments also showed a reduction in iodocarbon concentrations (when normalised to chlorophyll a) under high CO2. These changes may be the result of shifts in plankton community composition in response to the high CO2 conditions, and/or impacts on dissolved organic matter and the bacterial communities involved in the formation of these compounds. The response of bromocarbons was less clear cut during the experimental studies. Following investigations at a naturally-acidified fieldsite in Italy, it was concluded that this site was a poor natural analogue to the impact of future ocean acidification on marine trace gas production. Taking the results of the mesocosm and laboratory incubations into consideration, a combined decrease in both DMS and iodocarbons in response to ocean acidification may have considerable impacts on future atmospheric chemistry and global climate. iii Acknowledgements Many people have contributed to making my PhD experience both enjoyable and rewarding. Firstly, my supervisory team: Professor Peter Liss and Dr. Sue Turner at the University of East Anglia, Dr. Phil Nightingale at Plymouth Marine Laboratory (PML), and Dr. Michael Steinke at the University of Essex, all of whom have consistently provided invaluable guidance, advice, expertise and support. I am extremely grateful to Claire Hughes and Manuela Martino for providing training and advice on halocarbon analysis, and to Tom Bell and Dan Franklin for help and training in DMS/DMSP analysis. This work would not have been possible without the amazing technical assistance of Gareth Lee, both in the lab at UEA and during the mesocosm experiment in Norway. I also thank Gareth, as well as Andy Macdonald and Rob Utting of the UEA technical department, for organising the often tricky logistics involved in the transportation of equipment, analytical instruments, chemicals and gases to far-flung locations, including Norwegian fjords and Italian islands. I am indebted to all those involved in the mesocosm experiment in Bergen, Norway for making the experiment both a great experience and a success, in particular Ian Joint for his leadership of the experiment, Dorothee Bakker for the pCO2 measurements, Isabelle Mary for phytoplankton flow cytometry data and Claire Widdicombe for phytoplankton biomass data. I am also extremely grateful to Claire for taking the time to analyse plankton samples for my Plymouth incubation experiments. I gratefully acknowledge all those at PML who offered help, assistance, advice and friendship during the summer of 2007, in particular Rachael Beale, Laura Goldson, Susan Kimmance, Malcolm Woodward, Glen Tarran, Steve Archer and Malcolm Liddicoat, and made me feel part of the PML “family” during those months spent working at the lab. There were many people involved in the Ischia fieldwork that deserve lots of thanks: Matt Jones, Phil Kerrison, Jason Hall-Spencer, Riccardo Rodolfo-Metalpa, the staff at Institute Laboratorio di Ecologia del Benthos, (Stazione Zoologica Anton Dohrn, Ischia), Roger and Josie Phillips, Tony Dolphin and of course, Sue Turner. A special thank you goes to the ENV PhD gang, all of whom made the last 4 years some of the best of my life, especially my second family Helen Band and Simon Busby, and Nem Vaughan, Laura Bristow and Gemma Bates. Lots of love and thanks goes to my family (Hopkins and Pask!) for all their love and support, and for encouraging me to pursue a career in my love of all things marine. And finally, all my love to Edward Pask, for being more than I could ever have wished for. iv Frances E. Hopkins Table of Contents Table of Contents Page Abstract iii Acknowledgements iv List of Figures xi-xv List of Tables xv-xviii Chapter 1: Introduction and Literature Review 1 Introduction 1 1.1. The Global Carbon Cycle 1 1.1.1. Atmospheric CO2 in Earth’s Past 2 1.1.2. Anthropogenic CO2 emissions 3 1.1.3. Atmospheric C flux to the oceans 3 1.1.4. Seawater DIC, Total Alkalinity (TA) and carbonate equilibrium 4 1.1.5. Seawater pH Buffering Capacity 5 1.1.6. Biological Pump 6 1.2. Seawater CaCO3 Saturation and the Carbonate Compensation Depth 6 1.2.1. Forms of Carbonate 6 1.2.2. Factors controlling saturation states 7 1.3. Natural Variability of seawater pH 8 1.3.1. Average surface ocean pH 8 1.3.2. Natural variations in pH 9 1.3.3. Spatial pH variations 9 1.3.4. Seasonal variability 10 1.4. The Future of Atmospheric CO2 10 1.4.1. Emissions scenarios 10 1.4.2. Impacts on ocean chemistry and pH 12 1.5. Impacts of Anthropogenic CO2 Emissions on Oceanic Carbonate System 14 1.5.1. Impacts on seawater DIC 14 1.5.2. Future projections 16 1.6. Biological Impacts of Ocean Acidification 17 1.6.1. Introduction 17 1.6.2. Marine Phytoplankton 18 1.6.2.1. Introduction 18 1.6.2.2. Photosynthesis and growth rates 18 1.6.2.3. Calcification and C cycling 20 1.6.2.4. Organic C Export 22 1.6.2.5. Trace gas production 23 1.7. Marine Biogenic Trace Gases 24 1.7.1. DMS 24 1.7.1.1. Sources 25 1.7.1.2. Oceanic distribution 26 1.7.1.3. Sinks 28 1.7.1.4. Atmospheric consequences 29 1.7.1.5. DMS-CCN-Climate system 31 1.7.1.6. DMS-CCN-Climate interactions in a high CO2 world 32 1.7.2. Halocarbon Compounds 36 1.7.2.1. Sources 37 1.7.2.1.1. Macroalgae 37 v Frances E. Hopkins Table of Contents 1.7.2.1.2. Phytoplankton 38 1.7.2.1.3. Bacteria 41 1.7.2.1.4. Photochemistry 42 1.7.2.1.5. Reactions with ozone and organic matter 43 1.7.2.2. Sinks 43 1.7.2.2.1. Air-sea exchange 43 1.7.2.2.2. Hydrolysis and nucleophilic substitution 45 1.7.2.2.3. Photochemistry 46 1.7.2.2.4. Bacteria 46 1.7.2.3. Atmospheric consequences 47 1.7.2.3.1. Sea-to-land transfer 47 1.7.2.3.2. New particle formation 47 1.7.2.3.3. Interactions with ozone 48 1.8. Research Aims and Objectives 49 Chapter 2: Methods of Marine Trace Gas Analysis 2.1. Introduction 53 2.2. Analytical Procedures, Materials and Methods 53 2.2.1. Gas extraction and pre-concentration techniques 53 2.3. Halocarbon Analysis 54 2.3.1. Analytical techniques 54 2.3.1.1. Sample collection and preparation 54 2.3.1.2. Purge and cryogenic trap 54 2.3.1.3. Purge and trap on sorbent tubes 55 2.3.1.4. Markes UltrA autosampler and Unity TD platform 59 2.3.1.5. GC-MS system and methods 64 2.3.2. System sensitivity drift and surrogate analytes 68 2.3.3. Halocarbon system calibrations 71 2.4. Dimethylsulphide (DMS) and Dimethylsulphoniopropionate (DMSP) 76 Analysis 2.4.1. Analytical techniques 76 2.4.1.1. Sample collection and preparation 76 2.4.1.2. Purge and cryogenic trap 76 2.4.1.3. Headspace analysis 77 2.4.1.4. Gas chromatograph – Flame Photometric Detector (GC-FPD) 77 system and methods 2.4.2. GC-FPD system calibrations 78 2.5. Other measurements 80 2.5.1. Chlorophyll a and phaeopigments 80 2.5.2. Phytoplankton counts (Flow cytometry) 81 2.5.3. Phytoplankton enumeration (Microscopy) 82 2.5.4. Seawater pH measurements 82 2.6. Summary 85 Chapter 3: Marine biogenic trace gas production during a mesocosm CO2 perturbation experiment 3.1. Introduction 87 3.1.1. Mesocosm experiments in marine science research 87 3.1.2. Mesocosm experiments in ocean acidification research 88 vi Frances E. Hopkins Table of Contents 3.1.3. Results of past ocean acidification mesocosm studies 88 3.1.3.1. Photosynthesis and growth rate 89 3.1.3.2. Phytoplankton calcification and C cycling 89 3.1.3.3. Organic C Export 90 3.1.3.4. Trace gas production 90 3.1.4.
Recommended publications
  • Paleoceanographical Proxies Based on Deep-Sea Benthic Foraminiferal Assemblage Characteristics
    CHAPTER SEVEN Paleoceanographical Proxies Based on Deep-Sea Benthic Foraminiferal Assemblage Characteristics Frans J. JorissenÃ, Christophe Fontanier and Ellen Thomas Contents 1. Introduction 263 1.1. General introduction 263 1.2. Historical overview of the use of benthic foraminiferal assemblages 266 1.3. Recent advances in benthic foraminiferal ecology 267 2. Benthic Foraminiferal Proxies: A State of the Art 271 2.1. Overview of proxy methods based on benthic foraminiferal assemblage data 271 2.2. Proxies of bottom water oxygenation 273 2.3. Paleoproductivity proxies 285 2.4. The water mass concept 301 2.5. Benthic foraminiferal faunas as indicators of current velocity 304 3. Conclusions 306 Acknowledgements 308 4. Appendix 1 308 References 313 1. Introduction 1.1. General Introduction The most popular proxies based on microfossil assemblage data produce a quanti- tative estimate of a physico-chemical target parameter, usually by applying a transfer function, calibrated on the basis of a large dataset of recent or core-top samples. Examples are planktonic foraminiferal estimates of sea surface temperature (Imbrie & Kipp, 1971) and reconstructions of sea ice coverage based on radiolarian (Lozano & Hays, 1976) or diatom assemblages (Crosta, Pichon, & Burckle, 1998). These à Corresponding author. Developments in Marine Geology, Volume 1 r 2007 Elsevier B.V. ISSN 1572-5480, DOI 10.1016/S1572-5480(07)01012-3 All rights reserved. 263 264 Frans J. Jorissen et al. methods are easy to use, apply empirical relationships that do not require a precise knowledge of the ecology of the organisms, and produce quantitative estimates that can be directly applied to reconstruct paleo-environments, and to test and tune global climate models.
    [Show full text]
  • Secondary Organic Aerosol from Chlorine-Initiated Oxidation of Isoprene Dongyu S
    Secondary organic aerosol from chlorine-initiated oxidation of isoprene Dongyu S. Wang and Lea Hildebrandt Ruiz McKetta Department of Chemical Engineering, The University of Texas at Austin, Austin, TX 78756, USA 5 Correspondence to: Lea Hildebrandt Ruiz ([email protected]) Abstract. Recent studies have found concentrations of reactive chlorine species to be higher than expected, suggesting that atmospheric chlorine chemistry is more extensive than previously thought. Chlorine radicals can interact with HOx radicals and nitrogen oxides (NOx) to alter the oxidative capacity of the atmosphere. They are known to rapidly oxidize a wide range of volatile organic compounds (VOC) found in the atmosphere, yet little is known about secondary organic aerosol (SOA) 10 formation from chlorine-initiated photo-oxidation and its atmospheric implications. Environmental chamber experiments were carried out under low-NOx conditions with isoprene and chlorine as primary VOC and oxidant sources. Upon complete isoprene consumption, observed SOA yields ranged from 8 to 36 %, decreasing with extended photo-oxidation and SOA aging. Formation of particulate organochloride was observed. A High-Resolution Time-of-Flight Chemical Ionization Mass Spectrometer was used to determine the molecular composition of gas-phase species using iodide-water and hydronium-water 15 cluster ionization. Multi-generational chemistry was observed, including ions consistent with hydroperoxides, chloroalkyl hydroperoxides, isoprene-derived epoxydiol (IEPOX) and hypochlorous acid (HOCl), evident of secondary OH production and resulting chemistry from Cl-initiated reactions. This is the first reported study of SOA formation from chlorine-initiated oxidation of isoprene. Results suggest that tropospheric chlorine chemistry could contribute significantly to organic aerosol loading.
    [Show full text]
  • Use of Chlorofluorocarbons in Hydrology : a Guidebook
    USE OF CHLOROFLUOROCARBONS IN HYDROLOGY A Guidebook USE OF CHLOROFLUOROCARBONS IN HYDROLOGY A GUIDEBOOK 2005 Edition The following States are Members of the International Atomic Energy Agency: AFGHANISTAN GREECE PANAMA ALBANIA GUATEMALA PARAGUAY ALGERIA HAITI PERU ANGOLA HOLY SEE PHILIPPINES ARGENTINA HONDURAS POLAND ARMENIA HUNGARY PORTUGAL AUSTRALIA ICELAND QATAR AUSTRIA INDIA REPUBLIC OF MOLDOVA AZERBAIJAN INDONESIA ROMANIA BANGLADESH IRAN, ISLAMIC REPUBLIC OF RUSSIAN FEDERATION BELARUS IRAQ SAUDI ARABIA BELGIUM IRELAND SENEGAL BENIN ISRAEL SERBIA AND MONTENEGRO BOLIVIA ITALY SEYCHELLES BOSNIA AND HERZEGOVINA JAMAICA SIERRA LEONE BOTSWANA JAPAN BRAZIL JORDAN SINGAPORE BULGARIA KAZAKHSTAN SLOVAKIA BURKINA FASO KENYA SLOVENIA CAMEROON KOREA, REPUBLIC OF SOUTH AFRICA CANADA KUWAIT SPAIN CENTRAL AFRICAN KYRGYZSTAN SRI LANKA REPUBLIC LATVIA SUDAN CHAD LEBANON SWEDEN CHILE LIBERIA SWITZERLAND CHINA LIBYAN ARAB JAMAHIRIYA SYRIAN ARAB REPUBLIC COLOMBIA LIECHTENSTEIN TAJIKISTAN COSTA RICA LITHUANIA THAILAND CÔTE D’IVOIRE LUXEMBOURG THE FORMER YUGOSLAV CROATIA MADAGASCAR REPUBLIC OF MACEDONIA CUBA MALAYSIA TUNISIA CYPRUS MALI TURKEY CZECH REPUBLIC MALTA UGANDA DEMOCRATIC REPUBLIC MARSHALL ISLANDS UKRAINE OF THE CONGO MAURITANIA UNITED ARAB EMIRATES DENMARK MAURITIUS UNITED KINGDOM OF DOMINICAN REPUBLIC MEXICO GREAT BRITAIN AND ECUADOR MONACO NORTHERN IRELAND EGYPT MONGOLIA UNITED REPUBLIC EL SALVADOR MOROCCO ERITREA MYANMAR OF TANZANIA ESTONIA NAMIBIA UNITED STATES OF AMERICA ETHIOPIA NETHERLANDS URUGUAY FINLAND NEW ZEALAND UZBEKISTAN FRANCE NICARAGUA VENEZUELA GABON NIGER VIETNAM GEORGIA NIGERIA YEMEN GERMANY NORWAY ZAMBIA GHANA PAKISTAN ZIMBABWE The Agency’s Statute was approved on 23 October 1956 by the Conference on the Statute of the IAEA held at United Nations Headquarters, New York; it entered into force on 29 July 1957. The Headquarters of the Agency are situated in Vienna.
    [Show full text]
  • Soares, R. Et Al
    Original Article DOI: 10.7860/JCDR/2017/23594.9758 Assessment of Enamel Remineralisation After Treatment with Four Different Dentistry Section Remineralising Agents: A Scanning Electron Microscopy (SEM) Study RENITA SOARES1, IDA DE NORONHA DE ATAIDE2, MARINA FERNANDES3, RAJAN LAMBOR4 ABSTRACT these groups were remineralised using the four remineralising Introduction: Decades of research has helped to increase our agents. The treated groups were subjected to pH cycling over a knowledge of dental caries and reduce its prevalence. However, period of 30 days. This was followed by assessment of surface according to World Oral Health report, dental caries still remains microhardness and SEM for qualitative evaluation of surface a major dental disease. Fluoride therapy has been utilised in changes. The results were analysed by One-Way Analysis Of a big way to halt caries progression, but has been met with Variance (ANOVA). Multiple comparisons between groups were limitations. This has paved the way for the development of performed by paired t-test and post-hoc Tukey test. newer preventive agents that can function as an adjunct to Results: The results of the study revealed that remineralisation of fluoride or independent of it. enamel was the highest in samples of Group E (Self assembling Aim: The purpose of the present study was to evaluate the ability peptide P11-4) followed by Group B (CPP-ACPF), Group C (BAG) of Casein Phosphopeptide-Amorphous Calcium Phosphate and Group D (fluoride enhanced HA gel). There was a significant Fluoride (CPP ACPF), Bioactive Glass (BAG), fluoride enhanced difference (p<0.05) in the remineralising ability between the self assembling peptide P -4 group and BAG and fluoride Hydroxyapatite (HA) gel and self-assembling peptide P11-4 to 11 remineralise artificial carious lesions in enamel in vitro using enhanced HA gel group.
    [Show full text]
  • CHAPTER12 Atmospheric Degradation of Halocarbon Substitutes
    CHAPTER12 AtmosphericDegradation of Halocarbon Substitutes Lead Author: R.A. Cox Co-authors: R. Atkinson G.K. Moortgat A.R. Ravishankara H.W. Sidebottom Contributors: G.D. Hayman C. Howard M. Kanakidou S .A. Penkett J. Rodriguez S. Solomon 0. Wild CHAPTER 12 ATMOSPHERIC DEGRADATION OF HALOCARBON SUBSTITUTES Contents SCIENTIFIC SUMMARY ......................................................................................................................................... 12.1 12.1 BACKGROUND ............................................................................................................................................... 12.3 12.2 ATMOSPHERIC LIFETIMES OF HFCS AND HCFCS ................................................................................. 12.3 12.2. 1 Tropospheric Loss Processes .............................................................................................................. 12.3 12.2.2 Stratospheric Loss Processes .............................................................................................................. 12.4 12.3 ATMOSPHERIC LIFETIMES OF OTHER CFC AND HALON SUBSTITUTES ......................................... 12.4 12.4 ATMOSPHERIC DEGRADATION OF SUBSTITUTES ................................................................................ 12.5 12.5 GAS PHASE DEGRADATION CHEMISTRY OF SUBSTITUTES .............................................................. 12.6 12.5.1 Reaction with NO ..............................................................................................................................
    [Show full text]
  • Verification Program Manual and Mexico
    SHARE: Join Our Email List CLIMATE ACTION NEWS December 2020 A note from our President Greetings, The climate community is hopeful and excited for a new era of climate policy, action, and diplomacy. The incoming Administration has already indicated a serious commitment to addressing the climate crisis, with key appointments and statements portending well for the future of U.S. climate action on the federal level. We are excited for the U.S. to not only rejoin the Paris Agreement, but to provide the example, the innovation, and the thought-leadership to achieve GHG reductions at the scale and urgency required. The Reserve is working to support and inform international efforts to scale up, mobilize, and strengthen the effectiveness of voluntary carbon markets across the globe. Even though COP has been postponed this year, experts around the world continue to discuss and deliberate critical issues to help craft key underlying decisions on how markets should function, how to apply usage of carbon offsets, and how to ensure the environmental integrity and financial value of offset projects and credits. In addition to participating in international discussions, the Reserve is working to expand our work in Mexico. We are updating the Mexico Ozone Depleting Substances Protocol to add several halocarbons, which are refrigerants with high global warming potentials. We are also continuing to work with communities and organizations across Mexico with outreach and education on implementing forest carbon projects, as well as drafting agricultural offset protocols for consideration by the Mexican Government. Thank you again for your climate action and leadership throughout the year.
    [Show full text]
  • An Updated Synthesis of the Impacts of Ocean Acidification on Marine Biodiversity 2 3 ACKNOWLEDGEMENTS
    P a g e | 1 DRAFT FOR CBD PEER-REVIEW ONLY; NOT TO QUOTE; NOT TO CIRCULATE 1 An updated synthesis of the impacts of ocean acidification on marine biodiversity 2 3 ACKNOWLEDGEMENTS ....................................................................................................... 3 4 5 EXECUTIVE SUMMARY ....................................................................................................... 4 6 7 1. Background and introduction ............................................................................................... 8 8 1.1. Mandate of this review .......................................................................................................... 8 9 1.2. What is ocean acidification? ........................................................................................ 9 10 1.3. Re-visiting key knowledge gaps identified in the previous CBD review ................... 14 11 12 2. Scientific and policy framework ........................................................................................ 17 13 2.1. Steps towards global recognition and international science collaboration ................. 17 14 2.2. Intergovernmental interest in ocean acidification and actions to date ........................ 19 15 16 3. Global status and future trends of ocean acidification ....................................................... 23 17 3.1. Variability .................................................................................................................. 23 18 3.2. Modelled simulations of future ocean
    [Show full text]
  • Research on Ocean Acidification at the University of Malaya
    ADVANCINGResearch SUSTAINABLE on DEVELOPMENTOcean A INcidification LMEs DURING CLIMATE at theCHANGE University of Malaya Emienour Muzalina Mustafa, Choon-Weng Lee & Siew-Moi Phang Institute of Ocean & Earth Sciences, University of Malaya, Kuala Lumpur, Malaysia OCEANS IN A CHANGING CLIMATE OCEAN ↑ CO 2 ACIDIFICATION HUMAN IMPACTS: OCEAN MARINE POLLUTION WARMING BIOTA EUTROPHICATION OVERFISHING OCEAN DE- OXYGENATION Fig. 5. The palaeohistorical record of ocean pH demonstrates that present levels are unseen in the last 20 million years (Turley et al., 2006). Fig. 1. Projected regional changes in ocean chemistry likely to be experienced by particularly vulnerable ecosystems and compared to global-scale surface ocean changes. Global ocean surface averages (bottom) are shown, from left to right: CO2 partial pressure, pH(SWS) and calcite and aragonite saturation. Editorial, Marine Pollution Bulletin 60(2010): 787-792 Fig. 2. Photos of representatives of calcifying groups thought to be vulnerable to ocean acidification from top left to bottom right: pteropod (Jeremy Young, NHM), benthic foraminifer (James Rae, UBristol), coccolithophore (Jeremy Young, NHM), blue mussel (Frédéric Gazeau, Villefranche), sea urchin (Helen Findlay, PML), brittlestar (Sam Dupont, UGothenburg), tropical coral (Malcolm Shick, UMaine), coralline algae (Armin Form, IFM-GEOMAR), cold water coral (Karen Hissmann, IFM-GEOMAR). COMMERCIAL SPECIES IN ASIA THAT MAY BE IMPACTED BY OCEAN ACIDIFICATION Climate change and the oceans – What does the future hold? Jelle Bijma a,⇑, Hans-O. Pörtner a, Chris Yesson b, Alex D. Rogers Marine Pollution Bulletin 74 (2013) 495–505 Atmospheric pCO2 levels (ppmv CO2) that would be required to cause pH changes in Change in diversity as a function of ocean surface waters pH reduction for organisms living near the Ischia CO2 vents.
    [Show full text]
  • The Need for Fast Near-Term Climate Mitigation to Slow Feedbacks and Tipping Points
    The Need for Fast Near-Term Climate Mitigation to Slow Feedbacks and Tipping Points Critical Role of Short-lived Super Climate Pollutants in the Climate Emergency Background Note DRAFT: 27 September 2021 Institute for Governance Center for Human Rights and & Sustainable Development (IGSD) Environment (CHRE/CEDHA) Lead authors Durwood Zaelke, Romina Picolotti, Kristin Campbell, & Gabrielle Dreyfus Contributing authors Trina Thorbjornsen, Laura Bloomer, Blake Hite, Kiran Ghosh, & Daniel Taillant Acknowledgements We thank readers for comments that have allowed us to continue to update and improve this note. About the Institute for Governance & About the Center for Human Rights and Sustainable Development (IGSD) Environment (CHRE/CEDHA) IGSD’s mission is to promote just and Originally founded in 1999 in Argentina, the sustainable societies and to protect the Center for Human Rights and Environment environment by advancing the understanding, (CHRE or CEDHA by its Spanish acronym) development, and implementation of effective aims to build a more harmonious relationship and accountable systems of governance for between the environment and people. Its work sustainable development. centers on promoting greater access to justice and to guarantee human rights for victims of As part of its work, IGSD is pursuing “fast- environmental degradation, or due to the non- action” climate mitigation strategies that will sustainable management of natural resources, result in significant reductions of climate and to prevent future violations. To this end, emissions to limit temperature increase and other CHRE fosters the creation of public policy that climate impacts in the near-term. The focus is on promotes inclusive socially and environmentally strategies to reduce non-CO2 climate pollutants, sustainable development, through community protect sinks, and enhance urban albedo with participation, public interest litigation, smart surfaces, as a complement to cuts in CO2.
    [Show full text]
  • Biotribology Recent Progresses and Future Perspectives
    HOSTED BY Available online at www.sciencedirect.com Biosurface and Biotribology ] (]]]]) ]]]–]]] www.elsevier.com/locate/bsbt Biotribology: Recent progresses and future perspectives Z.R. Zhoua,n, Z.M. Jinb,c aSchool of Mechanical Engineering, Southwest Jiaotong University, Chengdu, China bSchool of Mechanical Engineering, Xian Jiaotong University, Xi'an, China cSchool of Mechanical Engineering, University of Leeds, Leeds, UK Received 6 January 2015; received in revised form 3 March 2015; accepted 3 March 2015 Abstract Biotribology deals with all aspects of tribology concerned with biological systems. It is one of the most exciting and rapidly growing areas of tribology. It is recognised as one of the most important considerations in many biological systems as to the understanding of how our natural systems work as well as how diseases are developed and how medical interventions should be applied. Tribological studies associated with biological systems are reviewed in this paper. A brief history, classification as well as current focuses on biotribology research are analysed according to typical papers from selected journals and presentations from a number of important conferences in this area. Progress in joint tribology, skin tribology and oral tribology as well as other representative biological systems is presented. Some remarks are drawn and prospects are discussed. & 2015 Southwest Jiaotong University. Production and hosting by Elsevier B.V. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). Keywords: Biotribology; Biosurface; Joint; Skin; Dental Contents 1. Introduction ...................................................................................2 2. Classifications and focuses of current research. ..........................................................3 3. Joint tribology .................................................................................4 3.1.
    [Show full text]
  • Climate Change and Ocean Acidification Impacts on Lower
    EGU Journal Logos (RGB) Open Access Open Access Open Access Advances in Annales Nonlinear Processes Geosciences Geophysicae in Geophysics Open Access Open Access Natural Hazards Natural Hazards and Earth System and Earth System Sciences Sciences Discussions Open Access Open Access Atmospheric Atmospheric Chemistry Chemistry and Physics and Physics Discussions Open Access Open Access Atmospheric Atmospheric Measurement Measurement Techniques Techniques Discussions Open Access Biogeosciences, 10, 5831–5854, 2013 Open Access www.biogeosciences.net/10/5831/2013/ Biogeosciences doi:10.5194/bg-10-5831-2013 Biogeosciences Discussions © Author(s) 2013. CC Attribution 3.0 License. Open Access Open Access Climate Climate of the Past of the Past Discussions Climate change and ocean acidification impacts on lower trophic Open Access Open Access levels and the export of organic carbon to the deepEarth ocean System Earth System Dynamics 1 1 1 2 1 Dynamics A. Yool , E. E. Popova , A. C. Coward , D. Bernie , and T. R. Anderson Discussions 1National Oceanography Centre, University of Southampton Waterfront Campus, European Way, Southampton SO14 3ZH, UK Open Access Open Access 2Met Office Hadley Centre, FitzRoy Road, Exeter EX1 3PB, UK Geoscientific Geoscientific Instrumentation Instrumentation Correspondence to: A. Yool ([email protected]) Methods and Methods and Received: 29 January 2013 – Published in Biogeosciences Discuss.: 25 February 2013 Data Systems Data Systems Revised: 18 July 2013 – Accepted: 19 July 2013 – Published: 5 September 2013 Discussions
    [Show full text]
  • Understanding the Ocean's Biological Carbon Pump in the Past: Do We Have the Right Tools?
    Manuscript prepared for Earth-Science Reviews Date: 3 March 2017 Understanding the ocean’s biological carbon pump in the past: Do we have the right tools? Dominik Hülse1, Sandra Arndt1, Jamie D. Wilson1, Guy Munhoven2, and Andy Ridgwell1, 3 1School of Geographical Sciences, University of Bristol, Clifton, Bristol BS8 1SS, UK 2Institute of Astrophysics and Geophysics, University of Liège, B-4000 Liège, Belgium 3Department of Earth Sciences, University of California, Riverside, CA 92521, USA Correspondence to: D. Hülse ([email protected]) Keywords: Biological carbon pump; Earth system models; Ocean biogeochemistry; Marine sedi- ments; Paleoceanography Abstract. The ocean is the biggest carbon reservoir in the surficial carbon cycle and, thus, plays a crucial role in regulating atmospheric CO2 concentrations. Arguably, the most important single com- 5 ponent of the oceanic carbon cycle is the biologically driven sequestration of carbon in both organic and inorganic form- the so-called biological carbon pump. Over the geological past, the intensity of the biological carbon pump has experienced important variability linked to extreme climate events and perturbations of the global carbon cycle. Over the past decades, significant progress has been made in understanding the complex process interplay that controls the intensity of the biological 10 carbon pump. In addition, a number of different paleoclimate modelling tools have been developed and applied to quantitatively explore the biological carbon pump during past climate perturbations and its possible feedbacks on the evolution of the global climate over geological timescales. Here we provide the first, comprehensive overview of the description of the biological carbon pumpin these paleoclimate models with the aim of critically evaluating their ability to represent past marine 15 carbon cycle dynamics.
    [Show full text]