An Assessment of Marine Ecosystem Damage from the Penglai 19-3 Oil Spill Accident
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Vegetation Demographics in Earth System Models: a Review of Progress and Priorities
Lawrence Berkeley National Laboratory Recent Work Title Vegetation demographics in Earth System Models: A review of progress and priorities. Permalink https://escholarship.org/uc/item/3912p4m3 Journal Global change biology, 24(1) ISSN 1354-1013 Authors Fisher, Rosie A Koven, Charles D Anderegg, William RL et al. Publication Date 2018 DOI 10.1111/gcb.13910 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Received: 11 April 2017 | Revised: 12 August 2017 | Accepted: 17 August 2017 DOI: 10.1111/gcb.13910 RESEARCH REVIEW Vegetation demographics in Earth System Models: A review of progress and priorities Rosie A. Fisher1 | Charles D. Koven2 | William R. L. Anderegg3 | Bradley O. Christoffersen4 | Michael C. Dietze5 | Caroline E. Farrior6 | Jennifer A. Holm2 | George C. Hurtt7 | Ryan G. Knox2 | Peter J. Lawrence1 | Jeremy W. Lichstein8 | Marcos Longo9 | Ashley M. Matheny10 | David Medvigy11 | Helene C. Muller-Landau12 | Thomas L. Powell2 | Shawn P. Serbin13 | Hisashi Sato14 | Jacquelyn K. Shuman1 | Benjamin Smith15 | Anna T. Trugman16 | Toni Viskari12 | Hans Verbeeck17 | Ensheng Weng18 | Chonggang Xu4 | Xiangtao Xu19 | Tao Zhang8 | Paul R. Moorcroft20 1National Center for Atmospheric Research, Boulder, CO, USA 2Lawrence Berkeley National Laboratory, Berkeley, CA, USA 3Department of Biology, University of Utah, Salt Lake City, UT, USA 4Los Alamos National Laboratory, Los Alamos, NM, USA 5Department of Earth and Environment, Boston University, Boston, MA, USA 6Department of Integrative Biology, -
Persistent Organic Pollutants in Marine Plankton from Puget Sound
Control of Toxic Chemicals in Puget Sound Phase 3: Persistent Organic Pollutants in Marine Plankton from Puget Sound 1 2 Persistent Organic Pollutants in Marine Plankton from Puget Sound By James E. West, Jennifer Lanksbury and Sandra M. O’Neill March, 2011 Washington Department of Ecology Publication number 11-10-002 3 Author and Contact Information James E. West Washington Department of Fish and Wildlife 1111 Washington St SE Olympia, WA 98501-1051 Jennifer Lanksbury Current address: Aquatic Resources Division Washington Department of Natural Resources (DNR) 950 Farman Avenue North MS: NE-92 Enumclaw, WA 98022-9282 Sandra M. O'Neill Northwest Fisheries Science Center Environmental Conservation Division 2725 Montlake Blvd. East Seattle, WA 98112 Funding for this study was provided by the U.S. Environmental Protection Agency, through a Puget Sound Estuary Program grant to the Washington Department of Ecology (EPA Grant CE- 96074401). Any use of product or firm names in this publication is for descriptive purposes only and does not imply endorsement by the authors or the Department of Fish and Wildlife. 4 Table of Contents Table of Contents................................................................................................................................................... 5 List of Figures ....................................................................................................................................................... 7 List of Tables ....................................................................................................................................................... -
Decontaminating Terrestrial Oil Spills: a Comparative Assessment of Dog Fur, Human Hair, Peat Moss and Polypropylene Sorbents
environments Article Decontaminating Terrestrial Oil Spills: A Comparative Assessment of Dog Fur, Human Hair, Peat Moss and Polypropylene Sorbents Megan L. Murray *, Soeren M. Poulsen and Brad R. Murray School of Life Sciences, University of Technology Sydney, PO Box 123, Sydney, NSW 2007, Australia; [email protected] (S.M.P.); [email protected] (B.R.M.) * Correspondence: [email protected] Received: 4 June 2020; Accepted: 4 July 2020; Published: 8 July 2020 Abstract: Terrestrial oil spills have severe and continuing consequences for human communities and the natural environment. Sorbent materials are considered to be a first line of defense method for directly extracting oil from spills and preventing further contaminant spread, but little is known on the performance of sorbent products in terrestrial environments. Dog fur and human hair sorbent products were compared to peat moss and polypropylene sorbent to examine their relative effectiveness in adsorbing crude oil from different terrestrial surfaces. Crude oil spills were simulated using standardized microcosm experiments, and contaminant adsorbency was measured as percentage of crude oil removed from the original spilled quantity. Sustainable-origin absorbents made from dog fur and human hair were equally effective to polypropylene in extracting crude oil from non- and semi-porous land surfaces, with recycled dog fur products and loose-form hair showing a slight advantage over other sorbent types. In a sandy terrestrial environment, polypropylene sorbent was significantly better at adsorbing spilled crude oil than all other tested products. Keywords: crude oil; petroleum contamination; disaster management; land pollution 1. Introduction Crude oils are complex in composition and form the basis of many materials and fuels in high demand by global communities [1]. -
The Foundation for Global Action on Persistent Organic Pollutants: a United States Perspective
The Foundation for Global Action on Persistent Organic Pollutants: A United States Perspective Office of Research and Development Washington, DC 20460 EPA/600/P-01/003F NCEA-I-1200 March 2002 www.epa.gov Disclaimer Mention of trade names or commercial products does not constitute endorsement or recommendation for use. Cover page credits: Bald eagle, U.S. FWS; mink, Joe McDonald/Corbis.com; child, family photo, Jesse Paul Nagaruk; polar bear, U.S. FWS; killer whales, Craig Matkin. Contents Contributors ................................................................................................. vii Executive Summary ....................................................................................... ix Chapter 1. Genesis of the Global Persistent Organic Pollutant Treaty ............ 1-1 Why Focus on POPs? ................................................................................................. 1-2 The Four POPs Parameters: Persistence, Bioaccumulation, Toxicity, Long-Range Environmental Transport ......................................................... 1-5 Persistence ......................................................................................................... 1-5 Bioaccumulation ................................................................................................. 1-6 Toxicity .............................................................................................................. 1-7 Long-Range Environmental Transport .................................................................. 1-7 POPs -
Emergent Biogeography of Microbial Communities in a Model Ocean
REPORTS germ insects not only uncovers those features es- mRNA localization indeed appears to be an sential to this developmental mode but also sheds important component of long-germ embryogene- light on how the bcd-dependent anterior patterning sis, perhaps even playing a role in the transition program might have evolved. Through analysis of from the ancestral short-germ to the derived long- the regulation of the trunk gap gene Kr in Dro- germ fate. sophila and Nasonia,wehavebeenabletodem- onstrate that anterior repression of Kr is essential References and Notes for head and thorax formation and is a common 1. G. K. Davis, N. H. Patel, Annu. Rev. Entomol. 47, 669 (2002). feature of long-germ patterning. Both insects 2. T. Berleth et al., EMBO J. 7, 1749 (1988). accomplish this task through maternal, anteriorly 3. W. Driever, C. Nusslein-Volhard, Cell 54, 83 (1988). localized factors that either indirectly (Drosophila) 4. J. Lynch, C. Desplan, Curr. Biol. 13, R557 (2003). or directly (Nasonia) repress Kr and, hence, trunk 5. J. A. Lynch, A. E. Brent, D. S. Leaf, M. A. Pultz, C. Desplan, Nature 439, 728 (2006). fates. In Drosophila, the terminal system and bcd 6. J. Savard et al., Genome Res. 16, 1334 (2006). regulate expression of gap genes, including Dm-gt, 7. G. Struhl, P. Johnston, P. A. Lawrence, Cell 69, 237 (1992). that repress Dm-Kr. Nasonia’s bcd-independent 8. A. Preiss, U. B. Rosenberg, A. Kienlin, E. Seifert, long-germ embryos must solve the same problem, H. Jackle, Nature 313, 27 (1985). Fig. 4. -
Meta-Ecosystems: a Theoretical Framework for a Spatial Ecosystem Ecology
Ecology Letters, (2003) 6: 673–679 doi: 10.1046/j.1461-0248.2003.00483.x IDEAS AND PERSPECTIVES Meta-ecosystems: a theoretical framework for a spatial ecosystem ecology Abstract Michel Loreau1*, Nicolas This contribution proposes the meta-ecosystem concept as a natural extension of the Mouquet2,4 and Robert D. Holt3 metapopulation and metacommunity concepts. A meta-ecosystem is defined as a set of 1Laboratoire d’Ecologie, UMR ecosystems connected by spatial flows of energy, materials and organisms across 7625, Ecole Normale Supe´rieure, ecosystem boundaries. This concept provides a powerful theoretical tool to understand 46 rue d’Ulm, F–75230 Paris the emergent properties that arise from spatial coupling of local ecosystems, such as Cedex 05, France global source–sink constraints, diversity–productivity patterns, stabilization of ecosystem 2Department of Biological processes and indirect interactions at landscape or regional scales. The meta-ecosystem Science and School of perspective thereby has the potential to integrate the perspectives of community and Computational Science and Information Technology, Florida landscape ecology, to provide novel fundamental insights into the dynamics and State University, Tallahassee, FL functioning of ecosystems from local to global scales, and to increase our ability to 32306-1100, USA predict the consequences of land-use changes on biodiversity and the provision of 3Department of Zoology, ecosystem services to human societies. University of Florida, 111 Bartram Hall, Gainesville, FL Keywords 32611-8525, -
Effects of Oil on Wildlife and Habitat the U.S
U.S. Fish & Wildlife Service Effects of Oil on Wildlife and Habitat The U.S. Fish and Wildlife Weathering reduces the more toxic elements in oil products over time as Service is the federal exposure to air, sunlight, wave and tidal action, and certain microscopic agency responsible for organisms degrade and disperse many of the nation’s fish oil. Weathering rates depend on factors such as type of oil, weather, and wildlife resources and temperature, and the type of shoreline one of the primary trustees and bottom that occur in the spill area. for fish, wildlife and habitat Types of Oil Although there are different types of at oil spills. oil, the oil involved in the Deepwater Horizon spill is classified as light crude. The Service is actively involved Light crude is moderately volatile and in response efforts related to the can leave a residue of up to one third of Deepwater Horizon oil spill that the amount spilled after several days. It occurred in the Gulf of Mexico on April leaves a film on intertidal resources and 20, 2010. Many species of wildlife, has the potential to cause long-term including some that are threatened or contamination. endangered, live along the Gulf Coast and could be impacted by the spill. Impacts to Wildlife and Habitat Oil causes harm to wildlife through Oil spills affect wildlife and their physical contact, ingestion, inhalation habitats in many ways. The severity and absorption. Floating oil can of the injury depends on the type and contaminate plankton, which includes quantity of oil spilled, the season and algae, fish eggs, and the larvae of MacKenzie FWS/Tom weather, the type of shoreline, and the various invertebrates. -
Chapter 4 – Steady State Models
CHAPTER 4 Steady State Models X.-Z. Kong, F.-L. Xu1, W. He, W.-X. Liu, B. Yang Peking University, Beijing, China 1Corresponding author: E-mail: xufl@urban.pku.edu.cn OUTLINE 4.1 Steady State Model: Ecopath as an 4.2.4.2 Changes in Ecosystem Example 66 Functioning 79 4.1.1 Steady State Model 66 4.2.4.3 Collapse in the Food 4.1.2 Ecopath Model 66 Web: Differences in 4.1.3 Future Perspectives 68 Structure 81 4.2.4.4 Toward an Immature 4.2 Ecopath Model for a Large Chinese but Stable Ecosystem 83 Lake: A Case Study 68 4.2.4.5 Potential Driving 4.2.1 Introduction 68 Factors and 4.2.2 Study Site 70 Underlying 4.2.3 Model Development 73 Mechanisms 84 4.2.3.1 Model Construction 4.2.4.6 Hints for Future Lake and Parameterization 73 Fishery and 4.2.3.2 Evaluation of Ecosystem Restoration 85 Functioning 74 4.2.3.3 Determination of 4.3 Conclusions 86 Trophic Level 76 References 86 4.2.4 Results and Discussion 76 4.2.4.1 Basic Model Performance 76 Ecological Model Types, Volume 28 Ó 2016 Elsevier B.V. http://dx.doi.org/10.1016/B978-0-444-63623-2.00004-9 65 All rights reserved. 66 4. STEADY STATE MODELS 4.1 STEADY STATE MODEL: ECOPATH AS AN EXAMPLE 4.1.1 Steady State Model Steady state ecological models are established to describe conditions in which the modeled components (mass or energy) are stable, i.e., do not change over time (Jørgensen and Fath, 2011). -
Models for an Ecosystem Approach to Fisheries
ISSN 0429-9345 FAO FISHERIES 477 TECHNICAL PAPER 477 Models for an ecosystem approach to fisheries Models for an ecosystem approach to fisheries This report reviews the methods available for assessing the impacts of interactions between species and fisheries and their implications for marine fisheries management. A brief description of the various modelling approaches currently in existence is provided, highlighting in particular features of these models that have general relevance to the field of ecosystem approach to fisheries (EAF). The report concentrates on the currently available models representative of general types such as bionergetic models, predator-prey models and minimally realistic models. Short descriptions are given of model parameters, assumptions and data requirements. Some of the advantages, disadvantages and limitations of each of the approaches in addressing questions pertaining to EAF are discussed. The report concludes with some recommendations for moving forward in the development of multispecies and ecosystem models and for the prudent use of the currently available models as tools for provision of scientific information on fisheries in an ecosystem context. FAO Cover: Illustration by Elda Longo FAO FISHERIES Models for an ecosystem TECHNICAL PAPER approach to fisheries 477 by Éva E. Plagányi University of Cape Town South Africa FOOD AND AGRICULTURE AND ORGANIZATION OF THE UNITED NATIONS Rome, 2007 The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. -
The Role and Regulation of Dispersants in Oil Spill Response
Fighting Chemicals with Chemicals: The Role and Regulation of Dispersants in Oil Spill Response Charles L. Franklin and Lori J. Warner or most Americans, and many American environmen- dentnews.gov/ (last visited July 17, 2011) (searching reported tal lawyers, the tragic Deepwater Horizon oil spill of incidents in which dispersants were evaluated and used). Even 2010 provided the first close-up look at the role that so, their use has not been without controversy. One of the oil dispersants and surfactant chemicals (dispersants) first documented uses of dispersing agents occurred in 1967 Fplay in modern-day oil spill response efforts. While dispersants during the response to the Torrey Canyon tanker spill off the have been used for decades, dispersants played a particularly English Coast. DOT, EPA, The Exxon Valdez Oil Spill: A Report pivotal, if controversial role, in the Gulf spill response, osten- to the President, Doc. No. OSWER-89-VALDZ, (May 1989) sibly helping to reduce the onshore impact of the release. Dis- [herinafter Exxon Valdez Report], App. D-23. This early effort persants were a workhorse of the recovery effort, and in turn, proved catastrophic, however, as the chemicals used in the arguably might be credited with limiting the land impacts of effort—little more than industrial degreasing agents devel- the largest spill in history. For some, however, the central role oped for cleaning tanks—resulted in an “ecological disaster” that chemical dispersants played in the Gulf cleanup effort in which extensive mortalities of animals and algae occurred is more a cause for question than credit. This article reviews immediately, and the natural recovery was severely slowed and the historic use and regulation of oil dispersants in oil spill still incomplete in some areas ten years later. -
Marine Pollution in the Caribbean: Not a Minute to Waste
Public Disclosure Authorized Public Disclosure Authorized Marine Public Disclosure Authorized Pollution in the Caribbean: Not a Minute to Waste Public Disclosure Authorized Standard Disclaimer: This volume is a product of the staff of the International Bank for Reconstruction and Development/the World Bank. The findings, interpreta- tions, and conclusions expressed in this paper do not necessarily reflect the views of the Executive Directors of the World Bank or the governments they represent. The World Bank does not guarantee the accuracy of the data included in this work. The boundaries, colors, denominations, and other information shown on any map in this work do not imply any judgment on the part of the World Bank concerning the legal status of any territory or the endorsement or acceptance of such boundaries. Copyright Statement: The material in this publication is copyrighted. Copying and/or transmitting portions or all of this work without permission may be a violation of applicable law. The International Bank for Reconstruction and Development/ The World Bank encourages dissemination of its work and will normally grant per- mission to reproduce portions of the work promptly. For permission to photocopy or reprint any part of this work, please send a request with complete information to the Copyright Clearance Center, Inc., 222 Rose- wood Drive, Danvers, MA 01923, USA, telephone 978-750-8400, fax 978-750-4470, http://www.copyright.com/. All other queries on rights and licenses, including subsidiary rights, should be addressed to the Office of the Publisher, The World Bank, 1818 H Street NW, Washington, DC 20433, USA, fax 202-522-2422, e-mail [email protected]. -
Fate of Marine Oil Spills
FATE OF MARINE OIL SPILLS TECHNICAL INFORMATION PAPER 2 Introduction When oil is spilled into the sea it undergoes a number of physical and chemical changes, some of which lead to its removal from the sea surface, while others cause it to persist. The fate of spilled oil in the marine environment depends upon factors such as the quantity spilled, the oil’s initial physical and chemical characteristics, the prevailing climatic and sea conditions and whether the oil remains at sea or is washed ashore. An understanding of the processes involved and how they interact to alter the nature, composition and behaviour of oil with time is fundamental to all aspects of oil spill response. It may, for example, be possible to predict with confidence that oil will not reach vulnerable resources due to natural dissipation, so that clean-up operations will not be necessary. When an active response is required, the type of oil and its probable behaviour will determine which response options are likely to be most effective. This paper describes the combined effects of the various natural processes acting on spilled oil, collectively known as ‘weathering’. Factors which determine whether or not the oil is likely to persist in the marine environment are considered together with the implications for response operations. The fate of oil spilled in the marine environment has important implications for all aspects of a response and, consequently, this paper should be read in conjunction with others in this series of Technical Information Papers. Properties of oil Crude oils of different origin vary widely in their physical and chemical properties, whereas many refined products tend to have well-defined properties irrespective of the crude oil from which they are derived.