Impacts of Plastic Pollution on Ecosystem Services, Sustainable Development Goals, and Need to Focus on Circular Economy and Policy Interventions
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An Assessment Report on Microplastics
An Assessment Report on Microplastics This document was prepared by B Stevens, North Carolina Coastal Federation Table of Contents What are Microplastics? 2 Where Do Microplastics Come From? 3 Primary Sources 3 Secondary Sources 5 What are the Consequences of Microplastics? 7 Marine Ecosystem Health 7 Water Quality 8 Human Health 8 What Policies/Practices are in Place to Regulate Microplastics? 10 Regional Level 10 Outer Banks, North Carolina 10 Other United States Regions 12 State Level 13 Country Level 14 United States 14 Other Countries 15 International Level 16 Conventions 16 Suggested World Ban 17 International Campaigns 18 What Solutions Already Exist? 22 Washing Machine Additives 22 Faucet Filters 23 Advanced Wastewater Treatment 24 Plastic Alternatives 26 What Should Be Done? 27 Policy Recommendations for North Carolina 27 Campaign Strategy for the North Carolina Coastal Federation 27 References 29 1 What are Microplastics? The category of ‘plastics’ is an umbrella term used to describe synthetic polymers made from either fossil fuels (petroleum) or biomass (cellulose) that come in a variety of compositions and with varying characteristics. These polymers are then mixed with different chemical compounds known as additives to achieve desired properties for the plastic’s intended use (OceanCare, 2015). Plastics as litter in the oceans was first reported in the early 1970s and thus has been accumulating for at least four decades, although when first reported the subject drew little attention and scientific studies focused on entanglements, ‘ghost fishing’, and ingestion (Andrady, 2011). Today, about 60-90% of all marine litter is plastic-based (McCarthy, 2017), with the total amount of plastic waste in the oceans expected to increase as plastic consumption also increases and there remains a lack of adequate reduce, reuse, recycle, and waste management tactics across the globe (GreenFacts, 2013). -
SIGMA-ALDRICH Sigma-Aldrich.Com Material Safety Data Sheet Version 5.0 Revision Date 12/13/2012 Print Date 12/10/2013
SIGMA-ALDRICH sigma-aldrich.com Material Safety Data Sheet Version 5.0 Revision Date 12/13/2012 Print Date 12/10/2013 1. PRODUCT AND COMPANY IDENTIFICATION Product name : PCB No 77 Product Number : 35496 Brand : Fluka Supplier : Sigma-Aldrich 3050 Spruce Street SAINT LOUIS MO 63103 USA Telephone : +1 800-325-5832 Fax : +1 800-325-5052 Emergency Phone # (For : (314) 776-6555 both supplier and manufacturer) Preparation Information : Sigma-Aldrich Corporation Product Safety - Americas Region 1-800-521-8956 2. HAZARDS IDENTIFICATION Emergency Overview OSHA Hazards No known OSHA hazards GHS Classification Acute toxicity, Oral (Category 1) Specific target organ toxicity - repeated exposure (Category 2) Acute aquatic toxicity (Category 1) Chronic aquatic toxicity (Category 1) GHS Label elements, including precautionary statements Pictogram Signal word Danger Hazard statement(s) H300 Fatal if swallowed. H373 May cause damage to organs through prolonged or repeated exposure. H410 Very toxic to aquatic life with long lasting effects. Precautionary statement(s) P264 Wash hands thoroughly after handling. P273 Avoid release to the environment. P301 + P310 IF SWALLOWED: Immediately call a POISON CENTER or doctor/ physician. P501 Dispose of contents/ container to an approved waste disposal plant. HMIS Classification Health hazard: 4 Flammability: 1 Physical hazards: 0 NFPA Rating Health hazard: 4 Fire: 1 Fluka - 35496 Page 1 of 7 Reactivity Hazard: 0 Potential Health Effects Inhalation May be harmful if inhaled. May cause respiratory tract irritation. Skin May be harmful if absorbed through skin. May cause skin irritation. Eyes May cause eye irritation. Ingestion May be fatal if swallowed. 3. COMPOSITION/INFORMATION ON INGREDIENTS Synonyms : 3,3′,4,4′-PCB 3,3′,4,4′-Tetrachlorobiphenyl Formula : C12H6Cl4 Molecular Weight : 291.99 g/mol No ingredients are hazardous according to OHSA criteria. -
RESIDENTIAL ENVIRONMENTAL HAZARDS: a Guide for Homeowners, Homebuyers, Landlords and Tenants 2011
CALIFORNIA ENVIRONMENTAL PROTECTION AGENCY RESIDENTIAL ENVIRONMENTAL HAZARDS: A Guide For Homeowners, Homebuyers, Landlords and Tenants 2011 This guide was originally developed by M. B. Gilbert Associates, under contract with the California Department of Real Estate in cooperation with the California Department of Health Services. The 2005 edition was prepared by the California Department of Toxic Substances Control, in cooperation with the California Air Resources Board and the California Department of Health Services, and meets all State and Federal guidelines and lead disclosure requirements pursuant to the Residential Lead-Based Paint Hazard Reduction Act of 1992. The 2005 edition incorporates the Federal “Protect Your Family from Lead” pamphlet. The 2011 update was developed California Department of Toxic Substances Control. This booklet is offered for information purposes only, not as a reflection of the position of the administration of the State of California. Residential Environmental Hazards Booklet Page 1 of 48 January 2011 Table of Contents INTRODUCTION 3 CHAPTER I ASBESTOS 3 CHAPTER II CARBON MONOXIDE 10 CHAPTER III FORMALDEHYDE 13 CHAPTER IV HAZARDOUS WASTE 17 CHAPTER V HOUSEHOLD HAZARDOUS WASTE 21 CHAPTER VI LEAD 24 CHAPTER VII MOLD 31 CHAPTER VIII RADON 36 APPENDIX A LIST OF FEDERAL AND STATE AGENCIES 42 APPENDIX B GLOSSARY 46 Residential Environmental Hazards Booklet Page 2 of 48 January 2011 Introduction The California Departments of Real Estate and Health Services originally prepared this booklet in response to the California legislative mandate (Chapter 969, Statutes of 1989, AB 983, Bane) to inform the homeowner and prospective homeowner about environmental hazards located on and affecting residential property. -
Endocrine Disruption: Where Are We with Hazard and Risk Assessment? 2
1 Title: Endocrine disruption: where are we with hazard and risk assessment? 2 3 Running head: Hazard and risk assessment of endocrine disrupters 4 Katherine Coady*†, Peter Matthiessen‡, Holly M. Zahner§1, Jane Staveleyǁ; Daniel J. Caldwell#; 5 Steven L. Levine††, Leon Earl Gray Jr‡‡, Christopher J. Borgert§§ 6 7 † The Dow Chemical Company, Midland, MI, USA; 8 Telephone: 989-636-7423; Fax: 989-638-2425; e-mail: [email protected]; ‡Independent 9 Consultant, Llanwrtyd Wells, UK; e-mail: [email protected] ; § United States 10 Food and Drug Administration, Center for Veterinary Medicine, Rockville, MD, USA; email: 11 [email protected] ; ǁExponent Inc., Cary, NC, USA; email: [email protected] ; 12 #Johnson & Johnson, New Brunswick, New Jersey, USA; email [email protected] ; 13 ††Monsanto Company, St. Louis, MO, USA;email [email protected]; ‡‡USEPA, 14 ORD, NHEERL, TAD, RTB. RTP, NC, USA; email: [email protected] ; §§Applied 15 Pharmacology and Toxicology, Inc., and, Center for Environmental and Human Toxicology, 16 University of Florida, Gainesville, FL, USA; e-mail: [email protected] 17 1The views presented in this article do not necessarily reflect those of the Food and Drug 18 Administration 19 * Corresponding Author: 20 Katherine Coady 21 The Dow Chemical Company, 1803 Building, Washington Street, Midland MI, USA, 48674. 22 Email address: [email protected] PeerJ Preprints | https://doi.org/10.7287/peerj.preprints.2580v1 | CC0 Open Access | rec: 4 Nov 2016, publ: 23 24 ABSTRACT 25 Approaches to assessing endocrine disruptors (EDs) differ across the globe, with some 26 regulatory environments using a hazard-based approach, while others employ risk-based 27 analyses. -
Settlement Patterns, Chiefdom Variability, and the Development of Early States in North China
JOURNAL OF ANTHROPOLOGICAL ARCHAEOLOGY 15, 237±288 (1996) ARTICLE NO. 0010 Settlement Patterns, Chiefdom Variability, and the Development of Early States in North China LI LIU School of Archaeology, La Trobe University, Melbourne, Australia Received June 12, 1995; revision received May 17, 1996; accepted May 26, 1996 In the third millennium B.C., the Longshan culture in the Central Plains of northern China was the crucial matrix in which the ®rst states evolved from the basis of earlier Neolithic societies. By adopting the theoretical concept of the chiefdom and by employing the methods of settlement archaeology, especially regional settlement hierarchy and rank-size analysis, this paper introduces a new approach to research on the Longshan culture and to inquiring about the development of the early states in China. Three models of regional settlement pattern correlating to different types of chiefdom systems are identi®ed. These are: (1) the centripetal regional system in circumscribed regions representing the most complex chiefdom organizations, (2) the centrifugal regional system in semi-circumscribed regions indicating less integrated chiefdom organization, and (3) the decentral- ized regional system in noncircumscribed regions implying competing and the least complex chief- dom organizations. Both external and internal factors, including geographical condition, climatic ¯uctuation, Yellow River's changing course, population movement, and intergroup con¯ict, played important roles in the development of complex societies in the Longshan culture. As in many cultures in other parts of the world, the early states in China emerged from a system of competing chiefdoms, which was characterized by intensive intergroup con¯ict and frequent shifting of political centers. -
Addicted to Plastic: Microplastic Pollution and Prevention
Addicted to plastic: Microplastic pollution and prevention This briefing outlines global issues relating to microplastic pollution and its prevention. Microplastics are particles that are smaller than 5mm and are formed by the fragmentation of larger plastic items or are intentionally or unintentionally released in the form of manufactured beads, granules, fibres and fragments. Once in the environment they are very difficult to remove and have the potential to accumulate in soil, freshwater and marine environments causing a range of known and unknown impacts. Contents Summary .............................................................................................................................................. 3 Recommendations ............................................................................................................................ 5 Our addiction to plastic .................................................................................................................. 6 In detail ................................................................................................................................................. 7 Sources of microplastics ........................................................................................................ 7 Impacts of microplastics ........................................................................................................ 8 Removal of microplastics through water treatment processes ........................... 10 Accumulation of microplastics ........................................................................................ -
Henan Wastewater Management and Water Supply Sector Project (11 Wastewater Management and Water Supply Subprojects)
Environmental Assessment Report Summary Environmental Impact Assessment Project Number: 34473-01 February 2006 PRC: Henan Wastewater Management and Water Supply Sector Project (11 Wastewater Management and Water Supply Subprojects) Prepared by Henan Provincial Government for the Asian Development Bank (ADB). The summary environmental impact assessment is a document of the borrower. The views expressed herein do not necessarily represent those of ADB’s Board of Directors, Management, or staff, and may be preliminary in nature. CURRENCY EQUIVALENTS (as of 02 February 2006) Currency Unit – yuan (CNY) CNY1.00 = $0.12 $1.00 = CNY8.06 The CNY exchange rate is determined by a floating exchange rate system. In this report a rate of $1.00 = CNY8.27 is used. ABBREVIATIONS ADB – Asian Development Bank BOD – biochemical oxygen demand COD – chemical oxygen demand CSC – construction supervision company DI – design institute EIA – environmental impact assessment EIRR – economic internal rate of return EMC – environmental management consultant EMP – environmental management plan EPB – environmental protection bureau GDP – gross domestic product HPG – Henan provincial government HPMO – Henan project management office HPEPB – Henan Provincial Environmental Protection Bureau HRB – Hai River Basin H2S – hydrogen sulfide IA – implementing agency LEPB – local environmental protection bureau N – nitrogen NH3 – ammonia O&G – oil and grease O&M – operation and maintenance P – phosphorus pH – factor of acidity PMO – project management office PM10 – particulate -
New Toxic Time Bomb: Contaminants in Marine Plastic Pollution
Contaminants in Marine Plastic Pollution: ‘the new toxic time-bomb’ Dr Mariann Lloyd-Smith Joanna Immig March 2016 1 This report is intended to be a living document and will be updated as new and important information is released. Contents 1. Summary 2. Production and Wastes 2.1 Types of Plastics 2.2 Plastics’ Toxic Additives 2.3 Degradation of Plastic 3. Levels of the Pollutants in Resin Pellets 3.1 Contamination of Pellets in the Australian Marine Environment 3.2 International Pellet Watch 3.3 Perfluorinated Compounds (PFCs) 4. Level of Pollutants in Other Forms of Microplastics 4.1 Polystyrene Foam in the Marine Environment 5. Chemical Impacts 5.1 Laboratory Tests 5.2 Contamination of Australian Seabirds 5.3 Microplastics and Baleen Whale Species 6. Conclusion 6.1 Recommendations Contaminants in Marine Plastic Pollution 2 1. Summary The United Nations Environment Program called marine plastics the “new toxic time- bomb”. Marine plastic is not only entangling and drowning wildlife, it is being mistaken for food and ingested along with its toxic contaminants. Marine plastics and in particular microplastics, provide a global transport medium for the most toxic chemicals into the marine food chain and ultimately, to humans. Persistent bioaccumulative toxins (PBTs) contaminate all forms of marine plastics (eg resin pellets, microbeads, polystyrene and microplastic debris like tiny threads from ropes and nets. Because microplastics have larger surface area to volume ratio, they accumulate and concentrate PBTs and metals. Once in marine environments plastic polymers undergo some weathering and degradation, aiding the adsorption of PBTs from the seawater, where they exist at very low concentrations. -
Tackling Marine Plastic Pollution
REPORT INT 2019 WWF POLICY PAPER TACKLING MARINE PLASTIC POLLUTION It is time to begin negotiations on a new legally binding agreement Tackling marine plastic pollution It is time to begin negotiations on a new global legally binding agreement Summary points • Marine plastic pollution has reached crisis levels. It is poisoning marine life and affecting human health and livelihoods in ways we are only now beginning to understand. It is estimated that around eight million tonnes of plastic waste enters the world’s oceans every year, threatening marine life, coastal livelihoods and potentially even human health. It is a global problem that urgently requires a global response. • As of today, there is no international treaty in place dedicated to fully tackling the issue. The existing legal framework covering marine plastic pollution is fragmented and ineffective, and does not provide the tools necessary for an effective global response to the problem. This issue cannot be solved on a national or regional level, or through non-binding, voluntary measures alone. It requires coordinated international action, shared responsibility and a common approach. • A new legally binding agreement is needed—one which clearly stipulates the vision (goal of zero discharge of plastic into the ocean), the ambition (strict national reduction targets), and the required means and measures for getting there (a comprehensive review system and implementation support architecture). The main elements of such an agreement, as proposed by WWF, are laid down in this paper. • WWF is calling on states to begin negotiations, as soon as possible, on a new international legally binding agreement to tackle marine plastic pollution. -
Spatial Heterogeneity of Microplastic Pollution on Cape Cod Beaches and the Impacts of Different Hydrographic Sources
Microplastic pollution on Cape Cod beaches 1 Plastic Beach (The Arrival) Spatial heterogeneity of microplastic pollution on Cape Cod beaches and the impacts of different hydrographic sources Hector Ricardo Salazar Connecticut College Project Mentors: Rut Pedrosa Pamies*, JC Weber, Maureen Conte Ecosystems Center Marine Biological Laboratory Semester in Environmental Science Class of 2018 *Corresponding author: Rut Pedrosa Pamies [email protected] Microplastic pollution on Cape Cod beaches 2 ABSTRACT Plastic has become a large source of global pollution; it has entered our marine ecosystems and we are only beginning to see the effects on ecosystem health, animals, and humans. Plastic is a great threat to the environment due to its non-biodegradable properties and long resonance time once in the environment. Plastic debris now contaminate sandy, estuarine, and subtidal habitats in the Europe, Asia, and the Americas, with the global extent of microplastic contamination remaining unknown. This study aimed to assess the distribution of microplastics on Cape Cod beaches, and understand how microplastic contamination is influenced by various hydrodynamic sources as well as local and regional contamination sources. Microplastics are the result of these degraded discarded plastics that become ubiquitous in the marine environment; they are defined as plastic particles less than 5 mm in size. The results of this study suggest that microplastics are ubiquitous in coastal systems of Cape Cod, with a highly variable distribution. Total abundance was about an order of magnitude higher in Nantucket Sound (60g/m3) and Buzzards Bay (120g/m3) than Cape Cod Bay and Atlantic Ocean beaches (~15g/m3), possibly reflecting seasonal and year-round population trends. -
Inland Fisheries Resource Enhancement and Conservation in Asia Xi RAP PUBLICATION 2010/22
RAP PUBLICATION 2010/22 Inland fisheries resource enhancement and conservation in Asia xi RAP PUBLICATION 2010/22 INLAND FISHERIES RESOURCE ENHANCEMENT AND CONSERVATION IN ASIA Edited by Miao Weimin Sena De Silva Brian Davy FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS REGIONAL OFFICE FOR ASIA AND THE PACIFIC Bangkok, 2010 i 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 (FAO) 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 mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. ISBN 978-92-5-106751-2 All rights reserved. Reproduction and dissemination of material in this information product for educational or other non-commercial purposes are authorized without any prior written permission from the copyright holders provided the source is fully acknowledged. Reproduction of material in this information product for resale or other commercial purposes is prohibited without written permission of the copyright holders. Applications for such permission should be addressed to: Chief Electronic Publishing Policy and Support Branch Communication Division FAO Viale delle Terme di Caracalla, 00153 Rome, Italy or by e-mail to: [email protected] © FAO 2010 For copies please write to: Aquaculture Officer FAO Regional Office for Asia and the Pacific Maliwan Mansion, 39 Phra Athit Road Bangkok 10200 THAILAND Tel: (+66) 2 697 4119 Fax: (+66) 2 697 4445 E-mail: [email protected] For bibliographic purposes, please reference this publication as: Miao W., Silva S.D., Davy B. -
Assessment of Health Risk Associated with Persistent Organic Pollutants in Water
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Springer - Publisher Connector Environ Monit Assess (2013) 185:497–508 DOI 10.1007/s10661-012-2570-8 Assessment of health risk associated with persistent organic pollutants in water Adam Pawełczyk Received: 9 October 2011 /Accepted: 10 February 2012 /Published online: 6 March 2012 # The Author(s) 2012. This article is published with open access at Springerlink.com Abstract This paper presents the results of analyses Keywords Environmental monitoring . Risk of water samples taken from water intakes supplying assessment . Polychlorinated biphenyls . one of the districts located near the city of Wrocław. Chloroorganic pesticides . Water pollution Surprisingly high concentrations of polychlorinated biphenyls and chloroorganic pesticides, classified as persistent organic pollutants (POPs), were detected in Introduction the monitored sites. Basing on the analytical and tox- icological data, the individual health risks related to Polychlorinated biphenyls and chloroorganic organic carcinogenic effects (excess cancer risk over a life- pesticides used on a massive scale in not so distant past time) in humans were assessed, resulting from direct still pose major health hazard to people and animals. ingestion of community water. Also noncarcinogenic Polychlorinated biphenyls are a mixture of congeners effects resulting from exposure to the examined POPs differing in their composition. Theoretically, 209 con- were determined. The conservative approach to risk