Science to Enable Sustainable Plastics
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Alternatives to Plastic Mulch
Alternatives to Plastic Mulch for Organic Vegetable Production Carol Miles, Kathryn Kolker, Jenn Reed and Gail Becker WSU Vancouver Research & Extension Unit 1919 NE 78th Street, Vancouver, WA 98665 (360) 576-6030, [email protected], http://agsyst.wsu.edu Introduction Weed control is one of the primary concerns in organic farming as it is labor intensive, expensive and time consuming. Since its introduction in the 1950s, plastic mulch has become a standard practice used by many farmers to control weeds, increase crop yield, and shorten time to harvest (Lamont, 1991). Plastic mulch has contributed significantly to the economic viability of farmers worldwide, and by 1999 almost 30 million acres worldwide were covered with plastic mulch, with more than 185,000 of those acres in the United States (American Plastics Council, 2004; Takakura and Fang, 2001). However, each year farmers must dispose of their plastic, and although agricultural plastic recycling has begun, the disposal option that most choose is the landfill (Garthe, 2002). Many organic farmers, especially those who are small-scale, choose not to use plastic mulch because of the waste disposal issues. An effective, affordable, degradable alternative to the now-standard plastic mulch would contribute the same production benefits as plastic mulch and in addition would reduce non-recyclable waste. Previous work. In 2003, we conducted a preliminary study at Washington State University Vancouver Research and Extension Unit (WSU VREU) to evaluate paper and cornstarch mulches as alternatives to plastic mulch. We used 81 lb Kraft paper with and without oil application. We evaluated three oils (soybean, linseed and tung) applied before and after laying the paper. -
Types of Plastic and Their Recycle Codes | Quality Logo Products®
7/24/2018 Types of Plastic and Their Recycle Codes | Quality Logo Products® Product Search Your privacy will be protected by redirecting your search to Search Encrypt. Learn More X ALL ABOUT MATERIALS Types of Plastic and Their Recycle Codes Other Lessons in This Course Types of Plastic Plastic is an essential component of many items, including water bottles, combs, and beverage containers. Knowing the difference, as well as the SPI codes, will help you make more informed decisions about recycling. The seven types of plastic include: Polyethylene Terephthalate (PETE or PET) High-Density Polyethylene (HDPE) Polyvinyl Chloride (PVC) Miscellaneous plastics (includes: polycarbonate, polylactide, acrylic, acrylonitrile butadiene, styrene, fiberglass, and nylon) When it comes to promotional giveaways, and even items we use around the house, there is no material more important than plastic. The same can be said for the items we use at the office. Most of our supplies contain at least a little bit of this material. In fact, humans have thus far produced 9.1 billion tons of plastic! For the sake of the environment, it’s important to know the different types of plastic and their uses, as well as the resin identification codes found on each for the sake of recycling. Recycling Codes for Plastic Understanding the different types of plastic can help consumers like you make more informed decisions related to your health and the environment. It’s important to become familiar with an item’s SPI (Society of the Plastics Industry) code, which is also known as a resin identification number and is used to classify the different types of plastic. -
AGRICULTURAL PLASTICS Q & a Vers Feb 8, 2016
Lois Levitan, PhD Recycling Agricultural Plastics Program Department of Communication Cornell University, Ithaca NY 14853 AGRICULTURAL PLASTICS Q & A vers Feb 8, 2016 • What are agricultural plastics? • What is plastic? • How is plastic film used on dairy farms? • How is plastic film used in producing fruits, vegetables & ornamentals? • What is done with waste plastic after it is no longer useful on the farm? • What new products are made from recycled agricultural plastics? • Why is plastic ground up or baled before shipping to markets? • Are all agricultural plastics made from the same material? • Is it ok to burn waste plastic in a back field on the farm? • What about pesticide containers? WHAT ARE AGRICULTURAL PLASTICS? ‘Agricultural Plastics’ are the array of plastic products and packaging used in agricultural production and sales. Most have a short useful life. Plastic products are typically lighter to lift and transport, less fragile, safer to use, and have a higher production efficiency than the concrete, glass, ceramic and other materials they have replaced over the past several decades. Silage Bags • Bunk Silo Covers • Polytwine • Bale Wrap • Netwrap • Maple Tubing • Irrigation Drip Tape & Polytubes • High Tunnels • Tarps • Seedling Plug Trays • Plant Pots • Mulch Film • Fumigation Film • Pesticide & Dairy Chemical Containers • Boat Wrap • Bee Hive Frames • Bird Netting • Aquaculture Supplies • Row Covers • O2 & Moisture-Barrier Film • Bags for Seed, Feed, Fertilizer, Peat, Wood Pellets, Potting Mix, etc. • Low Tunnels • • F.I.B.C. (totes, supersacks) • Grain Bags • Greenhouse Covers • Hoophouses • Solarization Film • WHAT IS PLASTIC? Plastics are solid materials that can be molded, pressed, or extruded into a variety of forms and shapes. -
Study of Polystyrene Degradation Using Continuous Distribution Kinetics in a Bubbling Reactor
Korean J. Chem. Eng., 19(2), 239-245 (2002) Study of Polystyrene Degradation Using Continuous Distribution Kinetics in a Bubbling Reactor Wang Seog Cha†, Sang Bum Kim* and Benjamin J. McCoy** School of Civil and Environmental Engineering, Kunsan National University, Kunsan 573-701, Korea *Department of Chemical Engineering, Korea University, Seoul 136-701, Korea **Department of Chemical Engineering and Material Science, University of California, Davis, CA 95616, USA (Received 3 April 2001 • accepted 10 September 2001) Abstract−A bubbling reactor for pyrolysis of a polystyrene melt stirred by bubbles of flowing nitrogen gas at at- mospheric pressure permits uniform-temperature distribution. Sweep-gas experiments at temperatures 340-370 oC allowed pyrolysis products to be collected separately as reactor residue(solidified polystyrene melt), condensed vapor, and uncondensed gas products. Molecular-weight distributions (MWDs) were determined by gel permeation chro- matography that indicated random and chain scission. The mathematical model accounts for the mass transfer of vaporized products from the polymer melt to gas bubbles. The driving force for mass transfer is the interphase differ- ence of MWDs based on equilibrium at the vapor-liquid interface. The activation energy and pre-exponential of chain scission were determined to be 49 kcal/mol and 8.94×1013 s−1, respectively. Key words: Pyrolysis, Molecular-Weight-Distribution, Random Scission, Chain-end Scission, Continuous Distribution Theory INTRODUCTION Westerout et al. proposed a random-chain dissociation (RCD) model, based on evaporation of depolymerization products less than Fundamental and practical studies of plastics processing, such a certain chain length. In a subsequent paper [Westerout et al., 1997b] as energy recovery (production of fuel) and tertiary recycle (recov- on screen-heater pyrolysis, the RCD model was further described. -
Primary Microplastics in the Oceans: a Global Evaluation of Sources Authors: Julien Boucher, Damien Friot
Primary Microplastics in the Oceans: a Global Evaluation of Sources Authors: Julien Boucher, Damien Friot INTERNATIONAL UNION FOR CONSERVATION OF NATURE Primary Microplastics in the Oceans: a Global Evaluation of Sources Authors: Julien Boucher, Damien Friot The designation of geographical entities in this book, and the presentation of the material, do not imply the expression of any opinion whatsoever on the part of IUCN concerning the legal status of any country, territory, or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. The views expressed in this publication do not necessarily reflect those of IUCN. Published by: IUCN, Gland, Switzerland Copyright: © 2017 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorised without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale or other commercial purposes is prohibited without prior written permission of the copyright holder. Citation: Boucher, J. and Friot D. (2017). Primary Microplastics in the Oceans: A Global Evaluation of Sources. Gland, Switzerland: IUCN. 43pp. ISBN: 978-2-8317-1827-9 DOI: dx.doi.org/10.2305/IUCN.CH.2017.01.en Authors: Julien Boucher EA – Shaping Environmental Action & University of Applied Sciences and Arts Western Switzerland // HES-SO, HEIG-VD, Yverdon-les-Bains, Switzerland Damien Friot EA – Shaping Environmental Action www.shaping-ea.com [email protected] Editor: Carl Gustaf Lundin and João Matos de Sousa External reviewers: Francis Vorhies (Earthmind, http://earthmind.org) François Galgani (IFREMER, Laboratoire LER/PAC) Mathieu Pernice (University of Technology, Sydney) Doug Woodring (www.oceanrecov.org) Designed by: Imre Sebestyén jr. -
The Facts About Plastic Bags: Recyclable, Affordable, and Convenient
THE FACTS ABOUT PLASTIC BAGS: RECYCLABLE, AFFORDABLE, AND CONVENIENT Plastic bags are 100% recyclable, reusable, made from natural gas, not oil, and a sustainable choice for consumers, communities and businesses. What’s more, the plastic bag manufacturing and recycling industry is a uniquely American industry that employs more than 30,000 Americans in 349 plants across the country, including more than 1,000 people in Washington state. Bans and taxes on plastic bags are misguided policies that don’t make sense. They don’t help the environment, force less sustainable options, threaten local manufacturing jobs and raise grocery costs for consumers. Instead of banning a reusable, 100% recyclable, American-made product, recycling solutions can help reduce litter, give consumers a choice, and protect American jobs. Plastic grocery bags are the best checkout option for our environment On a per bag basis, plastic bags are more resource efficient, reduce landfill waste and generate fewer greenhouse gas emissions. o They take up a lot less space in a landfill: 1,000 plastic bags weigh 13 pounds; 1,000 paper bags weigh 114 pounds.i o They generate 80 % less waste than paper bags.ii American plastic bags are made from natural gas, NOT oil. In the U.S., 85 percent of the raw material used to make plastic bags is produced from natural gas.iii Recycled plastic bags are used to make new plastic bags and building products, such as backyard decks, playground equipment, and fences. Bans haven’t worked in other places, and don’t protect the environment A ban would make no difference in litter reduction since plastic bags only make up a tiny fraction (less than 0.5 %) of the U.S. -
COT Microplastics Overarching Staement 2021
COMMITTEE ON TOXICITY OF CHEMICALS IN FOOD, CONSUMER PRODUCTS AND THE ENVIRONMENT Overarching statement on the potential risks from exposure to microplastics Background 1. Plastic pollution has been widely recognised as a global environmental problem (Villarrubia-Gómez et al., 2018). The adverse effects of plastic litter have been widely documented for marine animals (e.g. entanglement, ingestion and lacerations); however, the potential risks from exposure to smaller plastic particles i.e. micro- and nanoplastics in humans are yet to be fully understood. Scope and purpose 2. As part of horizon scanning, the Committee on Toxicity of Chemicals in Food, Consumer Products and the Environment (COT) identified the potential risks from microplastics as a topic it should consider. Upon review of the literature, it was decided that nanoplastics should also be included. An initial scoping paper was presented to the COT in October 2019 (TOX/2019/62)1, since when the topic and additional information has been discussed several times by COT with the final substantive discussion in December 2020. A list of all discussion papers considered by the COT during the review is given in Annex A. 3. The purpose of this overarching statement is to bring together these discussions, summarise the COT conclusions reached to date and provide a high-level overview of the current state of knowledge, data gaps and research needs with regards to this topic. 4. Future sub-statements, which will consider in detail the potential toxicological risks of exposure from microplastics via the oral and inhalation routes, are intended to provide supplementary material for this overarching statement. -
Pathways for Degradation of Plastic Polymers Floating in the Marine Environment
Environmental Science Processes & Impacts View Article Online CRITICAL REVIEW View Journal | View Issue Pathways for degradation of plastic polymers floating in the marine environment Cite this: Environ. Sci.: Processes Impacts ,2015,17,1513 Berit Gewert, Merle M. Plassmann and Matthew MacLeod* Each year vast amounts of plastic are produced worldwide. When released to the environment, plastics accumulate, and plastic debris in the world's oceans is of particular environmental concern. More than 60% of all floating debris in the oceans is plastic and amounts are increasing each year. Plastic polymers in the marine environment are exposed to sunlight, oxidants and physical stress, and over time they weather and degrade. The degradation processes and products must be understood to detect and evaluate potential environmental hazards. Some attention has been drawn to additives and persistent organic pollutants that sorb to the plastic surface, but so far the chemicals generated by degradation of the plastic polymers themselves have not been well studied from an environmental perspective. In this paper we review available information about the degradation pathways and chemicals that are formed by degradation of the six plastic types that are most widely used in Europe. We extrapolate that information Creative Commons Attribution 3.0 Unported Licence. to likely pathways and possible degradation products under environmental conditions found on the oceans' surface. The potential degradation pathways and products depend on the polymer type. UV-radiation and oxygen are the most important factors that initiate degradation of polymers with a carbon–carbon backbone, leading to chain scission. Smaller polymer fragments formed by chain scission are more susceptible to biodegradation and therefore abiotic degradation is expected to Received 30th April 2015 precede biodegradation. -
Plasticulture in California Vegetable Production
PUBLICATION 8016 Plasticulture in California Vegetable Production WAYNE L. SCHRADER, UC Cooperative Extension Vegetable Farm Advisor, San Diego County Plasticulture is the art of using plastic materials to modify the production environ- UNIVERSITY OF ment in vegetable crop production. Plasticulture began in the 1950s and early 1960s with the introduction and use of plastic films, mulches, and drip irrigation systems. CALIFORNIA Vegetable growers frequently use plastics in pest management, stand establishment, Division of Agriculture harvesting, and postharvest handling operations, and in containers for marketing. and Natural Resources Plasticulture system components can include http://anrcatalog.ucdavis.edu • plastic mulches to control soil temperature, control weeds, and repel insects • plastic films for erosion control, soil fumigation, or solarization • row covers for temperature control, wind or frost protection, and insect exclusion • drip irrigation for improved water management and for the application of chemi- cals (chemigation) and fertilizers (fertigation) during irrigation • plastic windbreaks • plastic barriers against vertebrate pests Plasticulture has developed into management systems that allow growers to achieve higher-quality produce, superior yields, and extended production cycles. Growers using plasticulture can produce vegetables for markets during the winter, early spring, and late fall that would otherwise be impossible to address. Benefits of plasticulture include • earlier production (7 to 30 days earlier) • increased -
How to Create Your Own Environmental Emphasis
HOW TO CREATE YOUR OWN ENVIRONMENTAL EMPHASIS 2019 ENVIRONMENTAL STUDIES PROGRAM, UCSB 2020 Because of the interdisciplinary design of the B.A. and B.S. Environmental Studies major requirements students are afforded the opportunity to customize their upper-division electives (Area B) and outside concentration (Area C) to create a distinct environmental emphasis or concentration unique to their personal and professional goals and needs. Students may choose from a wide selection of courses from the ES Program as well as departments across campus. This information sheet demonstrates how one may create a personalized concentration by offering some example emphases popular with current ES students. Although one may choose to follow one of the emphases included here, they are SUGGESTIVE ONLY! One may satisfy their major requirements with any combination of applicable courses/units as long as they form a coherent and comprehensive emphasis. Be sure to review the upper-division ES major requirements below before starting an emphasis. A Request to Petition Degree Requirements will be required to apply courses from multiple departments towards the Area C, and can be download here: www.es.ucsb.edu/degreerequirements Please Note: Pursuing an environmental emphasis as part of your Area B & C requirements can help prepare students for a specialized field or profession. However, one’s interdisciplinary emphasis will not be officially noted on their diploma or transcripts. One can highlight their emphasis on their resume and/or cover letter. Please consult an ES Academic Advisor (Bren Hall 4L, Rm. 4312 or 4313) if you have any questions. Review of ES Degree’s Upper-division Requirements: B.A. -
Issues in Environmental Science and Technology
ISSUES IN ENVIRONMENTAL SCIENCE AND TECHNOLOGY EDITORS: R. E. HESTER AND R. M. HARRISON 12 ROYAL SOCIETY OF CHEMISTRY ISBN 0-85404-255-5 ISSN 1350-7583 A catalogue record for this book is available from the British Library @ The Royal Society of Chemistry 1999 All rights reserved Apart from any lair dealing for the purposes of research or private study, or criticism or review as permitted under the terms of the UK Copyright, Designs and Patents Act, 1988, this publication may not be reproduced, stored or transmitted, in any form or by any means, without the prior permission in writing of The Royal Societ}' of Chemistry, or in the case ofreprographic reproduction only in accordance with the terms of the licence.~ issued b}' the Cop}Tight Licensing Agenc}' in the UK, or in accordance Ilith the terms of the licences issued by the appropriate Reproduction Rights Organization outside the UK. Enquiries concerning reproduction outside the terms stated here should be sent to The Royal Society of Chemistry at the addre.~.~ printed on this page. Published by The Royal Society of Chemistry, Thomas Graham House, Science Park, Milton Road, Cambridge CB4 OWF, UK For further information see our web site,at www.rsc.org Typeset in Great Britain by Vision Typesetting, Manchester Printed and bound by Redwood Books Ltd., Trowbridge, Wiltshire Editors Ronald E. Hester, BSc, DSc(London), PhD(Cornell), FRSC, CChem Ronald E. Rester is Professor of Chemistry in the University of York. He was for short periods a research fellow in Cam bridge and an assistant professor at Cornell before being appointed to a lectureship in chemistry in Y orkin 1965. -
Improving Plastics Management: Trends, Policy Responses, and the Role of International Co-Operation and Trade
Improving Plastics Management: Trends, policy responses, and the role of international co-operation and trade POLICY PERSPECTIVES OECD ENVIRONMENT POLICY PAPER NO. 12 OECD . 3 This Policy Paper comprises the Background Report prepared by the OECD for the G7 Environment, Energy and Oceans Ministers. It provides an overview of current plastics production and use, the environmental impacts that this is generating and identifies the reasons for currently low plastics recycling rates, as well as what can be done about it. Disclaimers This paper is published under the responsibility of the Secretary-General of the OECD. The opinions expressed and the arguments employed herein do not necessarily reflect the official views of OECD member countries. This document and any map included herein are without prejudice to the status of or sovereignty over any territory, to the delimitation of international frontiers and boundaries and to the name of any territory, city or area. For Israel, change is measured between 1997-99 and 2009-11. The statistical data for Israel are supplied by and under the responsibility of the relevant Israeli authorities. The use of such data by the OECD is without prejudice to the status of the Golan Heights, East Jerusalem and Israeli settlements in the West Bank under the terms of international law. Copyright You can copy, download or print OECD content for your own use, and you can include excerpts from OECD publications, databases and multimedia products in your own documents, presentations, blogs, websites and teaching materials, provided that suitable acknowledgment of OECD as source and copyright owner is given.