An Approach to Litter Generation and Littering Practices in a Mexico City Neighborhood
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Licensed Municipal Solid Waste Landfills County Facility Name
Licensed Municipal Solid Waste Landfills County Facility Name (place ID#) Facility Type Secondary Id Address Phone No. Ashtabula Geneva Landfill (54419) Municipal Solid Waste Landfill MSWL018758 4339 Tuttle Rd, Geneva, 44041 440‐466‐8804 Athens Athens‐Hocking Reclamation Center (3078) Municipal Solid Waste Landfill MSWL018746 17970 US Rte 33, Nelsonville, 45764 740‐385‐6019 Brown Rumpke Waste Inc Brown County Landfill (3916) Municipal Solid Waste Landfill MSWL018788 9427 Beyers Rd, Georgetown, 45121 513‐851‐0122 Clinton Wilmington Sanitary Landfill (6451) Municipal Solid Waste Landfill MSWL018744 397 S Nelson Ave, Wilmington, 45177 937‐382‐6474 Coshocton Coshocton Landfill Inc (7032) Municipal Solid Waste Landfill MSWL018823 19469 County Rd No 7, Coshocton, 43812 740‐787‐2327 Crawford Crawford County Landfill (7270) Municipal Solid Waste Landfill MSWL018774 5128 Lincoln Hwy East, Bucyrus, 44820 513‐851‐0122 Defiance Defiance County Sanitary Landfill (12919) Municipal Solid Waste Landfill MSWL018764 13207 Canal Rd, Defiance, 43512 419‐782‐5442 Erie Erie County Sanitary Landfill (13359) Municipal Solid Waste Landfill MSWL018741 10102 Hoover Road, Milan, 44846 419‐433‐5023 Fairfield Republic Services Pine Grove Regional Facility (13668) Municipal Solid Waste Landfill MSWL018818 5131 Drinkle Rd SW, Amanda, 43102 740‐969‐4487 Franklin SWACO Franklin County Sanitary Landfill (15005) Municipal Solid Waste Landfill MSWL018803 3851 London Groveport Rd, Grove City, 43123 614‐871‐5100 Gallia Gallia County Landfill (16671) Municipal Solid Waste Landfill -
Safe Use of Wastewater in Agriculture: Good Practice Examples
SAFE USE OF WASTEWATER IN AGRICULTURE: GOOD PRACTICE EXAMPLES Hiroshan Hettiarachchi Reza Ardakanian, Editors SAFE USE OF WASTEWATER IN AGRICULTURE: GOOD PRACTICE EXAMPLES Hiroshan Hettiarachchi Reza Ardakanian, Editors PREFACE Population growth, rapid urbanisation, more water intense consumption patterns and climate change are intensifying the pressure on freshwater resources. The increasing scarcity of water, combined with other factors such as energy and fertilizers, is driving millions of farmers and other entrepreneurs to make use of wastewater. Wastewater reuse is an excellent example that naturally explains the importance of integrated management of water, soil and waste, which we define as the Nexus While the information in this book are generally believed to be true and accurate at the approach. The process begins in the waste sector, but the selection of date of publication, the editors and the publisher cannot accept any legal responsibility for the correct management model can make it relevant and important to any errors or omissions that may be made. The publisher makes no warranty, expressed or the water and soil as well. Over 20 million hectares of land are currently implied, with respect to the material contained herein. known to be irrigated with wastewater. This is interesting, but the The opinions expressed in this book are those of the Case Authors. Their inclusion in this alarming fact is that a greater percentage of this practice is not based book does not imply endorsement by the United Nations University. on any scientific criterion that ensures the “safe use” of wastewater. In order to address the technical, institutional, and policy challenges of safe water reuse, developing countries and countries in transition need clear institutional arrangements and more skilled human resources, United Nations University Institute for Integrated with a sound understanding of the opportunities and potential risks of Management of Material Fluxes and of Resources wastewater use. -
Municipal Solid Waste Landfill Operation and Management Workbook
MUNICIPAL SOLID WASTE LANDFILL OPERATION AND MANAGEMENT WORKBOOK Revised April 2018 Preface In many ways, constructing, operating and maintaining a municipal solid waste landfill is similar to constructing, operating, and maintaining a highway, dam, canal, bridge, or other engineered structure. The most important similarity is that landfills, like other engineered structures, must be constructed and operated in a manner that will provide safe, long-term, and reliable service to the communities they serve. Proper design, construction, operation, monitoring, closure and post-closure care are critical because after disposal the waste can be a threat to human health and the environment for decades to centuries. This workbook is intended to provide municipal landfill operators and managers in Wyoming with the fundamental knowledge and technical background necessary to ensure that landfills are operated efficiently, effectively, and in a manner that is protective of human health and the environment. This workbook contains information regarding basic construction and operation activities that are encountered on a routine basis at most landfills. The basic procedures and fundamental elements of landfill permitting, construction management, monitoring, closure, post-closure care, and financial assurance are also addressed. The workbook includes informative tips and information that landfill operators and managers can use to conserve landfill space, minimize the potential for pollution, reduce operating costs, and comply with applicable rules and regulations. In addition to this workbook, operators and managers need to become familiar with the Wyoming Solid Waste Rules and Regulations applicable to municipal solid waste. The DEQ also provides numerous guidelines that may help understand regulatory requirements in more detail. -
The Biological Treatment of Organic Food Waste
The Biological Treatment of Organic Food Waste HALYNA KOSOVSKA KTH Chemical Engineering and Technology Master of Science Thesis Stockholm 2006 KTH Chemical Engineering and Technology Halyna Kosovska THE BIOLOGICAL TREATMENT OF ORGANIC FOOD WASTE Supervisor & Examiner: Monika Ohlsson Master of Science Thesis STOCKHOLM 2006 PRESENTED AT INDUSTRIAL ECOLOGY ROYAL INSTITUTE OF TECHNOLOGY TRITA-KET-IM 2006:2 ISSN 1402-7615 Industrial Ecology, Royal Institute of Technology www.ima.kth.se Abstract This Master Thesis “The Biological Treatment of Organic Food Waste” is done in the Master’s Programme in Sustainable Technology at the Royal Institute of Technology (KTH) in co-operation with the company SRV återvinning AB. The report is dedicated to analyze different biological treatment methods (that is composting and fermentation), which are used for the handling of organic food waste. From this analysis I will suggest the best method or methods for the company SRV återvinning AB (the Södertörn Area in Sweden) and for the Yavoriv Region in Ukraine in order to increase the environmental performance and to improve the environmental situation in the regions. To be able to do this, a lot of factors are taking into consideration and are described and discussed in this Thesis Work. General characteristic of the regions, different means of control for organic food waste handling, sorting methods of organic waste, as well as composting and fermentation methods for treatment of organic waste are described and the advantages and disadvantages of these methods, their treatment and investment costs are distinguished in the Thesis. Different treatment methods are discussed from technical and economical points of view for applying them for the SRV and the Södertörn Area in Sweden and for the Yavoriv Region in Ukraine and some solutions for these two regions are suggested. -
A Benefit–Cost Analysis of Food and Biodegradable Waste Treatment
sustainability Article A Benefit–Cost Analysis of Food and Biodegradable Waste Treatment Alternatives: The Case of Oita City, Japan Micky A. Babalola Graduate School of Education, Hiroshima University, 1-1-1 Kagamiyama, Higashi-Hiroshima, Hiroshima 739 8524, Japan; [email protected] Received: 27 January 2020; Accepted: 23 February 2020; Published: 3 March 2020 Abstract: As the generation of food scrap, kitchen, and biodegradable wastes increases, the proper handling of these wastes is becoming an increasingly significant concern for most cities in Japan. A substantial fraction of food and biodegradable waste (FBW) ends up in the incinerator. Therefore, an analytic hierarchy process (AHP) benefit–cost analysis technique was employed in this study to compare different FBW treatment technologies and select the most appropriate FBW disposal technology for Oita City. The four FBW treatment options considered were those recommended by the Japanese Food Waste Recycling Law: anaerobic digestion, compost, landfill, and incineration, which is currently in use. The fundamental AHP was separated into two hierarchy structures for benefit analysis and cost analysis. The criteria used in these two analyses were value added, safety, efficiency, and social benefits for benefit analysis, and cost of energy, cost of operation and maintenance, environmental constraints, and disamenity for cost analysis. The results showed that anaerobic digestion had the highest overall benefit while composting had the least cost overall. The benefit–cost ratio result showed that anaerobic digestion is the most suitable treatment alternative, followed by composting and incineration, with landfill being the least favored. The study recommends that composting could be combined with anaerobic digestion as an optimal FBW management option in Oita City. -
New Biodegradable Waste Management Plans Proposed and Evaluated
New biodegradable waste management plans proposed and evaluated Researchers have designed and proposed a new organic waste management plan for Catalonia, Spain, and presented it in a recent study. They say that the plan would reduce a number of environmental impacts that arise from landfilling 23 April 2015 biodegradable waste, including natural resource depletion, acidification, and Issue 411 eutrophication. Subscribe to free weekly News Alert To reduce the negative environmental effects of landfilling and to promote the sustainable management of biodegradable municipal waste, the EU Landfill Directive1 has Source: Colón, J., Cadena, E., Belen Colazo, A.B., set targets for EU Member States to limit the amount of landfilled biodegradable municipal Quiros, R., Sanchez, A., waste to no more than 35% of the amount produced in 1995, by 2020. Font, X. & Artola, A. For this study, the researchers proposed a new biowaste management plan. They used (2015). Toward the model simulations to examine the outcomes of using the plan to treat the annual amount of implementation of new regional biowaste organic municipal solid waste produced in Catalonia in 2012 (1218 gigagrams (Gg)). In management plans: particular, they looked at the impact of using anaerobic digestion for recycling biowaste to Environmental assessment produce biogas, adding sludge to soil, and various forms of industrial and home composting of different waste treatments. management scenarios in Catalonia. Resources, They compared this new plan with those of actual waste management in 2012 in terms of Conservation and impacts on abiotic (non-living) natural resource depletion, acidification, eutrophication, Recycling. 95: 143–155. global warming, ozone layer depletion and summer smog. -
Introduction to Municipal Solid Waste Disposal Facility Criteria C R Training Module Training
Solid Waste and Emergency Response (5305W) EPA530-K-05-015 A R Introduction to Municipal Solid Waste Disposal Facility Criteria C R Training Module Training United States Environmental Protection September 2005 Agency SUBTITLE D: MUNICIPAL SOLID WASTE DISPOSAL FACILITY CRITERIA CONTENTS 1. Introduction ............................................................................................................................. 1 2. Regulatory Summary .............................................................................................................. 2 2.1 Subpart A: General Requirements ................................................................................... 3 2.2 Subpart B: Location Restrictions ..................................................................................... 6 2.3 Subpart C: Operating Criteria .......................................................................................... 8 2.4 Subpart D: Design Criteria ..............................................................................................12 2.5 Subpart E: Groundwater Monitoring and Corrective Action ..........................................12 2.6 Subpart F: Closure and Post-Closure Care ......................................................................17 2.7 Subpart G: Financial Assurance Criteria .........................................................................19 Municipal Solid Waste Disposal Facility Criteria - 1 1. INTRODUCTION This module provides a summary of the regulatory criteria for municipal solid waste -
Overview of Anaerobic Digestion for Municipal Solid Waste
Global Methane Initiative Overview of Anaerobic Digestion for Municipal Solid Waste Updated: October 2016 1 About This Presentation . Introduces the process of anaerobic digestion (AD) for municipal solid waste (MSW) . Provides an overview of anaerobic digestion microbiology . Helps you understand how you might benefit from AD . Guides you through the key areas to consider when developing an AD project . Reviews the status of AD globally and provides selected case studies Using Bookmarks to Navigate This presentation contains bookmarks to help you navigate. Using the panel on the left, click the bookmark to jump to the slide. For Chrome users, the bookmarks can be viewed by clicking on the bookmark icon ( ) at the top right of the screen. 2 Global Methane Initiative GMI is a voluntary, multilateral partnership that aims to reduce global methane emissions and to advance the abatement, recovery and use of methane as a valuable clean energy source. OBJECTIVES BENEFITS . Reduce anthropogenic methane . Decline in methane concentrations emissions and advance the and methane utilization will result recovery and use of methane in: while: – Sustainability – Enhancing economic growth – Energy security – Promoting energy security – Health and safety – Improving local air quality – Profitability and public health. 3 GMI Partners . Grew from 14 to 42 Partner governments, plus the European Commission . Accounts for nearly 70% of global anthropogenic methane emissions 4 Main Menu 1. Introduction – what is AD and why should it interest me? Click here for an introduction to AD 2. Is AD suitable for me? Click here for more info about the potential for AD 3. Step-by-step guide Click here for detailed information about the key issues to consider when developing an AD project 4. -
Why Anaerobic Digestion? Anaerobic Digestion Occurs Naturally, in the Absence of Oxygen, As Bacteria Break Down Organic Materials and Produce Biogas
The Benefits of Anaerobic Digestion of Food Waste At Wastewater Treatment Facilities Why Anaerobic Digestion? Anaerobic digestion occurs naturally, in the absence of oxygen, as bacteria break down organic materials and produce biogas. The process reduces the amount of material and produces biogas, which can be used as an energy source. This technology is commonly used throughout the United States to break down sewage sludge at wastewater treatment facilities. In the past few years, there has been a movement to start adding food waste to anaerobic digesters already in place at wastewater treatment facilities. The anaerobic digestion of food waste has many benefits, including: • Climate Change Mitigation – Food waste in landfills generates methane, a potent greenhouse gas. Diverting food waste from landfills to wastewater treatment facilities allows for the capture of the methane, which can be used as an energy source. In addition to decreased methane emissions at landfills, there are greenhouse gas emissions reductions due to the energy offsets provided by using an on-site, renewable source of energy. • Economic Benefits – Wastewater treatment facilities can expect to see cost savings from incorporating food waste into anaerobic digesters. These include reduced energy costs due to production of on-site power and tipping fee for accepting the food waste. • Diversion Opportunities – Most municipalities are investing in ways to divert materials from landfills. This is usually due to reduced landfill space and/or recycling goals. Wastewater treatment facilities offer the opportunity to divert large amounts of food waste, one of the largest waste streams still going to landfills. Why Food Waste? Food waste is the second largest category of municipal solid waste (MSW) sent to landfills in the United States, accounting for approximately 18% of the waste stream. -
RCRA Orientation Manual: Table of Contents and Foreword
RCRA Saving Resources and Energy Orientation Manual 2014 RCRA Orienta Resource Conservation and Recovery Act Managing Materials Safely Promoting Recycling and eCycling Promoting Recycling and eCycling Reducing Priority Chemicals tion Manual 2014 tion Manual Forming Partnerships Forming Partnerships Reducing Priority Chemicals Reusing Industrial Materials Preventing Waste Reusing Industrial Materials United States Environmental Protection Agency Solid Waste and Emergency Response (5305W) Washington, DC 20460 Official Business Preventing Waste Penalty for Private Use $300 EPA530-F-11-003 October 2014 Recycled/Recyclable—Printed with Vegetable Oil Based Inks on www.epa.gov/epawaste 100% (Minimum 50% Postconsumer) Recycled Paper RCRA Orientation Manual THIS MANUAL WAS DEVELOPED BY: THE U.S. ENVIRONMENTAL PROTECTION AGENCY OFFICE OF RESOURCE CONSERVATION AND RECOVERY PROGRAM MANAGEMENT, COMMUNICATIONS, AND ANALYSIS OFFICE 1200 Pennsylvania Avenue, N.W. WASHINGTON, DC 20460 TABLE OF CONTENTS Foreword ........................................................................................................................................... i Chapter I: Introduction to the Resource Conservation and Recovery Act .................................... I-1 Chapter II: Managing Solid Waste—RCRA Subtitle D ................................................................ II-1 Chapter III: Managing Hazardous Waste—RCRA Subtitle C ...................................................... III-1 Hazardous Waste Identification ................................................................................ -
Utilization of Biodegradable Wastes As a Clean Energy Source in the Developing Countries: a Case Study in Myanmar
energies Article Utilization of Biodegradable Wastes as a Clean Energy Source in the Developing Countries: A Case Study in Myanmar Maw Maw Tun 1,2,* , Dagmar Juchelková 1,* , Helena Raclavská 3 and Veronika Sassmanová 1 1 Department of Power Engineering, VŠB-Technical University of Ostrava, 17. listopadu 15, 70833 Ostrava-Poruba, Czech Republic; [email protected] 2 Department of Energy Engineering, Czech Technical University, Zikova 1903/4, 166 36 Prague, Czech Republic 3 Centre ENET, VŠB-Technical University of Ostrava, 17. listopadu 15, 70833 Ostrava-Poruba, Czech Republic; [email protected] * Correspondence: [email protected] (M.M.T.); [email protected] (D.J.); Tel.: +420-773-287-487 (M.M.T.) Received: 12 October 2018; Accepted: 12 November 2018; Published: 16 November 2018 Abstract: Nowadays, waste-to-energy has become a type of renewable energy utilization that can provide environmental and economic benefits in the world. In this paper, we evaluated the quality of twelve biodegradable waste samples from Myanmar by binder laboratory heating and drying oven at 105 ◦C. The calculation methods of the Intergovernmental Panel on Climate Change (IPCC) and Institute for Global Environmental Strategies (IGES) were used for the greenhouse gas emission estimation from waste disposal at the open dumpsites, anaerobic digestion, and waste transportation in the current situation of Myanmar. Greenhouse gas (GHG) emission and fossil fuel consumption of the improved biodegrade waste utilization system were estimated and both were found to be reduced. As a result, volume and weight of the biodegradable wastes with 100% moisture reduction were estimated at approximately 5 million cubic meters per year and 2600 kilotonnes per year, respectively, in 2021. -
Tot, Bojana. ANALYSIS of BIODEGRADABLE WASTE
ANALYSIS OF BIODEGRADABLE WASTE TREATMENT IN ORDER TO REDUCE QUANTITY OF DISPOSED WASTE Bojana Tot1 , Svjetlana Jokanović1 , Goran Vujic1 , Bojan Batinić1, Nemanja Stanisavljević1, Bojana 1 1 Beronja , Dejan Ubavin 1 Department of Environmental Engineering and Occupational Safety and Health, Faculty of Technical Sciences, University of Novi Sad, Serbia ABSTRACT According to data obtained by analysis of quantity and composition of municipal solid waste in Republic of Serbia, the most significant waste fraction 40% represents organic waste, and roughly can be divided into food waste and garden or yard waste. In Serbia, practically all biodegradable waste ends up on non sanitary landfills, contributing to a large negative impact due to high production of methane, one of the most significant greenhouse gases (GHG). In order to comply with increasing national and international requirements, one of the main objectives is the reduction to 75% (by weight) of the total quantities of biodegradable municipal solid waste which ends up at landfill until 2016 a the first step to accomplish this requirements. This paper analyzes possible ways for the treatment of biodegradable waste from households in Serbian municipalities in order to achieve this goal. Therefore, in this paper, flows of garden and other biodegradable waste in municipal solid waste are analyzed by MFA (Material Flow Analysis) and two scenarios are presented. For decision makers in the field of waste management, the obtained information will be of great importance in order to develop an appropriate waste management system and to achieve specific targets for biodegradable waste treatment according to national and EU Directives. 1. INTRODUCION Organic waste can represent 20 to 80% of total municipal solid waste (MSW) stream, depending on the country economic development level.