The Bioreactor Landfill
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State of Utah DIVISION of WASTE MANAGEMENT GARY R
Department of Environmental Quality L. Scott Baird Executive Director State of Utah DIVISION OF WASTE MANAGEMENT GARY R. HERBERT AND RADIATION CONTROL Governor Ty L. Howard SPENCER J. COX Director Lieutenant Governor November 5, 2020 Cassady Kristensen Environmental Business Partner Rio Tinto Kennecott 4700 Daybreak Parkway South Jordan, UT 84009 RE: Kennecott Utah Copper Tailings Impoundment Refuse Class IIIb Landfill Permit Dear Ms. Kristensen: The Division of Waste Management and Radiation Control (Division) has completed its review of the application to permit the Rio Tinto Kennecott Utah Copper Tailings Impoundment Refuse Class IIIb Landfill located on the Rio Tinto Kennecott Tailings Impoundment facility in Salt Lake County, Utah. Enclosed with this letter is the approved Permit Number 1905 and applicable attachments from portions of the application. The Permit approval and expiration dates are shown on the permit cover page. Also, the Statement of Basis for this permit (DSHW-2020-014707) is included with the permit. If you have any questions, please call Doug Taylor at (801) 536-0240. Sincerely, Ty L. Howard, Director Division of Waste Management and Radiation Control (Over) DSHW-2020-014711 195 North 1950 West • Salt Lake City, UT Mailing Address: P.O. Box 144880 • Salt Lake City, UT 84114-4880 Telephone (801) 536-0200 • Fax (801) 536-0222 • T.D.D. (801) 536-4284 www.deq.utah.gov Printed on 100% recycled paper TLH/DT/ar Enclosures: Permit (DSHW-2020-004084) Attachment #1 - Landfill Design (DSHW-2020-004510) Attachment #2 – Operation Plan (DSHW- 2020-004512) Attachment #3 – Closure and Post-Closure Plan (DSHW-2020-004514) Statement of Basis (DSHW-2020-014707) c: Gary Edwards, MS, Health Officer, Salt Lake County Health Dept. -
Workplace Recycling
SETTING UP Workplace Recycling 1 Form a Enlist a group of employees interested in recycling and waste prevention to set up and monitor collection systems Recycling Team to ensure ongoing success. This is a great team-building exercise and can positively impact employee morale as well as the environment. 2 Determine Customize your recycling program based on your business. Consider performing a waste audit or take inventory of materials the kinds of materials in your trash & recycling. to recycle Commonly recycled business items: Single-Stream Recycling • Aluminum & tin cans; plastic & glass bottles • Office paper, newspaper, cardboard • Magazines, catalogs, file folders, shredded paper 3 Contact Find out if recycling services are already in place. If not, ask the facility or property manager to set them up. Point your facility out that in today’s environment, employees expect to recycle at work and that recycling can potentially reduce costs. If recycling is currently provided, check with the manager to make sure good recycling education materials or property are available to all employees. This will help employees to recycle right, improve the quality of recyclable materials, manager and increase recycling participation. 4 Coordinate Work station recycling containers – Provide durable work station recycling containers or re-use existing training containers like copy paper boxes. Make recycling available at each work station. with the Click: Get-Started-Recycling-w_glass or Get-Started-Recycling-without-glass to print recycling container labels. Label your trash containers as well: Get-Started-Trash-with-food waste or janitorial crew Get-Started-Trash -no-food waste. and/or staff Central area containers – Evaluate the type and size of containers for common areas like conference rooms, hallways, reception areas, and cafes, based on volume, location, and usage. -
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. -
Numerical Model of Leachate Recirculation in Bioreactor Landfills
water Article Numerical Model of Leachate Recirculation in Bioreactor Landfills with High Kitchen Waste Content Peng Zhang , Hailong Liu * , Xingyao Jiang, Hao Lv, Chunyi Cui and Zhen Huyan Department of Civil Engineering, Dalian Maritime University, Dalian 116026, China; [email protected] (P.Z.); [email protected] (X.J.); [email protected] (H.L.); [email protected] (C.C.); [email protected] (Z.H.) * Correspondence: [email protected] Abstract: Surface spraying, horizontal trenches, and vertical wells are the most common leachate recirculation system used at landfills in engineering practice. In order to quantify the efficiency of the three aforementioned recirculation systems, a hydro–biochem–mechanical-coupled model was developed in the present work, which can describe hydrodynamic and biochemical behaviors in food-waste-rich landfills. A typical landfill cell was modeled in COMSOL. The results indicate that leachate recirculation can accelerate the decomposition of municipal solid waste (MSW) with food- rich waste content, relieving acidification, improving gas generation efficiency, and consequently, increasing the early settlement in landfills. Keywords: municipal solid waste; landfill; leachate treatment; coupled model; numerical simulation Citation: Zhang, P.; Liu, H.; Jiang, X.; 1. Introduction Lv, H.; Cui, C.; Huyan, Z. Numerical Disposing of municipal solid waste (MSW) has been a worldwide environmental Model of Leachate Recirculation in issue for decades. Landfilling is a commonly used MSW management method all around Bioreactor Landfills with High the world [1,2]. Due to the biochemical reaction of degradable components in MSW, the Kitchen Waste Content. Water 2021, releasing of polluted leachate and landfill gas will be a long-term process that may take 13, 1750. -
Five Facts About Incineration Five Facts About Incineration
Five facts about incineration Five facts about incineration Across the globe, cities are looking for ways to improve their municipal solid waste systems. In the search for services that are affordable, green and easy to implement, many cities are encouraged to turn to waste-to-energy (WtE) technologies, such as incineration.1 But, as found in WIEGO’s Technical Brief 11 (Waste Incineration and Informal Livelihoods: A Technical Guide on Waste-to-Energy Initiatives by Jeroen IJgosse), incineration is far from the perfect solution and, particularly in the Global South, can be less cost-effective, more complicated and can negatively impact the environment and informal waste workers’ livelihoods. Below, we have collected the top five issues highlighted in the study that show why this technology is a risky choice: 1. Incineration costs more than recycling. How incineration may be promoted: Incineration is a good economic decision because it reduces the costs associated with landfill operations while also creating energy that can be used by the community. The reality: • In 2016, the World Energy Council reported that, “energy generation from waste is a costly option, in comparison with other established power generation sources.” • Setting up an incineration project requires steep investment costs from the municipality. • For incineration projects to remain financially stable long-term, high fees are required, which place a burden on municipal finances and lead to sharp increases in user fees. • If incinerators are not able to collect enough burnable waste, they will burn other fuels (gas) instead. Contract obligations can force a municipality to make up the difference if an incinerator doesn’t burn enough to create the needed amount of energy. -
Bioreactor Landfills: Experimental and Field Results
Waste Management 22 (2002) 7–17 www.elsevier.nl/locate/wasman Bioreactor landfills: experimental and field results Mostafa Warith Ryerson Polytechnic University, 350 Victoria Street, Toronto, Ontario, Canada M5B 2K3 Received 8 August 2000; received in revised form 29 January 2001; accepted 31 January 2001 Abstract Bioreactor landfills allow a more active landfill management that recognizes the biological, chemical and physical processes involved in a landfill environment. This paper presents the results of an experimental study carried out to determine the effect of solid waste size, leachate recirculation and nutrient balance on the rate of municipal solid waste (MSW) biodegradation. Higher rates of MSW biodegradation eventually cause a reduction of the contaminant life span of the landfill and decrease in the cost of long term monitoring. The study indicated that the smaller the size of the MSW the faster the biodegradation rate of the waste. In addition, the paper presents the results of leachate recirculation on solid waste biodegradation in a full-scale landfill site, which is located in Nepean, Ontario, Canada. The leachate was recirculated into the landfilled solid waste for 8 years through infiltration lagoons. Similar results to those obtained in the laboratory scale experiments were noted. The average pH of the leachate in the early stages of recirculation was on the acidic range of the pH scale, however, the pH value was in the range of 7–8 after 2 years of leachate recirculation. The concentration of chloride remained fairly constant at about 1000 mg/l during the leachate recirculation period. A decreasing trend of the organic load, measured as biological oxygen demand and chemical oxygen demand, was observed. -
Joint Technical Document, MSW Landfill B-19, Kettleman Hills
JOINT TECHNICAL DOCUMENT MSW LANDFILL B-19, KETTLEMAN HILLS FACILITY KINGS COUNTY, CALIFORNIA VOLUME 1 OF 2 June 2016 Prepared for: Chemical Waste Management, Inc. 35251 Old Skyline Road Kettleman City, California 93239 Original prepared by: EMCON/OWT, Inc. 1326 North Market Boulevard Sacramento, California 95834-1912 Project No.: 833760.02000000 JOINT TECHNICAL DOCUMENT MSW LANDFILL B-19, KETTLEMAN HILLS FACILITY KINGS COUNTY, CALIFORNIA PROFESSIONAL ENGINEERING CERTIFICATION This revision to the JTD was prepared under the supervision and direction of the undersigned. This report was prepared consistent with current and generally accepted geologic and environmental consulting principles and practices that are within the limitations provide herein. Scott Sumner, P.E. Engineering Manager, RCE 49769 B-19 JTD JUNE 2016 ii Table of Contents ________________________________________________ Title Page ............................................ ……………………………………………………………………………... i Professional Engineering Certification ……………………………………………………………………………... ii List of Figures ............................................................................................................................................... vii List of Appendices ........................................................................................................................................ vii CalRecycle/SWB Index………………………………………………………………………………………………viii 1.0 Introduction .................................................................................................................................... -
Dust Emissions from Landfill Due to Deposition of Industrial Waste: a Case Study in Malmberget Mine, Sweden
Dust Emissions from Landfill due to Deposition of Industrial Waste: A Case Study in Malmberget Mine, Sweden Qi Jia, Yi Huang, Nadhir Al-Ansari and Sven Knutsson Civil, Mining and Nature Resources Engineering of Luleå University of Technology Abstract A great amount of industrial wastes are produced in Sweden every year. In 2008 there were 97.9 million tons of wasted generated, among which 93 million tons industrial waste were produced. 64.1% of industrial wastes were deposited in the landfill sites. Dust generation is one of the most important problems associated with industrial waste and landfills. The particulate dust emissions come from the industrial waste may contain heavy metal and produce environmental problems and potential health risks. Active and passive samplers, deposition pans are common equipment to collect dust samples. Real-time monitors use laser diffraction to recording continuous dust concentration. Dust emission from Malmberget mine in Sweden was analyzed as a case study. Dust was collected by NILU deposit gauge from 26 stations. Generally speaking the amount of dust fallout was decreasing with time because of implemented dust control methods. During the period August 2009 to August 2010, among all the measuring stations through the year, the maximum and the minimum value were 1284 g/100m2/30d and 9 g/100m2/30d. Two sources of dust generation were identified. The first was located close to the open pit, and the second near the current mining industrial center. The dust generation due to road construction was calculated. On the other hand dust generation was also closely related to weather conditions. -
Health Effects of Residence Near Hazardous Waste Landfill Sites: a Review of Epidemiologic Literature
Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature Martine Vrijheid Environmental Epidemiology Unit, Department of Public Health and Policy, London School of Hygiene and Tropical Medicine, London, United Kingdom This review evaluates current epidemiologic literature on health effects in relation to residence solvents, polychlorinated biphenyls (PCBs), near landfill sites. Increases in risk of adverse health effects (low birth weight, birth defects, certain and heavy metals, have shown adverse effects types of cancers) have been reported near individual landfill sites and in some multisite studies, on human health or in animal experiments. and although biases and confounding factors cannot be excluded as explanations for these A discussion of findings from either epi findings, they may indicate real risks associated with residence near certain landfill sites. A general demiologic or toxicologic research on health weakness in the reviewed studies is the lack of direct exposure measurement. An increased effects related to specific chemicals is beyond prevalence of self-reported health symptoms such as fatigue, sleepiness, and headaches among the scope of this review. residents near waste sites has consistently been reported in more than 10 of the reviewed papers. It is difficult to conclude whether these symptoms are an effect of direct toxicologic action of Epidemiologic Studies on chemicals present in waste sites, an effect of stress and fears related to the waste site, or an Health Effects of Landfill Sites risks to effect of reporting bias. Although a substantial number of studies have been conducted, The majority of studies evaluating possible is insufficient exposure information and effects health from landfill sites are hard to quantify. -
III . Waste Management
III. WASTE MANAGEMENT Economic growth, urbanisation and industrialisation result in increasing volumes and varieties of both solid and hazardous wastes. Globalisation can aggravate waste problems through grow ing international waste trade, with developing countries often at the receiving end. Besides negative impacts on health as well as increased pollution of air, land and water, ineffective and inefficient waste management results in greenhouse gas and toxic emissions, and the loss of precious materials and resources. Pollution is nothing but An integrated waste management approach is a crucial part of interna- the resources we are not harvesting. tional and national sustainable development strategies. In a life-cycle per- We allow them to disperse spective, waste prevention and minimization generally have priority. The because we’ve been remaining solid and hazardous wastes need to be managed with effective and efficient measures, including improved reuse, recycling and recovery ignorant of their value. of useful materials and energy. — R. Buckminster Fuller The 3R concept (Reduce, Reuse, Recycle) encapsulates well this life-cycle Scientist (1895–1983) approach to waste. WASTE MANAGEMENT << 26 >> Hazardous waste A growing share of municipal waste contains hazardous electronic or electric products. In Europe ewaste is increasing by 3–5 per Hazardous waste, owing to its toxic, infectious, radioactive or flammable cent per year. properties, poses an actual or potential hazard to the health of humans, other living organisms, or the environment. According to UNEP, some 20 to 50 million metric tonnes of e-waste are generated worldwide every year. Other estimates expect computers, No data on hazardous waste generation are available for most African, mobile telephones and television to contribute 5.5 million tonnes to Middle Eastern and Latin American countries. -
Bioreactor Brochure
City of Columbia, Missouri Glossary of Terms Questions? Public Works Department Aerobic: living or existing in the presence of oxygen For more information, visit our web page at Airspace: the available space in a cell where trash is placed www.GoColumbiaMo.com (GoLandfill) or call the for disposal Solid Waste Division at 573-874-6290. BIOREACTOR Anaerobic: living or existing in the absence of free oxygen LANDFILL Bioreactor: a controlled landfill or landfill disposal cell MORE INFO: US EPA where liquid and gas conditions are actively managed in WASTE STABILIZATION order to accelerate or enhance biostabilization of waste GENERAL: http://www.epa.gov/garbage/landfill/bioreactors. Biosolids: treated residuals from wastewater treatment htm facilities The City of Columbia Public Works Cell: a contained area of the landfill where waste is SPECIFIC: deposited http://www.epa.gov/epaoswer/nonhw/muncpl/ Department has begun planning for landfill/biowork/index.htm the next sanitary landfill disposal cell. Inorganic: being or composed of matter other than plant As part of this planning process, or animal bioreactor technology is being ACKNOWLEDGEMENTS examined as a means to accelerate LCS: leachate collection system waste biostabilization. We thank the following individuals and Leachate: liquid that filters through MSW organizations for contributions to this brochure. LFG: landfill gas Camp Dresser and McKee Inc. Liner: an engineered impermeable barrier at the bottom of Engineering Consulting Firm the landfill cell to prevent liquid from leaving the landfill University of Missouri Methane: a colorless, odorless, flammable gas produced by Dr. John Bowders decomposition of organic matter Civil Engineering Department MSW: municipal solid waste Organic: relating to or derived from living things (plant or animals), containing carbon compounds City of Columbia Post Closure: covers a regulated (currently 30 years) Public Works Department period after waste is last accepted when the owner is Solid Waste Division financially obligated to maintain the area to the designed P. -
Waste Management
10 Waste Management Coordinating Lead Authors: Jean Bogner (USA) Lead Authors: Mohammed Abdelrafie Ahmed (Sudan), Cristobal Diaz (Cuba), Andre Faaij (The Netherlands), Qingxian Gao (China), Seiji Hashimoto (Japan), Katarina Mareckova (Slovakia), Riitta Pipatti (Finland), Tianzhu Zhang (China) Contributing Authors: Luis Diaz (USA), Peter Kjeldsen (Denmark), Suvi Monni (Finland) Review Editors: Robert Gregory (UK), R.T.M. Sutamihardja (Indonesia) This chapter should be cited as: Bogner, J., M. Abdelrafie Ahmed, C. Diaz, A. Faaij, Q. Gao, S. Hashimoto, K. Mareckova, R. Pipatti, T. Zhang, Waste Management, In Climate Change 2007: Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change [B. Metz, O.R. Davidson, P.R. Bosch, R. Dave, L.A. Meyer (eds)], Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA. Waste Management Chapter 10 Table of Contents Executive Summary ................................................. 587 10.5 Policies and measures: waste management and climate ....................................................... 607 10.1 Introduction .................................................... 588 10.5.1 Reducing landfill CH4 emissions .......................607 10.2 Status of the waste management sector ..... 591 10.5.2 Incineration and other thermal processes for waste-to-energy ...............................................608 10.2.1 Waste generation ............................................591 10.5.3 Waste minimization, re-use and