LANDFILL Landfill Mining

Total Page:16

File Type:pdf, Size:1020Kb

LANDFILL Landfill Mining LANDFIL L Landfill Mining: Current Trends Landfill mining is a term used to describe a process whereby landfilled solid waste is excavated and processed for beneficial purposes. BY BRUCE CLAR:<. ALYSOI~ DAGLY, AND "!ARC ROGOFF he beneficial purposes can Table 1. Landfill Mining/Reclamation Considerations include recovery of recyclable materials, recovery of soils for use as daily or intermediate Nuisances caused during mining (i.e., construction Gain additional airspace for active waste filling coverT in active landfills, or recovery of land traffic, fugitive dust) · Potential presence of hazardous materials, area for redevelopment. As urban sprawl Recycling potential of certain materials extra cost and delays has continued in many metropolitan areas, Recovery of cover soil for reuse Escape of leachate and/or nuisance odors during landfills-which previously were located in (if uncontaminated) mining operations areas relatively distant from the population Potential for recovery of materials that Few regulatory laws or standards centers-are less so, and the value of those could be used for energy production properties for redevelopment have increased. Land reclamation Projected volume of recyclables may not materialize In the US, however, the term "landfill Remediation of soil and Relatively long process that requires Owner's oversight mining" has increasingly become a mis- groundwater contamination and management commitment nomer, as the primary driver has been to reclaim the old footprint and develop it to meet current Subtitle C regulations (i.e., What About Recyclables? The production of a landfill mining typically at a minimum installing a bottom- Some landfill owners have opted to separate operation is mainly dependent on the lining system with leachate controls) and and sell recyclables obtained from a recla- size and number of pieces of equipment gain valuable additional airspace for active mation project; however, the value of these deployed, the types of soils used during waste filling. The reclamation of recyclable materials is elusive. Cal Recovery, Hercules, landfill operations (e.g., sandy versus clayey materials-like plastics, metals, and glass, CA, conducted a study for EPA of the Collier materials), the types of waste disposed, and plastics and paper for energy recovery- County, FL, landfill mining demonstration weather conditions, liquid levels in the are secondary and do not typically justify the process in 1993, and concluded that plastic landfill, and gas emissions. More equipment total cost to reclaim them with natural gas and metal were the only viable recyclables, but means more production, but more equip- energy, both abundant and relatively "cheap." were not of acceptable quality for the resale ment also means additional capital costs. As pointed out in the recent International market. They indicated that the actual "cost" Certain types of waste are more difficult Solid Waste Association (ISWA) publication of mining and separating the recyclables was to excavate and process than others, which on landfill mining, the concept of mining about $115 per ton. Extrapolating that cost to can slow productivity. High liquid levels and landfills is not new. Some 60 examples have today's dollars would cost approximately $250 highly saturated wastes require additional been cited in solid waste literature since the per ton. This cost is high, relative to the price steps to excavate and process, which, again, first reported project in Israel in the 1950s. being paid for recyclables as discussed in the slows production. Inclement weather is a less Landfill mining is a practice not unique to section on benefit-cost. controllable factor; however, the timing of any particular country or even region. The major excavation efforts can be scheduled to practice has both advantages and disadvan- Construction Timeframe take advantage of seasons with less inclem- tages, which are summarized in Table 1. Basic landfill mining equipment may include ent weather. Lastly, health and safety issues the following: associated with gas emissions such as com- Planning Aspects • Waste excavation: hydraulic excavators bustible gases, odorous gases, and such must An overview of the entire landfill mining (backhoes) be considered and can negatively impact process is helpful to be able to properly • Waste screening (large objects): surrounding properties if not controlled plan all of the parts of the process and have grizzly screen properly, ultimately impacting the excava- contingency plans ready if something does • Waste screening (smaller objects): tion and processing activities. not go according to plan. Table 2 presents a trommel screen Equipment involved in the waste excava- summary overview of the overall aspects to • Screen feed: front -end loader tion activities typically limits the actual consider on a mining project. • Waste hauling: dump trucks capacity of an operation. This equipment 56 MSW MANAGEMENT [ SEPTEMBER/OCTOBER 2016 ] A drilling and test pit program is usually An accurate waste thickness profile Baseline waste necessary to obtain a reasonable and a representative description of the characterization understanding of the depth of the wastes in-place waste ofthe waste is desirable. and the main materials. Soil and/or Can remediation be completed prior to Many proven new techniques are available groundwater that can relatively quickly remediate certain constructing a new landfill cell? contamination common types of contamination. Identify former areas used for disposal Special waste areas of asbestos, sludge, etc. Special health Develop a Contingency Plan for managing and safety issues will apply. these wastes if encountered. Large amounts of plastics could potentially Identify specific materials; soil, metals, Materials desired go to a WTE plant. Soil should be tested if plastics, etc. that are desired for reuse for separation on site (soil) or disposal offsite. any concern it may be contaminated and unsuitable for reuse as daily cover. Plan for waste disposal tonnage to Space required for your active cell to increase, potentially Assume low volume of cover soil excavated and all other materials filled back into relocated waste significantly, on a temporary basis, operating cell. with refilling of some old waste. Space required for Some old landfills can contain up to Ideally, the reclaimed cover soil should temporary storage 40% of cover soil. If soil has to be stored be transported from the screener of excavated temporarily, a significant area could be directly to your current soil source area. cover soil needed. Always a potential to discover this, Have a Contingency Plan for managing Hazardous wastes typically in drums. Special health these wastes if encountered. and safety issues will apply. is involved in excavating compacted waste, to stockpile recovered soils near or with other loading trucks, and moving as the excavation onsite cover stockpiles in order to handle the progresses. The other machines in a landfill materials only once. However, this approach mining operation, such as shredders, screens, may not always be feasible. If that is the case, magnets, and conveyors are generally static all of the mined soil may have to be tempo- (i.e., they are not moved for periods of rarily stockpiled separately. Soils can make time), and are processing materials that have up to 40% of the materials mined from old had some loosening and separation, and are landfills. In our previous example, that would for one function only, so their capacity usu- amount to approximately 153,000 cubic ally does not limit the operation. yards of soil, which would be equivalent to a If you are considering implementing a 4-acre stockpile area 40 feet high. landfill mining project, you should be real- istic about the time it will take to complete Benefit-Cost Assessment the project. This timeline needs to coordi- A benefit-cost assessment should be con- nated with the overalllandfilling activities ducted to justify pursuing a landfill mining of a site, assuming it's an active landfill, and project. One way to approach a benefit--cost remaining site life calculations. A mining assessment is to compare the estimated cost project and the necessity to dispose of much of mining the landfill cell against the value of the excavated materials back into the new of the "new" airspace that created by mining landfill can temporarily increase the landfill and used for future landfilling (Table 3), tonnage by up to 80% over your normal or the value of the reclaimed property. We throughput, if everything except the cover typically would not include the value of soils are put back in the landfill. any separated recyclables, because the value Take for example, an old landfill 40 feet of these recovered materials generally is high with a base dimension of 800 feet long inconsequential. by 500 feet wide, about a 9-acre footprint. That landfill will contain Table 3. Projected "Value" of New Airspace approximately 383,000 cubic yards Item Amount of material. Working with three Total volume 383,000 CY large bucket excavators (total bucket capacity 36 cubic feet), it Less reclaimed soil ~ 20% 76,600 CY would take at least a year, or more, Less all other materials ~ 42% 160,000 CY to complete excavating, working Net new airspace 146,400CY nine hours a day, 6 days a week, 102,500 tons without bad weather delay. Volume new waste at 1,400/CY The most efficient approach is "Value" of new airspace at $42/ton $4,305,000 [ www.mswmanagement.com l MSW MANAGEMENT 57 LANDFILL Table 2 summarizes a simple cost analysis x $4 per cubic yard) is equal to $1,532,000. Contrasting that to $250 per ton for mining for an example landfill mining project at Clearly, in this example, the reclamation and separation extrapolated from the Collier an active landfill based on the following benefit far outweighs the cost. If cover soil County study, plastic reclamation would not assumptions: has to be purchased from an outside source, provide any significant monetary benefit. • Landfill cell volume = 383,000 yd'. there could be another savings benefit by • Volume of reclaimed soil = 20% of reusing the recovered soil.
Recommended publications
  • Assessment of the Possible Reuse of Extractive Waste Coming from Abandoned Mine Sites: Case Study in Gorno, Italy
    sustainability Article Assessment of the Possible Reuse of Extractive Waste Coming from Abandoned Mine Sites: Case Study in Gorno, Italy Neha Mehta 1,2, Giovanna Antonella Dino 1,*, Iride Passarella 3, Franco Ajmone-Marsan 4, Piergiorgio Rossetti 1 and Domenico Antonio De Luca 1 1 Department of Earth Sciences, University of Turin, 10125 Torino, Italy; [email protected] (N.M.); [email protected] (P.R.); [email protected] (D.A.D.L.) 2 School of Mechanical and Aerospace Engineering, Queen’s University Belfast, Belfast, BT9 5AH, UK 3 Horizon s.r.l., 10095 Grugliasco (TO), Italy; [email protected] 4 Department of Agricultural, Forestry and Food Sciences, University of Turin, 10095 Grugliasco (TO), Italy; [email protected] * Correspondence: [email protected]; Tel.: +39-011-6705150 Received: 21 January 2020; Accepted: 17 March 2020; Published: 21 March 2020 Abstract: Supply of resources, a growing population, and environmental pollution are some of the main challenges facing the contemporary world. The rapid development of mining activities has produced huge amounts of waste. This waste, found in abandoned mine sites, provides the potential opportunity of extracting raw material. The current study, therefore, focuses on testing the validation of a shared methodology to recover extractive waste from abandoned mines, and applies this methodology to a case study in Gorno, northwest Italy. The methods focused on: (1) analyzing the impact of tailings and fine fraction of waste rock (<2 mm) on plants (Cress - Lepidium Sativum) to assess usability of both as soil additive, and (2) recovering raw materials from tailings and coarse fraction (>2 mm) of waste rock, by means of dressing methods like wet shaking table and froth flotation.
    [Show full text]
  • Integration of Resource Recovery Into Current Waste Management Through
    INTEGRATION OF RESOURCE RECOVERY INTO CURRENT WASTE MANAGEMENT THROUGH (ENHANCED) LANDFILL MINING Juan Carlos Hernández Parrodi 1,2,*, Hugo Lucas 3, Marco Gigantino 4, Giovanna Sauve 5, John Laurence Esguerra 6,7, Paul Einhäupl 5,7, Daniel Vollprecht 2, Roland Pomberger 2, Bernd Friedrich 3, Karel Van Acker 5, Joakim Krook 6, Niclas Svensson 6 and Steven Van Passel 7 1 Renewi Belgium SA/NV, NEW-MINE project, 3920 Lommel, Belgium 2 Montanuniversität Leoben, Department of Environmental and Energy Process Engineering, 8700 Leoben, Austria 3 RWTH Aachen University, Process Metallurgy and Metal Recycling, 52056 Aachen, Germany 4 ETH Zürich, Department of Mechanical and Process Engineering, 8092 Zürich, Switzerland 5 Katholieke Universiteit Leuven, Department of Materials Engineering, 3001 Leuven, Belgium 6 Linköping University, Environmental Technology and Management, 58183 Linköping, Sweden 7 Universiteit Antwerpen, Department of Engineering Management, 2000 Antwerpen, Belgium Article Info: ABSTRACT Received: Europe has somewhere between 150,000 and 500,000 landfill sites, with an estimat- 1 November 2019 Accepted: ed 90% of them being “non-sanitary” landfills, predating the EU Landfill Directive of 15 November 2019 1999/31/EC. These older landfills tend to be filled with municipal solid waste and Available online: often lack any environmental protection technology. “Doing nothing”, state-of-the- 23 December 2019 art aftercare or remediating them depends largely on technical, societal and eco- Keywords: nomic conditions which vary between countries. Beside “doing nothing” and land- Landfill mining strategies fill aftercare, there are different scenarios in landfill mining, from re-landfilling the Enhanced landfill mining waste into “sanitary landfills” to seizing the opportunity for a combined resource-re- Resource recovery covery and remediation strategy.
    [Show full text]
  • Cost of Organic Waste Technologies: a Case Study for New Jersey
    AIMS Energy, 3 (3): 450–462. DOI: 10.3934/energy.2015.3.450 Received date 28 June 2015, Accepted date 30 August 2015, Published date 15 September 2015 http://www.aimspress.com/ Research article Cost of organic waste technologies: A case study for New Jersey Gal Hochman 1,*, Shisi Wang 1, Qing Li 1, Paul D. Gottlieb 1, Fuqing Xu 2 and Yebo Li 2 1 Rutgers University, New Brunswick, NJ 08901, USA 2 The Ohio State University, Ohio 44691 * Correspondence: [email protected]; Tel: +1-848-932-9142 Abstract: This paper evaluates the benefits of converting food waste and manure to biogas and/or fertilizer, while focusing on four available waste treatment technologies: direct combustion, landfilling, composting, and anaerobic digestion. These four alternative technologies were simulated using municipal-level data on food waste and manure in New Jersey. The criteria used to assess the four technologies include technological productivity, economic benefits, and impact on land scarcity. Anaerobic digestion with gas collection has the highest technological productivity; using anaerobic digesters would supply electricity to nearly ten thousand families in New Jersey. In terms of economic benefits, the landfill to gas method is the least costly method of treating waste. In comparison, direct combustion is by far the most costly method of all four waste-to-energy technologies. Keywords: Organic waste; manure; combustion; land-fill gas; aerobic composting; anaerobic digestion 1. Introduction Population growth and urbanization yield an increase in the generation and disposal of waste. On average, each person in the U.S. produces 1.5 kilograms of municipal solid waste (MSW) per day.
    [Show full text]
  • Developing the Case for Enhanced Landfill Mining in the UK
    Developing the case for enhanced landfill mining in the UK Stuart Wagland Senior Lecturer, Energy & Environmental Chemistry IOSH Environmental Waste Management Group July 2021 www.cranfield.ac.uk Overview of webinar Enhanced landfill mining in the UK • Background- UK landfill legacy and concept of ELFM • Recent sampling work and experimental data • Risks associated with landfill mining and remediation • ELFM in Europe and the UK- the next steps 2 Landfills in UK Substantial resource for future exploitation Over 20,000 legacy and current landfills in the UK Licences required from 1974 under the Control of Pollution Act Over 4,000 licensed sites, most of which are now closed Currently over 40 million tonnes of waste from all sources is deposited in UK landfills each year 3 Firstly, what is enhanced landfill mining?? Landfill mining: Enhanced landfill mining [ELFM]: 'a process for extracting materials ‘the safe conditioning, excavation or other solid natural resources and integrated valorisation of from waste materials that (historic and/or future) landfilled previously have been disposed of waste streams as both materials by burying them in the ground' (Waste-to-Material, WtM) and energy (Waste-to-Energy, WtE), (Krook at al. 2012) using innovative transformation technologies and respecting the most stringent social and ecological criteria.' (Jones et al. 2013) 4 Landfill mining vs enhanced landfill mining 'Landfill mining' is limited to: ELFM goes further and aims to elicit higher recovery rates • Capturing of methane for and value: energy purposes • Recovery of some • In-situ and ex-situ recovery materials through physical • Waste to materials and excavation energy using innovative • Excavation for reclamation and state-of-the art of land (i.e.
    [Show full text]
  • Wastewater Disposal to Landfill-Sites
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Ghent University Academic Bibliography Journal of Environmental Management 128 (2013) 427e434 Contents lists available at SciVerse ScienceDirect Journal of Environmental Management journal homepage: www.elsevier.com/locate/jenvman Review Wastewater disposal to landfill-sites: A synergistic solution for centralized management of olive mill wastewater and enhanced production of landfill gas Vasileios Diamantis a,*, Tuba H. Erguder b, Alexandros Aivasidis a, Willy Verstraete c, Evangelos Voudrias a a Department of Environmental Engineering, Democritus University of Thrace, Vas. Sofias 12, 67100 Xanthi, Greece b Department of Environmental Engineering, Middle East Technical University, Ankara, Turkey c Laboratory of Microbial Ecology and Technology (LabMET), University of Ghent, Belgium article info abstract Article history: The present paper focuses on a largely unexplored field of landfill-site valorization in combination with Received 22 February 2013 the construction and operation of a centralized olive mill wastewater (OMW) treatment facility. The Received in revised form latter consists of a wastewater storage lagoon, a compact anaerobic digester operated all year round and 14 May 2013 a landfill-based final disposal system. Key elements for process design, such as wastewater pre- Accepted 25 May 2013 treatment, application method and rate, and the potential effects on leachate quantity and quality, are Available online 20 June 2013 discussed based on a comprehensive literature review. Furthermore, a case-study for eight (8) olive mill enterprises generating 8700 m3 of wastewater per year, was conceptually designed in order to calculate Keywords: fi Anaerobic digestion the capital and operational costs of the facility (transportation, storage, treatment, nal disposal).
    [Show full text]
  • Storing E-Waste in Green Infrastructure to Reduce Perceived Value Loss Through Landfill Siting and Landscaping: a Case Study in Nanjing, China
    sustainability Article Storing E-waste in Green Infrastructure to Reduce Perceived Value Loss through Landfill Siting and Landscaping: A Case Study in Nanjing, China Fu Chen 1,2,* , Xiaoxiao Li 2, Yongjun Yang 2, Huping Hou 2, Gang-Jun Liu 3 and Shaoliang Zhang 2 1 Low Carbon Energy Institute, China University of Mining and Technology, Xuzhou 221008, China 2 School of Environmental Science and Spatial Informatics, China University of Mining and Technology, Xuzhou 221008, China; [email protected] (X.L.); [email protected] (Y.Y.); [email protected] (H.H.); [email protected] (S.Z.) 3 Geospatial Science, College of Science, Engineering and Health, RMIT University, Melbourne, Victoria 3000, Australia; [email protected] * Correspondence: [email protected]; Tel.: +86-5168-388-3501 Received: 31 January 2019; Accepted: 25 March 2019; Published: 27 March 2019 Abstract: Electronic waste (e-waste) represents a severe global environmental issue due to the fast upgrading and updating of electronic products and the high environmental risk. Current low recycling technology, high economic cost, and weak disposal capability make it difficult for e-waste to be rendered 100% harmless. E-waste disposal requires new site-selection methods and site-saving technology to take into account the loss of public perceived value. This study attempts to improve e-waste disposal through siting and landscaping to reduce perceived value loss. The first step is to determine the minimum distance for landfill siting by surveying the minimum loss of perceived value and to use the geographic information system (GIS) to sketch the suitable landfill site thereafter.
    [Show full text]
  • Binning the Old Landfill Approach Using Global Innovations Presented By: Eric Mead
    Binning the Old Landfill Approach Using Global Innovations Presented By: Eric Mead 30 March 2017 © 2017 HDR, all rights reserved. Brisbane Sydney Melbourne HDR Overview 3 offices in Australia 10,000 professionals 250+ offices with a total of 150 staff “In the fight against litter and pollution, we still have so far to go.” - Iron Eyes Cody More focus on landfills means a greater need to: Maximise permitted airspace Optimise day-to-day operations Minimise expenditures Source: MSW in Texas 2015 Annual Review October 2016 Maximise Permitted Airspace MSE Walls Bioreactor Waffle Top Landfill Design Mining Mechanically Stabilised Earth (MSE) Walls Proposed Final Grades Property Boundary Permitted MSE Final Grades Wall MSE Walls Proposed Final Grades Permitted Final MSE Grades MSE Wall Wall Waffle Top Design . Hilltop vs ridges . Maintain highest elevation Bioreactor . Goal is to accelerate decomposition . Select waste . Control moisture . Renewable airspace Landfill Mining . Benefits o Cost reductions o Revenues o Increased property value o Additional disposal capacity . Risks o Unknown waste materials o LFG and odours o Water management o Dust and litter Landfill Mining Est. Waste Est. Waste Years Benefit of Source Property Value Landfill Volume Relocation Closed Removal Gained (USD) (Million M3) Cost (USD) Duvall 36 Medium 1.11 $25M $2M Houghton 50 Medium 0.93 $17M $31M Cedar Falls 31 High 1.22 $32M $2M Hobart 23 Low 1.30 $20M $2M Vashon 18 High 0.74 $24M $2M Puyallup 50 Medium 1.48 $27M $6M Enumclaw 24 Low 1.33 $24M $0M CHRLF 26 Medium 14.0 $146M $0M Optimise Day-to-Day Operations Intelligent Compaction Drones Fill Plans Equipment Aesthetics Environmental Traffic DENSITY Controls Human Resources Intelligent Compaction Drones .
    [Show full text]
  • Solid Waste Management in Ho Chi Minh City, Vietnam: Moving Towards a Circular Economy?
    sustainability Case Report Solid Waste Management in Ho Chi Minh City, Vietnam: Moving towards a Circular Economy? Petra Schneider 1,2,*, Le Hung Anh 3, Jörg Wagner 4, Jan Reichenbach 4 and Anja Hebner 5 1 C&E Consulting and Engineering GmbH, Jagdschänkenstraße 52, D-09117 Chemnitz, Germany 2 Department for Water, Environment, Civil Engineering and Safety, University of Applied Sciences Magdeburg-Stendal, Breitscheidstraße 2, D-39114 Magdeburg, Germany 3 Institute for the Environmental Science, Engineering & Management, Industrial University of Ho Chi Minh City, No. 12 Nguyen Van Bao, Ward 4, Ho Chi Minh City 00000, Vietnam; [email protected] 4 INTECUS GmbH Abfallwirtschaft und umweltintegratives Management, Pohlandstr. 17, D-01309 Dresden, Germany; [email protected] (J.W.); [email protected] (J.R.) 5 Vita 34 AG Business Unit BioPlanta, Deutscher Platz 5a, D-04103 Leipzig, Germany; [email protected] * Correspondence: [email protected]; Tel.: +49-391-886-4577 Academic Editor: Christian Zurbrügg Received: 30 November 2016; Accepted: 9 February 2017; Published: 17 February 2017 Abstract: The paper presents the current situation of the waste management system of the megacity Ho Chi Minh in Vietnam, and the options for waste and land recycling in a low income country. Generally, there is a large potential for circular economy in the city as the main proportion of the waste flows are recyclables. Due to the missing selective collection system, this potential is not used in the full extend yet, even if the collection of the entire waste volumes is envisaged in the National Waste Management Strategy by 2025.
    [Show full text]
  • Waste to Energy in the Age of the Circular Economy Best Practice Handbook
    WASTE TO ENERGY IN THE AGE OF THE CIRCULAR ECONOMY BEST PRACTICE HANDBOOK NOVEMBER 2020 ASIAN DEVELOPMENT BANK WASTE TO ENERGY IN THE AGE OF THE CIRCULAR ECONOMY BEST PRACTICE HANDBOOK NOVEMBER 2020 ASIAN DEVELOPMENT BANK Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) © 2020 Asian Development Bank 6 ADB Avenue, Mandaluyong City, 1550 Metro Manila, Philippines Tel +63 2 8632 4444; Fax +63 2 8636 2444 www.adb.org Some rights reserved. Published in 2020. ISBN: 978-92-9262-480-4 (print); 978-92-9262-481-1 (electronic); 978-92-9262-482-8 (ebook) Publication Stock No. TIM200330-2 DOI: http://dx.doi.org/10.22617/TIM200330-2 The views expressed in this publication are those of the authors and do not necessarily reflect the views and policies of the Asian Development Bank (ADB) or its Board of Governors or the governments they represent. ADB does not guarantee the accuracy of the data included in this publication and accepts no responsibility for any consequence of their use. The mention of specific companies or products of manufacturers does not imply that they are endorsed or recommended by ADB in preference to others of a similar nature that are not mentioned. By making any designation of or reference to a particular territory or geographic area, or by using the term “country” in this document, ADB does not intend to make any judgments as to the legal or other status of any territory or area. This work is available under the Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) https://creativecommons.org/licenses/by/3.0/igo/.
    [Show full text]
  • Economics of Landfill Mining
    Linköping Studies in Science and Technology Licentiate Thesis No. 1876 FACULTY OF SCIENCE AND ENGINEERING Esguerra Laurence John Linköping Studies in Science and Technology, Licentiate Thesis No. 1876, 2020 Department of Management and Engineering Economics of Linköping University SE-581 83 Linköping, Sweden Landfill Mining: www.liu.se Usefulness and Validity of Economics of Landfill Mining: Usefulness andValidity of Different Assessment Approaches Different Assessment Approaches John Laurence Esguerra Individual landfill mining project Landfill Input for Strategies mining the generic for the future economics model projects Multiple landfill mining projects in a region 2020 Linköping Studies in Science and Technology Licentiate Thesis No. 1876 Economics of Landfill Mining: Usefulness and Validity of Different Assessment Approaches John Laurence Esguerra Division of Environmental Technology and Management Department of Management and Engineering Linköpings universitet, SE-581 83 Linköping, Sweden Linköping, 2020 © John Laurence Esguerra, 2020 Printed in Sweden by LiU—Tryck, Linköping, 2020 ISBN 978-91-7929-852-4 ISSN 0280-7971 ii Economics of landfill mining: Usefulness and Validity of Different Assessment Approaches Abstract Landfill mining (LFM) is an alternative strategy to manage landfills that integrates remediation with secondary resource recovery. At present, LFM remains as an emerging concept with a few pilot-scale project implementations, which presents challenges when assessing its economic performance. These challenges include large knowledge deficits about the individual processes along the LFM process chain, lack of know-how in terms of project implementation and economic drivers, and limited applicability of results to specific case studies. Based on how these challenges were addressed, this thesis aims to analyze the usefulness and validity of different economic assessments of LFM towards the provision of better support for decision-making and in-depth learning for the development of cost-efficient projects.
    [Show full text]
  • Landfill Reclamation
    United States Solid Waste EPA530-F-97-001 Environmental Protection and Emergency Response July 1997 Agency (5306W) 1EPA Landfill Reclamation his fact sheet describes new and innovative technologies and products that meet the performance standards of the Criteria for Municipal Solid T Waste Landfills (40 CFR Part 258). Landfill reclamation is a relatively new approach used to expand municipal solid waste (MSW) landfill capacity and avoid the high cost of acquiring addi- tional land. Reclamation costs are often offset by the sale or use of recovered materials, such as recyclables, soil, and waste, which can be burned as fuel. Other important benefits may include avoided liability through site remediation, reductions in closure costs, and reclamation of land for other uses. Despite its many benefits, some potential drawbacks exist to landfill reclama- tion. This technology may release methane and other gases, for example, that result from decomposing wastes. It may also unearth hazardous materials, which can be costly to manage. In addition, the excavation work involved in reclamation may cause adjacent landfill areas to sink or collapse. Finally, the dense, abrasive nature of reclaimed waste may shorten the life of excavation equipment. To identify potential problems, landfill operators considering recla- mation activities should conduct a site characterization study. Landfill reclamation projects have been successfully implemented at MSW facilities across the country since the 1980s. This fact sheet provides information on this technology and presents case studies of successful reclamation projects. The Reclamation Soil Separation (Screening) A trommel (i.e., a revolving cylindrical sieve) Process or vibrating screens separate soil (including Landfill reclamation is conducted in a num- the cover material) from solid waste in the ber of ways, with the specific approach based excavated material.
    [Show full text]
  • Rawfill Landfill Miner Guide
    LANDFILL MINER GUIDE Copyright © 2021 RAWFILL Project partners, All rights reserved. Authors: Pascal Beese-Vasbender (BAV) David Caterina (University of Liège) Martje Ceulemans (VITO) Jonathan Chambers (British Geological Survey) Ben Dashwood (British Geological Survey) Renaud De Rijdt (ATRASOL) Stefanie De Smet (VITO) Alain Ducheyne (VITO) Cornelia Inauen (British Geological Survey) Itzel Isunza Manrique (University of Liège) Laura Lamair (SPAQuE) Simon Loisel (SAS Les Champs Jouault) Sébastien Moreaux (ATRASOL) Claudia Neculau (SPAQuE) Frédéric Nguyen (University of Liège) Marta Popova (SPAQuE) Michaël Van Raemdonck (OVAM) Gaëtan Vivien (SAS Les Champs Jouault) Arnaud Watlet (British Geological Survey) Eddy Wille (OVAM) This guide is the result of teamwork among the RAWFILL project partners. In detail, they respectively took responsibility for the following chapters: OVAM (Chapters 1, 2, 3 & 7), University of Liège and British Geological Survey (Chapter 4), ATRASOL (Chapters 5, 6, 8 & 9), SPAQuE (Chapters 9, 10 & 13) and VITO (Chapter 11). Table of contents 1 Rationale of RAWFILL project .......................................................................... 15 Introduction ........................................................................................... 15 Basic principles of the linear economy ........................................................ 15 Resources and reserves ........................................................................... 16 Scarcity, depletion and availability of resources: critical raw materials
    [Show full text]