Municipal Solid Waste Landfill Operation and Management Workbook
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Final Biosolids Management Plan September 2009 TABLE of CONTENTS
BIOSOLIDS MANAGEMENT PLAN Prepared for: Spokane County Division of Utilities 1026 West Broadway Avenue, Fourth Floor Spokane, WA 99260-0430 September 2009 Final Prepared by: HDR Engineering, Inc. TABLE of CONTENTS Table of Contents Introduction and Background .................................................................. 1 Previous Studies .................................................................................................. 1 Wastewater Facilities Plan ........................................................................ 1 Wastewater Facilities Plan Amendment .................................................... 2 Ecology Approval of Wastewater Facilities Plan ........................................ 3 Changes after the Wastewater Facilities Plan Amendment ....................... 3 2006 Wastewater Facilities Plan Amendment ........................................... 4 Environmental Analysis ............................................................................. 4 Authorization ........................................................................................................ 4 Purpose ................................................................................................................ 4 Plan Overview ...................................................................................................... 5 Spokane County Regional Water Reclamation Facility Overview ........ 6 SCRWRF Residuals ............................................................................................. 6 SCRWRF Biosolids -
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. -
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 -
GHOST GEAR: the ABANDONED FISHING NETS HAUNTING OUR OCEANS Sea Turtle Entangled in Fishing Gear in the Mediterranean Sea © Marco Care/Greenpeace CONTENTS
GHOST GEAR: THE ABANDONED FISHING NETS HAUNTING OUR OCEANS Sea turtle entangled in fishing gear in the Mediterranean Sea © Marco Care/Greenpeace CONTENTS 4 Zusammenfassung 5 Executive summary 6 Introduction 8 Main types of fishing – Nets – Lines – Traps & pots – FADs 11 Ghost gear impacts – Killing ocean creatures – Damaging habitats – Economic and other impacts 13 Current regulations – International agreements and recommendations – Other programmes and resolutions – A cross-sector approach – The need for a Global Ocean Treaty 16 References 2019 / 10 Published by Greenpeace Germany November 2019 Stand Greenpeace e. V., Hongkongstraße 10, 20457 Hamburg, Tel. 040/3 06 18 - 0, [email protected] , www . greenpeace . de Authors Karli Thomas, Dr. Cat Dorey and Farah Obaidullah Responsible for content Helena Spiritus Layout Klasse 3b, Hamburg S 0264 1 Contents 3 DEUTSCHE ZUSAMMENFASSUNG DER STUDIE GHOST GEAR: THE ABANDONED FISHING NETS HAUNTING OUR OCEANS → Rund 640.000 Tonnen altes Fischereigerät inklusive Geisternetzen, Bojen, Leinen, Fallen und Körbe landen jährlich als Fischereimüll in den Ozeanen. → Weltweit trägt altes Fischereigerät zu etwa zehn Prozent zum Plastikeintrag in die Meere bei. → 45 Prozent aller Arten auf der Roten IUCN-Liste hatten bereits Kontakt mit Plastik im Meer. → Sechs Prozent aller eingesetzten Netze, neun Prozent aller Fallen und 29 Prozent aller Langleinen gehen jährlich auf den Ozeanen verloren und enden als Meeresmüll. → Treibnetze, Fallen und Fischsammler (Fish Aggregating Devices, FADs) gehen weltweit am häufigsten als Müll auf den Ozeanen verloren und bergen die meisten Risiken für Meereslebewesen. → Durch FADs sterben 2,8 bis 6,7 Mal mehr Tiere - darunter bedrohte Arten wie Haie – als Beifang als die Zielarten, für die sie eingesetzt werden. -
PW061119-07 Project 2448 Cell 16 Final Cover Exhibit a Scope of Work
EXHIBIT A SCOPE OF SERVICES Cell 16 Final Cover Project No. 18-2448 / CIP 51202 The City of Rapid City has determined the need to procure professional engineering services including Preliminary Design Services, Final Design Services, and Bidding Services for the installation and placement of a final cover system and Gas Collection and Control System (GCCS) over the in-place municipal solid waste (MSW) in Cell 16. Basic Construction Services and Expanded Construction Services will be negotiated at a later date as a separate contract. In addition to the Cell 16 Final Cover and GCCS design, the City also has determined the need for professional services for the design, bidding, and construction of litter control netting along the perimeter of Cell 18 with emphasis on the western and northern portion. Services through construction of the litter control netting will be included in this scope of services but will be allocated exclusively to subtasks 1.13, 2.23, and 3.07. Task 4 and Task 5 in their entirety are exclusively reserved for the litter control project component. It is anticipated that the Cell 16 Final Cover improvements will include the following: 1. Preliminary final cover system design which will incorporate current permit requirements and South Dakota Department of Environment and Natural Resources (DENR) standards. 2. Analysis of current fill grades and relationship to final permitted contours. A ground survey will be required to determine if Landfill Operations has reached or exceeded permitted waste grades. 3. On-site geotechnical investigations for clay materials and borrow areas. 4. Integrating the proposed final cover system into the existing capped cells located to the north and east; also ensuring the future cells to the south may be filled adequately and efficiently against the proposed capped cells. -
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. -
Decommissioning Or Relining Domestic Wastewater Ponds
Decommissioning or Relining Domestic Wastewater Ponds Requirements and Procedures Purpose The purpose of this fact sheet is to describe regulatory requirements and provide guidance for the decommissioning or relining of domestic wastewater treatment ponds. These requirements may include (but are not limited to): • removal and disposal of biosolids • sealing/capping of any groundwater monitoring wells • proper demolition, capping, and elimination of treatment components Permittees with a domestic wastewater treatment pond system that are eliminating the use of ponds (either through replacement with a new treatment system, or closure of the treatment system altogether) cannot abandon the ponds “as is”, due to potential safety, environmental and human health hazards. Biosolids accumulated on the pond bottom contain a number of pollutants, nutrients, and pathogenic organisms that must be handled properly before abandoning or re-using the structure. When are Ponds Decommissioned? After domestic wastewater ponds cease to receive wastewater for treatment and all the flows are conveyed to another facility, the biosolids in them are subject to one of the following rules and must meet requirements for use or disposal. Rules and Regulations that Apply • 40 Code of Federal Regulation [CFR], ch. 503 Standards for the Use of Disposal of Sewage Sludge. This rule covers the options for the use or disposal of biosolids that are based on risk assessments done by the Environmental Protection Agency. This rule forms the basis of Minn. R. ch. 7041 for land application. • Minn. R. ch. 7041 – Biosolids Management Rule. This rule covers biosolids that are applied to the land for treatment and beneficial use. It also applies to the biosolids in a wastewater treatment pond once it ceases to receive wastewater. -
Urbanization As a Threat to Biodiversity: Trophic Theory, Economic Geography, and Implications for Conservation Land Acquisition
Proceedings of a Symposium at the Society for Conservation Biology 2004 Annual Meeting URBANIZATION AS A THREAT TO BIODIVERSITY: TROPHIC THEORY, ECONOMIC GEOGRAPHY, AND IMPLICATIONS FOR CONSERVATION LAND ACQUISITION Brian Czech1 ABSTRACT—Habitat loss is often cited as the primary cause of species endangerment in the United States, followed by invasive species, pollution, and direct take. Urbanization, one type of habitat loss, is the leading cause of species endangerment in the contiguous United States and entails a relatively thorough transformation from the “economy of nature” to the human economy. Principles of economic geography indicate that urbanization will continue as a function of economic growth, while principles of conservation biology indicate that the most thorough competitive exclusion occurs in urban areas. These findings suggest the need for an ecologically macroeconomic approach to conservation land acquisition strategies. “Habitat loss” is often cited as the primary cause of species these types of habitat loss are considered separate causes of endangerment in the United States, followed by invasive species endangerment, invasive species are identified as the species, pollution, disease, and direct take. However, vari- leading cause of species endangerment in the United States, ous types of habitat loss are readily identified, such as log- including Hawaii and Puerto Rico (Czech et al. 2000). On ging, mining, agriculture, and urbanization (table 1). When the mainland United States, however, urbanization is the Table 1.— Causes of endangerment for the first 877 (of the current 1,262) species in the United States and Puerto Rico classified as threatened or endangered by the United States Fish and Wildlife Service (from Czech et al. -
Toxic Tide: the Threat of Marine Plastic Pollution in Australia
The Senate Environment and Communications References Committee Toxic tide: the threat of marine plastic pollution in Australia April 2016 © Commonwealth of Australia 2016 ISBN 978-1-76010-400-9 Committee contact details PO Box 6100 Parliament House Canberra ACT 2600 Tel: 02 6277 3526 Fax: 02 6277 5818 Email: [email protected] Internet: www.aph.gov.au/senate_ec This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivs 3.0 Australia License. The details of this licence are available on the Creative Commons website: http://creativecommons.org/licenses/by-nc-nd/3.0/au/. This document was printed by the Senate Printing Unit, Parliament House, Canberra Committee membership Committee members Senator Anne Urquhart, Chair ALP, TAS Senator Linda Reynolds CSC, Deputy Chair (from 12 October 2015) LP, WA Senator Anne McEwen (from 18 April 2016) ALP, WA Senator Chris Back (from 12 October 2015) LP, WA Senator the Hon Lisa Singh ALP, TAS Senator Larissa Waters AG, QLD Substitute member for this inquiry Senator Peter Whish-Wilson (AG, TAS) for Senator Larissa Waters (AG, QLD) Former members Senator the Hon Anne Ruston, Deputy Chair (to 12 October 2015) LP, SA Senator the Hon James McGrath (to 12 October 2015) LP, QLD Senator Joe Bullock (to 13 April 2016) ALP, WA Committee secretariat Ms Christine McDonald, Committee Secretary Mr Colby Hannan, Principal Research Officer Ms Fattimah Imtoual, Senior Research Officer Ms Kirsty Cattanach, Research Officer iii iv Table of Contents List of recommendations ..................................................................................vii List of abbreviations ....................................................................................... xiii Chapter 1: Introduction ..................................................................................... 1 Conduct of the inquiry ............................................................................................ 1 Acknowledgement ................................................................................................. -
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. -
Rates of Particulate Pollution Deposition Onto Leaf Surfaces: Temporal and Inter-Species Magnetic Analyses
ARTICLE IN PRESS Environmental Pollution xxx (2010) 1–7 Contents lists available at ScienceDirect Environmental Pollution journal homepage: www.elsevier.com/locate/envpol Rates of particulate pollution deposition onto leaf surfaces: Temporal and inter-species magnetic analyses R. Mitchell a,*, B.A. Maher a, R. Kinnersley b a Centre for Environmental Magnetism and Palaeomagnetism, Lancaster Environment Centre, University of Lancaster, Lancaster LA1 4YQ, UK b Evidence Directorate, Environment Agency, Olton Court, 10 Warwick Road, Olton, Solihull B92 7HX, UK This research uses biomagnetic techniques to enable quantitative mapping of particulate pollution distribution at uniquely high spatial resolution. article info abstract Article history: Evaluation of health impacts arising from inhalation of pollutant particles <10 mm (PM10) is an active Received 1 September 2009 research area. However, lack of exposure data at high spatial resolution impedes identification of Received in revised form causal associations between exposure and illness. Biomagnetic monitoring of PM10 deposited on tree 11 December 2009 leaves may provide a means of obtaining exposure data at high spatial resolution. To calculate ambient Accepted 16 December 2009 PM10 concentrations from leaf magnetic values, the relationship between the magnetic signal and total PM10 mass must be quantified, and the exposure time (via magnetic deposition velocity (MVd) Keywords: calculations) known. Birches display higher MV (w5cmÀ1) than lime trees (w2cmÀ1). Leaf saturation Magnetic biomonitoring d w Deposition velocity remanence values reached ‘equilibrium’ with ambient PM10 concentrations after 6 ‘dry’ days (<3 mm/day rainfall). Other co-located species displayed within-species consistency in MV ; robust PM10 monitoring d Tree leaves inter-calibration can thus be achieved, enabling magnetic PM10 biomonitoring at unprecedented spatial Inter-species calibration resolution. -
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.