Environmental and Health Risks Associated with Biomedical Waste Management
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Non-Incineration Medical Waste Treatment Technologies
Non-Incineration Medical Waste Treatment Technologies A Resource for Hospital Administrators, Facility Managers, Health Care Professionals, Environmental Advocates, and Community Members August 2001 Health Care Without Harm 1755 S Street, N.W. Unit 6B Washington, DC 20009 Phone: 202.234.0091 www.noharm.org Health Care Without Harm 1755 S Street, N.W. Suite 6B Washington, DC 20009 Phone: 202.234.0091 www.noharm.org Printed with soy-based inks on Rolland Evolution, a 100% processed chlorine-free paper. Non-Incineration Medical Waste Treatment Technologies A Resource for Hospital Administrators, Facility Managers, Health Care Professionals, Environmental Advocates, and Community Members August 2001 Health Care Without Harm www.noharm.org Preface THE FOUR LAWS OF ECOLOGY . Meanwhile, many hospital staff, such as Hollie Shaner, RN of Fletcher-Allen Health Care in Burlington, Ver- 1. Everything is connected to everything else, mont, were appalled by the sheer volumes of waste and 2. Everything must go somewhere, the lack of reduction and recycling efforts. These indi- viduals became champions within their facilities or 3. Nature knows best, systems to change the way that waste was being managed. 4. There is no such thing as a free lunch. Barry Commoner, The Closing Circle, 1971 In the spring of 1996, more than 600 people – most of them community activists – gathered in Baton Rouge, Up to now, there has been no single resource that pro- Louisiana to attend the Third Citizens Conference on vided a good frame of reference, objectively portrayed, of Dioxin and Other Hormone-Disrupting Chemicals. The non-incineration technologies for the treatment of health largest workshop at the conference was by far the one care wastes. -
Biomedical Waste
CHAPTER 31 BIOMEDICAL WASTE by George F. Indest III, JD, MPA, LL.M SCOPE Every physician's office or clinic in the state of Florida that uses or generates any type of sharps (including needLes, bLades, test tubes, etc.) or waste that may be saturated with bodily fluids (including gauze, bandages, swabs, etc.) must have in pLace a biomedicaL waste pLan. This must include written procedures on handLing, storing and disposing of biomedicaL waste. The requirements for storing, trans porting or disposing of any type of biomedicaL waste are set forth in various Florida Administrative Code sections, which are reviewed in detail in this chapter. We aLso present a sampLe PoLicy and Procedures that may be adopted for physicians' offices and a more detailed sampLe BiomedicaL Waste PLan that meets aLL state require ments that may be adapted for use by physicians' offices. SYNOPSIS §31.0 1 Key Terms and Definitions §31.02 Generators of Biomedical Waste §31.03 Mixed Waste §31.04 Treatment §31.05 Regulatory Authority for Biomedical Waste §31.06 Permits and Fees [1] Permits [2] Fees §31.07 Inspections §31.08 Procedures for Biomedical Waste [1] Written Policies and Procedures (DC Press) 31-1 31-2 THE FLORIDA HEALTHCARE PROFESSIONALS' MEDICO-LEGAL GUIDE §31.01 [2] Training [3] Records §31.09 Storage, Containment and Labeling [1 ] Storage [2] Containment [A] "Red Bags " [B] Sharps Containers [C] Outer Containers [D] Compacting by Generators [3] Labeling §31.10 Treatment of Biomedical Waste §31.11 Methods for Treatment of Biomedical Waste §31.12 Acute -
DTE Green Waste to Fuel™ Technology
DTE Green Waste to Fuel™ Technology The DTE Green Waste to Fuel™ Series of Reports A Report by Delta Thermo Energy Labs, a Division of Delta Thermo Energy™ June 25, 2016 Notice Delta Thermo Energy Labs reports, white papers and legal updates are made available for educational purposes only. Our purpose is to provide general information only. At the time of publication all information referenced in our reports, white papers and updates, is as current and accurate as we could determine. As such, any additional developments or research, since publication, will not be reflected in this report. Please note that these materials may be changed, improved, or updated without notice. Delta Thermo Energy is not responsible for any errors or omissions in the content of this report or for damages arising from the use of this report under any circumstances. Delta Thermo Energy, Inc. Confidential and Proprietary Material Page 2 of 17 Copyright June 1, 2016 - All Rights Reserved Disclaimer Many of the competitive technologies identified within this report are many years old and some have been in use for many decades. Delta Thermo Energy many not be aware of the latest advances put in place by individual plant operators or by their suppliers and subcontractors. Comparisons with new Delta Thermo Energy DTE Green Waste to Fuel technology and the underlying core technology we use is based upon publicly available information available to us. Our core technology, DTE Hydrothermal Decomposition™, is supported by proprietary and unique intellectual property protected by existing and pending patents. Trade secrets are also part of our operating procedures and implementation and our necessary to achieve stated performance levels. -
Reclamation of Acidic Copper Mine Tailings Using Municipal Biosolids1
RECLAMATION OF ACIDIC COPPER MINE TAILINGS USING MUNICIPAL BIOSOLIDS1 by M. T. Rogers, S.A. Bengson, and T.L. Thompson2 Abstract: Reclamation of copper mine tailings in a cost effective, successful, and sustainable manner is an ongoing area of evaluation in the arid southwest. A study was initiated in September, 1996 near Hayden, Arizona to evaluate the use of municipal biosolids for reclaiming acidic copper mine tailings (pH of 2.5 to 4.0). The main objectives of the study were to I) define an appropriate level of biosolids application for optimum plant growth, and 2) evaluate the effects of green waste and lime amendments. The experiment was a randomized complete block design with four biosolid rates of 20, 70, 100 and 135 dry tons/acre (45, 157, 224, 303 Mg/ha), three amendment treatments (none, green waste, and green waste plus lime); with three replications. Non-replicated controls (no treatment, green waste only and lime only) were included for comparison. Shortly after biosolids incorporation to a depth of 10-12 inches (25.4-30.5 cm), composite soil samples (0- 12 inches) of each plot were taken. Biosolids incorporation increased the pH of the tailings (>5. 75) and additional increases in pH were noted with lime application. In January 1997, the plots were seeded and sprinkler irrigation was commenced. A total of 4.47 inches (11.4 cm) of rainfall and 3.8 inches (9.7 cm) of irrigation were applied until harvest in May 1997. Data from the first growing season indicates optimum growth (>66 lbs/acre or >74 kg/ha) at biosolids rates of 70-100 dry tons/acre. -
“Disposal of Biomedical Waste and Law”, *Rahul Chourey
Volume 2, July 2018 ISSN 2581-5504 “Disposal of Biomedical Waste and Law” Rahul Chourey B.A.LL.B. (Hons.) Indore Institute of Law Introduction Since beginning hospitals are health care institution which provide treatment to patients by performing different methods but people are unaware about its effect of waste generated. The adverse effect of the garbage generated by hospitals on the environment and human being is dangerous. It is creating health hazard to the health care workers, general public and nearby flora & fauna. The waste generated from the hospitals is biomedical waste. It is a kind of waste contain infectious materials and may also include the used and unused bandages, infusion kits and other laboratory waste which contain biomolecules or organism that are restricted for environment release. It may be in solid or liquid form. Definition Bio medical waste means any waste, which is generated during the diagnosis, treatment or immunization of human beings or animals or in research activities pertaining there to or in the testing of biological and including categories mentioned in schedule 1.1 The biological waste excised from a patient during surgery, which is disposed of in hazardous waste receptacles at the end of the procedure.2 The Biomedical Management Rules In year 1986 the act was passed by the ministry of environment and forest and notified the rules in July 1998 relating to Bio-medical waste (management and handling). According to act passed by the ministry in 1986 and rules notified in July 1998, it is the duty of occupier of the institution, to take all the necessary step to dispose of the waste generated out of his possession without any adverse effect to environment, flora and fauna and human being. -
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. -
Preliminary Assessment Waste Management
Executive Summary 1 The purpose of this report is to make a preliminary assessment of green jobs potentials in the waste management sector in Lebanon, including solid waste management, hazardous waste management and wastewater treatment. This report provides an overview of waste management in Lebanon, considers potentials for greening the sector, and estimates current and future green jobs in waste management. The current state of the waste management sector in Lebanon is far from ideal. Collection activities are fairly advanced when it comes to municipal solid waste, but insufficient for wastewater, and totally lacking for hazardous waste. Currently only two-thirds of the total generated solid waste undergoes some form of treatment, while the remainder is discarded in open dumpsites or directly into nature. Moreover, wastewater treatment is insufficient and Lebanon currently lacks any effective strategy or system for dealing with most hazardous waste. Incrementally, the sector is nonetheless changing. In recent years green activities such as sorting, composting and recycling have become more common, advanced medical waste treatment is being developed, and several international organisations, NGOs and private enterprises have launched initiatives to green the sector and reduce its environmental impact. Also large-scale governmental initiatives to close down and rehabilitate dumpsites and construct new waste management facilities and wastewater treatment plants are currently being planned or implemented, which will have a considerable impact in greening the waste management sector in Lebanon. In this report, green jobs in waste management are defined as jobs providing decent work that seek to decrease waste loads and the use of virgin resources through reuse, recycling and recovery, and reduce the environmental impact of the waste sector by containing or treating substances that are harmful to the natural environment and public health. -
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 -
Recycling Tips
RECYCLING TIPS www.KeepingVenturaCountyClean.com Recyclable Materials Paper Material Cardboard Plastic • Books (paperback and hard cover okay) • Cereal & Food Boxes (Flatten for more recycling) • Bottles, Jars, Jugs, Tubs (look for recycling • Catalogs / Brochures / Phone Books • Clean Pizza Boxes (no wax coating and or food logo on bottom labeled #1 - #7, no need to rinse) • Junk Mail & Envelopes (windows okay) waste) • Grocery Bags • File Folders Glass • Nursery Pots • Milk & Juice Cartons • Bottles & Jars- Green, Brown, Clear (lids & • Plastic Toys • Magazines & Newspappers labels okay, no need to rinse) • Yogurt Containers • Paper - All colors (staples in paper okay) Aluminum & Tin Cans Other • Paper Grocery Bags • Aluminum Food Trays • Shredded Paper (put in plastic bag and tie • Beverage Cans • Athletic Shoes securely) • Vegetable & Soup Cans Non-Recyclable Materials • Animal Waste • Liquids • Restaurant Grease/Oil • Bubble Wrap Packaging • Laminated Paper • Sharps • Chip Bags & Candy Wrappers • Napkins • Solar Panels • Electronic Waste (computers, monitors, lap tops, • Paper Towels • Tires mobile devices) • Plastic 3-Ring Binders • Used Paper Plates & Cups • Fluorescent Light Bulbs • Plastic Cups, Lids & Straws • Used Plastic Utensils • Food Waste (including fruit) • Plastic Food Wrapping • Window Pane Glass/Mirrors • Hazardous Waste (paint, automotive oil, • Polystyrene foam including foam cups, • Yard Waste (grass clippings, branches, batteries, solvents) plates, and packing materials leaves) WARNING! Electronic, Sharps, or Hazard -
Biomedical Waste Management
BIOMEDICAL WASTE MANAGEMENT PLEASE REFER TO THE USF BIOMEDICAL WASTE PLAN OR CONTACT EH&S FOR MORE INFORMATION IDENTIFICATION Biomedical waste is any solid or liquid waste which may present a threat of infection to humans. · Body fluids (excluding urine, feces, vomit, saliva, sweat, tears and sputum) · Blood and blood products · Animals, animal and human parts/tissues/blood that contain human disease-causing agents · Used absorbent materials such as bandages, gauze, or sponges which are saturated with blood or body fluids - Non-absorbent items visibly contaminated with body fluids (i.e. plastic, vinyl, latex, rubber, glass devices) · All Needles and needle-syringe units. Do not recap Universal Biomedical Waste Symbol needles. · Scalpels, razor blades, hard plastic or glass contaminated with tissues, blood, blood products, or body fluids. LABELING & HANDLING All sealed biomedical red bags and sharps SEGREGATION containers must be labeled with the universal Biomedical waste must be separated from all other biomedical waste symbol and the words waste and placed in either a sharps container or a “Biomedical Waste”, the facility name (e.g. USF), red bag at the point of origin. address, phone number and contact name Biomedical waste mixed with chemical waste must Wear a lab coat and gloves and use a rolling cart be managed as hazardous waste. Separate if to transfer waste to an outside storage container. possible. STORAGE & TRANSPORT Dispose of only biomedical waste into biomedical Red bags must meet ASTM D1922-89 and ASTM waste containers – no regular trash. D1709 -91 standards. Contact the manufacturer to The following may be placed into the regular trash if ensure requirements are met prior to ordering. -
Speedway Recycling Facility Planned Area Development Speedway Boulevard and Prudence Road Tucson, Arizona
This document was printed on recycled paper certified by the Sustainable Forestry Initiative Speedway Recycling Facility Planned Area Development Speedway Boulevard and Prudence Road Tucson, Arizona Submitted to: City of Tucson Planning and Development Services Department 201 North Stone Avenue Tucson, Arizona 85701 Prepared for: The Fairfax Companies, LLC P.O. Box 31748 Tucson, Arizona 85751 Telephone: (520) 624-5600 Prepared by: The Planning Center 110 South Church Avenue, Suite 6320 Tucson, Arizona 85701 Telephone: (520) 623-6146 With assistance from: Curtis Lueck & Associates 1568 North Wild Bart Court Tucson, Arizona 85745 Telephone: (520)207-3358 And: Rick Engineering Company 3945 East Fort Lowell Road Tucson, Arizona 85712 Telephone: (520) 795-1000 FINAL VERSION June 18, 2013 This document was printed on recycled paper certified by the Sustainable Forestry Initiative Speedway Recycling Facility Planned Area Development I. Introduction ................................................................................... 1 A. Background .................................................................................................................... 1 B. Project Overview ............................................................................................................ 1 C. Rationale and Benefits for Use of a PAD ....................................................................... 6 D. Conformance with the General Plan and City Land Use Plans ...................................... 6 E. Compatibility with Adjoining Land -
Standards for Treatment and Disposal of Bio-Medical Waste by Incineration Size
STANDARDS FOR TREATMENT AND DISPOSAL OF BIO-MEDICALWASTE BY INCINERATION AND PLASMA PYROLYSIS OR GASIFICATION (As per Schedule II of the Bio-medical Waste Management Rules, 2016) 1. STANDARDS FOR INCINERATION.- All incinerators shall meet the following operating and emission standards- A. Operating Standards 1). Combustion efficiency (CE) shall be at least 99.00%. 2). The Combustion efficiency is computed as follows: %C02 C.E. = ------------ X 100 %C02 + % CO 3). The temperature of the primary chamber shall be a minimum of 800 0C and the secondary chamber shall be minimum of 10500C + or - 500C. 4). The secondary chamber gas residence time shall be at least two seconds. B. Emission Standards Sl. Parameter Standards No. 1. 2. 3. 4. Limiting Sampling Duration in minutes, concentration in unless stated 3 mg/Nm unless stated 1. Particulate matter 50 30 or 1NM3 of sample volume, whichever is more 2. Nitrogen Oxides NO and 400 30 for online sampling or grab NO2 expressed asNO2 sample 3. HCl 50 30 or 1NM3 of sample volume, whichever is more 4. Total Dioxins and Furans 0.1ngTEQ/Nm3 (at 8 hours or 5NM3 of sample 11% O2) volume, whichever is more 5. Hg and its compounds 0.05 2 hours or 1NM3 of sample volume, whichever is more C. Stack Height: Minimum stack height shall be 30 meters above the ground and shall be attached with the necessary monitoring facilities as per requirement of monitoring of ‘general parameters’ as notified under the Environment (Protection) Act, 1986 and in accordance with the CPCB Guidelines of Emission Regulation Part-III.