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Environmental implications of incineration of municipal solid waste and ash disposal.

Owing to unsightliness and the threat of groundwater pollution, landfilling of municipal solid waste (MSW) is giving way to incineration in many communities. Environmental contamination from particulate and gaseous emissions containing heavy metals, polychlorinated dibenzodioxins (PCDD) and polychlorinated dibenzofurans (PCDF), polycyclic aromatics (PCA), acids and other compounds from such incinerators, as well as safe ash disposal, are of great concern. Concentration ranges of elements and organic toxicants in incinerator ashes, emissions and cooling waters are given. The literature is reviewed concerning the effects of incinerator operating parameters on emissions. Incinerators equipped with modern pollution control devices (electrostatic precipitators, fabric filters, dry scrubbers, spray towers) and operated at optimum temperature with sufficient oxygen, turbulence (mixing) and residence time for complete combustion appear to minimize ash, elemental, gaseous and organic emissions. Environmental aspects of MSW incineration are considered and reviewed. The presence of metals and organics in incinerator quench water and in leachates from ash disposed in landfills are reviewed, as well as their toxicity to fish. The behavior and effects of atmospheric emissions in soils and plants are discussed. Research on the effect of ash-derived PCDD and PCDF on hepatic microsomal mixed function oxidase activity and the immune system in laboratory animals is cited. The presence of metals, organics and mutagens in the incinerator workplace air and the possible effects of air-borne contaminants on inhabitants nearby is reviewed. Several studies dealing with human risk assessment of MSW incineration are cited.

Animals↗

Canadian mercury inventories: the missing pieces.

Research was conducted to determine the significance of the deliberate use of mercury in products in Canada and the associated releases from these sources. Through a combination of literature review and new calculations, the reservoir, flux, and releases of mercury from eight product sources were calculated, and these results compared to historical Canadian inventories. Mercury contributions from the waste sector were also assessed and compared to total Canadian mercury releases and to mercury releases from coal-fired generating stations. Results suggest the use and release of mercury associated with release of mercury associated with its use in products is 4.5 times what previous inventories indicate. Including dental amalgam and sewage sludge, the total releases of mercury to all environmental compartments in Canada totals 20 tonnes per year. This accounts for less than one-half of the 44 tonnes per year of mercury released from mercury waste disposal each year in Canada. Waste mercury contributions from hazardous waste imports, unknown product sources, and incomplete information on the use of mercury in known products may account for this discrepancy. Waste-related mercury releases and transfers for disposal and recycling are 11 times greater than that of electricity generation in Canada. Results indicate that Canadian inventories have underestimated the significance of mercury use and release associated with products, calling into question the current priorities for mercury management. This paper was developed as part of a panel session at the International Joint Commission "Mercury in the Ecosystem" workshop, February 26-27, 2003, Windsor, ON, Canada, as a complement to the information on Canadian Inventories presented by Luke Trip (Senes Consulting, Ottawa, ON, Canada).

Canada↗

Management of infectious waste from hospitals.

In October 1980, 80% (120/150) of North Carolina (NC) hospitals responded to a comprehensive solid waste questionnaire intended to identify their solid waste disposal practices. NC hospitals generated an average of 13 lb. of solid waste/patient/day and infectious waste comprised 5% to 11% of the total hospital waste. Most hospitals (greater than 66%) considered blood, isolation, laboratory (including microbiology), pathology, and autopsy waste as infectious, while other sources of solid waste were generally considered non-infectious. The infectious wastes were normally incinerated or steam sterilized before discarding. Nearly all hospitals (95%) used a Class A landfill to dispose of the non-infectious waste. Two-thirds of the NC hospitals are discarding blood, microbiological, pathological, and isolation waste in accordance with the CDC recommendations, while the compliance rates for the JCAH and EPA recommendations for these wastes were 94% and 24%, respectively. If the EPA modified its recommendations to include incineration of microbiological waste, which is practiced by 50 responding NC hospitals, the compliance rate would be 95.5% for these wastes and 61.7% overall.

Centers for Disease Control and Prevention, U.S.↗

Disposal of faeces of children under two years old and diarrhoea incidence: a case-control study.

This is a report on the relationship of disposal of faeces of children under two years old and diarrhoeal incidence from a clinic-based case-control study. Based on data on 275 cases and 381 controls recruited from 16 clinics in Metropolitan Cebu in the Philippines over a five-month period, the results showed that unsanitary disposal of young children's stools was associated with a 34% increase (OR = 1.34) in clinically diagnosed diarrhoeas and a 63% increase (OR = 1.63) in pathogen-positive diarrhoeas relative to those who were following sanitary practices. Despite several methodological limitations, the findings suggest that the exposure variable under investigation might be an important risk factor for diarrhoeas. Further studies are indicated because of the value of identifying specific hygiene behaviours related to the transmission of enteric pathogens for purposes of formulating interventions.

Case-Control Studies↗

Environmental justice in Indian country: dumpsite remediation on the Swinomish Indian reservation.

The U.S. Environmental Protection Agency (EPA) defines environmental justice as the "fair treatment for people of all races, cultures, and incomes, regarding the development of environmental laws, regulations, and policies." The last decade has focused considerable national attention on the environmental pollution inequity that persists among the nation's poorest communities. Despite these environmental justice efforts, poor communities continue to face adverse environmental conditions. For the more than 550 Native American communities, the struggle to attain environmental justice is more than a matter of enforcing national laws equitably; it is also a matter of a federal trust duty for the protection of Indian lands and natural resources, honoring a promise that Native American homelands would forever be sustainable. Equally important is the federal promise to assist tribes in managing their reservation environments under their reserved powers of self-government, an attribute that most distinguishes tribes from other communities. The PM Northwest, Inc. (PMNW) dumpsite is located within the boundaries of the Swinomish Indian Reservation in Washington State. Between approximately 1958 and 1970, PMNW contracted with local oil refineries to dispose of hazardous wastes from their operations at the reservation dumpsite. Almost two decades would pass before the Swinomish tribe was able to persuade EPA that a cleanup action under Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) was warranted. This article reviews the enduring struggle to achieve Indian environmental justice in the Swinomish homeland, a process that was dependent upon the development of the tribe's political and environmental management capacity as well as EPA's eventual acknowledgement that Indian environmental justice is integrally linked to its federal trust responsibility.

Environment↗

Determination of polybrominated diphenyl ethers in soil and sediment from an electronic waste recycling facility.

Soil and sediment collected in the vicinity of an open electronic waste disposal and recycling facility located in Guiyu, Guangdong, China, were analyzed for the levels of common polybrominated diphenyl ethers (PBDEs) by using soxhlet extraction and gas chromatography/mass spectrometry. The PBDEs were detected in the soil and sediment samples at levels of 0.26-824 ng/g (dry weight). The obtained isomer profiles of PBDEs from the two soil samples collected from different contamination sites were found to be similar to various technical formulations of fire retardant products.

China↗

Integrated analysis for pre-sorting and waste collection schemes implemented in Spanish cities.

Over recent years, European cities have been questioning their traditional pre-sorting and waste collection practices and looking for new schemes to improve environmental problems generated by waste disposal. This paper presents an integral methodology for four pre-sorting practices that are beginning to be implemented in Spanish cities. A great effort has been made to compile information to be able to estimate a large number of valuation indexes. Based on this information, the methodology is supported by the forecasting of waste generation, the use of GIS techniques, the definition of objectives and their evaluation taking into account legal, social, performance, environmental and economic issues. Special attention is given to environmental impact, for which life cycle assessment methodology is used.

Cities↗

European policy on biodegradable waste: a management perspective.

The main characteristics of the European environmental policy are reviewed. Focusing on EU policy on waste, the paper presents the principles on which EU waste management is founded, particularly the waste hierarchy. In this hierarchy, priority shall be given to prevention of the generation of wastes and of its hazardousness. Secondly, the reuse and the recovery of materials (recycling), which implies the separation of waste at source involving consumers in the scheme of waste management. Priority should be given to material recycling over energy recovery. The less desirable option is the disposal of waste. The paper reviews specific directives on organic waste management, following the scheme of the waste hierarchy, together with the general trends observed in producing common regulations for all types of organic residuals. Afterwards, key issues and measures for the implementation of a feasible strategy for organic residuals management, e.g. quality requirements and quality assurance, are discussed. Finally, there is a view from a manager's perspective on the current EU policy, public acceptance and suitable waste management operations.

Biodegradation, Environmental↗

Hazard to man and the environment posed by the use of urban waste compost: a review.

This review presents the current state of knowledge on the relationship between the environment and the use of municipal waste compost in terms of health risk assessment. The hazards stem from chemical and microbiological agents whose nature and magnitude depend heavily on the degree of sorting and on the composting methods. Three main routes of exposure can be determined and are quantified in the literature: (i) The ingestion of soil/compost mixtures by children, mostly in cases of pica, can be a threat because of the amount of lead, chromium, cadmium, PCDD/F and fecal streptococci that can be absorbed. (ii) Though concern about contamination through the food chain is weak when compost is used in agriculture, some authors anticipate accumulation of pollutants after several years of disposal, which might lead to future hazards. (iii) Exposure is also associated with atmospheric dispersion of compost organic dust that convey microorganisms and toxicants. Data on hazard posed by organic dust from municipal composts to the farmer or the private user is scarce. To date, microorganisms are only measured at composting plants, thus raising the issue of extrapolation to environmental situations. Lung damage and allergies may occur because of organic dust, Gram negative bacteria, actinomycetes and fungi. Further research is needed on the risk related to inhalation of chemical compounds.

Agriculture↗

The flux and mass balance of PCDD/F in a MSW incineration full scale plant.

PCDD/F are one of the most significant environmental concerns of municipal solid waste disposal through incineration processes. With the main purpose of evaluating their presence along the flue gas line and establishing a mass balance over the whole system, an extensive research study was performed on a full scale plant. Present paper reports the main results obtained, with particular reference to the PCDD/F concentration profiles and mass balance in the post-furnace region. where significant formation of these compounds might take place. PCDD/F mass fluxes evaluated in all the residues arising from the process are also reported.

Air Pollutants↗

Disposal of arsenic in copper discharge slags.

Arsenic, which is a toxic pollutant, is present in copper minerals in concentrations to around 1 wt.%. During processing of such copper feed materials, the arsenic has to be transformed into an environmentally acceptable form. Laboratory experiments have been carried out to determine the feasibility of incorporating the arsenic in discharge slags for long-term disposal. Iron arsenate (FeAsO(4)) samples were prepared and tested under various conditions. Upon heating to about 900 degrees C, basically no arsenic was lost. However, at and above 1000 degrees C, iron arsenate decomposes rapidly and arsenic volatilizes. The incorporation of iron arsenate in liquid slags at around 1250 degrees C was difficult due to rapid arsenate decomposition and dust losses during the injection process. Although the leaching tests showed that the slags could meet environmental regulations, the fraction of arsenic leached was no less for the slag samples than for the initial iron arsenate itself.

Arsenic↗

An overview of EPA regulation of the safe disposal of transuranic waste at the Waste Isolation Pilot Plant.

In March of 1999, the Waste Isolation Pilot Plant (WIPP) in southeast New Mexico, the world's first deep geological repository for radioactive materials, began receiving defense-related transuranic waste. The WIPP was designed and constructed by the U.S. Department of Energy, but critical to its opening was certification by the U.S. Environmental Protection Agency that the repository complies with the radioactive waste disposal regulations set forth as environmental radiation protection standards (40 CFR Part 191) and compliance criteria (40 CFR Part 194). This paper provides a summary of the regulatory process, including the Environmental Protection Agency's waste containment, groundwater protection, and individual dose regulations for the WIPP; the Department of Energy's performance assessment and the other parts of its compliance certification application; and the Environmental Protection Agency's review and analysis of the compliance certification application and related documentation.

Government Agencies↗

The blighted hills of Roro, Jharkhand, India: a tale of corporate greed and abandonment.

In the Chaibasa region of the West Singhbhum district of Jharkhand, India, an abandoned chrysotile asbestos mine is a health scourge for villagers and former mine workers. A massive pile of asbestos waste mixed with chromite has lain atop the hilltops of Roro village for two decades, gradually seeping into the land, water, homes, and bodies of the tribal communities living at the foothills of Roro. To investigate the status of the asbestos waste and its impact on the community and the environment, a fact-finding team made a preliminary assessment. Its findings suggest that the careless closure of the mines and the unscientific disposal of toxic asbestos and chromite waste by the mining company pose a serious threat to the health of the local community and the environment. The preliminary health survey of 14 villages around the Roro hills, with 45% of the respondents being former workers of the Roro asbestos mines, indicates a highly probable link between the asbestos exposures and several adverse health effects such as low back pain, dyspnea, hemoptysis, and blindness.

Adult↗

Use of selected waste materials in concrete mixes.

A modern lifestyle, alongside the advancement of technology has led to an increase in the amount and type of waste being generated, leading to a waste disposal crisis. This study tackles the problem of the waste that is generated from construction fields, such as demolished concrete, glass, and plastic. In order to dispose of or at least reduce the accumulation of certain kinds of waste, it has been suggested to reuse some of these waste materials to substitute a percentage of the primary materials used in the ordinary portland cement concrete (OPC). The waste materials considered to be recycled in this study consist of glass, plastics, and demolished concrete. Such recycling not only helps conserve natural resources, but also helps solve a growing waste disposal crisis. Ground plastics and glass were used to replace up to 20% of fine aggregates in concrete mixes, while crushed concrete was used to replace up to 20% of coarse aggregates. To evaluate these replacements on the properties of the OPC mixes, a number of laboratory tests were carried out. These tests included workability, unit weight, compressive strength, flexural strength, and indirect tensile strength (splitting). The main findings of this investigation revealed that the three types of waste materials could be reused successfully as partial substitutes for sand or coarse aggregates in concrete mixtures.

Construction Materials↗

Numerical modelling of the generation and transport of heat in a bottom ash monofill.

Municipal solid waste is incinerated to reduce its volume, toxicity and reactivity. Several studies have shown that the resulting bottom ash has a high exothermic capacity. Temperature measurements in municipal solid waste incineration (MSWI) bottom ash landfills have found temperatures up to 90 degrees C. Such high temperatures may affect the stability of the landfill's flexible polymer membrane liner (FML) and may also lead to an accelerated desiccation of the clay barrier. The purpose of this study was to gain detailed knowledge of temperature development under several disposal conditions in relation to the rate of ash disposal, the variation of layer thickness, and the environmental conditions in a modern landfill. Based on this knowledge, a simulation was developed to predict temperature development. Temperature development was simulated using several storage periods prior to the deposition and several modes of emplacement. Both the storage time and the mode of emplacement have a significant influence on the temperature development at the sensitive base of the landfill. Without a preliminary storage of the fresh quenched bottom ash, high temperatures at the bottom of a landfill cannot be avoided.

Air Movements↗

Why confined aquatic disposal cells often make sense.

Confined aquatic disposal (CAD) cells are increasingly becoming the selected option for the management of unacceptably contaminated sediments. CAD cells are selected as the preferred alternative because this approach provides an acceptable compromise when cost, logistics, regulatory acceptance, environmental risk, and perception of various alternatives are considered. This preference for CAD cells often occurs even when other alternatives with similar risk reduction and less cost, such as an open water capping alternative, are considered as options. This paradox is largely a result of subjective factors that affect regulatory acceptance such as public perceptions.

Costs and Cost Analysis↗

[Carcass disposal in Hungary (author's transl)].

In Hungary more than half of the entire livestock is kept in industrial breeding plants i.e. under mass breeding conditions. So long as the industrial capacity of the plants remains insufficient to process the volume of carcasses, the animal breeding plants are compelled to find their own solutions for the disposal and/or rendering of the carcasses and waste. On some state farms the carcasses are processed into so-called meat-mash which must be utilised as fodder within 48 hours after the death of the animal. High-quality meat-meal can only be obtained from fresh carcasses. Carcasses are processed for reasons of economy, but the methods of carcass disposal are subject to stringent requirements imposed by the public health service, veterinary hygiene inspectorates and by the environment protection authorities. The carcasses or slaughter-house waste destined for processing must not contain any pathogens likely to be injurious to man or animal or to threaten the health of the persons concerned with the carcass processing. For this reason the carcasses must be kept in boilers for 2 to 4 hours at a pressure of 4 atü. The formulation of the factory rules and the technology of processing must make due allowance for these stipulations.

Abattoirs↗

Trees as indicators of subterranean water flow from a retired radioactive waste disposal site.

Tree sampling helped locate a subterranean flow of tritiated water from a low-level radioactive waste disposal site that had not been detected by well water monitoring alone. Deciduous trees growing in a natural forest on the hillsides downslope from the site were sampled for the presence of tritiated water in sap of maple trees and in leaf water extracted from oak and hickory trees. Elevated concentrations of 3H were detected in the leaf water extracted from several trees located 50 m downslope from the western boundary of the fenced exclusion zone. A 3-m-deep well drilled near these trees indicated that the source of tritiated water was a narrow zone of subterranean flow.

Radioactive Waste↗