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At least 19 recordsLinked to original sources

Hazardous wastes, hazardous materials and environmental health inequity.

This paper reviews issues associated with the equity of locating hazardous waste sites and hazardous materials. Reports and case studies indicate that hazardous waste sites and the locations of hazardous materials are disproportionately situated near minority communities, especially African-American communities. This inequitable placement of hazardous waste sites is of concern, since exposure to toxic waste can adversely affect human health. Proximity to these sites may place these minority communities at higher risk of developing cancers and respiratory, cardiovascular, and neurological diseases, and of incurring increased levels of individual and family stress. The health of persons in minority communities near hazardous waste sites is further compromised by their lack of access to adequate health care. The potential health risks borne by racial and ethnic minorities and by low income communities as a consequence of exposure to toxic waste constitutes environmental inequity. In order to decrease the burden of these risks, we recommend developing environmental policies that address environmental inequity; conducting detailed demographic and health studies that assess the impact of exposure to toxic waste on minority populations; and devising educational programs to sensitize professional service providers and prevent exposure by community residents. This paper identifies research needs and opportunities.

Environmental Exposure↗

Handling hazardous waste.

Hazardous waste management is a concern for every healthcare organization. A system for managing such waste must meet guidelines from various sources and be comprehensive enough to ensure the safety of the institution's employees and guests, and of the community. An integral part of a hazardous waste management system is employee training. "Employees must be trained to make use of the information that will be available to them. This includes knowing the hazards of the materials they use, how to use the appropriate protective clothing and equipment, what steps to take if there is an accidental release or over-exposure..." and much more. The institution's success in managing hazardous wastes and maintaining a safe environment will depend on the adequacy of its employee training.

Accident Prevention↗

Hazardous waste management system: standards applicable to generators of hazardous waste and standards applicable to owners and operators of hazardous waste treatment, storage, and disposal facilities--Environmental Protection Agency. Proposed rule.

The Environmental Protection Agency (EPA) is today proposing amendments to its hazardous waste regulations under Subtitle C of the Resource Conservation and Recovery Act (RCRA). These amendments would replace the annual reporting requirements for hazardous waste generators and owners and operators of hazardous waste treatment, storage, ad disposal (TSD) facilities with a biennial survey of representative samples of those populations. This approach will provide verifiable data on a wider range of topics, better serve EPA's long term regulatory needs under RCRA, and reduce significantly the information burden on the regulated community.

Refuse Disposal↗

Hazardous waste management system standards for owners and operators of hazardous waste treatment, storage, and disposal facilities and EPA administered permit programs; hazardous waste permit program. Environmental Protection Agency. Interim final amendments to rule.

On May 19, 1980, EPA promulgated regulations applicable to owners and operators of hazardous waste treatment, storage, and disposal facilities which prohibited the landfill disposal of most containerized liquid waste or waste containing free liquid on and after November 19, 1981. Further on June 29, 1981, EPA amended its hazardous waste management regulations so as to extend the compliance date of the restriction on the landfill disposal of containerized liquid ignitable wastes to coincide with the compliance data of the general restriction on landfill disposal of liquids. The Agency is today extending the compliance date on both these requirements until May 26, 1982, and, in a separate action, is proposing amendments to these restrictions. This extension of compliance dates is provided for the sole purpose of allowing time to complete the rulemaking action on today's proposed amendments. The Agency is also today exempting from the requirements of the hazardous waste management regulations, the acts of adding absorbent material to hazardous waste in containers and adding hazardous waste to absorbent material in a container, at the time waste is first placed in the container, in order to reduce the free liquids in a container.

Refuse Disposal↗

A rating system for determination of hazardous wastes.

Although hazardous waste lists and their classification methodologies are nearly the same in most of the countries, there are some gaps and subjectiveness in determining the waste as hazardous waste. A rating system for the determination of waste as a hazardous waste is presented in this study which aims to overcome the problems resulted from the existing methodologies. Overall rating value (ORV) calculates and quantifies the waste as regular, non-regular or hazardous waste in an "hourglass" scale. "ORV" as a cumulative-linear formulation in proposed model consists of components such as ecological effects of the waste (Ee) in terms of four main hazard criteria: ignitability, reactivity, corrosivity and toxicity; combined potential risk (CPR) including carcinogenic effect, toxic, infectious and persistence characteristics; existing lists and their methodology (L) and decision factor (D) to separate regular and non-regular waste. Physical form (f) and quantity (Q) of the waste are considered as factors of these components. Seventeen waste samples from different sources are evaluated to demonstrate the simulation of the proposed model by using "hourglass" scale. The major benefit of the presented rating system is to ease the works of decision makers in managing the wastes.

Hazardous Waste↗

Hazardous waste management system: identification and listing of hazardous waste--Environmental Protection Agency. Interim final rule and request for comments.

The Environmental Protection Agency [EPA] is today revising the regulations for hazardous waste management under the Resource Conservation and Recovery Act to exempt certain categories of mixtures of solid wastes and hazardous wastes from the presumption of hazardousness presently contained in the regulations. EPA is taking this action because the Agency believes that the risk posed to human health and the environment from the management of these waste mixtures is not substantial, so that automatically defining these waste mixtures as hazardous is inappropriate. This amendment will substantially reduce the regulatory burden to those persons who would otherwise have applied the regulations for hazardous waste management to these mixtures.

Hospitals↗

Hazardous waste management system; standards applicable to generators of hazardous waste; state program requirements. Environmental Protection Agency. Final rule.

On February 26, 1980 and May 19, 1980, under the Resource Conservation and Recovery Act (RCRA), the Environmental Protection Agency (EPA) published regulations establishing a system to manage hazardous waste. Those regulations allowed hazardous waste generators to accumulate hazardous waste on-site without obtaining a permit or meeting financial responsibility requirements if they shipped the waste off-site within 90 days. On November 19, 1980, the Agency published an interim final rule which expanded the scope of the provision to include generators who treat, store or dispose of hazardous waste on-site. The final rule published today retains this change. As a result of public comments, the Agency is making several changes to the interim final rule. These changes (1) Clarify that the provision is applicable to all generators, including those who accumulate hazardous waste for the purpose of use, reuse, recycling and reclamation, (2) remove the requirement for use of DOT containers, (3) revise the labelling and marking requirements for wastes accumulated in containers and tanks; and (4) allow an extension to the 90-day accumulation limit in certain circumstances.

Refuse Disposal↗

Hazardous waste management system; identification and listing of hazardous waste--EPA. Final rule and response to comments.

On May 19, 1980, as part of its regulations implementing section 3001 of the Resource Conservation and Recovery Act (RCRA). EPA promulgated a series of criteria for listing wastes as hazardous. On July 19, 1991, the Agency proposed to conform the language of the regulation to reflect the Agency's intent and consistent interpretation of that regulation. Today's rule finalizes the proposed rule.

Hazardous Waste↗

A new Hazardous Waste Index.

Hazardous wastes, once generated, have to be stored, transported, treated, disposed off, recycled, depending upon the situation. With laws being tightened, all of the above operations have to be done safely without causing harm to people and environment. Before any operation is carried out, it is vital to know the hazardous characteristics of the waste to be handled. Because waste, generally, is a mixture instead of a pure compound, its hazardous characteristics are difficult to determine and generalize because each waste is specific. A new Hazardous Waste Index (HWI) is proposed in this paper. The index measures hazards related to flammability, reactivity, toxicity and corrosivity as well as the pH value for a hazardous waste. Two examples are given for its use. The index can be modified to include radioactive or mixed waste.

Environmental Pollution↗

Illinois, phase I interim authorization of state hazardous waste management program--Environmental Protection Agency, Region V. Granting of phase I interim authorization to state hazardous waste program.

The State of Illinois has applied for Interim Authorization of its hazardous waste program under Subtitle C of the Resource Conservation and Recovery Act of 1976, as amended (RCRA) and EPA guidelines for the approval of State hazardous waste programs (40 CFR Part 123, Subpart F). USEPA has reviewed the Illinois hazardous waste program and has determined that the Illinois hazardous waste program is substantially equivalent to the Federal program. USEPA is hereby granting Phase I Interim Authorization to Illinois to operate a hazardous waste program in lieu of Phase I of the Federal hazardous waste program in its jurisdiction.

Environmental Health↗

Mutagenicity in salmonella of hazardous wastes and urine from rats fed these wastes.

15 hazardous industrial waste samples were evaluated for mutagenicity in the Salmonella plate-incorporation assay using strains TA98 and TA100 in the presence and absence of Aroclor 1254-induced rat liver S9. Dichloromethane/methanol extracts of the crude wastes were also evaluated. 7 of the crude wastes were mutagenic, but only 2 of the extracts of these 7 wastes were mutagenic; extracts of 2 additional wastes also were mutagenic. In addition, 10 of the crude wastes were administered by gavage to F-344 rats, and 24-h urine samples were collected. Of the 10 raw urines evaluated, 3 were mutagenic in strain TA98 in the presence of S9 and beta-glucuronidase. The 3 crude wastes that produced these 3 mutagenic urines were, themselves, mutagenic. Adequate volumes of 6 of the 10 raw urines were available for extraction/concentration. These 6 urines were incubated with beta-glucuronidase and eluted through Sep-Pak C18 columns; the methanol eluates of 3 of the urines were mutagenic, and these were the same 3 whose raw urines also were mutagenic. In general, the C18/methanol extraction procedure reduced the cytotoxicity and increased the mutagenic potency of the urines. To our knowledge, this is the first report of the mutagenicity of urine from rodents exposed to hazardous wastes. Based on the present results, the use of only strain TA98 in the presence of S9 might be adequate for general screening of hazardous wastes or waste extracts for genotoxicity. The urinary mutagenesis assay does not appear to be a useful adjunct to the Salmonella assay for screening hazardous wastes. The problems associated with chemically fractionating diverse types of hazardous wastes for bioassay are also discussed.

Animals↗

Local health officers' views on hazardous waste remediation.

Hazardous waste sites are a priority for local health officers in New Jersey. However, most officers feel that they are not adequately briefed or consulted by federal and state officials who manage site remediation. Consequently, many local health officers tend to be neutral or negative about federal and state site remediation plans. Consultation with local health officers should be formally built into the site remediation process, and officers should directly approach their state governments to gain access.

Hazardous Waste↗

Effects of limestone addition and sintering on heavy metal leaching from hazardous waste incineration slag.

Hazardous waste incineration (HWI) in rotary kilns and the disposal of the residual slag on landfills play an important role in German waste treatment. In order to save disposal costs the elution behaviour of HWI-slag should be further optimised. Quality-improved slag may be disposed off on cheaper landfill sites still applying to landfill regulations. In a new process-integrated approach hazardous waste is mixed with limestone, which initiates chemical reactions with heavy metals in the rotary kiln yielding new compounds of different solubility. In this work HWI-slag/limestone mixtures are thermally treated and then examined by elution tests. Experimental data indicate that the heavy metals pertinent to landfill class assignment of a HWI-slag share a solubility minimum at a CaO-content of about 15%. Such improved HWI-slags are allowed to be disposed off on cheaper landfill sites. Furthermore, a new combination of thermodynamic calculation methods is applied to predict heavy metal solubility for different process conditions. Used models hold the opportunity to explain the tendencies of heavy metal leaching and propose plausible chemical reactions. With it, a new tool to examine the impact of temperature treatment and slag composition on heavy metal elution from HWI-slag is presented.

Calcium Carbonate↗