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PubMed2006

Comparison of techniques for the detection of helminth ova in drinking water and wastewater.

Many countries use wastewater for irrigation. The World Health Organization established, as reuse guidelines, a maximum value of 1 helminth ovum/L for irrigation. Various techniques for enumerating helminth ova in water have been published. To determine the most adequate method for Mexico, four techniques were compared: the U.S. Environmental Protection Agency (U.S. EPA), membrane-filter, Leeds I, and Faust. Two types of water were used: drinking water and municipal wastewater effluent. Sensitivity, discrimination coefficients, precision, recovery efficiency, and cost were determined. In addition, several unseeded wastewater samples were analyzed. For drinking water, U.S. EPA and the membrane-filter techniques demonstrated comparable results; however, when wastewater was used, the membrane technique showed some deficiencies. Because the U.S. EPA technique may be used for samples with both high and low solids content, allows for the recovery of helminth ova with different specific gravities, and has the lowest total cost, it was selected as the best technique.

Agriculture↗
PubMed1999

Particle size separation via soil washing to obtain volume reduction.

A pilot-plant study was performed using a soil washing pilot plant originally designed by the Environmental Protection Agency (EPA) to demonstrate scale-up and potential full-scale remediation. This pilot plant named VORCE (Volume Reduction/Chemical Extraction) was modified to meet the specific requirements for treatment of the Formerly Utilized Sites Remedial Action Program (FUSRAP) and a Department of Energy site soils. After a series of tests on clean soils to develop operating parameters and system performance, the machine was used to treat soils, one contaminated with Thorium-232 and the other with Cesium-137. All indicate that soil washing is very promising for volume reduction treatment. In addition, cost data was generated and is given herein.

Cesium Radioisotopes↗
PubMed2005

A statistical analysis of visibility-impairing particles in federal Class I areas.

It is widely agreed that visibility conditions in many Class I areas are impaired to some extent. This paper provides an estimate of the degree of impairment in many of the Class I areas with respect to each of the six haze-forming aerosol classes as described in the supporting documents to the U.S. Environmental Protection Agency Regional Haze Rule. Analyses are performed comparing data from the Interagency Monitoring of Protected Visual Environments network to a modified version of the default natural conditions estimates from the Regional Haze Rule. Uncertainties in the measured annual mean concentrations and biases in the default natural condition estimates because of the effects of geography and meteorology are discussed. It is determined that all of the Class I areas in the contiguous 48 United States are significantly impaired with respect to sulfate aerosols, most of the Class I areas are significantly impaired with respect to nitrate and elemental carbon aerosols, and impairment with respect to organic mass, soil mass, and coarse mass is generally less discernable. No attempt is made to determine adverse impacts with respect to any specific source or group of sources.

Air Pollution↗
PubMed2006

The case for integrating low dose, beneficial responses into US EPA risk assessments.

When conducting risk assessments, the US Environmental Protection Agency (EPA) does not currently consider the beneficial effects from exposure to concentrations of agents below the no observed adverse effect level (NOAEL). If such benefits were observed, and if the beneficial and toxicological mechanisms of action were identical, this would probably be represented as a 'j-shaped' hormetic dose-response curve. If such data are available, they should be considered when assigning uncertainty factors for safe exposure calculations. However, when such data are not readily available, as is likely the case when the mechanism of action of the benefit differs from that of toxicity, current US EPA methods appear adequate.

Dose-Response Relationship, Drug↗
PubMed2002

Assessing human health response in life cycle assessment using ED10s and DALYs: part 1--Cancer effects.

Life cycle assessment (LCA) is a framework for comparing products according to their total estimated environmental impact, summed over all chemical emissions and activities associated with a product at all stages in its life cycle (from raw material acquisition, manufacturing, use, to final disposal). For each chemical involved, the exposure associated with the mass released into the environment, integrated over time and space, is multiplied by a toxicological measure to estimate the likelihood of effects and their potential consequences. In this article, we explore the use of quantitative methods drawn from conventional single-chemical regulatory risk assessments to create a procedure for the estimation of the cancer effect measure in the impact phase of LCA. The approach is based on the maximum likelihood estimate of the effect dose inducing a 10% response over background, ED10, and default linear low-dose extrapolation using the slope betaED10 (0.1/ED10). The calculated effects may correspond to residual risks below current regulatory compliance requirements that occur over multiple generations and at multiple locations; but at the very least they represent a "using up" of some portion of the human population's ability to accommodate emissions. Preliminary comparisons are performed with existing measures, such as the U.S. Environmental Protection Agency's (U.S. EPA's) slope factor measure q1*. By analyzing bioassay data for 44 chemicals drawn from the EPA's Integrated Risk Information System (IRIS) database, we explore estimating ED10 from more readily available information such as the median tumor dose rate TD50 and the median single lethal dose LD50. Based on the TD50, we then estimate the ED10 for more than 600 chemicals. Differences in potential consequences, or severity, are addressed by combining betaED10 with the measure disability adjusted life years per affected person, DALYp. Most of the variation among chemicals for cancer effects is found to be due to differences in the slope factors (betaED10) ranging from 10(-4) up to 10(4) (risk of cancer/mg/kg-day).

Carcinogens, Environmental↗
PubMedDate not supplied

Application of counterpropagation artificial neural network for modelling properties of fish antibiotics.

The present study focuses on fish antibiotics which are an important group of pharmaceuticals used in fish farming to treat infections and, until recently, most of them have been exposed to the environment with very little attention. Information about the environmental behaviour and the description of the environmental fate of medical substances are difficult or expensive to obtain. The experimental information in terms of properties is reported when available, in other cases, it is estimated by standard tools as those provided by the United States Environmental Protection Agency EPISuite software and by custom quantitative structure-activity relationship (QSAR) applications. In this study, a QSAR screening of 15 fish antibiotics and 132 xenobiotic molecules was performed with two aims: (i) to develop a model for the estimation of octanol--water partition coefficient (logP) and (ii) to estimate the relative binding affinity to oestrogen receptor (log RBA) using a model constructed on the activities of 132 xenobiotic compounds. The custom models are based on constitutional, topological, electrostatic and quantum chemical descriptors computed by the CODESSA software. Kohonen neural networks (self organising maps) were used to study similarity between the considered chemicals while counter-propagation artificial neural networks were used to estimate the properties.

Animals↗
PubMedDate not supplied

Disposal options for infectious medical waste generated during home-based dental care.

The number of dentists providing mobile care is increasing. One of the challenges the mobile dentist faces is proper handling and disposal of infectious medical waste generated during patient care. Mobile dentists must concern themselves with meeting Federal, state, and local regulations. Federal agencies that have jurisdiction over this issue are the Environmental Protection Agency (EPA) and the Occupational Safety and Health Administration (OSHA). EPA guidelines are summarized and clarified with respect to pre-transportation and transportation issues. Compliance with OSHA standards are addressed through presentation of a sample protocol for handling infectious medical waste. It is beyond the scope of this paper to discuss in detail the policies of each municipality, and practitioners are advised to consult with state and local authorities regarding proper handling and transportation of this material. Using the information presented in this paper, the mobile dentist can approach this complex issue in an organized manner.

Aged↗
PubMed2004

Accuracy and repeatability of commercial geocoding.

The authors estimated accuracy and repeatability of commercial geocoding to guide vendor selection in the Life Course Socioeconomic Status, Social Context and Cardiovascular Disease study (2001-2002). They submitted 1,032 participant addresses (97% in Maryland, Minnesota, Mississippi, or North Carolina) to vendor A twice over 9 months and measured repeatability as agreement between levels of address matching, discordance (%) between statistical tabulation areas, and median distance (d, in meters) and bearing (theta;, in degrees) between coordinates assigned on each occasion (H(o):Sigma(i)( = 1 -->) (n) [theta;(i) /n] = 180 degrees ). They also submitted 75 addresses of nearby air pollution monitors (77% urban/suburban; 69% residential/commercial) to vendors A and B and then measured accuracy by comparing vendor- and US Environmental Protection Agency (EPA)-assigned geocodes using the above measures. Repeatability of geocodes assigned by vendor A was high (kappa = 0.90; census block group discordance = 5%; d < 1 m; theta; = 177 degrees ). The match rate for EPA monitor addresses was higher for vendor B versus A (88% vs. 76%), but discordance at census block group, tract, and county levels also was, respectively, 1.4-, 1.9-, and 5.0-fold higher for vendor B. Moreover, coordinates assigned by vendor B were further from those assigned by the EPA (d = 212 m vs. 149 m; theta; = 131 degrees vs. 171 degrees ). These findings suggest that match rates, repeatability, and accuracy should be used to guide vendor selection.

Aged↗
PubMed1994

An alternative approach to dietary exposure assessment.

The method of dietary exposure assessment currently used by the Environmental Protection Agency (EPA), the Dietary Residue Evaluation System (DRES), combines a consumption distribution derived from the United States Department of Agriculture (USDA) 1977-1978 Nationwide Food Consumption Survey (NFCS) with a single estimate of residue level. The National Academy of Sciences recommended that EPA incorporate both the distribution of residues and the distribution of consumption into their exposure assessment methodology and proposed using a Monte Carlo approach. This paper presents an alternative method, the Joint Distributional Analysis (JDA), that combines the consumption and residue distributions, without relying on random sampling or fitting theoretical distributions like the Monte Carlo method. This method permits simultaneous analysis of the entire diet, including assessing exposure from residues in different foods.

Aldicarb↗
PubMed1994

Summary of the workshop on issues in risk assessment: quantitative methods for developmental toxicology.

This report summarizes the proceedings of a conference on quantitative methods for assessing the risks of developmental toxicants. The conference was planned by a subcommittee of the National Research Council's Committee on Risk Assessment Methodology in conjunction with staff from several federal agencies, including the U.S. Environmental Protection Agency, U.S. Food and Drug Administration, U.S. Consumer Products Safety Commission, and Health and Welfare Canada. Issues discussed at the workshop included computerized techniques for hazard identification, use of human and animal data for defining risks in a clinical setting, relationships between end points in developmental toxicity testing, reference dose calculations for developmental toxicology, analysis of quantitative dose-response data, mechanisms of developmental toxicity, physiologically based pharmacokinetic models, and structure-activity relationships. Although a formal consensus was not sought, many participants favored the evolution of quantitative techniques for developmental toxicology risk assessment, including the replacement of lowest observed adverse effect levels (LOAELs) and no observed adverse effect levels (NOAELs) with the benchmark dose methodology.

Animals↗
PubMed2003

No evidence of dioxin cancer threshold.

The U.S. Environmental Protection Agency (EPA) has developed an estimate of the human cancer risk from dioxin, using the standard low-dose linear extrapolation approach. This estimate has been controversial because of concern that it may overestimate the cancer risk. An alternative approach has been published and was presented to the U.S. EPA Science Advisory Board's Dioxin Review Panel in November 2000. That approach suggests that dioxin is a threshold carcinogen and that the threshold is an order of magnitude above the exposure levels of the general population. We have reexamined the threshold analysis and found that the data have been incorrectly weighted by cohort size. In our reanalysis, without the incorrect weighting, the threshold effect disappears.

Carcinogens↗
PubMed2005

A river water quality model integrated with a web-based geographic information system.

Scientists often use mathematical models to assess river water quality. However, the application of the models in environmental management and risk assessment is quite limited because of the difficulty of preparing input data and interpreting model output. This paper presents a study that links ArcIMS, a Web-based Geographic Information System (GIS) software to ROUT, a national and regional scale river model which evolved from the US Environmental Protection Agency's Water Use Improvement and Impairment Model, to create a WWW-GIS-based river simulation model called GIS-ROUT. GIS-ROUT is used to predict chemical concentrations in perennially flowing rivers throughout the continental United States that receive discharges from more than 10,000 publicly owned wastewater treatment plants (WWTPs). The WWTP chemical loadings are calculated from per capita per day disposal of product ingredients and the population served by each plant. Each WWTP, containing data on treatment type and influent and effluent flows, is spatially associated with a specific receiving river segment. Based on user defined treatment-type removal rates for a particular chemical, an effluent concentration for each WWTP is calculated and used as input to the river model. Over 360,000 km of rivers are modeled, incorporating dilution and first order loss of the chemical in each river segment. The integration of spatial data, GIS, the WWW, and modeling in GIS-ROUT makes it possible to organize and analyze data spatially, and view results on interactive maps as well as tables and distribution charts. The integration allows scientists and managers in different locations to coordinate and share their estimations for environmental exposure and risk assessments.

Geographic Information Systems↗
PubMed2003

Improvements to EPA method 531.1 for the analysis of carbamates that resulted in the development of U.S. EPA Method 531.2.

This project is undertaken to fully optimize the U.S. Environmental Protection Agency Method 531.1 post-column chemistries and to incorporate recent advances in liquid chromatographic separation, post-column derivatization, and detection techniques. Sample preservation and storage stability studies establish citric acid as a suitable replacement for the caustic monochloroacetic acid in the current method and confirm its antimicrobial effectiveness. Performance of an alternate set of commercially available post-column reagents is also investigated. This research has resulted in the publication of Method 531.2, a high-performance liquid chromatographic direct injection method for the analysis of N-methylcarbamoyloximes and N-methylcarbamates using post-column derivatization and fluorescence detection.

Carbamates↗
PubMed1986

EDB: a case study in communicating risk.

This is a report on the Environmental Protection Agency's (EPA's) efforts to communicate with the public about the risks of ethylene dibromide (EDB), what the agency said it was doing about these risks and what information the public actually received through television and newspapers. Although special in many ways, the EDB case illustrates the problems that regulatory agencies have when they must take regulatory action and assure the public that the risks in question are being dealt with adequately. It also illustrates issues that the press faces. Above all, it illustrates the barriers to communication presented by the different perspectives of regulatory agencies and individuals and the types of information they each are most interested in.

Carcinogens↗
PubMed2006

Managing hazardous waste in the laboratory.

This article offers an introduction to the federal U.S. Environmental Protection Agency (EPA) regulations as they relate to hazardous wastes generated by clinical and anatomic pathology laboratories. Traditionally, the EPA has targeted "heavy" industries such as manufacturing for compliance auditing, but it recently turned an eye toward health-care facilities since they are identified as important sources of hazardous waste generation. Enforcement of EPA regulations within health-care facilities presents the challenge of a new labyrinth of definitions, rules, and compliance methods for laboratorians who have already made it through other regulatory agency mazes, including the Joint Commission on Accreditation of Healthcare Organizations (JCAHO) standards, the College of American Pathologists (CAP) checklists, and the Occupational Safety and Health Administration (OSHA) standards.

Hazardous Waste↗
PubMed1991

EPA use of in vivo germ cell mutagenicity data.

The Toxic Substances Control Act (TSCA) provides the U.S. Environmental Protection Agency, Office of Toxic Substances (EPA, OTS) with the authority to regulate chemical use by requiring testing and use restrictions as appropriate to protect human health. Regulation on the basis of heritable mutation induction is specifically mentioned in the Test Rule section of the law and has also been pursued for new chemical substances. A tiered scheme of mutagenicity testing has been employed and recently revised to assess mutagenicity hazard. In vivo assay systems play key roles at all three levels in the scheme, beginning with the first level of determining intrinsic mutagenicity hazard. Once intrinsic mutagenicity has been identified, the revised scheme requires an assay or assays to assess chemical interaction with gonadal DNA. Finally, the scheme contains tests that permit risk assessment for a chemical. The recently-revised Office of Pesticide Programs (OPP) mutagenicity testing requirements closely parallel those of OTS.

Animals↗
PubMed1989

Overview of proposed revisions to the superfund hazard ranking system.

The Comprehensive Environmental Response, Compensation, and Liability Act of 1980 required the federal government to establish criteria for setting priorities among releases of hazardous substances, pollutants, and contaminants. The U.S. Environmental Protection Agency responded by developing the Hazard Ranking System (HRS), which is a scoring system used to establish the National Priorities List (NPL). The Superfund Amendments and Reauthorization Act of 1986 required EPA to amend the HRS so it will more accurately assess relative risks and take into account certain specific elements of risk. On December 23, 1988, EPA published in the Federal Register the proposed rule to revise the HRS. EPA expects to issue the final rule in 1990 after reviewing public comments. This paper describes the proposed revisions and summarizes major technical findings that support the revisions. As a result of the HRS revisions, there may be some changes in the types of sites that score high enough to be placed on the NPL. A projection of those changes is discussed.

Environmental Pollutants↗
PubMed2006

Lead and copper in drinking water fountains--information for physicians.

BACKGROUND: Lead and copper are potentially toxic metals. The objective of our work was to test the water from the drinking fountains of a large public access office complex in southwest Houston, Texas, for the presence of lead, copper, and microbiologic contamination. The data for the water fountains were compared with what we found in the local municipal drinking water supplies. METHODS: Samples were collected as the first draw at the beginning of the work week. These samples were acidified to prevent the precipitation of heavy metals and analyzed using United States Environmental Protection Agency (USEPA) approved procedures and quality control. RESULTS: Traces of lead were detected in 37.5% and copper in 100% of the tested water fountains. In two buildings, concentrations in some fountains exceeded the USEPA action level for lead (by up to 12-fold) and for copper (by up to 3.9 fold). One sample was positive for total coliform and Escherichia coli bacteria. Comparison with samples from the local municipal drinking water supplies indicated that both metals and bacteria were the result of secondary contamination at the water fountain sites. CONCLUSIONS: This study showed that drinking water fountains can be an unexpected and unappreciated source of intake of metal and bacterial contaminants.

Copper↗