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PubMed2004

An unrecognized source of PCB contamination in schools and other buildings.

An investigation of 24 buildings in the Greater Boston Area revealed that one-third (8 of 24) contained caulking materials with polychlorinated biphenyl (PCB) content exceeding 50 ppm by weight, which is the U.S. Environmental Protection Agency (U.S. EPA) specified limit above which this material is considered to be PCB bulk product waste. These buildings included schools and other public buildings. In a university building where similar levels of PCB were found in caulking material, PCB levels in indoor air ranged from 111 to 393 ng/m3; and in dust taken from the building ventilation system, < 1 ppm to 81 ppm. In this building, the U.S. EPA mandated requirements for the removal and disposal of the PCB bulk product waste as well as for confirmatory sampling to ensure that the interior and exterior of the building were decontaminated. Although U.S. EPA regulations under the Toxic Substances Control Act stipulate procedures by which PCB-contaminated materials must be handled and disposed, the regulations apparently do not require that materials such as caulking be tested to determine its PCB content. This limited investigation strongly suggests that were this testing done, many buildings would be found to contain high levels of PCBs in the building materials and potentially in the building environment. The presence of PCBs in schools is of particular concern given evidence suggesting that PCBs are developmental toxins.

Boston↗
PubMed2003

Quantitative structure-activity relationships for predicting potential ecological hazard of organic chemicals for use in regulatory risk assessments.

The use of quantitative structure-activity relationships (QSARs) for deriving the predicted no-effect concentration of discrete organic chemicals for the purposes of conducting a regulatory risk assessment in Europe and the United States is described. In the United States, under the Toxic Substances Control Act (TSCA), the TSCA Interagency Testing Committee and the U.S. Environmental Protection Agency (U.S. EPA) use SARs to estimate the hazards of existing and new chemicals. Within the Existing Substances Regulation in Europe, QSARs may be used for data evaluation, test strategy indications, and the identification and filling of data gaps. To illustrate where and when QSARs may be useful and when their use is more problematic, an example, methyl tertiary-butyl ether (MTBE), is given and the predicted and experimental data are compared. Improvements needed for new QSARs and tools for developing and using QSARs are discussed.

Animals↗
PubMed1980

Improvements in the NIOSH registry of toxic effects of chemical substances.

Subsequent to the publication of the 1977 edition of the NIOSH Registry of Toxic Effects of Chemical Substances (RTECS), several additions and changes were introduced that substantially improved the content and accessibility of the RTECS data file. Content additions included primary irritation data for both skin and eyes, in vitro mutagenicity data, and citations to toxicology review articles and to the Toxic Substances Control Act inventory. Also undertaken was a re-evalution of existing tumorigenic entries based on revised selection criteria. Accessibility to RTECS data has been facilitated by the introduction of on-line interactive computer searching, and the preparation and distribution of Computer Output Microfiche (COM-fiche) and magnetic tape copies of the file which supplement the annual publication.

Carcinogens↗
PubMed1989

Biocidal activity of ozone versus formaldehyde against poultry pathogens inoculated in a prototype setter.

Ozone was evaluated as an alternative hatchery disinfectant to replace formaldehyde in the event that the Environmental Protection Agency regulates the use of formaldehyde under the Toxic Substances Control Act. Cultures of Staphylococcus, Streptococcus, and Bacillus species previously isolated from poultry hatcheries and selected culture collections of Escherichia coli, Pseudomonas fluorescences, Salmonella typhimurium, Proteus species, and Aspergillus fumigatus were spread-plated on open petri plates and independently fumigated with ozone or formaldehyde in a prototype laboratory poultry setter. Ozone (1.52% to 1.65% by weight) resulted in bacterial reductions of greater than 4 to 7 log10 and fungal reductions of greater than 4 log10, whereas formaldehyde achieved reductions of greater than 7 log10 and greater than 5 log10, respectively, after 8 min of exposure to either disinfectant. Potential mutagenic effects were observed in ozonated E. coli colonies resulting in decreased superoxide dismutase activity and increased catalase activity when compared with nonozonated control colonies. In this study ozone reduced microorganism counts but not as much as formaldehyde. Ozone may be used as a disinfectant against selected microorganisms, although further testing under actual hatchery conditions is needed before making recommendations to the industry.

Animals↗
PubMed2000

Asbestos worker protection. Environmental Protection Agency (EPA). Final rule.

In this Final Rule, EPA is amending both the Asbestos Worker Protection Rule (WPR) and the Asbestos-in-Schools Rule. The WPR amendment protects State and local government employees from the health risks of exposure to asbestos to the same extent as private sector workers by adopting for these employees the Asbestos Standards of the Occupational Safety and Health Administration (OSHA). The WPR's coverage is extended to State and local government employees who are performing construction work, custodial work, and automotive brake and clutch repair work. This final rule cross-references the OSHA Asbestos Standards for Construction and for General Industry, so that future amendments to these OSHA standards are directly and equally effective for employees covered by the WPR. EPA also amends the Asbestos-in-Schools Rule to provide coverage under the WPR for employees of public local education agencies who perform operations, maintenance, and repair activities. EPA is issuing this final rule under section 6 of the Toxic Substances Control Act (TSCA).

Asbestos↗
PubMed2002

Ecological impact and environmental fate of perfluorooctane sulfonate on the zooplankton community in indoor microcosms.

There is presently a substantial amount of information being gathered concerning the environmental risk associated with the perfluorooctane sulfonate (PFOS) compound. The U.S. Environmental Protection Agency (U.S. EPA) is requiring that more research be completed before making definitive decisions concerning the regulatory issues covered in the significant new use rule (18/10-2000) under the Toxic Substance Control Act. However, there are no risk assessment requirements under seminatural conditions in microcosms. The PFOS can enter, and has been found in, the aquatic environment through different pathways, including spills associated with use of fire-fighting foams containing PFOS, leaching from washing Scotchgard-treated clothes with the wastewater, leaching from various coatings, discharges as residual waste from fluorochemical production, or volatilization and transportation atmospherically. The biota is the sink of PFOS rather than the sediment or soil. The aim of this article is to determine a 35-d community no-observable-effect concentration (NOECcommunity) for freshwater zooplankton and the fate of PFOS during the course of study. The PFOS persisted in the water phase with only slight reductions over the study; only the decrease from 33.9 mg/L at day 1 to 29.8 mg/L at day 35 was significant. A 90 to 100% reduction (p < 0.01) of the total zooplankton population was found after one week of exposure to 30 mg PFOS/L and a similar reduction after two weeks at 10 mg PFOS/L. The Daphnia magna 21-d NOECsurvival of 12 mg/L has previously been found in a standard laboratory bioassay by 3M. The rank order of susceptibility for the test community was Copepoda > Cladocera > Rotifera, assuming all adverse direct effects.

Alkanesulfonic Acids↗
PubMed2003

Predicting ready biodegradability of premanufacture notice chemicals.

Chemical substances other than pesticides, drugs, and food additives are regulated by the U.S. Environmental Protection Agency (U.S. EPA) under the Toxic Substances Control Act (TSCA), but the United States does not require that new substances be tested automatically for such critical properties as biodegradability. The resulting lack of submitted data has fostered the development of estimation methods, and the BioWIN models for predicting biodegradability from chemical structure have played a prominent role in premanufacture notice (PMN) review. Until now, validation efforts have used only the Japanese Ministry of International Trade and Industry (MITI) test data and have not included all models. To assess BioWIN performance with PMN substances, we assembled a database of PMNs for which ready biodegradation data had been submitted over the period 1995 through 2001. The 305 PMN structures are highly varied and pose major challenges to chemical property estimation. Despite the variability of ready biodegradation tests, the use of at least six different test methods, and widely varying quality of submitted data, accuracy of four of six BioWIN models (MITI linear, MITI nonlinear, survey ultimate, survey primary) was in the 80+% range for predicting ready biodegradability. Greater accuracy (>90%) can be achieved by using model estimates only when the four models agree (true for 3/4 of the PMNs). The BioWIN linear and nonlinear probability models did not perform as well even when classification criteria were optimized. The results suggest that the MITI and survey BioWIN models are suitable for use in screening-level applications.

Biodegradation, Environmental↗
PubMed1991

Regulating the introduction of new chemicals under section 5 of TSCA: improving the efficiency of the process and reducing potential injury in the workplace through the use of operational MSDS and exposure limits.

The Toxic Substances Control Act (TSCA) authorizes the EPA to take appropriate actions to ensure that new and existing chemicals do not pose "unreasonable risk" to health or the environment. Section 2(b)(3) of the Act directs the Agency to accomplish this objective in a manner that does "not impede unduly or create unnecessary economic barriers to technological innovation." In recent years, critics have felt that the EPA has failed to achieve these primary goals of TSCA. This paper considers some of the reasons for this criticism and advocates an alternate approach of exposure limits and operationally sufficient controls to assist in achieving these goals. An illustration of how this alternate approach might work under practical conditions is presented, using as an example a new chemical substance from the class of acrylate monomers. These concepts and risk assessments provide data for a better design of future studies according to good laboratory practice and quality assurance.

Chemical Industry↗
PubMed1990

EPA's intervention into workplace health and safety--the other OSHA.

Primarily but not exclusively through the Toxic Substance Control Act (TSCA) and the Superfund Amendment Reauthorization Act Title III, EPA's involvement is significant because they are now a "key player" in providing regulatory direction to those responsible for workplace health and safety. A comparative matrix is presented as a database demonstration of the similarities and differences between OSHA and EPA in the standards setting, compliance, and public policy areas. This matrix demonstrates the impact that EPA now has on specific aspects of workplace health and safety and on the conduct of United States business activity. EPA's restrictive powers are clearly greater than those of OSHA. Conclusions derived from specific interventions of the EPA into workplace health and safety are (1) the industrial hygienist has no choice but to get involved in the compliance and regulatory process evolving from EPA. (2) Industrial hygiene professional societies must likewise become equally aware and involved. (3) There is a strong need for coordination and cooperation between OSHA and EPA leading to effective regulations and avoidance of redundancy. (4) National and global impacts must be optimized to enhance worker health and safety and not be barriers to technical and economic advances. (5) Private sector risk management functions must be integrated to avoid redundancies and omissions. (6) Finally, compliance initiatives can be leveraged to build strong relations with the public and employees.

Environmental Health↗
PubMed2001

Bilateral dissected spleens and thymuses in rodents exhibit homogeneity in leukocyte markers.

Histopathologic evaluation and/or archiving of sections of spleen or thymus from all study animals may be mandated by study protocol (e.g., Toxic Substances Control Act-compliant studies). In such cases, whole spleen or thymus is not available for immunophenotyping. It has not been previously demonstrated that immunologic data representative of whole organs can be reliably obtained using a section of the spleen or using one thymic lobe. Light-scatter characteristics and immune cell-surface antigen expression were therefore compared in the right and left halves of the spleen and in the right and left thymic lobes of young adult female C57B1/6 mice and Sprague-Dawley rats. Antigens compared were: mouse spleen - CD11b, CD45R, CD90; rat spleen - CD11b, CD45RA, Pan-T/Ox-52; mouse and rat thymus - CD4, CD8a. There were no significant differences in distribution of cells by size or by expression level for any of these antigens when the right part of the organs was compared to the left part. These data indicate that use of entire spleen or both thymic lobes is not required to reliably quantify resident immune cell subpopulations.

Animals↗