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Arsenic
Chromium VI Dense Nonaqueous Phase Liquids (DNAPLs) 1,4-Dioxane Dioxins Mercury MTBE Perchlorate POPs PCBs TCE Other Contaminants
Toxicology Because of pervasiveness of TCE in the environment, most people are exposed to low levels of TCE. The general U.S. population is exposed via inhalation, ingestion, or dermal pathways. The most important pathways appear to be inhalation of contaminated ambient air and ingestion of contaminated drinking water. Consumers are exposed through their use of wood stains, varnishes, finishes, lubricants, adhesives, typewriter correction fluid, paint removers, and cleaners that contain TCE. Occupational exposure results primarily from use of TCE as a degreasing or metal cleaning agent; workers in the vapor degreasing industry are exposed to the highest levels through inhalation. Elevated exposure might occur to people living near waste facilities, those being exposed through occupational activities, and residents of some urban and industrial areas where TCE-contaminated media occur. TCE has been detected in breast milk, hence nursing infants may be exposed via this pathway. TCE does not accumulate or build up in the cells of plants or animals, so it typically is not found in the food chain. For most people, the level of exposure to TCE through food, beverages, or drinking water is very low. The health effects from TCE vary depending on the amount of TCE to which a person is exposed and how long the exposure lasts. Levels of TCE in the normal environment generally are well below levels of those in the workplace. Health effects similar to those described below are unlikely to be observed in the general public. Dizziness, headache, slowed reaction time, sleepiness, and facial numbness have occurred in workers breathing TCE or in people who use TCE-containing products in small, poorly ventilated areas; concentrations causing these effects are higher than the allowable occupational exposure level. Irritation of the eyes, nose, and throat also occur under these conditions. In general, the effects that result from one or several exposures to TCE disappear when exposure ends. Studies in animals show that ingesting or breathing levels of TCE that are higher than typical environmental levels can produce nervous system changes; liver and kidney damage; effects on the blood; tumors of the liver, kidney, lung, and male sex organs; and possibly cancer of the tissues that form the white blood cells (leukemia). Results of a few studies in some pregnant animals exposed to TCE in air or food showed effects in unborn animals or in newborns. None of these effects has been definitely shown to occur in humans. EPA currently is reevaluating under which class of carcinogen TCE will fall. Adapted from:
Assessing the Human Health Risks of Trichloroethylene: Key
Scientific Issues
Consumer Fact Sheet on: Trichloroethylene
Screening values for a specific chemical may vary among states and even among different regions of EPA. The ITRC Risk Team examined and documented the screening values for five specific contaminants—arsenic, benzo(a)pyrene, lead, polychlorinated biphenyls, and trichloroethene—that are often identified as drivers for management actions at contaminated sites.
TCE Issue Papers These documents were prepared to provide an overview of recent studies with bearing on different aspects of TCE risk assessment in support of the National Research Council committee's review of EPA's 2001 draft TCE health risk assessment report. The issue papers summarize and outline some of the recently published scientific literature but are not intended to provide a complete survey and synthesis of the literature.
ToxFAQs™ for Trichloroethylene (TCE) Toxicological Profile for Trichloroethylene (TCE) Trichloroethylene Health Risk Assessment: Synthesis and Characterization, External Review Draft
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