Polycyclic Aromatic Hydrocarbons (PAHs) are a group of chemicals that are formed during the incomplete burning of coal, oil, gas, wood, garbage, or other organic substances, such as tobacco and charbroiled meat. There are more than 100 PAHs. PAHs generally occur as complex mixtures (for example, as part of products such as soot), not as single compounds. PAHs are found throughout the environment in the air, water, and soil. As part of its mandate, the Agency for Toxic Substances and Disease Registry (ATSDR) prepares toxicological profiles on hazardous chemicals, including PAHs (ATSDR, 1995), found at facilities on the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) National Priorities List (NPL) and which pose the most significant potential threat to human health, as determined by ATSDR and the Environmental Protection Agency (EPA). These profiles include information on health effects of chemicals from different routes and durations of exposure, their potential for exposure, regulations and advisories, and the adequacy of the existing database. Assessing the health effects of PAHs is a major challenge because environmental exposures to these chemicals are usually to complex mixtures of PAHs with other chemicals. The biological consequences of human exposure to mixtures of PAHs depend on the toxicity, carcinogenic and noncarcinogenic, of the individual components of the mixture, the types of interactions among them, and confounding factors that are not thoroughly understood. Also identified are components of exposure and health effects research needed on PAHs that will allow estimation of realistic human health risks posed by exposures to PAHs. The exposure assessment component of research should focus on (1) development of reliable analytical methods for the determination of bioavailable PAHs following ingestion, (2) estimation of bioavailable PAHs from environmental media, particularly the determination of particle-bound PAHs, (3) data on ambient levels of PAHs metabolites in tissues/fluids of control populations, and (4) the need for a critical evaluation of current levels of PAHs found in environmental media including data from hazardous waste sites. The health effects component should focus on obtaining information on (1) the health effects of mixtures of PAHs particularly their noncarcinogenic effects in humans, and (2) their toxicokinetics. This report provides excerpts from the toxicological profile of PAHs (ATSDR, 1995) that contains more detailed information.
We live in a chemical world, and exposure to xenobiotics is a fact of life. Humans are exposed daily to a variety of chemicals including but not limited to large categories of pesticides, pharmaceuticals, household products, and food additives. Chemical exposures can be intentional or unintentional, to a single chemical or to a mixture of chemicals. Exposures to environmental chemicals occur in populations living in inner cities near chemical manufacturing plants and hazardous waste sites, and in the near field runoffs from fields and fertilizers. An overturned cargo train or transportation truck can spill chemicals in a pristine environment and become a source of pollution, contamination, and exposure, and eventually lead to an emergency response event. Exposures to environmental chemicals can affect humans, animals, and plants. Thus people of various interests and backgrounds are concerned about environmental exposures. Everyone carries a body burden of chemicals that range from primary elements and radioactive materials to synthetic, persistent chemicals such as dioxins, polychlorinated biphenyls (PCBs), and certain chlorinated pesticides. The major issue is not whether we are being exposed to mixtures of chemicals, but whether these exposure levels exceed the body's ability to detoxify, adapt, or otherwise compensate. Following a chemical exposure, the body exhibits a spectrum of biologic responses. For many chemicals, low‐level human exposures do not produce observable health effects. Physiologically, the body adjusts to the presence of chemicals at this level through adaptive mechanisms. As chemical exposure increases, effects such as enzyme induction and certain biochemical and subcellular changes of uncertain significance may result. The body may have compensatory mechanisms at this level of chemical exposure. However, as chemical exposures continue to increase, observable adverse effects may ensue as the body exhausts its adaptive and compensatory mechanisms. Such adverse effects could lead to biochemical, pathophysiologic, histopathologic changes resulting in organ dysfunction. Exposure to higher levels of pollutants could lead to morbidity and mortality. Exposures from multiple sources or pathways may lower the threshold for adverse health effects along this continuum. Considering that humans generally lack homogeneity in biochemical characteristics, some groups within the population will be more susceptible to chemical exposures than others. Thus it is important that exposure to environmental chemicals be viewed in the context of overall chemical exposures. The potential for combined chemical exposures to compromise physiologic systems may be greater in susceptible populations that include children, elderly persons, women of childbearing age, fetuses, persons with certain genetic disorders, and persons with preexisting infirmities. Historically, health concerns from exposure to single chemicals drive criteria derivation procedures. Usually, the target chemical, or group of chemicals, is identified by a government agency, international organization, or an advisory body based on legislative mandate, evidence or potential for human risk, or community concerns. However, most exposures are not to single chemicals, but to complex mixtures of chemicals that can affect public health through multiple routes of exposure. The Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA, or Superfund) of 1980, the Clean Air Act of 1990, and the Food Quality and Protection Act of 1996 all mandate organizations and agencies to consider multiple chemical exposures, sequentially or simultaneously, while setting the criteria to protect public health from potential health effects of chemicals. Thus one has to consider comprehensive risk to populations that are exposed not only to a specific mixture but also to additional environmental agents and naturally occurring compounds that may enhance, inhibit, or contribute to the health risks posed by that mixture. In very few cases, the available information on a mixture and its components is reviewed and a criteria for the mixture are derived. The purpose of this chapter is to highlight issues relevant to the joint toxicity assessment of chemical mixtures through the use of representative published studies, to present the alternative experimental testing approaches for mixtures, and to promote the use of innovative techniques to advance joint toxicity assessment methods.
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