Page 46 - Veterinary Toxicology, Basic and Clinical Principles, 3rd Edition
P. 46

Concepts in Veterinary Toxicology Chapter | 1  13




  VetBooks.ir  estimate the exposure to the agent, both as to intensity,  classification scheme used by IARC. One area of contro-
                                                                  Controversy continues over the carcinogen hazard
             i.e., concentration and duration. In short, risk is a product
             of exposure and the potency of the agent for causing
                                                                versy concerns evaluating cancer hazards related to tech-
             the effect. Paustenbach (2001) provides an excellent  nologies, especially to technologies whose emissions may
             review of the practice of exposure assessment.     change over time. A specific chemical such as benzene
                There has been a tendency for regulatory agencies, such  remains constant over time with a continual increase in
             as the USEPA, to use their experience with classifying  the knowledge that will inform the cancer hazard classifi-
             chemicals as to their carcinogenic potential as a template for  cation process. Benzene studied in 2017 is the same mole-
             also classifying chemicals as to their potential for producing  cule as was studied at earlier times. The situation may be
             other noncancer hazards. Thus, there has been a trend  for different specific technologies that are constantly
             toward classifying chemicals as to their potential hazard for  changing, sometimes with changes to reduce emissions.
             causing different health outcomes and labeling them as  An excellent example is the diesel engine, the compression
             such, i.e., neurotoxins, reproductive toxins, hepatic toxins,  ignition engine using liquid hydrocarbon fuel invented by
             etc. Indeed, some even broader classifications have  Rudolph Diesel in the 1890s (McClellan et al., 2012). The
             emerged, i.e., endocrine-disrupting chemicals. In my view,  utility and efficiency of diesel engines resulted in their rapid
             this shorthand approach to identifying and classifying  deployment and use in many applications. A pre World War
             hazardous agents as to their potential to cause cancer or  II concern for diesel exhaust emissions focused on their odor
             other effects is often confusing to the public. In my opinion,  and impact on visibility. Demonstrations in the 1970s that
             the labeling approach has contributed to both radiation  extract of diesel exhaust particles painted on mouse skin
             phobia and chemical phobia and sometimes irrational  caused cancer and were mutagenic in the newly developed
             actions. It certainly flies in the face of the fact that for many  Ames assay raised concern for inhalation exposure of diesel
             chemicals the admonishment of Paracelsus that “the dose  exhaust potentially causing lung cancer. These concerns stimu-
             makes the poison” remains true. For numerous chemicals,  lated research using multiple approaches. A number of
             even when toxic effects are apparent at high doses, these  epidemiological studies yielded results suggesting that expo-
             same adverse effects are no longer manifest at sufficiently  sure to exhaust from diesel engines in use in the 1950s and
             low doses. Gold et al. (2003) has discussed the challenge of  1960s caused an increase in lung cancer. Four different labora-
             using high-exposure (dose) animal studies to identify either  tories in the United States, Germany, Switzerland, and Japan
             man-made or natural chemicals as human carcinogens.  reported that long-term exposure to high concentrations of
                In recent years increasing attention has been given to  diesel exhaust particulate material caused an increase in lung
             developing safer products and technologies, especially when  cancer in rats (Hesterberg et al., 2005, 2011; McClellan et al.,
             concerns have been raised with regard to the hazards of an  2012). Mauderly et al. (1987) is an example of one of those
             existing product or technology. In some cases, the focus has  studies of traditional diesel exhaust. An IARC (1989) panel on
             been on developing products that do not have carcinogenic  which I served evaluated the evidence and classified exposure
             properties to replace products that have been classified as  to diesel exhaust as a probable human carcinogen. Soon new
             human carcinogens or probable or possible human carcino-  research provided evidence that the increase in lung cancer in
             gens by IARC or as known or reasonably anticipated to be  rats to high concentrations of exhaust particles for long periods
             human carcinogens in the Report on Carcinogens periodi-  of time involved a nonspecific overload phenomena suggest-
             cally prepared by the NTP. Endpoints other than cancer have  ing that the effects observed in rats were not relevant for
             increasingly drawn attention for chemicals such as Bisphenol  evaluating human hazards/risks at low levels of exposure
             A, which has been under attack as an endocrine-disrupting  (Wolff et al., 1987; Nikula et al., 1995). Nikula et al. (1995)
             chemical. A committee of the National Academies of  showed that chronic exposure of rats to high concentrations of
             Science, Engineering and Medicine chaired by a Veterinary  carbon black particles free of hydrocarbons produced an
             Toxicologist, David Dorman, has recently released a report  increase in lung cancer.
             (NASEM, 2017) that will guide future assessments of what it  In response to the 1988 IARC hazard classification, a
             calls endocrine active chemicals. In general, chemicals that  related evaluation by the NTP, and an independent hazard
             persist in the environment and have a long residence time in  evaluation by the USEPA, the EPA issued stringent emis-
             animals and humans, even when shown to have low hazard  sion standards for particulate matter and NO 2 emissions
             potential, have become targets for replacement. In yet other  from diesel engines and mandated the use of ultra-low
             cases, the approach has been to identify replacements for  sulfur fuel (less than 15 ppm) for on-road vehicles.
             chemicals that are persistent in the environment and have  Industry responded with advances in engine technology,
             long residence time in animals and humans. In other cases,  exhaust after-treatment, and electronic control systems
             the approach has been to find ways to minimize the use of  that, along with use of ultra-low sulfur fuel, met the strin-
             the chemical viewed as being unsafe. These activities have  gent particulate matter emission standards in 2007 and
             givenrisetoafieldofscience sometimesreferredtoas   also stringent NO 2 emission standards in 2010 (McClellan
             “green chemistry” (Anastas and Warner, 1998).      et al., 2012).
   41   42   43   44   45   46   47   48   49   50   51