HOW TO GET RID OF BEDBUGS
Find the solution to your infestation.
Maximum Residue Limits for Pesticides on Foods in Canada
When pesticides are used on crops or when animals are fed crops treated with pesticides, residues may remain in or on the food when it is sold. Before registering a pest control product for use in Canada, the PMRA must determine that consumption of the residues that are likely to remain in or on the food when the pesticide is used according to label directions will not pose an unacceptable health risk. This amount is then legally established as a maximum residue limit (MRL) under the Food and Drugs Act (FDA).
These MRLs apply to both domestic and imported food. In order to prevent
residues in or on the imported food from posing an unacceptable health risk,
MRLs are also established for pesticides not registered for use in Canada
and for Canadian registered pesticides with respect to uses that are not
authorized in Canada. If residues exceeding an MRL are found, the food is
considered adulterated and is prohibited under the FDA from sale in Canada.
Chris F. Wilkinson
Cancer is a special disease. Cancer of one type or another will eventually claim the life of one in every four or five Americans; indeed, few will escape the suffering of losing a friend or family member to the disease. Second only to heart disease as a leading cause of death in the United States, cancer is responsible for close to 500,000 deaths per year. Quite apart from its importance as a factor in human mortality, the very thought of cancer arouses a special dread in their minds of most individuals.
Public awareness and fear of cancer in the United States intensified during the late 1960s as a result of widely publicized associations between human cancer and a number of environmental factors associated with modern technology. In particular, attention was focused on the possible carcinogenic risks associated with the many products and byproducts of the chemical industry, and there was enormous public pressure for prompt legislative action to regulate human exposure to potential carcinogens.
As a result, legislation directed toward the protection of human health and the environment has increased dramatically during the past two decades. Approximately 30 such laws have been enacted, and although they differ in their objectives and regulatory authority, most are designed to control the carcinogenic and other health risks of chemicals introduced into commerce, released into the environment, or encountered in the workplace.
Despite substantial progress in the past few years, basic understanding of carcinogenic mechanisms and the major factors causing human cancer still leaves much to be desired. There remains considerable uncertainty in current procedures for identifying and regulating potential human carcinogens. Unfortunately, the development of an acceptable policy for the regulation of chemical carcinogens constitutes a particularly troublesome problem, because it seeks to match argument based on uncertain science against the deep-seated human fear of cancer. It is not surprising that the question of how to regulate cancer risks in the United States has become a highly divisive issue in which the limited amount of good science that is available either is not used to maximum advantage or rapidly becomes lost in a tangle of emotions and subjective value judgments.
It is frequently alleged, and widely and uncritically accepted by a large segment of the public, that the United States is currently in the midst of a veritable explosion of human cancer; futhermore, we are told, the situation continues to deteriorate. Although different statistical sources use different methods of analysis and data presentation , and although selective analyses can be used to support particular viewpoints, it is difficult to understand how the data can be interpreted as being indicative of a cancer epidemic.
No one will argue that more people are dying from cancer each year; some 433,795 Americans died of cancer in 1982, a 56% increase over the 278,562 deaths that occurred in 1962 (1). This is a sobering figure. However, when the trends are adjusted for the increased size of the population and for changes in age distribution the total cancer mortality rate from 1962 to 1982 has increased 8.7% (0.4%/year) and cancer incidence rate form 1973 to 1981 has increased 8.5% (1.1%/year) (1).
When site-specific analyses are conducted, the most obvious trends that become apparent during the past 35 years are the enormous increase in the incidence of lung cancer (greater than 200%) and the marked decrease in the incidence of stomach cancer; the incidence of cancers at most other sites has remained more or less constant. Lung cancer is of such dominance that if the mortality with which it is associated is excluded from the overall cancer mortality data over the last 30 years or so, the 8% increase in mortality becomes a 13% decrease (1). Indeed, when the effects of lung and skin cancer were excluded, a steady decline appeared in overall cancer mortality over the last 50 years in people under 65 years of age, according to a study by Doll and Peto (2). There is some evidence that, as a result of underreporting in the past, age-adjusted mortalities from many types of cancer (except lung cancer) have been declining significantly for decades (3).
Consequently, the only real evidence of a cancer epidemic in the American population (similar effects are also observed in other countries) is in relation to lung cancer, which is now generally considered to result primarily from smoking cigarettes (4). Sadly, this largely preventable disease is responsible for almost 30% of all human cancer deaths in the United States; it has been the major killer in males for some 20 years and now surpasses breast cancer as the major cause of cancer mortality in women.
Causes of human cancer
Not very many years ago it was generally believed that cancer was caused by a limited number of discrete chemical, physical, or biological (e.g., viruses) agents. Today, cancer is recognized as a highly complex, multifactorial disease caused, in part, by endogenous metabolic or other imbalances associated with age or genetic makeup and, in part, by a wide variety of exogenous factors including diet, lifestyle, and exposure to ionizing radiation and chemicals of natural or man-made origin.
As a result of early epidemiological studies suggesting the predominance of exogenous over hereditary factors in many human cancers, the search for causes of cancer was focused on the physical environment (4). At a time of intense public awareness of the potentially adverse impacts of technology on the environment it was perhaps inevitable that human cancer would be attributed to the many drugs, pesticides, plastics, food additives, and other materials generated by the chemical industry. Unfortunately, despite the absence of supporting data, a large segment of the public continues to believe that most human cancers are directly associated with exposure to synthetic chemicals.
There is now general consensus that the personal and cultural habits of individuals are the predominant determinants of human cancer (2,4,5). Thus cigarettes smoking alone accounts for about 30% of all male cancer in the United States, and other "bad" habits such as consumption of alcohol and sexual promiscuity may cause an additional 10%. Diet is a highly variable factor, and its importance can be expected to change markedly with geographic and ethnic background. It is estimated that factors associated with diet are responsible for about 35% of human cancer (2,5). Even in the most highly industrialized countries, it appears that very few cancers can be attributed to exposure to synthetic chemicals. Occupational exposure to a variety of chemicals or industrial processes probably accounts for no more than 5% of human cancer, and the total contribution of environmental pollution is estimated to be only 1-2% (2).
Naturally occurring carcinogens
The fact that human cancer incidence has not changed significantly during the last 50 years provides convincing evidence for the existence of a variety of long-established cancer risk factors not associated with modern technology. Consonant with the epidemiological association of cancer with diet, there is increasing evidence that the human diet contains substantial amounts of a wide variety of natural mutagens and carcinogens (6,7). Many of these -- such as the hydrazine derivatives in mushroom species, pierine, and safrole in black pepper and other plants, theobromine in cocoa and tea, chlorogenic acid in coffee, the pyrrolizidine alkaloids in many species, and the potent mycotoxins such as aflatoxin -- are established mutagens and animal carcinogens and often occur in plants at concentrations of 2-10% by weight (6,7). Clearly, a multitude of other naturally occurring materials of unknown toxicity remain to be isolated and characterized.
Other potent carcinogens are produced as a result of cooking various foods. These include the materials present in charred or browned protein and the mutagenic pyrolysis product methyglyoxal, which is present in coffee (6-8).
It is important to consider our current obsession with identifying, regulating, and generally worrying about what often appear to be trivial carcinogenic risks associated with many synthetic chemicals against the truly overwhelming background of natural carcinogens. The common belief that everything "natural" is good is simply not true, and we must consider naturally occurring chemicals as potentially important causative factors in human cancer. Indeed, in view of the fact that our total daily intake of natural carcinogens could exceed our intake of synthetic materials by as much as 10,000-fold (6,7), it is highly unlikely that, for the general population, the combined carcinogenic effects of all synthetic chemicals can ever be distinguished from the natural background.
What is a carcinogen?
By analogy with previous experience with infectious diseases, the initial concept of a carcinogen was of some discrete physical, chemical, or biological entity. This view was strengthened by early studies showing that, under certain conditions, cancer could indeed be induced by exposing animals to single test chemicals. Today, although most of the public continues to subscribe to the concept of discrete causal agents of cancer, the scientist's view of what constitutes a carcinogen has become far more complex.
Cancer is now considered to be the end result of a multistage process in which a large number of endogenous and exogenous factors interact, simultaneously or in sequence, to disrupt normal cell growth and division (9,10). Cancer, therefore, is a complex disease that may involve a number of different mechanisms. Consequently chemical carcinogenicity should not be considered as an inherent property of a chemical but rather as an outcome of the interaction of a chemical with a complex biological system influenced by many factors.
Traditionally, the development of cancer has been divided into two major stages, initiation and promotion. Initiation describes the process whereby a chemical or other agent damages the DNA of the cell, and promotion refers to the subsequent progression and proliferation of the "transformed" cell through a variety of pathological states (e.g., hyperplasia, neoplasia) leading eventually to a malignant tumor (9,10). It is now recognized that initiation and promotion each consist of several stages and may involve distinct mechanisms; some of these stages are reversible and some are not, but probably all are susceptible to a variety of modulating factors through which they may be enhanced or inhibited.
Initiation can result directly from a mutagenic effect of the chemical (or its metabolite) on DNA, or indirectly from chronic cytotoxicity (resulting in cell turnover and natural errors in cell replication), the activation of cellular oncogenes, or other mechanisms. Initiation can be modulated by factors that change the efficiency of DNA repair or immune surveillance, and, in the case of chemicals that require metabolic activation, initiation will be affected by factors that modify metabolism.
Because these and a large number of other physiological (e.g., age, sex, hormone balance, nutritional status) and exogenous (e.g., stress, dietary fiber, and fat) factors are often key determinants in the development of cancer, should they be defined as carcinogens? Certainly an excess level of a natural hormone can be just as important a causal agent in human cancer as a pesticide residue. How to define carcinogen is not simply of academic importance; it has profound conceptual and practical implications in relation to the development of a reasonable national policy for the regulation of chemical carcinogens. It is also of importance to a confused public that constantly is being barraged by news of an ever-lengthening list of "carcinogens."
The International Agency for Research in Cancer (IARC) has defined chemical carcinogenesis as "the induction by chemicals of neoplasms that are not usually observed, the earlier induction by chemicals or neoplasms that are usually observed, and the induction by chemicals of more neoplasms than are usually found" (11). Although this is a useful operational definition, it does not attempt to address the fundamental distinction between direct-acting carcinogens and those acting indirectly through complex interactions with the test organism (12).
Clearly, a classification of carcinogens based on their mechanisms of action would be preferable, because, in some cases, this might provide an opportunity to adopt a more appropriate regulatory approach. A tilt in this direction is indicated by increasing use of terms like "genotoxic" and "nongenotoxic" (or "epigenetic") carcinogens to distinguish chemicals capable of damaging DNA from those apparently acting by other mechanisms (12,13). Unfortunately, current bioassay procedures do not allow us to classify all carcinogens according to their modes of action.
Although there is mounting evidence that some chemicals are acting through nongenotoxic mechanisms for which thresholds or no-effect dose levels might be anticipated, current regulatory policy requires that all are treated as though they are genotoxic "complete" carcinogens. In 1983, a somewhat simplistic and premature attempt by the EPA to place "epigenetic" carcinogens in a lower regulatory risk category than those considered to be "genotoxic" was greeted by such an uproar or dissent that it was quickly dropped from further consideration (14). A more fruitful approach, recommended by the Office of Science and Technology and others, evaluates each chemical on a case-by-case basis using all available data to understand its mechanism of action (9,15,16).
The search for chemical carcinogens
Efforts to identify chemicals likely to pose a potential cancer threat to humans have intensified in recent years and have relied mainly on the results of chronic bioassays with animals, short-term in vitro tests for genotoxicity, and epidemiological studies in human populations. Chronic bioassay with laboratory animals, mainly rats and mice, remains the major and most practical experimental procedure for identifying potential carcinogens. It is also a procedure beset by many practical and theoretical uncertainties relating to both the design and conduct of the test itself and the subsequent interpretation of the data.
Major limitations of chronic animal bioassays are that they are inherently insensitive and highly variable in nature. Furthermore, there is always a great deal of uncertainty associated with the fact that all such tests ultimately require the extrapolation of data obtained under one set of conditions (i.e., with rodents exposed to very high doses in the laboratory) to predict those likely to occur under an entirely different set of conditions (i.e., with humans exposed to very low doses in the real world). Such dose and species extrapolations are particularly troublesome in the generation of quantitative estimates of human cancer risk.
As a result of the increasing reliance of U.S. regulators on precise numerical estimates of theoretical, upper-bound, human cancer risk (e.g., 1 in a million or, worse, 1.3 or 1.33 in a million) and the matter-of-fact way in which these estimates are reported as real risks by the media, there are many who believe we have exquisitely sensitive testing capabilities. Nothing could be further from the truth. In a typical two-year rodent oncogenicity study utilizing a total of about 600 animals, a cancer occurring at a frequency of 5 in every 1000 would almost certainly go unnoticed. The practical implications of this are considerable because a cancer frequency of 5 in 1000 translates into more than 1 million cases of cancer in the current U.S. population.
In attempts to increase the sensitivity of the animal bioassay, high exposure levels at or approaching the maximum tolerated dose (MTD) are employed and, indeed, are required by most regulatory guidelines (17,18). The importance of the MTD in ensuring a successful outcome to the search for carcinogens is illustrated by the fact that of a group of 52 chemicals judged positive in NTP (National Toxicity Program) chronic bioassays, two-thirds would not have been so classified had the high dose selected been one-half of the MTD actually used (19). Does this increased "power of detection" really reflect true carcinogenic potential, or is it a false positive resulting from cytotoxicity or dose-dependent differences in metabolism and pharmacokinetics? Does it have any relevance to assessing low-dose effects in any species?
Regulatory policy continues to cling to the concept that there is no finite threshold below which carcinogens will not exert an effect. Consequently, although the true shape of the dose-response curve at doses lower than those actually used in the test is not known, low-dose effects can only be estimated by extrapolation to zero of effects observed at high doses (9,18,20). It should be noted that although chronic bioassays typically involve two or three doses spanning perhaps one order of magnitude, extrapolations are often four, five, or more orders of magnitude below the experimental range. Such extrapolations would not even be attempted in most areas of science.
The question of how to extrapolate has led to the development of a number of statistical models for the estimation of low-dose effects, and noisy debate over which is most appropriate has overemphasized this aspect to the problem. It has also led to the generation of precise mathematical risk estimates that are simply not justified by the quality of the toxicology data from which they are derived (21). The selection of the model to be used often dominates the results; although most models are in general agreement in the range of experimentally observed responses, they may provide estimates of low-dose responses that vary to several orders of magnitude (16,22). New and more biologically realistic models currently being developed will be described in future articles in this series (22,23).
It should be noted that risk estimates prepared by federal agencies are described as upper-bound estimates, not actual estimates, of risk. Real risks are judged to be below the upper-bound values and could be as low as zero. This is seldom made explicit in regulatory agency communications and is certainly not understood by either the media or the general public.
There is no question that the "no threshold" concept for carcinogens -- and the "zero tolerance," Delaney-type philosophy with which it is associated -- will continue to cause endless grief as long as it is a part of regulatory policy. Regardless of theoretical arguments for adopting a "no threshold" approach, it seems clear from a practical standpoint that thresholds must exist. If this were not the case the human race would have been long extinct as a result of exposure to natural carcinogens. Surely our regulatory policy must be based on realism rather than theory.
These are but some of the many sources of scientific uncertainty that severely limit current capabilities of interpreting the results of chronic animal bioassays for cancer. Others relate to properly identifying, quantifying, and assessing the relevance to humans of a variety of animal tumor types (pathology) and to evaluating the significance of tumors that occur spontaneously in several strains of test animals. Some of these uncertainties will undoubtedly be obviated as our understanding of the molecular biology of cancer and the mechanisms of carcinogenesis continue to improve. Some will not, however, and the need to extrapolate with respect to both dose and species will continue to present serious problems in evaluating the relevance of animal tests data to humans.
During the past two decades, a variety of short-term tests for genotoxicity have been developed to augment chronic animal bioassays for carcinogenesis (24). These include the well-known Ames Salmonella test for mutagenicity and several other in vitro and in vivo assays based on a number of genotoxic end points such as sister chromatid exchange, unscheduled DNA synethesis, and chromosome aberrations.
Many of these short-term tests have been widely used, but it has become increasingly apparent that there is often little correlation between the results of these tests and those of the chronic bioassays (25). Furthermore, there is considerable inconsistency among the results of different short-term tests themselves. The reasons for the former undoubtedly relate to the fact that carcinogenicity can occur through a variety of both genotoxic and nongenotoxic mechanisms and that many of the short-term tests simply fail to replicate the overall metabolic and pharmacokinetic conditions that exist in the intact test species. Differences between the results of the short-term tests probably reflect the different biological systems involved.
To avoid the problem of deciding which, if any, of the short-term tests is the most useful, it has become common practice to evaluate genotoxicity on the basis of the total weight of evidence from a battery of such tests.
Ashby has criticized this nonscientific approach (26) and has suggested a common-sense strategy that would reduce the number of short-term tests required to demonstrate genotoxic potential to just one or two in vitro tests (e.g., Ames) and one or two in vivo tests (e.g., mouse bone marrow micronucleus assay).
Doubt regarding the utility of many of the short-term tests for genotoxicity has also been raised by a recent NTP study that compared the results of chronic carcinogenesis bioassays and four short-term in vitro (not in vivo) tests for each of a group of 73 chemicals evaluated in the NTP/NCI program (27). Major conclusions from this rather limited study were
The IARC has developed a qualitative classification scheme that divides chemicals into groups with varying degrees of evidence for carcinogenicity in humans (28). These groupings are based on the strength of positive evidence available from animal studies, short-term tests, and human epidemiology, the evidence in each category being related as sufficient, limited, or inadequate. It is of interest that, of some 600 chemicals, chemical mixtures, or processes evaluated by IARC expert working groups, only 23 chemicals and 7 processes are considered causally associated with cancer in humans (Group 1). An additional 14 chemicals (Group 2A) are considered probably carcinogenic to humans. No new human carcinogens have been identified by IARC during the past 10 years; with improving tests procedures and decreasing levels of human exposure, it seems unlikely that many more will be identified.
The IARC has not been able to establish strong links with human cancer for more than a handful of chemicals, but it is equally true that very few chemicals tested are given an unequivocally clean bill of health. Of the first 192 bioassays conducted by the NCI, 98 were judged positive, 91 were judged suggestive or inconclusive, and only 3 were considered negative (29). The NCI guidelines require tests to be conducted on both sexes for each of two rodent species. A chemical is judged "positive" if it yields a positive response in one well-conducted test (i.e., in one sex of one species). A "negative" classification requires a uniformly negative response in each of the four tests. If the test results are equivocal or if the tests themselves are considered to have been inadequately designed or conducted, the conclusion with respect to carcinogenic potential is usually suggestive or inconclusive. Unfortunately, no matter how tenuous the data, these latter terms are frequently interpreted as positive by nonscientists who are unable to understand that a negative can never be demonstrated experimentally.
Regulatory goals and directions
The development of a sound regulatory policy that not only protects the public against the potentially adverse health effects of chemicals but also creates the incentive for industry to develop new materials of real benefit to society is, indeed, a difficult task. It is particularly difficult when, as is almost always the case today, the major focus of concern is cancer.
Despite the fact that there is no epidemic of human cancer in the United States and despite the fact that, of the cancer that does occur, only a very small percentage can be attributed to synthetic chemicals, we continue to pour billions of dollars worth of time, effort, and resources into attempts to identify carcinogens. Hindered by the scarcity and uncertainty of the science and complicated by the inevitable involvement of policy and value judgments, the results of such efforts are seldom clear-cut or cost-effective.
The current obsession for regulating carcinogenic risk in the United States seems to be based more on the public's perception of risk and fear of cancer than on risks that actually can be demonstrated. We are caught up in a vicious circle in which, in attempting to respond to public pressure, regulators are focusing on and identifying increasingly smaller risks that in turn further alarm the public and create yet more pressure to regulate. We seem unable, in a regulatory sense, to distinguish toxicological trivia from more clear-cut problems, and as a society we spend our time worrying about cancer risks that are orders of magnitude smaller than those risks most of us face driving to work each day.
Surely the time has come to pause and take serious stock of our regulatory goals and directions. We have limited resources, and we must concentrate these on resolving real problems that require immediate attention. Despite the inherent difficulties it entails, we must address the issue of what constitutes a significant health risk; in developing policy, we must balance this against what we as a nation can afford in terms of remedial action to reduce risks. We cannot afford to go blindly along, throwing large amounts of money into attempts to resolve imaginary problems. Instead, we must carefully identify and rank the areas of real health concern and develop appropriate strategies by which the associated risks can be avoided or minimized.
(1) Bailar, K.C. III; Smith, E.M. N. Engl. J. Med. 1986, 314, 1226-32.
(2) Doll, R.; Peto, R. The Causes of Cancer; Oxford University Press: New York, 1981.
(3) Gori, G.B.; Lynch , C.J. Reg. Toxicol. Pharmacol. 1986, 6(3), 261-73.
(4) Higginson, J.; Muir, C.S. J. Natl. Cancer Inst. 1979, 63 1291-98.
(5) Higginson, J. Environ. Mutagen. 1983, 5, 929-40.
(6) Ames, B.N. Science 1983, 221, 1256-64.
(7) Ames, B.N.; Magaw, R.; Gold, L.S. Science 1987, 236, 271-80.
(8) Sugimura, T.; Sato, S. Cancer Res. 1983, 43, 2415s.
(9) Office of Science and Technology Policy. "Chemical Carcinogens: A Review of the Science and its Associated Principles"; Fed. Regist. 1985, 50, 10371-442.
(10) Farber, E. Cancer Res. 1984, 44, 5463-74.
(11) International Agency for Research on Cancer (IARC). "IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans"; IARC: Lyons, France, 1982; Vol. 29, p. 16.
(12) Weisburger, J; Williams, G. In Toxicology: The Basic Science of Poisons, 2nd ed.; Doull, J.; Klaassen, C.D.; Amdur, M. O., Eds.; MacMillan: New York, 1980; pp. 84-138.
(13) Weisburger, J. Jpn. J. Cancer Res. 1985, 76, 1244-46.
(14) Marshall, E. Science 1983, 220, 36-37.
(15) Squire, R.A.. Science 1981, 214-877-80.
(16) Panel report; Science 1984, 225, 682-87.
(17) International Life Science Institute (ILSI). In Current Issues in Toxicology; Grice, H.C., Ed.; Springer-Verlag: New York, 1984; pp. 9-49.
(18) Environmental Protection Agency (EPA). "Guidelines for Carcinogen Risk Assessment"; Fed. Regist. 1986, 51, 33993-34014.
(19) Haseman, J. K. Fund. Appl. Toxicol. 1985, 5, 66-78.
(20) National Toxicology Program (NTP). "Report of the NTP Ad Hoc Panel on Chemical Carcinogenesis Testing and Evaluation"; U.S. Dept. of Health and Human Services: Washington, D.C. 1984.
(21) Krewski, D.; Van Ryzin, J. In Statistics and Related Topics; Csorgo, M. et al., Eds.; Elsevier/North Holland: Amsterdam, 1981; pp. 201-31.
(22) Menzel, D. ES&T, in press.
(23) Sielken, R. ES&T, in press.
(24) Weisburger, J.H.; Williams, G. In Chemical Carcinogens; 2nd ed.; Searle, C.E., Ed.; American Chemical Society: Washington, D.C., 1984; Vol. 2, pp. 1323-73.
(25) Shelby, M.D.; Stasiewicz, S. Environ. Mutgen. 1984, 6, 871-76.
(26) Ashby, J. Mutagenesis 1986, 1, 3-16.
(27) Tennant, R..W. et al. Science 1987, 236, 933-41.
(28) International Agency for Research on Cancer (IARC). "IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans"; IARC: Lyons, France, 1982; Supplement 4, pp. 7-23.
(29) Hottendorf, G.H.; Pachter, J. Toxicol. Pathol. 1982, 10, 22-26.
Please report any errors or omissions to
Your comments, suggestions, ideas are welcome.