The precautionary principle has provoked a spirited debate among environmentalists worldwide, but it is equally relevant to public health and shares much with primary prevention. Its central components are (1) taking preventive action in the face of uncertainty; (2) shifting the burden of proof to the proponents of an activity; (3) exploring a wide range of alternatives to possibly harmful actions; and (4) increasing public participation in decision making.

Precaution is relevant to public health, because it can help to prevent unintended consequences of well-intentioned public health interventions by ensuring a more thorough assessment of the problems and proposed solutions. It can also be a positive force for change. Three aspects are stressed: promoting the search for safer technologies, encouraging greater democracy and openness in public health policy, and stimulating reevaluation of the methods of public health science.

IN MARCH 1999, THE LOS Angeles Unified School District, the nation's largest school district, announced a new policy on use of pesticides in its school buildings. The district committed to a policy of integrated pest management, giving priority to nonchemical approaches to pest control, and set a long-term goal of eliminating all chemical controls. In establishing this policy, the school district invoked the precautionary principle, saying:

The Precautionary Principle is the long-term objective of the District. The principle recognizes that:

1.

No pesticide product is free from risk or threat to human health, and

2.

Industrial producers should be required to prove that their pesticide products demonstrate an absence of [human health risks] rather than requiring that the government or the public prove that human health is being harmed.1

By stating a set of basic tenets (all pesticides are potentially harmful, and nonchemical methods shall be preferred) and a long-term objective (“to provide for the safest and lowest risk approach to control pest problems while protecting people, the environment, and property”), the policy stimulates the search for safer alternatives without tying the hands of the district when no alternative to a pesticide can be found. The policy is also significant for what it does not include: there is no list of banned substances, nor a stipulation of an “acceptable” level of risk.

Whether or not one agrees with this approach to pesticide management (we do), it seems clear that the school district's invocation of the precautionary principle raises important issues for public health scientists and activists.

In this commentary, we briefly describe the key elements of the precautionary principle, emphasizing several aspects important to public health. Our perspective is informed by a university– community collaborative effort to refine the meaning of the precautionary principle and develop strategies for applying it to environmental health policy.2,3 We argue that the precautionary principle is good for public health because it promotes the search for safer technologies, encourages greater democracy and openness in public health policy, and stimulates reevaluation of the methods of public health science.

The definition of the precautionary principle developed for the Rio Declaration of 1992 is often cited,4 and the 1998 Wingspread Statement contains similar language: “when an activity raises threats of harm to human health or the environment, precautionary measures should be taken even if some cause and effect relationships are not fully established scientifically.”5 The statement also lists 4 central components of the principle: (1) taking preventive action in the face of uncertainty, (2) shifting the burden of proof to the proponents of an activity, (3) exploring a wide range of alternatives to possibly harmful actions, and (4) increasing public participation in decision making.

The term “precautionary principle” was introduced into English as a translation of the German word Vorsorgeprinzip. An alternative translation might have been “foresight principle,” which carries a connotation of anticipatory action—a positive, active idea—rather than precaution, which to many sounds negative. In German environmental policy, the Vorsorgeprinzip stimulates social planning for innovation, sustainability, and job creation.6

In the United States, the precautionary principle is being promoted by environmental and public health advocates.3 To these groups, US environmental policy often seems to be more reactionary than precautionary, requiring a high degree of certainty of harm before preventive action is taken and emphasizing management of risks rather than prevention. The precautionary principle is viewed as an opportunity to shift the terms of environmental debates by calling for preventive action even when there is uncertainty (but with credible evidence of potentially significant impacts), by shifting the burden of monitoring and hazard assessment onto those who propose potentially hazardous policies and by emphasizing alternatives and democracy.5

The American Public Health Association recently passed a resolution reaffirming its support of the principle and urging its application in the protection of children's health from environmental hazards.7 Strong support for precaution is also found in the environmental policies of the European Union.8

The precautionary principle has been advocated for public health because of the importance of anticipating unintended health consequences of well-intentioned public health interventions.9 Seeking to avoid creating new problems while solving existing ones is an important aspect of the precautionary principle, but it is not the only way in which precaution can benefit public health.

The identification of safer alternatives and opportunities for prevention is central to the precautionary principle. Too frequently, policymakers ask the question “How much risk does this activity pose, and is it significant?” or “What level of risk is acceptable?” These questions, deeply ingrained in the regulatory approaches of many government agencies, tend to focus on the quantification of potential hazards rather than the prevention of pollution.1012 They often provoke a sharp debate about whether the risk has been characterized accurately. When public health advocates and environmentalists enter into this debate, they may inadvertently be ceding the most powerful position, that of questioning whether the hazardous substance or intervention is needed at all.

A different, and potentially more precautionary, way to think about uncertain risks is to begin from a different set of questions: Is the proposed activity needed, and if so, how much contamination can be avoided while still achieving societal goals? and Are there alternatives to this activity that clearly avoid hazards? For example, chlorinated solvents fulfill a cleaning function that can often be accomplished by aqueous solutions. This shift in perspective requires a set of skills not always found in regulatory agencies—technology and product design, full-cost accounting and other management systems. It also requires the broadest possible perspective on the potential unintended consequences of policy choices.

A variety of methodologies exist with which to evaluate policy alternatives and identify potential unintended consequences. Trade-off analysis has been proposed as an alternative to traditional cost– benefit analysis and risk assessment; in trade-off analysis, the full range of risks and benefits of competing technology options are assessed without the requirement to translate the potential impacts into a single quantitative figure.13 Health impact assessments provide a means to detect the negative health implications of non–health-related governmental policies.14 Work-environment impact assessments can be used to identify ways in which an intervention in the work environment may result in unanticipated health risks to workers,15 and the Pollution Prevention Options Analysis System provides a comprehensive semiquantitative approach to comparing and evaluating the potential adverse effects of technologies designed to reduce chemical use and waste.16

Shifting the questions that frame the problem reorients the focus of environmental policy from quantification of risks to analysis of solutions and thus permits a broader examination of all the available evidence on hazard, exposure, uncertainty, and alternatives. The precautionary principle is a means of saying yes to innovative, cleaner technologies (although critics have argued that it will only lead to stopping new technologies). A thorough alternatives assessment may identify needs for cleaner technologies, which in turn can inform the planning of sustainable economic development activity.11

Quantitative risk assessment plays a central role in environmental health policy in the United States. Weighing policy alternatives will inevitably involve assessing and comparing risks, but the determination of whether a risk is too big depends in part on whether there are alternatives to reduce that risk. Availability of a safer alternative can obviate the need for a costly, contentious, and potentially misleading quantitative risk assessment.

The decision to ban the use of certain phthalate plasticizers in toys provides an illustration. The Danish Environment Agency justified this action with the following reasoning: There is evidence of children's exposure and evidence of toxicity to animals; children are particularly susceptible to many toxic substances; alternative materials exist; and the product serves no necessary function. The agency concluded that the plasticizers should not be used in toys (L. Seedorf, MS, Director, Chemicals Division, Danish Environmental Protection Agency, oral communication, May, 1999). The US Consumer Product Safety Commission reached a similar decision, but only after a costly, time-consuming quantitative risk assessment. The commission concluded that given uncertainties in the size of the risk, manufacturers should voluntarily remove these substances from toys.17 In the end the outcomes were the same, but the decision-making approach and the costs to the public were quite different.

Foresight should involve setting long-term goals, a practice that is fairly common in public health. Examples are the smallpox eradication campaign, the US Public Health Service Healthy People 2010 priorities, and national nutrition goals. Goal setting focuses not on what future events are likely to happen but rather on how desirable future outcomes can be obtained.18 Once established, goals help to focus attention on the development of policies and measures to achieve goals while minimizing social disruption and unintended consequences.

With regard to hazardous substances, goals could include reducing exposures to such substances, reducing production of hazards (e.g., phasing out the most hazardous chemicals), and reducing the incidence of environmentally related diseases. Another suggested goal is to reduce general population body burdens of broad classes of potentially toxic substances by 5% to 10% per year.19 Such an effort is likely to have a positive health impact, even though it may never be possible to understand all of the ways in which mixtures of low concentrations of chemicals may affect health.

Participation and transparency are essential components of a more precautionary approach to public health decision making. Fiorino has identified several reasons for democratizing environmental decision making. First, because nonexperts think more broadly and are not bound by disciplinary constraints, they see problems, issues, and solutions that experts miss. Second, lay judgments reflect a sensitivity to social and political values and common sense that experts' models do not acknowledge. Third, the lay public may be better than experts at accommodating uncertainty and correcting errors.20 Openness brings different perspectives, which may reduce the danger of an unintended consequence. Also, the weighing of alternative policies should include many points of view, because the benefits and costs of public health and environmental policy choices may accrue to different groups.

When there is much uncertainty about alternative courses of action, it is risky for experts to decide without input from affected communities. The usual strategy is to attempt to present the options as clear and the science as convincing. However, a long series of public health and environmental crises that were apparently unforeseen by scientists have undermined public confidence, making it more difficult for simple reassurances to be effective. The list includes the Three Mile Island and Chernobyl nuclear accidents, Love Canal, the destruction of the ozone layer, and global warming. An increasingly educated citizenry has begun to challenge the apparent confidence of the experts. Add to this the successful campaigns of AIDS activists and breast cancer survivors to participate in the planning of health research, and it appears to be time to fundamentally change the way that the public participates in the use of public health science.

Broader public participation processes may increase the quality, legitimacy, and accountability of complex decisions. Given the public nature of environmental decisions (which involve highly uncertain, contested values), more effective processes for involving affected communities could increase trust in government. Such processes must be both fair and competent, meaning that they allow all those who want to participate to have substantive access to the decision-making process from the beginning and that they provide financial and technical resources so citizens can participate on equal terms with experts.21 In addition, there must be clearly defined mechanisms by which citizen input is fed into the policymaking process.

A long-term educational strategy to increase the public's understanding of the strengths and limits of scientific evidence is needed as part of increasing public participation. The Danish Board of Technology has been experimenting for several years with innovative forms of decision making on broad technology policy decisions. These “consensus conferences” involve lay panels trained in the science and other aspects of a contemporary concern, resulting in a focused dialogue between the general public and experts. To date, more than 20 such conferences have been held in Denmark, informing government policy on topics including genetically modified foods, the human genome project, and air pollution.22

Environmental scientists study highly complex, poorly understood systems, in which causal links between exposures and disease are difficult to quantify. In this uncertain terrain, what are the appropriate standards of evidence for science to inform public health policy? The answer must be tailored to the task. We believe that there are ways in which the methods of scientific inquiry often implicitly impede precautionary action, making it more difficult for policymakers to take action in the face of uncertainty.2 Often, scientific research focuses on narrowly defined quantifiable aspects of a problem while the reality is more complex, requiring systems-level thinking and interdisciplinary research methods.

Public health scientists may be able to assist in the cause of precaution by choosing research methods, well within the bounds of good practice, that would be more helpful to policymakers faced with high-stakes decisions and scientific uncertainty. For example, more and better investigation and communication of uncertainties (what we know, what we do not know, and what we cannot know) in study results will assist a more open decision-making process. Public health scientists could also use qualitative methods more effectively to characterize the complexities of the populations, communities, and ecosystems from which quantitative results are drawn.

Finally, the precautionary principle should challenge scientists to explore new areas of research—interactions, cumulative effects, and effects on different levels of systems (individuals, families, communities, nations)—and new collaborations between disciplines and scientists and the lay public. Multidisciplinary teams will be more likely to develop hypotheses that lead to insights not possible from narrow disciplinary viewpoints, as well as to identify data that may not be accessible to one particular group. The development of the environmental endocrine disruption hypothesis provides one example.23

The precautionary principle represents a call to reevaluate the ways in which science informs policy, and in particular the ways in which scientific uncertainty should be handled. Scientific research plays an essential role in evaluating the costs, risks, and benefits of proposed public health policies, but the scientific data are often limited by large areas of uncertainty. In these gray areas, activities that potentially threaten public health are often allowed to continue because the norms of traditional science demand high confidence to reject null hypotheses and so detect harmful effects. This scientific conservatism is often interpreted as favoring the promoters of a potentially harmful technology or activity when the science does not produce overwhelming evidence of harm. Being “conservative” in science is not the same as being precautionary.

When there is substantial scientific uncertainty about the risks and benefits of a proposed activity, policy decisions should be made in a way that errs on the side of caution with respect to the environment and the health of the public.2

The precautionary principle has been criticized for being overly vague.24,25 To some extent the critics are correct, but much work is now under way to define what precaution means in practice and how it can improve decision making regarding uncertain, complex hazards.2,26,27 This is an opportunity for the public health community to affect the ways in which precaution is defined in practice. At the same time, there is a risk that proponents of the principle will be held to an unrealistically high standard—an assumption that all public health problems should somehow be resolved through the application of precaution. Where science and politics collide, there will always be ambiguity and contention, and it seems unreasonable to expect any single new idea to sweep these away entirely. We should be careful not to overuse the precautionary principle, particularly when there is clear evidence that damage has been done or there is no reasonable evidence to suspect a risk to public health.

If the precautionary principle represents a desirable goal in public health, one may ask, What is the “not sufficiently precautionary principle” on which policies are currently based? Too often, we believe, public health and environmental policies are based on a principle of reaction rather than precaution. Government regulatory agencies are often put in the position of having to wait until evidence of harm is established beyond all reasonable doubt before they can act to prevent harm. A shift from reaction to precaution is entirely consistent with the core values of public health practice. We believe that public health officials, researchers, and advocates should embrace the precautionary principle as an opportunity to reinvigorate the great preventive tradition of public health action in the face of uncertainty.

This work was supported in part by grants from the John Merck Fund, the Jessie B. Cox Charitable Trust, the New York Community Trust, the V. Kann Rasmussen Foundation, and the Mitchell Kapor Foundation.

The Science and Precaution Working Group participated in discussions that helped to define and clarify our understanding of the precautionary principle. We thank Dr Margaret Quinn for many helpful comments. Dr Carlos Eduardo Siqueira suggested that it might be useful to define reaction as the status quo principle impeding precaution.

References

1. Los Angeles Unified School District, unpublished policy, cited in Rachel's Environment & Health News No. 684, January 27, 2000. Available at: http://www.rachel.org/bulletin/index. cfm?St=4. Accessed June 18, 2001. Google Scholar
2. Kriebel D, Tickner J, Epstein P, et al. The precautionary principle in environmental science. Environ Health Perspect. In press. Google Scholar
3. Ketelsen L. The Massachusetts Precautionary Principle Project: a model for public health organizing and integrating public values into “public” health. Paper presented at: Annual Meeting of the American Public Health Association; Boston, Mass; November 15, 2000. Google Scholar
4. Rio Declaration on Environment and Development. Available at: http:// www.igc.org/habitat/agenda21/rio-dec.html. Accessed June 18, 2001. Google Scholar
5. Raffensperger C, Tickner J, eds. Protecting Public Health and the Environment: Implementing the Precautionary Principle. Washington, DC: Island Press; 1999. Google Scholar
6. Boehmer-Christiansen S. The precautionary principle in Germany—enabling government. In: O'Riordan T, Cameron J, eds. Interpreting the Precautionary Principle. London, England: Earthscan; 1994:31–61. Google Scholar
7. APHA policy statement 200011: the precautionary principle and children's health. Am J Public Health. 2001; 91:495–496. LinkGoogle Scholar
8. Commission of the European Community. Communication from the Commission on the Precautionary Principle. Brussels, Belgium: Commission of the European Community; 2000. Publication COM(2000)1. Google Scholar
9. Goldstein BD. The precautionary principle also applies to public health actions. Am J Public Health.2001;91: 1358–1361. LinkGoogle Scholar
10. Gauging Control Technology and Regulatory Impacts in Occupational Safety and Health. Washington, DC: Office of Technology Assessment, US Congress; 1995. OTA-ENV-635. Google Scholar
11. Quinn MM, Kriebel D, Geiser K, Moure-Eraso R. Sustainable production: a proposed strategy for the work environment. Am J Ind Med.1998;34:297– 304. Crossref, MedlineGoogle Scholar
12. Commoner B. Making Peace with the Planet. New York, NY: Pantheon; 1990. Google Scholar
13. Ashford N. The role of risk assessment and cost/benefit analysis in decisions concerning safety and the environment. In: FDA Symposium on Risk/ Benefit Decisions and the Public Health. Colorado Springs, Colo: Office of Public Affairs, Food and Drug Administration; 1980:159–168. Google Scholar
14. Scott-Samuel A, Birley M, Ardern K. Merseyside Guidelines for Health Impact Assessment. Merseyside, UK: Merseyside Health Impact Assessment Steering Group; 1998. Also available at: http://www.liv.ac.uk/~mhb/publicat/merseygui/index.html. Accessed June 18, 2001. Google Scholar
15. Rosenberg BJ, Barbeau EM, Moure-Eraso R, Levenstein C. The work environment impact assessment: a methodologic framework for evaluating health-based interventions. Am J Ind Med.2001;39:218–226. Crossref, MedlineGoogle Scholar
16. Tickner J. Pollution Prevention Options Analysis System—P2OASYS—Users Guide. Lowell: Massachusetts Toxics Use Reduction Institute; 1997. Google Scholar
17. The Risk of Chronic Toxicity Associated with Exposure to Diisononyl Phthalate (DINP) in Children's Products. Washington, DC: US Consumer Product Safety Commission; 1998. Also available at: http://www.cpsc.gov. Accessed June 18, 2001. Google Scholar
18. Dreborg K. Essence of backcasting. Futures.1996;28:813–838. CrossrefGoogle Scholar
19. Jackson R. Unburdening ourselves. Silent Spring Review. Fall 2000. Available at: http://www.silentspring.org. Accessed June 18, 2001. Google Scholar
20. Fiorino D. Citizen participation and environmental risk: a survey of institutional mechanisms. Issues in Science and Technology.1990;15:226–243. Google Scholar
21. Renn O, Webler T, Wiedermann P. Fairness and Competence in Citizen Participation. Dordrecht, the Netherlands: Kluwer Academic Publishers; 1995. Google Scholar
22. Deniel P, Renn O. Planning cells: a gate for “fractal” mediation. In: Renn O, Webler T, Wiedemann P, eds. Fairness and Competence in Citizen Participation: Evaluating Models for Environmental Discourse. Boston, Mass: Kluwer Academic Publishers; 1995:141–156. Google Scholar
23. Colborn T, Clement C. Chemically Induced Alterations in Sexual and Functional Development: The Wildlife/Human Connection. Princeton, NJ: Princeton Scientific Publishing Co; 1992. Google Scholar
24. Bodanksy D. The precautionary principle in US environmental law. In: O'Riordan T, Cameron J, eds. Interpreting the Precautionary Principle. London, England: Earthscan; 1994:203–228. Google Scholar
25. Graham J. Perspectives on the precautionary principle. Human and Ecological Risk Assessment.2000;6:383–385. CrossrefGoogle Scholar
26. Tickner J, Raffensperger C, Myers N. The Precautionary Principle in Action: A Handbook. Windsor, ND: Science and Environmental Health Network; 1999. Google Scholar
27. Tickner J, Raffensperger C. The American view on the precautionary principle. In: O'Riordan T, Cameron J , Jordan A, eds. Reinterpreting the Precautionary Principle. London, England: Cameron & May; 2001. Google Scholar

Related

No related items

TOOLS

SHARE

ARTICLE CITATION

David Kriebel, ScD, and Joel Tickner, ScD The authors are with the Lowell Center for Sustainable Production, Department of Work Environment, University of Massachusetts, Lowell. “Reenergizing Public Health Through Precaution”, American Journal of Public Health 91, no. 9 (September 1, 2001): pp. 1351-1355.

https://doi.org/10.2105/AJPH.91.9.1351

PMID: 11527753