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When risk characterization is complete, a description of the risk assessment is communicated to the risk manager (Figure 28.1) to support a risk management decision. This communication usually is a report and might include:
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A description of risk assessor/risk manager planning results. A review of the conceptual model and the assessment end points. A discussion of the major data sources and analytical procedures used. A review of the stressor-response and exposure pro les. A description of risks to the assessment endpoints, including risk estimates and adversity evaluations. A summary of major areas of uncertainty and the approaches used to address them. A discussion of science policy judgments or default assumptions used to bridge information gaps, and the basis for these assumptions.
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After the risk assessment is completed, risk managers may consider whether additional follow-up activities are required. Depending on the importance of the assessment, con dence level in the assessment results, and available resources, it may be advisable to conduct another iteration of the risk assessment in order to facilitate a nal management decision. Ecological risk assessments are frequently designed in sequential tiers that proceed from simple, relatively inexpensive evaluations to more costly and complex assessments. Initial tiers are based on conservative assumptions, such as maximum exposure and ecological sensitivity. When an early tier cannot suf ciently de ne risk to support a management decision, a higher assessment tier that may require either additional data or applying more re ned analysis techniques to available data may be needed. Higher tiers provide more ecologically realistic assessments while making less conservative assumptions about exposure and effects. Another option is to proceed with a management decision based on the risk assessment and develop a monitoring plan to evaluate the results of the decision. For example, if the decision is to mitigate risks through exposure reduction, monitoring will help determine whether the desired reduction in exposure (and effects) is being achieved. Monitoring is also critical for determining the extent and nature of any ecological recovery that may be occurring. Ecological risk assessment is important for environmental decision making because of the high cost of eliminating environmental risks associated with human activities and the necessity of making regulatory decisions in the face of uncertainty. Ecological risk assessment provides only a portion of the information required to make risk
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management decisions, but this information is critical to scienti cally defensible risk management. Thus ecological risk assessments should provide input to a diverse set of environmental decision-making processes, such as the regulation of hazardous waste sites, industrial chemicals, and pesticides, and improve the management of watersheds affected by multiple nonchemical and chemical stressors.
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Bartell, S. M., R. H. Gardner, and R. V. O Neill. Ecological Risk Estimation. Boca Raton, FL: Lewis Publishers, 1992. Cardwell, R. D., B. R. Parkhurst, W. Warren-Hicks, and J. S. Volosin. Aquatic ecological risk. Water Environ. Technol. 5: 47 51, 1993. Harwell, M. A., W. Cooper, and R. Flaak. Prioritizing ecological and human welfare risks from environmental stresses. Environ. Manag. 16: 451 464, 1992. Kendall, R. J., T. E. Lacher, C. Bunck, B. Daniel, C. Driver, C. E. Grue, F. Leighton, W. Stansley, P. G. Watanabe, and M. Whitworth. An ecological risk assessment of lead shot exposure in non-waterfowl avian species: Upland game birds and raptors. Environ. Toxicol. Chem. 15: 4 20, 1996. National Research Council. A paradigm for ecological risk assessment. In Issues in Risk Assessment. Washington, DC: National Academy Press, 1993. National Research Council. Science and Judgment in Risk Assessment. Washington, DC: National Academy Press, 1994. National Research Council. Understanding Risk: Informing Decisions in a Democratic Society. Washington, DC: National Academy Press, 1996. Ruckelshaus, W. D. Science, risk, and public policy. Science 221: 1026 1028, 1983. Solomon, K. R., D. B. Baker, R. P. Richards, K. R. Dixon, S. J. Klaine, T. W. La Point, R. J. Kendall, C. P. Weisskopf, J. M. Giddings, J. P. Geisy, L. W. Hall, W. M. Williams. Ecological risk assessment of atrazine in North American surface waters. Environ. Toxicol. Chem. 15(1): 31 76, 1996. Suter, G. W., II. Endpoints for regional ecological risk assessments. Environ. Manag. 14: 19 23, 1990. Suter, G. W., II. Ecological Risk Assessment. Boca Raton, FL: Lewis Publishers, 1993. Suter, G. W., II. A critique of ecosystem health concepts and indexes. Environ. Toxicol. Chem. 12: 1533 1539, 1993. US Environmental Protection Agency. Summary report on issues in ecological risk assessment. Washington, DC: Risk Assessment Forum, USEPA, 1991. EPA/625/3-91/018. US Environmental Protection Agency. Framework for ecological risk assessment. Washington, DC: Risk Assessment Forum, USEPA, 1992. EPA/630/R-92/001. US Environmental Protection Agency. Peer review workshop report on a framework for ecological risk assessment. Washington, DC: Risk Assessment Forum, USEPA, 1992. EPA/625/391/022. US Environmental Protection Agency. A review of ecological assessment case studies from a risk assessment perspective. Washington, DC: Risk Assessment Forum, USEPA, 1993. EPA/630/R92/005. US Environmental Protection Agency. Ecological risk assessment issue papers. Washington, DC: Risk Assessment Forum, USEPA, 1994. EPA/630/R-94/009. US Environmental Protection Agency. Proposed guidelines for ecological risk assessment. Washington, DC: Risk Assessment Forum, USEPA, 1996. EPA/630/R-95/002B.
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