|
3-1
|
|
Transition in EPA Human Health Risk-Assessment Characteristics According to EPA,
|
|
69
|
|
4-1
|
|
Examples of Factors Affecting Susceptibility to Effects of Environmental Toxicants,
|
|
109
|
|
5-1
|
|
Potential Approaches to Establish Defaults to Implement the Unified Framework for Dose-Response Assessment,
|
|
175
|
|
6-1
|
|
Examples of Explicit EPA Default Carcinogen Risk-Assessment Assumptions,
|
|
194
|
|
6-2
|
|
Examples of Explicit EPA Default Noncarcinogen Risk-Assessment Assumptions,
|
|
195
|
|
6-3
|
|
Examples of “Missing” Defaults in EPA “Default” Dose-Response Assessments,
|
|
196
|
|
7-1
|
|
Modified Version of Stressor-Based Cumulative-Risk-Assessment Approach from Menzie et al. (2007) Oriented Around Discriminating among Risk- Management Options,
|
|
222
|
|
C-1
|
|
Timeline of Selected EPA Risk-Assessment Activities,
|
|
284
|
|
D-1
|
|
Environmental Protection Agency Response to National Research Council Recommendations of 1983-2006: Policy, Activity, and Practice,
|
|
301
|
|
E-1
|
|
Nine Evaluation Criteria for Superfund Remedial Alternatives,
|
|
378
|
|
E-2
|
|
Examples of Default Exposure Values with Percentiles,
|
|
380
|