|
|
Technical Note DOER-R1
September 1998
survival or reproduction of these receptors?" The Tier I characterization of the sediments relies on
available results of prior chemical testing, measurements of physical characteristics, organic carbon
content, grain size, and review of regulatory records and published literature regarding the material
to be dredged (published studies, permit reviews, Federal databases, etc.). This information is
generally sufficient for a risk assessor to develop the Hazard Identification and a list of contaminants
of concern (COCs). Note that specifying COCs is an integral part of risk assessment that will have
already been accomplished as a Tier I activity based on explicit criteria in the Dredged Material
Testing Manuals.
The identification of COCs during Tier I depends in part on the toxicological importance of each
contaminant. This Tier I task therefore provides a start on the risk assessment's Toxicity or Effects
Assessment, which answers the question, "Is there a known quantity of the chemical or physical
hazard that results in an adverse effect to the likely receptors?" The risk assessment may require
that this information be reformulated to conform to the parameters used in human health or
ecological exposure models. This is generally accomplished by reference to on-line USEPA and
USACE databases or an expanded literature review.
The exposure assessment addresses the question, "Are there any conservative but realistic activities
or physical and biological pathways by which the receptors may encounter the chemical or physical
hazards?" This is a considerable expansion of Tier I sediment characterizations or Tier II modeling
activities and also incorporates the bioaccumulation testing conducted in Tier III. This is the risk
assessment component that will require the most expansion upon prior data gathering activities
because this is the point that integrates the site selection information with the dredged material
evaluation. Although it generally will not require new data collection, it will require a reformulation
of the information into a site-specific conceptual model. The conceptual model attempts to link
management technology, site characteristics, and dredged material evaluations (Figure 1).
In summary, the activities of site selection and dredged material evaluation provide most of the
information needed to conduct a risk assessment. There will be some necessary renewed literature
reviews and a reformulation of the data, but expensive, time-consuming field data collections are
unlikely.
What is the role of risk assessment in the dredged material risk management
process? Risk assessment alone cannot compel a decision at a dredged material management
site. In those cases where the dredged material manager chooses to apply risk assessment, he or she
should consider it as part of a larger risk analysis process that includes risk management. In prior
considerations of risk management, USACE (1995) views this process as a function of several
factors: risk and uncertainty, cost, schedule, value of resources protected, regulatory requirements,
political factors, economic factors, technical feasibility, environmental justice/equity. The role of
the risk assessment in this general process is to provide realistic assessments, not hypothetical or
highly conservative assessments that do not provide meaningful risk information to decision makers.
Within the risk management process, the risk assessment contributes most readily to the evaluation
of alternatives.
The Framework Document (USEPA/USACE 1992) provides comprehensive guidance on
identifying, screening, and selecting "reasonable" dredged material disposal alternatives. The
9
|
Privacy Statement - Press Release - Copyright Information. - Contact Us - Support Integrated Publishing |