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ERDC TN-DOER-E9
May 2000
CONCLUSIONS: More than 20 years ago, the existing literature did not permit a "neat compila-
tion and analysis" of the ecological consequences of dredging (Morton 1977). Despite continued
concern and research in this area, particularly with respect to effects of suspended sediments,
assessments of potential impacts on aquatic organisms remain highly subjective. Clearly, many
past investigations focused upon detrimental effects induced by dosages well above those likely to
occur at dredging project sites. Also obvious is the fact that appropriately designed studies to address
dredging impacts are very limited in number and breadth of coverage, both with respect to taxa and
life history stage. The lack of relevant data continues to foster controversy in impact assessments.
Extrapolations from responses at inappropriate concentrations or exposure durations are widespread
and engender interpretations rife with opportunities for false conclusions. Likewise, generic
assessments of impacts based on responses across broad taxonomic lines should be viewed with
extreme caution.
Until adequate data are available quantifying biological responses to appropriate concentration/
exposure duration dosages, assessment of potential dredging-induced impacts must unfortunately
remain subjective. The authors endorse the construction of models (e.g., Newcombe and Jensen
1996) to integrate "best available knowledge" and to optimize objectivity in the assessment process.
However, it is strongly recommended that any assessment consider not only the concentration
threshold aspect of the dosage issue, but also realistic estimates of the likelihood and duration of
exposure above that threshold. Tools to assist in this process are currently being developed under
the Dredging Operations and Environmental Research Program, such as SSFATE, a numerical
model customized for simulations of dredging-related suspended-sediment plume dynamics (see
Johnson et al. 2000).
POINTS OF CONTACT: For additional information contact Dr. Douglas Clarke (601-634-3770,
clarked@wes.army.mil), or the Program Manager of the Dredging Operations and Environmental
Research Program, Dr. Robert M. Engler (601-634-3624, englerr@wes.army.mil). This technical
note should be cited as follows:
Clarke, D. G., and Wilber, D. H. (2000). "Assessment of potential impacts of dredging
operations due to sediment resuspension," DOER Technical Notes Collection (ERDC
TN-DOER-E9), U.S. Army Engineer Research and Development Center, Vicksburg, MS.
www.wes.army.mil/el/dots/doer
REFERENCES
Auld, A. H., and Schubel, J. R. (1978). "Effects of suspended sediment or fish eggs and larvae: A laboratory
assessment," Estuarine and Coastal Marine Science 6, 153-164.
Boehlert, G. W., and Morgan, J. B. (1985). "Turbidity enhances feeding abilities of larval Pacific herring. Clupea
harengus pallasi," Hydrobiologia 123, 161-170.
Bricelj, V. M., and Malouf, R. E. (1984). "Influence of algal and suspended-sediment concentrations on the feeding
physiology of the hard clam Mercenaria mercenaria," Marine Biology 84, 155-165.
Bricelj, V. M., Malouf, R. E., and De Quillfeldt, C. (1984). "Growth of juvenile Mercenaria mercenaria and the effect
of resuspended bottom sediments," Marine Biology 84, 167-173.
Cake, E. W., Jr. (1983). "Habitat suitability index models: Gulf of Mexico American oyster," FWS/OBS/-82/10.57,
U S. Department of the Interior Fish and Wildlife Service, Washington, DC.
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