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ERDC TN-DOER-E14
August 2001
CONCLUSION: Navigation dredging is common in coastal waters. Measured sound levels from
bucket dredging activities can exceed ambient levels out to considerable distances as was seen in
this study. Sounds produced from bucket dredging operations were quite variable, depending on
the phase of the operation. In this study the strongest sound was associated with the bucket striking
the channel bottom, although absolute sound levels were highly dependent on substrate type.
Dredging in coarse sediments produced the most intense sounds, whereas bottom contact in
unconsolidated mud emitted considerably less intense sound. The second strongest sound source
was the winch motor that pulled the loaded clamshell bucket back to the surface. This noise
exceeded the bucket striking the channel bottom event when dredging in soft sediment. The bucket
digging event produced noises at peaks similar to those generated by the winch motor, but only
when dredging in coarse sediment. In comparison with other dredging events, the bucket closing
event generally produced the least intense sounds. Additionally, sounds from this event were
sporadic and were not always audible. Of all events evaluated, noise produced from dumping
material into the hopper barge attenuated most rapidly with increasing distance from the sound
source. No audible sounds from this event were detected beyond 1,200 m.
When estimating the level of noise that may be introduced into a shallow coastal environment from
bucket dredging, consideration of sediment type may be very important. In general, considerably
less noise is generated when dredging in soft sediment. Maintenance dredging produced sounds
that extended outward only to 3,000 m in this study, and these were most audible for the bucket
striking the channel bottom. Many of the other events such as digging into the soft sediment were
audible at comparatively short distances from the sound source. Other factors that may be important
in bucket dredge sound production include size of the bucket (not directly evaluated herein) and
state of repair of the various types of equipment involved. Additional factors influencing received
noise levels include hydrodynamic conditions, notably prevailing suspended sediment loads and
sea state conditions, as well as skill of the dredge plant operator. With respect to the latter,
considerable sound variation was observed among repetitive dredge cycles due to variation in speed
of the winching operations, the position and orientation of the bucket relative to the water surface
when the downward plunge began, and the consequent angle at which the bucket impacted the
bottom.
These data should provide a better foundation for consideration of environmental concerns stem-
ming from underwater noise associated with bucket dredging operations. Sounds produced by
hydraulic hopper draghead dredges and hydraulic pipeline cutterhead dredges will be characterized
in ensuing notes.
ACKNOWLEDGMENTS: This underwater sound characterization study is a joint effort by the
U.S. Army Engineer District, Alaska, Anchorage, AK, and the U.S. Army Engineer Research and
Development Center, Vicksburg, MS, under the Dredging Operations and Environmental Research
(DOER) Program. The authors wish to express thanks to Mr. Guy McConnell, Planning Division,
Alaska District, for providing support for field efforts in 1999 and 2000. Manson Dredging
graciously provided vessel support and cooperated fully by adjusting their dredging operations to
satisfy field data collection requirements. Dr. Peter Scheifele of the National Undersea Research
Center at Avery Point, CT, provided helpful assistance with sound data analyses.
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