Why haven’t marine vibrators been adopted for marine seismic surveying? In part, because of a general perception that their acoustic output is too low to yield useful images, and more importantly because there has been an unfavorable capital allocation to support development. Increased concern about the impacts of seismic noise warrants further research into their benefits.
There is a wealth of knowledge available on the physics of underwater acoustic noise, but sensational claims are often made about the potential physiological and behavioral effects of acoustic noise on marine animals at various ranges, magnitudes and duration. In reality, there has been no documented scientific evidence of noise from air guns used in geological and geophysical (G&G) seismic activities adversely affecting marine animal populations or coastal communities, and the only publications that describe physiological damage involved the deliberate firing of air guns in the immediate proximity of marine animals for sustained periods.
At the heart of all claimed impacts of traditional marine sources is the fact that air guns have an impulsive acoustic signature. The rise time between the ambient background noise level and the maximum acoustic amplitude is only a few milliseconds, 99% of the energy is typically released into the water in only about 30 milliseconds (0.03 seconds), and the maximum amplitude is comparable to or louder than the calls of large whales.
By comparison, the acoustic signature of marine vibrators has a continuous (or transient) nature: The rise time between the ambient background noise level and the maximum acoustic amplitude may be several seconds, the energy is emitted in a reasonably uniform manner over 5 to 30 seconds (or more), and the maximum amplitude may be significantly less than impulsive acoustic seismic sources. Furthermore, the acoustic amplitude emitted at frequencies above about 100 Hz will be substantially weaker by comparison to impulsive acoustic seismic sources.
The activity of seismic surveys in areas designated as environmentally sensitive is regulated by a series of established received sound metrics which include sound pressure level (SPL) and sound exposure level (SEL); together applicable to both impulsive (air gun) and transient (marine vibrator) acoustic noise types. Specific SPL and SEL thresholds are used to dictate how surveys may operate at various distances from either observed marine mammals, marine parks, commercial fisheries, and so on.
A comparison of SEL versus range is made in the figure below for a 3090 cubic inch array of Bolt LLXT air guns, a single 150 cubic inch eSource air gun (Type C setting), and a compact marine vibrator array. The SEL is computed by integrating the emitted energy over the entire duration of the modeled source signatures: 2 seconds for the air gun array and the eSource air gun, and 10 seconds for the marine vibrator array, and all plotted at a common depth of 30 meters below sea level. At 1000 m range the marine vibrator array SEL of 115 dB is 34 dB (98%) less than the air gun array SEL of 149 dB, and 6 dB (50%) less than the single eSource air gun SEL of 121 dB. At 3000 m range the marine vibrator array SEL of 96 dB is 35 dB (98.2%) less than the air gun array SEL of 131 dB, and 6 dB (50%) less than the single eSource air gun SEL of 102 dB (both acoustic wavefields decay equally with increasing range).
On face value, these are compelling numbers, but again it is noted that the air gun array has a short impulsive signal with negligible masking effects, and the marine vibrator array has a continuous signal with potential (albeit unproven) masking effects. Note that no auditory threshold filters for specific marine species have been applied to the modeled SEL values.