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thrusters, machinery noise (esp. the propulsion system), pumps, and propeller singing 14 . Manoeuvring,<br />

loading, hull design and operator’s behaviour also affect the amount of noise each vessel g<strong>en</strong>erates.<br />

Poor vessel maint<strong>en</strong>ance can increase the noise of a vessel: McK<strong>en</strong>na et al. (2<strong>01</strong>3) found that 10 % of all<br />

container ships transiting Santa Barbara Channel produced additional narrowband high frequ<strong>en</strong>cy tones:<br />

these are likely associated with propeller damage and/or onboard machinery requiring maint<strong>en</strong>ance.<br />

Shipping noise is broadband and can ext<strong>en</strong>d to greater than 100 kHz, but it is usually the lower<br />

frequ<strong>en</strong>cies that are of concern because they travel furthest. Although oft<strong>en</strong> not considered in<br />

describing large scale changes to the ambi<strong>en</strong>t noise <strong>en</strong>vironm<strong>en</strong>t in an area, small to medium size<br />

vessels, including coastal freighters, tugs, fishing vessels, pleasure craft, and whale-watching vessels,<br />

also contribute to the underwater soundscape.<br />

Table A7. Source spectral d<strong>en</strong>sities for differ<strong>en</strong>t types of commercial vessels underway, for several<br />

frequ<strong>en</strong>cies (from NRC 2003).<br />

@ 1 m)<br />

Source spectral d<strong>en</strong>sity (dB re 1 µPa 2 /Hz<br />

Ship Type L<strong>en</strong>gth Speed 10 Hz 25 Hz 50 Hz 100 300 Hz<br />

(m) (m/s)<br />

Hz<br />

Supertanker 244- 7.7-11.3 185 189 185 175 157<br />

355<br />

Large tanker 155- 7.7-9.3 175 179 176 166 149<br />

214<br />

Tanker 122- 6.2-8.2 167 171 169 159 143<br />

153<br />

Merchant 84-122 5.1-7.7 161 165 163 154 137<br />

Fishing 15-46 3.6-5.1 143 143 141 132 117<br />

Noise associated with construction and industrial activities is also a significant concern. Harbours can be<br />

particularly noisy, not just due to vessel traffic, but because of pile driving, dredging, and shipyard<br />

activities, amongst other sources. An additional and possibly significant but poorly docum<strong>en</strong>ted source<br />

of noise in harbours is nearshore land based machinery noise that propagates through the substrate into<br />

the marine <strong>en</strong>vironm<strong>en</strong>t (NRC, 2003).<br />

Pile driving noise is of concern both in air and in water because the sound <strong>en</strong>ergy of each pulse has a<br />

very fast rise time and high peak pressure, and the strikes are repeated for up to thousands of times per<br />

day. Driv<strong>en</strong> piles are used to support structures such as docks, bridges, wind turbines and navigational<br />

aids. The piles are driv<strong>en</strong> into the substrate using impact hammers, or alternatively, vibratory hammers<br />

or press-in piles. The amount of noise produced by driving piles dep<strong>en</strong>ds on the diameter of the pile,<br />

14 Propeller singing is audible to the human ear and typically ranges from 10-1,200 Hz but up to 12 kHz, and is due<br />

to the vortices associated with the trailing edge of the propeller as it turns. It is oft<strong>en</strong> mediated by notching the<br />

trailing edge of the propeller.<br />

82

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