acoustic measurements have been made on a few str<strong>and</strong>ed or rehabilitated cetaceans (Ridgeway<strong>and</strong> Carder 2001).Caution should be encouraged in the use <strong>of</strong> captive or str<strong>and</strong>ed (<strong>and</strong> therefore compromised)animals to obtain data.7.2.5. S<strong>of</strong>tware modelsComputational models <strong>of</strong> whale auditory sensitivities, such as the humpback whale hearingmodel (Helweg et al. 2000) may be <strong>of</strong> assistance in determining cetacean sensitivity to sound.S<strong>of</strong>tware models to estimate the potential effects <strong>of</strong> <strong>noise</strong> impacts have proved valuable for whalewatching (Erbe <strong>and</strong> Farmer 2000).A spatial model <strong>of</strong> collision risk has been developed (Tregenza et al. 2000). This model hasidentified that mitigation procedures are urgently required. For example, the model indicates thata population <strong>of</strong> short finned pilot whales <strong>of</strong>f the Canary Isl<strong>and</strong>s is at risk <strong>of</strong> extinction fromcollisions, unless consistent <strong>and</strong> effective mitigation action is carried out.Autopsied animals, <strong>and</strong> computational studies that do not require the use <strong>of</strong> trained or wildcetaceans, should be used wherever possible to obtain auditory data. Correlational studies, such ascorrelations <strong>of</strong> str<strong>and</strong>ings with increases in <strong>noise</strong> levels or military manoeuvres, are generallypreferred to experimental ones (Whitehead <strong>and</strong> Weilgart 2001).7.3. Long-term impactsHESS (1997) stated that behavioural effects <strong>of</strong> concern related to feeding, social behaviour,migration, avoidance <strong>and</strong> ab<strong>and</strong>onment <strong>of</strong> critical habitat. Changes in these behaviours could have aneffect that could impact a population over the longer term. It generally remains difficult to detectthese changes <strong>and</strong> therefore designation <strong>of</strong> certain critical areas as sacrosanct is urgently required.Unlike l<strong>and</strong>-based critical habitat, marine critical habitat is likely to be less fixed. Thus, it may benecessary to adjust the boundaries or zones over time as, for example, cetacean distributions changewith oceanic conditions. With larger overall protection areas, it can be easier to adjust or move theboundaries <strong>of</strong> the core reserve or critical habitat zones. One precautionary tool is the marineprotected area, where core components <strong>of</strong> highly protected areas should ideally be nested within anetwork <strong>of</strong> multi-zone areas.There has been an increase in the number <strong>of</strong> forums held specifically for discussion <strong>of</strong> <strong>noise</strong>impacts to cetaceans <strong>and</strong> suitable mitigation procedures in recent years. The majority <strong>of</strong> theseforums have been focused on activities that propagate over large ocean areas, for example,seismic activities (see HESS 1997; etc) <strong>and</strong> even outside the dominion <strong>of</strong> national EEZs, as is thecase for some military activities (see Gisiner 1998). Other forums have looked more generally atthe issue <strong>of</strong> <strong>noise</strong> pollution <strong>and</strong> cetaceans (see, for example, NZ 1996; JASA 2001; 2000).7.4. Cumulative impactsThe cumulative impacts <strong>of</strong> <strong>noise</strong> pollution should be considered alongside individual mitigationmeasures for a particular activity, or part <strong>of</strong> that activity. For example, there are <strong>of</strong>ten rules forwhale watch vessels, limiting the number <strong>of</strong> vessels at one time, <strong>and</strong> designating a larger distance<strong>of</strong> protection around the animals as the number <strong>of</strong> vessels increases (see Annex 2A for anexample <strong>of</strong> detailed whale watching guidelines).71
Noise pollution also needs to be considered in synergy with other factors, such as chemicalpollution <strong>and</strong> habitat degradation, that can also be expected to impact cetaceans. <strong>Conservation</strong>management that considers cumulative <strong>and</strong> synergistic impacts over large habitat areas (includingnational jurisdictions, as well as the high seas, where appropriate) would seem to be the wayforward.The cumulative impacts <strong>of</strong> some forms <strong>of</strong> <strong>noise</strong> pollution have been considered through a process<strong>of</strong> Strategic Environmental Assessment (SEA). This approach requires consideration <strong>of</strong> allecosystem threats, considering individual impacts in unison rather than discretely. Such a processcan make recommendations that lead to further scientific underst<strong>and</strong>ing, monitoring <strong>of</strong>environmental effects <strong>and</strong> review <strong>and</strong> assessment <strong>of</strong> the cumulative effects. For example, the UKSEA policy document makes specific reference to study behavioural responses <strong>of</strong> marinemammals to seismic <strong>noise</strong> (DTI 2001).The cumulative or synergistic effects <strong>of</strong> all such stresses can be expected to further affectindividual viability, through a reduction in calving rates, avoidance <strong>of</strong> critical habitat <strong>and</strong> othersuch impacts that may lead to increases in mortality.A range <strong>of</strong> literature has been produced that include potential mitigation procedures for variousforms <strong>of</strong> <strong>noise</strong> pollution. Richardson (2000) has produced a document listing needed researchconcerning airgun effects on marine mammals (also see Moscrop <strong>and</strong> Swift 1999; Hess 1997).Aburto et al. (1997) make recommendations for further research, with particular reference toactive sonar military operations, <strong>and</strong> Vella et al. (2001) for wind farms. Ketten (1998) suggestsmitigation <strong>and</strong> research needs for fisheries acoustic devices <strong>and</strong> Kastelein et al. (2000) forpingers. Erbe (2001) presents future research suggestions for whale watching vessels.A more generic list to develop an underst<strong>and</strong>ing <strong>of</strong> the effects <strong>of</strong> sound on marine mammals hasbeen identified in National Research Council (2000) (relating to low frequency sound) <strong>and</strong> byRichardson et al. (1995), Richardson <strong>and</strong> Wursig (1997) <strong>and</strong> Richardson (1997).7.5. CommunicationThe International Whaling Commission (IWC) recognised that anthropogenic <strong>noise</strong> is a complexsubject <strong>and</strong> that scientific study on this issue involves the integration <strong>of</strong> a broad range <strong>of</strong>disciplines including acoustics, audiology, physiology, behaviour, behavioural ecology, ecology,oceanography, <strong>and</strong> population biology (IWC 1999).Research will be most useful if it is independent <strong>and</strong> non-aligned, co-ordinated <strong>and</strong> committed toimproving environmental legislation. Better access to data would help in monitoring long-termeffects <strong>and</strong> in planning mitigation (Gisiner 1998). St<strong>and</strong>ardisation <strong>of</strong> field procedures <strong>and</strong> dataformats should be encouraged where feasible (Gisiner 1998).It might be useful to convene an independent legislative panel consisting <strong>of</strong> relevant internationalscientists to continually review the mitigation procedures that are put in place for major forms <strong>of</strong><strong>noise</strong> pollution. Such a panel was recommended by Moscrop <strong>and</strong> Swift (1999) in connection withlicensing <strong>of</strong> the oil <strong>and</strong> gas industry. This may <strong>of</strong>fer a practical solution to ongoing issuesinvolved in mitigation, including future decision-making processes such as the nature <strong>of</strong> thenecessary format for collected data <strong>and</strong> details <strong>of</strong> a st<strong>and</strong>ardised training protocol for observers.This panel could be responsible for prioritising research needs <strong>and</strong> guiding national <strong>and</strong>international regulation.72
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its propagation beyond those declar
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2.1.2. Measuring sound intensityIde
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In the EEZ, in comparison to the te
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Appendix A - Some international ins
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Convention for the Protection of th
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Available at:http://www.unep.ch/sea
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BucharestConventionArticle XIPollut
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environment1. The Contracting Parti
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e) no sudden or repeated change in
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Ref: Nowacek et al. 2001.Location:
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Location: Arctic• Vocal behaviour
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• Vaquita surfacing duration and
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• 6% of small delphinids (n=264;
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Species type: Boto, Inia geoffrensi
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• There was no evidence of minke
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• Northern right whales may be ap
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to Ensenada De La Paz, Mexico. Aqua
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distribution of humpback whales, Me
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Richardson, C.R. Greene, C.I. Malme
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Zhou, K., Pilleri, G. and Li, Y. 19
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6. surveys for Cuvier’s beaked wh