Harbour porpoises have a gestation period of 10 to 11 months 67 . Calves are seen betweenFebruary and September in UK waters, with a peak in June 68 .Due to the lack of markings that would allow recognition of individual animals (as is possible withmany other cetacean species), it is not presently known whether harbour porpoises display sitefidelity or have regular movement patterns between areas 69 . However, some researchers havereported resighting highly marked individuals over periods of time 70 which may indicate a degree ofsite fidelity. Genetic studies have demonstrated that female harbour porpoises disperse less thanmale harbour porpoises 71 and this may indicate that female harbour porpoises show site fidelity forthe places they calve and nurse their young, returning to preferred areas for these activities 72 .Important foraging habitat for harbour porpoises includes areas of strong tidal currents, usuallynear islands or headlands, where the currents combine with the seafloor topography and seem tocreate conditions where prey become aggregated 73 . At several places around the UK theselocations correspond with high porpoise densities.The patchy nature of survey effort makes it sometimes difficult to determine whether changes insightings rates are indications of seasonal movements or an artefact of the varying levels of searcheffort 74 . An additional issue is that the low profile and small size of the harbour porpoise make themconsiderably more challenging to see in poorer weather and higher seas 75 . Sightings rates thereforedecrease markedly as sea state increases and for this reason, harbour porpoises are likelyunderestimated in offshore areas and winter months when sea states tend to be higher. Difficultiesin sighting harbour porpoises, combined with the general situation of less research conducted awayfrom the coast and in winter due to the rougher seas and expense of working in such conditions, isa significant hindrance to gaining a more complete understanding of this species.Harbour porpoises are typically seen individually or in small groups of up to three animals.Occasionally large groups are sighted, usually associated with foraging. It is not presently known ifthere is a social or co-operative feeding element to these associations, as is the case with manyother cetaceans 76 .2267Jefferson et al, 200868Evans, 1992 (in Goodwin, 2007)69Pierpoint et al, 199870Ibid71Walton, 199772Baines and Earl, 199973Pierpoint et al, 2004; de Boer, 2006; Evans, 1997 (in Evans et al, 2003); Embling et al, 201074Reid et al, 200375Palka, 199676Goodwin, 2007
Although there is some variation in prey depending on area, season and age of the porpoise,dietary studies have found that sandeels (Ammodytes marinus) are the most important preyspecies for north east Atlantic harbour porpoises during the spring and summer, and whiting(Merlangius merlangus) in the autumn and winter months 77 . These will be supplemented withother fish such as herring (Clupea harengus), mackerel (Scomber scombrus) and gobies(Pomatoschistus sp.) throughout the year.Anatomical and genetic studies on harbour porpoises to elucidate population structure haveindicated that several populations and subpopulations exist in the North Atlantic. In UK waters,work suggests that genetically differentiated subpopulations exist in the Irish Sea/Wales and theNorth Sea, with some possible further divisions of the North Sea population 78 .Understanding population structure is important for conservation efforts. It is likely that the effectsof regional threats such as bycatch will be underestimated if animals are thought to be part of asingle, wider population but actually form discrete subpopulations 79 .See Annex II for summary tables with information from the individual papers used.West and south west ScotlandSeveral studies have shown west Scotland, and especially the Hebrides, to be of particularimportance to harbour porpoises 80 . The SCANS II survey which took place in July 2005, recordedone of the highest densities of harbour porpoises in the north east Atlantic for the Hebrides, at0.394 animals/km 2 (see Figure 4.5, p.22). Other density estimates produced in the region coveredtwo smaller areas, the Inner Hebrides and the Firth of Clyde (see Figure 4.7, below), again for thesummer months. A very high density estimate of 1.071 animals/km 2 was reported for the InnerHebrides, an area frequently reported to host concentrations of harbour porpoises 81 . The samestudy also recorded a high density of porpoises for the Firth of Clyde, 0.823 animals/km 2 . Thereare much less data available for the Firth of Clyde compared to the Inner Hebrides, but this highdensity estimate suggests it may also be of importance for harbour porpoises. High densities ofharbour porpoises during the summer, the time of year when these animals breed andproduce young, suggests these waters may be important for these functions. This shouldbe investigated further.77Santos and Pierce, 200378Anderson et al, 2001; Walton, 199779Anderson et al, 2001; Walton, 199780Including Evans and Wang, 2002; Northridge et al, 199581Pollock et al, 2000; Embling et al, 2010; Marubini et al, 2009; Evans and Wang, 200223
- Page 1 and 2: WDCS, the Whale and Dolphin Conserv
- Page 3 and 4: Towards Marine ProtectedAreas for C
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- Page 7 and 8: CONTENTSExecutive Summary 2Acknowle
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- Page 13 and 14: 2. IDENTIFYING MARINE PROTECTED ARE
- Page 15 and 16: 3. CRITICAL HABITATInterest in the
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6. IDENTIFYING CRITICAL HABITAT IN
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6.1.1 HARBOUR PORPOISEWest and sout
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Assessment: Critical HabitatHigh re
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11. Area: Off Land's End, Cornwall
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Threats, status and relative import
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East Scotland3. Area: North east Sc
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Threats, status and relative import
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6.1.4 COMMON MINKE WHALEWest and so
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6.1.5 WHITEBEAKED DOLPHINWest and s
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Coastal Wales2. Area: Bardsey Islan
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6.1.8 ATLANTIC WHITESIDED DOLPHINNo
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Other areasOne other area was asses
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6.1.11 BEAKED WHALESThe northern Ro
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7. PROTECTING CRITICAL HABITAT - RE
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considered in the area, each of whi
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7.4 EAST SCOTLANDWithin the east Sc
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7.5 SOUTH WEST ENGLANDWithin the so
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An SAC is already in place for bott
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7.9 SUMMARYFour areas of identified
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iv. Licensing processes for industr
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9. IDENTIFICATION AND PRIORITISATIO
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Recommendations on particular data
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Coastal Wales northern Pembrokeshir
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ANNEX II SPECIES ACCOUNTS SUMMARY
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HARBOUR PORPOISEEast ScotlandStudyH
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HARBOUR PORPOISESouth West EnglandS
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HARBOUR PORPOISECoastal WalesStudyT
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BOTTLENOSE DOLPHINStudyTemporalReso
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SHORTBEAKED COMMON DOLPHINStudyTemp
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SHORTBEAKED COMMON DOLPHINStudyTemp
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COMMON MINKE WHALEWest ScotlandStud
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WHITEBEAKED DOLPHINStudyTemporalRes
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KILLER WHALEStudyTemporalResolution
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ATLANTIC WHITESIDED DOLPHINStudyTem
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SPERM WHALEStudyTemporalResolutionS
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BALEEN WHALESStudyTemporalResolutio
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ANNEX III THREATS TO CETACEANS - RE
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Actual orPotential ThreatActivitySp
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North ScotlandSpecies of most relev
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East EnglandSpecies of most relevan
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South East EnglandSpecies of most r
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South West EnglandSpecies of most r
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Irish SeaSpecies of most relevance
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Actual orPotential ThreatActivitySp
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Bravington, M., Borchers, D. and No
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Evans, P.G.H. and Anderwald, P. 200
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ICES WGMME. 2006. Report of the Wor
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ECS/ASCOBANS/ACCOBAMS Workshop held
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marine protected areas effective to
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ISBN: 9781901386233