SCANS II (in July, 2005) estimated an abundance of 11,141 common dolphins and a density of0.056 animals/km 2 (CV 0.61) in the south west UK region 256 . This was a moderate level of densitycompared to other regions but spatial modelling to reveal finer-scale distribution predicted a highdensity area off south east Ireland and stretching over the southern end of the Celtic Deep 257 .The Celtic Deep − St. George's Channel region is an area particularly noted for high abundance ofcommon dolphins, from May to November 258 . Effort is low during winter and spring months but itappears that this cluster of high abundance disperses into the wider Celtic Sea during the laterautumn and winter. It has been suggested that the high summer abundance is a result of the CelticSea Front that persists in this area over the summer. Fronts are biologically productive areas thatresult in increased prey through enhanced local primary productivity and/or convergence processesthat act to aggregate prey 259 . From November to April, the waters in the Celtic Sea are mixed,but from May to November thermal stratification dominates and a surface front develops 260 thatcan be observed using satellite imagery 261 . As well as high encounter rates in the Celtic Deep −St. George's Channel area, studies have reported a high proportion of sightings of young animals.One study reported that between July and September, 51% of sightings consisted of groupsof adults with calves, often young calves, suggesting they were born recently, in or near thestudy area 262 .Although genetic differences within the population have not been detected, that part of thepopulation remains in on-shelf waters over the summer while another moves offshore, suggestingthat ecological differences exist. This has already been indicated by dietary studies whichinvestigated cadmium exposure in common dolphins and found different levels between animals inoffshore and nearshore waters 263 . These studies suggested the existence of two ecological stockswithin the north east Atlantic, a coastal and a neritic stock, that have accumulated different levelsof this element through the exploitation of different prey species 264 . Further research will benecessary to confirm the existence of at least two stocks of common dolphins, and todetermine if further divisions exist.Abundance of common dolphins increases in the south west England region during the wintermonths 265 , and their distribution mainly seems to be in offshore Celtic Sea waters and the western<strong>English</strong> Channel. Data are too sparse to know if there is a movement of animals into this area fromoff-shelf waters, or whether numbers remain high in offshore areas too. There are also insufficientdata to identify locations within the Celtic Sea with particular concentrations of animals. Moreinformation is available for the western <strong>English</strong> Channel, however, including a density estimate of0.74 individuals/km 2 for a small area south of Cornwall 266 . This is the only density estimate availablefor common dolphins in the winter in UK waters and shows there are high numbers of animals inthe region at this time of year. The survey area was small so it is unknown at present how much ofthe rest of the area has similarly high abundance of common dolphins. Little survey work hasbeen carried out here in the winter but other studies have also shown a high relative abundanceof common dolphins in much of the western Channel area 267 , some reporting a 10-fold increaseover summer numbers 268 . Large aggregations of prey species are in the region at this time of year,such as sprat, horse mackerel and herring, and are likely the reason for the high abundance ofcommon dolphins 269 .38256SCANS II, 2006257Ibid258Reid et al, 2003; Baines and Evans, 2009; Earl et al, 2004; Earl et al, 2005259Bost et al, 2009 ; Hyrenbach et al, 2000260Brown et al, 2003261see for example, Goold et al, 1998 (abstract only seen)262Earl et al, 2004 and 2005263Lahaye et al, 2005264Lahaye et al, 2005265Northridge and Kingston, 2009266De Boer et al, 2008267Reid et al, 2003; MacLeod et al, 2009; De Boer and Simmonds, 2003268Brereton et al, 2005269Northridge and Kingston, 2009
4.4.4 COMMON MINKE WHALE (Balaenoptera acutorostrata)Minke whale sightings are frequent and widespread from May to October in UK waters. The generalpattern appears to be an increased use of coastal areas as the season progresses, peaking July toSeptember when large feeding aggregations can be observed in coastal waters 270 . Outside thesemonths sightings are fewer and little is known about their winter distribution. Some individuals atleast remain close to the UK and Ireland 271 but for the majority, it is unclear if they undergo alatitudinal migration or simply move further offshore for the winter months. In some locations aroundthe UK at least, photo-ID studies have found individuals to be resident seasonally 272 , or possiblyyear round 273 .Sandeels, herring and sprat (Sprattus sprattus) have been noted as principal prey items of minkewhales in British waters 274 but other fish species, such as mackerel, cod and capelin (Mallotusvillosus), are also eaten 275 . Minke whale distribution and abundance during the summer feedingseason, partly spent in UK waters, ultimately depends on prey distribution and abundance 276 .Minke whales are often noted feeding in association with seabirds, including kittiwakes, gullsand shearwaters 277 .The first SCANS survey of 1994 produced an estimate of 8,445 (95% CI = 4,987-13,546; CV =0.24) for minke whales in the North Sea. SCANS II (in July, 2005) resulted in an estimate of 10,541(CV = 0.32) for the same area but this difference was not significant 278 . The CODA offshorecetacean survey produced an estimated abundance of 6,765 (95% CI = 1,239-36,925; CV = 0.99)for minke whales, with sightings restricted to the northern blocks of the survey area, in UK andIrish offshore waters. Figures 4.17 (below), 4.19 (p.40) and 4.21 (p.41) display density estimatesproduced by SCANS, SCANS II and CODA respectively. Figures 4.18 (below) and 4.20 (p.40) showthe estimated density surfaces produced using SCANS and SCANS II data 279 .270Evans et al, 2003; Northridge et al, 1995; Reid et al, 2003; Macleod et al, 2007271Anderwald and Evans, 2007; Gill et al, 2000272Gill et al, 2000273MacLeod et al, 2004274Pierce et al, 2004; Macleod et al, 2004; Anderwald and Evans, 2007275Reid et al, 2003; Anderwald and Evans, 2007276MacLeod et al, 2004;277Robinson and Tetley, 2007; Skov et al, 1995; Reid et al, 2003278SCANS II, 2006279Reproduced with permission. SCANS II, 2006. Please note that density surface maps show estimated densityderived from a spatial model and should not be overinterpreted, particularly at a fine spatial scale.39
- Page 1 and 2: WDCS, the Whale and Dolphin Conserv
- Page 3 and 4: Towards Marine ProtectedAreas for C
- Page 5 and 6: South west EnglandCeltic Deep - com
- Page 7 and 8: CONTENTSExecutive Summary 2Acknowle
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- Page 39: South west EnglandBased on observat
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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