Scottish Marine and Freshwater Science Volume 5 Number 9: Strategic Surveys of Seabirds off the West Coast of Lewis to Determine Use of Seaspace in Areas of Potential Marine Renewable Energy Developments
By 2020 the percentage of Scotland‟s energy coming from renewable sources will increase. Studies have identified that there is a need to research how offshore renewable developments affect wildlife populations. The surveys presented here will help to find
Appendix II. Tables
Table 2 - Summary of shore point counts undertaken to compliment aerial surveys along the NW coast (Butt of Lewis southwest to Great Berneray). A tick symbol indicates that a count was undertaken. The Shader shore point was counted from grid ref NB37912/55211 on the April survey (*). The SHA and MEL shore points were counted on the day before that shown for May and September. 'dis' indicates that surveys were discontinued due to the poor view of the sea from that shore point. 'n.c.' indicates that no count was made, either due to unsuitable sea conditions (summer) or time constraints due to day length (winter). Note the June aerial survey was cancelled. Map IDs relate to locations on Figure 1
Map ID | Shore Point Name | Code | Grid reference | 19 Apr 2012 |
02 May 2012 |
18 Jun 2012 |
26 Jul 2012 |
22 Sep 2012 |
16 Dec 2012 |
02 Feb 2013 |
---|---|---|---|---|---|---|---|---|---|---|
1 | Dalbeg | DAL | 22508 45887 | dis. | dis. | dis. | dis. | dis. | dis. | |
2 | South Shawbost | SSH | 23991 47372 | n.c. | n.c. | n.c. | ||||
3 | North Shawbost | NSH | 25797 48282 | n.c. | ||||||
4 | Bragar | BRA | 28971 49230 | |||||||
5 | Brue | BRU | 33311 50751 | dis. | dis. | dis. | dis. | dis. | dis. | |
6*&7 | Shader | SHA | 38748 55663* | n.c. | n.c. | n.c. | ||||
8 | Melbost | MEL | 40974 57811 | |||||||
9 | South Galston | SGA | 43631 59411 | n.c. | n.c. | |||||
10 | Aird Dell | AIR | 47192 61950 | |||||||
11 | Swainbost | SWA | 50973 64320 | |||||||
12 | Butt of Lewis West | BLW | 51367 66366 | n.c. | n.c. | |||||
13 | Butt of Lewis East | BLE | 52195 66265 | |||||||
14 | Port of Ness | PON | 54198 64050 |
Shore points with restricted views or poor elevation were given lower priority; counts were completed at these only if there was sufficient time on the survey day. Note the June aerial survey was cancelled. The Upper Shader shore point used on the April survey was subsequently dropped in favour of the nearby LWA vantage point. On most occasions the LWA VPs were counted either the day before or day after the date shown.
Table 3 - Names and grid references of Loch Roag vantage point locations. Map IDs relate to locations on Figure 1
Map ID | Shore Vantage Point Name | VP easting | VP northing |
---|---|---|---|
LR01 | Cliobh | 108673 | 936531 |
LR02 | Bhaltos | 109956 | 936597 |
LR03 | Miabhaig | 109319 | 934039 |
LR04 | Geisiadar | 111922 | 932395 |
LR05 | Einacleit | 112177 | 928337 |
LR06 | Giosla | 113418 | 925038 |
LR07 | Bernera bridge | 116496 | 934249 |
LR08 | Sruth Iarsiadair | 116055 | 934265 |
LR09 | Tobson | 113491 | 938215 |
LR10 | Crothair | 115922 | 939402 |
LR11 | Circebost/Totarol | 118941 | 934339 |
LR12 | Lundal | 118601 | 932677 |
LR13 | Linsiadar | 121169 | 931135 |
LR14 | Beinn Hulabhig | 122586 | 929821 |
LR15 | Tolsta Chaolais | 118944 | 938238 |
LR16 | Breasecleit /Pier | 120692 | 935973 |
LR17 | Callinish Pier | 121300 | 932600 |
LR18 | Garynahire Bridge | 123400 | 931400 |
LR19 | Carishader | 109800 | 933400 |
LR20 | Bosta E | 114500 | 940250 |
LR21 | Bosta W | 113800 | 940400 |
LR22 | Borrowston | 119000 | 942400 |
LR23 | Valasay | 114800 | 936100 |
LR24 | Barraglom | 117700 | 934500 |
LR25 | Hacklete | 114500 | 934800 |
LR26 | Breaclete | 116100 | 937700 |
LR27 | Dubh Thob | 118300 | 935900 |
Table 4 - Species included in species groups
Species group | Species included | Comments |
---|---|---|
Auk species | Guillemot, Razorbill, Puffin, Little Auk, Black Guillemot | Used when features are not available to allow further identification to a smaller class or species |
Large Auk | Guillemot, Razorbill | Used when Puffin/Little Auk can be excluded on size and Black Guillemot on plumage |
Small Auk | Puffin, Little Auk | Used when the bird is definitely an auk smaller than Guillemot or Razorbill but further features are not clearly defined |
Auk / small gull | Guillemot, Razorbill, Puffin, Little Auk, Black Guillemot, Kittiwake, Black-headed Gull, Common Gull, Little Gull | Usually used when poor contrast makes apparently white objects unreliable |
Gull species | Kittiwake, Black-headed Gull, Common Gull, Little Gull, Great Black-backed Gull, Lesser Black-backed Gull, Herring Gull, plus rarer gulls, such as Glaucous Gull and Iceland Gull | Used for gulls when size and other features do not allow identification to a smaller class or species. In some cases some species falling into this category could be excluded, however, it would be impractical to create species groups for all eventualities |
Small gull species | Kittiwake, Black-headed Gull, Common Gull, Little Gull | Usually used for small gulls sitting on the water when other identification features are not obvious |
Small Gull (excluding Little) | Kittiwake, Black-headed Gull, Common Gull | Introduced because Little Gull can frequently be excluded on size alone |
Large gull species | Great Black-backed Gull, Lesser Black-backed Gull, Herring Gull, Glaucous Gull, Iceland Gull | Often used for sitting immature birds where plumage is less diagnostic, or for images where contrast makes colour unreliable |
Pale Gull | Kittiwake, Black-headed Gull, Common Gull, Herring Gull, Glaucous Gull, Iceland Gull | Used when mantle colour but not size can be distinguished in adult birds, most often loafing on sand or rocks where size is less obvious due to the oblique angle |
Large Gull Including Common | Common Gull, Great Black-backed Gull, Lesser Black-backed Gull, Herring Gull, Glaucous Gull, Iceland Gull | Primarily used for immature birds, where aspect or contrast prevents further identification |
Kittiwake / Common Gull | Kittiwake, Common Gull | |
Grey gull species (Herring or Common) | Herring Gull, Common Gull | |
Black-backed gull species | Great Black-backed Gull, Lesser Black-backed Gull | |
Fulmar / gull species | Fulmar, Kittiwake, Black-headed Gull, Common Gull, Little Gull, Great Black-backed Gull, Lesser Black-backed Gull, Herring Gull, Glaucous Gull, Iceland Gull | Used almost exclusively for sat birds, often when contrast obscures darker plumage |
Fulmar / Small Gull (excluding Little Gull) | Fulmar, Kittiwake, Black-headed Gull, Common Gull, Great Black-backed Gull, Lesser Black-backed Gull, Herring Gull, Glaucous Gull, Iceland Gull | Little Gull can be excluded on size alone in cases where Fulmar cannot be excluded |
Big Bird | All bird species larger than 48cm in length (minimum length in range provided for Lesser Black-backed Gull in Collins Bird Guide 2nd edition) | Predominately used as the species group category where Gannet has been identified at the species level. Very rarely used when extreme conditions obscure most or all identifying features apart from size. For example direct sunlight can very occasionally cause sat Eider and Gannet to be indistinguishable. In most cases many species falling into this category could be excluded however it would be impractical to create species groups for all eventualities. |
Small Bird | All bird species smaller than 48cm in length (minimum length in range provided for Lesser Black-backed Gull in Collins Bird Guide 2nd edition) | Occasionally groups of terrestrial birds will cross over survey areas and it may not be possible to discern whether these are, for example, a migratory passerine species or a small wader species. Although many other species falling into this category could be excluded it would be impractical to create species groups for all eventualities given their very rare occurrence and, arguably, irrelevance to these surveys |
Diver species | Red-throated Diver, Black-throated Diver, Great Northern Diver, White-billed Diver | |
Large Auk / Throated Diver | Razorbill, Guillemot, Red-throated Diver, Black-throated Diver | During winter months when both divers and the larger auk species have white faces, it can occasionally be difficult to distinguish them |
Duck species | Common Scoter, Surf Scoter, Velvet Scoter, Eider, Wigeon, Gadwall, Teal, Mallard, Pintail, Shoveler, Pochard, Tufted Duck, Scaup, Shelduck, Long-tailed Duck, Goldeneye, Smew, Red-breasted Merganser, Goosander | Used as the species group where a duck species has been identified and when a lack of features makes further identification impossible. Often in large flocks. Although species falling into this category could often be excluded it would be impractical to create species groups for all eventualities when a species cannot be identified |
Grebe species | Great Crested Grebe, Red-necked Grebe, Slavonian Grebe, Black-necked Grebe, Little Grebe | The smaller or larger grebe species can almost always be excluded, however, they are usually identified to species anyway and encountered so rarely that more specific species groups have so far been unnecessary |
Shearwater species | Manx Shearwater, Balearic Shearwater, Sooty Shearwater, Cory's Shearwater, Great Shearwater | |
Large Shearwater | Sooty Shearwater, Cory's Shearwater, Great Shearwater | Used when plumage details are indiscernible but size is apparent |
Small Shearwater | Manx Shearwater, Balearic Shearwater | Used when larger species can be excluded but survey area and visible plumage mean that Balearic Shearwater cannot be ruled out |
Shearwater species / auk species | Manx Shearwater, Balearic Shearwater, Sooty Shearwater, Cory's Shearwater, Great Shearwater, Guillemot, Razorbill, Puffin, Black Guillemot, Little Auk | Generally assumed to apply only to Manx Shearwater and Guillemot, Razorbill and Puffin |
Tern species | Arctic Tern, Common Tern, Little Tern, Sandwich Tern, Roseate Tern, Black Tern | |
Arctic / Common Tern | Arctic Tern, Common Tern | The two species are very similar and extremely difficult to separate |
Tern (Excluding Little) | Arctic Tern, Common Tern, Sandwich Tern, Roseate Tern, Black Tern | Used when the tern is larger than a small tern however can't be identified further |
Tern / small gull | Arctic Tern, Common Tern, Sandwich Tern, Roseate Tern, Black Tern, Kittiwake, Black-headed Gull, Common Gull, Little Gull | Used in certain conditions or angles where small gulls (especially little gulls) can look similar |
Skua species | Great Skua , Arctic Skua, Pomarine Skua, Long-tailed Skua | |
Skua (Excluding Great) | Arctic Skua, Pomarine Skua, Long-tailed Skua | Used for the smaller skua species that are clearly not Great Skua |
Cormorant / Shag | Cormorant, Shag | Can be very difficult to separate. Usually easier in flight |
Unidentified storm-petrel | British Storm-Petrel, Leach's Storm Petrel | Used as the two species are very small and superficially similar |
Large wader species | Curlew, Whimbrel, Black & Bar-tailed Godwit | Waders godwit sized in length or larger |
Medium wader species | Redshank, Spotted Redshank, Woodcock, Snipe, Lapwing etc. | Waders between a Redshank and a godwit in length |
Small wader species | Dunlin, Knot, Sanderling, Turnstone, sandpipers, stints, phalaropes, smaller plovers etc | Anything smaller than a Redshank |
Wader species | If size is difficult to establish | |
Passerine species | Mainly used for small passerines. Clearly identified as not a small seabird or wader. Usually small often brown migrating passerines. | |
Swan species | Mute Swan, Bewick's Swan, Whooper Swan | |
Goose species | Canada Goose, Greylag Goose, Bean Goose, Pink-footed Goose, White-fronted Goose, Snow Goose, Barnacle Goose | |
Dabbling ducks | Wigeon, Gadwall, Teal, Mallard, Pintail, Shoveler, Pochard, Shelduck | Only used on Inshore areas such as lakes, ponds and rivers |
Seal species | Grey Seal, Harbour Seal | |
Dolphin species | Bottlenose Dolphin, Common Dolphin, White-beaked Dolphin, White-sided Dolphin, Risso's Dolphin | Although Orca (Killer Whales) are dolphins they would come under Large Cetacean species |
Small cetacean species | Harbour Porpoise, dolphin Sp. | Includes Harbour Porpoise and all the dolphin species not including Orca (Killer Whale) |
Large cetacean species | Long-finned Pilot whale, Minke Whale, etc, Orca | Any whale species and Orca. |
Cetacean species | Sometimes used when size is difficult to judge e.g. Submerged animals, but cetacean features can be identified | |
Shark species | Basking Shark, Blue Shark, Porbeagle, etc. | Used for any shark sighting |
Small cetacean / seal species | Harbour Porpoise, dolphin Sp, Harbour Seal, Grey Seal | Used when features to define either a seal or a small cetacean ( e.g. Fluke or flippers) are not visible. This may occur in submerged animals |
Cetacean species / seal species / shark species | Cetacean sp., seal sp., shark species | Used when the object is not clear e.g. Adverse weather conditions or submerged or turbid underwater conditions |
Jellyfish | Species not usually recorded | |
Turtle species | Leatherback turtle | Mainly the leatherback turtle occurs in the UK during the summer however odd sightings and standings of other species have been recorded, so these will be recorded where identified |
No ID | Used very rarely in adverse weather conditions when features cannot be used to identify objects to any one animal class |
Table 5 Species recorded from digital aerial surveys from April to July 2012
Species | April | May | June | July | Sept | Dec | Feb |
---|---|---|---|---|---|---|---|
Arctic / Common Tern | 3 | 3 | 2 | ||||
Auk / Small Gull | 15 | 9 | 5 | ||||
auk species | 65 | 40 | 78 | 30 | 24 | 82 | 156 |
Basking Shark | 1 | 1 | 5 | ||||
Big Bird | 1 | 1 | |||||
Black Guillemot | 2 | ||||||
black-backed gull species | 1 | 33 | 1 | ||||
Black-headed Gull | 4 | 1 | 1 | ||||
Cetacean/Seal/Shark species | 1 | ||||||
Common Dolphin | 2 | ||||||
Common Gull | 16 | 2 | 1 | 3 | |||
Common Scoter | 2 | 2 | |||||
Cormorant | 2 | 1 | |||||
Cormorant/Shag species | 1 | ||||||
diver species | 6 | 1 | 2 | 26 | 3 | ||
duck species | 2 | 3 | 1 | 16 | |||
Eider | 2 | 25 | 12 | 13 | |||
Fulmar | 318 | 84 | 105 | 114 | 28 | 133 | 186 |
Fulmar / gull species | 80 | 5 | 25 | 6 | 2 | 11 | 27 |
Fulmar / Small Gull (excluding Little Gull) | 46 | 1 | 1 | 1 | |||
Gannet | 44 | 91 | 69 | 199 | 247 | 2 | 5 |
Great Black-backed Gull | 1 | 1 | 1 | 1 | 2 | 11 | |
Great Northern Diver | 1 | ||||||
Great Skua | 4 | 1 | |||||
grey gull species (Herring or Common) | 1 | ||||||
Grey Seal | 2 | 1 | 2 | ||||
Greylag Goose | 2 | 10 | 3 | 16 | 122 | 1 | 5 |
Guillemot | 35 | 1 | 3 | 13 | 11 | 2 | 1 |
gull species | 3 | 1 | 1 | 1 | 1 | 27 | 8 |
Harbour Porpoise | 6 | 15 | 5 | 2 | 2 | 1 | |
Herring Gull | 2 | 3 | 7 | 2 | 2 | 6 | 14 |
Iceland Gull | 1 | ||||||
Kittiwake | 30 | 2 | 9 | 8 | 4 | 22 | 121 |
Large Auk | 88 | 12 | 81 | 63 | 28 | 6 | 13 |
Large Auk / Throated Diver | 2 | 1 | |||||
large gull (including Common) | 1 | ||||||
large gull species | 1 | 3 | 17 | 5 | |||
Lesser black-backed Gull | 1 | 1 | 3 | 2 | 9 | 1 | |
Minke Whale | 1 | ||||||
Oystercatcher | 1 | ||||||
Puffin | 10 | 22 | 32 | 15 | 1 | 2 | 5 |
Razorbill | 6 | 4 | 3 | ||||
Red-throated Diver | 2 | 1 | 3 | 1 | |||
Risso's Dolphin | 4 | ||||||
seal species | 1 | 5 | 2 | 3 | |||
Shag | 1 | 1 | 1 | ||||
shearwater species | 1 | ||||||
shearwater species / auk species | 1 | ||||||
skua species | 1 | ||||||
Small Auk | 7 | 1 | 2 | 3 | 2 | ||
Small Bird | 17 | 3 | 6 | 14 | 1 | ||
Small Cetecean / Seal Species | 1 | ||||||
Small Gull (Excluding Little) | 2 | 1 | |||||
small gull species | 1 | 1 | 3 | 3 | |||
small wader species | 1 | 1 | |||||
Tern (excluding little) | 7 | ||||||
Tern / Small Gull | 1 | 1 | |||||
tern species | 15 | 6 | 3 | ||||
Unidentified storm-petrel | 3 | 15 | |||||
wader species | 5 | 4 | |||||
White-beaked Dolphin | 4 | 3 | |||||
Total | 803 | 347 | 516 | 541 | 507 | 412 | 590 |
Table 6 - Estimates of bird species abundance in the study area. Values with coefficients of variation (% CVs) and lower and upper confidence intervals were estimated through design based analysis of encounter rate corrected for survey effort. 1Where only one observation was recorded this was just multiplied by 10 to correct for 10% survey coverage. Individual diver and auk species abundances were also estimated using proportions of records that were identified to species in each survey 2
Species/ Group | April | May | June | July | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
N(% CV) | LCI | UCI | N(% CV) | LCI | UCI | N(% CV) | LCI | UCI | N(% CV) | LCI | UCI | |
Eider | 20(106) | 3 | 117 | 244(70) | 68 | 879 | 117(101) | 21 | 642 | 0 | - | - |
Common Scoter | 0 | - | - | 0 | - | - | 20(106) | 3 | 116 | 0 | - | - |
diver species | 69(48) | 28 | 174 | 0 | - | - | 29(79) | 7 | 121 | 10 1 | - | - |
Red-throated Diver 2 | 0 | - | - | 0 | - | - | 29 | - | - | 10 | - | - |
Great Northern Diver 2 | 69 | - | - | 0 | - | - | 0 | - | - | 0 | - | - |
Fulmar | 3161(26) | 1887 | 5294 | 819(35) | 408 | 1645 | 1024(35) | 513 | 2046 | 1108(14) | 836 | 1469 |
Gannet | 426(32) | 225 | 805 | 888(18) | 620 | 1271 | 673(17) | 481 | 941 | 1935(10) | 1588 | 2358 |
Cormorant | 0 | - | - | 20(78) | 5 | 84 | 0 | - | - | 0 | - | - |
Shag | 0 | - | - | 10 1 | - | - | 0 | - | - | 10 1 | - | - |
Great Skua | 40(66) | 12 | 134 | 0 | - | - | 0 | - | - | 10 1 | - | - |
Kittiwake | 297(35) | 148 | 596 | 20(105) | 3 | 115 | 88(49) | 34 | 225 | 78(44) | 33 | 181 |
Black-headed Gull | 0 | - | - | 0 | - | - | 39(83) | 9 | 169 | 0 | - | - |
Common Gull | 0 | - | - | 156(49) | 61 | 399 | 20(78) | 5 | 84 | 10 1 | - | - |
Lesser Black-backed Gull | 10 1 | - | - | 0 | - | - | 10 1 | - | - | 29(63) | 9 | 96 |
Herring Gull | 20(106) | 3 | 117 | 29(63) | 9 | 96 | 68(44) | 29 | 159 | 19(78) | 5 | 83 |
Great Black-backed Gull | 0 | - | - | 10 1 | - | - | 10 1 | - | - | 10 1 | - | - |
all auks | 2051(22) | 1312 | 3205 | 741(25) | 446 | 1234 | 1912(19) | 1314 | 2783 | 1264(15) | 934 | 1711 |
auk sp | 674(22) | 431 | 1054 | 390(28) | 222 | 684 | 1073(20) | 712 | 1618 | 418(21) | 272 | 643 |
large auk sp | 1258(24) | 777 | 2039 | 127(36) | 63 | 256 | 819(20) | 543 | 1236 | 778(17) | 548 | 1105 |
small auk sp | 119(71) | 32 | 435 | 224(38) | 106 | 473 | 20(106) | 3 | 116 | 68(56) | 24 | 197 |
Guillemot 2 | 1536 | - | - | 144 | - | - | 911 | - | - | 755 | - | - |
Razorbill 2 | 263 | - | - | 0 | - | - | 0 | - | - | 232 | - | - |
Black Guillemot 2 | 0 | - | - | 0 | - | - | 0 | - | - | 25 | - | - |
Puffin 2 | 251 | - | - | 597 | - | - | 1001 | - | - | 244 | - | - |
Species/ Group | September | December | February (2013) | ||||||
---|---|---|---|---|---|---|---|---|---|
N(% CV) | LCI | UCI | N(% CV) | LCI | UCI | N(% CV) | LCI | UCI | |
Eider | 0 | - | - | 0 | - | - | 130(97) | 25 | 672 |
Common Scoter | 0 | - | - | 0 | - | - | 20(123) | 2 | 181 |
diver species | 50(79) | 12 | 209 | 269(91) | 56 | 1299 | 30(94) | 5 | 169 |
Red-throated Diver | 30(0.8) | 6 | 158 | 0 | - | - | 0 | - | - |
Red-throated Diver 2 | 50 | - | - | 0 | - | - | 0 | - | - |
Great Northern Diver 2 | 0 | - | - | 0 | - | - | 0 | - | - |
Fulmar | 279(42) | 123 | 634 | 1324(33) | 688 | 2548 | 1853(43) | 799 | 4296 |
Gannet | 2464(13) | 1886 | 3219 | 20(99) | 2 | 210 | 50(68) | 14 | 182 |
Cormorant | 0 | - | - | 0 | - | - | 0 | - | - |
Shag | 0 | - | - | 0 | - | - | 0 | - | - |
Great Skua | 0 | - | - | 0 | - | - | 0 | - | - |
Kittiwake | 40(78) | 9 | 173 | 219(38) | 105 | 456 | 1206(24) | 744 | 1953 |
Black-headed Gull | 0 | - | - | 0 | - | - | 0 | - | - |
Common Gull | 30(94) | 5 | 169 | 0 | - | - | 0 | - | - |
Lesser Black-backed Gull | 20(99) | 2 | 212 | 90(85) | 20 | 399 | 0 | - | - |
Herring Gull | 20(99) | 2 | 211 | 60(60) | 19 | 191 | 139(46) | 57 | 339 |
Great Black-backed Gull | 0 | - | - | 20(99) | 2 | 211 | 110(44) | 47 | 256 |
all auks | 668(23) | 428 | 1043 | 916(21) | 603 | 1391 | 1763(19) | 1197 | 2597 |
auk sp | 249(43) | 109 | 570 | 816(22) | 522 | 1275 | 1614(19) | 1094 | 2380 |
large auk sp | 419(25) | 256 | 686 | 80(54) | 28 | 223 | 130(57) | 45 | 375 |
small auk sp | 0 | - | - | 20(99) | 2 | 211 | 20(122) | 2 | 181 |
Guillemot | 110(43) | 47 | 254 | 20(99) | 2 | 211 | 0 | - | - |
Razorbill | 30(81) | 6 | 158 | 0 | - | - | 0 | - | - |
Black Guillemot | 0 | - | - | 0 | - | - | 0 | - | - |
Puffin | 0 | - | - | 20(99) | 2 | 211 | 50(109) | 8 | 3002 |
Guillemot 2 | 513 | - | - | 733 | - | - | 1175 | - | - |
Razorbill 2 | 140 | - | - | 0 | - | - | 0 | - | - |
Black Guillemot 2 | 0 | - | - | 0 | - | - | 0 | - | - |
Puffin 2 | 16 | - | - | 183 | - | - | 588 | - | - |
Table 7 - Summary of number of birds counted from shore points. Birds flying through the count area were not counted except where indicated by an asterisk (*). Counts include birds seen on rocks and cliffs. The SIA and MEL shore points were counted on the day before that shown in June and September. 'n.c.' indicates that no count was made on that date (see Table 1). Shore point names are given in Table 1.
Species/Survey month | DAL | SSH | NSH | BRA | BRU | SHA | MEL | SGA | AIR | SWA | BLW | BLE | PON | Total |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Red-throated diver | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | n.c. | 0 | 0 | 1 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 1 | 3 |
June 2012 | n.c. | 0 | 0 | 1 | n.c. | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 0 | 4 |
July 2012 | n.c. | n.c. | n.c. | 1 | n.c. | 0 | 0 | 2 | 2 | 2 | 0 | 0 | 0 | 7 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 2 |
Dec. 2012 | n.c. | n.c. | 0 | 1 | n.c. | n.c. | 0 | n.c. | 1 | 1 | n.c. | 0 | 0 | 3 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 1 | 0 | 1 |
Black-throated diver | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 1 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Great northern diver | ||||||||||||||
April 2012 | 0 | 2 | 1 | 0 | 0 | 2 | 2 | 1 | 1 | 1 | n.c. | 0 | 0 | 10 |
May 2012 | n.c. | 3 | 4 | 4 | n.c. | 2 | 6 | 1 | 1 | 2 | 1 | 0 | 0 | 24 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 2 | 1 | 0 | 1 | 0 | 4 |
July 2012 | n.c. | n.c. | n.c. | 2 | n.c. | 0 | 3 | 1 | 0 | 0 | 0 | 1* | 0 | 7 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 2 | 1 | n.c. | n.c. | 3 | n.c. | 2 | 1 | n.c. | 1 | 0 | 10 |
Feb. 2013 | n.c. | n.c. | 0 | 2 | n.c. | n.c. | 2 | n.c. | 0 | 1 | 0 | 0 | 0 | 5 |
Slavonian grebe | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 2 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Fulmar | ||||||||||||||
April 2012 | 4 | 2 | 11 | 0 | 3 | 0 | 0 | 0 | 4 | 7 | n.c. | 3 | 15 | 49 |
May 2012 | n.c. | 1 | 8 | 0 | n.c. | 0 | 0 | 1 | 2 | 0 | 14 | 7 | 18 | 51 |
June 2012 | n.c. | 3 | 0 | 1 | n.c. | 2 | 2 | 1 | 0 | 0 | 20 | 19 | 39 | 87 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 20 | 0 | 25 | 45 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 21 | n.c. | 40 | 22 | 83 |
Feb. 2013 | n.c. | n.c. | 1 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 6 | 112 | 69 | 242 | 430 |
Storm petrel | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Gannet | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | n.c. | 1 | 0 | 6 |
May 2012 | n.c. | 4 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 5 |
June 2012 | n.c. | 4 | 0 | 2 | n.c. | 0 | 0 | 1 | 3 | 5 | 2 | 3 | 6 | 26 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 1 | 0 | 0 | 0 | 4 | 0 | 0 | 5 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 56 | 25 | 29 | 14 | 37 | 161 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 1 | 0 | 0 | 0 | 0 | 1 |
Cormorant | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 1 | 0 | 1 |
May 2012 | n.c. | 0 | 0 | 2 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 2 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 1 |
Sep. 2012 | n.c. | 0 | 0 | 2 | n.c. | 0 | 0 | 0 | 0 | 4 | 0 | 0 | 0 | 6 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Shag | ||||||||||||||
April 2012 | 1 | 0 | 1 | 1 | 0 | 2 | 0 | 0 | 0 | 0 | n.c. | 6 | 4 | 15 |
May 2012 | n.c. | 1 | 1 | 1 | n.c. | 0 | 0 | 0 | 0 | 2 | 2 | 2 | 9 | 18 |
June 2012 | n.c. | 0 | 2 | 1 | n.c. | 0 | 0 | 0 | 2 | 1 | 4 | 6 | 4 | 20 |
July 2012 | n.c. | n.c. | n.c. | 5 | n.c. | 0 | 2 | 0 | 6 | 27 | 4 | 11 | 11 | 66 |
Sep. 2012 | n.c. | 0 | 3 | 3 | n.c. | 1 | 0 | 0 | 1 | 53 | 28 | 4 | 6 | 99 |
Dec. 2012 | n.c. | n.c. | 3 | 3 | n.c. | n.c. | 1 | n.c. | 1 | 6 | n.c. | 10 | 2 | 26 |
Feb. 2013 | n.c. | n.c. | 2 | 4 | n.c. | n.c. | 5 | n.c. | 4 | 7 | 2 | 20 | 1 | 45 |
Eider | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 62 | n.c. | 0 | 0 | n.c. | 0 | 0 | 62 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 1 | 0 | 0 | 0 | 1 |
Red-breasted merganser | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 10 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 10 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Arctic skua | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 4 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 1* | 0 | 1 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Great skua | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | n.c. | 0 | 0 | 1 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 2 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Black-headed gull | ||||||||||||||
April 2012 | 0 | 0 | 24 | 36 | 0 | 0 | 3 | 0 | 0 | 2 | n.c. | 0 | 4 | 69 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 2 |
June 2012 | n.c. | 0 | 2 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Common gull | ||||||||||||||
April 2012 | 0 | 2 | 57 | 46 | 2 | 0 | 88 | 0 | 0 | 1 | n.c. | 3 | 15 | 214 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 1 | 2 | n.c. | 0 | 0 | 0 | 5 | 0 | 0 | 0 | 0 | 8 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 2 | 2 | 0 | 2 | 6 |
Sep. 2012 | n.c. | 0 | 1 | 0 | n.c. | 0 | 6 | 0 | 0 | 1 | 0 | 1 | 0 | 9 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 1 | 2 | n.c. | 1 | 0 | 4 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Lesser black-backed gull | ||||||||||||||
April 2012 | 0 | 2 | 0 | 11 | 0 | 0 | 3 | 0 | 0 | 0 | n.c. | 3 | 0 | 19 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 2 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 9 | 0 | 9 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Herring gull | ||||||||||||||
April 2012 | 0 | 22 | 4 | 4 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 5 | 3 | 38 |
May 2012 | n.c. | 0 | 1 | 0 | n.c. | 3 | 0 | 0 | 0 | 0 | 0 | 37 | 0 | 41 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 1 | 0 | 8 | 0 | 28 | 0 | 37 |
July 2012 | n.c. | n.c. | n.c. | 2 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 12 | 2 | 16 |
Sep. 2012 | n.c. | 0 | 1 | 0 | n.c. | 0 | 0 | 0 | 0 | 13 | 3 | 0 | 0 | 17 |
Dec. 2012 | n.c. | n.c. | 10 | 0 | n.c. | n.c. | 6 | n.c. | 0 | 0 | n.c. | 17 | 0 | 33 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 2 | 31 | 70 | 103 |
Iceland gull | ||||||||||||||
April 2012 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 1 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Great black-backed gull | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 1 | 0 | n.c. | 2 | 0 | 4 |
May 2012 | n.c. | 0 | 0 | 1 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 4 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 1 | 0 | 3 | 0 | 4 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 4 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 5 | 0 | 8 | 0 | 13 |
Dec. 2012 | n.c. | n.c. | 4 | 0 | n.c. | n.c. | 2 | n.c. | 2 | 1 | n.c. | 8 | 1 | 18 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 2 | n.c. | 2 | 1 | 1 | 3 | 1 | 10 |
Kittiwake | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 12 | 15 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | 5 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 2 | n.c. | 0 | 2 | 4 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 1 | n.c. | 6 | 1 | 2 | 1 | 0 | 11 |
Common tern | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 1 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Arctic tern | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 4 | 1 | n.c. | 0 | 0 | 0 | 0 | 18 | 0 | 0 | 1 | 24 |
July 2012 | n.c. | n.c. | n.c. | 2 | n.c. | 0 | 0 | 1 | 1 | 0 | 0 | 0 | 0 | 4 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Guillemot | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 3 | 3 | n.c. | 0 | 4 | 10 |
May 2012 | n.c. | 1 | 0 | 0 | n.c. | 0 | 0 | 0 | 1 | 0 | 1 | 7 | 36 | 46 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 5 | 0 | 0 | 4 | 4 | 5 | 49 | 68 | 135 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 4 | 2 | 1 | 2 | 6 | 15 |
Sep. 2012 | n.c. | 0 | 1 | 0 | n.c. | 0 | 1 | 0 | 0 | 0 | 1 | 1 | 0 | 4 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 1 | n.c. | 0 | 0 | 1 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 45 | 45 |
Razorbill | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | n.c. | 0 | 1 | 6 |
May 2012 | n.c. | 7 | 8 | 0 | n.c. | 2 | 2 | 0 | 0 | 5 | 4 | 3 | 1 | 32 |
June 2012 | n.c. | 0 | 2 | 0 | n.c. | 0 | 0 | 0 | 0 | 4 | 1 | 0 | 1 | 8 |
July 2012 | n.c. | n.c. | n.c. | 1 | n.c. | 0 | 0 | 0 | 4 | 5 | 0 | 0 | 0 | 10 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 3 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 2 | 0 | 0 | 2 |
Unidentified guillemot/razorbill | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 | 3 | n.c. | 0 | 1 | 6 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 3 | 8 | 11 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 1 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Black guillemot | ||||||||||||||
April 2012 | 0 | 2 | 0 | 0 | 1 | 1 | 1 | 0 | 0 | 0 | n.c. | 0 | 3 | 8 |
May 2012 | n.c. | 6 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 1 | 7 | 0 | 2 | 16 |
June 2012 | n.c. | 1 | 0 | 0 | n.c. | 0 | 3 | 0 | 4 | 0 | 12 | 5 | 2 | 27 |
July 2012 | n.c. | n.c. | n.c. | 2 | n.c. | 3 | 1 | 1 | 1 | 5 | 10 | 1 | 5 | 29 |
Sep. 2012 | n.c. | 1 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 1 | n.c. | 1 | 1 | n.c. | 0 | 0 | 3 |
Feb. 2013 | n.c. | n.c. | 1 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 1 |
Puffin | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 4 | 0 | 0 | n.c. | 4 | 0 | 0 | 0 | 0 | 11 | 0 | 0 | 19 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 3 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Table 8 - Summary of number of marine mammals and sharks counted from shore points. The SIA and MEL shore points were counted on the day before that shown in June and September. 'n.c.' indicates that no count was made on that date (see Table 1). Shore point names are given in Table 1
Species/Survey month | DAL | SSH | NSH | BRA | BRU | SHA | MEL | SGA | AIR | SWA | BLW | BLE | PON | Total |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Grey seal | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 1 | 0 | 0 | 0 | 1 | 0 | 2 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 2 | 0 | 0 | 0 | 1 | 0 | 1 | 4 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 8 | 0 | 0 | 0 | 8 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 1 | 0 | 1 |
Unidentified dolphin sp. | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 2 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Harbour porpoise | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 3 | 4 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Basking shark | ||||||||||||||
April 2012 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | n.c. | 0 | 0 | 0 |
May 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
June 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
July 2012 | n.c. | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 1 |
Sep. 2012 | n.c. | 0 | 0 | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 1 |
Dec. 2012 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | n.c. | 0 | 0 | 0 |
Feb. 2013 | n.c. | n.c. | 0 | 0 | n.c. | n.c. | 0 | n.c. | 0 | 0 | 0 | 0 | 0 | 0 |
Table 9 - Loch Roag survey dates, sea state and weather conditions
Date | Time | Weather | Comment |
---|---|---|---|
28 April 2012 | 07:50-20:00 | Sea state 0-1 becoming 1-2 by 14:00. 0-1 swell. Fine, mostly overcast. | Excellent survey conditions |
5 June 2012 | 07:25-16:30 | Sea state 0-1 becoming 2-3 by 15:00. No swell. Fine, overcast. | Excellent survey conditions |
7 July 2012 | 14:00-17:30 | Sea state 1. No swell. Fine, overcast. | Excellent survey conditions |
8 July 2012 | 08:00-1230 | Sea state 2, 0-0.5m swell, fine, partly overcast. Slow deterioration and by end sea-state 2-3, overcast and continuous rain and low cloud. | Excellent at start becoming good then poor. Survey visit abandoned due to onset of continuous rain and low cloud, which lasted rest of day. |
27 July 2012 | 11:00-17:40 | Sea state 1-2, 0-0.5m swell, fine, overcast. Prolonged heavy showers after 14:00 | Very good conditions most of the time, good-poor conditions during showers. Survey work temporarily halted during worst of showers. Survey abandoned at 17:40 when rain and low cloud set in for rest of day. Survey work on Great Berneray only. |
2 October 2012 | 08:20-17:40 | Sea state 1-2, occasionally 3, 0 swell, mostly fine, partly overcast. Occasional short showers. | Excellent conditions most of the time, conditions reducing to very good or good at times due to showers. Survey work temporarily halted during worst of showers. |
10 January 2012 | 09:10-15:51 | Sea state 1-2, occasionally 3, Wind SSE 0-2, 0 swell, fine, overcast. | Excellent survey conditions. Western parts of survey area counted. |
11 January 2012 | 09:15-15:51 | Sea state 1-3, occasionally 4, Wind SW 1-3, 0 swell, fine, partly overcast. | Mix of good and excellent survey conditions depending on sea state. Eastern parts of survey area counted. |
08 February 2013 | 08:35-16:32 | Sea state 1-3, occasionally 4, Wind variable direction 1-2. Occ. light shower, overcast. | Mostly excellent survey conditions, reducing to Good conditions in showers. Western parts of survey area counted. |
09 February 2013 | 08:33-15:51 | Sea state 1-2 before 14:30, sea state 3 afterwards. Wind SE 2-3, 0 swell, fine, overcast. | Excellent survey conditions most of the time, becoming Good later. Eastern parts of survey area counted. |
Table 10 - Summary of results for seabirds recorded in the Loch Roag survey area. These achieve close to complete coverage of Loch Roag, although some western part were not covered in July. Includes flying and sitting birds
Seabirds | April 2012 | June 2012 | July 2012 | Oct. 2012 | Jan 2013 | Feb 2013 | Total | Mean Ap. - July | Mean Oct. - Feb |
---|---|---|---|---|---|---|---|---|---|
Black-throated Diver | 6 | 0 | 1 | 1 | 7 | 12 | 27 | 2.3 | 6.7 |
Great Northern Diver | 44 | 9 | 1 | 1 | 80 | 95 | 230 | 18.0 | 58.7 |
Red-throated Diver | 39 | 22 | 26 | 10 | 14 | 4 | 115 | 29.0 | 9.3 |
Slavonian Grebe | 2 | 0 | 0 | 3 | 16 | 13 | 34 | 0.7 | 10.7 |
Little grebe | 0 | 0 | 0 | 0 | 1 | 2 | 3 | 0.0 | 1.0 |
Black Guillemot | 49 | 55 | 33 | 17 | 22 | 54 | 230 | 45.7 | 31.0 |
Guillemot | 7 | 13 | 5 | 8 | 0 | 0 | 33 | 8.3 | 2.7 |
Razorbill | 3 | 52 | 11 | 5 | 2 | 1 | 74 | 22.0 | 2.7 |
Guillemot/razorbill | 0 | 8 | 0 | 0 | 0 | 0 | 8 | 2.7 | 0.0 |
Cormorant | 2 | 4 | 32 | 18 | 29 | 29 | 114 | 12.7 | 25.3 |
Shag | 38 | 36 | 25 | 118 | 139 | 181 | 537 | 33.0 | 146.0 |
Gannet | 0 | 26 | 41 | 1 | 0 | 0 | 68 | 22.3 | 0.3 |
Fulmar | 0 | 16 | 11 | 0 | 93 | 45 | 165 | 9.0 | 46.0 |
Manx Shearwater | 0 | 0 | 3 | 0 | 0 | 0 | 3 | 1.0 | 0.0 |
Common Tern | 0 | 33 | 6 | 0 | 0 | 0 | 39 | 13.0 | 0.0 |
Arctic Tern | 0 | 9 | 47 | 0 | 0 | 0 | 56 | 18.7 | 0.0 |
'commic' Tern | 0 | 0 | 9 | 0 | 0 | 0 | 9 | 3.0 | 0.0 |
Table 11 - Summary of results for gull and wildfowl species recorded in the Loch Roag survey area. The surveys achieve close to complete coverage of Loch Roag, although some western part were not covered in July. Includes flying and sitting birds
Gulls and wildfowl | April 2012 | June 2012 | July 2012 | Oct. 2012 | Jan 2013 | Feb 2013 |
---|---|---|---|---|---|---|
Black-headed Gull | 2 | 0 | 7 | 5 | ||
Common Gull | 17 | 5 | 16 | 22 | 21 | 2 |
Herring Gull | 41 | 116 | 72 | 41 | 37 | 39 |
Lesser Black-backed Gull | 0 | 0 | 2 | 0 | 0 | 0 |
Great Black-backed Gull | 6 | 16 | 16 | 12 | 15 | 13 |
Kittiwake | 0 | 1 | 5 | 0 | 0 | 0 |
Glaucous Gull | 0 | 1 | 0 | 0 | 0 | 0 |
Red-breasted Merganser | 23 | 2 | 0 | 14 | 39 | 36 |
Eider | 275 | 92 | 219 | 145 | 136 | 141 |
Common Scoter | 5 | 1 | 0 | 0 | 0 | 2 |
Shelduck | 2 | 2 | 2 | 0 | 0 | 0 |
Long-tailed duck | 0 | 0 | 0 | 0 | 1 | 3 |
Goldeneye | 0 | 0 | 0 | 0 | 0 | 5 |
Teal | 0 | 0 | 3 | 6 | 11 | 0 |
Greylag Goose | 9 | 24 | 126 | 0 | 7 | 29 |
Mallard | 2 | 0 | 6 | 2 | 8 | 0 |
Table 12 - Summary of results for waders, heron and eagle recorded in the Loch Roag survey area. The surveys achieve close to complete coverage of Loch Roag, although some western part were not covered in July. Includes flying and sitting birds
Waders, heron, eagles | April 2012 | June 2012 | July 2012 | Oct. 2012 | Jan 2013 | Feb 2013 |
---|---|---|---|---|---|---|
Common Sandpiper | no count | no count | 3 | no count | no count | no count |
Curlew | no count | no count | 4 | no count | no count | no count |
Greenshank | no count | no count | 5 | no count | no count | no count |
Lapwing | no count | no count | 10 | no count | no count | no count |
Ringed Plover | no count | no count | 2 | no count | no count | no count |
Grey Heron | no count | no count | 11 | no count | no count | no count |
White-tailed eagle | 0 | 0 | 0 | 0 | 1 | 0 |
Table 13 - Summary of results for marine mammals recorded in the Loch Roag survey area. The surveys achieve close to complete coverage of Loch Roag, although some western part were not covered in July. Includes flying and sitting birds
Marine mammals | April 2012 | June 2012 | July 2012 | Oct. 2012 | Jan 2013 | Feb 2013 |
---|---|---|---|---|---|---|
Common Seal | 12 | 1 | 12 | 8 | 9 | 5 |
Grey Seal | 0 | 1 | 0 | 3 | 1 | 83 |
Seal sp. | 0 | 0 | 1 | 0 | 0 | 0 |
Table 14 - Red-throated diver: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 16 | 1 | 8 | 8 | 6 | 39 |
Jun-2012 | 13 | 5 | 1 | 3 | 0 | 22 |
Jul-2012 | 0 | 9 | 15 | 2 | 0 | 26 |
Oct-2012 | 3 | 1 | 5 | 1 | 0 | 10 |
Jan-2013 | 9 | 0 | 3 | 2 | 0 | 14 |
Feb-2013 | 1 | 1 | 1 | 0 | 1 | 4 |
Table 15 - Black-throated diver: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 2 | 0 | 0 | 2 | 2 | 6 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 0 | 1 | 0 | 1 |
Oct-2012 | 0 | 0 | 0 | 1 | 0 | 1 |
Jan-2013 | 7 | 0 | 0 | 0 | 0 | 7 |
Feb-2013 | 12 | 0 | 0 | 0 | 0 | 12 |
Table 16 - Great northern diver: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 4 | 23 | 17 | 0 | 0 | 44 |
Jun-2012 | 1 | 2 | 5 | 1 | 0 | 9 |
Jul-2012 | 0 | 0 | 1 | 0 | 0 | 1 |
Oct-2012 | 0 | 0 | 1 | 0 | 0 | 1 |
Jan-2013 | 25 | 22 | 31 | 2 | 0 | 80 |
Feb-2013 | 27 | 27 | 35 | 6 | 0 | 95 |
Table 17 - Little grebe: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 1 | 0 | 0 | 0 | 1 |
Feb-2013 | 0 | 1 | 1 | 0 | 0 | 2 |
Table 18 - Slavonian grebe: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 2 | 0 | 2 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Oct-2012 | 2 | 0 | 1 | 0 | 0 | 3 |
Jan-2013 | 8 | 0 | 0 | 8 | 0 | 16 |
Feb-2013 | 5 | 1 | 0 | 6 | 1 | 13 |
Table 19 - Fulmar: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 16 | 0 | 0 | 0 | 0 | 16 |
Jul-2012 | 0 | 10 | 1 | 0 | 0 | 11 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 93 | 0 | 0 | 0 | 0 | 93 |
Feb-2013 | 20 | 0 | 25 | 0 | 0 | 45 |
Table 20 - Manx shearwater: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 3 | 0 | 0 | 3 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 21 - Gannet: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 25 | 0 | 1 | 0 | 0 | 26 |
Jul-2012 | 2 | 17 | 22 | 0 | 0 | 41 |
Oct-2012 | 1 | 0 | 0 | 0 | 0 | 1 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 22 - Cormorant: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 1 | 0 | 0 | 0 | 1 | 2 |
Jun-2012 | 1 | 2 | 1 | 0 | 0 | 4 |
Jul-2012 | 0 | 4 | 7 | 4 | 0 | 15 |
Oct-2012 | 2 | 4 | 11 | 0 | 1 | 18 |
Jan-2013 | 12 | 5 | 12 | 0 | 0 | 29 |
Feb-2013 | 0 | 7 | 3 | 18 | 1 | 29 |
Table 23 - Shag: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 20 | 12 | 2 | 7 | 0 | 41 |
Jun-2012 | 21 | 13 | 2 | 0 | 0 | 36 |
Jul-2012 | 0 | 15 | 10 | 0 | 0 | 25 |
Oct-2012 | 75 | 16 | 20 | 6 | 1 | 118 |
Jan-2013 | 37 | 53 | 40 | 7 | 2 | 139 |
Feb-2013 | 64 | 31 | 36 | 45 | 5 | 181 |
Table 24 - Greylag Goose: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit. In addition, a total of 78 goslings were seen accompanying adults in July (*)
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 3 | 3 | 3 | 0 | 0 | 9 |
Jun-2012 | 4 | 0 | 3 | 17 | 0 | 24 |
Jul-2012 | 0 | 7* | 14* | 87* | 19* | 127 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 7 | 0 | 0 | 0 | 0 | 7 |
Feb-2013 | 4 | 25 | 0 | 0 | 0 | 29 |
Table 25 - Shelduck: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 2 | 0 | 2 |
Jun-2012 | 0 | 0 | 0 | 2 | 0 | 2 |
Jul-2012 | 0 | 0 | 0 | 2 | 0 | 2 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 26 - Teal: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 3 | 0 | 0 | 3 |
Oct-2012 | 0 | 0 | 0 | 6 | 0 | 6 |
Jan-2013 | 0 | 0 | 0 | 0 | 11 | 11 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 27 - Mallard: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 2 | 0 | 2 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 2 | 0 | 4 | 0 | 6 |
Oct-2012 | 0 | 0 | 0 | 2 | 0 | 2 |
Jan-2013 | 0 | 0 | 0 | 0 | 8 | 8 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 28 - Eider: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit. In addition, a total of 12 ducklings were seen accompanying adults in July (*)
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 198 | 77 | 0 | 0 | 0 | 275 |
Jun-2012 | 59 | 33 | 0 | 0 | 0 | 92 |
Jul-2012 | 0 | 203* | 16* | 0 | 0 | 219 |
Oct-2012 | 137 | 4 | 1 | 3 | 0 | 145 |
Jan-2013 | 136 | 0 | 0 | 0 | 0 | 136 |
Feb-2013 | 140 | 1 | 0 | 0 | 0 | 141 |
Table 29 - Long-tailed duck: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 1 | 0 | 1 |
Feb-2013 | 0 | 2 | 0 | 1 | 0 | 3 |
Table 30 - Common scoter: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 5 | 0 | 0 | 0 | 0 | 5 |
Jun-2012 | 0 | 0 | 1 | 0 | 0 | 1 |
Jul-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 2 | 0 | 0 | 0 | 0 | 2 |
Table 31 - Goldeneye: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 4 | 0 | 1 | 0 | 5 |
Table 32 - Red-breasted merganser: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 19 | 4 | 23 |
Jun-2012 | 0 | 0 | 0 | 1 | 1 | 2 |
Jul-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Oct-2012 | 0 | 0 | 0 | 12 | 2 | 14 |
Jan-2013 | 2 | 8 | 5 | 18 | 6 | 39 |
Feb-2013 | 0 | 18 | 7 | 5 | 6 | 36 |
Table 33 - Black-headed gull: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 1 | 0 | 0 | 1 | 0 | 2 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 0 | 7 | 0 | 7 |
Oct-2012 | 4 | 0 | 0 | 1 | 0 | 5 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 34 - Common gull: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 3 | 1 | 13 | 0 | 0 | 17 |
Jun-2012 | 1 | 0 | 2 | 0 | 2 | 5 |
Jul-2012 | 0 | 0 | 4 | 7 | 2 | 13 |
Oct-2012 | 11 | 3 | 2 | 6 | 0 | 22 |
Jan-2013 | 2 | 3 | 1 | 15 | 0 | 21 |
Feb-2013 | 2 | 0 | 0 | 0 | 0 | 2 |
Table 35 - Lesser black-backed gull: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jul-2012 | 0 | 0 | 1 | 1 | 0 | 2 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 36 - Herring gull: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 19 | 15 | 1 | 6 | 0 | 41 |
Jun-2012 | 74 | 37 | 0 | 0 | 5 | 116 |
Jul-2012 | 4 | 50 | 9 | 5 | 4 | 72 |
Oct-2012 | 11 | 7 | 13 | 7 | 3 | 41 |
Jan-2013 | 22 | 12 | 1 | 1 | 1 | 37 |
Feb-2013 | 8 | 1 | 28 | 2 | 0 | 39 |
Table 37 - Glaucous gull: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 1 | 0 | 0 | 0 | 1 |
Jul-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 38 - Great black-backed gull: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 4 | 0 | 1 | 1 | 0 | 6 |
Jun-2012 | 2 | 13 | 0 | 1 | 0 | 16 |
Jul-2012 | 2 | 1 | 5 | 4 | 0 | 12 |
Oct-2012 | 4 | 0 | 5 | 3 | 0 | 12 |
Jan-2013 | 8 | 1 | 4 | 2 | 0 | 15 |
Feb-2013 | 3 | 1 | 6 | 3 | 0 | 13 |
Table 39 - Kittiwake: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 1 | 0 | 0 | 0 | 0 | 1 |
Jul-2012 | 0 | 3 | 2 | 0 | 0 | 5 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 40 - Common tern: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit. In addition, nine unidentified 'commic' terns were recorded in July (*)
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 0 | 30 | 2 | 1 | 33 |
Jul-2012 | 0 | 0* | 1* | 5 | 0 | 6 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 41 - Arctic tern: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit. In addition, nine unidentified 'commic' terns were recorded in July (*)
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 7 | 0 | 0 | 2 | 0 | 9 |
Jul-2012 | 2 | 16* | 16* | 13 | 0 | 47 |
Oct-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 42 - Common guillemot: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit. In addition, eight unidentified guillemot/razorbill were recorded in June (*)
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 2 | 3 | 2 | 0 | 7 |
Jun-2012 | 7* | 4 | 2 | 0 | 0 | 13 |
Jul-2012 | 0 | 1 | 5 | 0 | 0 | 6 |
Oct-2012 | 2 | 0 | 5 | 1 | 0 | 8 |
Jan-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Feb-2013 | 0 | 0 | 0 | 0 | 0 | 0 |
Table 43 - Razorbill: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit. In addition, eight unidentified guillemot/razorbill were recorded in June (*), and a total of five chicks were seen accompanying adults in July (**)
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 1 | 2 | 0 | 0 | 0 | 3 |
Jun-2012 | 10 | 39 | 3 | 0 | 0 | 52 |
Jul-2012 | 0 | 6** | 5** | 0 | 0 | 11 |
Oct-2012 | 1 | 0 | 4 | 0 | 0 | 5 |
Jan-2013 | 0 | 0 | 0 | 2 | 0 | 2 |
Feb-2013 | 0 | 1 | 0 | 0 | 0 | 1 |
Table 44 - Black guillemot: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 22 | 2 | 14 | 11 | 0 | 49 |
Jun-2012 | 32 | 3 | 7 | 13 | 0 | 55 |
Jul-2012 | 0 | 12 | 13 | 7 | 0 | 32 |
Oct-2012 | 9 | 1 | 6 | 1 | 0 | 17 |
Jan-2013 | 9 | 4 | 1 | 8 | 0 | 22 |
Feb-2013 | 22 | 16 | 9 | 7 | 0 | 54 |
Table 45 - Common seal: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit. In addition, a single unidentified seal was recorded in July (*)
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 8 | 4 | 12 |
Jun-2012 | 0 | 1 | 0 | 0 | 0 | 1 |
Jul-2012 | 0 | 0* | 1 | 11 | 0 | 12 |
Oct-2012 | 0 | 0 | 1 | 7 | 0 | 8 |
Jan-2013 | 2 | 0 | 0 | 5 | 2 | 9 |
Feb-2013 | 0 | 1 | 0 | 3 | 1 | 5 |
Table 46 - Grey seal: the number of birds recorded in each sub-section of the Loch Roag survey area on each visit. In addition, a single unidentified seal was recorded in July (*)
Month | Kyles Pabay & Valtos | West Great Bernera | East Loch Roag | Lochs Barraglom & Hulavig | Little Loch Roag | Whole survey area |
---|---|---|---|---|---|---|
Apr-2012 | 0 | 0 | 0 | 0 | 0 | 0 |
Jun-2012 | 0 | 1 | 0 | 0 | 0 | 1 |
Jul-2012 | 0 | 0* | 0 | 0 | 0 | 0 |
Oct-2012 | 1 | 0 | 1 | 1 | 0 | 3 |
Jan-2013 | 0 | 0 | 1 | 0 | 0 | 1 |
Feb-2013 | 0 | 80 | 3 | 0 | 0 | 83 |
Table 47 - Abundance (N) and density estimates with % CV and 95% confidence levels obtained from density surface modelling of the most commonly recorded species and species groups from the digital aerial surveys. The GAM model used was N ~ s(x, y, k = 10) + offset, Family = Negative binomial, Theta = 0.166, gamma=1.4. with automatic smooth selection by REML. n is the number of segments in the survey. k was set to 10 and gamma 1.4 to reduce the likelihood of overfitting. Where the estimated degrees of freedom (edf) approached 9 (k-1) conventionally k might be increased to reduce residuals however, this was maximum k and was fixed. The adjusted r-squared (r-sq) is the proportion of variance explained as a goodness of fit, Chi squared (Chi.sq) the test statistic and the p-value the probability of the null hypothesis that the model parameter is zero being true. *** = significant at <0.001 level '*' significant at 0.05 level, '.' at the 0.1 level. The REML score is used in automatic smooth selection. Note that some models, such as gannets in May '12 had low significance and % deviance explained due to birds being more randomly distributed with only weak patterns in x and y
Survey | Species | n | edf | r-sq | Chi.sq | p-value | REML score | % Deviance explained | Density birds km -2 | N | % CV | LCL | UCL |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Apr '12 | Fulmar | 499 | 7.427 | 0.0403 | 85.15 | <2e-16 *** | 371.11 | 36.5 | 3.203 | 3197 | 23.50 | 1725 | 4669 |
Gannet | 499 | 4.436 | 0.0317 | 21.83 | 3.53e-05 *** | 129.19 | 24.3 | 0.416 | 415 | 26.57 | 199 | 631 | |
auks | 499 | 4.041 | 0.0577 | 29.09 | 1.79e-07 *** | 377.01 | 15.4 | 2.081 | 2077 | 20.92 | 1225 | 2929 | |
May '12 | Fulmar | 504 | 5.255 | -0.295 | 56.48 | 1.47e-12 *** | 162.8 | 39.1 | 1.161 | 1159 | 29.66 | 485 | 1833 |
Gannet | 504 | 0.0003054 | 0.00139 | 0 | 0.558 | 250.78 | 0.000208 | 0.934 | 932 | 16.11 | 638 | 1226 | |
auks | 504 | 4.726 | 0.0584 | 39.27 | 6.1e-09 *** | 183.37 | 32.7 | 0.761 | 760 | 25.31 | 383 | 1137 | |
Jun '12 | Fulmar | 505 | 6.006 | 0.03 | 45.99 | 1.09e-09 *** | 202.18 | 33 | 0.978 | 976 | 26.43 | 470 | 1482 |
Gannet | 505 | 6.968 | 0.0446 | 24.9 | 0.000316 *** | 193.21 | 24.5 | 0.685 | 684 | 24.07 | 361 | 1007 | |
auks | 505 | 5.307 | 0.074 | 22.09 | 0.000115 *** | 359.3 | 12.7 | 1.817 | 1813 | 20.48 | 1085 | 2541 | |
Jul '12 | Fulmar | 505 | 1.804 | 0.0311 | 10.17 | <2e-16 *** | 292.77 | 6.85 | 1.123 | 1121 | 17.52 | 736 | 1506 |
Gannet | 505 | 1.329 | 0.00964 | 5.018 | 0.0285 * | 427.46 | 2.81 | 2.039 | 2035 | 26.89 | 963 | 3107 | |
auks | 505 | 0.02529 | -0.00229 | 0.025 | 0.362 | 297.44 | 0.0238 | 1.351 | 1348 | 20.25 | 813 | 1883 | |
Sept '12 | Fulmar | 511 | 3.145 | 0.0209 | 17.93 | 0.000119 *** | 94.137 | 22.4 | 0.303 | 302 | 29.85 | 125 | 479 |
Gannet | 511 | 0.5967 | 0.00222 | 1.216 | 0.142 | 474.1 | 0.811 | 2.576 | 2571 | 15.21 | 1805 | 3337 | |
auks | 511 | 2.205 | 0.0112 | 5.226 | 0.0504. | 199.19 | 4.97 | 0.677 | 676 | 29.62 | 284 | 1068 | |
Dec '12 | Fulmar | 508 | 5.662 | 0.0211 | 24.23 | 5.94e-05 *** | 259.42 | 13.4 | 1.298 | 1295 | 21.38 | 752 | 1838 |
Gannet | 508 | 2.665 | 0.12 | 2.816 | 0.363 | 9.9752 | 70.5 | 0.020 | 20 | 91.13 | 0 | 56 | |
auks | 508 | 3.239 | 0.0383 | 16.85 | 0.000147 *** | 234.19 | 11.9 | 0.889 | 887 | 29.32 | 377 | 1397 | |
Feb '13 | Fulmar | 507 | 6.153 | 0.0685 | 60.03 | 1.42e-12 *** | 221.36 | 38.3 | 1.693 | 1690 | 28.70 | 739 | 2641 |
Gannet | 507 | 1.334 | 0.0157 | 5.791 | 0.015 * | 22.873 | 32.5 | 0.050 | 50 | 50.27 | 1 | 99 | |
auks | 507 | 3.056 | 0.0441 | 16.6 | 0.000117 *** | 368.29 | 8.92 | 1.768 | 1765 | 27.66 | 808 | 2722 |
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