We believe re-scoring of all birds on the basis of various projects should be avoided because a standard against which individual projects can be measured is needed. If everyone did their own scoring, there would be no standard, and projects evaluated by different investigators would not be comparable. If a species list for the project area and standard point scores are used, the level of involvement for many species and perhaps for most species will be properly identified. As with any system, there will be exceptions and the assessor will need to deal with these as appropriate. The result will still be to focus attention on those species and impacting factors where it is most needed.
| OVI 1-20 | OVI 21-40 | OVI 41-60 | OVI 61-80 | OVI 81-100 | |||||
|---|---|---|---|---|---|---|---|---|---|
| Marsh hawk | 19 | Great blue heron | 29 | Common loon | 47 | Pelagic cormorant | 63 | Pigeon guillemot | 82 |
| 52 species, rare or occasional (one point each) | 52 | Canada goose | 34 | Arctic loon | 58 | Oldsquaw | 66 | Marbled murrelet | 84 |
| White-fronted goose | 36 | Red-throated loon | 49 | White-winged scoter | 72 | ||||
| Snow goose | 32 | Red-necked grebe | 44 | Surf scoter | 72 | ||||
| Mallard | 36 | Horned grebe | 48 | Black oystercatcher | 65 | ||||
| Pintail | 36 | Whistling swan | 50 | Northern phalarope | 62 | ||||
| Green-winged teal | 34 | Trumpeter swan | 63 | Common murre | 70 | ||||
| American wigeon | 36 | Greater scaup | 52 | ||||||
| Semipalmated plover | 28 | Lesser scaup | 52 | ||||||
| Killdeer | 26 | Common goldeneye | 48 | ||||||
| Common snipe | 29 | Barrow's goldeneye | 56 | ||||||
| Spotted sandpiper | 24 | Bufflehead | 52 | ||||||
| Greater yellowlegs | 30 | Harlequin duck | 60 | ||||||
| Lesser yellowlegs | 30 | Common merganser | 56 | ||||||
| Pectoral sandpiper | 32 | Red-breasted merganser | 56 | ||||||
| Least sandpiper | 34 | Bald eagle | 58 | ||||||
| Herring gull | 38 | Peregrine falcon | 41 | ||||||
| Bonaparte's gull | 40 | Black turnstone | 57 | ||||||
| Arctic tern | 32 | Rock sandpiper | 59 | ||||||
| Belted kingfisher | 28 | Dunlin | 41 | ||||||
| Common raven | 21 | Short-billed dowitcher | 41 | ||||||
| Western sandpiper | 47 | ||||||||
| Glaucous-winged gull | 56 | ||||||||
| Thayer's gull | 42 | ||||||||
| Mew gull | 44 | ||||||||
| Northwestern crow | 47 | ||||||||
| Totals | 71 | 665 | 1,324 | 470 | 166 | ||||
| OVI 1-20 | OVI 21-40 | OVI 41-60 | OVI 61-80 | OVI 81-100 | |||||
|---|---|---|---|---|---|---|---|---|---|
| 80 species, rare or occasional (one point each) | 80 | Canada goose | 34 | Fulmar | 57 | Fork-tailed storm-petrel | 67 | Pigeon guillemot | 82 |
| Least sandpiper | 34 | Slender-billed shearwater | 53 | Leach's storm-petrel | 63 | Whiskered auklet | 88 | ||
| Arctic tern | 32 | Greater scaup | 52 | Pelagic cormorant | 63 | ||||
| Common raven | 21 | Common goldeneye | 48 | Red-faced cormorant | 63 | ||||
| Bufflehead | 52 | Black Brant | 70 | ||||||
| Harlequin duck | 60 | Emperor goose | 70 | ||||||
| Bald eagle | 58 | Oldsquaw | 66 | ||||||
| Peregrine falcon | 41 | Steller's eider | 72 | ||||||
| Ruddy turnstone | 44 | Common eider | 68 | ||||||
| Rock sandpiper | 59 | King eider | 70 | ||||||
| Western sandpiper | 47 | White-winged scoter | 72 | ||||||
| Red phalarope | 58 | Common scoter | 72 | ||||||
| Parasitic jaeger | 43 | Black oystercatcher | 65 | ||||||
| Glaucous-winged gull | 56 | Red-legged kittiwake | 66 | ||||||
| Black-legged kittiwake | 49 | Common murre | 70 | ||||||
| Thick-billed murre | 70 | ||||||||
| Ancient murrelet | 74 | ||||||||
| Parakeet auklet | 80 | ||||||||
| Crested auklet | 76 | ||||||||
| Least auklet | 80 | ||||||||
| Horned puffin | 72 | ||||||||
| Tufted puffin | 72 | ||||||||
| Totals | 80 | 121 | 777 | 1,541 | 170 | ||||
We have used our OVI system to show the vulnerability of birds to oil, but it seems likely that the vulnerability index could be applied on a much broader scale to help make decisions in other areas of human activity and resource development. The vulnerability index system could be applied to terrestrial as well as aquatic species by adding or subtracting impacting factors, as appropriate. Indexes relating the impact of man upon each North American species could have broad uses in the field of conservation. Population explosions, as well as declines, might be predictable. Human activity could be better adjusted to favor or depress wildlife populations, as appropriate.
We believe that this vulnerability index system has promise for aiding in the decision-making processes upon which future bird conservation will depend.
References
American Ornithologists' Union. 1957. Check-list of North American birds. 5th ed. Lord Baltimore Press, Baltimore, Maryland.
Fay, F. H., and T. J. Cade. 1959. An ecological analysis of the avifauna of St. Lawrence Island, Alaska. Univ. Calif. Publ. Zool. 63(2):73-150.
Gabrielson, J. N., and F. C. Lincoln. 1959. The birds of Alaska. The Stackpole Company, Harrisburg, Pa., and Wildlife Management Institute, Washington, D.C. 922 pp.