Top Birds at North Mt. Loretto SF in August
relative to other locations within 25 miles of New York City, United States
based on 10 checklists
This page shows the probability of a species appearing on a checklist at North Mt. Loretto SF in August. The difference in probability relative to other nearby locations is also shown, to highlight which birds are particularly likely to be found (or not found) at this specific location. The chart shows how many distinct species have historically been observed at this location for each month of the year.
| Evidence | Sampling | Score | |||||||
|---|---|---|---|---|---|---|---|---|---|
| # | Links | Species | Media | Years | Birders | Hits | Frequency | Percentile | |
| 1 | American Robin | 0 | 6 | 8 | 7 | 70.0% | 71% | ||
| 2 | Blue Jay | 0 | 5 | 7 | 6 | 60.0% | 66% | ||
| 3 | Osprey | 0 | 5 | 5 | 6 | 60.0% | 73% | ||
| 4 | Hairy Woodpecker | 0 | 3 | 5 | 4 | 40.0% | 84% | ||
| 5 | Northern Cardinal | 0 | 3 | 3 | 3 | 30.0% | 34% | ||
| 6 | American Goldfinch | 0 | 3 | 3 | 3 | 30.0% | 40% | ||
| 7 | Great Blue Heron | 0 | 3 | 3 | 3 | 30.0% | 48% | ||
| 8 | Red-bellied Woodpecker | 0 | 3 | 3 | 3 | 30.0% | 53% | ||
| 9 | Red-eyed Vireo | 0 | 2 | 3 | 3 | 30.0% | 79% | ||
| 10 | Black-capped Chickadee | 0 | 3 | 3 | 3 | 30.0% | 69% | ||
| 11 | Mourning Dove | 0 | 2 | 2 | 2 | 20.0% | 11% | ||
| 12 | Gray Catbird | 0 | 2 | 2 | 2 | 20.0% | 17% | ||
| 13 | Double-crested Cormorant | 0 | 2 | 2 | 2 | 20.0% | 22% | ||
| 14 | American Herring Gull | 0 | 2 | 2 | 2 | 20.0% | 23% | ||
| 15 | Barn Swallow | 0 | 2 | 2 | 2 | 20.0% | 26% | ||
| 16 | Northern Mockingbird | 0 | 2 | 2 | 2 | 20.0% | 32% | ||
| 17 | Common Grackle | 0 | 2 | 2 | 2 | 20.0% | 33% | ||
| 18 | Northern Flicker | 0 | 2 | 2 | 2 | 20.0% | 31% | ||
| 19 | Carolina Wren | 0 | 2 | 2 | 2 | 20.0% | 32% | ||
| 20 | Downy Woodpecker | 0 | 2 | 2 | 2 | 20.0% | 37% | ||
| 21 | House Wren | 0 | 2 | 3 | 2 | 20.0% | 57% | ||
| 22 | White-breasted Nuthatch | 0 | 2 | 2 | 2 | 20.0% | 46% | ||
| 23 | Tufted Titmouse | 0 | 2 | 2 | 2 | 20.0% | 52% | ||
| 24 | Yellow-billed Cuckoo | 0 | 2 | 2 | 2 | 20.0% | 90% | ||
| 25 | European Starling | 0 | 1 | 1 | 1 | 10.0% | 3% | ||
| 26 | House Sparrow | 0 | 1 | 1 | 1 | 10.0% | 3% | ||
| 27 | Canada Goose | 0 | 1 | 1 | 1 | 10.0% | 10% | ||
| 28 | Rock Pigeon | 0 | 1 | 1 | 1 | 10.0% | 8% | ||
| 29 | Red-winged Blackbird | 0 | 1 | 1 | 1 | 10.0% | 16% | ||
| 30 | Chimney Swift | 0 | 1 | 1 | 1 | 10.0% | 13% | ||
| 31 | American Redstart | 0 | 1 | 1 | 1 | 10.0% | 23% | ||
| 32 | Northern Yellow Warbler | 0 | 1 | 1 | 1 | 10.0% | 24% | ||
| 33 | Eastern Kingbird | 0 | 1 | 1 | 1 | 10.0% | 22% | ||
| 34 | Cedar Waxwing | 0 | 1 | 1 | 1 | 10.0% | 26% | ||
| 35 | Greater Yellowlegs | 0 | 1 | 1 | 1 | 10.0% | 33% | ||
| 36 | Black-and-white Warbler | 0 | 1 | 1 | 1 | 10.0% | 24% | ||
| 37 | Baltimore Oriole | 0 | 1 | 1 | 1 | 10.0% | 24% | ||
| 38 | Tree Swallow | 0 | 1 | 1 | 1 | 10.0% | 27% | ||
| 39 | Green Heron | 0 | 1 | 1 | 1 | 10.0% | 33% | ||
| 40 | Warbling Vireo | 0 | 1 | 1 | 1 | 10.0% | 36% | ||
| 41 | Wood Duck | 0 | 1 | 1 | 1 | 10.0% | 33% | ||
| 42 | Eastern Wood-Pewee | 0 | 1 | 1 | 1 | 10.0% | 32% | ||
| 43 | Great Crested Flycatcher | 0 | 1 | 1 | 1 | 10.0% | 36% | ||
| 44 | Canada Warbler | 0 | 1 | 1 | 1 | 10.0% | 49% | ||
| 45 | Turkey Vulture | 0 | 1 | 1 | 1 | 10.0% | 35% | ||
| 46 | Chestnut-sided Warbler | 0 | 1 | 1 | 1 | 10.0% | 50% | ||
| 47 | Ovenbird | 0 | 1 | 1 | 1 | 10.0% | 50% | ||
| 48 | Willow Flycatcher | 0 | 1 | 1 | 1 | 10.0% | 48% | ||
| 49 | Solitary Sandpiper | 0 | 1 | 1 | 1 | 10.0% | 50% | ||
| 50 | Blue-winged Warbler | 0 | 1 | 1 | 1 | 10.0% | 62% | ||
| 51 | Purple Martin | 0 | 1 | 1 | 1 | 10.0% | 47% | ||
| 52 | Eastern Phoebe | 0 | 1 | 1 | 1 | 10.0% | 56% | ||
| 53 | Bald Eagle | 0 | 1 | 1 | 1 | 10.0% | 50% | ||
| 54 | Brown Thrasher | 0 | 1 | 1 | 1 | 10.0% | 63% | ||
| 55 | Indigo Bunting | 0 | 1 | 1 | 1 | 10.0% | 53% | ||
| 56 | Wood Thrush | 0 | 1 | 2 | 1 | 10.0% | 42% | ||
| 57 | Scarlet Tanager | 0 | 1 | 1 | 1 | 10.0% | 74% | ||
| 58 | Worm-eating Warbler | 0 | 1 | 1 | 1 | 10.0% | 75% | ||