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. 2018 Nov 14;8(23):11410–11422. doi: 10.1002/ece3.4556

Table 1.

Sample sizes and summary statistics for all wild‐caught individuals. N = Number of specimens, H E = Mean expected heterozygosity, H O = Mean observed heterozygosity, A = Total allelic richness (based on a minimum sample size of 13 individuals), F IS = Wright's inbreeding coefficient, N e = Effective population size, with 95% confidence intervals

River system Sampling location N H E H O A F IS N e
Hudson Calamity Brook 29 0.63 0.64 60.39 −0.004 27.2 (19.0–42.4)
Nate Pond Brook 26 0.68 0.70 69.67 −0.028 44.8 (29.0–85.7)
Huntley Pond Inlet 30 0.69 0.71 71.13 −0.029 67.4 (41.8–147.1)
Blue Ledge Tributary 16 0.63 0.64 59.88 −0.012 14.8 (9.4–26–2)
Boreas Slide Brook 17 0.51 0.51 58.33 0.019 75.6 (27.2–∞)
Snyder Brook 28 0.55 0.51 59.62 0.083 33.0 (21.6–58.8)
Durgin Brook 27 0.60 0.57 67.70 0.040 114.8 (50.9–∞)
Vanderwhacker Brook 17 0.62 0.58 60.58 0.062 17.3 (10.8–32.9)
Unnamed Brook 1 30 0.61 0.63 64.80 −0.045 315.3 (80.3–∞)
Schroon Dix‐Elk Tributaries 25 0.60 0.58 62.72 0.039 254.3 (67.3–∞)
Gulf Brook 17 0.56 0.53 43.70 0.043 74.6 (26.3–∞)
Unnamed Brook 2 13 0.61 0.57 64.00 0.065 46.4 (18.1–∞)
Platt Creek 29 0.56 0.57 59.40 −0.012 60.7 (33.2–200.7)
Shanty Bottom Brook 27 0.62 0.60 64.24 0.041 60.7 (33.9–185.9)