Table 2. Apparent survival rate (φ) estimates (and standard errors) are based on data collected on two 100-ha plots in Ecuador, 2001–2012.
2001 – 2012 data | 2001 – 2006 data | |||||||||||
Species | Model | I/Ra | ΔAICc b | wi c | φ1 | SE | φ2 | SE | ΔAICc | wi | φ2 | SE |
Nonpasserines | ||||||||||||
Trochilidae | ||||||||||||
Phaethornis malaris | φ(2./.)p(.) | 265/100 | 0.0 | 1.0 | 0.08 | 0.03 | 0.42 | 0.05 | 0.0 | 0.99 | 0.53 | 0.08 |
Bucconidae | ||||||||||||
Malacoptila fusca | φ(.)p(.) | 57/22 | 0.0 | 0.67 | 0.61 | 0.08 | 0.61 | 0.08 | ||||
Passerines | ||||||||||||
Furnariidae | ||||||||||||
Automolus infuscatus | φ(2./.)p(.) | 190/158 | 0.0 | 0.74 | 0.34 | 0.07 | 0.54 | 0.04 | ||||
φ(.)p(.) | 0.0 | 0.68 | 0.48 | 0.05 | ||||||||
Glyphorynchus spirurus | φ(2./.)p(.) | 892/916 | 0.0 | 0.99 | 0.41 | 0.03 | 0.62 | 0.02 | 0.0 | 0.90 | 0.59 | 0.03 |
Hyloctistes subulatus | φ(.)p(.) | 72/35 | 0.0 | 0.71 | 0.57 | 0.06 | 0.57 | 0.06 | 0.0 | 0.64 | 0.59 | 0.14 |
Philydor erythrocercum | φ(.)p(.) | 87/36 | 0.0 | 0.71 | 0.53 | 0.06 | 0.53 | 0.06 | 0.0 | 0.75 | 0.63 | 0.10 |
Sclerurus caudacutus | φ(.)p(.) | 62/57 | 0.0 | 0.66 | 0.59 | 0.05 | 0.59 | 0.05 | 0.0 | 0.70 | 0.66 | 0.08 |
Xenops minutus | φ(2./.)p(.) | 85/60 | 0.0 | 0.54 | 0.43 | 0.14 | 0.71 | 0.05 | ||||
φ(.)p(.) | 0.33 | 0.46 | 0.68 | 0.04 | 0.68 | 0.04 | 0.0 | 0.51 | 0.52 | 0.12 | ||
Xiphorhynchus ocellatus | φ(.)p(.) | 75/62 | 0.0 | 0.59 | 0.70 | 0.04 | 0.70 | 0.04 | 0.0 | 0.61 | 0.72 | 0.09 |
Thamnophilidae | ||||||||||||
Hylophylax naevius | φ(.)p(.) | 244/101 | 0.0 | 0.59 | 0.69 | 0.03 | 0.69 | 0.03 | 0.0 | 0.71 | 0.73 | 0.07 |
Epinecrophylla fjeldsaai | φ(.)p(.) | 94/42 | 0.0 | 0.56 | 0.55 | 0.06 | 0.55 | 0.06 | 0.0 | 0.75 | 0.53 | 0.14 |
Gymnopithys leucaspis | φ(2./.)p(.) | 124/91 | 0.0 | 0.55 | 0.36 | 0.09 | 0.55 | 0.05 | ||||
φ(.)p(.) | 0.43 | 0.45 | 0.51 | 0.04 | 0.51 | 0.04 | 0.0 | 0.72 | 0.56 | 0.06 | ||
Myrmeciza fortis | φ(.)p(.) | 71/18 | 0.0 | 0.75 | 0.65 | 0.08 | 0.65 | 0.08 | ||||
Myrmoborus myotherinus | φ(.)p(.) | 195/71 | 0.0 | 0.72 | 0.60 | 0.04 | 0.60 | 0.04 | 0.0 | 0.48 | 0.59 | 0.08 |
Myrmotherula axillaris | φ(2./.)p(.) | 121/28 | 0.0 | 0.85 | 0.15 | 0.10 | 0.69 | 0.08 | ||||
Myrmotherula hauxwelli | φ(2./.)p(.) | 171/90 | 0.0 | 0.53 | 0.90 | 0.19 | 0.62 | 0.04 | ||||
φ(.)p(.) | 0.23 | 0.47 | 0.65 | 0.04 | 0.65 | 0.04 | 0.0 | 0.69 | 0.64 | 0.09 | ||
Myrmotherula longipennis | φ(.)p(.) | 103/44 | 0.0 | 0.71 | 0.51 | 0.06 | 0.51 | 0.06 | 0.0 | 0.68 | 0.47 | 0.10 |
Pithys albifrons | φ(2./.)p(.) | 278/214 | 0.0 | 0.94 | 0.24 | 0.05 | 0.47 | 0.04 | 0.69 | 0.22 | 0.43 | 0.06 |
φ(2./.)p(t) | 0.0 | 0.31 | 0.42 | 0.06 | ||||||||
Thamnomanes ardesiacus | φ(.)p(.) | 241/91 | 0.0 | 0.56 | 0.60 | 0.04 | 0.60 | 0.04 | 0.51 | 0.43 | 0.60 | 0.07 |
φ(2./.)p(.) | 0.0 | 0.55 | 0.67 | 0.08 | ||||||||
Thamnomanes caesius | φ(.)p(.) | 235/43 | 0.0 | 0.69 | 0.46 | 0.06 | 0.46 | 0.06 | 0.0 | 0.72 | 0.57 | 0.13 |
Willisornis poecilinotus | φ(.)p(.) | 309/224 | 0.0 | 0.73 | 0.56 | 0.03 | 0.56 | 0.03 | 0.0 | 0.66 | 0.55 | 0.04 |
Conopophagidae | ||||||||||||
Conopophaga peruviana | φ(.)p(.) | 104/28 | 0.0 | 0.61 | 0.57 | 0.07 | 0.57 | 0.07 | ||||
Formicariidae | ||||||||||||
Formicarius colma | φ(.)p(.) | 65/38 | 0.0 | 0.72 | 0.44 | 0.06 | 0.44 | 0.06 | 0.0 | 0.76 | 0.55 | 0.09 |
Tyrannidae | ||||||||||||
Corythopis torquatus | φ(.)p(.) | 61/20 | 0 | 0.69 | 0.64 | 0.08 | 0.64 | 0.08 | ||||
Mionectes oleagineus | φ(.)p(.) | 169/58 | 0.0 | 0.65 | 0.45 | 0.05 | 0.45 | 0.05 | 1.62 | 0.23 | 0.32 | 0.09 |
φ(.)p(t) | 0.0 | 0.52 | 0.32 | 0.09 | ||||||||
Myiobius barbatus | φ(2./.)p(.) | 74/41 | 0.0 | 0.69 | 0.34 | 0.13 | 0.71 | 0.06 | ||||
φ(.)p(.) | 1.56 | 0.31 | 0.65 | 0.05 | 0.65 | 0.05 | 0.0 | 0.68 | 0.68 | 0.09 | ||
Platyrinchus coronatus | φ(.)p(.) | 78/62 | 0.0 | 0.71 | 0.61 | 0.05 | 0.61 | 0.05 | 0.0 | 0.74 | 0.57 | 0.10 |
Pipridae | ||||||||||||
Chiroxiphia pareola | φ(2./.)p(.) | 90/63 | 0.0 | 0.84 | 0.37 | 0.12 | 0.76 | 0.05 | ||||
φ(.)p(.) | 0.0 | 0.74 | 0.55 | 0.09 | ||||||||
Lepidothrix coronata | φ(2./.)p(.) | 445/222 | 0.0 | 0.65 | 0.44 | 0.07 | 0.61 | 0.03 | ||||
φ(.)p(.) | 1.27 | 0.35 | 0.58 | 0.02 | 0.58 | 0.02 | 0.0 | 0.70 | 0.58 | 0.04 | ||
Pipra filicauda | φ(2./.)p(.) | 226/153 | 0.0 | 0.64 | 0.45 | 0.09 | 0.69 | 0.03 | ||||
φ(.)p(.) | 1.93 | 0.24 | 0.66 | 0.03 | 0.66 | 0.03 | 0.0d | 0.69 | 0.60 | 0.06 | ||
Dixiphia pipra | φ(2./.)p(.) | 173/76 | 0.0 | 0.52 | 0.41 | 0.11 | 0.63 | 0.05 | ||||
φ(.)p(.) | 0.18 | 0.48 | 0.60 | 0.04 | 0.60 | 0.04 | 0.0 | 0.73 | 0.52 | 0.09 | ||
Vireonidae | ||||||||||||
Hylophilus ochraceiceps | φ(.)p(.) | 53/25 | 0.0 | 0.75 | 0.68 | 0.07 | 0.68 | 0.07 | ||||
Troglodytidae | ||||||||||||
Henicorhina leucosticta | φ(.)p(.) | 66/31 | 0.0 | 0.70 | 0.80 | 0.06 | 0.80 | 0.06 | 0.0 | 0.73 | 0.80 | 0.15 |
Microcerculus marginatus | φ(.)p(.) | 47/39 | 0.0 | 0.56 | 0.51 | 0.07 | 0.51 | 0.07 | 0.0 | 0.72 | 0.50 | 0.11 |
Turdidae | ||||||||||||
Turdus albicollis | φ(.)p(.) | 97/72 | 0.0 | 0.69 | 0.66 | 0.04 | 0.66 | 0.04 | 0.0 | 0.69 | 0.57 | 0.08 |
Cardinalidae | ||||||||||||
Habia rubica | φ(.)p(.) | 52/29 | 0.0 | 0.74 | 0.64 | 0.07 | 0.64 | 0.07 | 0.0 | 0.76 | 0.65 | 0.12 |
Cyanocompsa cyanoides | φ(.)p(.) | 59/38 | 0.0 | 0.56 | 0.43 | 0.06 | 0.43 | 0.06 | 0.0 | 0.71 | 0.50 | 0.12 |
Results are based on the first six years of data (2001–2006; see [8]) and for the full 12 years. Competitive models (ΔAICc<2.0) are ordered by AICc rankings for the full 12-year results; corresponding results from the reduced data set of 2006 follow that ranking (estimates for some species were not calculated for the reduced data set). Estimates are shown for both the first (φ1) and subsequent capture periods [φ2, i.e., TSM models, e.g. φ(2./.)p(.)] for the full data set (2001–2012) but only φ2 for the reduced set (2001–2006 data).
I/R - number of individuals captured/number of recaptures (excluding individuals only captured during the final sample) over the 12-year period.
ΔAICc - differences in AICc.
wi - relative strength (weight) of evidence for selected models.
Model included p(t) rather than p(.).