| Literature DB >> 33117543 |
Eveling A Tavera1,2,3, Glenn E Stauffer4, David B Lank1, Ronald C Ydenberg1.
Abstract
BACKGROUND: Age at maturity and the timing of first breeding are important life history traits. Most small shorebird species mature and breed as 'yearlings', but have lower reproductive success than adults. In some species, yearlings may defer northward migration and remain in non-breeding regions ('oversummering') until they reach 2 years of age. Some adults also oversummer. Oversummering would be favoured by natural selection if survival were as a result raised sufficiently to compensate for the missed breeding opportunity. Several thousand Semipalmated Sandpipers (Calidris pusilla) spend the non-breeding period at Paracas, Perú, including individuals with long bills (likely from eastern Arctic breeding populations ~ 8000 km distant) and short bills (likely from western Arctic breeding populations, up to 11,000 km distant), with short-billed birds more likely to oversummer. We tested the prediction that oversummering birds have higher survival than migrants, and that the magnitude of this higher survival for oversummering birds is enough to compensate for their lost breeding season.Entities:
Keywords: Calidris pusilla; Distance-dependant; Migratory strategy; Multi-state mark-recapture model; Oversummering; Paracas; Perú; Shorebirds; Survivorship
Year: 2020 PMID: 33117543 PMCID: PMC7590707 DOI: 10.1186/s40462-020-00226-6
Source DB: PubMed Journal: Mov Ecol ISSN: 2051-3933 Impact factor: 3.600
Fig. 1Location of the study site, La Aguada Beach at Paracas National Reserve, Department of Ica, Perú
Fig. 2State transitions for Semipalmated Sandpipers at Paracas, Perú. Solid arrows denote compulsory transitions, and dashed transitions denote probalistic transitions estimated by the multi-state mark-recapture (MSMR) model. Sampling occasions (Winter 1, Winter2, Spring, Summer and Fall) are not of equal length The split of Winter 1 and Winter 2 made them all comparable with each other with equal lengths S{Winter} = S {Summer}. States are defined in the text: J (juvenile/yearling), A (adult), M1 (migrant yearling), and M2 (migrant adult)
Set of models fitted for Semipalmated Sandpiper survival analysis. There are twelve structures for annual survival (S), three structures for probability of resighting (p), and a single structure for transition probability (), not shown here. The 36 models are presented in ascending order by ΔAICc
| Survival structure | Detection structure | N | AICc | Δ AICc | weight | Deviance |
|---|---|---|---|---|---|---|
| S(age + strategy+age*strategy) | p(age + season+age.season) | 10 | 15,889.45 | 0.00 | 0.41 | 5554.57 |
| S(age + strategy) | p(age + season+age.season) | 9 | 15,891.20 | 1.74 | 0.17 | 5558.32 |
| S(age + season+strategy+age*strategy) | p(age + season+age.season) | 11 | 15,891.23 | 1.78 | 0.17 | 5554.34 |
| S(age + season+strategy) | p(age + season+age.season) | 10 | 15,892.54 | 3.08 | 0.09 | 5557.65 |
| S(age + season+strategy+age*season+age*strategy) | p(age + season+age.season) | 12 | 15,893.22 | 3.77 | 0.06 | 5554.31 |
| S(strategy) | p(age + season+age.season) | 8 | 15,894.13 | 4.68 | 0.04 | 5563.26 |
| S(age + season+strategy+age*season) | p(age + season+age.season) | 11 | 15,894.23 | 4.77 | 0.04 | 5557.33 |
| S(season+strategy) | p(age + season+age.season) | 9 | 15,894.93 | 5.48 | 0.03 | 5562.06 |
| S(age) | p(age + season+age.season) | 8 | 15,916.89 | 27.44 | 0.00 | 5586.02 |
| S(age + season) | p(age + season+age.season) | 9 | 15,918.79 | 29.33 | 0.00 | 5585.91 |
| S(season) | p(age + season+age.season) | 8 | 15,919.64 | 30.18 | 0.00 | 5588.76 |
| S(age + strategy+age*strategy) | p(season) | 9 | 15,920.33 | 30.87 | 0.00 | 5587.45 |
| S(age + season+age*season) | p(age + season+age.season) | 10 | 15,920.77 | 31.32 | 0.00 | 5585.88 |
| S(age + season+strategy+age*strategy) | p(season) | 10 | 15,922.14 | 32.68 | 0.00 | 5587.25 |
| S(age + season+strategy+age*season+age*strategy) | p(season) | 11 | 15,923.82 | 34.37 | 0.00 | 5586.92 |
| S(age + strategy) | p(season) | 8 | 15,926.58 | 37.13 | 0.00 | 5595.71 |
| S(age + season+strategy) | p(season) | 9 | 15,927.72 | 38.26 | 0.00 | 5594.84 |
| S(age + season+strategy+age*season) | p(season) | 10 | 15,928.41 | 38.95 | 0.00 | 5593.52 |
| S(strategy) | p(season) | 7 | 15,931.19 | 41.73 | 0.00 | 5602.32 |
| S(season+strategy) | p(season) | 8 | 15,931.55 | 42.10 | 0.00 | 5600.68 |
| S(age + season+strategy+age*season+age*strategy) | p(age + season) | 10 | 15,936.68 | 47.23 | 0.00 | 5601.79 |
| S(age + strategy+age*strategy) | p(age + season) | 8 | 15,937.69 | 48.24 | 0.00 | 5606.82 |
| S(age + season+strategy+age*strategy) | p(age + season) | 9 | 15,938.94 | 49.49 | 0.00 | 5606.06 |
| S(age + season+strategy+age*season) | p(age + season) | 9 | 15,939.24 | 49.79 | 0.00 | 5606.36 |
| S(age + strategy) | p(age + season) | 7 | 15,941.32 | 51.87 | 0.00 | 5612.45 |
| S(age + season+strategy) | p(age + season) | 8 | 15,942.31 | 52.86 | 0.00 | 5611.44 |
| S(strategy) | p(age + season) | 6 | 15,945.32 | 55.87 | 0.00 | 5618.46 |
| S(season+strategy) | p(age + season) | 7 | 15,945.72 | 56.27 | 0.00 | 5616.86 |
| S(age) | p(season) | 7 | 15,947.46 | 58.01 | 0.00 | 5618.59 |
| S(age + season) | p(season) | 8 | 15,949.38 | 59.93 | 0.00 | 5618.51 |
| S(age + season+age*season) | p(season) | 9 | 15,950.89 | 61.44 | 0.00 | 5618.01 |
| S(season) | p(season) | 7 | 15,951.94 | 62.49 | 0.00 | 5623.08 |
| S(age) | p(age + season) | 6 | 15,962.15 | 72.70 | 0.00 | 5635.29 |
| S(age + season+age*season) | p(age + season) | 8 | 15,963.11 | 73.66 | 0.00 | 5632.24 |
| S(age + season) | p(age + season) | 7 | 15,964.12 | 74.67 | 0.00 | 5635.25 |
| S(season) | p(age + season) | 6 | 15,965.74 | 76.29 | 0.00 | 5638.88 |
Seasonal (six-month) survival estimates (model averaged) for juvenile/yearlings (J) and adults (A) during Winter (October to March), Summer (April to September) and migration seasons. UCL/LCL = Upper/Lower 95% Confidence Limits
| State | Survival estimate | 95%LCI | 95%UCL |
|---|---|---|---|
| 0.829 | 0.643 | 0.929 | |
| 0.810 | 0.701 | 0.885 | |
| 0.904 | 0.838 | 0.945 | |
| 0.894 | 0.839 | 0.932 | |
| 0.670 | 0.518 | 0.794 | |
| 0.679 | 0.625 | 0.728 |
Fig. 3Seasonal (six-month) survivorship estimates of migrant and oversummering Semipalmated Sandpiper adults (left) and yearlings (right). Vertical lines are 95% confidence intervals
Detection probabilities (model averaged) of juveniles and adults in the (six-month) Winter (October to March) and Summer (April to September) seasons UCL/LCL Upper/Lower Confidence Limits (95%)
| STATE | Probability | LCL95% | UCL95% |
|---|---|---|---|
| 0.594 | 0.489 | 0.691 | |
| 0.171 | 0.171 | 0.268 | |
| 0.444 | 0.424 | 0.464 | |
| 0.390 | 0.372 | 0.409 |
Fig. 4Calculated survival of migrant yearling Semipalmated Sandpipers at Paracas, in relation to culmen length (mm). Method described in the text. Longer culmens are associated with eastern breeding populations and shorter migration distance. Oversummering survival adjusted to 0.81 (upper line), 0.87 (middle line), or 0.93 (lower line)
The number of sampling occasions in which birds marked in each year were (re-) encountered, ranging from 1 (= initial capture only), to 16 (includes initial capture). A total of 1963 were marked, of which 855 (43.6%) were encountered only during the sampling period when intially captured
| Year | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | 11 | 12 | 13 | 14 | 15 | 16 | Total |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 309 | 247 | 119 | 96 | 71 | 48 | 20 | 24 | 19 | 18 | 6 | 9 | 4 | 2 | 1 | 1 | 994 | |
| 196 | 100 | 54 | 32 | 20 | 16 | 7 | 10 | 4 | 4 | 2 | . | . | . | . | . | 445 | |
| 117 | 38 | 25 | 11 | 7 | 5 | 5 | 1 | 1 | . | . | . | . | . | . | . | 210 | |
| 68 | 38 | 14 | 12 | 6 | 7 | 4 | . | . | . | . | . | . | . | . | . | 149 | |
| 165 | . | . | . | . | . | . | . | . | . | . | . | . | . | . | . | 165 | |
| 855 | 423 | 212 | 151 | 104 | 76 | 36 | 35 | 24 | 22 | 8 | 9 | 4 | 2 | 1 | 1 | 1963 |
Mean number of sampling occasions and mean number of years in which individually-marked Semipalmated Sandpipers were subsequently re-encountered at Paracas, Perú, both by year birds were initially marked
| No. sampling occasions | Number of years | ||||||
|---|---|---|---|---|---|---|---|
| Mean | SD | Range | Mean | SD | Range | N | |
| 2.17 | 2.62 | 1–15 | 1.14 | 1.23 | 1–5 | 994 | |
| 1.49 | 2.04 | 1–10 | 0.82 | 0.98 | 1–4 | 445 | |
| 1.04 | 1.61 | 1–8 | 0.54 | 0.83 | 1–3 | 210 | |
| 1.24 | 1.62 | 1–6 | 0.40 | 0.88 | 1–2 | 149 | |
| 0 | 0 | 0 | 0 | – | – | 165 | |
| 1.64 | 2.31 | 15 | 0.85 | 1.09 | 1–5 | 1963 | |
Calculations of the survival of migrant Semipalmated Sandpipers at Paracas in each culmen length size class. For example, survival in the 17 mm culmen length size class is 0.710. These constitute 23% of the birds at Paracas. We estimate using the above procedure that 57% are migrants, so 43% oversummer. Oversummer survival is 0.81. Therefore, if overall survival of the size class is 0.710, migrant survival is 0.635, and oversummering gives a survival advantage of 18%
| Culmen (mm) | Proportion | Survival | Prop. (migrants) | Prop. (oversummer) | Migrant survival | Survival advantage |
|---|---|---|---|---|---|---|
| 15.0 | 0.01 | 0.720 | 0.15 | 0.85 | 0.207 | 0.60 |
| 16.0 | 0.06 | 0.715 | 0.29 | 0.71 | 0.482 | 0.33 |
| 17.0 | 0.23 | 0.710 | 0.57 | 0.43 | 0.635 | 0.18 |
| 18.0 | 0.31 | 0.705 | 0.75 | 0.25 | 0.671 | 0.14 |
| 19.0 | 0.23 | 0.701 | 0.84 | 0.16 | 0.680 | 0.13 |
| 20.0 | 0.09 | 0.696 | 0.88 | 0.12 | 0.680 | 0.13 |
| 21.0 | 0.05 | 0.691 | 0.92 | 0.08 | 0.681 | 0.13 |
| 22.0 | 0.01 | 0.686 | 0.96 | 0.04 | 0.681 | 0.13 |
| 23.0 | 0.01 | 0.681 | 1.00 | 0.00 | 0.681 | 0.13 |