| Literature DB >> 35428801 |
Clare E Holleley1, Alice C Grieve2, Alicia Grealy2,3, Iliana Medina4, Naomi E Langmore5.
Abstract
Defences of hosts against brood parasitic cuckoos include detection and ejection of cuckoo eggs from the nest. Ejection behaviour often involves puncturing the cuckoo egg, which is predicted to drive the evolution of thicker eggshells in cuckoos that parasitise such hosts. Here we test this prediction in four Australian cuckoo species and their hosts, using Hall-effect magnetic-inference to directly estimate eggshell thickness in parasitised clutches. In Australia, hosts that build cup-shaped nests are generally adept at ejecting cuckoo eggs, whereas hosts that build dome-shaped nests mostly accept foreign eggs. We analysed two datasets: a small sample of hosts with known egg ejection rates and a broader sample of hosts where egg ejection behaviour was inferred based on nest type (dome or cup). Contrary to predictions, cuckoos that exploit dome-nesting hosts (acceptor hosts) had significantly thicker eggshells relative to their hosts than cuckoos that exploit cup-nesting hosts (ejector hosts). No difference in eggshell thicknesses was observed in the smaller sample of hosts with known egg ejection rates, probably due to lack of power. Overall cuckoo eggshell thickness did not deviate from the expected avian relationship between eggshell thickness and egg length estimated from 74 bird species. Our results do not support the hypothesis that thicker eggshells have evolved in response to host ejection behaviour in Australian cuckoos, but are consistent with the hypothesis that thicker eggshells have evolved to reduce the risk of breakage when eggs are dropped into dome nests.Entities:
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Year: 2022 PMID: 35428801 PMCID: PMC9012832 DOI: 10.1038/s41598-022-09872-9
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.996
Figure 1The ratio of normalised eggshell thickness between cuckoos and their ejector versus acceptor hosts. (A) In the smaller sample size dataset that includes only hosts with known egg ejection rates, there is no significant difference in the cuckoo:host ratio of eggshell thickness between acceptors and ejectors at either point measured (apex: F1,1.98 = 2.31, P = 0.27; meridian: F1,5.6 = 0.99, P = 0.36). (B) When all hosts are considered and ejection behaviour is inferred from nest type, cuckoos that exploit acceptor hosts have thicker eggshells relative to their hosts than cuckoos that exploit ejectors, at both the apex (F1,12.47 = 7.72, P = 0.02) and the meridian of the egg (F1,14.32 = 8.86, P = 0.01).
Figure 2Eggshell thickness of cuckoos (orange) and their hosts (blue). Eggshell thickness was measured at two points on the egg: (A) the meridian of the egg, which is the circumference around the widest part of the egg and (B) the apex of the egg, which is the most conical end opposite the air sac. Eggshell thickness was normalised for interspecies comparisons by dividing the mean eggshell thickness of each egg by its length. The total eggshell thickness distribution is shown as black dots (Supplementary data file 1). Box plots are the median, interquartile range (Q1–Q3) and range (min–max). Raw data prior to normalisation are displayed in Fig. S3.
Figure 3Eggshell thickness as a function of egg length in avian species. Eggshell thickness was measured at two points on the egg: (A) the meridian of the egg, which is the circumference around the widest part of the egg (N = 73) and (B) the apex of the egg, which is the most conical end opposite the air sac (N = 59). Linear regression was conducted on species that do not employ a brood parasitic reproductive strategy (circles). Brood parasitic cuckoos were plotted separately (filled black markers). Cuckoo species that parasitise acceptor hosts without egg ejection (black triangles) and cuckoo species that exploit egg-ejecting hosts (black diamonds) fell within the 95% confidence limit (grey shaded area) predicted for non-parasitic species. Figures of residuals when using phylogenetic correction are presented in supplementary material (Figs. S5 and S6).
Characteristics of Australian cuckoo eggs and the eggs of their hosts used in this study. Summary statistics for morphological egg measurements, details of host species, and the rates of cuckoo egg ejection are reported for experimental, non-mimetic model eggs.
| Cuckoo species | Mass (mg) ± SD | Length (mm) ± SD | Breadth (mm) ± SD | Apex thickness (um) ± SD | Meridian thickness (um) ± SD | Host species | Mass (mg) ± SD | Length (mm) ± SD | Breadth (mm) ± SD | Apex thickness (um) ± SD | Meridian thickness (um) ± SD | Nest type | Ejection behaviour | Ejection rate | References | ||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 3 | 79.33 ± 7.37 | 17.53 ± 0.19 | 12.00 ± 0.53 | 80.73 ± 5.27 | 86.18 ± 4.49 | 2 | 71 ± 9.85 | 20.05 ± 5.92 | 14.57 ± 3.82 | 62.53 ± 1.70 | 79.18 ± 5.26 | Dome/Closed | Acceptor | 10% | Langmore et al.[ | ||
| 2 | 83.5 ± 3.61 | 16.96 ± 1.16 | 11.86 ± 0.18 | 82.43 ± 3.42 | 98.04 ± 6.66 | 2 | 74 ± 0 | 17.25 ± 1.06 | 13.08 ± 0.24 | 78.03 ± 6.72 | 70.76 ± 3.31 | Dome/Closed | Acceptor | 0% | Langmore et al.[ | ||
| 2 | 86.5 ± 2.12 | 17.54 ± 0.82 | 12.40 ± 0.54 | 89.54 ± 12.15 | 101.39 ± 10.90 | 2 | 94 ± 7.07 | 21.42 ± 3.90 | 14.95 ± 3.08 | 81.46 ± 0.43 | 101.52 ± 0.27 | Dome/Closed | No Data | – | |||
| 3 | 85.0 ± 3.61 | 24.44 ± 78.92 | 17.46 ± 5.89 | 80.62 ± 11.69 | 104.51 ± 15.29 | 1 | 75 | 16.19 | 11.67 | 77.81 | 95.85 | Dome/Closed | Acceptor | 12.50% | Langmore et al.[ | ||
| 6 | 88.50 ± 5.89 | 18.67 ± 2.63 | 13.08 ± 2.56 | 88.16 ± 12.28 | 92.51 ± 6.95 | 10 | 70.90 ± 4.79 | 19.32 ± 4.02 | 13.75 ± 2.89 | 78.71 ± 11.56 | 80.65 ± 6.97 | Dome/Closed | Acceptor | 10.60% | Langmore et al.[ | ||
| Mean | 85.14 ± 3.40 | 19.09 ± 2.77 | 13.18 ± 2.14 | 81.92 ± 6.94 | 96.05 ± 6.63 | ||||||||||||
| 12 | 82.21 ± 7.35 | 19.33 ± 4.98 | 13.57 ± 3.23 | 79.33 ± 18.09 | 78.57 ± 9.48 | 7 | 69 ± 7.79 | 20.45 ± 6.03 | 14.61 ± 3.66 | 64.88 ± 9.13 | 72.91 ± 5.73 | Dome/Closed | Acceptor | 10% | Langmore et al.[ | ||
| 2 | 70.50 ± 0.71 | 17.29 ± 0.18 | 12.28 ± 0.41 | 65.07 ± 1.81 | 68.85 ± 3.24 | 3 | 56.50 ± 4.36 | 25.24 ± 8.01 | 17.95 ± 5.51 | 61.65 ± 10.87 | 69.65 ± 4.40 | Dome/Closed | No Data | – | |||
| 7 | 86.21 ± 11.46 | 18.14 ± 0.71 | 12.66 ± 0.39 | 72.46 ± 8.66 | 78.36 ± 10.30 | 4 | 67.71 ± 5.79 | 23.40 ± 5.43 | 16.84 ± 3.81 | 61.06 ± 8.90 | 70.54 ± 7.10 | Dome/Closed | Acceptor | 12.50% | Langmore et al.[ | ||
| 1 | 83 | 17.21 | 12.66 | NA | 81.7 | 1 | 84 | 17.49 | 12.97 | 55.93 | 81.51 | Dome/Closed | Acceptor | 10.60% | Langmore et al.[ | ||
| Mean | 80.45 ± 6.87 | 17.99 ± 0.99 | 12.79 ± 0.55 | 72.29 ± 7.13 | 76.87 ± 5.56 | ||||||||||||
| 2 | 199.50 ± 12.02 | 23.20 ± 0.00 | 17.05 ± 0.47 | 100.55 ± 3.37 | 109.35 ± 5.61 | 2 | 215.00 ± 4.95 | 17.10 ± 1.99 | 12.11 ± 2.12 | 106 | 113.58 ± 6.93 | Cup/Open | No Data | – | |||
| 3 | 238.33 ± 44.77 | 24.65 ± 0.51 | 17.62 ± 0.15 | 104.35 ± 27.80 | 115.69 ± 18.64 | 2 | 428.50 ± 30.41 | 28.12 ± 3.26 | 20.70 ± 2.84 | 150.09 | 144.76 | Cup/Open | Ejector | 42.90% | Langmore et al.[ | ||
| 2 | 204.00 ± 24.04 | 24.17 ± 0.10 | 16.88 ± 0.45 | 89.02 | 103.03 | 1 | 139 | 30.93 | 21.23 | 81.92 | 100.73 | Cup/Open | No Data | – | |||
| 1 | 240 | 24.51 | 17.84 | 104.03 | 116.38 | 3 | 312.67 ± 81.77 | 20.46 ± 4.75 | 14.89 ± 3.34 | 148.30 ± 36.94 | 138.64 ± 4.85 | Cup/Open | Ejector | * | Landstrom et al.[ | ||
| 3 | 242.33 ± 7.51 | 24.23 ± 1.42 | 17.52 ± 0.30 | 88.40 ± 15.00 | 122.44 ± 6.89 | 2 | 105.50 ± 7.78 | 17.82 ± 0.33 | 13.02 ± 0.35 | 82.59 ± 9.76 | 93.81 ± 11.46 | Cup/Open | Ejector | * | Starling et al.[ | ||
| 2 | 221.00 ± 4.24 | 23.72 ± 0.14 | 16.99 ± 0.26 | 78.23 ± 3.20 | 112.32 ± 4.82 | 2 | 108.50 ± 20.51 | 17.77 ± 1.17 | 12.95 ± 1.25 | 76.36 ± 12.52 | 94.15 ± 10.41 | Cup/Open | No Data | – | |||
| 2 | 241.00 ± 35.36 | 24.45 ± 0.40 | 17.13 ± 1.43 | 91.84 ± 1.23 | 124.62 ± 4.29 | 2 | 170.00 ± 7.07 | 19.80 ± 2.26 | 15.27 ± 1.34 | 115.87 ± 23.35 | 115.78 ± 5.80 | Cup/Open | No Data | – | |||
| 2 | 231.00 ± 19.80 | 20.63 ± 5.08 | 8.77 ± 10.81 | 88.47 ± 4.94 | 114.72 ± 4.28 | 2 | 107.50 ± 6.36 | 27.17 ± 3.88 | 19.35 ± 1.84 | 70 | 81.40 ± 1.6 | Cup/Open | No Data | – | |||
| 3 | 244.00 ± 21.79 | 27.10 ± 4.79 | 19.68 ± 3.80 | 95.23 ± 14.67 | 119.92 ± 11.30 | 1 | 104 | 16.8 | 11.87 | NA | 101.94 | Cup/Open | No Data | – | |||
| 1 | 179 | 22.51 | 17.03 | 87.39 | NA | 1 | 94 | 16.24 | 12.66 | 67.63 | 87.87 | Cup/Open | No Data | – | |||
| 1 | 239 | 24.02 | 18.52 | 107.29 | 116.28 | 1 | 113 | 19.19 | 14.06 | NA | 103.7 | Cup/Open | No Data | – | |||
| 2 | 197.50 ± 30.41 | 22.72 ± 0.57 | 16.81 ± 0.49 | 90.65 ± 18.01 | 117.75 ± 7.02 | 2 | 120.00 ± 18.38 | 24.55 ± 11.07 | 16.84 ± 6.15 | 93.00 ± 17.73 | 98.18 ± 11.65 | Cup/Open | Ejector | 36% | Landstrom et al.[ | ||
| Mean | 223.06 ± 22.33 | 23.83 ± 1.54 | 16.82 ± 2.67 | 93.79 ± 8.65 | 115.68 ± 6.01 | ||||||||||||
| 6 | 621.43 ± 100.30 | 31.02 ± 6.15 | 22.16 ± 4.53 | 158.43 ± 12.76 | 165.85 ± 19.19 | 6 | 273.13 ± 25.24 | 27.14 ± 6.06 | 19.84 ± 4.44 | 126.19 ± 23.69 | 129.38 ± 8.99 | Cup/Open | No Data | – | |||
| 6 | 683.33 ± 35.12 | 31.20 ± 6.30 | 21.70 ± 4.61 | 158.89 ± 9.16 | 171.15 ± 11.97 | 5 | 429.80 ± 37.82 | 26.50 ± 7.83 | 18.89 ± 5.56 | 134.64 ± 15.57 | 146.50 ± 10.96 | Cup/Open | Ejector | 38% 4% 42.9% | Abernathy[ Abernathy et al.[ Langmore et al.[ | ||
| 7 | 719.57 ± 55.21 | 32.29 ± 6.89 | 22.66 ± 4.73 | 163.31 ± 11.85 | 169.66 ± 6.52 | 7 | 390.14 ± 34.13 | 23.47 + /0 5.79 | 17.02 ± 4.25 | 126.44 ± 6.66 | 144.43 ± 4.90 | Cup/Open | Ejector | 91% 89% | Abernathy[ Abernathy et al.[ | ||
| 6 | 725.67 ± 78.74 | 34.56 ± 1.22 | 24.82 ± 1.07 | 152.55 ± 12.66 | 165.22 ± 6.52 | 7 | 512.86 ± 13.67 | 22.69 ± 7.05 | 16.57 ± 4.74 | 148.93 ± 21.46 | 154.02 ± 4.13 | Cup/Open | No Data | – | |||
| Mean | 687.5 ± 47.85 | 32.27 ± 1.63 | 22.84 ± 1.38 | 158.30 ± 4.42 | 167.97 ± 2.89 |
*For these hosts, rates of egg ejection were unknown, but egg ejection behaviour by hosts could be inferred from quantitative analyses revealing that the cuckoo eggs are near perfect mimics of the host eggs, suggesting that the cuckoos have been subject to strong selection for egg mimicry through host egg ejection[54,72].
Egg size and eggshell thickness of bird species from 12 avian orders and 34 families.
| Order | Family | Common name | Scientific name | Egg | Length (mm) | Width (mm) | Meridian | Mean meridian thickness (µM) | Apex | Mean apex thickness (µM) | Data source |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Accipitriformes | Accipitridae | Wedge-tailed eagle | 3 | 70.4 | 63.0 | 3 | 629.58 | 3 | 562.35 | This study | |
| Accipitriformes | Accipitridae | Little eagle | 3 | 55.2 | 42.8 | 3 | 409.39 | 3 | 373.12 | This study | |
| Accipitriformes | Pandionidae | Eastern osprey | 2 | 62.6 | 45.9 | 2 | 641.17 | 2 | 665.69 | This study | |
| Anseriformes | Anatidae | Wood duck | 39 | 49.9 | 38.0 | 39 | 326.00 | 38 | 120.00 | Peterson et al.[ | |
| Anseriformes | Anatidae | Mallard | 2 | 56.7 | 40.9 | 2 | 339.00 | 2 | 337.00 | Peterson et al.[ | |
| Caprimulgiformes | Apodidae | Australian swiftlet | 1 | 21.7 | 13.0 | 1 | 103.75 | 1 | 115.86 | This study | |
| Charadriiformes | Burhinidae | Beach stone-curlew | 1 | 62.0 | 41.3 | 1 | 397.66 | 0 | NA | This study | |
| Charadriiformes | Charadriidae | Western snowy plover | 35 | 30.7 | 22.3 | 34 | 165.00 | 27 | 165.00 | Peterson et al.[ | |
| Charadriiformes | Charadriidae | Red-kneed dotterel | 1 | 29.7 | 23.0 | 1 | 184.34 | 0 | NA | This study | |
| Charadriiformes | Charadriidae | Inland dotterel | 1 | 37.9 | 26.7 | 1 | 235.66 | 1 | 201.11 | This study | |
| Charadriiformes | Laridae | Black noddy | 2 | 47.4 | 32.9 | 1 | 268.63 | 2 | 247.68 | This study | |
| Charadriiformes | Laridae | Caspian tern | 62 | 63.3 | 43.8 | 62 | 329.00 | 60 | 303.00 | Peterson et al.[ | |
| Charadriiformes | Laridae | California gull | 175 | 65.0 | 45.3 | 175 | 352.00 | 162 | 348.00 | Peterson et al.[ | |
| Charadriiformes | Laridae | Bridled tern | 1 | 46.5 | 33.0 | 1 | 298.09 | 1 | 586.47 | This study | |
| Charadriiformes | Laridae | Black skimmer | 11 | 47.8 | 34.6 | 11 | 247.00 | 11 | 226.00 | Peterson et al.[ | |
| Charadriiformes | Laridae | Roseate tern | 2 | 40.5 | 28.1 | 2 | 246.85 | 2 | 404.55 | This study | |
| Charadriiformes | Laridae | Forster's tern | 1103 | 42.8 | 30.1 | 1085 | 203.00 | 946 | 194.00 | Peterson et al.[ | |
| Charadriiformes | Laridae | California least tern | 340 | 30.7 | 22.4 | 332 | 144.00 | 249 | 140.00 | Peterson et al.[ | |
| Charadriiformes | Recurvirostridae | Black-necked stilt | 204 | 43.3 | 31.0 | 201 | 217.00 | 179 | 204.00 | Peterson et al.[ | |
| Charadriiformes | Recurvirostridae | American avocet | 844 | 49.2 | 34.1 | 843 | 242.00 | 773 | 226.00 | Peterson et al.[ | |
| Columbiformes | Columbidae | Superb fruit-dove | 1 | 33.4 | 23.4 | 1 | 185.22 | 1 | 155.09 | This study | |
| Falconiformes | Falconidae | Brown falcon | 1 | 48.6 | 40.3 | 1 | 438.51 | 1 | 395.23 | This study | |
| Falconiformes | Falconidae | Nankeen kestrel | 1 | 39.4 | 28.2 | 1 | 290.03 | 1 | 249.01 | This study | |
| Galliformes | Phasianidae | Stubble quail | 1 | 31.2 | 22.5 | 1 | 286.75 | 0 | NA | This study | |
| Galliformes | Phasianidae | King quail | 1 | 32.4 | 24.5 | 1 | 162.06 | 1 | 166.01 | This study | |
| Galliformes | Phasianidae | Brown quail | 1 | 29.8 | 24.5 | 1 | 325.67 | 0 | NA | This study | |
| Gruiformes | Rallidae | Lewin's rail | 2 | 35.6 | 26.8 | 2 | 207.31 | 2 | 174.61 | This study | |
| Passeriformes | Acanthizidae | Yellow-rumped thornbill | 10 | 19.7 | 14.2 | 10 | 75.74 | 7 | 64.98 | This study | |
| Passeriformes | Acanthizidae | Striated thornbill | 2 | 26.2 | 18.7 | 2 | 66.01 | 1 | 69.91 | This study | |
| Passeriformes | Acanthizidae | Brown thornbill | 7 | 22.9 | 16.6 | 6 | 69.18 | 5 | 64.406 | This study | |
| Passeriformes | Acanthizidae | Buff-rumped thornbill | 2 | 17.3 | 13.1 | 2 | 70.76 | 2 | 78.03 | This study | |
| Passeriformes | Acanthizidae | Southern whiteface | 2 | 21.4 | 15.0 | 2 | 101.52 | 1 | 81.77 | This study | |
| Passeriformes | Acanthizidae | Weebill | 1 | 16.0 | 11.8 | 1 | 82.06 | 1 | 84.69 | This study | |
| Passeriformes | Artamidae | White-breasted woodswallow | 2 | 18.5 | 13.6 | 2 | 118.48 | 0 | NA | This study | |
| Passeriformes | Campephagidae | Ground cuckoo-shrike | 1 | 31.7 | 24.0 | 1 | 221.91 | 0 | NA | This study | |
| Passeriformes | Campephagidae | Black-faced cuckoo-shrike | 1 | 32.5 | 23.8 | 1 | 160.94 | 1 | 178.38 | This study | |
| Passeriformes | Campephagidae | Cicadabird | 1 | 31.3 | 21.4 | 1 | 158.59 | 0 | NA | This study | |
| Passeriformes | Cisticolidae | Golden-headed cisticola | 1 | 15.8 | 11.4 | 1 | 90.85 | 0 | NA | This study | |
| Passeriformes | Climacteridae | Brown treecreeper | 1 | 22.5 | 18.6 | 1 | 218.93 | 0 | NA | This study | |
| Passeriformes | Corcoracidae | White-winged chough | 1 | 42.5 | 28.0 | 1 | 235.24 | 1 | 255.66 | This study | |
| Passeriformes | Cracticidae | Australian magpie | 1 | 41.1 | 28.2 | 1 | 214.08 | 1 | 201.65 | This study | |
| Passeriformes | Cuculidae | Horsfield’s bronze-cuckoo | 18 | 19.2 | 13.4 | 18 | 95.27 | 18 | 83.94 | This study | |
| Passeriformes | Cuculidae | Shining bronze-cuckoo | 24 | 18.7 | 13.1 | 21 | 77.68 | 23 | 78.27 | This study | |
| Passeriformes | Cuculidae | Eastern/Pacific koel | 27 | 32.2 | 22.8 | 22 | 168.30 | 26 | 158.50 | This study | |
| Passeriformes | Cuculidae | Pallid cuckoo | 24 | 24.0 | 16.8 | 20 | 116.48 | 23 | 94.22 | This study | |
| Passeriformes | Dicruridae | Spangled drongo | 2 | 28.6 | 21.4 | 2 | 151.89 | 2 | 297.32 | This study | |
| Passeriformes | Maluridae | Superb fairy-wren | 13 | 19.2 | 13.7 | 12 | 80.73 | 11 | 76.43 | This study | |
| Passeriformes | Meliphagidae | Spiny-cheeked honeyeater | 1 | 25.4 | 17.2 | 1 | 129.86 | 1 | 110.88 | This study | |
| Passeriformes | Meliphagidae | Red wattlebird | 2 | 28.1 | 20.7 | 2 | 144.76 | 1 | 150.09 | This study | |
| Passeriformes | Meliphagidae | Blue-faced honeyeater | 1 | 32.0 | 22.0 | 1 | 178.90 | 1 | 155.86 | This study | |
| Passeriformes | Meliphagidae | White-fronted chat | 1 | 17.6 | 12.3 | 1 | 68.51 | 0 | NA | This study | |
| Passeriformes | Meliphagidae | Yellow-throated miner | 3 | 22.7 | 16.9 | 4 | 137.85 | 1 | 121.49 | This study | |
| Passeriformes | Meliphagidae | Bell miner | 1 | 22.4 | 16.5 | 1 | 119.29 | 1 | 96.84 | This study | |
| Passeriformes | Meliphagidae | Black-headed honeyeater | 2 | 17.8 | 13.0 | 2 | 93.81 | 2 | 82.59 | This study | |
| Passeriformes | Meliphagidae | White-naped honeyeater | 2 | 17.8 | 13.0 | 2 | 94.16 | 2 | 76.36 | This study | |
| Passeriformes | Meliphagidae | Strong-billed honeyeater | 2 | 19.8 | 15.3 | 2 | 115.78 | 2 | 115.87 | This study | |
| Passeriformes | Meliphagidae | Helmeted friarbird | 2 | 30.9 | 22.2 | 2 | 186.91 | 2 | 148.42 | This study | |
| Passeriformes | Meliphagidae | Little friarbird | 6 | 26.3 | 13.0 | 5 | 125.99 | 5 | 129.50 | This study | |
| Passeriformes | Meliphagidae | Noisy friarbird | 5 | 26.5 | 18.9 | 5 | 146.50 | 5 | 134.64 | This study | |
| Passeriformes | Meliphagidae | White-cheeked honeyeater | 1 | 19.8 | 15.0 | 1 | 96.57 | 1 | 93.05 | This study | |
| Passeriformes | Meliphagidae | Fuscous honeyeater | 2 | 27.2 | 19.4 | 2 | 81.40 | 0 | NA | This study | |
| Passeriformes | Meliphagidae | Yellow-plumed honeyeater | 1 | 16.8 | 11.9 | 1 | 101.94 | 0 | NA | This study | |
| Passeriformes | Meliphagidae | Grey-fronted honeyeater | 1 | 16.2 | 12.7 | 1 | 87.87 | 1 | 67.63 | This study | |
| Passeriformes | Monarchidae | Magpie-lark | 7 | 23.5 | 17.0 | 7 | 144.43 | 7 | 126.44 | This study | |
| Passeriformes | Oriolidae | Yellow oriole | 1 | 31.7 | 22.7 | 1 | 168.40 | 1 | 172.91 | This study | |
| Passeriformes | Oriolidae | Australasian figbird | 6 | 23.5 | 17.3 | 6 | 153.66 | 6 | 150.47 | This study | |
| Passeriformes | Pachycephalidae | Golden whistler | 1 | 24.5 | 17.9 | 1 | 116.93 | 0 | NA | This study | |
| Passeriformes | Petroicidae | Eastern yellow robin | 1 | 21.5 | 16.4 | 1 | 104.90 | 1 | 75.60 | This study | |
| Passeriformes | Petroicidae | Grey-headed robin | 2 | 26.0 | 18.6 | 2 | 118.63 | 2 | 132.61 | This study | |
| Passeriformes | Petroicidae | Jacky winter | 1 | 19.2 | 14.1 | 1 | 103.70 | 0 | NA | This study | |
| Passeriformes | Petroicidae | Red-capped robin | 1 | 14.6 | 12.4 | 0 | NA | 1 | 74.23 | This study | |
| Passeriformes | Pomatostomidae | Chestnut-crowned babbler | 1 | 26.0 | 18.5 | 1 | 171.45 | 0 | NA | This study | |
| Passeriformes | Ptilonorhynchidae | Spotted bowerbird | 2 | 27.4 | 19.7 | 1 | 216.63 | 2 | 157.81 | This study | |
| Passeriformes | Rhipiduridae | Willie wagtail | 2 | 24.6 | 16.8 | 2 | 98.18 | 2 | 93.00 | This study | |
| Passeriformes | Turdidae | Eurasian blackbird | 1 | 29.5 | 21.0 | 1 | 194.97 | 1 | 224.69 | This study | |
| Pelecaniformes | Ardeidae | Great egret | 3 | 59.7 | 40.5 | 3 | 296.00 | 3 | 303.00 | Peterson et al.[ | |
| Psittaciformes | Psittaculidae | Scaly-breasted lorikeet | 1 | 25.8 | 20.9 | 1 | 184.32 | 1 | 151.62 | This study | |
| Suliformes | Phalacrocoracidae | Double-crested cormorant | 90 | 61.0 | 39.0 | 88 | 418.00 | 89 | 394.00 | Peterson et al.[ |
*Brood parasitic cuckoo species.
†Host species of the cuckoos in this study.