Abstract
Understanding wetland bird responses to landscape patterns is central for wetland management and bird conservation. This is particularly relevant on islands, where most of the global extinctions have occurred. In this study, we identified landscape patterns in wetlands on Cozumel Island that best explained abundance of birds grouped in 13 trophic guilds at 3 spatial scales (145, 300, and 850 m radius from count points). By using ordination techniques and generalized linear models we found a scale dependent dissimilarity between the use of extensive estuarine and small inland brackish wetlands. At finer spatial scales, abundance of birds in trophic guilds that mainly use estuarine or inland brackish wetlands was associated with the proportion of land cover types of the corresponding wetland type, whereas at the broadest spatial scale, connectivity of such land cover types was more important. Abundance of birds in trophic guilds that do not prefer any particular type of wetland did not show any relationship with landscape diversity nor connectivity of land cover types, but their abundance showed relationships with specific land cover types from both estuarine and inland brackish wetlands as well as with bordering wetland vegetation. We concluded that the presence of continuous extents of land cover types of both extensive estuarine and small inland brackish wetlands are important for the conservation of distinct wetland bird assemblages on Cozumel Island.
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Acknowledgements
This research was funded by the Fondo de Investigación Científica y Desarrollo Tecnológico de El Colegio de la Frontera Sur (Fideicomiso No. 784) and the National Council for Science and Technology (CONACYT) of Mexico through a postgraduate scholarship granted to JTA (406071). Idea Wild supplied some of the field equipment. We thank to the personnel of the FPMC (Cozumel Parks and Museums Foundation) and CONANP (National Commission for Natural Protected Areas) for the loan of boats, logistical support, and field assistance. We are grateful to D. Navarrete-Gutiérrez and O. Martínez-López for their help and advice to generate the geographical information and figures, and to M. Ruiz-Bruce-Taylor and two anonymous reviewers for their constructive comments. To T. Gonzáles-Gamboa, N. Rivas-Camo, G. Jorge-Lara, P. Sabido-Villanueva, and H. González-Cortés for their assistance during fieldwork.
Funding
This research was funded by the Fondo de Investigación Científica y Desarrollo Tecnológico de El Colegio de la Frontera Sur (Fideicomiso No. 784) and the National Council for Science and Technology (CONACYT) of Mexico through a postgraduate scholarship granted to JTA (406071). Idea Wild supplied field equipment.
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Appendix
Appendix
Trophic guild membership of bird species based on key food resources reported in literature and field observations in the wetlands of Cozumel Island. Abundance was based on the highest count obtained for each species in each one of the 40 surveyed points. Status: resident (R), reproductive resident with visiting populations on winter (Rw), transient (T), winter visitor (W), winter visitor with non-reproductive populations on summer (Ws). Coarse status: resident (R) and migratory (M).
Trophic guild | Species | Bird group | Abundance within the guild (%) | Status | Coarse status | References |
---|---|---|---|---|---|---|
Brackish omnivores (bO) | Dendrocygna autumnalis | Whistling-Ducks | 34.2 | R | R | |
Spatula discors | Ducks | 35.4 | W | M | Bellrose (1980), Rappole et al. (1983), Botero and Rusch (1994) | |
Porzana carolina | Rails | 0.9 | W | M | Webster (1964), Rundle and Sayre (1983), Rappole et al. (1983) | |
Porphyrio martinicus | Gallinules | 0.4 | R | R | ||
Gallinula galeata | Gallinules | 7.6 | R | R | Rappole et al. (1983) | |
Fulica americana | Coots | 21.4 | W | M | Rappole et al. (1983), McKnight and Hepp (1998), Villamanga et al. (2010) | |
Estuarine shoreline invertivores (eSI) | Charadrius wilsonia | Plovers | 20.1 | Rw | R | Rappole et al. (1983), Iribarne and Martínez (1999), Paulson (2005) |
Charadrius semipalmatus | Plovers | 63.8 | Rw | R | Baker and Baker (1973), Rappole et al. (1983), Smith and Nol (2000) | |
Arenaria interpres | Turnstones | 6.0 | Ws | M | ||
Calidris spp. (C. pusilla and C. mauri) | Sandpipers | 10.1 | W | M | ||
Brackish shoreline invertivores (bSI) | Laterallus ruber | Rails | 14.6 | R | R | Rappole et al. (1983) (Congener), del Hoyo et al. (1996) (Congener) |
Charadrius vociferus | Plovers | 52.1 | Rw | R | Brooks (1967), Rundle (1982), Rappole et al. (1983), Baldassarre and Fischer (1984), Fair et al. (1995) | |
Calidris melanotos | Sandpipers | 8.3 | T | M | Brooks (1967), Rappole et al. (1983), Holden and Cleeves (2002) | |
Tringa solitaria | Sandpipers | 25.0 | W | M | Bent (1929), Palmer (1967), Johnsgard (1981), Rappole et al. (1983), Moskoff (1995) | |
Shoreline invertivores (SI) | Pluvialis squatarola | Plovers | 13.7 | Ws | M | |
Calidris minutilla | Sandpipers | 41.6 | W | M | Baker and Baker (1973), Brooks (1967), Rappole et al. (1983), Paulson (2005) | |
Calidris fuscicollis | Sandpipers | 32.4 | T | M | Rappole et al. (1983), Beltzer (1991), Montalti et al. (2003), Hernández and Bala (2007) | |
Actitis macularius | Sandpipers | 12.3 | W | M | ||
Estuarine wading invertivores (eWI) | Tringa semipalmata | Sandpipers | 28.2 | Ws | M | Rappole et al. (1983), Paulson (2005), Castillo-Guerrero et al. (2009) |
Tringa melanoleuca | Sandpipers | 71.8 | W | M | ||
Brackish wading and pecking invertivores (bWPI) | Jacana spinosa | Jacanas | 96.2 | R | R | |
Phalaropus tricolor | Phalaropes | 2.5 | T | M | ||
Plegadis falcinellus | Ibises | 1.3 | T | M | Rappole et al. (1983), Acosta et al. (1996), Macías et al. (2004), Taylor and Taylor (2015) | |
Wading invertivores (WI) | Himantopus mexicanus | Stilts | 87.8 | R | R | |
Tringa flavipes | Sandpipers | 12.2 | W | M | Brooks (1967), Baker and Baker (1973), Rappole et al. (1983), Weber and Haig (1997), Paulson (2005) | |
Estuarine probing invertivores (ePI) | Numenius phaeopus | Curlews | 8.7 | T | M | |
Calidris himantopus | Sandpipers | 4.3 | W | M | Brooks (1967), Burton (1972), Baldassarre and Fischer (1984) | |
Limnodromus griseus | Dowitchers | 87.0 | Ws | M | Baker and Baker (1973), Rappole et al. (1983), Weber and Haig (1997) | |
Estuarine generalists (eG) | Rallus crepitans | Rails | 10.4 | R | R | |
Eudocimus albus | Ibises | 57.0 | R | R | ||
Platalea ajaja | Spoonbills | 32.6 | R | R | ||
Brackish generalists (bG) | Tachybaptus dominicus | Grebes | 75.6 | R | R | Howell and Webb (1995) |
Podilymbus podiceps | Grebes | 7.8 | W | M | Rappole et al. (1983) | |
Nyctanassa violacea | Herons | 16.7 | R | R | ||
Generalists (G) | Ixobrychus exilis | Herons | 4.8 | R | R | Rappole et al. (1983) |
Egretta caerulea | Herons | 29.0 | Rw | R | Wunderle (1981), Rappole et al. (1983), Miranda and Collazo (1997), Olmos et al. (2001) | |
Butorides virescens | Herons | 66.2 | R | R | ||
Estuarine shallow water piscivores (eSP) | Ardea herodias | Herons | 2.0 | Rw | R | |
Ardea alba | Herons | 8.8 | Rw | R | Rappole et al. (1983), Ramo and Busto (1993), Miranda and Collazo (1997) | |
Egretta thula | Herons | 34.6 | R | R | Rappole et al. (1983), Ramo and Busto (1993), Miranda and Collazo (1997) | |
Egretta tricolor | Herons | 40.4 | R | R | Rappole et al. (1983), Ramo and Busto (1993), Miranda and Collazo (1997) | |
Egretta rufescens | Herons | 10.2 | R | R | ||
Cochlearius cochlearius | Herons | 4.0 | R | R | ||
Estuarine deep water piscivores (eDP) | Mergus serrator | Mergansers | 1.1 | W | M | Rappole et al. (1983), del Hoyo et al. (2001), Bur et al. (2008) |
Phalacrocorax brasilianus | Cormorants | 59.3 | R | R | ||
Pelecanus occidentalis | Pelicans | 8.8 | R | R | ||
Pandion haliaetus | Ospreys | 13.2 | Rw | R | ||
Megaceryle alcyon | Kingfishers | 17.6 | W | M | ||
Brackish deep water piscivores (bDP) | Anhinga anhinga | Anhingas | 100.0 | R | R |
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Thompson-Ambriz, J., Moreno, C.E., Rangel-Salazar, J.L. et al. Multi-scale response of wetland bird assemblages to landscape patterns on a Neotropical island: when wetland type matters more than size. Wetlands Ecol Manage 28, 251–269 (2020). https://doi.org/10.1007/s11273-020-09711-6
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DOI: https://doi.org/10.1007/s11273-020-09711-6