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105 results for “Cormorants”
Double-crested Cormorant (Nannopterum auritum) nesting colony and environmental data in Biscayne National Park, Florida, USA (2009-2024)
Double-crested Cormorant (DCCO) nesting data were collected from colonies in Biscayne National Park (BISC) by the South Florida/Caribbean Inventory and Monitoring Network as part of the Colonial Nesting Birds vital sign monitoring program. Nesting data collected from 2010 to 2023 are included in this dataset. Salinity, chlorophyll, and ammonia data were acquired from sites monitored in the Surface Water Quality Monitoring Program managed by the Miami-Dade County Division of Environmental Management’s Department of Regulatory and Economic Resources (RER-DERM). Seagrass data were acquired from sites monitored by RER-DERM as a part of the Biscayne Bay Benthic Habitat Monitoring Program. Mangrove fish and epifauna data were acquired from the U.S. National Oceanic and Atmospheric Administration's (NOAA) Integrated Biscayne Bay Ecological Assessment and Monitoring Project (IBBEAM). Environmental data (salinity, chlorophyll, ammonia, seagrass, mangrove fish, and epifauna) were manipulated in order to examine the relationship between DCCO nesting trends and the BISC ecosystem. This data package is completed. Code included is pertinent to the methods described in "Assessment of ecosystem health in Biscayne National Park, Florida according to Double-crested Cormorant (Nannopterum auritum) nesting trends" by Taylor et al. 2025, currently submitted to and under review by Ecological Indicators.
Fig. 2 in Diet, Prey Selection and Biomass Consumption of the Great Cormorant (Phalacrocorax carbo) in Algeria
Fig. 2. Monthly variation of the biomass of consumed fish by the great cormorant in Beni Haroun Dam Lake in Algeria.
Figure 15 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 15. Sterna from Spectacled Cormorants Urile perspicillatus in the National Museum of Natural History, Washington, DC (USNM 19417); scale bars in mm (© J. Watanabe)
Figure 12 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 12. Femur and tarsometatarsi from Spectacled Cormorants Urile perspicillatus in the National Museum of Natural History, Washington, DC (USNM 17041 and USNM 19417); scale bars in mm (© J. Watanabe)
Figure 9 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 9. Osteological specimens of Spectacled Cormorant Urile perspicillatus in the National Museum of Science and Nature, Tsukuba Research Centre, Tsukuba, Japan (NSM PV 24191); note the differing scale for the ulna (right; both scale bars equal to 50 mm) (© J. Watanabe)
Figure 3 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 3 (top). Spectacled Cormorant Urile perspicillatus skin in the collection of the Zoological Institute of the Russian Academy of Sciences, St. Petersburg (ZISP 137178) (© V. Vysotsky) Figure 4 (right). Spectacled Cormorant Urile perspicillatus mount in the collection of the Zoological Institute of the Russian Academy of Sciences, St. Petersburg (ZISP 137179) (© V. Vysotsky) Figure 5 (below).Osteological specimens of Spectacled Cormorant Urile perspicillatus in the collection of the Zoological Institute of the Russian Academy of Sciences, St. Petersburg (various registration numbers and unregistered material); note that the carpometacarpus in the top right of the photograph has been reidentified to a different species since this photograph was taken (© V. Vysotsky)
Figure 14 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 14. Tibiotarsi from Spectacled Cormorants Urile perspicillatus in the National Museum of Natural History, Washington, DC (USNM 19417); scale bars in mm (© J. Watanabe)
Figure 11 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 11. Left and right coracoid, carpometacarpus, and ulna from Spectacled Cormorants Urile perspicillatus in the National Museum of Natural History, Washington, DC (USNM 17041 and USNM 19417); scale bars in mm (© J. Watanabe)
Figure 13 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 13. Tibiotarsi from Spectacled Cormorants Urile perspicillatus in the National Museum of Natural History, Washington, DC (USNM 17041); scale bars in mm (© J. Watanabe)
Figure 8 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 8. Unmounted skin of Spectacled Cormorant Urile perspicillatus in the Natural History Museum, Tring (NHMUK 1858.2.3.1) (J. Jackson, © Trustees of the Natural History Museum, London)
Figure 6 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 6 (left and below). Detailed photographs of Spectacled Cormorant Urile perspicillatus skull and mandible in the collection of the Zoological Institute of the Russian Academy of Sciences, St Petersburg (ZISP 1112) (© V. Vysotsky)
Figure 10 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 10. Humeri from Spectacled Cormorants Urile perspicillatus in the National Museum of Natural History, Washington, DC (USNM 17041 and USNM 19417); scale bars in mm (© J. Watanabe)
Figure 16 in Specimens of the extinct Spectacled Cormorant Urile perspicillatus
Figure 16 (above). Pelvic girdles from Spectacled Cormorants Urile perspicillatus in the National Museum of Natural History, Washington, DC (USNM 17041 and USNM 19417); scale bars in mm (© J. Watanabe) Figure 17 (right). Maxillae or rostra from Spectacled Cormorants Urile perspicillatus in the National Museum of Natural History, Washington, DC (USNM 17041 and USNM 19417); scale bars in mm (© J. Watanabe)
Figure 1 in Mammals under a colony of great cormorants: population structure and body condition of yellow-necked mice
Figure 1. Location of Zones A–E in the colony of great cormorants near Juodkrantė, West Lithuania, 2011–2013.
Figure 4 in Impact of overwintering cormorants (Phalacrocorax carbo) on springtail (Hexapoda: Collembola) communities of the Azov and Black Sea coastal forests
Figure 4. Relative total abundance, genus richness, and abundance of the different functional groups of springtails (abundance in impact sites/abundance in controls ± SE) in forests with active overwintering cormorant colonies (Black Sea) and abandoned forests (Azov Sea). Totabu: Total abundance, Genrich: Genus richness, Epied: Epiedaphic, Hemied: Hemiedaphic, Eued: Euedaphic, EMC: Euedaphic microorganism consumers, HMC: Hemiedaphic microorganism consumers, EPMC: Epiedaphic plant and microorganism consumers, EAMC: Epiedaphic animal and microorganism consumers. *: Statistically significant differences between the control and impact sites according to the Tukey HSD test.
Figure 2 in Impact of overwintering cormorants (Phalacrocorax carbo) on springtail (Hexapoda: Collembola) communities of the Azov and Black Sea coastal forests
Figure 2. Abundance of different functional groups of springtails (ind. m–2 ± SE, n = 2) at the control and impact sites of forests abandoned by cormorants (Azov Sea). Epied: Epiedaphic, Hemied: Hemiedaphic, Eued: Euedaphic, EMC: Euedaphic microorganism consumers, HMC: Hemiedaphic microorganism consumers, EPMC: Epiedaphic plant and microorganism consumers, EAMC: Epiedaphic animal and microorganism consumers. *: Statistically significant differences between the control and impact sites according to the Tukey HSD test.
Figure 3 in Impact of overwintering cormorants (Phalacrocorax carbo) on springtail (Hexapoda: Collembola) communities of the Azov and Black Sea coastal forests
Figure 3. PCA of the relationship between springtail genera abundance (shown as gray lines and diamond-shaped symbols) and edaphic parameters (black lines and dots). AOC impact: Impact sites with active overwintering colonies (Black Sea), AOC control: Control sites close to active overwintering colonies (Black Sea), AF impact: Impact sites in abandoned forests (Azov Sea), AF control: Control sites in abandoned forests (Azov Sea). 1) Mesaphorura, 2) Pseudachorutes, 3) Xenylla, 4) Folsomia gr. quadrioculata, 5) Parisotoma, 6) Isotomiella, 7) Cryptopygus, 8) Isotoma, 9) Lepidocyrtus, 10) Pseudosinella, 11) Entomobrya.
Figure 1 in Impact of overwintering cormorants (Phalacrocorax carbo) on springtail (Hexapoda: Collembola) communities of the Azov and Black Sea coastal forests
Figure 1. Abundance of different functional groups of springtails (ind. m–2 ± SE, n = 2 at the control and impact sites of forests with active overwintering cormorant colonies (Black Sea). Epied: Epiedaphic, Hemied: Hemiedaphic, Eued: Euedaphic, EMC: Euedaphic microorganism consumers, HMC: Hemiedaphic microorganism consumers, EPMC: Epiedaphic plant and microorganism consumers, EAMC: Epiedaphic animal and microorganism consumers. *: Statistically significant differences between the control and impact sites according to the Tukey HSD test.
Fig. 7 in Protozoal encephalitis associated with Sarcocystis calchasi and S. falcatula during an epizootic involving Brandt's cormorants (Phalacrocorax penicillatus) in coastal Southern California, USA
Fig. 7. Gel electrophoresis of the 28S PCR on the brain (B) and muscle (M) tissues from eight Brandt's cormorants submitted from Coastal Southern California. All eight birds demonstrate a band positive for sarcocystis species. C3 is brain from a pigeon with S. calchasi used as control tissue and SN is the S. neurona positive control.
Fig. 5 in Protozoal encephalitis associated with Sarcocystis calchasi and S. falcatula during an epizootic involving Brandt's cormorants (Phalacrocorax penicillatus) in coastal Southern California, USA
Fig. 5. Brain photomicrograph of cormorant No. 8, polyclonal IHC for S. falcatula and S. neurona. (A) Cerebellum exhibiting foci of dense protozoal immunopositivity, and (B) showing the large numbers of immunoreactive schizonts forming the foci. Sequencing revealed these are S. falcatula schizonts.
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