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Crystal Cove Marine Conservation Area Citizen Science Monitoring
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FIGURE 102 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 102. Dipterygonotus balteatus (Valenciennes 1830), Al Abdeh, 11 August 2017, AUBM (OS3931), Bariche & Fricke (2018).
FIGURE 109 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 109. Pseudupeneus prayensis (Cuvier 1829), Palm islands, December 2016, AUBM (OS3925), Crocetta & Bariche in Gerovasileiou et al. (2017).
FIGURE 86. Syngnathus abaster Risso 1827 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 86. Syngnathus abaster Risso 1827, Beirut, 28 April 2009 (female below) and 21 May 2011 (male above), AUBM (OS3836, OS3969).
FIGURE 107 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 107. Equulites popei (Whitley 1932), Tripoli, March 2016, AUBM (OS3920), Crocetta & Bariche in Gerovasileiou et al. (2017).
FIGURE 120 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 120. Sillago suezensis (Golani, Fricke & Tikochinski 2013), Beirut, 28 April 2009, AUBM (OS3832).
FIGURE 50 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 50. Pseudocaranx dentex (Bloch & Schneider 1801), Beirut, 8 December 2009, AUBM (OS3679).
FIGURE 59 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 59. Thorogobius ephippiatus (Lowe 1839), Tripoli, 2012, picture extracted from an underwater video.
FIGURE 13 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 13. Dalatias licha (Bonnaterre 1788), Bouar, 12 December 2015, photograph: Massoud Jean-Paul.
FIGURE 16 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 16. Taeniurops grabatus (Geoffroy St. Hilaire 1817), Tripoli, 4 April 2018, photograph: unknown (posted on local social media).
FIGURE 12 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 12. Centrophorus granulosus (Bloch & Schneider 1801), Batroun, 13 September 2017, photograph: Fatfat Samer.
FIGURE 9 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 9. Cetorhinus maximus (Gunnerus 1765), Tyre, 7 February 2006, photograph: unknown (posted on local social media).
FIGURE 103. Heniochus intermedius Steindachner 1893 in The marine ichthyofauna of Lebanon: an annotated checklist, history, biogeography, and conservation status
FIGURE 103. Heniochus intermedius Steindachner 1893, Palm Islands, 16 July 2011, AUBM (OS3779), Bariche (2012).
Data from: Evolution of movement rate increases the effectiveness of marine reserves for the conservation of pelagic fishes
Current debates about the efficacy of no-take marine reserves (MR) in protecting large pelagic fish such as tuna and sharks have usually not considered the evolutionary dimension of this issue, which emerges because the propensity to swim away from a given place, like any other biological trait, will probably vary in a heritable fashion among individuals. Here, based on spatially-explicit simulations, we investigated whether selection to remain in MRs to avoid higher fishing mortality can lead to the evolution of more philopatric fish. Our simulations, which covered a range of life histories among tuna species (skipjack tuna vs. Atlantic Bluefin tuna) and shark species (great white sharks vs. spiny dogfish) suggested that MRs were most effective at maintaining viable population sizes when movement distances were lowest. Decreased movement rate evolved following the establishment of marine reserves, and this evolution occurred more rapidly with higher fishing pressure. Evolutionary reductions in movement rate led to increases in within-reserve population sizes over the course of the 50 years following MR establishment, although this varied among life-histories, with skipjack responding fastest and great white sharks slowest. Our results suggest the evolution of decreased movement can augment the efficacy of marine reserves, especially for species, such as skipjack tuna, with relatively short generation times. Even when movement rates did not evolve substantially over 50 years (e.g., given long generation times or little heritable variation), marine reserves were an effective tool for the conservation of fish populations when mean movement rates were low or MRs were large.
FIGURE 2 in The reef fish assemblage of the Laje de Santos Marine State Park, Southwestern Atlantic: annotated checklist with comments on abundance, distribution, trophic structure, symbiotic associations, and conservation
FIGURE 2. Habitat types found at the Laje de Santos Marine State Park.
Supplementary material 1 from: Sabdono A, Lestari ES, Sibero MT (2022) Biogeographic assessment of Gorgonian-associated bacteria with antipathogenic Urinary Tract Infections (UTIs) in Karimunjawa Marine National Park, Java Sea, Indonesia. Nature Conservation 49: 137-151. https://doi.org/10.3897/natureconservation.49.84825
Tables S1–S3
Figure 1 from: Katsanevakis S, Mackelworth P, Coll M, Fraschetti S, Mačić V, Giakoumi S, Jones P, Levin N, Albano PG, Badalamenti F, Brennan R, Claudet J, Culibrk D, D'Anna G, Deidun A, Evagelopoulos A, García-Charton J, Goldsborough D, Holcer D, Jimenez C, Kark S, Sørensen T, Lazar B, Martin G, Mazaris A, Micheli F, Milner-Gulland E, Pipitone C, Portman M, Pranovi F, Rilov G, Smith R, Stelzenmüller V, Vogiatzakis I, Winters G (2017) Advancing marine conservation in European and contiguous seas with the MarCons Action. Research Ideas and Outcomes 3: e11884. https://doi.org/10.3897/rio.3.e11884
Figure 1 - European and contiguous seas. The distribution of population in European and adjacent coastal areas is shown as well as the existing Marine Protected Areas (including the Natura-2000 sites; based on the September 2015 version of the World Database on Protected Areas) and the terrestrial and marine borders (not all shown EEZs have been ratified – in the case of non-agreed marine borders the median line is shown in the map).
Figure 6 from: Sampaio FDF, Silva-de-Assis HC, Bettim FL, Fávaro LF, Freire CA (2019) Water acidification causes death of marine ornamental fish (Perciformes: Pomacentridae) during transport: contributing to the conservation of wild populations. Zoologia 36: 1-10. https://doi.org/10.3897/zoologia.36.e25083
Figure 6 Transport water volume (ml) per gram of fish weight versus total body length (cm). Black circles, fish that were alive at the end of the experiment; white circles, fish that died during the experiment. Vertical and horizontal dashed lines respectively indicate maximum suggested length for the transport of A.saxatilis (6 cm) to ensure survival, and maximum water volume/fish weight relationship (125 ml/g fish) to minimize transport costs.
Figures 4-5 from: Sampaio FDF, Silva-de-Assis HC, Bettim FL, Fávaro LF, Freire CA (2019) Water acidification causes death of marine ornamental fish (Perciformes: Pomacentridae) during transport: contributing to the conservation of wild populations. Zoologia 36: 1-10. https://doi.org/10.3897/zoologia.36.e25083
Figures 4-5 Relationship between weight (g) and total length (cm) of A.saxatilis: (4) weight (g) as a function of the total length (cm) of the fish. Black circles, fish that were alive at the end of the experiment (n = 53); white circles, fish that died during the experiment (n = 14). (5) Weight/length ratio versus fish length, with separate linear regressions for living (solid line) and dead (dashed line) fish, and respective r2 values.
Figures 7-8 from: Sampaio FDF, Silva-de-Assis HC, Bettim FL, Fávaro LF, Freire CA (2019) Water acidification causes death of marine ornamental fish (Perciformes: Pomacentridae) during transport: contributing to the conservation of wild populations. Zoologia 36: 1-10. https://doi.org/10.3897/zoologia.36.e25083
Figures 7-8 3-D mesh plots showing the relationship among the 3 water parameters, whole set of data. NH3-N (mg/L) versus DO(mg/L) versus pH, for live (7) and dead (8) fish. Legend illustrates color codes for pH interpolation.
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Allen Brain Atlas
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