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101 results for “, Marine reserve”
Fishery impacts - CA commercial lobster catch and effort, and trap distribution around marine reserves
These data describe landings and fishing effort for the CA commercial spiny lobster fishery. Data are contained in two tables: 1) a time series collected by the California Fish and Wildlife (CDFW) of lobster catch (kg) and effort (lobster trap pulls) by year (1998-2020) and location (geographic fishery blocks). Catch is recorded and reported to CDFW by fish processors (buyers) with “fish tickets”. Trap pulls are recorded and reported by fishermen with logbooks. 2) The number of traps counted in the water at increasing distances from the boundary of marine reserves, three reserves located in the northern region of the fishery and three from the southern region of the fishery, in November 2022.
SBC LTER: Theme 1B: Lobster trap data from marine reserves
These data describe catches of California spiny lobster (Panuliris interruptus) in the Santa Barbara Channel. Lobster count and weight were collected from Santa Cruz Island between 2006 and 2018. Data are contained in two tables: 1) Catch per trap across all sites 2) the weight in lobster caught in traps from all sites. This is a data package to support manuscript: Hunter S. Lenihan, Sean P. Fitzgerald, Daniel C. Reed, Jennifer K.K. Hofmeister, and Adrian C. Stier. Increasing spillover enhances southern California spiny lobster catch along marine reserve borders. Ecosphere.
Fig. 9 in Ichthyoplankton of Arvoredo Biological Marine Reserve, Santa Catarina, Brazil
Fig. 9. Profile the temperature and salinity of the water column (Diagram TS) recorded in Arvoredo Biology Marine Reserve (Brazil) region during winter/2007 (a), winter/2008 (b), summer/2008 (c), and summer/2009 (d).
Fig. 8 in Ichthyoplankton of Arvoredo Biological Marine Reserve, Santa Catarina, Brazil
Fig. 8. Temperature and salinity of the water column (Diagram TS) recorded in Arvoredo Biology Marine Reserve (Brazil) region during winter/2007 (a), winter/2008 (b), summer/2008 (c), and summer/2009 (d). CW = Coastal Water; SACW = South Atlantic Central Water; STSW = Subtropical Shelf Water.
Fig. 5 in Ichthyoplankton of Arvoredo Biological Marine Reserve, Santa Catarina, Brazil
Fig. 5. Relative abundance (%) of larvae collected in Arvoredo Biology Marine Reserve (Brazil) during winter (a) and summer (b). In campaign 1 (1997/1998), 2 (2007/2008) and 3 (2008/2009).
Fig. 1 in Ichthyoplankton of Arvoredo Biological Marine Reserve, Santa Catarina, Brazil
Fig. 1. Location of sampling stations in the Arvoredo Biology Marine Reserve region and adjacent areas in campaign 1 (1997/ 1998) (stations 7-12), campaign 2 (2007/2008) (stations 1-12) and campaign 3 (2008/2009) (stations 1-12).
Fig. 10 in Ichthyoplankton of Arvoredo Biological Marine Reserve, Santa Catarina, Brazil
Fig. 10. Canonical Correspondence Analysis of the (a) eight most abundant families, and (b) stations in Arvoredo Biology Marine Reserve (Brazil) region in relation to temperature, salinity and chlorophyll-a. Note: W-07 - Winter/2007; S-08 - Summer/ 2008; W-08 - Winter/2008 and S-09 - Summer/2009
Fig. 6 in Ichthyoplankton of Arvoredo Biological Marine Reserve, Santa Catarina, Brazil
Fig. 6. Cluster analysis of 59 samples collected in theArvoredo Biology Marine Reserve (Brazil) region during the summer (1998, 2008 and 2009) and winter (1997, 2007, and 2008), based on relative abundance of the different taxa fish larvae identified. Note: w - Winter; s - Summer
Fig. 7 in Ichthyoplankton of Arvoredo Biological Marine Reserve, Santa Catarina, Brazil
Fig. 7. Rarefaction curve of larval fish species collected during six sampling periods in the Arvoredo Biology Marine Reserve (Brazil) region.
Рис. 2. A, B. Modiolus (Modiolus) kurilensis Bernard, 1983: леваЯ створка снаружи (A), иЗнутри (B). Длина раковины 26.4 мм, высота – 47.3 мм; C, D. Gari (Gobraeus) kazusensis (Yokoyama, 1922): леваЯ створка снаружи (C), иЗнутри (D). Длина раковины 71.0 мм, высота – 39.9 мм. E, F. Panomya norvegica (Spengler, 1973): леваЯ створка снаружи (E), праваЯ створка иЗнутри (F). Длина раковины 70.8 мм, высота – 44.5 мм, толЩина – 36.7 мм. Fig. 2. A, B. Modiolus (Modiolus) kurilensis Bernard, 1983: left valve (A) outside, (B) inside. Shell length 26.4 mm, height – 47.3 mm. C, D. Gari (Gobraeus) kazusensis (Yokoyama, 1922): left valve (C) outside, (D) inside. Shell length 71.0 mm, height – 39.9 mm. E, F. Panomya norvegica (Spengler, 1973): left valve (E) outside, right valve (F) inside. Shell length 70.8 mm, height – 44.5 mm, thickness – 36.7 mm. in On the species composition of marine bivalves of the Sikhote-Alin Reserve (northern Primorye, Japan/East Sea)
Рис. 2. A, B. Modiolus (Modiolus) kurilensis Bernard, 1983: леваЯ створка снаружи (A), иЗнутри (B). Длина раковины 26.4 мм, высота – 47.3 мм; C, D. Gari (Gobraeus) kazusensis (Yokoyama, 1922): леваЯ створка снаружи (C), иЗнутри (D). Длина раковины 71.0 мм, высота – 39.9 мм. E, F. Panomya norvegica (Spengler, 1973): леваЯ створка снаружи (E), праваЯ створка иЗнутри (F). Длина раковины 70.8 мм, высота – 44.5 мм, толЩина – 36.7 мм. Fig. 2. A, B. Modiolus (Modiolus) kurilensis Bernard, 1983: left valve (A) outside, (B) inside. Shell length 26.4 mm, height – 47.3 mm. C, D. Gari (Gobraeus) kazusensis (Yokoyama, 1922): left valve (C) outside, (D) inside. Shell length 71.0 mm, height – 39.9 mm. E, F. Panomya norvegica (Spengler, 1973): left valve (E) outside, right valve (F) inside. Shell length 70.8 mm, height – 44.5 mm, thickness – 36.7 mm.
FIGURE 1 in Folk taxonomy of the gray mullets (Mugilidae: Mugiliformes) in a marine extractivist reserve of northern Brazil
FIGURE 1 | Map of Ajuruteua Plateau, on the northern coast of Brazil, showing the two villages at which the ethnotaxonomic data on the fish of the family Mugilidae were collected in the present study.
FIGURE 4 in Folk taxonomy of the gray mullets (Mugilidae: Mugiliformes) in a marine extractivist reserve of northern Brazil
FIGURE 4 | Results of the Redundancy Analysis (RDA) of the definition of the ethnospecies by the artisanal fishers from the Caeté-Taperaçu Marine Extractive Reserve in Bragança, northern Brazil, with the characteristics that best identify each taxon. A. CA: 'caica', PA: 'pratiqueira', PR: 'pratiqueira/ ribação', SR: 'sajuba/ribação', RI: 'ribação', UR: 'urubarana', PQ: 'pratiqueirão', FI: 'filhotes'; B: narrow body, B1: juvenile of large mullet, D: does not grow a lot, G: narrow headed, I: small headed, M: small eyed, P: small scales, U: does not jump, Z: smells. B. TA: 'tainha', TM: 'tainha macho', TBR: 'tainha branca', TB: 'tainha boi', TC: 'tainha chata', TGP: 'tainha grande/puá', TG: 'tainha grande', TCU: 'tainha curimã', CT: 'caica tamatarana', SA: 'sajuba', A: rounded body, C: grows a lot, E: back dark/bluish, F: flattened head, H: rounded head, J: large headed, L: large eyed, N: red eyed, O: large scales, Q: rounded scales, R: shiny scales, S: scales close together, V: smart, X: stupid. C. PB: 'pratiqueira/barrasco', BA: 'barrasco', BR: 'barrasco/ribação', SBR: 'sajuba/barrasco/ribação', IR: 'irichona', A1: sexual dimorphism, C1: 'baby mullet'.
FIGURE 3 in Folk taxonomy of the gray mullets (Mugilidae: Mugiliformes) in a marine extractivist reserve of northern Brazil
FIGURE 3 | Folk taxonomy designated by the artisanal fishers of the Caeté-Taperaçu Marine Extractive Reserve for the gray mullet (Mugilidae) and the corresponding scientific classification. The numbers within parentheses indicate the number of fishers reporting the ethnospecies. * = the number of fishers who stated that they did not know the ethnospecies or that it did not occur in the region.
FIGURE 2 in Folk taxonomy of the gray mullets (Mugilidae: Mugiliformes) in a marine extractivist reserve of northern Brazil
FIGURE 2 | Morphological features of a gray mullet (Mugilidae), showing the terminology used by the fishers of the Caeté-Taperaçu Marine Extractive Reserve in Bragança, Pará, Brazil.
Figure 2. – Mean abundance per 750 m2 in Changes in distribution patterns of two vulnerable fish species (Epinephelus marginatus and Sciaena umbra) in the Scandola marine reserve (Corsica, NW Mediterranean): a possible effect of increased boat tourism
Figure 2. – Mean abundance per 750 m2 (± SE) of the dusky grouper Epinephelus marginatus (A) and the brown meagre Sciaena umbra (B) according to protection level at Scandola in 2012 and 2018. IR: integral reserve, BZ: buffer zone, UP: unprotected zone. Interannual difference are indicated for each protection level, *: significant at p <0.05, ns: not significant.
Figure 1 in Changes in distribution patterns of two vulnerable fish species (Epinephelus marginatus and Sciaena umbra) in the Scandola marine reserve (Corsica, NW Mediterranean): a possible effect of increased boat tourism
Figure 1. – Location of sites surveyed for dusky grouper and brown meagre populations inside and outside the Scandola MNR (Corsica, NW Mediterranean), according to protection status in summer 2012 and 2018. Dark blue arrows = integral reserve (IR), light blue arrows = buffer zone (BZ), red arrows = unprotected zones (UP). Blue stars = surveyed only in 2012, red star = site surveyed only in 2018.
Figure 5 in Changes in distribution patterns of two vulnerable fish species (Epinephelus marginatus and Sciaena umbra) in the Scandola marine reserve (Corsica, NW Mediterranean): a possible effect of increased boat tourism
Figure 5. – Size structure of Epinephelus marginatus and Sciaena umbra at Scandola in 2012 and 2018. Size classes = 10 cm for the dusky grouper and 5 cm for the brown meagre.
Figure 3 in Observations of a rapid decline in invasive macroalgal cover linked to green turtle grazing in a Hawaiian marine reserve
Figure 3. Mean hourly temperatures (°C) (a.), total rainfall (mm h-1) (b.), wind (km h−1) (c.), and PAR (µmol photons m−2) (d.) in 2015 (red triangle), 2016 (blue square), and 2017 (black circle). Data was obtained from Hawai'i Institute of Marine Biology Weather Station (http://www.pacioos.hawaii.edu/weather/obs-mokuoloe/).
Figure 1 in Observations of a rapid decline in invasive macroalgal cover linked to green turtle grazing in a Hawaiian marine reserve
Figure 1. Green turtle, Chelonia mydas, feeding on Gracilaria salicornia in the back lagoon of Moku o Lo'e, Kāneʻohe Bay, Oʻahu, Hawaiʻi in March 2017. Photo by KD Bahr.
Figure 2. Surveyed sites around Moku o in Observations of a rapid decline in invasive macroalgal cover linked to green turtle grazing in a Hawaiian marine reserve
Figure 2. Surveyed sites around Moku o Loʻe, Kāneʻohe Bay, Oʻahu, Hawaiʻi in April (left) and May (right) depicting proportion of substratum classified as coral (brown), rubble (grey), sand (yellow), or Gracilaria salicornia (green). Numbers within pie charts indicate number of turtles observed at each site during the survey. Red outlined pie charts denote areas with limited accessability (only during high tides) to Chelonia mydas.
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Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
OpenNeuro
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