Find research datasets worth reusing

opencc-by-4.0Dec 2023View details →

Figure 1 in Evaluation of Plastic Shipping Bags for Hypothenemus hampei (Ferrari) (Coleoptera: Curculionidae) Containment

Figure 1. Diagram of Hypothenemus hampei (Ferrari) shipping bag observation arenas used in this experiment. Arenas were constructed of lidded 3.78 L (1-gal) glass jars with drying treated coffee in one of nine bag treatments suspended from the top by a hot-glued string tether to allow escaping (left) or not escaping (right) H. hampei observation in the bottom of the jar.

opencc-zeroJun 2024View details →

Dataset: Grindrod Shipping Holdings Ltd. (GRIN) Stock Performance

This dataset provides historical stock market performance data for specific companies. It enables users to analyze and understand the past trends and fluctuations in stock prices over time. This information can be utilized for various purposes such as investment analysis, financial research, and market trend forecasting.

Figure 4 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 4. Taxa distribution on ships' hulls of the three studied vessels (Esmeralda, USA and ARG tankers) (a) nMDS showing the taxa assemblages in protected vs. exposed areas of the ships' hulls. (b) Taxa richness in exposed and protected areas of the hulls of the three studied vessels. (c) Relationship between the number of taxa found on the hulls and the number of ports visited by each ship.

Figure 6 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 6. Distribution of the COI haplotypes of Ciona robusta per sample, with their number indicated in the barplot. For each sample, the number of specimens is indicated in parentheses. The correspondence between the haplotypes found in this study, and those referenced in GenBank is given in Table S3.

Figure 2 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 2. Location of the different areas of the vessel from which the samples were obtained. Protected areas: sea box, rope guard, water discharge holes, top of the rudder and the Kort nozzle. Exposed areas: bilge keel, the helm in general and the rudder. Modified from Sylvester and MacIsaac (2010).

Figure 5 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 5. Taxa richness recorded in the Talcahuano port on settlement plates made of different types of materials and maintained at different depths for two months total, considering the two periods of time. Values include averages and ± one standard error.

Figure 1 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 1. The black circle corresponds to the locality where the sampling was carried out in each type of sampling (ships, settlement plates in the port of Talcahuano and natural substrates in the El Manzano pier).

Figure 3. Graphical representation using a in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 3. Graphical representation using a nMDS based on Bray-Curtis distances, of the taxa assemblages in each sampling type (ships, settlement plates in the Talcahuano port, and natural substrates at El Manzano pier). Stress value is 0.17.

Figure 8 in Do ship strikes threaten the recovery of endangered eastern North Pacific blue whales?

Figure 8. Results for the long-term approach to future status. Equilibrium abundance relative to carrying capacity is shown for Sobs ¼ 10 and a range of multipliers of current levels of 2013 vessels. The model was projected forward 100 yr for each posterior sample under a constant multiplier (x-axis value). Model trajectories are shown as filled gray areas representing the 0.95, 0.75, 0.5, 0.25, and 0.05 posterior percentiles. The probability that the population is depleted (i.e., below 60% of K) is shown as a curved line. The solid vertical line denotes the median ratio of vessels in 2050 to 2013, i.e., the multiplier in 2050 estimated by our vessel model.

Figure 7 in Do ship strikes threaten the recovery of endangered eastern North Pacific blue whales?

Figure 7. Results of the short-term approach to future status. Future ship strikes, abundances, and abundances relative to carrying capacity for Sobs ¼ 10 are shown for three mitiga2013 tion cases (columns). Model trajectories are shown as filled gray areas representing the 0.95, 0.75, 0.5, 0.25, and 0.05 posterior percentiles. "Status quo" means no additional mitigation, "mitigation" refers to halving the ship strikes after 2013, and "none" is a complete elimination of future ship strikes. The horizontal lines at 0.6 denote the level below which the population is considered depleted.

Figure 4 in Do ship strikes threaten the recovery of endangered eastern North Pacific blue whales?

Figure 4. Posterior densities for the abundance relative to carrying capacity in 2013 for Sobs ¼ 10 (top) and Sobs ¼ 35 (bottom) and the two priors for r. The vertical line at 0.6 2013 2013 denotes the level below which the population is considered depleted.

Figure 6 in Do ship strikes threaten the recovery of endangered eastern North Pacific blue whales?

Figure 6. Absolute abundance, the abundance estimates and anthropogenic mortalities for Sobs ¼ 10 and the two priors for r. The rectangles at the bottom denote total estimated mor2013 talities (median catches + median strikes) for each year. The five abundance estimates (points) are shown with their 95% confidence intervals (bars). Model trajectories are shown as filled gray areas representing the 0.95, 0.75, 0.5, 0.25, and 0.05 posterior percentiles.

Figure 2 in Do ship strikes threaten the recovery of endangered eastern North Pacific blue whales?

Figure 2. Results of the vessel model. The points are data from worldwide statistics for vessels over 100 gross tons from Lloyd's of London, as used in Laist et al. (2001). Model trajectories are shown as filled gray areas representing the 0.95, 0.75, 0.5, 0.25, and 0.05 posterior percentiles.

Figure 1 in Do ship strikes threaten the recovery of endangered eastern North Pacific blue whales?

Figure 1. Prior and marginal posterior probability distributions for the parameters of the theta-logistic population dynamics model for Sobs ¼ 10 and both priors for r (columns).

Figure 3 in Do ship strikes threaten the recovery of endangered eastern North Pacific blue whales?

Figure 3. Results of the ship strike model. Predicted ship strikes for the uninformative prior for r and observed ship strikes in 2013 as 10 or 35. Annual trajectories (panels A and B) are shown as filled gray areas representing the 0.95, 0.75, 0.5, 0.25, and 0.05 posterior percentiles. Panels C and D show the posterior distributions of strikes in 2013 (histogram) as well as the Poisson likelihood (line).

Figure 5 in Do ship strikes threaten the recovery of endangered eastern North Pacific blue whales?

Figure 5. Trajectories for Abundance relative to carrying capacity for Sobs ¼ 10 and both 2013 priors for r. Model trajectories are shown as filled gray areas representing the 0.95, 0.75, 0.5, 0.25, and 0.05 posterior percentiles. The horizontal lines at 0.6 denote the level below which the population is considered depleted.