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Fig. 8 in Exploitation status and stock assessment of the smooth clam Callista chione (Linnaeus, 1758) in the northern Alboran Sea (GSA01-W Mediterranean Sea)

Fig. 8: Time trajectories from 2002 to 2015 and forecasting for the next 20 years (2016-2036) of the relative fishing mortality rate (F/Fmsy) and relative population biomass (B/Bmsy) estimated using a non-equilibrium surplus production model, setting maximum sustainable yield (MSY) at a level corresponding to the value of the latest year. The dotted lines represent the upper and lower 80% confidence limits.

Fig. 7 in Exploitation status and stock assessment of the smooth clam Callista chione (Linnaeus, 1758) in the northern Alboran Sea (GSA01-W Mediterranean Sea)

Fig. 7: Trajectories from 2002 to 2015 of relative fishing mortality and biomass for Callista chione in the northern Alboran Sea.

Fig. 3 in Exploitation status and stock assessment of the smooth clam Callista chione (Linnaeus, 1758) in the northern Alboran Sea (GSA01-W Mediterranean Sea)

Fig. 3: Distribution of artisanal fisheries by fishing gear and landing port from March 2013 to March 2014. Values are given as percentage contribution of each fishery in tonnes.

Fig. 4 in Exploitation status and stock assessment of the smooth clam Callista chione (Linnaeus, 1758) in the northern Alboran Sea (GSA01-W Mediterranean Sea)

Fig. 4: Number of vessels by landing port targeting bivalves with mechanised dredges, in the northern Alboran Sea.

Fig. 1 in Exploitation status and stock assessment of the smooth clam Callista chione (Linnaeus, 1758) in the northern Alboran Sea (GSA01-W Mediterranean Sea)

Fig. 1: Geographical subareas of the General Fisheries Commission for the Mediterranean (GFCM) and map of the study area in the northern Alboran Sea (W Mediterranean Sea), showing the locations of the fishing ports.

Fig. 5 in Exploitation status and stock assessment of the smooth clam Callista chione (Linnaeus, 1758) in the northern Alboran Sea (GSA01-W Mediterranean Sea)

Fig. 5: Evolution of catches and CPUE for Callista chione in the northern Alboran Sea between 2001 and 2015.

Fig. 2 in Exploitation status and stock assessment of the smooth clam Callista chione (Linnaeus, 1758) in the northern Alboran Sea (GSA01-W Mediterranean Sea)

Fig. 2: Number and average technical characteristics (gross tonnes, length, and engine power) of artisanal vessels per landing port along the Alboran Sea.

opencc-by-4.0May 2024View details →

FIG. 68. Smooth elytral morphotypes. A, B. Morphotype 62, VMNH 97505. C, D. Morphotype 63, VMNH 99030. E, F. Morphotype 64, VMNH 95504. G, H. Morphotype 65, VMNH 97607. I, J. Morphotype 66, VMNH 97319. K, L. Morphotype 67, VMNH 97104 in Remarkable Diversity Of Beetles (Coleoptera) In The Late Triassic (Norian) "Solite Deposit" Of Virginia And North Carolina

FIG. 68. Smooth elytral morphotypes. A, B. Morphotype 62, VMNH 97505. C, D. Morphotype 63, VMNH 99030. E, F. Morphotype 64, VMNH 95504. G, H. Morphotype 65, VMNH 97607. I, J. Morphotype 66, VMNH 97319. K, L. Morphotype 67, VMNH 97104. Scale bars: 0.5 mm.

Figure 5 in Confirmation and differential metabolism associated with quinclorac resistance in smooth crabgrass (Digitorio ischoemum)

Figure 5. Amount of quinclorac (mg g−1 plant, mean ± SE) detected by liquid chromatography–diode array detector (DAD) in extracts of plants (aerial parts) from susceptible (SMT2) and two resistant (MSU1 and MSU2) Digitorio ischoemum populations, with previous application of 2 kg malathion ha−1 followed by 0.84 kg quinclorac ha−1 (QM), 0.84 kg quinclorac ha−1 (Q1X), no application of quinclorac or malathion (Q0X), and application of 2 kg malathion ha−1 alone (M), evaluated at 72 and 168 h after treatment (HAT). Means within an evaluation time and treatment with the same capital letter are not significantly different at the 5% level as determined by Fisher's protected least significant difference (LSD) test; means for the same population and evaluation time with the same letter are not significantly different at the 5% level as determined by the LSD test.

Figure 4. Specific glutathione S-transferase activity changes toward 1 in Confirmation and differential metabolism associated with quinclorac resistance in smooth crabgrass (Digitorio ischoemum)

Figure 4. Specific glutathione S-transferase activity changes toward 1-chloro-2,4- dinitrobenzene in Digitorio ischoemum tissues after (A) 0.84 kg quinclorac ha−1 or (B) 7.56 kg quinclorac ha−1. Data were expressed as a percentage change of the nontreated. Values are presented as mean ± SE. Error bars indicate the standard error of the mean. R, resistant; S, susceptible.

Figure 2 in Confirmation and differential metabolism associated with quinclorac resistance in smooth crabgrass (Digitorio ischoemum)

Figure 2. Aboveground dry mass of susceptible and resistant Digitorio ischoemum at 28 d after treatment. The D. ischoemum was at the 3-leaf stage of growth when herbicide was applied. Data were expressed as a percentage decrease of the mean dry mass of the nontreated control. Error bars show the standard error of the mean. R, resistant; S, susceptible.

Figure 1 in Confirmation and differential metabolism associated with quinclorac resistance in smooth crabgrass (Digitorio ischoemum)

Figure 1. Visual control of susceptible and resistant Digitorio ischoemum crabgrass at 28 d after treatment. The crabgrass was at the three-leaf stage of growth when herbicide was applied. Control was visually assessed on a 0%–100% scale (0% = no plant death; 100% = complete plant death). The data were normalized relative to the nontreated control. Error bars show the standard error of the mean. R, resistant; S, susceptible.

Figure 3 in Confirmation and differential metabolism associated with quinclorac resistance in smooth crabgrass (Digitorio ischoemum)

Figure 3. Cyanide content of susceptible and resistant Digitorio ischoemum at 3 d after treatment. Data were expressed as a percentage increase of the mean control. Error bars indicate the standard error of the mean. R, resistant; S, susceptible.

Fig. 2 in Flexibility is everything: prey capture throughout the seasonal habitat switches in the smooth newt Lissotriton vulgaris

Fig. 2 Frame shots showing the four feeding modes in the smooth newt. In the aquatic stage: a suction feeding under water and b jaw prehension on land. In the terrestrial stage: c suction feeding under water and d tongue prehension on land. The prey (maggot) is indicated by the arrow.

Fig. 1 Landmarks used for the kinematic analyses. 1 upper jaw tip, 2 lower jaw tip, 3 in Flexibility is everything: prey capture throughout the seasonal habitat switches in the smooth newt Lissotriton vulgaris

Fig. 1 Landmarks used for the kinematic analyses. 1 upper jaw tip, 2 lower jaw tip, 3 hyoid (throat), 4 jaw joint, 5 nape, 6 dorsal trunk reference, 7 tongue tip (only digitized when visible)

Fig. 4 in Flexibility is everything: prey capture throughout the seasonal habitat switches in the smooth newt Lissotriton vulgaris

Fig. 4 Scatter plot of the first two principal components. Principal component 1 (PC1) and principal component 2 (PC2) are derived from the 12 kinematic variables to illustrate the relationship among kinematic patterns for the four feeding modes coded by symbols and the ten individuals coded by color. Each data point represents one feeding event, and the ellipses indicate 95 % confidence interval in the four feeding modes. P@1 explains 57 % and P@2 explains 15.5 % of the total variance. See Table 3 for complete loadings of each principal component

Fig. 3 in Flexibility is everything: prey capture throughout the seasonal habitat switches in the smooth newt Lissotriton vulgaris

Fig. 3 Kinematic profiles of the four feeding modes. Kinematic means (dark and bold curves)±SD (pale and slim curves) of gape (blue), hyoid (Vreen), head rotation (oranVe), and tongue movement (Vray, only shown

opencc-by-4.0Jun 2016View details →

Fig. 2 in A new case of facultative paedomorphosis in Smooth Newts, Lissotriton vulgaris (Caudata: Salamandridae), in Turkey

Fig. 2. The general view of habitat (A) and a male paedomorphic Lissotriton vulgaris (B, C) from Lake Sazlı (Izmir, Turkey). The arrows show the cloaca (B) and the gills (C).

opencc-by-4.0Oct 2018View details →

Binary data file needed for the Shen et al. (2011) equation of state implemented in the Phantom smoothed particle hydrodynamics and magnetohydrodynamics code

** this file is downloaded automatically from this repository on running Phantom ** Contains information needed to load the <a href="http://adsabs.harvard.edu/abs/2011PhRvC..83c5802S">Shen, Horowitz & Teige (2011)</a> equation of state for nuclear matter in Phantom simulations The data file is a binary data file that enables a fast read of the information listed in the ascii tables given in the supplementary material of the Shen et al paper. The original ascii data files can be found here: <a href="https://journals.aps.org/prc/supplemental/10.1103/PhysRevC.83.035802">https://journals.aps.org/prc/supplemental/10.1103/PhysRevC.83.035802</a> For information on how to read this file, see the Phantom source code (<a href="https://github.com/danieljprice/phantom/blob/master/src/main/eos_shen.f90">eos_shen.f90</a>)