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opencc-by-4.0Sep 2018View details →

Fig. 2 in Analyzing the mass-rearing system of the California red scale parasitoid Aphytis melinus (Hymenoptera: Aphelinidae)

Fig. 2. Production of Aphytis melinus over the period in which the pilot system was working, from 18 March 2010 to 20 Jun 2011: (a) Total production per day, when different cages were in production at the same time and collection was every 2 to 3 days; (b) Total production per cage. Each bar in (b) represents the production of an individual cage, and is displayed as the date when parasitoid emergence began.

opencc-by-4.0Sep 2018View details →

Fig. 1 in Analyzing the mass-rearing system of the California red scale parasitoid Aphytis melinus (Hymenoptera: Aphelinidae)

Fig. 1. Parasitoid (Aphytis melinus) production (as percentage of the total production given as mean ± SE) in the production cages: (a) daily emergence; (b) cumulative emergence.

Fig. 2 in Comparison of two traps for monitoring California red scale (Hemiptera: Diaspididae)

Fig. 2. (A) Mean (± SE) number of California red scale per trap by sampling date, based on estimate California red scale counts. Male flight periods are delimited with vertical dashed lines. (B) Degree-d accumulation across sampling dates, for temperature data collected from onsite weather station and regional weather station. Solid horizontal lines correspond to the degree-d requirements for the second and fourth male flights.

Fig. 1 in Comparison of two traps for monitoring California red scale (Hemiptera: Diaspididae)

Fig. 1. The California red scale traps used in this study deployed in the field. (A) Single-sided California red scale trap, consisting of a wirelessly networked digital camera mounted to a sticky card platform. (B) A commercial double-sided California red scale trap.

Fig. 3 in Comparison of two traps for monitoring California red scale (Hemiptera: Diaspididae)

Fig. 3. (A) Mean (± SE) California red scale counts (based on estimated California red scale counts) for all trap locations in this study. (B) Schematic of relative position of trap locations in our field plot; shape indicates estimated marginal mean California red scale counts. In (A) and (B) circles are <500 California red scale, triangle is 501 to 1,000 California red scale, and squares> 1,000 California red scale. (C) Mean (± SE) California red scale trap counts by flight number. Bars with different letters are significantly different (α = 0.05).

Fig. 4 in Comparison of two traps for monitoring California red scale (Hemiptera: Diaspididae)

Fig. 4. The probability of a trap capturing> 1,000 California red scale in a sampling period, based on (A) actual California red scale counts, and (B) estimated California red scale counts. Male flight periods are delimited with vertical dashed lines.

opencc-by-4.0Dec 2015View details →

Figure 2. - K2P in Range extension of Gerres infasciatus (Perciformes: Gerreidae) from the Red Sea and the Arabian Gulf, with distributional implications for the G. filamentosus complex

Figure 2. - K2P distance neighbouring-joining tree of COI sequences (615 bp) of gerreid species in the Gerres filamentosus complex; G. oyena used as outgroup.

opencc-by-4.0Dec 2015View details →

Figure 1. - Gerres filamentosus complex. A in Range extension of Gerres infasciatus (Perciformes: Gerreidae) from the Red Sea and the Arabian Gulf, with distributional implications for the G. filamentosus complex

Figure 1. - Gerres filamentosus complex. A: Gerres infasciatus. SMF 35412, 99.5 mm SL, off Jizan, Saudi Arabia, Red Sea; B: G. microphthalmus, NSMT-P 45901, holotype, female, 189 mm SL, Kyushu, Japan; C: G. macracanthus, SMF 35037, 98 mm SL, off Jizan, Saudi Arabia, Red Sea; D: G. filamentosus, KAUMI 12250, 139 mm SL, off Sabah, Borneo Island, Malaysia. Photographs (A, C) were taken by S.V. Bogorodsky and (D) by M. Matsunuma.

Figure 2 in Objective record of Pterois russelii (Scorpaenidae: Pteroinae) from the Red Sea

Figure 2. – Relationship between supraocular tentacle length and standard length (mm) in Pterois russelii, showing ontogenetic change of the former.

Figure 1 in Objective record of Pterois russelii (Scorpaenidae: Pteroinae) from the Red Sea

Figure 1. – Fresh specimen of Pterois russelii from the Red Sea [SMF 35752 (KAU 14-168), 99.7 mm standard length, off Jizan, Saudi Arabia]. Photo by S. V. Bogorodsky.

opencc-by-4.0Dec 2021View details →

Fig. 1 in Morphological and molecular analyses of Taenia and Mesocestoides species from red foxes (Vulpes vulpes) in northwestern China

Fig. 1. Phylogenetic relationships of Taenia and Mesocestoides species from red foxes based on cox1 sequences.

Fig. 4 in Temporal variation of epi- and endofaunal assemblages associated with the red sponge Tedania ignis on a rocky shore (São Sebastião Channel), SE Brazil

Fig. 4. MDS ordination of epifaunal (open symbols) and endofaunal (closed symbols) assemblages associated with Tedania ignis at Praia das Cigarras, São Sebastião, São Paulo, Brazil during one year. Stress = 0.06.

Fig. 3 in Temporal variation of epi- and endofaunal assemblages associated with the red sponge Tedania ignis on a rocky shore (São Sebastião Channel), SE Brazil

Fig. 3. Temporal variation of the main taxonomic groups of epifaunal (open symbols) and endofaunal (closed symbols) assemblages associated with Tedania ignis at Praia das Cigarras, São Sebastião, São Paulo, Brazil. Values are means ± SE.

Fig. 2 in Temporal variation of epi- and endofaunal assemblages associated with the red sponge Tedania ignis on a rocky shore (São Sebastião Channel), SE Brazil

Fig. 2. Variation of density, taxon richness and Shannon diversity index of epifaunal (open symbols) and endofaunal (closed symbols) assemblages associated with Tedania ignis in relation to sponge biomass and organic matter content at Praia das Cigarras, São Sebastião, São Paulo, Brazil.

Fig. 1 in Temporal variation of epi- and endofaunal assemblages associated with the red sponge Tedania ignis on a rocky shore (São Sebastião Channel), SE Brazil

Fig. 1. Temporal variation of sponge biomass, and density, taxon richness and Shannon diversity index of epifaunal (open symbols) and endofaunal (closed symbols) assemblages associated with Tedania ignis at Praia das Cigarras, São Sebastião, São Paulo, Brazil. Values are means ± SE.

opencc-by-4.0Mar 2009View details →

Fig. 4 in Red Devonian trilobites with green eyes from Morocco and the silicification of the trilobite exoskeleton

Fig. 4. Map of Hamar Laghdad showing the mud−mounds, the distribution of the red facies, the position of the red cliff, erosional remnants of the Cretaceous transgression conglomerate and the distribution of outcrops of Middle Devonian sediments (map based on satellite images, the topographic map sheet "Erfoud, feuille NH−30−XX−2, Carte du Maroc 1/100000", and Berkowski 2006: fig. 1).

opencc-by-4.0Mar 2009View details →

Fig. 3 in Red Devonian trilobites with green eyes from Morocco and the silicification of the trilobite exoskeleton

Fig. 3. SEM−SE image of cephalon PIMUZ 27076 and results of the element analyses ("EDX−spektrum X"). A. SEM−SE image of the eye and result of the element analysis of a lense ("EDX−spektrum 1"). Note the absence of iron and silica. B. SEM−SE image of the glabella and result of the element analysis ("EDX−spektrum 9"). Iron and silica are present. C. Analysis performed in the intralensar area ("EDX−spektrum 2") of the glabella(see A). Iron and silica are present.

opencc-by-4.0Mar 2009View details →

Fig. 1 in Red Devonian trilobites with green eyes from Morocco and the silicification of the trilobite exoskeleton

Fig. 1. Geologic map of Morocco and the Tafilalt (eastern Anti−Atlas), showing the position of the "red cliff" at Hamar Laghdad (modified after Klug 2007).

opencc-by-4.0Dec 2022View details →

Fig. 15 in Morphological description and multilocus genotyping of Onchocerca spp. in red deer (Cervus elaphus) in Switzerland

Fig. 15. Dendrogram of Onchocerca from this study, various other Onchocerca sequences and Litomosoides sigmodontis as an outgroup based on a dataset of 579 positions of the mitochondrial cox1 gene, estimated by using the Maximum Likelihood method and TN93 + G + I substitution model (Tamura and Nei, 1993). The tree with the highest log likelihood (– 2902.13) is shown. Bootstrap values over 50 are shown next to the branches. Sequences newly generated in this study are in bold.