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Figure 3. - Millerigobius macrocephalus. A in Three new records of Gobiidae from Malta with morphology, colouration and identification of the smallest known juveniles of two small gobiid species

Figure 3. - Millerigobius macrocephalus. A: Preserved specimen, PMR VP2879, juvenile of unidentified sex, 8.5 + 2.4 mm, Manoel Island B, Malta. B: Preserved specimen, PMR VP2881, juvenile of unidentified sex, 11.5 + 2.9 mm, Manoel Island B, Malta. C: Map of the Mediterranean showing previous records (▲) and new finding (●).

Figure 1 in Three new records of Gobiidae from Malta with morphology, colouration and identification of the smallest known juveniles of two small gobiid species

Figure 1. - Map of the Maltese Islands showing the sixteen sampling locations: (▲) sites with gobiid records; (●) sites from where no gobiid species were identified. Key: A: Wied l-Ghasri; B: Ħondoq Bay; C: Ix-Xatt l-Ahmar; D: Mġarr ix-Xini; E: Mellieha Bay; F: Mistra Bay; G: Qawra; H1-H6: Tigné A – Tigné F; I1-I2: Manoel Island A – Manoel Island B; J1-J4: Ta' Xbiex A – Ta' Xbiex D; K: Ħofra ż-Żghira; L: Marsaxlokk; M: Wied ix-Xoqqa; N: Wied iż-Żurrieq; O: Fomm ir-Rih Bay; P: Ġnejna Bay.

Figure 2. - Gobius couchi. A in Three new records of Gobiidae from Malta with morphology, colouration and identification of the smallest known juveniles of two small gobiid species

Figure 2. - Gobius couchi. A: Preserved specimen, PMR VP2884, juvenile of unidentified sex, 18.2 + 4.2 mm, Tigné E, Malta. B: Map of the Mediterranean showing previous records (▲) and new finding (●).

Figure 2. - A in The family Bramidae (Perciformes) from the Canary Islands (Northeastern Atlantic Ocean), with three new records

Figure 2. - A: Pterycombus brama (TFMC-VP/01919, 328 mm SL); B: Taractes asper (TFMCBM-VP/1936, 228 mm SL); and C: Taractes rubescens (772 mm SL) from the Canary Islands.

Figure 1 in Histological distinction between immature and regenerating females and its effect on maturity ogive estimation in three tropical hermaphroditic groupers

Figure 1. - Histological sections of ovaries in female Epinephelus morio (a), Mycteroperca bonaci (b) and Mycteroperca microlepis (c) in the regenerating phase (1), immature phase (2) and uncertain maturity phase (3). a1: E. morio, 72 cm FL, collected Jun. 1990; a2: E. morio, 68 cm FL, collected Jun. 1989; a3: E. morio, 51 cm FL, collected Aug. 1989. b1: M. bonaci, 107 cm FL, collected Jul. 1997; b2: M. bonaci, 62 cm FL, collected Oct. 1997; b3: M. bonaci, 65 cm FL, collected Jun. 1998. c1: M. microlepis, 97 cm FL, collected Jul. 1998; c2: M. microlepis, 82 cm FL, collected Aug. 1997; c3: M. microlepis, 89 cm FL, collected Jul. 1998. C, cord; BV, blood vessel; GW, gonad wall; MB, muscle bundle; OL, ovarian lamellae; PG, primary growth oocyte. Gabe and Martoja one-step trichrome stain. Scale bars = 300 microns.

Figure 4 in Histological distinction between immature and regenerating females and its effect on maturity ogive estimation in three tropical hermaphroditic groupers

Figure 4. - Size-frequency distributions of Mycteroperca microlepis females in immature, uncertain maturity, regenerating and mature active (developing, spawning capable, actively spawning and regressing) phases, collected in inshore and offshore waters of Campeche Bank, southern Gulf of Mexico.

Figure 2 in Histological distinction between immature and regenerating females and its effect on maturity ogive estimation in three tropical hermaphroditic groupers

Figure 2. - Size-frequency distributions of Epinephelus morio females in immature, uncertain maturity, regenerating and mature active (developing, spawning capable, actively spawning and regressing) phases, collected in inshore and offshore waters of Campeche Bank, southern Gulf of Mexico.

Figure 3 in Histological distinction between immature and regenerating females and its effect on maturity ogive estimation in three tropical hermaphroditic groupers

Figure 3.- Size-frequency distributions of Mycteroperca bonaci females in immature, uncertain maturity, regenerating and mature active (developing, spawning capable, actively spawning and regressing) phases, collected in inshore, offshore waters and coral reefs of Campeche Bank, southern Gulf of Mexico.

Fig. 4 in The effects of three essential oils on adult repellency, larval fumigant toxicity, and egg hatch of Tribolium castaneum (Coleoptera: Tenebrionidae)

Fig. 4. Mean red flour beetle egg hatch (± SE) during exposure to rice grains treated with 1 of 3 essential oils at varying exposure times. Means with a different letter for each time interval are significantly different (Tukey's HSD post hoc test, P <0.05).

Fig. 3 in The effects of three essential oils on adult repellency, larval fumigant toxicity, and egg hatch of Tribolium castaneum (Coleoptera: Tenebrionidae)

Fig. 3. Mean percent (± SE) repellency of adult red flour beetles at varying intervals of exposure, tested separately to 1 of 3 essential oils. Means with a different letter for each time interval are significantly different (Tukey's HSD post hoc test, P <0.05).

Fig. 2 in The effects of three essential oils on adult repellency, larval fumigant toxicity, and egg hatch of Tribolium castaneum (Coleoptera: Tenebrionidae)

Fig. 2. Mean (± SE) repellency of adult red flour beetles at varying intervals of exposure, tested separately to 1 of 3 essential oils. Means with an asterisk for each time interval are significantly different (Chi-square test, P <0.05).

Fig. 1 in The effects of three essential oils on adult repellency, larval fumigant toxicity, and egg hatch of Tribolium castaneum (Coleoptera: Tenebrionidae)

Fig. 1. Diagram of adult repellency test apparatus showing cotton wick (source of essential oils) placed at the bottom of both legs, which were half filled with rice grains.

Fig. 5 in The effects of three essential oils on adult repellency, larval fumigant toxicity, and egg hatch of Tribolium castaneum (Coleoptera: Tenebrionidae)

Fig. 5. Mean percent (± SE) mortality of red flour beetle larvae during separate exposure, as a fumigant, to 1 of 3 essential oils, at varying exposure times. Means

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Fig. 1 in Defensive warning behavior expressed by three species of polistine wasps

Fig. 1. Diagram of foraging area, nest yard, and sting threshold point. Foraging territory is the area surrounding the nest in which colony workers scout for and obtain their prey, paper, and other resources. Outside the nest yard, they remain non-defensive unless they are subjected to personal threat. The nest yard includes the area around the nest but outside of the sting threshold point in which warning behaviors are expressed. An intruder who approaches the nest in the area within the sting threshold point is likely to experience stinging behavior.

opencc-by-4.0Apr 2023View details →

Fig. 2 in Defensive warning behavior expressed by three species of polistine wasps

Fig. 2. Flow chart of defensive behavior expressed by polistine wasp workers toward vertebrate intrusion, as determined in this research and other investigations (Hermann 2017; Hermann & Dirks 1974). As initial lines of defense, aposematic coloration and pattern, along with nest location, offer some degree of colony protection. Once an intruder enters the nest yard, warning expressions are displayed by workers. Size of the nest yard and the stinging threshold point generally are species specific. Following the initial pretarsal twitching and the more obvious antennal raising and wing spreading, a wide array of defensive expressions ensue, terminating in stinging flights. There also are some interspecific differences in the display of certain warning expressions, as discussed in the text.

opencc-by-4.0Sep 2021View details →

(09)-Pereyra2021A-DS0001--DS0003 – Three Tribolium castaneum long-term live imaging datasets of embryonic development acquired with light sheet fluorescence microscopy

<p>(09)-Pereyra2021A-DS0001--DS0003 – Three <em>Tribolium castaneum</em> long-term live imaging datasets of embryonic development acquired with light sheet fluorescence microscopy</p>

Figure 8 in High endemic freshwater mussel (Bivalvia: Unionida) diversity in western Borneo, with description of three new species

Figure 8. (A) maximum likelihood (ML) phylogenetic tree of Pseudodon and (B) haplotype network of P. walpolei inferred from the COI dataset. Values at nodes indicate Bayesian inference (BI) posterior probability percentage/ML ultrafast bootstrap values. Support values>95% for both phylogenetic analyses are indicated by an asterisk. Support values marked with '-' indicate nodes that differ in the BI tree.

Figure 7 in High endemic freshwater mussel (Bivalvia: Unionida) diversity in western Borneo, with description of three new species

Figure 7. (A) phylogenetic tree of Lens, and (B) haplotype network of the L. contradens–lugens–micropterus clade inferred from the COI dataset.

Figure 6 in High endemic freshwater mussel (Bivalvia: Unionida) diversity in western Borneo, with description of three new species

Figure 6. (A) maximum likelihood (ML) phylogenetic tree and (B) haplotype network of Rectidens inferred from the COI dataset. Values at nodes indicate Bayesian inference (BI) posterior probability percentage/ML ultrafast bootstrap values. Support values>95% for both phylogenetic analyses are indicated by an asterisk. Support values marked with '-' indicate nodes that differ in the BI tree.

Figure 5 in High endemic freshwater mussel (Bivalvia: Unionida) diversity in western Borneo, with description of three new species

Figure 5. Images of type localities of (A) Ctenodesma mawonae, i.e. Sungai Sebua Jebung in the Sarawak River basin, Jambusan, Bau, Sarawak, Malaysian Borneo, and (B) Ctenodesma bersinara and Rectidens lauris, i.e. Sungai Rempangi, Pawan River basin, West Kalimantan, Indonesian Borneo.