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Fig. 1 in Maconellicoccus hirsutus (Hemiptera: Pseudococcidae) in Brazil: recent spread, natural enemies, and new hosts

Fig. 1. Geographic distribution of Maconellicoccus hirsutus (Green) (Hemiptera: Pseudococcidae) in Brazil, and M. hirsutus collection locations in the state of Espírito Santo, Brazil.

opencc-by-4.0Aug 2021View details →

Fig. 2 in Description of the tadpole and natural history notes of Incilius spiculatus (Mendelson, 1997), an Endangered toad endemic to the Sierra Madre de Oaxaca, Mexico

Fig. 2. Breeding behavior of Incilius spiculatus. (A–B) Amplexus (axillary type) and oviposition, (C) egg string staggered in unilayered tube, (D–E) dorsal and ventral views of the tadpole head at Gosner stage 24 showing the "elongated mouth," (F) Rio Coyul, San Pedro Yolox; (G) lateral view of tadpole at Gosner stage 39, and (H) lateral view of metamorphic individual.

opencc-by-4.0Aug 2021View details →

Fig. 1 in Description of the tadpole and natural history notes of Incilius spiculatus (Mendelson, 1997), an Endangered toad endemic to the Sierra Madre de Oaxaca, Mexico

Fig. 1. Tadpole of Incilius spiculatus. (A) Oral disc at Gosner stage 37, (B) lateral view at Gosner stage 35, and (C) dorsal view at Gosner stage 35.

opencc-by-4.0Oct 2023View details →

Fig. 1 in Phenological stages of a soybean crop affect the number of mating pairs and egg load in Rhyssomatus nigerrimus (Coleoptera: Curculionidae) females under natural conditions

Fig. 1. Effect of soybean crop phenological stages on matings per linear meter of Rhyssomatus nigerrimus pairs.Estimated values are 95% confidence intervals ±SE.

opencc-by-4.0Oct 2023View details →

Fig. 2 in Phenological stages of a soybean crop affect the number of mating pairs and egg load in Rhyssomatus nigerrimus (Coleoptera: Curculionidae) females under natural conditions

Fig. 2. Effect of time of day on matings per linear meter of Rhyssomatus nigerrimus copulating in the R7 phenological stage in a soybean crop. Estimated values are 95% confidence intervals ±SE.

opencc-by-4.0Apr 2023View details →

Fig. 2 in Spread and distribution of the naturalized orchid bee Euglossa dilemma in Florida

Fig. 2. Spread of Euglossa dilemma in Florida from the first detection in Broward County in 2003 to much of central Florida by 2022. County names appear on the map illustrating the first occurrence of the bee in the county during that time period. Locality data are from collection and identification records the Florida State Collection of Arthropods in Gainesville from 2003 to 2022, and iNaturalist observations 2015 to 2022.

opencc-by-4.0Apr 2023View details →

Fig. 1 in Spread and distribution of the naturalized orchid bee Euglossa dilemma in Florida

Fig. 1. Current distribution of Euglossa dilemma in Florida. Red dots are collection and identification record localities from the Florida State Collection of Arthropods from 2003 to 2022. Blue dots are iNaturalist observations from 2015 to 2022. Gray shading is the predicted potential distribution by the Maxent model (Hinojosa-Díaz et al. 2009).

Fig. 6 in Discovery of a reproducing population of the Mindo Glassfrog, Nymphargus balionotus (Duellman, 1981), at the Río Manduriacu Reserve, Ecuador, with a literature review and comments on its natural history, distribution, and conservation status

Fig. 6. Nymphargus balionotus breeding behavior. (A) Calling male; (B) Male and female in amplexus; (C) Egg mass deposited on the bottom surface on a leaf. Photos by Ross J. Maynard (A) and Jaime Culebras (B–C).

Fig 5 in Discovery of a reproducing population of the Mindo Glassfrog, Nymphargus balionotus (Duellman, 1981), at the Río Manduriacu Reserve, Ecuador, with a literature review and comments on its natural history, distribution, and conservation status

Fig 5. Iris variation in Nymphargus balionotus. Photos by Jaime Culebras (A–C) and Scott Trageser (D).

Fig. 4 in Discovery of a reproducing population of the Mindo Glassfrog, Nymphargus balionotus (Duellman, 1981), at the Río Manduriacu Reserve, Ecuador, with a literature review and comments on its natural history, distribution, and conservation status

Fig. 4. Metamorphic life stage of Nymphargus balionotus; dorsal (A) and ventral (B) views (ZSFQ 3895). Photos by Ross J. Maynard.

Fig. 3 in Discovery of a reproducing population of the Mindo Glassfrog, Nymphargus balionotus (Duellman, 1981), at the Río Manduriacu Reserve, Ecuador, with a literature review and comments on its natural history, distribution, and conservation status

Fig. 3. Pattern and color variation in adult Nymphargus balionotus. (A) Male, uncollected; (B) Male, ZSFQ 0531; (C) Male, uncollected; (D) Male, uncollected; (E–F) Male, ZSFQ 0532; (G–H) Gravid female, uncollected. Photos by Ross J. Maynard.

Fig. 2 in Discovery of a reproducing population of the Mindo Glassfrog, Nymphargus balionotus (Duellman, 1981), at the Río Manduriacu Reserve, Ecuador, with a literature review and comments on its natural history, distribution, and conservation status

Fig. 2. Audio spectrogram (top), oscillogram (middle), and power spectrum (bottom) graphs of a single male Nymphargus balionotus advertisement call.

Fig. 1 in Discovery of a reproducing population of the Mindo Glassfrog, Nymphargus balionotus (Duellman, 1981), at the Río Manduriacu Reserve, Ecuador, with a literature review and comments on its natural history, distribution, and conservation status

Fig. 1. Distribution map of known localities for Nymphargus balionotus. Information tags to the left summarize data reported for each locality, including (in order): name of collection site, department/province, number of specimens reported, elevation, and year specimens were collected or observed. Blue circle represents the Río Manduriacu Reserve; red circle marks the type locality; yellow and gray circles represent remaining localities reported in the literature, with the gray (Campamento Chancos) population believed to be a distinct lineage by Cisneros-Heredia and McDiarmid (2006). Note: the "El Tambo" locality in the department of Cauca, Colombia, has been placed as accurately as possible based on available information (see Discussion).

Fig. 4 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia

Fig. 4. Habitat suitability estimate (upper left panel), minimum convex polygon of extent of occurrence (EEO, upper right panel), and area of occupation (AOO, lower left panel) of Atelopus laetissimus. The total deforested area for the analyzed period and species occurrence locations are provided in red.

Figure 3 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia

Figure 3. Acoustic repertoire of the advertisement call of Atelopus laetissimus. Conventional pulsed call (A), unpulsed short call (B), partially pulsed short call (C), pulsed short call (D), partially pulsed short call before pulsed call (E), and partially pulsed short call within pulsed call (F). The corresponding author will provide tables of raw data for individual specimens on request.

Fig. 2 in Detection of Ophidiomyces ophiodiicola at two mid-Atlantic natural areas in Anne Arundel County, Maryland and Fairfax County, Virginia, USA

Fig. 2. Location of Huntley Meadows Park (HMP) snake capture locations. Black markers = all samples positive; white markers = all samples negative; gray markers = samples either positive or negative.

Fig. 2 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia

Fig. 2. Temporal variation of the number of recaptures (A) and movement patterns (B) of Atelopus laetissimus.

Fig. 1 in Detection of Ophidiomyces ophiodiicola at two mid-Atlantic natural areas in Anne Arundel County, Maryland and Fairfax County, Virginia, USA

Fig. 1. The ventral scales of a symptomatic Northern Black Racer (Coluber constrictor) infected with Ophidiomyces ophiodiicola. This 41 g male was captured and swabbed on 20 May 2018 at Huntley Meadows Park. Its total length was 123.2 cm and snout-to-vent length was 94.6 cm. Photo by Eva Lorentz.

Fig. 3 in Detection of Ophidiomyces ophiodiicola at two mid-Atlantic natural areas in Anne Arundel County, Maryland and Fairfax County, Virginia, USA

Fig. 3. Location of Smithsonian Environmental Research Center (SERC) snake capture locations. Black markers = all samples positive; white markers = all samples negative; gray markers = samples either positive or negative.

Fig. 1 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia

Fig. 1. (A) Temporal variation of relative abundance (ind/[h × obs]). (B) Population density (m2) per habitat of Atelopus laetissimus. Roman numerals represent the months of the surveys.