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opencc-by-4.0Oct 2014View details →

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

Fig. 15 in New records of Adelidae from forested habitats of Calabria (South Italy) with an update of the Italian ckecklist (Lepidoptera: Adeloidea)

Fig. 15 – Distribution of Adelidae in the Calabria region. Map created with SimpleMappr (http://www.simplemappr.net).

Figs 11-12 in New records of Adelidae from forested habitats of Calabria (South Italy) with an update of the Italian ckecklist (Lepidoptera: Adeloidea)

Figs 11-12 – Comparison of antennae in the genus Nematopogon. 11, N. robertella, Pietra del Signore; 12, N. garganellus, Bosco dei Gesuiti.

Fig. 10 in New records of Adelidae from forested habitats of Calabria (South Italy) with an update of the Italian ckecklist (Lepidoptera: Adeloidea)

Fig. 10 – Male genitalia of Nematopogon robertella, Pietra del Signore (microscope slide: CREA-0237).

Figs 1-8 in New records of Adelidae from forested habitats of Calabria (South Italy) with an update of the Italian ckecklist (Lepidoptera: Adeloidea)

Figs 1-8 – Adults of Adelidae. 1, Nemophora metallica, Croce di Magara, 17mm; 2, Nemophora scopolii, Croce di Magara, 21mm; 3, Adela mazzolella, Righio, 12mm; 4, Adela reaumurella, Passo della Crocetta, 15mm; 5, Nematopogon robertella, Pietra del Signore, 15mm; 6, Nematopogon sericinellus, Carraci, 14mm; 7, Nematopogon swammerdamella, Timpone Magara, 22mm; 8, Nematopogon garganellus, Bosco Gesuiti, 19mm.

Fig. 4 in Seasonal and spatial dispersal patterns of select ambrosia beetles (Coleoptera: Curculionidae) from forest habitats into production nurseries

Fig. 4. Mean (± SE) captures of Cnestus mutilatus, Xylosandrus compactus, X. cra`ssiusculus, and X. germanus in ethanol-baited Baker traps deployed at various distances from the nursery–forest interface at 2 sites in South Carolina in 2011 and 2012.

Fig. 3 in Seasonal and spatial dispersal patterns of select ambrosia beetles (Coleoptera: Curculionidae) from forest habitats into production nurseries

Fig. 3. Mean captures of Cnestus mutilatus, Xylosandrus compactus, X. crassiusculus, and X. germanus in ethanol-baited Baker traps at 2 sites in Louisiana and Mississippi in 2013 and 2014.

Fig. 1 in Seasonal and spatial dispersal patterns of select ambrosia beetles (Coleoptera: Curculionidae) from forest habitats into production nurseries

Fig. 1. Satellite image of the Mississippi research site (Google, Mountain View, California, USA) with an overlay showing a randomized complete block design of 5 blocks. Representing the 2013 test, each block shown here had a trap placed at −25, 25, 50, 100, and 200 m from the nursery–forest interface.

Fig. 5 in Seasonal and spatial dispersal patterns of select ambrosia beetles (Coleoptera: Curculionidae) from forest habitats into production nurseries

Fig. 5. Mean (± SE) captures of Cnestus mutilatus, Xylosandrus compactus, X. crassiusculus, and X. germanus in ethanol-baited Baker traps deployed at various distances from the nursery–forest interface at 2 sites in Louisiana and Mississippi in 2013 and 2014.

Fig. 4 in Habitat requirements and occurrence of Crematogaster pilosa (Hymenoptera: Formicidae) ants within intertidal salt marshes

Fig. 4. Logistic regression model (P = 0.03) of the probability of Crematogaster pilosa as a function of brown leaf density between 0.61 and 1.20 m. Stars indicate plots containing ants, and open symbols indicate plots not containing ants. Vertical dashed line represents a 50% probability of ants and occurs at a brown leaf density of 2.5 m−1, which equals 1.5 brown leaves between 0.61 and 1.20 m above the marsh surface.

Fig. 2 in Habitat requirements and occurrence of Crematogaster pilosa (Hymenoptera: Formicidae) ants within intertidal salt marshes

Fig. 2. Mean vegetation heights for marsh plots containing ants (n = 8) and plots not containing ants classified by their dominant vegetation type: short (n = 7) and tall (n = 2). All plots were from Dean Creek and Odum's Marsh. Mean heights are the weighted average of all vegetation counts within plots. Letters above whiskers signify significant difference using Tukey's HSD with P <0.05.

Fig. 1 in Habitat requirements and occurrence of Crematogaster pilosa (Hymenoptera: Formicidae) ants within intertidal salt marshes

Fig. 1. Southern tip of Sapelo Island, Georgia (USA). Location of Crematogaster pilosa observations and vegetation assessments in Odum's Marsh (A) and Dean Creek (C). Presence/absence of ants along Lighthouse Creek (B) from canoe and baited trap survey. Sites containing C. pilosa were labeled "ants", those not containing ants were labeled by their vegetation (i.e., short or tall) based on maximum vegetation height.

Fig. 3 in Habitat requirements and occurrence of Crematogaster pilosa (Hymenoptera: Formicidae) ants within intertidal salt marshes

Fig. 3. Height-specific vegetation density for marsh plots with and without ants in Dean Creek and Odum's Marsh. Vegetation density is the number of vegetation features (i.e., stems and leaves) per vertical meter above an average point on the marsh surface. Integrating vertically produces the average number of vegetation features above a single point. All plots containing Crematogaster pilosa were grouped (ants); plots not containing ants were classified by the maximum vegetation height of Spartina alterniflora (i.e., tall or short). Vegetation density distributions are the means for tall (n = 2), ants (n = 8), and short (n = 7) plots.

opencc-by-4.0Dec 2015View details →

Fig. 2 in Predation of stink bugs (Hemiptera: Pentatomidae) by a complex of predators in cotton and adjoining soybean habitats in Georgia, USA

Fig. 2. Least squares means (± SE) for number of stink bugs (species combined) and Orius insidiosus per 1.83 m length of row and percentage of predators positive for stink bug DNA in soybean and cotton by treatment. Within an insect group in a crop, treatment means with the same lowercase letter are not significantly different (Tukey's HSD, P> 0.05).

opencc-by-4.0Dec 2015View details →

Fig. 4 in Predation of stink bugs (Hemiptera: Pentatomidae) by a complex of predators in cotton and adjoining soybean habitats in Georgia, USA

Fig. 4. Least squares means (± SE) for number of stink bugs (species combined) and Oxyopes salticus per 1.83 m length of row and percentage of predators positive for stink bug DNA in (A) soybean and cotton by treatment and (B) soybean and cotton by sampling week. Within an insect group in a crop, treatment or week means with the same lowercase letter are not significantly different (Tukey's HSD, P> 0.05). Only 1 Ox. salticus individual screened positive for stink bug (Nexara viridula) DNA in cotton. No predators were collected for PCR analyses in weeks 4 and 5 in cotton.

opencc-by-4.0Oct 2022View details →

Fig. 1 in Short Communication Contribution to the knowledge of Ypsolophidae from forested habitats of Southern Italy with an update of the Italian checklist of the genus Ypsolopha Latreille 1796 (Lepidoptera: Yponomeutoidea)

Fig. 1 - Species of the genus Ypsolopha found in Calabria. / Specie del genere Ypsolopha trovate in Calabria. a) Y. alpella, 01.X.2019, Campanella, Sellia, Catanzaro. b) Y. mucronella, 10.V.2016, Il Palmento, Serra San Bruno, Vibo Valentia. c) Y. nemorella, 7.VIII.2013, Fosso Cucolo, Donnici, Cosenza. d) Y. parenthesella, 31.VIII.2016, Piano del minatore, Saracena, Cosenza. e) Y. persicella, 9.XI.2015, Glicarello, Montalto Uffugo, Cosenza. f) Y. scabrella, 17.VIII.2017, Sciortaglie, Alessandria del Carretto, Cosenza. g) Y. sequella, 19.VII.2017, Sciortaglie, Alessandria del Carretto, Cosenza. h) Y. ustella, 25.IX.2019, Coturelle, Albi, Catanzaro. i) Y. vittella, 5.VIII.2013, Pianette, Dipignano, Cosenza.

opencc-by-4.0Oct 2022View details →

Fig. 1 in Epiphytic lichens of woodland habitats in the lower Ticino river valley and in the "Bosco Siro Negri" Integral Nature State Reserve (NW Italy)

Fig. 1 - The study area, corresponding to the lower Ticino River valley. The "Bosco Siro Negri" Integral Nature State Reserve is indicated with a black star, the 15 well-preserved woodlands with white stars, the 15 degraded woodlands with white triangles and the 15 poplar plantations with white circles. Patches of vegetation attributed to Habitat 91F0 are highlighted with a vertical line pattern. / L'area di studio, corrispondente alla bassa valle del Ticino. La Riserva Naturale Integrale Statale "Bosco Siro Negri" è indicata con una stella nera, i 15 boschi ben conservati con stelle bianche, i 15 boschi degradati con triangoli bianchi e i 15 pioppeti con cerchi bianchi. Le aree con vegetazione attribuita all'Habitat 91F0 sono evidenziate con una trama a linee verticali.

opencc-by-4.0Oct 2022View details →

Fig. 1 in Habitat selection of the roe deer Capreolus capreolus (Artiodactyla: Cervidae) in an agroforestry system

Fig. 1 - Study area: Vallevecchia (Venice). The walked transects (T1 to T6) are highlighted in red. / Area di studio: Vallevecchia (Venezia). I transetti percorsi (da T1 a T6) sono evidenziati in rosso.

opencc-by-4.0Jul 2014View details →

Fig. 1 in Eurasian badger Meles meles habitat and sett site selection in the northern Apennines

Fig. 1 - Geographic position of the study area, with Sett Points, Random Points and water (rivers and streams) layer.