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Fig. 1 in The Alpheid Shrimp Genus Leptalpheus Williams, 1965, In The Tropical Western Pacific, With Descriptions Of Two New Species (Crustacea: Decapoda: Caridea)

Fig. 1. Leptalpheus denticulatus, new species, female paratype from Nhatrang Bay, Vietnam (USNM 1110002): a, frontal region, dorsal view; b, same, lateral view; c, frontal margin of carapace, lateral view; d, carapace, lateral view; e, right eye, ventrolateral view; f, first segment of right antennular peduncle, lateral view; g, lateral flagellum of right antennule, lateral view; h, right uropod, dorsal view; i, same, detail of exopod, setae omitted; j, telson, dorsal view; k, same, detail of posterior half; l, sixth pleonite and tail fan, setae omitted, lateral view. Scale bars = 1 mm.

Fig. 3 in The Alpheid Shrimp Genus Leptalpheus Williams, 1965, In The Tropical Western Pacific, With Descriptions Of Two New Species (Crustacea: Decapoda: Caridea)

Fig. 3. Leptalpheus denticulatus, new species, female paratype from Nhatrang Bay, Vietnam (USNM 1110002): a, major (left) cheliped, lateral view; b, same, mesial view; c, same, chela, carpus and distal merus, ventrolateral view; d, same, distal portion of chela, mesial view; e, minor (right) cheliped, lateral view; f, same, chela, ventrolateral view. Scale bars = 1 mm.

Fig. 6 in The Alpheid Shrimp Genus Leptalpheus Williams, 1965, In The Tropical Western Pacific, With Descriptions Of Two New Species (Crustacea: Decapoda: Caridea)

Fig. 6. Leptalpheus denticulatus, new species, male from Yaqara Bay, Viti Levu, Fiji (LACM CR 2005-007.1): a, major (left) cheliped, lateral view; b, same, ventrolateral view; c, same, distal chela, ventromesial view; d, same, ventrolateral view; e, minor (right) cheliped, lateral view; f, same, chela, ventrolateral view. g, second pereiopod, lateral view; h, third pereiopod, lateral view; i, fifth pereiopod, lateral view. Scale bars = 1 mm.

Fig. 2 in The Alpheid Shrimp Genus Leptalpheus Williams, 1965, In The Tropical Western Pacific, With Descriptions Of Two New Species (Crustacea: Decapoda: Caridea)

Fig. 2. Leptalpheus denticulatus, new species, a–k: female paratype from Nhatrang Bay, Vietnam (USNM 1110002); l, m: male holotype from Nhatrang Bay (MNHN-Na 17064): a, mandible, mesial view; b, same, molar process; c, maxillule, lateral view; d, maxilla, lateral view; e, first maxilliped, lateral view; f, second maxilliped, lateral view; g, third maxilliped, lateral view; h, second pereiopod, lateral view; i, third pereiopod, lateral view; j, same, distal carpus, propodus and dactylus; k, fifth pereiopod, lateral view; l, second pleopod, lateral view; m, same, detail of appendix masculina and appendix interna. Scale bars = 1 mm; m drawn without scale.

Fig. 10 in The Alpheid Shrimp Genus Leptalpheus Williams, 1965, In The Tropical Western Pacific, With Descriptions Of Two New Species (Crustacea: Decapoda: Caridea)

Fig. 10. Leptalpheus dworschaki, new species, female paratype (ZRC 2005.0085): a, habitus; male holotype (NMCR 27540): b, mandible, mesial view; c, same, dorsolateral view; d, maxillule, lateral view; e, maxilla, lateral view; f, first maxilliped, lateral view; g, second maxilliped, lateral view; h, third maxilliped, lateral view. Scale bar = 1 mm.

opencc-by-4.0Feb 2012View details →

Fig. 2 in Spatial Distribution Of Tropical Estuarine Nematode Communities In Sarawak, Malaysia (Borneo)

Fig. 2. Principal component analysis derived from the mean percentage of particle fractions in each study site. PC 1 and 2

Fig. 1 in Influence of a tropical marina on nearshore fish communities during a harmful algal bloom event

Fig. 1. Stylised maps of Singapore and Raffles Marina (inset). Dotted lines indicate areas outside Raffles Marina where fish traps were deployed.

Fig. 3. Average a in Influence of a tropical marina on nearshore fish communities during a harmful algal bloom event

Fig. 3. Average a) Species richness, b) catch abundance, and c) species diversity (Shannon Wiener index) of fish communities within and outside Raffles Marina before and after a harmful algal bloom event in February 2014 (all means ± SE). DJF-13: December 2013– February 2014; MAM-14: March 2014–May 2014; JJA-14: June 2014–August 2014; SON-14: September 2014–November 2014; DJF-14: December 2014–February 2015. Seasons that are not significantly different are denoted by the same letter (lower case – within marina; upper case – outside marina).

Fig. 2 in Influence of a tropical marina on nearshore fish communities during a harmful algal bloom event

Fig. 2. Principal coordinates analysis of fish communities within and outside Raffles Marina before the harmful algal bloom event in February 2014. The two principal coordinates explained 55.1% of total variation. Factors shown within the circle correlate with PCO1 or PCO2 with a factor of at least 0.5.

Fig. 5 in Influence of a tropical marina on nearshore fish communities during a harmful algal bloom event

Fig. 5. Principal coordinates analysis of fish communities outside Raffles Marina before and after a harmful algal bloom event in February 2014. The two principal coordinates explained 43.2% of total variation. Factors shown within the circle correlate with PCO1 or PCO2 with a factor of at least 0.5. (DJF-13: December 2013–February 2014; MAM-14: March 2014–May 2014; JJA-14: June 2014–August 2014; SON-14: September 2014– ovember 2014; DJF-14: December 2014–February 2015).

Fig. 4 in Influence of a tropical marina on nearshore fish communities during a harmful algal bloom event

Fig. 4. Principal coordinates analysis of fish community within Raffles Marina before and after a HAB event in February 2014. The two principal coordinates explained 38.1% of total variation. Factors shown within the circle correlate with PCO1 or PCO2 with a factor of at least 0.5. (DJF-13: December 2013–February 2014; MAM-14: March 2014–May 2014; JJA-14: June 2014–August 2014; SON-14: September 2014–November 2014; DJF-14: December 2014–February 2015).

Fig. A3 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. A3. Map of the occurrences of Zonitoides arboreus s.l. and Zonitoides nitidus used for the calculation of climatic suitability for the 20 km grid resolution.

Fig. A4 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. A4. Global climatic suitability for: (a) Zonitoides arboreus s.l.; and (b) Zonitoides nitidus based on Mahalanobis distances using the 20 km grid resolution. The higher the threshold, the more dissimilar are the climatic conditions to those of the majority of known occurrences, and>100% means that the climatic conditions are dissimilar to those of any other available record. Please note that the deserts of Africa, Arabia and Australia are unlikely places for a snail that inhabits (temperate) forests in its native range (Z. arboreus s.l.), and that the Great Lakes Region that seems well inhabited by Z. nitidus does not fully match its climate, what can only be explained from effects of averaging local climates at a larger grid scale.

Fig. A1 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. A1. Map of the occurrences of Zonitoides arboreus s.l. used for the calculation of climatic suitability for the 10 km grid resolution.

Fig. 4 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. 4. Position of the new locations (L1 and L2, enumeration for each species separately) in Sabah in relation to the Mahalanobis distances of climatic variables for: (a) Zonitoides arboreus s.l., and (b) Z. nitidus. Record ID refers to the order of the data entry.

Fig. 2 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. 2. Global climatic suitability for (a) Zonitoides arboreus s.l. and (b) Zonitoides nitidus based on Mahalanobis distances from the 10 km grid resolution. The higher the threshold, the more dissimilar are the climatic conditions to those of the majority of known occurrences, and>100 % means that the climatic conditions are dissimilar to those of any other available record.

Fig. 1 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. 1. Estimation of the phylogenetic relationships of the COI barcoding sequence from the Zonitoides specimens and two outgroups (labeled with their BOLD or GenBank accession numbers) using the Maximum Likelihood method based on the Tamura-Nei model. The tree with the highest log likelihood (−2138.3583) is shown. Branch lengths equal genetic distances in terms of the number of base substitutions per site. The percentage of replicate trees in which the associated taxa clustered together in the bootstrap test (500 replicates) are shown next to the branches. The tree was constructed in MEGA 6.0. Please note that the shell of (living) Z. nitidus is darkly pigmented, and that the extended animal of the depicted Z. nitidus started fading.

opencc-by-4.0Mar 2016View details →

Fig. 1 in Pattern of co-occurrence between ant-mimicking jumping spiders and sympatric ants in a Bornean tropical rainforest

Fig. 1. Dorsal views of the model ants and their ant-mimicking spiders, showing the body parts removed legs and antennae. A, Camponotus saundersi; B, Myrmarachne alticephalon; C, Polyrhachis olybia; D, Myrmarachne maxillosa; E, Polyrhachis boltoni; F, Polyrhachis phalerata; G. Myrmarachne malayana.

Fig. A2 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. A2. Map of the occurrences of Zonitoides nitidus used for the calculation of climatic suitability for the 10 km grid resolution.