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Fig. 5 in Proliferation of the invasive termite Coptotermes gestroi (Isoptera: Rhinotermitidae) on Grand Cayman and overall termite diversity on the Cayman Islands

Fig. 5. Termite sampling localities from UF Termite Collection (for purposes of space, the geographic positions of Little Cayman and Cayman Brac are not related to that of Grand Cayman).

Fig. 9 in Proliferation of the invasive termite Coptotermes gestroi (Isoptera: Rhinotermitidae) on Grand Cayman and overall termite diversity on the Cayman Islands

Fig. 9. Areas predicted as infested by the simulation model for Coptotermes gestroi over Grand Cayman Island. Sampled termite locations in 2014 are mapped (points). Yellow, orange, and red cells indicate the>0%, ≥50%, and 100% occupancy envelopes, respectively.

Fig. 10 in Proliferation of the invasive termite Coptotermes gestroi (Isoptera: Rhinotermitidae) on Grand Cayman and overall termite diversity on the Cayman Islands

Fig. 10. Caribbean basin survey localities for all termites (blue dots) and for Microcerotermes species only (orange dots) (Source: UF Termite Collection).

Fig. 2. Hierarchical cluster analysis with 2 in Proliferation of the invasive termite Coptotermes gestroi (Isoptera: Rhinotermitidae) on Grand Cayman and overall termite diversity on the Cayman Islands

Fig. 2. Hierarchical cluster analysis with 2 (a), 3 (b), 4 (c), and 5 (d) clusters for Coptotermes gestroi over Grand Cayman Island.

Fig. 4 in Proliferation of the invasive termite Coptotermes gestroi (Isoptera: Rhinotermitidae) on Grand Cayman and overall termite diversity on the Cayman Islands

Fig. 4. Vector-type layers used to obtain a surface of unsuitable habitat for Coptotermes gestroi on Grand Cayman Island.

Fig. 3. Collection localities for Coptotermes gestroi over Grand Cayman Island and 102 in Proliferation of the invasive termite Coptotermes gestroi (Isoptera: Rhinotermitidae) on Grand Cayman and overall termite diversity on the Cayman Islands

Fig. 3. Collection localities for Coptotermes gestroi over Grand Cayman Island and 102 random points.

Fig. 1 in Proliferation of the invasive termite Coptotermes gestroi (Isoptera: Rhinotermitidae) on Grand Cayman and overall termite diversity on the Cayman Islands

Fig. 1. Coptotermes gestroi localities in the greater Caribbean Basin (Source: UF Termite Collection).

Fig. 1 in Morphological and genetic evidence for the synonymy of Reticulitermes species: Reticulitermes dichrous and Reticulitermes guangzhouensis (Isoptera: Rhinotermitidae)

Fig. 1. Photomicrographs of dorsal (A, D, E, F, I, and J), ventral (B and G), and lateral (C and H) views of Reticulitermes dichrous (A to E) and Reticulitermes guangzhouensis (F to J) soldier heads and pronotums.

Fig. 4 in Morphological and genetic evidence for the synonymy of Reticulitermes species: Reticulitermes dichrous and Reticulitermes guangzhouensis (Isoptera: Rhinotermitidae)

Fig. 4. Maximum likelihood phylogenetic tree of Reticulitermes guangzhouensis and Reticulitermes dichrous relative to other Reticulitermes species based on the 16S rRNA gene. Bootstrap values are indicated at the nodes and represent 1,000 pseudoreplicates.

Fig. 3 in Morphological and genetic evidence for the synonymy of Reticulitermes species: Reticulitermes dichrous and Reticulitermes guangzhouensis (Isoptera: Rhinotermitidae)

Fig. 3. Maximum likelihood phylogenetic tree of Reticulitermes guangzhouensis and Reticulitermes dichrous relative to other Reticulitermes species based on the COII gene. Bootstrap values are indicated at the nodes and represent 1,000 pseudoreplicates.

Fig. 2 in Morphological and genetic evidence for the synonymy of Reticulitermes species: Reticulitermes dichrous and Reticulitermes guangzhouensis (Isoptera: Rhinotermitidae)

Fig. 2. Cluster dendrogram of 12 populations of Reticulitermes guangzhouensis and 8 populations of Reticulitermes dichrous.

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Fig. 3 in Use of baits for the evaluation of underground termites (Blattodea: Rhinotermitidae) in different habitats of the southern Amazon region

Fig. 3. Queen of Heterotermes tenuis (center circle) in early stage of egg production (circle on lef), and colony formation inside the cardboard bait in southern Amazonia.

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Fig. 2 in Use of baits for the evaluation of underground termites (Blattodea: Rhinotermitidae) in different habitats of the southern Amazon region

Fig. 2. Predominant termites in this study in southern Amazonia: (A) Nasutitermes sp. soldier; (B) Heterotermes tenuis soldier.

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Fig. 1 in Use of baits for the evaluation of underground termites (Blattodea: Rhinotermitidae) in different habitats of the southern Amazon region

Fig. 1. Spatial arrangement of Termitrap® baits within plots for subterranean termite survey in different environments in southern Amazonia.

Fig. 4 in Methods for collecting large numbers of exuviae from Coptotermes (Blattodea: Rhinotermitidae) termite colonies

Fig. 4. (A) Coptotermes gestroi workers under observation on a filter paper with a 0.05% Nile Blue A and deionized water solution in a Petri dish; (B) media pad with deionized water taped to the cover of the Petri dish; (C) plastic Petri dish used to hold recently molted termites and termites that acquired dye; (D) vial used to hold exuviae; and (E) plastic container lined with a paper towel moistened with deionized water.

Fig. 3 in Methods for collecting large numbers of exuviae from Coptotermes (Blattodea: Rhinotermitidae) termite colonies

Fig. 3. Coptotermes gestroi workers (n = 1,000) on a media pad saturated with a 0.05% Nile Blue A and deionized water solution in a Petri dish wrapped with Parafilm.

Fig. 2 in Methods for collecting large numbers of exuviae from Coptotermes (Blattodea: Rhinotermitidae) termite colonies

Fig. 2. Overview of the methods. Coptotermes gestroi workers (n = 1,000) were placed on a Nile Blue A-dyed media pad for 2 d in a Petri dish. Dyed and non-dyed workers were separated. Non-dyed workers, potentially under pre-molt fast, were placed on a Nile Blue A-dyed filter paper and observed for 7 d in a Petri dish. Exuviae, newly molted workers, dyed workers (that acquired dye from the filter paper during the 7 d observation), and cadavers were collected.

Fig. 1 in Methods for collecting large numbers of exuviae from Coptotermes (Blattodea: Rhinotermitidae) termite colonies

Fig. 1. Laboratory colony rearing units. (A) Plastic cylindrical vial containing moistened organic soil, wood blocks, and agar used to house termite colonies from 0 to 1-yr-old; (B) larger cylindrical vial the colony was transferred to for colonies 1 to 2-yr-old; (C) plastic container in which the uncapped cylindrical vial (pictured in B) was placed into for colonies 2 to 4-yr-old; (D) plastic container in which the uncovered container (from C) was placed into for colonies aged 4+ yr. Red line points to vial within the box that usually contains the central nest (location of reproductives and brood).

Fig. 6 in Methods for collecting large numbers of exuviae from Coptotermes (Blattodea: Rhinotermitidae) termite colonies

Fig. 6. Mean ± standard error of (A) exuviae collected; (B) newly molted individuals observed; (C) workers that acquired Nile Blue A dye during the 7 d observation; and (D) cadavers collected during observation of 163.0 ± 48.2 Coptotermes gestroi workers (n = 3) that were potentially in pre-molt fast.