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Fig. 4 in Assemblages of carabid beetles (Coleoptera: Carabidae) as zoo-indicator of water tourism impact on forest - lake ecotones

Fig. 4. Cluster analysis of the study sites (euclidic distances, Ward˙s method) based on carabid beetle assemblages

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Fig. 3 in Assemblages of carabid beetles (Coleoptera: Carabidae) as zoo-indicator of water tourism impact on forest - lake ecotones

Fig. 3. Model of state of carabid beetle assemblages in pine woodlands (B) and alder woodlands (A) in control area (0), medium pressure (1) and high pressure (2).

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Fig.2 in Assemblages of carabid beetles (Coleoptera: Carabidae) as zoo-indicator of water tourism impact on forest - lake ecotones

Fig.2. Whittaker diagrams of species-abundance of carabid species in alder woodland (left side) and pine woodlands (right side).

Fig. 2 in Molecular and epidemiological surveillance of Plasmodium spp. during a mortality event affecting Humboldt penguins (Spheniscus humboldti) at a zoo in the UK

Fig. 2. Histopathology associated with mortality of a Humboldt penguin (Spheniscus humboldti) infected with Plasmodium sp. Penguin paraffinembedded heart tissue section (5 μm) stained with haematoxylin and eosin a. Four sites of chromogenic in situ hybridization with a Plasmodium-specific probe occurred in what appeared to be cardiac macrophages. Magnification: x10. b. Same Penguin heart tissue sections inspected under light microscopy. Magnification: x100. Exoerythrocytic meronts are seen breaking out of a cardiac macrophage (ellipse).

Fig. 3 in Molecular and epidemiological surveillance of Plasmodium spp. during a mortality event affecting Humboldt penguins (Spheniscus humboldti) at a zoo in the UK

Fig. 3. Temporal distribution of mosquito and Plasmodium spp. prevalence at Chester Zoo between May and November 2017. Continuous top line: total number of mosquitoes collected on a weekly basis; Continuous bottom line: total number of Plasmodium infections; Dashed line: parasite prevalence estimated as a proportion of infected mosquitoes of the total captured on a weekly basis.

Fig. 1 in Molecular and epidemiological surveillance of Plasmodium spp. during a mortality event affecting Humboldt penguins (Spheniscus humboldti) at a zoo in the UK

Fig. 1. Mosquito abundance and Plasmodium prevalence compared at ten sampling sites across Chester Zoo. The Chester Zoo site (zoo perimeter is outlined) overlaid with a heat map of total mosquito numbers trapped at 10 sampling sites. Locations of traps are indicated by numbers 1–7, 10–12 inclusive. The location of the penguin exhibit in 2017 is indicated by a penguin symbol. a. Mosquito abundance. b. Plasmodium prevalence in trapped mosquitoes. Heat maps were generated using Heatmapper with a Gaussian radius multiplier of 1.

Fig. 4 in Molecular and epidemiological surveillance of Plasmodium spp. during a mortality event affecting Humboldt penguins (Spheniscus humboldti) at a zoo in the UK

Fig. 4. Maximum likelihood phylogeny of Plasmodium spp. cytb sequences. The phylogeny was estimated from a 378bp multiple sequence alignment using a GTR+Γ+І model (α = 0.488; proportion of invariant sites = 0.248). The tree is rooted with an outgroup of Leucocytozoon sequences (boxed). Node accuracy is indicated by an SH-like log-Likelihood ratio metric; bootstrap values greater than 0.5 are displayed in the tree. Novel sequences obtained in this study are shaded with their corresponding reference sequence; P. matutinum (MK443241), P. vaughani (MK652243) and P. relictum (JN164731). The clusters contain sequences derived from penguins, mosquitoes or wild birds, which is indicated by a penguin, mosquito or a bird symbol. One wild bird sequence is present in the P. matutinum cluster (OM912814); and three (MW814062, MW814149, MW814045), two (MW814453, MW814028) and two (MW814503, MW814500) mosquito sequences are present in the P. matutinum, P vaughani and P. relictum clusters respectively. The rest of the sequences in those clusters correspond to 23 novel sequences from penguins infected in the UK, indicating their origin (CZ: Chester Zoo, LZ: London Zoo, PZ: Paignton Zoo, BZ: Blackpool Zoo, CWP: Cotswold Wildlife Park) and year of sampling, if not 2017. Other shade sequences correspond to recognized morphospecies. P. vaughani cluster represents 145 novel sequences, P. matutinum cluster represents 345 novel sequences and P. relictum clusters represents 31 novel sequences. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

Fig. 4 in Giardia duodenalis in a clinically healthy population of captive zoo chimpanzees: Rapid antigen testing, diagnostic real-time PCR and faecal microbiota profiling

Fig. 4. | Faecal bacterial community profile of captive chimpanzees infected with Giardia duodenalis detected by rapid antigen test. (A) Relative abundance of colour coded bacterial phyla separated based on presence (+) or absence (‒) of Giardia using rapid antigen test (RAT). The sample identity is located at the bottom of the graph with two labels (C20, C3) shaded indicating samples that were found as Giardia positive by real-time PCR. (B) Alpha diversity based on observed OTU and Shannon's index plotted as box plot and evaluated using t-tests. (C) Principal coordinates analysis (PCoA) 2D plot using first two principal components from Bray-Curtis dissimilarity matrix at the genus taxonomic levels. The clustering between Giardia positive (RAT+) and negative (RAT-) samples was tested using ANOSIM. (D) Linear discriminant analysis effect size (LEfSe) used plot of significant factors discriminating G. duodenalis positive from negative sample. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

Fig. 3 in Giardia duodenalis in a clinically healthy population of captive zoo chimpanzees: Rapid antigen testing, diagnostic real-time PCR and faecal microbiota profiling

Fig. 3. | Faecal bacterial community profile of captive chimpanzees infected with Giardia duodenalis as detected by rapid antigen test and real-time PCR combined. (A) Relative abundance of colour coded bacterial phyla separated based on presence (+) or absence (‒) of Giardia. The sample identity is located at the bottom of the graph. (B) Alpha diversity based on observed OTU and Shannon's index plotted as box plot and evaluated using t-tests. (C) Principal coordinates analysis (PCoA) 2D plot using first two principal components from Bray-Curtis dissimilarity matrix at the genus taxonomic levels. The clustering between Giardia positive (+) and negative (‒) samples was tested using ANOSIM. (D) Linear discriminant analysis effect size (LEfSe) used plot of significant factors discriminating G. duodenalis positive from negative sample. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

Fig. 2 in Giardia duodenalis in a clinically healthy population of captive zoo chimpanzees: Rapid antigen testing, diagnostic real-time PCR and faecal microbiota profiling

Fig. 2. | Results of Giardia duodenalis rapid antigen test applied on faecal samples from chimpanzees. A positive result for the Giardia duodenalis rapid antigen test (RAT, Anigen Rapid Giardia AG Test Kit) is represented by the line in the 'T' position in the window along with the positive control line in the 'C' position.

Fig. 1 in Giardia duodenalis in a clinically healthy population of captive zoo chimpanzees: Rapid antigen testing, diagnostic real-time PCR and faecal microbiota profiling

Fig. 1. Captive chimpanzees and their enclosure in Sydney, Australia. (A) Main chimpanzee open air exhibit with multiple climbing structures. (B) View from the other direction showing entry to the indoor area at the end of the exhibit. (C) smaller exhibit with mesh covering and more climbing and sleeping structures. (D) Members of the chimpanzee troop at the Taronga Zoo.

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Fig. 1. a in Parasitological examination results of zoo animals in Germany between 2012 and 2022

Fig. 1. a) Trichodina spp. from a koi; b) Egg of Ascaridia platyceri from a Platycercus elegans; c) Egg of Oxyurida from a turtle; d) Egg of Enterobius vermicularis from a chimpanzee; e) Haematomyzus elephantis from an elephant; f) Ornithonyssus bacoti from a hamster.

Figure 6 in Zoo-based amphibian research and conservation breeding programs

Figure 6. Visitor experience. An interactive educational amphibian exhibit at St. Petersburg Zoo, Russian Federation, not only informs, but also provides tactility to increase fun and experience retention. Image by Mikhail Bagaturov.

Figure 5 in Zoo-based amphibian research and conservation breeding programs

Figure 5. Fea's tree frog (Rhacophorus feae) from SE Asia, possibly the largest species of tree frog in the world. Found in high montane forests and recently captive bred for the first time at Leningrad Zoo. Image by Mikhail F. Bagaturov.

Figure 3. Hellbender sperm sampling. A in Zoo-based amphibian research and conservation breeding programs

Figure 3. Hellbender sperm sampling. A team led by Dale McGinnity, Nashville Zoo at Grassmere, Tennessee, USA, is creating the first genetically representative gene bank for any amphibian put forth using the hellbender (C. alleganiensis). Image by Sally Nofs.

Figure 2 in Zoo-based amphibian research and conservation breeding programs

Figure 2. Neurergus kaiseri. In a pioneering program, Sedg- wick County Zoo, Kansas, USA, is breeding for sale the critically endangered Loristan newt (Neurergus kaiseri) to support field work and conservation in Iran and to increase stocks with private breeders. Image by Nate Nelson.

Figure 4 in Zoo-based amphibian research and conservation breeding programs

Figure 4. Trachycephalus nigromaculatus. The black-spotted casque-headed treefrog (Trachycephalus nigromaculatus) is an excellent display species because it is large (10 cm), spectacu- lar, and sits in the open. These frogs are very popular pets in the Russian Federation. Image by Mikhail Bagaturov.

Figure 1 in Zoo-based amphibian research and conservation breeding programs

Figure 1. Research in zoos, such as this study on tadpole growth and development at Antwerp Zoo, can make substan- tial contributions to conservation breeding programs. Image by Robert Browne.

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Linked collectors and determiners for: BHZB - Herbário do Jardim Botânico da Fundação Zoo-Botânica de Belo Horizonte.

Natural history specimen data linked to collectors and determiners held within, "BHZB - Herbário do Jardim Botânico da Fundação Zoo-Botânica de Belo Horizonte". Claims or attributions were made on Bionomia by volunteer Scribes, <a href="https://bionomia.net/dataset/fd99455d-f6e9-4421-930a-5d8e23ac8895">https://bionomia.net/dataset/fd99455d-f6e9-4421-930a-5d8e23ac8895</a> using specimen data from the dataset aggregated by the Global Biodiversity Information Facility, <a href="https://gbif.org/dataset/fd99455d-f6e9-4421-930a-5d8e23ac8895">https://gbif.org/dataset/fd99455d-f6e9-4421-930a-5d8e23ac8895</a>. Formatted as a Frictionless Data package.