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opennotspecifiedAug 2011View details →

Distribution. Sulawesi and adjacent Is (Buton, Kabaena, Muna, Peleng, Lembeh, and on some of the Togian Is); thought to be extinct on Selayar I. Pigs have been widely domesticated through the Indonesian archipelago and beyond. This primarily involved the Eurasian Wild Pig (S. scrofa), but also S. celebensis, the only other species of pig successfully domesticated. Mitochondrial DNA studies of the dispersion of these domesticated forms agree on three major dispersal events, two involving S. scrofa and one S. celebensis. Evidence supports an early human-mediated translocation of S. celebensis to Flores and Timor and two later, separate human-mediated dispersals of domestic pig through islands of SE Asia into Oceania. In addition to Flores and Timor, S. celebensis is also thought to occur in its domesticated form on Halmahera, Lendu, Roti, and Savur Is, and even on Simeulue and Nias Is to the W of Sumatra and far from its island of origin, Sulawesi. In the Moluccas, and possibly elsewhere in this region, introduced S. celebensis are thought to have hybridized with other introduced pigs of S. scrofa derivation, and apparent hybrids between these species are now reported to survive on a number of islands, including Salawatti, Great Kei, Dobu, Seram, Ambon, Bacan, Ternate, Morotai, and New Guinea. It is also reported that in the 19" century the sows of domestic pigs in Sulawesi frequently mated with wild animals, after which they returned to their villages. in Suidae

Distribution. Sulawesi and adjacent Is (Buton, Kabaena, Muna, Peleng, Lembeh, and on some of the Togian Is); thought to be extinct on Selayar I. Pigs have been widely domesticated through the Indonesian archipelago and beyond. This primarily involved the Eurasian Wild Pig (S. scrofa), but also S. celebensis, the only other species of pig successfully domesticated. Mitochondrial DNA studies of the dispersion of these domesticated forms agree on three major dispersal events, two involving S. scrofa and one S. celebensis. Evidence supports an early human-mediated translocation of S. celebensis to Flores and Timor and two later, separate human-mediated dispersals of domestic pig through islands of SE Asia into Oceania. In addition to Flores and Timor, S. celebensis is also thought to occur in its domesticated form on Halmahera, Lendu, Roti, and Savur Is, and even on Simeulue and Nias Is to the W of Sumatra and far from its island of origin, Sulawesi. In the Moluccas, and possibly elsewhere in this region, introduced S. celebensis are thought to have hybridized with other introduced pigs of S. scrofa derivation, and apparent hybrids between these species are now reported to survive on a number of islands, including Salawatti, Great Kei, Dobu, Seram, Ambon, Bacan, Ternate, Morotai, and New Guinea. It is also reported that in the 19" century the sows of domestic pigs in Sulawesi frequently mated with wild animals, after which they returned to their villages.

opencc-zeroApr 2022View details →

Microbiomes of guppy populations translocated in Trinidadian streams

An organisms' gut microbiome can alter its fitness, yet we do not know how gut microbiomes change as their hosts evolve in the wild. We took advantage of a five-decade 'chronosequence' of translocated fish populations to examine associated changes in the gut microbiome. Populations of Trinidadian guppies have displayed parallel phenotypic convergence six times when moved from high predation (HP) to low predation (LP) environments. Across four drainages, we found microbiomes of fish translocated 5-6 years prior to sampling were already distinct from the microbiomes of their HP source populations. Changes in environmental conditions were most important in driving this shift, followed by phenotypic shifts in gut morphology. After 30-60 years in LP environments, microbiome composition was still distinct from native LP populations, but microbiome function was not. We found some evidence that nitrogen fixation enhanced gut nutrient absorption, but most functional shifts were not parallel across drainages. Stream-and drainage-specific signatures were present for both composition and function, despite our overall finding of consistent microbiome change across drainages. As we unravel the complexities of host-microbiome evolution in the wild, studies should consider environmental microbial colonization, host phenotypic plasticity in nature, and more realistic environmental conditions excluded from laboratory studies.

opennotspecifiedJun 2015View details →

Distribution. SW Australia, only known from Fitzgerald River National Park in Western Australia and on Boullanger and Whitlock Is. Successfully translocated into Peniup proposed nature reserve, Stirling Range National Park, and Escape I, all in Western Australia. in Dasyuridae

Distribution. SW Australia, only known from Fitzgerald River National Park in Western Australia and on Boullanger and Whitlock Is. Successfully translocated into Peniup proposed nature reserve, Stirling Range National Park, and Escape I, all in Western Australia.

opennotspecifiedJun 2015View details →

Distribution. SW Australia, only known from Fitzgerald River National Park in Western Australia and on Boullanger and Whitlock Is. Successfully translocated into Peniup proposed nature reserve, Stirling Range National Park, and Escape I, all in Western Australia. in Dasyuridae

opennotspecifiedNov 2017View details →

Distribution. Extensive, but sparse and discontinuous, distribution in monsoonal N Australian mainland, extending S to the Pilbara region; present also on Thevenard I, oft NW Western Australia. Translocated to nearby Serrurier I. in Muridae

Distribution. Extensive, but sparse and discontinuous, distribution in monsoonal N Australian mainland, extending S to the Pilbara region; present also on Thevenard I, oft NW Western Australia. Translocated to nearby Serrurier I.

opencc-by-4.0Jun 2021View details →

Nanopore Translocation Signal

This dataset contains a set of nanopore translocation current traces. It is divided in two parts. Part I: This part contains artificially generated traces with different levels of background noise (SNR = 4, 2, 1, 0.5, and 0.25) For each noise level, three parameters are varied in data generation: a. Twenty different concentrations of nanoparticles as the analytes (Cnp): 0.013, 0.016, 0.020, 0.025, 0.032, 0.040, 0.050, 0.063, 0.080, 0.1, 0.13, 0.16, 0.20, 0.25, 0.32, 0.40, 0.50, 0.63, 0.80, and 1, with the unit of nano-molar, [nM]. b. Fifteen different diameters of the nanoparticles (Dnp): 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14, 15, 16, and 17, with the unit of nanometer, [nm]. c. Five different translocation durations (Duration): 0.5, 1.0, 1.5, 3.0, and 5.0, with the unit of millisecond, [ms]. In total we have 20*15*5=1500 current traces for each SNR. There are three datasets: training, validation and test. Traces in training datasets are of 20 seconds, traces in validation and test datasets are 10 seconds long. For SNR = 4, training, validation and test datasets are provided. For other SNRs, only test traces are provided. Pert II: This part contains real experimental datasets, the translocation of Lambda DNA and Streptavidin with 6 current traces each at different bias voltages. Each Lambda DNA trace has 71 seconds, while each Streptavidin trace has 126 seconds. Two truncated pyramid shape nanopores were used in our experiments, one with a side length of 7.5 nm and another 16 nm, both in a 55 nm-thick silicon layer, for DNA and protein streptavidin translocation, respectively. The DNA and streptavidin were dispersed in 500 mM KCl electrolyte with a concentration of 78 pM and 84 nM, respectively.   Details of artificially generated data and experimental data can be found in our paper: Dario Dematties, Chenyu Wen, Mauricio David Pérez, Dian Zhou, Shi-Li Zhang. Deep learning of nanopore sensing signals using a bi-path network. arXiv:2105.03660. Trained and Validated Models In this data set we also include all the trained and best validated models evaluated in our paper. Nanopore Translocation Detector Trained and Validated Models  In this data set we also include all the trained and best validated models evaluated in our newer paper: A Generalized Transformer-Based Pulse Detection Algorithm

opencc-zeroJul 2022View details →

Evolutionary processes in an undescribed eucalypt: implications for the translocation of a critically endangered species

Background and Aims Knowledge of the evolutionary processes responsible for the distribution of threatened and highly localised species is important for their conservation. Population genomics can provide insights into evolutionary processes to inform management practices, including the translocation of threatened plant species. In this study, we focus on a critically endangered eucalypt, Eucalyptus sp. Cattai, which is restricted to a 40 km 2 area of Sydney, Australia and is threatened by increased urbanisation. Eucalyptus sp. Cattai is yet to be formally described in part due to its suspected hybrid origin. Here, we examined evolutionary processes and species boundaries in E. sp. Cattai to determine whether translocation was warranted. Methods We used genome-wide scans to investigate the evolutionary relationships of E. sp. Cattai with related species, and to assess levels of genetic health and admixture. Morphological trait and genomic data were obtained from seedlings of E. sp. Cattai propagated in a common garden to assess their genetic provenance and hybrid status. Key Results All analyses revealed that E. sp. Cattai was strongly supported as a distinct species. Genetic diversity varied across populations, and clonality was unexpectedly high. Interspecific hybridisation was detected, and was more prevalent in seedlings compared to in situ adult plants, indicating that post-zygotic barriers may restrict the establishment of hybrids. Conclusions Multiple evolutionary processes (e.g., hybridisation and clonality) can operate within the one rare and restricted species. Insights regarding evolutionary processes from our study were used to assist with the translocation of genetically 'pure' and healthy ex situ seedlings to nearby suitable habitat. Our findings demonstrate that it is vital to provide an understanding of evolutionary relationships and processes with an examination of population genomics in the design and implementation of an effective translocation strategy.

opencc-zeroOct 2022View details →

Post-release survival and dispersal of translocated crest-tailed mulgara Dasycercus cristicauda

Initial translocations are inherently risky due to uncertainty around species-specific responses to novel environments. Incorporating a range of release protocols can minimise risks of translocation failure. We identified post-translocation hyperdispersal as a risk to the first translocation of the crest-tailed mulgara (Dasycercus cristicauda), an Australian carnivorous marsupial, and tested temporary confinement and releasing females with pouch young as mitigation strategies. We released 16 females with pouch young and 3 males into unoccupied burrows within a 20 km2 feral animal exclosure, either within temporary confinement pens (n = 10) or without confinement (immediate release) (n = 9). Temporary confinement did not influence survival but did influence dispersal behaviour. Thirty-seven percent of translocated individuals (all 3 males, 4 of 16 females) hyperdispersed (3.0–11.6 km) outside the study exclosure after release, including 42% immediate release animals and 29% temporary confinement animals. No males remained in the exclosure at the study end. Confined females settled closer to their release site. Release of females with pouch young led to an increase in the translocated population from 9 to 58 individuals within 4 months. Releasing females with young from geographically distant sites may be important to offset male hyperdispersal. Our results suggest that temporary confinement and translocating breeding females are important release protocols for species with a propensity for hyperdispersal post-translocation.

opencc-zeroMay 2024View details →

Successful conservation translocation: Population dynamics of tiger recovery in Panna Tiger Reserve, Central India

Tiger (Panthera tigris) is an indicator species of ecological health and conservation efforts. Due to excessive poaching, the tiger was locally extinct in Panna Tiger Reserve, central India. Subsequent successful reintroduction efforts have brought the species back from the verge of extinction and have demonstrated the success of conservation translocations in response to such critical situations. To understand the demographic characteristics of the tigers reintroduced to Panna Tiger Reserve, we used an ensemble approach of different sampling techniques and direct observations from a long-term data-set spanning more than 10 years. We evaluated different demographic indicators (population status, growth rate, mean litter size, inter-birth interval, and survival probability). Since reintroduction in 2009, 18 females have recruited 120 cubs from 45 litters. This led to 59 individuals in 2021 with a growth rate of ~26%. The mean litter size was 2.66 (SE 0.1), and the inter-birth interval was 19.16 months (SE 0.5). The high survival rate of the reintroduced population (0.82±0.2) helped to achieve the success of reintroduction. We observed non-constant mortality trajectories for both sexes (higher survival probabilities for females) with a moderately higher risk of death in younger (<1 year) and older (>10 years) individuals. Our results showed the effectiveness of translocation and conservation efforts. The recovered population can be used as a founder for augmentation in other recovering tiger populations. A long-term tiger-centric management plan should be implemented in the area adjacent to Panna Tiger Reserve to conserve and secure the habitat of the entire landscape for the long-term survival of the reintroduced population in a metapopulation framework.

opencc-by-4.0Sep 2024View details →

European Plant Translocation Database

Open the record for dataset details and reuse information.

opencc-by-4.0Oct 2024View details →

Controlled translocation of proteins through a biological nanopore for single-protein fingerprint identification

Electrophysiology data corresponding to the main text and supporting information figures. The data subsets were grouped based on the nanopore mutant and the supporting information figure the nanopore corresponds to. For each mutant, one representative data set within the triplicate was included.

restrictedcc-by-4.0Oct 2024View details →

Data from: The extent of amphibian, fish and water plant translocations by garden pond owners

To determine how frequently garden pond owners translocate plants, amphibians or fish between their ponds and natural areas, and over what distances, we set out a survey. The 2023 survey was designed in LimeSurvey and consisted of three components: (A) information about ownership of garden ponds, terrariums, and aquariums, (B) information about plants and animals and (C) sociodemographic information. Component A was used to determine whether respondents owned a garden pond, terrarium or aquarium. If so, the respondents were asked at what postal code their pond, terrarium or aquarium was located. This was necessary because the postal codes were used to determine the approximate location of the respondents’ home and calculate translocation distances. Respondents were able to enter a different postal code for each confinement type. In case respondents moved and had, for example, a garden pond on both addresses, they were asked to pick the postal code of the address where they had lived the longest or the one they could tell the most about. The introductory text of the questionnaire was phrased neutrally and did not mention exotic species, diseases or other issues. We did so to reduce the risk of social-desirability bias. The respondents who indicated that they had a garden pond, a terrarium or an aquarium were led through a series of questions about fish, amphibians and water plants in compartment B of the survey. If a respondent indicated that a species group was present in their pond, terrarium, or aquarium, they were asked how they acquired that species and additionally, if they had ever removed any species from its confinement. Multiple answers were possible for both obtainment and removal. If no appropriate answer was on the list, respondents could describe an additional answer. In case the options “collected/caught in nature” and/or “released/dumped in nature” were picked, the respondents were asked if they could pinpoint the location(s) on a map (that worked with OpenStreetMap). They could enter up to ten locations. For each location, they were asked what species they collected or released. Participants who translocated species but could not pinpoint any locations were asked to list all species at once. Species were only taken into account if it was clear what type of animal or plant was described. Full species names were not a necessity, but vague descriptions such as “oxygen plant” were counted as “unknown”. Participants who translocated animals or plants were asked how many times they had done so. Sufficient instructions were supplied to explain that, for this question, it did not matter where and how many individuals were caught or released each time. The respondents were also asked to formulate the most important reason for collecting or releasing plants and animals. In case respondents indicated that they transferred species from inside (terrarium or aquarium) to outside (pond) or vice versa when asked about the acquirement and removal of species, they were asked to list the species they had moved. These questions could be answered twice, once for the pond and once for the aquarium or terrarium regarding fish and amphibians. In such cases, information about what species were moved was combined. Terrarium or aquarium owners were not specifically asked about translocating plants to, and especially from, aquariums or terrariums because our main focus was on garden ponds and to prevent the survey from becoming too long, yet participants were able to note down which plants they moved from their pond to their aquarium or terrarium and vice versa as part of the questions concerning garden ponds. No questions were asked about hypothetical scenarios as we were only interested in what translocations had already happened and why, and not in uncertain future behavior of garden pond owners. Here we archive an anonymized version of the resulting datasets. Postal codes, longitudinal and latitudinal data, and additional comments provided by the respondents at the end of the survey were removed to anonymize the dataset. Those questions remain, but the cells are empty. We have provided a csv file with a side-by-side translation of the survey questions and the answers to multiple choice questions in the dataset. Please see ESM_2 for the original survey and ESM_3 of Prins et al. (provisionally accepted) for a translated version including conditional rules. Respondents could formulate their own answer when they picked other as an answer to the multiple choice questions about how they acquired plants or animals and the questions about what they did with plants and animals when removed from their enclosures. We categorized these additional answer by adding an extra column named Andere categorieën (Other categories). In here, we wrote down to what category the additional answers belonged. That could be the extra category Spontaan (Spontaneous) that we added for the questions about how plants and animals were acquired, Overig (Other) or one of the three overarching categories: Gekocht (Bought), Gehad (Received as gift), and weggegeven (Given away). Additional answers that only added explanation to one of the picked answer options, were not sorted into new or overarching categories. The answers to the motivation questions were categorized as well. We did this by adding an extra column named Categorie (Category) and noting down to what category (or categories) the answers belonged. We created seven motivation categories for the collection of plants and animals and three for their removal. See the table below for a translation of each category.    <table> <tbody> <tr> <td> Motivations for collecting water plants and animals form nature </td> </tr> <tr> <td> Categorie </td> <td> Category </td> </tr> <tr> <td> Leven </td> <td> Ecosystem functioning </td> </tr> <tr> <td> Esthetiek </td> <td> Aesthetic preferences </td> </tr> <tr> <td> Kosten </td> <td> Expenses and availability </td> </tr> <tr> <td> Dierenleed </td> <td> Animal suffering </td> </tr> <tr> <td> Soortbescherming </td> <td> Species preservation </td> </tr> <tr> <td> Educatie </td> <td> Education </td> </tr> <tr> <td> Overig </td> <td> Other </td> </tr> <tr> <td> Motivations for releasing water plants and animals in nature after removing them from a garden pond </td> </tr> <tr> <td> Categorie </td> <td> Category </td> </tr> <tr> <td> Overlast </td> <td> Overcrowding and hinder </td> </tr> <tr> <td> Verblijf </td> <td> Enclosure </td> </tr> <tr> <td> Overig </td> <td> Other </td> </tr> </tbody> </table>   This archive contains 3 files: Side_by_side_translation.csv provides English translations of all questions in our Dutch questionnaire in 2023. results-survey-anonymized.csv contains the anonymized answers by the respondents in 2023. Response IDs have been shuffled and no longer indicate the chronological order of the responses. 2023_translocations_with_distance_anonymized.csv contains the calculated distances between the postal code of the garden pond and natural area where species were collected or released. The responseIDs match with those in the previous file.

opencc-zeroDec 2013View details →

Data from: Is population structure in the European white stork determined by flyway permeability rather than translocation history?

European white stork are long considered to diverge to eastern and western migration pools as a result of independent overwintering flyways. In relatively recent times, the western and northern distribution has been subject to dramatic population declines and country-specific extirpations. A number of independent reintroduction programs were started in the mid 1950s to bring storks back to historical ranges. Founder individuals were sourced opportunistically from the Eastern and Western European distributions and Algeria, leading to significant artificial mixing between eastern and western flyways. Here we use mitochondrial and microsatellite DNA to test the contention that prior to translocation, eastern and western flyways were genetically distinct. The data show a surprising lack of structure at any spatial or temporal scale suggesting that even though birds were moved between flyways, there is evidence of natural mixing prior to the onset of translocation activities. Overall a high retention of genetic diversity, high Nef, and an apparent absence of recent genetic bottleneck associated with early 20th century declines suggest that the species is well equipped to respond to future environmental pressures.

opencc-zeroDec 2017View details →

Data from: The genetic legacy of 50 years of desert bighorn sheep translocations

Conservation biologists have increasingly used translocations to mitigate population declines and restore locally extirpated populations. Genetic data can guide the selection of source populations for translocations and help evaluate restoration success. Bighorn sheep (Ovis canadensis) are a managed big game species that suffered widespread population extirpations across western North America throughout the early 1900's. Subsequent translocation programs have successfully re-established many formally extirpated bighorn herds, but most of these programs pre-date genetically-informed management practices. The state of Nevada presents a particularly well-documented case of decline followed by restoration of extirpated herds. Desert bighorn sheep (O. c. nelsoni) populations declined to less than 3,000 individuals restricted to remnant herds in the Mojave Desert and a few locations in the Great Basin Desert. Beginning in 1968, the Nevada Department of Wildlife translocated ~2,000 individuals from remnant populations to restore previously extirpated areas, possibly establishing herds with mixed ancestries. Here we examined genetic diversity and structure among remnant herds and the genetic consequences of translocation from these herds using a genotyping-by-sequencing approach to genotype 17,095 loci in 303 desert bighorn sheep. We found a signal of population genetic structure among remnant Mojave Desert populations, even across geographically proximate mountain ranges. Further, we found evidence of a genetically distinct, potential relict herd from a previously hypothesized Great Basin lineage of desert bighorn sheep. The genetic structure of source herds was clearly reflected in translocated populations. In most cases, herds retained genetic evidence of multiple translocation events and subsequent admixture when founded from multiple remnant source herds. Our results add to a growing literature on how population genomic data can be used to guide and monitor restoration programs.

opencc-zeroJul 2021View details →

Single molecule images for: An empirical energy landscape reveals mechanism of proteasome in polypeptide translocation

The ring-like ATPase complexes in the AAA+ family perform diverse cellular functions that require coordination between the conformational transitions of their individual ATPase subunits. How the energy from ATP hydrolysis is captured to perform mechanical work by these coordinated movements is not known. In this study, we developed a novel approach for delineating the nucleotide-dependent free-energy landscape (FEL) of the proteasome's heterohexameric ATPase complex based on complementary structural and kinetic measurements. We used the FEL to simulate the dynamics of the proteasome and quantitatively evaluated the predicted structural and kinetic properties. The FEL model predictions were widely consistent with experimental observations in this and previous studies and suggested novel features of the mechanism of proteasomal ATPase. We find that the cooperative movements of the ATPase subunits result from the design of the ATPase hexamer entailing a unique free-energy minimum for each nucleotide-binding state. ATP hydrolysis dictates the direction of substrate translocation by triggering an energy-dissipating conformational transition of the ATPase complex.

Figure 18 in Integrative taxonomy of Parasabella and Sabellomma (Sabellidae: Annelida) from Australia: description of new species, indication of cryptic diversity, and translocation of some species out of their natural distribution range

Figure 18. Sabellomma cupoculata sp. nov., colour micrographs. A–D, live specimens. A, anterior end, ventral view. B, specimen missing posterior abdominal chaetigers, lateral view. C, radiolar crown and anterior thoracic chaetigers, lateral view. D, same, dorsal view. E–M, preserved specimens. E–G, detail of radiolar eyes along radiolar lateral margins. H, base of crown, ventral view, with crown opened showing ventral lips, dorsal lips with long radiolar appendages, and anterior thoracic chaetigers with ventral shields in contact with neuropodial tori and a dark pigment spot in between. I, J, half of radiolar crown showing dorsal lips with long radiolar appendages and pinnular appendages (arrow); dyed with methylene blue. K, thoracic chaetigers, holotype, lateral view, lacking inter-ramal eyes. L, thoracic chaetigers and collar. M, posterior thoracic and anterior abdominal chaetigers, lacking conspicuous inter-ramal eyes. A–D, AM W.37060; E–H, AM W.37060; I, J: AM W.37029; K, AM W.47193 (holotype); L, M, AM W.47189.

Figure 17 in Integrative taxonomy of Parasabella and Sabellomma (Sabellidae: Annelida) from Australia: description of new species, indication of cryptic diversity, and translocation of some species out of their natural distribution range

Figure 17. Parasabella sp. cf. Parasabella rugosa, scanning electron microscope photographs. A, anterior thoracic chaetigers and base of radiolar crown, dorsal view, showing large collar dorsal margins. B, midthoracic parapodium with elongate, narrowly hooded (arrow) superior chaetae and broadly hooded (type B) in inferior group. C, detail of inferior thoracic broadly hooded chaetae of type B. D, thoracic uncini. E, companion chaetae, lateral view. F, companion chaetae, frontal view. G, midabdominal neurochaetae narrowly hooded. H, abdominal uncini. I, posterior abdominal chaetigers and (damaged) pygidium. A–I, AM W.36431.

Figure 15 in Integrative taxonomy of Parasabella and Sabellomma (Sabellidae: Annelida) from Australia: description of new species, indication of cryptic diversity, and translocation of some species out of their natural distribution range

Figure 15. Parasabella sp. cf. Parasabella japonica, scanning electron microscope photographs. A, anterior thoracic chaetigers and base of radiolar crown, ventral view, showing ventral shields separated from neuropodial tori, and ventral lappets. B, anterior chaetigers, lateral view. C, same, dorsal view. D, midthoracic parapodium, elongate, narrowly hooded superi- or chaetae and broadly hooded type B chaetae in inferior group. E, detail of inferior, broadly hooded type B chaeta. F, thoracic uncini and companion chaetae. G, thoracic uncini, detail. H, companion chaetae showing the laterally compressed hood. I, midabdominal narrowly hooded neurochaetae. J, abdominal uncini. A–J, AM W.36450.

Figure 16 in Integrative taxonomy of Parasabella and Sabellomma (Sabellidae: Annelida) from Australia: description of new species, indication of cryptic diversity, and translocation of some species out of their natural distribution range

Figure 16. Parasabella sp. cf. Parasabella rugosa, colour micrographs of preserved specimens. A, anterior thoracic chaetigers, ventral view, showing posterior peristomial ring collar, and ventral shields in contact with neuropodial tori. B, complete thorax, lateral view. C, same, dorsal view. D, posterior abdominal chaetigers and pygidium, ventral view. A, NMV F.108844; B–D, AM W.36431.

Figure 12 in Integrative taxonomy of Parasabella and Sabellomma (Sabellidae: Annelida) from Australia: description of new species, indication of cryptic diversity, and translocation of some species out of their natural distribution range

Figure 12. Parasabella crassichaetae sp. nov. complex, colour micrographs of preserved specimens. A, whole specimen, lateral view. B, anterior chaetigers, showing the base of crown and the collar margins. C, specimens with detached crown showing the peristomial eyes (arrows) near the insertion site of the radiolar lobes. A–B, AM W.31103; C, AM W.37028.