Skip to main content
Download PDF

The illusion of rarity in an epibenthic jellyfish: facts and artefacts in the distribution of Tesserogastria musculosa (Hydrozoa, Ptychogastriidae)

Helgoland Marine Research volume 72, Article number: 12 (2018) Cite this article

Abstract

Epibenthic and benthopelagic medusae are rarely collected by standard benthic or pelagic sampling methods, and many species are considered uncommon and geographically restricted. Peer-reviewed scientific literature contains only two records of medusae belonging to the monotypic genus Tesserogastria Beyer, 1958 since their original description, both from the vicinity of the type locality in Oslofjord, contributing to an illusion of extreme rarity and restricted distribution. Our analysis of fresh samples and a thorough evaluation of all previous records of this taxon from both peer-reviewed scientific sources and “gray” literature show that the species is both more common and widespread than suggested by the scant records in primary scientific literature, and represents an example of an overlooked taxon in the epibenthos. High numbers of medusae of Tesserogastria musculosa Beyer, 1958 were collected at Raunefjord in western Norway. New data, together with validated observations from fjords in western and eastern Norway as well as western Sweden, demonstrate that the species is much more common than is evident from published records. Data on the mitochondrial 16S ribosomal RNA and cytochrome oxidase I molecular markers for the species are provided for the first time, as well as new observations on the morphology of living animals. Tesserogastria musculosa constitutes an example of a hydrozoan species with a misleading reported distribution, a situation likely to occur in all members of family Ptychogastriidae and other delicate epibenthic invertebrates. Sampling techniques specifically targeting the epibenthos and careful processing of the samples are essential for correctly assessing the presence of the species, suggesting that the lack of records for this and other epibenthic medusae may in part be an artefact of the commonly used sampling methods. A comparison of molecular data for species and genus delimitation in Ptychogastriidae, presented here for the first time, highlights the need for a thorough taxonomic revision of the family.

Background

Epibenthic and benthopelagic medusae are an important but easily overlooked component of neritic and oceanic bottoms around the world. More than 45 species of hydromedusae live either attached to or closely associated with the substrate [1], and many representatives of the families Cladonematidae, Olindiidae, Ptychogastriidae, and Rhopalonematidae are morphologically adapted to life in a benthic habitat [2]. Epibenthic medusae can be locally abundant, likely playing a significant role in bentho-pelagic coupling [3] but, for the majority of the species, only a handful of records exist and information on their distribution, population dynamics and ecology is lacking. The scarcity of records for epibenthic and benthopelagic medusae may be partially attributed to methodological limitations. Sampling with traditional plankton nets generally does not reach the epibenthos or the water column immediately above the bottom, while specimens are easily damaged beyond recognition during collection with dredges or bottom trawls, and their fragments are often discarded as planktonic contaminants.

The “mud jellyfish” Tesserogastria musculosa, the sole species in the genus and a member of the poorly known family Ptychogastriidae, is one of the lesser-known species of benthic hydromedusae. It was first collected in the mid-1950s by Beyer at Digerud in the Oslofjord [4]. Beyer later reported on T. musculosa’s local distribution and abundance, suggesting that these medusae could be used as bioindicators of pollution in the area [5]. Subsequent work published in 1971 by Hesthagen, one of Beyer’s students, resulted in a complete account of the morphology and behaviour of the species, and also constitutes the third and last record of the species published in a peer-reviewed scientific journal and the last report on the taxon in English [6]. The presence of T. musculosa has since been documented in Oslofjord—where it has, at times, been one of the most abundant components of the hyperbenthos—as well as in other Norwegian fjords (e.g. Fensfjord, Fanafjord, Sognefjord) [7,8,9], but these data are only available in technical reports, unpublished theses, and personal observations included in the so-called “gray” literature. The low accessibility of these sources has led to a serious bias in the estimation of the current and historical distribution of the species, resulting in its categorization as a rare taxon known exclusively from Oslofjord. In this paper, we challenge this view by reporting on the occurrence of high numbers of T. musculosa in Raunefjord (western Norway) and critically evaluating the existing peer-reviewed and “gray” literature records for the species. We also provide the first COI and 16S sequences for this taxon, and argue on the importance of careful sampling and processing of specimens for correct assessment of the presence of this and other benthic jellyfish.

Methods

Live individuals of T. musculosa were collected in Raunefjord, western Norway on February 10th 2017, using a Rothlisberg and Pearcy (RP)-sledge [10] with a 500 μm plankton net affixed horizontally over a thick rubber mat behind a steel sampling box. With the start position 60° 16.950′ N, 5° 11.212′ E, and a towing-speed of 0.5 knots for an approximate of 20 min bottom-time in a southerly direction, we covered a roughly 600 m transect of sandy mud at depths ranging between 142 (start) and 170 (end) m. As the opening width of the sledge is 1 m, the sampled area is ~ 600 m2, even though it should be taken into due consideration that the RP-sledge is a semi-quantitative gear [11] as it is not possible to check if there are any “jumps” off the bottom during the transect.

Upon retrieving the sample, the cod-end was immediately separated from the net-contents, and carefully rinsed into a tub of seawater. The net-contents were carefully washed into a separate tub with seawater and kept under a covering of water until processing. The slow towing-speed and keeping the samples submerged in water at all times ensured that the many fragile hyper-benthic species were collected intact. The sample was slowly and repeatedly decanted over to a 500 μm sieve submerged in seawater. Tesserogastria musculosa medusae were individually handpicked from the sample over a light table with a broad-mouthed pipette prior to fixing the rest of the sample in 96% ethanol. In addition to the epibenthic sampling, a WP3 plankton net (780 μm mesh and non-filtering cod-end) coupled to a CTD instrument (SAIV sd200, frequency of measurement 1 s, parameters salinity, temperature, dissolved oxygen) was hauled from ca. 10 m above the bottom to the surface at a speed of 0.3 ms−1. Medusae of T. musculosa were also searched for in this plankton sample, and the accompanying environmental data were used to characterize the sampled locality.

After collection, the medusae were brought to the laboratory and identified to species level with the aid of specialized literature [4, 12]. Specimens were then fixed either in 4% formalin (for morphological analysis) or 96% ethanol (for DNA barcoding), with the latter group of specimens photographically documented prior to fixation. Live and formalin-preserved specimens were examined under a stereomicroscope (Olympus SZX16), and their detailed morphology was observed using a compound microscope (Leica CTR 6000). A subsample of 50 randomly chosen formalin-fixed individuals were measured (bell height on the oral/aboral axis; from umbrella margin to apex), and their sex determined before being deposited as vouchers in the University Museum of Bergen (UMB, Norway, catalogue number ZMBN 123772). The size distribution and sex ratio of T. musculosa in Raunefjord were determined, and the skewness coefficient (g1) and associated standard error (SES) of the size frequency distribution calculated following Joanes and Gill [13], skewness being detected whenever the absolute value of g1/SES is > 2 or < − 2.

For DNA barcoding, a ~ 1 mm3 tissue fragment was taken from the umbrella margin of three ethanol-fixed specimens. These samples were subsequently sent to the Canadian Centre of DNA Barcoding (CCDB) in Guelph for DNA extraction and sequencing according to their protocols [14]. Specimens were sequenced for both mitochondrial cytochrome oxidase I (COI) and 16S ribosomal RNA markers. The PCR primer pairs C_LepFolF/C_LepFolR (for COI), and 16SgaF/16SgaR (for 16S) were used in PCR [15]. The hydrozoan origin of the sequences was verified by BLAST searches against the GenBank database of the National Center for Biotechnology Information. High quality gene fragments resulting from assembly of forward and reverse sequences were labelled as barcode compliant according to the criteria of BOLDSYSTEM and are available, together with voucher pictures and metadata, at Boldsystems.org (sample ID HYPNO_488 to 490) and GenBank (accession numbers MG700373 to MG700375 for 16S, MG700376 to MG700378 for COI). An alignment was created independently for each of the markers using MUSCLE [16] as implemented in MEGA v.7.0.26 [17], including the sequences of T. musculosa and those of all other available members of family Ptychogastriidae (see taxa and GenBank accession numbers in Table 1). Pairwise Kimura 2-parameter distances were calculated based on these alignments to estimate genetic differentiation among species.

Table 1 Percentage distancea for mitochondrial 16S and COI between Tesserogastria musculosa and other ptychogastriids
Full size table

A molecular phylogeny of the Ptychogastriidae was estimated independently for the above 16S and COI alignments. The sequences were analyzed using a phylogenetic approach based on (a) maximum likelihood (ML) optimality criterion in PAUP* 4.0a [18] and (b) Bayesian inference using MrBayes v. 3.2.6 [19]. The best-fit model for each dataset was calculated using jModelTest (v. 2.1.5; [20]) with default settings and chosen using the Akaike Information Criterion (AIC). For the 16S dataset, the best-fit model was TIM2 + I, while for the COI dataset the best fit model was GTR + G + I. In the ML analyses, a maximum likelihood consensus tree was generated for each marker in PAUP* by conducting a heuristic search and bootstrapping with 200 replicates. In the Bayesian analyses four parallel Markov chain Monte Carlo runs were carried out for 500,000 generations. Trees were sampled every 100 generations, discarding the 0.25% of trees as burnin.

To evaluate the previous assumption of spatial and temporal rarity of T. musculosa, we estimated its distribution based on all published and peer-reviewed occurrence records and mentions in the scientific literature, as well as in the “gray” literature (i.e. publicly available documents with low accessibility, not subjected to peer-review, and often published in a language other than English). We validated these records by (1) examining the corresponding specimens deposited in the scientific collections of the natural history museums of the University of Bergen and the University of Oslo, and (2) contrasting the information contained in each of them against the original description of the species. Examined material included the holotype (a single medusa mounted on a permanent slide) and 16 individuals designated as paratypes, all deposited in the Natural History Museum of the University of Oslo (ZMO, catalogue number B 860 and B 861, respectively). In all, ca. 60 years of issues (1958–2017) of scientific and technical reports from local, regional and national sources (e.g. NIVA–Norwegian Institute for Water Research, BIBSYS Brage) were analyzed, and a comprehensive search for relevant unpublished thesis and dissertations from Scandinavian universities was performed through online repositories (e.g. DUO/University of Oslo, BORA/University of Bergen; GUTEA/University of Gothenburg; NTNU Open; UiT Open Research Data). Publicly available distributional and occurrence data were also compiled from the online repositories OBIS (Ocean Biogeographic Information System) and GBIF (Global Biodiversity Information Facility), and from the online collections catalogues of the Natural History Museum London and the Royal Belgian Institute of Natural Sciences.

Results

A total of 260 individual medusae were collected in Raunefjord from an estimated sampled area of 600 m2, corresponding to a density of approximately 0.43 ind/m2. The sampled bottom consisted of sandy mud, with high amounts of organic degraded material. Our sample was dominated by various flatfish, holothurians and Myxine glutinosa L, 1758. Apart from the macrofauna, the main hyperbenthic taxa were T. musculosa and several crustaceans (i.e. Mysidacea, Amphipoda and juvenile Decapoda), with Polychaeta and Ophiuroidea present in large amounts in the heavy fraction remaining after the decanting. Within Amphipoda (a taxon with a close relationship to the substrate similar to that of T. musculosa) Oedicerotidae was the dominating family, as would be expected in a station with such soft, organic sediments. This is a family that is known for being fragile, with long thin legs that often break off during sampling. Stratification of temperature, salinity, and oxygen concentration was pronounced in the surface waters above the sampling locality, but conditions below ~ 130 m depth were relatively uniform (Fig. 1a). Mean values (± SD) of salinity, temperature, and dissolved oxygen in the water column below 200 m depth were 34.93 ± 0.010, 8.58 ± 0.003 °C, and 7.81 ± 0.036 mg/L, respectively.

Fig. 1
figure1

Environmental data and size structure of Tesserogastria musculosa from Raunefjord in February 2017. a Vertical profiles of temperature (°C), salinity, and oxygen concentration (mg/l). b Size distribution of the umbrella height of a randomly chosen subsample of the population. g1 = Skewness coefficient. SES = Standard error of skewness. n = number of medusae measured. Skewness is observed when the absolute value of g1/SES is > 2 (population positively skewed) or < − 2 (population negatively skewed)

Full size image

The average umbrella height of T. musculosa in Raunefjord ranged from 0.9 to 2.4 mm, with a mean (± SD) of 1.71 ± 0.37 mm. The majority of the medusae were in the intermediate size classes (1.5–1.9 mm). The skewness coefficient (g1/SES = − 0.95) indicated that the size distribution in Raunefjord at the time of sampling was not significantly different from a symmetric/unimodal frequency distribution (Fig. 1b). Mature female medusae were readily recognized upon visual examination of the gonads through the umbrella, but the identification of males and immature females required assessment of histological preparations. The analysis of a subsample (n = 20) showed that all individuals larger than 1.5 mm were mature, and the ratio of female to male in medusa larger than this size approached 1:1. The ratio of immature to mature medusae was 1:3.

The morphology of the collected T. musculosa is typical of the species, with a bell-shaped umbrella about as high as broad (0.9–2.4 mm), ending in a small, blunt apical projection surrounded by a circular depression (Fig. 2a, b). The otherwise thin umbrellar mesoglea is thickened at the margin in a belt of chordal cells, where up to 350 tentacles are inserted at 3–5 levels without any apparent grouping. Most of the collected specimens were completely devoid of tentacles, and only the drop-shaped scars left by shed tentacles remained (Fig. 2d, e). The few tentacles available for examination were all filiform, blunt, circular in transversal section, with evenly-distributed nematocysts (slightly more abundant in the tip), and were devoid of any adhesive structure. The manubrium is four-lobed, cross-shaped in transversal section (Fig. 2c), lacks mesenteries and a peduncle, and often extends beyond the bell margin before ending in a square mouth with four simple lips. Eight rather narrow radial canals connect the base of the manubrium to the broad circular canal situated next to the conspicuous nematocyst ring at the umbrellar margin (Fig. 2b). The velum is broad and strongly muscular. There are eight short-stalked interradial statocysts, each with a single statolith (Fig. 2f). The gonads are organized in eight masses forming four perradial pairs (each pair corresponding to one manubrium lobe) and are evident in mature individuals: in females the eggs are arranged in 1–3 visible rows inside each gonadal mass (Fig. 2h, i), while in males the gonads appear homogenous (Fig. 2j, k). Three distinct nematocyst types, distributed in the umbrella margin and tentacles, were observed (Fig. 2g): almost spherical stenoteles [(6–8) × (6–7) μm], tear drop-shaped microbasic euryteles [(6–7) × (4–6) μm], and small atrichous isorhizas (1.5–2 μm). The umbrella of the living specimens is translucent, with 8 interradial yellow spots, roughly square or rectangular in shape, situated at its margin, corresponding with the statocysts. The distal portion of the radial canals is also pigmented, giving the appearance of faint and roughly-defined yellow triangles on the portion of the radial canals immediately above the intersections of the circular canal and the radial canals.

Fig. 2
figure2

Tesserogastria musculosa Beyer, 1958 from Raunefjord, Western Norway. a, b General morphology of the medusae in lateral and aboral view. c Cross-section of manubrium. d, e Tentacle stump (black arrow) and appearance of the marginal rim. f Statocyst with statolith (white arrow). g Undischarged nematocyst capsules: stenotele (st), microbasic eurytele (eu), and atrichous isorhiza (is). h Manubrium of a female mature medusa. i Close-up of developing eggs in gonadic tissue. j Manubrium of male mature medusa. k Close-up of homogeneous gonad

Full size image

The sequenced products of COI from three analyzed individuals were identical to each other, as were the 16S products. All sequences were free of gaps and had a final length (after alignment and trimming) of 658 and 542 base pairs, respectively. When blasted against the GenBank database, all T. musculosa sequences were shown to be most similar to other ptychogastriid sequences, confirming the lack of contamination. The genetic distances between T. musculosa and the rest of the genera in family Ptychogastriidae are presented in Table 1, evidencing the clear separation between the 16S and COI sequences of T. musculosa and all other analyzed taxa. Preliminary comparisons of 16S and COI sequence data from the three valid ptychogastriid genera are shown in Fig. 3, further confirming the separation of T. musculosa, but also suggesting the non-monophyly of Ptychogastria polaris Allman, 1878.

Fig. 3
figure3

Phylogenetic hypothesis of Ptychogastriidae. Phylogenetic hypothesis based on mithocondrial 16S (a) and COI (b). For both markers the topology of the ML and Bayesian trees was identical. Numbers above the branches indicate the posterior probability in the Bayesian analysis and percentage of bootstrap support in the corresponding ML tree, respectively. Branches in black indicate high support values, while grey branches represent low support values. Members of Rhopalonematidae are included as outgroups following [3]. GenBank accession numbers are provided for all sequences

Full size image

In all, 57 previous records of T. musculosa from 30 localities were validated (Fig. 4, Table 2, Additional file 1). Twenty-three different sources providing validated records were identified, 87% of them from “gray” literature. The known distributional range of the species is expanded to include fjords in the north-eastern section of the Skagerrak strait (numerous localities inside and around Oslofjord in eastern Norway, and Gullmarfjord in western Sweden), and the northernmost sector of the North Sea (the western Norwegian fjords of Sognefjord, Fensfjord and Fanafjord), demonstrating that the presence of at times high numbers of T. musculosa has been continuously documented for almost six decades in the North Sea region, particularly in the Oslofjord, from 1958 to 2017.

Fig. 4
figure4

Validated records of Tesserogastria musculosa, with a detailed view of the Oslofjord

Full size image
Table 2 Validated previous records of Tesserogastria musculosa Beyer, 1958 summarized by reference
Full size table

Discussion

The distinctive morphology of the collected specimens prevented confusion with any other hydromedusa species in the area and allowed for a straightforward identification of the animals as T. musculosa Beyer, 1958, subsequently confirmed through a detailed comparison with the holotype of the species. The morphology of the medusae is in close agreement with both the original description by Beyer [4] and the subsequent account by Hesthagen [6], except for the coloration pattern. Previous accounts on the coloration of T. musculosa include the presence of white to yellow epidermal spots located at the perradial junctions of the radial canals with the ring canal [6]. In the individuals from Raunefjord, however, the entire ring canal and the distal parts of the radial canals were pigmented, with eight additional interradial pigment patches not associated with the radial canals present on the umbrella margin. A potential role of exumbrellar pigment spots as photoreceptors has been discussed previously for this species, since the medusae are known to spawn in response to strong illumination under the microscope in laboratory conditions [6], but further research is needed to determine the degree of interaction between light cues and ectodermal pigments in T. musculosa. When examined alive under the direct light of the microscope at different intensities, medusae from both Raunefjord (present study) and Oslofjord [6] did not show any phototaxic response, suggesting that these bottom-living medusae may not depend on light for orientation and movement. It has been suggested that the adult medusae permanently remain on the sea bottom, with the possible exception of swimming as a flight response [6, 8].

The number and position of the statocysts are diagnostic characters separating Tesserogastria from all other genera in family Ptychogastriidae [12, 21]. However, some confusion exists regarding the exact position of these structures in T. musculosa, as they have been alternatively described in scientific accounts as adradial [6] or interradial [12]. The original description of the species does not include information on the position and number of statocysts because Beyer was unable to find any in formalin-preserved animals, presumably due to the disintegration of the statoliths in this fixative [4]. Nevertheless, the statocysts from medusae from Raunefjord fixated with neutral-buffered formalin were evident even after 6 months of preservation, allowing us to confirm that in T. musculosa the statocysts are invariably interradial and can be used as a reliable character separating Tesserogastria from both Ptychogastria and Glaciambulata.

For both the 16S and COI markers, the sequences generated for this study show a large degree of differentiation (> 20%) between T. musculosa and individuals of the other two species in the family for which genetic data are available (i.e. Glaciambulata neumayeri Galea et al., 2016 and P. polaris), highlighting the value of these two markers as DNA-barcodes for this species. At genus level, all three ptychogastriid genera show a similarly large degree of differentiation, which is comparable to the distances observed by Grange et al. between individuals identified as P. polaris from the Antarctic Peninsula and the Sea of Japan [3]. Our P. polaris individuals from Hjeltefjord are again clearly different from both the Antarctic and Japanese specimens, and the preliminary phylogenetic analysis suggests that the taxonomy of the Ptychogastriidae, and in particular the hypothesis of monophyly of genus Ptychogastria, needs to be revised, as the intraspecific degree of differentiation within this genus appears comparable to the degree of differentiation between genera. It is unlikely that DNA sequences from either the holotype or the paratypes of T. musculosa will be available in the near future, since in both cases the specimens have been subjected to fixation and long-term storage in formalin. The 16S and COI sequences provided here for T. musculosa constitute thus a useful tool for identification, as well as the first molecular evidence of the relationships of the genus with both Glaciambulata and Ptychogastria.

Tesserogastria musculosa was a common component of the epibenthic community in the sampled locality, with the estimated density (ca. 0.5 ind/m2) similar to what has been reported for other ptychogastriid medusae in boreal waters (0.01–0.91 ind/m2 for P. polaris in northeast Greenland, and 0.01–0.76 ind/m2 for the same species in the Barents Sea) [22, 23]. The density of T. musculosa was however considerably lower than the maximum densities reported for ptychogastriid medusae in Antarctic waters (up to 13 ind/m2 for P. polaris in Antarctic fjords) [3]. In Digerud and neighbouring localities, T. musculosa has reached maximum values of > 10 ind/m3, being the most abundant organism in at least one sampling station [5], while subsequent observations in Oslofjord have shown that the species is common and, at times, highly abundant in soft bottoms [9, 24,25,26]. The medusae from Raunefjord and Oslofjord shared similar size ranges and unimodal distribution of bell height, but the mean umbrella height in this study (1.71 mm) was higher than the mean height (0.96–1.03 mm) reported for the same species in the type locality at any given time of the year [6].

The high numbers of medusae in some localities along Oslofjord allowed Beyer to analyze the local distribution of the species. This lead him to suggest that T. musculosa is an indicator of non-polluted bottoms, with the number of individuals rapidly increasing towards the open sea [5]. Later on, the consistent patterns of decreasing abundance towards the inner parts of the fjord caused Beyer and Indrehus to advocate the species as an indicator of oceanic and unpolluted conditions in the area [9]. Despite this general pattern, the population has fluctuated during the recent decades, with a dramatic population reduction in the inner fjord starting in the 1960s and continuing until the mid-1990s [9]. Remarkably high numbers of medusae were observed again in 1996 [26], and the species has since been recorded rather consistently in Oslofjord until as recently as 2012 [27], but without information on population density or abundance.

High densities of ptychogastriid medusae in soft sediments have been linked to high productivity in subantarctic fjords [3, 28], and to the accumulation of organic and inorganic debris in the seafloor of relatively isolated deep environments [4, 29]. Raunefjord’s sediment characteristics and oceanographic processes (e.g. enhanced benthic productivity, vertical flux, trapping of detritus) are likely to provide a suitable habitat for epibenthic medusae in an analogous way to the observed abundance of P. polaris in subantarctic fjords [3], Ptychogastria asteroides (Haeckel 1879) in Mediterranean canyons [29], and T. musculosa in Oslofjord [4].

Contrary to the interannual variation, significant seasonal population fluctuations have not been observed for T. musculosa in its type locality, with high numbers of medusae collected throughout the year in seasonal surveys [6]. In West-Norwegian Fanafjord, however, strong seasonality in T. musculosa was reported by Kaartvedt, who observed the highest abundances in June and much fewer specimens in April, September and December [8]. Unpredictable, sporadic and episodic population fluctuations are widely documented for planktonic jellyfish [30, 31] and some benthic hydrozoans [32], but the mechanisms behind these remain poorly understood [31, 33]. Episodes of bloom-and-bust have never been reported for benthic ptychogastriid hydromedusae and these organisms may not be part of the subset of medusozoan species with life-cycle attributes that predispose them to bloom [34]. Existing evidence appears to suggest that epibenthic medusae in genera Ptychogastria and Tesserogastria do not form blooms with abrupt periods of presence in the environment followed by completely disappearance, and instead maintain rather stable large populations in habitats such as the bottom of Boreal, Arctic and Antarctic fjords, and deep submarine canyons [3, 6, 22, 23]; although the observed variations in the abundance of T. musculosa in Fanafjord [8] could instead indicate that seasonal dynamics differ widely among populations of this species in different habitats.

For a relatively easy-to-identify species distributed in the well-studied vicinities of active marine biological stations in both Oslofjord and Raunefjord, T. musculosa has a puzzlingly low number of records in the published, peer-reviewed scientific literature. Subsequently, it has been generally considered a rare and geographically restricted species. Based on our data and a thorough review of the “gray” literature, this perception is most likely incorrect, and T. musculosa in fact appears to be a relatively common and widely distributed component of the epibenthos in several fjords along the North Sea coast. The lack of published records for T. musculosa does not result from the rarity of the species, neither can it be attributed to undersampling of its habitat, as numerous studies have been conducted on the benthic fauna of the areas surrounding both the Marine Biological Station in Drøbak and the Espeland Marine Biological Station in Raunefjord since their founding in 1894 and mid-1950s, respectively [35, 36].

More than with other epibenthic animals, our ability to detect the presence of T. musculosa—and most likely other gelatinous epibenthos—appears to depend on a combination of the chosen sampling gear and a careful processing technique. In the original description, Beyer stressed the importance of the sampling gear in finding T. musculosa in Oslofjord, stating that his specially designed sledge, known as the Beyer sledge, consistently yielded catches of T. musculosa [4]. In the localities where abundant medusae have been caught with sledges, sampling with plankton net hauls from above the bottom has never yielded a single specimen, either in Oslofjord [4] or Raunefjord and the surrounding fjords [37]. Beyer suggests that “the species has probably been caught many times in grab and Mortensen dredge samples, but has then been disregarded together with the plankton inevitably caught in these apparatus”, thus highlighting the importance of gentle sampling, adequate sample processing techniques, and correct identification for observing this species [4]. Prior to the current study, all specimens of T. musculosa ever collected have been obtained with Beyer’s epibenthic sledge (illustrated in [38]) with a 50 cm closing plankton net mounted on a steel toboggan, designed for the purpose of catching organisms on or immediately above the bottom [5, 6, 8, 9, 27, 39]. In the current study, a slightly less gentle and much larger Rothlisberg and Pearcy (RP) sledge was used, but this was compensated for by the careful processing of the samples, as well as the very slow transect and retrieval speed. It is not surprising that careful processing of samples will result in higher numbers of species found: in Kiel Bay, Remane found > 300 new species after modifying his sampling techniques and adopting a more careful handling approach of the samples [40].

The population assessment of benthic ptychogastriid medusae has only recently become feasible thanks to improved sampling techniques and in situ observations by divers or ROVs, resulting in the description of new species and several new records for the already-known ones [3, 12]. Other multidisciplinary approaches (e.g. sediment traps) have also been successfully used for the collection of well-preserved ptychogastriid medusae in remote locations such as submarine canyons [29], and thus represent a potential source of valuable information for this taxon. Ptychogastriid medusae were rarely reported before the late 1990s [22, 23], partly due to the difficulties of sampling deep marine environments, but also because the medusae, often damaged beyond recognition, were readily considered planktonic contaminants. The standard processing of benthic samples with sieves often results in the gelatinous species getting extruded and destroyed, leading to them remaining unreported. The lack of records for T. musculosa and other benthic and benthopelagic medusae [41] may thus be an artefact of the commonly used sampling techniques.

A second issue contributing to the perceived rarity of T. musculosa is the poor accessibility of the bulk of the records, which consist of technical reports, unpublished theses, and museum collection catalogues. Many basic and applied studies in biogeography, phylogenetics, and ecology rely on species distribution data compiled exclusively from the published scientific literature but, for some species, such as T. musculosa, these data are incomplete and may contain serious biases. While the use of unverified anecdotal occurrences and unpublished observations for the assessment of the current and historical ranges of rare species can certainly lead to large errors of omission and commission [42], for some taxa, such as T. musculosa, inclusion of records from the “gray” literature is crucial for a realistic estimation of their distribution. Common complaints against the inclusion of “gray” literature data in distributional analyses include the low quality and low accessibility of the sources. While the latter is also an issue in the case of T. musculosa (e.g. all records are in languages other than English and several unpublished documents are not available online), the quality of the data they contain is in general quite high: all observations were made by trained professionals working in the field of marine biology/ecology, in many cases in collaboration with the original author of the species or with one of his students, using established and well documented sampling protocols.

In the particular case of T. musculosa, reviewing and including occurrence records from “gray” literature considerably alters the perception of its distribution and commonness. Furthermore, due to the hyperbenthic habitat and the gelatinous morphology of the medusa, the species is unlikely to be collected or recorded by the most commonly used pelagic or benthic sampling methods. A similar methodological bias applies to other epibenthic and benthopelagic medusae, which remain a poorly known group [37]. Targeted sampling with suitable gear and processing protocols, or using ROVs and other optical platforms, is required to establish a better understanding of diversity and ecology of ptychogastriids and other gelatinous benthos.

In addition to updating our knowledge of the distribution of the species, the reconstruction of the taxonomic history of T. musculosa also allowed us to clarify the existing confusion regarding its date of description. Although the paper by Beyer was actually published in 1958, some authors have mistaken the date of this publication as 1959 [2, 12, 21] probably based on a series of copies of Vol. 6 of the Nytt Magasin for Zoology printed in that year. The error has become widespread in the peer-reviewed scientific literature, although it has not completely permeated the “gray” literature produced in Norway. Beyer himself reported the date as 1958 in subsequent works, as did his students and collaborators (e.g. Hesthagen clearly states that the species was first described by Beyer in 1958) [6]. An enquiry into the publications of the University of Oslo (publisher of Nytt Magasin for Zoology) has confirmed that the correct date of publication is 1958, the correct date for the genus is Tesserogastria Beyer, 1958, and the correct name of the species is Tesserogastria musculosa Beyer, 1958.

Conclusions

Tesserogastria musculosa is not restricted to its type locality; freshly collected samples and validated observations from fjords in western and eastern Norway as well as western Sweden demonstrates that the species is more common and widespread than is evident from published records. Our current ideas about the restricted distributions of other epibenthic medusae need to be reassessed, as they are likely to be similarly biased, and further sampling at additional localities will likely provide more records of these organisms, including T. musculosa. Sampling techniques specifically targeting the epibenthos and careful processing of the samples are essential for correctly assessing the presence of epibenthic medusae, and the lack of records for these organisms may in part be an artefact of the commonly used sampling methods, but thorough validation and reassessment of previous records, including those in “gray” literature, are also necessary to estimate the real distributional area of delicate epibenthic invertebrates. The comparison of molecular data for species and genus delimitation in Ptychogastriidae, presented here for the first time, shed further insight into the diversity and distributional range of epibenthic trachyline medusae and highlighted the need for a thorough taxonomic revision within the family.

References

  1. 1.

    Larson RJ, Matsumoto GI, Madin LP, Lewis LM. Deep-sea benthic and benthopelagic medusae: recent observations from submersibles and a remotely operated vehicle. Bull Mar Sci. 1992;51:277–86.

    Google Scholar 

  2. 2.

    Bouillon J, Gravili C, Pagès F, Gili JM, Boero F. An introduction to hydrozoa. Mém Mus Natl d’Hist Nat. 2006;194:1–592.

    Google Scholar 

  3. 3.

    Grange LJ, Smith CR, Lindsay DJ, Bentlage B, Youngbluth MJ. High abundance of the epibenthic trachymedusa Ptychogastria polaris Allman, 1878 (Hydrozoa, Trachylina) in Subpolar Fjords along the West Antarctic Peninsula. PLoS ONE. 2017;12:e0168648.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  4. 4.

    Beyer F. A new, bottom-living Trachymedusa from the Oslofjord. Nytt Mag Zool. 1958;6:121–43.

    Google Scholar 

  5. 5.

    Beyer F. Zooplankton, zoobenthos, and bottom sediments as related to pollution and water exchange in the Oslofjord. Helgol Wiss Meeresunters. 1968;17:496–509.

    Article  Google Scholar 

  6. 6.

    Hesthagen IH. On the biology of the bottom-dwelling Trachymedusa Tesserogastria musculosa Beyer. Norw J Zool. 1971;19:1–19.

    Google Scholar 

  7. 7.

    Brattegard T, Høisæter T. Supplerende undersøkelser av Fensfjordens dype bløtbunners dyreliv—Rapport til Norsk Hydro, Best. nr. T. 67402/NH/Mo; 1973:1–71.

  8. 8.

    Kaartvedt S. Hyperfauna i Fanafjordens dypbasseng: døgnvandringsmønstre, døgn- og sesong-variasjoner i hyperfaunaens sammensetning. MSc dissertation. Bergen: Universitetet i Bergen; 1982.

  9. 9.

    Beyer F, Indrehus J. Effekter av forurensning og dypvannsutskiftning på faunaen langs bunnen av Oslofjorden basert på materiale samlet siden 1952, vol. 1. Oslo: Universitetet i Oslo, Biological Institute; 1995.

    Google Scholar 

  10. 10.

    Rothlisberg P, Pearcy WG. An epibenthic sampler used to study the ontogeny of vertical migrations of Pandalus jordani (Decapoda, Caridea). Fish Bull. 1977;74:994–7.

    Google Scholar 

  11. 11.

    Brattegard T, Fosså JH. Replicability of an epibenthic sampler. J Mar Biol Ass UK. 1991;71:153–66.

    Article  Google Scholar 

  12. 12.

    Galea HR, Roder C, Walcher C, Warmuth M, Kohlberg E, Fischer PF. Glaciambulata neumayeri gen. et sp. nov., a new Antarctic trachymedusa (Cnidaria: Hydrozoa), with a revision of the family Ptychogastriidae. Eur J Taxon. 2016;252:1–30.

    Google Scholar 

  13. 13.

    Joanes DN, Gill CA. Comparing measures of sample skewness and kurtosis. Statistician. 1998;47:183–9.

    Google Scholar 

  14. 14.

    Ratnasingham S, Hebert PD. BOLD: The Barcode of Life Data System (http://www.barcodinglife.org). Mol Ecol Notes. 2007;7:355–364.

  15. 15.

    BOLD primer database. Barcode of Life, Guelph. 2018. http://www.boldsystems.org/index.php/Public_Primer_PrimerSearch. Accessed 13 March 2018.

  16. 16.

    Edgar RC. MUSCLE: multiple sequence alignment with high accuracy and high throughput. Nucleic Acids Res. 2004;32:1792–7.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  17. 17.

    Kumar S, Stecher G, Tamura K. MEGA7: molecular evolutionary genetics analysis version 7.0 for bigger datasets. Mol Biol Evol. 2016;33:1870–4.

    Article  PubMed  CAS  Google Scholar 

  18. 18.

    Swofford DL. PAUP* 4.0. Phylogenetic analysis using parsimony (*and other methods). Beta version 4.0b4a. Sinauer Associates, Sunderland, USA. 2002.

  19. 19.

    Ronquist F, Teslenko M, van der Mark P, Ayres DL, Darling A, Höhna S, Larget B, Liu L, Suchard MA, Huelsenbeck JP. MrBayes 3.2: efficient Bayesian phylogenetic inference and model choice across a large model space. Syst Biol. 2012;61:539–42.

    Article  PubMed  PubMed Central  Google Scholar 

  20. 20.

    Darriba D, Taboada GL, Doallo R, Posada D. jModelTest 2: more models, new heuristics and parallel computing. Nat Methods. 2012;9:772.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  21. 21.

    Kramp PL. Synopsis of the medusae of the world. J Mar Biol Ass UK. 1961;40:7–382.

    Article  Google Scholar 

  22. 22.

    Stübing D, Piepenburg D. Occurrence of the benthic trachymedusa Ptychogastria polaris Allman, 1878 (Cnidaria: Hydrozoa) off northeast Greenland and in the northern Barents Sea. Polar Biol. 1998;19:193–7.

    Article  Google Scholar 

  23. 23.

    Panteleeva NN, Frolova EA, Sheiko OV. New records of the benthic medusa Ptychogastria polaris Allman, 1878 (Trachylida, Hydroidea) in the Barents Sea and off the Kurile Islands (Pacific Ocean). Polar Biol. 1999;22:372–8.

    Article  Google Scholar 

  24. 24.

    Hesthagen IH, Gjermundsen B. Replicability of samplic hyper-benthic region by means of Beyer’s 50-cm epibenthic closing net. Meeresforsch Rep Mar Res. 1978;26:1–10.

    Google Scholar 

  25. 25.

    Fritzvold W. Vertikale vandringer hos hyperbenthos sett i relasjon til dyp og årstid. Cand Real thesis. Oslo: University of Oslo; 1981.

  26. 26.

    Magnusson J, Johnsen T, Lømsland E, Beyer F, Røysted UE. Overvåking av forurensningssituasjonen i indre Oslofjord 1996. NIVA, Oslo. Rapport nr. 701/97. Oslo: Norwegian Institute for Water Research; 1997.

  27. 27.

    Berge JA, Amundsen R, Fredriksen L, Bjerkeng B, Gitmark J, Holt TF, Haande S, Hylland K, Johnsen T, Kroglund T, Ledang A, Lenderink A, Lømsland ER, Norli M, Magnusson J, Rohrlack T, Sørensen K, Wisbech C. Overvåking av Indre Oslofjord i 2012—Vedleggsrapport. NIVA, Oslo. Rapport nr. 6534. Oslo: Norwegian Institute for Water Research; 2013.

  28. 28.

    Grange LJ, Smith CR. Megafaunal communities in rapidly warming fjords along the West Antarctic Peninsula: Hotspots of abundance and beta diversity. PLoS ONE. 2013;8:e77917.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  29. 29.

    Gili J-M, Pagès F, Bouillon J, Palanques A, Puig P, Heussner S, Calafat A, Canals M, Monaco A. A multidisciplinary approach to the understanding of hydromedusan populations inhabiting Mediterranean submarine canyons. Deep Sea Res 1 Oceanogr Res Pap. 2000;47:1513–33.

    Article  Google Scholar 

  30. 30.

    Boero F, Bouillon J, Gravili C, Miglietta MP, Parsons T, Piraino S. Gelatinous plankton: irregularities rule the world (sometimes). Mar Ecol Prog Ser. 2008;356:299–310.

    Article  Google Scholar 

  31. 31.

    Lucas CH, Dawson MN. What are jellyfishes and thaliaceans and why do they bloom? In: Pitt KA, Lucas CH, editors. Jellyfish blooms. Dordrecht: Springer; 2014. p. 9–44.

    Google Scholar 

  32. 32.

    Betti F, Bavestrello G, Bianchi CN, Morri C, Righetti E, Bava S, Bo M. Long-term life cycle and massive blooms of the intertidal hydroid Paracoryne huvei in the North-western Mediterranean Sea. Mar Biol Res. 2017;13:538–50.

    Article  Google Scholar 

  33. 33.

    Bavestrello G, Puce S, Cerrano C, Zocchi E, Boero F. The problem of seasonality of benthic hydroids in temperate waters. Chem Ecol. 2006;22(Suppl 1):197–205.

    Article  CAS  Google Scholar 

  34. 34.

    Hamner WM, Dawson MN. A review and synthesis on the systematics and evolution of jellyfish blooms: advantageous aggregations and adaptive assemblages. Hydrobiologia. 2009;616:161–91.

    Article  Google Scholar 

  35. 35.

    Brattström H. The biological stations of the Bergens Museum and the University of Bergen 1892–1967. Sarsia. 1967;29:7–80.

    Article  Google Scholar 

  36. 36.

    Ruud JT. Introduction to the studies of pollution in the Oslofjord. Helgol wiss Meeresunters. 1968;17:455–61.

    Article  Google Scholar 

  37. 37.

    Hosia A, Bamstedt U. Seasonal changes in the gelatinous zooplankton community and hydromedusa abundances in Korsfjord and Fanafjord, western Norway. Mar Ecol Prog Ser. 2007;351:113–27.

    Article  Google Scholar 

  38. 38.

    Holme NA. Methods of sampling the benthos. Adv Mar Biol. 1964;2:171–260.

    Article  Google Scholar 

  39. 39.

    Magnusson J, Berge JA, Bjerkeng B, Bokn T, Gjøsæter J, Johnsen T, Lømsland E, Schram TA, Solli A. Overvåking av forurensningssituasjonen i indre Oslofjord 2000. NIVA, Oslo. Rapport nr. 85. Oslo: Norwegian Institute for Water Research; 2001.

  40. 40.

    Remane A. Verteilung und organisation der benthonischen mikrofauna der Kieler Bucht. Wiss Meeresunters Kiel NF. 1933;21:161–221.

    Google Scholar 

  41. 41.

    Hosia A, Pagès F. Unexpected new species of deep-water Hydroidomedusae from Korsfjorden, Norway. Mar Biol. 2007;151:177–84.

    Article  Google Scholar 

  42. 42.

    McKelvey KS, Aubry KB, Schwartz MK. Using anecdotal occurrence data for rare or elusive species: the illusion of reality and a call for evidentiary standards. BioSci. 2008;58:549–555; 71:153–166.

  43. 43.

    Bouillon J, Massin C, Kresevic R. Hydroidomedusae de l’Institut Royal des Sciences naturelles de Belgique. Doc Travail l’Inst roy Sci Nat Belg. 1995;78:1–110.

    Google Scholar 

  44. 44.

    Rygg B. Bløtbunnsfauna i dype områder i ytre Oslofjord. NIVA, Oslo. Rapport lnr. 4419–2001. Oslo: Norwegian Institute for Water Research; 2001.

  45. 45.

    Magnusson J, Berge JA, Amundsen R, Gjøsæter J, Johnsen T, Lømsland E, Solli A. Overvåking av forurensningssituasjonen i indre Oslofjord 2001. NIVA, Oslo. Rapport nr. 88. Oslo: Norwegian Institute for Water Research; 2002.

  46. 46.

    Magnusson J, Andersen T, Amundsen R, Bokn T, Berge JA, Gjøsæter J, Johnsen T, Kroglund T, Lømsland E, Solli A. Overvåking av forurensningssituasjonen i indre Oslofjord 2002. NIVA, Oslo. Rapport nr. 91. Oslo: Norwegian Institute for Water Research; 2003.

  47. 47.

    Magnusson J, Andersen T, Amundsen R, Berge JA, Bjerkeng B, Gjøsæter J, Johnsen T, Lømsland E, Paulsen Ø, Schøyen M. Overvåking av forurensningssituasjonen i indre Oslofjord 2004. NIVA, Oslo. Rapport nr. 97. Oslo: Norwegian Institute for Water Research; 2005.

  48. 48.

    Magnusson J, Andersen T, Amundsen R, Berge JA, Bjerkeng B, Gjøsæter J, Hylland K, Johnsen T, Lømsland E, Paulsen Ø, Ruus A, Schøyen M, Walday M. Overvåking av forurensningssituasjonen i indre Oslofjord 2005. NIVA, Oslo. Rapport nr. 99. Oslo: Norwegian Institute for Water Research; 2006.

  49. 49.

    Berge JA, Andersen T, Amundsen R, Bjerkeng B, Bjerknes E, Gitmark JK, Gjøsæter J, Johnsen T, Lømsland ER, Magnusson J, Nilsson HC, Paulsen Ø, Rohrlack T, Sørensen K, Walday M. Overvåking av forurensningssituasjonen i indre Oslofjord 2008. NIVA Rapport nr. 104. Oslo: Norwegian Institute for Water Research; 2009.

  50. 50.

    Berge JA, Amundsen R, Bjerkeng B, Bjerknes E, Espeland SH, Hylland K, Imrik C, Johnsen T, Lømsland ER, Magnusson J, Nilsson HC, Rohrlack T, Sørensen K, Walday M. Overvåking av forurensningssituasjonen i Indre Oslofjord 2009. NIVA Rapport nr. 5985. Oslo: Norwegian Institute for Water Research; 2010.

  51. 51.

    Online collections catalogue of the NHM. Natural History Museum, London. 2018. http://data.nhm.ac.uk/object/512ae93a-e451-4ea5-a03a-3d3be9591d47. Accessed 13 March 2018.

  52. 52.

    Online collections catalogue of the NHM. Natural History Museum, London. 2018. http://data.nhm.ac.uk/object/bc92bc6e-bd73-462e-8960-90617284be82. Accessed 13 March 2018.

  53. 53.

    Online collections catalogue of the NHM. Natural History Museum, London. 2018. http://data.nhm.ac.uk/object/2ccbd041-9003-436b-96e7-b16d3b34ebef. Accessed 13 March 2018.

Download references

Authors’ contributions

LM and AH conceived the study; LM, AH, and AHST collected samples and performed the experiments; AH and AHST secured funding and provided resources; LM wrote the first draft of the manuscript. All authors read and approved the final manuscript.

Acknowledgements

The authors thank the crew of RV Hans Brattström and Christine Østensvig for their help in collecting the medusae and the staff at the Espegrend Marine Biological Station for providing facilities. Thanks are also due to the staff and curators of the Natural History Collections of the University Museum in Bergen and the Natural History Museum of the University of Oslo for providing loans and access to relevant material, to Prof. Endre Willassen for commenting on the phylogenetic methods and results, and to the anonymous reviewers for their useful comments on the manuscript.

Competing interests

The authors declare that they have no competing interests.

Availability of data and materials

All data generated or analyzed during this study are included in this published article and its Additional file.

Consent for publication

Not applicable.

Ethics approval and consent to participate

Not applicable.

Funding

The present study was funded by the Norwegian Taxonomy Initiative projects 70184233/HYPNO (LM and AH) and 70184235/NorAmph (AHST). The funder had no role in study design, data collection, data analysis, data interpretation, or writing of the manuscript.

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Author information

Affiliations

  1. Department of Natural History, University Museum of Bergen, University of Bergen, P.O. Box 7800, 5020, Bergen, Norway

    Luis Martell, Anne Helene S. Tandberg & Aino Hosia

Authors
  1. Luis Martell
    View author publications

    You can also search for this author in PubMed Google Scholar

  2. Anne Helene S. Tandberg
    View author publications

    You can also search for this author in PubMed Google Scholar

  3. Aino Hosia
    View author publications

    You can also search for this author in PubMed Google Scholar

Corresponding author

Correspondence to Luis Martell.

Additional file

Additional file 1.

Validated records of Tesserogastria musculosa Beyer, 1958. List of all the records of Tesserogastria musculosa Beyer, 1958 validated for this study and used to generate Fig. 4.

Rights and permissions

Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Martell, L., Tandberg, A.H.S. & Hosia, A. The illusion of rarity in an epibenthic jellyfish: facts and artefacts in the distribution of Tesserogastria musculosa (Hydrozoa, Ptychogastriidae). Helgol Mar Res 72, 12 (2018). https://doi.org/10.1186/s10152-018-0515-5

Download citation

Keywords

  • Hydromedusa
  • Trachylina
  • Soft bottom
  • DNA-barcoding
  • Benthic medusa

Helgoland Marine Research

ISSN: 1438-3888

Contact us