ORIGINAL RESEARCH article

Front. Environ. Sci., 21 December 2023

Sec. Freshwater Science

Volume 11 - 2023 | https://doi.org/10.3389/fenvs.2023.1305077

Comparative diversity in glochidia of Australasian freshwater mussels

  • 1. Australian Rivers Institute, Griffith University, Nathan, QLD, Australia

  • 2. Malacology, Department of Aquatic Zoology, Western Australian Museum, Welshpool, WA, Australia

  • 3. Centre for Ecosystem Science, School of Biological, Earth and Environmental Sciences, The University of New South Wales, Sydney, NSW, Australia

  • 4. Environmental Research Institute of the Supervising Scientist (ERISS), Department of Climate Change, Energy, the Environment and Water, Darwin, NT, Australia

  • 5. National Institute of Water and Atmospheric Research, Hamilton, New Zealand

  • 6. Arthur Rylah Institute for Environmental Research, Department of Energy, Environment, and Climate Action, Heidelberg, VIC, Australia

  • 7. Applied Chemistry and Environmental Science, RMIT University, Melbourne, VIC, Australia

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Abstract

Most freshwater mussels have larvae (glochidia in Unionidae, Margaritiferidae and Hyriidae) that are parasitic on fishes. This study describes and compares the diversity of glochidia among 17 species of Australasian Hyriidae. Here, scanning electron microscopy was used to illustrate shell morphology, while patterns of diversity in size, shape and morphological characteristics were analysed quantitatively and qualitatively with Principal Component, Linear Discriminant, and Multiple Correspondence Analyses to separate species with varying degrees of discrimination. Results showed shell lengths ranged from 50 to 390 μm. Shape varied, from sub-oval to sub-triangular, bilaterally symmetrical to scalene, and hook morphology varied from unicuspid, bicuspid, tricuspid or complex with varying length and structure. Unique observations of this study include the consistent variation in glochidial release mechanisms among Australian subfamilies and New Zealand genera. Hyridellini species and Echyridella aucklandica (Gray and Dieffenbach, 1843) are released either freely or as “mesoconglutinates” (presumed brood lures), whereas Velesunioninae and Echyridella menziesii (Gray and Dieffenbach, 1843) release glochidia in “amorphous mucous conglutinates”. Hyridellini predominantly occur within perennially flowing rivers of coastal south-eastern Australia with generally low turbidity, whereas the Velesunioninae occur more typically in slower flowing, intermittent waters, many prone to extended periods of high turbidity. Thus, where Hyridellini occur, mesoconglutinates as visual brood lures may be a more efficient mechanism for infesting host fishes than the passive infestation strategy typical of velesunionine species frequenting more turbid waters. Finally, this study presents systematic descriptions of glochidia and a provisional key for identification of Australasian hyriid glochidia, making an important contribution to the current understanding of taxonomy and life history traits, both critical for hyriid conservation.

1 Introduction

Extant freshwater mussels (Bivalvia) of the order Unionoida occupy waterbodies on every continent except Antarctica, with a global diversity approaching 1,000 species (Bogan and Roe, 2008; Graf and Cummings, 2021). During reproduction, males release sperm into the water column that are then taken in through the inhalant siphons of females; eggs are fertilised internally and brooded in specialised chambers of the ctenidia called marsupia. Widely accepted as a dispersal strategy, the larvae of almost all freshwater mussel species are parasitic on fishes and rarely, amphibians (Howard, 1915; Kat, 1984). Larvae occur in two distinct forms: lasidia in the Etheriidae, Iridinidae and Mycetopodidae and glochidia in the Unionidae, Margaritiferidae and Hyriidae (Bauer and Wächtler, 2001). This study focuses on the glochidia of Australasian Hyriidae.

The mechanism of glochidial release and host infestation strategy varies widely. Some species broadcast individual glochidia directly to the water column to infest host fishes specifically during spawning migrations (Araujo et al., 2000; Hastie and Young, 2003; Soler et al., 2018). Other species have evolved modifications of the simple glochidia broadcast release strategy, such as Unio crassusNilsson, 1822, that moves into shallow water to spurt water streams while releasing glochidia, presumably to attract potential hosts (Vicentini, 2005). In the Lampsilini (Unionidae), strategies for attracting hosts include mimicry via the production of various types of conglutinates, mantle lures and host-trapping (Barnhart et al., 2008). Functional conglutinates are structures that contain glochidia that often resemble food or prey items that infest hosts with glochidia when ingested; these vary in form and complexity (Barnhart et al., 2008; Watters, 2008). In amorphous, mucous conglutinates (or “mucous strands” or “mucous strings”), glochidia are released in a loose mucous matrix that dissociates in water (Watters, 2008). This type of glochidial release mechanism usually facilitates passive infestation where hosts contact glochidia as they swim through suspended mucus and glochidia (e.g., Matteson, 1948; Barnhart et al., 2008). The snuffbox mussel, Epioblasma triquetra (Rafinesque, 1820), has taken this further to actively trap the host between its modified shell valves whilst releasing glochidia for infestation (Barnhart and Roston, 2005; Barnhart et al., 2008).

Among species, glochidia vary widely in size, shape, and morphological features. Shell sizes range in length from 47.5 µm in Margaritifera margaritifera (Linnaeus, 1758) (Soler et al., 2018) to 500 µm in Strophitus undulatus (Say, 1817) (Hoggarth, 1999), while in shape outline they can vary from subtriangular (equilateral, isosceles, or scalene), suborbicular, hatchet-shaped (Ortmann, 1921; Kat, 1984; Jones et al., 1986; Hoggarth, 1999; Bauer and Wächtler, 2001; Sayenko, 2006, 2016; Pimpão et al., 2012) to an amorphous shape and bilateral asymmetry of opposing valves (Pfeiffer and Graf, 2015 and references therein). The glochidial stage of development in freshwater mussels is monomyarian, possessing a single adductor muscle that redevelops into a dimyarian state during metamorphosis to the juvenile stage (Bauer and Wächtler, 2001). Apart from Lillie (1895), there have been few studies of early development in freshwater mussels, but specific morphological features have been investigated, including sensory hairs, the larval mantle, ciliary fields and the larval filament, the latter of which is either present or absent, depending on species (Bauer and Wächtler, 2001; Nivischenko et al., 2022). The ventral apex of the glochidial valves in many species are equipped with hooks (as defined by Carter et al., 2012) of varying forms, also referred to as ‘larval teeth’, that assist in attachment to their host (Bauer and Wächtler, 2001). Morphological and morphometrical studies of glochidia and marsupia, as well as the mechanism and timing of glochidial release, have proven valuable in systematics and taxonomy (Ortmann, 1921; Parodiz and Bonetto, 1963; Heard and Guckert, 1970; Pimpão et al., 2012; O’Brien et al., 2019; Chernyshev et al., 2020), mode of parasitism (Barnhart et al., 2008; Huber and Geist, 2019), identification of host fishes (Shephard et al., 2021), conservation (Zając and Zając, 2021; Aldridge et al., 2022) and captive breeding programs (Benedict and Geist, 2021).

Among the glochidia-bearing families of freshwater mussels, extant Hyriidae are restricted to the Southern Hemisphere in Australasia (including Australia, New Zealand, Papua New Guinea, Solomon Islands, and Indonesian West Papua) and South America (Graf and Cummings, 2007; Bogan, 2008; Miyahira et al., 2017). The Australasian Hyriidae are split between two subfamilies: the Velesunioninae (genera: Alathyria, Lortiella, Microdontia, Velesunio and Westralunio), exclusive to Australia and New Guinea, and the Hyriinae (genera: Cucumerunio, Hyridella and Virgus), but the taxonomic position of the New Zealand genus, Echyridella, remains uncertain as representatives of this genus have not been included in recent molecular phylogenetic studies of the Hyriidae (Graf et al., 2015; Santos-Neto et al., 2016; Miyahira et al., 2017). Consequently, Graf and Cummings (2021) have assigned Echyridella as incertae sedis within the Hyriinae. The Hyriinae are partitioned into three tribes from South America, Hyriini, Castaliini and Rhipidodontini, and one tribe from eastern Australia and Papua New Guinea, Hyridellini (genera: Cucumerunio, Hyridella and Virgus) (Walker et al., 2014; Graf and Cummings, 2021). Glochidial morphology and morphometry, and in some cases, release mechanisms and host fishes, have been documented for several species of Hyriidae from Australia (McMichael and Hiscock, 1958; Parodiz and Bonetto, 1963; Atkins, 1979; Walker, 1981; Humphrey and Simpson, 1985; Jones et al., 1986; Widarto, 1993; Jupiter and Byrne, 1997; Klunzinger et al., 2012, Klunzinger et al., 2013; Klunzinger, 2020; Klunzinger, 2023a), South America (Bonetto, 1951; Bonetto, 1959; Bonetto, 1961; Bonetto and Ezcurra, 1963; Parodiz and Bonetto, 1963; Alvarenga and Ricci, 1977; Bonetto et al., 1986;Mansur, 1999; Mansur and Campos-Velho, 1990; Ricci et al., 1990; Semenas et al., 1994; Mansur and Silva, 1999; Viozzi and Brugni, 2001; Beasley et al., 2005; Pimpão et al., 2012) and New Zealand (Percival, 1931; Clearwater et al., 2014; Brown et al., 2017; Hanrahan, 2019; Melchior et al., 2021a; Melchior et al., 2021b). However, glochidial morphometry and morphology and their mechanism of release, remain unknown in many Hyriidae. This study incorporates published information, together with new observations from recent acquisitions of glochidia, to describe and illustrate behavioural, morphological and morphometrical data for a total of 17 species of Australasian Hyriidae from 24 localities of Australia, New Zealand, and Papua New Guinea, supplemented with a provisional dichotomous key for their identification.

2 Materials and methods

2.1 Mussel collections and new observations

Details of collection localities and glochidial taxa included in this study are provided in Table 1. Distributions of focal taxa included in this study (based on Marshall et al., 2014; Walker et al., 2014; Klunzinger et al., 2022; Ponder et al., 2023) are provided in Supplementary Figure S1. Taxonomy follows Walker et al. (2014), Marshall et al. (2014), Klunzinger et al. (2022), Ponder et al. (2023) and Graf and Cummings (2023). Live samples of adult mussels of Cucumerunio novaehollandiae (Gray, 1843), Hyridella australis (Lamarck, 1819), Hyridella drapeta (Iredale, 1934), Hyridella glenelgensis (Dennant, 1898), Hyridella narracanensis (Cotton and Gabriel, 1932), and Velesunio angasi (Sowerby II, 1867) were hand-collected from multiple localities at varying times of the year; known times of brooding were gleaned from a combination of unpublished field observations and literature (Humphrey and Simpson, 1985; Jones et al., 1986; Playford and Walker, 2008; Jones, 2014; Treby, 2016). Atkins (1979) described the glochidia of H. drapeta from Diamond Creek, Victoria as having hooks, a larval filament and release mechanism resembling that of Velesunio ambiguus (Philippi, 1847) (as per Walker, 1981). Jones et al. (1986) found freshwater mussel specimens from the Macleay River, New South Wales, consistent with published and museum collections of H. drapeta, but the glochidia did not match the descriptions of Atkins (1979). Samples of glochidia from the species resembling H. drapeta were collected from adults in Diamond Creek (Table 1) to determine whether Atkins (1979) had potentially misidentified the species. Velesunio ambiguus was absent from the locality and subsequent investigations indicate that the species most recently collected has affinities with H. drapeta, but unpublished molecular sequence data indicate that it is an undescribed taxon, hereafter, Hyridella sp. ‘Diamond Creek’ (Klunzinger et al., unpublished data). Hand-collected mussels were retained in vessels containing water from each collection site, maintained at room temperature, and observed for glochidial release over several days, except for H. sp. ‘Diamond Creek’, where glochidia were collected directly from gravid females’ ctenidia and observed for maturity under a compound microscope in the field. Glochidia are deemed mature when they expand their valves to rupture vitelline membranes and then begin “winking”: rapidly opening and closing of the glochidial valves (cf. Jones et al., 1986; Kleinhenz et al., 2019). Glochidia of E. aucklandica and E. menziesii were collected and observed according to methods described by Melchior et al. (2021a). Glochidia of Alathyria profuga (Gould, 1851) were collected according to methods described by Jones et al. (1986). Samples of glochidia of Lortiella froggattiIredale, 1934 were obtained, under license, from gravid females held in the malacology collection of the Australian Museum, Sydney (Museum Voucher No. C.414981).

TABLE 1

TaxonCollection dateCollection localityLatitude (° S)Longitude (° E)Source
Subfamily incertae sedis
Echyridella aucklandicaJanuary 2019Ohautira Stream, New Zealand37.7619174.9802Melchior et al., 2021a + this study
E. menziesiipre-1932Lake Sarah, Canterbury, New Zealand--Percival, 1931; McMichael and Hiscock, 1958
December 2011Waikato River, New Zealand37.9466175.5861Jones unpublished, this study
January 2019Ohautira Stream, New Zealand37.7619174.9802Melchior et al., 2021a + this study
Hyriinae: Hyridellini
Cucumerunio novaehollandiaeMay 1983Macleay River, NSW, Australia30.7548152.1907Jones et al., 1986 + this study
June 2010Gloucester River, NSW, Australia31.8962152.0974this study (unpublished data from Jones, 2014)
May 2021Mary River, Qld, Australia26.5475152.7556this study
Hyridella australisApril 1983Macleay River, NSW, Australia30.7548152.1907Jones et al., 1986 + this study
2007Williams River, NSW Australia32.5587151.7987this study (unpublished data from Jones, 2014)
April 2022South Pine River, Qld, Australia27.3500152.9462this study
H. drapeta*pre-1958Williams River, NSW Australia--McMichael and Hiscock, 1958*
2007Williams River, NSW Australia32.5587151.7987this study (unpublished data from Jones, 2014)
March 2018South Pine River, Qld, Australia27.3500152.9462this study
H. sp. ‘Diamond Creek’December 2012Diamond Creek, Vic, Australia37.6762145.1522this study
H. depressa1983Macleay River, NSW, Australia30.7647152.3655Jones et al., 1986 + this study
1995Lake Burragorang, NSW, Australia33.9384150.4291Jupiter and Byrne (1997)
H. glenelgensisDecember 2019Crawford River, Vic, Australia37.9308141.3055this study
H. narracanensisDecember 2015Ruby Creek, Vic, Australia31.4319145.9513this study (unpublished data from Treby, 2016)
Velesunioninae
Alathyria jacksoniNovember 1977River Murray, SA, Australia34.1864140.2920Walker (1981)
A. pertexta pertextapre-1958Larcom Creek, Qld, Australia--McMichael and Hiscock (1958)
March 2018Murray Lagoon, Qld, Australia23.4022150.4888this study
October 2018Isaac River, Qld, Australia22.6828149.1800Klunzinger, 2020 + this study
August 2019Mary River, Qld, Australia26.5475152.7556
A. cf. profugapre-1986Macleay River, NSW Australia--Jones et al., 1986 + this study
A. profugapre-1958Williams River, NSW, Australia--McMichael and Hiscock (1958)
October 2005Mill Dam Falls (Williams River), NSW, Australia32.5586151.8043this study
Lortiella froggattiMay 1988Fitzroy River, WA, Australia18.1116125.7009this study (AMS C.414981)
Velesunio ambiguuspre-1958River Murray, SA, Australia--McMichael and Hiscock (1958)
November 1977River Murray, SA, Australia34.1864140.2920Walker (1981)
V. angasi*pre-1993Ross River, Qld, Australia--Widarto (1993)
October 2022Mudginberri Billabong, NT, Australia12.5926132.8759this study
Westralunio albertisiJune 2018Levame Oxbow, Fly River, PNG7.5484141.4288Klunzinger, 2023a + this study
W. carteriDecember 2011Canning River, Behind Fancote Park, Kelmscott, WA, Australia32.0674116.0102Klunzinger et al., 2013 + this study
Collie River, 100 m downstream from Southwest Highway, WA, Australia32.3022115.8175

Provenance details of glochidia from Australasian Hyriidae included in this study. NSW—New South Wales , NT—Northern Territory, PNG—Papua New Guinea, Qld—Queensland, SA—South Australia, Vic—Victoria, WA—Western Australia. *Note: McMichael and Hiscock (1958) incorrectly identified Hyridella drapeta as Hyridella australis in their glochidia figure and Widarto (1993) reported data for Velesunio ambiguus, but the species does not occur in the Ross River, Queensland and is more likely Velesunio angasi. Coordinate system: WGS 1984 EPSG: 4326.

Definitions of glochidial release mechanisms follow Watters (2008) and Haag (2012). Material released from exhalent siphons of live mussels was collected using a glass pipette, placed on a glass slide, and examined under light microscopy for the presence of glochidia with their behaviour observed. In C. novaehollandiae, H. australis and H. drapeta, brooding was confirmed by prying open the shell valves with reverse pliers or through dissection by inserting a scalpel between the two valves to cut adductor muscles to observe the inner pair of demibranchs for the presence of thickened, red-brown marsupia. Dissection was not performed in H. glenelgensis or H. narracanensis given these species have small sub-populations, restricted in geographic range, and listed as threatened (critically endangered or endangered) under the IUCN Red List, the Victorian Flora and Fauna Guarantee Act 1988, and the Commonwealth of Australia Environment Protection and Biodiversity Conservation Act 1999 (Klunzinger, 2023b). Live individuals of each of these two species were returned to the wild after glochidia were collected.

2.2 Glochidial morphometry and morphology

Samples of live-released glochidia from H. sp. ‘Diamond Creek’ were collected by glass pipette, fixed in 2% glutaraldehyde following Jupiter and Byrne (1997) and rinsed and stored in Sorenson’s sodium phosphate buffer for later study. Samples of live-released V. angasi (Mudginberri Billabong, Magela Creek, Northern Territory, Australia, Table 1) and Westralunio carteriIredale, 1934 (from Canning River, Western Australia, Table 1) were separately collected by glass pipette, placed on a glass slide, and digitally photographed under compound light microscopy to capture details of soft tissues. Samples of glochidia from L. froggatti and A. profuga were flushed from the ctenidia of ethanol-preserved specimens of gravid females using a glass pipette. Samples of live-released glochidia for other species were collected by glass pipette and held in a glass jar with tap water for several days or up to a week, after which time glochidia had died and soft tissues had autolyzed, confirmed by examining a small sample of glochidia on a glass slide under light microscopy. Glochidial shells were then transferred by glass pipette into 5–mL microcentrifuge tubes containing 95% ethanol for preservation. Preserved glochidia were then deposited onto specimen stubs affixed with double-sided carbon tape using a glass pipette and allowed to air dry. Samples of H. drapeta and H. sp. ‘Diamond Creek’ were photographed on a Hitachi TM 3030 Plus Scanning Electron Microscope (SEM) and associated software at the Western Australian Museum in May 2019. Other samples were sputter-coated with platinum using a Safematic CCU-010 Compact Coating Unit and photographed using a Hitachi TM4000 Plus SEM and associated digital software at the University of Queensland Centre for Microscopy and Microanalysis between April 2022 and August 2023. Images or illustrations of glochidia from other studies (Alathyria jacksoniIredale, 1934 and V. ambiguus, as per Walker, 1981; Hyridella depressa (Lamarck, 1819), as per Jones et al., 1986; W. carteri, as per Klunzinger et al., 2013; H. narracanensis, as per Treby, 2016; Alathyria pertexta pertextaIredale, 1934, as per Klunzinger, 2020; Westralunio albertisiClench, 1957, as per Klunzinger, 2023a; H. sp. ‘Diamond Creek’, taken at the Australian Centre for Microscopy and Microanalysis, University of Sydney, using a Zeiss EVO SEM (Jones, unpublished)) were also included for additional details of hook morphology.

Glochidia were measured to the nearest 1 µm from scale-imprinted SEM images for length (L), height (H), hinge length (Hg) and larval hook length (LHL) and to the nearest 1 degree (°) for angle of obliquity (Á) (see Figure 1). The Á was measured on just one individual valve that appeared to be resting flat on the specimen stub for each individual glochidium. The LHL values for each individual glochidium were measured either as the mean of two larval hooks (in the case where two opposing larval hooks could be accurately measured from an individual glochidium) or as an individual LHL (in the case where only one larval hook could be measured on an individual glochidium). Size was determined as the average of L and H. Additional data on shell size measurements of glochidia of various Australasian hyriid taxa were included from published literature and unpublished data of the authors.

FIGURE 1

2.3 Statistical analyses

All statistical analyses were carried out using the R statistical package (R Core Team, 2022). To understand the similarities of complex glochidial shapes across species, metrics of glochidial dimensions and shape (H, L, Hg, H/L, Hg/L, LHL and Á) were normalised and Principal Component Analysis (PCA) used to reduce shape complexity into two or three explanatory dimensions. The closer two glochidial samples are in this reduced dimensional space, the more similar their overall shape. Samples within this space were then coded by their species affinity, highlighting species differentiation based on glochidial shape.

To further understand the specific morphometrical variables (i.e., discriminant functions) that best separated species, Linear Discriminant Analysis (LDA) was used (MASS package: Venables and Ripley, 2002); this analysis tests for group structure in multivariate data and identifies linear combinations of variables that best separate the input categories, in this case, the species.

Three measures of accuracy were then calculated to assess the classification of the glochidial samples into the species (as categories) based on morphological traits: 1) overall classification accuracy, 2) errors of omission (also known as producer’s accuracy) and 3) errors of commission (also called user’s accuracy) (Story and Congalton, 1986). An error of omission is the proportion of incorrectly classified glochidia for a known reference species, calculated as the number of correctly classified glochidia (on the major diagonal of the confusion matrix), divided by the number of samples of the reference species (i.e., the column total for the reference species). An error of commission is a measure of the reliability of the classification rule and addresses the question, “What percentage of glochidia classified as species i are actually species i?”. This is calculated as number of correctly classified glochidia divided by the row total for species i (i.e., the number of glochidia classified as species i). Error matrices compare the allocation of glochidia among species using discriminant functions with their known species identities.

In addition to quantitative analysis of glochidial shell metrics, multiple correspondence analysis (MCA) was used to group species according to qualitative measures of glochidial morphology and to overlay species associations with morphological characters (Table 2) using the functions in the FactoMineR package (Lê et al., 2008). Multiple correspondence analysis is essentially PCA of qualitative (i.e., categorical) variables instead of quantitative measurements (Abdi and Williams, 2012). Qualitative glochidial characters were scored for the glochidia of all species of Australasian freshwater mussels for which there were data (Table 1), and MCA was used to ordinate species in two dimensions.

TABLE 2

Variable nameCategorical definitions
glochidia sizesmall, glochidia <100 μm
large, glochidia >100 μm
shapesubtriangular, ventral apex comes to a point and forms a triangular shape relative to the apices of the anterior and posterior ends of the hinge plane
suborbicular, ventral apex rounded and overall shape oval to nearly circular
H/L ratiolow, <85%
medium, 85%–110%
high, >110%
valve symmetrybilateral, ventral apex approximately mid-way between either end of the hinge line and mean Á <5°
scalene, ventral apex off-centre relative to either end of the hinge line and mean Á >5°
cusp typeunicuspid, hooks come to a singular point (cusp) in either valve
bicuspid, hooks with two cusps in each valve
tricuspid, hooks with central well-formed tooth/blade bounded by two smaller cusps in at least one valve
complex, hooks may have singular or multiple cusps and varying in form from blunt or rounded to pointed
hook formbuttressed, having distinctive supporting buttresses either side of the hook running from the ventral edge of the shell, gradually tapering off to below the cusp
long, sigmoidal, LHL >20 μm and form an s-shape when viewed from the side
reduced, hook reduced to a broad base from which a pair of hooks project, LHL <20 μm
larval filamentpresent or
absent

Definitions of categorical variables used in multiple correspondence analysis (MCA) of glochidia of Australasian freshwater mussels (Unionoida: Hyriidae). Each defined category for a particular variable is provided in italic font.

3 Results

3.1 Marsupial occupancy and glochidial release

Marsupia occupied the majority of the inner demibranchs of ctenidia in C. novaehollandiae, the inner four-fifths in H. australis, and the inner two-thirds in H. drapeta and H. sp. ‘Diamond Creek’. Additionally, in H. australis, the dorsal one-third of the marsupia within the inner demibranchs were thickened and white in two dissected females. Marsupia occupied the upper four-fifths of the inner demibranchs of ctenidia in E. aucklandica (Melchior et al., 2021a) and the inner one third in E. menziesii (McMichael and Hiscock, 1958; Melchior et al., 2021a). The marsupia of members of the Velesunioninae generally occupy the inner two-thirds of the inner demibranchs (Humphrey and Simpson, 1985; Walker, 1981; Klunzinger et al., 2013; Klunzinger, 2020; 2023a; Jones, pers. obs.). Reproductive output for H. depressa is positively correlated with nutrient status of ambient waters (Byrne, 1998), while under eutrophic conditions, the marsupia may occupy the entire inner demibranchs in V. angasi (Humphrey and Simpson, 1985). As gravid adult females of H. glenelgensis and H. narracanensis were not dissected, the proportion of ctenidia occupied by marsupia was not determined.

Undissected H. australis released several white botuliform conglutinates, approximately 20–30 mm in length within 4 days post-collection. Glochidia released from H. glenelgensis and H. narracanensis released glochidia contained within sticky white to light yellow conglutinates, preceded by an enlargement of the exhalent siphon that turned from pale grey to dark grey or reddish brown and exhibited a “waving” motion prior to the release of conglutinates (Figure 2A–D, Figures 2G–L for H. glenelgensis and H. narracanensis, respectively); glochidia were only released after disturbance by squirting water in short bursts against the siphons of H. glenelgensis or tapping the shells of H. narracanensis with a blunt probe. Glochidia were released from C. novaehollandiae freely and were not contained in amorphous mucous conglutinates or any other form of conglutinate within 2 days post-capture (Figures 2E, F). Glochidia of H. drapeta were extruded from the exhalent siphons of brooding females as clear, amorphous, mucous conglutinates. Hyridella sp. ‘Diamond Creek’ are also thought to release glochidia as amorphous mucous conglutinates (Atkins, 1979, see discussion), although glochidial release of this taxon was not observed in the present study. Live samples of glochidia of H. sp. ‘Diamond Creek’ examined during the present study did not possess larval threads, unlike Atkins (1979) who described them as being present, presumably from the same taxon collected from the same stream. Westralunio carteri, A. pertexta pertexta and V. angasi release glochidia in amorphous mucous conglutinates (Humphrey and Simpson, 1985; Klunzinger et al., 2013; Klunzinger, 2020). Echyridella menziesii has been observed to release glochidia singularly and in amorphous mucous conglutinates (Melchior et al., 2021a). This form of glochidial release is illustrated in Figures 2M, N for E. menziesii and A. pertexta pertexta, respectively. Glochidia are released as functional conglutinates resembling vermiform macroinvertebrate prey items of fishes in E. aucklandica (Melchior et al., 2021a, Figures 2O–Q), similar in form to conglutinates released by those of H. australis (Jones et al., 1986; see also Section 4.1 below).

FIGURE 2

3.2 Glochidial morphology

Of the species studied, glochidia of E. menziesii and all velesunionine taxa except A. profuga possess larval filaments (Table 3). None of the glochidia in the Hyridellini in this study possessed larval filaments. Glochidia varied in size and shape among species and to a lesser extent within species. A summary of traditional morphometrical measurements obtained by this study, in comparison with other species and populations of Australasian glochidia for which published information is available, is provided in Table 4. The raw data from which this summary was tabulated are provided in Supplementary Table S1. To illustrate the variation in size and shape of glochidia, SEM images of shell valves are provided in Figure 3. Hook morphology is illustrated in Figure 4 with more detailed views and additional images of glochidia provided in the Supplementary Material (Supplementary Figures S2-S18). Soft anatomy of glochidia was generally not available, owing to the methods of preservation in this study, but an example of soft anatomical features from a live V. angasi glochidium, including adductor musculature and sensory hairs, is provided in Figure 5A and an example of a larval filament from a live image of W. carteri is shown in Figure 5B. Two valve shapes were apparent in the glochidia from this study (Table 3 and Figure 3): suborbicular in C. novaehollandiae, H. glenelgensis and H. narracanensis and subtriangular for all other species in this study. The H/L ratio, a measure of “squatness”, varied from tall and narrow (H/L >100%) to short and broad (H/L <100%) with the two extremes in form represented by C. novaehollandiae and H. australis (H/L 110%–128%) compared with E. aucklandica, A. profuga and W. carteri (H/L 81%–85%). In terms of valve symmetry, most glochidia studied here are scalene, apart from A. jacksoni, C. novaehollandiae, E. aucklandica, H. australis, H. glenelgensis, H. narracanensis and one population of V. ambiguus that have ventral apices located approximately mid-way between either end of the hinge line (Á, 0–5°), imparting bilaterally symmetrical valves (Table 3). The most bilaterally asymmetrical species is W. carteri that has a much larger Á (19.8°) than other scalene species which ranged from about 8 to 10° in A. profuga, H. drapeta, A. pertexta pertexta and V. angasi, to about 12–13° in L. froggatti, W. albertisi and one population of V. ambiguus, with E. menziesii having the second largest Á at 15.2°.

TABLE 3

Taxon codeTaxonSizeShapeH/L ratioValve symmetryCusp typeHook formLarval filament
Subfamily incertae sedis
EaucEchyridella aucklandicasmallsubtriangularmediumbilateralunicuspidbuttressedabsent
EmnzE. menziesiilargesubtriangularlowscaleneunicuspidbuttressedpresent
Hyriinae: Hyridellini
CnovCucumerunio novaehollandiaesmallsuborbicularhighbilateralbicuspidreducedabsent
HausHyridella australissmallsubtriangularhighbilateralbicuspidreducedabsent
HdrpH. drapetalargesubtriangularmediumscalenebicuspidlong, sigmoidalabsent
Hdia“H.” sp. ‘Diamond Creek’largesubtriangularlowscalenetricuspidlong, sigmoidalabsent
HdepH. depressalargesubtriangularmediumscalenebicuspidlong, sigmoidalabsent
HgleH. glenelgensislargesuborbicularmediumbilateralbicuspidreducedabsent
HnarH. narracanensislargesuborbicularmediumbilateralbicuspidreducedabsent
Velesunioninae
AjacAlathyria jacksonilargesubtriangularmediumbilateralunicuspidlong, sigmoidalpresent
AperA. pertexta pertextalargesubtriangularmediumscaleneunicuspidlong, sigmoidalpresent
AprfA. profugalargesubtriangularlowscaleneunicuspidlong, sigmoidalabsent
LfrgLortiella froggattilargesubtriangularmediumscaleneunicuspidlong, sigmoidalpresent
VambVelesunio ambiguuslargesubtriangularmediumscaleneunicuspidlong, sigmoidalpresent
VangV. angasilargesubtriangularmediumscaleneunicuspidlong, sigmoidalpresent
WalbWestralunio albertisilargesubtriangularmediumscaleneunicuspidlong, sigmoidalpresent
WcarW. carterilargesubtriangularlowscalenecomplexlong, sigmoidalpresent

Qualitative traits of Australasian glochidia used in multiple correspondence analysis (MCA). Definitions of each trait are provided in Table 2.

TABLE 4

TaxonLarval threadnL (µm)H (µm)Size (µm)Hg (µm)H/L (%)Hg/L (%)LHL (µm)Á (°)LocalitySource
Subfamily incertae sedis
Echyridella aucklandicaabsent-360280320-77.8---Lake Sarah, NZPercival (1931)
-323277300-85.8---McMichael and Hiscock (1958)
28101.9 ± 0.7195.7 ± 0.7498.8 ± 0.5564.8 ± 0.6694.1 ± 0.9363.6 ± 0.5913.8 ± 0.45 (n = 4)2.1 ± 0.42 (n = 20)Ohautira Stream, NZMelchior et al., 2021a; this study
E. menziesiipresent30301.3±1.20252.0 ± 0.90276.0 ± 1.02209.0 ± 1.6083.6 ± 0.2769.5 ± 0.6081.3 ± 2.67 (n = 15)15.2 ± 0.73 (n = 5)Ohautira Stream, NZMelchior et al., 2021a; this study
Hyriinae: Hyridellini
Cucumerunio novaehollandiaeabsent5055.2 ± 0.0864.1 ± 0.0359.735.8 ± 0.75 (n = 2)116.164.98.0 (n = 1)-Macleay River, NSWJones et al., 1986 + this study
1054.5 ± 0.76 (n = 7)64.4 ± 0.5059.0 ± 0.60 (n = 7)-116.7 ± 0.01 (n = 7)---Gloucester River, NSWJones, 2014 + this study
2051.1 ± 0.2656.5 ± 0.3153.8 ± 0.2332.3 ± 0.41110.7 ± 0.7263.3 ± 0.805.0 ± 0.53 (n = 10)0.9 ± 0.26 (n = 20)Mary River, Qldthis study
Hyridella australisabsent5073.9 ± 0.0794.7 ± 0.0484.34012868--Macleay River, NSWJones et al., 1986 + this study
2075.6 ± 0.3688.7 ± 0.4582.1 ± 0.2539.8 ± 0.27117.3 ± 0.9252.6 ± 0.3817.1 ± 1.60 (n = 7)0.9 ± 0.32 (n = 20)South Pine River, Qldthis study
H. drapeta*absent-250240245-96.0---Williams River, NSWMcMichael and Hiscock (1958)
1250233241.515593.262.0--Jones, 2014 + this study
20274.5 ± 1.70250.0 ± 1.78262.3 ± 1.43192.0 ± 1.1791.1 ± 0.7070.0 ± 0.5150.8 ± 1.49 (n = 3)8.7 ± 0.63 (n = 10)South Pine River, Qldthis study
H. sp. ‘Diamond Creek’present30330.0 ± 1.8230.0 ± 1.828024870.6 ± 2.7---Diamond Creek, VicAtkins (1979)
absent20331.0 ± 0.69250.0 ± 0.00290.5 ± 0.34261.0 ± 0.7875.5 ± 0.1678.9 ± 0.1571.5 ± 1.40 (n = 11)-this study
H. depressaabsent50253.0 ± 0.70244.0 ± 0.70248.5152.0 ± 0.8597.060.0--Macleay River, NSWJones et al., 1986 + this study
5243 ± 5.38249 ± 1.79246-102.5-44.4 ± 0.002 (n = 2)-Lake Burragorang, NSWJupiter and Byrne (1997)
H. glenelgensisabsent20249.3 ± 0.78225.0 ± 1.20236.9 ± 0.85150.0 ± 0.2590.1 ± 0.4460.1 ± 0.1929.2 ± 0.52 (n = 20)3.8 ± 0.31 (n = 20)Crawford River, Victhis study
H. narracanensisabsent10258.0 ± 2.49236.0 ± 2.67247.0 ± 2.00150.0 ± 4.9496.0 ± 1.1858.3 ± 2.22-4.8 ± 0.76 (n = 10)Ruby Creek, VicTreby, 2016 + this study
Velesunioninae
Alathyria jacksonipresent10272.0 ± 2.97210.0 ± 3.89238.0173.0 ± 2.9493.071.050.05.0River Murray, SAWalker (1981)
A. pertexta pertextapresent-270250260-92.6---Larcom Creek, QldMcMichael and Hiscock (1958)
10257.1 ± 2.47242.5 ± 1.88249.8 ± 1.95175.8 ± 3.42 (n = 9)94.4 ± 0.7669.0 ± 0.96 (n = 9)--Murray Lagoon, Rockhampton, Qldthis study
80268.1 ± 1.21243.0 ± 1.22255.5 ± 0.96191.0 ± 0.6390.7 ± 0.5271.3 ± 0.2770.2 ± 1.04 (n = 29)9.5 ± 0.78 (n = 20)Mary and Isaac Rivers, QldKlunzinger, 2020 + this study
A. cf. profugaabsent20239.0 ± 0.89204.0 ± 0.45221.5165.0 ± 0.8985.069.0--Macleay River, NSWJones et al., 1986 + this study
A. profugaabsent-245200222.5-81.6---Williams River, NSWMcMichael and Hiscock (1958)
17238.8 ± 1.69201.1 ± 1.21 (n = 16)220.1 ± 1.24 (n = 16)159.0 ± 1.61 (n = 15)84.2 ± 0.01 (n = 16)66.4 ± 0.06 (n = 15)40 (n = 1)8.5 (n = 2)Mill Dam Falls (Williams River), NSWJones, 2014 + this study
Lortiella froggattipresent46260.6 ± 1.2231.8 ± 0.7246.2 ± 0.8183.9 ± 0.889.0 ± 0.470.6 ± 0.473.0 (n = 1)11.8 ± 0.35 (n = 20)Fitzroy River, WAthis study
Velesunio ambiguuspresent-250220235-88.0---River Murray, SAMcMichael and Hiscock (1958)
10247.0 ± 2.97210.0 ± 3.89228.5173.0 ± 2.9485.070.060.73.0Walker (1981)
V. angasi*present15263232247.520088.276.0--Ross River, QldWidarto (1993)
60254.0 ± 1.29223.7 ± 1.10238.9 ± 0.97178.5 ± 1.1689.3 ± 0.5370.0 ± 0.4150.8 ± 1.26 (n = 22)9.6 ± 0.30 (n = 60)Mudginberri Billabong, NTthis study
Westralunio albertisiunknown60260.0 ± 1.11233.1 ± 1.32246.6 ± 0.99183.6 ± 0.9989.7 ± 0.5370.6 ± 0.3353.6 ± 0.84 (n = 3)12.9 ± 0.28 (n = 60)Levame Oxbow (Fly River), PNGKlunzinger, 2023a + this study
W. carteripresent120307.8 ± 0.83251.0 ± 0.73279.4 ± 0.63212.0 ± 0.7881.6 ± 0.2868.8 ± 0.2753.9 ± 1.66 (n = 5)19.8 ± 0.71 (n = 13)Canning and Collie Rivers, WAKlunzinger et al., 2013 + this study

Glochidial dimensions in Australasian freshwater mussels (Bivalvia: Hyriidae) included in this study. Values presented are means ± standard errors. Taxonomy follows Walker et al. (2014) and Marshall et al. (2014); note, unpublished preliminary analysis of genetic sequences suggest Hyridella sp. ‘Diamond Creek’ is an undescribed species. Abbreviations: H, height; L, length; Hg, hinge length; LHL, larval hook length; Á, angle of obliquity; Australia: NSW—New South Wales, NT—Northern Territory, Qld—Queensland, SA—South Australia, Vic—Victoria, WA—Western Australia; NZ—New Zealand; PNG—Papua New Guinea. Data of individually measured glochidia are provided in Supplementary Material. *Note: data reported for Hyridella drapeta was originally misidentified by McMichael and Hiscock 1958 as Hyridella australis and data reported for Velesunio angasi was originally misidentified as Velesunio ambiguus by Widarto (1993).

FIGURE 3

FIGURE 4

FIGURE 5

The glochidia of Velesunioninae generally have unicuspid sigmoidal hooks, apart from W. carteri that has complex hooks which are variably uni-, bi-, or tricuspid (Table 3; Figures 4H–M). The hooks of E. aucklandica are distinctly unicuspid. In E. menziesii they are also unicuspid although the cusps of the opposing hooks in E. menziesii are not identical (Table 3; Figure 4C). In E. menziesii one hook terminates as a spatulate knob with a spinose tooth projecting from the end; the opposing hook is more claw-like but with two notches on each side of the hook (Figure 4G) that may allow the hook to snap off when the valves close.

Glochidial hook morphology in the Hyridellini is much more morphologically diverse than in the Velesunioninae (Table 3; Figures 4A, B, D, E, F). The Hyridellini generally have bicuspid hooks, apart from H. sp. ‘Diamond Creek’ that is tricuspid (Figure 4F). Hooks in C. novaehollandiae, E. aucklandica, H. australis, H. glenelgensis, and H. narracanensis are greatly reduced in length compared to other species studied (Tables 3, 4; Figures 4A, B, D, E; Supplementary Material), having a common base with two sharp cusps on either valve, but the length of teeth and degree of separation between cusps varies among taxa. In C. novaehollandiae, hooks are reduced to a pair of sharp spines just below the apex of each valve (Figure 4A) but in H. glenelgensis and H. narracanensis, the paired spines are longer, separated by a blade-like cutting edge (Figure 4D; Supplementary Material). The modified hooks of H. australis differ again and consist of a pair of curved, conjoined spines united on a common, slightly-raised base, that curve in the latero-dorsal plane (Figure 4B).

3.3 Comparative analyses

The five metrics of glochidial valve dimensions (L, H, Hg, H/L and Hg/L) were highly correlated, especially L, H, and Hg (Table 5). PCA separated the glochidial species into two distinct groups along the first principal component (Figures 6A, B), based mainly on size and H/L ratio along PC1, which explained 81% of the total variation (Table 6). Glochidia were further separated along the second and third principal component axes (explaining an additional 15% of variation) according to shape (Á and H/L ratio) and LHL (Table 6). Principal Component 2 can be interpreted as contrasting scalene glochidia with those that have high H/L ratios and possess long sigmoidal hooks. Principal Component 3 contrasts glochidia that are tall (high H/L ratio) and bilaterally symmetrical with scalene glochidia that have short, wide valves. Many of the medium-sized and large glochidia could not be separated using these morphometrical criteria.

TABLE 5

LengthHeightHinge lengthAngle of obliquity
Height0.99
Hinge length0.990.97
Angle of obliquity0.750.700.80
Height/Length ratio−0.84−0.78−0.84−0.67

Pearson correlations between pairs of glochidial morphology variables.

FIGURE 6

TABLE 6

Morphometric variablePC1PC2PC3
Length0.447−0.0210.102
Height0.431−0.226−0.081
Hinge length0.445−0.1050.087
Height/length ratio−0.381−0.396−0.706
Larval tooth length0.382−0.598−0.230
Angle of obliquity0.3540.651−0.652

Loadings on morphological variables for the first three principal components. The first three principal components accounted for 96% of the variation in glochidial morphometry (81.1%, 8.9% and 6.2% for PC1, PC2 and PC3, respectively).

LDA showed that 97.5% of the between-group variance was accounted for by the first discriminant function (LD1), which reflected glochidial size and H/L ratio (Table 7). Only 1.8% of the between-group variance was accounted for by the second discriminant function (LD2), which further emphasized size but also separated species on hook length. The first two discriminant functions (LD1 and LD2) had an overall classification accuracy of 82.7%, a substantial improvement on the first discriminant function alone (57.5%). The three species with small glochidia, C. novaehollandiae, H. australis and E. aucklandica, were readily distinguished from all other species (Figure 6C) with no errors of omission or commission (Tables 8, 9). While there was considerable overlap in glochidial morphometrics of the remaining ten species, the first two discriminant functions classified most species with a high level of accuracy (Table 8). Linear Discriminant Analysis misclassified 27.5% of A. pertexta pertexta and 17% of L. froggatti glochidia. The largest errors of omission and commission were between V. angasi and W. albertisi, which show considerable overlap in size and shape metrics (Supplementary Table S2); 28% of V. angasi glochidia were misclassified as W. albertisi while 16.6% of W. albertisi were misclassified as V. angasi (Table 9).

TABLE 7

VariableLD1LD2LD3LD4
Variance explained(97.5%)(1.8%)(0.5%)(0.2%)
log(size)−36.39−11.91−0.565.96
H/L ratio6.691.645.9324.65
log(hook length)−2.037.253.54−1.85
angle of obliquity0.020.25−0.380.16

Linear discriminant coefficients of Australasian glochidial morphometrics.

TABLE 8

Observed species
Predicted speciesAperAprfCnovEaucEmnzHausHdrpHgleHnarLfrgVangWalbWcar
A. pertexta21000000004110
A. profuga01200000000300
C. novaehollandiae00100000000000
E. aucklandica00010000000000
E. menziesii00001400000001
H. australis00000200000000
H. drapeta1000008000000
H. glenelgensis00000002020000
H. narracanensis0000000080000
L. froggatti50000000029000
V. angasi000000000039100
W. albertisi000000100217480
W. carteri20001010000114

Confusion matrix summarising the classification accuracy of the first two linear discriminant functions in assigning glochidia to the correct species class. See Table 3 for species abbreviations.

TABLE 9

AperAprfCnovEaucEmnzHausHdrpHgleHnarLfrgVangWalbWcar
Producer’s accuracy72.410010010093.3100801008082.9658063.3
User’s accuracy77.88010010093.310088.990.910085.379.670.673.7

Accuracy measures (%) for each species from an LDA classification based on two discriminant functions. See Table 3 for species abbreviations. Overall accuracy is 82.7%.

Differences among species were also assessed using qualitative morphological traits by MCA (Figures 6D, E). Dimension 1 explained 40% of the variance in glochidial morphology; Dimension 2 explained 17%; and Dimension 3 explained 13% of the variance. Glochidia were partitioned into two broad morphological groups in the MCA biplots: i) large, subtriangular, scalene shells with a low to medium H/L ratio, and ii) small, suborbicular, bilaterally symmetrical shells with a high H/L ratio. The latter group also lacked a larval filament, and in the Australian Hyridellini, the hooks were bicuspid with a pair of short teeth projecting from a reduced base. Five of the velesunionine species shared the same morphological characters (Table 3) and were grouped together as “VELESUN” in the MCA biplots. The glochidia of Velesunioninae were typically large, subtriangular, and scalene with a sigmoidal hook terminating in a fluted, single pointed cusp (Figures 6D, E) except for W. carteri that had a complex cusp. The glochidia of all known members of the Velesunioninae possessed a larval filament except for A. profuga. The glochidia of several members of the Hyriinae, including E. menziesii from New Zealand, were similar in morphology to those of the Velesunioninae. Glochidia of the Hyridellini differed from those of the Velesunioninae in having bicuspid larval hooks or, in the case of H. sp. ‘Diamond Creek’, tricuspid. The hooks of E. menziesii were unicuspid, like those of the glochidia of the Velesunioninae but were also spinose and had more claw-like cusps, compared with the Velesunioninae that had hooks that were more fluted and had more blade-like cusps. In addition, the sigmoidal hooks of Echyridella spp. were buttressed and reinforced along their length.

4 Discussion

While adult freshwater mussels are moderately sedentary, the potential widespread dispersal is facilitated during the (usually) parasitic larval phase, a comparatively rapid phase in their otherwise relatively long lifespan. The ecology of glochidial release from adult mussels and the morphology of the glochidia themselves are therefore integral components of freshwater mussel survival. Freshwater mussels globally are threatened and while the focus has often been on the adult life stage, an understanding of glochidial form, function and environmental requirements is also important for their conservation (Ferreira-Rodríguez et al., 2019; Aldridge et al., 2022; Geist et al., 2023). This study is the first to statistically compare the morphology and release mechanisms of glochidia from a large suite of species belonging to the Australasian Hyriidae. The addition of new data in the present study significantly expands the current knowledge of glochidial release mechanisms and glochidial morphological diversity among Australasian Hyriidae which are inherently important in taxonomy and conservation.

4.1 Glochidial release mechanism

The first description of glochidial release in functional conglutinates in Australasian Hyriidae (H. australis) was made by Jones et al. (1986); the present study now provides illustrations and descriptions of similar release mechanisms in a further two Australian hyriids (H. glenelgensis and H. narracanensis). Laboratory studies of the hyriid E. aucklandica provided the first photographic evidence of mesoconglutinate release (Melchior et al., 2021a) with further studies demonstrating that fishes are attracted to the mesoconglutinate as a food item that resembles prey (Melchior et al., 2021b); this supported the conjecture of Jones et al. (1986) that the conglutinate is a form of lure (i.e., functional conglutinate). Preliminary evidence indicates that glochidia of H. glenelgensis attach to the gills of Galaxias maculatus (Jenyns, 1842) (= Mesites attenuatus and M. maculatus) suggesting the mesoconglutinates may be ingested by host fish and thus, may indeed be a lure (Raadik et al., unpublished data). This phenomenon is not dissimilar to some species of North American Lampsilini (Unionidae) that release mesoconglutinates in a similar way (Barnhart et al., 2008). However, by comparison, the conglutinates of the hyriids are not as elaborate and sophisticated as seen in some Unionidae, such as the blackfly pupae mimics of Ptychobranchus subtentum (Say, 1829) (see Barnhart et al., 2008), complex baited brood lures of Cyprogenia stegaria (Rafinesque, 1820) or complex tethered pisciform brood lures of Hamiota perovalis(Conrad, 1834) (Hewitt et al., 2021).

The release of mesoconglutinates from H. glenelgensis and H. narracanensis was consistent with the observations of Jones et al. (1986) for H. australis, as well as H. australis from South Pine River, Queensland, observed in this study. Laboratory observations confirm that the glochidia of H. glenelgensis attach to the gills of fish but may not be retained on the fins (Fernando and Raadik, unpublished data). Although glochidial infestation on wild-caught fishes or from laboratory exposure studies have not been reported for these Hyridella species, the release of mesoconglutinates would suggest that glochidia of these species preferentially attach to gills in a manner like the glochidia of E. aucklandica (Melchior et al., 2021b). The colour change of the exhalant siphons in H. glenelgensis and H. narracanensis and pulsating or “waving” behaviour exhibited by H. glenelgensis and H. narracanensis (and by H. australis from Jones et al., 1986) may also provide additional stimulus to attract host fishes. Similarly, distinct morphological changes in siphon colour, size and shape prior to glochidial release have also been observed for the South American hyriid, Castalia ambiguaLamarck, 1819, that the authors suggested were host attraction mechanisms, although this species does not release conglutinates (Santos et al., 2021).

The present study also offers some contradictions on larval release to those reported in the literature; the glochidia from the Diamond Creek population of H. sp. ‘Diamond Creek’ did not possess a larval filament despite Atkins (1979) previously reporting its presence, and the glochidia of E. menziesii examined in this study does possess a larval filament (H.A. Jones, pers. obs.), although it was not reported by Melchior et al. (2021a). Larval filaments have also been reported in the velesunionine glochidia of A. jacksoni (Walker, 1981), A. pertexta pertexta (Klunzinger, 2020), V. ambiguus (Parodiz and Bonetto, 1963; Walker, 1981), V. angasi (Humphrey and Simpson, 1985), W. carteri (Klunzinger et al., 2013), and L. froggatti (this study). Amorphous mucous conglutinates are typically a passive entanglement mechanism and the larval filament may assist glochidia to remain in suspension over habitat substrates such as aquatic macrophytes, silty sediment, and woody debris, where potential host fishes are likely to frequent and subsequently contact glochidia from mucous webs (Matteson, 1948; Haag and Warren, 2003; Watters, 2008; Haag, 2012; Klunzinger et al., 2012; Klunzinger et al., 2013; Melchior et al., 2021a; Melchior et al., 2021b).

Glochidia arising from amorphous mucous conglutinates typically attach to the fins of host fishes, but occasionally also to gills and other body surfaces (Humphrey and Simpson, 1985; Barnhart et al., 2008; Klunzinger et al., 2012; Haag, 2012), whereas species that release glochidia via mantle lures, mesoconglutinates or freely into the water column, preferentially parasitise gills as a consequence of active host predation (Bauer and Wächtler, 2001; Strayer, 2008; Haag, 2012). While it was beyond the scope of this paper to explore host-fish relationships and deeper discussions about host fish use, the literature indicates that Australasian hyriid glochidia are host fish generalists, utilising a broad suite of both native and alien fishes that support metamorphosis to the juvenile stage, although not in equal proportions. The exception to this, however, is the glochidia of E. aucklandica that have only been found on the gills of New Zealand smelt, Retropinna retropinna (Richardson, 1848) and no other fishes, and indeed this has been the only host fish species to date shown capable of supporting metamorphosis of glochidia to the juvenile stage under laboratory conditions (Melchior et al., 2021b).

The glochidia of a larger group of hyriids, including C. novaehollandiae, H. australis, H. depressa, H. drapeta, H. glenelgensis, H. narracanensis, A. profuga and E. aucklandica, lack larval filaments. Cucumerunio novaehollandiae produces many more glochidia than other Australasian hyriids, owing to the small size of the glochidia and the large marsupia of adult female mussels (Jones et al., 1986; Jones, 2014). Jones (2014) found that some C. novaehollandiae produce broods of up to 4 million glochidia, whereas H. depressa has glochidial counts of less than 120,000 (Byrne, 1998). However, C. novaehollandiae reproduces once per year whereas other hyriids can produce multiple broods throughout the warmer months of the year (e.g., H. depressa from Jones et al., 1986; Byrne, 1998). Cucumerunio novaehollandiae is also a known gill parasite (Jones, 2014) and release of free glochidia into the water column and surrounding habitat (that tends to be free from fine sediments that could otherwise smother glochidia) as fish pass by would mean that their mode of release is passive. A strategy of release of mesoconglutinates for this species may be negated by scour and potential dislodgement from the stronger currents in which this species inhabits; thus, releases of free glochidia but in very large numbers may nullify losses in faster stream currents. On the other hand, C. novaehollandiae occupies microhabitats that are between or in the lee of large boulders, so the glochidia may accumulate within the protection of the separation zones and within the boundary layer of the stream where fishes may seek shelter from water currents, resulting in close contact with the large numbers of glochidia and infestation of the gills. At least some margaritiferids release their tiny glochidia in a similar way and occupy similar habitats elsewhere (Araujo et al., 2000; Hastie et al., 2000). Melchior et al. (2021a) reported a mean fecundity in E. aucklandica of 17,840 glochidia (range 1,737 to 34,570) compared to nearly double that exhibited by coexisting E. menziesii (mean 44,016, range 28,840 to 72,000). Here, through its specialised “brood luring” mesoconglutinates, E. aucklandica may face a trade-off in increased energy costs for reduced fecundity. Conversely, E. menziesii, as a host generalist, uses a more energy-efficient reproductive strategy, which may allow for greater reproductive output.

The Australian Hyriinae are almost exclusively associated with lowland sections of coastal rivers of Victoria, New South Wales, and southern Queensland (Walker et al., 2014) that arise steeply in the escarpment of the Great Dividing Range (Rustomji et al., 2009). By Australian standards, this region is relatively high in species diversity with as many as six species of freshwater mussel occurring within a river system. The rivers of southeastern, coastal Australia are perennial, with good water quality, relatively high in dissolved oxygen and water clarity (Jones and Byrne, 2014; Walker et al., 2014). Echyridella aucklandica, which produces mesoconglutinates, is almost exclusively a lotic habitat species, occurring primarily in relatively clear northern New Zealand coastal streams (Marshall et al., 2014; Melchior et al., 2021a). In contrast, velesunionine species of Australia and E. menziesii of New Zealand are widely distributed in lakes and rivers throughout much of each country and are typically resident in more languid and (periodically at least) turbid waters, many of which are characteristic of temporary and/or lentic waterbodies (Marshall et al., 2014; Walker et al., 2014). Studies on patterns of distribution and abundance of Australasian freshwater mussels are limited, but generally, predation pressures and food limitation are thought not to limit freshwater mussel distribution (Haag and Warren, 1998; Raikow and Hamilton, 2001; Hewitt et al., 2021). The available, albeit limited, data show Australian freshwater mussels to be host generalists, coinciding with studies pertaining to species that release glochidia freely or contained in amorphous mucous conglutinates; there is little evidence amongst these species that the distribution patterns of freshwater mussels, within drainages, are limited by host fish behaviour and movements (Walker, 1981; Humphrey and Simpson, 1985; Klunzinger et al., 2012; Jones, 2014). Rather, spatial patterns within rivers appear to be controlled by abiotic factors (Humphrey and Simpson, 1985; Brainwood et al., 2006, Brainwood et al., 2008a, Brainwood et al., 2008b; Jones, 2006, Jones, 2014; Jones and Byrne, 2010, Jones and Byrne, 2014; Klunzinger et al., 2015), but contemporary distributions have been fragmented by habitat loss (Jones and Byrne, 2010, Jones and Byrne, 2014; Klunzinger et al., 2015; Sheldon et al., 2020) and declines in fish populations in many waterbodies may be inhibiting recruitment of young freshwater mussels (Byrne, 1998; Walker, 2017). Haag and Warren (1998), however, found no evidence of partitioning amongst unionids in North American streams because of limited space, but highlighted the importance of the host-fish and glochidial release relationship, noting host-specificity for species that utilise lure mechanisms to attract host species. It is worth noting that the concept of host-specificity amongst unionid mussels using such glochidial prey-mimetic lures rarely applies to a single fish species, but rather to a very limited number of fish species (e.g., Hewitt et al., 2021). Hewitt et al. (2019) noted as well that many glochidial–host interactions still remain to be identified, making it difficult in some cases to assign particular freshwater mussel species as either host specialists or host generalists. In locations where Australian freshwater mussel diversity is relatively high, whether seasonality in glochidial release and host specificity may have evolved to partition host fish resources is debatable, particularly given the currently limited published data available to pursue this hypothesis. Nevertheless, in high clarity waters where most Australasian Hyriinae occur, mesoconglutinates may be a more efficient mechanism for infesting host fishes than the passive infestation strategy typical of velesunionine species that tend to occur in more turbid habitats (for which visual attractants would serve limited purpose). Only more complete data on field-infested fishes to identify hosts for species that release glochidia in mesoconglutinates may elucidate the underlying evolutionary advantage of this strategy amongst the Hyriinae.

4.2 Glochidial shell morphology

In agreement with Jones et al. (1986), glochidia from Queensland populations of C. novaehollandiae, H. australis and H. drapeta have bifurcated hooks, and similar shell size and shape. Hyridella glenelgensis and H. narracanensis also have hook bifurcation, although the separation between cusps is set wider apart than other species studied to date, apart from H. australis. Hooks are, however, much straighter, and perpendicular to opposing valves than H. australis that are more laterally splayed. Bifurcated hooks in glochidia of H. depressa were illustrated in each of Jones et al. (1986) and Jupiter and Byrne (1997) (see also Supplementary Figure S4).

Atkins (1979) illustrated H. sp. ‘Diamond Creek’ glochidia as having hooks similar in form to several members of the Velesunioninae, including A. jacksoni and V. ambiguus (Walker, 1981; Klunzinger, 2020), L. froggatti and A. profuga (this study), V. angasi (Humphrey and Simpson, 1985 and this study), and A. pertexta pertexta (Klunzinger, 2020), which typically have s-shaped hooks with singular pointed cusps on opposing valves. We questioned whether the species Atkins (1979) illustrated may have been V. ambiguus given this similarity and because research by Jones et al. (1986) revealed hooks that are bifurcated in Hyridella species, very different in form to velesunionine glochidia. Furthermore, the dimensions of this species’ glochidia are distinct from northern populations of H. drapeta. To investigate, specimens of gravid adults were collected from the same location as in Atkins (1979); however, whilst the adults were similar in form to other H. drapeta, unpublished genetic evidence has indicated that the taxon is not H. drapeta and is an undescribed species. The present study confirmed that this taxon does indeed have s-shaped hooks, in support of Atkins (1979); however, upon closer examination of hooks from SEM photography, the cusps were revealed to be tripartite rather than singular as illustrated by Atkins (1979), and thus different to the velesunionine glochidia, thereby supporting their position in the Hyridellini as opposed to Velesunioninae as originally implicated by the illustrations of Atkins (1979). Similarly, hooks of E. menziesii superficially resemble those of Velesunioninae, but the hooks are distinctively spinose with wide supporting buttresses and may also be mildly tripartite. Westralunio carteri has atypical and complex hooks in comparison to other Velesunioninae (Klunzinger et al., 2013 and this study). Westralunio albertisi, however, has glochidia that are morphologically similar to other Velesunioninae and although Klunzinger (2023a) described them as being divergent, there is the possibility that the specimens examined may have not been fully mature and hooks had not yet fully developed.

Glochidia from C. novaehollandiae, H. australis and E. aucklandica were exceptional in their smaller size compared to those of the other species included in this study. Cucumerunio novaehollandae has perhaps one of the smallest recorded glochidia globally, rivalled only by a few margaritiferid species, Margaritifera dahurica (Middendorff, 1850), Margaritifera falcata (Gould, 1851), M. margaritifera and Cumberlandia monodonta (Say, 1829) (see Harms, 1909; Howard, 1915; Murphy, 1942; Bauer, 1994; Nezlin et al., 1994; Pekkarinen and Valovirta, 1996; Baird, 2000; Ieshko et al., 2014; Vikhrev et al., 2019), all of which are similarly miniscule in shell length (<60 μm). It has been proposed that such small glochidia (<65 μm in size) may be an adaptation to enhance suspension in the water column (Barnhart et al., 2008). At the other extreme, glochidia of E. menziesii, W. carteri and H. sp. ‘Diamond Creek’ are the largest of the Australasian hyriids measured to date with mean shell lengths between 300 and 330 μm. While they are certainly not the largest in the world, they are comparable in size to several unionids including Prolasmidonta heterodon (Lea, 1859) (= Alasmidonta heterdon), Pressodonta viridis (Rafinesque, 1820) (= Alasmidonta viridis), Utterbackiana suborbiculata (Say, 1831) (= Anodonta suborbiculata), Anodonta cygnea (Linnaeus, 1758) and Utterbackia imbecillis (Say, 1829) (see Surber, 1912; Claes, 1987; Niemeyer, 1992 in Wächtler et al., 2001; Hoggarth, 1999; Kennedy and Haag, 2005). Among Hyriidae, few glochidia exceed shell lengths of more than 300 μm, although the South American hyriids Diplodon charruanus (d’Orbigny, 1835) (= Diplodon trivialis), Diplodon martensi (Ihering, 1893) (= Diplodon decipiens + Diplodon suppositus), Diplodon delodontus (Lamarck, 1819), Diplodon multistriatus (Lea, 1831) (= Diplodon expansus), Diplodon garbei (Ihering, 1910), Diplodon uruguayensis (Lea, 1859) (= Diplodon hasemani), Diplodon iheringi (Simpson, 1914), Diplodon obsolescens (Baker, 1913), Diplodon paulistus (Ihering, 1893) (= D. paulista), Diplodon suavidicus (Lea, 1859), Diplodon rhuacoicus (d’Orbigny, 1835) (= Diplodon trivialis + Diplodon yaguaronis) and Triplodon corrugatus (Lamarck, 1819) reach lengths of 300–320 μm (Bonetto, 1951; Bonetto, 1959; Bonetto, 1961; Bonetto and Ezcurra, 1963; Parodiz and Bonetto, 1963; Alvarenga and Ricci, 1977; Bonetto et al., 1986; Mansur, 1999; Mansur and Campos-Velho, 1990; Ricci et al., 1990; Semenas et al., 1994; Mansur and Silva, 1999; Viozzi and Brugni, 2001; Beasley et al., 2005; Pimpão et al., 2012), making the glochidia of H. sp. ‘Diamond Creek’ perhaps the largest among the Hyriidae.

Small glochidia that either lack hooks or have short hooks are typically gill parasites (Hoggarth and Gaunt, 1988; Araujo and Ramos, 1998; Bauer, 2001; Barnhart et al., 2008; Haag, 2012). The position of the adductor muscle in such glochidia results in long resistance arms, adapted for a large area of sweep that aids in attachment to host gill tissue (Hoggarth and Gaunt, 1988). In comparison, larger glochidia with longer hooks tend to parasitize the fins or epidermis of their hosts and are adapted for stronger gripping strength with a hook (or “larval tooth”), a large adductor muscle and depressed shell (Hoggarth and Gaunt, 1988; Bauer, 2001; Barnhart et al., 2008; Haag, 2012). Small glochidia that parasitise gills of their host fishes have also been shown to metamorphose to their juvenile form and grow considerably in size while still on the host (Araujo and Ramos, 1998; Bauer, 2001), whereas larger, hooked glochidia that typically parasitise fins and epithelia tend not to grow while on their host (Bauer, 2001). This is corroborated in Australasian studies of glochidial parasitism. The small, short-hooked glochidia of C. novaehollandiae and E. aucklandica parasitise gills of their hosts, grow while on the fish and are attached to their host for a considerable period (Jones, 2014; Melchior et al., 2021b). Indeed, Melchior et al. (2021b) showed that E. aucklandica larvae increased in size from 99.5 ± 4.7 µm SD to 449.2 ± 28.2 µm SD during metamorphosis while encysted on New Zealand Common Smelt R. retropinna, a quadrupling in size during the parasitic mussel stage. Similarly, C. novaehollandiae undergoes a considerable increase in size while attached to host fishes (Jones, 2014). In contrast, glochidia with larger shells that are equipped with larger hooks, e.g., A. profuga, A. jacksoni, E. menziesii, H. drapeta, V. angasi, V. ambiguus and W. carteri, do not appear to grow much on the host, if at all, and may be largely phoretic (Walker, 1981; Humphrey and Simpson, 1985; Widarto, 1993; Klunzinger et al., 2012; Jones, 2014; Melchior et al., 2021b; Melchior, 2021).

Most of the glochidia from species in this study are typical of those from other Hyriidae (i.e., South American Hyrrinae), in having shells with a subtriangular outline. Hyridella glenelgensis, H. narracanensis and to a lesser extent, C. novaehollandiae, are atypically round and more ‘horseshoe’ or nearly D-shaped. Cucumerunio novaehollandiae bears some resemblance in outline to South American glochidia of C. ambigua (Pimpão et al., 2012), albeit with much smaller glochidial shells. Although glochidia of C. novaehollandiae appear more rounded than most other hyriid glochidia, with a non-protruding ventral apex, their shells still come to a narrower point along the ventral edge than the wider hinge line, unlike D-shaped or horseshoe shaped glochidia such as North American Lampsilis or Quadrula species (Surber, 1912), for example, that have a much broader ventral edge, wider than their hinge line, giving a characteristic D-shape or horseshoe shape.

The soft anatomy of Australasian hyriid glochidia has not been examined in detail, but Jupiter and Byrne (1997), Percival (1931), and Parodiz and Bonetto (1963) have hinted at anatomical variation among species. The preservation techniques used in this study focused on glochidial shell examination for detailed SEM photography of shell structures. However, some preserved specimens show sensory hair arrangements and other soft anatomy in H. sp. ‘Diamond Creek’ and H. australis (see Supplementary Material), while a live image of V. angasi collected at the time of glochidial release shows sensory hair arrangements like those illustrated by Parodiz and Bonetto (1963). It would appear from the few images or illustrations available that V. ambiguus and V. angasi have sensory hairs located toward the dorsal portion of the shell, more basally to the adductor muscle, whereas H. australis and H. depressa have series of sensory hairs in several locations from just behind the larval hooks as well as medially and basally to the adductor muscle. The arrangement of sensory hairs may be a function of different attachment mechanism in gill versus fin parasitism (Hoggarth and Gaunt, 1988; Nivischenko et al., 2022).

4.3 Values and limitations of glochidial diversity in phylogenetic relationships

Although glochidial morphology and metrics of shell characters have some value as a tool to help identify some taxa (e.g., Kennedy and Haag, 2005; Pimpão et al., 2012), and indeed have been used for taxonomic re-arrangements in some instances (e.g., Pimpão et al., 2012; Pfeiffer and Graf, 2015; Cruz and Quesada, 2017; Lopes-Lima et al., 2018; Miyahira et al., 2019; Chernyshev et al., 2020), they are not always sufficiently unique within species or among taxonomic groups, as this study has demonstrated. Yet, this study also showed that for most taxa examined, certain characteristics were common at the subfamily and tribal level. For instance, larval hook bifurcation is a trait that appears to be restricted exclusively to the Hyridellini (C. novaehollandiae, H. australis, H. depressa, H. drapeta, H. glenelgensis and H. narracanensis). This is not yet fully resolved, however, given that glochidia of Hyridella guppyi (Smith, 1885), Hyridella misoolensis (Schepman, 1897) and Virgus beccarianus (Tapparone Canefri, 1883) have not yet been examined. Additionally, if H. sp. ‘Diamond Creek’ proves to be a member of the Hyridellini, it would be the only exception to this characteristic given its very different hook to other Hyridellini.

Glochidia of the vast majority Velesunioninae (A. jacksoni, A. pertexta pertexta, L. froggatti, V. ambiguus, V. angasi, W. albertisi and W. carteri) have a larval filament and subtriangular scalene shells of a relatively similar size, although A. profuga is the exception in being smaller and lacking a larval filament. In terms of hook morphology, most velesunionines have long, sigmoidal singularly pointed, fluted hooks whereas W. carteri has a complex hook structure. The glochidia of W. carteri are also much more scalene in shape and larger than the other glochidia within the subfamily. Again, however, glochidial characteristics are not yet fully resolved for the subfamily given that glochidia of additional taxa within the Velesunioninae remain to be examined (see note in provisional glochidia key below).

As for the New Zealand Echyridella, glochidia of the two species included in this study exhibit wide differences in several characters including size, shape, hook length, presence or absence of shell sculpturing, and the presence or absence of a larval filament. Both, however, have spinose hooks with wide buttressed supports. The glochidia of the third New Zealand hyriid, Echyridella onekakaFenwick and Marshall, 2006, remains unknown. In a practical sense, identifying glochidia on host fishes could be problematic for L. froggatti and Velesunio species, A. jacksoni and V. ambiguus, and A. pertexta and V. ambiguus groupings, that may be sympatric in distribution and may produce glochidia around the same time of year (Walker, 1981; Humphrey and Simpson, 1985; Jones et al., 1986; Klunzinger, 2020). However, where LDA failed to accurately predict some species on glochidial shell metrics, in most cases this would be a moot point. For instance, where W. carteri was mistaken for E. menziesii or L. froggatti for A. profuga and vice versa, this would be irrelevant given these species are found in widely separate geographical ranges. Where uncertainty is an issue, genetic barcoding of glochidia on host fishes has proven useful for resolving such uncertainty (Kneeland and Rhymer, 2007; Boyer et al., 2011; Zieritz et al., 2012, 2018). Thus, using glochidial characteristics in species identification must be treated with caution.

5 Conclusion

  • (1) Of the 29 extant species of Australasian Hyriidae, glochidia are now described from 17 species (58.6%), five of which (17.2%) are described in this study for the first time.

  • (2) In combination with other published studies covered in the discussion, this study has added to the diversity of glochidia and mechanisms of release among Australasian freshwater mussels and this will be beneficial in helping to understand host fish use, dispersal mechanisms and designing captive breeding technologies in future work.

  • (3) Through statistical comparative analyses, this study highlights the utility of glochidial morphological diversity as an important aspect of systematics that, when coupled with genetic analyses, is likely to aid in modernizing the taxonomy of the Australasian Hyriidae. However, as statistical analyses showed in this study, reliance on glochidial characters alone for freshwater mussel systematics is not recommended, even though it revealed similarities and differences among and between taxonomic groups. Examining yet unknown Australasian hyriid glochidia and integrating glochidial characters with adult and juvenile morphology and molecular phylogenetic techniques will be a logical next step for modernizing the taxonomy of the Australasian Hyriidae and indeed for the Unionoida as a whole.

  • (4) Different glochidial release mechanisms were found between the Hyridellini and Velesunioninae. While this distinction appears to be related to different riverine typologies, the evolutionary significance remains to be fully explored among and between taxa.

Provisional key to the glochidia of Australasian Hyriidae

1. Glochidia small, length <100 μm; larval thread absent—2

- Glochidia large, length >100 μm, larval thread absent—4

2(1). Glochidial height/length ratio >105%; hooks unicuspid

…………………………………. .Echyridella aucklandica.

- Glochidial height/length ratio <105%; hooks bicuspid—3

3(2). Glochidial shape suborbicular; hooks reduced to a pair of spinose cusps set on a broad base (larval hook length <10 µm) ……………………………. .Cucumerunio novaehollandiae

- Glochidial shape subtriangular; hooks conjoined and arching (larval hook length >10 µm) ………………Hyridella australis

4(1). Glochidial shape suborbicular, larval hook reduced, length <20 μm; larval thread absent—5

- Glochidial shape subtriangular; larval hook length long, >20 μm; larval thread present or absent—6

5(4). Glochidial length <253 μm, height <230 µm and size <240 µm

…………………………………. ..Hyridella narracanensis

- Glochidial length >253 μm, height >230 µm and size >240 µm

……………………………………. ..Hyridella glenelgensis

6(4). Larval hook widely buttressed; larval thread present ………………………………………. ..Echyridella menziesii

- Hook not widely buttressed; larval thread present or absent—7

7(6). Glochidial length <300 μm; larval thread present—8

- Glochidial length <300 μm; larval thread present or absent—9

8(7). Hinge length >220 μm; larval hook length >60 µm and cusps tripartite Hyridella sp. ‘Diamond Creek’

- Hinge length <220 μm; larval hook length <60 µm …………………………………………. Westralunio carteri

9(7). Larval hook bicuspid; larval thread absent—10

- Larval hook unicuspid; larval thread present or absent—11

10(9). Larval hook length >58 µm …………Hyridella drapeta

- Larval hook length <58 µm …………………Hyridella depressa

11(9). Glochidial height/length ratio <86%; larval thread present or absent—12

- Glochidial height/length ratio >86%; larval thread present—13

12(11). Larval hook length >50 μm; larval thread present …………………………………………Velesunio ambiguus

- Larval hook length <50 μm; Larval thread absent ……………………………………………. Alathyria profuga

13(11). Larval hook length >60 µm—14

- Larval hook length <60 µm—16

14(13). Glochidial height <235 µm ………. .. Lortiella froggatti

- Glochidial height >235 µm—15

15(14). Larval hook length <60 µm ………Alathyria jacksoni

- Larval hook length >60 µm …………………………………. .. Alathyria pertexta pertexta

16(13). Larval hook length <52 μm; mean Á <15° …………………………………………….Velesunio angasi

- Larval hook length >52 μm; mean Á >15° …………………………………………. Westralunio albertisi

Note: the following taxa of Australasian Hyriidae are excluded from this identification guide because no information on their glochidia is currently available:

Hyriinae: Hyridellini

Hyridella misoolensis (Schepman, 1897).

Hyridella guppyi guppyi (Smith, 1885).

Hyridella guppyi aipianaMcMichael, 1956.

Hyridella sp. Jones et al., unpublished data (see Jones et al., 1986).

Hyridella sp. ‘Southwest Victoria’ Raadik et al., unpublished data

Velesunioninae

Velesunio wilsonii (Lea, 1859).

Velesunio sentaniensis (Haas, 1924).

Velesunio sp. B (see Baker et al., 2004).

Velesunio sp. D (see Baker et al., 2004).

Velesunio sp. ‘Magela Creek’ (see Kleinhenz et al., 2019).

Microdontia anodontaeformisTapparone Canefri, 1883.

Alathyria pertexta wardi (Iredale, 1943a).

Alathyria pertexta magnificaMcMichael and Hiscock, 1958.

Alathyria condolaIredale, 1943b.

Westralunio flyensis (Tapparone Canefri, 1883).

Westralunio inbisi inbisiKlunzinger, Whisson, Zieritz, Benson, Stewart & Kirkendale, 2022.

Westralunio inbisi meridiemusKlunzinger, Whisson, Zieritz, Benson, Stewart & Kirkendale, 2022.

Lortiella rugata (Sowerby, 1868).

Lortiella opertaneaPonder and Bayer, 2004.

Subfamily incertae sedis

Echyridella onekakaFenwick and Marhsall, 2006.

Statements

Data availability statement

The original contributions presented in the study are included in the article/Supplementary Material, further inquiries can be directed to the corresponding author.

Ethics statement

The manuscript presents research on animals that do not require ethical approval for their study.

Author contributions

MK: Conceptualization, Data curation, Formal Analysis, Investigation, Methodology, Project administration, Resources, Software, Supervision, Validation, Visualization, Writing–original draft, Writing–review and editing. HJ: Conceptualization, Data curation, Formal Analysis, Investigation, Methodology, Software, Visualization, Writing–original draft, Writing–review and editing, Validation. CH: Conceptualization, Data curation, Investigation, Methodology, Resources, Validation, Visualization, Writing–review and editing. MM: Conceptualization, Data curation, Investigation, Methodology, Resources, Validation, Visualization, Writing–review and editing. TR: Conceptualization, Data curation, Investigation, Methodology, Resources, Validation, Visualization, Writing–review and editing. ST: Investigation, Visualization, Writing–review and editing. LC: Investigation, Resources, Writing–review and editing, Visualization. FS: Conceptualization, Funding acquisition, Investigation, Methodology, Project administration, Resources, Supervision, Validation, Writing–review and editing.

Funding

The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This research was funded by Griffith University.

Acknowledgments

This study was presented at the joint meeting of the Australian Freshwater Sciences Society, the New Zealand Freshwater Sciences Society, and the Society for Freshwater Science held in Brisbane, Queensland, Australia 3–7 June 2023 (Klunzinger et al., 2023). The authors thank the reviewers and the editor whose comments and suggestions greatly improved the manuscript. We thank Erica Lovas, Candice Goodwin, Nicole Scheiber, Jennifer Brown and Ron Rasch of the University of Queensland Centre for Microscopy and Microanalysis and Lisa Kirkendale, Corey Whisson and Janelle Ritchie of the Western Australian Museum for technical support in the use and access to scanning electron microscope laboratories. We thank Timothy Fernando from Arthur Rylah Institute for Environmental Research, Department of Energy, Environment, and Climate Action (Heidelberg, Victoria) for generously providing images of recently released mesoconglutinates of Hyridella glenelgensis during a captive rearing trial in September 2023.

Conflict of interest

This study was conducted in a manner free from any activity that could be construed as a conflict of interest.

The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

The author(s) declared that they were an editorial board member of Frontiers, at the time of submission. This had no impact on the peer review process and the final decision.

Publisher’s note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

Supplementary material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fenvs.2023.1305077/full#supplementary-material

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Summary

Keywords

Unionoida, Hyriidae, conglutinate, glochidial release, reproduction, New Zealand, Australia, bivalve larvae

Citation

Klunzinger MW, Jones HA, Humphrey CL, Melchior M, Raadik TA, Treby S, Chandler L and Sheldon F (2023) Comparative diversity in glochidia of Australasian freshwater mussels. Front. Environ. Sci. 11:1305077. doi: 10.3389/fenvs.2023.1305077

Received

30 September 2023

Accepted

17 November 2023

Published

21 December 2023

Volume

11 - 2023

Edited by

Benjamin Cook, FRC Environmental, Australia

Reviewed by

Arthur Bogan, North Carolina Museum of Natural Sciences, United States

Ian Duggan, University of Waikato, New Zealand

Updates

Copyright

*Correspondence: Michael W. Klunzinger,

Disclaimer

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.

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