Like marine mussels, freshwater zebra and quagga mussels adhere via the byssus, a proteinaceous attachment apparatus. Attachment to various surfaces allows these invasive mussels to rapidly spread, however the adhesion mechanism is not fully understood. While marine mussel adhesion mechanics has been studied at the individual byssal-strand level, freshwater mussel adhesion has only been characterized through whole-mussel detachment, without direct interspecies comparisons on different substrates. Here, adhesive strength of individual quagga and zebra mussel byssal plaques were measured on smooth substrates with varying hydrophobicity—glass, PVC, and PDMS. With increased hydrophobicity of substrates, adhesive failures occurred more frequently, and mussel adhesion strength decreased. A new failure mode termed 'footprint failure' was identified, where failure appeared to be adhesive macroscopically, but a microscopic residue remained on the surface. Zebra mussels adhered stronger and more frequently on PDMS than quagga mussels. While their adhesion strengths were similar on PVC, there were differences in the failure mode and the plaque-substrate interface ultrastructure. Comparisons with previous marine mussel studies demonstrated that freshwater mussels adhere with comparable strength despite known differences in protein composition. An improved understanding of freshwater mussel adhesion mechanics may help explain spreading dynamics and will be important in developing effective antifouling surfaces.
The invasive freshwater mussel species Dreissena polymorpha (zebra mussel) and Dreissena rostriformis bugensis (quagga mussel) have rapidly spread across North America since their arrival in the 1980s1,2. An important factor in their rampant dispersal is their ability to attach to a wide variety of materials. This attachment is mediated by the byssus, a collection of proteinaceous threads each terminated by an adhesive plaque3,4. Upon their introduction to North America, the two dreissenid species initially displayed different distribution profiles, with zebra mussels settling nearshore and quagga mussels establishing in deeper areas5. Since then; however, quagga mussels have also settled in shallow waters, gradually displacing and zebra mussels and limiting their habitats to mouths of inflowing rivers6, where zebra mussels’ ability to anchor stronger and faster in flow provides an advantage7. Since marinas are typically located in mouths of rivers, zebra mussels are able to hitchhike frequently on watercrafts, allowing them to spread faster than quagga mussels6. Anchoring better in flow (on acrylic plates) has been attributed to faster byssal production rates and stronger attachment by zebra mussels7, but whether this holds true across substrates with different properties remains to be seen; the ability to attach to different substrates could have important implications on the spread of these fouling organisms.
Material properties such as surface roughness and surface energy are known to influence mussel adhesion frequency and attachment strength3,4,8,9,10,11. However, studies that directly compare zebra and quagga mussel attachment on different substrates are limited. Previous studies have independently shown that freshwater mussel attachment strength is greatest on natural materials such as wood and stone, on PVC, and on rough, high energy surfaces3,10,11. Ackerman et al. investigated the attachment strength of quagga and zebra mussels on various substrates, but the results are not directly comparable between the two species12, as different detachment methods were utilized in each study3,12,13. Although Kobak investigated zebra mussel adhesion on different surfaces, the material properties of the substrates (e.g. surface roughness, surface energy) were not characterized4. Balogh et al. recently ascertained that zebra mussels only attach stronger than quagga mussels while they are younger, but the analysis was limited to polypropylene14. Indirect comparison studies looked at the differences in byssogenesis (Grutters et al.15) and behaviour (Naddafi and Rudstam16), but under various induced conditions such as temperature, salinity, brightness, and the presence of predators15,16. Direct, side-by-side interspecies comparison across different substrates would allow a better understanding of freshwater mussel spread and population dynamics, along with the development of an effective antifouling surface against freshwater mussels.
While whole mussel detachment tests provide the best measure of the force required to remove the animal from a substrate, it is not possible to directly determine the strength of the plaque-substrate interface from these tests. Whole mussel detachment force depends on a variety of factors, including numbers of plaques, orientation of the thread, and failure modes17,18. In order to evaluate differences in the plaque-substrate adhesive interface between zebra and quagga mussel adhesion, single-plaque tensile detachment studies are necessary, as have been performed for marine mussels8,19,20,21. To our knowledge, single-plaque detachment tests have not been previously conducted for freshwater mussels.
The plaque-substrate contact region is critical for byssal adhesion. High-resolution structural characterization of the zebra mussel adhesion interface on epoxy revealed a continuous 10–20 nm thick electron-dense adhesive layer, which partially remained on the substrate after plaque detachment22. The ultrastructure of the plaque-substrate adhesion interface may vary by substrate and species, affecting the attachment strength as a consequence, but this has not yet been investigated. In this work, we measured the adhesive strength of individual quagga and zebra mussel byssal plaques on smooth substrates with varying hydrophobicity, namely glass, PVC, and PDMS, in order to understand the contributions of the plaque-substrate interface directly to adhesion. The failure mode was analyzed for the first time at the microscopic level, and the ultrastructure plaque-substrate interface on PVC was examined by TEM.
Materials and methods
Borosilicate glass and polyvinyl chloride (PVC) were purchased from Fisher Scientific (Ottawa, Ontario, Canada). Polydimethylsiloxane (PDMS) was prepared using the Dow Corning Sylgard® 184 elastomer kit (Midland, Michigan, USA). The hydrosilylation-curable PDMS base and the crosslinking agent were mixed in a 10:1 ratio for 5 min then vacuum degassed at room temperature, and then cured overnight at 70 °C.
The water contact angle of each substrate was measured in triplicate by taking an image with a Dino-Lite Digital Microscope Pro (Torrance, CA USA) and then using the Low-Bond Axisymmetric Drop Shape Analysis (LBADSA) National Institutes of Health ImageJ plug-in23. To measure the surface roughness, the substrates were observed under a Bruker Contour GT-K 3D Optical Microscope (Billerica, MA USA). The resulting profile was then analyzed using the Bruker Vision64 Map software.
Mussel attachment assay
Zebra mussels 13 to 25 mm in lateral shell length were collected from Round Lake, Ontario, Canada. Quagga mussels were collected from Elwin Island, Ontario, Canada, ranging in size from 13 to 25 mm. These quagga mussels all had the profundal phenotype24,25. The mean and standard deviation in lateral shell length of mussels used was 19 ± 3 mm (n = 113) for quagga mussels and 18 ± 3 mm (n = 47) for zebra mussels. Both mussels were obtained in May, and were used to collect data within 2 months. Mussel species were kept separated in 9 L tanks with a constant flow of 20 °C UV-sterilized aerated artificial freshwater26. A water pH above 7.4 and ammonia levels below 1 mg/L were maintained. Mussels were collectively fed 1 tablespoon of dried green Chlorella27 dispersed in artificial freshwater three times a week and experienced daily cycles of illumination, with ambient lighting during standard working hours and low-light conditions in the evenings.
Mussels were individually placed on individual, rectangular substrates (glass, PVC, or PDMS) and caged with stainless-steel mesh28. They were then placed on the bottom of the tank (12 per tank) in a random order and left undisturbed for 3–4 days to provide adequate time for attachment11. Up to four tanks were used simultaneously, and mussels were rotated through the different tanks. The attached mussels were cut away using a pair of fine scissors, leaving the substrates with the adhered plaques and the corresponding threads. The substrates were lightly patted dry and observed under a stereomicroscope. Patting the substrates dry did not damage the byssal strands. The frequency of attachment and the total number of byssal thread-plaques were recorded. Dead or unhealthy mussels were excluded from the count and further analysis.
The strength of the plaque-substrate interfacial adhesion was measured through single-plaque tensile detachment testing19,20. Under the stereomicroscope, individual byssal strands (one per mussel) were gently maneuvered to orient them normal to the substrate surface. The sample was then loaded into a custom-built apparatus equipped with an Omega DFG55-5 force gauge (Laval, QC Canada). The byssal strand was clamped to the apparatus as closely to the plaque as possible. A small drop of water was placed on the byssal plaque to maintain hydration. The plaque was then displaced vertically at a rate of 2 mm/s until detachment. A Celestron Handheld Digital Microscope Pro (Torrance, CA USA) was used to record the detachment tests. A sample video of plaque detachment is provided in Supplementary Information (Movie S1). The plaque area was subsequently measured using the Lumenera Analyze image analysis software (Ottawa, ON Canada). The resulting data was plotted as a force–displacement curve, and the adhesive strength and the adhesion energy were determined from it: the strength was calculated as the quotient of the force at failure and the plaque area, and the area under the force–displacement curve divided by plaque area gave adhesion energy. Following each tensile detachment test, the surface of the substrate was observed under the microscope and the video recording of the test was reviewed to determine the mode of failure. Samples from each failure mode and substrate were imaged using scanning electron microscopy (SEM). Failed byssal strands were air dried and fixed to SEM stubs with carbon tape. They were then carbon coated and imaged using a Hitachi SU3500 SEM at 3 kV accelerating voltage.
The plaque-substrate interface on PVC was examined via transmission electron microscopy (TEM). The attached plaques were first fixed in freshly prepared 2% glutaraldehyde for 1 h at room temperature and at 4 °C overnight. They were then post-fixed with 0.1% osmium tetroxide for 2 h, and en bloc stained with 2% aq. uranyl acetate for 2 h, followed by dehydration in an acetone gradient. Dehydrated samples were infiltrated with a graded series of EMbed 812 resin (Electron Microscopy Sciences, Hatfield, PA, USA), and then cured overnight at 60 °C. Sections 60–100 nm thick were cut along the sagittal plane using a Leica EM UC6-NT ultramicrotome, placed onto 100 mesh bare copper grids, and post-stained with 2% aq. uranyl acetate for 15 min and Reynold’s lead citrate for 5 min. All sections were imaged with a Talos L120C transmission electron microscope operating at 120 kV. Micrographs were taken with a 4 K × 4 K CETA CMOS camera.
Statistical analysis was adapted and modified from Kimmins et al.29. As described in Kimmins et al.29, statistical comparisons between the different substrates and mussels were made via analysis of variance (ANOVA) followed by Tukey’s HSD post-hoc analysis in JASP 0.14.1 for data sets satisfying the assumptions of ANOVA. Each type of substrate was grouped with the mussel species. For data sets without equal variance, Brown-Forsythe and Welch corrections were made, and Games-Howell post-hoc test was performed instead. Levene’s test was used to check for homogeneity of variances. Freeman-Halton extension of the Fisher’s exact test and chi-squared test were conducted to determine significance between the different attachment frequencies. Significance is noted as * for comparisons with p ≤ 0.05, ** for p ≤ 0.01, and *** for p ≤ 0.001. Standard deviation (SD) is presented as ± in text. Error bars in figures also represent SD. Statistical comparisons are summarized in Table S1.
Results and discussion
To compare the wettability of the substrate used for mussel attachment, the water contact angle of each substrate type was measured. Glass, PVC, and PDMS were chosen to represent a wide range of hydrophobicity. These substrates were also selected based on practical considerations: borosilicate glass contains a high amount of silica (a main component of hard substrates in natura such as rocks), PVC is a common piping material, and PDMS typically has a low adhesion strength and is often used in antifouling applications29. The water contact angles measured were 11.4 ± 3.8° on glass, 75.2 ± 2.4° on PVC, and 105.1 ± 0.9° on PDMS, indicating that the wettability of these substrates ranged from hydrophilic (glass) to hydrophobic (PDMS) as expected. The average surface roughness (Ra) was determined by optical profilometry. The Ra values were 1.79 ± 0.49 nm, 49.45 ± 4.24 nm, and 23.30 ± 9.11 nm on glass, PVC, and PDMS, respectively, demonstrating that while slight differences exist, the surfaces are all relatively smooth, and thus mechanical interlock is not expected to play a large role in adhesion.
To investigate whether there are differences in adhesion between the two freshwater mussel species, zebra and quagga mussels collected in the wild were placed on glass, PVC, and PDMS substrates in lab aquaria and allowed to reattach. Quagga mussels showed a significantly lower attachment rate on PDMS compared to glass and PVC, while zebra mussels showed a consistent attachment rate across all three substrate types (Fig. 1). The plaque area of individual plaques showed no statistically significant differences across species and substrates (Fig. 2). The present study reveals a significant difference in the rate of attachment of quagga mussels to PDMS compared to zebra mussels. This indicates that factors such as hydrophobicity and substrate stiffness may elicit a different response for zebra and quagga mussels, respectively. Although our approach is limited by the fact that fully developed mussels were placed on the substrate rather than veliger mussels, and that the quagga mussel population utilized may not represent all possible morphotypes24,25,30, this nonetheless suggests that zebra mussels display a more universal adhesion than quagga mussels. Previously, it has been reported that zebra mussels adhered more on hard substrates and quagga mussels on soft substrates as observed in natura, but our results suggest this may only be the case in soft and hard substrates that naturally exist in nature, such as silts, clays, and stones31. In fact, a recent study on the efficacy of antifouling coatings showed that zebra mussels adhered more on soft substrates than quagga mussels32, consistent with our study.
To compare the adhesion of zebra and quagga mussels, pull-off testing of individual plaques was performed on the different substrates and the adhesion failure mode was analysed. Adhesive failure encompasses a complete detachment of the plaque from the substrate while cohesive failure entails a failure in the structural elements of the byssus (i.e. root, stem, thread, thread-plaque junction, or within the plaque). Upon inspection of the substrate surface by optical microscopy after what appeared to be adhesive failures, in some instances the substrate surface appeared clean (Fig. 3A), while in others a residue imprint of the plaque was observed (Fig. 3B), indicating that the plaque had not completely detached at the microscopic level. When the underside of detached plaques that left a residue were imaged via SEM, distinct smooth and rough regions—mirroring the residue leftover on the surface—were clearly visible (Figs. 3C, S1). Because the adhesive residue is known as a footprint33, we named this newly identified failure mode as ‘footprint failure’. The occurrence of footprint failure instead of adhesive failure indicates an incomplete detachment, demonstrating a stronger adhesion at the plaque-substrate interface. The notion of an adhesion failure in the footprint is further supported by previous TEM studies of zebra mussel plaques on epoxy, wherein parts of the footprint layer were visibly torn after detachment22.
On glass, quagga mussel plaques failed primarily via mixed failure (part adhesive, part footprint), whereas cohesive failure was predominant in zebra mussel plaques, along with mixed failure (Fig. 4). Quagga mussel plaques on PVC failed exclusively through adhesive failure, identified by the absence of footprint in the area where the plaque was in contact with the substrate (Fig. 3A) and a predominantly smooth plaque underside in SEM (not shown). On the other hand, zebra mussel plaques on PVC failed via cohesive and mixed failures, much like on glass (Fig. 3B,C), indicating a stronger plaque-substrate interaction. Zebra mussel plaques on PDMS showed an increase in the frequency of adhesive failures, suggesting a weaker adhesive interaction at the plaque-substrate interface compared to PVC. Quagga mussel plaques on PDMS demonstrated adhesive failures, but we were not able to quantify adhesion strength as the force was below the limit of detection for our apparatus. As such, they are not included in the adhesion strength analysis (Fig. 5). A complete set of representative substrate images after detachment can be found in Fig. S2.
Quantification of zebra and quagga mussel adhesive strengths via tensile testing was determined only from plaques that failed via adhesive failure, as this provides the best measure of plaque-substrate interaction. On the other hand, attachment strength encompasses all failure modes, providing a measure of the overall adhesive strength of an individual byssal thread/plaque; this is more representative of mussel adhesion in natura. Both zebra and quagga mussels displayed a decrease in adhesion strength (Fig. 5) with increased substrate hydrophobicity. Interspecies comparison revealed that quagga mussels adhered significantly stronger than zebra mussels on glass, but significant differences were not observed on PVC between the two species, despite the observed difference in failure modes (Fig. 4). Zebra mussels on PDMS displayed a much stronger adhesion strength than quagga mussels on PDMS, which attached too weakly to measure (less than 1 kPa). The attachment strength (Fig. S3) was similar to the adhesion strength but had a wider spread, as it took every mode of failure into account. The adhesion energy data provided further insight, revealing significant differences between quagga mussels on PVC and zebra mussels on glass and PVC, and between zebra mussels on PDMS and zebra mussels on glass and PVC (Fig. 6). Because adhesion strength only captures the maximum force required for a plaque-substrate detachment, adhesion energy is a better measure of the total interaction with the substrate and is consistent with the difference observed in failure mode. The wide distribution of adhesion energy for quagga mussels on glass is attributed to the differences in failure dynamics; the adhesion energy of an individual plaque can be strongly affected by the insertion angle of the thread to the plaque, which can affect the failure mechanism20.
Given the differences in adhesion of quagga mussels and zebra mussels to PVC (different failure modes and adhesion energy), we were interested in investigating whether there are any ultrastructural differences at the plaque-substrate interface in these two species. Cross-sections of the plaque-substrate interface on PVC were observed via TEM, and differences were clearly visible. Zebra mussel plaques formed an electron-dense interface at the substrate contact point, as has been observed on epoxy22, with granules present both in the bulk and at the interface (Fig. 7A). Quagga mussel plaques, on the other hand, had no granules in the bulk plaque, and those at the interface were more electron-dense, larger in size, and more spread out than those of zebra mussels (Fig. 7B). Granules migrating more to the surface and fusing reflects a stage of maturation, as we observed for zebra mussels on epoxy, previously34. This may indicate that quagga mussels may be forming the interface faster than zebra mussels (i.e., synthesis and transport of the adhesive precursors are complete in the quagga mussel plaque. However, we never observed such large granules at the interface for zebra mussels as are present for the quagga mussels on PVC. Although it is not yet clear how the different interfacial morphologies are related to adhesion strength, it is nevertheless notable that morphological differences do exist.
Together, these findings demonstrate that zebra mussels adhere better to PVC and PDMS than quagga mussels and indicate that adhesion at the plaque-substrate interface is dependent on the mussel species as well as the substrate properties. It is still not clear whether these differences are a result of different structure at the plaque-substrate interface and/or and protein composition. This warrants a complete investigation of the composition and spatial–temporal distribution of the adhesive proteins at the interface. Currently, efforts are underway to obtain protein-level differences between the composition of the bulk plaque and footprint via quantitative proteomic analysis, which will assist in further deciphering the morphological differences seen above and the mechanism of adhesion.
Whole marine mussel detachment forces are much higher than freshwater mussels (mytilids: 20–60 N, dreissenids: 1–2 N)35,36,37. The amino acid 3,4-dihydroxyphenylalanine (DOPA) is thought to be the key driver in marine mussel adhesion38. Seemingly in keeping with this, freshwater mussel byssi only contain trace amounts of DOPA (~ 0.6 mol% and ~ 0.1 mol% in zebra and quagga mussels, respectively)39 while mytilids contain 11–30 mol% DOPA in their adhesive foot proteins40,41,42,43, The single plaque adhesion tests performed here enable for the first time a comparison of plaque adhesion and attachment strength of freshwater mussels to literature values for marine mussels. Interestingly, D. polymorpha and D. bugensis plaque adhesion and attachment strengths were comparable to Mytilus edulis and Perna viridis across all substrates (Figs. 8 and S4)8,19. It should be noted that the pull angle in single-plaque tensile detachment tests can influence the failure mode and force, as plaques make different angles with the thread20,44. In all three studies compared, however, the pull angle consistent at 90°. Notwithstanding this issue, the comparable adhesion strengths of freshwater mussels to marine mussels despite a lower DOPA content may indicate that non-DOPA dependent mechanisms of adhesion play an important role in freshwater mussels, or that not as much DOPA is required in a freshwater environment. While other charged species have been revealed to play a role in marine mussel adhesion45,46,47,48 more information about the composition of freshwater adhesive proteins is required to make conclusions in this regard.
Zebra and quagga mussels show distinct adhesion characteristics from one another. Both zebra and quagga mussel adhesion strength decreased with increasing substrate hydrophobicity, along with an increased occurrence of adhesive failures. Quagga mussels displayed lower frequency of attachment and weaker attachment to PVC and PDMS than zebra mussels, suggesting that zebra mussels adhere better on hydrophobic substrates than quagga mussels. It was also shown that morphological differences exist between the zebra mussel and quagga mussel adhesion interface. Furthermore, zebra and quagga mussel plaques adhere with strengths comparable to marine mussels, despite having much lower DOPA content in their adhesive proteins. Further probing the differences in adhesion between freshwater and marine mussels will not only allow us to understand freshwater mussel adhesion and spread better, but ultimately to design a targeted antifouling solution against freshwater mussel biofouling.
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This work was supported by Discovery grant (#342455) to EDS from the National Sciences and Engineering Research Council (NSERC) of Canada (RGPIN-2019-06210). The authors gratefully acknowledge Michael McCartney (University of Minnesota) for helpful discussions, and Judith Ng, Kate Li, Derek Ratz, and Trevor Gilbert for collecting quagga and zebra mussels.
The authors declare no competing interests.
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James, B.D., Kimmins, K.M., Nguyen, MT. et al. Attachment of zebra and quagga mussel adhesive plaques to diverse substrates. Sci Rep 11, 23998 (2021). https://doi.org/10.1038/s41598-021-03227-6