Larvae of the caridean shrimp Hippolyte inermis persist in the plankton of the Mediterranean up to about one month. Since they need to reach appropriate coastal areas for their recruitment in seagrass meadows, we hypothesized that leaves of Posidonia oceanica or, alternatively, algae present in their epiphytic biofilms, might be physically recognised as target substrates and trigger larval metamorphosis and settlement. Chemical cues could improve the finding of suitable habitats for settlement. Thus, the effects of leaves of P. oceanica and biofilms of the diatom Cocconeis scutellum parva, seasonally abundant in the leaf epiphytic stratum, were investigated along with the effect of volatile organic compounds (VOCs) extracted from the epiphytic diatom. The physical induction with P. oceanica accelerated larval settlement, stimulating an earlier and faster metamorphosis of larvae. C. scutellum parva produced a weaker effect on settlement; however, diatom’s VOCs had evident influence and accelerated metamorphosis and settlement. We concluded that such chemical cues as the VOCs produced by epiphytic diatoms, reinforce the effect of physical cues for the identification of suitable settlement locations for this shrimp.
Moulting and settlement are key processes in aquatic environments, and the identification of suitable locations for recruitment strongly influences the fitness of invertebrates and the connectivity of their natural populations1,2. Settlement may be defined as either the attachment of a larval foot to the substrate (in case of sessile organisms) or the shift from a planktonic larval life to a benthic post-larva (in case of vagile organisms), preceded or followed by an irreversible developmental event of metamorphosis. Larval competency of natantia decapods, often preceding settlement, involves a noticeable resorption of plumose appendages and a significant elongation of eyestalks and walking legs, leading to the shape of a shrimp quite similar to adults of the same species3. The transition is associated with larval competency and metamorphosis of most decapods4. Since settling in an inadequate environment (higher probability of predation or scarce trophic resources) results in a failure of the reproductive event, invertebrate larvae evolved the ability to persist until suitable environmental conditions are reached5,6. The shrimp Hippolyte inermis Leach passes through a variable number of larval stages7. Each stage has a variable time of completion, according to the abundance and quality of food, temperature and other external stimuli. However, its larval development is completed consistently in about 40 days when fed on enriched Artemia salina nauplii and rotiferids, passing through 9 zoeal stages up to the last metamorphosis. The settlement percentage of cultured larvae, in our experimental conditions, varies from 65 to 95%8. Similarly, Octopus spp. paralarvae may last in a planktonic phase until appropriate environments are reached9, and various invertebrates developed the ability to recognize chemical1, biological10,11,12,13 or physical signals14,15 to identify appropriate substrates for settlement4 or the presence of adults of their own species16.
Habitat-specific environmental cues ensure successful larval recruitment for benthic invertebrates17. The presence of biofilms18 and in particular, specific metabolites released by bacteria and protozoans, are important settlement19 cues for larvae of sponges20 and an effect of chemical cues (e.g., humic acids, volatile infochemicals, ammonia and various ions, dissolved gases, organic compounds) on various invertebrate larvae4,13,21 was demonstrated. A nearly universal mechanism of settlement induction by bacterial cues has been proposed, able to strongly influence such different taxa of invertebrates as cnidarians17,22, bryozoans23, molluscs16, annelids24, echinoderms19,25, crustaceans26 and even ascidians27. A non-polar metabolite extracted from bacteria (Tetrabromopyrrole)28 is also responsible for partial or complete metamorphosis in coral planulae, which demonstrated a highly specific response to single infochemicals29. In addition, specific ions are recognised by larvae of the mussel Mytilus galloprovincialis to identify their target substrates30. Various coralline algae, as Hydrolithon reinboldii and Neogoniolithon fosliei, produce compounds that influence the settlement and further development of coral larvae1. The role of various algae-produced cues was also demonstrated for echinoderms31, corals1 and polychaetes32. Both physical and morphological cues influence the settlement of larvae, and the final choice depends on a multi-factorial strategy including surface topography5 and the availability of trophic resources, along with chemical signals4. Furthermore, chemical properties of substrates are important cues for habitat selection33,34. For these reasons, rather than investigating “if” a given species uses specific cues to improve the settlement process, we should strive to understand “which” cues influence the larval settlement, “how” they work and “why” they are employed, according to ecological and physiological needs of given invertebrates. However, a limited number of studies demonstrated the effects of physical and chemical cues on metamorphosis and settlement of marine crustacean decapods35, mainly on brachyuran crabs.
With this perspective we hypothesized that the shrimp Hippolyte inermis, strictly associated with the seagrass Posidonia oceanica in the Mediterranean sea36, might perceive and react to the presence of plant leaves. H. inermis is a stimulating subject of study, because of its close association with the leaves of the host seagrass and the trophic relationships with diatoms of the genus Cocconeis, influencing its ecology, physiology and sex reversal37. The leaf stratum of Posidonia oceanica represents its main habitat38 but shrimp larvae may be dispersed for a long time7 over wide areas, while their target P. oceanica meadows only cover narrow coastal areas7,39. However, competent larvae need to settle on seagrass leaves (normally distributed from 1 to 35 m depth)40 to survive, as they are delicate and strictly adapted to this environment41. Apart from plant leaf as physical cues, shrimp larvae could also perceive the presence of Cocconeis diatoms, typical epiphytes of P. oceanica. In fact, Cocconeis spp. are a key food item for H. inermis42 and the shrimp might improve its reproductive success if larvae could recognize its presence and select adequate locations for settlement, as it has been demonstrated for other decapod crustaceans. For example, substrate cues can shorten the instars and affect the subsequent nutritional condition in pueruli of the spiny lobster Jasus edwardsii43 and the Caribbean spiny lobster Palinurus elephas2. Accordingly, the main aims of this study were: (a) to test the effects of physical and chemical cues within the known time for post-larvae production8; (b) to test the effects of diatom films on the settlement of H. inermis and those of volatile organic compounds (VOCs) produced by C. scutellum parva8,44; and (c) to compare the proportion of larvae metamorphosing in presence of inducers and in controls, as suggested by Forward et al.3 for larvae of brachyuran crabs.
Material and Methods
Animal collection and maintenance
Ovigerous females of Hippolyte inermis were collected in fall 2017 in a Posidonia oceanica meadow off Lacco Ameno d’Ischia (Bay of Napoli, Italy. 40° 45′ 6″N; 13° 53′ 29″E) by trawling a plankton net over the leaves. Shrimp females were sorted on boat and transferred into plastic containers filled with clean water, until their transfer to the laboratory. Taxonomical identification was confirmed under the stereomicroscope. Shrimp females were individually reared in 2 L Erlenmeyer flasks containing 1.5 L of filtered and aerated seawater (at salinity 38.1 PSU), housed in a thermostatic chamber at 18 °C with a 12/12 day/night photoperiod. These conditions, routinely applied to our shrimp cultures, are close to those recorded in the field during the reproductive seasons. Seawater was filtered overnight by means of a canister filter (Eheim Classic 250 charged with synthetic foam and activated charcoal) and UV sterilized before use, to consistently provide a suitable rearing medium. Flasks were inspected daily for the presence of larvae and water was partially replaced with clean medium. Immediately after hatching, larvae were collected over a 60 µm mesh plastic filter, counted and individually transferred into 1 L flasks containing 800 mL of filtered seawater. Artemia salina nauplii (4 ind. mL−1) and Brachionus plicatilis (5 ind. mL−1) were added to the cultures as a food source. At the start of larval cultures, 80 larvae (pooled from several females) were stocked in each conical flask (1 ind/10 mL of seawater). Culture vessels were kept in the same thermostatic chamber at 18 °C, as specified above; the culture medium was renewed daily, and the number of larvae was recorded. Larvae were inspected daily under a stereomicroscope to follow the succession of zoeal stages45 up to the phases preceding the metamorphosis (zoeae VIII- IX), when plumose appendages were strongly reduced and the eyestalks started to be elongated. These characters, indicating the imminent reaching of a competent stage, occurred after 25–30 days46, according to temperature, season and feeding regimes. Larvae were transferred in glass plates after this stage, to start settlement experiments as further described.
Experimental design and protocol
Settlement experiments, aimed at checking the reaching of final metamorphosis and the transformation of larvae into post-larvae (based on they morphology)47, were performed according to three treatments represented by (a) Posidonia oceanica leaves, (b) biofilms of Cocconeis scutellum parva and (c) diatom’s volatile organic compounds (VOCs). Each treatment was made up of 5 replicate 500 mL glass plates (14 cm diameter) filled with 400 mL of filtered seawater (pH 8.1, salinity 38.1 ppm, absence of measurable pollutants). Each plate, covered with a plastic lid and gently aerated, was stocked with a pool of 25 larvae. Artemia salina nauplii (5 ind mL−1) were provided during the test period and until the last zoea was settled as a post-larva. In addition, 5 mg of composed feed (Spirulina, Enriched Artemia and Micro-Granules by SHG, Ovada, Italy) were added daily to the bottom of each plate. Plates were kept in the same thermostatic chamber described above (12/12 photoperiod; 18 °C). Larvae assigned to each replicate treatment and its paired control were obtained from the same flask. Therefore, 50 out of the 80 larvae stocked in each replicate conical flask, were used for bioassays (25 for a replicate test; 25 for a paired control) while the remaining larvae were discarded. While paired controls were run according to the above experimental specifications, treatments were conducted in plates containing also a putative settlement inducer, either P. oceanica leaves, fresh C. scutellum parva biofilms or VOCs extracted from the diatoms.
Leaf and diatom film treatments
Plates assigned to the treatment with seagrass leaves were provided with a 7 cm fragment of a Posidonia oceanica leaf. Only green parts were used, after rubbing leaves with cotton gauze to remove all epiphytes48. Leaves were replaced every 5 days to avoid leaching of decomposition products. The amount of leaf biomass used for this experiment simulates the presence of a P. oceanica meadow in the vicinity and it is aimed at testing the ability of larvae, to recognize its physical presence. Plates assigned to the treatment with diatom biofilms were pre-conditioned with an inoculum of Cocconeis scutellum parva (obtained from the strain collection of the Stazione Zoologica) 15 days prior to the beginning of the experiment. Diatoms were incubated in Guillard’s f/2 medium49 to obtain a continuous biofilm with an average density of 35,000 cells. mm−2, as commonly measured on P. oceanica leaves50 in spring. Additional plates were inoculated with diatoms at 5-day intervals and used to transfer shrimps during the bioassay. Culture medium was replaced with sterilized natural seawater prior to the start of bioassays. The amount of infochemicals possibly emitted by intact diatom biofilms is quite low under these conditions, since this diatom produces wound-activated infochemicals only when mechanically damaged44. Thus, only a small fraction of diatoms naturally decaying (evaluated as 3–5% of the total biomass per day, according to our previous investigations) will produce infochemicals in the culture vessels. Diatom biofilms may hence be considered as physical cues, because Cocconeis spp. dominate the epiphytic layer of P. oceanica leaves in spring, during larval settlement51.
Plates assigned to the treatment “VOC” were prepared as described for controls but small amounts of volatile compounds were added daily to check if diatom chemical cues may influence the metamorphosis and settlement rates. In particular, we tested an ecological scenario represented by a leaf area of 2 cm2 covered with diatom biofilms and grazed by a herbivore, dispersed in the surrounding environment. As previously demonstrated8, the wounding by animal consumers of diatoms present in such a small area produces volatile compounds readily recognized by adults of H. inermis. We hypothesized that VOCs could be recognized by larvae as a settlement cue even at this low concentration, that decreases according to the distance from leaves. For this purpose, VOCs were extracted twice from sonicated diatom suspensions (2 × 40 mL) obtained from four 14-cm Petri Dishes covered with C. scutellum parva cultures. VOCs were concentrated by closed-loop stripping52 performed at 22 °C for 45 min and extracted on a Tenax TA cartridge, after addition of 10 g NaCl53,54. The cartridge was removed and eluted with 6 mL diethyl ether. The ether was gradually evaporated using nitrogen gas (N2, grade 5.0) and the residue re-dissolved into 300 µL of pure ethanol. Controls were prepared according to the same procedure, but stripping was performed on a sterile culture medium. All VOC samples and controls were stored at −80 °C until the start of bioassays. Every day, 1 µL of diatom VOC solution (corresponding to the VOCs produced by 2 cm2 of grazed diatom film) was added in each test plate, after a total change of the culture water, and 1 µL of VOC control solution was added in each control plate. This low dose was administered taking into account that a cue in the field should have maximum effect even in trace amounts55.
Analysis of data
The abundance of larvae and post-larvae present in each plate was recorded daily for 15 days, to perform survival analyses by means of Kaplan-Meier estimates and detect influences of treatments on the temporal rates of settlement. Kaplan-Meier is a non-parametric method used to estimate the survival function from lifetime data. Mortality rates were recorded daily in each replicate and total mortality rates for each treatment were computed at the end of the experiment. One-way ANOVA was employed to test the significance of differences in mortality rates among treatments. Settlement curves were analysed as well by means of the Kaplan-Meier model56 and the significance of differences between treatments and their controls were tested by means of the Log-Rank (Mantel-Cox) technique using GraphPad Prism version 8.0.0, GraphPad Software (San Diego, California USA). In addition, since the abundance of newly metamorphosed juvenile shrimps may show daily fluctuations, the average number of post-larvae produced every 3 days in each plate was computed and compared in treatments and controls, to test the null hypothesis “No effect of the cue on the trends of production of postlarvae” using multiple t-tests, adapted for multiple comparisons using the Holm-Šídák method, with the assumption of homoscedasticity. Multiple t-tests were chosen in order to permit comparisons between couples of treatments vs. their paired controls, given the constraints of the experimental plan. The percentages of post-larvae produced at the end of the experimental time were computed as well and compared among treatments. Z-test on proportions was applied to check the significance of differences between the rates of post-larvae produced in induction treatments at each 3-day interval, and those produced in paired control plates. Finally, the average number of post-larvae produced after the half-time of the experiment, at the 9th day of test, was calculated and compared between test plates and controls, using Z-test on proportions, to evaluate the effects of physical cues and volatile infochemicals on the process of settlement and the speed of maturation up to metamorphosis.
Effects of physical and chemical cues
In total, 36 ovigerous females were collected and reared up to the production of larvae. Larvae of cultured shrimp completed their growth within 25–30 days, reaching the stage of Zoea IX. At this stage, the induction experiments started. All treatments exhibited low mortality rates (Fig. 1), ranging between 0.4% ± 0.9 (in VOC treatments and controls) and 2.6% ± 1.9 (in the Posidonia treatment) of the total number of individuals. Differences in mortality rates among treatments were not significant (ANOVA, p > 0.05; Table 1) although Posidonia treatment exhibited slightly higher mortality rates than other treatments. Within 15 days, all treatments and controls exhibited similar trends of settlement and metamorphosis (Fig. 2a–c) and the reduction in the number of larvae in each treatment followed a logarithmically decreasing pattern. According to the Kaplan-Meier model, settlement rates in the Posidonia treatment and its controls differed significantly (at p < 0.001; Log-Rank test, Table 2). In contrast, settlement rates in Cocconeis treatment and its controls were not significantly different. Settlement rates differed significantly between the VOC treatment and its controls (at p < 0.01; Table 2). Less than 50% of larvae were still in a planktonic phase after 5 days, in most replicates, while most individuals had metamorphosed into juvenile shrimps. Posidonia treatments differed from their controls (Fig. 2a), but a decrease of metamorphosis was consistently observed after the 12th day, as also recorded in the treatment Cocconeis (Fig. 2b). Variable rates of settlement and metamorphosis were observed according to treatments: 73.3% of larvae settled in Posidonia treatment, 95.1% in Cocconeis treatment and 98.6% in VOC treatment. In the VOC treatment the process was completed earlier than in other treatments (at the 10th day) and a different pattern of settlement was exhibited by VOC-treated larvae in respect to their controls (Fig. 2c).
Temporal patterns of larval settlement
The pools of post-larvae (PL) produced every three days (Fig. 3) in test plates were quite variable, ranging between 0.9 ± 0.35 and 11 ± 2.0 (Fig. 3a). Significant differences of PL production were detected among treatments (multiple t-tests; Table 3) but a gaussian pattern was consistently exhibited, with maximum values between the 6th and 12th day. In particular, the trends of PL production significantly differed between Posidonia and its control (Fig. 3a) and between VOC and its control (Fig. 3c), at most time-lags. In contrast, the differences between Cocconeis treatment and its controls were not significant (Fig. 3b) according to multiple t-tests (Table 3). Posidonia and VOC treatments showed different proportions of post-larvae produced in the first period of the experiment (z-test; p < 0.01), at the 3rd and 6th day, both producing a higher number of larvae metamorphosed as compared to the controls (Fig. 3a,c). After 6 days of treatment, the physical induction with Posidonia produced an increase of larval settlement and metamorphosis of 18.5% compared to the controls. The chemical induction with diatom VOCs triggered an increase of larval settlement and metamorphosis of 46.6% at the 6th day, with respect to controls. The number of post-larvae produced in controls increased at the end of the experimental period (15 d) both in Posidonia and VOC treatments, indicating a delay in the completion of settlement as compared to induction treatments. The physical induction with Cocconeis biofilms did not produce any difference with respect to controls (Fig. 3b; Table 3).
Speed of metamorphosis in presence of inducers
The percentage of post-larvae settled and metamorphosed in the first half of the experiment (9 days) was 63.25% in the Posidonia treatment and 51.31% in its controls (Fig. 4). Similarly, 89.28% of larvae metamorphosed in the treatment VOC within the 9th day of the experiment, as compared to 53.01% in its controls. In contrast, at the same time, 63.97% of larvae settled and metamorphosed in the Cocconeis treatment, compared to 67.41% in its controls (Fig. 4) which was not significantly different between treatment and control (p > 0.05). Overall, the production of post-larvae and settlement in induction tests and their controls significantly differed in VOC (p < 0.01) and Posidonia (p < 0.01) treatments but not in the test between Cocconeis and its controls.
A delayed metamorphosis of competent larvae, from a few days to several months, was demonstrated in various marine invertebrates in the absence of specific inducers57, associated with the recognition of adult habitats. The total time to complete the production of post-larvae was quite consistent among treatments, in accordance with previous observations3, indicating that in given conditions of culture the number of larval stages (from 5 to 9) and the persistence of each stage may be consistent, according to feed quality and temperature. The typical succession of zoeae was observed7, up to the production of competent larvae. Then metamorphosis and settlement continued according to a Gaussian trend during the next 15 days of the experiment. About 15% of post-larvae settled during the first and the last periods of test (the tails of a normal pattern), while most individuals metamorphosed between the 6th and 12th day of experiment, in all treatments. The exposure to P. oceanica leaves triggered a significant acceleration of this process. In fact, the treatments exposed to the presence of a green leaf yielded, on average, the settlement of 11.16% of post-larvae after 3 days of test, as compared to 3.84% of post-larvae settled in controls in the same period. An even higher difference was demonstrated at the time lag of 6 days (24.47 in Posidonia vs. 5.48 in controls). In the main period of competence (from the 6th to 12th day) the differences were less evident. This period also corresponds to the maximum rates of settlement, probably due to biological limitations for the species to delay metamorphosis before it becomes too costly9,53. Only in the last three days, at the completion of the process, the average number of post-larvae produced in controls was higher (18.48%) than the larvae produced in Posidonia treatments (8.04%). On the overall, the rates of individuals metamorphosed in the treatments containing Posidonia leaves were significantly higher than those exhibited by controls (80.43% vs. 64.41%). This trend is quite typical. It indicates that the presence of recognized cues triggers a shift to an earlier settlement and that, in the absence of inducers, larvae complete the development later, at the end of their period of competence21. Similar patterns were prompted by the addition of various ions (Li+, Cs+, RB+ and Ca2+) to the culture medium for the mussel Mytilus galloprovincialis. They produced a reduction (up to 25%) of the time for settlement, according to their concentrations30. This evidence stresses the importance of doses, since larvae may be sensible to various amounts of compounds having a direct or indirect effect in the settlement progression55. Thus, a different ratio of P. oceanica biomass vs. the volume of water could produce even stronger effects58. Similarly, various biofilms influence the settlement patterns and metamorphosis of M. galloprovincialis12, including diatoms, although the cue for molluscs was found to be mainly produced by the close association of algae and bacteria59.
The exposure of H. inermis to Cocconeis scutellum parva biofilms elicited less clear effects, as the rates of post-larvae production did not differ significantly in the presence of the diatom. However, volatile organic compounds released after wounding of C. scutellum parva cells had a marked effect on the metarmorphosis of H. inermis, which demonstrates that diatom VOCs may have an ecological function as infochemicals29. Nearly all known cases of chemical induction of larval settlement and metamorphosis involved substances adsorbed to the benthic substratum or sequestered in plants or bacteria encrusting substrates60,61,62. Decapod crustaceans have been often considered to dependent little on chemical cues for settlement and metamorphosis induction, probably because they retain their mobility after metamorphosis57 and waterborne compounds only rarely demonstrated to have an effect on these processes55. The choice to test this class of compounds was due to the demonstrated effect of diatom’s VOCs as infochemicals for adult shrimps8. Previous investigations demonstrated that plant VOCs were mainly recognized as warning signals, since they could indicate the presence of predators and they produce a negative chemotactic reaction in adults of H. inermis44. However, VOCs produced by the diatoms upon wounding triggered a different effect in shrimp larvae. This topic requires further attention, since infochemicals may change their “meaning” according to environmental contexts and life stages44. While in other invertebrates the larval receptors used to detect biofilms or bacterial cues are lost after metamorphosis13, in H. inermis the ability to recognize diatom VOCs is conserved in larvae and adults, but the “meaning” of the chemical signal as well as the elicited response changes according to life stages. Cocconeis diatoms send an attractive signal associated to gustatory receptors of adult shrimps, when consumed51, and a repulsive signal associated to olfactory receptors (indicating the presence of possible predators) when produced in low abundance in neighbouring areas40. In addition they produce a metamorphosis cue, in cooperation with the physical cues of P. oceanica leaves, recognized by shrimp’s competent larvae. The “thrifty” use of infochemicals and ancient receptors4, employed by the shrimp for a range of purposes, indicates an interesting area for future studies, aimed at detecting the evolution and co-evolution63 of chemical messages and their meaning throughout the life cycles of marine invertebrates.
This investigation confirms a substantial theoretical argument, suggesting the possibility for settlement and metamorphosis induction by waterborne VOCs produced by benthic diatoms. Diatom VOCs were previously known to play a role as infochemicals for adult H. inermis, but their signal has evidently also an importance for shrimp larvae searching for a feasible substrate. Both the seagrass leaves and VOCs extracted from an epiphyte diatom have been proven to be important for the shrimp8 and shortened its time of development to metamorphosis. This finding is remarkable, considering that multiple chemical cues may have a critical importance for settlement of invertebrates59. Thus, the association of P. oceanica physical influence and C. scutellum chemical cues might produce a stronger induction activity on larval metamorphosis, as observed for the mud crab Panopeus herbstii9. Also in this case, water-soluble compounds produced by microorganisms and other cues accelerated the metamorphosis of the crab megalopae. The tuning of metamorphosis according to environmental constraints (e.g., substrate recognition) may facilitate the settlement in adequate locations and explains the ecological success of this species in its seagrass environment. In addition, this study demonstrates that chemical messages, whose recognition was previously demonstrated only for adult individuals8, may be as important as physical cues to induce the metamorphosis of H. inermis and this finding could open interesting research opportunities for other species of decapods, for ecological and biotechnological purposes. In fact, larval biology issues and information on settlement and metamorphosis cues are essential for the development of aquaculture techniques as well as for the management of sustainable fisheries35.
Our results confirm the hypothesis that larvae of marine invertebrates do not settle randomly in any area, accepting the risk to survive only if they were lucky enough to encounter an acceptable site13. It demonstrates that also in vagile invertebrates, as marine shrimps, multiple cues improve the probability to select an ideal substrate to start their benthic life21. This finding reinforces the close relationship existing between shrimp and diatoms, co-evoluted in P. oceanica meadows, fundamental to facilitate its sex reversal in spring51. Thus, H. inermis may represent a good model to investigate the effect of metamorphosis cues during the search for a specific target environment, a seagrass having a narrow spatial distribution along the coastal areas of the Mediterranean.
Compliance with ethical standards
This study was funded by the Flagship Project ModRes (SZN Flagship Project nr. 4) of the Stazione Zoologica di Napoli. Francesca Glaviano performed the bioassays funded by the flagship project ModRes of the Stazione Zoologica. Mirko Mutalipassi performed the bioassays while funded by a SZN Open University PhD project (V. Zupo as Director of Studies). All authors declare they have no conflicts of interest. This research involves the development of decapod crustaceans, not directly ruled by National Laws on animal welfare; however, all applicable international, national, and/or institutional guidelines for the care and use of animals were followed.
All data sheets relative to the tests run are available at the Benthic Ecology Centre of Stazione Zoologica.
Tebben, J. et al. Chemical mediation of coral larval settlement by crustose coralline algae. Sci. Rep. 5, 10803 (2015).
Goldsteina, J. S. & Butler, M. J. Behavioral enhancement of onshore transport by postlarval Caribbean spiny lobster (Panulirus argus). Limnol. Oceanogr. 54, 1669–1678 (2009).
Lin, C. Y., Wu, H., Tjeerdema, R. S. & Viant, M. R. Evaluation of metabolite extraction strategies from tissue samples using NMR metabolomics. Metabolomics 3, 55–67 (2007).
Forward, R. B., Tankersley, R. A. & Rittschof, D. Cues for metamotphosis of brachyuran larvae: An overview. Amer. Zool. 41, 1108–1122 (2001).
Whalan, S., Abdul Wahab, M. A., Sprungala, S., Poole, A. J. & De Nys, R. Larval settlement: The role of surface topography for sessile coral reef invertebrates. PLoS One 10 (2015).
Juinio-Meñez, M. A. & Bangi, H. G. P. Extrinsic and intrinsic factors affecting the metamorphic rate of Tripneustes gratilla (Echinodermata: Echinoidea). Mar. Ecol. Prog. Ser. 402, 137–145 (2010).
Regnault, M. Etude experimentale de la nutrition d’Hippolyte inermis LEACH (Decapode, Natantia) au cours de son developpement larvaire, au laboratoire. Int. Rev. der gesamten Hydrobiol. und Hydrogr. 54, 749–764 (1969).
Maibam, C. et al. Relevance of wound-activated compounds produced by diatoms as toxins and infochemicals for benthic invertebrates. Mar. Biol. 161, 1639–1652 (2014).
Crespi-Abril, A. C., Villanueva Gomila, G. L., Venerus, L. A. & Barón, P. J. Spatial distribution of cephalopod paralarvae in San José Gulf (Northern Patagonia, Argentina): The role of tidal circulation in larval dispersal. Fish. Res. 152, 13–20 (2014).
Rodriguez, R. A. & Epifanio, C. E. Multiple cues for induction of metamorphosis in larvae of the common mud crab Panopeus herbstii. Mar. Ecol. Prog. Ser. 195, 221–229 (2000).
Alfaro, A. C., Young, T. & Ganesan, A. M. Regulatory effects of mussel (Aulacomya maoriana Iredale 1915) larval settlement by neuroactive compounds, amino acids and bacterial biofilms. Aquaculture 322–323, 158–168 (2011).
Bao, W. Y., Satuito, C. G., Yang, J. L. & Kitamura, H. Larval settlement and metamorphosis of the mussel Mytilus galloprovincialis in response to biofilms. Mar. Biol. 150, 565–574 (2007).
Hadfield, M. G. Biofilms and marine invertebrate larvae: what bacteria produce that larvae use to choose settlement sites. Ann. Rev. Mar. Sci. 3, 453–470 (2011).
Forward, R. B., Burke, J. S., Rittschof, D. & Welch, J. M. Photoresponses of larval Atlantic menhaden (Brevoortia tyrannus Latrobe) in offshore and estuarine waters: Implications for transport. J. Exp. Mar. Bio. Ecol. 199, 123–135 (1996).
Watson, M. G., Scardino, A. J., Zalizniak, L. & Shimeta, J. A larval-settlement assay method for the gregarious serpulid polychaete, Galeolaria caespitosa. J. Exp. Mar. Bio. Ecol. 496, 49–55 (2017).
Bonniwell, S. M., Breitburg, D. L., Luckenbach, M. W. & Tamburri, M. N. Settlement of Crassostrea ariakensis larvae: effects of substrate, biofilms, sediment and adult chemical cues. J. Shellfish Res. 27, 601–608 (2008).
Freckelton, M. L., Nedved, B. T. & Hadfield, M. G. Induction of invertebrate larval settlement; different bacteria, different mechanisms? Sci. Rep. 7, 42557 (2017).
Simith, D., de, J., de, B., Abrunhosa, F. A. & Diele, K. Metamorphosis of the edible mangrove crab Ucides cordatus (Ucididae) in response to benthic microbial biofilms. J. Exp. Mar. Bio. Ecol. 492, 132–140 (2017).
Huggett, M. J., Williamson, J. E., De Nys, R., Kjelleberg, S. & Steinberg, P. D. Larval settlement of the common Australian sea urchin Heliocidaris erythrogramma in response to bacteria from the surface of coralline algae. Oecologia 149, 604–619 (2006).
Abdul Wahab, M. A., De Nys, R., Webster, N. & Whalan, S. Larval behaviours and their contribution to the distribution of the intertidal coral reef sponge Carteriospongia foliascens. PLoS One 9 (2014).
Hadfield, M. G. & Paul, V. J. Natural chemical cues for settlement and metamorphosis of marine-invertebrate larvae. Marine Chemical Ecology, https://doi.org/10.1201/9781420036602 (2001).
Webster, N. S. et al. Metamorphosis of a scleractinian coral in response to microbial biofilms. Appl. Environ. Microbiol. 70, 1213–1221 (2004).
Dobretsov, S. & Qian, P. Y. Facilitation and inhibition of larval attachment of the bryozoan Bugula neritina in association with mono-species and multi-species biofilms. J. Exp. Mar. Bio. Ecol. 333, 263–274 (2006).
Gibbs, V. K. et al. Optimizing dietary levels of menhaden and soybean oils and soybean lecithin for pre-gonadal somatic growth in juveniles of the sea urchin Lytechinus variegatus. Aquaculture 446, 198–205 (2015).
Nielsen, S. J., Harder, T. & Steinberg, P. D. Sea urchin larvae decipher the epiphytic bacterial community composition when selecting sites for attachment and metamorphosis. FEMS Microbiol. Ecol. 91 (2015).
Khandeparker, L., Chandrashekar Anil, A. & Raghukumar, S. Relevance of biofilm bacteria in modulating the larval metamorphosis of Balanus amphitrite. FEMS Microbiol. Ecol. 58, 425–438 (2006).
Roberts, B. et al. A complement response may activate metamorphosis in the ascidian Boltenia villosa. Dev. Genes Evol. 217, 449–458 (2007).
Tebben, J. et al. Induction of larval metamorphosis of the coral Acropora millepora by tetrabromopyrrole isolated from a Pseudoalteromonas bacterium. PLoS One 6 (2011).
Fink, P. Ecological functions of volatile organic compounds in aquatic systems. Mar. Freshw. Behav. Physiol. 40, 155–168 (2007).
Yang, J. L., Li, S. H., Bao, W. Y., Yamada, H. & Kitamura, H. Effect of different ions on larval metamorphosis of the mussel Mytilus galloprovincialis. Aquac. Res. 46, 155–162 (2015).
Agatsuma, Y., Seki, T., Kurata, K. & Taniguchi, K. Instantaneous effect of dibromomethane on metamorphosis of larvae of the sea urchins Strongylocentrotus nudus and Strongylocentrotus intermedius. Aquaculture 251, 549–557 (2006).
Yang, J. L., Satuito, C. G., Bao, W. Y. & Kitamura, H. Larval settlement and metamorphosis of the mussel Mytilus galloprovincialis on different macroalgae. Mar. Biol. 152, 1121–1132 (2007).
Pawlik, J. R. Chemical induction of larval settlement and metamorphosis in the reef-building tube worm Phragmatopoma californica (Sabellariidae: Polychaeta). Mar. Biol. 91, 59–68 (1986).
Jensen, R. A. & Morse, D. E. Chemically induced metamorphosis of polychaete larvae in both the laboratory and ocean environment. J. Chem. Ecol. 16, 911–930 (1990).
Anger, K. Contributions of larval biology to crustacean research: A review. Invertebr. Reprod. Dev. 49, 175–205 (2006).
Tieleman, B. I. & Williams, J. B. Chapter 14 - Measuring invertebrate grazing on seagrasses and epiphytes. In Global Seagrass Research Methods 271–292, https://doi.org/10.1016/B978-044450891-1/50015-3 (2001).
Zupo, V., Juẗtner, F., Maibam, C., Butera, E. & Blom, J. F. Apoptogenic metabolites in fractions of the benthic diatom Cocconeis scutellum parva. Mar. Drugs 12, 547–567 (2014).
d’Udekem d’Acoz, C. The genus Hippolyte Leach, 1814 (Crustacea: Decapoda: Caridea: Hippolytidae) in the East Atlantic Ocean and the Mediterranean Sea, with a checklist of all species in the genus. Zoologische Verhandelingen Leiden 303 (1996).
Zupo, V., Buia, M. C. & Mazzella, L. A production model for Posidonia oceanica based on temperature. Estuar. Coast. Shelf Sci. 44, 483–492 (1997).
Gambi, M. C., Lorenti, M., Russo, G. F., Scipione, M. B. & Zupo, V. Depth and seasonal distribution of some groups of the vagile fauna of the Posidonia oceanica leaf stratum: structural and trophic analyses. Mar. Ecol. 13, 17–39 (1992).
Zupo, V. et al. Do benthic and planktonic diatoms produce equivalent effects in crustaceans? Mar. Freshw. Behav. Physiol. 40, 169–181 (2007).
Zupo, V. Strategies of sexual inversion in Hippolyte inermis Leach (Crustacea, Decapoda) from a Mediterranean seagrass meadow. J. Exp. Mar. Bio. Ecol. 178, 131–145 (1994).
Stanley, J. A., Hesse, J., Hinojosa, I. A. & Jeffs, A. G. Inducers of settlement and moulting in post-larval spiny lobster. Oecologia 178, 685–697 (2015).
Jüttner, F., Messina, P., Patalano, C. & Zupo, V. Odour compounds of the diatom Cocconeis scutellum: Effects on benthic herbivores living on Posidonia oceanica. Mar. Ecol. Prog. Ser. 400, 63–73 (2010).
Sartori, D., Scuderi, A., Sansone, G. & Gaion, A. Echinoculture: the rearing of Paracentrotus lividus in a recirculating aquaculture system - experiments of artificial diets for the maintenance of sexual maturation. Aquac. Int. 23, 111–125 (2014).
Zupo, V. Effect of microalgal food on the sex reversal of Hippolyte inermis (Crustacea: Decapoda). Mar. Ecol. Prog. Ser. 201, 251–259 (2000).
Zupo, V. & Buttino, I. Larval development of decapod crustaceans investigated by confocal microscopy: an application to Hippolyte inermis (Natantia). Mar. Biol. 138, 965–973 (2001).
Buia, M. C., Zupo, V. & Mazzella, L. Primary production and growth dynamics in Posidonia oceanica. Mar. Ecol. 13, 2–16 (1992).
Guillard, R. R. L. & Ryther, J. H. Studies of marine planktonic diatoms: I. Cyclotella nana Hustedt, and Detonula confervacea (cleve) Gran. Can. J. Microbiol. 8, 229–239 (1962).
De Stefano, M., Marino, D. & Mazzella, L. Marine taxa of cocconeis on leaves of Posidonia oceanica, including a new species and two new varieties. Eur. J. Phycol. 35, 225–242 (2000).
Zupo, V. Influence of diet on sex differentiation of Hippolyte inermis Leach (Decapoda: Natantia) in the field. Hydrobiologia 449, 131–140 (2001).
Sartori, D., Pellegrin, D., Macchia, S. & Gaion, A. Can echinoculture be a feasible and effective activity? Analysis of fast reliable breeding conditions to promote gonadal growth and sexual maturation in Paracentrotus lividus. Aquaculture 451, 39–46 (2016).
Fink, P., Von Elert, E. & Jüttner, F. Oxylipins from freshwater diatoms act as attractants for a benthic herbivore. Arch. für Hydrobiol. 167, 561–574 (2006).
Fink, P., Von Elert, E. & Jüttner, F. Volatile foraging kairomones in the littoral zone: attraction of an herbivorous freshwater gastropod to algal odors. J. Chem. Ecol. 32, 1867–1881 (2006).
Zimme‐Faust, R. K. & Tamburri, M. N. Chemical identity and ecological implications of a waterborne, larval settlement cue. Limnol. Oceanogr. 39, 1075–1087 (1994).
Greene, W. H. Nonparametric and Semiparametric Approaches. in Econometric Analysis (ed. Battista, D.) 909–912 (Prentice Hall, 2012).
Gebauer, P., Paschke, K. & Anger, K. Delayed metamorphosis in Decapod crustaceans: Evidence and consequences. in. Revista Chilena de Historia Natural 76, 169–175 (2003).
Zupo, V. et al. Chemoreception of the seagrass Posidonia oceanica infochemicals by benthic invertebrates is altered by seawater acidification. J. Chem. Ecol., https://doi.org/10.1007/s10886-015-0610-x (2015).
Bao, W. Y., Yang, J. L., Satuito, C. G. & Kitamura, H. Larval metamorphosis of the mussel Mytilus galloprovincialis in response to Alteromonas sp. 1: Evidence for two chemical cues? Mar. Biol. 152, 657–666 (2007).
Morse, A. N. C. & Morse, D. E. Recruitment and metamorphosis of Haliotis larvae induced by molecules uniquely available at the surfaces of crustose red algae. J. Exp. Mar. Bio. Ecol. 75, 191–215 (1984).
Weiner, R. M., Walch, M., Bonar, D. B. & Colwell, R. R. Effect of biofilms of the marine bacterium Alteromonas colwelliana (LST) on set of the oysters Crassostrea gigas (Thunberg, 1973) and C. virginica (Gmelin, 1791). J. Shellfish Res. 8, 117–123 (1981).
Maki, J. S. et al. Effect of marine bacteria and their exopolymers on the attachment of barnacle cypris larvae. Bull. Mar. Sci. 46, 499–511 (1990).
Zupo, V. Co-evolution of the shrimp Hippolyte inermis and the diatoms Cocconeis spp. in Posidonia oceanica: sexual adaptations explained by ecological fitting. In: Springer Nature Switzerland AG 2019 1 Mérillon, J. M. & Ramawat, K. G. (eds), Co-Evolution of Secondary Metabolites Reference Series in Phytochemistry, https://doi.org/10.1007/978-3-319-76887-8_27-1, 1–13 (2019)
A.C. Buono performed experiments within her degree thesis, supervised by V. Zupo. F. Glaviano was partially supported by the project ModRes of the Stazione Zoologica Anton Dohrn. M. Mutalipassi was supported by an OU-SZN PhD fellowship funded by Stazione Zoologica Anton Dohrn. Alberto Macina and Davide Caramiello provided technical support. We thank Cpt. V. Rando for the indispensable cooperation during the collection operations. Three referees provided a deep, expert and detailed revision of the original manuscript and their essential contribution to the final version was invaluable. Aniela Martin (University of Southampton) and Mrs. R. Messina kindly revised the English text. We thank F.P. Patti (head of SIST at SZN) for providing software platforms for statistical analyses of data.
The authors declare no competing interests.
Publisher’s note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
About this article
Cite this article
Zupo, V., Mutalipassi, M., Glaviano, F. et al. Inducers of settlement and metamorphosis of the shrimp Hippolyte inermis Leach in Posidonia oceanica. Sci Rep 9, 12336 (2019). https://doi.org/10.1038/s41598-019-48110-7