# Potential of fascaplysin and palauolide from Fascaplysinopsis cf reticulata to reduce the risk of bacterial infection in fish farming

T. Mai, J. Toullec, S. van Wynsberge, M. Besson, S. Soulet, Sylvain Petek, E.

Aliotti, M. Ekins, K. Hall, D. Erpenbeck, et al.

► To cite this version:

T. Mai, J. Toullec, S. van Wynsberge, M. Besson, S. Soulet, et al. Potential of fascaplysin and palauolide from Fascaplysinopsis cf reticulata to reduce the risk of bacterial infection in fish farming. Fisheries and Aquatic Sciences, 2019, 22, pp.30. 10.1186/s41240-019-0145-0. hal-02503506

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# Potential of fascaplysin and palauolide from *Fascaplysinopsis cf reticulata* to reduce the risk of bacterial infection in fish farming

Tepoerau Mai<fnref n="1" />* ID, Jordan Toullec<fnref n="1" />,², Simon Van Wynsberge<fnref n="1" />,³,⁴, Marc Besson⁵,⁶, Stephanie Soulet<fnref n="1" />, Sylvain Petek<fnref n="1" />,², Emmanuelle Aliotti<fnref n="1" />, Merrick Ekins⁷,⁸, Kathryn Hall⁷, Dirk Erpenbeck⁹, David Lecchini⁵, Mehdi A. Beniddir¹⁰, Denis Saulnier<fnref n="1" /> and Cécile Debitus<fnref n="1" />,²

## Abstract

Marine natural products isolated from the sponge *Fascaplysinopsis cf reticulata*, in French Polynesia, were investigated as an alternative to antibiotics to control pathogens in aquaculture. The overuse of antibiotics in aquaculture is largely considered to be an environmental pollution, because it supports the transfer of antibiotic resistance genes within the aquatic environment. One environmentally friendly alternative to antibiotics is the use of quorum sensing inhibitors (QSIs). Quorum sensing (QS) is a regulatory mechanism in bacteria which control virulence factors through the secretion of autoinducers (AIs), such as acyl-homoserine lactone (AHL) in gram-negative bacteria. Vibrio harveyi QS is controlled through three parallel pathways: HAI-1, AI-2, and CAI-1. Bioassay-guided purification of F. cf reticulata extract was conducted on two bacterial species, i.e., Tenacibaculum maritimum and V. harveyi for antibiotic and QS inhibition bioactivities. Toxicity bioassay of fractions was also evaluated on the freshwater fish Poecilia reticulata and the marine fish Acanthurus triostegus. Cyclohexanic and dichloromethane fractions of F. cf reticulata exhibited QS inhibition on V. harveyi and antibiotic bioactivities on V. harveyi and T. maritimum, respectively. Palauolide (1) and fascaplysin (2) were purified as major molecules from the cyclohexanic and dichloromethane fractions, respectively. Palauolide inhibited QS of V. harveyi through HAI-1 QS pathway at 50 µg ml⁻<fnref n="1" /> (26 µM), while fascaplysin affected the bacterial growth of V. harveyi (50 µg ml⁻<fnref n="1" />) and T. maritimum (0.25 µg). The toxicity of fascaplysin-enriched fraction (FEF) was evaluated and exhibited a toxic effect against fish at 50 µg ml⁻<fnref n="1" />. This study demonstrated for the first time the QSI potential of palauolide (1). Future research may assess the toxicity of both the cyclohexanic fraction of the sponge and palauolide (1) on fish, to confirm their potential as alternative to antibiotics in fish farming.

**Keywords:** Porifera, Marine natural products, Quorum sensing inhibitors, Antibiotic, *Fascaplysinopsis cf reticulata*

## Background

The overuse of antibiotics in the environment may have important economic and sanitary outcomes (Martinez 2009; Hatosy and Martiny 2015). Indeed, the release of antibiotics in natural environments exerts a strong pressure on bacteria strains and supports the selection of resistant bacteria. The recurrent use of antibiotics decreases their effectiveness over time (Blair et al. 2015). To reduce the overuse of antibiotics and minimize the impacts to the environment and human society, there is

an urgent need for alternatives to antibiotics (Editorials 2013; Spellberg and Gilbert 2014).

In aquaculture antibiotic resistance causes mass mortality of cultured species (Karunasagar et al. 1994) which result in economic loss for farmers (Shrestha et al. 2018). Aquaculture itself largely contributes to the dissemination of antibiotics resistance genes in the aquatic environment (WHO, 2006; Shah et al. 2014), which increases the risks on human health (Aly and Albutti 2014). Policy on antibiotics in aquaculture is becoming more strict, and antibiotics are forbidden in some countries (Lulijwa et al. 2019). Finding antibiotic alternatives in this field is the focus of the current research (Pérez-Sánchez et al. 2018) due to

<footnote>* Correspondence: mai.tepoerau@live.fr</footnote>

<footnote n="1">¹EIO, ILM, IFREMER, IRD, UPF, BP 6570, 98702 FAA'A, Tahiti, French Polynesia</footnote>

<footnote>Full list of author information is available at the end of the article</footnote>
the promising market they represent. To reduce the selective pressure exerted on bacteria strains, novel strategies target natural products that inhibit the expression of virulence genes without exerting a strong bactericide activity (Moloney 2016; Spellberg and Gilbert 2014). Such promising products include inhibitors of quorum sensing (Chen et al. 2018; Pérez-Sánchez et al. 2018) which exhibited in vitro and in vivo effectiveness in aquaculture (Manefield et al. 2000; Brackman et al. 2008; Pande et al. 2013).

Quorum sensing (QS) is a cell-to-cell communication process in bacteria based on the secretion and detection of signal molecules (i.e., autoinducers) by bacteria. Specifically for gram-negative bacteria, autoinducers (AIs) consist of small molecules, mainly acyl-homoserine lactone (AHL) derivatives (Waters and Bassler 2005). Quorum sensing allows the expression of target genes involved in biofilm formation, toxin secretion, and bioluminescence (Henke and Bassler 2004a). It is influenced by the concentration in AIs related to the bacterial density and the genetic similarity of bacteria neighbors (Schluter et al. 2016).

A model species for testing the relevance of antibiotic alternatives in aquaculture is *V. harveyi*. *Vibrio harveyi* is a luminescent bacteria inhabiting the marine environment and pathogens in aquaculture, specifically when it is associated with *Tenacibaculum maritimum* (Reverter et al. 2016). The QS of *V. harveyi* is well documented, with three parallel QS systems that are regulated by three couples of signal molecules and cognate sensors: *V. harveyi* autoinducer-1 (HAI-1) and LuxN sensor; autoinducer-2 (AI-2) and LuxPQ sensor; *Cholerae* autoinducer-1 (CAI-1); and CqsS sensor (Henke and Bassler 2004a). Together these three systems encode bioluminescence and virulence factors as biofilm formation, type III secretion, and a secreted metalloprotease genes (Henke and Bassler 2004a; Henke and Bassler 2004b).

Quorum sensing inhibitors (QSIs) of *V. harveyi* have already been identified from a variety of marine organisms, including bacteria, algae, and sponges (Givskov et al. 1996; Peters et al. 2003; Rasch et al. 2004; Teasdale et al. 2009; Dobretsov et al. 2011; Natrah et al. 2011; Kalia 2013; Tello et al. 2013; Saurav et al. 2017). Marine sponges are promising sources of antibiotic alternatives because (i) they are known to be a reservoir of diverse microbial communities (Thomas et al. 2016) and (ii) as primitive sessile organisms featured with a simple multicellular structure, their main defense against pathogen rely on the production of secondary metabolites with antibiotic and antibiofilm (Feng et al. 2013), and QS inhibition activities against pathogens (Blunt et al. 2005; Müller et al. 2013; Quévrain et al. 2014). In this study, *Vibrio harveyi* and *T. maritimum* were used as model species to test antibiotic and QS inhibition bioactivities of two compounds isolated from the sponge *Fascaplysinopsis cf. reticulata* collected in French Polynesia. Because

of the cytotoxicity of fascaplysin (2) reported in the literature (Hamilton 2014), we also evaluated the toxicity of *F. cf reticulata* extract on two fish species (*Poecilia reticulata* and *Acanthurus triostegus*) to check the safety of using this sponge in fish farming.

## Methods

### Sponge sampling

Sponge samples were collected manually using SCUBA, between 45 and 65 m depth in the Tuamotu Archipelago (French Polynesia) during the 2011 Tuam expedition aboard the Alis vessel (Debitus 2011), on the outer reef of Anuanuaro Atoll (20°25.394'S, 143°32.930'W). Samples were frozen immediately at -20 °C on board until being processed.

### Purification and characterization of secondary metabolites.

The sponge collected was freeze dried and grounded to obtain 95 g of dry sponge powder. It was extracted using 100 ml of 80% ethanol and then rinsed twice in 100% ethanol. The solvent was evaporated under reduced pressure, and the remaining ethanolic extract was dissolved in water and successively partitioned three times with cyclohexane and three times with dichloromethane. The cyclohexanic fraction was subjected to silica gel chromatography (40–60-µm mesh) and then eluted with cyclohexane and ethyl acetate mixtures of increasing polarity. Further semi-preparative HPLC on normal phase column eluted with cyclohexane/ethyl acetate 55/45 vol/vol allowed the isolation of palauolide (1) (5 mg). The purification of the dichloromethane fraction (called fascaplysin-enriched fraction (FEF)) using reverse phase HPLC (column: Interchrom Uptisphere strategy, 5 µm; solvent: (water/acetonitrile 70:30), TFA 0.1%) led to the isolation of fascaplysin (2) (17% of FEF, 0.02% dry sponge weight, 19 mg). High-performance liquid chromatography analysis was performed on HPLC (Agilent Technologies 1260 Infinity) with diode array (Agilent G1315C) and evaporative light-scattering (Agilent G4260C) detection. Yields were calculated using the ratio compound weight/freeze-dried sponge weight. Structure elucidation of the two known compounds was performed on the basis of ¹H and ¹³C NMR and mass spectra.

### Fish toxicity bioassay

The toxicity effect of *F. cf reticulata*'s FEF on fish was evaluated on two fish species that can be easily found in French Polynesia and reared in the laboratory: *P. reticulata* (the guppy or mosquito fish) and *A. triostegus* (the convict tang fish). *Poecilia reticulata* specimens (5–8 cm length) were collected from a freshwater pool at Tahiti at night. *Poecilia reticulata* specimens were appealed with a flashlight and then caught with a landing net (5-mm mesh size) and kept in 3 L plastic jar containing
freshwater. Young settlers (or recruits, 1,5, 2 cm length) and juveniles (3–7 cm length) of *A. triostegus* (at the two distinct developmental stages) were caught during full moon nights on the foreshore puddles and on the reef crest using a net of the northeast coast of Moorea Island (17°29'52.19"S, 149°45'13.55"W). *Acanthurus triostegus* recruits (fish larvae undergoing metamorphosis) were transparent at the time of capture, demonstrating that they had just entered the reef following their pelagic larval stage, while the juveniles (old settlers, already metamorphosed and settled when captured) were already fully pigmented when caught, demonstrating that they had already settled in this reef area for at least a week (Lecchini et al. 2004).

A preliminary assay was performed on *P. reticulata* by balneation, as described previously for environmental toxicity studies of acetylcholinesterase (AChE) inhibitor pesticides (Wester and Vos 1994; Bocquené and Galgani 2004; El-Demerdash et al. 2018). Fascaplysin-enriched fraction ethanolic solution was further tested in duplicate at 1 and 5 µg ml⁻¹ during 72 h (chronic toxicity) and at 50 µg ml⁻¹ during 1 h (acute toxicity) in 2-L tanks, each containing five fishes. Solvent controls were run for each experiment. For the 72-h experiment, water, FEF, and EtOH were renewed, and fishes were fed once a day with commercial flakes. Abnormal behavior of fishes after exposure to FEF was evaluated qualitatively, such as swimming difficulties (i.e., irregularity of swim velocity, asymmetric pectorals fins movements, upside down swimming, and quick jumps) and loss of appetite.

Since the preliminary assay highlighted a modification of *P. reticulata* behavior by FEF (see results section), a second toxicity assay was performed on *A. triostegus* focusing on feeding behavior by using a quantitative method. The effect on FEF exposition on *A. triostegus* feeding behavior was assessed on two distinct developmental stages in order to compare the activity of FEF at both stages of development. The bioassays on *A. triostegus* were performed in 3-L tanks. Fishes (young settlers or juveniles) were exposed to FEF at 1 µg ml⁻¹ in groups of four or five individuals during 24, 48, and 72 h. Rubble with encrusting turf algae were placed in the tank for fish to feed on 1 h per day during 3 days. The feeding behavior was assessed by counting the number of bites on the algae encrusted rubble in each aquarium. Six video sequences of 5 or 10 min per aquarium per day were analyzed. Results are expressed in number of bites per fish per hour.

Antibacterial and quorum sensing inhibition bioassays on
Vibrio harveyi

Every purified compound was tested in triplicate at four concentrations, 1, 5, 10, and 50 µg ml⁻¹ against the wild strain *V. harveyi* BB120 (Johnson and Shunk 1936; Bassler

et al. 1997), and three derived mutants, JAF 375 (Freeman and Bassler 1999), JMH 597, and JMH 612 (Henke and Bassler 2004a). All strains were obtained from Bassler laboratory (Bassler et al. 1997; Freeman and Bassler 1999; Henke and Bassler 2004a). Each mutant only expressed one of the three QS systems of *V. harveyi*: JAF 375 (CAI-1 activated), JMH 597 (AI-2 activated), or JMH 612 (HAI-1 activated) (Freeman and Bassler 1999; Henke and Bassler 2004a). Quorum sensing inhibition bioassay was performed by combining simultaneously luminescence kinetics (in relative luminescence units, RLU) and absorbance kinetics (at λ = 600 nm) (Givskov et al. 1996; Brackman et al. 2008; Steenackers et al. 2010). Absorbance kinetics was used to measure the growth of *V. harveyi* with any tested compound or controls. Data was obtained using a Fluostar Omega spectrophoto-luminometer (BMG Labtech Fluostar OPTIMA, Ortenberg, Germany).

The quorum sensing inhibition bioassay was modified from Mai et al. (2015). A *V. harveyi* colony was grown on Zobell agar plates (BD Bacto™ peptone, 5 g; BD BBL™ yeast extract, 1 g; BD Bacto™ agar, 17 g; sterilized sea water, 1 L) for 24 h. The plates were then suspended in liquid Lennox L broth base medium (Invitrogen, Carlsbad, CA, USA) which was supplemented with artificial sea salts (Sigma Aldrich Co., St Louis, MO, USA) at 40 g l⁻¹ and was then incubated for 16 h under constant orbital stirring at 27 °C. This suspension (50 µl) was then diluted in Marine Broth (CONDA®, Madrid, Spain) (10 ml) and was incubated for 30 min while stirring at 27 °C. Compounds were dissolved in absolute ethanol, deposited in sterile 96-µClear® bottom wells microplates (Greiner Bio-One, Germany) that were dried at room temperature under a laminar flow hood. Each sample was tested in triplicate for each concentration of purified compound tested (1, 5, 10, and 50 µg ml⁻¹). Compounds were then dissolved in Marine Broth (100 µl) by sonication at 50/60 Hz for 30 min, and a bacterial suspension (100 µl) was added in the appropriate wells. The 96 wells plates were incubated at 27 °C for 12 h in a microplate incubator reader, with luminescence and absorbance reading conducted every 10 min, after 1 min of double orbital stirring. The sterility of the culture medium was checked throughout the experiment, as well as the absorbance of each tested compound. Luminescence and absorbance data at the N-cycle reading (L<sub>N-cycle</sub> and A<sub>N-cycle</sub>) were respectively obtained after subtracting the mean of the first ten cycles of the luminescence and absorbance (L<sub>mean first 10 cycles</sub> and A<sub>mean first 10 cycles</sub>) from the raw data (L<sub>N-cycle raw data</sub> and A<sub>N-cycle raw data</sub>) (Eqs. 1 and 2).

$$L_{\text{N-cycle}} = L_{\text{N-cycle raw data}} - L_{\text{mean first 10 cycles}} \quad (1)$$

$$A_{\text{N-cycle}} = A_{\text{N-cycle raw data}} - A_{\text{mean first 10 cycles}} \quad (2)$$

The kinetic curves obtained were sigmoidal. Any delay or inhibition of both growth and luminescence curves
compared to the control curves (which mean an inhibition of growth rate) is translated to an antibiotic effect of the compound. By contrast, no change in bacterial growth between tested and control curves associated with a delay of luminescence between tested and control curves translated to a QSI effect of the compound.

## Antibacterial activity on *Tenacibaculum maritimum*

Antibiotic activity on *T. maritimum* could not be performed through the absorbance kinetics method as previously described for *V. harveyi* strains, because *T. maritimum* precipitated at the beginning of the experiment which prevented measuring absorbance. Antibiotic activity on *T. maritimum* was tested using the disk diffusion method on solid agar medium (Bauer et al. 1966). This bioassay was performed on a strain of the marine bacteria named TFA4 (Reverter et al. 2016). Pure compounds were dissolved in 100% ethanol to obtain impregnated disks (celulose disks, 6 mm diameter) with 0.5, 0.25, 0.125, and 0.0625 µg of compound. Disks were air-dried in a laminar flow cabinet and then deposited on Zobell agar plates, previously seeded with TFA4 strain. Petri dishes were incubated at 27 °C for 2 days.

## Statistical analyses

Absorbance was modeled as a logistic function of time (t) (Kingsland 1982) according to Equation 3, where $A_{max}$ is the maximum or asymptotic value of absorbance, k is the steepness of the curve, and $t_0$ is the x value of the sigmoid's midpoint.

$$Y = \frac{A_{max}}{1 + \exp(-k(t-t_0))} \quad (3)$$

$$Y = \frac{L_{max}}{1 + a\exp(-k(t-t_0))} \quad (4)$$

Luminescence was also modeled as a logistic function, following Equation 4, where $L_{max}$ is the maximum or asymptotic value of luminescence. Equation 4 includes an a parameter to adequately model the high steepness found for luminescence curves. For each compound and concentration tested, the parameters of the logistic curve were fitted using the function “nls” of the package “stat” in R.3.1.0. The effect of compounds on the growth and the bioluminescence of *V. harveyi* populations were evaluated by comparison of the growth rate (assimilated to the parameter k) and the curve inflection points. For the absorbance kinetics, the inflection point was equal to $t_0$. For the luminescence kinetics, the derivative ($Y'$) of the sigmoid function was calculated, and the inflection point was identified as the time for which $Y'$ was maximal. Furthermore, to provide comparable values of bioluminescence, luminescence values were compared at a fixed

bacterial concentration (i.e., fixed absorbance A = 0.055, which corresponded to half the maximum absorbance $A_{max}$ of control).

For all parameters involved in QS activity (k and inflection points) as well as in toxicity (number of bites per unit of time per fish), differences between concentration were tested using the non-parametric *Kruskal-Wallis* test (function kruskal.test of pgirmess package in R.3.1.0) and a multiple comparison test after Kruskal-Wallis (function kruskalmc), suitable for small samples. A QSI activity was evidenced when (1) *V. harveyi* population growth rate (k, see Eq. 3) was not significantly lower with compound (or extract) compared to control (Kruskal-Wallis test and multiple comparison test after Kruskal-Wallis, $\alpha$ = 0.05) and (2) the inflection point of luminescence is significantly higher with compound (or extract) compared to control (Kruskal-Wallis test and multiple comparison test after Kruskal-Wallis, $\alpha$ = 0.05).

## Results

### Purification of the *Fascaplysinopsis cf reticulata* extract

The hydro-alcoholic extraction of sponge powder (95 g) provided 2.8 g of extract. The partitioning of this extract led to cyclohexanic (1.46 g, yield 1.54% w/w) and dichloromethane (0.112 g, yield 0.11% w/w) fractions. The purification of the cyclohexanic fraction conducted to the known palauolide (1) (0.005 g, yield 0.005% w/w) and the dichloromethylenic fraction to the alkaloid fascaplysin (2) (0.019 g, yield 0.02% w/w) (Fig. 1).

### Quorum sensing inhibition

#### Effect of palauolide

Absorbance and luminescence kinetics of the *V. harveyi* wild strain (Fig. 2 a and b) highlighted a dose-dependent effect of palauolide (1) on BB120 bacterial growth. During the growth of *V. harveyi* bacterial strains, the growth

<figure><img src="image_2.png" /><figcaption>Palauolide (1)</figcaption></figure>

<figure><img src="image_3.png" /><figcaption>Fascaplysin (2)</figcaption></figure>

<caption>Fig. 1 Chemical structure of palauolide (1) and fascaplysin (2)</caption>
<figure><img src="image_4.png" /><figcaption>**Fig. 2** Effect of palauolide (1) on BB120 strain. (a) Absorbance kinetics, (b) luminescence kinetics (RLU), (c) steepness data (k) of absorbance kinetic, (d) luminescence value (RLU) measured for absorbance at 0.055 (represented on (A) by a dashed line, corresponding to the absorbance value at the inflection point of control) without palauolide (black, control), with palauolide 1 µg ml⁻¹ (blue, C4), 5 µg ml⁻¹ (green, C3), 10 µg ml⁻¹ (orange, C2), and 50 µg ml⁻¹ (red, C1). Data are reported as means ± SD from three technical replicates (*significant Kruskal-Wallis *p* value < 0.05 by comparing with control)</figcaption></figure>

rate (k parameter) of absorbance increased as the con-
centration of palauolide (1) increased (Table 1, Fig. 2c).
As a consequence, the sigmoid midpoint (t₀) decreased
as concentration of palauolide (1) increased (data not
shown). At 50 µg ml⁻¹ of palauolide (1), the growth rate
of absorbance (k = 0.0127 ± 0.0005) reached values sig-
nificantly higher than for controls (k = 0.0086 ± 0.0008;
multiple comparison test after Kruskal-Wallis; *p* < 0.05).
Also not significant due to the lack of statistical power,
similar trends were obtained for the three derived QS
mutants (Table 1). Despite the stimulating effect of
palauolide (1) on V. harveyi growth, a delay in lumines-
cence activation of approximately 17 min was observed
for the highest concentrations tested 50 µg ml⁻¹, com-
pared to the luminescence curve of the control (Fig. 2b,
red and black curves, respectively). At the same growth
stage (A = 0.055), a decrease in RLU was observed for
the highest concentration of palauolide (1) compared to
control. Such decrease was found for the BB120 wild
strain (RLU respectively at 106 210 ± 24 385 at 50 µg
ml⁻¹ (26 µM) of palauolide (1) compared to 172 416 (±
2 489) for control; Table 1; Fig. 2d) and the JMH 612
mutant only (RLU respectively at 99 806 ± 18 002 at 50
µg ml⁻¹ (26 µM) of palauolide (1) compared to 189 392
± 2 609 for control; Table 1; Fig. 2d). For the JMH 612
mutant, the delay between the luminescence kinetics at
50 µg ml⁻¹ and the luminescence kinetics of control was

50 min in average. These results indicate that palauolide
(1) boosted bacterial growth and inhibited V. harveyi QS
through HAI-1 QS pathway.

Effect of fascaplysin

Vibrio harveyi BB120 population growth rate (k, see Eq. 3) was significantly lower with fascaplysin (2) at 50 µg ml⁻¹ (k = 0.0021) compared to control (k = 0.0121; *p* value < 0.05). Similar results were obtained for mutant JAF 375, with lower growth rate (k = 0.0036) and with fascaplysin (2) at 50 µg ml⁻¹ compared to control (k = 0.0119). Strong decreases of population growth rate were also obtained for mutants JMH 597 and JMH 612 with fascaplysin (2) at 50 µg ml⁻¹ compared to control. For several replicates involving the two last mutants, population growth was null or negative with fascaplysin (2) at 50 µg ml⁻¹, which prevented the growth model to be fitted and k estimates to be provided (Table 2; Additional file 1). This suggests an antibiotic effect of fascaplysin (2) on V. harveyi and prevents concluding on a QS inhibition effect.

Antibiotic bioassay

Palauolide did not display any antibiotic activity against
the marine pathogen *T. maritimum*. By contrast fasca-
plysin (2) displayed antibiotic activity at 0.25 µg per disk
(11 mm) and 0.5 µg per disk (18 mm) against *T. mariti-
mum* (TFA4) (disk diffusion bioassay).
<table><caption>**Table 1** Steepness of absorbance kinetic (k) and luminescence value measured for absorbance at 0.055 (RLU) estimated for various concentration of palauolide (1) and Vibrio harveyi strains</caption><thead><tr><th>Strain</th><th>Concentration of palauolide</th><th>Replicate</th><th>k</th><th>RLU</th></tr></thead><tbody><tr><td rowspan="12">BB120</td><td rowspan="4">Control</td><td>1</td><td>0.0093</td><td>173985</td></tr><tr><td>2</td><td>0.0088</td><td>173717</td></tr><tr><td>3</td><td>0.0077</td><td>169546</td></tr><tr><td>All</td><td>0.0086 (± 0.0008)</td><td>172416 (± 2489)</td></tr><tr><td rowspan="4">C4</td><td>1</td><td>0.0100</td><td>173727</td></tr><tr><td>2</td><td>0.0104</td><td>174212</td></tr><tr><td>3</td><td>0.0093</td><td>172441</td></tr><tr><td>All</td><td>0.0099 (± 0.0006)</td><td>173460 (± 915)</td></tr><tr><td rowspan="4">C3</td><td>1</td><td>0.0105</td><td>178786</td></tr><tr><td>2</td><td>0.0116</td><td>179795</td></tr><tr><td>3</td><td>0.0107</td><td>179754</td></tr><tr><td>All</td><td>0.0110 (± 0.0006)</td><td>179445 (± 571)</td></tr><tr><td rowspan="4">C2</td><td>1</td><td>0.0119</td><td>174835</td></tr><tr><td>2</td><td>0.0116</td><td>178950</td></tr><tr><td>3</td><td>0.0117</td><td>178843</td></tr><tr><td>All</td><td>0.0117 (± 0.0001)</td><td>177542 (± 2345)</td></tr><tr><td rowspan="4">C1</td><td>1</td><td>0.0122</td><td>107211</td></tr><tr><td>2</td><td>0.0131</td><td>81339</td></tr><tr><td>3</td><td>0.0129</td><td>130080</td></tr><tr><td>All</td><td>0.0127 (± 0.0005)*</td><td>106210 (± 24385)</td></tr><tr><td rowspan="12">JAF 375</td><td rowspan="4">Control</td><td>1</td><td>0.0144</td><td>131953</td></tr><tr><td>2</td><td>0.0140</td><td>134519</td></tr><tr><td>3</td><td>0.0135</td><td>131708</td></tr><tr><td>All</td><td>0.0139 (± 0.0005)</td><td>132727 (± 1557)</td></tr><tr><td rowspan="4">C4</td><td>1</td><td>0.0160</td><td>129253</td></tr><tr><td>2</td><td>0.0168</td><td>131105</td></tr><tr><td>3</td><td>0.0183</td><td>130501</td></tr><tr><td>All</td><td>0.0170 (± 0.0012)</td><td>130286 (± 944)</td></tr><tr><td rowspan="4">C3</td><td>1</td><td>0.0151</td><td>146894</td></tr><tr><td>2</td><td>0.0154</td><td>146197</td></tr><tr><td>3</td><td>0.0171</td><td>145802</td></tr><tr><td>All</td><td>0.0159 (± 0.0011)</td><td>146298 (± 553)</td></tr><tr><td rowspan="4">C2</td><td>1</td><td>0.0172</td><td>140852</td></tr><tr><td>2</td><td>0.0163</td><td>141282</td></tr><tr><td>3</td><td>0.0160</td><td>140905</td></tr><tr><td>All</td><td>0.0165 (± 0.0006)</td><td>141014 (± 235)</td></tr><tr><td rowspan="4">C1</td><td>1</td><td>0.0170</td><td>159632</td></tr><tr><td>2</td><td>0.0179</td><td>158643</td></tr><tr><td>3</td><td>0.0165</td><td>158767</td></tr><tr><td>All</td><td>0.0171 (± 0.0007)</td><td>159014 (± 539)</td></tr><tr><td rowspan="3">JMH 597</td><td rowspan="3">Control</td><td>1</td><td>0.0094</td><td>147880</td></tr><tr><td>2</td><td>0.0081</td><td>146686</td></tr><tr><td>3</td><td>0.0100</td><td>147955</td></tr></tbody></table>
<table><caption>**Table 1** Steepness of absorbance kinetic (k) and luminescence value measured for absorbance at 0.055 (RLU) estimated for various concentration of palauolide (1) and Vibrio harveyi strains (Continued)</caption><thead><tr><th>Strain</th><th>Concentration of palauolide</th><th>Replicate</th><th>k</th><th>RLU</th></tr></thead><tbody><tr><td rowspan="12">JMH 612</td><td rowspan="4">C4</td><td>All</td><td>0.0091 (± 0.0010)</td><td>147507 (± 712)</td></tr><tr><td>1</td><td>0.0120</td><td>150354</td></tr><tr><td>2</td><td>0.0118</td><td>147321</td></tr><tr><td>3</td><td>0.0121</td><td>147103</td></tr><tr><td rowspan="4">C3</td><td>All</td><td>0.0119 (± 0.0001)</td><td>148259 (± 1818)</td></tr><tr><td>1</td><td>0.0132</td><td>154515</td></tr><tr><td>2</td><td>0.0138</td><td>152906</td></tr><tr><td>3</td><td>0.0140</td><td>153875</td></tr><tr><td rowspan="4">C2</td><td>All</td><td>0.0137 (± 0.0004)</td><td>153765 (± 810)</td></tr><tr><td>1</td><td>0.0129</td><td>152211</td></tr><tr><td>2</td><td>0.0123</td><td>151867</td></tr><tr><td>3</td><td>0.0122</td><td>152261</td></tr><tr><td rowspan="4">C1</td><td>All</td><td>0.0125 (± 0.0003)</td><td>152113 (± 214)</td></tr><tr><td>1</td><td>0.0159</td><td>150802</td></tr><tr><td>2</td><td>0.0183</td><td>161802</td></tr><tr><td>3</td><td>0.0145</td><td>157737</td></tr><tr><td rowspan="12">Control</td><td>All</td><td>0.0162 (± 0.0019)</td><td>156780 (± 5562)</td></tr><tr><td>1</td><td>0.0057</td><td>186864</td></tr><tr><td>2</td><td>0.0083</td><td>192076</td></tr><tr><td>3</td><td>0.0087</td><td>189235</td></tr><tr><td>All</td><td>0.0076 (± 0.0017)</td><td>189392 (± 2609)</td></tr><tr><td rowspan="4">C4</td><td>1</td><td>0.0074</td><td>186349</td></tr><tr><td>2</td><td>0.0076</td><td>189886</td></tr><tr><td>3</td><td>0.0087</td><td>189302</td></tr><tr><td>All</td><td>0.0079 (± 0.0007)</td><td>188512 (± 1896)</td></tr><tr><td rowspan="4">C3</td><td>1</td><td>0.0088</td><td>187819</td></tr><tr><td>2</td><td>0.0076</td><td>174498</td></tr><tr><td>3</td><td>0.0078</td><td>184672</td></tr><tr><td>All</td><td>0.0081 (± 0.0007)</td><td>182330 (± 6963)</td></tr><tr><td rowspan="4">C2</td><td>1</td><td>0.0089</td><td>190911</td></tr><tr><td>2</td><td>0.0086</td><td>188991</td></tr><tr><td>3</td><td>0.0089</td><td>188746</td></tr><tr><td>All</td><td>0.0088 (± 0.0002)</td><td>189549 (± 1186)</td></tr><tr><td rowspan="4">C1</td><td>1</td><td>0.0106</td><td>120398</td></tr><tr><td>2</td><td>0.0097</td><td>91967</td></tr><tr><td>3</td><td>0.0091</td><td>87053</td></tr><tr><td>All</td><td>0.0098 (± 0.0008)</td><td>99806 (± 18002)</td></tr></tbody></table>

Control, C4, C3, C2, and C1, respectively, refer to palauolide (1) concentration at 0, 1, 5, 10, and 50 µg ml⁻¹. Estimated values of k and RLU are provided for each replicate (n = 3) and for all replicates (mean ± standard deviation over the three replicated). Values significantly different from controls (α = 0.05) are marked with a star (*)

## Fish toxicity assay

At 50 µg ml⁻¹ of FEF, *P. reticulata* exhibited signs of hyperventilation as well as motility disarrangement (i.e., jerky movements with sudden accelerations or motionless

periods) within the first hour of treatment. None motility disarrangement was observed at 1 µg ml⁻¹ FEF solutions, but changes to the feeding behavior were noticed for *P. reticulata*, i.e., *P. reticulata* tasted the food flakes but did
<table><caption>**Table 2** Steepness of absorbance kinetic (k) estimated with fascaplysin (2) at 50 µg ml⁻¹ (C1), and without fascaplysin (control), for the various Vibrio harveyi strains</caption><thead><tr><th>Strain</th><th>Dose</th><th>Replicate</th><th>k</th></tr></thead><tbody><tr><td rowspan="6">BB120</td><td rowspan="3">Control</td><td>1</td><td>0.0118</td></tr><tr><td>2</td><td>0.0123</td></tr><tr><td>All</td><td>0.0121</td></tr><tr><td rowspan="3">C1</td><td>1</td><td>0.0024</td></tr><tr><td>2</td><td>0.0017</td></tr><tr><td>All</td><td>0.0021</td></tr><tr><td rowspan="6">JAF 375</td><td rowspan="3">Control</td><td>1</td><td>0.0117</td></tr><tr><td>2</td><td>0.0120</td></tr><tr><td>All</td><td>0.0119</td></tr><tr><td rowspan="3">C1</td><td>1</td><td>0.0051</td></tr><tr><td>2</td><td>0.0021</td></tr><tr><td>All</td><td>0.0036</td></tr><tr><td rowspan="6">JMH 597</td><td rowspan="3">Control</td><td>1</td><td>0.0108</td></tr><tr><td>2</td><td>0.0118</td></tr><tr><td>All</td><td>0.0113</td></tr><tr><td rowspan="3">C1</td><td>1</td><td>0.0019</td></tr><tr><td>2</td><td>&lt; 0</td></tr><tr><td>All</td><td>-</td></tr><tr><td rowspan="6">JMH 612</td><td rowspan="3">Control</td><td>1</td><td>0.0137</td></tr><tr><td>2</td><td>0.0119</td></tr><tr><td>All</td><td>0.0128</td></tr><tr><td rowspan="3">C1</td><td>1</td><td>&lt; 0</td></tr><tr><td>2</td><td>&lt; 0</td></tr><tr><td>All</td><td>-</td></tr></tbody></table>

not ingest them. At 5 µg ml⁻¹ of FEF, all of the *P. reticulata* died within 12 h.

The experiment on *A. triostegus* was only performed at 1 µg ml⁻¹ of FEF. For each time of incubation (24, 48, and 72 h), the number of bites of *A. triostegus* (both recruits and juveniles) decreased significantly compared to control *A. triostegus* (Fig 3). After 24 h of incubation with 1 µg ml⁻¹ FEF solution, the number of bites decreased by 91.3% (± 1.6%, *p* value < 0.01) for recruits and by 95.9% (±0.8%, *p* value < 0.001) for juveniles compared to the control *A. triostegus* (Fig 3). This trend was confirmed for others times of exposition.

Discussion

The isolation of palauolide (1) and the major compound fascaplysin (2) from the French Polynesian *F. cf reticulata* extracts is similar to those results obtained by Sullivan and Faulkner (1982) on Palauan sponges.

The QSI potential of the French Polynesian sponge *F. cf reticulata* against the QS-dependent phenotypic expression in *V. harveyi* was demonstrated for the first

time. Palauolide (1) revealed a potential as QSI by inhibiting *V. harveyi* luminescence at 26 µM. In quantitative analysis, palauolide (1) delayed the activation of bio-luminescence expression to 50 min of *V. harveyi* BB120. The *V. harveyi* growth rate was also significantly increased (*p* value < 0.05). The boosted growth rate of *V. harveyi* with palauolide (1) can be interpreted as a consequence of QS inhibition, because the expression of bioluminescence slows down bacterial growth rate to save energy (Nackerdien et al. 2008). The present data corroborates well with the result obtained previously on the QSI at 23 µM of isonaamidine A isolated from the sponge *Leucetta chagosensis* (Mai et al. 2015). Other studies compared bioluminescence data at a time *t*, to determine the inhibition of QS (Brackman et al. 2008; Teasdale et al. 2009; Natrah et al. 2011). For example, Brackman et al. (2008) showed inhibition of *V. harveyi* bioluminescence with cinnamaldehyde and derivatives at 100 µM, 6 h after the addition of compounds (Brackman et al. 2008). Skindersoe et al. (2008) found that palauolide, a compound of similar structure to palauolide (1), inhibits QS at $IC_{50}$ = 0.66 µM. The better bioactivity of palauolide compared to palauolide (1) could be explained from the sensitivity of the intracellular bioassay used by authors.

The mode of action of palauolide (1) on the inhibition of QS has potential as an antibiotic alternative in aquaculture for *Vibrio* species. Our bioassay on *V. harveyi* double mutants JAF 375, JMH 597, and JMH 612 highlighted interference of palauolide (1) on *V. harveyi* QS, specifically with the acyl-homoserine lactone: HAI-1. Quorum sensing regulates bioluminescence and virulence factors of bacteria through autoinducers (Henke and Bassler 2004a) such as HAI-1 used for intraspecies communication (Waters and Bassler 2005; Yang et al. 2011). Acyl-homoserine lactone molecules are found in the family *Vibrionaceae* (Yang et al. 2011). Palauolide (1) can therefore interfere with *Vibrio* species QS through HAI-1 pathway and then be used as an antivirulent against *Vibrio* species as antagonist of AIs. Most of antagonists of QS sensors are small molecules (Swem et al. 2008; Gamby et al. 2012) with structural similarities to AIs such as brominated furanone derivatives (Givskov et al. 1996; Rasch et al. 2004; Steenackers et al. 2010). Palauolide (1) is a sesterterpene composed by a δ-hydroxybutenolide moiety and a carbon skeleton. The potential of palauolide as a competitor of HAI-1 is most likely due to its small structure and the moderate polarity of its chemical structure. This enables palauolide (1) to cross over the external membrane lipid of bacteria and to bind on the periplasmic sensors Lux N (Swem et al. 2008). Further research would indicate if there is an antagonist effect of palauolide (1) on the HAI-1 sensor, such as testing against additional *V. harveyi* mutants (Swem et al. 2008; Blair and Doucette 2013).
<figure><img src="image_5.png" /></figure>

Fascaplysin (2) supplies a broad range of biological activity within *F. cf. reticulata*. First, as other β-carboline alkaloids as dysideanin (20 µg) and didemnolines A-D (100 µg), fascaplysin is a strong antibiotic (0.25 µg) (Charan et al. 2002; Hamilton 2014). In the sponge, fascaplysin (2) is the major compound which represents 0.02% of the lysophilized sponge weigh. It exhibits many biological activities including cytotoxicity against tumoral cells (Segraves et al. 2004; Shafiq et al. 2012; Hamilton 2014; Cells et al. 2015; Kumar et al. 2015), antimicrobial activities (Roll et al. 1988), and the inhibition of acetylcholinesterase (Bharate et al. 2012; Manda et al. 2016). For microbial disease treatments in aquaculture, fascaplysin (2) is not ideal. Despite its antibiotic activity against marine pathogens *V. harveyi* (Table 2) and *T. maritimum*, fascaplysin (2) is toxic toward both fresh and saltwater fish, *P. reticulata* and *A. triostegus*, respectively. Indeed, fascaplysin (2) modified fish behavior and displayed an anorexic effect. The AchE inhibition properties of fascaplysin (Bharate et al. 2012) could explain both its toxicity (Bocquené and Galgani 2004; Modesto and Martinez 2010; Assis et al. 2012) and its effect on loss of appetite of fish (Schneider 2000).

The toxicity of palauolide (1) on fish was not tested in this study because previous work highlighted a weaker cytotoxic activity of palauolide (1) compared to fascaplysin (2) (Charan et al. 2002; Hamilton 2014). However, we recommend performing additional toxicity bioassays of palauolide (1) on fish before using it as alternative of antibiotic in fish farming.

## Conclusion

In conclusion, the presence of palauolide (1) and fascaplysin (2) in *F. cf. reticulata*, with QS inhibition and antibiotic properties, respectively, could act as complementary where

QSIs help and increase antibiotic action on biofilm formation (Brackman et al. 2011). However, the toxicity on fish of the major compound of *F. cf. reticulata* fascaplysin (2) (yield 0.02% w/w) prevents the use of the sponge extract in fish farming context. We recommend in future research to test toxicity of the cyclohexanic fraction of the sponge and palauolide (1) on fish before concluding on the potential of the cyclohexanic fraction and palauolide (1) as an alternative to antibiotics in fish farming.

## Acknowledgements

This work is part of TM's PhD thesis. We acknowledge ANR, Netbiome, French Polynesian authorities, and Délégation à la Recherche-France in Tahiti for their grant, help, and support, IRD and GOPS for funding the field trips aboard R/V ALIS, her crew and IRD's diving team for their on-field help, and Laboratoire d'Excellence LabEx CORAIL, 66100 Perpignan, France. We would also like to thank Johanna Loacker and Christina Piotrowski from Calacademy for their help with the loan of some comparative material.

## Author's contribution

CD supervised sponge sampling and TM's PhD thesis. SP supervised the setup of the extract library for biological screening. ME, KH, and DE identified sponge samples. TM and MAB carried out chemical experiments. JT, CD, MB, and DL carried out fish toxicity bioassay, and TM, EA, DS, and CD carried out antibiotic and *quorum sensing* bioassays. SVW was in charge of statistical analyses. TM wrote the manuscript. All authors reviewed and approved the manuscript.

## Funding

This research was supported by the research grant ANR-11-EBIM-006-1 (Project: POMARE) from ANR and Netbiome, and the grant 113-163 (Project: Biopolyval) from French Polynesian authorities and Délégation à la Recherche-France in Tahiti.

## Availability of data and materials

Not applicable.

## Ethics approval and consent to participate

Not applicable.

## Consent for publication

Not applicable.
**Competing interests**

The authors declare that they have no competing of interest.

**Author details**

¹EIO, ILM, IFREMER, IRD, UPF, BP 6570, 98702 FAA'A, Tahiti, French Polynesia.

²IRD, Univ. Brest, CNRS, IFREMER, LEMAR, F-29280 Plouzane, France. ³Institut de Recherche pour le Développement, UMR 9220 ENTROPIE (Institut de Recherche Pour le Développement, Université de la Réunion, Centre National de la Recherche Scientifique), Nouméa, New Caledonia. ⁴LEAD-NC, 98848 Nouméa, New Caledonia. ⁵PSL Research University: EPHE-UPVD-CNRS, USR 3278 CRIOBE, BP 1013-Moorea, French Polynesia. ⁶Observatoire Océanologique de Banyuls-sur-Mer, Université Pierre et Marie Curie Paris, Banyuls-sur-Mer, France. ⁷Queensland Museum, PO Box 3300, South Brisbane BC, Queensland 4101, Australia. ⁸School of Biological Sciences, University of Queensland, St Lucia, Queensland 4072, Australia. ⁹Department of Earth and Environmental Sciences & GeoBio-Center, Ludwig-Maximilians-Universität München, Richard-Wagner Str. 10, 80333 Munich, Germany. ¹⁰Biocis, Equipe "Pharmacognosie-Chimie des substances naturelles", CNRS, Université de Paris Sus, Univ. Paris-Saclay, Faculté de pharmacie, 5 rue J-B Clément, 92293 Châtenay-Malabry cedex, France.

Received: 31 July 2019 Accepted: 26 November 2019

Published online: 19 December 2019

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