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First published online February 15, 2006
Journal of Experimental Biology 209, 801-809 (2006)
Published by The Company of Biologists 2006
doi: 10.1242/jeb.02068
Giant liposomes as delivery system for ecophysiological studies in copepods
1 Stazione Zoologica `Anton Dohrn' Villa Comunale, 80121 Napoli,
Italy
2 Dipartimento di Chimica Farmaceutica e Tossicologica, Università
degli Studi di Napoli Federico II, Via D. Montesano, 49, 80131 Napoli,
Italy
3 Istituto di Chimica Biomolecolare, Consiglio Nazionale delle Ricerche
(ICB-CNR), Via Campi Flegrei, 34, 80078 Pozzuoli, Italy
* Author for correspondence (e-mail: buttino{at}szn.it)
Accepted 29 December 2005
| Summary |
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Key words: Temora stylifera, Prorocentrum minimum, giant liposome, diatom, unsaturated aldehyde, copepod egg viability, delivery system, confocal microscopy, feeding experiment
| Introduction |
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Several studies have focused on the biochemical composition of copepod
diets in terms of fatty acids and amino acids
(Jónasdóttir and
Kiørboe, 1996
; Kleppel
et al., 1998
; Laabir et al.,
1999
). Commonly, the methods used are to incubate copepods in
different algal cultures with known biochemical composition and then compare
reduction of egg production and hatching success to the lack of some essential
nutrients. However, these methods are circuitous and more direct methods, e.g.
microparticulate carriers (Caldwell et al.,
2004
) are required to assess the nutritional requirements of
copepods.
Food quality can also be related to the presence of phytoplankton toxicants
that negatively impact copepod reproductive fitness. For example, several
studies have shown that some diatoms strongly reduce copepod egg viability or
induce malformations in newly hatched larvae
(Ianora et al., 2004
and
references therein). The compounds responsible for these effects are linear
poly-unsaturated aldehydes (PUAs) produced by some diatom species within
seconds after crushing of cells, as occurs during grazing by copepods
(Miralto et al., 1999
;
Pohnert, 2000
). Inhibition of
egg-hatching success and teratogenic effects induced by these compounds were
first demonstrated through classical feeding experiments, in which ripe
copepod females were fed uni-algal diatom cultures
(Ianora and Poulet, 1993
;
Poulet et al., 1995b
).
Successively, the negative effects of PUAs on embryo viability in different
invertebrates were studied by directly incubating embryos in known
concentrations of pure molecules (Caldwell
et al., 2002
; Caldwell et al.,
2003
; Romano et al.,
2003
; Tosti et al.,
2003
) or using the alga Prorocentrum minimum as live
carrier cells (Ianora et al.,
2004
). However in vitro incubations are not appropriate
to study in vivo effects mediated by female diets for several
reasons: (i) in natural conditions, females are exposed to these compounds
after grazing and crushing of the diatom cells; (ii) owing to the high
volatility of these compounds, their concentration in the water may change
with time; (iii) toxicants that are freely dissolved in the water may not only
be ingested by females, but also adsorbed through the exoskeleton; (iv) live
carrier cells could metabolically transform active molecules in non-active
ones. Hence, new methods using carriers for nutrients, antibiotics or other
substances to enhance copepod production for aquaculture, or to study the
effects of algal toxicants, could be very advantageous.
Here we propose giant liposomes as a delivery system of different bioactive
molecules, including essential nutrients or potential toxicants such as diatom
PUAs, to study their effects on the physiology of copepods. Liposomes are
small particles composed of a lipidic bilayer surrounding one or more aqueous
cavities, largely used in the pharmaceutical and cosmetic fields. When natural
lipids are employed, liposomes are biodegradable and not toxic; furthermore,
the presence of hydrophobic and hydrophilic portions makes liposomes a very
versatile carrier, allowing for the encapsulation of both lipophilic and
hydrophilic compounds (Crommelin,
1994
). In aquaculture, small liposomes have already been used as
nutrient supplements or as drug carriers for first-feeding marine fish larvae
(Koven et al., 1995
) and the
brine shrimp Artemia sp.
(Hontoria et al., 1994
;
Touraki et al., 1995
;
Ozkizilcik and Chu, 1994
).
However, they have never been used as a delivery system for copepods. In this
study, liposomes were prepared with a mean size in the same range as the food
ingested by copepods. A fluorescent dye was encapsulated to follow copepod
ingestion and palatability with the aid of confocal laser scanning microscopy
(CLSM), and liposome ingestion rates were calculated using
3H-labelled liposomes. Copepod egg production rate, percentage egg
viability and faecal pellet production were also assessed in short-term
feeding experiments, to evaluate the effect of the liposome diet alone, or
combined with a dinoflagellate species, on copepod reproduction.
| Material and methods |
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Liposome preparation
Liposomes were prepared by a modified hand-shaking method
(Bangham et al., 1965
).
Briefly, a lipid mixture containing 110 mg of SPC and 40 mg of cholesterol in
5 ml of a chloroform/methanol solvent mixture (2:1 v/v) was introduced into a
250 ml round-bottomed flask. In the case of 3H-labelled liposomes
(LIPOR), 1 mCi (37 MBq) of [7(n)-3H]cholesterol, corresponding to
0.12% (w/w) of the total cholesterol, was added to the lipid mix. The solvent
was removed in a rotary evaporator (Laborota 4010 digital, Heidolph,
Schwabach, Germany) until formation of a lipid film on the wall of the flask.
To prepare blanks and 3H-labelled liposomes or fluorescently
labelled liposomes (LIPOF; FitcDx-encapsulating liposomes), the lipid film was
hydrated with 5 ml of 0.22 µm filtered seawater (FSW) or FSW containing
0.05% (w/v) fluorescein isothiocyanate-dextran (FitcDx), respectively. The
resulting suspension was gently mixed in the presence of glass beads (0.5 g)
until the lipid layer was removed from the glass wall. The flask was then
attached to the evaporator again, rotated at room temperature for about 30
min, and left at room temperature for 2 h. After preparation, FitcDx loaded
liposomes were washed two times as follows: the suspension was centrifuged at
7200 g for 20 min, the supernatant was removed, replaced with
FSW, and resuspended by vortex. All liposome formulations were stored at
4°C under nitrogen until use in copepod feeding experiments.
Liposome characterization
The mean diameter and size distribution of liposomes were determined by
laser light scattering (Coulter LS, 100Q, Beckman Coulter, Miami, USA) on a
dispersion of liposomes in FSW. Particle size was expressed as mean volume
diameter ± standard deviation (s.d.) of values collected from three
different batches.
Confocal laser scanning microscopy (CLSM; LSM-410, Zeiss, Jena, Germany) using a 63x water immersion objective was used to obtain images of LIPOF, after dilution in FSW and mounting with Confocal Matrix (Micro Tech Lab, Graz, Austria).
For transmission electron microscopy (TEM), liposomes were centrifuged at 7200 g for 20 min, the supernatant was removed and liposomes were fixed in 1% (v/v) glutaraldehyde solution in FSW for 1 h. After post-fixation in 1% osmium tetroxide (w/v) for 1 h and dehydration in a graded alcohol series, liposomes were embedded in EPON® 812 and sectioned with a Reichert ultramicrotome (Hamburg, Germany). Sections were stained with uranyl acetate and lead citrate and examined with a Philips 400 transmission electron microscope (Eindhoven, The Netherlands).
To measure the amount of FitcDx entrapped within the liposomes, 0.9 ml of liposome suspension was mixed with 0.1 ml of Triton X-100 and fluorescence was quantified using a luminescence spectrometer (Perkin-Elmer Ltd, Buckinghamshire, UK). Encapsulation efficiency was calculated as percentage ratio between the amount of FitcDx entrapped and that initially added within liposomes. The results are presented as mean ± s.d. of three different experiments.
Copepod feeding experiments
Zooplankton were collected in the Gulf of Naples (Italy) from July 2003 to
May 2004 with a 200 µm mesh net and transported, in an insulated box, to
the laboratory where ripe male and female Temora stylifera (Dana)
copepods were immediately sorted. T. stylifera couples were incubated
individually in 50 ml crystallizing dishes containing 30 ml of 0.22 µm FSW
(starved group; time 0). After 24 h, 25 couples were transferred to
crystallizing dishes containing 30 ml FSW and the dinoflagellate
Prorocentrum minimum Pavillard (Sciller) (PRO), in the exponential
growth phase, at a final concentration of approx. 4x103 cells
ml1, corresponding to a carbon daily intake of 720 µg C
l1 (Carotenuto et al.,
2002
). Another group of 25 couples was incubated in 30 ml FSW
containing approx. 4x105 LIPOF ml1, and a
third group of 25 couples was incubated in 30 ml FSW containing both PRO and
LIPOF (LIPOF+PRO) at the same concentrations reported above. Liposome
concentrations were assessed with the Coulter Multisizer II (Beckman Coulter).
Each group of copepods was incubated in a temperature-controlled incubator at
20°C and on a 12 h:12 h light:dark cycle. After 24 h, couples were
transferred to new crystallizing dishes containing either PRO, LIPOF or
LIPOF+PRO, at the same concentrations, and eggs and faecal pellets were
counted with an inverted Zeiss microscope. Percentage egg viability was
calculated 48 h after spawning, as described by Ianora et al.
(1995
), by counting empty
membranes and hatched nauplii. Egg production rates, egg viability and faecal
pellet production were determined 24 and 48 h after feeding on PRO, LIPOF and
LIPOF+PRO.
In a separate experiment we also quantified copepod ingestion rates of liposomes, with and without PRO, using liposomes containing [7(n)-3H]cholesterol (LIPOR). After 24 h starvation, three female T. stylifera were incubated in 50 ml bottles containing 30 ml of FSW and 30 µl of LIPOR (2x105 liposome ml1) or LIPOR + PRO (6000 cells ml1). After 30 min females were collected on a filter, rinsed in SW, placed individually in scintillation vials with 450 µl of Solvable® (Perkin-Elmer, Groningen, The Netherlands), and incubated overnight at 60°C. To differentiate radioactivity of non-ingested liposomes adhering to the copepod body from those ingested, the same experiments were performed with females killed with 4% formalin, and incubated for 30 min in LIPOR or LIPOR + PRO suspensions. Experiments were performed in triplicates. Activity (in d.p.m.) was measured in 5 ml of scintillation cocktail (Ultima Gold, Packard-Bioscience, Milan Italy) using a Beckman LS 6500 liquid scintillation counter.
Filtration rate (ml copepod1 h1) was calculated as: (RfRd)0.45 ml/(RsRsw)30 min, where Rf is the radioactivity of the female, Rd is the radioactivity of dead females; Rs is the radioactivity of the liposome suspension, and Rsw is the radioactivity of the seawater, all in d.p.m.
Confocal laser scanning microscopy
Temora stylifera fed PRO, LIPOF and LIPOF+PRO for 24 and 48 h,
were observed with CLSM to detect gut fluorescence. Live fed and starved
females were mounted on a slide, immobilized with a coverglass, and observed
by CLSM using an inverted microscope (Zeiss LSM-410) equipped with a 10x
water immersion objective. 488 and 543 nm wavelength (
) lasers were
used to excite fluorescein and chlorophyll, respectively. Each female was
optically z-sectioned and the final image was reconstructed
three-dimensionally using the Zeiss software. Light-transmitted images were
acquired, at a single faecal plane, using a 633 nm
laser. Focal
pellets, produced by females and males fed PRO, LIPOF and LIPOF+PRO for 24 and
48 h, were also observed using CLSM, with the same setting reported above, to
detect chlorophyll and FitcDx fluorescence.
| Results |
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Fig. 4 shows fluorescent, reconstructed three-dimensional images of T. stylifera females (Fig. 4A,C,E,G) and the same images in transmitted light (Fig. 4B,D,F,H), observed using CLSM. Females that had been starved for 24 h showed only an external autofluorescence (yellow colour) due to the chitinous wall (Fig. 4A). The chitin lining the oesophagus also appeared autofluorescent while no fluorescence was detected inside the body. In transmitted light, dark and mature gonads and diverticula of the oviducts were clearly visible (Fig. 4B). The gut of females fed the dinoflagellate PRO for 24 and 48 h has strong red fluorescence, due to ingested phytoplankton cells (Control, Fig. 4C). In transmitted light (Fig. 4D), fluorescent regions appeared dark and the faecal pellet was clearly visible in the hindgut (Fig. 4D). Females fed the diet LIPOF for 24 and 48 h, showed a strong green fluorescence in the gut, indicating that liposomes had been ingested (Fig. 4E). Fig. 4G-H is an example of a female fed the mixed diet LIPOF+PRO for 24 h; the oesophagus and hindgut emitted both green and red fluorescence. In transmitted light, the same fluorescent regions appeared dark and the faecal pellet was clearly visible in the hindgut (Fig. 4H).
|
Ingestion rate calculated using 3H-labelled liposomes was higher when females were fed with a mixed diet of liposomes and P. minimum (28515.5±10832.2 liposomes female1 h1; mean ± s.d.) compared to a diet of liposomes alone (14161.6±1930.5 liposomes female1 h1). These values correspond to a 16% and 7.6% uptake of liposomes, respectively. Student's t-test analysis confirms that the difference is statistically significant (P<0.05; t=2.26; d.f.=4), suggesting that the presence of the algal food was necessary to enhance feeding by the copepods.
Faecal pellets, produced by T. stylifera fed PRO, LIPOF and LIPOF+PRO, were collected and observed with CLSM in fluorescence and transmitted mode (Fig. 5). Fig. 5A shows an example of faecal pellets produced by copepods fed the dinoflagellate PRO for 24 h. PRO cells were clearly visible inside the pellet, because of the red fluorescence of chlorophyll. In transmitted light, the same faecal pellet consisted mainly of empty dinoflagellate cell walls (Fig. 5B). Faecal pellets produced by copepods fed LIPOF for 24 h(Fig. 5C) showed only green fluorescence and in transmitted light they appeared dense and dark (Fig. 5D). Copepods fed LIPOF+PRO produced faecal pellets that fluoresced both green and red (Fig. 5E). In transmitted light, they appeared dark and their structure was similar to faecal pellets produced by copepods fed LIPOF (Fig. 5F).
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Initial egg viability was 8688% in all females (Fig. 6B). This value remained constant after feeding on the dinoflagellate diet PRO for 24 h (91.9±3.0) and 48 h (96.1±2.9). Percentage egg viability decreased slightly after 48 h, to 79.4±8.7%, in females fed LIPOF+PRO, but this value was not significantly different from the PRO diet (Table 1). However, percentage egg hatching success calculated for females fed LIPOF, dropped dramatically to 49.1±12.8% after 24 h, and to 37.5±23.9% after 48 h. These values were significantly lower than those recorded for both PRO and LIPOF+PRO diets after 24 and 48 h (Table 1).
Initial faecal pellet production rates were very low (mean of 11.5 faecal pellets couple1) but increased after 24 h with PRO (30.8±3.8) and doubled with LIPOF+PRO (57.8±3.4) diets. By contrast, the number of faecal pellets produced by couples fed LIPOF for 24 and 48 h, remained similar to that recorded at time zero (17.1±2.9 and 14.9±1.8, respectively). All three treatments showed statistically different faecal pellet production rates (Table 1), with maximum production recorded for couples fed the LIPOF+PRO diet.
| Discussion |
|---|
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Liposomes observed with TEM and CLSM appeared as vesicles formed by a
single large aqueous cavity surrounded by a thick membrane. A similar
morphology has already been described for multilamellar vesicles composed
entirely of neutral lipids, which tend to form very packed multilayer
assemblies, with the adjacent bilayer stacked very closely upon the other, and
with very little aqueous space between them
(New, 1990
). The sealing of
bilayer sheets, observed in TEM images, may also have contributed to high
liposome stability during storage.
Liposomes were loaded with FitcDx to follow the fate of liposomes in the
copepod gut. We used a fluorescent dye covalently bonded to a high molecular
mass hydrophilic compound to limit the escape of the fluorescent dye from the
aqueous cavities. FitcDx was successfully entrapped within liposomes with an
encapsulation efficiency higher than usually expected with this preparation
technique for hydrophilic compounds (New,
1990
). Females fed liposomes alone produced the lowest number of
eggs, suggesting that liposomes were not sufficient to sustain copepod
reproduction. As a consequence of this very low egg production (<1 egg
female1), percentage egg hatching success was highly
variable, ranging from 085%. In addition, the number of faecal pellets
produced with the liposome diet alone was similar to the number produced by
starved animals (time 0). With a mixed diet (dinoflagellate and liposomes
together), however, both egg production rate and egg viability were similar to
values recorded for females fed the control diet. This suggests that the
liposome formulation per se had no supplementary effect on copepod
egg production and did not impair egg-hatching success. Interestingly, the
number of faecal pellets produced with the mixed diet LIPOF+PRO was double
that recorded for the control diet PRO, indicating that significant numbers of
liposomes were ingested when they were included in the algal diet. Previous
studies have shown that copepods can discriminate between flavoured or
unflavoured foods (De Mott,
1988
; Kerfoot and Kirk,
1991
). Our results on liposome ingestion rate, calculated using
radiolabelled cholesterol, confirm that liposomes were actively ingested by
copepods, in both experimental feeding conditions, with or without the
dinoflagellate diet. However, with a diet of liposomes and P.
minimum, copepods grazed twice as much compared to a diet of liposomes
alone. Also in other experiments with inert particles, copepods grazed more if
particles were coated with fresh algal exudates
(Kerfoot and Kirk, 1991
). In
our protocol, the presence of algal cells increased ingestion rates with
respect to an unflavoured liposome diet.
Recently, several authors have speculated on the use of liposomes as a
standardized carrier system for diatom-derived PUAs in order to calculate the
relationship between ingestion of these PUAs and toxicity in copepods
(Caldwell et al., 2004
;
Paffenhöfer et al.,
2005
). Since ingestion of diatoms reduce copepod embryo viability
and block embryonic divisions in several other marine organisms
(Buttino et al., 1999
;
Miralto et al., 1999
;
Caldwell et al., 2002
;
Caldwell et al., 2003
;
Romano et al., 2003
;
Tosti et al., 2003
) there is a
need to better understand the molecular and cellular target(s) of these
compounds. Here, we propose liposomes as a vehicle system to relate aldehyde
ingestion to reproductive response, such as egg mortality or induction of
teratogenesis, in copepods. Moreover, liposomes containing labelled compounds,
such as radioisotopes, or fluorescent probes, could also be used as carriers
to verify the fate of toxins in grazers. At present, diatom species have been
shown to produce several different short-chain PUAs
(Miralto et al., 1999
;
d'Ippolito et al., 2002a
;
d'Ippolito et al., 2002b
;
d'Ippolito et al., 2003
);
liposomes might make it possible to differentiate the effect of one chemical
with respect to another, or to study the antagonistic/synergic effect of
different diatom-derived aldehydes on the reproductive physiology of copepods.
Testing the combined effects of different chemicals is, in fact, a requisite
to understand phytoplankton-herbivore interactions at sea. A major debate in
the study of diatom-copepod interactions has focused on whether reduced
hatching is due to the lack of some essential nutrients in diatoms, or to the
presence of antimitotic compounds (Ianora
et al., 1999
; Paffenhöfer
et al., 2005
). Since liposomes do not add any nutritional value to
the diet, they could also be used as carriers of specific nutrients to
evaluate if a deficiency of nutritive compounds reduces egg and embryo
viability in copepods. The use of liposomes could clarify this controversy,
differentiating toxic from nutritive effects.
On a more general basis, our giant liposomes could be used in studies on
food quality effects and nutritional requirements of herbivorous copepods, a
topic that has been poorly addressed in copepods compared to other
zooplankters. For example, the nutritional needs for growth and reproduction
in the freshwater crustacean, Daphnia sp., have been extensively
investigated using different supplementation methods such as lipid emulsions
(De Mott and Müller-Navarra,
1997
), bovine serum albumin beads
(von Elert and Wolffrom,
2001
), inert algal carriers
(von Elert, 2002
;
Becker and Boersma, 2003
) and
liposomes <5 µm diameter (Ravet et
al., 2003
). To our knowledge, only Hasset
(Hasset, 2004
) used homogenate
or gelatine-acacia microcapsules, as carriers for cholesterol, to supplement
copepod diets. In comparison with these carriers, liposomes seem to be more
versatile because of the possibility of entrapping molecules of a different
chemical nature.
Liposomes have already been employed for nutrient enrichment of brine
shrimp (Artemia salina) larvae, which is one of the key organisms
used as food for larval fish rearing in commercial mariculture (for a review,
see Coutteau and Sorgeloos,
1997
), and have recently been proposed as carriers of nutrients
and therapeutic agents in mollusc aquaculture
(Lai et al., 2004
).
Considering the increasing attention that copepods are receiving as
alternative live preys to Artemia
(Støttrup, 2000
;
McKinnon et al., 2003
), we
suggest the use of liposomes as specific nutrient and/or drug carriers for
copepod mass cultivation in aquaculture.
Since marine copepods constitute an important pathway in the trophic
transfer to top-level carnivores, they are recommended in baseline studies for
xenobiotic toxicity (AMAP,
1995
). Another application for liposomes could therefore be in
ecotoxicological studies; until now, toxicity of chemicals on copepods have
been tested by dissolving contaminants in the water, or by exposing copepods
to contaminated food (Hook and Fisher,
2001
; Willis and Ling,
2004
). As an alternative, giant liposomes could be used to test
toxicity of poorly water-soluble substances. This technique has already been
applied to test pesticide toxicity on the freshwater cladoceran
Daphnia (Fliedner,
1997
). Our liposomes could be used to deliver different pollutants
to copepods, allowing for more in-depth studies on bioaccumulation processes
through the marine food chain.
| List of abbreviations |
|---|
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| Acknowledgments |
|---|
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