Dinophysis species associated with diarrhetic shellfish poisoning episodes in North Patagonian gulfs (Chubut, Argentina).
KEY WORDS: Dinophysis tripos, Dinophysis acuminata, diarrhetic shellfish poisoning, mouse bioassay, liquid chromatographytandem mass spectrometry, North Patagonian gulfs
Diarrhetic shellfish poisoning (DSP) is a specific type of food poisoning and a severe gastrointestinal illness caused by the ingestion of filter-feeding bivalves contaminated with a specific suite of marine toxins (Yasumoto et al. 1984, Dominguez et al. 2010). Diarrhetic shellfish poisoning is globally reported with recurring cases in Europe, South America, and Southeast Asia (Hallegraeff 1993, Van Dolah 2000, Reguera et al. 2012). The most characteristic symptoms of DSP intoxication are diarrhea, nausea, vomiting, abdominal pain, and chill. No human fatalities attributed to DSP have been reported; however, some of the DSP toxins may promote stomach tumors and thus cause chronic problems in shellfish consumers (Suganuma et al. 1988, Larsen & Moestrup 1992).Three chemically different lipophilic groups of toxins have been historically associated with DSP: okadaic acid (OA) and dinophysistoxins (DTX), pectenotoxins (PTX), and yessotoxins (Dominguez et al. 2010). Both OA and the DTX are acid polyethers that inhibit protein phosphatases, and are the only toxins of the old "DSP complex" with diarrheogenic effects (Reguera et al. 2012). Okadaic acid and its congeners DTX-1 and DTX-2 are the main toxins responsible for the DSP syndrome (Yasumoto et al. 1985); however, PTX and yessotoxins have been considered as DSP toxins mainly because they are extracted together with OA and DTX for DSP testing (Yasumoto et al. 1985, Murata et al. 1987, Dominguez et al. 2010). The PTX are polyether-lactones, some of which are hepatotoxic to mice by intraperitoneal injection. The PTX-2 and its shellfish-mediated derivative, PTX-2 seco acid (PTX-2sa), are not toxic to mice when administered orally and their potential threat to human health is currently under debate (Miles et al. 2004, Reguera et al. 2012). Yessotoxins are disulfated polycyclic polyether toxins and are toxic to mice only by intraperitoneal injection (Aune et al. 2002, Tubaro et al. 2003).
Okadaic acid and DTX are mainly produced by planktonic dinoflagellates of the genus Dinophysis and Prorocentrum Uma Ehrenberg (Dodge) (Gayoso et al. 2002, Maranda et al. 2007). To date, 12 species of Dinophysis have been reported to contain lipophilic toxins (Yasumoto et al. 1985, Reguera & Pizarro 2008, Rodriguez et al. 2012). Of these species, seven (Dinophysis acuminata, Dinophysis acuta Ehrenberg, Dinophysis caudata Saville-Kent, Dinophysis fortii Pavillard, Dinophysis miles Cleve, Dinophysis ovum Schiitt, Dinophysis sacculus Stein) have been associated with DSP events (Reguera et al. 2012). In New Zealand, Chile, and along the Atlantic coasts of Europe, Dinophysis acuminata and D. acuta have been reported as the main causative agents of lipophilic shellfish toxin events in shellfish above regulatory levels (van Egmond et al. 1993, Raho et al. 2008, Reguera & Pizarro 2008). Previously, many questions about the ecology, behavior, toxin content, and genetic diversity of Dinophysis populations remained unanswered. This is partly due to the fact that researchers were unable to successfully establish laboratory cultures of Dinophysis species for many years. This obstacle was overcome when Park et al. (2006) successfully cultured an isolate of D. acuminata by providing the ciliate prey Mesodinium rubrum (Lohmann) Hamburger and Buddenbrock which in turn was allowed to feed on the cryptophyte Teleaulax sp. As a result of this culturing achievement, D. fortii (Nagai et al. 2008), D. caudata (Nishitani et al. 2008a), D. acuta (Jaen et al. 2009) and Dinophysis infundibulus Schiller (Nishitani et al. 2008b) have also been successfully cultured. Later, Rodriguez et al. (2012) described morphological, toxicological and genetic characteristics of D. tripos from cultures fed with the ciliate Mesodinium rubrum. This was the first report of the presence of PTX-2 in D. tripos and of the establishment of cultures of this species.
The first record of potential DSP producers along the Patagonian coast dates back to 1980. Gil et al. (1989) reported the occurrence of Dinophysis acuminata and Dinophysis fortii in the San Jose Gulf, being the first report of DSP producers from Chubut Province, northern Patagonia, Argentina. One year after D. acuminata was reported from the Chubut River Estuary (Sastre et al. 1990) and D. acuminata and Prorocentrum lima were recorded in phytoplankton samples from the San Jose Gulf and Nuevo Gulf (Santinelli et al. 1994, Santinelli et al. 2002). Later the occurrence of D. acuminata in Nuevo Gulf was also recorded in December 1993 and November 1994 (Santinelli 2008).
Even though DSP producing species in this region had been observed before, it was not before 1999 that the first recognized DSP outbreak reported by Gayoso and Ciocco (2001) and Gayoso et al. (2002). At a celebration, more than 40 people suffered from gastrointestinal disorders after consuming shellfish, with diarrhea, nausea, and vomiting. This episode coincided with the presence of the epibenthic Prorocentrum lima in the stomach content of mussels Aulacomya atra Molina and Mytilus edulis platensis d'Orbigny and in water samples from San Jose and Nuevo Gulfs. Eleven years later, Sar et al. (2010) detected the toxigenic Dinophysis species Dinophysis acuminata and Dinophysis caudata and lipophilic shellfish toxins in two bivalve species from the coast of Buenos Aires Province. This was the first record of detection of an outbreak of DSP associated with the presence of Dinophysis species in Argentina. Most recently, another PTX producing species, Dinophysis tripos, was reported for the Argentine Sea (Fabro et al. 2015). Previous work was further supplemented by the survey carried out by Sar et al. (2012), which focused on the detection of DSP toxins in shellfish samples. Their results showed that shellfish were contaminated with a DSP toxin profile composed of OA, DTX-1 and DTX-3. Besides this report, however, little nothing is known about the linkage of positive DSP mouse bioassays and the original phytoplankton toxin profiles in this area. For this reason the major aim of this study was to investigate the toxin profile of toxigenic phytoplankton present in shellfish harvesting areas during harvest closure due to DSP in the Chubut Province in the years 2009 to 2011.
MATERIALS AND METHODS
Phytoplankton Monitoring Program
Data included in the present study came from the Harmful Algal Bloom and Shellfish Toxicity Monitoring Program, carried out through a working agreement between the Subsecretaria de Pesca, Universidad Nacional de la Patagonia "San Juan Bosco" (UNPSJB), Centro Nacional Patagonico (CENPAT), Ministerio de Ambiente, Secretaria de Turismo y Areas Protegidas and Secretaria de Salud. The monitoring program includes a total of 13 stations along the coast of Chubut that were sampled from 2000 (Fig. 1). Field sampling was carried out in the North Patagonian gulfs (between 41[degrees] and 43[degrees] S): San Matias, San Jose and Nuevo, located on the Northeastern coast of the Chubut Province, Argentina. Between 2009 and 2011 samples were collected monthly and occasionally biweekly at stations Puerto Lobos (San Matias Gulf), Bengoa, Larralde and Riacho (San Jose Gulf), and Playa Parana (Nuevo Gulf) (Fig. 1).
Water samples for quantitative phytoplankton analyses, taken in the frame of the monitoring program, were collected using a tube sampler of 80 cm length and 11 cm diameter, to obtain integrated water column samples (Franks 1995). Subsamples of 250 ml were preserved with Lugol's solution and stored for species identification and enumeration. In addition, qualitative phytoplankton samples were taken using a 25-[micro]m mesh net through oblique tows, and fixed with formaldehyde at a final concentration of 4%.
A sampling survey to collect phytoplankton for toxin analysis was carried out during February 2015 in Larralde. Bengoa, Riacho, and Playa Parana. The phytoplankton samples were collected by oblique net tows from 5 m depth to surface with a 25-[micro]m mesh net on a boat. Net haul samples were concentrated to 175 ml. Ten-millimeter aliquots of the captured material was preserved in Lugol's solution for microscopic observation and used to calculate the cells concentration, and the remainders of the samples were then filtered through Whatman GF/F filters and frozen (-20[degrees]C) until analysis.
Mouse bioassays were performed at the Direccion de Salud Ambiental (Chubut Province).
The shellfish samples for analysis of DSP toxins were collected from harvested natural beds and removed from subtidal sand beds and from the substrate by underwater diving at 5-25 m depth. The shellfish samples were obtained from Larralde, Bengoa, Riacho, and Puerto Lobos at the same time as the phytoplankton samples. Shellfish samples were scallops (Aequipecten tehuelchus d'Orbigny), clams (Ameghinomya antique King & Broderip), mussels (Mytilus edulis platensis) and Panopea clams (Panopea abbreviate Valenciennes), which were frozen until analysis. The mouse bioassays were performed as described by Yasumoto et al. (1984) and modified as described by Fernandez et al. (2002). In brief, toxins were extracted from shellfish tissue using acetone and after evaporation the residue was dissolved in a small volume of 1 % Tween 60. The extract was injected intraperitoneally into mice with a body weight of about 20 g and the survival was monitored from 24 to 48 h according to Decision 2002/225/CEE published in the Official Journal of the European Community (EC 2002).
Dinophysis Species Identification ami Analyses
All phytoplankton samples were analyzed in the Laboratorio de Hidrobiologia of the Universidad Nacional de la Patagonia "San Juan Bosco".
Lugol's preserved samples were counted using the Utermohl method (Utermohl 1958) with a phase contrast inverted microscope (Leica DMIL). For qualitative estimation, net samples were standardized into an abundance scale. Abundance estimates were obtained by counting number of Dinophysis cells in three 0.1-ml aliquots. The abundance classification was performed from six ranges (Table 1) according to the abundance of this species in natural populations.
A Lugol-fixed aliquot of phytoplankton samples for toxin analysis (from February 2015) was collected to determine cell density under the light microscope using a Sedgewick-Rafter chamber. Between 20 and 30 images were taken from each station using a Leica DFC450C camera mounted on a Leica DM2500 microscope at the microscopy service of the Centro Nacional Patagonico (CENPAT)-CONICET. Lengths and widths of cells were determined using Leica Application Suite (LAS) V 4.5.0 Software. Species identification was performed using the morphological criteria proposed by Balech (1988).
Further selected samples were washed in distilled water, dried under air, and coated with gold. Scanning electron microscopy observations of the samples were made with a Jeol JSM-6360 LV scanning electron microscopy at the Facultad de Ciencias Naturales y Museo, Universidad Nacional de La Plata, and with Zeiss Supra 40 at the advanced microscopy center of the Universidad de Buenos Aires (UBA).
Filters were transferred into FastPrep vials and 700 [micro]L methanol were added. Samples were subsequently homogenized with 0.9 g of lysing matrix D by reciprocal shaking at maximum speed (6.5 m/sec) for 45 sec in a Bio 101 FastPrep instrument (Thermo Savant, Illkirch. France). After homogenization, samples were centrifuged at 16,100 x g at 4[degrees]C for 15 min. The supernatant was transferred to a spin-filter (0.45 pore size, Millipore Ultrafree, Eschborn, Germany) and centrifuged for 30 sec at 800 x g, followed by transfer to autosampler vials. Analysis of multiple lipophilic toxins was performed by liquid chromatography coupled to tandem mass spectrometry, as described in Krock et al. (2008).
A one-way analysis of variance was used to compare cell dimensions among stations using R (R Core Team 2012). The extent to which the positive results for DSP were correlated with relative abundances of Dinophysis tripos was evaluated by means of a Spearman's rank order correlation matrix using R (R Core Team 2012).
The positive results of the mouse bioassays are shown in Table 2 that also includes abundances of potentially toxic Dinophysis species present in the phytoplankton samples.
In 2009, a total of 121 samples were analyzed out of which 2 were found positive for DSP toxins; in 2010, 3 out of 55 samples were found positive; and in 2011, 2 out of 68 samples were found positive. The abundance of Dinophysis tripos was significantly correlated with positive results of the mouse bioassays (R = 0.23, P < 0.05). Despite the positive DSP results in 2009 and 2010, only in July 2011 the Subsecretaria de Pesca closed the harvest of molluscs due to DSP for the first time in Riacho. Before then the shellfish beds had been closed for harvesting annually only due to paralytic shellfish poisoning.
The administrative prohibition of harvesting of these shellfish species in Riacho was extended for a month until the results from mouse bioassays were negative again.
Relative Abundance and Cell Density of Dinophysis Species
The results of relative abundance analyses showed that the Dinophysis species most frequently found during the study period were Dinophysis tripos and Dinophysis acuminata. In addition. Dinophysis rotundata (Phalacroma rotundatum) Claparede and Lachmann was observed with lowest frequency at Larralde and Playa Parana (Fig. 2B. E) and Dinophysis caudata was only observed at Puerto Lobos (Fig. 2D).
Almost the whole year, Dinophysis tripos was observed at all stations with lower frequency at Riacho and Playa Parana. In Puerto Lobos, D. tripos had two clear abundance peaks in June and August 2010 and it was most frequently present (Fig. 2D). In autumn and winter, D. tripos was mainly present with abundances of 4 and 5 in the abundance scale (Fig. 2A, D).
The abundance of Dinophysis acuminata was very variable between years and months. They were observed most frequently at Larralde and with a lower frequency at Bengoa, Puerto Lobos, and Playa Parana. This species was present in spring and summer mainly, with an abundance of 3 in the abundance scale (Fig. 2B) and was exceptionally abundant in Riacho in autumn 2011 (Fig. 2C).
The results of cell density analyses showed that Dinophysis tripos appeared mainly at Puerto Lobos and Bengoa, in autumn and winter. At both stations, D. tripos reached high cell density, with maximum cell concentrations of 8,400 cells/l in Bengoa and 5,880 cells/l in Puerto Lobos. At Riacho, D. tripos was present with a high cell density of 6,720 cells/l, but was present just once (Fig. 3A).
In spring and summer, Dinophysis acuminata, however, appeared mainly at Larralde. In this station, D. acuminata reached the maximum cell concentration of 4,200 cells/l. In the remaining stations, D. acuminata was present sporadically (Fig. 3B).
Morphology and Cell Dimensions 0/Dinophysis spp. Associated with DSP
The analyzed cells of Dinophysis tripos, very distinctive species, showed morphological characteristics in agreement with the descriptions of Balech (2002) and Faust and Gulledge (2002). The cells are laterally compressed with a small, cap-like epitheca and a much larger hypotheca. The sizes of the cells are large, anterioposteriorly elongated and asymmetrical with two posterior hypothecal projections; a longer ventral process and a shorter dorsal one. Hypothecal projections with toothed posterior ends, and well-developed left sucal list widens posteriorly and reticulated. The thick thecal plates are heavily areolated (Fig. 4B).
The cells of Dinophysis tripos varied between 90 and 108 [micro]m in length and 41 and 58 [micro]m in dorsoventral depth with a length: width ratio of 1.98. Of the four analyzed sites, Bengoa only presents significant differences in maximal length (analysis of variance, P < 0.05; Table 3).
The morphological traits of analyzed cells agree with the descriptions of Faust and Gulledge (2002) and Balech (2002). Cells are small and somewhat oval shaped, with a convex dorsal margin (Fig. 4D). The thick thecal plates were covered with prominent circular areolae, each with a pore. The antapex is rounded, and cells had well developed small knob-shaped posterior protrusions (Fig. 4D).
The cell size varied between 39 and 44 [micro]m in length and 32-37 [micro]m in dorsoventral width, and the length:width ratio was 1.2.
Toxin Measurements and Species Distribution
Qualitative plankton samples from four different locations were taken in which Dinophysis cells were enumerated and lipophilic toxins were determined. The only two Dinophysis species detected were Dinophysis tripos and Dinophysis acuminata, the latter never exceeding 1.3% of total Dinophysis cells present in the samples. The toxin profiles in all four samples were very similar consisting mainly of PTX-2 followed by PTX-11 and PTX-2sa (Fig. 5). The highest amount of Dinophysis was found at Riacho, whereas the highest amount of PTX was detected at Playa Parana. The calculated total PTX cells quotas of the Dinophysis cells in these four samples range from 1.2 pg PTX per cell (Bengoa) to 3.8 pg PTX per cell (Larralde).
Shellfish Toxicity Associated with Dinophysis spp.
The intensification of Dinophysis tripos blooms in North Patagonian gulfs occurred in parallel with the confirmed presence of DSP toxins in shellfish. In July 2011. mussel and clam beds in Riacho were closed for harvesting due to positive results for DSP in the mouse bioassays, being the first shellfish harvesting closure due to the DSP toxins in the San Jose Gulf.
Mouse bioassays for DSP toxins gave positive results for San Jose and San Matias gulfs mainly in the austral autumn and winter months. Only one positive result was registered in spring. High abundances of Dinophysis tripos were registered usually in close temporal and spatial proximity to shellfish samples that contained DSP toxins. Only in one of these plankton samples in addition to D. tripos, low abundance of Dinophysis acuminata (less than 1.5% of total Dinophysis) was detected so that all positive results for DSP correlate with moderate to high relative abundances of D. tripos (Table 2). Thus, our data suggest that D. tripos was clearly associated with this DSP event. These results also suggest that high levels of DSP toxins in shellfish occur when D. tripos is highly abundant. This finding contradicts the report of Reguera et al. (2012) that mentions the absence of reports of DSP outbreaks associated with D. tripos or cases in which this species would have been the only potentially toxic Dinophysis species present in the microplankton community (Caroppo et al. 1999, Pazos et al. 2010). Our findings, however, strongly support the results of Fabro et al. (2015) who recorded the association between D. tripos and pectenotoxins in Argentine Sea. The co-occurrence of Dinophysis species and DSP toxins highlight the need of additional field studies as well as culture establishment to unambiguously elucidate the toxin profiles of D. tripos and D. acuminata in the South West Atlantic.
Distribution and Abundances of Dinophysis spp.
The species Dinophysis tripos has been reported to be widely distributed in tropical and warm-temperate waters, and occasionally found in colder areas (Larsen & Moestrup 1992) transported by warm-water currents, such as in the Norwegian Sea and subantarctic waters of the South Atlantic (Johnsen & Lomsland 2010). In the Argentine Sea, it is known to occur between 36[degrees] and 55[degrees] S (Balech 2002). But D. tripos has never been cited as the causative agent of DSP events when it was the only or the overwhelmingly dominant species of Dinophysis in the microphytoplankton (Reguera et al. 2014). In contrast, Dinophysis acuminata has been identified as the causative agent of DSP in Southern Brazil (Proenca et al. 2007) and, combined with Dinophysis caudata, in Uruguay (Mendez & Ferrari 2002) and Argentina (Sar et al. 2010). A coastal species, D. acuminata, has a strong negative impact on shell fisheries, because it is an early blooming species with a very long growing season (spring to autumn). This is the most cosmopolitan Dinophysis species associated with DSP events (Reguera et al. 2014).
Several Dinophysis species were reported in quantitative samples between the start of the monitoring program in 2000 and the study period of this work (2009 to 2011). For example, Dinophysis acuminata was registered in San Matias, San Jose, Nuevo, and San Jorge gulfs, and in Bahia Engano and Bahia Camarones being present in spring and summer mainly. In November 2007, D. acuminata reached a maximum cell density of 5 x [10.sup.3] cells/l in the San Jose Gulf. The species Dinophysis tripos has been detected in San Matias, San Jose, Nuevo, and San Jorge gulfs, and Bahia Engano throughout all seasons. It was recorded for first time in May 2007 with a cell density of 2 x [10.sup.3] cells/l (Puerto Lobos) and reached a maximum cell density of 8 x [10.sup.3] cells/l in August 2010 (Bengoa). With a highest cell density of 4 x [10.sup.2] cells/l, Dinophysis fortii was registered in January 2006 at the Puerto Madryn City. Two species, Dinophysis rotundata (Phalacroma rotundatum) and Dinophysis caudata, were not found in quantitative samples, although they were registered in qualitative samples in October 2005 (Caleta Malaspina) and February 2009 (Puerto Lobos), respectively (data unpublished).
At present, high densities of Dinophysis species are known to occur in North Patagonian gulfs. In fact, the blooms of Dinophysis tripos (8 X [10.sup.3] cells/1) and Dinophysis acuminata (5 X [10.sup.3] cells) mentioned above, constitute examples of the fact that they are the two most common and abundant Dinophysis species found in North Patagonian gulfs in the last decades. In addition, densities of these Dinophysis species increased from moderate to high (>1,000 cells/1) through the years. The other Dinophysis species we found in North Patagonian gulfs throughout our study period were Dinophysis caudata and Dinophysis rotwulata, although they occurred only sporadically and in low densities (Fig. 2B-E).
Abundances of Dinophysis tripos occurring throughout the year at all analyzed stations, suggest that temperature was not an important factor in determining the seasonal distribution of this species; although, highest abundances were detected in fall and winter (Fig. 2A, C. D). In contrast, the presence of Dinophysis acuminata is restricted mostly to spring and summer months (Fig. 2A-C). Abundances of D. acuminata were variable spatially and temporarily; however, the presence was higher at Larralde (Fig. 2B).
In the quantitative analyses high cell concentrations of Dinophysis tripos were found mainly in autumn and winter, but restricted mostly to Puerto Lobos and Bengoa (Fig. 3A). In contrast, Dinophysis acuminata was present with high cell concentrations in December, but it was infrequently at all stations (Fig. 3B). These results are in accordance with the results of relative abundance of both Dinophysis species.
These results showed that Dinophysis species only appeared sporadically in quantitative samples. There are two possible explanations for this finding: on one hand, the sporadic occurrence in quantitative plankton samples may be due to low cell densities, a common feature among Dinophysis spp., which makes it difficult to acquire accurate quantitative information and will often be associated with high counting errors (Reguera et al. 2012). On the other hand, it is known that populations of Dinophysis are aggregated in patches or in thin layers of the water column and thus may escape observation with conventional sampling methods (Escalera et al. 2012).
Morphological Characterization of Dinophysis spp.
The species identified through morphological analyses were Dinophysis tripos and Dinophysis acuminata. The length, width. and length: width ratio of the North Patagonian gulfs samples were well within the range of those reported globally for D. tripos and D. acuminata (Larsen & Moestrup 1992) (Table 3). The morphological characteristics of Dinophysis species were in accordance with those previously described by Balech (2002) and Faust and Gulledge (2002) (Fig. 4).
The shape of the cell in lateral view is the most important criterion used for identification of Dinophysis tripos (Taylor et al. 1995); however, the size and shape varies considerably in this species (Larsen & Moestrup 1992). Nevertheless, in the present study, cells of D. tripos did not exhibit the marked morphological variability as those observed by Rodriguez et al. (2012). They reported that besides the normal shape of D. tripos another two different forms, intermediate and small cells, are commonly observed. We found that all the analyzed cells had a dorsal projection and similar dimensions.
Toxin Profiles of Dinophysis tripos from Field Samples
In the present study, the toxin profiles of the plankton samples can be regarded to be with Dinophysis tripos, because the contribution of Dinophysis acuminata to the PTX profiles can be neglected in this case, as the maximum proportion of D. acuminata did not exceed 1.3% of total Dinophysis cells in any of the samples and no other PTX producer were present.
Fabro et al. (2015) found Dinophysis tripos to be mainly associated with PTX-2sa and to a lesser degree with PTX-2 and PTX-11, whereas our results show a clear association of D. tripos with PTX-2 and PTX-11, but we found only minor amounts of PTX-2sa in field planktonic samples. Taking into account that the samplings of Fabro et al. (2015) and of the present study took place in the same geographic region makes these results appear a contradiction. On the other hand, there are differences between both studies: Fabro et al. (2015) sampled in austral spring 2012 and fall 2013, whereas our samples originate from summer 2015. Furthermore, this study used samples from the San Jose and Nuevo Gulfs, whereas Fabro et al. (2015) sampled only outside theses gulfs, namely in the San Matias Gulf and along the Argentine coastline. Even though these small differences are not likely to explain different toxin profiles of the same species, it should be considered that PTX-2 and PTX-2sa are not independent compounds, but the lactone PTX-2 is easily hydrolyzed under low and high pH to form PTX-2sa. This is the reason why in bivalves mostly PTX-2sa is found, but hardly ever PTX-2. On the other side, in fresh planktonic samples containing Dinophysis spp. the most abundant variant normally is PTX-2. In this sense our data suggest that D. tripos in fact is a de novo producer of PTX-2, which is also consistent with the findings of Rodriguez et al. (2012). If hydrolysis of PTX-2 to PTX-2sa in D. tripos is due to factors such as environmental parameters or senescence remains to be investigated and clearly shows the need for the isolation and culture establishment of this species.
The species Dinophysis tripos could be identified as a PTX-producing species in North Patagonian gulfs, and thus most likely was responsible for positive DSP mouse bioassays in the region.
The PTX-2 production associated with Dinophysis tripos along the Chubut coast is in accordance with recent observations in the Argentine Sea as well as in other regions. Our study suggests that D. tripos blooms associated with the presence of DSP toxins in shellfish are becoming a recurrent phenomenon in the North Patagonian gulfs.
We would like to thank the Subsecretaria de Pesca and the Direccion de Salud Ambiental from Chubut Province for the data provided for this study and Patricia DellArciprete from Centro Nacional Patagonico for graphical assistance. We also thank Urban Tillmann for revising this manuscript.
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LEILEN GRACIA VILLALOBOS, (1) * NORMA SANTINELLI, (2) VIVIANA SASTRE, (2) BERND KROCK (3) AND JOSE LUIS ESTEVES (1)
(1) Centro Nacional Patagonico (CONICET), Boulevard Brown 2915, 9120 Puerto Madryn, Chubut, Argentina; (2)Facultad de Ciencias Naturales, Universidad Nacional de la Patagonia "San Juan Bosco", Julio Argentino Roca 115 1 piso, 9100 Trelew, Chubut, Argentina; (3)Alfred Wegener Institui-Helmholtz Zentrum fur Polar-und Meeresforschung, Chemische Okologie, Am Handelshafen 12, 27570 Bremerhaven, Germany
* Corresponding author. E-mail: email@example.com
TABLE 1. Abundance scales of Dinophysis species from net samples. Scales Cells/l Absent 0 0 Very scarce 1 1-10 Scarce 2 10-100 Frequent 3 100-1000 Abundant 4 1000-10000 Very abundant 5 >10000 TABLE 2. Positive results for DSP in the mouse bioassays and Dinophysis spp. concentration according to the abundance scale (Table 1). Dinophysis Dinophysis tripos acuminate Date Stations Shellfish abundance abundance 6/24/2009 Puerto Lobos Panopea 3 0 9/22/2009 Larralde Clams 3 2 7/22/2010 Puerto Lobos Panopea 4 0 7/22/2010 Riacho Scallops 4 0 7/22/2010 Bengoa Clams 4 0 7/7/2011 Riacho Clams 3 0 7/7/2011 Riacho Mussels 3 0 TABLE 3. Length (L) and dorsoventral depth (H) of the hypothecal plates of cells of Dinophysis tripos. Bengoa Larralde Riacho Playa Parana L range 89-105 93-108 95-108 94-106 H range 43-58 45-55 41-54 45-58 L average 97 101 100 100 H average 50 50 50 51 L:H average 1.96 2 1.91 1.96
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|Author:||Villalobos, Leilen Gracia; Santinelli, Norma; Sastre, Viviana; Krock, Bernd; Esteves, Jose Luis|
|Publication:||Journal of Shellfish Research|
|Date:||Dec 1, 2015|
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