Rapid detection of natural cells of Alexandrium tamarense and A. catenella (Dinophyceae) by fluorescence in situ hybridization

The marine toxic dinoflagellates Alexandrium tamarense (Lebor) Balech and A. catenella (Whedon and Kofoid) Taylor that cause paralytic shellfish poisoning (PSP) are identified on the basis of morphological features in routine monitoring. Rapid and simple identification is, however, often difficult because of the morphological similarity. Fluorescent in situ hybridization (FISH) using ribosomal RNA (rRNA)-targeted probes has been studied as a method of easily identifying and enumerating species responsible for harmful algal blooms (HABs). Its application to monitoring natural populations of HAB species, however, is limited. Here, we applied the FISH method to identify and enumerate cells of A. tamarense and A. catenella in natural plankton assemblages collected from Japanese coastal waters. A. tamarense-specific (Atm1) and A. catenella-specific (Act1) probes were established based on the D2 region of the large-subunit ribosomal RNA gene (28S rDNA). With these two probes, natural cells of A. tamarense or A. catenella in field samples could easily be identified when the following three conditions were met. First, cells should be concentrated by filtration, not centrifugation, in order to avoid the loss of cells. Second, autofluorescence should be minimized; acetone was an effective decolorization reagent. Third, samples should be stored at −20 or −80 °C for long-term preservation. The results indicate that FISH is a useful tool for the rapid identification of toxic Alexandrium spp. and can facilitate the analysis of numerous natural samples.     

Comparative studies on morphology, ITS sequence and protein profile of Alexandrium tamarense and A. catenella isolated from the China Sea

The Alexandrium tamarense species complex is a closely related cosmopolitan toxigenic group of morphology-based species, including A. tamarense, A. catenella and A. fundyense. This study investigated the morphology, internal transcribed spacer (ITS) sequence and protein profile of A. tamarense and A. catenella grown in the same culture conditions using a combination of scanning electronic microscope (SEM), molecular and proteomic approaches. The results showed that all Alexandrium strains had the plate formula of Po, 4′, 6″, 6C, 8S, 5″′, 2″″. The ventral pore, a key conventional morphological feature to discriminate A. tamarense and A. catenella, was usually present in the first apical plate of ten A. tamarense strains, however, it was found to be absent in some cells of one Alexandrium strain, ATGX01. A. tamarense and A. catenella shared an identical ITS sequence with a minor variation at intraspecific level. Protein profiles of A. catenella DH01 and A. tamarense DH01, isolated from the same region of the East China Sea, showed no significant difference, the similarity of protein profiles of the two species reached 99% with a few proteins unique to one or the other. The present results suggest that the ventral pore is not a consistent morphological feature in the Alexandrium genus, and that A. tamarense and A. catenella are conspecific and should be redesignated to one species.     

Quantification methods for Alexandrium catenella, a toxic dinoflagellate: Comparison of competitive enzyme-linked immunosorbent assay and sandwich hybridization integrated with a nuclease protection assay

Alexandrium catenella (Whedon et Kofoid) Balech, a toxic dinoflagellate, is a bloom-forming planktonic species in cold water coastal regions. It produces strong paralytic shellfish poisoning (PSP) toxins which are transmitted via tainted shellfish. These toxins can affect humans, other mammals, fish and birds. In this study, polyclonal antiserum against A. catenella was produced, and a competitive enzyme-linked immunosorbent assay (cELISA) was developed to detect A. catenella. The antiserum against A. catenella showed good specificity, the linear detection range was relatively large, between 38 and 600,000 cells. In addition, specific probes were designed to target the small subunit ribosomal RNA (SSU rRNA) of A. catenella, and quantitative sandwich hybridization integrated with a nuclease protection assay (NPA-SH) was established in order to identify and quantify A. catenella. The NPA-SH assay did not show good specificity as well as cELISA, by which A. catenella and A. tamarense could not be distinguished. Samples in different cell growth phases were analyzed with cELISA and NPA-SH. The results showed that the cell concentration calculated by cELISA was very similar with microscopy, while that of NPA-SH was sometimes higher than that of microscopy, especially in log phase. Comparing the two methods, both assays allow rapid identification of A. catenella without time-consuming microscopy when multiple sites need to be considered in routine monitoring. Meanwhile, cELISA was more specific and accurate in detection of A. catenella than NPA-SH.     

Probable origin and toxin profile of Alexandrium tamarense (Lebour) Balech from southern Brazil

The distribution of the toxic dinoflagellate Alexandrium tamarense Lebour has apparently expanded within the southern hemisphere during the last 2 decades. Toxic blooms of A. tamarense were recorded in Argentinean coastal waters since 1980; however, the first documented bloom in southern Brazil was in 1996. In this study, 13 strains of A. tamarense from southern Brazil were isolated and kept in culture. Phylogenetic analysis using RFLP and DNA sequences of the D1–D2 region of large subunit ribosomal DNA (rDNA) clearly indicates that Brazilian strains are most closely related to other South American strains. The strains from South America are placed firmly within a phylogenetic clade which contains strains from North America, northern Europe and northern Asia, previously called the North American clade. Possible dispersal hypotheses are discussed. The cultures were also analyzed for saxitoxin and its derivatives by high performance liquid chromatography (HPLC). The main saxitoxin groups found were the low toxicity N-sulfocarbamoyl group, C1, 2 (30–84%), followed by the high potency carbamate toxins, gonyautoxins 1, 4 (6.6–55%), gonyautoxins 2, 3 (0.3–29%), neosaxitoxin (1.4–24%) and saxitoxin (0–4.4%). The toxin composition is similar to that of other strains from South America, supporting a close relationship between A. tamarense from southern Brazil and other areas of South America. Toxicity values were variable (7.07–65.92 pg STX cell⁻¹), with the higher range falling among the most toxic values recorded for cultures of A. tamarense, indicating the significant risk for shellfish contamination and human intoxication during blooms of this species along the southern Brazilian coast.     

Phylogenetic relationship of Alexandrium tamiyavanichii (Dinophyceae) to other Alexandrium species based on ribosomal RNA gene sequences

The phylogenetic relationship of the thecate PSP-toxin producing dinoflagellate Alexandrium tamiyavanichii Balech to other species of Alexandrium was studied based on nucleotide sequences of the ITS1, ITS2, 5.8S, 18S and 28S subunits of the ribosomal RNA gene. These are the first such sequences available for A. tamiyavanichii, which is one of the producers of paralytic shellfish poisoning toxins in tropical waters. Based on the nucleotide sequences of the 28S, 18S and 5.8S subunits of the rRNA gene, A. tamiyavanichii grouped together with A. tamarense, A. catenella and A. fundyense. More interestingly, A. tamiyavanichii was most closely affiliated to A. tamarense isolates from Thailand. This result reaffirmed conclusions from previous studies that, for the A. tamarense/fundyense/catenella species complex, geographical origin rather than morphology seems to determine genetic relatedness. Results of this study also suggest that A. tamiyavanichii most probably belongs to the same species complex. Ribosomal RNA gene sequences do not separate the PSP toxin producing from the non-producing species of Alexandrium.     

Immunolocalization of theca antigens on Alexandrium catenella and their use to isolate cells from fixed phytoplankton samples

Murine monoclonal antibodies were generated and selected for their ability to specifically recognize theca antigens of Alexandrium catenella (Whedon et Kafoid) Balech cells. The specificity of the monoclonal antibodies for theca antigens was shown by indirect immunofluorescence and by confocal microscopic analysis. Using these antibodies we demonstrate, for the first time, the presence of different theca antigens on the cell surface. The fluorescent signal analysis suggests that these antigens differ in their distribution and quantities in the theca.Also, using the antibodies we developed a rapid method to isolate A. catenella cells from a lugol-fixed phytoplanktonic sample. The method uses a mixture of different monoclonal antibodies to bind the cells, which then are pulled off from the sample by means of a second anti-mouse antibody coupled to 0.8 μm magnetic beads.     

Molecular quantification of toxic Alexandrium fundyense in the Gulf of Maine using real-time PCR

The toxic dinoflagellate Alexandrium fundyense is widespread in the northeastern part of North America, including the Gulf of Maine, and is responsible for seasonal harmful algal blooms in these regions. Even at low cell densities, A. fundyense toxins can accumulate in shellfish and result in paralytic shellfish poisoning (PSP). PSP can be debilitating or lethal to humans and other shellfish consumers and is a public health concern. As a result, accurate measurements of A. fundyense distributions, particularly at low cell density, are critical to continued PSP monitoring and mitigation efforts. Towards this end we have developed a real-time quantitative PCR (qPCR) method to monitor A. fundyense. Laboratory validation indicates that the qPCR assay is sensitive enough to detect 10 cells per sample, and that it does not detect co-occurring dinoflagellates such as Alexandrium ostenfeldii. The qPCR methodology was used to quantify A. fundyense cell densities in samples collected during a spring 2003 transect in the Gulf of Maine, and the data were compared to those obtained in parallel from light microscope and DNA hybridization-based methods. Results show that A. fundyense cell density was low during this period relative to typical cell densities required for PSP contamination of local shellfish, and that qPCR values were comparable to numbers determined by independent methods.     

First report of Alexandrium taylori and Alexandrium peruvianum (Dinophyceae) in Malaysia waters

The occurrence of Alexandrium taylori and Alexandrium peruvianum is reported for the first time in Malaysia waters. The Malaysian A. taylori isolates were pyriform in shape with a transdiameter range of 36–40 μm and a cell length range of 33–37 μm. The first apical plate (1′) was pentagonal with two distinctive anterior margins. No direct connection between 1′ and the apical pore complex was observed. The posterior sulcal plate (S.p.) was large, elongated and oblique to the right with anterior projections. The ventral pore (vp) was relatively large and situated at a confluence point of 1′, the second apical (2′) and the fourth apical (4′) plates. Cells of A. peruvianum were slightly anteriorly and posteriorly compressed. S.p. had an irregular pentagonal shape, with the anterior margin divided into 2 portions. 1′ was boomerang-shaped with a large and truncated ventral pore in the middle right margin. The anterior right margin of 1′ was straight. The sixth precingular plate (6″) was wider than long. The anterior sulcal plate (S.a.) was triangular and lacked a left portion extension. In laboratory cultures, both A. taylori and A. peruvianum produced paralytic shellfish toxins, with GTX4 and GTX6 as the predominant toxin, respectively. This is the first report of PSP toxins production for both species as well as the occurrences in Malaysia waters.     

The toxigenic marine dinoflagellate Alexandrium tamarense as the probable cause of mortality of caged salmon in Nova Scotia

The toxins associated with paralytic shellfish poisoning (PSP) are potent neurotoxins produced by natural populations of the marine dinoflagellate Alexandrium tamarense. In early June 2000, a massive bloom (>7×10⁵ cells l⁻¹) of this dinoflagellate coincided with an unusually high mortality of farmed salmon in sea cages in southeastern Nova Scotia. Conditions in the water column in the harbour were characterised by the establishment of a sharp pycnocline after salinity stratification due to abundant freshwater runoff. In situ fluorescence revealed a high sub-surface (2–4 m depth) chlorophyll peak related to the plankton bloom. The intense bloom was virtually monospecific and toxicity was clearly related to the concentration of Alexandrium cells in plankton size fractions. Cultured clonal isolates of A. tamarense from the aquaculture sites were very toxic on a per cell basis and yielded a diversity of PSP toxin profiles, some of which were similar to those from plankton concentrates from the natural bloom population. The toxin profile of plankton concentrates from the 21–56 μm size fraction was complex, dominated by the N-sulfocarbamoyl derivative C2, with levels of other PSP toxins GTX4, NEO, GTX5 (=B1), GTX3, GTX1, STX, C1, and GTX2, in decreasing order of relative abundance. Although no PSP toxin was found systemically in the fish tissues (liver, digestive tract) from this salmon kill event, the detection of Alexandrium cells and low levels of PSP toxins in salmon gills provide evidence that the enhanced mortalities were caused by direct exposure to toxic Alexandrium cells and/or to soluble toxins released during the bloom.     

Experimental study on the impact of dinoflagellate Alexandrium species on populations of the rotifer Brachionus plicatilis

To investigate harmful effects of the dinoflagellate Alexandrium species on microzooplankton, the rotifer Brachionus plicatilis was chosen as an assay species, and tested with 10 strains of Alexandrium including one known non-PSP-producer (Alexandrium tamarense, AT-6). HPLC analysis confirmed the PSP-content of the various strains: Alexandrium lusitanicum, Alexandrium minutum and Alexandrium tamarense (ATHK, AT5-1, AT5-3, ATCI02, ATCI03) used in the experiment were PSP-producers. No PSP toxins were detected in the strains Alexandrium sp1, Alexandrium sp2.Exposing rotifer populations to the densities of 2000 cells ml⁻¹ of each of these 10 Alexandrium strains revealed that the (non-PSP) A. tamarense (AT-6) and two other PSP-producing algae: A. lusitanicum, A. minutum, did not appear to adversely impact rotifer populations. Rotifers exposed to these three strains were able to maintain their population numbers, and in some cases, increase them. Although some increases in rotifer population growth following exposures to these three algal species were noted, the rate was less than for the non-exposed control rotifer groups.In contrast, the remaining seven algal strains (A. tamarense ATHK, AT5-1, AT5-3, ATCI02, ATCI03; also Alexandrium sp1 and Alexandrium sp2) all have adverse effects on the rotifers. Dosing rotifers with respective algal cell densities of 2000 cells ml⁻¹ each, for Alexandrium sp1, Alexandrium sp2, and A. tamarense strains ATHK and ATCI03 showed mean lethal time (LT₅₀) on rotifer populations of 21, 28, 29, and 36h, respectively. The remaining three species (A. tamarense strains AT5-1, AT5-3, ATCI02) caused respective mean rotifer LT₅₀s of 56, 56, and 71 h, compared to 160 h for the unexposed “starved control” rotifers. Experiments to determine ingestion rates for the rotifers, based on changes in their Chlorophyll a content, showed that the rotifers could feed on A. lusitanicum, A. minutum and A. tamarense strain AT-6, but could graze to little or no extent upon algal cells of the other seven strains. The effects on rotifers exposed to different cell densities, fractions, and growth phases of A. tamarense algal culture were respectively compared. It was found that only the whole algal cells had lethal effects, with strongest impact being shown by the early exponential growth phase of A. tamarense. The results indicate that some toxic mechanism(s), other than PSP and present in whole algal cells, might be responsible for the adverse effects on the exposed rotifers.     

Toxin profile of Alexandrium catenella from the Chilean coast as determined by liquid chromatography with fluorescence detection and liquid chromatography coupled with tandem mass spectrometry

The profile of tetrahydropurine neurotoxins associated with paralytic shellfish poisoning (PSP) was determined from a Chilean strain of the marine dinoflagellate Alexandrium catenella. The toxin composition was compared with that of toxic shellfish, presumably contaminated by natural blooms of A. catenella from the same region in southern Chile. Ion pair-liquid chromatography with post-column derivatization and fluorescence detection (LC-FD) was employed for relative quantitative analysis of the toxin components, whereas unambiguous identification of the toxins was confirmed by tandem mass spectrometry (LC–MS/MS). In the dinoflagellate strain from Chile, the N-sulfocarbamoyl derivatives (C1/C2, B1) and the carbamoyl gonyautoxins GTX1/GTX4 comprise >90% of the total PSP toxin content on a molar basis. This toxin composition is consistent with that determined for A. catenella populations from the Pacific coast in the northern hemisphere. The characteristic toxin profile is also reflected in the shellfish, but with evidence of epimerization and metabolic transformations of C1 and C2 to GTX2 and GTX3, respectively. This work represents the first unequivocal identification and confirmation of such PSP toxin components from the Chilean coast.     

Alexandrium (Dinophyceae) species in Malaysian waters

A study was carried out to determine the presence of paralytic shellfish poisoning (PSP) toxin-producing dinoflagellates in the coastal waters of Peninsula Malaysia. This followed first ever occurrences of PSP in the Straits of Malacca and the northeast coast of the peninsula. The toxic tropical dinoflagellate Pyrodinium bahamense var. compressum was never encountered in any of the plankton samples. On the other hand, five species of Alexandrium were found. They were Alexandrium affine, Alexandrium leei, Alexandrium minutum, Alexandrium tamarense and Alexandrium tamiyavanichii. Not all species were present at all sites. A. tamiyavanichii was present only in the central to southern parts of the Straits of Malacca. A. tamarense was found in the northern part of the straits, while A. minutum was only found in samples from the northeast coast of the peninsula. A. leei and A. affine were found in both the north and south of the straits. Cultured isolates of A. minutum and A. tamiyavanichii were proven toxic by the receptor binding assay for PSP toxins but A. tamarense clones were not toxic. Mean toxin content for the A. tamiyavanichii and A. minutum clones were 26 and 15 fmol per cell STX equivalent, respectively. This study has provided evidence on the presence of PSP toxin-producing Alexandrium species in Malaysian waters which suggests that PSP could increase in importance in the future.     

Molecular identification of toxic Alexandrium tamiyavanichii (Dinophyceae) using two DNA probes

To improve labeling-intensity of whole-cell fluorescence in situ hybridization (FISH) in the molecular identification of toxic Alexandrium tamiyavanichii, two DNA probes (TAMID2 plus TAMIS1 designed from the LSU and SSU rDNA regions, respectively) were used to test the labeling intensity of targeted cultured A. tamiyavanichii cells. The cross-reactivity of the DNA probe to natural seawater samples and six Alexandrium species: A. affine, A. catenella, A. fraterculus, A. insuetum, A. pseudogonyaulax and A. tamarense, was also tested. The labeling intensity of the DNA probe TAMID2S1, a combination of two separate probes that target different regions of the rRNA, was 1.7–2.7 times higher than that of the single DNA probe TAMID2. With cultured A. tamiyavanichii cells in the dead growth phase at 30 days, the TAMID2S1 intensity was 1.9 times higher than that of TAMID2. During a 30-day culture, the labeling intensity of A. tamiyavanichii cells hybridized with TAMID2S1 decreased to 49.4% of the original intensity. No cross-reactivity to various microorganisms in natural seawater samples was found. The two DNA probes together, designated as TAMID2S1, readily detected A. tamiyavanichii added to natural seawater samples, even aged cultured cells.     

Molecular cloning and nucleotide sequence analysis of psbA from the dinoflagellates: Origin of the dinoflagellate plastid

Cloning and sequencing of psbA, the gene encoding D1 protein of photosystem II, from six species of dinoflagellates harboring a peridinin type plastid [Prorocentrum micans Ehrenberg, Amphidinium carterae Hulburt, Heterocapsa triquetra Stein, Lingulodinium polyedra (Dodge) Stein, Alexandrium tamarense (Lebour) Balech and Alexandrium catenella (Whedon et Kofoid) Balech] is reported. Using the polymerase chain reaction technique, the psbA gene was detected in a satellite DNA band isolated from total DNA of A. catenella by CsCl-Hoechst 33258 gradient ultracentrifugation. This finding suggests that in dinoflagellates psbA is encoded in the plastid genome. The deduced amino acid sequences of D1 from the dinoflagellates did not reveal a typical ‘C-terminus extension’, which should be removed by proteolytic cleavage from the D1 precursor. Molecular phylogenetic analysis based on the deduced amino acid sequences of D1 revealed that the six species of dinoflagellates are monophyletic and also showed that dinoflagellates cluster with rhodophytes, a cryptophyte and heterokonts. These results support the hypothesis that the peridinin type plastid in dinoflagellates originated from an engulfed red alga.     

Morphogenetic diversity and biotoxin composition of Alexandrium (Dinophyceae) in Irish coastal waters

The diversity of Alexandrium spp. in Irish coastal waters was investigated through the morphological examination of resting cysts and vegetative cells, the determination of PSP toxin and spirolide profiles and the sequence analysis of rDNA genes. Six morphospecies were characterised: A. tamarense, A. minutum, A. ostenfeldii, A. peruvianum, A. tamutum and A. andersoni. Both PSP toxin producing and non-toxic strains of A. tamarense and A. minutum were observed. The average toxicities of toxic strains for both cultured species were respectively 11.3 (8.6 S.D.) and 2.3 (0.5 S.D.) pg STX equiv. cell⁻¹. Alexandrium ostenfeldii and A. peruvianum did not synthesise PSP toxins but HPLC–MS analysis of two strains showed distinct spirolide profiles. A cyst-derived culture of A. peruvianum from Lough Swilly mainly produced spirolides 13 desmethyl-C and 13 desmethyl-D whereas one of A. ostenfeldii, from Bantry Bay, produced spirolides C and D. Species identification was confirmed through the analyses of SSU, ITS1-5.8S-ITS2 and LSU rDNA genes. Some nucleotide variability was observed among clones of toxic strains of A. tamarense, which all clustered within the North American clade. However, rDNA sequencing did not allow discrimination between the toxic and non-toxic forms of A. minutum. Phylogenetic analysis also permitted the differentiation of A. ostenfeldii from A. peruvianum. Resting cysts of PSP toxin producing Alexandrium species were found in Cork Harbour and Belfast Lough, locations where shellfish contamination events have occurred in the past, highlighting the potential for the initiation of harmful blooms from cyst beds. The finding of supposedly non-toxic and biotoxin-producing Alexandrium species near aquaculture production sites will necessitate the use of reliable discriminative methods in phytoplankton monitoring.     

A comparative study on recurrent blooms of Alexandrium minutum in two Mediterranean coastal areas

Alexandrium minutum is a toxic dinoflagellate widespread along the Mediterranean coasts. This species is frequently detected year-round at low concentrations within the Mediterranean basin. However, it only proliferates recurrently in some localities. Two affected areas are the Catalan and Sicilian coasts. In order to identify the factors determining the A. minutum blooms in the Mediterranean Sea, we compare the bloom conditions in two harbours: Arenys de Mar (Catalan coast, Spain) and Syracuse (Sicily, Italy), during 2002–2003. Arenys de Mar harbour is a fishing and leisure harbour and receives an input of freshwater rich in nutrients. Likewise, the Syracuse harbour – located on the Ionian coast of Sicily – is subject to freshwater inputs. Some points of this site are used for productive activities such as shellfish farming. A. minutum from the two areas studied were morphologically and genetically identical. In both sites, recurrent blooms take place from winter to spring. Surface water temperatures and salinities during A. minutum bloom events were 12–14.5 °C and 32–38, and 16–24 °C and 32–37.7 for Arenys and Syracuse, respectively. During the blooms, the spatial distribution of A. minutum in the two harbours, the physicochemical characteristics and the phytoplankton community were studied. Similarities in composition of the phytoplankton community were evidenced, with a clear dominance of dinoflagellates over the other taxa. In Arenys, the second dominant species was Prorocentrum micans followed by Scrippsiella spp. and Dinophysis sacculus. The same species were found in Syracuse although P. triestinum, and alternatively Lingulodinium polyedrum, reached cell densities much higher than the other dinoflagellates giving marked water discolourations.     

Phylogeny, biogeography, and species boundaries within the Alexandrium minutum group

The geographic range and bloom frequency of the toxic dinoflagellate Alexandrium minutum and other members of the A. minutum group have been increasing over the past few decades. Some of these species are responsible for paralytic shellfish poisoning (PSP) outbreaks throughout the world. The origins of new toxic populations found in previously unaffected areas are typically not known due to a lack of reliable plankton records with sound species identifications and to the lack of a global genetic database. This paper provides the first comprehensive study of minutum-group morphology and phylogeny on a global scale, including 45 isolates from northern Europe, the Mediterranean, Asia, Australia and New Zealand.Neither the morphospecies Alexandrium lusitanicum nor A. angustitabulatum was recoverable morphologically, due to large variation within and among all minutum-group clonal strains in characters previously used to distinguish these species: the length:width of the anterior sulcal plate, shape of the 1′ plate, connection between the 1′ plate and the apical pore complex, and the presence of a ventral pore. DNA sequence data from the D1 to D2 region of the LSU rDNA also fail to recognize these species. Therefore, we recommend that all isolates previously designated as A. lusitanicum or A. angustitabulatum be redesignated as A. minutum. A. tamutum, A. insuetum, and A. andersonii are clearly different from A. minutum on the basis of both genetic and morphological data.A. minutum strains from Europe and Australia are closely related to one another, which may indicate an introduction from Europe to Australia given the long history of PSP in Europe and its recent occurrence in Australia. A minutum from New Zealand and Taiwan form a separate phylogenetic group. Most strains of A. minutum fit into one of these two groups, although there are a few outlying strains that merit further study and may represent new species. The results of this paper have greatly improved our ability to track the spread of A. minutum species and to understand the evolutionary relationships within the A. minutum group by correcting inaccurate taxonomy and providing a global genetic database.     

Intracellular damage and death caused by protease inhibitors on Alexandrium catenella natural cysts and vegetative cells

Proteases from a Chilean clone of Alexandrium catenella were studied using gelatin–zymogram gel and protease fluorescent substrate to facilitate their visual identification in vitro and in vivo, respectively. Proteolytic activity bands were grouped arbitrarily according to their molecular weight as P1 (150 and 120 kDa), P2 (100 kDa), P3 (70 and 65 kDa), P4 (60, 55 and 50 kDa) and P5 (25 kDa). Protease inhibitors affect differentially P2 and P3 proteases. Only P2 activity increased in the presence of 1–10 phenanthroline (σPhe), pepstatin A (pepA), leupeptin (leup) and phenylmethanesulfonyl fluoride (PMSF), while P2 and P3 become inactivated with ρ-aminobenzamidine. The protease inhibitors lethal dose was determined by incubating cells with different concentration of the protease inhibitor and evaluating their effect on cell viability. Furthermore, cells treated for 4 h with one lethal dose of 1–10 phenanthroline and ρ-aminobenzamidine, caused serious damage to the intracellular vacuolar system and nuclear material. Live cysts also die when treated independently with these two protease inhibitors. Future work will be aimed at chemically designing species-specific inhibitors for their potential use in killing cysts transported within the sediment of ship ballast water before washing them off to the environment.     

Geographic differences in paralytic shellfish poisoning toxin profiles among Japanese populations of Alexandrium tamarense and A. catenella (Dinophyceae)

To reconsider whether toxin profile could be used as a marker for populations from different geographical areas, clonal isolates of the toxic dinoflagellates Alexandrium tamarense (Lebour) Balech and Alexandrium catenella (Whedon et Kofoid) Balech from Ofunato Bay (Iwate Prefecture), Atsumi Bay (Aichi Prefecture), Tanabe Bay (Wakayama Prefecture), Harima‐Nada (Kagawa Prefecture), Uranouchi Bay (Kochi Prefecture), Hiroshima Bay (Hiroshima Prefecture) and Yamakawa Bay (Kagoshima Prefecture), which were identified on the basis of morphotaxonomy, immunological and molecular biological techniques, were subjected to analysis of paralytic shellfish poisoning toxins by high performance liquid chromatography‐fluorometric method. All the isolates except A. tamarense OF152 from Ofunato Bay contained mainly N‐sulfocarbamoyl toxins (C1 +2) with various amounts of derivatives, and a typical north‐to‐south trend of decreasing toxicity was observed. In both A. tamarense and A. catenella, toxin profiles were rather constant within a geographical area and divergent among different geographical areas. The toxin profiles of A. tamarense from Harima‐Nada were well conserved among different bloom years. Toxin profile showed that isolates of A. tamarense from Ofunato Bay, A. tamarense from Harima‐Nada isolated in 1988 and A. catenella from Uranouchi Bay were heterogeneous. However, only two or three groups of isolates with different toxin profiles were observed in a geographical region, suggesting that several representative isolates express the genotype in a given region. These observations confirmed that toxin composition could be used as a marker to discriminate different geographical populations of these species.