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A new pectenotoxin, which has been named pectenotoxin-11 (PTX11), was isolated from the dinoflagellate Dinophysis acuta collected from the west coast of New Zealand. The structure of PTX11 was determined as 34S-hydroxypectenotoxin-2 by tandem mass spectrometry and UV and NMR spectroscopy. PTX11 appears to be only the third pectenotoxin identified as a natural biosynthetic product from algae after pectenotoxin-2 and pectenotoxin-12. The LD50 of PTX11 determined by mouse intraperitoneal injection was 244 microg/kg. The LD(min) of PTX11 in these experiments was 250 microg/kg. No signs of toxicity were recorded in mice following an oral dose of PTX11 at 5000 microg/kg. No diarrhea was observed in any of the animals administered with the test substance by either route of administration. Unlike pectenotoxin-2 (PTX2), PTX11 was not readily hydrolyzed to its corresponding seco acid by enzymes from homogenized green-lipped mussel (Perna canaliculus) hepatopancreas.

In laboratory experiments, oysters ( Crassostrea virginica ) were fed Alexandrium fundyense (strain CB501) vegetative cells or resting cysts (from strains CB501 and GMT25) produced from laboratory cultures. The toxicity per cyst was 1.7 pg STXequiv/cyst and for vegetative cells 3.9 pg STXequiv/cell. The toxic, resting cysts and vegetative cells were removed from suspension in the experimental containers within about 4 h. Oysters fed toxic vegetative cells digested 72% of cells ingested, and 28% survived gut passage by forming temporary cysts. Toxin levels of oysters fed vegetative cells averaged 27 μg STXequiv/100 g meat. Resting cysts added to the experimental containers adhered to the walls so that only 40% of the cysts added were available to the oysters during the experiment. Of the cysts that were ingested, approximately 59% were digested, and oysters accumulated toxins (an average of 1.2 μg STXequiv/100 g meat), showing that consumption of resting cysts can cause toxicity in oysters. Direct consumption of resting cysts, thus, may explain shellfish toxicity in areas without known blooms, but with toxic resting cysts in the sediment. These results suggest a possible role of toxic cysts in mediating time-lags between surface blooms and appearance of toxicity in benthic grazers, and the possible role of benthic grazers in controlling seed populations, except in anoxic areas, which can serve as cyst “refuges” from grazing mortality.

Dinophysis acuminata and D. norvegica were observed in plankton net samples during the summer of 2002 from the Kandalaksha Gulf in the White Sea (North European Russia). Prorocentrum lima was found as an epiphyte on subtidal macroalgae in August, but not observed in plankton net samples. Protein phosphatase 2A (PP2A) inhibition measured 127.8 ng OA-equivalent/g of mussel ( Mytilus edulis ) hepatopancreas from samples collected a few days after when Dinophysis was recorded at a density of 1550 cells L −1 . Liquid chromatography–mass spectrometry confirmed presence of several classes of lipophilic shellfish toxins associated with Dinophysis spp. in the mussels including okadaic acid, dinophysistoxin-1, pectenotoxins and yessotoxins. No azaspiracid was detected. This represents the first identification of phycotoxicity in the White Sea.

The toxin load of shellfish hepatopancreas harvested from the Caucasian Black Sea Coast of the Russian Federation was investigated. The majority of the toxin load was shown to be yessotoxin (YTX), 45-hydroxy-yessotoxin (45-OH-YTX), and homoyessotoxin (homoYTX). Concurrent with the mussel intoxication, the dinoflagellates Lingulodinium polyedrum and Gonyaulax spinifera were found in high concentrations.

Using LC/MS methodology, spirolides were detected in two clonal isolates of Alexandrium ostenfeldii isolated from Limfjorden, Denmark. Examination of the LC/MS profiles of extracts from these Danish cultures revealed the presence of two dominant peaks representing two previously unidentified spirolide components and one minor peak identified as the previously reported desmethyl spirolide C (1). Culturing of these clonal strains, LF 37 and LF 38, of A. ostenfeldii resulted in the accumulation of sufficient cell biomass to allow for the isolation and structure elucidation of two new spirolides, 13,19-didesmethylspirolide C (2) and spirolide G (3). While 2 was found to differ from 1 only in that it contained one less methyl group, 3 was the first spirolide to be isolated that contained a 5:6:6-trispiroketal ring system. The effect of this new feature on the toxicity of 3 relative to other spirolides is presently being pursued.

Cultured mussels sampled in the spring of 2002 and 2003 from Skjer, a location in the Sognefjord, Norway, tested positive in the mouse bioassay for lipophilic toxins. In a previous report, it was established that a number of spirolides, cyclic imine toxins produced by the phytoplankton Alexandrium ostenfeldii, were present in the mussels and were responsible for the observed toxicity. The main toxin proved to be a new compound named 20-methyl spirolide G. In subsequent studies, a delayed onset of spirolide-like symptoms in the mouse bioassay exceeding the usual time limit of 20 min was observed in some samples, with symptoms and death appearing as long as 45–50 min after injection. It is well known that shellfish can extensively metabolize other toxins, such as okadaic acid and the dinophysistoxins, to fatty acid acyl esters and it is also known that a delayed onset of toxic symptoms with such metabolites can occur. Analyses performed with liquid chromatography/tandem mass spectrometry (LC/MS/MS) have revealed a complex mixture of esters of 20-methyl spirolide G in the contaminated mussels. Precursor ion scanning has delineated the range of fatty acid esters involved, while product ion scanning has provided information on structure. Identity was also supported through reaction of 20-methyl spirolide G with palmitic anhydride, which produced a derivative with a retention time and spectrum identical with one putative metabolite, 17-O-palmitoyl-20-methyl spirolide G. Copyright © 2006 Crown in the right of Canada. Published by John Wiley & Sons, Ltd.

A rapid multiple toxin method based on liquid chromatography with mass spectrometry (LC/MS) was developed for the detection of okadaic acid (OA), dinophysistoxin-1 (DTX-1), DTX-2, yessotoxin (YTX), homoYTX, 45-hydroxy-YTX, 45-hydroxyhomo-YTX, pectenotoxin-1 (PTX-1), PTX-2, azaspiracid-1 (AZA-1), AZA-2, and AZA-3. Toxins were extracted from shellfish using methanol-water (80%, v/v) and were analyzed using a C8 reversed-phase column with a 5 mM ammonium acetate-acetonitrile mobile phase under gradient conditions. The method was validated for the quantitative detection of OA, YTX, PTX-2, and AZA-1 in 4 species (mussels, Mytilus edulis; cockles, Cerastoderma edule; oysters, Crassostrea gigas; king scallop, Pecten maximus) of shellfish obtained from United Kingdom (UK) waters. Matrix interferences in the determination of the toxins in these species were investigated. The validated linear range of the method was 13-250 microg/kg for OA, PTX-2, and AZA-1 and 100-400 microg/kg for YTX. Recovery and precision ranged between 72-120 and 1-22%, respectively, over a fortification range of 40-160 microg/kg for OA, PTX-2, and AZA-1 and 100-400 microg/kg for YTX. The limit of detection, reproducibility, and repeatability of analysis showed acceptable performance characteristics. A further LC/MS method using an alkaline hydrolysis step was assessed for the detection of OA, DTX-1, and DTX-2 in their esterified forms. In combination with the LC/MS multiple toxin method, this allows detection of all toxin groups described in Commission Decision 2002/225/EC.

Alexandrium cf. tamarense was recorded for the first time along the north-eastern coast of the Black Sea in July 2001. Since then, it has been observed annually between May and October. A maximum density of Alexandrium spp. of 9 000 cells l–1 was recorded during August 2004. Examination of the Black Sea Alexandrium spp. by scanning electron microscopy showed both A. tamarense and A. minutum to be present. Monitoring during 2000–2004 included the collection of mussel hepatopancreas samples and subsequent analysis for paralytic shellfish poisoning (PSP) toxins. A receptorbinding assay showed a maximum value of 14ìg STXdiHCl equivalents 100g–1 tissue to correspond to ambient concentrations of A. tamarense of 300 cells l–1. Analysis of the PSP toxins by liquid chromatography with fluorescence detection showed the presence of GTX2, GTX3 and GTX5 in mussel hepatopancreas extracts. PSP in humans has not been reported in the Black Sea region of Russia. Nevertheless, the presence of Alexandrium spp. and of PSP toxins in shellfish are compelling reasons for the introduction of phycotoxin control methods and monitoring in Russian waters.

Hydrophilic interaction liquid chromatography (HILIC) was examined for the separation of paralytic shellfish poisoning (PSP) toxins using the stationary phase TSK-gel Amide-80®. The parameters tested included type of organic modifier and percentage in the mobile phase, buffer concentration, pH, flow rate and column temperature. Using mass spectrometric (MS) detection, the HILIC column allowed the determination of all the major PSP toxins in one 30 min analysis with a high degree of selectivity and sensitivity. The high percentage of organic modifier in the mobile phase and the omission of ion pairing reagents, both favored in HILIC, provided limits of detection (LOD) in the range 50–1000 nM in selected ion monitoring (SIM) mode on a single quadrupole LC–MS system. LOD in selected reaction monitoring (SRM) mode on a sensitive triple quadrupole system were as low as 5–30 nM. Excellent linearity of response was observed.

Mussels sampled in the spring of 2002 and 2003 from Skjer, a location in Sognefjord, Norway, tested positive in the mouse bioassay for lipophilic toxins. The symptoms, which included cramps, jumping, and short survival times (as low as 4 min), were not characteristic of toxins previously observed in Norway. A survey of the algae present at the aquaculture sites showed that the toxicity correlated with blooms of Alexandrium ostenfeldii. Up to 2200 cells/L were found at the peak of one bloom. In Canadian waters, this alga is known to be a producer of the cyclic imine toxins, spirolides. Analysis of mussel extracts from Skjer in the spring of 2002 and 2003, using liquid chromatography tandem mass spectrometry, revealed the presence of several new spirolides. The same compounds were also found in algal samples dominated by A. ostenfeldii, which had been sampled from Skjer in February 2003. A large-scale extraction of mussel digestive glands and chromatographic fractionation of the extracts allowed the isolation and structure elucidation of the main spirolide, 20-methyl spirolide G, with a molecular weight of 705.5. This is the first confirmed occurrence of spirolides in mussels and plankton from Norway.

Alexandrium ostenfeldii is a thecate, mixotrophic dinoflagellate recently linked to a novel suite of toxins called spirolides. This study provides the first description of the regional distribution of A. ostenfeldii in the Gulf of Maine (GOM), and the first report and analysis of spirolide toxicity in A. ostenfeldii in waters south of Nova Scotia. Morphological examination of cells in field samples and of clonal cultures isolated from several stations in the GOM confirmed the presence of A. ostenfeldii. A genus-specific antibody probe, and an A. ostenfeldii species-specific oligonucleotide probe labeled these cells; a probe specific for the North American A. fundyense/tamarense/catenella species complex did not label A. ostenfeldii cells. Cell size ranged from 20 to nearly 90 μm, and most cells contained food vacuoles, with a total vacuole size from 1 to 48 μm. The hydrographic forcings controlling the distribution of A. ostenfeldii in the GOM are quite similar to those acting on the A. fundyense population at the same time of the year. The highest concentrations of A. ostenfeldii were observed nearshore, to the east of Penobscot Bay, at times with an offshore-turning branch of high cell concentration to the south of Penobscot Bay. Casco Bay appears to be an area of accumulation for A. ostenfeldii cells advected toward shore from the core of the population to the northeast. Concentrations of A. ostenfeldii were generally higher at the surface than deeper, except at locations where the pooling of lower-salinity water at the surface may have led to the subduction of the population flowing in from the east. PSP toxins were detected in field populations containing A. ostenfeldii and A. fundyense , but not in A. ostenfeldii cultures isolated from the GOM. Spirolide toxins were found in 36 of 60 field samples. More than 83% of samples containing A. ostenfeldii cells had one or more of spirolide congeners A, B, C2 and D2. The total concentration of spirolides per cell at each station where A. ostenfeldii was detected ranged from non-detectable to 282 fmol cell −1 . A. ostenfeldii cultures originating from different locations showed a great diversity in spirolide content and composition. All cultures contained spirolides, ranging from 28 to 113 fmol cell −1 . Spirolide congeners desMeC, C and D were present in some cultures, but were not detected in any of the field samples. Based on differences and similarities between their toxin profiles, five toxin phenotypes were identified. The highest per cell spirolide contents in the cultures were nearly two times lower than the highest levels observed in field samples. Currently there is no routine monitoring for spirolide toxins in shellfish in the region, but it may be necessary eventually to expand ongoing toxin monitoring in the GOM to include analysis for spirolides.

Two novel pectenotoxins (PTXs) were detected by LC-MS in solid phase extracts of net hauls taken at Flodevigen, Norway, in June 2002 that were dominated by Dinophysis acuminata and Dinophysis norvegica. The new compounds were isolated as minor components from a large collection of a Dinophysis acuta-dominated bloom obtained from Skjer, Sognefjorden, Norway, in October 2002. LC-MS and NMR analyses revealed that the new components, 36S-PTX-12 and 36R-PTX-12, occurred as a pair of equilibrating diastereoisomers differing from PTX-2 in that they contained an exocylic olefinic methylene rather than a methyl group at C-38. Analyses of shellfish extracts revealed that PTX-12 accumulated in Norwegian blue mussels (Mytilus edulis) and cockles (Cerastoderma edule), along with PTX-12 seco acids occurring as a complex mixture of diastereoisomers. LC-MS analysis of algal cells picked from the net haul from Flodevigen revealed that PTX-12 predominated in D. acuta and D. norvegica, whereas PTX-2 was the predominant pectenotoxin in D. acuminata. Preliminary observations indicate that the relative contents of PTX-2 and PTX-12 vary between sites and years in Norway, even within a single species of Dinophysis. Our data also suggest that heterotrophic dinoflagellates may accumulate toxins from their prey.

41a-homoyessotoxin (1), a new analogue of yessotoxin (7), was isolated from extracts of Protoceratium reticulatum grown in culture. In addition, 9-methyl-41a-homoyessotoxin (2) and a nor-ring A-yessotoxin (3) were identified as the major components of a mixed fraction. The structural information was initially obtained from LC-UV and LC-MS3 chromatograms, with subsequent definitive structure determination by NMR, LC-MS/MS, and high-resolution MS. Full 1H and indirectly detected 13C NMR assignments for all but two carbon atoms were obtained from ca. 100 microg of 1. Full 1H NMR assignments for 2 and 3 and identification of three new heptanor-41-oxo-analogues of 3 (4-6) during LC-MS3 analysis of a fraction containing 1-3 and 7 are also reported.

The dinoflagellate Dinophysis acuta has been associated with various incidents of diarrhetic shellfish poisoning. A sample of Dinophysis acuta collected from New Zealand waters in 2002 was previously found to contain high levels of pectenotoxins, but only a very low level of the diarrhea-inducing okadaic acid (OA). After hydrolysis under basic conditions, however, the concentration of OA increased substantially, indicating the presence of conjugated forms of OA. Using various liquid chromatography/electrospray ionization tandem mass spectrometry (LC/ESI-MS/MS) techniques, a number of OA esters were detected in the original extract. The principal compound was identified as a C8 diol-ester of OA (OA-D8), which had been identified previously in another dinoflagellate, Prorocentrum lima. The retention time, as well as positive and negative ion MS, MS/MS and UV spectra of the D. acuta compound, matched exactly those of OA-D8 isolated from P. lima. In addition to OA-D8, several other novel OA esters were detected in the D. acuta but these have not yet been identified. This is the first report identifying the presence of OA esters in Dinophysis species.

The paralytic shellfish poison family has been recently extended by the discovery of several analogues possessing a hydoxybenzoate moiety instead of the carbamoyl group one finds in saxitoxin, the parent molecule of this toxin family. We have investigated the potency of these new analogues on a representative isoform of the pharmacological target of these toxins, the voltage gated sodium channel. These toxins were found to have K I 's in the low nanomolar range, only slightly less potent than saxitoxin. The hydroxybenzoate group may increase the lipophilicity of these toxins and improve their ability to pass through epithelia and therefore its uptake and elimination in both intoxication victims and animals that bioaccumulate paralytic shellfish toxins.

The acid-catalyzed inter-conversion of spiroketal isomers of pectenotoxins PTX1, PTX6 and PTX2 were studied by liquid chromatography–electrospray ionization-tandem mass spectrometry (LC–MS–MS). Using a C8-silica reversed-phase column and a mobile phase of aqueous acetonitrile containing 2 mM ammonium formate and 50 mM formic acid, the known spiroketal stereoisomers of PTX1 eluted in order of PTX1, PTX4 and PTX8, while those of PTX6 eluted in the order PTX6, PTX7 and PTX9. Acid treatment of PTX2 yielded two novel spiroketal stereoisomers, which have been named PTX2b and PTX2c. LC–MS–MS spectra obtained for the [M+NH4]+ ions of PTX2, PTX2b and PTX2c were essentially identical. As an application of the LC–MS–MS methodology, a sample of the toxic dinoflagellate Dinophysis acuta collected from the coast of New Zealand was analyzed for pectenotoxins. PTX2 and a new pectenotoxin, which has been named PTX11, were detected as the most predominant compounds. Novel PTX2 and PTX11 isomers were also found in the D. acuta although the levels of these compounds were low.

Small-volume batch cultures of the toxic marine dinoflagellate Alexandrium ostenfeldii (Paulsen) Balech et Tangen were exposed to gradients of salinity, light, and inorganic nitrogen to determine their effects on growth and toxin production. Cell growth was determined by in vivo fluorometry and microscopic cell counts, and spirolide production through the culture cycle was measured by liquid chromatography-mass spectrometry. Growth of A. ostenfeldii was a function of environmental conditions, and was strongly limited under sub-optimal regimes of light (≥ 150 pmol m - 2 s - 1 ), salinity (≤ 15 psu), and low nutrients (≤ 20 μM initial nitrate). Cell concentration and in vivo fluorescence were highly correlated (r 2 = 0.83 to 0.97, n = 6) but the relationship varied slightly depending on experimental conditions. Nevertheless, except under nitrogen limitation, fluorometry was an accurate method for tracking cell growth. The growth characteristics indicated that this estuarine isolate of A. ostenfeldii from Atlantic Canada was moderately "shade-adapted", had a broad salinity tolerance, and could effectively utilize much higher levels of inorganic nitrogen than commonly occur in the natural environment. Analysis of toxin production and composition throughout the culture cycle showed that total concentration of spirolides in the cellular fraction of the culture (pmol l - 1 ) increased with cell concentration, but cell spirolide quota (Q s ) and toxin composition (% molar) did not vary substantially in response to variations in environmental regime. Spirolides accumulated in the growth medium, but the concentration remained low (< 15 % of total) in comparison to that in the cellular fraction. This study supports the conclusion that cell growth is directly responsive to changes in environmental variables, but spirolide production is constitutive and susceptible to acclimation in culture.

In parallel trials with the mouse bioassay, MIST Alert for Paralytic Shellfish Poisoning (PSP), a rapid diagnostic test for PSP, detected 100% of the toxic extracts in over 2100 regulatory samples. Toxic extracts contained at least 80 microg saxitoxin equivalents (STX equiv.) in 100 g of shellfish tissue, or more, as measured by the regulatory AOAC mouse bioassay. Only one potentially toxic sample, which contained 78 and 86 microg STX equiv./100 g shellfish tissue in two different mouse bioassays, was recorded as negative in one replicate of MIST Alert. All other toxic extracts among more than 2100 regulatory shellfish tissue samples were detected by MIST Alert for PSP. The MIST Alert for PSP also detected the majority of extracts containing PSP toxin greater than 32 microg STX equiv./100 g, which is the mouse bioassay detection limit. The MIST Alert for PSP gave a false positive result compared to the mouse bioassay at an average rate of about 14% over all sites, although some differences were seen between sites. Further analysis by high performance liquid chromatography (HPLC) of the (false positive) extracts showed that many contained PSP toxicity in the range of 20-40 microg STX equiv./100 g, below the level detectable by the mouse bioassay. The MIST Alert for PSP gave false positive results from extracts containing less than 20 microg STX equiv./100 g shellfish tissue only about 6% of the time. The PSP family of toxin analogues can occur in any combination in naturally contaminated shellfish tissue and the antibody mixture in the MIST Alert tests detect each of the different PSP toxin analogues with different efficacy. It is therefore impossible to provide an exact detection limit for the MIST Alert that would be applicable for all possible toxin profiles. Through the experience of comparison testing with the regulatory mouse bioassay in many parts of the world, with over 2100 different samples, the MIST Alert for PSP has proven its ability to detect all types of profiles of the PSP toxin analogues. The detection limit for MIST Alert for PSP was about 40 microg STX equiv./100 g for the 'average' profile of PSP toxin analogues. Since the detection limit depends on the toxin profile in the individual extract, it will also vary depending on the profile of analogues most commonly found at each geographic location. This was observed in our study. Over all sites in the trials, approximately 5% of samples below 40 microg STX equiv./100 g were positive, and 5% of samples between 40-80 microg STX equiv./100 g were negative. This is a reflection of the different analogue profiles found in naturally contaminated extracts, even after acid hydrolysis using the AOAC extraction method.

The combination of hydrophilic interaction liquid chromatography with electrospray mass spectrometry (HILIC-MS) has been investigated as a tool for the analysis of assorted toxins produced by cyanobacteria. Toxins examined included saxitoxin and its various analogues (1-18), anatoxin-a (ATX-a, 19), cylindrospermopsin (CYN, 20), deoxy-cylindrospermopsin (doCYN, 21), and microcystins-LR (22) and -RR (23). The saxitoxins could be unequivocally detected in one isocratic analysis using a TSK gel Amide-80 column eluted with 65% B, where eluent A is water and B is a 95% acetonitrile/water solution, both containing 2.0 mM ammonium formate and 3.6 mM formic acid. The analysis of ATX-a, CYN and doCYN required 75% B isocratic. Simultaneous determination of 1-21 was also possible by using gradient elution. HILIC proved to be suitable for the analysis of microcystins, but peak shape was not symmetric and it was concluded that these compounds are best analyzed using existing reversed phase methods. The HILIC-MS method was applied to the analysis of field and cultured samples of Anabaena circinalis and Cylindrospermopsis raciborskii. In general the method proved quite robust with similar results obtained in two different laboratories using different instrumentation.

The ferrous oxidation-xylenol orange (FOX) assay was adapted for quantifying lipid hydroperoxides (LOOHs) in plant extracts. Excised pieces of several fruit and vegetable species were exposed to 83 kJ m(-2) day(-1) of biologically effective ultraviolet B irradiance (UV-B(BE)) for 10-12 days to induce cellular oxidation. The LOOH and thiobarbituric acid reactive substance (TBARS) concentrations of these plant tissues were assessed with the FOX and iodometric assays for the former and a modified TBARS assay for the latter. There was generally good agreement between the FOX and iodometric methods both prior to and following the UV exposure. However, the iodometric assay appeared to have some difficulty in consistently quantifying lower LOOH levels (11 microM), whereas the FOX assay measured LOOH concentrations as low as 5 microM. All tissues exhibited UV-induced increases in TBARS, indicating a marked degree of cellular oxidation in the exposed tissue segments. Compared with the iodometric assay, the FOX method consistently generated less variable LOOH values. The presence of authentic linoleic acid-OOHs in spiked avocado and spinach samples (11 microM) was identified with liquid chromatography-mass spectrometry techniques, which validated corresponding FOX assay results. The FOX method is inexpensive, is not sensitive to ambient O2 or light levels, and can rapidly generate LOOH measurements. The physiological value of the FOX assay resides in its ability to measure initial rather than more advanced fatty acid oxidation; hence, early membrane-associated stress events in plant tissue can be detected.

This study compared five methods of measuring paralytic shellfish toxins (PSTs) including the long-used mouse lethality bioassay, a commercially available cell culture test (MIST® Quantification kit), HPLC analysis, and two newly developed radioreceptor assays utilizing mammalian sodium channels and saxiphilin. Methods were challenged with toxic shellfish extracts prepared according to the AOAC official method. The best correlations between predicted toxicity values being 0.9 or better, were those between HPLC analysis when compared with both radioreceptor assays and the mouse lethality bioassay, as well as that between the saxiphilin and the sodium channel radioreceptor assays. In all cases, statistically significant correlations existed between the toxicity measurements of the same extracts. The ratios between some methods were not unitary as measured by the slopes of the regression lines used for correlation analyses. HPLC analysis predicted more toxicity than all of the bioassays. The saxiphilin assay underestimated toxicity relative to the mouse bioassay, the MIST® kit determinations and the sodium channel assay. The sodium channel assay predicted there to be less toxicity than the mouse bioassay and the MIST® kit. Of all of the techniques used, the MIST® kit correlation with the mouse bioassay was nearest to one. Each method possesses different virtues and it may be that a multi-method approach would harness the benefits of each method for various aspects of a shellfish testing regime.

During 1998 and early 1999, shellfish samples from sites in Scotland were found to contain the amnesic shellfish poisoning toxin, domoic acid (DA). Two different techniques, liquid chromatography (LC) with UV diode-array detection and LC with mass spectrometric (MS) detection, were used to detect and confirm DA in shellfish extracts. The LC/UV method was validated for routine monitoring by recovery experiments on spiked mussel and scallop tissues with a certified mussel tissue used as reference material. Crude extracts of selected samples as well as extracts cleaned with strong anion exchange (SAX) were analyzed by both LC/UV and LC/MS. Good correlation (linear regression r2 = 0.996, slope = 0.93) between the 2 methods was found for cleaned extracts. Analyses of crude extracts by LC/UV produced false-positive results in 2 crab samples, whereas LC/MS analyses gave accurate results. It was concluded that LC/UV is a valid approach for routine monitoring of DA in shellfish when cleanup is performed with a SAX cartridge to prevent false positives. A variety of shellfish species were surveyed for DA content, including Pecten maximus (king scallops), Chlamys opercularis (queen scallop), Mytilus edulis (blue mussels), Cancer pugaris (crab), and Ensis ensis (razor fish). The highest concentration of DA was 105 μg/g in Pecten maximus.

Cylindrospermopsin, a hepatotoxin produced by cyanobacteria, has been unambiguously detected in cyanobacteria collected from a recreational lake in the Wellington region of New Zealand. To our knowledge this is the first report of cylindrospermopsin in New Zealand. Cylindrospermopsin and several microcystins were identified by reversed phase high-performance liquid chromatography-mass spectrometry (LC-MS) and tandem mass spectrometry (LC-MS/MS) using an atmospheric-pressure ionization source and an ionspray interface. The presence of cylindrospermopsin in New Zealand highlights the risk of direct cyanobacterial toxin exposure in recreational waters.

Three additional marine toxins, spirolides A (1), C (3), and 13-desmethyl-C (7), were isolated from contaminated scallops and phytoplankton collections obtained from a Nova Scotian aquaculture site, as well as from batch cultures of the dinoflagellate Alexandrium ostenfeldii obtained as a single-cell isolate from these phytoplankton assemblages. The structures of these new spirolide derivatives, characterized by mass spectrometry and NMR, indicate a close relationship with spirolides B (2) and D (4) isolated previously from contaminated shellfish in the same area. All of these compounds display “fast-acting” toxicity in the traditional bioassay used for monitoring shellfish, and this is related to the presence of a cyclic imine function in all these compounds. Those spirolides containing a vicinal dimethyl group in the seven-membered ring are resistant to oxalic acid hydrolysis, whereas those that do not are readily hydrolyzed. These observations suggest that the extra methyl group on the seven-membered imine ring of 3, 4, and 7 appears to block the process of imine hydrolysis perhaps by stereochemical interference.

Previous investigations into the comparative toxicity of the diarrhetic shellfish poisoning (DSP) toxins to Thalassiosira weissflogii (Grun.) Fryxell et Hasle found that this diatom oxidatively metabolized okadaic acid diol-ester (OA diol-ester) to a more watersoluble product. This oxidative transformation of OA diol-ester by the diatom is significant for two reasons. First, it is known that dinophysistoxin-4 (DTX4), the primary DSP toxin produced by the dinoflagellate Exuviaella lima (Ehr.) Butschli, will be hydrolyzed to the diol-ester following cell rupture (e.g. ingestion by a predator). Second, it implies that the ester, an uncharged, lipophilic intermediate, can easily enter cells and therefore may play an important role in the uptake and transfer of DSP toxins through the food web. It has been suggested that the water soluble DTX-4 may also be the form in which DSP toxins are excreted from the producing cell. Therefore, the stability of DTX-4 was examined when incubated either in fresh seawater medium into which washed cells of E. lima were introduced or in seawater medium conditioned by E. lima cells. Rapid hydrolysis of DTX-4 to the diol-ester took place in both cases. Thus, regardless of the route by which DTX-4 is liberated from the cell, either by cell disruption or excretion, the diol-ester will be the dominant form of the toxin to challenge associated organisms. To examine the metabolism of OA diol-ester by T. weissflogii in more detail, serial cultures of the diatom were challenged with OA diol-ester at a concentration of 2.0 m g·mL 2 1 . The metabolism and fate of the diol-ester in both cellular and medium fractions were monitored over 3 days using liquid chromatography with either ultraviolet (LC-UV) or mass spectrometric (LC-MS) detection. During the course of the experiment, all of the diol-ester was metabolized. LC-MS analysis revealed the presence of multiple oxidative products of OA diol-ester in the medium fraction, including a carboxylic acid derivative. The major metabolites were isolated in sufficient quantity to permit structural elucidation by NMR and MS. All the metabolites identified resulted from oxidation of the diol-ester side chain with the primary sites of attack at the terminal, subterminal, and unsaturated carbons. OA was found in both cellular and medium fractions, and its production was directly correlated with the metabolism of the diol-ester. The relative partitioning of both OA diol-ester and its oxidation products between cells and medium supports the contention that OA diol-ester can readily enter cells, be metabolized, and then excreted in more watersoluble forms.

A suite of biologically active compounds, fast-acting toxins called spirolides, were recently isolated and characterized from shellfish and plankton samples collected from southeastern Nova Scotia, Canada. Circumstantial evidence from natural plankton assemblages has linked spirolides to gonyaulacoid dinoflagellates, particularly athecate cells (GB-42) that are derived from motile stages from this group. After repeated attempts to isolate spirolide-producing taxa from enriched size-fractionated field samples, numerous isolates of potential source organisms, including Alexandrium ostenfeldii (Paulsen) Balech et Tangen, Alexandrium tamarense (Lebour) Balech, Fragilidium subglobosum (von Stosch) Loeblich III, Gonyaulax spinifera (Claparède et Lachmann) Diesing, Protoceratium reticulatum (Claparède et Lachmann) Bütschli, and Scrippsiella trochoidea (Stein) Loeblich III were successfully cultured. Among all cultured dinoflagellate species harvested in late exponential growth phase and analyzed for spirolide content, only A. ostenfeldii was found to produce these compounds. Detailed morphological examination of field specimens and cultured cells of A. ostenfeldii by Nomarski and epifluorescence optical microscopy and by scanning electron microscopy showed that in most major aspects specimens from the western Atlantic coast closely resemble this species as described from Scandinavian waters. Key diagnostic features are the globose morphology and the presence of a large kidney-shaped ventral pore at the margin of the first apical (I') plate. Analysis by liquid chromatography with detection by tandem mass spectrometry (LC–MS/MS) of the spirolides in an isolate from Ship Harbour, Nova Scotia, indicated that only the C/D type was present in significant amounts. The principal spirolide (90% molar), a desmethyl-C derivative (MW 691), was present at a mean concentration of 54 pg cell−1. This profile is consistent with that found in bulk plankton samples collected from the same site, thereby confirming A. ostenfeldii as the primary source of spirolides in this region.

Further studies on mussel samples from Galicia, Spain, have revealed the presence of okadaic acid (OA), dinophysistoxin 2 (DTX2), and the fatty acid acyl esters of both of these toxins as the “DTX3” complex. Measurements were performed with an improved in situ method for the formation of 9-anthryldiazomethane (ADAM) derivatives followed by liquid chromatography with fluorescence detection. Base hydrolysis of DTX3 toxins gave free OA and DTX2, which were determined following ADAM derivatization. Results were confirmed by liquid chromatography/mass spectrometry analyses, and in most of the samples, free DTX2 was the most abundant toxin. However, the OA/DTX2 ratio in the DTX3 conjugated form was different, with OA being the most abundant in all cases. This difference could be due to different rates of metabolism of OA and DTX2 to the acyl esters or due to contamination of the shellfish by the two toxins at different points in time, resulting in less acyl ester formation for one toxin versus the other. The second possibility would be reasonable if two different source organisms were producing the toxins.

Since January 1993, neurological symptoms and rapid deaths (5 to 10 min) were typically observed in the mouse bioassay of acetone extracts of digestive glands from Arcachon and Toulon (France) during the winter season. It was assumed initially that a new lipophilic toxin was present because tests using the AOAC mouse bioassay for paralytic shellfish toxins on acid extracts of whole shellfish meat were negative, no known lipophilic toxins were detected and no toxic phytoplankton species were observed in the area during the poisoning events. In this study, however, preparative isolation of the toxic factor from toxic mussel digestive glands has revealed the presence of paralytic shellfish toxins, the principal ones being gonyautoxins-2 and -3 at Arcachon and gonyautoxins-1, -4, -2 and -3 at Toulon. The toxin concentrations recorded were below levels harmful to consumers and therefore represent a false positive in the mouse bioassay for lipophilic toxins based upon acetone extraction. The origin of the toxins remains to be determined. Copyright © 1999 John Wiley & Sons, Ltd.

Profiles of diarrhetic shellfish poisoning (DSP) toxins produced throughout the growth cycle and the cell cycle of the toxigenic marine dinoflagellate Prorocentrum lima were studied in triplicate unialgal batch cultures. Cells were pre-conditioned at 18 ± 1 °C, under a photon flux density (PFD) of 90 ± 5 μmol m−2 s−1 on a 14 h light:10 h dark photoperiod. In exponential growth phase, cultures were synchronized in darkness for 17 d. After dark synchronization, cultures were transferred back to the original photoperiod regime. Cells were harvested for DSP toxin analysis by LC-MS (liquid chromatography with mass spectrometry), and double-stranded (nuclear) DNA was quantified by flow cytometry. The cell populations became asynchronous within approximately 3 d after transition from darkness to the 14 h light:10 h dark photoperiod. This may be due to the prolonged division cycle (5 to 7 d) that is not tightly phased by the photoperiod. Unlike other planktonic Prorocentrum spp., cytokinesis in P. lima occurred early in the dark and ceased by “midnight”. Cellular levels of the four principal DSP toxins, okadaic acid (OA), OA C8-diol-ester (OA-D8), dinophysistoxin-1 (DTX1) and dinophysistoxin-4 (DTX4), ranged from 0.37 to 6.6, 0.02 to 1.5, 0.04 to 2.6, and 1.8 to 7.8 fmol cell−1, respectively. No toxin production was evident during the extended period of dark synchronization nor during the initial period when NH4 was consumed as the major nitrogen source. Soon after the cells were returned to the 14 h light:10 h dark cycle and they began to take up NO3, cellular levels of all four toxins gradually increased. This increase in DSP toxins usually occurred in the light, marked by a rise in DTX4 levels that preceded an increase in the cellular concentration of OA and DTX1 (delayed by 3 to 6 h). Thus, DTX4 synthesis is initiated in the G1 phase of the cell cycle and persists into S phase (“morning” of the photoperiod), whereas OA and DTX1 production occurs later during S and G2 phases (“afternoon”). No toxin production was measured during cytokinesis, which happened early in the dark. The evidence indicates that toxin synthesis is restricted to the light period and is coupled to cell cycle events.

The protein phosphatase inhibition assay for okadaic acid, the major DSP toxin, modified to use the fluorescence substrates methylumbelliferyl phosphate (MUP) and fluorescein diphosphate (FDP), was compared to the assay using p-nitrophenylphosphate (p-NPP) and the bioluminescence assay using luciferin phosphate (L-P). Under the standard assay conditions used okadaic acid inhibited the enzyme activity dose-dependently with IC50 values of 1.5 nM (MUP) and 1.2 nM (FDP). This compares to IC50 values of 0.9 and 6 nM using L-P and p-NPP respectively. CDP-star, a chemiluminescence substrate, was not hydrolysed by the enzyme. Decreasing the enzyme concentration lowered the IC50 for the colorimetric method (IC50=2 nM [p-NPP], 0.75 nM enzyme) but no shift was observed with fluorimetry. However at enzyme concentrations1.5 nM (standard assay) the error margin was too great for routine analysis. The method using fluorimetry allowed detection of okadaic acid concentrations to levelsor = 1 microg/100 g of mussel tissue which is well below the limit of 20 microg/100 g (mouse bioassay) set by some regulatory agencies. Determination of the toxin content in naturally contaminated mussels in three separate experiments gave coefficients of variance ranging from 16 to 29% (MUP) and from 8 to78% (p-NPP). Multicomparison studies showed that concentrations of okadaic acid in naturally contaminated mussel samples determined by fluorescence generally agreed with those obtained using ELISA and LC-MS procedures, and with the mouse bioassay. However using the mouse bioassay as the standard, values determined by the ELISA, PP-2A and LC-MS all scored false negative results compared to those for the mouse bioassay in the range 20-40 microg/100 g mussel, and at the limit of the mouse bioassay the values by the other three methods were substantially less. With few exceptions the methods scored okadaic acid with highest to lowest values in the following order: mouse bioassayELISAPP-2ALC-MS. The fluorimetric assay was both more sensitive and accurate than the colorimetric assay (the latter showed a propensity towards false positives in the region 20 microg/100 g), and the moderate increase in equipment cost appears to be outweighed by the performance of the method.

The diarrhetic shellfish poisoning (DSP) toxin okadaic acid ( 1 ) is found in extracts of the dinoflagellate Prorocentrum lima together with a suite of diol esters such as 2 . When 2 was added to the culture medium of the centric diatom Thalassiosira weissflogii , it was transformed into a range of products within three days. Three of these products, 3 , 4 and 5 , were isolated from the medium and identified as oxidation products 2 , suggesting that the diatom produces DSP metabolites of greater polarity as a means of detoxification. In addition, another diol ester product 6 was identified as a minor impurity of 2 .

Application of a method for the "in situ" generation of 9-anthryldiazomethane (ADAM) to the derivatization of the carboxyl function in diarrhetic shellfish poisoning (DSP) toxins revealed the formation of artifact products. Using liquid chromatography-mass spectrometry, it was determined that these artifacts were due to base-catalyzed reactions between the solvent, ethyl acetate, and the hydroxyl groups of the analyte to produce O-acetylated ADAM derivatives. Using a new formulation, with tetrahydrofuran as solvent, it was possible to eliminate these artifact reactions. Various reaction parameters have also been re-optimized to ensure quantitative derivatizations. An assessment method was developed that was useful not only for optimizing reaction parameters, but also for evaluating the reagent potency before use on important samples. Finally, application of the method to the determination of DSP toxins in plankton and mussel tissue was demonstrated.

Quantitative structure-activity relationships were determined for the diarrhetic shellfish poisoning (DSP) toxins, okadaic acid (OA), OA diol-ester and dinophysistoxin-4 (DTX-4), using a sensitive bioassay procedure with the diatom Thalassiosira weissflogii. OA diol-ester was found to be nearly as toxic as OA. This result contradicted the accepted idea that only the free acid toxins, such as DTX-1 and OA, are potent phosphatase inhibitors. Postassay analyses using liquid chromatography-mass spectrometry (LC-MS) of cultures incubated with OA diol-ester showed that the ester had partially decomposed to OA, which explained some but not all of the observed toxicity. The formation of OA during the bioassay raised the possibility that cells exposed to inactive DSP toxin esters could metabolically activate them. This was examined in an additional experiment which showed that the hydrolysis of both DTX-4 and OA diol-ester was spontaneous and apparently not mediated by the presence of T. weissflogii cells. However, cells of T. weissflogii challenged with OA diol-ester rapidly metabolized most of the toxin to a more water-soluble product. From interpretation of mass spectral data obtained using ion-spray LC-MS, the metabolite was identified as an oxygenated diol-ester of OA, implying that it was the product of a monooxygenase-detoxification pathway. It is postulated that OA diol-ester, as a lipid-soluble, uncharged molecule with a propensity to hydrolyse to OA, may facilitate the transfer of OA across cell walls and membranes.

Publisher Summary This chapter describes the analysis of marine toxins using liquid chromatography–mass spectrometry (LC–MS). The important task of monitoring seafood products for toxins presents significant challenges to the analytical chemist. Toxins range from polar, low-molecular-weight compounds to high-molecular-weight lipophilic substances. The electrospray and ion-spray ionization techniques have provided keys to the trace analysis of marine toxins through the combined techniques of LC–MS and capillary electrophoresis (CE)–MS. The generation of precise quantitative data, performance of multitoxin analyses, discovery of new toxins, analogs, and metabolites, and generation of structural information on new toxins are invaluable to toxin research. Although the equipment required is expensive, the possibility of performing automated, unattended analyses can justify such an investment if large numbers of samples are to be screened. In addition, the only MS ionization methods reported to be suitable for very polar, thermally labile compounds are fast atom bombardment (FAB), thermospray, electrospray, and ion spray.

Complex mixtures of polycyclic aromatic hydrocarbons (PAHs) generated from fuel-rich combustion of ethylene-naphthalene mixtures in a jet-stirred-plug-flow reactor were chemically characterized by combined mass spectrometric techniques to yield product composition data that cover the molecular mass region from simple PAHs (naphthalene, 128 u) to large molecules comparable in molecular size (1792 u) to nanoparticles of soot. Two techniques based on atmospheric-pressure chemical ionization mass spectrometry (APCI-MS) were investigated: (1) APCI-MS combined with high-performance liquid chromatography through a heated nebulizer interface was found suitable for PAHs up to C36 (448 u). (2) For the characterization of larger PAHs beyond C36, direct liquid introduction (DLI) of sample into an atmospheric-pressure chemical ionization mass spectrometer through a heated nebulizer gave protonated molecular ions for PAHs over the m/z 400–2000 range. Although unequivocal elemental composition information is unattainable from the unit-resolution DLI/APCI-MS data, by starting with structural data from identified C16 to C32 PAHs, and applying PAH molecular growth principles, it was possible to generate PAH molecular maps from the DLI/APCI-MS data from which values for the elemental composition could be derived for all major peaks.

Diarrhetic shellfish poisoning (DSP) is a severe gastrointestinal illness caused by consumption of shellfish contaminated with toxigenic dinoflagellates. The main toxins responsible for DSP are okadaic acid (OA), DTX-1, DTX-2, and DTX-3, the latter being a complex mixture of 7-O-acyl derivatives of the first 3. In this study, existing methods based on liquid chromatography (LC) combined with mass spectrometry (LC–MS) and LC with fluorometric detection (LC–FLD) of anthryldiazomethane (ADAM) derivatives were improved upon to achieve a high degree of accuracy and precision for the determination of DSP toxins in a new mussel tissue reference material (MUS-2). All experimental parameters were examined comprehensively, and a new internal standard and a new solid-phase extraction cleanup method were introduced. Quantitative extraction of DSP toxins from shellfish tissue was achieved by exhaustive extraction with aqueous 80% methanol. Cleanup was accomplished by partitioning the crude aqueous methanol extract with hexane to remove lipids and then with chloroform to isolate the toxins. A further cleanup based on an aminopropylsilica column was useful for LC-MS and looks promising for the ADAM/LC-FLD method. The internal standard, 7-O-acetylokadaic acid, synthesized by partial acetylation of OA, improved accuracy and precision by correcting for incomplete recoveries in extraction, cleanup, and derivatization steps and for volumetric errors and instrumental drift. An improved silica cleanup after ADAM derivatization also was developed by controlling the activities of both sorbent and solvents. The methods were tested with various mussel tissue samples. The resulting improved methods will be useful to analysts involved in routine monitoring of DSP tox ins.

Increasing incidences of phytoplankton blooms with the potential danger of toxin release into the food chain have necessitated the search for new diagnostic methods that can detect toxins quickly and reliably. A competitive enzymelinked immunosorbent assay (ELISA) was developed to quantitate okadaic acid in shellfish and phytoplankton extracts. To determine the specificity of the assay, a number of toxins, such as calyculin A, brevetoxin-1, and dinophysistoxins-1, -2, and -3 were analyzed. Both dinophysistoxins-2 and -1 could be detected by the assay but in concentration ranges 10- and 20-fold higher than that for okadaic acid, respectively. Dinophysistoxin-3, calyculin A, or brevetoxin-1 could not be detected with this assay. To validate the accuracy of the method, 18 mussel and 7 phytoplankton extracts were analyzed in parallel for okadaic acid content by ELISA and liquid chromatography combined with either fluorescence or mass spectrometric detection. Very high correlation between the results was found.

A liquid chromatography-mass spectrometry (LC-MS/MS) method using hydrophilic interaction liquid chromatography (HILIC) was developed for the analysis of neurotoxins β-N-methylamino-L-alanine (BMAA) and 2,4-diaminobutyric acid (DAB), using multiple reaction monitoring (MRM) scan mode. Oasis-MCX and Strata-X-C polymeric cation-exchange cartridges were used to clean extracts of cyanobacterial cultures, including two strains of Microcystis aeruginosa and one strain of Nostoc sp. The performance of the solid-phase extraction (SPE) cartridges for BMAA and DAB were evaluated using mixed standards and spiked cyanobacterial extracts, which demonstrated recoveries of BMAA and DAB ranging from 66% to 91%. Matrix effects in LC-MS/MS were evaluated, and while there was no effect on BMAA quantitation, suppression of DAB was found. Full scan (Q1) and enhanced product ion (EPI) monitoring showed that the DAB suppression may be due to closely eluting compounds, including lysine, histidine, arginine and three other compounds with [M + H](+) m/z of 88, 164 and 191. The procedures developed allow the sensitive and effective analysis of trace BMAA and DAB levels in cyanobacteria. While DAB was confirmed to be present, no BMAA was found in the cyanobacterial samples tested in the present study.

Several derivatization reagents for the conversion of okadaic acid and related DSP toxins to fluorescent derivatives for analysis by liquid chromatography have been examined, viz: 9-anthryldiazomethane (ADAM), 1-pyrenyldiazomethane (PDAM), 4-diazomethyl-7-methoxycoumarin (DMMC), 4-bromomethyl-7-methoxycoumarin (BrMMC), 4-bromomethyl-7,8-benzcoumarin (BrMBC), 4-bromomethyl-7-acetoxycoumarin (BrMAC), and 4-bromomethyl-6,7-dimethoxycoumarin (BrDMC). The ADAM reagent provides the greatest selectivity and sensitivity, but its application on a routine basis has been limited by its instability and cost. Improvement of this method was achieved through the production of ADAM in situ from the stable 9-anthraldehyde hydrazone. A detection limit of 30 ng/g hepatopancreas (equivalent to 6 ng/g whole tissue) was achieved. The other aryldiazomethane reagents were found to have insufficient reactivity. Of the bromomethylcoumarin reagents, BrDMC was found to have the greatest promise. The reagent is inexpensive and has excellent stability and purity. Quantitative derivatization may be achieved in a 2 hour reaction at 45 degrees C with N,N-diisopropylethylamine as a catalyst. Unfortunately, the lower reaction selectivity of BrDMC compared to that of ADAM limits its application to isolated toxins, plankton samples, and shellfish tissues with high levels of DSP toxins. The use of BrDMC for the determination of how toxin levels in shellfish tissues will require development of a more extensive clean-up prior to derivatization. Successful application of the ADAM and coumarin derivatization methods to real-world samples has been demonstrated.

The chromatographic performance of erythromycin A (EA) is improved significantly over that achieved on polymeric columns by using a sterically shielded octyldiisopropylsilica (Zorbax Rx-C8) column and a neutral mobile phase consisting of 5 mM aqueous sodium perchlorate—acetonitrile (50:50). This mobile phase facilitates electrochemical detection of EA at the 3-pmol level. Temperature control of both column and detection cell is important for minimizing detector noise and drift. A clean-up procedure, based on aminopropylsilica solid-phase extraction, allows the detection of EA in salmon flesh down to the 0.2-ppm level. Some of the metabolites of EA that retain the tertiary amine may also be detected by this method.

Periodate oxidation of the toxins responsible for paralytic shellfish poisoning (PSP) yields fluorescent purines suitable for trace analysis by reversed-phase LC. Mobile phases containing perfluorinated acids, such as heptafluorobutyric acid, as ion-pair agents were found to provide high capacity factors for the oxidized products. Gradient elution on a microbore column with large volume injections and fluorescence detection permitted the detection of femtomole quantities of PSP toxins. A fully automated pre-column oxidation procedure was developed for an LC autosampler system in order to improve precision and allow unattended analyses. The complete method was applied successfully to various samples, including shellfish and toxic phytoplankton.

Plasma concentrations and urinary excretion of DTZ and its metabolites were determined in 20 healthy volunteers (10 males and 10 females) after they had each been given a single oral 90 mg dose of DTZ. DTZ and six of its metabolites which included N-monodesmethyl DTZ (MA), deacetyl DTZ (M1), deacetyl N-monodesmethyl DTZ (M2), deacetyl O-desmethyl DTZ (M4) and deacetyl DTZ N-oxide (M1NO) and deacetyl N,O-didesmethyl DTZ (M6), were determined by a sensitive and specific HPLC assay. The major metabolites measurable in the plasma of all the volunteers were MA, M1, and M2. The terminal half-lives (t1/2) of M1 and M2 were considerably longer than those of DTZ and MA. Less than 5% of the dose was excreted as unchanged DTZ in the urine over the 24 h period. The major urinary metabolite was MA, followed by M6, M2, and then M1. Except for the urinary excretion of M4 there were no statistically significant differences in any of the pharmacokinetic parameters between the males and the females. The mean 24 h urinary recovery of M4 was higher in the males than in the females (P < 0.05). However there were large inter-individual variations in the plasma concentrations and urinary excretion of DTZ and its metabolites with some parameters differing by more than 20-fold. In addition, O-desmethyl DTZ (Mx) and N,O-didesmethyl DTZ (MB) were identified as two other major urinary metabolites.

Fullerene-rich soot generated by resistive heating of graphite has been gently extracted with toluene, in order to remove some C60 and C70 compounds, followed by extraction with boiling 1,2,4-trichlorobenzene at 214°C. After filtration and removal of the solvent, the residue was re-dissolved in dichloromethane and characterized by non-aqueous reversed phase liquid chromatography coupled on-line with atmospheric pressure chemical ionization mass spectrometry. Several novel fullerenes were detected, including C72, C80, C86, and C88 as well as other fullerenes up to C108 and higher. The results indicate that chromatographic separation of large fullerene molecules can be achieved with low boiling point solvents and conventional liquid chromatographic techniques.

A reverse-phase liquid chromatography/mass spectrometry (LC/MS) method, incorporating gradient elution, is described for the characterization of residual erythromycin A and its metabolites in salmon tissue. The method uses ion-spray, a mild atmospheric pressure ionization technique which provides an abundant protonated molecule well suited for selected ion monitoring experiments. Tandem mass spectrometry (MS/MS) using collision-induced dissociation was used to provide structural information. The LC/MS method was tested for the analysis of salmon tissue spiked with erythromycin A at levels between 0.01 and 1 p.p.m. A simple extraction and clean-up procedure, slightly modified from that described by Takatsuki et al. (J. Assoc. Off. Anal. Chem. 70, 708 (1987)), was used in this work. Using selected ion and selected reaction monitoring techniques, the LC/MS and LC/MS/MS methods provided detection limits of < 10 and 50 ng g-1, respectively. Confirmatory full-scan LC/MS and LC/MS/MS spectra were obtained at the 0.5 and 1 microgram g-1 levels, respectively. Using a combination of these techniques, the presence of residual erythromycin A was confirmed in the tissue of fish administered medicated feed containing the antibiotic. In addition, several metabolites and degradation products of erythromycin A, including anhydro-erythromycin and N-demethyl-erythromycin, were detected and where possible confirmed by comparison with authentic compounds. Although this analytical method has been shown to afford the necessary sensitivity and precision, application of these techniques to high-throughput quantitative analyses will require development of an improved clean-up procedure and preferably also of a suitable surrogate internal standard.

A novel method for the detection of acylated diarrhetic shellfish poisoning toxins is reported. Direct determination of these compounds is possible using high performance liquid chromatography coupled with ion-spray mass spectrometry. An extract, purified from the digestive glands of toxic mussels (Mytilus edulis) contaminated with okadaic acid, dinophysistoxin-1, and a recently reported analog, dinophysistoxin-2, was also shown to contain small amounts of dinophysistoxin-3, a mixture of 7-O-acyl ester derivatives of dinophysistoxin-1. In addition, acyl ester derivatives of okadaic acid and dinophysistoxin-2 were also detected by direct LC-MS analysis and confirmed by analysis of their hydrolysis products. This is the first report of the detection of other naturally occurring 7-O-acyl esters similar to dinophysistoxin-3.

The Third Canadian Workshop on Harmful Marine Algae, May 12-14, 1992, Mont-Joli, Québec, Canada, Series: Canadian Technical Report of Fisheries and Aquatic Sciences; no. 1893