The use of photoperiods to provide year round spawning in lumpfish Cyclopterus lumpus.

In order to provide year round spawning broodstock, lumpfish (initial size 746 g and 24.9 cm) were reared under four different photoperiod regimes from January 2017 to July 2018. One group was reared under simulated natural photoperiod (LDN, control group) for Tromsø (70°N). The second group was transferred to continuous light (LD240) on 30 January 2017 and reared at LD24:0 throughout the trial period. Two compressed and phase advanced photoperiods were also established. Both groups were moved from LDN to LD24:0 on 30 January 2017, and after that reared at compressed natural photoperiods where the annual photoperiod was compressed down to six months (L6) or nine months (L9) for the duration of the study. Spawning time was shifted in both compressed groups during both years of the study. Spawning activity in the second year of the study was higher and followed more closely the expected spawning period in the compressed and the LDN groups. Spawning in the LD240 group was spread out over the experimental period with no distinct peak in spawning. A seasonal and pronounced drop in condition factor was found for females in the L9, L6 and the LDN groups. This post-spawning loss in condition was closely related to the spawning activity of each group. The current findings suggest that photoperiod has a strong influence on the timing of lumpfish maturation and can be used as an efficient and inexpensive tool to secure lumpfish reproduction operations i.e. year-round supply of egg and milt and/or timing with optimal temperature regimes.

First evidence of an extensive northern European distribution of azaspiracid poisoning (AZP) toxins in shellfish.

Azaspiracids have recently been identified as the toxins responsible for a series of human intoxications in Europe since 1995, following the consumption of cultured mussels (Mytilus edulis) from the west coast of Ireland. Liquid chromatography-mass spectrometric (LC-MS) methods have been applied in the study reported here to investigate the new human toxic syndrome, azaspiracid poisoning. Separation of azaspiracid (AZA1) and its analogues, 8-methylazaspiracid (AZA2) and 22-demethylazaspiracid (AZA3), was achieved using reversed-phase LC and coupled, via an electrospray ionisation source, to an ion-trap mass spectrometer. These azaspiracids have now been identified in mussels from Craster (north-east England) and Sognefjord (south-west Norway) using source collision induced dissociation-MS and multiple tandem MS detection. AZA1 was the predominant toxin and toxin profiles were similar to those found in contaminated Irish shellfish. This is the first report of the occurrence of these azaspiracids outside Ireland with the significant implications that these toxins may occur in shellfish throughout northern Europe.

Clarification of the C-35 stereochemistries of dinophysistoxin-1 and dinophysistoxin-2 and its consequences for binding to protein phosphatase.

Okadaic acid analogues are well known as protein phosphatase inhibitors and occur naturally in marine shellfish feeding on dinoflagellates of the genus Dinophysis, leading to diarrhetic shellfish poisoning of shellfish consumers. Knowledge of the correct structures for these toxins is important in understanding their toxicology, biochemistry, and biosynthesis. We have performed extensive NMR analyses on okadaic acid (1), dinophysistoxin-1 (DTX-1), and dinophysistoxin-2 (DTX-2) obtained from natural sources. Consequently, we were able to unambiguously deduce the stereochemistries at C-35 for DTX-1 and DTX-2 based on analysis of NMR coupling constants and NOE interactions. Our results revealed that DTX-2 (3) has a stereochemistry opposite to that of DTX-1 (2) at C-35. Molecular modeling of the docking of 1-3 with protein phosphatase-1 and protein phosphatase 2A (PP2A) suggested that the reduced affinity of DTX-2 for PP2A may be due to the newly defined stereochemistry at the 35-methyl group. The implications of these findings for biosynthesis and toxicology are discussed.

Detection and identification of spirolides in norwegian shellfish and plankton.

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.

A novel pectenotoxin, PTX-12, in Dinophysis spp. and shellfish from Norway.

Two novel pectenotoxins (PTXs) were detected by LC-MS in solid phase extracts of net hauls taken at Flødevigen, 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 Flødevigen 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.