Comparative determination of paralytic shellfish toxins (PSTs) using five different toxin detection methods in shellfish species collected in the Aleutian Islands, Alaska

Paralytic shellfish poisoning (PSP), a human illness caused by the ingestion of shellfish contaminated with paralytic shellfish toxins (PSTs), has been reported in Alaska for decades. These poisoning incidents have resulted in losses to local economies due to shellfish harvest closures. Thus the development of an effective biotoxin monitoring program designed specifically for the remote regions of Alaska would provide protection for public health and allow for a viable shellfish industry. The present study provides data useful for the development of an effective toxin screening protocol by comparing PST levels quantified in shellfish by many of the currently available PST detection techniques. Seven bivalve species were collected along beaches of the Aleutian Islands from June 2006 to September 2007. The concentration of PSTs was quantified and compared using five different analytical methods: the mouse bioassay, high performance liquid chromatography (HPLC), receptor-binding assay, the commercially available Jellett Rapid PSP Test strips, and an enzyme linked immunosorbent assay technique. The Association of Official Analytical Chemists (AOAC)-approved HPLC method proved to be valuable for characterizing the suite of individual PSTs in each species for research purposes, but was not considered practical for rapid toxin screening in remote Alaskan regions due to its time-consuming nature and requirement of expensive equipment and considerable expertise. In the present study, Jellett test strips were shown to be an effective tool for rapid screening, however due to the high percentage of false positives, subsequent validation via AOAC-approved methods would be required to prevent unnecessary closures.     

First detection of cyanobacterial PSP (paralytic shellfish poisoning) toxins in Spanish freshwaters

Presence of the paralytic shellfish toxins (PSTs) saxitoxin, neosaxitoxin, decarbamoyl saxitoxin and gonyautoxin-5 was analyzed by mass spectrometry in 41 Spanish freshwaters and 13 strains of potential PST-producing planktonic cyanobacteria. Toxins were detected in five waterbodies, but were absent from the isolated strains. PST containing samples belonged to the same geographical region (South Western Spain) and were most likely related to the presence of the genus Aphanizomenon.     

Transformation of paralytic shellfish poisoning toxins in Crassostrea gigas and Pecten maximus reference materials

Matrix reference materials are an important requirement for the assessment of method performance characteristics and for routine quality control. In the field of marine toxin testing where biological assays have been used and where modern analytical testing methods are now becoming available, this requirement has become an urgent one. Various approaches are utilised for preparation of such materials in the absence of available naturally occurring toxic shellfish samples. Toxin-free shellfish may be artificially fortified through the addition of cultured toxic phytoplankton or shellfish may be incurred through natural feeding on toxic algae in a laboratory environment. Both of these approaches may be potentially affected by issues relating to the degradation or transformation of toxin analytes, so studies were conducted to assess these effects within our laboratory. A range of PSP-toxic shellfish tissues were prepared using the two approaches, in both Pacific oyster (Crassostrea gigas) and king scallops (Pecten maximus). Additionally, sub-samples of incurred Pacific oyster tissue were further treated, through addition of artificial chemical stabilisers and gamma irradiation. Two separate month-long stability trials were conducted at +4 °C on each material. Results highlighted clear evidence for improved stability of materials following shellfish feeding experiments in comparison with the tissues which had been spiked with plankton. In addition, there were clear differences in stability of toxins between the two shellfish species studied. There was evidence for good stability of C1&2 toxins in both the incurred tissues and improved stability of some toxins in tissues which had been subjected to either gamma irradiation or treatment with chemical additives. The results therefore highlighted the benefits of conducting shellfish feeding if suitable stable reference materials are to be prepared containing a full range of PSP toxin analytes. The study also highlighted the benefits of post-production treatment to prolong the stability of the materials. Work is ongoing to assess the full characteristics of candidate reference materials prepared with these approaches with the aim of producing a homogenous and stable PSP reference material in Pacific oysters.     

Uptake, distribution and depuration of paralytic shellfish toxins from Alexandrium minutum in Australian greenlip abalone, Haliotis laevigata

Farmed greenlip abalone Haliotis laevigata were fed commercial seaweed-based food pellets or feed pellets supplemented with 8 × 10⁵Alexandrium minutum dinoflagellate cells g⁻¹ (containing 12 ± 3.0 μg STX-equivalent 100 g⁻¹, which was mainly GTX-1,4) every second day for 50 days. Exposure of abalone to PST supplemented feed for 50 days did not affect behaviour or survival but saw accumulation of up to 1.6 μg STX-equivalent 100 g⁻¹ in the abalone foot tissue (muscle, mouth without oesophagus and epipodial fringe), which is ∼50 times lower than the maximum permissible limit (80 μg 100 g⁻¹ tissue) for PSTs in molluscan shellfish. The PST levels in the foot were reduced to 0.48 μg STX-equivalent 100 g⁻¹ after scrubbing and removal of the pigment surrounding the epithelium of the epipodial fringe (confirmed by both HPLC and LC-MS/MS). Thus, scrubbing the epipodial fringe, a common procedure during commercial abalone canning, reduced PST levels by ∼70%. Only trace levels of PSTs were detected in the viscera (stomach, gut, heart, gonad, gills and mantle) of the abalone. A toxin reduction of approximately 73% was observed in STX-contaminated abalone held in clean water and fed uncontaminated food over 50 days. The low level of PST uptake when abalone were exposed to high numbers of A. minutum cells over a prolonged period may indicate a low risk of PSP poisoning to humans from the consumption of H. laevigata that has been exposed to a bloom of potentially toxic A. minutum in Australia. Further research is required to establish if non-dietary accumulation can result in significant levels of PSTs in abalone.     

Trophic transfer of paralytic shellfish toxins from the cladoceran (Moina mongolica) to larvae of the fish (Sciaenops ocellatus).

The dynamic transmission and transformation of paralytic shellfish toxins (PSTs) from the toxic dinoflagellate Alexandrium tamarense to the cladoceran Moina mongolica and subsequently to the larvae of the fish Sciaenops ocellatus were investigated under laboratory conditions. The results showed that PSTs could be transferred to S. ocellatus when they preyed on PST-containing M. mongolica. During the experimental period, A. tamarense, M. mongolica and the digestive glands of the fish larvae contained C(1/2) toxins, and the viscera of S. ocellatus contained neoSTX. The proportion of beta toxin (C2) in C(1+2) toxins increased when PSTs were transferred from A. tamarense to M. mongolica, but in the subsequent transfer from M. mongolica to S. ocellatus the proportion of alpha toxin (C1) increased. During depuration, the contents of C1 and C2 toxins in fish larvae decreased with the duration of depuration, but neoSTX remained relatively constant. The present results indicated that, using a cladoceran as the vector, PSTs can be transferred from toxic algae to a high trophic level fish and metabolized in the fish. Future work should address the metabolic characteristics of PSTs in cladocerans and the end result when they are transferred to fishes.     

Occurrence of paralytic shellfish poison (PSP) in the starfish Asterina pectinifera collected from the Kure Bay, Hiroshima Prefecture, Japan.

Assays were made for paralytic toxicity of marine invertebrates inhabiting at the coasts of Hiroshima Bay, where the infestation of bivalves such as cultured oysters with paralytic shellfish poison (PSP) has been occurred. The starfish Asterina pectinifera collected at the estuary of Nikoh River, Hiroshima Bay, was found to contain moderate levels of paralytic toxicity. Its highest toxicities as PSP found on July 30, 1999 were 12.5 MU/g for whole body, 11.0 MU/g for integument tissues and 3.9 MU/g for viscera, respectively. The toxicity of integument was changed from 3.6 to 11.0 MU/g in 1 year. Its paralytic toxin principles were identified as PSP toxins, composing mainly from saxitoxin (STX) group toxins such as carbamoyl-N-hydroxy neosaxitoxin (hyneoSTX), and STX, by HPLC and LC-MS, accounting for over 90 mol%. The PSP toxins contained in the starfish A. pectinifera considered to be transferred from bivalves or detritus living in the same area, which were contaminated with PSP. However, the involved pathway may be different from that of Asterias amurensis which was infested directly through food chain from its food bivalves, for its toxin pattern.     

First evidence of azaspiracids (AZAs): A family of lipophilic polyether marine toxins in scallops (Argopecten purpuratus) and mussels (Mytilus chilensis) collected in two regions of Chile

Azaspiracids are a family of lipophilic polyether marine biotoxins that have caused a number of human intoxication incidents in Europe since 1995 following the consumption by consumers of intoxicated shellfish (Mytilus edulis). These azaspiracids have now been identified in mussels (Mytilus chilensis) and scallops (Argopecten purpuratus) from two Chilean locations. This is the first report of the occurrence of azaspiracid toxins in these species (Mytilus chilensis and Argopecten purpuratus) from Chile. The areas studied were Bahía Inglesa (III Region, 27° SL) and Chiloé Archipelago, both important scallop and mussels farming areas. Separation of azaspiracid (AZA1), azaspiracid isomer (AZA6) and its analogues, 8-methylazaspiracid (AZA2) and 22-demethylazaspiracid (AZA3), was achieved using reversed-phase LC and toxins were identified using a turbo electrospray ionisation (ESI) source, to a triple quadrupole mass spectrometer.In mussels, AZA1 was the predominant toxin in mussel hepatopancreas with AZA2, AZA3 and AZA6 present in approximate equivalent amounts in the remaining tissues, 20-30% of the AZA1 level. AZA2 predominated in the scallop samples with the toxin almost entirely present in the hepatopancreas (digestive gland). AZA1 was only observed in some of the scallop samples and was present at 12-15% of the AZA2 levels.Whilst the levels of AZAs in Chilean samples are below the EU regulatory limit of 160 μg/kg, it is significant that this toxin is present in Pacific Ocean species. Consequently measures should be taken by regulatory authorities to implement regular seafood monitoring to ensure safety of harvested product.     

Purification and characterization of a metalloproteinase, Porthidin-1, from the venom of Lansberg’s hog-nosed pitvipers (Porthidium lansbergii hutmanni)

Porthidium lansbergii hutmanni is a small pit viper found on Margarita Island, Venezuela. Local tissue damage is one of the most obvious characteristics of P. l. hutmanni envenomation, which can lead to diverse pathological effects, such as hemorrhage, edema, blistering, necrosis, lymphatic vessel damage and degradation of extracellular matrix. Metalloproteinases are one of the major components in venoms responsible for these effects. To date, very little is known or has been reported on P. l. hutmanni venom. Crude P. l. hutmanni venom had a LD₅₀ of 2.5 mg/kg and was considered very hemorrhagic (minimal hemorrhagic dose [MHD]: 0.98 μg) when compared to other hemorrhagic (Bothrops) venoms in Venezuela. Crude P. l. hutmanni venom also inhibited ADP-induced platelet aggregation. A metalloproteinase, Porthidin-1, from this venom was isolated by three chromatography steps (Sephadex G100, Superose 12 HR10/30 and Bioscale Q2). Porthidin-1 falls in the SVMP P-I class having a molecular weight of 23 kDa, verified by both SDS-PAGE and mass spectrometry. High-resolution mass spectrometry and a database search identified a peptide from Porthidin-1 (YNGDLDK) belonging to the SVMP family of proteins. Porthidin-1 contained hemorrhagic, fibrino(geno)lytic, caseinolytic and gelatinolytic activities, and these activities were capable of being neutralized by metalloproteinase inhibitors but not serine proteinase inhibitors. The peptide YNGDLDK shared similarities with five venom proteins with a BLAST e-value of <1. This work details the biochemical and pathophysiological effects that can result from envenomations, and highlights the importance and significance for characterizing unknown or poorly documented venoms from different geographical regions.     

The Structural and Functional Role of the B‐chain C‐terminal Arginine in the Relaxin‐3 Peptide Antagonist,R3(BΔ23‐27)R/I5

Relaxin‐3, a member of the insulin superfamily, is involved in regulating stress and feeding behavior. It is highly expressed in the brain and is the endogenous ligand for the receptor RXFP3. As relaxin‐3 also interacts with the relaxin receptor RXFP1, selective agonists and antagonists are crucial for studying the physiological function(s) of the relaxin‐3/RXFP3 pair. The analog R3(BΔ23‐27)R/I5, in which a C‐terminally truncated human relaxin‐3 (H3) B‐chain is combined with the INSL5 A‐chain, is a potent selective RXFP3 antagonist and has an Arg residue remaining on the B‐chain C‐terminus as a consequence of the recombinant protein production process. To investigate the role of this residue in the RXFP3 receptor binding and activation, the analogs R3(BΔ23‐27)R/I5 and R3(BΔ23‐27)R containing the B‐chain C‐terminal Arg as well as R3(BΔ23‐27)/I5 and R3(BΔ23‐27), both lacking the Arg, were chemically assembled and their secondary structure and receptor activity assessed. The peptides generally had a similar conformation but those with the extra Arg residue displayed a significantly increased affinity for the RXFP3. Interestingly, in contrast to R3(BΔ23‐27)R and R3(BΔ23‐27)R/I5, the peptide R3(BΔ23‐27) is a weak agonist. This suggests that the C‐terminal Arg, although increasing the affinity, alters the manner in which the peptide binds to the receptor and thereby prevents activation, giving R3(BΔ23‐27)R/I5 its potent antagonistic activity.     

Genotoxicity studies of organically grown broccoli (Brassica oleracea var. italica) and its interactions with urethane,methyl methanesulfonate and 4-nitroquinoline-1-oxide genotoxicity in the wing spot test of Drosophila melanogaster

Broccoli (Brassica oleracea var. italica) has been defined as a cancer preventive food. Nevertheless, broccoli contains potentially genotoxic compounds as well. We performed the wing spot test of Drosophila melanogaster in treatments with organically grown broccoli (OGB) and co-treatments with the promutagen urethane (URE), the direct alkylating agent methyl methanesulfonate (MMS) and the carcinogen 4-nitroquinoline-1-oxide (4-NQO) in the standard (ST) and high bioactivation (HB) crosses with inducible and high levels of cytochrome P450s (CYPs), respectively. Larvae of both crosses were chronically fed with OGB or fresh market broccoli (FMB) as a non-organically grown control, added with solvents or mutagens solutions. In both crosses, the OGB added with Tween–ethanol yielded the expected reduction in the genotoxicity spontaneous rate. OGB co-treatments did not affect the URE effect, MMS showed synergy and 4-NQO damage was modulated in both crosses. In contrast, FMB controls produced damage increase; co-treatments modulated URE genotoxicity, diminished MMS damage, and did not change the 4-NQO damage. The high dietary consumption of both types of broccoli and its protective effects in D. melanogaster are discussed.