Biological and physical dynamics of domoic acid production off the Washington coast

The relationship among Pseudo-nitzschia distributions, particulate toxin levels in seawater, and the energetic and highly variable water masses of an upwelling-dominated region are explored using data collected during summer cruises off the Washington coast in 1997 and 1998. In the early summer of both years, an area of maximum domoic acid (DA) accumulation was located approximately 50 km off the coast within a counterclockwise, cold feature known as the Juan de Fuca eddy. The stations in the eddy with the highest domoic acid concentrations coincided with high numbers of Pseudo-nitzschia pseudodelicatissima (Hasle) Hasle (2.7 µg DA equivalents L-1, up to 0.6 X 106 cells L-1 in 1997 and 0.2 µg DA equivalents L-1, up to 0.2 X 106 cells L-1 in 1998), a species known to produce toxin in this region. Other known toxin-producing species were sometimes present, but at ≪5% of the total Pseudo-nitzschia population when ≫0.1 µg DA equivalents L-1 were measured. In 1998, large-scale surveys indicated that high levels of particulate DA in seawater persisted at least until 1 October, covering a maximum area of 100 km2 off the Washington coast in midsummer. The appearance of high levels of DA (up to 2.7 µg DA equivalents L-1), coincident with high numbers of P. pseudodelicatissima (up to 15.4 X 106 cells L-1) at Kalaloch beach on the central coast in late September, was followed by the accumulation of record levels of toxin in razor clams. This toxic episode was preceded by a downwelling-favorable wind event, with associated onshore transport in near-surface layers. We suggest that the Juan de Fuca eddy may be one source of DA to the Washington coast. The duration of upwelling and the exact timing of fall storms likely play an influential role in the intensity of the bloom and the movement of toxic cells from the eddy to the coast.

[1]  M. Busman,et al.  Domoic acid production near California coastal upwelling zones, June 1998 , 2000 .

[2]  Grethe Rytter Hasle,et al.  Diatoms: Cleaning and Mounting for Light and Electron Microscopy , 1970 .

[3]  N. Adams,et al.  Environmental conditions associated with domoic acid in razor clams on the Washington coast , 2000 .

[4]  F. G. Plumley,et al.  Harmful algal blooms and red tide problems on the U.S. west coast , 1997 .

[5]  J. R. Postel,et al.  Toxic diatoms in western Washington waters (U.S. west coast) , 1993, Hydrobiologia.

[6]  F. Chavez,et al.  Autecology of the diatom Pseudonitzschia australis, a domoic acid producer, from Monterey Bay, California , 1992 .

[7]  D. Mackas,et al.  A performance comparison for two lagrangian drifter designs , 1989 .

[8]  The vorticity balance on the Southern British Columbia continental shelf , 1989 .

[9]  Roman Marin,et al.  Mortality of sea lions along the central California coast linked to a toxic diatom bloom , 2000, Nature.

[10]  K. Denman,et al.  Distribution of Nitzschia pungens in Coastal Waters of British Columbia , 1991 .

[11]  D. Hampson,et al.  A microplate receptor assay for the amnesic shellfish poisoning toxin, domoic acid, utilizing a cloned glutamate receptor. , 1997, Analytical biochemistry.

[12]  M. Quilliam,et al.  AN OUTBREAK OF DOMOIC ACID POISONING ATTRIBUTED TO THE PENNATE DIATOM PSEUDONITZSCHIA AUSTRALIS 1 , 1992 .

[13]  H. Barnett,et al.  Salt clean-up procedure for the determination of domoic acid by HPLC. , 1994, Natural toxins.

[14]  W. Crawford,et al.  Spread of oil from theTenyo Maru, off the Southwest coast of Vancouver Island , 1993 .

[15]  M. Busman,et al.  Pseudo-nitzschia sp. cf. pseudodelicatissima — a confirmed producer of domoic acid from the northern Gulf of Mexico , 2001 .

[16]  H. Barnett,et al.  Occurrence of domoic acid in Washington state razor clams (Siliqua patula) during 1991-1993. , 1994, Natural toxins.

[17]  Adriana Huyer,et al.  The coastal ocean off Oregon and northern California during the 1997–8 El Niño , 2002 .