Event name: | ES-02-004 | |
Country: | SPAIN | |
Nature of the harmful event: |
Seafood toxins | |
Event directly affected: |
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Toxicity detected: | Yes (Approximate range: DSP positive.) | |
Associated syndrome: | DSP | |
Unexplained toxicity: | No | |
Species implicated in toxin transmission (transvector): | ||
Report the outcome of a monitoring programme: | Yes (Monitoring Programme of the Centro de Control do Medio Mariño.) | |
Event occurred before in this location: | Yes (The DSP episodes caused by Dinophysis acuminata are a recurrent phenomenom in the Galician Rías with more or less incidence depending on the year.) | |
Individuals to contact: | MANEIRO, Juan , PAZOS, Yolanda , SALGADO, Covadonga |
Location: | Latitude: 42.340000, Longitude: -8.791667 | |
General location information: |
Ría de Foz, Ría de Vicedo-Barqueiro, Ría de A, Galicia, NW Spain. HAB Area code(s): ES-05 ES-06 ES-07 ES-08 |
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Additional location information: | 43º 44' - 42º 08.22' N ; 07º 15' - 09º 59' W. The affected area is dedicated to intensive mussel cultivation in rafts and to a high production of other molluscs in natural banks: clams, cockles, oyster and scallops are the main species exploited. | |
Bloom event dates (yyyy/mm/dd): |
Event Date:2002-09-23 Start: 2002-09-09, End: 2002-11-19 |
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Quarantine levels dates (yyyy/mm/dd): | ||
Additional date-related information: |
Causative organism known: | Yes | |
Causative Species/Genus: |
Dinophysis acuminata
(18,440 cells/L)
42º 20.40' N; 08º 47.50' W (St. P8) on 23/09/02 |
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Co-Ocurring Species/Genus: |
Rhizosolenia alata
(62,640 cells/L)
42º 20.40' N; 08º 47.50' W (St. P8) on 23/09/02 Ceratium fusus (23,760 cells/L) Leptocylindrus danicus (6,960 cells/L) |
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Chlorophyll concentration, if known: | 3.2 µg/L Chlª. µg/l | |
Additional bloom information: | ||
Event-related bibliography: |
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Nutrient information: |
AMONIUM:
0.37 - 0.74 mg/L
NITRITE: 0.03 - 0.12 mg/L PHOSPHATE: 0.27 - 0.42 mg/L |
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Temperature Range During Event: | Max: 19 °C, Min: 12 °C | |||||||||||||||||||||||||
Salinity Range During Event: | Max: 35, Min: 10 | |||||||||||||||||||||||||
Bloom location in the water column: |
Subsurface |
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Growth: |
Advected
In situ |
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Growth Comments | ||||||||||||||||||||||||||
Additional Environmental information: | Wind velocity: 24 Km/h. |
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Kit used: No | Type of kit used: | |||||||||||||||||||||||||||||||
Additional information: | The official detection method is by mouse bioassay: Yasumoto et al., Seafood toxins, 1984, 207-214. Some samples are analyzed by HPLC: Lee et al., Agric. Biol. Chem., 1987, 51, 877. | |||||||||||||||||||||||||||||||
Economic losses: | Not evaluated. | |||||||||||||||||||||||||||||||
Management decision: | Harvesting was closed in culture areas affected. Wild mussels (Mytilus galloprovincialis) are used as bioindicator for infaunal molluscs, then when assays are possitive for this species, infaunal molluscs are closed in that area. | |||||||||||||||||||||||||||||||
Additional harmful effect information: | Closures due to the presence of toxicity in molluscs is usual in the area and resource explitation strategies allows to face these closures without great problems. |