Controlled artificial upwelling in a fjord to stimulate non-toxic algae

Abstract During the summer, primary production in the surface layers of some fjords depletes the nutrients to the degree that some species of toxic algae can dominate. We describe field experiments employing a bubble curtain and a submerged freshwater outlet to lift significant amounts of nutrient-rich seawater to the light zone to provide an environment in which non-toxic algae can bloom. The motivation for the experiment is to provide a local region with stimulated growth of non-toxic phytoplankton and thereby creating a possibility for mussels to be cleansed from the effects of toxic algae. In the first experiment, a 100-m long bubble curtain, using three perforated pipes submerged to 40 m depth, was operated in the Arnafjord, a side arm of Sognefjorden in western Norway. An air supply of 44 Nm 3 each minute lifted 65 m 3 /s of deeper seawater to the upper layer with intense mixing during a period of 3 weeks. The mixed water flowed from the mixing region at depths from 5 to 15 m. Within a few days, the mixture of nutrient-rich water covered most of the inner portion of Arnafjord. In the second experiment, the 40 m deep, 26 m 3 /s discharge of freshwater from the Jostedal hydropower plant to Gaupnefjord, another side arm of Sognefjorden, was manipulated to enhance the upwelling of seawater by using a diffuser plate. The increased entrainment of seawater to the buoyant plume led to an intrusion of the discharge into the compensation current at 5–10 m depth and a longer residence time in the local fjord arm. The field experiment showed an entrainment of 117 m 3 /s of nutrient-rich seawater to the rising plume compared with 140 m 3 /s obtained in a small-scale laboratory simulation, implying a sub-optimal placement of the plate over the outlet plume. This, however, was still more energy-efficient than the bubble curtain. In both experiments (bubbles and freshwater discharge) the increased nutrient inputs to the light zone resulted in increased growth of phytoplankton with a relative reduction of toxic algae.

[1]  M. Rocchi,et al.  Potentially harmful microalgal distribution in an area of the NW Adriatic coastline: Sampling procedure and correlations with environmental factors , 2006 .

[2]  Ø. Strand,et al.  Primary production enhancement by artificial upwelling in a western Norwegian fjord , 2007 .

[3]  E. G. Vrieling,et al.  Harmful and Toxic Algal Blooms , 1996 .

[4]  P. Carlsson,et al.  The Ecological Significance of Phagotrophy in Photosynthetic Flagellates , 1998 .

[5]  S. Svensson Depuration of Okadaic acid (Diarrhetic Shellfish Toxin) in mussels, Mytilus edulis (Linnaeus), feeding on different quantities of nontoxic algae , 2003 .

[6]  P. Truquet,et al.  The diurnal vertical migrations of Dinophysis acuminata in an outdoor tank at Antifer (Normandy, France) , 1990 .

[7]  J. Berntsen,et al.  Production enhancement by artificial upwelling: a simulation study , 2002, Hydrobiologia.

[8]  Benoit Beliaeff,et al.  Explaining dinophysis cf. acuminata abundance in Antifer (Normandy, France) using dynamic linear regression , 1997 .

[9]  K. Stamnes,et al.  UV transmission in Norwegian marine waters: controlling factors and possible effects on primary production and vertical distribution of phytoplankton , 2005 .

[10]  Donald M. Anderson,et al.  Physiological ecology of harmful algal blooms , 1998 .

[11]  B. Reguera,et al.  Autoecology and some life history stages of Dinophysis acuta Ehrenberg , 1995 .

[12]  R. Margalef Life-forms of phytoplankton as survival alternatives in an unstable environment , 1978 .

[13]  H. Fischer Mixing in Inland and Coastal Waters , 1979 .

[14]  A. Godhe,et al.  Oceanographic settings explain fluctuations in Dinophysis spp. and concentrations of diarrhetic shellfish toxin in the plankton community within a mussel farm area on the Swedish west coast , 2002 .

[15]  M. Ledoux,et al.  Influence of initial toxicity and extraction procedure on paralytic toxin changes in the mussel. , 1993, Toxicon : official journal of the International Society on Toxinology.

[16]  A. Herbland,et al.  Environmental conditions which lead to increase in cell density of the toxic dinoflagellates Dinophysis spp. in nutrient-rich and nutrient-poor waters of the French Atlantic coast , 1992 .

[17]  E. G. Vrieling,et al.  Development of a Dinophysis acuminata bloom in the river Rhine plume (North Sea) , 1996 .

[18]  MARICULT Research Programme: background, status and main conclusions , 2002 .

[19]  E. Berdalet,et al.  Phytoplankton in a turbulent world , 1997 .

[20]  D. L. Aksnes,et al.  Nutrient enrichment experiments in plastic cylinders and the implications of enhanced primary production in Lindåspollene, western Norway , 1985 .