UoB : Bergen Marine : Installations

Marine Biological Station

For enquiries about the Espeland Marine Biological Station not directly related to the Bergen Marine funding please contact the Manager: agnes.aadnesen@ifm.uib.no

 

The Marine Biological Station is located at Espeland, in the Raunefjord, 20 km South of downtown Bergen and about 5 km from the airport. The Station is especially equipped for large-scale experimental work on primary and secondary production, and at the same time is a gateway for diverse and well described particular habitats and model environments. The most outstanding feature at the station is the Mesocosm Laboratory

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View of the floating mesocosm

 
The mesocosm laboratory has been appointed as the National Mesocosm Centre by the Research Council of Norway, which has recently funded its upgrading. The centre has been designed for large-scale experimental work on primary and secondary production and consists in enclosed water masses with volumes between 2 and 30 m3 whose physical, chemical and biological parameters can be manipulated in a semi natural environment. Typical mesocosm experiments last for 3-6 weeks and are usually carried out by interdisciplinary teams. 

The National Mesocosm Centre includes a floating mesocosm laboratory and a land-based mesocosm system. Both units have water regulating devices and access to continous water supply from the surface or from 40 m depth.  Instruments for monitoring environmental factors are also available:
           - Light recorder (Li-Cor sea and land sensor with data logging appliance)
           - OTS recorder (Sea Bird Instr., records profiles or logs data continuously)

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One of the floating seawater enclosures

The floating mesocosm unit is located on a raft (approx. 50 m2) located at about 200 m from the shore. The enclosures consist of polyethylene bags (transmitting 90 % of the PAR) supported by floating frames. Up to 10 enclosures can be attached to the raft. The enclosures can be filled and continuously supplied with water from the surface or from 40 m depth.The floating mesocosm is equipped with:

     - 8 frames for enclosures with 1 m diametre
     - 6 frames for enclosures with 2 m diametre
     - electric supply

      - 2 pumps for water supply to the enclosures
      - air lifts for water circulation enhancement

The land-based mesocosm unit
is especially suitable for experiments where physical control, e.g. turbulence, is required. It is also suitable for other pelagic experiments dealing with the lower trophic levels not requiring large sample volumes. 

 

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Partial view of the land-based mesocosm

Sampling the land-based mesocosm

The land based mesocosm unit consists of:
- 12 fiberglass tanks (Ø: 1.5 m;  height: 1.5 m)
- 4  fiberglass tanks (Ø: 5 m; hight: 1.5 m)

Four of the small tanks can be placed inside one of the 5m diameter tanks. This functions as a water bath, and running water in the outer tank can provide daily temperature fluctuations. The thanks can be filled with sea water from 40 m, from the surface, or with fresh water.

 

Supporting Infrastructure:

 

Main Building

- auditorium for 52 people

- course lab for 12 students

- sorting lab with air hoods

- wet lab with aquaria and running seawater

- walk-in cool-rooms (2-20°C)

      - 2 with running seawater

      - 1 for culture of microalgae

- offices

- copy machine, phone, fax, internet, ISDN line

Guest House

- 20 rooms wiht private bath

- restaurant-type kithchen

- living-dining room and terrace with view to the fjord

- sauna

Equipment

- Analitical instruments

- Microscopes and some other lab equipment

- Some diving equipment

- 4 outboard motor boats

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Partial view of the Marine Biological Station: Main Building (in the middle and to the left), guest-house (dark building in the back), workshop and boat-house (white buildings on the right), live-zooplankton collector (on the left)

- Sampling devices: dredges, sledges, fishing gear and plankton nets

- the R/V "Hans Brattstrøm" can also dock at the Station

- Equipment for continuous collection of live zooplankton (Hydrotech; approx. 5 m3/min)

Some recent studies conducted at the UoB Marine Biological Station

Bratbak G, A. Jacobsen, M. Heldal, K. Nagasaki & F. Thingstad 1998   Virus production in Phaeocystis pouchetii and its relation to host cell growth and nutrition. Aquat. Microb. Ecol. 16:1-9.

Bratbak G, A. Jacobsen & M. Heldal 1998 Viral lysis of Phaeocystis pouchetii and bacterial secondary production. Aquat. Microb. Ecol. 16:11-16.

Båmstedt U, Nejstgaard JC, Solberg PT (1999) Utilisation of small-sized food algae by Calanus finmarchicus (Copepoda: Calanoida) and adaptation responses in its life-cycle. Sarsia 84:19-38

Castberg, T, Larsen, A, Sandaa, RA, Brussard CPD, Egge, JK, Heldal, M, Thyrhaug, R, van Hannen, EJ & Bratbak G (2001). Microbial population dynamics and diversity during a bloom of the marine coccolithophorid Emiliania huxleyi (Haptophyta) Mar. Ecol. Prog. Ser. 221:39-46

Egge, J.K. (1998). Are diatoms poor competitors at low phosphate concentrations ? J. Mar. Sys. 16: 191-198.

Evans C, SD Archer, S Jacquet & WH Wilson (In press) Viral lysis and microzooplankton grazing contribute to the decline of a Micromonas spp. population. Aquatic Microbial Ecology

Francis DTI, KG Foote, T Knutsen & L Calise. 1999.  Modelling the target strength of Calanus finmarchicus.  Acta Acoustica, 85: S124 & J. acoust. Soc. Am., 105: 1050.

Gorsky G, PR Flood, MJ Youngbluth, M Picheral & J-M Grisoni.  2000. Zooplankton distribution in four Western  Norwegian fjords. Estuar.Coast.Shelf Sci. . 50(1): 129-135

Hansen BW, BH Hygum, M Brozek, F Jensen & C Rey. 2000. Food web interactions in a Calanus finmarchicus dominated pelagic ecosystem – a mesocosm study. Journal of Plankton Research 22(3): 569-588

Hygum BH, C Rey & BW Hansen. 2000. Growth and development rates of Calanus finmarchicus nauplii during a diatom spring bloom. Marine Biology 136(6): 1075-1085.

Hygum BH, C Rey, BW Hansen & F Carlotti. 2000. Rearing cohorts of Calanus finmarchicus (Gunnerus) in mesocosms. ICES Journal of Marine Science 57: 1740-1751

Hygum BH, C Rey, BW Hansen & K Tande. 2000. Importance of food quantity to structural growth rate and neutral lipid reserves accumulated in Calanus finmarchicus. Marine Biology 136(6): 1057-1073.

Hoffmann F, Rapp HT, Zöller T, and Reitner J (in press) Growth and regeneration in cultivated fragments of the boreal deep water sponge Geodia barretti Bowerbank, 1858 (Geodiidae, Tetractinellida, Demospongiae). Journal of Biotechnology

Jacquet S, M Heldal, D Iglesias-Rodriguez, A Larsen, W Wilson, G Bratbak. 2002.  Flow cytometric Analysis of an E. huxleyi bloom terminated by viral infection. Aquatic Microbial Ecology 27:111-124.

Joint I, P Henriksen, GA Fonnes, D Bourne, TF Thingstad, B Riemann (2002) Competition for inorganic nutrients between phytoplankton and bacterioplankton in nutrient manipulated mesocosms. Aquat.Microb.Ecol. 29:145-159

Larsen A, Castberg T, Sandaa RA, Brussaard CPD, Egge J, Heldal M, Paulino A, Thyrhaug R, van Hannen EJ, Bratbak G (2001). Population dynamics and diversity of phytoplankton, bacteria and viruses in a seawater enclosure. Mar.Ecol. Prog. Ser. 221:47-57

Nejstgaard, J.C. 1997. Food web dynamics in flagellate-dominated marine environments. Trophic interactions between haptophytes, calanoid copepods and microzooplankton. Thesis for the partial fulfilment of the Dr. scient. degree. University of Bergen, Department of Fisheries and Marine Biology. 116 pp.

Nejstgaard, J.C., I. Gismervik, P.T. Solberg 1997 Feeding and reproduction by Calanus finmarchicus, and microzooplankton grazing during mesocosm blooms of diatoms and the coccolithophore Emiliania huxleyi. Marine Ecology Progress Series 147:197-217

Nejstgaard JC, BH Hygum, LJ Naustvoll & U Båmstedt. 2001. Zooplankton growth, diet and reproductive success compared in simultaneous diatom and flagellate-microzooplankton dominated plankton blooms. Marine Ecology Progress Series 221:77-91

Rey C, F Carlotti, . Tande & BH Hygum. 1999. Egg and faecal pellet production of female Calanus finmarchicus from controlled mesocosms and in situ populations: influence of age and feeding history. Marine Ecology Progress Series 188:133-148.

Svensen C, Egge, JK & Stiansen JE (2001). Can silicate and turbulence regulate the vertical flux of biogenic matter ? A mesocosm study. Mar. Ecol. Prog. Ser. 217: 67-80

Svensen C, Nejstgaard JC, Egge JK, Wassmann P (2002) Pulsing versus constant supply of nutrients (N,P, and Si): effect on phytoplankton, mesozooplankton and vertical flux of biogenic matter. Sci. Mar. 66(3):189-203

Søndergaard, M., P.J. leB. Williams, G. Cauwet, B. Riemann, C. Robinson, S. Terzic, E. Malcolm, S. Woodward and J. Worm. 2000. Net accumulation and flux of dissolved organic carbon and dissolved organic nitrogen in marine plankton communities. Limnology and Oceanography 45(5):1097-1111

Thingstad, T. F., H. Havskum, H. Kaas, T. G. Nielsen, B. Riemann, D. Lefevre & P. J. le B. Williams. 1999. Bacteria-protist interactions and organic matter degradation under P-limited conditions: Analysis of an enclosure experiment using a simple model Linmol. Oceanogr. 44:62-79

Williams, PJL & Egge, JK 1998. The management and behaviour of the mesocosms. Estu Coastl Shelf Sci 46, 3-14.