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dc.contributor.authorBroch, Ole Jacob
dc.contributor.authorEllingsen, Ingrid H.
dc.contributor.authorForbord, Silje
dc.contributor.authorWang, Xinxin
dc.contributor.authorVolent, Zsolt
dc.contributor.authorAlver, Morten
dc.contributor.authorHandå, Aleksander
dc.contributor.authorAndresen, Kjersti
dc.contributor.authorSlagstad, Dag
dc.contributor.authorReitan, Kjell Inge
dc.contributor.authorOlsen, Yngvar
dc.contributor.authorSkjermo, Jorunn
dc.date.accessioned2018-02-20T15:02:48Z
dc.date.available2018-02-20T15:02:48Z
dc.date.created2013-08-15T11:11:39Z
dc.date.issued2013
dc.identifier.citationAquaculture Environment Interactions. 2013, 4 (2), 187-206.nb_NO
dc.identifier.issn1869-215X
dc.identifier.urihttp://hdl.handle.net/11250/2486076
dc.description.abstractA 3-dimensional hydrodynamic−ecological model system (SINMOD) was used to estimate the full-scale cultivation potential of the brown alga Saccharina latissima in integrated multi-trophic aquaculture (IMTA) with Atlantic salmon Salmo salar. A previously developed model for the frond size and composition (carbon and nitrogen content) of S. latissima sporophytes was adjusted to data from an outdoor mesocosm growth experiment and then coupled and run online with the 3-dimensional model system. Results from simulations were compared with data from an IMTA field experiment, providing partial validation of the hydrodynamic–ecological– kelp model system. The model system was applied to study the large-scale cultivation potential of S. latissima in IMTA with salmon and to quantify its seasonal bioremediation potential. The results suggest a possible yield of 75 t fresh weight S. latissima ha−1 in 4 mo (February to June) and about 170 t fresh weight ha−1 in 10 mo (August to June). The results further suggest that the net nitrogen consumption of a 1 ha S. latissima installation in the vicinity of a fish farm producing approximately 5000 t salmon in a production cycle is about 0.36 (0.15) t NH4 +-N, or a removal of 0.34% (0.41%) of the dissolved inorganic nitrogen effluent with a cultivation period from August (February) to June. Due to the differing seasonal growth patterns of fish and kelp, there was a mismatch between the maximum effluent of NH4 +-N from the fish farm and the maximum uptake rates in S. latissima.nb_NO
dc.language.isoengnb_NO
dc.publisherInter Researchnb_NO
dc.rightsNavngivelse 4.0 Internasjonal*
dc.rights.urihttp://creativecommons.org/licenses/by/4.0/deed.no*
dc.titleModelling the cultivation and bioremediation potential of the kelp Saccharina latissima in close proximity to an exposed salmon farm in Norwaynb_NO
dc.typeJournal articlenb_NO
dc.typePeer reviewednb_NO
dc.description.versionpublishedVersionnb_NO
dc.source.pagenumber187-206nb_NO
dc.source.volume4nb_NO
dc.source.journalAquaculture Environment Interactionsnb_NO
dc.source.issue2nb_NO
dc.identifier.doi10.3354/aei00080
dc.identifier.cristin1043343
dc.relation.projectNotur/NorStore: NN2967Knb_NO
dc.description.localcode© The authors 2013. Open Access under Creative Commons by Attribution Licence. Use, distribution and reproduction are un - restricted. Authors and original publication must be credited.nb_NO
cristin.unitcode194,66,10,0
cristin.unitcode194,63,25,0
cristin.unitnameInstitutt for biologi
cristin.unitnameInstitutt for teknisk kybernetikk
cristin.ispublishedtrue
cristin.fulltextoriginal
cristin.qualitycode1


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