Biogeochemical malfunctioning in sediments beneath a deep-water fish farm

We investigated the environmental impact of a deep water fish farm (190 m). Despite deep water and low water currents, sediments underneath the farm were heavily enriched with organic matter, resulting in stimulated biogeochemical cycling. During the first 7 months of the production cycle benthic fl...

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Veröffentlicht in:Environmental pollution (1987) 2012-11, Vol.170, p.15-25
Hauptverfasser: Valdemarsen, Thomas, Bannister, Raymond J., Hansen, Pia K., Holmer, Marianne, Ervik, Arne
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container_issue
container_start_page 15
container_title Environmental pollution (1987)
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creator Valdemarsen, Thomas
Bannister, Raymond J.
Hansen, Pia K.
Holmer, Marianne
Ervik, Arne
description We investigated the environmental impact of a deep water fish farm (190 m). Despite deep water and low water currents, sediments underneath the farm were heavily enriched with organic matter, resulting in stimulated biogeochemical cycling. During the first 7 months of the production cycle benthic fluxes were stimulated >29 times for CO2 and O2 and >2000 times for NH4+, when compared to the reference site. During the final 11 months, however, benthic fluxes decreased despite increasing sedimentation. Investigations of microbial mineralization revealed that the sediment metabolic capacity was exceeded, which resulted in inhibited microbial mineralization due to negative feed-backs from accumulation of various solutes in pore water. Conclusions are that (1) deep water sediments at 8 °C can metabolize fish farm waste corresponding to 407 and 29 mmol m−2 d−1 POC and TN, respectively, and (2) siting fish farms at deep water sites is not a universal solution for reducing benthic impacts. ► We studied the biogeochemistry in sediments beneath a deep-water fish farm. ► Initially, sediment biogeochemical cycling was stimulated to high levels. ► After 10 months, microbial mineralization was inhibited due to organic overloading. ► Conclusion: deep water sediment has an upper limit for organic matter mineralization. ► Conclusion: deep water fish farms can lead to negative environmental impacts. Siting fish farms at deep water farming locations is not a universal solution for alleviating benthic impacts.
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Psychology ; General aspects ; Geologic Sediments - chemistry ; Methane - analysis ; mineralization ; N-mineralization ; organic matter ; oxygen ; Salmon - growth &amp; development ; Seawater - chemistry ; Sedimentation ; sediments ; solutes ; Sulfate reduction ; Sulfide ; Sulfide-buffering ; Threshold ; wastes ; water currents ; Water Pollutants - analysis</subject><ispartof>Environmental pollution (1987), 2012-11, Vol.170, p.15-25</ispartof><rights>2012 Elsevier Ltd</rights><rights>2014 INIST-CNRS</rights><rights>Copyright © 2012 Elsevier Ltd. 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Despite deep water and low water currents, sediments underneath the farm were heavily enriched with organic matter, resulting in stimulated biogeochemical cycling. During the first 7 months of the production cycle benthic fluxes were stimulated &gt;29 times for CO2 and O2 and &gt;2000 times for NH4+, when compared to the reference site. During the final 11 months, however, benthic fluxes decreased despite increasing sedimentation. Investigations of microbial mineralization revealed that the sediment metabolic capacity was exceeded, which resulted in inhibited microbial mineralization due to negative feed-backs from accumulation of various solutes in pore water. Conclusions are that (1) deep water sediments at 8 °C can metabolize fish farm waste corresponding to 407 and 29 mmol m−2 d−1 POC and TN, respectively, and (2) siting fish farms at deep water sites is not a universal solution for reducing benthic impacts. ► We studied the biogeochemistry in sediments beneath a deep-water fish farm. ► Initially, sediment biogeochemical cycling was stimulated to high levels. ► After 10 months, microbial mineralization was inhibited due to organic overloading. ► Conclusion: deep water sediment has an upper limit for organic matter mineralization. ► Conclusion: deep water fish farms can lead to negative environmental impacts. Siting fish farms at deep water farming locations is not a universal solution for alleviating benthic impacts.</description><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Aquaculture</subject><subject>Atlantic salmon</subject><subject>biogeochemical cycles</subject><subject>Biological and medical sciences</subject><subject>C-mineralization</subject><subject>carbon dioxide</subject><subject>Carbon Dioxide - analysis</subject><subject>Ecological and Environmental Phenomena</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>environmental impact</subject><subject>Environmental Monitoring</subject><subject>fish farms</subject><subject>Fishes</subject><subject>Fundamental and applied biological sciences. 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subjects Animal, plant and microbial ecology
Animals
Applied ecology
Aquaculture
Atlantic salmon
biogeochemical cycles
Biological and medical sciences
C-mineralization
carbon dioxide
Carbon Dioxide - analysis
Ecological and Environmental Phenomena
Ecotoxicology, biological effects of pollution
environmental impact
Environmental Monitoring
fish farms
Fishes
Fundamental and applied biological sciences. Psychology
General aspects
Geologic Sediments - chemistry
Methane - analysis
mineralization
N-mineralization
organic matter
oxygen
Salmon - growth & development
Seawater - chemistry
Sedimentation
sediments
solutes
Sulfate reduction
Sulfide
Sulfide-buffering
Threshold
wastes
water currents
Water Pollutants - analysis
title Biogeochemical malfunctioning in sediments beneath a deep-water fish farm
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