Hydroxylated and Methoxylated Brominated Diphenyl Ethers in the Red AlgaeCeramium tenuicorneand Blue Mussels from the Baltic Sea

2005 ◽  
Vol 39 (9) ◽  
pp. 2990-2997 ◽  
Author(s):  
Anna Malmvärn ◽  
Göran Marsh ◽  
Lena Kautsky ◽  
Maria Athanasiadou ◽  
Åke Bergman ◽  
...  
Chemosphere ◽  
2011 ◽  
Vol 84 (4) ◽  
pp. 527-532 ◽  
Author(s):  
Karin Löfstrand ◽  
Xitao Liu ◽  
Dennis Lindqvist ◽  
Sören Jensen ◽  
Lillemor Asplund

2018 ◽  
Vol 198 ◽  
pp. 240-256 ◽  
Author(s):  
Josefine Larsson ◽  
Katarzyna Smolarz ◽  
Justyna Świeżak ◽  
Magda Turower ◽  
Natalia Czerniawska ◽  
...  

2009 ◽  
Vol 43 (10) ◽  
pp. 3494-3499 ◽  
Author(s):  
Heli Routti ◽  
Robert J. Letcher ◽  
Shaogang Chu ◽  
Bert van Bavel ◽  
Geir W. Gabrielsen

2020 ◽  
Vol 7 ◽  
Author(s):  
Anna-Lucia Buer ◽  
Daniel Taylor ◽  
Per Bergström ◽  
Lukas Ritzenhofen ◽  
Annemarie Klemmstein

Marine Drugs ◽  
2020 ◽  
Vol 18 (5) ◽  
pp. 244 ◽  
Author(s):  
Sea-Yong Kim ◽  
Sara Rydberg

The neurotoxic non-protein amino acid β-N-methylamino-l-alanine (BMAA) is connected to the development of neurodegenerative diseases. BMAA has been shown to accumulate in aquatic ecosystems, and filter-feeding molluscs seem particularly susceptible to BMAA accumulation. The blue mussels farmed along the Swedish coastline in the Baltic Sea are, due to their small size, exclusively used to produce feed for chicken and fish in the agro–aqua cycle. We have investigated the possible biotransfer of BMAA from mussels, via mussel-based feed, into chickens. Chickens were divided into two groups, the control and the treatment. BMAA was extracted from the muscle, liver, brain, and eye tissues in both chicken groups; a UPLC-MS/MS method was subsequently used to quantify BMAA. The results indicate detectable concentrations of BMAA in both chicken groups. However, the BMAA concentration in chicken was 5.65 times higher in the treatment group than the control group, with the highest concentration found in muscle tissue extracted from the treatment group chickens. These data suggest that there is a BMAA transfer route within the agro-aqua cycle, so further investigation is recommended before using mussel-based feed in the chicken industry.


2005 ◽  
Vol 39 (21) ◽  
pp. 8235-8242 ◽  
Author(s):  
Anna Malmvärn ◽  
Yngve Zebühr ◽  
Sören Jensen ◽  
Lena Kautsky ◽  
Erik Greyerz ◽  
...  

1985 ◽  
Vol 1985 (1) ◽  
pp. 485-490 ◽  
Author(s):  
O. Linden ◽  
A. Rosemarin ◽  
A. Lindskog ◽  
C. Hoglund ◽  
S. Johansson

ABSTRACT The effects of a North Sea oil with or without the addition of dispersant were studied in a model of the littoral ecosystem of the Baltic Sea. Experiments were carried out in six pools with a volume of 8 m3 each, with flowthrough seawater and an ecosystem of the shallow rocky Baltic archipelago. All major fauna and flora were transferred into the pools in normal numbers and proportions. Two of the pools were exposed to oil alone. The amount of oil was equivalent to 20 ppm assuming total mixture. Two other pools were exposed to the same amount of oil and an oil dispersant (Corexit 9550, Exxon), and two pools served as controls. The effects studied were those on abundance of heterotrophic bacteria, periphyton photosynthesis, growth of bladder wrack, phytoplankton growth, zooplankton abundance and diversity, benthic fauna, physiological responses of certain crustaceans and molluscs, and the growth of blue mussels. In addition, the total photosynthesis and respiration of the ecosystem was studied. Concentrations of oil in water and in blue mussels were monitored. The experiments showed that almost all the measured parameters were affected. When comparing the effects between the pools, several of the results indicated a stronger response for oil alone compared to oil and dispersant. This was particularly obvious when monitoring the total production and respiration of the ecosystems. The explanation may be that the ecosystems in the pools exposed to oil and dispersant were exposed less time compared to those in the pools where oil alone was added. The oil and dispersant mixture obviously left the system much faster due to the water exchange compared to the oil without dispersant. In the latter case the oil adhered to surfaces and detritus and thus tended to stay longer in the environment. These results may provide valuable information for decision makers faced with an oil spill in shallow waters and who have an option to use oil spill dispersant.


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