Biomarker responses and PAH uptake in Mya truncata following exposure to oil-contaminated sediment in an Arctic fjord (Svalbard).
Expanding industrial activity (notably oil and gas exploration) in the Arctic requires assessment of the potential impact of chemicals on marine organisms living in seawater at low temperature. The bivalve Mya truncata is common in Svalbard fjord (Norway) where it experiences low temperature throughout the year. To measure the impact of polycyclic aromatic hydrocarbons (PAH) on M. truncata, the responses of three biomarkers [total oxyradical scavenging capacity-assay (TOSC), plasma membrane stability of haemocytes and respiration rates] were investigated from bivalves exposed to sediment contaminated with a PAH mixture (crude oil). After two weeks of exposure to the contaminated sediment, TOSC showed no change. The high TOSC value (4010+/-1339 unit mg(-1) protein) of Mya truncata (control group) is thought to protect biomolecules with a low turnover rate efficiently in a low food availability environment. In the exposed bivalves, the haemocyte cellular membranes were significantly destabilised compared with controls (P<0.05). Respiration rate of control and PAH-exposed individuals (0.055+/-0.020 mg O(2) dw(-1) h(-1)) was similar and relatively low as is typical for polar bivalves, reflecting a strategy to minimise energy expenditure to cope with 9 months of starvation. Bioaccumulation of PAH by M. truncata was also low, due probably to a combination of low metabolic rate and reduced solubility of the oil compounds at low temperature. Data indicated an uptake of mainly low molecular weight compounds (two and three ring molecules). A good correlation of logBAF(lipid) (bioaccumulation factor) and logK(ow) (octanol/water partitioning coefficient) was shown (r(2)=0.87). Tissue sensitivity and/or functional differences (digestive gland vs. haemocytes), PAH uptake route (dietary vs. gills), the low metabolic rate of M. truncata and the low environmental temperature (reducing the bioavailability of PAH) are factors that help explain these findings.
Camus
L
L
Akvamiljø as, Mekjarvik 12, N-4070 Randaberg, Norway. Lionel.camus@unis.no
Birkely
S R
SR
Jones
M B
MB
Børseth
J F
JF
Grøsvik
B E
BE
Gulliksen
B
B
Lønne
O J
OJ
Regoli
F
F
Depledge
M H
MH
D000818:Animals; D001110:Arctic Regions; D001682:Biological Availability; D015415:Biomarkers / Q000032:analysis; D049872:Bivalvia; D004781:Environmental Exposure; D004784:Environmental Monitoring; D019015:Geologic Sediments; D008970:Molecular Weight; D010578:Petroleum; D011084:Polycyclic Aromatic Hydrocarbons / Q000009:adverse effects / Q000032:analysis / Q000493:pharmacokinetics*; D012995:Solubility; D013696:Temperature; D014018:Tissue Distribution
D015415:Biomarkers; D010578:Petroleum; D011084:Polycyclic Aromatic Hydrocarbons