Dietary ingestion of fine sediments and microalgae represent the dominant route of exposure and metal accumulation for Sydney rock oyster (Saccostrea glomerata): A biokinetic model for zinc.
Past studies disagree on the extent to which dissolved or dietary uptake contribute to metal bioaccumulation in the filter-feeding Sydney rock oyster (Saccostrea glomerata) in urbanized estuaries. Although most data support the assumption that fine sediments are a major route of metal uptake in these bivalves, some studies based in the Sydney estuary, Australia, have indicated a poor correlation. In the present study, seawater, sediment and microalgae were radiolabelled with (65)Zn tracer and exposed to S. glomerata to assess the influence of dissolved and dietary sources to Zn bioaccumulation. Oysters in the dissolved-phase uptake experiment (5, 25 and 50 μg L(-1) (65)Zn for 4 d followed by 21 days of depuration) readily accumulated (65)Zn for all three concentrations with an uptake rate constant of 0.160±0.006 L dry weight g(-1) d(-1). Oysters in the dietary assimilation experiment (1h pulse-feed of either (65)Zn-radiolabelled suspended fine-fraction (<63 μm) sediment or the microalgae Tetraselmis sp.) accumulated (65)Zn, with assimilation efficiencies of 59 and 67% for fine sediment and microalgae, respectively. The efflux rates were low for the three experiments (0.1-0.5% d(-1)). A bioaccumulation kinetic model predicts that uptake of Zn will occur predominantly through the dietary ingestion of contaminated fine sediment particles and microalgae within the water column, with considerably greater metal bioaccumulation predicted if oysters ingested microalgae preferentially to sediments. However, the model predicts that for dissolved Zn concentrations greater than 40 μg L(-1), as observed during precipitation events, the uptake of the dissolved phase may contribute ≥50% to accumulation. Overall, the results of the present study suggest that all three sources may be important exposure routes to S. glomerata under different environmental conditions, but contributions from dietary exposure will often dominate.
Environmental Geology Group, School of Geosciences, The University of Sydney, Sydney, NSW, Australia. Electronic address: jungho.lee@sydney.edu.au.
J-H
JH
Lee
Environmental Geology Group, School of Geosciences, The University of Sydney, Sydney, NSW, Australia.
G F
GF
Birch
Institute for Environmental Research, Australian Nuclear Science and Technology Organisation, Sydney, NSW, Australia.
T
T
Cresswell
Institute for Environmental Research, Australian Nuclear Science and Technology Organisation, Sydney, NSW, Australia.
M P
MP
Johansen
Centre for Environmental Contaminants Research, CSIRO Land and Water, Sydney, NSW, Australia.
M S
MS
Adams
Centre for Environmental Contaminants Research, CSIRO Land and Water, Sydney, NSW, Australia.
S L
SL
Simpson
D000818:Animals; D001315:Australia; D004032:Diet; D063366:Estuaries; D019015:Geologic Sediments / Q000737:chemistry*; D058086:Microalgae / Q000737:chemistry*; D010125:Ostreidae / Q000187:drug effects* / Q000378:metabolism*; D012623:Seawater / Q000737:chemistry; D014874:Water Pollutants, Chemical / Q000633:toxicity; D015032:Zinc / Q000378:metabolism / Q000633:toxicity*
D014874:Water Pollutants, Chemical; D015032:Zinc
Bioaccumulation; Biokinetic modelling; Metals; Oysters; Radioisotopes