Abstract:Arsenic concentrations in estuarine sediments from England and Wales range over three orders of magnitude. The highest concentrations, up to 2500 figjg, occur in the sediments of estuaries in south west England associated with past or present metalliferous mining activity. Strong correlations exist between arsenic and iron in 1 N-HC1 extracts of different estuarine sediments. The As/Fe ratio in those estuaries not contaminated with mine wastes is n x 10 ~4, increasing to 190 x 10 ~4 in metalliferous sediments.… Show more
“…Any single change in metal concentration may reflect either one or the simultaneous influence of both variables. The effect of weight-driven changes on trace metal concentrations can be significant (Phillips 1976, Simpson 1979, this paper) and if not accounted for, can seriously compromise results from organisms used as bioindicators to monitor contamination (Goldberg et al 1978) or to study metal bioavailability (Whitfield & Lewis 1976, Langston 1980, 1982, Luoma & Bryan 1982.…”
The influence of seasonal changes in the weight of soft tissues on temporal fluctuations in tissue concentrations of Cu and Zn was examined in 4 populations of the clam Macoma balthica sampled in San Francisco Bay for a period of 2 to 5 yr. Fluctuations in metal concentration expected from changes in tissue weight between sampling dates were estimated by assuming that whole body metal burden was constant during the sampling interval. Comparison of estimated and actual metal concentrations showed that the degree to which fluctuations in trace metal concentrations were driven by weight changes d~ffered considerably among stations, among years at a single station, and between metals.
“…Any single change in metal concentration may reflect either one or the simultaneous influence of both variables. The effect of weight-driven changes on trace metal concentrations can be significant (Phillips 1976, Simpson 1979, this paper) and if not accounted for, can seriously compromise results from organisms used as bioindicators to monitor contamination (Goldberg et al 1978) or to study metal bioavailability (Whitfield & Lewis 1976, Langston 1980, 1982, Luoma & Bryan 1982.…”
The influence of seasonal changes in the weight of soft tissues on temporal fluctuations in tissue concentrations of Cu and Zn was examined in 4 populations of the clam Macoma balthica sampled in San Francisco Bay for a period of 2 to 5 yr. Fluctuations in metal concentration expected from changes in tissue weight between sampling dates were estimated by assuming that whole body metal burden was constant during the sampling interval. Comparison of estimated and actual metal concentrations showed that the degree to which fluctuations in trace metal concentrations were driven by weight changes d~ffered considerably among stations, among years at a single station, and between metals.
“…Trace metals that are associated with the EP, CP, ERP, MRP, and OSP (Agemain and Chau 1976) have been demonstrated to be strongly correlated to the concentration of trace metals in various aquatic organisms after normalizing with naturally occurring sediment associated geochemical components (Louma and Bryan 1978;Langston 1980Langston , 1982Tessier et al 1984;Bourgoin et al 1991). Trace metals concentrations in the sediment non-residual fraction from all stations are illustrated in Figure 3.…”
Section: N O N -R E S I D U a L Trace M E T A L Concentrationsmentioning
confidence: 98%
“…Bivalves are generally assumed to be reliable bio-indicators to provide a time-integrated measure of aquatic contaminants (e.g., trace metals) bioavailability (Phillips and Segar 1986). Therefore, studies have demonstrated that concentrations of trace metals in benthic organisms are strongly correlated to the sediment easily leachable trace metals fractions after normalizing with Fe, organic matter, or the sulphur content of the adjacent sediments (Luoma and Bryan 1978;Langston 1980;Bourgoin et al 1991). However, in the case of A. granosa, further laboratory and field studies are needed to evaluate its bioindicator capacity particularly in the uptake, accumulation, and retention of available trace metals.…”
Section: N O N -R E S I D U a L Trace M E T A L Concentrationsmentioning
Abstract. Trace metals in the sediments non-residual fraction and their relative abundance in various sedimentary components from the culture bed ofAnadara granosa were investigated. High levels of Cd (40%), Ni (40%), and Pb (43%) were associated with the sediment exchangeable phase (EP). The sediment moderately reducible phase (MRP) was more predominant than the easily reducible phase (ERP) and the organic sulphide phase (OSP) in the sorption of available trace metals. However, this area was not considered to be heavily impacted by trace metal pollution. Since there was no significant concentration gradients observed in sediments and bivalves collected from all stations, trace metal enrichment factors were determined. A. granosa collected from this area was enriched by Zn, Cu, Pb, Ni, Cd, and Ni.
“…What exactly causes these differences is not quite well understood, but it can be hypothesized that they are related to: (i) differences in diet; (ii) differences in the form of ingested arsenic; (iii) seasonal changes, and (iv) the geographical area. Langston [15] reported a contamination of the mollusk Srobicularia plana, at the southwestern coast of UK and related the elevated As levels to contamination of the sediment. It seemed that seasonal variations, together with phytoplanktonic activity that changed the chemical form of dissolved As in the water column, influenced the accumulation of As by the mollusks greatly.…”
Section: As Concentrations In Fish and Shellfishmentioning
Total and toxic (sum of As(III), As(V), monomethylarsenic (MMA), and dimethylarsenic (DMA)) As concentrations were assessed in 19 respectively 4 different fish and shellfish species from the North Sea. Following results were obtained: (i) for fish an average total As concentration of 12.8 microg/g ww and a P90 value of 30.6 microg/g ww; (ii) for shellfish an average total As concentration of 21.6 microg/g ww and a P90 value of 40.0 microg/g ww; (iii) for fish an average toxic As concentration of 0.132 microg/g ww and a P90 value of 0.232 microg/g ww; (iv) for shellfish an average toxic As concentration of 0.198 microg/g ww and a P90 value of 0.263 microg/g ww. For the Belgian consumer the average daily intake of total arsenic from fish, shellfish, fruit, and soft drinks (the main food carriers of As in Belgium) amounts to 285 microg/day with more than 95% coming from fish and shellfish, while for a high level consumer it amounts to 649 microg/day, more than twice the average value. Using the same daily consumption pattern for the selected food products as for total As, we find that the average daily intake of toxic As amounts to 5.8 microg/day, with a 50% contribution of fish and shellfish and the high level intake to 9.5 microg/day. When considering the FOA/WHO Expert Committee's recommendation for inorganic As intake of 2 microg/kg bw/day or 140 microg/day for a 70 kg person, the toxic dose in Belgium is thus an order of magnitude lower.
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