Temporal and spatial trends in heavy metal concentrations in the marine mussel Mytilus edulis from the Western Scheldt estuary (The Netherlands)

Since the first North Sea Conference (1984, Bremen), all countries bordering the North Sea made commitments to reduce discharge of hazardous substances into the North Sea. From Belgium and The Netherlands, large reductions (upto 90) in heavy metal emissions from land-based sources have been reported between 1985 and 2000. Recently, some studies in the Western Scheldt estuary (WS) have shown that total metal concentration in the water, sediments and suspended particles have decreased compared to levels in the 70s. However, data on aquatic organisms is still very limited and it is therefore difficult to confirm whether the reductions in pollution input and generally improving water quality in the WS have a corresponding impact on the levels of heavy metals in aquatic organisms. The current study measured metal concentrations in the soft tissues of mussels, Mytilus edulis (known to be good indicators of environmental metal pollution) during the period 1996–2002. Spatial (salinity and pollution gradients), temporal and seasonal variations were also studied. Results showed a down-stream decreasing trend for the metals studied (Cd, Co, Cr, Cu, Fe, Mn, Ni, Pb and Zn) during all sampling campaigns. There was also a significant seasonal effect on tissue metal concentrations, with a peak observed around spring in both WS and the nearby less polluted Eastern Scheldt (ES). On temporal trends, a clear drop of metals in mussels was observed in the early 80s coinciding with the start of the efforts to reduce chemical pollution input into the North Sea. Since those early reductions, metal concentrations in mussels generally remained unchanged upto mid 90s. However, in recent times metal concentration in mussels have increased significantly, for example Cd in 2002 was almost 10 times the values in 1983 and similar to levels seen during the peak in the 70s. Other metals also increased in the 90s also reaching levels seen in the 70s. As there is no indication of recent increase in metal input into the estuary, we suggest that increased metal concentrations observed in mussels in recent years especially in the upper estuary are most likely a result of changes in physical and chemical speciation and metal bioavailability. Such changes may be caused by changes in some water quality parameters in the estuary (i.e. increased dissolved oxygen, concentration of organic matter), resulting in conditions that favour releases of sediment-bound metals into the water column. The relationship between metal content and season showed very similar annual profiles in the polluted WS and less polluted ES. Thus, seasonal variations in metal concentrations appear to be largely controlled by biological processes, while total body burdens are dependent on environmental levels and bioavailability.     

Evidence that arginyl-glycyl-aspartate peptides and fibrinogen gamma chain peptides share a common binding site on platelets

Synthetic peptides corresponding to the carboxyl terminus of the fibrinogen gamma chain inhibit the binding of fibrinogen, fibronectin, and von Willebrand factor to platelets, yet the active decapeptide sequence has only been found in fibrinogen to date. In contrast, all three proteins contain Arg-Gly-Asp sequences, and peptides containing Arg-Gly-Asp are potent inhibitors of their binding to activated platelets. We have analyzed the relationship between these peptide sets by direct binding assays. H12 (gamma 400-411) inhibited the binding of an Arg-Gly-Asp-containing peptide to platelets with similar dose response to inhibition of fibronectin binding. We have previously reported that GPIIb-IIIa binds to immobilized Arg-Gly-Asp peptides and can be eluted by Arg-Gly-Asp-containing peptides in solution. Both H12 and L10 (gamma 402-411) completely eluted GPIIb-IIIa bound to immobilized Arg-Gly-Asp peptides. Conversely, when GPIIb-IIIa was bound to immobilized L10, either L10 or an Arg-Gly-Asp peptide could elute it. Peptide specificity was established by the failure of Gly-Arg-Gly-Glu-Ser-Pro or acetylated L10 to elute GPIIb-IIIa from the immobilized peptides. These results indicate that the two peptide sets interact with the same receptor which contains GPIIb-IIIa.     

The Streptomyces K15 DD-peptidase/penicillin-binding protein. Active site and sequence of the N-terminal region.

Fragments of the lipophosphoglycan of Leishmania donovani were generated by phospholipase C digestion and mild acid hydrolysis. The fragments were purified and examined for inhibitory activity on protein kinase C isolated from rat brains. On a molar basis, the 1-O-alkylglycerol portion of LPG exhibited the most inhibitory activity, whereas the carbohydrate domain was not as effective. In addition, several glycolipid antigens from L. major, which contain short carbohydrate chains attached to phosphatidylinositol, were also efficient inhibitors of the enzyme. These results are consistent with the hypothesis that protein kinase C may be a key target for the parasites to overcome within host macrophages.     

Additional regular echinoids from the upper cretaceous in the maastricht area (belgium)

Four additional species of regular echinoids from the Maastricht type-area, brought to light by intensive collecting, are described. Three of these were never reported before from the Low Countries. Their taxonomic status is discussed.     

High-resolution mapping by YAC fragmentation of a 2.5-Mb Xp22 region containing the human RS, KFSD and CLS disease genes

The disease loci for X-linked Retinoschisis (RS), Keratosis follicularis spinulosa decalvans (KFSD), and Coffin-Lowry syndrome (CLS) have been localized to the same, small region in Xp22 on the human X Chromosome (Chr). To generate a high-resolution map of the available contig in this area, we have used the YAC fragmentation vectors pBP108/ADE2 and pBP109/ADE2 and generated fragmented YACs from a 2.5-Mb YAC (y939H7) spanning the mentioned disease gene candidate regions. Forty-seven fragmented YACs were generated and analyzed, ranging in size from 170 kb to over 2400 kb. The resulting YAC fragmentation panel was used to construct a detailed restriction map of the region and has been used to bin clones and markers. As a deletion panel, it will present a valuable resource for further mapping. Received: 31 December 1996 / Accepted: 22 February 1997     

Towards a methodology for taking physical degradation of ecosystems into account in LCA

An analytic procedure has been followed to select adequate methods to express ecosystem degradation in LCA. This procedure consisted of problem definition, identification of relevant issues, of a quantitative expression for ecosystem degradation and of possible nature value indicators and building a framework of criteria for selecting adequate methods. With the selection framework a first screening of methods was performed. For full quantification the following formula is proposed: ED = L (N_r- N_a), with land use I. = A t and nature value change (N_r- N_a) Degradation due to an activity appears difficult to operationalise, but ecosystem suppression by activities can well be assessed. N_r is then the natural background or would-be natural situation. N_a can best be described by the actual state during the activity, unless hard data on restoration is available. N_a and N_r can be expressed in the biomass production indicator NPP - NCR Biodiversity and/or erosion may be added to include irreversible effects.