The determination of copper (Cu) speciation and its bioavailability in natural waters is an important issue due to its specific role as an essential micronutrient but also a toxic element at elevated concentrations. Here, we report an improved anodic stripping voltammetry (ASV) method for organic Cu speciation, intended to eliminate the important problem of surface-active substances (SAS) interference on the voltammetric signal, hindering measurements in samples with high organic matter concentration. The method relies on the addition of nonionic surfactant Triton-X-100 (T-X-100) at a concentration of 1 mg L−1. T-X-100 competitively inhibits the adsorption of SAS on the Hg electrode, consequently 1) diminishing SAS influence during the deposition step and 2) strongly improving the shape of the stripping Cu peak by eliminating the high background current due to the adsorbed SAS, making the extraction of Cu peak intensities much more convenient. Performed tests revealed that the addition of T-X-100, in the concentration used here, does not have any influence on the determination of Cu complexation parameters and thus is considered "interference-free." The method was tested using fulvic acid as a model of natural organic matter and applied for the determination of Cu speciation in samples collected in the Arno River estuary (Italy) (in spring and summer), characterized by a high dissolved organic carbon (DOC) concentration (up to 5.2 mgC L−1) and anthropogenic Cu input during the tourist season (up to 48 nM of total dissolved Cu). In all the samples, two classes of ligands (denoted as L1 and L2) were determined in concentrations ranging from 3.5 ± 2.9 to 63 ± 4 nM eq Cu for L1 and 17 ± 4 to 104 ± 7 nM eq Cu for L2, with stability constants logKCu,1 = 9.6 ± 0.2–10.8 ± 0.6 and logKCu,2 = 8.2 ± 0.3–9.0 ± 0.3. Different linear relationships between DOC and total ligand concentrations between the two seasons suggest a higher abundance of organic ligands in the DOM pool in spring, which is linked to a higher input of terrestrial humic substances into the estuary. This implies that terrestrial humic substances represent a significant pool of Cu-binding ligands in the Arno River estuary.

14Chromium is a toxic element naturally present in natural waters whose chemical speciation 15 regulates its cycling, mobility and bioavailability. We present here: 1-an improved analytical 16 method for chromium speciation (Cr(VI) vs Cr(III)) in estuarine samples by catalytic 17 adsorptive cathodic stripping voltammetric (cat-AdCSV) and 2-a study highlighting a 18 significant change of redox speciation during summer and winter. Initial measurements first 19 revealed that surface-active substances (SAS) present in estuarine samples strongly influenced 20 the analytical determination of Cr by partially masking the Cr peak through an increase of the 21 background current. We found that the application of a low negative accumulation potential (-22 1.65 V) resulted in much better voltammograms compared to those obtained using the usual 23 accumulation potential of -1.0 V . Using humic acid (HA) as a model SAS of natural origin, 24we show that this negative potential clearly prevents adsorption of SAS on the Hg-electrode 25 surface, which in turns benefits the adsorption of the in-situ formed Cr(III)-DTPA complex 26 and the resulting signal. The optimised method was applied to determine chromium redox 27 speciation and distribution along the 23 km long salinity gradient, well oxygenated, Krka 28 River estuary (Croatia). Cr(VI) was found to be the dominant redox species in both summer 29 and winter, with Cr(III) contribution being lower in summer (up to ~30%, average of ~5%) 30 than in winter (up to ~50%, average of ~30%). In summer, lower concentrations of Cr(VI) 31 were found in the freshwater end-member (2.5 nM) than in the seawater end-member (4-5 32 nM), while the opposite trend was found in winter. Hexavalent chromium exhibited a non-33 conservative behaviour along the salinity gradient for both seasons. Chromium predominantly 34 exists in dissolved phase, and contribution of particles reactive Cr(III) was minor. 35

Environmental contextPlatinum concentrations in natural waters such as oceans, rivers and lakes are extremely low, hindering studies of Pt distributions and biogeochemical cycles. An improved electrochemical method was used to reliably determine Pt in estuarine conditions at trace concentrations. Platinum displayed a near-conservative behaviour along the salinity gradient of the estuary, with about 90% remaining in the dissolved form. AbstractExtremely low concentrations of platinum in natural waters require very sensitive analytical techniques, with adsorptive cathodic stripping voltammetry (AdCSV) being one of the most frequently used techniques. A ‘fine tuning’ of the voltammetric parameters, along with advanced data treatment based on derivative transformations, allowed us to determine reliably Pt levels down to 50 fM (0.05 pM). By using short modulation and interval times of the differential pulse stripping waveform, and applying a 4th derivative transformation to the voltammograms, the limit of detection (LOD) was lowered down to 10 fM. Although very small concentrations of surface-active substances (e.g. 0.025mgL−1 fulvic acid) strongly influenced the method sensitivity, recoveries of spiked samples were not impacted (~100%). The application of a desorption step (Eds=−1.35V; tds=2s) at the end of the accumulation significantly improved the sensitivity, presumably through the removal of adsorbed surface-active substances. Using this optimised methodology, we determined the Pt distribution in the pristine Krka River estuary in the winter and summer periods by performing both horizontal transects and vertical profiles (salinity ~1 to 39). In surface waters, dissolved Pt concentrations gradually increased towards the seawater end-member (from ~0.15 to ~0.3 pM). A small deviation from the conservative mixing line was observed at salinities below 10, which may reflect changes in Pt redox speciation. In bottom waters, the trend was opposite with dissolved Pt concentrations increasing towards the freshwater end-member, probably owing to progressive accumulation related to seawater residence time. On average, 90% of Pt was present in the dissolved form.

A size partitioning of several trace metals (Zn, Cd, Pb, Cu, Ni, Co, Mn, Fe and Al) between five size fractions (<3 kDa, 3 kDa–0.1 µm, 0.1 µm–1.2 µm, 1.2 µm–5 µm and >5 µm) was studied in the vertical salinity gradient of the highly stratified Krka River estuary. The results indicated a dominant river source for Zn, Co, Mn, Fe and Al and a diluting effect on Cd, Pb and Ni. The truly dissolved fraction (<3 kDa) dominated the Zn, Cd, Cu, Ni and Co pool, and a large part of Pb, Mn, Fe and Al was present in >5 µm particles. Pb, Mn, Fe and Al were closely related, showing a precipitation and colloidal aggregation in the surface layers and dissolution in the seawater layer. The highest percentage (30–37%) of colloids (3 kDa–0.1 µm) in the dissolved pool was found for Pb, Cu, Fe and Al. Differences in size distribution between low and high river flow periods revealed that Zn, Pb, Co, Mn, Fe and Al are introduced by the river mostly in the 3 kDa–5 µm size range. Therefore, a low percentage of colloidally bound metals compared to other coastal areas can be explained by a limited riverine input of terrigenous material, characteristic for this estuary. Correlation with PARAFAC components revealed associations of Cu with protein-like substances and Co with humic-like substances. The accumulation of Cu at the freshwater-seawater interface coupled with an increase of its colloidal fraction was observed, apparently governed by biologically produced organic ligands.

Description The Symposium on Materials Performance and the Deep Sea was presented during the Seventy-first Annual Meeting of the Society held in San Francisco, Calif., 23—29 June 1968. The symposium was sponsored by Committees G01 on Corrosion of Metals and G03 on Deterioration of Nonmetallic Materials in cooperation with the Marine Technology Society, Bay Chapter. H. W. Dubach, U.S. Naval Oceanographic Office, served as chairman of this symposium, and J. C. Freche, National Aeronautics and Space Administration, served as co-chairman. J. V. Dwyer, Bechtel Corp., presided at the Session on Nonmetals, and F. M. Rinehart, U.S. Naval Civil Engineering Laboratory, presided at the Session on Metals. Members of the program committee consisted of: W. H. Ailor, Jr., Reynolds Metal Co.; W. M. Bejuki, Bioscience Information Corporation of Biological Abstracts; C. J. Wessel, John I. Thompson Co.; H. L. Hamilton, Ocean City Research Corp.; John Padan, Bureau of Mines; and A. W. Anderson, Washington Science Center.