Speciation of dissolved copper and nickel in South San Francisco Bay: a multi-method approach

A multi-method approach was used to investigate the chemical speciation of dissolved copper and nickel in South San Francisco Bay. Dissolved copper speciation was determined by four different analytical approaches: competitive ligand equilibration-cathodic stripping voltammetry [CLE-CSV], differential pulse anodic stripping voltammetry using a thin mercury film rotating glassy carbon disk electrode [DPASV(TMF-RGCDE)], DPASV using a hanging mercury drop electrode [DPASV(HMDE)], and chelating resin column partitioning-graphite furnace atomic absorption spectrometry [CRCP-GFAAS]. Dissolved nickel speciation was determined by CLE-CSV and CRCP-GFAAS. Each of the methods employed provided useful insight into the chemical speciation of dissolved copper and nickel. CLE-CSV provided the best characterization of the stronger (but less predominant) of the two organic copper-complexing ligands detected, while DPASV(TMF-RGCDE) provided the truest measurement of inorganic copper, and therefore, the best characterization of the weaker organic copper-complexing ligand which exerted the strongest influence on dissolved copper speciation. These methods provide complementary results which can be combined to provide a more complete understanding of the chemical speciation of copper. DPASV(HMDE) and CRCP-GFAAS both provide an operational measurement of labile copper which includes some fraction of labile organic complexes in addition to inorganic copper species. CLE-CSV and CRCP-GFAAS both yielded similar results for nickel speciation indicating the presence of a single class of extremely strong nickel-complexing ligands. The dissolved copper in South San Francisco Bay is found to exist predominantly as organic complexes (80–92%). About 27% of dissolved copper was complexed with the stronger (L1; [CuL1 ≈ 13 nM, log K′CuL1 > 13.5) of the copper-complexing ligands detected, while copper complexed with the weaker ligand L2 comprised the greatest fraction of total dissolved copper species (52–65%; [CuL2] = 20–30 nM; log K′CuL2 = 9.0–9.6). A third to a half of total dissolved nickel was complexed by one, extremely strong class of organic ligands ([NiL] = 17–28 nM; log K′NiL > 17); the remaining total dissolved nickel existed as inorganic or labile forms.

[1]  R. Guillard,et al.  Limitation of marine phytoplankton reproductive rates by zinc, manganese, and iron1 , 1983 .

[2]  J. Moffett,et al.  Solvent extraction of copper acetylacetonate in studies of copper(II) speciation in seawater , 1987 .

[3]  W. Sunda,et al.  Measurement of free cupric ion concentration in seawater by a ligand competition technique involving copper sorption onto C18 SEP-PAK cartridges1 , 1987 .

[4]  P. Santschi,et al.  Metals in aquatic systems. , 1988, Environmental science & technology.

[5]  W. Sunda,et al.  The use of chemiluminescence and ligand competition with EDTA to measure copper concentration and speciation in seawater , 1991 .

[6]  J. Donat,et al.  A new cathodic stripping voltammetric method for determining organic copper complexation in seawater , 1992 .

[7]  M. Nimmo,et al.  The chemical speciation of dissolved nickel, copper, vanadium and iron in Liverpool Bay, Irish Sea , 1989 .

[8]  W. Sunda,et al.  Effect of chemical speciation on toxicity of cadmium to grass shrimp, Palaemonetes pugio: importance of free cadmium ion , 1978 .

[9]  C. V. D. Berg Determination of copper, cadmium and lead in seawater by cathodic stripping voltammetry of complexes with 8-hydroxyquinoline , 1986 .

[10]  W. Davison Defining the electroanalytically measured species in a natural water sample , 1978 .

[11]  A. R. Flegal,et al.  Dissolved trace element cycles in the San Francisco Bay estuary , 1991 .

[12]  K. Bruland,et al.  Copper complexation in the Northeast Pacific , 1988 .

[13]  J. Donat,et al.  Determination and data evaluation of copper complexation by organic ligands in sea water using cathodic stripping voltammetry at varying detection windows , 1992 .

[14]  I. Ruzic THEORETICAL ASPECTS OF THE DIRECT TITRATION OF NATURAL WATERS AND ITS INFORMATION YIELD FOR TRACE METAL SPECIATION , 1982 .

[15]  M. Nimmo,et al.  Determination of interactions of nickel with dissolved organic material in seawater using cathodic stripping voltammetry , 1987 .

[16]  Andrew G. Dickson,et al.  The equilibrium speciation of dissolved components in freshwater and sea water at 25°C and 1 atm pressure , 1981 .

[17]  J. P. Riley,et al.  An electrochemical study of Ni, Sb, Se, Sn, U and V in the estuary of the Tamar , 1991 .

[18]  H. P. Leeuwen Voltammetric titrations involving metal complexes: Effect of kinetics and diffusion coefficients. , 1987 .

[19]  J. R. Kramer,et al.  Determination of complexing capacities of ligands in natural waters and conditional stability constants of the copper complexes by means of manganese dioxide , 1979 .

[20]  C. V. D. Berg Organic and inorganic speciation of copper in the Irish Sea , 1984 .

[21]  E. Duursma,et al.  Organic complexation and its control of the dissolved concentrations of copper and zinc in the Scheldt estuary , 1987 .

[22]  J. Cloern,et al.  Trace metal associations in the water column of South San Francisco Bay, California , 1989 .

[23]  M. Gardner,et al.  An investigation of copper complexation in the severn estuary using differential pulse cathodic stripping voltammetry , 1990 .

[24]  Kenneth W. Bruland,et al.  ANALYSIS OF SEAWATER FOR DISSOLVED CADMIUM, COPPER AND LEAD: AN INTERCOMPARISON OF VOLTAMMETRIC AND ATOMIC ABSORPTION METHODS , 1985 .

[25]  K. Bruland,et al.  Direct determination of dissolved cobalt and nickel in seawater by differential pulse cathodic stripping voltammetry preceded by adsorptive collection of cyclohexane-1,2-dione dioxime complexes , 1988 .

[26]  R. Guillard,et al.  Reduction of marine phytoplankton reproduction rates by copper and cadmium , 1986 .

[27]  B. McDuffie,et al.  Use of Chelex resin for determination of labile trace metal fractions in aqueous ligand media and comparison of the method with anodic stripping voltammetry , 1979 .

[28]  D. Turner,et al.  Effects of the detection window on the determination of organic copper speciation in estuarine waters. , 1990 .

[29]  C. V. D. Berg Determination of the complexing capacity and conditional stability constants of complexes of copper(II) with natural organic ligands in seawater by cathodic stripping voltammetry of copper-catechol complex ions , 1984 .

[30]  C. V. D. Berg Determination of copper complexation with natural organic ligands in seawater by equilibration with MnO2 II. Experimental procedures and application to surface seawater , 1982 .

[31]  F. Morel,et al.  A field comparison of two methods for the determination of copper complexation: Bacterial bioassay and fixed-potential amperometry , 1987 .

[32]  K. Cantrell,et al.  The influence of temperature and pH on trace metal speciation in seawater , 1988 .