Use of laboratory toxicity tests with bivalve and echinoderm embryos to evaluate the bioavailability of copper in San Diego Bay, California, USA

Copper concentrations in parts of San Diego Bay (CA, USA) exceed ambient water quality criteria (WQC; currently 3.1 microg/L dissolved, U.S. Environmental Protection Agency [U.S. EPA]). In order to better understand the bioavailability of copper to water-column organisms in the bay, toxicity tests were performed with copper added to surface water collected from various sites in the estuary over a three-year period. The species and endpoints used, bivalve and echinoderm embryo-larval development, are among the most sensitive in the U.S. EPA's national toxicity dataset, which is used to derive WQC. No toxicity was observed in ambient bay water samples, as indicated by high proportions of normally developed larvae in control treatments, averaging 93+/-5% across all sites and all sampling events. Median effects concentrations (EC50), obtained by copper spiking of ambient water samples, ranged from 1.7 to 3.4 times lower at sites located near the mouth compared to sites near the back of the bay. These data indicate a gradient in complexation capacity increasing from the mouth to the back of the bay, which is consistent with similar trends in dissolved organic carbon and total suspended solids. For the bay as a whole, estimates for total recoverable and dissolved water-effect ratios (WER) ranged from 2.07 to 2.27 and 1.54 to 1.67, respectively. Water-effect ratios of this magnitude suggest that adoption of a somewhat higher site-specific WQC for San Diego Bay still would achieve the level of protection that is intended by the WQC guidelines.

[1]  Ignacio Rivera-Duarte,et al.  Modeling the mass balance and fate of copper in San Diego Bay , 2004 .

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

[3]  J. Moffett,et al.  Intercomparison of voltammetric techniques to determine the chemical speciation of dissolved copper in a coastal seawater sample , 2000 .

[4]  S. Bay,et al.  Status and Applications of Echinoid ( Phylum Echinodermata ) Toxicity Test Methods , 1993 .

[5]  S. Luoma Reassessment of metals criteria for aquatic life protection , 1997 .

[6]  R. Beiras,et al.  Effect of humic acids on speciation and toxicity of copper to Paracentrotus lividus larvae in seawater. , 2002, Aquatic toxicology.

[7]  A. Flegal,et al.  Comparable levels of trace metal contamination in two semi-enclosed embayments: San Diego Bay and South San Francisco Bay , 1993 .

[8]  R. Eriksen,et al.  Copper bioavailability and amelioration of toxicity in Macquarie Harbour, Tasmania, Australia , 2000 .

[9]  H. Allen,et al.  The importance of trace metal speciation to water quality criteria , 1996 .

[10]  Stephen H. Lieberman,et al.  Measurement of copper and zinc in San Diego Bay by automated anodic stripping voltammetry , 1978 .

[11]  P. Paquin,et al.  Biotic ligand model of the acute toxicity of metals. 1. Technical Basis , 2001, Environmental toxicology and chemistry.

[12]  Wayne G. Landis,et al.  Environmental toxicology and risk assessment , 1993 .

[13]  Herbert E. Allen,et al.  Influence of dissolved organic matter on the toxicity of copper to Ceriodaphnia dubia: Effect of complexation kinetics , 1999 .

[14]  D. J. Mackey,et al.  Copper speciation and toxicity in Macquarie Harbour, Tasmania: an investigation using a copper ion selective electrode , 2001 .

[15]  Bradley K Esser,et al.  At-sea high-resolution trace element mapping: San Diego Bay and its plume in the adjacent coastal ocean. , 2002, Environmental science & technology.

[16]  Michael Martin,et al.  Toxicities of ten metals to Crassostrea gigas and Mytilus edulis embryos and Cancer magister larvae , 1981 .

[17]  M. Gu,et al.  Physicochemical Factors Affecting the Sensitivity of Ceriodaphnia dubia to Copper , 2001, Environmental monitoring and assessment.

[18]  D. B. Chadwick,et al.  Spatial and temporal variations in copper speciation in San Diego Bay , 2004 .

[19]  J. Link,et al.  Comparative sensitivity of sea urchin sperm bioassays to metals and pesticides , 1989, Archives of environmental contamination and toxicology.

[20]  J. Meador THE INTERACTION OF PH, DISSOLVED ORGANIC CARBON, AND TOTAL COPPER IN THE DETERMINATION OF IONIC COPPER AND TOXICITY , 1991 .

[21]  S. Apte,et al.  A bacterial bioassay for the assessment of copper bioavailability in freshwaters , 1998 .

[22]  J S Tucker,et al.  The influence of organic chelators on the toxicity of copper to embryos of the pacific oyster,Crassostrea gigas , 1981, Archives of environmental contamination and toxicology.

[23]  Duane A. Benoit,et al.  The effects of water chemistry on the toxicity of copper to fathead minnows , 1996 .

[24]  K. Mopper,et al.  Automated High-Performance, High-Temperature Combustion Total Organic Carbon Analyzer , 1996 .

[25]  P. Paquin,et al.  Biotic ligand model of the acute toxicity of metals. 2. Application to acute copper toxicity in freshwater fish and Daphnia , 2001, Environmental toxicology and chemistry.

[26]  John C Hall,et al.  Water quality criteria for copper : A need for revisions to the national standard , 1997 .