Copper detection in the Asiatic clam Corbicula fluminea: optimum valve closure response.

When exposed to a contaminant, bivalves close their shell as a protective strategy. The aim of the present study was to estimate the maximum expected dissolved copper sensitivity in the freshwater bivalve Corbicula fluminea using a new approach to determine their potential and limit to detect contaminants. To take into account the rate of spontaneous closures, we integrated stress problems associated with fixation by a valve in usual valvometers and the spontaneous rhythm associated with nycthemeral activity, to optimize the response in conditions where the probability of spontaneous closing was lowest. Moreover, we used an original system with impedance valvometry, using lightweight impedance electrodes, to study free-ranging animals in low stress conditions combined with an analytical approach describing dose-response curves by logistic regression, with valve closure reaction as a function of response time and concentration of contaminant. In C. fluminea, we estimated that copper concentrations > 4 microg/l (95% confidence interval (CI95%), 2.3-8.8 microg/l) must be detected within 5 h after Cu addition. Lower values could not be distinguished from background noise. The threshold values were 2.5 times lower than the values reported in the literature.

[1]  I. R. Hill,et al.  Freshwater Field Tests for Hazard Assessment of Chemicals , 1994 .

[2]  A. Boudou,et al.  Relationship between feeding‐induced ventilatory activity and bioaccumulation of dissolved and algal‐bound cadmium in the Asiatic clam Corbicula fluminea , 2002, Environmental toxicology and chemistry.

[3]  H. Kay Environmental Health Criteria , 1980 .

[4]  David W. Hosmer,et al.  Applied Logistic Regression , 1991 .

[5]  D. Kampbell,et al.  Total, dissolved, and bioavailable metals at Lake Texoma marinas. , 2003, Environmental pollution.

[6]  Tim M. Curtis,et al.  Simultaneous, long-term monitoring of valve and cardiac activity in the blue mussel Mytilus edulis exposed to copper , 2000 .

[7]  C. Neal,et al.  A summary of river water quality data collected within the Land-Ocean Interaction Study: core data for eastern UK rivers draining to the North Sea , 2000, The Science of the total environment.

[8]  A. Boudou,et al.  Mechanism for maintaining oxygen consumption under varying oxygenation levels in the freshwater clam Corbicula fluminea , 2000 .

[9]  Dick de Zwart,et al.  The valve movement response of mussels: a tool in biological monitoring , 1989 .

[10]  A. R. Manley The effects of copper on the behaviour, respiration, filtration and ventilation activity of Mytilus edulis , 1983, Journal of the Marine Biological Association of the United Kingdom.

[11]  A case study of logistic QSAR modeling methods and robustness tests. , 2002, Ecotoxicology and environmental safety.

[12]  P L Brown,et al.  Valve movement responses of Velesunio angasi (Bivalvia: Hyriidae) to manganese and uranium: an exception to the free ion activity model. , 2000, Aquatic toxicology.

[13]  H Sluyts,et al.  A dynamic new alarm system for use in biological early warning systems , 1996 .

[14]  S. Mansour,et al.  Ecotoxicological Studies. 3. Heavy metals contaminating water and fish from Fayoum Governorate, Egypt , 2002 .

[15]  S. Mcneill,et al.  Bioaccumulation of heavy metals by aquatic macro-invertebrates of different feeding guilds: a review , 1999 .

[16]  A. Floch Un capteur biologique original enregistrant les mouvements valvaires des mollusques bivalves , 1998 .

[17]  A. Boudou,et al.  How water oxygenation level influences cadmium accumulation pattern in the Asiatic clam Corbicula fluminea: A laboratory and field study , 2001, Environmental toxicology and chemistry.

[18]  Damien Tran,et al.  Estimation of potential and limits of bivalve closure response to detect contaminants: Application to cadmium , 2003, Environmental toxicology and chemistry.

[19]  K. Ham,et al.  Effect of fluctuating low‐level chlorine concentrations on valve‐movement behavior of the asiatic clam (Corbicula fluminea) , 1994 .

[20]  W. Slooff,et al.  Detection limits of a biological monitoring system for chemical water pollution based on mussel activity , 1983, Bulletin of environmental contamination and toxicology.

[21]  J. Davenport A study of the effects of copper applied continuously and discontinuously to specimens of Mytilus edulis (L.) exposed to steady and fluctuating salinity levels , 1977, Journal of the Marine Biological Association of the United Kingdom.

[22]  A. J. Bailer,et al.  Toxicant‐ and response‐specific comparisons of statistical methods for estimating effective concentrations , 2001, Environmental toxicology and chemistry.

[23]  J. Meador,et al.  Modeling dose response using generalized linear models , 1996 .

[24]  Alain Monfort,et al.  Asymptotic properties of the maximum likelihood estimator in dichotomous logit models , 1981 .

[25]  J. Davenport,et al.  The detection of heightened sea-water copper concentrations by the mussel Mytilus edulis , 1978, Journal of the Marine Biological Association of the United Kingdom.