The role of various dissolved organic matter forms on chlorpyrifos bioavailability to the estuarine bivalve Mercenaria mercenaria.
Dissolved organic matter (DOM) is comprised of a myriad of macromolecules with specific physical and chemical properties that may influence the bioavailability of hydrophobic pesticides to animals. This study was conducted to assess the role of various forms of DOM on the uptake and bioconcentration of the organophosphate insecticide chlorpyrifos (CHPY) to the bivalve Mercenaria mercenaria. Bivalves were exposed to DOM-free seawater (30 per thousand) or to seawater containing a single form of DOM. DOM forms included two filtrate fractions of natural salt-marsh sediment DOM (DOM-(<0.45 mum) and DOM-(<3 kDa)); natural purified humic (HA) and fulvic (FA) acids; and water soluble cyclic oligosaccharides alpha and beta cyclodextrins (CD-alpha and CD-beta). In (14)C-CHPY uptake and elimination experiments, juvenile bivalves were exposed to uniformly-labeled (14)C-CHPY and collected at time intervals during 48 h. The remaining bivalves were transferred to (14)C-CHPY-free elimination chambers with bivalve collection at time intervals over 144 h. Total uptake of (14)C-CHPY by bivalves in DOM-free seawater was >40% greater than in bivalves exposed to (14)C-CHPY in the presence of most DOM forms. These results are consistent with much faster (14)C-CHPY uptake rates estimated using a simple two parameter model. After the elimination period, bivalves exposed to DOM-free seawater had (14)C-CHPY body residue concentrations between 25% and 86% greater than bivalves in the presence of DOM forms. Experiments with larger bivalves showed that pulse-chase exposures with a 1.5 h exposure period to (14)C-CHPY was not long enough to detect differences in (14)C-CHPY tissue accumulation efficiencies across treatments. Our findings suggest that natural forms of DOM, at environmentally realistic organic carbon concentrations, reduced pesticide uptake and bioconcentration, consistent with much lower uptake rates relative to bivalves exposed to (14)C-CHPY in the absence of DOM. Interestingly, at the tested organic carbon concentrations CD-alpha and CD-beta did not reduce (14)C-CHPY bioconcentration in M. mercenaria.
Bejarano
Adriana C
AC
Department of Environmental Health Sciences, Norman J. Arnold School of Public Health, University of South Carolina, Columbia, SC 29208, USA. ACBejara@mailbox.sc.edu
Decho
Alan W
AW
Chandler
G Thomas
GT
D000704:Analysis of Variance; D000818:Animals; D001578:Benzopyrans / Q000494:pharmacology; D001682:Biological Availability; D001692:Biological Transport / Q000187:drug effects; D049872:Bivalvia / Q000378:metabolism*; D001822:Body Burden; D002250:Carbon Radioisotopes / Q000493:pharmacokinetics*; D004390:Chlorpyrifos / Q000493:pharmacokinetics*; D003505:Cyclodextrins / Q000494:pharmacology; D005243:Feces / Q000737:chemistry; D006812:Humic Substances; D007306:Insecticides / Q000493:pharmacokinetics*; D008954:Models, Biological; D009844:Oligosaccharides / Q000494:pharmacology; D012044:Regression Analysis; D012588:Scintillation Counting; D012623:Seawater
D001578:Benzopyrans; D002250:Carbon Radioisotopes; D003505:Cyclodextrins; D006812:Humic Substances; D007306:Insecticides; D009844:Oligosaccharides; D004390:Chlorpyrifos; C005023:fulvic acid