Influence of dissolved organic matter on copper binding, and calcium on cadmium binding, by gills of rainbow trout

被引:45
作者
Hollis, L [1 ]
Muench, L [1 ]
Playle, RC [1 ]
机构
[1] WILFRID LAURIER UNIV,DEPT BIOL,WATERLOO,ON N2L 3C5,CANADA
关键词
cadmium; copper; rainbow trout; dissolved organic matter; calcium; fathead minnows; modelling;
D O I
10.1006/jfbi.1996.0334
中图分类号
S9 [水产、渔业];
学科分类号
0908 ;
摘要
Complexation of Cu by 5 mg C l(-1) dissolved organic matter (DOM) from a marsh kept Cu from binding to gills of small rainbow trout Oncorhynchus mykiss in 9-day exposures to 0.5 mu m Cu in soft water. The protective effect of DOM occurs because the formation of Cu-DOM complexes reduces the amount of free Cu in the water, so the disruptive effects of Cu on ionoregulation, such as inhibited Na uptake, cannot develop. The Cu-DOM complexes themselves do not bind to the gills. Calcium (1100 mu M) reduced the accumulation of Cd by trout gills in short, 2-h exposures through competition for gill binding sites but not over longer, 7-day exposures to 0.14 mu M Cd. However, the protective effect of Ca against Cd toxicity persisted throughout the longer experiment, likely due to the decrease in the electrochemical gradient for diffusive loss of Ca from the fish to the water. Rainbow trout and fathead minnows Pimephales promelas accumulated Cu and Cd on their gills in a similar manner; thus, binding constants for metal-gill interactions determined for one species of fish can be generalized to other fish species. When literature binding constants determined for fathead minnows were applied to our studies with rainbow trout, computer modelling of Cu-gill and Cu-DOM interactions simulated our results well. In contrast Cd-gill and Ca-gill modelling predicted the initial competitive effect of Ca against Cd accumulation by trout gills, but did not predict the longer-term accumulation of Cd by trout gills. (C) 1997 The Fisheries Society of thr British Isles.
引用
收藏
页码:703 / 720
页数:18
相关论文
共 48 条
[1]  
Alberts J. J., 1983, Aquatic and terrestrial humic materials, P333
[3]  
COMHAIRE S, 1994, COMP BIOCHEM PHYS C, V109, P63, DOI 10.1016/0742-8413(94)00039-D
[4]  
DALY H R, 1990, Environmental Toxicology and Chemistry, V9, P1013
[5]   PROTON BINDING TO HUMIC SUBSTANCES .2. CHEMICAL HETEROGENEITY AND ADSORPTION MODELS [J].
DEWIT, JCM ;
VANRIEMSDIJK, WH ;
KOOPAL, LK .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1993, 27 (10) :2015-2022
[6]   The effects of water chemistry on the toxicity of copper to fathead minnows [J].
Erickson, RJ ;
Benoit, DA ;
Mattson, VR ;
Nelson, HP ;
Leonard, EN .
ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY, 1996, 15 (02) :181-193
[7]   THE FISH GILL - SITE OF ACTION AND MODEL FOR TOXIC EFFECTS OF ENVIRONMENTAL-POLLUTANTS [J].
EVANS, DH .
ENVIRONMENTAL HEALTH PERSPECTIVES, 1987, 71 :47-58
[8]  
FLIK G, 1993, J EXP BIOL, V184, P17
[9]   DETERMINATION OF TRACE-ELEMENT SPECIATION AND THE ROLE OF SPECIATION IN AQUATIC TOXICITY [J].
FLORENCE, TM ;
MORRISON, GM ;
STAUBER, JL .
SCIENCE OF THE TOTAL ENVIRONMENT, 1992, 125 :1-13
[10]   MULTIPLE METAL-ION EXCHANGE EQUILIBRIA WITH HUMIC-ACID [J].
GAMBLE, DS ;
SCHNITZER, M ;
KERNDORFF, H ;
LANGFORD, CH .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1983, 47 (07) :1311-1323