Lethal and Sublethal Effects of Binary Mixtures of Cyanide and Hexavalent Chromium, Zinc, or Ammonia to the Fathead Minnow(Pimephales Promelas) And Rainbow Trout (Salmo Gairdneri)

1979 ◽  
Vol 36 (2) ◽  
pp. 164-172 ◽  
Author(s):  
Steven J. Broderius ◽  
Lloyd L. Smith Jr.

Various models have been proposed to predict the combined interactive effect on fish of mixtures of poisons from separate toxicities of individual substances. The success of these models was tested, using data describing the lethal and sublethal effects of individual substances or binary mixtures of HCN and Cr(VI), Zn(II), or ammonia to the fathead minnow (Pimephales promelas) and rainbow trout (Salmo gairdneri). Using the strictly additive toxic unit and additive index approach, it was determined from log-dosage mortality curves that the Zn–HCN and ammonia–HCN mixtures were more acutely toxic and Cr–HCN less toxic than predicted. The concentration and response addition models, which have been proposed for toxicants whose joint action is similar or independent, respectively, could not be used to predict dosage–mortality curves for the HCN mixtures. Linear regression lines representing the growth response of fish to log concentration for toxicants alone and in binary combinations were not significantly different. Thus, for the toxic substances tested, the sublethal joint action of individual toxicants was not predictable from existing models and, in most cases, no interaction was indicated. The interactive nature of toxicants may be a function of the concentrations tested causing different biological processes to be affected (e.g. mortality vs. growth), and therefore different responses to be measured. A need still exists for development of a valid multiple toxicity approach for evaluating and predicting the toxicity of chemical combinations. Key words: multiple toxicity, binary mixtures, joint action, fish, bioassay, toxic substances

1984 ◽  
Vol 41 (1) ◽  
pp. 157-165 ◽  
Author(s):  
P. W. Webb

Experiments with teleosts attacking fathead minnow (Pimephales promelas) prey showed that piscivore locomotor tactics vary with body/fin morphology. Predators were tiger musky (Esox sp.), rainbow trout (Salmo gairdneri), smallmouth bass (Micropterus dolomieui), and rock bass (Ambloplites rupestris) representing several morphological series from more flexible to more rigid bodies, elongate to gibbose bodies, soft-rayed to acanthopterygian median/paired fin patterns, and more to less myotomal muscle. Two predicted optimal tactics were common to the four predators: (1) strike at the prey center of mass and (2) strike prey from the side. Other tactics varied among the predators. Tiger musky always used S-start fast-starts, rainbow trout used steady swimming with body/caudal fin movements, and smallmouth and rock bass used steady swimming with body/caudal fin movements for closer prey and started attacks on distant prey with pectoral propulsion. Tiger musky overshot prey, this being prevented by the use of paired fins as brakes in the two centrarchids. Rainbow trout regularly chased prey, but effective braking coupled with suction feeding appeared to make chases less necessary for smallmouth and rock bass. Speeds in strikes increased according to rock bass < smallmouth bass < rainbow trout < tiger musky consistent with expectations based on morphology. Each species used attack speeds likely to minimize closure times, which is the general optimal strategy for interceptors. Tiger musky attacked at maximum speeds but rainbow trout and smallmouth and rock bass attacked at speeds very much lower than their maximum potential. The prey has a low response threshold for these three species compared with tiger musky when high speeds and associated large prey reaction distances would increase closure times.


2021 ◽  
pp. 105884
Author(s):  
Roxanne Bérubé ◽  
Charles Gauthier ◽  
Thibault Bourdin ◽  
Marilou Bouffard ◽  
Gaëlle Triffault-Bouchet ◽  
...  

1979 ◽  
Vol 36 (1) ◽  
pp. 84-87 ◽  
Author(s):  
C. M. Neville

Dorsal aorta blood samples were taken from cannulated rainbow trout (Salmo gairdneri) exposed to pH 4.0 (acid group) or pH 7.0 (controls) in normocapnic conditions at 10 °C. Over a 5-d period there was a significant gradual decrease in pH and total CO2 in the acid group but no significant difference in pO2 and lactate compared to the controls. After uncannulated rainbow trout were exposed to the same conditions for 12 d there were significant increases in hemoglobin, hematocrit, and erythrocyte levels in caudal vein samples from the acid group. The results show that rainbow trout exposed to acid without hypercapnia develop acidaemia which is not a result of anaerobic respiration. The increase in erythrocyte concentration probably offsets the effects of acidaemia upon blood oxygen carrying capacity. Differences in ambient pCO2 and/or species differences could account for varying acid-base values in acid exposed fish reported by different workers. Key words: environmental acidification, acidaemia, lactate, pH, total carbonate, fish


1988 ◽  
Vol 45 (2) ◽  
pp. 287-293 ◽  
Author(s):  
K. G. Doe ◽  
W. R. Ernst ◽  
W. R. Parker ◽  
G. R. J. Julien ◽  
P. A. Hennigar

Three pesticides, fenitrothion, 2,4-D, and aminocarb, were tested in static 96-h acute lethal toxicity tests using fingerling rainbow trout (Salmo gairdneri) at pH 4.6, 5.6, 6.9, and 8.5. The toxicity of aminocarb, a base, increased significantly with increasing pH. Conversely, the toxicity of the acidic pesticide 2,4-D increased with decreasing pH. The toxicity of the neutral pesticide fenitrothion did not change significantly with changing pH. Subsequent tests were performed on trout fingerlings with aminocarb to determine the effect of two exposure pH's on brain acetylcholinesterase activity and whole-body aminocarb residue. Brain acetylcholinesterase was found to be inversely proportional to whole-body aminocarb content of fish. In fish exposed at pH 4.6, brain acetylcholinesterase was maximally depressed at 6 h, after which it recovered to within the control range. Whole-body aminocarb concentrations rose to a maximum within 6 h and subsequently declined to low levels. In fish exposed at pH 8.2, brain acetylcholinesterase dropped below the control range by 1 h and remained low until all fish died by 72 h. A maximum whole-body aminocarb concentration was reached within 1 h and remained elevated until the fish died. Several explanations for the observed results are presented.


1971 ◽  
Vol 28 (12) ◽  
pp. 1841-1845 ◽  
Author(s):  
John W. Arthur ◽  
John G. Eaton

The amphipod Gammarus pseudolimnaeus was subjected to 96-hr and 15-week exposures, and the fathead minnow (Pimephales promelas) to a 21-week exposure, to various chloramine concentrations under continuous-flow conditions. The most marked sublethal effects were reductions in the number of young produced by the amphipod and in egg production by the minnow. The 96-hr median tolerance limit for the amphipod was 220 μg/liter total chloramine. Fathead minnows in the long-term study were all killed at the highest concentration, 154 μg/liter total chloramine, within 3 days. The lowest measured total chloramine concentration in the long-term tests having no significant effect was < 3.4 μg/liter for the amphipod and 16.5 μg/liter for the fathead minnow.


1997 ◽  
Vol 54 (6) ◽  
pp. 1387-1390 ◽  
Author(s):  
Michael W Greene ◽  
Richard M Kocan

Ethylene glycol (EG) and thiram, an aldehyde dehydrogenase inhibitor, are components of the seed protectant Vitavax-200. EG is a common solvent, thought to be nontoxic, whereas thiram, a dithiocarbamate known to be toxic to fish, is an active ingredient in Vitavax-200. When the\i toxicities of EG and thiram were investigated individually and as a mixture in rainbow trout (Oncorhynchus mykiss) and fathead minnow (Pimephales promelas), a strong synergistic toxic effect was observed. Using a constant sublethal concentration of thiram, a 5- to 19-fold increase and a 2- to 2.4-fold increase in EG toxicity was observed in fathead minnow and rainbow trout, respectively. The toxicity of EG following pretreatment of rainbow trout with pyrazole, an alcohol dehydrogenase inhibitor, was decreased by 22% whereas pretreatment with cyanamide, an aldehyde dehydrogenase inhibitor, increased toxicity 3.4-fold. The results indicate that thiram inhibits the complete metabolism of EG, resulting in the buildup of a toxic aldehyde intermediate and increasing the toxicity of EG.


1993 ◽  
Vol 50 (7) ◽  
pp. 1348-1355 ◽  
Author(s):  
B. E. Hickie ◽  
N. J. Hutchinson ◽  
D. G. Dixon ◽  
P. V. Hodson

The acute lethality of a fixed-ratio mixture of Al, Mn, Fe, Ni, Zn, Cu, and Pb (75:60:60:12:12:6:6 μg∙L−1 = 1.0 acid lake concentration or ALC, representative of Ontario lakes acidified to pH 5.8) was examined with alevin rainbow trout (Oncorhynchus mykiss) and larval fathead minnow (Pimephales promelas). All testing was done in extremely soft, acidic water (2.5 mg Ca∙L−1; pH 4.6–5.8). For the acid-tolerant trout alevins (144-h LC50 = pH 4.32), median lethal metal mixture levels at pH 5.8 were 5.0 ALC. Toxicity of the mixture increased at lower pHs, with a median lethal threshold of 1.0 ALC at pH 4.9. A mixture of Al, Zn, and Cu was equivalent in toxicity to the full mixture; mixture toxicity was caused by Cu alone at pH 5.8 and by Al alone at pH 4.9. For the acid-sensitive fathead minnow larvae (144-h LC50 = pH 5.54), the mixture of metals typical of lakes acidified to pH 5.8 was lethal (LC50 = 0.84 ALC); again, toxicity was associated with Al, Cu, and Zn. This research implies that Cu could be an important factor contributing to the demise of acid-sensitive fish at pHs above those associated with increased Al solubility and toxicity.


1995 ◽  
Vol 52 (1) ◽  
pp. 13-22 ◽  
Author(s):  
R. D. Handy

Rainbow trout (Oncorhynchus mykiss), goldfish (Carassius auratus), and the fathead minnow (Pimephales promelas) were exposed continuously or intermittently (24-h exposure: 24-h recovery) to a nominal peak concentration of 3 μg∙L−1 mercuric chloride for 120 h. There were no differences in the target organs or the distribution of the toxicant within internal organs between the two exposure regimes. Mercury concentrations in the tissues of intermittently exposed fish were less than those of continuously exposed fish. The lower mercury concentrations in the intermittently exposed groups arose from reduced or negligible accumulation during recovery periods rather than mercury excretion. The accumulation of mercury during intermittent exposure is roughly proportional to the exposure duration, and could therefore be predicted from a continuous exposure of equivalent total exposure duration. This proportionality exists when (1) peak concentrations of mercury are the same in both regimes, and (2) the recovery periods are short compared with the biological half-life for mercury.


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