Multiple effects of acid and aluminum on brood stock and progeny of fathead minnows, with emphasis on histopathology

1990 ◽  
Vol 68 (2) ◽  
pp. 234-244 ◽  
Author(s):  
R. L. Leino ◽  
J. H. McCormick ◽  
K. M. Jensen

Thirty-day-old fathead minnows, Pimephales promelas, were reared at different pH values in softened Lake Superior water enriched with aluminum: pH 7.5–35 μg Al/L, pH 5.5–30 μg Al/L, pH 5.2–35 and 60 μg Al/L, including a background level of 15 μg Al/L, and at pH 7.5, 6.0, 5.5, and 5.2 at background Al levels. Spawning was greatly reduced at pH 6.0, pH 5.5–30 μg Al/L, and pH 5.5 and failed at pH 5.2 with or without added Al. The adult brood stock exhibited abnormalities at low pH, which could have contributed to poor spawning success or energy utilization: (i) thickened respiratory epithelium in the gills, (ii) hyperplasia of primary lamellar epithelium in the gills, (iii) increased number of gill chloride cells, (iv) reduced gill perfusion, (v) immature ovaries and oocyte atresia, (vi) immature and pathologic testes, (vii) abnormal distal tubules and collecting ducts in the kidneys, and (viii) reduced blood osmolality at pH 5.5 and 5.2 when no Al was added. Hatching success and larval survival were reduced when spawning occurred at or below pH 6.0; these larvae often had retarded swim bladder development and yolk absorption and some stages had abnormal gills, kidneys, and liver glycogen reserves. This study further supports the relationship between acidification, histological changes, ionoregulatory disturbances, altered energy metabolism, and recruitment failure.

Author(s):  
Richard L. Leino ◽  
Jon G. Anderson ◽  
J. Howard McCormick

Groups of 12 fathead minnows were exposed for 129 days to Lake Superior water acidified (pH 5.0, 5.5, 6.0 or 6.5) with reagent grade H2SO4 by means of a multichannel toxicant system for flow-through bioassays. Untreated water (pH 7.5) had the following properties: hardness 45.3 ± 0.3 (95% confidence interval) mg/1 as CaCO3; alkalinity 42.6 ± 0.2 mg/1; Cl- 0.03 meq/1; Na+ 0.05 meq/1; K+ 0.01 meq/1; Ca2+ 0.68 meq/1; Mg2+ 0.26 meq/1; dissolved O2 5.8 ± 0.3 mg/1; free CO2 3.2 ± 0.4 mg/1; T= 24.3 ± 0.1°C. The 1st, 2nd and 3rd gills were subsequently processed for LM (methacrylate), TEM and SEM respectively.Three changes involving chloride cells were correlated with increasing acidity: 1) the appearance of apical pits (figs. 2,5 as compared to figs. 1, 3,4) in chloride cells (about 22% of the chloride cells had pits at pH 5.0); 2) increases in their numbers and 3) increases in the % of these cells in the epithelium of the secondary lamellae.


1978 ◽  
Vol 35 (7) ◽  
pp. 997-1002 ◽  
Author(s):  
D. L. DeFoe ◽  
G. D. Veith ◽  
R. W. Carlson

Fathead minnows were exposed to Aroclor® 1248 and 1260 in flow-through bioassays to determine the acute (30-d) and chronic (240-d life cycle) effects on the larvae and adults, as well as the bioconcentration of the mixtures of PCBs in the fish. Newly hatched larvae (< 8 h old) were the most sensitive; the calculated 30-d LC50 was 4.7 μg/L for Aroclor 1248 and 3.3 μg/L for Aroclor 1260. Reproduction in fathead minnows occurred at concentrations as high as 3 μg/L for Aroclor 1248 and 2.1 μg/L for Aroclor 1260, concentrations that significantly affected larval survival. The 20% reduction in the standing crop in the second-generation fish at concentrations as low as 0.4 μg/L was due to the death of the larvae soon after hatching. The bioconcentration factor for PCBs was independent of the PCB concentration in the water; in adult females at 25 °C it was ~ 1.2 × 105 for Aroclor 1248 and 2.7 × 105 for Aroclor 1260. Females accumulated about twice as much PCBs as the males because of the greater amount of lipid in the female. Exposed fish placed in untreated Lake Superior water eliminated < 18% of the body burden after 60 d. Key words: PCBs, bioassay, bioconcentration, chronic toxicity, embryo-larval, depuration


1983 ◽  
Vol 17 (1) ◽  
pp. 47-63 ◽  
Author(s):  
James A. Zischke ◽  
John W. Arthur ◽  
Kathleen J. Nordlie ◽  
Roger O. Hermanutz ◽  
Douglas A. Standen ◽  
...  

2004 ◽  
Vol 23 (12) ◽  
pp. 2900 ◽  
Author(s):  
Katherine L. Sciera ◽  
J. Jeffery Isely ◽  
Joseph R. Tomasso ◽  
Stephen J. Klaine

1972 ◽  
Vol 29 (5) ◽  
pp. 583-587 ◽  
Author(s):  
A. R. Carlson

When fathead minnows (Pimephales promelas) were exposed to five concentrations (0.008–0.68 mg/liter) of the insecticide carbaryl for 9 months and throughout a life cycle, the highest concentration prevented reproduction and decreased survival. At the high concentration, testes contained motile sperm and ovaries were in a flaccid condition and appeared to be in a resorptive state. At the 0.68 mg/liter concentration, carbaryl appeared to contribute to mortality of larvae (produced by unexposed parents) within 30 days of hatching. Survival of young grown in the 0.008 mg/liter concentration was reduced. Since no demonstrable effects were noted for survival, growth, or reproduction at the 0.017, 0.062, and 0.21 mg/liter concentrations, this low survival value is considered not due to carbaryl. The 96-hr median tolerance concentration (TL 50) and the lethal threshold concentration (LTC) for 2-month-old fathead minnows were 9.0 mg/liter. The maximum acceptable toxicant concentration (MATC) for fathead minnows exposed to carbaryl in water with a hardness of 45.2 mg/liter and a pH of 7.5 lies between 0.21 and 0.68 mg/liter. The application factors (MATC/96-hr TL50 and MATC/LTC) both lie between 0.023 and 0.075.


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