Role of Organic Complexation in the Toxicity of Aluminum to Rana pipiens Embryos and Bufo americanus Tadpoles

1990 ◽  
Vol 47 (1) ◽  
pp. 217-224 ◽  
Author(s):  
Joseph Freda ◽  
Vandy Cavdek ◽  
D. Gordon McDonald
Keyword(s):  
Organic Compounds ◽  
Rana Pipiens ◽  
Aluminum Toxicity ◽  
Pond Water ◽  
Toxicity Tests ◽  
Bufo Americanus ◽  
Organic Complexation ◽  
Toxic Agents ◽  
Water Pond ◽  
Acid Toxicity

This study investigated the influence of naturally occurring organic compounds on the survival of amphibian embryos and larvae in acidic, aluminum contaminated water. A series of laboratory tests were conducted which measured aluminum toxicity in artificial soft water (ASW) diluted with varying amounts of pond water which contained dissolved organic compounds. At pH 4.5 for tadpoles of Bufo americanus and pH 4.8 for embryos of Rana pipiens, the organic compounds (DOC 5.7 to 16.2 mg∙L−1) complexed the aluminum and thus increased the LC50 for total aluminum by more than two fold. At pH 4.2, 100% ASW and the four dilutions of pond water were toxic to R. pipiens embryos (75–96% mortality), in contrast to higher pH's, aluminum ameliorated acid toxicity which resulted in a 26% reduction in mortality in 100% ASW at 250 mg∙L−1 total aluminum. Although the organic compounds in the pond water also complexed aluminum at pH 4.2, protective levels of labile aluminum [Formula: see text] were still present at 450 μg∙L−1 total aluminum. However, at a given level of labile aluminum in pH 4.2 water, pond water was more toxic to embryos than ASW. At pH 4.2, pond water without added Al was also significantly more toxic to embryos than 100% ASW with 0 μg∙L−1 Al. Toxicity tests using purified humic and fulvic acid sugested that these compounds may be the toxic agents in high dissolved organic carbon (DOC) pond water.

Development and transmission of Gyrinicola batrachiensis (Walton, 1929) Adamson, 1981 (Pharyngodonidae: Oxyuroidea)

1981 ◽  
Vol 59 (7) ◽  
pp. 1351-1367 ◽  
Author(s):  
Martin L. Adamson
Keyword(s):  
Rana Pipiens ◽  
Early Stage ◽  
Tap Water ◽  
Pond Water ◽  
Rana Clamitans ◽  
Adult Males ◽  
Bufo Americanus ◽  
Individual Female ◽  
Adult Females ◽  
Water Pond

Individual female Gyrinicola batrachiensis from tadpoles produce thin-shelled larvated eggs and thick-shelled eggs containing embryos in an early stage of cleavage. Larvae in thin-shelled eggs hatched soon after deposition and survived for less than 1 h in aged tap water, pond water, or diluted buffer. Results presented herein show that thin-shelled eggs are autoinfective whereas thick-shelled eggs are transmission agents. Thick-shelled eggs isolated from natural infections in Rana clamitans, Rana pipiens, and Bufo americanus were infective to tadpoles of R. clamitans, R. sylvatica, Pseudacris triseriata, and B. americanus but not to transformed anurans. All worms recovered from tadpoles experimentally infected with eggs from natural infections in B. americanus were females and only 15% of worms examined from tadpoles experimentally infected with eggs from natural infections in R. clamitans were males. Development of G. batrachiensis was studied in experimentally infected R. clamitans held at 20 and 25 °C. Development was more rapid at 25 °C and males developed more rapidly than females at both temperatures. Adult males were first observed after 9 days (25 °C) and 16 days (20 °C) and adult females were first observed after 12 days (25 °C) and 19 days (20 °C).

Enumeration and Identification of Coliform Bacteria Injured by Chlorine or Fungicide Mixed with Agricultural Water

2016 ◽  
Vol 79 (10) ◽  
pp. 1789-1793 ◽  
Author(s):  
HIDEMI IZUMI ◽  
YUJI NAKATA ◽  
AYANO INOUE
Keyword(s):  
Cell Injury ◽  
Pond Water ◽  
Coliform Bacteria ◽  
Agricultural Water ◽  
Isolation And Identification ◽  
Electrolyzed Water ◽  
Selective Media ◽  
E Coli ◽  
Pure Cultures ◽  
Water Pond

ABSTRACT Chemical sanitizers may induce no injury (bacteria survive), sublethal injury (bacteria are injured), or lethal injury (bacteria die). The proportion of coliform bacteria that were injured sublethally by chlorine and fungicide mixed with agricultural water (pond water), which was used to dilute the pesticide solution, was evaluated using the thin agar layer (TAL) method. In pure cultures of Enterobacter cloacae, Escherichia coli, and E. coli O157:H7 (representing a human pathogen), the percentage of chlorine-injured cells was 69 to 77% for dilute electrolyzed water containing an available chlorine level of 2 ppm. When agricultural water was mixed with electrolyzed water, the percentage of injured coliforms in agricultural water was 75%. The isolation and identification of bacteria on TAL and selective media suggested that the chlorine stress caused injury to Enterobacter kobei. Of the four fungicide products tested, diluted to their recommended concentrations, Topsin-M, Sumilex, and Oxirane caused injury to coliform bacteria in pure cultures and in agricultural water following their mixture with each pesticide, whereas Streptomycin did not induce any injury to the bacteria. The percentage of injury was 45 to 97% for Topsin-M, 80 to 87% for Sumilex, and 50 to 97% for Oxirane. A comparison of the coliforms isolated from the pesticide solutions and then grown on either TAL or selective media indicated the possibility of fungicide-injured Rahnella aquatilis, Yersinia mollaretii, and E. coli. These results suggest the importance of selecting a suitable sanitizer and the necessity of adjusting the sanitizer concentration to a level that will kill the coliforms rather than cause sanitizer-induced cell injury that can result in the recovery of the coliforms.

Effects of Aluminum on the Leopard Frog, Rana pipiens: Life Stag Comparisons and Aluminum Uptake

1990 ◽  
Vol 47 (1) ◽  
pp. 210-216 ◽  
Author(s):  
Joseph Freda ◽  
D. Gordon McDonald
Keyword(s):  
Rana Pipiens ◽  
Low Ph ◽  
The Body ◽  
Leopard Frog ◽  
Whole Body ◽  
Toxicity Tests ◽  
Al Content ◽  
Wide Range ◽  
Water Ph ◽  
Percent Mortality

In this study, we conducted a series of toxicity tests investigating the response of embryos, prestage 25 tadpoles and 3-wk old tadpoles of the leopard frog (Rana pipiens) to a wide range pf pH (4.2–4.8) and Al (0–1000 μg∙:L−1}, and to pH 6.5 with no Al present. In embryos and prestage 25 tadpoles, Al ameliorated the toxic effects of very low pH's (4.2–4.4), while becoming toxic at higher pH's (4.6–4.8). Although both embryos and prestage 25 tadpoles were killed by low pH (pH 4.2–4.4 and 4.2, respectively) and elevated Al ([Formula: see text] and [Formula: see text] Al, respectively), embryos were relatively more sensitive (i.e. higher percent mortality) to low pH, whereas prestage 25 tadpoles were relatively more sensitive to Al Three week old tadpoles did not die at any test pH (without Al) and mortality (>20%) caused by Al occurred at only pH 4.8 and 750–1000 μg∙L−1 Al. The body sodium concentrations of 3-wk old tadpoles that survived high Al exposure were depressed indicating sublethal stress. Whole body Al uptake in 3-wk old tadpoles was also elevated in water containing high concentrations of Al, but it was positively related to water pH and exposure time. This result suggests that body Al content is not an accurate indicator of Al exposure in tadpoles living in acidic, Al contaminated ponds.

The biology of Trypanosoma andersoni n. sp. and Trypanosoma grylli Nigrelli, 1944 (Kinetoplastida) from Hyla versicolor LeConte, 1825 (Anura)

1982 ◽  
Vol 60 (2) ◽  
pp. 116-123 ◽  
Author(s):  
Brian O. Reilly ◽  
P. T. K. Woo
Keyword(s):  
Rana Pipiens ◽  
Rana Catesbeiana ◽  
Rana Sylvatica ◽  
Hyla Versicolor ◽  
Bufo Americanus ◽  
Hyla Cinerea ◽  
Southern Ontario ◽  
Osteopilus Septentrionalis ◽  
Centrifugation Technique ◽  
Acris Gryllus

From May 1979 to July 1980, the blood of 196 mature Hyla versicolor LeConte from six sites in southern Ontario and southeastern Manitoba was examined for trypanosomes using the haematocrit centrifugation technique. Trypanosoma andersoni n. sp. and Trypanosoma grylli Nigrelli were found in 5.2 and 5.6% of the frogs examined. Three frogs (1.5%) were infected with both species of trypanosomes. Blood trypomastigotes of both species were monomorphic. Blood trypomastigotes of T. andersoni n. sp. were long and slender, tapering at both ends, whereas those of T. grylli were pyriform with a rounded posterior and tapered anterior.Both blood and culture forms of these trypanosomes were infective to laboratory-raised H. versicolor and Hyla crucifer Wied. Trypanosoma grylli was also infective to a field-collected Acris gryllus (LeConte). Neither trypanosome was infective to laboratory-raised Rana catesbeiana Shaw, Rana clamitans Rafinesque tadpoles, Rana pipiens Schreber, Rana sylvatica LeConte, or Xenopus laevis Daudin. Trypanosoma andersoni n. sp. was also not infective to laboratory-raised Bufo americanus Holbrook, Pseudacris triseriata (Wied), or to field-collected Hyla cinerea (Schneider) and Osteopilus septentrionalis Dumeril and Bibron. Neither species was infective to field-collected Notophthalmus viridescens (Rafinesque).

Amphibian Distribution with Respect to Pond Water Chemistry near Sudbury, Ontario

1992 ◽  
Vol 49 (S1) ◽  
pp. 114-121 ◽  
Author(s):  
V. Glooschenko ◽  
W. F. Weller ◽  
P. G. R. Smith ◽  
R. Alvo ◽  
J. H. G. Archbold
Keyword(s):  
Discriminant Analysis ◽  
Water Chemistry ◽  
Principal Components ◽  
Rana Sylvatica ◽  
Pond Water ◽  
Bufo Americanus ◽  
Breeding Sites ◽  
Metal Levels ◽  
Components Analysis ◽  
Detailed Chemical

Amphibians were present in 118 potential breeding sites 9–66 km northeast and southwest of Sudbury, Ontario. Detailed chemical analyses were done for 38 ponds, and 23 variables were subjected to principal components analysis to summarize the main gradients in pond chemistry. Discriminant analysis using scores of the first three principal components showed that the presence of Rana pipiens, R. clamitans and Hyla crucifer was positively related to buffering status (alkalinity, pH, and other correlated variables); the presence of H. crucifer was also negatively related to atmospheric deposition status (cadmium, nickel, other correlated metals, and sulphate). Discriminant analysis using the original water chemistry variables confirms these general patterns. Two species show relationships with buffering status variables: Rana sylvatica with conductivity and R. clamitans with alkalinity. Three species also show negative correlation with metal levels in pond water: Bufo americanus with nickel, R. clamitans with aluminum, and R. pipiens with zinc. Although most of the species expected do occur in the Sudbury area, the distributions of several species appear related to buffering status and metals present in their immediate environemnt. There were only two observations of Ambystoma maculatum, and low numbers of egg masses were noted for R. sylvatica.

The extent of long-term temperature compensation for jumping distance in the frog, Rana pipiens, and the toad, Bufo americanus

1983 ◽  
Vol 61 (6) ◽  
pp. 1284-1287 ◽  
Author(s):  
J. M. Renaud ◽  
E. D. Stevens
Keyword(s):  
Nervous System ◽  
Test Temperature ◽  
Temperature Compensation ◽  
Rana Pipiens ◽  
Acclimation Temperature ◽  
Thermal Compensation ◽  
Muscular System ◽  
Bufo Americanus ◽  
Toad Bufo

The effects of acclimation to either 5 or 25 °C were studied on the longest jumping distances of Rana pipiens and Bufo americanus to estimate their capacity for long-term compensation. Animals were tested randomly at 5, 10, 15, 20, and 25 °C. Both Rana and Bufo jumped further at higher temperatures. For both species, acclimation temperature modified the effect of test temperature. At test temperatures of 20 and 25 °C, frogs acclimated to 25 °C jumped further than those acclimated to 5 °C. There was no evidence for thermal compensation in toads, but half of those acclimated to 25 °C would not jump when tested at 5 °C, whereas only 1 out of 16 cold-acclimated toads did not jump. We suggest that the acclimation effects on the jumping ability of R. pipiens at high temperatures are important in increasing their ability to escape predation and that this effect depends on an effect on the nervous system rather than the muscular system.

Xenobiotic organic compounds in leachates from ten Danish MSW landfills—chemical analysis and toxicity tests

2004 ◽  
Vol 38 (18) ◽  
pp. 3845-3858 ◽  
Author(s):  
A. Baun ◽  
A. Ledin ◽  
L.A. Reitzel ◽  
P.L. Bjerg ◽  
T.H. Christensen
Keyword(s):  
Chemical Analysis ◽  
Organic Compounds ◽  
Toxicity Tests

Toxicity of Amphibian Breeding Ponds in the Sudbury Region

1993 ◽  
Vol 50 (7) ◽  
pp. 1497-1503 ◽  
Author(s):  
Joseph Freda ◽  
D. Gordon McDonald
Keyword(s):  
Organic Compounds ◽  
Rana Sylvatica ◽  
Low Ph ◽  
Ambystoma Maculatum ◽  
Bufo Americanus ◽  
Spotted Salamander ◽  
Water Ph ◽  
Dissolved Organic Compounds ◽  
High Concentrations ◽  
Toad Bufo

We measured the survival of transplanted embryos and tadpoles of the wood frog (Rana sylvatica), the American toad (Bufo americanus), and the spotted salamander (Ambystoma maculatum) in 16 ponds located approximately 60 km south of Sudbury, Ontario. Mortality of embryos of all species and mortality of B. americanus tadpoles were correlated only with water pH. In two low-pH ponds, high concentrations of dissolved organic compounds might have been a toxic component. Aluminum and pH were correlated with mortality for only R. sylvatica tadpoles. Overall, Al did not appear to be very toxic in both laboratory and field exposures possibly due to complexation by dissolved organic compounds.

Effects of pH, Aluminum, and Calcium on Survival and Growth of Eggs and Fry of Brook Trout (Salvelinus fontinalis)

1990 ◽  
Vol 47 (8) ◽  
pp. 1580-1592 ◽  
Author(s):  
C G. Ingersoll ◽  
D. R. Mount ◽  
D. D. Gulley ◽  
T. W. La Point ◽  
H. L. Bergman
Keyword(s):  
Brook Trout ◽  
Salvelinus Fontinalis ◽  
Aluminum Toxicity ◽  
Life Stage ◽  
Recovery Period ◽  
Yolk Sac ◽  
Aluminum Concentration ◽  
Effects Of Ph ◽  
Life Stage Sensitivity ◽  
Acid Toxicity

Freshly fertilized eggs, eyed eggs, yolk-sac fry, and swim-up fry of brook trout (Salvelinus fontinalis) were exposed to a matrix of 84 combinations of pH (4.0–6.5), aluminum (0–1000 μg/L), and calcium (0.5–8.0 mg/L) in 21–91-d experiments. The response to pH, aluminum, and calcium exposure was dependent on life stage. Sensitivity to acid toxicity generally decreased with age (freshly fertilized eggs>eyed eggs>yolk-sac fry = swim-up fry). Survival or hatching of freshly fertilized and eyed eggs decreased at pH 5.2 and below, whereas survival of yolk-sac and swim-up fry was reduced at pH 4.4–4.0. Sensitivity to aluminum toxicity generally increased with age (freshly fertilized eggs = eyed eggs<yolk-sac fry<swim-up fry). At low pH, survival of freshly fertilized and eyed eggs increased with exposure to increasing aluminum concentrations, in contrast, elevated aluminum [Formula: see text] was often toxic to fry. Increasing calcium was beneficial to all life stages, although the magnitude of this benefit depended on life stage and on the specific pH and aluminum concentration. Survival after previous exposure to toxic combinations of pH, aluminum, and calcium generally improved during a post-exposure recovery period at pH 6.5. However, increased mortality in many exposure combinations did not begin until this recovery period.

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