Minnows Pimephales Promelas Research Articles

Spatial and Temporal Patterns of Intraspecific Morphological Variation In Dactylogyrus simplexus from Fathead Minnows In Nebraska

Dactylogyrus simplexus Monaco and Mizelle, 1955, occurs on the gills of fathead minnows (Pimephales promelas). Previous research on parasites of fathead minnows from 3 converging Nebraska streams, Elk Creek, Oak Creek, and West Oak Creek, shows that fish in each stream constitute distinct populations. To determine whether their parasites had diverged structurally in response to such isolation, or in response to seasonal change, we searched for patterns of intraspecific morphometric variation among D. simplexus. Over 3 collection dates in fall 2007, spring 2008, and fall 2009, 203 D. simplexus were collected from Elk and West Oak Creeks. We ran 1-way ANOVA to compare differences in 15 distinct point-to-point measurements of sclerotized parts across sites and collection dates. Significant differences were found in some D. simplexus measurements between Elk and West Oak Creeks for all 3 collection dates, but the characteristics that differed and the trend of variation between the creeks were not consistent over time. Dactylogyrus simplexus from both Elk and West Oak Creeks showed consistent patterns of variation over time for 5 measurements, including hamulus gap width, bar length, marginal hook length, sickle length, and sickle width. In conclusion, D. simplexus demonstrate consistent patterns of seasonal variation, but not spatial.

A computational model of the hypothalamic - pituitary - gonadal axis in female fathead minnows (Pimephales promelas) exposed to 17α-ethynylestradiol and 17β-trenbolone

BackgroundEndocrine disrupting chemicals (e.g., estrogens, androgens and their mimics) are known to affect reproduction in fish. 17α-ethynylestradiol is a synthetic estrogen used in birth control pills. 17β-trenbolone is a relatively stable metabolite of trenbolone acetate, a synthetic androgen used as a growth promoter in livestock. Both 17α-ethynylestradiol and 17β-trenbolone have been found in the aquatic environment and affect fish reproduction. In this study, we developed a physiologically-based computational model for female fathead minnows (FHM, Pimephales promelas), a small fish species used in ecotoxicology, to simulate how estrogens (i.e., 17α-ethynylestradiol) or androgens (i.e., 17β-trenbolone) affect reproductive endpoints such as plasma concentrations of steroid hormones (e.g., 17β-estradiol and testosterone) and vitellogenin (a precursor to egg yolk proteins).ResultsUsing Markov Chain Monte Carlo simulations, the model was calibrated with data from unexposed, 17α-ethynylestradiol-exposed, and 17β-trenbolone-exposed FHMs. Four Markov chains were simulated, and the chains for each calibrated model parameter (26 in total) converged within 20,000 iterations. With the converged parameter values, we evaluated the model's predictive ability by simulating a variety of independent experimental data. The model predictions agreed with the experimental data well.ConclusionsThe physiologically-based computational model represents the hypothalamic-pituitary-gonadal axis in adult female FHM robustly. The model is useful to estimate how estrogens (e.g., 17α-ethynylestradiol) or androgens (e.g., 17β-trenbolone) affect plasma concentrations of 17β-estradiol, testosterone and vitellogenin, which are important determinants of fecundity in fish.

The use of field-based mesocosm systems to assess the effects of uranium milling effluent on fathead minnow (Pimephales promelas) reproduction

Northern Saskatchewan, Canada is home to a uranium milling operation that discharges a complex milling effluent containing nutrients, cations and anions, and many metals including selenium (Se). Se has the potential to accumulate in a system even when water concentrations are low. This study evaluated the effects of treated uranium milling effluent and contaminated sediment in combination and in isolation to determine the contribution and importance of each source to fathead minnow (Pimephales promelas) reproduction and survival. Trios of fathead minnows were allocated to one of four treatments for 21-days where the following were evaluated; survival (adult and 5 day larval), larval deformities, reproductive effects (egg production, spawning events) and metal tissue burdens (muscle, gonad, eggs and larvae). In addition Se speciation analysis was conducted on fish tissues. Effects were solely effluent-mediated with little contribution observed due to the presence of contaminated sediments. The contaminated sediments tested were taken from the actual receiving environment and represented the sediment composition found in greatest abundance. Results showed egg production significantly increased in the effluent treatments compared to the reference water treatments. Although egg production increased following effluent exposure, there was reduced hatching and larval survival and a significant increase in skeletal deformities in 5 day old larvae. Despite these effects on the offspring, when examined in an integrated manner relative to increased egg production, the mean number of normal larvae did not differ among treatments. Total selenium significantly increased in the effluent exposed, algae, female muscle, gonad, eggs and larvae in addition to other metals. A shift in the proportion of species of selenium was evident with changing exposure conditions. Biofilm/algae was key in the transfer of available Se into the food chain from the water and a source of direct dietary exposure in fish and possibly invertebrates.

Replication of the hypothalamus-pituitary-gonadal axis of fathead minnow (Pimephales promelas) on a chip

Replication of the hypothalamus-pituitary-gonadal axis of fathead minnow (Pimephales promelas) on a chip

Identification and expression analysis of two growth hormone receptors in zanzibar tilapia (Oreochromis hornorum)

Growth hormone plays important roles in various physiological processes such as growth, metabolism, and reproduction. In this study, two cDNAs encoding growth hormone receptor (GHR) were isolated from the liver of zanzibar tilapia (Oreochromis hornornum). The two cDNAs were 2,831 and 2,044bp in length and named GHR1 and GHR2, respectively. GHR1 and GHR2 shared 57.4% similarity in nucleotide sequences and 33.5% similarity in deduced amino acid sequences. Consequently, it was presumed that they were two different genes. Conserved regions of GHR1 and GHR2 in zanzibar tilapia were different from those of other vertebrates. For example, conserved box2 regions of GHR1 and GHR2 in zanzibar tilapia were, respectively, WVELM and WVEFT, while it was WVEFI for GHRs in other vertebrates. Similar to other fish species, GHR1 and GHR2 were expressed in brain, gill, liver, muscle, spleen, gonad, stomach, kidney, and pituitary in zanzibar tilapia. The expression levels were the highest in liver. Unlike fathead minnow (Pimephales promelas) and mossambique tilapia (O. mossambicus), the expression levels of GHR1 in most female fish tissues were higher than those in male fish. No significant difference in GHR2 expression was found in all the tissues in male and female of zanzibar tilapia. Under fasting condition, the expressions of GHRs and IGF-II were significantly up-regulated (P<0.05) in liver, while the expression of IGF-I remained stable. This observation would contribute to understanding the evolution of the GHR family in further investigation of growth regulation of zanzibar tilapia.

The Response of a Piscivore (Micropterus salmoides) to a Venomous Prey Species (Noturus gyrinus)

ABSTRACT The tadpole madtom (Noturus gyrinus) is highly prized as bait in the upper Mississippi River valley, where it is marketed as the “willow cat,” yet it has venom glands associated with spines in its pectoral and dorsal fins. The response of a predatory fish to this defense was tested by exposing tadpole madtoms to largemouth bass (Micropterus salmoides). Results were compared to the response by bass to fathead minnows (Pimephales promelas). Each of four bass was used in six trials with madtoms and six trials with minnows. Trials with madtoms and minnows were alternated, and all trials were videotaped. Largemouth bass were just as likely to consume tadpole madtoms as minnows. Bass sometimes took longer to handle and consume tadpole madtoms than minnows, but the likelihood of attack did not change as the number of trials increased. Behaviors that may be associated with discomfort, such as gill flaring and coughing, occurred significantly more often after consumption of madtoms, but bass always seemed ready to consume additional prey, and no bass displayed any negative long term effects.

Using support vector regression coupled with the genetic algorithm for predicting acute toxicity to the fathead minnow

The potential toxicity of chemicals may present adverse effects to the environment and human health. The quantitative structure–activity relationship (QSAR) provides a useful method for hazard assessment. In this study, we constructed a QSAR model based on a highly heterogeneous data set of 571 compounds from the US Environmental Protection Agency, for predicting acute toxicity to the fathead minnow (Pimephales promelas). An approach coupling support vector regression (SVR) with the genetic algorithm (GA) was developed to build the model. The generated QSAR model showed excellent data fitting and prediction abilities: the squared correlation coefficients (r 2) for the training set and the test set were 0.826 and 0.802, respectively. Only eight critical descriptors, most of which are closely related to the toxicity mechanism, were chosen by GA-SVR, making the derived model readily interpretable. In summary, the successful case reported here highlights that our GA-SVR approach can be used as a general machine learning method for toxicity prediction.

A bioaccumulation bioassay for freshwater sediments

A laboratory bioassay is described for determining the bioavailability of contaminants from freshwater sediments. The bioassay consists of 10-d exposures to whole sediments under flow-through conditions. After testing five species, the fathead minnow (Pimephales promelas) and the earthworm (Lumbricus terrestris) were recommended for use in the test. When the availability of polychlorinated biphenyls (PCBs), Hg and Zn from Great Lakes sediments was examined in laboratory exposures, only the PCBs were accumulated. A field validation study demonstrated that the magnitude of accumulation in laboratory exposures was similar to that in organisms caged in the field. A protocol is recommended for using the test as a standardized bioaccumulation bioassay.

Effects of predaceous and nonpredaceous introduced fish on the survival, growth, and antipredation behaviours of long-toed salamanders

Simultaneous introduction of complex suites of exotic organisms into indigenous populations have poorly known magnitudes and consequences. We compared the effects of introduced piscivorous rainbow trout ( Oncorhynchus mykiss (Walbaum, 1792)) and nonpiscivorous fathead minnows ( Pimephales promelas Rafinesque, 1820) on growth, survival, susceptibility to predation, and antipredator behaviours of naïve long-toed salamanders ( Ambystoma macrodactylum Baird, 1850). Trout reduced salamander hatchling and larvae survival to nearly zero in predation trials and caused a 39% reduction in salamander survival within outdoor mesocosms. Salamander larvae did not increase their refuge use or alter activity patterns in the presence of trout. These results imply that allotopic distributions of trout and salamanders observed in several field surveys likely result from the inability of larvae to recognize introduced predators as a threat. Minnows also caused significant reductions in salamander survival (41%) and growth (37%) in mesocosms, and exposure to minnow cues caused larvae to spend more time within a refuge. Reduced salamander survivorship and growth in the mesocosms was likely due to competition for limiting zooplankton and (or) cannibalism. These results indicate that introductions of small-bodied, nonpiscivorous fishes can reduce amphibian survival and growth to at least the same extent as introduced trout.

Characteristics of Baitfish Retailers in Kentucky: Evidence of a Market to Support a Regional Industry

Bait shops in Kentucky and surrounding states rely primarily on large-scale suppliers for baitfish. However, these suppliers provide specific species and sizes of fish. This creates a potential market where small-scale producers could supply bait shops with uncommon species and size combinations of baitfish. This study describes baitfish and bait crayfish marketing parameters in Kentucky by reporting results of a survey that elicited marketing information from local baitfish dealers. The results showed 94% of the respondents were interested in purchasing baitfish from local producers. The types of baitfish wanted by these bait dealers from local suppliers included rosy red minnows (Pimephales promelas), catfish (Ictalurus punctatus), and large golden shiners (Notemigonus crysoleucas). The survey provided evidence of significant niche marketing opportunities in baitfish in states such as Kentucky, where baitfish production is not a major industry.

MIA-QSTR study of different organic compounds to Pimephales promelas

A quantitative structure–toxicity relationship (QSTR) model based on multivariate image analysis was built to predict the toxicity of 30 organic compounds against fathead minnow (Pimephales promelas), a fish species of wide occurrence. The derived multivariate image analysis (MIA) applied to QSTR (MIA-QSTR) model provided good correlation between chemical structure and toxicity, i.e., r 2 of 0.96, q 2 of 0.59, and $$ q^{ 2}_{ 20\% } $$ of 0.61 – the squared correlation coefficients of the linear regression of experimental versus predicted 50% lethal concentration (LC50) plots for the calibration, leave-one-out,and leave-20%-out cross-validation, respectively. The method demonstrated the potential to be used as a tool for prediction of toxicity data in vertebrate animals.

Phenotypic anchoring transcriptional responses of the fathead minnow (Pimephales promelas) during chronic Pb exposures and influence of ambient water chemistry

Phenotypic anchoring transcriptional responses of the fathead minnow (Pimephales promelas) during chronic Pb exposures and influence of ambient water chemistry

Demonstration of a Landscape-Scale Approach for Predicting Acute Copper Toxicity to Larval Fathead Minnows (Pimephales promelas) in Surface Waters

Watersheds have historically been used as the appropriate spatial classification unit for managing water resources. However, geology, soil type, predominant vegetation, and climate have obvious influences on water quality and are not constrained by watercourses or political boundaries. This concept has evolved for several decades and developed the concept of ecoregions and other spatial schemes. While this approach to water resource management has considered the interaction between water quality and biological integrity (aquatic community structure and assemblage), it has not been applied in the context of predicting aquatic toxicity. As such, a previously published study providing a chemical and toxicological data set consisting of 24 sampling sites in South Carolina, USA, and was used to develop empirical models for predicting acute copper (Cu) toxicity to larval fathead minnows (Pimephales promelas). Moreover, numerous spatial classifications (hydrologic units, ecoregions, stream order, adjacent land use, and proximity to certain land uses) and seasonality were used to delineate sites and develop empirical models based on these different classifications. An independent sampling and testing regime was implemented to determine the performance of the empirical models and whether certain classifications could be used to extrapolate toxicity data across spatial landscapes. Additionally, a computational model (biotic ligand model [BLM]) for deriving site-specific water quality criteria for Cu also was used as a reference for current regulatory application. Empirical models based on delineations of stream order, hydrologic unit, and downstream distance to urbanization accurately predicted at least 60% of the observed Cu toxicity values within the supplemental data set. Delineations based on adjacent land use, ecoregions, and seasons were not as useful for predicting acute Cu toxicity but demonstrated better performance than the BLM.

RELEASE OF THE LIPID PEROXIDATION MARKER 8-EPI-PROSTAGLANDIN F2α FROM ISOLATED GILL PAVEMENT CELLS

The aim of the present study was to evaluate oxidative injury in gill pavement cells (GPCs) from fathead minnow (Pimephales promelas) using F2-isoprostane (F2-iP) release as an index of lipid peroxidation. Cells were isolated from pooled gill tissue by collagenase treatment, mechanical sieving, and Percoll density gradient centrifugation. Baseline levels of 8-epi-prostaglandin F2 alpha (8-epi-PGF2 alpha) were measured by incubating GPCs in physiological buffer (10(6) cells/ml) and enzyme immunoassay. After 60 min, the amount of immunoreactive 8-epi-PGF2 alpha (ir8-epi-PGF2 alpha) in control medium ranged from 1,374 to 5,515 pg/ml. Lead nitrate, 0.6 to 120 microM, did not influence ir8-epi-PGF2 alpha release, whereas FeCl3 stimulated release at 500 microM but not at 5 microM. Incubation medium was extracted for acidic lipids and analyzed by liquid chromatography/mass spectrometry/electrospray ionization. A compound in the medium exhibited a retention time on reverse-phase high-performance liquid chromatography nearly identical to that of synthetic 8-epi-PGF2 alpha The mass spectrum taken from the total ion chromatogram from 14.8 to 15.1 min contained a prominent ion at m/z 353, as expected for the molecular ion of 8-epi-PGF2 alpha. Similar results were obtained with tissue subjected to base hydrolysis. Mass spectra of extracted ion chromatograms obtained with gill extracts and authentic standard showed a close correspondence of fragment ions, providing definitive evidence for production and storage of F2-iPs by fish gills. In summary, F2-iP release occurs during lipid peroxidation injury to fish gill epithelium, and its measurement may facilitate aquatic toxicology studies of metallic and nonmetallic contaminants.

Handling uncertainties in toxicity modelling using a fuzzy filter

A fundamental concern in the Quantitative Structure-Activity Relationship approach to toxicity evaluation is the generalization of the model over a wide range of compounds. The data driven modelling of toxicity, due to the complex and ill-defined nature of eco-toxicological systems, is an uncertain process. The development of a toxicity predicting model without considering uncertainties may produce a model with a low generalization performance. This study presents a novel approach to toxicity modelling that handles the involved uncertainties using a fuzzy filter, and thus improves the generalization capability of the model. The method is illustrated by considering a data set dealing with the fathead minnow (Pimephales promelas) toxicity of 568 organic compounds.

The Relationships among CYP1A Induction, Toxicity, and Eye Pathology in Early Life Stages of Fish Exposed to Oil Sands

Exposure of the early life stages of fish to oil sands constituents is associated with mortality and larval malformations such as edemas, hemorrhages, and skeletal, craniofacial, and eye defects. In fathead minnow (Pimephales promelas) and white sucker (Catostomus commersoni) larvae, indices of total eye pathology increased significantly following oil sands exposure. Structural, cytoplasmic, inflammatory, and degenerative eye alterations included poor retinal differentiation, microphthalmia, optic fissures, dysphasic retinas and lenses, inflammatory infiltrates, retinal epithelial lifting, and necrotic foci. Cytochrome P-4501A (CYP1A) was expressed in ocular (retina, lens) and kidney endothelial tissues, as indicated by immunohistochemistry. Although the kinetics of exposure-response curves for mortality and CYP1A expression were similar in both species, species differences in the magnitude and sensitivity of the responses were observed. Oil sands were twofold more toxic to fathead minnows (TPAH LC50 = 47–330 μg/g) than to white sucker (TPAH LC50 = 95–860 μg/g) larvae. For both species, larval mortality was significantly related to CYP1A protein concentrations in kidneys, and severity of these effects rose with oil sands exposure. The relationships among eye damage, mortality, and CYP1A indices warrants further investigation, and may lead to the use of CYP1A induction as an indicator of adverse effects rather than just contaminant exposure.

Induction of CYP1A and DNA damage in the fathead minnow (Pimephales promelas) following exposure to biosolids

Biosolids (treated sewage sludge) are increasingly disposed of on land. Thus particle-sorbed and dissolved constituents have the potential to enter nearby watersheds. Although organic contaminants are known to be present in biosolids these are not currently regulated and little data exist on their potential toxicity to aquatic organisms. We exposed Pimephales promelas to two concentrations of biosolids (0.5 and 2.5 g l(-1)) for 28-days (static-renewal) and characterized contaminants present and the extent of CYP1A and DNA damage induction at various time points. Many organic contaminants were detected in the biosolids, with polycyclic aromatic hydrocarbons (PAHs) being the dominant class. Substantial levels of polybrominated diphenyl ethers (PBDEs) and nonylphenols (NPs) were also present. Significant induction of hepatic CYP1A protein compared with controls (P<0.05) was observed in both low (0.5 g l(-1)) and high (2.5 g l(-1)) exposed fish from Day 7. CYP1A levels peaked at Day 21 with 21-fold and 8-fold inductions over controls in high and low dose fish respectively. Induction of DNA damage in hepatocytes (single strand breaks as measured using the COMET assay) was observed in both exposures compared with controls on Days 14 and 28 (P<0.05). A significant correlation was found between CYP1A induction and DNA damage (Pearson correlation index, P<0.05). It is plausible that activation of PAHs may be responsible for the induction of CYP1A and resulting increase in DNA damage. Our data show the potential for detrimental effects in the event of exposure of aquatic organisms to biosolids and the need for further investigations of possible impacts due to constituents not covered by current guidelines.

Effects of methylmercury and spatial complexity on foraging behavior and foraging efficiency in juvenile White Ibises (Eudocimus albus)

Methylmercury is a globally distributed neurotoxin, endocrine disruptor, and teratogen, the effects of which on wildlife at environmentally relevant levels are largely unknown. In birds, foraging efficiency and learning may be sensitive endpoints for sublethal methylmercury toxicity, and these endpoints also may be biologically relevant at the population level. In the present study, groups of wild-caught, prefledgling white ibises (Eudocimus albus) were raised in a free-flight, open-air aviary on diets that approximated the measured range of methylmercury exposure in the Everglades ecosystem (0, 0.05, 0.1, and 0.3 mg/kg/d). The effect of methylmercury exposure on group foraging efficiency was examined by allowing birds to forage on 200 fathead minnows (Pimephales promelas) in artificial ponds for 15 min by straining the arenas' contents through a seine net and counting all remaining prey. Additionally, we varied the difficulty of foraging by these tactile feeding birds by adding multiple levels of structural complexity (e.g., increased vegetation and prey refugia) to the pond. Structural complexity affected both foraging efficiency and the rate of increase in efficiency over time (improvement). Methylmercury exposure affected foraging efficiency (p = 0.03). It did not affect foraging improvement in the face of increasingly challenging environments, however, and the dose-response relationship was nonlinear (e.g., the control and high-exposure groups were the least efficient foragers). Evidence for an effect of methylmercury on foraging efficiency therefore was inconclusive because of unpredicted results and no interaction with time or habitat complexity. These data suggest a nonlinear dose-response relationship at low levels of methylmercury exposure; future research is needed to verify this hypothesis. This appears to be the first experimental demonstration of the effects of habitat complexity on foraging efficiency in long-legged wading birds.

Development of quantitative real-time PCR assays for fathead minnow (Pimephales promelas) gonadotropin â subunit mRNAs to support endocrine disruptor research

Development of quantitative real-time PCR assays for fathead minnow (Pimephales promelas) gonadotropin â subunit mRNAs to support endocrine disruptor research

Determining Site-Specific Toxicity of Copper to Daphnids and Fishes in a Brown-Water Ecosystem

ABSTRACT We examined the influence that wetland brown water had on the toxicity of copper to aquatic species in Swamp Creek basin, Wisconsin. Copper was added to Swamp Creek water and to laboratory-prepared reconstituted water and tested for toxicity using daphnids (Ceriodaphnia dubia and Ceriodaphnia reticulate), larval fathead minnows (Pimephales promelas), and larval walleye (Stizostedion vitreum). The toxicities of copper in Swamp Creek water, which contained dissolved organic carbon (DOC), were significantly lower than in water with no DOC. Therefore in successive experiments. using cultured C. dubia as the test organism, we experimentally reduced DOC in Swamp Creek water. We established that increased concentrations of DOC and hardness increased the odds of survival of C. dubia in the presence of potentially lethal concentrations of copper. In the Swamp Creek watershed which contains brown water and in watersheds where DOC concentrations are substantial, DOC, and hardness could be the principal factors in developing site-specific criteria involving copper and perhaps other metals.