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Biomedical subjects

David E Hinton

Publications and source records attributed to David E Hinton.

At least 19 recordsLinked to original sources

Vulnerable windows for developmental ethanol toxicity in the Japanese medaka fish (Oryzias latipes).

Ethanol (EtOH) is a well-known developmental toxicant that produces a range of abnormal phenotypes in mammalian systems including craniofacial abnormalities, cognitive deficits and growth retardation. While the toxic potential of developmental EtOH exposure is well characterized clinically, the effect of timing on the extent of toxicity remains unknown. Fish models such as the Japanese medaka, Oryzias latipes, provide a convenient system for investigating the effects of developmental EtOH exposure in vivo. In this study, medaka embryo toxicity tests were used to assess temporal variations in developmental EtOH toxicity. Fertilized eggs were collected and incubated during early, middle or late egg development (e.g., 0-3, 3-6 or 6-9 days post-fertilization) with various sub-lethal concentrations of EtOH [0.1% (17.2 mM), 0.5% (86.0 mM) or 1% (172 mM)]. Uptake of EtOH by the embryo was 60-68% of the solution concentration across all windows. Time to hatch, head width, total body length and whole embryo caspase activity were used to assess toxicity. Hatching delays were noted only at the highest concentration of EtOH. Head width was affected at all ethanol levels, regardless of the window of exposure. EtOH-induced decreases in body length, however, appeared to be most pronounced when exposure occurred either during the first or last window. The effect on caspase-3/7 activity also depended on the window of exposure, with increases in caspase noted in embryos treated on days 1 or 2 (first window) and decreases seen in embryos treated on day 6 (second window) or day 8 (third window). In general, these data suggest that critical periods for heightened sensitivity to developmental EtOH exposure may vary according to the specific endpoint used to assess toxicity.

Animals↗

Age-dependent in situ hepatic and gill CYP1A activity in the see-through medaka (Oryzias latipes).

We used a recently introduced strain of medaka, the see-through medaka, whose internal organs can be seen through the skin, to develop an in situ toxicity assay of ethoxyresorufin-O-deethylase (EROD) activity that detected fluorescence from resorufin, a metabolite of ethoxyresorufin and thus an indicator of CYP1A activity. EROD activity in the liver and gills of 2-week post-hatch see-through medaka exposed simultaneously to various concentrations of 3-methylcholanthrene and 200 microg/L ethoxyresorufin for 24 h was proportional to the 3-methylcholanthrene dose. Activities in the liver and gills peaked at 40 microg/L of 3-methylcholanthrene and then decreased at higher doses, possibly because of 3-methylcholanthrene toxicity. At 1-week post-hatch stage, however, constant high EROD activity was observed in controls and at all 3-methylcholanthrene doses. Four-week post-hatch see-through medaka exhibited less EROD activity than 2-week post-hatch see-through medaka, and activity in the liver peaked at 100 microg/L of 3-methylcholanthrene. Adult see-through medaka were not suitable for fluorescence detection owing to their thick skin, muscle and/or tissue. In tests of oxidative activity response to ethoxyresorufin, 1-day and 1-week post-hatch see-through medaka exhibited high intrinsic EROD activity in the liver, gills, and other organs in the absence of 3-methylcholanthrene. This intrinsic activity declined with growth and explained the high constant EROD activity at 1-week post-hatch stage.

Aging↗

Biological assessment of bisphenol A degradation in water following direct photolysis and UV advanced oxidation.

Endocrine disrupting compounds (EDCs) are exogenous environmental chemicals that can interfere with normal hormone function and present a potential threat to both environmental and human health. The fate, distribution and degradation of EDCs is a subject of considerable investigation. To date, several studies have demonstrated that conventional water treatment processes are ineffective for removal of most EDCs and in some instances produce multiple unknown transformation products. In this study we have investigated the use of direct photolysis with low-pressure (LP) Hg UV lamps and UV+hydrogen peroxide (H(2)O(2)) advanced oxidation process (AOP) for the degradation of a prototypic endocrine disrupter, bisphenol A (BPA), in laboratory water. Removal rates of BPA and formation of degradation products were determined by high performance liquid chromatography (HPLC) analysis. Changes in estrogenic activity were evaluated using both in vitro yeast estrogen screen (YES) and in vivo vitellogenin (VTG) assays with Japanese medaka fish (Oryzias latipes). Our results demonstrate that UV alone did not effectively degrade BPA. However, UV in combination with H(2)O(2) significantly removed BPA parent compound and aqueous estrogenic activity in vitro and in vivo. Removal rates of in vivo estrogenic activity were significantly lower than those observed in vitro, demonstrating differential sensitivities of these bioassays and that certain UV/AOP metabolites may retain estrogenic activity. Furthermore, the UV/H(2)O(2) AOP was effective for reducing larval lethality in treated BPA solutions, suggesting BPA degradation occurred and that the degradation process did not result in the production of acutely toxic intermediates.

Animals↗

Adapting the medaka embryo assay to a high-throughput approach for developmental toxicity testing.

Chemical exposure during embryonic development may cause persistent effects, yet developmental toxicity data exist for very few chemicals. Current testing procedures are time consuming and costly, underlining the need for rapid and low cost screening strategies. While in vitro methods are useful for screening, these methods do not replicate all the intricacies of embryonic development and should ideally be complemented by an in vivo screening strategy. In this study, we modify a medaka fish embryo assay to meet the requirements of high-throughput, developmental toxicant testing in vivo. The Japanese medaka (Oryzias latipes) offers several advantages over traditional mammalian model systems, including economic husbandry, high fecundity, and rapid ex utero development. In most studies where fish eggs are exposed to a chemical, the exposure takes place in a common vessel, with many embryos being exposed to the same solution. This type of design is not amenable to high-throughput methodology, does not allow the investigator to follow the same embryo throughout gestation, and may confound statistical analysis of the results. Therefore, we developed a 96-well microtiter plate method to facilitate exposure of individual medaka embryos in single wells and compared this approach to the common vessel method using the industrial solvent dimethyl sulfoxide (DMSO) as the test compound. At lower DMSO concentrations (0% or 1%), the 96-well microtiter plate assay replicated results obtained using the common vessel exposure method. There was, however, increased lethality and decreased hatching rate in the bottle-reared embryos treated with the higher DMSO concentrations (5% or 10%). Because the embryos reared in the 96-well microtiter plates never showed increased adverse effects (as compared to the bottle-reared embryos) at any DMSO concentration, we conclude that the 96-well microtiter plate assay provides a rapid and efficient alternative for developmental toxicity screens that utilize fish embryos.

Age Factors↗

Toxic actions of dinoseb in medaka (Oryzias latipes) embryos as determined by in vivo 31P NMR, HPLC-UV and 1H NMR metabolomics.

Changes in metabolism of Japanese medaka (Oryzias latipes) embryos exposed to dinoseb (2-sec-butyl-4,6-dinitrophenol), a substituted dinitrophenol herbicide, were determined by in vivo (31)P NMR, high-pressure liquid chromatography (HPLC)-UV, and (1)H NMR metabolomics. ATP and phosphocreatine (PCr) metabolism were characterized within intact embryos by in vivo (31)P NMR; concentrations of ATP, GTP, ADP, GDP, AMP and PCr were determined by HPLC-UV; and changes in numerous polar metabolites were characterized by (1)H NMR-based metabolomics. Rangefinding exposures determined two sublethal doses of dinoseb, 50 and 75 ppb, in which embryos survived from 1-day post fertilization (DPF) through the duration of embryogenesis. In vivo (31)P NMR data were acquired from 900 embryos in 0, 50, and 75 ppb dinoseb at 14, 62, and 110 h (n = 6 groups) after initiation of exposure. After 110 h, embryos were observed for normal development and hatching success, then either preserved in 10% formalin for growth analysis or flash frozen and extracted for HPLC-UV and (1)H NMR analysis. Dinoseb exposure at both concentrations resulted in significant declines in [ATP] and [PCr] at 110 h as measured by in vivo (31)P NMR (p < 0.01), HPLC-UV (p < 0.001) and NMR-based metabolomics. Reduced eye growth and diminished heart rate occurred in a concentration-dependent fashion. Metabolic effects measured by in vivo (31)P NMR showed a significant increase in orthophosphate levels (P(i); p < 0.05), and significant decreases in [ATP], [PCr] and the PCr/P(i) ratio (p < 0.05). Metabolomics revealed a dose-response relationship between dinoseb and endogenous metabolite changes, with both dinoseb concentrations producing significantly different metabolic profiles from controls (p < 0.05). Metabolic changes included decreased concentrations of ATP, PCr, alanine and tyrosine, and increased concentrations of lactate with medaka embryotoxicity. This study demonstrated that medaka embryos respond to dinoseb with significant changes in metabolism, reduced growth and heart rates, and increased abnormal development and post-exposure mortality. All three analytical methods confirmed similar trends, and utilization of PCr to compensate for ATP loss was found to be a consistent indicator of sublethal stress-one that could be used to quantify stress associated with medaka embryotoxicity.

2,4-Dinitrophenol↗

Dynamic gene expression changes precede dioxin-induced liver pathogenesis in medaka fish.

A major challenge for environmental genomics is linking gene expression to cellular toxicity and morphological alteration. Herein, we address complexities related to hepatic gene expression responses after a single injection of the aryl hydrocarbon receptor (AHR) agonist 2,3,7,8-tetrachlorodibenzo-p-dioxin (dioxin) and illustrate an initial stress response followed by cytologic and adaptive changes in the teleost fish medaka. Using a custom 175-gene array, we find that overall hepatic gene expression and histological changes are strongly dependent on dose and time. The most pronounced dioxin-induced gene expression changes occurred early and preceded morphologic alteration in the liver. Following a systematic search for putative Ah response elements (AHREs) (5'-CACGCA-3') within 2000 bp upstream of the predicted transcriptional start site, the majority (87%) of genes screened in this study did not contain an AHRE, suggesting that gene expression was not solely dependent on AHRE-mediated transcription. Moreover, in the highest dosage, we observed gene expression changes associated with adaptation that persisted for almost two weeks, including induction of a gene putatively identified as ependymin that may function in hepatic injury repair. These data suggest that the cellular response to dioxin involves both AHRE- and non-AHRE-mediated transcription, and that coupling gene expression profiling with analysis of morphologic pathogenesis is essential for establishing temporal relationships between transcriptional changes, toxicity, and adaptation to hepatic injury.

Animals↗

Resolving mechanisms of toxicity while pursuing ecotoxicological relevance?

In this age of modern biology, aquatic toxicological research has pursued mechanisms of action of toxicants. This has provided potential tools for ecotoxicologic investigations. However, problems of biocomplexity and issues at higher levels of biological organization remain a challenge. In the 1980s and 1990s and continuing to a lesser extent today, organisms residing in highly contaminated field sites or exposed in the laboratory to calibrated concentrations of individual compounds were carefully analyzed for their responses to priority pollutants. Correlation of biochemical and structural analyses in cultured cells and tissues, as well as the in vivo exposures led to the production and application of biomarkers of exposure and effect and to our awareness of genotoxicity and its chronic manifestations, such as neoplasms, in wild fishes. To gain acceptance of these findings in the greater environmental toxicology community, "validation of the model" versus other, better-established often rodent models, was necessary and became a major focus. Resultant biomarkers were applied to heavily contaminated and reference field sites as part of effects assessment and with investigations following large-scale disasters such as oil spills or industrial accidents. Over the past 15 years, in the laboratory, small aquarium fish models such as medaka (Oryzias latipes), zebrafish (Danio rerio), platyfish (Xiphophorus species), fathead minnow (Pimephales promelas), and sheepshead minnow (Cyprinodon variegatus) were increasingly used establishing mechanisms of toxicants. Today, the same organisms provide reliable information at higher levels of biological organization relevant to ecotoxicology. We review studies resolving mechanisms of toxicity and discuss ways to address biocomplexity, mixtures of contaminants, and the need to relate individual level responses to populations and communities.

Animals↗

Functional characterization of medaka CYP3A38 and CYP3A40: kinetics and catalysis by expression in a recombinant baculovirus system.

Phylogenic analysis of the teleost genomic lineages has demonstrated the precedent for multiple genome duplications. Among many of the genes duplicated, cytochrome P450 genes have undergone independent diversification, which can be traced to a single ancestral gene. In teleosts, cytochrome P450s, from all major families, have been identified. Among these, the CYP3A family has been cloned in several teleost species and demonstrated to contain multiple paralogs differing in gene expression patterns and tissue distribution. Herein we characterized the catalytic and kinetic activities of two medaka CYP3A paralogs (CYP3A38 and CYP3A40) with benzyloxyresorufin (BFC), a fluorescent 3A-selective substrate, and testosterone, a known metabolic substrate for CYP3A enzymes. Recombinant CYP3A was produced using the baculovirus expression vector system in Spodoptera frugiperda (Sf9) and Trichoplusia ni (Tn5) insect cells and accounted for up to 24% of total cellular protein. Following addition of a heme-albumin conjugate to log phase cells, spectral P450 content reached a maximum of 560 and 2350 pmol/mg microsomal protein for CYP3A38 and CYP3A40, respectively. Incubations containing recombinant CYP3A, human NADPH-cytochrome P-450 oxidoreductase reductase, human cytochrome b5, and a NADPH generation system catalyzed the dealkylation of BFC and hydroxylation of testosterone with a high degree of stereoselectivity. However, efficiencies and specificities were significantly different between the two isoforms. Km and Vmax activities based on BFC-catalysis were 0.116 and 0.363 muM, and 7.95 and 7.77 nmol/min/nmol P450 for CYP3A38 and CYP3A40, respectively. CYP3A38 preferentially catalyzed testosterone hydroxylation at the 6beta-, 2beta- and 16beta-positions with minor hydroxylation at other positions within the steroid nucleus. Testosterone catalysis with CYP3A40 was limited predominantly to the 6beta- and 2beta-positions. Putative identification of CYP3A substrate recognition sites (SRS) 1-6 indicates that 12 of the 49 amino acid differences between CYP3A38 and CYP3A40 OFRs occur in SRS regions previously known to be associated with steroid hydroxylation. We suggest that differences in kinetics and catalytic activities are a result of amino acid substitutions in SRS regions 1, 3 and 5 within the CYP3A38 and CYP3A40 protein sequence.

Amino Acid Sequence↗

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) induces organ- specific differential gene expression in male Japanese medaka (Oryzias latipes).

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a ubiquitous environmental contaminant with well-known adverse effects in fish. In this study, we initially exploited suppression subtractive hybridization (SSH) as a screening tool to assess qualitative gene expression changes in whole brain, liver, and testis of adult male Japanese medaka (Oryzias latipes) exposed for 48 h to a single intraperitoneal-injected dose of TCDD (10 microg TCDD/kg body weight). Across these three organs, SSH identified a total of 335 unique genes. Each set of forward- and reverse-subtracted organ cDNA libraries consisted of a distinct gene list and corresponding distribution of biological processes, suggesting that transcript profiles of these libraries were highly organ-specific. Based on sequence match significance and frequencies within each set of organ libraries, genes hypothesized to be strongly responsive (42 total) within male medaka brain, liver, or testis were semi-quantitatively screened with replicate cDNA nylon membrane arrays. In addition, TCDD-treated male medaka were surveyed for gross histological analysis of brain, liver, and testis. In general, adverse histopathological changes were not observed in the brain, and glycogen depletion was observed only in the liver. However, significant histological changes occurred in the testis, and included disorganization of spermatogenesis at the testis periphery, disruption of the interstitium, Leydig cell swelling, and Sertoli cell vacuolation. Of the 42 genes screened by cDNA array analysis, cytochrome P450 1A (CYP1A) mRNA was the only transcript significantly higher in TCDD-exposed brain, whereas 12 transcripts (including CYP1A) were significantly higher in TCDD-exposed liver, and 34 transcripts were significantly lower in TCDD-exposed testis. Therefore, the degree of TCDD-induced alterations observed in each organ at a gross histological level corresponded well with the number and ontology of gene transcripts affected on the array. Based on real-time reverse transcription polymerase chain reaction (RT-PCR), relative CYP1A (but not AHR1) transcript levels were confirmed to be significantly higher in TCDD-treated brain and liver. However, CYP1A was not significantly induced in TCDD-exposed testis, suggesting that gene expression and histopathological responses observed in the testis at 48 h may be CYP1A-independent. Based on these data, unique liver-specific and testis-specific mRNA-level targets in male medaka were identified as promising biomarkers of acute TCDD-induced toxicity.

Animals↗

Metabolic changes in Japanese medaka (Oryzias latipes) during embryogenesis and hypoxia as determined by in vivo 31P NMR.

In vivo (31)P nuclear magnetic resonance spectroscopy (NMR) was used to determine phosphometabolite changes in medaka (Oryzias latipes) during embryogenesis and hypoxia. NMR data were acquired using a flow-through NMR tube perfusion system designed to both deliver oxygenated water to embryos and accommodate a hypoxic challenge. Measurements of embryogenesis at 12- and 24-h intervals throughout 8 days of development (n = 3 per time point, 900 embryos per replicate) and during acute hypoxia (n = 6, 900 embryos at Iwamatsu stage 37 per replicate) were performed via NMR, and replicate samples (n = 4, 250 embryos each) were flash frozen for HPLC analysis. The hypoxic challenge experiment consisted of data acquisition with recirculating water (pre-hypoxic control period; 1 h), without recirculating water (hypoxic challenge; 1 h), then again with recirculating water (recovery period; 1.3 h). Concentrations of ATP, phosphocreatine (PCr), orthophosphate (P(i)), phosphomonoesters (PME), phosphodiesters (PDE), and intracellular pH (pH(i)) were determined by NMR, and ATP, ADP, AMP, GTP, GDP, and PCr were also determined via HPLC. During embryogenesis, [ATP] and [PCr] as determined by HPLC increased from 1-day post fertilization (DPF) levels of 0.93+/-0.08 and 2.48+/-0.21 micromol/mg (dry tissue), respectively, to 7.24+/-0.77 and 15.66+/-1.08 micromol/mg, respectively, by day 8. [ATP] and [PCr] measured by both NMR and HPLC fluctuated over 1-3 DPF, then increased significantly (p<0.05) over 3-8 DPF, while [PME] and [PDE] decreased (p<0.05) throughout embryogenesis. NMR and HPLC measurements revealed 1-3, 4-5, and 6-8 DPF as periods of embryogenesis significantly different from each other (p<0.05), and representing important transitions in metabolism and growth. During hypoxic challenge, [ATP] and [PCr] declined (p<0.05), [PME] and [PDE] decreased slightly, and [P(i)] increased (p<0.05). All phosphometabolites returned to pre-hypoxia concentrations during recovery. The pH(i) decreased (p<0.05) from 7.10+/-0.03 to 6.94+/-0.03 as a result of hypoxia, and failed to return to pre-hypoxic levels within the 1.3-h recovery phase. Results demonstrate the utility of in vivo (31)P NMR to detect significant alterations in phosphorylated nucleotides and phosphometabolites at specific developmental stages during medaka development and that late-stage medaka utilize PCr to generate ATP under hypoxic conditions.

Animals↗

ras oncogene mutations in diethylnitrosamine-induced hepatic tumors in medaka (Oryzias latipes), a teleost fish.

Medaka fish are an established non-mammalian research model for the study of liver carcinogenesis and exposure to environmental pollutants. Studies have emphasized the development of hepatic neoplasms in medaka following exposure to model carcinogens. To date however, little information is known regarding the mechanisms underlying initiation of hepatic tumors in this species. The aim of this study was to relate our understanding of diethylnitrosamine (DEN)-induced tumor formation to ras gene activation in hepatic neoplasms of exposed medaka. Initial studies were conducted to identify medaka ras exons 1 and 2 by reverse transcriptase polymerase chain reaction (RT-PCR). Amplification of ras exons 1 and 2 from untreated medaka liver resulted in the identification of three polymorphic ras sequence variants exhibiting a high degree of homology to other teleost and mammalian ras genes. Exposure of medaka to 159 ppm of DEN resulted in a wide range of hepatic neoplasms including: hepatocellular adenomas, hepatocellular carcinomas, cholangiomas, and mixed hepatocholangiocellular carcinomas. Individual liver tumors were examined for oncogenically activating ras mutations by probing genomic DNA with probes specific for activating point mutations or by direct cloning and sequencing of ras transcripts using RT-PCR. Using allele-specific oligonucleotide (ASO) analysis, a single point mutation was detected in codon 12 position two in 8/25 (32%) tumors examined. Mutated ras alleles were additionally detected in 12 of 39 (30%) medaka liver tumors by sequence analysis. Ten of the 12 mutations identified contained a single point mutation at codon 12 resulting in a Gly to Asp amino acid substitution. Two unique mutations were identified at codon 16 resulting in either Lys to Asn or Lys to Thr amino acid substitutions. Our results show that ras mutations are induced by DEN and are present in over 30% of the fish that developed tumors. A ras mutation incidence of 30% is similar to that reported in mammalian species exposed to DEN. While mutations at codon 12 have previously been reported, the present study is the first in vivo report of ras point mutations at codon 16.

Amino Acid Sequence↗

Stage sensitivity of medaka (Oryzias latipes) eggs and embryos to permethrin.

The effects of exposure to permethrin on gametes, fertilization and embryonic development were examined in medaka (Oryzias latipes). Following range finding (25, 50, 100, 200 or 300 microg/l) and duration of exposure (0, 120, 144, 168, 192, 216, or 240-h) assays, the relative sensitivity was studied when initiation of exposure to permethrin (100 microg/l, for 192-h) occurred at one of four different stages, i.e., unfertilized egg (0-h), late morula (5-h), early neurula (24-h), and early organogenesis (40-h). The later exposure interval proved the most sensitive. Also, differences were observed in rates of recovery in larvae initially affected following the earliest exposure treatment (0-h, gametes prior to fertilization). Permethrin (100 microg/l) did not affect fertilization success and no lethal effects were observed in embryos. Sublethal effects were primarily observed at hatch. Toxicity endpoints in larvae included: delayed swim bladder inflation; inability of hatchling to respond to stimulus; uncoordinated movements, myoskeletal defects and transient enlargement of gall bladder. These changes were characteristic for all hatchlings exposed to nominal concentrations of 50 microg/l. While certain of the above alterations were reversed within 72-h after hatching, lack of swim bladder inflation and inability to respond to stimuli were two features that persisted with significant incidences. Based on persistence of sublethal effects, results from this work indicate the importance of exposures to gametes and to embryos prior to water hardening. The approach taken herein may better reflect environmental risk conditions than assays limited to exposure of embryonated eggs.

Animals↗

Influence of water hardening of the chorion on cadmium accumulation in medaka (Oryzias latipes) eggs.

This report describes a study in which in vitro fertilization methods were used to expose medaka (Oryzias latipes) eggs to cadmium (Cd(2+)). This approach was applied to address the differential sensitivity and cumulative potential of Cd(2+) when exposure was initiated early (before fertilization and water hardening of the chorion) versus later during embryo development (i.e., well after the chorion has undergone water hardening). Following range finding exposures (2.5, 10, 20, 40 or 80 mg/l) under artificially controlled experimental procedures, results from hatching success and embryo malformations showed the earlier exposure interval more sensitive than the assay involving only the embryonated egg. Subsequent accumulation studies have shown that the exposure initiated before fertilization apparently led to more Cd(2+) deposition in the chorion compared to the exposure during embryonated stages of the eggs. Similarly, values for total Cd(2+) indicated higher concentrations in those eggs exposed prior to--and during--water hardening. Results suggest an alteration of the properties of the zona radiata in the early-stage eggs, making it more permeable to the potential exit or entrance of waterborne agents even after water hardening. Ongoing studies must now address the development of more realistic exposure conditions of the gametes by using incubation media with osmolarities similar to surface waters, and by shortening duration for gamete exposure. Also, sensitive methods to localize Cd(2+) and to delineate the transfer from the chorion to the embryo are needed.

Animals↗

Joint acute toxicity of esfenvalerate and diazinon to larval fathead minnows (Pimephales promelas).

California (USA) agriculture employs pyrethroid and organophosphate insecticides to control insects in orchards and other crops. Diazinon and esfenvalerate were selected for this study because of their application overlaps. Toxicological and biochemical responses of larval fathead minnows (Pimephales promelas) exposed singly and in combinations to esfenvalerate and diazinon were determined. Exposures were 96-h static renewal tests that used standard U.S. Environmental Protection Agency acute toxicity test methods. After pesticide exposures, larvae were evaluated for carboxylesterase and acetylcholinesterase activity, and histopathological effects. Carboxylesterase activity was examined because of its potential influence on the toxicity of both organophosphates and pyrethroids. In vivo studies demonstrated that diazinon significantly inhibited carboxylesterase activity at nominal water concentrations as low as 50 microg/L. However, esfenvalerate did not affect carboxylesterase activity at any concentration tested. Liver glycogen depletion was the only histopathological effect observed; this effect was demonstrated with the individual pesticides and pesticide combinations (i.e., mixtures). The combinations of diazinon and esfenvalerate causing acute toxicity to fathead minnow larvae appeared to be greater than additive (i.e., synergistic) in all three tests.

Acetylcholinesterase↗

Effects of husbandry practices, gender, and normal physiological variation on growth and reproduction of Japanese medaka, Oryzias latipes.

Japanese medaka, Oryzias latipes, are currently used in a variety of research applications for toxicological and carcinogenesis research, yet the impact of certain husbandry factors on study outcome has received limited attention. In this study, we demonstrated significant effects of stocking density (SD), dietary restriction (DR) and photoperiod on somatic growth in medaka. Higher stocking densities significantly inhibited somatic and hepatic growth in females, while having no similar effects on males. Daily egg production declined in a step-wise manner in groups of fish stocked at densities ranging from 0.38 to 2.6 fish per l. Significantly slower somatic growth was observed in fish fed on a mildly restrictive dietary protocol compared with those fish fed to excess. Further significant declines were observed in somatic growth of fish fed at a rate comparable to that used in research studies (3-4% body weight (BW) per day). Fish reared at an 8-h light:16-h dark (8L/16D) photoperiod were significantly smaller than cohorts reared at a 16-h light:8-h dark (16L/8D) photoperiod and female sexual maturity was delayed in the short photoperiod cohort. In normal female medaka, a high degree of individual variation was observed in daily egg production, as well as diurnal fluctuations in ovarian weight, gonadosomatic index (GSI) and hepatosomatic index (HSI). These results indicate some husbandry factors affect growth, sexual maturation and egg production in medaka and should be taken into consideration in studies evaluating endpoints that may be impacted by growth and reproductive performance, i.e. carcinogenesis and endocrine disruption studies. The high degree of individual variation among normal females and daily fluctuations in organ weights should also be considered in study design.

Animal Husbandry↗

Selenium biotransformations into proteinaceous forms by foodweb organisms of selenium-laden drainage waters in California.

Selenium contamination represents one of the few clear cases where environmental pollution has led to devastation of wildlife populations, most notably in agricultural drainage evaporation and power plant coal-fly ash receiving ponds. Complex biogeochemistry, in particular extensive biotransformations and foodchain transfer, governs Se ecotoxicology and toxicology, for which the mechanism(s) are still elusive. However, total waterborne Se concentration has been widely used as a criterion for regulating and mitigating Se risk in aquatic ecosystems, which does not account for Se biogeochemistry and its site-dependence. There is a need for more reliable indicator(s) that encompass Se ecotoxicity and/or toxicity. Selenomethionine warrants special attention since it simulates Se toxicosis of wildlife in laboratory feeding studies. While low in free selenomethionine, microphytes isolated from Se-laden agricultural evaporation ponds were abundant in proteinaceous selenomethionine. This prompted a more extensive survey of Se speciation in foodchain organisms including microphytes, macroinvertebrates, fish, and bird embryos residing mainly in the agricultural drainage systems of the San Joaquin Valley, California. Total Se in biomass, water-soluble fractions, and protein-rich fractions were measured along with GC-MS analysis of proteinaceous selenomethionine. In all foodchain organisms, water-soluble Se constituted the major fraction of total biomass Se, while proteinaceous Se was a substantial, if not dominant, fraction of the water-soluble Se. In turn, proteinaceous selenomethionine comprised an important fraction of proteinaceous Se. In terms of total biomass Se, an average 1400-fold of Se biomagnification from water to microphytes was observed while subsequent transfer from microphytes to macroinvertebrates exhibited an average of only 1.9-fold. The latter transfer was more consistent and greater in extent for proteinaceous Se and proteinaceous selenomethionine, which is consistent with their importance in foodchain transfer. Proteinaceous Se in the omnivorous carp (Cyprinus carpio) liver also demonstrated a relation to ovarian lesions, while deformed stilt (Himantopus mexicanus) embryo was more abundant in proteinaceous selenomethionine than were normal embryos. Although limited in the number of organisms surveyed, these findings provide an impetus for further field and laboratory feeding studies to substantiate the hypothesis that proteinaceous selenomethionine underlies Se ecotoxicity, which may in turn prove to be a reliable indicator of Se risk in aquatic ecosystems.

Animals↗