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At least 145 records · Page 8Linked to original sources
PubMed2006

Peliosis hepatis: microscopic and macroscopic type, time pattern, and correlation with liver cell apoptosis in a model of toxic liver injury.

Macroscopic and microscopic types of peliosis hepatis, time pattern, and correlation with hepatocyte and sinusoidal cell apoptosis were investigated. Male Wistar rats were injected with a dose of cadmium (6.5 mg CdCl(2)/kg body weight, intraperitoneally; group I). Putrescine (300 micromol/kg body weight, intraperitoneally; group II) was injected at 2, 5, and 8 hours and vascular endothelial growth factor (VEGF; 400 ng/animal, intravenously; group III) at 2 hours. Animals from each group were humanely killed 0, 6, 12, 24, 48, or 60 hours after cadmium intoxication. Liver tissue was histologically assessed for necrosis, apoptosis, and peliosis. Apoptosis was also quantified by the TUNEL assay for hepatocytes and nonparenchymal liver cells. The discrimination between hepatic cell subpopulations was done histochemically. Sinusoidal cell apoptosis and macroscopic peliosis hepatis evolved in a monophasic pattern and correlated closely. Putrescine or VEGF administration totally reversed macroscopic peliosis. Putrescine exerted a major protective effect on hepatocytes, whereas the protective effect of VEGF was more pronounced for nonparenchymal liver cells. Microscopic peliosis also evolved in a monophasic pattern preceding macroscopic type. The extent of the lesion was reduced by putrescine and almost totally reversed by VEGF. Macroscopic peliosis progresses as a compound lesion closely correlating with nonparenchymal cell apoptosis. Both hepatocyte and nonparenchymal cell injury are prerequisites for the genesis of the lesion. Microscopic peliosis precedes macroscopic peliosis and up to a degree seems to be independent of initial hepatocyte injury, but it seems to depend on nonparenchymal cell injury.

Animals↗
PubMed1999

Characterization of the baboon responses to Shiga-like toxin: descriptive study of a new primate model of toxic responses to Stx-1.

The baboon response to intravenous infusion of Shiga toxin 1 (Stx-1) varied from acute renal failure, proteinuria, hyperkalemia, and melena with minimal perturbation of host inflammatory and hemostatic systems (high-dose group, 2.0 microg/kg; n = 5) to renal failure with hematuria, proteinuria, thrombocytopenia, schistocytosis, anemia, and melena (low-dose group, 0.05 to 0.2 microg/kg; n = 8). Both groups exhibited renal shutdown and died in 57 hours or less. Both groups produced urine that was positive for tumor necrosis factor and interleukin-6 although neither of these cytokines was detectable (</=5 ng/ml) in the general circulation. Light and electron microscopy showed organelle disintegration and necrosis of the renal proximal tubular epithelium and of the intestinal mucosal epithelium at the tips of the microvilli, both of which were previously shown to bear Gb3 receptors. The renal distal tubular epithelium was spared. The renal proximal tubular epithelial changes were accompanied by swelling of visceral epithelial cells (podocytes) and by swelling and detachment of endothelial cells of the glomerular capillaries. In addition, all of the animals receiving low-dose Stx-1 showed microvascular fibrin deposition and thrombosis in renal glomerular and peritubular capillaries in association with a fall in hematocrit and platelet count and a rise in schistocyte count. The gastrointestinal villous tip lesions were accompanied by varying degrees of mucosal and submucosal congestion, hemorrhage, or necrosis. Electron microscopic images of cerebral cortex and cerebellum showed diffuse unraveling of myelin sheaths with occasional disintegration of neuronal cell bodies. In contrast to the gastrointestinal mucosal and renal proximal tubular epithelium, the Gb3 receptor glycolipid of the renal glomerular and neuronal tissues as determined using toxin overlay thin-layer chromatography plates was below the limit of detection (<13 pM/g wet tissue). We conclude that, depending on the status of the host and amount of toxin infused, Stx-1 can produce a variety of responses ranging from damage to cells carrying the Gb3 receptor (renal proximal tubular epithelial cells and gastrointestinal mucosa) to damage to renal glomerular tissues with microvascular thrombosis as a result of the host's inflammatory response localized to the kidney. We conclude that this thrombotic coagulopathy arises from local changes in the kidney because the appearance of host inflammatory mediators was limited to the urine. This suggests that the initial host response is localized in the kidney, and that the systemic thrombocytopenia, anemia, and schistocytosis may arise secondarily.

Animals↗
PubMed2002

Cytosine-phosphate-guanine (CpG) motifs are sensitizing agents for lipopolysaccharide in toxic shock model.

OBJECTIVE: Unmethylated cytosine-phosphate-guanine (CpG) oligodeoxynucleotides are highly frequent motifs in bacterial DNA and rare in the mammalian genome. They are potent inducers of inflammatory cytokines and act synergistically with lipopolysaccharide (LPS) for the induction of tumor necrosis factor alpha (TNF-alpha) production in vivo. It has therefore been suggested that innate immune reaction to bacterial unmethylated CpG motifs might contribute to the development of septic shock. We designed this study to assess the sensitization role of CpG motifs in LPS-induced shock using the D-galactosamine (D-GalN)-sensitized mouse model. DESIGN: A prospective, randomized in vivo animal laboratory study. SETTING: Experimental research laboratory. INTERVENTION: We performed experiments in which CpG, LPS and D-GalN were administrated sequentially in various orders or simultaneously in 8 week-old BALB/c mice. MEASUREMENTS AND RESULTS: Cytosine-phosphate-guanine treatment potentiated LPS action only if injected prior to LPS. A combination of predefined sublethal doses of CpG (1 nmol/mouse) and LPS (1 ng/mouse) not only had a synergetic effect on TNF-alpha production (20.3+/-9.2 IU/ml versus 2.5+/-1.4 IU/ml and 5.6+/-3.4 IU/ml for CpG and LPS groups, respectively, p<0.05), but also led to animal death (5/5). An CpG effect requires de novo mRNA synthesis, since the sensitizing effect was inhibited by co-administration of mRNA transcription inhibitors such as D-GalN and pentoxifylline, which is a specific TNF-alpha transcription inhibitor. Furthermore, CpG treatment provoked a strong TNF-alpha mRNA production in the liver that was dramatically reduced by pre-treatment with D-GalN. CONCLUSION: Our findings indicate that CpG motifs act synergistically with LPS by initializing the synthesis of TNF-alpha and/or TNF-alpha regulating factors, thereby acting as a sensitizing agent.

Animals↗
PubMed1984

Chemical models for toxic metabolites of bromobenzene derivatives. Relative toxicity toward isolated hepatocytes.

In the rat the hepatotoxicity of bromobenzene is greatly enhanced by the introduction of a cyano group adjacent to the bromine (i.e. o-bromobenzonitrile). Epoxide metabolites of these aryl halides are believed to be the actual toxic species, but epoxides of the latter compound also possess a second site of chemical reactivity not found in epoxides of bromobenzene, i.e. a Michael acceptor group formally related to acrylonitrile. Because these epoxides have never been isolated or synthesized for direct evaluation of their toxicity we have determined the toxicity toward isolated rat hepatocytes of a series of cyclohexene and cyclohexadiene derivatives containing epoxide and/or alpha, beta-unsaturated nitrile functional groups. Simple epoxides and unsaturated nitriles were much less toxic than bromobenzene itself, even if both groups were present in the same molecule. However, alpha, beta-unsaturated epoxides were found to be 2-3 times more toxic than bromobenzene, and at least 10 times more toxic than their saturated analogs, which is consistent with their relatively greater chemical reactivity. It is unlikely that Michael acceptor metabolites account for the increased toxicity of o-bromobenzonitrile relative to bromobenzene.

Alanine Transaminase↗
PubMed1988

Evaluation of the effects of multiple-dose activated charcoal on the absorption of orally administered salicylate in a simulated toxic ingestion model.

The effects of multiple-dose activated charcoal administration on the absorption of orally administered salicylate were evaluated in a simulated overdose model. Thirteen adult volunteers were each given 24 81-mg aspirin tablets during a control phase, and during three randomized treatment periods the volunteers received 50 g activated charcoal for one, two, or three doses (separated by four hours). The control phase and treatment periods were separated by a one-week interval. Urine was collected for 48 hours to determine percent total salicylate excretion. Ten subjects completed all four phases of the study. Mean +/- SD percent recovery of salicylate from urine was: control, 91.0 +/- 6.12; one-dose charcoal, 68.3 +/- 12.46; two-dose charcoal, 65.9 +/- 13.48; and three-dose charcoal, 49.2 +/- 12.48. Each charcoal treatment significantly lowered the absorption of aspirin as compared with the control (P less than .01). There was no significant difference between one-dose and two-dose charcoal regimens. There was a statistically significant decrease in salicylate absorption with the three-dose charcoal regimen as compared to one-dose and two-dose regimens (P less than .01). We conclude that activated charcoal is effective in inhibiting absorption of orally administered salicylate, in a small-dose aspirin ingestion model, with a three-dose multiple charcoal regimen being superior to either single-dose or two-dose regimens.

Administration, Oral↗
PubMed1990

Pentoxifylline in amphotericin B toxicity rat model.

The mechanism of acute nephrotoxicity following the administration of amphotericin B (AmpB) remains unclear despite a number of studies describing hypermagnesuria, hyperkaluria, and hemodynamic changes. The present experiments attempted to elucidate the mechanism by using a novel hemorheologic probe, pentoxifylline (PTX). Acute studies were performed with rats given single intravenous doses of AmpB (1 mg/kg of body weight) with or without intraperitoneal PTX (45 mg/kg). Renal function, assessed by inulin clearance (CLIN) and electrolyte handling, and morphology were compared with those of controls given sterile water and PTX. A significant decrease in CLIN not observed in rats given AmpB and PTX or in the controls was found in rats given AmpB. Electrolyte handling was not different among groups. Whereas pronounced (3 and 4+ on a scale of mild to significant [1+ to 4+]) vascular congestion was found in rats given AmpB, rats coadministered PTX had mild (1 and 2+) medullary and glomerular vascular congestion. In chronic studies, intravenous AmpB (1 mg/kg per day) or sterile water was coadministered with intraperitoneal PTX (45 mg/kg every 12 h) or saline for 10 days. Mean CLIN of rats coadministered AmpB and PTX was not significantly different from that of PTX control rats (1.61 +/- 0.19 versus 1.31 +/- 0.29 ml/min per g of kidney weight). A 46% decline in CLIN was found in rats treated with AmpB and saline (P less than 0.05). Renal sodium and potassium excretions were increased in both AmpB-treated groups compared with controls. Coupled with histologic evidence of the acute studies, these data suggest that the benefit of PTX in the prevention of AmpB-induced nephrotoxicity is, in part, due to vascular decongestion.

Amphotericin B↗
PubMed2006

Lgl1 is suppressed in oxygen toxicity animal models of bronchopulmonary dysplasia and normalizes during recovery in air.

Bronchopulmonary dysplasia (BPD), a major cause of morbidity in premature infants, is characterized by arrest of lung growth and inhibited alveologenesis. We had earlier cloned late-gestation lung 1 (LGL1), a glucocorticoid (GC)-induced, developmentally regulated gene in lung mesenchyme, and showed that reduced levels of late-gestation lung 1 protein (lgl1) inhibit lung branching. Maximal fetal expression of LGL1 is concordant with the onset of alveolar septation, suggesting an additional role for lgl1 in alveologenesis. At postnatal d 7, during the period of maximal septation in postnatal rat lung, lgl1 concentrates at the tips of budding secondary alveolar septa. We studied two models of impaired postnatal alveologenesis generated by exposure of newborn rats to 60% O2 for 2 wk or 95% O2 for 1 wk. A profound decrease of lgl1 expression with oxygen exposure was observed in both animal models. Animals exposed to 95% O2 for 1 wk recovered in air over a 3-wk period, associated with normalization of lgl1 levels. Changes in lung levels of alpha-actin (a marker of myofibroblast differentiation associated with alveologenesis) and the mesenchymal marker vimentin were significant but less marked. Our findings support a role for lgl1 in postnatal lung development. We speculate that deficiency of lgl1 contributes to the arrested alveolar partitioning observed in BPD and that recovery is associated with normalization of lgl1 levels.

Actins↗
PubMed1982

Pertussis antigens--screening models on toxicity.

From the same batch of B. pertussis bacteria two types of DPT-vaccines were produced after harvest of the inactivated organisms by centrifugation or acid precipitation. The first vaccine contained whole pertussis bacteria and the second an extracted antigen complex. In a screening programme with reliable animal tests, such as a modified mouse-weight-gain assay, mouse leukocytosis test, histamine sensitization in mice, allergic encephalitis in rats, and the limulus test it could be demonstrated that the vaccine with whole inactivated bacteria was more toxic than that with extracted antigens. Cell material harvested by centrifugation showed a lower rate of toxicity than that containing acid-precipitated pertussis organisms.

Animals↗
PubMed2005

Toward a biotic ligand model for freshwater green algae: surface-bound and internal copper are better predictors of toxicity than free Cu2+-ion activity when pH is varied.

The freshwater green microalgae Chlorella sp. and Pseudokirchneriella subcapitata (P. subcapitata) were chronically (48 and 72 h, respectively) exposed to copper at various pH levels, i.e., pH 6-7.5 and pH 5.9-8.5, respectively. Concentrations resulting in 50% inhibition of exponential growth rate (EC50) were determined as dissolved Cu, estimated chemical activity of the free Cu2+ ion (as pCu = - log{Cu2+ activity as molarity}), and as external (surface-bound) Cu and internal Cu in the algal cells. With increasing pH, EC50dissolved decreased from 30 to 1.1 microg of Cu L(-1) for Chlorella sp. and from 46 to 18 microg of Cu L(-1) for P. subcapitata. The pH effect on copper toxicity was even more obvious when expressed as Cu2+ activity. The EC50pCu increased on average 1.4 pCu unit per pH unit for Chlorella sp. and 1.1 pCu unit per pH unit for P. subcapitata, thus indicating a marked increase of Cu2+ toxicity at higher pH (more than 1 order of magnitude per pH unit). In contrast, it was found that EC50 values expressed as surface bound or external copper (EC50external) and as internal copper (EC50internal) did not vary substantially when pH was increased. External Cu was operationally defined as the Cu fraction removable from the algal cell by short-term contact with ethylenediaminetetraacetic acid; internal copper was defined as the nonremovable fraction. For Chlorella sp. the EC50external varied between 5 and 10 fg of Cu/ cell (factor of 2 difference) and the EC50internal between 25 and 40 fg of Cu/cell (factor of 1.6 difference). For P. subcapitata the EC50external varied between 10 and 28 fg of Cu/cell (factor of 2.8 difference) and the EC50internal between 42 and 71 fg of Cu/cell (factor of 1.7 difference). Because the observed variation in EC50external and EC50internal is much less than the variation in EC50Cu2+, it is concluded that both external and internal copper are better predictors of copper toxicity than Cu2+ when pH is varied. From the perspective of toxicity modeling, this observation is the first step toward considering the use of the cell surface as the algal biotic ligand for Cu in a similar way as fish gills fulfill this role in the biotic ligand model for predicting metal toxicity to fish species.

Chlorophyta↗
PubMed2004

Using multiple metal-gill binding models and the toxic unit concept to help reconcile multiple-metal toxicity results.

Metal-gill binding models and biotic ligand models (BLMs) in general are designed to predict metal toxicity to aquatic organisms. These models calculate the amount of a metal-binding to a sensitive biological membrane, such as a fish gill, which equates with metal toxicity. Cation competition at the metal-binding site and anionic complexation in the water decrease metal-binding to the membrane, decreasing metal toxicity. These models have, to date, been developed for individual metals. To assess how these models handle multiple-metal interactions, metal-gill binding models for two to six metals were created and their behavior tested against the toxic unit (TU) concept assuming strict additivity. The multiple-metal models yield greater than strict additivity at low aqueous metal concentrations (Sigma < 1 TU), strict additivity at intermediate metal concentrations (Sigma = 1 TU), and less than strict additivity at high metal concentrations (Sigma > 1 TU), independent of the combination of metals. Deviations from strict additivity are due to the non-linear nature of the models, where greater than linear filling of binding sites occurs at low metal concentrations, and where strong competition for binding sites occurs at high metal concentrations, with a point of strict additivity between, where the metals sum to one toxic unit. Simulations with natural organic matter (NOM) show similar trends but are complex. Mathematical modeling of multiple-metal interactions may help in the interpretation of toxicity results from mixed-metal exposures to aquatic organisms.

Animals↗
PubMedDate not supplied

GB toxicity reassessed using newer techniques for estimation of human toxicity from animal inhalation toxicity data: new method for estimating acute human toxicity (GB).

Estimated human inhalation toxicity values for Sarin (GB) were calculated using a new two independent (concentration, exposure time), one dependent (toxic response), non-linear dose response (toxicity) model combined with re-evaluated allometric equations relating to animal and human respiration. Historical animal studies of GB toxicity containing both exposure and fractional animal response data were used to test the new process. The final data set contained 6621 animals, 762 groups, 37 studies and 7 species. The toxicity of GB for each species was empirically related to exposure concentration (C; mg m(-3)) and exposure time (T; min) through the surface function Y = b0 + b1 Log10C + b2 Log10T or Y = b0 + b2 Log10C(n)T where Y is the Normit, b0, b1 and b2 are constants and n is the 'toxic load exponent' (Normit is PROBIT - 5). Between exposure times of 0.17 and 30 min, the average value for n in seven species was 1.35 +/- 0.15. The near parallel toxic load equations for each species and the linear relationship between minute volume/body weight ratio and the inhalation toxicity (LCt50) for GB were used to create a pseudo-human data set and then an exposure time/toxicity surface for the human. The calculated n for the human was 1.40. The pseudo-human data had much more variability at low exposure times. Raising the lower exposure limit to 1 min, did not change the LCt50 but did result in lower variability. Raising the lower value to 2 min was counterproductive. Based on the toxic load model for 1-30 min exposures, the human GB toxicities (LCt01, LCt05, LCt50 and LCt95) for 70 kg humans breathing 15 l min(-1) were estimated to be 11, 16, 36 and 83; 18, 25, 57 and 132 and 24, 34, 79 and 182 mg x min m(-3) for 2, 10 and 30 min exposures, respectively. These values are recommended for general use for the total human population. The empirical relationships employed in the calculations may not be valid for exposure times >30 min.

Algorithms↗
PubMed1999

Ecotoxicological characterization of energetic substances using a soil extraction procedure.

The acetonitrile-sonication extraction method (US EPA SW-846 Method 8330) and aquatic-based toxicity tests were used on laboratory and field samples, to characterize the ecotoxicity of soils contaminated with energetic substances. Spiked soil studies indicated that 2,4, 6-trinitrotoluene (TNT)-dependent soil toxicity could be measured in organic extracts and aqueous leachates using the 15-min Microtox (Vibrio fischeri, IC50=0.27 to 0.94 mg TNT/liter incubation medium) and 96-h Selenastrum capricornutum growth inhibition (IC50=0.62 to 1. 14 mg/liter) toxicity tests. Analyses of leachates of composite soil samples [containing TNT and some TNT metabolites, 1,3,5-trinitro-1,3, 5-triazacyclohexane (RDX), and 1,3,5,7-tetranitro-1,3,5, 7-tetrazacyclooctane (HMX)] from an explosives manufacturing facility, indicated toxicities similar to those found in the TNT-spiked soil studies and pure TNT in solution, and suggested that TNT was the major toxicant. Using TNT as a model toxicant in soils having different moisture contents (20% vs dry) and textures (sandy vs clayey-sandy) but similar organic matter content (3-4%), multi-factorial analyses of Microtox test data revealed that these soil factors significantly influenced the TNT extractability from soil and subsequent toxicity measurements. Taken together, data indicate that the modified Method 8330 may be used in conjunction with ecotoxicity tests to reflect the toxic potential of soils contaminated with energetic substances.

Acetonitriles↗
PubMed1996

Protective effects of tirilazad mesylate in a cellular model of peroxynitrite toxicity.

Following CNS trauma or ischemia, peroxynitrite may be a toxic intermediate which forms in vivo when nitric oxide condenses with superoxide. Alone, peroxynitrite appears to directly react with aromatic and sulfhydryl nucleophiles. However, at physiological pH, peroxynitrite is protonated and, in that form, will rapidly (within seconds) decompose to species with hydroxyl radical and nitrogen dioxide characteristics. These reactive species are shown to initiate lipid peroxidation, hydroxylate aromatic residues, and nitrate aromatic residues. This reactivity may contribute to differential toxicity in vivo and in vitro. Tirilazad mesylate (TZ) is a lipid-soluble antioxidant shown to inhibit iron-dependent lipid peroxidation. It is an effective therapy in a variety of CNS injury and ischemia models and is currently undergoing human clinical evaluation in stroke, head injury, and spinal injury. This study was designed to investigate the cytoprotective properties of TZ in a cerebellar granule cell model of peroxynitrite toxicity. Cytoprotective efficacy of TZ was based on viability measurements, blockade of lipid hydroperoxide generation, and blockade of nitrotyrosine formation. Cell viability was determined by [3H]-aminoisobutyric acid (3H-AIB) uptake, and lipid hydroperoxide and nitrotyrosine content were determined by HPLC assays. Tirilazad mesylate was found to have similar cytoprotective effects (approximately 50% protection at 100 microM) when applied before or after exposure of cells to peroxynitrite. In contrast, post-treatment with superoxide dismutase (50 units/ml) or allopurinol (100 microM) failed to produce any cytoprotection. Furthermore, we discovered that TZ inhibited the peroxynitrite-induced increase of phosphatidylethanolamine hydroperoxide (PEOOH), but did not affect the peroxynitrite-induced formation of nitrotyrosine formation. This suggests that the ability of TZ to afford cytoprotection in this peroxynitrite toxicity model is due to the inhibition of membrane-localized lipid peroxidation, and not to the inhibition of nitration of tyrosine residues.

Aminoisobutyric Acids↗