Neuroendocrine and immunotoxicity of polyaromatic hydrocarbon, chrysene in crustacean post larvae.

Polyaromatic hydrocarbons are a group of chemical pollutants which cause a significant threat to the living organisms in estuaries and marine ecosystems. We report the effect of chrysene, a major PAH pollutant found in Cochin Estuary along the southwest coast of India, on the neuroendocrine and immune gene expression of the post larvae (PL-25) of Penaeus monodon. The PL- 25 of P. monodon were administered with feed coated with increasing concentrations of chrysene (1, 2 and 3 µg/g) for 10 days and the gene expression was studied on 7th, 11th and 15th day. The PL exposed to chrysene showed moulting stress and changes in the levels of moult-inhibiting hormone I (MIH I) indicated by irregular moulting in the experimental tanks. At the molecular level, the higher concentration of chrysene induced two-fold upregulation of neuroendocrine (MIH I) and downregulation of immune (ProPO and crustin) gene on the 7th day of exposure. The expression of MIH I gene reduced on withdrawing the experimental feed (on 11th day), while continued downregulation of ProPO and crustin were observed on the 11th day. The results of the present study indicate that the microgram levels of PAH can impinge the neuroendocrine and immune system of the P. monodon, which may induce morbidity and mortality to the larvae in polluted coastal ecosystems. Therefore, more attention may be given to avoid PAH pollution in the estuaries to maintain a healthy ecosystem and to protect the animals from extinction.

The safety, tolerability, and pharmacokinetic profile of GSK2838232, a novel 2nd generation HIV maturation inhibitor, as assessed in healthy subjects.

This work aimed to assess the safety, tolerability, pharmacokinetics (PK), and relative bioavailability of GSK2838232, an investigational HIV maturation inhibitor. GSK2838232 was administered over four dose-escalation studies in healthy subjects which assessed single oral doses (5-250 mg) and repeat doses (up to 200 mg once or twice daily) ±100 mg ritonavir (RTV) once daily. GSK2838232 administration (up to 250 mg) to 124 subjects across four studies resulted in few mild adverse events (AEs) with similar frequencies to placebo. There were no clearly identified drug-related AEs. GSK2838232 tested fasted was quickly absorbed with a tmax of 2-3 hours. With food, the absorption was delayed and more variable, with ~60% increase in AUC and Cmax. Overall, following single doses GSK2838232 AUC and Cmax generally exhibited proportional PK from 50 to 100 mg dose without RTV and from 50 to 250 mg with RTV and following repeated doses of 20-200 mg with RTV. In relative bioavailability studies, a micronized formulation was found to be suitable for development. At steady state, RTV increased GSK2838232 AUC and Cmax by 10- and 3-fold, respectively. Half-life was prolonged from ~17 hours nonboosted to ~34 hours with RTV. This boosting effect was also seen in repeat-dose GSK2838232 studies, which achieved the targeted plasma exposure with GSK2838232 as a once-daily regimen of up to 200 mg with RTV. The results of these studies demonstrated a favorable safety and PK profile for GSK2838232 and support its investigation for the treatment of HIV infection.

Comparative oesophageal cancer risk assessment of hot beverage consumption (coffee, mate and tea): the margin of exposure of PAH vs very hot temperatures.

BACKGROUND: Consumption of very hot (> 65 °C) beverages is probably associated with increased risk of oesophageal cancer. First associations were reported for yerba mate and it was initially believed that high content of polycyclic aromatic hydrocarbons (PAH) might explain the risk. Later research on other beverage groups such as tea and coffee, which are also consumed very hot, found associations with increased risk of oesophageal cancer as well. The risk may therefore not be inherent in any compound contained in mate, but due to temperature. The aim of this study was to quantitatively assess the risk of PAH in comparison with the risk of the temperature effect using the margin of exposure (MOE) methodology. METHODS: The human dietary benzo[a]pyrene (BaP) and PAH4 (sum of benzo[a]pyrene, benzo[a]anthracene, chrysene, and benzo[b]fluoranthene) exposure through consumption of coffee, mate, and tea was estimated. The oesophageal cancer risk assessment for both PAH and temperature was conducted using the MOE approach. RESULTS: Considering differences in the transfer of the PAH from the leaves of mate and tea or from the ground coffee to the infusion, and considering the different preparation methods, exposures may vary considerably. The average individual exposure in µg/kg bw/day arising from consumption of 1 cup (0.2 L) of infusion was highest for mate (2.85E-04 BaP and 7.22E-04 PAH4). The average per capita exposure in µg/kg bw/day was as follows: coffee (4.21E-04 BaP, 4.15E-03 PAH4), mate (4.26E-03 BaP, 2.45E-02 PAH4), and tea (8.03E-04 BaP, 4.98E-03 PAH4). For all individual and population-based exposure scenarios, the average MOE for BaP and PAH4 was > 100,000 independent of beverage type. MOE values in this magnitude are considered as a very low risk. On the contrary, the MOE for the temperature effect was estimated as < 1 for very hot drinking temperatures, corroborating epidemiological observations about a probable oesophageal cancer risk caused by this behaviour. CONCLUSIONS: The temperature effect but not PAH exposure may pose an oesophageal cancer risk. Consumer education on risks associated with consumption of 'very hot' beverages and policy measures to threshold serving temperatures should be discussed.

Ozonation of chrysene: evaluation of byproduct mixtures and identification of toxic constituent.

The effects of chrysene and the ozonated byproducts on in vitro gap junctional intercellular communication (GJIC) were evaluated using the scrape loading/dye transfer (SL/DT) technique. A 1 mM solution of chrysene was ozonated at dosages of 1.75, 3, 4.25, and 5 mol O3/mol chrysene (Chr). The early ozonation mixture, 1.75 mol O3/mol Chr, exhibited greater inhibition to GJIC than chrysene and irreversible damage to cells leading to cell death. To determine the compounds potentially responsible for the increase in toxicity, the byproducts formed upon treatment with 1.44 mol O3/mol Chr were separated into 14 fractions using RP-HPLC. The major compounds identified in the fractions were 2-(2'-formyl) phenyl-1-naphthaldehyde, 2-(2'formyl) phenyl-1-naphthoic acid, and 2-2-carboxyphenyl-1-naphthoic acid. 2-(2'-Formyl) phenyl-1-naphthaldehyde was determined to be the compound causing GJIC inhibition in sample fractions and byproduct mixtures.

Targeting of lung cancer mutational hotspots by polycyclic aromatic hydrocarbons.

BACKGROUND: Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous in combustion products of organic matter, including cigarette smoke. Metabolically activated diol epoxides of these compounds, including benzo[a]pyrene diol epoxide (B[a]PDE), have been suggested as causative agents in the development of lung cancer. We previously mapped the distribution of B[a]PDE adducts within the p53 tumor suppressor gene (also known as TP53), which is mutated in 60% of human lung cancers, and found that B[a]PDE adducts preferentially form at lung cancer mutational hotspots (codons 154, 157, 158, 245, 248, and 273). Other PAHs may be important in lung cancer as well. METHODS: Here we have mapped the distribution of adducts induced by diol epoxides of additional PAHs: chrysene (CDE), 5-methylchrysene (5-MCDE), 6-methylchrysene (6-MCDE), benzo[c]phenanthrene (B[c]PDE), and benzo[g]chrysene (B[g]CDE) within exons 5, 7, and 8 of the p53 gene in human bronchial epithelial cells. RESULTS: CDE exposure produced only low levels of adducts. Exposure of cells to the other activated PAHs resulted in DNA damage patterns similar to those previously observed with B[a]PDE but with some distinct differences. 5-MCDE, 6-MCDE, B[g]CDE, and B[c]PDE efficiently induced adducts at guanines within codons 154, 156, 157, 158, and 159 of exon 5, codons 237, 245 and 248 of exon 7, and codon 273 of exon 8, but the relative levels of adducts at each site varied for each compound. B[g]CDE, B[c]PDE, and 5-MCDE induced damage at codon 158 more selectively than 6-MCDE or B[a]PDE. The sites most strongly involved in PAH adduct formation were also the sites of highest mutation frequency (codons 157, 158, 245, 248, and 273). CONCLUSION: The data suggest that PAHs contribute to the mutational spectrum in human lung cancer.

A phase I and pharmacological study of protracted infusions of crisnatol mesylate in patients with solid malignancies.

This Phase I and pharmacological study was performed to assess the feasibility of administering the polycyclic aromatic hydrocarbon crisnatol in increasingly prolonged continuous i.v. infusions to patients with advanced solid malignancies. The study also sought to characterize the-principal toxicities of crisnatol on this schedule, to recommend doses for subsequent disease-directed studies, and to characterize possible associations between pharmacological parameters and toxicity. Sixteen patients were treated with 40 courses of crisnatol administered as a continuous i.v. infusion. The initial dose-schedule was 750 mg/m2/day for 6 days, and the duration of the infusion was to be progressively increased by 3-day increments to 9, 12, 15, 18, and 21. Courses were to be repeated every 4 weeks. Moderate to severe central nervous system (CNS) toxicity precluded the administration of crisnatol 750 mg/m2/day for longer than 6 days, and, therefore, the dose of crisnatol was reduced to 600 mg/m2/day. At this dose, three of five patients receiving a 12-day infusion experienced dose-limiting toxicity, which consisted of pulmonary thromboembolism (two patients) and grade 4 thrombocytopenia (one patient). None of the six patients completing a 9-day infusion at 600 mg/m2/day developed dose-limiting toxicity during the first or second course of crisnatol. At this dose level, the plasma concentrations at steady state (Css) averaged 1607.8+/-261.1 ng/ml, which exceeds minimal inhibitory concentrations for most tumors in vitro (1000 ng/ml). In fact, the administration of crisnatol at a dose of 600 mg/m2/day for 9 days resulted in the longest duration that biologically relevant plasma crisnatol concentrations have been sustained. Plasma Css values were significantly higher in patients who experienced severe CNS toxicity compared with those who did not (2465.3+/-1213.5 versus 1342+/-447.3 ng/ml; P = 0.04). There were no relationships evident between the clearance of crisnatol and indices reflecting renal and hepatic functions. One patient with a glioblastoma multiforme experienced a partial response lasting 14 months. The relative lack of intolerable CNS toxicity at the recommended dose for Phase II studies of crisnatol, 600 mg/m2/day for 9 days, as well as the magnitude of the Css values achieved and the antitumor activity observed at this dose, are encouraging. However, the mechanisms for the apparently increased thrombogenicity observed in this trial are unclear and require further elucidation.

Lack of p53-mediated G1 arrest in response to an environmental carcinogen.

The environmental carcinogen, 5-methylchrysene, is a component of cigarette smoke. Its reactive metabolite, anti-5-methylchrysene-1, 2-dihydrodiol-3,4-epoxide (5-MeCDE) mainly reacts with the N(2)-position of guanine residues in the DNA molecule. In this study, we demonstrate that the tumor suppressor protein p53 is stabilized in response to DNA damage by 5-MeCDE but fails to induce the cells' protective mechanism of G1 arrest in the human breast carcinoma cell line, MCF-7. In contrast, actinomycin D treatment of these cells did lead to G1 arrest. Western analyses revealed that, though both actinomycin D and 5-MeCDE treatment stabilized p53, only trace levels of p21(waf1/cip1) were seen in the latter case. This lack of p21(waf1/cip1) expression in 5-MeCDE-treated cells is attributed to a stealth characteristic of this environmental carcinogen that allows it to damage DNA and still escape the p53-mediated cellular defense mechanism of G1 arrest.

Long-term response to crisnatol mesylate in patients with glioma.

A total of 26 patients (6 with anaplastic astrocytoma; 20 with glioblastoma) were treated with crisnatol mesylate. All patients had residual or progressive disease following surgery and standard radiotherapy; nine patients had prior chemotherapy. Crisnatol was administered as a 72-hour infusion every 21 days at a starting dose of 2250 mg/m2. Two patients who had not received prior chemotherapy achieved a complete response and remain in continuous complete remission over seven and six years, respectively, post-diagnosis. Two other patients remained stable on crisnatol for 10 months before disease progression. One patient with mixed oligodendroglioma/glioblastoma progressed after 12 months on crisnatol. He survives at 7 years post-diagnosis, with Karnofsky Performance Status of 60 following other therapies. One patient with anaplastic astrocytoma stopped treatment by request after 10 months and remains stable 64 months post diagnosis. Seventeen evaluable patients, including nine patients with prior chemotherapy, progressed after 2-9 courses of therapy. Median survival is 9.25 months, with a one year survival rate of 30% and 2 years survival rate of 17%. Neurotoxicity was acute and dose-limiting. Side effects were tolerable and limited to duration of infusion. Two complete, long-lasting responses to crisnatol mesylate in patients with progressive malignant glioma are encouraging results and warrant further investigation.

Crisnatol mesylate: phase I dose escalation by extending infusion duration.

Crisnatol mesylate is a rationally designed cytotoxic arylmethylamino-propanediol with broad spectrum cytotoxic activity. A phase I study with an unconventional escalation scheme was developed using a constant drug infusion rate (mg/m2/hr) and prolonging the infusion duration from 6 to 96 hours. Sixty-five patients received crisnatol at doses from 18 mg/m2 in 6 hrs to 3400 mg/m2 in 72 hours. The dose-limiting toxicity in two of five patients at 2700 mg/m2 and two of three patients at 3400 mg/m2 was neurologic and consisted of a syndrome of confusion, agitation, and disorientation. Phlebitis mandated the use of a central line. The mean terminal phase half-life (T1/2 beta) was 3.3 hours with a total body clearance (CL) of 22.8 L/hr/m2 and a volume of distribution (Vdss) of 53 L/m2. The median steady-state peak plasma concentration (Css) at 2700 mg/m2/72 hours was 2.7 micrograms/ml and at 3400 mg/m2/72 hours was 3.8 micrograms/ml. No responses were seen. The maximum tolerated dose (MTD) on this schedule is 2700 mg/m2/72 hours in patients with no liver disease and good performance status.

Phase I evaluation of crisnatol (BWA770U mesylate) on a monthly extended infusion schedule.

Crisnatol is an arylmethylaminopropanediol derivative that has shown promise as an antitumor agent in preclinical testing. In a phase I trial using a monthly six-hour infusion schedule the recommended dose for future phase II trials was found to be 388 mg/m2. Neurologic toxicity was dose-limiting in that trial and correlated with the attainment of a threshold plasma concentration of greater than 4.5 micrograms/ml. In this study we treated 15 patients with escalating doses of crisnatol from 450 mg/m2 to 900 mg/m2 administered at a rate of 50 mg/m2/hr over 9, 12, 15, and 18 hours. Toxicity was mild to moderate at all dose levels. However, serious central nervous system effects were noted in one patient at 900 mg/m2 over 18 hours whose plasma level was 6.5 micrograms/ml. This study has demonstrated higher total doses of crisnatol can be given if the drug is administered as a prolonged infusion in an attempt to avoid high plasma levels of the agent.

Phase I and clinical pharmacology trial of crisnatol (BWA770U mesylate) using a monthly single-dose schedule.

Crisnatol is a novel lipophilic arylmethylaminopropanediol with significant antineoplastic activity in a variety of murine and human tumor models which functions as a DNA intercalator. In this Phase I trial, a 6-h infusion of the drug was administered i.v. in 700 to 1500 ml of 5% dextrose in water every 28 days. Eighty-five courses at doses of 7.5 to 516 mg/m2 were administered to 43 patients with refractory solid tumors. Reversible neurological toxicity was dose limiting at 516 mg/m2 and was manifested as somnolence, dizziness, blurred vision, unsteady gait, and alpha-slowing on electroencephalogram at the end of infusion. All neurological signs and symptoms were reversible. No hematological toxicity was observed. Other toxicities included phlebitis, mild to moderate nausea and vomiting, reversible sinus node arrest in one patient, and hypertension. Crisnatol plasma concentrations were determined by high-pressure liquid chromatography. After infusion, plasma concentrations declined biexponentially with a terminal t1/2 of 2.9 h. Using a two-compartment model, the mean apparent volume of distribution at steady state and total-body clearance were 58.8 liters/m2 and 18.3 liters/h/m2, respectively, indicative of extensive tissue distribution and rapid hepatic clearance. Peak plasma levels occurred at the end of infusion and correlated with the onset of neurological toxicity. The recommended Phase II dose for this schedule is 388 mg/m2.