The metabolism of the dual endothelin receptor antagonist macitentan in rat and dog.

1. The metabolism of the endothelin receptor antagonist macitentan has been characterized in bile duct-cannulated rats and dogs. 2. In both species, macitentan was metabolized along five primary pathways, i.e. conjugation with glucose (M9), oxidative depropylation (M6), aliphatic hydroxylation (M7), oxidative cleavage of the ethylene glycol linker (M4) and hydrolysis of the sulfamide moiety (M3). Most of the primary metabolites underwent subsequent biotransformation including conjugation with glucuronic acid or glucose, hydrolysis of the sulfamide group or secondary oxidation of the ethylene glycol moiety. 3. Though there were species differences in their relative importance, all metabolic pathways were present in rat and dog. The depropylated M6 was the only metabolite present in plasma of both species. 4. Metabolism was a prerequisite for macitentan excretion as relevant amounts of parent drug were neither detected in bile nor urine. Biliary excretion was the major elimination pathway, while renal elimination was of little importance.

Mass balance, pharmacokinetics and metabolism of the selective S1P1 receptor modulator ponesimod in humans.

1. Ponesimod [(R)-5-[3-chloro-4-(-2,3-dihydroxy-propoxy)-benzylidene]-2-propylimino-3-o-tolyl-thiazolidin-4-one] is an orally administered, selective S1P1 receptor modulator that blocks the egress of lymphocytes from lymphoid organs and reduces the availability of circulating effector T/B-cells. 2. The mass balance, pharmacokinetics and metabolism of 40 mg (14)C-ponesimod were investigated in six healthy male subjects. The total radioactivity in whole blood, plasma, urine, faeces and expired CO2 was determined by liquid scintillation counting. Metabolite profiling was performed by high-performance liquid chromatography and detection by mass spectrometry. 3. The majority of the radioactivity (% of administered dose) was recovered in faeces (57.3-79.6%), followed by urine (10.3-18.4%) and a small proportion in CO2 from expired air (0.6-1.9%). The average cumulative recovery (mass balance) of (14)C-associated radioactivity in faeces and urine was 77.9% of the administered dose. Unchanged ponesimod made up 25.9% of total radioactivity in faeces; none was detected in urine. Ponesimod was extensively metabolised and two pharmacologically inactive metabolites, M12 (ACT-204426) and M13 (ACT-338375), were detected in the circulation. M12 corresponded to 8.1% and M13 to 25.7% of the total drug-related radioactive exposure (AUC0-∞) in plasma. M12 was highly abundant in faeces (22.3% of total radioactivity) and to a smaller extent in urine (2.5% of total radioactivity).

First-in-humans study of the safety, tolerability, and pharmacokinetics of ACT-451840, a new chemical entity with antimalarial activity.

Emerging resistance to antimalarial agents raises the need for new drugs. ACT-451840 is a new compound with potent activity against sensitive and resistant Plasmodium falciparum strains. This was a first-in-humans single-ascending-dose study to investigate the safety, tolerability, and pharmacokinetics of ACT-451840 across doses of 10, 50, 200, and 500 mg in healthy male subjects. In the 200- and 500-mg dose groups, the effect of food was investigated, and antimalarial activity was assessed using an ex vivo bioassay with P. falciparum. No (serious) adverse events leading to discontinuation were reported. At the highest dose level, the peak drug concentration (Cmax) and the area under the plasma concentration-time curve from zero to infinity of ACT-451840 under fasted conditions reached 11.9 ng/ml and 100.6 ng·h/ml, respectively, and these were approximately 13-fold higher under fed conditions. Food did not affect the half-life (approximately 34 h) of the drug, while the Cmax was attained 2.0 and 3.5 h postdose under fasted and fed conditions, respectively. The plasma concentrations estimated by the bioassay were approximately 4-fold higher than those measured by liquid chromatography-tandem mass spectrometry (LC-MS/MS). Several potentially active metabolites were also identified. ACT-451840 was well tolerated across all doses. Exposure to ACT-451840 significantly increased with food. The bioassay indicated the presence of circulating active metabolites. (This study has been registered at ClinicalTrials.gov under registration no. NCT02186002.).

Elucidation of the metabolic pathways and the resulting multiple metabolites of almorexant, a dual orexin receptor antagonist, in humans.

Almorexant [(2R)-2-{(1S)-6, 7-dimethoxy-1-[2-(4-trifluoromethyl-phenyl)-ethyl]-3,4-dihydro-1H-isoquinolin-2-yl}-N-methyl-2-phenyl-acetamide], a tetrahydroisoquinoline derivative, is a dual orexin receptor antagonist with sleep-promoting properties in both animals and humans. This study investigated the disposition, metabolism, and elimination of almorexant in humans. After oral administration of a 200-mg dose of ¹4C-almorexant, almorexant was rapidly absorbed (Tmax = 0.8 hour), and the apparent terminal half-life (t(1/2)) was 17.8 hours. The radioactive dose was almost completely recovered with 78.0% of the administered radioactive dose found in feces and 13.5% in urine. Unchanged almorexant was not found in urine and represented 10% of the administered dose in feces. In total, 47 metabolites were identified of which 21 were shown to be present in plasma. There are four primary metabolites, the isomeric phenols M3 and M8, formed by demethylation, the aromatic isoquinolinium ion M5, formed by dehydrogenation, and M6, formed by oxidative dealkylation with loss of the phenylglycine moiety. Most of the subsequent products are formed by permutations of these primary metabolic reactions followed by conjugation of the intermediate phenols with glucuronic or sulfonic acid. The percentage of dose excreted in urine or feces for any of the metabolites did not exceed 10% of the administered radioactive dose, nor did any of the metabolites represent more than 10% of the total drug-related exposure. In conclusion, after rapid absorption, almorexant is extensively metabolized, and excretion of metabolites in feces is the predominant route of elimination in humans.

Biodegradation of linear alkylbenzene sulfonates in sulfate-leached soil mesocosms.

Aromatic sulfonates (R-SO(3)(-)) can be used as sulfur sources by sulfate-starved bacteria in laboratory cultures and the corresponding phenols are excreted from the cells. The present study was conducted to demonstrate whether such desulfonation reactions also occur in sulfate-leached agricultural soil, where desulfonation of organic sulfur compounds may have agronomic importance as a S source for plants. Xenobiotic linear alkylbenzene sulfonates (LAS) were added to nominal concentrations of 0, 10 and 100 mgkg(-1) dry weight in a sandy soil that was depleted in sulfate by leaching the soil with water (sulfate depletion, approximately 75%). The soil was incubated at 20 degrees C in duplicate 3-dm(3) mesocosms for 8 weeks. Primary degradation of LAS was rapid with half-lives of 1-4 days. Sulfophenylcarboxylates were identified and quantified as intermediates, whereas linear alkylphenols (the expected primary desulfonation products) were not detected by high-pressure liquid chromatography coupled with both fluorescence and electrospray ionization-mass spectrometry. Thus, LAS was used by the bacteria as a source of energy and carbon, rather than as a source of sulfur. Measurements of soil pH, fluorescein diacetate (FDA) hydrolysis and arylsulfatase activity showed that stable microbial conditions prevailed in the soil mesocosms. FDA hydrolysis (a measure of total microbial activity) was transiently inhibited at the highest LAS concentrations. Arylsulfatase activity (i.e., hydrolysis of aromatic sulfate esters) was not significantly affected by the soil incubation, although arylsulfatases may be upregulated in sulfate-starved bacteria. However, an increased production of arylsulfatase may be difficult to detect due to the background of extracellular arylsulfatases stabilised in the soil. Therefore, the present data does not exclude a regulatory response to sulfate depletion by the soil microorganisms. However, the importance of desulfonation reactions in natural environments still needs to be demonstrated.